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2011-3037-Ordinance No. 2011-008 Recorded 10/6/2011
REVIEWED . DESCHUTES COUNTY OFFICIAL RECORDS CJ 2011'3031 LEGA COUNSEL NANCY BLANKENSHIP, COUNTY CLERK COMMISSIONERS' JOURNAL 1111111 11 10/06/201110:17:32 AM II I II IIIIII I it I III III T 11-30 7 BEFORE THE BOARD OF COUNTY COMMISSIONERS OF DESCHUTES COUNTY, OREGON An Ordinance Amending Title 23, of the Deschutes County Comprehensive Plan, Adopting a South * ORDINANCE NO. 2011-008 County Local Wetland Inventory, and Declaring an Emergency WHEREAS, in 2009 the Deschutes County Community Development Department ("CDD") initiated the process for conducting a South County Local Wetland Inventory ("South County LWI"), and WHEREAS, the South County LWI process was completed on July 19, 2011; and WHEREAS, amendments to the Deschutes County Comprehensive Plan are necessary to comply with OAR 141-086-0185(1)(2) and OAR 660-023-0100(5); and WHEREAS, the Deschutes County Planning Commission held a work session on August 25, 2011, to review the South County LWI consistent with Deschutes County Code 22.12.010; and WHEREAS, the Board of County Commissioners ("Board") held a duly noticed public hearing on September 26, 2011; and WHEREAS, the Board finds it in the public interest to adopt the South County LWI into the Comprehensive Plan; now, therefore, THE BOARD OF COUNTY COMMISSIONERS OF DESCHUTES COUNTY, OREGON, ORDAINS as follows: Section 1. AMENDMENT. DCC 23.104.030, Fish and Wildlife, is amended to read as described in Exhibit "A," attached hereto and by this reference incorporated herein, with new language underlined and language to be deleted in stfiletlifeugh. Section 2. AMENDMENT. 23.112, Water Resources, is amended to read as described in Exhibit "B," attached hereto and by this reference incorporated herein, with new language underlined and language to be deleted in strikeflifeugk. Section 3. FINDINGS. The Board adopts as its findings Exhibit "C," attached and incorporated by reference herein. PAGE 1 OF 2 - ORDINANCE NO. 2011-008 Section 4. EMERGENCY. This Ordinance being necessary for the immediate preservation of the public peace, health and safety, an emergency is declared to exist, and this Ordinance takes effect on its passage. Xl' Dated this of , 2011 BOARD OF COUNTY COMMISSIONERS OF DESfJJUTES COUNTY, OREGON TAMMY BANEY, Chair ANTHONY DEBONE, Vice Chair ATTEST: Recording Secretary ALAN UNGER, Commissioner Date of 1St Reading: day of '2011. Date of 2"d Reading: (~p day of , 2011. Record of Adoption Vote: Commissioner Yes No Abstained Excused Tammy Baney Anthony DeBone Alan Unger Effective date: Z4-p- day of , 2011. PAGE 2 OF 2 - ORDINANCE NO. 2011-008 Denotes portions of the code not amended by Ordinance 2011-008. Chapter 23.104. FISH AND WILDLIFE 23.104.030. Policies. 23.104.030. Policies. 1. In light of the need to protect deer winter range and to be consistent with plan policies restricting rural sprawl, the Metolius, North Paulina, Tumalo and Grizzly deer winter ranges shall be protected by special zones. The winter ranges shall be as designated on the Big Game Habitat - Wildlife Area Combining Zone Map contained in this plan's resource element. Within the winter ranges the minimum lot size shall be 40 acres, except that in the Rural Residential Zone and the Multiple Use Agricultural Zone planned or cluster developments are required for new land divisions. In planned and cluster developments man's activities must be limited to 20 percent of the development's lands with 80 percent left as open space. The density of planned and cluster developments shall be determined by the underlying zone. 2. The County shall enforce an animal control ordinance which prohibits dogs to be at large or not under the complete control of a capable person. 3. In the Bend/La Pine deer migration corridor identified in the comprehensive plan resource element, new land divisions, where the underlying zone is Rural Residential - 10, shall be cluster developments. 4. Because public access to fish and wildlife areas is so important to the economic and livability aspects of Deschutes County, walking easements and periodic boat access points shall be provided in areas where public river access is limited, as determined appropriate by the County and State Department of Fish and Wildlife. 5. Consistent with Policy 4 and in order to protect the sensitive riparian areas, as well as to protect people and property from flood damage, the zoning ordinance shall prohibit development (except floating docks) within 100 feet of the mean high water mark of a perennial or intermittent stream or lake. Exceptions may be permitted on lots created prior to November 1, 1979 where adherence to the 100-foot setback would cause a hardship. 6. In addition to State and Federal laws, County ordinances shall require all identified nesting sites for eagles, ospreys, prairie falcons or other species listed on the Oregon State or Federal threatened or endangered species list shall be protected. 7. Sensitive bird habitat sites (bald eagle, golden eagle, osprey, great grey owl, prairie falcon nests, great blue heron rookeries, and sage grouse leks) and mammal habitat sites (Townsend's big-eared bat hibernating and nesting caves) identified in the Resource Element of this plan shall be protected by a Sensitive Bird and Mammal Overlay Zone. A protection program acceptable to the Oregon Department of Fish and Wildlife for the nests or sites shall be submitted by the applicant for a development or land use permit and used implemented during and after construction of the development. 8. The antelope range and antelope winter range identified on the Big Game Habitat-Wildlife Area Combining Zone Map included in the Resource Element of this plan shall be protected by a wildlife area combining zone. The minimum lot size for new parcels shall be 320 acres. The Rural Service Centers of Brothers, Hampton and Millican shall be exempt from the provisions of the Wildlife Area Combining Zone. PAGE 1 OF 2 - EXHIBIT "A" TO ORDINANCE 2011-008 9. The areas containing land identified as significant elk habitat on the Big Game Habitat Map - Wildlife Area Combining Zone Map included in the Resource Element of this plan shall be protected by a wildlife area combining zone. The minimum lot size for new parcels shall be 160 acres in the combining zone. 10. The County shall notify the Oregon Department of Fish and Wildlife of all land use applications for lands located in the WA Combining Zone or the Sensitive Bird and Mammal Overlay Zone. 11. The County shall work with ODFW and the Deschutes Basin Resource Committee to review existing protection of riparian and wetland area vegetation and recommend comprehensive plan and ordinance amendments, if necessary, by December 31, 1993. 12. When site specific information is available to the County on the location, quality and quantity of threatened and endangered fish and wildlife species listed by State or Federal wildlife agencies and the Oregon Department of Fish and Wildlife develops protection criteria for the species, the County shall proceed with a Goal 5 ESEE analysis in compliance with OAR 660 Div. 16. 13. The County shall review the La Pine and Bull Flat elk habitat areas and the Metolius deer migration corridor designated as "1 B" Goal 5 resources during the next periodic review or as additional information on the location, quality and quantity of the habitat areas becomes available. 14. The County shall maintain an inventory of County-owned property in the Bend/La Pine deer migration corridor. Prior to sale or exchange of County owned property in the corridor, the County shall consult the Oregon Department of Fish and Wildlife to determine the value of the land for deer migration and make reasonable efforts to consolidate properties to maintain habitat characteristics important to preserving the migration corridor. 15. The County shall work with ODFW to identify specific areas where the County and ODFW shall encourage public retention and acquisition of land or seek conservation easements for the protection of the deer migration corridor. 16. The County shall retain and encourage public ownership of significant fish and wildlife habitat and riparian areas. 17. County-owned land shall be managed to protect and enhance fish and wildlife habitat except where a conflicting public use outweighs the loss of habitat. 18. The County shall notify the Oregon Division of State Lands and the Oregon Department of Fish and Wildlife of any development applications for land within a wetland identified on the National Wetlands Inventory or South Deschutes County Local Wetland Inventory maps. 19. The County shall encourage the formation of nonprofit land trusts for the protection of fish and wildlife habitat, wetland, riparian and natural areas. The County should provide support and assistance when deemed appropriate by the Board of County Commissioners. (Ord. 2011-008 U. 2011; 2002-005 §1, 2002; Ord. 80-203, 1980) PAGE 2 OF 2 - EXHIBIT "A" TO ORDINANCE 2011-008 Chapter 23.112. WATER RESOURCES 23.112.010. Water Resources. 23.112.020. Goals. 23.112.030. Policies. 23.112.040. Goal 5 Inventory - Riparian Areas. 23.112.010. Water Resources. Water in adequate quality and quantity is important to all communities, but in a semi-arid region such as where Deschutes County is located it is of particular importance. Drought is a recurring natural phenomenon which has done much to direct the County's growth and to determine its economic base. Unfortunately, inadequate information exists on water supplies and on water quality. The County health Department, Oregon Health Division, Oregon Department of Environmental Quality, and U.S. Geological Survey are all presently involved with studies or ongoing programs to provide a greater understanding of the area's water resources. Given the expected continued growth of the area and the existence of water quality and quantity problems already the results of these studies will prove useful in updating this plan and safely accommodating the new growth while protecting existing industries and residents. It does appear that little additional water for agricultural expansion may be expected locally, except for some new wells in such areas as Lower Bridge and Cloverdale. The use of irrigation water for domestic purposes has not only reduced available water supplies for agriculture but also raised questions about possible health hazards resulting from people drinking from irrigation ditches. Some water quality problems have been identified as resulting from domestic effluent and agricultural operations. At present the domestic effluent is clearly a more pressing concern than agricultural activities (because of local soils, climate, topography and farm operations). The continued use of drill holes for sewage disposal has been noted as a subject of particular concern. To indicate the County's concern and to serve as important long range objectives the following goals have been identified. (Ord. 2002-005 §1, 2002; Ord. 2000-017 §1, 2000; Ord. 94-003, 1994; PL-20,1979) 23.112.020. Goals. 1. To maintain existing water supplies at present quality and quantity. 2. To improve the efficiency with which water is supplied to meet the growing needs of Deschutes County residents. (Ord. 2002-005 § 1, 2002; Ord. 2000-017 § 1, 2000; Ord. 94-003, 1994; PL-20, 1979) 23.112.030. Policies. In order to achieve the desired results three general policy directions have been determined, each general topic composed of several specific policies. 1. Resource Study: To obtain better information than that presently available so as to assure the safe use of the area's water resources the following policies shall be adopted: a. Obtain funding to conduct a complete County-wide hydrology study. Particular emphasis shall be placed on study of urban areas, irrigation water seepage into local water tables, stream flow and limits to water availability. b. The County, in conjunction with appropriate State and Federal agencies, shall conduct a study on the location and characteristics of local aquifers and streams, emphasizing the La Pine area first. PAGE 1 OF 5 - EXHIBIT "B" TO ORDINANCE 2011-008 c. The County shall conduct a study of the legal, economic and environmental consequences of the use of irrigation water for non-agricultural uses. d. When information is available on the location, quality and quantity of groundwater resources, the county will determine the significance of the resource and complete the Goal 5 process for groundwater resources in accordance with OAR 660-16. 2. Water supply. The second general topic is the protection and improvement in efficiency of local water supplies. a. The County shall work with local irrigation districts, private and municipal water suppliers as well as adjacent Counties and the State to assist water management planning. b. Consistent with acceptable environmental, social and economic impacts, the County shall cooperate with State and Federal agencies in irrigation canal lining, reservoir construction and watershed management. c. The County shall continue to serve as a sponsor for Federal and State grants for water system improvements. 3. Water quality. The final general policy direction is the protection and improvement of the area's water quality so that the County's new population can be safely accommodated without serious public safety, environmental and economic costs. a. The County shall work with State and Federal agencies in planning for water quality (i.e., Sections 208 and 303e) and in the enforcement of anti-pollution regulations. Also, if found necessary, create and enforce local anti-pollution ordinances. b. The County, through educational programs and other similar activities, should encourage the use of non-toxic, rapidly biodegradable chemicals. c. Plans, ordinances, cooperative agreements and other legal and educational tools shall be fostered by the County to protect watersheds, reduce erosion and inappropriate run-off, and otherwise preserve local water quality from undesirable building, agriculture or other practices. d. Any project which would endanger the purity of local ground water shall be vigorously discouraged. e. To protect the public's health and safety irrigation ditch water shall not be an approved domestic water source for subdivisions, partitions or other developments after adoption of this plan. This will not affect existing legal subdivisions, partitions or other developments. (Ord. 2002-005 §1, 2002; Ord. 2000-017 §1, 2000; Ord. 94-003, 1994; Ord. 80-203, 1980; PL-20, 1979) 23.112.040. Goal 5 Inventory - Riparian Areas. 1. Inventory: Riparian areas are areas adjacent to rivers, streams, lakes or ponds where there is vegetation that requires free or unbound water or conditions that are more moist than normal. Riparian areas form an interconnected system within a watershed. At the water's edge they define the transition zone between aquatic systems and terrestrial systems. Riparian areas often contain a diversity of vegetation not found in upland areas. Riparian areas are limited in Deschutes County and are important habitats for both fish and wildlife. In Deschutes County significant riparian habitat is located in one or more of the following three areas: a. The area within 100 feet of the ordinary high watermark of an inventoried river or stream. The 100 foot wide area may contain both riparian vegetation and upland vegetation. Wetlands and flood plain are also frequently within 100 feet of a stream or river. In some cases the riparian vegetation may extend beyond 100 feet from the ordinary high water mark if it is a designated wetland or flood plain. PAGE 2 OF 5 - EXHIBIT "B" TO ORDINANCE 2011-008 In forested areas, the Oregon Department of Forestry identifies the riparian management area along Class 1 streams as an area on each side of a stream averaging three times the stream width but not averaging less than 25 feet or more than 100 feet. The Oregon Department of Fish and Wildlife (ODFW) Land Use Planning Guide contains a section identifying protection policies and standards for various habitats and species. The recommended model ordinance for riparian areas in the handbook identifies a 100-foot area as measured from the ordinary high water line of all Class I and Class H streams. b. The area adjacent to an inventoried river or stream and located within a flood plain mapped by the Federal Emergency Management Agency and zoned Flood Plain by the County. The flood plain may extend beyond 100 feet from the ordinary high water mark of the stream and may contain wetland. c. The area adjacent to a river or stream and inventoried as a wetland on the National Wetlands Inventory or South Deschutes County Local Wetland Inventory Map. A riparian wetland may extend beyond 100 feet from the ordinary high water mark and may be included in a flood plain. The County has not conducted an inventory of riparian areas adjacent to lakes and ponds on private land in most of Deschutes County. However, because of a state grant, the County was able to hire a consultant to conduct an inventory in South Deschutes County. Additionally, many of these other areas of the County are included in the National Wetland Inventory Maps and are subject to County, State and/or Federal wetland fill and removal regulations. Riparian areas adjacent to the many lakes on federal lands are managed and protected under the federal land and resource management plans and are not included in the County inventory and are not considered in the ESEE analysis of conflicting uses. The three areas described above are further identified in the Deschutes County/City of Bend River Study, the Federal Emergency Management Agency (FEMA) Flood Plain maps, the U.S. Department of the Interior National Wetlands Inventory maps, South Deschutes Coun , Local Wetland Inventory, the Deschutes County Comprehensive Plan and Title 18 of the Deschutes County Code. 2. Deschutes County/City of Bend River Study. The Deschutes County/City of Bend River Study (1986) inventoried the following significant riparian habitat and completed an ESEE analysis of this habitat. The River Study inventory and ESEE analysis for riparian habitat are incorporated herein by reference. The River Study resulted in adoption of a 100-foot setback for structures and septic systems, fill and removal regulations, provisions for conservation easements and prohibition of hydroelectric facilities on certain reaches of the Deschutes River and its tributaries. a. Riparian Area Inventoried In River Study. Table 6-2 STREAMS ACRES Deschutes River 1,440 Little Deschutes River 2,920 Paulina Creek 846 Fall River 43 Crooked River 38 Wh chus Creek 47 Tumalo Creek 50 Indian Ford Creek 573 TOTAL 5,966 b. FEMA maps. The Federal Emergency Management Agency (FEMA) maps flood plain adjacent to the following rivers and streams. The flood plain along these rivers and streams is zoned Flood Plain (FP) by Deschutes County. PAGE 3 OF 5 - EXHIBIT "B" TO ORDINANCE 2011-008 Deschutes River Little Deschutes River Whychus Creek Crooked River Paulina Creek Long Prairie Dry River Spring River Indian Ford Creek Portions of Indian Ford Creek and the Deschutes River near Sunriver have not been surveyed and mapped by FEMA. These areas are not zoned flood plain. However, the Flood Plain Zone, Title 18.96.020, states: "When base flood elevation data has not been provided in the flood insurance study, the Planning Division will obtain, review and reasonably utilize any base flood elevation or flood way data available from federal, state or other sources in determining the location of a flood plain or flood way." 3. I-Wienal Wetlands Inventory Maps. The U.S. Department of Interior National Wetlands Inventory Maps and South Deschutes County Local Wetland Inventory are the County inventory of wetland habitat. These mapped wetlands are subject to County, state and federal fill and removal regulations. 4. Deschutes County Comprehensive Plan. The Deschutes County Comprehensive Plan, adopted in 1979, mapped riparian areas along the following rivers and streams. River or Stream Ownership Deschutes River Private/Federal Little Deschutes River Private/Federal Fall River Private/Federal Tumalo Creek Private/Federal Three Creek Private/Federal Whychus Creek Private/Federal Trout Creek Private/Federal Dry Creek Private/Federal Cache Creek Private/Federal Indian Ford Creek Private/Federal Cultus River Federal Charlton Creek Federal Deer Creek Federal Cultus Creek Federal Quinn Creek Federal Fall Creek Federal Moore Creek Federal Title 18.88, the Wildlife Area Combining Zone, contained a provision which required advice from the Oregon Department of Fish and Wildlife to determine the minimum lot sizes in these mapped riparian areas. This provision was deleted from Title 18.88 by Ordinance 92-042 because it was not a clear and objective standard. The Comprehensive Plan map was repealed and replaced with a Wildlife Habitat Combining Zone Map that does not include mapped riparian areas. Title 18 - Deschutes County Zoning Ordinance. DCC 18.04.030 includes the following streams in the definition of "perennial stream." These streams, in addition to all those listed above, are subject to the 100-foot setback for structures and septic systems. Perennial Streams Listed in DCC 18.04.030 Bottle Creek Metolius Creek Bridge Creek Park Creek - East Fork PAGE 4 OF 5 - EXHIBIT "B" TO ORDINANCE 2011-008 Brush Draw Park Creek - West Fork Bull Creek Pole Creek Cache Creek Rock Creek Charlton Creek Snow Creek Cultus Creek Soap Creek Cultus River Spring Creek Deer Creek Soda Crater Creek Dry Creek Whychus Creek-North Fork Fall Creek Three Creek First Creek Todd Lake Creek Full Creek Trout Creek Goose Creek Tumalo Creek-North Fork Indian Ford Creek Tumalo Creek-Middle Fork Jack Creek Tumalo Creek-South Fork Kaleetan Creek All of these streams, except portions of Indian Ford Creek, Cache Creek and Dry Creek, are located on federal land and are subject to either the Deschutes National Forest or the Bureau of Land Management Resource Management Plans. 6. Goal 5 Inventory - Wetlands. Inventory: Deschutes County Ordinance 92-045 adopted all wetlands identified on the U. S. Fish and Wildlife Service National Wetland Inventory Maps as the Deschutes County wetland inventory. Additionally, Deschutes County Ordinance 2011-008 adopted a Local Wetland Inventory covering 18,937 acres in South Deschutes County. Wetlands are those areas that are inundated or saturated by surface or ground water at a frequency and duration sufficient to support, and that under normal conditions do support a prevalence of vegetation typically adapted for life in saturated soil conditions. (Ord. 2011-008 §1, 2011; 2002-005 §1, 2002; Ord. 2000-017 §1, 2000; Ord. 94-003, 1994; PL-20, 1979) PAGE 5 OF 5 - EXHIBIT "B" TO ORDINANCE 2011-008 FINDINGS The Deschutes County Planning Commission held a work session on August 25, 2011 to review Ordinance 2011-008. These legislative plan amendments to Deschutes County Code (DCC) 23.104, Fish and Wildlife, and 23.112, Water Resources, formally recognize a South Deschutes County Local Wetland Inventory recently approved by the Oregon Department of State Lands (DSL). Consistent with DCC 22.12.010, the Board of County Commissioners held a public hearing on September 26, 2011.' National Wetland Inventory (NWI) Deschutes County's NWI was developed by the U.S. Fish and Wildlife Service in the 1980s and covers the entire county. It relies on high-altitude aerial photos, with limited field work. While the NWI is extremely useful for many resource management and planning purposes, its small scale, accuracy limitations, age, and absence of property boundaries make it unsuitable for parcel-based decision making. Local Wetland Inventory (LWI) To augment the NWI where more detailed inventory information is needed, DSL developed guidelines and rules for LWIs. An LWI aims to map all wetlands at least 0.5 acres or larger. The LWI maps and report provide information about the inventory area and the individual wetlands, including: • Total acreage of wetlands in the inventory area • Acreage of each wetland type in the inventory area (e.g., 18 acres of forested wetland) • Location, approximate size, and classification (type) of each wetland mapped • A description of each mapped wetland • A functions and condition assessment of all mapped wetlands • All tax lots containing wetlands By adopting Ordinance 2011-008, the South County Local Wetland Inventory (South County LWI) will replace the NWI map for South County and improve the accuracy in the identification of jurisdictional wetland characteristics in the upper Deschutes Basin because unlike the NWI, the South County LWI identifies wetlands within an accuracy of 5 meters (16.4 feet). As a parcel based document, the South County LWI is designed to be a useful tool for County and DSL staff in review of development permits potentially affecting wetlands in the La Pine sub-basin. An approved LWI must be used by the local government (in place of the NWI) for the Wetland Land Use Notification process (a local-state 1 http://www.co.deschutes.or.us/dccode/title22/docs/chai)ter%2O22.12.doc. A public notice was published in the Bulletin on September 11, 2011. PAGE 1 OF 12 - EXHIBIT "C" TO ORDINANCE 2011-008 coordination process) when a land use application is in a mapped wetland area.2 The South County LWI will not change the way Deschutes County regulates development in wetland areas. As described below, since 1986 Deschutes County required (and will continue to require) a conditional use permit for any vegetation removal, and fill and removal of a wetland. These requirements are in DCC 18.128.270. In these cases, an applicant is required, among others to demonstrate no practicable alternative and coordinate with the Oregon Department of Fish and Wildlife (ODFW) and DSL.3 The DSL is involved because Oregon's Removal-Fill Law (ORS 196.795-990) requires people who plan to remove or fill material in waters of the state to obtain a state permit. The purpose of the law, enacted in 1967, is to protect public navigation, fishery and recreational uses of the waters. "Waters of the state" are defined as: natural waterways including all tidal and nontidal bays, intermittent streams, constantly flowing streams, lakes, wetlands and other bodies of water in this state, navigable and nonnavigable, including that portion of the Pacific Ocean that is in the boundaries of this state. The law applies to all landowners, whether private individuals or public agencies. Wetlands and waterways, regardless of whether or not they are mapped, may be regulated under the State Removal-Fill Law. If ground-altering site work is proposed, a more precise wetland boundary may need to be located (a "delineation") to know where state permit requirements apply. Compliance with wetland and waterway regulations remains the responsibility of the landowner. BACKGROUND A. Central Oregon Endangered Species Act Risk Evaluation Steelhead trout, which are listed as threatened under the Endangered Species Act, are being reintroduced into the upper Deschutes Basin. The cities and counties of Central Oregon, in 2009, evaluated whether current local government policies and practices are sufficiently protective of steelhead trout and their habitat. Specifically, the jurisdictions desire to avoid the "take" of reintroduced steelhead trout, and reduce the potential of Endangered Species Act-related enforcement actions and third-party lawsuits. A September 2009 report produced by ICF Jones & Stokes evaluated Deschutes County policies and practices to determine its potential for take of listed steelhead trout. ICF Jones & Stokes gathered the information for this evaluation from County documents and from information gathered in a meeting with County staff in February 2009. 2 ORS 215.418. http://www.oregon.gov/DSLMETLAND/227-350.shtmi 3 DCC 18.128.270(D)(2)(a) as a condition of approval requires an application to obtain all state and federal permits. DSL administers Oregon's Removal-Fill Law. Section 404 of the Clean Water Act regulates the discharge of dredged, excavated, or fill material in wetlands, streams, rivers, and other U.S. waters. The U.S. Army Corps of Engineers is the federal agency authorized to issue Section 404 Permits for certain activities conducted in wetlands or other U.S. waters. PAGE 2 OF 12 - EXHIBIT "C" TO ORDINANCE 2011-008 Because the County does not authorize or participate in high-risk activates such as water diversions, there is minimal risk that the County's activities could directly cause steelhead trout mortality. There are however, policies and practices that can be improved through programmatic adjustments to further minimize the exposure to Endangered Species Act risk and enhance environmental benefits. Important areas for improvement include riparian, floodplain development, stormwater management and sediment control Best Management Practices. One recommended action identified in the ICF Jones & Stokes report recognized: • The County should conduct a wetland inventory to gather more comprehensive wetland data and mapping in south Deschutes County.4 B. South County LWI Grant Funding In 2009, Deschutes County coupled an $80,000 grant from the Deschutes River Mitigation and Enhancement Program with a $35,440 grant from the Oregon Watershed Enhancement Board to conduct an LWI and assessment in the La Pine sub-basin. ESA Adolfson (ESA), a wetland consulting firm, was selected through a Request for Proposal process in January 2010. ESA ultimately prepared the South County LWI with technical assistance by Deschutes County and DSL. C. Overview of the Inventory Process An LWI is the foundation of wetland planning in the State of Oregon. Requirements are outlined in the LWI Rule (Oregon Administrative Rule [OAR] 141-086-0210). The LWI includes a comprehensive survey and map of all potential wetlands within a local government study area. The LWI process involves survey, identification and mapping of all wetlands larger than 0.5 acre that occur within a defined study area. For the South County LWI, the study area covers 18,937 acres from Sunriver to south of La Pine. This is the largest LWI that has been done in Oregon to date. An LWI is also a refinement of the NWI, which was undertaken by the US Fish in Wildlife Service in the 1980s. The NWI is a series of maps that show the likely location of wetlands across the nation; however, these maps are not very accurate because they were derived from high altitude images of the landscape and are based on imagery from the 1980s. Local Wetland Inventories are required by statewide planning goals and are useful for local planners as well as landowners. The South County LWI will help the County protect wetlands that provide important water quality functions because it has a higher degree of accuracy then the NWI. For landowners who are proposing a development project on their property, the South County LWI maps show the general location of a wetland so that development in a wetland can be avoided (if possible) or disturbance to the wetland can be minimized. A state-approved wetland delineation report for wetlands identified in an LWI is usually needed prior to site development. 4 Central Oregon ESA Risk Evaluation: Deschutes County Findings and Recommendations. ICF Jones and Stokes. Pages 4 and 10. PAGE 3 OF 12 - EXHIBIT "C" TO ORDINANCE 2011-008 Deschutes County, citizens, wetland scientists from ESA, and DSL all played a role in the inventory process. The County began the effort by scheduling a public meeting in March 2010 to inform citizens of the LWI and by obtaining permission from landowners to allow wetland scientists to access private property. ESA compiled existing data on wetlands including NWI maps, aerial photos and soils maps, and then conducted field observations to confirm the information sources. Where needed and where property access was permitted, ESA collected data on the vegetation, soils, and hydrology of a parcel to determine if the area is or is not a wetland. ESA also assessed the functions and values of the wetlands using the Oregon Rapid Wetland Assessment Protocol (ORWAP). The DSL reviewed the draft South County LWI to ensure it was conducted according to state standards and to provide quality control and quality assurance. The final South County LWI consists of a set of maps that show the approximate location of wetlands and streams, and descriptive information about the wetlands and the main functions they provide. This level of detail does not exist for the NWI. Functions that were evaluated included wildlife habitat quality, contribution to fish habitat or water quality improvement, and floodwater retention capability. Every attempt is made by the wetland consultants during the development of the South County LWI to map wetlands correctly on parcels and wetland boundaries to an accuracy of at least 5 meters (16.4 feet). There may be areas where the boundary is less accurate, especially on large tracts with few geographic reference points, and areas where property access was denied. D. Public Involvement The County organized the public involvement efforts for this project. Letters sent in February 2010 describing the project and seeking property access permission were mailed to all property owners within the study area, including those whose tax lots intercepted hydric soil layers and/or NWI-mapped wetlands and streams, or whose tax lots showed soil saturation (darker areas) indicative of wetlands in the aerial photographs. A public open house was held at Sunriver on March 16, 2010, at the Three Rivers Elementary School. Approximately 100 members of the public attended the meeting. Access permission was ultimately granted to 1,286 of 4,652 properties within the study area, for a permission rate of 28 percent. According to DSL, this is the highest permission rate of any LWI project in Oregon to date. Letters were sent in October 2010 to all landowners whose land contain or abut mapped wetlands identified on the draft South County LWI. The letter announced the October 29 release of the draft South County LWI and a November 16, 2010 public workshop. At the second workshop, also held at the Three Rivers Elementary School, ESA, DSL, and Deschutes County staff set up stations to answer questions. Approximately 90 people attended. The public comment period closed on December 31. PAGE 4 OF 12 - EXHIBIT "C" TO ORDINANCE 2011-008 E. Overview of Oregon Rapid Wetland Assessment Protocol The ORWAP was developed to rapidly and qualitatively assess the functions and values of all types of wetlands throughout the state of Oregon. The ORWAP is intended to be completed by wetland professionals and was designed for planning and educational purposes. The methodology, as outlined in The Manual to the Oregon Rapid Wetland Assessment Protocol (version 2.0) (Adamus et al., 2009), consists of a series of questions with multiple-choice responses. The questions cover a wide variety of features that can be observed rapidly when visiting a wetland or in some cases, obtained from aerial imagery or other sources. These particular questions are believed to correlate with the relative levels of various functions that a wetland can perform and the values potentially associated with those functions. After a user answers all the questions, ORWAP uses the responses to automatically compute a score for each function and its potential value. "Functions" are things that wetlands do naturally, like store water, purify run-off, and provide habitat (to name a few). Not all wetlands perform the same function equally. For example, some wetlands provide habitat well-suited for nesting ducks, while others (such as densely forested wetlands) do not. The responses to ORWAP questions predict that potentially associated with those functions. After a user answers all the questions, ORWAP uses the responses to automatically compute a score for each function and its potential value. The ORWAP Raw Data, Glossary and Summary Scores are located in the South County LWI, Appendices F and G. F. South County LWI Incorporated into Statewide Inventory On July 19, 2011, DSL approved the South County LWI and incorporated it into the Statewide Inventory (Attachment). OAR 141-086-0185(1)(2) requires Deschutes County to use the South County LWI in place of the NWI for notifying DSL of land use applications affecting mapped wetlands and other waters. Deschutes County subsequently notified landowners of record by mail in mid-August, as required by OAR 141-086-0240 and ORS 215.503, whose parcel contains or abuts a mapped wetland or probable wetland identified on the South County LWI. The letter also alerted property owners to the Planning Commission work session and Board of County Commissioner September 26, 2011 public hearing and emphasized that the LWI will not change the way Deschutes County regulates development in wetland areas. G. South County LWI Results ESA identified and recorded a total of 114 wetlands within the study area. Seventy-one (71) probable wetlands (PW) were also mapped as defined by OAR 141-086-0200. In some cases, a PW represents a small portion of a larger wetland that is located outside of the study area. Probable wetlands appeared to have wetland characteristics but were either less than 0.50 acre or small and of an underdetermined size. They may or may not be state or federally jurisdictional. Twenty-nine (29) artificially created wetlands were found as well; three stormwater treatment ponds, two irrigation channels, two excavated PAGE 5 OF 12 - EXHIBIT "C TO ORDINANCE 2011-008 ponds, three golf course ponds, two fish hatchery ponds, one landscape pond, eleven stock ponds, and three other ponds. The summary statistics derived from ORWAP indicate that most of the 114 mapped wetlands in the Upper Deschutes are currently capable of performing all functions commonly attributed to wetlands except for providing habitat to anadromous fish and nesting waterbirds habitat. The inventoried wetlands do not provide anadromous fish habitat because of the lack of access to the project area by anadromous fish. Also, the inventoried wetlands do not provide much habitat for nesting waterbird because of the scarcity of large wetlands that remain ponded throughout the summer. Waterbirds do nest in riverine wetlands along the Deschutes River within the study area, but even this nesting is very limited. The functions scoring the highest overall for the wetlands inventoried are: Organic Matter Export, Pollinator Habitat, and Aquatic Invertebrate Habitat. Some functions show relatively little variation among the project wetlands (e.g., Carbon Sequestration, Native Plant Diversity), while others vary considerably (e.g., Nitrate Removal, Organic Matter Export). Although most of the assessed wetlands perform similar functions, the values associated with performance of these functions vary considerably. The ORWAP identified the following three functions as having the highest value in the project area: • Phosphorus Retention, • Aquatic Invertebrate Habitat, and • Nitrate Removal. The value of some functions varies little among the project wetlands (Pollinator Habitat, Public Use & Access) while the value of others shows large spatial variation (Aquatic Invertebrate Habitat, Water Storage & Delay). PROPOSED PLAN AMENDMENT The proposed amendments to Deschutes County's Comprehensive Plan are described in Ordinance 2011-008, Exhibits A and B. Added language is underlined and deleted shown as stF*kethFough. REVIEW CRITERIA Ordinance 2011-008 formally recognizes a South County LWI recently approved by DSL. Oregon Administrative Rule 141-086-0185(1)(2) requires Deschutes County to use the South County LWI in place of the NWI for notifying DSL of land use applications affecting mapped wetlands and other waters. The South County LWI will not change the way Deschutes County regulates development in wetland areas. Since 1992, Deschutes County required (and will continue to require) a conditional use permit for any excavation, grading, vegetation removal and fill and removal of a wetland. In these cases, an applicant is required, among others to demonstrate no practicable alternative and coordinate with ODFW and DSL. PAGE 6 OF 12 - EXHIBIT "C" TO ORDINANCE 2011-008 Deschutes County lacks specific criteria in DCC Titles 18, 22, or 23 for reviewing a legislative plan amendment. Nonetheless, because this is a Deschutes County initiated plan amendment, the County bears the responsibility for justifying that the amendments are consistent with the statewide planning goals and its Comprehensive Plan. FINDINGS 1. Statewide Planning Goals The parameters for evaluating these specific amendments are based on an adequate factual base and supportive evidence demonstrating consistency with Statewide Planning Goals. The following findings demonstrate that Ordinance 2011-008 complies with applicable statewide planning goals and state law. Goal 1, Citizen Involvement, is met through this adoption process because these amendments will receive one public hearing before the Board of County Commissioners, consistent with ORS 215.060 and DCC 22.12.010. • Goal 2, Land Use Planning, is met because ORS 197.610 allows local governments to initiate post acknowledgments plan amendments (PAPA). An Oregon Land Conservation and Development Department 45-day notice was initiated on August 4, 2011.5 This FINDINGS document provides the adequate factual basis and documented analysis for this plan update. Goal 3, Agricultural Lands and Goal 4, Forest Lands, is met because the South County LWI replaces the NWI for the purpose of identifying mapped wetlands and probable wetlands. Many of the Exclusive Farm Use (EFU) and Forest Use (F1 or F2) zoned tax lots that have areas designated as NWI and/or LWI are very small, sliver pieces of property. A comparison of the NWI with the South County LWI within the resource zones are: NWI (EFU): 62 taxlots affected NWI (F1 or F2): 83 taxlots affected LWI (EFU): 61 taxlots affected LWI (F1 or F2): 35 taxlots affected As mentioned throughout the FINDINGS, the South County LWI will not change the way Deschutes County regulates development in wetland areas. Since 1992, Deschutes County required (and will continue to require) a conditional use permit for any excavation, grading, vegetation removal and fill and removal of a wetland. In these cases, an applicant is required, among others to demonstrate no practicable alternative and coordinate with ODFW and DSL. 5 Deschutes County completed period review on January 23, 2003. PAGE 7 OF 12 - EXHIBIT "C TO ORDINANCE 2011-008 • Goal 5, Natural Resources, Scenic and Historic Areas, and Open Spaces, is met because the South County LWI replaces the NWI for the purpose of identifying mapped wetlands and probable wetlands. Oregon Administrative Rule 660-023- 0250(3) recognizes that local governments are not required to apply Goal 5 inconsideration of a PAPA unless the PAPA affects a Goal 5 resource. In one of the underlying LUBA opinions, Johnson v. Jefferson County,-Or LUBA_, (LUBA No. 2007-015, 2007-017, 2007-019, 2007-020, 2007-023, 2007-024, 2007-028 and 2007-029, February 11, 2008), LUBA reaffirmed that when a local government has already balanced the importance of conflicting uses with a Goal 5 resource, it may not need to re-justify those choices when adopting a PAPA that does not result in significantly different effects on that Goal 5 resource. This plan amendment does not result in significantly different effects on wetland resources because Deschutes County is not changing its wetland regulations and those regulations have been acknowledged as protecting wetlands. Deschutes County completed periodic review in 2003. The South County LWI will replace the NWI map for South Deschutes County and improve the accuracy in the identification of jurisdictional wetland characteristics in the upper Deschutes Basin. The South County LWI is designed to be a useful tool for County and DSL staff in review of development permits potentially affecting wetlands in the La Pine sub-basin. Unlike the NWI, which utilized high altitude aerial maps from the 1980s, the South County LWI aims to map all wetlands at least 0.5 acres or larger at an accuracy of approximately 5 meters on a parcel-based map. The South County LWI will not change the way Deschutes County regulates development in wetland areas. Deschutes County's wetland program has been in existence since 1986. Ordinance 86-12418 required a conditional use permit for any fill or removal, or removal of vegetation, regardless of the amount, within the bed and banks of any stream or river or in any wetland. During periodic review, Deschutes County adopted three ordinances in 1992 pertaining specifically to the NWI. Excerpts of each ordinance are summarized below: o Ordinance 92-040, Amending Comprehensive Plan (PL-20), Fish and Wildlife Section, Policy 18, County shall notify the Oregon Division of State Lands and the Oregon Department of Fish and Wildlife (ODFW) of any development applications for land within a wetland identified on the National Wetlands Inventory maps.s o Ordinance 92-041, Amending Comprehensive Plan (PL-20), Adopting Fish and Wildlife Resource Element and economic, social, environment, and energy consequence analysis (ESEE), Ordinance 92-045 adopted all wetlands identified in the U. S. Fish and Wildlife Service NWI Maps as the Deschutes County wetland inventory.7 6 Ordinance 92-040, Exhibit A, Page 5. 7 Ordinance 92-041, Exhibit A, Page 73. PAGE 8 OF 12 - EXHIBIT "C" TO ORDINANCE 2011-008 (Program to Achieve Goal)8 In all zones, the county zoning ordinance requires a 100 foot setback from the ordinary high water mark of all streams or lakes for all sewage disposal installations and structures. Title 18.96, Flood Plain Zone - protects riparian habitat and wetlands by requiring a conditional use for any development. Title 18.128(W), Fill and Removal - requires a conditional sue permit for any fill and removal, including vegetation in wetlands or within the bed and banks of any streams or river. o Ordinance 92-045, Adoption of Wetland Maps, Resource Element of the Comp Plan is amended to adopt and incorporate by reference, the National Wetlands Inventory, as published by the U. S. Department of the Interior, Fish and Wildlife Service, falling within the borders of Deschutes County. 9 In 1994, Deschutes County adopted Ordinance 94-007 as a result of a Land Conservation and Development Commission Remand Order (93-RA-883), requiring an amendment to the Comprehensive Plan Resource Element ESEE for riparian and wetlands in order to comply with periodic review. o Ordinance 94-007, Wetlands and Riparian Areas inventory and ESEE analysis adopted by Ordinance 92-041 (p. 73-76) be deleted and replaced by the inventory and ESEE analysis contained in Exhibit A, Riparian Areas, and Exhibit B, Wetlands. (Exhibit A) In all zones a conditional use permit is required for fill and removal of any material, including vegetation, within a wetland or within the bed and banks of an inventoried stream. This provision applies to all wetlands mapped on the National Wetland Inventory Maps. 10 (Exhibit B) Title 18.128(W), Fill and Removal, establishes the criteria for the conditional use permit. All zones in the county outside of UGBs require a conditional use permit for fill and removal activity in a wetland or within the bed and banks of a stream or river. The criteria require: (1) review by ODFW,• (2) control of erosion; (3) minimizing disturbance of existing vegetation; (4) a determination that there is no s Ibid. Pages 75-76 9 Ordinance 92-045, Page 1. 10 Ordinance 94-007, Exhibit A. Page 13. PAGE 9 OF 12 - EXHIBIT "C" TO ORDINANCE 2011-008 practicable alternative for development. A conservation easement is required as a condition for a fill and removal conditional use permit." • Goal 6, Air, Water and Land Resources Quality, is met because, unlike the NWI, the South County LWI, using ORWAP, identifies wetland function and values. The summary statistics derived from ORWAP indicate that most wetlands in the upper Deschutes are currently capable of performing all functions commonly attributed to wetlands, including organic matter export, sediment retention and stabilization, phosphorous retention, nitrate removal and retention, thermoregulation, water storage and delay, and carbon sequestration. Two functions showing the highest value in the project area include phosphorous retention and nitrate removal. Because the existing county regulations in DCC 18.128.270(D) protect wetlands by requiring a conditional use permit for the "fill or removal of material or vegetation within the bed and banks of a stream, river or wetland", the wetlands are protected sufficiently to allow them to continue to perform their natural functions as described in the previous paragraph. • Goal 7, Natural Hazards, is met because the South County LWI will replace the NWI map and improve the accuracy in the identification of jurisdictional wetland characteristics in the upper Deschutes Basin. The South County LWI is designed to be a useful tool for County and DSL staff in review of development permits potentially affecting wetlands in the La Pine sub-basin. Unlike the NWI, which utilized high altitude aerial maps from the 1980s, the South County LWI aims to map all wetlands at least 0.5 acres or larger at an accuracy of approximately 5 meters on a parcel-based map. • Goal 8, Recreational Needs, is not applicable because no destination resorts are currently mapped in the study area. Although an application was made for parcels near the Sunriver urban unincorporated community to be mapped to become eligible for siting a destination resort, none of the wetlands identified in the South County LWI that were not also included in the NWI are located on those parcels. Goal 9, Economic Development, is met because, Unlike the NWI, which utilized high altitude aerial maps from the 1980s, the South County LWI aims to map all wetlands at least 0.5 acres or larger at an accuracy of approximately 5 meters on a parcel-based map. Lands designated for economic development (EFU and F1 or F2 zoned tax lots) have areas designated as NWI and/or LWI that are very small, sliver pieces of property. A comparison of the NWI with the South County LWI for these lands are: NWI (EFU): 62 taxlots affected NWI (171 or F2): 83 taxlots affected LWI (EFU): 61 taxlots affected LWI (F1 or F2): 35 taxlots affected " Ibid. Exhibit B. Page 4 PAGE 10 OF 12 - EXHIBIT "C" TO ORDINANCE 2011-008 Since the South County LWI mapping designations on EFU and F1 and F2 lands are such that they do not interfere with the ability to have economically viable agricultural and forest uses, the adoption of the LWI complies with this goal. Furthermore, the South County LWI will not change the way Deschutes County regulates development in wetland areas. Since 1992, Deschutes County required (and will continue to require) a conditional use permit for any excavation, grading, vegetation removal and fill and removal of a wetland. In these cases, an applicant is required, among others to demonstrate no practicable alternative and coordinate with ODFW and DSL. An approved LWI must be used by the local government (in place of the NWI) for the Wetland Land Use Notification process (a local-state coordination process) when a land use application is in a mapped wetland area. • Goal 10, Housing is not applicable because, unlike municipalities, unincorporated areas are not obligated to fulfill certain housing requirements. • Goal 11, Public Facilities and Goal 12, Transportation, is not applicable because the South County LWI replaces the NWI for the purpose of identifying mapped wetlands and probable wetlands. The South County LWI can be used as a tool for public facility and transportation facility planning to avoid and/or minimize impacts to jurisdictional wetlands. • Goal 13, Energy Conservation, is not applicable because the South County LWI replaces the NWI for the purpose of identifying mapped wetlands and probable wetlands. The wetland inventory does not alter land uses from the context of energy conservation, energy utilization, depletion of non-renewable energy, or recycling as underscored by Goal 13 and its respective guidelines. • Goal 14, Urbanization, is not applicable because no expansion of an urban area is proposed with these amendments. • Goals 15 through 19 are not applicable to any amendments to the County's comprehensive plan because the county has none of those types of lands. 2. Comprehensive Plan / Fish and Wildlife Chapter The South County LWI will replace the NWI for the La Pine sub-basin and improve the accuracy in the identification of jurisdictional wetland characteristics in the upper Deschutes Basin. This plan amendment is consistent with the Comprehensive Plan, DCC 23.104, Fish and Wildlife Goals and Policies. This amendment fulfills Goals 1 and 4 by conserving and maintaining wildlife areas through an LWI that has been incorporated into the State Wetland Inventory and, upon adoption of Ordinance 2011- 008, integrated into Deschutes County's existing wetland regulations. 12 Policy 18, as shown in DCC 23.104.030, 13 now references the South County LWI in the requirement 12 http://www.co.deschutes.or.us/dccode/title23/docs/chapter%2O23.104.doc 13 Ordinance 2011-008, Exhibit A. PAGE 11 OF 12 - EXHIBIT "C" TO ORDINANCE 2011-008 for County staff to notify DSL and ODFW of any development applications for land within a wetland identified on the NWI or LWI.14 3. Comprehensive Plan / Water Resources Chapter This plan amendment is consistent with the Comprehensive Plan, DCC 23.112, Water Resources Goals and Policies. As shown in Ordinance 2011-008, Exhibit B, a riparian wetland is now recognized on the NWI and South County LWI.15 The citations for the County's Wetland Inventory Maps have also been updated.16 4. Consistency with Deschutes County Comprehensive Plan Land use planning implemented through Deschutes County policies and zoning will enable residents, stakeholders, and property owners in the La Pine sub-basin to maintain and enhance wetland resources. The LWI identified and recorded a total of 114 wetlands within the study area. Additionally, 71 probable wetlands (PW) and 27 artificial wetlands were identified in the study area. Twenty-nine (29) artificially created wetlands were found in the study area. The summary statistics derived from ORWAP indicate that most wetlands in the Upper Deschutes are currently capable of performing all functions commonly attributed to wetlands except for providing habitat to anadromous fish and nesting waterbirds habitat. The South County LWI will help the County protect wetlands that provide important water quality functions. For landowners who are proposing a development project on their property, the South County LWI maps will show the general location of a wetland so that development in a wetland can be avoided (if possible) or so that disturbance to the wetland can be minimized. The South County LWI is designed to be a useful tool for County and DSL staff in review of development permits potentially affecting wetlands in the La Pine sub-basin. The South County LWI consists of a set of maps that show the approximate location of wetlands and streams, and descriptive information about the wetlands and the main functions they provide. In 2003, upon completing periodic review, DCC 23.104, Fish and Wildlife and DCC 23.112, Water Resources were found to be in compliance with the County's comprehensive plan. Adopting the South County LWI into these two chapters helps Deschutes County to continue implementing land use policies pertaining specifically to wetland inventories recognized on the Statewide Inventory. Attachment Oregon Department of State Lands Letter Approving South County LWI 14 Ibid. Page 2. 15 Ordinance 2011-008. Exhibit B, Page 3. 16 Ibid. Pages 4 and 5. PAGE 12 OF 12 - EXHIBIT "C" TO ORDINANCE 2011-008 SOUTH DESCHUTES COUNTY LOCAL WETLAND INVENTORY & MAPS Prepared for Deschutes County Funded by: Oregon Watershed Enhancement Board Deschutes River Mitigation and Enhancement Program June 2011 SA --.A Paul Adamus Harper Houf Peterson Righellis Inc. South Deschutes County Local Wetland Inventory Report • TABLE OF CONTENTS 1.0 INTRODUCTION .............................................................................................................1 1.1 OVERVIEW OF THE INVENTORY PROCESS ...............................................................................1 1.2 PUBLIC INVOLVEMENT ...........................................................................................................2 2.0 STUDY AREA AND LANDSCAPE SETTING .............................................................3 3.0 METHODS ........................................................................................................................4 3.1 PRELIMINARY MAPPING AND RESEARCH ................................................................................4 3.2 REQUIRED INFORMATION SOURCES ................4 3.3 WETLAND DETERMINATIONS ................5 3.3.1 On-site Determinations ................5 3.3.2 Off-site Determinations ................5 3.4 FIELD MAPPING AND DATA COLLECTION ................6 3.4.1 Wetlands ................6 3.4.2 Probable Wetlands 8 3.4.3 Wetland/Upland Mosaics ................8 3.4.4 Sample Plots ................9 3.4.5 Guidance on How to Find Sample Plot Data and Other Information 9 3.5 OVERVIEW OF OREGON RAPID WETLAND ASSESSMENT PROTOCOL ................9 3.5.1 ORWAP Methods ..............11 4.0 RESULTS .........................................................................................................................12 4.1 WETLANDS ...........................................................................................................................12 4.2 DEEPWATER HABITAT ..........................................................................................................13 4.3 ARTIFICIALLY CREATED WETLANDS ....................................................................................13 4.4 SUMMARY OF PROBABLE WETLANDS (PWS) .......................................................................13 • 4.5 ORWAP RESULTS ................................................................................................................13 4.6 GOAL 6 WATER QUALITY RESOURCES 16 5.0 LIMITATIONS ...............................................................................................................17 6.0 LITERATURE CITATIONS .........................................................................................18 ATTACHMENT 1- SOUTH DESCHUTES COUNTY LOCAL WETLAND INVENTORY LIST OF APPENDICES Appendix A: Figures A-1 Figure 1 Vicinity Map Figures 2.1 to 2.7 National Wetland Inventory Maps Figures 3.1 to 3.7 Soils Maps Appendix B: Staff Qualifications ....................................................................................B-1 Appendix C: Wetland Determination Forms ..................................................................C-1 Appendix D: Wetland Summary Sheets D-1 Appendix E: Cowardin Glossary of Terms ....................................................................E-1 Appendix F: ORWAP Raw Data F-1 Appendix G: ORWAP Glossary and Summary Scores, Tables G1 to G4 G-1 Appendix H. Overview of Groundwater Quality H-1 • ESA Adolfson Page i June 2011 South Deschutes County Local Wetland Inventory Report LIST OF TABLES Table 1. Summary of Wetlands in the South Deschutes County LWI 12 Table 2. Summary Statistics for Function Scores of South Deschutes County Wetlands (n=114) 14 Table 3. Summary Statistics for Value Scores of South Deschutes County Wetlands (n=114) 15 C7 is Page ii ESA Adolfson June 2011 South Deschutes County Local Wetland Inventory Report • 1.0 INTRODUCTION The South Deschutes County Local Wetland Inventory (LWI) has been prepared and funded through an Oregon Watershed Enhancement Board (OWEB) Technical Assistance Grant which also leverages funding from the Deschutes River Mitigation and Enhancement program. ESA Adolfson (ESA) has prepared this report and mapping with technical assistance by Deschutes County and Oregon Department of State Lands (DSL). ESA was assisted in the field inventory by Paul Adamus and Harper Houf Peterson Righellis Inc., (HHPR). As requested by the County, Paul Adamus also provided technical expertise in the use of the Oregon Rapid Wetland Assessment Protocol (ORWAP). Local wetland inventories are used by local governments to identify water resources during comprehensive plan development to meet statewide planning goals. The South Deschutes County Local Wetland Inventory (LWI) will allow the County to better identify potential wetland areas that provide important water quality functions and identify areas where development will avoid or minimize impacts to those wetlands. The LWI will also help identify areas where restoration projects may improve water quality and other wetland functions. Similarly the LWI may assist landowners in planning for potential project permitting for development of a property. Most impacts to wetlands and streams are regulated by DSL and the U.S. Army Corps of Engineers (Corps) and usually require an approved wetland delineation report as well as permits prior to site • development. This inventory did not include wetland delineations or detailed studies necessary to support permitting of a specific project. LWI requirements are outlined in the LWI Rule (Oregon Administrative Rule [OAR] 141-086-0180 through 141-086-0240). 1.1 Overview of the Inventory Process The LWI process involves survey, identification and mapping of all wetland areas larger than 0.5 acre that occur within a defined study area. For the South Deschutes County LWI, the study area covers 18,937 acres from Sunriver to south of LaPine (Figure 1, Appendix A). This is the largest LWI that has been completed in Oregon to date. A local wetland inventory is also a refinement of the National Wetland Inventory (NWI), which was a national effort undertaken by the U.S. Fish and Wildlife Service in the 1980s. The NWI shows the likely location of wetlands across the nation; however, these maps are not as accurate as LWIs because they were derived from high altitude images of the landscape and are based on imagery from the 1980s. Deschutes County (County), citizens, wetland scientists from ESA, and the Oregon Department of State Lands (DSL) have all played a role in the inventory process for South Deschutes County. The County began the effort by scheduling a public meeting to inform citizens of the LWI and by obtaining permission from landowners to allow wetland scientists to access private property. ESA compiled existing data on wetlands • including NWI maps, aerial photos and soils maps, and then conducted field observations to confirm the information sources. Where needed and where property access was ESA Adolfson Page I June 2011 South Deschutes County Local Wetland Inventory Report permitted, ESA collected data on the vegetation, soils, and hydrology of a parcel to determine if the area is or is not a wetland. ESA also assessed the functions and values of the wetlands using the ORWAP. DSL reviewed the draft LWI to ensure it was conducted according to state standards and to provide quality control/quality assurance. The final LWI consists of a set of maps that show the approximate location of wetlands and streams, and descriptive information about the wetlands and the main functions they provide. Functions that are evaluated include wildlife habitat quality, contribution to fish habitat or water quality improvement, and floodwater retention capability. Every attempt was made to map wetlands correctly on parcels and to map wetland boundaries to an accuracy of at least 5 meters (m) or 16.4 feet. There may be areas where the boundary is less accurate, especially on large tracts with few geographic reference points, and areas where property access was denied. Ultimately, the LWI will replace the National Wetland Inventory (NWI) map for South Deschutes County and improve the accuracy in the identification of jurisdictional wetland characteristics in the upper Deschutes Basin. Upon approval of this report and mapping, Deschutes County will formally adopt the LWI into its Comprehensive Plan and Goal 6 Inventory. Staff members who participated in the South Deschutes County LWI include the following wetland scientists from ESA: John Gordon, Sarah Hartung, Alison Sigler, Aaron Booy, Rosemary Baker, and Adam Merrill. In addition, the project team included local wetland scientists Paul Adamus and Alessandra Capretti from HHPR. Project • principals from ESA include Tom McGuire, Cathie Conolly, and Teresa Vanderburg. All field staff received training from Paul Adamus in the ORWAP methods prior to field investigations. Refer to Appendix B for a complete list of staff qualifications and experience. 1.2 Public Involvement The County organized the public involvement efforts for this project. Letters describing the project and seeking property access permission were sent to all property owners whose tax lots intercepted hydric soil layers and/or NWI-mapped wetlands and streams, or whose tax lots showed soil saturation (darker areas) indicative of wetlands in the aerial photographs. Access permission was granted to 1,286 of 4,652 properties within the study area, for a permission rate of 28 percent. A public open house was held at Sunriver on March 16, 2010, at the Three Rivers Elementary School, 56900 Enterprise Drive. Approximately 100 members of the public attended the meeting. The County conducted a second public meeting on November 16, 2010, to present the draft LWI results. The County will also schedule and facilitate a public meeting to present the final LWI results in 2011. Dates, times, and locations for these future meetings will be determined by the County. 41 Page 2 ESA Adolfson June 2011 South Deschutes County Local Wetland Inventory Report • 2.0 STUDY AREA AND LANDSCAPE SETTING The South Deschutes County study area is located in south central Deschutes County in the Upper Deschutes River sub-watershed (Figure 1, Appendix A). The study area covers 18,937 acres. This is the largest LWI that has been undertaken in the state. The Upper Deschutes River sub-watershed is within the U.S. Geological Survey eight-digit hydrologic unit codes (HUC) 17070301 and 17070302, and includes portions of the Deschutes River, Little Deschutes River, and Fall River. The Fall River and the Little Deschutes River flow into the Deschutes River near Three Rivers, Oregon. The Deschutes River flows north into the Columbia River. Deschutes County is situated between the Cascades Mountains to the west and the high desert to the east. Deschutes County's land use consists mostly of forested land at higher elevations and agricultural and rural residential land at the lower elevations. The forested land tends to be fragmented and is dominated by lodgepole pine (Pinus contorta) with some ponderosa pine (Pinus ponderosa) (Franklin and Dyrness, 1988). The study area terrain is mostly flat, characteristic of wide floodplains, and is predominantly publicly- owned national forest land with scattered privately held farms, ranches, and housing tracts. Irrigated agriculture is used to produce hay and provide pasture. In recent years, Deschutes County has been one of the fastest growing counties in Oregon. Little Lava Lake is the headwaters of the Deschutes River and is located northwest of La Pine. Most of the water in the Upper Deschutes is diverted for irrigation and two • reservoirs are located upstream from the study area. Wetlands located on these large river systems tend to be wetland/upland mosaics dominated by only a few wetland plant species. Common wetland species include water sedge (Carex aquatilis), Nebraska sedge (Carex nebrascensis), narrowleaf willow (Salix exigua), grey alder (Alnus incana) and lodgepole pine (Pinus contorta). Weather in and around Deschutes County consists of cold winters with snow and hot, dry summers, typical of the High Lava Plains physiographic province (Franklin and Dyrness, 1988). The growing season is short and day and night temperature fluctuations can be great. 0 ESA Adolfson Page 3 June 2011 South Deschutes County Local Wetland Inventory Report 3.0 METHODS • The Local Wetland Inventory process is described in OAR 141-086-0180 through 141- 086-0240. Methods used to inventory wetland resources in the South Deschutes County study area are in conformity with these state rules. However, due to the extensive area covered by the South Deschutes LWI, DSL has agreed to the presentation of the inventory information on maps at a one inch to 660 foot (1" = 660') scale instead of the standard 1" = 200' scale. Also due to the large scale of this LWI, Cowardin habitat classes greater than 0.5 acre within a wetland were mapped as separate polygons, instead of those greater than 0.25 acre in size as written in the OARS. This adjustment to the methods was approved by DSL and the County. 3.1 Preliminary Mapping and Research Preliminary mapping and research was completed prior to field investigations to determine which sites within the study area were likely to contain wetlands. The County compiled preliminary wetland maps based on NWI mapped wetlands (Figures 2.1 to 2.7 in Appendix A). The County also provided wetland delineations obtained from DSL. ESA reviewed and expanded the preliminary wetland mapping provided by the County based on existing wetland delineation data and a review of aerial photographs, soil survey maps (Figures 3.1 to 3.7, Appendix A), and topographic mapping. These preliminary wetland maps were used to determine which residents to contact for access permission. ESA identified and recommended tax lots to which access should be requested for conducting wetland field work. The County sent access requests to the owners of those tax lots and then provided preliminary maps indicating the lots where access was granted. 3.2 Required Information Sources The South Deschutes County LWI is based on several sources of information, including the following GIS data layers and technical documents: • Geographic Information Systems (GIS) layers of: Aerial digital imagery (Deschutes County, 2010); LWI study area (Deschutes County, 2010); Tax lot access permissions (Deschutes County, 2010); Tax lots (Deschutes County); Potential wetlands (ESA, 2010); Wetland assessment units (ESA, 2010); La Pine/Wickiup Junction Local Wetland Inventory (DSL, 1996);National Wetlands Inventory (NWI), (U.S. Fish and Wildlife Service, 2009); Soil Survey of Upper Deschutes River Area, Oregon (NRCS, 1992); 40 Page 4 ESA Adolfson June 2011 South Deschutes County Local Wetland Inventory Report • o Streams (Deschutes County, 2007); Rivers (Deschutes County, 2006); and Public Land Survey System reference grids (Deschutes County, 2005) DSL existing wetland delineations/determinations (various citations). • USGS quadrangle maps including: La Pine, Finley Butte, Anns Butte, Pistol Butte, Round Mountain, Masten Butte and Wickiup Dam. Other information sources used to develop the LWI include local landowner knowledge. 3.3 Wetland Determinations Wetland determinations were made for all wetlands based on either on-site or off-site investigations, depending on access permission. Refer to Appendix C for the Wetland Determination Forms. 3.3.1 On-site Determinations For parcels with access permission, on-site determinations were made according to the Corps 1987 Manual (Environmental Laboratory, 1987), Regional Supplement to the Corps of Engineers Wetland Delineation Manual: Western Mountains, Valleys, and Coast is Region (Corps, 2010) and the Regional Supplement to the Corps of Engineers Wetland Delineation Manual: Arid West Region (Corps, 2008). During the first week of field work (May 3 to 7, 2010) field crews utilized the Arid West Supplement when conducting investigations. However, after speaking with DSL scientists who have worked in the Deschutes area, ESA was directed to instead use the Western Mountains Supplement. All data collected after May, including field investigations conducted on June 21 through 25 and August 9 and 10, 2010, were collected using the Western Mountains, Valleys, and Coast Regional Supplement. Determinations were made on parcels that were judged to have wetlands or wetland characteristics based on preliminary mapping and research efforts. Sample plots were established to document typical vegetation, soil, and hydrology characteristics and to determine the approximate location of the wetland boundary. 3.3.2 Off-site Determinations ESA did not enter properties where property owners denied access. For those parcels, off-site determinations were made by observing site characteristics from adjacent public rights-of-way (e.g. public streets or sidewalks) or from nearby parcels with access permission. Where feasible, sample plots were established in road rights-of-way and labeled "off-site" to characterize wetland conditions for adjacent parcels where site access was denied by the property owner. Along several waterways (e.g. the Deschutes River and the Little Deschutes River), we were able to observe a number of inaccessible wetlands from parcels on the opposite shoreline where ESA was granted access. Binoculars were used to observe many of these inaccessible wetlands. Field observations ESA Adolfson Page S June 2011 South Deschutes County Local Wetland Inventory Report of hydrology and vegetation were assessed in combination with existing data such as published soil survey data, NWI maps and/or known DSL delineations, landscape setting, aerial photography, and staff experience. Positive off-site field observations of wetland hydrology were assessed by noting evidence of soil saturation (i.e. glistening on the surface or shallow inundation) in the wetland using the naked eye and/or binoculars. Some wetlands could not be observed in the field from any vantage point due to lack of access to adjacent parcels, lack of public roads and/or unsafe road conditions (lack of shoulders). In these cases, where we lacked "visual access" ESA staff relied upon aerial imagery and observations of the general landscape to determine wetland boundaries. Sample plot data were not created for wetlands that could not be observed or accessed. 3.4 Field Mapping and Data Collection All field data were collected and recorded using hand-held Trimble Yuma, Global Positioning System/Geographic Information System (GPS/GIS) data recorders. Prior to field investigations, aerial imagery and shapefiles of the study area were loaded onto the GPS units for reference in the field. The GPS/GIS units enabled field crews to digitize wetland boundaries in ArcPad and edit existing wetland boundaries as necessary, based on observations. Trimble GPS units were also used to map probable wetlands, mark artificial wetlands, and identify locations of sample plots and streams. Other information recorded on the GPS/GIS units includes field notes and wetland delineation/determination data on digital data forms. After the field work, data were uploaded onto a desktop computer for viewing and final editing. 3.4.1 Wetlands Wetland boundaries were mapped per OAR 141-086-0210 with an accuracy target of 5 in (16.4 feet) on sites where property access was obtained. The actual accuracy may be less for some wetlands that could not be visually confirmed in the field due to lack of access permission or lack of visual access from nearby roads. Wetlands greater than or equal to 0.5 acre were assigned a unique identification code (1, 2, 3, etc) generally from north to south within the study area. Wetlands were given unique numeric identifiers, with some exceptions, according to the following criteria: • The wetland is separate from other wetland areas and lies further than 50 feet away from another wetland (Example A). • The wetland is located on one side or the other of the Deschutes River (Example B). The Deschutes River is on average wider than 100 feet and wetlands that occurred on both sides of the channel were generally labeled as separate features. • The wetland is a continuous feature that encompasses both sides of one of the smaller river or stream systems within the study area, including the Fall River, Little Deschutes River, Paulina Creek, and Long Prairie Slough (Examples C and D). These rivers and streams are on average less than 50 feet in width and wetlands that occurred on both sides of one of these channels were generally labeled as the same wetland. Page 6 ESA Adolfson June 2011 South Deschutes County Local Wetland Inventory Report C7 J • 21 B If's SIP 19 PEME PEMA 98 f' 24 ~PEM P'1i11 'L PEMY t'"'O"'~\ _ Example A: Wetland 98 is greater than 0.5 acre Example B: Wetlands 20 and 22 are typical and not within 50 feet of another wetland. features along the Deschutes River. Wetlands 96 and 97 (Example Q are typical features of the Little Deschutes River floodplain that contain relic and current oxbows as well as upland hummocks. The breaks between these large, continuous features were often roadways or a narrowing of the feature. i r",9e- .1 --v.-_._ PSSE 96 Narrowing' between 76 raac 76 and 77 SS 221 DO ~aiitlC} Unnamed roadway !rv - , r FEW LITTLE DESCHUTES RIVER vw raac 4 97 MDR& P r' wetlandtk Example C: Wetlands 96 and 97 are large Example D: The dividing point between wetlands features along the Little Deschutes River and 76 and 77 is a narrowing east of Aspen Place. are separated b an unnamed road. Wetlands that were separated by a roadway and that were deemed hydrologically connected were assigned a letter after the unique numeric identifier to indicate the wetlands were considered sections of one wetland unit (Examples E and F). ESA Adolfson June 2011 Page 7 South Deschutes County Local Wetland Inventory Report k 13 a ¢ i ~ J PW ( L _J 13b BI - G BUCK'LN _ --Wetland/Upland SP9A 50a, ~O1 - F Sob FISHEfUN' SP 12A isalc , . PFD 51 Example E: Wetland 13 has four sections that Example F: 50a and 50b are connected by a are separated by roadways but hydrologically culvert, but no culvert was observed between 49 connected via culverts. and 50a-b or 51 and 50a-b. Wetlands 49 and 51 are more than 50 feet away from 50a-b. r, u Wetlands that extend beyond the study area boundary were digitized to reflect only the area within the study limits. In some cases a wetland extends in and out of the study area resulting in two or more seemingly separate polygons; however, these polygons are considered one unit since they were on-site portions of a larger off-site wetland. Previously delineated or determined DSL wetland delineations within the study area were field verified and edited if the current size was found to be different from the recorded i size. 3.4.2 Probable Wetlands Areas that appeared to meet wetland criteria but were less than 0.5 acre within the study area were digitized as a point and recorded as a "probable wetland" (PW), as defined by OAR 141-086-0200. In some cases, a PW represents a small portion of a larger wetland that is located outside of the study area. 3.4.3 Wetland/Upland Mosaics Wetlands with upland inclusions were identified on the maps as "wetland/upland mosaics." Wetland/upland mosaics are classified as a "landscape where wetland and non-wetland components are too closely associated to be easily delineated or mapped separately." Also the microtopography consists of, "ridges and hummocks supporting non-hydrophytic species are often interspersed throughout a wetland matrix having clearly hydrophytic vegetation, hydric soils, and wetland hydrology," (Corps, 2010). A majority of the wetland/upland mosaics occurred on the floodplains of the Deschutes River, Little Deschutes River Fall River, Long Prairie Slough, and Paulina Creek. In most cases, we had minimal field access to these large wetland mosaic features. However, we observed an interspersion of wetland and upland habitats in each of the • floodplain areas. In other cases a wetland was considered a mosaic due to uneven Page 8 ESA Adolfson June 2011 South Deschutes County Local Wetland Inventory Report • excavation and fill within a degraded wetland. Aerial imagery was used in conjunction with field investigations to aid in determinations of wetland/upland mosaic conditions. Site-specific causes for designation as a wetland/upland mosaic are provided on the wetland summary sheets (Appendix D). 3.4.4 Sample Plots Sample plots (SP) were established for each wetland (except wetlands on file with DSL) and for areas that appeared to have wetland characteristics. There were several deviations from this method related to wetland size. When there were many wetlands within a small area and the wetlands exhibited similar wetland characteristics, one sample plot was used to represent characteristics in all of the wetlands. Additional sample plots were established in larger wetlands when necessary to describe variable habitats. Sample plots located in upland areas were established based on the original assessment units to confirm that upland conditions were present. Refer to Appendix C for wetland determination forms. Sample plots were not established for wetlands for which no access was granted if these wetlands were not visually accessible from rights-of-way. 3.4.5 Guidance on How to Find Sample Plot Data and Other Information For landowners and other users interested in finding sample plot data for a particular parcel, use the following steps: • Step 1) Go to the Local Wetland Inventory Index Maps and the appropriate location based on the sub-area maps (e.g. Map B.2). Step 2) Pull-up the sub-area map (e.g. B.2) to identify the unique wetland code (in this example Wetland 5) and corresponding sample plot number(s) (e.g. SP 201). Step 3) Using the sample plot number (e.g. SP 201), find the corresponding wetland determination form in Appendix C based on that sampling point (e.g. SP 201). The sample plot symbol (SP 201) on Map B.2 is located in the right-of-way because access permission was not granted for the parcel and observations of the wetland were made from the side of the road. The property owner or interested user may also obtain additional wetland information by reviewing the corresponding Wetland Summary Sheet from Appendix D. In this example, one would look for Wetland Code 5 for the appropriate Wetland Summary Sheet. 3.5 Overview of Oregon Rapid Wetland Assessment Protocol The functions and values of each wetland in the study area were assessed using ORWAP. The ORWAP was developed to rapidly and qualitatively assess the functions and values of all types of wetlands throughout the state of Oregon. ORWAP is intended to be • completed by wetland professionals and was designed for planning and educational purposes. The methodology, as outlined in The Manual to the Oregon Rapid Wetland ESA Adolfson Page 9 June 2011 South Deschutes County Local Wetland Inventory Report Assessment Protocol (version 2.0) (Adamus et al., 2009), consists of a series of questions with multiple-choice responses. The questions cover a wide variety of features that can be observed rapidly when visiting a wetland or in some cases, obtained from aerial imagery or other sources. These particular questions were designed to correlate with the relative levels of various functions that a wetland can perform and the values associated with those functions. After a user answers all the questions, ORWAP uses the responses to automatically compute a score for each function and its value. "Functions" are actions that wetlands naturally perform, like hold floodwater, purify stormwater runoff, and provide waterfowl habitat (to name a few). Not all wetlands perform the same function equally. For example, some wetlands provide thermoregulation (i.e. temperature control), while others do not. The responses to ORWAP provide a relative index to quantify how well a wetland performs a given function. For example, water storage (if that function occurs in a given wetland) may be valued much more highly if buildings downstream are at risk of river flooding, because storage of water in wetlands located upstream can lessen the risk of those buildings being flooded. In contrast, the value of the wetland's flood storage function might be considered less if there are no buildings downstream. Thus, as long as a function is being performed at some minimum level, its function and value scores are independent of each other. Function scores are mostly driven by physical and biological features in and around a wetland. In contrast, value scores are driven in by socioeconomic features located upslope and/or downslope of the wetland, or in some cases depend on whether social institutions have assigned a special designation to the particular wetland, its species, or the wetland type. ORWAP evaluates each wetland for the following functions and values: 1) water storage (WS), 2) sediment retention and stabilization (SR), 3) phosphorous retention (PR), 4) nitrate removal (NR), 5) thermoregulation (T), 6) carbon sequestration (CS), 7) organic matter export (OE), 8) aquatic invertebrate habitat (INV), 9) anadromous (FA) and non-anadromous fish habitat (FR), 10) amphibian and reptile habitat (AM), 11) waterbird habitat including feeding (WBF) and breeding (WBN), 12) songbird, raptor, and mammal habitat (SBM), 13) pollinator habitat (POL), 14) native plant diversity (PD), 15) wetland sensitivity, (Sens) 16) wetland ecological condition, (Cond) 17) wetland stressors, (Stress) 18) public recognition and use (PUv), and • 19) provisioning services (PSv). Page 10 ESA Adolfson June 2011 South Deschutes County Local Wetland Inventory Report • ORWAP scores for both functions and values are expressed on a scale of zero to 10. However the range of scores for each function or value across a group of assessed wetlands will vary. While ideally or theoretically each function or value score may range from zero to ten actual real world conditions may rarely combine to result in scores that cover the entire range. Because of the diversity of functions and values and the sometimes contradictory factors that control them, no "overall" or "average" wetland score is given. While ideally or theoretically each function or value score may range from zero to 10, actual real world conditions may rarely combine to result in scores that cover the entire theoretical range. Individual function or value scores may be compared relative to that particular function or value score across the assessed wetlands. This provides a relative basis to distinguish among assessed wetlands but the scores should not be interpreted on an absolute scale of zero to ten, nor as a direct comparison or ranking between functions or values. It is rare for any given wetland to be considered "perfect" for any single function, let alone for all or most of the 16 separate functions in the ORWAP methodology. To get an idea how wetlands in Oregon generally score for functions and values, a user can compare scores from a particular wetland with those from scores calculated for 221 wetlands of all types throughout Oregon during ORWAP field testing. The state-wide results are summarized in the excel spreadsheet ORWAP_SuppInfo file, AllSites tab, availablefrom the DSL web site: 40 http://www.oregonstatelands.us/DSLAVETLAND/or wet prot.shtml. Navigate to the ORWAP Supplemental Information link to open or download the file. A common misperception is that only pristine or unaltered wetlands are highly functioning. Although it is true that pristine wetlands usually provide valuable functions, other wetlands can also be highly functioning. For example, impounding water by placing small berms or dikes in an otherwise unaltered but seasonally dry wetland may enhance water storage functions and habitat for nesting waterfowl, although perhaps at some cost to other wetland functions such as anadromous fish habitat. 3.5.1 ORWAP Methods A majority of wetland assessments were completed during the May 2010 field visit. All wetlands with access permission were assessed on-site. When permission was not granted, wetlands were assessed off-site with visual access from a public right-of-way or adjacent parcels in combination with aerial imagery. In cases where no public or view access existed, wetlands were assessed using current aerial photographs and other existing data compiled for the LWI as well as the wetland scientists' experience with similar conditions. After field efforts were completed, the data were entered into an ORWAP template spreadsheet, which contains formulas that simultaneously process and display data from all 114 wetlands. J0 ESA Adolfson Page 11 June 2011 South Deschutes County Local Wetland Inventory Report 4.0 RESULTS 4.1 Wetlands ESA identified and recorded 114 wetlands within the study area totaling 3,459 acres. Summaries of the 114 mapped wetlands and tax lots for each wetland are provided in Appendix D. Acreages for each wetland are presented in Table 1. Additionally, 71 probable wetlands (PW) and 29 artificial wetlands were identified and mapped for the study area. Refer to Attachment 1 for the LWI index and individual maps. A glossary of terms to aid in review of the LWI maps is provided in Appendix E. Table 1. Summary of Wetlands in the South Deschutes County LWI Wetland Code Size (acres) Wetland Code Size (acres) 1 3.5 58 0.9 2 1.0 59 2.2 3 12.7 60 3.9 4 2.2 61 2.1 5 8.0 62 3.1 6a-b 0.6 63 10.4 7 0.7 64 2.0 8 1.1 65 0.7 9 6.8 66 1.4 10 9.2 67 0.8 11 3.8 68 0.3 12 2.2 69 39.1 13a-d 0.7 70 0.6 14 9.8 71 a-b 0.5 15 4.3 72 0.9 16 2.0 73 46.8 17 2.5 74a-c 94.9 18 10.7 75 0.7 19 2.3 76 72.7 20 3.7 77 23.4 21 7.8 78 0.5 22 4.5 79 142.2 23 1.1 80 91.6 24 3.0 81 17.3 25 5.0 82 10.4 26a-b 2.5 83 93.7 27a-c 12.1 84 7.9 28a-b 1.8 85 32.0 29a-c 5.8 86 95.2 30 1.7 87a-b 41.1 31 0.8 88 1.4 32 1.4 89 85.0 33 3.7 90 65.5 34 4.3 91 2.9 35 2.5 92a-b 48.8 36 2.4 93a-b 340.0 Page 12 ESA Adolfson June 2011 • Cj s South Deschutes County Local Wetland Inventory Report • • • Wetland Code Size (acres) Wetiand Code Size (acres) 37 1.9 94 104.1 38 2.3 95 69.1 39 1.8 96 82.3 40 3.5 97 64.3 41 34.0 98 7.7 42 34.8 99 232.7 43a-e 32.3 100a-b 15.0 44 12.3 101 1.2 45 21.0 102 2.3 46 25.3 103a-b 200.4 47 2.8 104a-b 1.2 48 27.4 105 97.2 49 1.5 106 159.3 50a-c 14.8 107 100.4 51 3.4 108 48.0 52 2.4 109 112.8 53 4.2 110 221.0 54 36.8 111 8.6 55 4.0 112 15.3 56 8.5 113 78.0 57 0.9 114 31.0 TOTAL 3,458.9 4.2 Deepwater Habitat There is no deepwater habitat within the South Deschutes County study area. 4.3 Artificially Created Wetlands Twenty-nine (29) artificially created wetlands were found in the study area; three stormwater treatment ponds, two irrigation channels, two excavated ponds, three golf course ponds, two fish hatchery ponds, one landscape pond, eleven stock ponds, two dammed ponds, and three other ponds. Artificially created wetlands may or may not be state or federally jurisdictional. 4.4 Summary of Probable Wetlands (PWs) Seventy-one (71) probable wetlands (PWs) were mapped within the study area. Probable wetlands appeared to have wetland characteristics but were either less than 0.50 acre or were small and of an undetermined size. PWs may or may not be state or federally jurisdictional. 4.5 ORWAP Results ORWAP summary statistics are presented in Table 2 (functions) and Table 3 (values) below. The median of a list of numbers can be found by arranging all the observations ESA Adolfson June 2011 Page 13 South Deschutes County Local Wetland Inventory Report from lowest value to highest value and selecting the number in the middle position. If there is an even number of observations, the median is defined as the average of the two middle values. The 75th percentile is the score for which 75 percent of the wetlands scored lower and only 25 percent higher. The 90th percentile is the score for which 90 percent of the wetlands scored lower and only 10 percent higher. ORWAP raw data results for wetlands in the study area are located in Appendix F. Summary scores for the individual site functions and values are shown in Appendix G. The summary statistics indicate that most wetlands in the Upper Deschutes are currently capable of performing all functions commonly attributed to wetlands except for Anadromous Fish Habitat and Waterbird Nesting Habitat (Table 2). Lack of the former is due simply to lack of access to the project area by anadromous fish, and lack of the latter is due to scarcity of large wetlands that remain ponded throughout the summer. Waterbirds do nest in riverine wetlands along the Deschutes River within the study area, but even this nesting is very limited. Table 2. Summary Statistics for Function Scores of South Deschutes County Wetlands (n=114) Functions Median Min Max 75TH percentile 90 TH percentile Water Storage & Delay (WS) 2.52 0.00 6.00 3.05 3.70 Sediment Retention & Stabilization (SR) 4.40 2.58 10.00 5.08 6.47 Phosphorus Retention (PR) 4.47 1.94 10.00 4.88 7.74 Nitrate Removal & Retention (NR) 3.85 2.81 10.00 4.54 5.43 Thermoregulation (T) 3.00 0.00 5.83 3.61 4.42 Carbon Sequestration (CS) 2.24 1.41 3.95 2.39 2.78 Organic Matter Export (OE) 6.61 0.00 8.58 7.12 7.60 Aquatic Invertebrate Habitat (INV) 4.82 2.68 7.07 5.34 5.85 Anadromous Fish Habitat (FA) 0.00 0.00 0.00 0.00 0.00 Non-anadromous Fish Habitat (FR) 3.25 0.58 7.69 4.26 4.77 Amphibian & Reptile Habitat (AM) 3.72 1.83 6.87 4.10 5.90 Waterbird Feeding Habitat (WBF) 3.93 2.15 5.98 4.33 4.63 Waterbird Nesting Habitat (WBN) 0.00 0.00 5.51 2.09 4.26 Songbird, Raptor, & Mammal Habitat (SBM) 3.98 2.14 5.79 4.84 5.15 Pollinator Habitat (POL) 5.79 3.19 7.36 6.52 7.05 Native Plant Diversity (PD) 4.49 2.63 5.58 4.89 5.16 Note: Functions with a high median score are shown in bold. r~ • Page 14 ESA Adolfson June 2011 South Deschutes County Local Wetland Inventory Report • High scoring functions include: Organic Matter Export, Aquatic Invertebrate Habitat, and Pollinator Habitat. Some functions show relatively little variation among the project wetlands (e.g., Carbon Sequestration, Native Plant Diversity), while others vary considerably (e.g., Nitrate Removal, Organic Matter Export). Table 3 includes a summary of the values scores for the 114 wetlands evaluated. Table 3. Summary Statistics for Value Scores of South Deschutes County Wetlands (n=114) • Note: Values with a high median score are shown in bold. Values Median Min Max 75r" percentile 90 TH percentile Water Storage & Delay (WS) 6.46 1.25 7.29 6.46 7.29 Sediment Retention & Stabilization (SR) 6.09 3.25 8.19 7.44 7.83 Phosphorus Retention (PR) 6.18 3.03 6.99 6.51 6.68 Nitrate Removal & Retention (NR) 5.12 3.37 5.75 5.35 5.56 Thermoregulation (T) 3.33 0.00 3.33 3.33 3.33 Aquatic Invertebrate Habitat (INV) 7.00 3.54 7.69 7.00 7.00 Anadromous Fish Habitat (FA) 3.93 2.15 5.98 4.33 4.60 Non-anadromous Fish Habitat (FR) 3.33 1.75 7.48 6.95 7.14 Amphibian & Reptile Habitat (AM) 4.00 0.67 7.33 4.00 7.33 Waterbird Feeding Habitat (WBF) 6.00 0.67 10.00 6.00 10.00 Waterbird Nesting Habitat (WBN) 4.00 0.50 7.33 4.00 5.50 Songbird, Raptor, & Mammal Habitat (SBM) 6.00 1.00 6.00 6.00 6.00 Pollinator Habitat (POL) 1.94 0.00 10.00 10.00 10.00 Native Plant Diversity (PD) 6.00 2.91 6.87 6.00 6.23 Public Use & Access (PUv) 1.67 0.00 4.00 2.33 3.33 Provisioning Services (PSv) 0.00 0.00 2.00 2.00 2.00 Ecological Condition (Cond) 5.10 2.16 7.41 5.73 6.90 The functions which ORWAP indicates are currently of highest value in the project area are: • Aquatic Invertebrate Habitat, • Water Storage & Delay, and • Phosphorus Retention. • ESA Adolfson June 2011 Page 15 South Deschutes County Local Wetland Inventory Report The value of some functions varies little among the project wetlands (Nitrate Removal & Retention) while the value of others shows large spatial variation (Amphibian and Reptile Habitat, Waterbird Feeding Habitat). 4.6 Goal 6 Water Quality Resources Several considerations are pertinent to deciding which wetland sites identified in the South Deschutes County LWI could be candidates for a Goal 6 Water Quality Resource (WQR) designation: 1. Which function or functions should be the basis for this designation? Should all functions be weighted equally? 2. To what extent should the current values of these functions be considered? 3. What should be the score threshold(s) that determines whether a particular site should be nominated as a Goal 6 Water Quality Resource? ESA recommends that the Nitrate Removal function of wetlands be used as one of the principal determinants of site nomination for Goal 6 Water Quality Resource protection, with other functions used as secondary determinants, because nitrate contamination has been identified as a primary concern in the project area (Hinkle et al., 2007). Refer to the discussion on groundwater quality in Appendix H for more information. Specifically, we recommend that Goal 6 Water Quality Resources be those sites that meet any of the following three criteria: Criterion 1. Nitrate Removal (NR) function score is equal to or greater than the 90th percentile of the scores for this function among all wetlands in the project area (i.e., 5.43); AND/OR Criterion 2. Nitrate Removal (NR) function score is equal to or greater than the 75th percentile of the scores for this function among all wetlands in the project area (i.e., 4.54), AND the NR value score of the site is greater than the 75th percentile of the NR value score among all wetlands in the project area (i.e., 5.35); AND/OR Criterion 3. The wetland's score for at least 3 other wetland functions are greater than or equal to the 90th percentile for those functions in the project area. Based upon the above criteria, the analysis results in the following wetlands potentially designated as a WQR wetland in South Deschutes County: 1. Sites that meet Criterion 1 (12 sites): 3, 10, 13a-d, 21, 23, 26a-b, 27a-c, 28a-b, 29a-c, 75, 98, and 103a-b; 2. Sites that meet Criterion 2 (5 sites): 23, 36, 88, 105, and 106; 3. Sites that meet Criterion 3 (18 sites): 42, 63, 64, 65, 66, 67, 68, 69, 81, 82, 83, 84, 93a-b, 100a-b, 102, 109, 111, and 113. A summary of the high scoring • Page 16 ESA Adolfson June 2011 South Deschutes County Local Wetland Inventory Report • functions for the wetlands that meet Criterion 3 is provided in Table G4, Appendix G. Application of these three criteria results in potential designation of 35 sites, which is 30 percent of all wetlands in study area. Limitations of the ORWAP Analysis Although ORWAP represents a significant technical advance over OFWAM (the method previously prescribed for use in Local Wetland Inventories in Oregon) and other methods for assessing wetland ecosystem services, like most rapid assessment tools, it does have several limitations. These are detailed in the ORWAP Manual (Adamus et al. 2009b), which may be found on-line at: http://www.oregonstatelands.us/DSL/WETLAND/or_wet_prot.shtml. The most significant limitations of ORWAP are: 1. ORWAP is not a mechanistic model of ecosystem processes and thus cannot be expected to account for many interactions and feedbacks among important variables. ORWAP uses only the variables that can be observed easily, but factors that control many functions are unobservable except with sophisticated equipment and long-term expensive sampling. 2. Like all rapid assessment methods for wetlands, ORWAP has not been • validated against actual measures of the functions it estimates. 3. ORWAP is intended to simply be an estimate of function effectiveness averaged over an entire wetland assessment unit. For most functions, ORWAP does not account for wetland size, but size should be taken into account in some manner when proposing candidate sites (wetland assessment units) for WQR status. Determining the boundaries of wetland assessment units (not the boundary between wetland and upland) has a subjective component. Despite guidance in the ORWAP manual, decisions of whether and where to divide two hydrologically connected wetlands into multiple units for purposes of applying ORWAP are sometimes subjective. 5.0 LIMITATIONS This report documents the investigation, best professional judgment, and conclusions of the investigators. It is correct and complete to the best of our knowledge and based upon the conditions observed during field work conducted in the spring and summer of 2010. Mapping provided should be considered a preliminary inventory map of wetlands and other waters and used for planning purposes only. A formal wetland delineation reviewed and approved by DSL is required for state removal-fill permits. Contact the DSL or Corps with any regulatory questions. E ESA Adolfson Page 17 June 2011 South Deschutes County Local Wetland Inventory Report 6.0 LITERATURE CITATIONS Adamus, P., J. Morlan, and K. Verble. 2009. Manual for the Oregon Rapid Wetland Assessment Protocol (ORWAP). Version 2.0. Oregon Dept. of State Lands, Salem, OR. hqp://oreg_onstatelands.us/DSL/WETLAND/or wet prot.shtml Adamus, P., J. Morlan, and K. Verble. 2009. Oregon Rapid Wetland Assessment Protocol (ORWAP): calculator spreadsheet, databases, and data forms. Oregon Dept. of State Lands, Salem, OR. http://oregonstatelands.us/DSLAVETLAND/or wet prot.shtml Cowardin, L.M., V. Carter, F.C. Golet, and E.T. LaRoe. 1979. Classification of Wetlands and Deepwater Habitats of the United States. FWS/OBS-79/31. U.S. Fish and Wildlife Service. ed. J. S. Wakeley, R. W. Lichvar, and C. V. Noble. ERDC/EL TR-08-28.Environmental Laboratory. 1987. Corps of Engineers Wetlands Delineation Manual. Technical Report Y-87-1. U.S. Army Engineer Waterways Experiment Station, Vicksburg, MS. Franklin, J. F. and C. T. Dyrness. 1988. Natural Vegetation of Oregon and Washington. Oregon State University Press. Corvallis, Oregon. Google Earth. 2010. Aerial imagery of the Deschutes County vicinity. Available at: hqp://earth.g_oO lg e.com. • Hinkle, S.R., Morgan, D.S., Orzol, L.L., and Polette, D.J. 2007. Ground water redox zonation near La Pine, Oregon-Relation to River Position within the Aquifer- Riparian Zone Continuum. U.S. Geological Survey Scientific Investigations Report 2007-5239. Natural Resources Conservation Service (NRCS). 1992. Oregon Soil Survey Data for Upper Deschutes River Area, Oregon., including parts of Deschutes, Jefferson, and Klamath, Counties Soil, Oregon. Available: http://www.or.nres.usda.gov/pnw_soil/or_data.html.Last updated: February 10, 2010. Accessed: March 20, 2011. Oregon Department of Environmental Quality (DEQ). 2004/2006.2004/2006 Section 303(d) List, Integrated Report. Portland, Oregon. Available at: http://www.deq.state.or.us/wq/assessment/rpt0406/search. asp.Rempel, M., P. Adamus, and J. Kagan. 2009. Oregon Wetlands Explorer: an internet tool for ORWAP wetland assessment support and data archiving. Oregon State University Library and Institute for Natural Resources, Oregon State University, Corvallis, OR. hlW://oregoneUlorer.info/wetlands/orwat/ Rich, Barbara et. al., in collaboration with Deschutes County Environmental Health Division, Oregon Department of Environmental Quality and US Geological Survey. Undated. La Pine National Decentralized Wastewater Treatment Demonstration Project, 1999 - 2005. State of Oregon. 2010. Department of State Lands, Division 86, Wetland Conservation Plan. Local Wetlands Inventory (L WI) Standards and Guidelines OAR 141-086- 0180 through 141-086-0240. Available: http://arcweb.sos.state.or.us/rules/OARS 100/OAR 141/141 086.html • Page 18 ESA Adoljson June 2011 South Deschutes County Local Wetland Inventory Report • State of Oregon. 1996. Department of State Lands, La Pine/Wickiup Junction Local Wetland Inventory. Compiled by Martin Sehott, Ph.D. and Jay Lorenz, Ph.D. US Army Corps of Engineers (Corps). 2008. Regional Supplement to the Corps of Engineers Wetland Delineation Manual: Arid West Region (Version 2.0). U.S. Army Corps of Engineers (Corps). 2010. Regional Supplement to the Corps of Engineers Wetland Delineation Manual: Western Mountains, Valleys, and Coast Region (Version 2. 0), ed. J. S. Wakeley, R. W. Lichvar, and C. V. Noble. ERDC/EL TR-10-3. Vicksburg, MS: U.S. Army Engineer Research and Development Center. U.S. Census. 2000. Search Deschutes County, Oregon Quick Facts. http://quickfacts.census.gov/gfd/states/41/41017.htm1. Last Updated: August 16, 2010. Accessed: September 27, 2010. U.S. Fish and Wildlife Service (USFWS). 2010. National Wetlands Inventory. Available: http://www.fws.gov/wetlands/. Last updated: January 22, 2010. Accessed: April 2010.Vicksburg, MS: U.S. Army Engineer Research and Development Center. U.S. Geological Survey (USGS). 2007. Ground Water Redox Zonation near La Pine, Oregon: Relation to River Position within the Aquifer-Riparian Zone Continuum, Scientific Investigations Report 2007-5239, • • ESA Adolfson Page 19 June 2011 South Deschutes County Local Wetland Inventory Report • APPENDIX A: FIGURES 0 0 ESA Adolfson June 2011 Appendix A a Sunriver `~~t sunnwEr ` f Avport e KLA* Little Deschutes River L O' Lo"KAUM Bt ~Riv1 Fall River . O ax"T ~ 6U Iff.l,y! N; Deschutes River . _-1 fND OTAIN - ss ~yrlt j t i La Pine La e ` Deschutes ! - I National Forest r Wickiup Reservoir , Burgess Rd MQQUP autrl~ i i i' NAN BUT 1 FATON eY!"1E W OilC ST r I Legend ASTEA t Q Study Area a7 a l t - a7 Il _ , eaacAVa t 0 150 300 Miles SOURCE: ESRI, 2009. 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I N DI I - I I - ` ' 1 W I A AI I `I ll1~ ~NI NI ~ 0 Z to o 0r 0 r (n c Z c r < d (n 0 r 0 2 x o' O7. 7 Q. 0 :3 c a? a o o `D z v m m Q j CL n F)' CD 11 7 v n 7 n N Q ° a cn' CI C Q o m m 9 7 N CL X co ' 1;2 D o a1 s = v 0) 3 3 a y n c_ CD C N N z v -n rt U) ~ N v x M o r.Ipl D 0 _ :3 r , ~ m r* 0 Q Appendix A Figure 3 Deschutes County Soil Inventory Soil Map Unit Legend • Map symbol and Component Percent Landform Hydric Hydric map unit name of map rating criteria unit 29A: Cryaquolls 85 Flood plains Yes 2133 Cryaquolls, 0 to 3 percent slopes 114C: Shanahan 90 Lava plains No Shanahan loamy coarse sand, 0 to 15 Cryaquolls 1 terraces Yes 2133 percent slopes 114D: Shanahan 90 Hillslopes No Shanahan loamy coarse sand, 15 to 30 percent slopes 115A: Shanahan, low 90 Lava plains No hanahan loamy coarse nd, low, 0 Cryaquolls 1 Terraces Yes 2133 to 3 percent slopes 130D: Steiger, high 85 Hillslopes No Steiger loamy coarse sand, elevation high elevation, 15 to 30 percent slopes 130E: Steiger, high 85 Hillslopes No Steiger loamy coarse sand, elevation high elevation, 30 to 50 percent slopes 144A: Sunriver 85 Stream terraces No Sunriver sandy loam, 0 to 3 Cryaquolls percent 8 Mountains Yes 2133 slopes 153A: Tutni 85 Stream terraces No Tutni loamy coarse sand, 0 to 3 percent slopes Cryaquands, 5 Stream terraces Yes 2133 very poorly drained W: Water Water 100 No 1 1 South Deschutes County Local Wetland Inventory Report APPENDIX B: STAFF QUALIFICATIONS 0 40 ESA Adolfson June 2011 Appendix B ESAdln CATHERINE CONOLLY, PWS Wetlands Program Manager Cathie brings over 20 years of experience in the environmental field to her role as Project Director for this project. She has experience with projects ranging from Environmental Assessments and Biological Assessments, to wetlands inventories, to Critical Areas Code updates. Cathie has managed large project teams including sub-consultants, and knows how to provide the oversight to bring projects in on time and in budget. She has provided quality control and assurance for projects over 10 years. Relevant Experience Education M.S., Botany 1993, University Wetland Inventory, City of Newcastle, Washington. Project Manager Cathie of Washington is the project manager of this on-call environmental services contract. The first B.S., Botany 1984, University task was the preparation of a wetlands inventory for the City of Newcastle, of Washington which included air photo interpretation and ground-truthing. A representative Natural Science and Outdoor Education 1980, Outdoor sample of city wetlands were evaluated using the Washington State Department University of Vermont of Ecology Wetlands Rating System for Western Washington (2006). Thirty- five wetlands were identified in the City, and 16 were rated by both the current Registrations/Certifications (2004) Washington Department of Ecology rating methodology and the 1993 • Professional Wetland rating methodology. Scientist, Society of Wetland Scientists, Certified Wetland Specialist, Pierce County Invasive Species and Lake Management Project. Project Pierce County Manager. Cathie was manager of this project for Pierce County Water 24-Hour Hazardous Materials Programs. ESA Adolfson scientists and sub-consultants inventoried over 1,000 Certification Program acres of Pierce County-owned properties to document the presence and Preferred Wetland approximate extent of invasive plant species, concentrating on aquatic, wetland, Consultant, King County. and riparian species. Site-specific information was collected on GPS units, and Washington Department of points and data entered into GIS; GIS information will be linked to an Access Transportation Biological database. ESA Adolfson reviewed existing invasive species management Assessment Qualified Senior Author (February 2007) requirements in a Regulatory Memorandum, and prepared a Gap Analysis. Completed Western Washington Wetlands Rating Tacoma Open Space Habitat and Recreation Plan. Project Manager. Cathie System Training, Department was the project manager for this project for ESA Adolfson. ESA Adolfson of Ecology Coastal Training scientists performed an inventory of open space lands in the City of Tacoma in Program (October 2007) support of the preparation of the Tacoma Open Space Habitat and Recreation 21 Years Experience Plan. The City of Tacoma has partnered with the Tahoma Audubon and the Cascade Land Conservancy, to form the "GreenTacoma Partnership" to coordinate City, non-profit, and volunteer efforts to protect and enhance open spaces within the City. Adolfson staff performed over 300 hours of field time studying open space lands in the city, collecting data on current conditions and use of open space lands, evaluating the restoration potential of the sites. Data was logged with GPS units that tied field data to locations. 0 Catherine Conolly, PWS Page 2 • Relevant Experience (Continued) University of Washington Wetlands Science and Management Certificate Program. Cathie has served on the Advisory Board for this program since its inception (1995). The program was developed to provide a well-rounded education in wetlands issues to regulators, consultants, and concerned citizens. The year-long program provides college-level education in the science and policy implicit in wetlands science. Cathie has served as an instructor for Wetlands Functional Assessment (3 years) and Wetlands Field Botany (11 years). She has also served as advisor to students in the program each year in development of their practicum, where they implement their new skills and knowledge to perform a wetlands project. Wetland Inventory, Swinomish Tribe, Washington. Project Manager. Cathie was project manager for this project. ESA Adolfson conducted a review of existing information and aerial photographs of wetland and stream resources on the Reservation. Cathie worked with the Tribal Community to identify priority sub-basins for immediate ground-truthing, and conducted field verification of estuarine wetlands (by boat) and freshwater wetlands on the approximately 3,000-acre reservation. She assessed the functions and values of the field- verified wetlands by the USFWS classification, and the Hydrogeomorphic (HGM) method. Cathie prepared overlay maps for digitizing in GIS and a technical report on findings. • City of Redmond Habitat Plan, King County, Washington. Project Manager Cathie was manager of this project to inventory and map wildlife habitat remaining in the City, documenting habitat changes from 1996 to 1999. ESA Adolfson developed a standardized rating system to characterize and evaluate habitat, and mapped the wildlife habitats in GIS. A technical report was prepared documenting the findings of the inventory and a policy review with recommendations for strengthening and implementing critical area policies and regulations. ESA Adolfson presented findings and recommendations at public open houses, citizen's advisory committee meetings, professional conferences, and at public hearings for the planning commission. Projects Performed While Working For King County: 1990 Wetlands Inventory Update, King County, Washington. While working for King County, Washington, (area 2,126 square miles). Cathie conducted field verification of wetlands identified from air photos for the 1990 update for the King County Sensitive Areas Map Folio. She prepared mylar overlays on orthophotos including wetland boundaries and classifications for incorporation into county map database. Puget Sound Wetlands and Stormwater Management Study, King County, Washington. Cathie was part of the team of scientists assessing the effects of urban stormwater on lowland Puget Sound wetlands over a 7-year period. She conducted botanical, wetland, and zoological field work. I~ Y c • TERESA H. VANDERBURG Practice Lead, Biological Resources Teresa has 20 years of experience in natural resource management and scientific analyses. She is the Practice Lead for the Biological Resources Group. Teresa is an experienced project manager and has managed environmental permits and mitigation planning for several large-scale public infrastructure projects, including the Seattle Public Utilities Tolt Water Supply Pipeline No. 2 in King County, and the North Fork Clover Creek Regional Detention Pond in Pierce County, Washington. She has reviewed and/or performed hundreds of wetland assessments, delineations, and wetland mitigation projects. Teresa's expertise also includes shoreline master plan (SMP) updates for eight cities and two counties in western Washington. She has also developed critical area ordinances using "best available science" for Tukwila, Kent, Burien, Kenmore, Gig Harbor, Sumner and Tacoma. Teresa also serves as an expert witness in hearings, trials and other legal proceedings. Teresa participated in a Local Government Wetland Advisory Team assisting Washington State Department of Ecology in development of management regulations for wetlands statewide. She also serves as a senior advisor to the University of Washington Wetlands Management Certificate program. Relevant Experience Education • M.S., Environmental Science, Clark County SMP Update, WA. Scientific Lead Clark County and six cities Washington State University therein are working together to update their SMPs. Clark County shorelines B.S., Biology, Eastern include significant waterbodies such as the Columbia River, Lewis River, Kentucky University Vancouver Lake and Washougal River. Teresa is the lead on the shoreline 20 Years of Experience inventory and analysis report which was completed in Draft form for Ecology review in June 2010. Teresa has coordinated with the Technical Advisory Registrations/certifications Committee and Shoreline Stakeholder Advisory Committee on technical issues Jurisdictional Delineation of Wetlands in the Pacific regarding shoreline jurisdiction, GIS analysis, scientific data and creation of the Northwest, National Wetlands map folio. Three draft inventory reports were prepared and reviewed by Science Training Cooperative stakeholders in the spring. Teresa has also supervised completion of the Draft (1990) Restoration Plan during this same time frame and coordinated completion of a Certified Wetland Biologist, Pierce County (current) summary table for development of the preliminary shoreline environment designations for the County. Society of Wetland Scientists, Professional Wetland Scientist (PWS) City of Auburn Wetland and Stream Inventory, WA. Project Manager. Teresa conducted an inventory of stream and wetland resources on Professional Affiliations approximately 14,550 acres within the City limits of Auburn, Washington. The Society of Wetland Scientists inventory updated information from an earlier wetland inventory. Work included Ecological Society of America comprehensive field reconnaissance work, wetland descriptions, stream Senior Advisor for the UW classifications, GIS maps and associated metadata and a summary technical Wetland Management report. Historical permit information from approximately 90 historical permit Certificate Program files was incorporated into the GIS metadata and maps to allow the City to track past permit activities by parcel. C J Teresa Vanderburg, PWS Page 2 Relevant Experience (Continued) Marysville UGA Wetland and Stream Inventory, WA. Project Manager. Teresa managed an extensive inventory of wetlands, streams, and habitat in an approximately 2,000-acre area in the Lakewood-Smokey Point region of Marysville's Urban Growth Area. The project was undertaken to evaluate lands to be annexed into the city for residential, commercial and industrial development. The study included wetland descriptions and functional evaluations, descriptions of stream habitat, documentation of fish presence or absence, and water quality testing. Other elements of the study included assessment of future build-out conditions within the planning sub-area and evaluating potential mitigation concepts. Prepared a wetland and stream inventory report, including field maps and habitat data, for review and approval by both the City of Marysville and the Washington Department of Ecology. City of Kenmore Gap Analysis, Review of Endangered Species Act Compliance, WA. Scientific Lead. Teresa served as Task Lead for this "gap analysis" for the City of Kenmore to identify potential gaps and deficiencies in City codes, regulations, plans and policies in relation to the Endangered Species Act. This report will specifically address the local jurisdiction requirements in the Final 4(d) Rule by National Marine Fisheries Services (NMFS) for protecting and avoiding "take" of Puget Sound chinook and other federally- listed fish. ESA is reviewing sensitive areas ordinances, the Comprehensive Plan, stormwater regulations and road maintenance standards and practices for ESA compliance. Also part of this work is to review the Tri-County Proposal (King, Snohomish and Pierce Counties) for compliance with the 4(d) rule and discuss the differences between this proposal and Kenmore's current practices and plans. A list of recommendations for "next-step" items is currently being developed to guide the City in its response to NMFS regarding salmon protection and recovery. PG& E Gas Transmission Pipeline Expansion, ID, WA, OR. Project Manager. Teresa managed technical studies for rare plants, wetlands, habitats, noxious weeds and stream crossings for a proposed 250-mile long natural gas transmission line expansion project. The project included expansion of the transmission pipeline right-of-way as well as upgrades to several Main Line Valves and Compressor Stations. The project extended from the Canadian border through Idaho, eastern Washington and eastern Oregon. Teresa managed data collection and field biologists tasked with the identification and mapping of rare plants, noxious weeds, wetland boundaries, and streambanks using hand held GPS units. In addition, rare plant locations were identified and marked as were noxious weeds and general vegetation habitat types. Work products included preparation of two resource reports to the Federal Energy Regulatory Commission (FERC) and a set of supporting maps documenting the location of biological and water resources in the project area. L' ESAt TOM MCGUIRE Portland Office Director Tom has over 20 years experience in environmental planning, resource management, policy development, and land use and environmental permitting. He has a diverse background and experience in all phases of natural resource evaluation and protection. Tom specializes in interpreting and writing complex land use and environmental planning regulations and has extensive experience working with Oregon Statewide Planning Goals, Washington Growth Management Act, NEPA, NPDES, FEMA, and ESA. Tom also has extensive experience conducting natural resource inventories and wildlife habitat assessments. He is an accomplished project manager with excellent working relationships with local, state, and federal agency staff in Oregon and Washington. Relevant Experience Education Masters of Urban and Local Wetland Inventory for City of Lakeview, OR. Project Manager. Tom Regional Planning, Emphasis in Environmental Planning, was ESA's project manager for a Local Wetland Inventory for the City of Portland State University Lakeview, Oregon. The inventory included identifying and mapping wetlands (1989) within the urban growth boundary, wetland functional assessments, and B.S., Geography- designating significant wetlands as required by statewide land-use planning Goal • Environmental Studies, Minor in Plant Ecology, University of 5. Tom worked with the City of Lakeview to develop a regulatory program for Iowa wetland protection in compliance with state requirements. He also attended 20 Years of Experience. public meetings and Planning Commission and City Council hearings. Goal 5 Planning, Multnomah County Drainage District, Portland, OR. Project Manager. Tom worked with the Multnomah County Drainage District #1 and two other stakeholders, the Columbia Corridor Association and the Port of Portland, to determine possible approaches to Goal 5 compliance within the Columbia Slough Watershed. Tom helped the three stakeholders determine the most effective and efficient ways to reduce their compliance burden in the Metro Regional Goal 5 process and the compliance projects of the Cities of Portland, Fairview, Wood Village, Troutdale, and Gresham. Tom prepared an action plan detailing the options available, created a timeline, and recommended a course of action necessary for implementing the preferred compliance strategy. Goal 5 Economic, Social, Environmental, and Energy (ESEE) analysis and program, Forest Grove, OR. Project Manager. Tom provided natural resources planning services related to the development of an economic analysis and regulatory program to comply with Oregon State Planning Goal 5 and to be consistent with the Tualatin Basin program. He first compiled information and performed a Geographic Information System (GIS) analysis for the economic, social, environmental, and energy (ESEE) analysis portion of the Goal 5 project. Tom assisted Forest Grove City staff in assessing site specific areas for adjustment of the Goal 5 "limit" decisions-looking at four sites in particular. He also worked with the City staff to develop codes and regulations for their 40 Goal 5 program. Tom McGuire Page 2 • Relevant Experience (Continued) Environmental Assessment and Permitting, Tualatin Valley Water District Water Supply Improvement Program, Clackamas and Washington Counties, OR. Project Manager. Tom was project manager for a project with the Tualatin Valley Water District to conduct an environmental screening of regional pipeline route alternatives. The project includes a new water distribution system pipeline, pump stations, and storage reservoirs and Tom led the effort to identify potential permits and their processes and timelines for each of the alternatives. Environmental issues in the Tualatin Valley that were addressed include potential stream and wetland crossings, local Goal 5 Environmental and Title 3 Water Quality Resource Area ordinances, and the presence of listed species in the vicinity of project construction. Potential land use issues were also evaluated for the full length of the corridor alternatives. Tom prepared a permit matrix identifying the regulatory permits necessary for construction of the various pipeline routes, the permit triggers, permit linkages, level of design needed for application, typical review times, overall schedule estimates, and potential permit obstacles. Results of the preliminary environmental screening were incorporated into the analysis of the alignment alternatives and documented in technical memoranda. Portland Japanese Garden Master Plan, Portland, OR. Project Manager. Tom worked with the Portland Japanese Garden Association and a team of landscape architects to help prepare a comprehensive Master Plan to guide the future growth of the garden. Tom conducted a resource inventory and assessment of the project site that included plant communities, wildlife habitat, geology, soils, water features, and hazards. He also attended workshop and strategy sessions providing detail knowledge of the City of Portland land use and permitting requirements for expansion alternatives discussed. Tom provided technical memorandums covering the assessment of site resources and addressing sustainability and permitting issues for the final three alternatives. Big Four Corners Management Plan, Bureau of Environmental Services, Portland, OR. Project Manager. Tom worked with the Bureau of Environmental Services (BES) to compile existing riparian, wetland, and upland habitat assessment and restoration materials into a comprehensive Big Four Corners Management Plan for a natural resource property purchased with Oregon Watershed Enhancement Board (OWEB) Acquisition Grant funding. Tom reviewed all relevant documents and wrote the management plan with emphasis on a summary of the site inventory and assessment, desired future ecological conditions, management recommendations, and a monitoring strategy. The management plan was submitted to OWEB by BES in October, 2007 to satisfy Acquisition Grant and Conservation Easement requirements. ESAAdoI#son JOHN GORDON Biological Resources Program Manager John is a wetland biologist with over 12 years of experience. He has provided a full spectrum of wetland consulting services in Oregon, Washington, Idaho, Montana, Nevada and Utah. He is a project manager on multidisciplinary projects with wetland, Endangered Species Act and National Historic Preservation Act components. He has extensive experience working with clients in both the public and private sectors, and with natural resource agency scientists. Selected Relevant Experience Education B.S., Biology, Portland State City of Klamath Falls Local Wetland Inventory and Riparian Assessment, University Klamath Falls, Oregon. John was the project manager for the City of Klamath Falls Local Wetland Inventory (LWI) and Riparian Assessment. This is the Selected Training largest LWI in the state, including parts of more than 60 Sections in the study Engineers Army Corps Wetland of Engineers area of over 23,000 acres. John met with City officials and staff from Oregon Delineation Training, 1995. Department of State Lands (DSL), and made presentations at public meetings. Interim Regional Supplement He analyzed aerial photographs and other resources as required in Oregon to the Corps of Engineers Administrative Rules to locate probable wetlands for the preparation of wetland Delineation Manual: preliminary wetland maps. John planned and scheduled work, supervised Arid West Region, 2007. wetland staff in the field to collect accurate inventory data, and participated in Interim Regional Supplement to the Corps of Engineers all aspects of the inventory. He supervised staff in the office to analyze field data wetland Delineation Manual: and produce LWI maps and reports, and provided QA/QC review. This LWI Western Mountains, Valleys, was approved and adopted by the City and DSL. It has been incorporated into and Coast Region, 2008. Oregon's statewide wetland inventory. Oregon Rapid Wetland Assessment Protocol, 2009. City of Gresham Local Wetland Inventory, Gresham, Oregon. John was the Oregon Streamflow Duration Assessment Methodology, project manager for the City of Gresham LWI, with a study area of about 15,000 2009. acres. John met with City officials and DSL staff, and made presentations at Certified consultant for ODOT public meetings. He analyzed resources specified in LWI rules to locate possible Biological Assessment wetlands. He analyzed the sites using the U.S. Army Corps of Engineers 1987 Deliverables, 2007. Wetland Delineation Manual to determine their wetland status. He supervised a Certified ODOT CS3 staff of wetland scientists and cartographers on the project. John and his team Consultant, 2005. evaluated the wetlands with the Oregon Freshwater Wetland Assessment Methodology (OFWAM) to make Locally Significant Wetland determinations, Affiliations and prepared reports and maps to meet LWI standards. Both the City of Member, Society of Wetland Scientists. Gresham and DSL approved and adopted this inventory. Over 12 Years of Experience Oregon Rapid Wetland Assessment Protocol (ORWAP). John was contracted by DSL to conduct preliminary testing of ORWAP on representative wetlands. John served on the DSL Technical Advisory Committee for the development of ORWAP. He received project-specific training from Dr. Paul Adamus, author of ORWAP, prior to conducting the work. 0 John Gordon Page 2 • Relevant Experience (Continued) City of Beaverton Local Wetland Inventory, Washington County, Oregon; City of Vernonia Local Wetland Inventory, Columbia County, Oregon; City of Clatskanie Local Wetland Inventory, Columbia County, Oregon; City of Woodburn Local Wetland Inventory, Marion County, Oregon; City of Silverton Local Wetland Inventory, Marion County, Oregon; City of Oregon City Local Wetland Inventory, Clackamas County, Oregon. On each of these LWIs, John used resources specified in LWI protocols to locate possible wetlands for preparation of preliminary wetland maps. He mapped wetlands and evaluated them with OFWAM to determine if they met standards for Locally Significant Wetlands. He prepared reports and worked with cartographers to prepare maps to meet LWI requirements. These inventories were approved by the respective cities and DSL. Great Basin National Park Wetland and Riparian Inventory, Great Basin NP, Nevada. John mapped over 200 wetland and riparian sites on a 77,000-acre study area for this joint project between the U.S. Fish and Wildlife Service National Wetlands Inventory (NWI) and the National Park Service. He produced a report for the National Park Service Water Resources Division, and the NWI. Zion National Park Wetland and Riparian Inventory, Zion NP, Utah. John is mapped and classified wetlands and riparian vegetation along 20 miles of the Virgin River in southwest Utah. He interpreted aerial photographs, USGS topographic maps, National Wetlands Inventory data and GPS equipment to identify and locate wetlands. He classified wetlands according to the Cowardin classification system. Duck Valley Reservation Wetland Inventory, Duck Valley Reservation, Idaho and Nevada. John worked with a team of wetland scientists and tribal members to inventory approximately 10,000 acres of wetlands on 45,000 acres of the Shoshone - Paiute Duck Valley Reservation. He interpreted aerial photographs, soil survey maps, and topographic maps to determine the probable location of wetlands. He traversed the area to document wetland characteristics. This work was conducted to facilitate a Reservation wetland management plan. Columbia River Wetland Mapping Project, Oregon and Washington. John performed wetland determinations on over 100 sites along the Columbia River downstream from Portland, Oregon and Vancouver, Washington. Using maps from the U.S. Army Corps of Engineers, U.S. Fish and Wildlife Service National Wetland Inventory and hydric soil maps from the USDA Natural Resource Conservation Service, John analyzed the sites to determine their wetland status. 0 ESAa - ~..e`. i SARAH C. HARTUNG Wetlands Scientist Sarah is a wetlands scientist with eleven years of consulting experience in Oregon and Washington. Her experience includes wetland determinations and delineations, botanical surveys, species-specific surveys, and joint wetland permit applications. Sarah has delineated hundreds of wetlands and has prepared delineation reports for several large-scale transportation projects in the Pacific Northwest. She brings a proven record of obtaining wetland permits from the Department of State Lands and the U.S. Army Corps of Engineers in a timely manner. Sarah also has extensive experience preparing wetland mitigation and habitat restoration plans. Relevant Experience Education M.S., Avian Ecology, ODOT - Highway 97 Improvement Project - Baseline Studies and Wetland University of Illinois , Champaign-Urbana Delineations, Deschutes and Klamath Counties, OR. Project Manager and B.A., Biology, Hamline Field Lead. Sarah managed this transportation project and was part of a University, St. Paul, subconsultant field crew to conduct environmental baseline surveys and wetland Minnesota determinations for the Hwy 97 Improvement Project. ODOT proposed to repave Selected Training Hwy 97 along a 15-mile corridor from south of LaPine to Creswell, replace • Oregon Rapid Wetland failing culverts, install stormwater treatment facilities, and redesign Assessment Protocol transportation lanes in downtown Creswell. ESA reviewed existing data such as (ORWAP) soil survey mapping, orthophoto aerial images of the site, and topographic Oregon Streamflow Duration mapping. Sarah led the field crew that conducted wetland determinations, Assessment Method (OSDAM) botanical surveys, and assessed potential habitat for sensitive species. ESA mapped the locations of noxious weeds using Global Positioning Systems (GPS) Interim Regional Supplement to the Corps of Engineers and prepared technical memoranda for review by ODOT. Wetland Delineation Manual: Western Valleys, Mountains Highway 97 North of Bend, Oregon. Project Scientist. and Coast Range Sarah performed wetland and waterway scoping as well as wetland ODOT Certification for determinations for this ODOT project. ODOT is proposing to construct an Preparing Biological Assessments alternate highway route to relieve congestion and reduce traffic accidents north Interim Regional Supplement of Bend. Sarah also mapped noxious weed locations throughout the project area. to the Corps of Engineers and assisted with writing memoranda documenting the findings of field Wetland Delineation Manual: investigations. Arid West Region Advanced Soils Training Lane County Sign Replacement Project. Lane County, OR. Project Affiliations Manager and Wetland Scientist. Sarah served as project manager and field Member and Wetland scientist for this large-scale transportation sign upgrade project. ODOT proposed Professional in Training, to replace approximately 500 road signs along a 30-mile stretch of 1-5 in Lane Society of Wetland Scientists County to meet current FHWA readability standards. Sarah and another ESA 11 Years of Experience wetland scientist determined the presence of wetlands within 25 feet of proposed sign locations based on existing data and field reconnaissance. Approximately 200 potential wetlands were identified. She conducted delineations at 10 sign locations with proposed impacts to wetlands and completed the joint permit • application for approval from the U.S. Army Corps of Engineers (Corps). Sarah facilitated timely review of the JPA and assisted project engineers with construction specifications for avoiding impacts. Sarah C. Hartung Page 2 • Relevant Experience (Continued) ODOT - I-5 Bridges Vertical Improvements, Lane, Linn, and Marion Counties, OR. Project Manager and Field Lead Sarah served as project manager and field crew leader for wetland field reconnaissance, wetland delineations, botanical surveys, and endangered species act documentation at eleven bridge overpasses along the I-5 corridor from south of Salem to Eugene, Oregon. ODOT proposes to increase the vertical clearance of the bridges, which will require extensive grading, repaving, and site restoration. Sarah and field technicians delineated approximately 45 wetlands and waterways at 11 bridge sites. Sarah prepared the delineation report and facilitated concurrence from the Department of State Lands (DSL). Sarah also prepared the joint permit application and facilitated approval from DSL and the Corps. ODOT Region 3 Wetlands, Douglas and Josephine Counties, OR. Project Scientist. Sarah delineated wetlands, determined ordinary high water levels (OHWL) and assessed wetland functions for this highway improvement project. Sarah worked at two different sites: the Calapooya Creek Bridge on OR 138 to determine OHWL and to review a previous wetland delineation. At the Del Rio site, in Roseburg, Sarah delineated wetlands for the road realignment project and assessed the functions and values of over 20 wetlands using the judgmental method. Sarah prepared the wetland delineation report and assisted with the functional assessment report for the Del Rio Site. ODOT Region 5 - US 730 Umatilla River Bridge Repair, Umatilla, OR; and US 26 Culvert Repairs Project, John Day, OR. Project Scientist. Sarah conducted data review, wetland and waterway scoping, wetland delinations, OHWL flagging, and report writing for these two transportation projects. For the Umatilla Bridge Project, Sarah and another ESA Adolfson scientist determined the presence of wetlands along the Umatilla River at the US 730 bridge crossing and prepared a scoping memorandum per ODOT's template to document the findings. The second project involves replacing and/or repairing four culverts along US 26 east of John Day to improve fish passage. Sarah assisted with wetland and waterway delineations along these four tributaries of the John Day River and prepared the delienation report for submittal to DSL. Sarah is currently coordinating with NMFS and ODOT to determine if the project would qualify for a programmatic biological opinion under SLOPES IV. Frenchman Hills Wasteway Supplemental Feed Route Wetland Delineation, Quincy, Washington. Project Scientist. Sarah conducted wetland delineations along the Frenchman Hills Wasteway using the Arid West Supplement in support of a proposal to widen a culvert crossing. The culvert widening is part of Ecology and the Bureau of Reclamation's project to improve water delivery to the Potholes Reservoir. Sarah prepared a wetland delineation report for submittal to Ecology. Local Wetland Inventory, Lakeview, OR. Project Scientist. Sarah assisted with the processing and quality control of field data for this wetland inventory in • central Oregon. Sarah also assisted with preparing maps and finalizing the inventory for local and state approval. ESA,.` `j-~1 MIKE LEECH Senior GIS Analyst Mike is a Senior GIS Analyst with over 8 years of experience in GIS database development, analysis, management and cartography in natural resource management. He is an expert in design of GIS-linked MS Access databases for robust storage and retrieval of information. Mike is working with local cities and counties as they update their Shoreline Master Programs while also managing the GIS daily operations. He is adept at providing technical solutions to complex environmental problems using GIS. Mike has also developed a curriculum of intensive hands-on courses for the Northwest Environmental Training Center in areas of GIS software applications, spatial database development and information management. In addition, Mike also supports all of the GPS technology used by field staff in the Pacific Northwest region. Relevant Experience Education Geography, Western ODOT Region 3 Wetlands, Douglas and Josephine Counties, Oregon. Washington University 2006 Was GIS Analyst. Mike provided GPS and GIS technical support for this project Emphasis Resource Conservation and and also was responsible for preparing the maps and figures for the reports. Management Mike supported the field staff with Trimble GeoXT handheld GPS units and led B.A. Biology Indiana the post-processing and conversion to GIS format. Mike also helped to deliver , • University 1996 the digital data products to the ODOT R3 staff. B.A. Environmental Studies, Indiana University 1996 Shoreline Master Program Update, Pierce County, Washington. GIS Developer/Manager. Mike is coordinating GIS analysis and mapping to support A s io Affiliations/Activities Pierce County's SMP Update. He is also working with the County's Technical o ciationon for for American Association Geographers (AAG) Advisory Group, made up of County staff, Department of Ecology staff, tribal representatives, and other stakeholders. As part of this project, Mike developed a NW GIS Users Group web-based application using ArcGIS Server to support the technical document Relevant Skills review process for the project team and includes over 80 data layers from a Database Development variety of sources. He has also prepared a series of landscape analysis maps to GIS Manager support the inventory and characterization. Mike has also attended and presented Modeler information to the shoreline technical advisory group as well as helped with the facilitation of the public working group meetings. Technical Lead Natural Resource Policy Disturbance Mapping Project, USACE, Walla Walla, Washington. GIS Public Outreach Manager/Database Developer. Mike is the GIS/Database Coordinator for the Shoreline Planning USACOE Walla Walla District Disturbance Mapping Project. Mike and his GIS 8 Years of Experience support staff created a comprehensive database and GIS mapping system to depict areas of earth disturbance related to dam construction and related facilities. Mike is supervising other GIS staff in geo-referencing scanned historical documents and digitizing archaeological resources that may have been disturbed previously through excavation, shoreline erosion, or other construction activities. The final product delivered to the USACE was a robust GIS-linked Access database and a companion bound hard copy map atlas. Mike also prepared a hands-on training seminar with the project staff at the Walla Walla • District office to demonstrate the applications of the digital data as it relates to on-current/on-going projects at the CORPS. Mike Leech Page 2 • Relevant Experience (Continued) Birch Bay Watershed Characterization and Restoration Prioritization, Whatcom County, Washington. GIS Analyst. Mike worked with project staff to develop and apply a watershed characterization approach that synthesizes the findings of ecosystem process and habitat diversity models with models of potential land use change within the within the Birch Bay watershed of Whatcom County. Mike assisted with adapting and applying remote sensing protocols for identifying and characterizing wetland and riparian conditions within the watershed. He has helped to support the build-out scenario models for the Birch Bay watershed to track potential development patterns and impacts within the watershed. Northwest Environmental Training Center, Seattle, Washington. MS Access Database /GIS Instructor. Mike is also currently facilitating intensive hands-on courses for environmental professionals in areas of GIS software applications, spatial database development and information management. Mike has been responsible for developing training curriculum and lead instruction for MS Access 2003 Database Design and Management courses and on-going development of GIS Applications for Wildlife Biologists courses. Salmon Fisheries Management Tool, Upper Skagit Indian Tribe, Sedro- Woolley, Washington. Database Developer/GIS Analyst. Mike worked closely is with the Natural Resources & Fisheries staff to develop an in-season management tool based on 20 years of salmon catch data from the Skagit River for the Upper Skagit Indian Tribe. Mike developed an easy-to-use database and facilitated statistical analysis (linear regression modeling) for in-season updates to fisheries biologists. Mike also provided technical support, including training and comprehensive manuals for Microsoft Access databases and ArcGIS 9.x projects. He was responsible for the development of GIS-Linked MS Access databases for Public Works, Environmental Planning and Natural Resources Departments Other projects include CAD conversion of parcel data to GIS data, ortho-rectification of historical aerial photographs, and production of maps for grants and reports. Mapping Plant Communities at the Alliance Level, Oahu Forest National Wildlife Refuge. Satellite Image Processor. Mike used high-resolution IKONOS satellite imagery to compare pixel and object-based methods for mapping plant communities and canopy-dominant invasive species on US Fish & Wildlife lands. Mike used several advanced remote sensing tools including object-oriented image analysis package eCognition to assess the changes in accuracy between the two approaches. The final product (GIS database) is currently being used as a management tool by resource mangers in the Oahu Forest National Wildlife Refuge. • - 46 ERIC SCHNIEWIND Technical Associate Mr. Schniewind has over 15 years of experience as a hydrogeologist and geologist specializing in soil and groundwater contamination studies, environmental remediation planning and implementation, and pre- acquisition site assessments. He has supervised and conducted numerous contaminated groundwater site assessments, field operations, and remediation system installation projects. His experience includes project management, analysis of laboratory results, site historical research, report preparation, and aquifer and well test analysis. In addition, Mr. Schniewind has been involved in fault hazard and landslide hazard studies. His general responsibilities include providing geological, hydrogeologic, geotechnical, hydrological, and hazardous materials technical support for NEPA and CEQA documents such as EIRs, EISs, and EAs. Relevant Experience Education B.A., Geological Sciences, UC Santa Barbara Sandy River Pipeline Project, Sandy River OR. Hazardous Materials Specialist and Hydrologist. Eric provided consultation of contaminated plume identified in tunneling spoils on large construction project immediately adjacent to the Sandy River. In addition, Eric provided technical assistance on retained dewatering water with constituents that were outside of discharge requirements. ESA Adolfson is currently providing construction monitoring for this long term construction project and enforcing required BMPs to protect water quality. Grand Ronde, Road Construction, Grand Ronde, OR. Hazardous Materials Specialist and Hydrologist. Provided technical guidance and consultation services on contaminated soil characterization for excavated soils targeted for reuse on another site. Following local controversy on the potential presence of contaminants in excavated materials, Eric assisted in characterization of soils for potential presence of petroleum hydrocarbons. The construction project involved the widening of an existing local highway and requisite grading and earthwork activities while adhering to established BMPs. Grand Ronde Elder Housing, Grand Ronde, OR. Hydrologist. Eric provided technical data on stormwater pollutants anticipated for proposed housing development. The project calls for converting a large area of pervious surfaces to impervious surfaces that would drain directly into a creek that is habitat for protected aquatic species. The initial work also included an evaluation of potential stormwater quality concerns during the construction phase. Oak to Ninth Avenue Waterfront Development EIR. Geologist, Hydrologist, and Hazardous Materials Specialist Analyzed subsurface soil stability, soil and groundwater quality, shoreline erosion potential, effects of dredged sediments for use as fill, and the presence of contaminated groundwater and potential impacts to the public. The project would redevelop this underutilized maritime industrial area along the Estuary and the Embarcadero in Oakland into a mixed use revitalized area. The issues analyzed in the EIR included redevopment on • poorly engineered fill materials and Bay Muds, contaminated soils and groundwater from range of constituents, use of dredged materials as fill, and shoreline improvements to protect from erosion. Eric Schniewind, REA Page 2 • Relevant Experience (Continued) Treasure Island Naval Base, Redevelopment Plan, Hazardous Materials Specialist and Hydrogeologist. Provided technical analysis of former naval base with long history of hazardous materials use. The base has been divided into separate areas determined by historical releases of wide range of contaminants. The proposed project will include development of wetland for treatment of stormwater runoff. Lawrence Berkeley National Laboratory Building 51 and Bevatron Demolition Project, CEQA/NEPA analysis. Geologist and Hydrologist. Evaluated geologic, hydrologic, and hazardous materials related impacts for both the EIR and EA. The project entailed dismantling and removing the Bevatron particle accelerator, a facility listed on the National Register of Historic Places for its contribution to the development of the country's atomic energy program in the 1950s. Major environmental issues being analyzed include mitigation of significant impacts to historic resources, traffic and circulation associated with hauling of demolition materials through the city of Berkeley, handling and disposal of hazardous and radioactive materials, noise, air quality, public health and safety, visual quality and land use and planning. Fairfield-Suisun Sewer District (FSSD) Sewer System and Treatment Plant Master Plan EIR. Geologist. Analyzed potential geological hazards for system- wide wastewater flow improvements. Elements included upgrading wastewater treatment plant, construction of new outfalls on soft Bay Muds, construction of new pipelines and expanding stormwater catch basin infrastructure. Provided analysis of potential impacts and mitigation measures to address numerous geologic hazards. City of Eureka Balloon Tract EIR. Geologist, Hydrologist, and Hazardous Materials Specialist. Provided analysis for EIR on 43 acre Mixed Use project site located in the Coastal Zone. Former operations at the site included railroad car maintenance and repair and fueling of locomotives. Rail operations at the site included the use of Bunker C oil, diesel fuel, and gasoline. Environmental issues include soil and groundwater contamination from hazardous material releases, transportation, air quality, noise, biology, geology, and aesthetics. Canyon Rock Quarry Expansion Project EIR. Geologist and Hydrologist. Analyzed and prepared Response to Comments relating to geology, hydrology and water quality concerns in the DEIR for the FEIR. Issues of the expansion included potential impacts to the groundwater supply and potential impacts to neighboring water supply wells, water quality impacts to the nearby creek, groundwater recharge, and adequacy of retention basins, as well as traffic, air quality, noise, and water quality (potential sedimentation into an adjacent creek). 0 ESAj is -A 41 10 Years of Experience. MICHELLE LENNOX Project Scientist and GIS Analyst Michelle has over ten years of professional experience supporting a variety of environmental projects. She has assisted with wetland delineations, wildlife surveys, and habitat assessments. Michelle has also prepared wetland delineation reports, environmental assessments, biological assessments, and other documents needed for permitting, including National Environmental Policy Act (NEPA) and Endangered Species Act compliance. She is experienced in data management, GIS analysis, and digital imaging. Education Graduate Certificate in Geographic Information Systems (GIs), Portland State University, Portland, Oregon M.S., Biology, Towson University, Towson, Maryland B.S., Marine Biology, University of Maryland, College Park, Maryland Environmental reviews and permitting Wildlife surveys, habitat assessments, and wetland delineations Restoration planning and monitoring GIS analysis and remote ODOT Highway 97, North of Bend, OR. GIS Analyst. Michelle assisted with sensing mapping over 90 wetlands and waterways along Highways 97 and 20 north of Data compilation and Bend, for a proposed highway realignment project. She also conducted surveys management for rare mammals within the area of potential impact (API). Michelle led the QA/QC effort for the GIS maps and figures to illustrate the location of waterways, wetlands, and noxious weeds in the API. Relevant Experience Shoreline Master Program Update, Clark County, WA. GIS Analyst. Michelle is assisting with the GIS analysis and mapping to support Clark County's SMP Update. She has attended public meetings and has assisted the public in explaining how the shoreline boundaries were derived in GIS and helped them locate their properties to determine whether they are affected by shoreline planning area. Michelle will also create a series of landscape analysis maps to support the inventory and characterization. ODOT Region 3 Wetlands, Douglas and Josephine Counties, OR. GIS Analyst. ESA delineated wetlands and waterways at three sites in ODOT Region 3, near Grants Pass and Roseburg. Michelle assisted in mapping over 100 delineated wetlands and waterways on this project and provided QA/QC for the mapping portion of the project. She also instructed staff on procedures for collecting GPS data using a handheld Trimble unit, and used this data to create GIS maps of the wetlands and waterways for all three project sites. Elder Housing Wetland Delineation, Grand Ronde Tribal Housing Authority, Grand Ronde, OR. Project Manager. Michelle prepared a NEPA environmental assessment (EA) for the development of an approximately 10- acre site for elder housing facilities for the Confederated Tribes of Grand Ronde. The EA project includes preparation of an HUD Checklist and presentation of the final EA to the Bureau of Indian Affairs. Major issues addressed in the EA included wetlands and wildlife, transportation, cultural resources, and stormwater. Michelle was responsible for writing EA chapters, attending meetings, and coordinating with subconsultants. 0 Michelle Lennox Page 2 • Relevant Experience (Continued) Orient Drive Wetland Permitting, Gresham, OR. Project Scientist Michelle assisted with the re-flagging of a wetland resource at a property previously delineated by ESA. Phase II of the project included revising the wetland delineation report and assisting with preparation of a joint permit application for review by the Department of State Lands and the U.S. Army Corps of Engineers. Michelle coordinated with local agencies regarding wetland regulations affecting the site. River Bend Wetland Delineation, Independence, OR. Project Scientist. Michelle conducted a delineation of wetlands within the area likely to be disturbed by mining, access roads, and the fish egress channel. Wetland boundaries were marked in the field with flagging. ODOT I-5 Capitol Highway to the Willamette River Bridge Natural Resource Baseline Conditions and Biological Assessment, Clackamas, Multnomah, and Washington Counties, OR. Project Scientist. ODOT is proposing to widen shoulders along I-5 from Capitol Highway to the Willamette River Bridge and to construct several stormwater treatment facilities to treat new and existing impervious surface. To determine baseline conditions and potential project impacts, Michelle assisted with field review of the presence of wetlands, waterways, listed species habitat, and noxious weeds within the right-of-way of I-5 and helped prepare a technical memoranda summarizing the findings. LC Construction Wetland Delineation, Oregon City, OR. Project Scientist. Michelle assisted with a wetland delineation in Oregon City collecting information on existing vegetation, soils, and hydrologic regime. Michelle compiled the findings in a wetland delineation report for review by Oregon City and the Department of State Lands. Jordan Valley Airport Wetland Delineation, Jordan Valley, OR. Project Scientist. Michelle assisted with wetland delineation of a 23-acre site for a project proposing the construction of an emergency airport to service southeastern Oregon. Commuter Rail Impact Assessment and Mitigation, Washington County, OR. Project Scientist Michelle assisted with wetland delineations as part of the mitigation planning process for wetland impacts associated with a proposal to establish commuter rail service in Washington County. Road Renovation EA, Grand Ronde, OR. Project Scientist. Michelle assisted with conducting wetland delineations in the vicinity of Grand Ronde Road between Highway 18 and Highway 22, collecting information on existing vegetation, soils, and hydrologic regime. She assisted with compiling the findings to help determine whether the past wetland documentation was still adequate for permitting purposes. ESA "I.- son • ALISON SIGLER Staff Scientist Alison has five years of professional experience supporting environmental projects. She assists with wetland delineations and habitat assessments in Oregon, Washington and Idaho. She prepares biological assessments, wetland delineation reports, wetland functional assessment and impact reports, compensatory wetland mitigation reports, and other documents necessary for permitting. She has experience with data management, interpreting aerial photographs, creating maps, and GIS analysis. Education B.S., Biology, Washington State University, Pullman, Washington Basic Wetland Delineation Training, Portland State University, Portland, Oregon GIS for Natural Scientists, Portland State University, Portland, Oregon Relevant Experience Wetland Delineation Report and Buffer Assessment, Clackamas County, OR. Staff Scientist. Alison is assisting with a wetland delineation report of an industrial-zoned parcel in Clackamas County. A wetland delineation and buffer assessment is necessary for proposed expansion of the existing facility. Alison's contribution to the report includes reviewing and summarizing existing information, a site visit and photo documentation. The report is written following requirements from Oregon Department of State Lands and Clackamas County. 5 years experience Draft Environmental Impact Statement (DEIS, Lane Transit District, Eugene, OR. Staff Scientist. Alison is assisting with a wetland inventory and functional assessment analysis of wetlands located along the project alternatives for this rapid bus transit (RBT) project. Lane Transit District is proposing to extend RBT into West Eugene to reduce congestion and promote economic development. Compensatory Mitigation Plan Monitoring and Report Corvallis, OR. Staff Scientist. Alison conducted vegetation and woody species monitoring and compiled the annual monitoring report in support of Corvallis Station's compensatory wetland mitigation. Corvallis Station is a compensatory wetland mitigation site in its third year of monitoring. Tasks include identifying and assessing survival and cover of woody shrubs and vegetation, photo documentation, writing and editing the monitoring report. The report followed requirements set by Army Corps of Engineers and Oregon Department of State Lands. ODOT Region 5 US 26 Culvert Repairs Project, Grant County, OR. Staff Scientist. Alison is preparing a biological assessment and assisting with preparation of a wetland delineation report required for the US 26 Culvert Repairs Project. This work involves replacing or upgrading four culverts on four streams in the Upper John Day River Basin, improving fish passage, stream flow and gradients. Tasks include collecting and summarizing background information and aiding in the determination of potential action areas and report drafting. Alison updated the following chapters of the Biological Assessment: Introduction, Environmental Baseline, and Natural History and Species Occurrence. • Alison Sigler Page 2 • Relevant Experience (Continued) Sandy River Conduit Relocation Construction Monitoring, Clackamas County, OR. Staff Scientist The Portland Water Bureau is burying Conduits 2 and 4 of the City's drinking water system eighty feet below ground at the Sandy River crossing. As part of the construction monitoring over-sight provided by ESA, Alison is reviewing daily logs recorded by the Design-Builder to ensure compliance with environmental permits and approvals issued for the project, including a Removal-Fill permit, Section 404/Section 10 permit, and a Biological Opinion. She updates the bi-weekly monitoring report each month and periodically conducts site visits to evaluate environmental compliance. Eastmoreland Golf Course Tree Inventory, Portland, OR. Staff Scientist Alison is assisting with a comprehensive tree inventory which involves identifying species and measuring tree diameters on the Eastmoreland Golf Course. She is also assisting with the data processing and quality control of the data in GIS. The course was planted a century ago with native and non-native species. The goal of this inventory is to identify trees to remove for the purpose of improving play, improving air circulation in the tree canopy, and improving the overall health of the landscaping. ESA staff identified approximately 60 different tree species and surveyed over 1,300 trees using Global Positioning Systems (GPS). Biological Assessment Survey for Pipeline Transmission. Mount Hood National Forest, OR. Staff Scientist. Alison assisted with wetland delineations; noxious weed and sensitive species surveys; wildlife habitat surveys in support of a biological assessment for a pipeline transmission project. She was responsible for field data collection and management. The project goal was to record ecological conditions of the potential natural gas pipeline corridor to determine project impacts. GIS Mapping for Wild Salmon Conservation, Portland, OR. Staff Scientist. Alison created maps in GIS in support of salmon conservation non-profit research. She expanded and reorganized the GIS data server, reviewed and added metadata as needed and repaired missing data on existing maps. Ground Truthing LiDAR Imagery. Cowlitz, Yakima and Skamania Counties, WA. Staff Scientist Alison conducted field work ground truthing LiDAR imagery to check for image accuracy. Tasks included interpreting aerial photos and LiDAR imagery, collecting sample plot survey information including identifying and measuring trees and shrubs, reviewing and editing collected data superimposed on LiDAR imagery. • ESA,oA ROSEMARY BAKER Staff Wetland Ecologist/Botanist Rosemary has a background in restoration, native plant conservation and landscaping. Rosemary has worked for several years in the restoration of a variety of local stream, wetland, and forested habitats in urban parks and natural areas in and around Washington. She specializes in identification of Washington native plants and invasive species. Rosemary has delineated wetlands in eastern and western Washington, and is experienced in wetland rating and assessment. Relevant Experience Education B.S., Environmental Studies, King County Lands Invasive Plant Survey. King County, Washington. The Evergreen State College, Primary Field Botanist. Rosemary managed daily field survey operations and 2004 logistics, site selection, field forms, and all data entry. The survey was Wetland Science and conducted on 21,000 acres of county-owned properties that were deemed high- Management Certificate, value conservation lands. Each habitat type i.e. closed forest, freshwater University of Washington, 200 shoreline, etc. was evaluated for the percent presence of target invasive species, including county-listed noxious weeds. Surveyed data were entered in a database Professional Affiliations which county managers will use as a tool to better manage invasive species on EarthCorps 2005-2006 high-value county owned lands. Washington Native Plant Society 2005-present Pierce County Invasive Species and Lake Management Project, Pierce County, Washington. Field Botanist. Rosemary assisted in field surveys during 2 Years of Experience 2008. Data on weed presence and percent cover collected served as the basis for an invasive species management plan. Tasks performed included identification and coverage assessment of a variety of invasive plants and county listed noxious weeds, as well as documentation of hydrologic features and wildlife habitat suitability. Redmond PSE Trail Phase 3 Trail Improvements, Redmond, Washington. Wetland Scientist. Rosemary delineated wetlands on City of Redmond property and prepared a Critical Areas Report including assessment of impacts for the Puget Sound Energy trail reroute. D208519. Northeast Redmond Neighborhood Park Master Plan. Wetland Scientist. Rosemary delineated wetlands and streams, characterized wildlife habitat areas, and assisted in preparation of a critical areas study. The undeveloped park, located in the City of Redmond, Washington, contains wetlands, a salmonid-bearing stream, and regulated wildlife habitat. City of Kenmore On-Call 2008, Kenmore, Washington. Wetland Scientist. Rosemary reviewed permit submittals with regard to the City of Kenmore Critical Areas Code reviews for the City, as part of ESA's on-call contract with the City. Tasks included review of submitted documents for conformance with • Kenmore Municipal Code, site visits to verify wetlands and boundaries, mitigation monitoring, and preparation of letters to the city regarding applicant's conformance with City code. Rosemary Baker Page 2 • Relevant Experience (Continued) Gentry Critical Area Permitting Assistance, King County, Washington. Wetland Scientist. Rosemary prepared both a conceptual wetland buffer enhancement plan and a planting plan for a private homeowner on Shady Lake in unincorporated King County. Vintage I Office Park, Federal Way, Washington. Field Botanist. Rosemary assisted in the 2008 monitoring of stream buffer plantings installed installed on property adjacent to a tributary of Hyllebos Creek. She also assisted in assessing competitive bids for an additional planting, ordered plants, and helped manage installation logistics. Japanese Gulch Trail, Mukilteo, Washington. Volunteer Coordinator. Rosemary assisted in managing a volunteer planting event within the City of Mukilteo. She helped with on-site event logistics, bare-root planting demonstrations and public safety. The city was required to mitigate impacts to a wetland for the installation of a pedestrian and biking trail within Japanese Gulch. Experience Prior to Joining ESA Adolfson Ravenna Park Wetland Restoration Project, Seattle, Washington. In alliance with the City's Green Seattle Partnership, and sponsor Washington Native Plant Society, Rosemary managed a wetland restoration in Ravenna Park at the 15`h Ave Bridge. The site is a groundwater-fed sloped wetland at the base of the ravine draining into Ravenna Creek. Hummocks were constructed to establish longer term conifer survival and live stakes were installed in areas with Reed-canary grass. Rosemary's group continues to plant a diversity of native emergents and shrubs and remove invasives in the wetland. ESA Wolfson 0 ADAM MERRILL Watershed Scientist • Adam has over seven years of experience conducting and supporting a variety of biological and ecological studies. He regularly performs wetland delineations, wetland ratings, functional assessments, and prepares wetland reports and mitigation plans for permit applications. In addition, Adam has experience planning and prioritizing wetland and stream restoration activities at a watershed scale. Adam's knowledge and experience also includes stream habitat assessment, water quality monitoring, erosion and sediment control monitoring, forestry studies, and shoreline inventories. Adam is trained in the use of GPS technology and ArcGIS 9.3 software, and is skilled at using geospatial data to identify and analyze aquatic habitats. Relevant ESA Adolfson Experience Education B.S., Environmental Science, I-405 Corridor Program Wetland Studies, King County, Washington. ESA Western Washington University, 2001 Adolfson (ESA) was contracted with the Washington Department of Transportation (WSDOT) to conduct wetland investigation and mitigation M.S., Resource Management, Central Washington development for multiple sections of the I-405 road improvements and Nickel University, Expected projects in King County. The projects include: SR 169 to I-90 Renton to Graduation Winter 2010 Bellevue Project, Kirkland Nickel Improvement Project, Bellevue Nickel Certifications Improvement Project, and Renton Nickel Improvement Project. Adam's duties Certified Erosion and have included wetland identification, delineation, functional assessment, and Sediment Control Lead state and local rating for over 100 wetlands along approximately 25 miles of I- (CESCL) 405. He has co-authored two discipline reports, two biology reports, and a Fluvial Ordinary High Water mitigation plan in support of an Environmental Assessment and other Mark (OHWM) Certification environmental documentation. Washington State Wetland Rating System (Revised) Everett Riverfront Development, Everett, Washington. ESA is currently Certification contracted to the city of Everett to provide technical and permitting assistance Relevant Experience for a large, mixed-use redevelopment of a formally industrial site on the Wetland identification, Snohomish River. Adam's duties included wetland delineation, rating, and delineation, rating, functional assessment, mitigation functional assessment for several wetlands in the project area. In addition, Adam wrote technical memoranda analyzing the potential impacts to plants, shoreline inventories animals, streams, and wetlands resulting from the public amenity improvement Watershed characterization, and environmental restoration phase of the project. planning, and restoration Water Quality Monitoring Union Hill Phase II Project, City of Redmond, Washington. ESA was contracted by the City of Redmond and INCA Engineers, Inc. to conduct an Stream Habitat Assessment environmental study in support of the Union Hill Phase II Project, in the City of 7 Years of Experience Redmond. The proposed road improvements will occur near Bear Creek, a Washington Department of Fish and Wildlife listed priority habitat. Adam was the lead biologist for the field study, which included a stream and wetlands survey and an assessment of fish and wildlife habitat. Adam also drafted the critical areas study, in accordance with City of Redmond's critical areas ordinance. is Adam Merrill Page 2 Relevant Experience (Continued) Spanaway Creek Fish Passage Improvement Project, Pierce County, Washington. In support of a fish passage improvement project at Spanaway Creek in Pierce County, ESA conducted a wetland analysis and habitat assessment at the site of an existing dam on the creek at Bresemann Forest. Adam's duties included conducting wetland delineations, wetland ratings, and authoring the wetland portion of the critical areas study. SR 522 Corridor Improvements, City Kenmore, Washington. At the request of the City of Kenmore and Butcher, Willis and Ratliff, Inc., ESA is conducting permitting support for the SR 522 Corridor Improvement project in the City of Kenmore, Washington. For this project, Adam has coordinated with the Army Corps of Engineers to permit the wetland impacts in the project area. He has also authored an environmental feasibility study for proposed intersection improvements near the project area. Adam also assisted the city in selecting a wetland mitigation site for the wetland impacts in the project area. On-Call Projects for the cities of Kenmore, Newcastle, and Kent, Washington. ESA currently provides assistance to the City of Kenmore and the City of Kent planning departments through long-term on-call contracts. This work addresses wetlands, streams, and other sensitive areas and provides guidance to the cities in administering sections of their zoning codes. Adam has . evaluated many wetland studies, stream determinations, and mitigation plans submitted to the cities of Kenmore, Newcastle, and Kent as part of proposed development applications. Cathcart Custodial Transfer Site Wetland and Stream Reconnaissance, Snohomish County, Washington. Adam conducted a wetland and stream reconnaissance on the 200-acre Custodial Transfer Site in Snohomish County, Washington. The purpose of the study was to assist Snohomish County with future site planning. Adam was the lead biologist for the field work, and he drafted a technical memo detailing the findings of the wetland and stream reconnaissance. Other Experience Identification and Prioritization of Aquatic Habitat Restoration Projects at a Watershed Scale, Birch Bay, Washington To fulfill the thesis requirement for a M.S. degree in Resource Management at Central Washington University, Adam conducted a watershed-scale aquatic habitat restoration plan for the Birch Bay watershed, in western Whatcom County. Based upon a GIS analysis of existing data sources coupled with field verifications, Adam identified potential wetland and riparian restoration areas. He also developed a methodology for prioritizing these restoration areas, based upon their potential to provide wildlife habitat, floodwater attenuation, and water quality functions. Lastly, Adam suggested ecological restoration techniques for the identified areas, for the purpose of aiding future restoration planners in developing detailed, site-specific restoration plans. is • u AARON BOOY Natural Resources Specialist Aaron has five years of experience in both aquatic ecology and environmental planning. His knowledge of local, state and federal regulatory processes have contributed to a wide range of SEPA and NEPA documents, permit acquisition strategies, shoreline plans, and community land use planning efforts. Aaron is skilled in natural resource management and the use of science in developing environmental and land use policies. Aaron also has background in aquatic and fisheries science and brings an interdisciplinary approach to all of his planning projects. He has field experience in stream and riparian habitat surveys, wetland delineation, and water quality monitoring. Relevant Experience Education B.S., Aquatic and Fisheries McCormick Park Reconnaissance and Assessment, Duvall, WA. Project science, university of Washington, Seattle Manager. Aaron is the project manager for the City of Duvall's McCormick B.A., Design and Planning: Park Reconnaissance and Assessment. He managed project scoping and in-field Community and activities, including use of GPS equipment to inform the assessment and Environmental Planning mapping of access and restoration opportunities within the McCormick Park Seattle University of Washington, area. The study area stretches across the City's Snoqualmie River shoreline, and includes unique environments and current land uses. Aaron's work on this 5 Years of Experience project is informing planning for the shoreline area, including the SNIP Update. Hood Property Critical Areas Study, Snohomish County, WA. Wetlands Specialist At the request of Mr. Hood, ESA conducted a critical areas study in support of a proposed single family residential development in unincorporated Snohomish County, Washington. Aaron's duties included conducting wetland and stream delineations, developing a conceptual mitigation plan for proposed stream buffer impacts, and drafting a Critical Areas Study per Snohomish County regulations. City of Duvall On-Call Environmental Consultant, WA. Project Manager. ESA currently provides assistance to the City of Duvall planning department through a long-term on-call contract. This work addresses wetlands, streams, and other sensitive areas and provides guidance to the City in administering sections of the zoning code. As the Project Manager, Aaron manages receipt and tracking of submittals, site visits, and review for all submittals received. Aaron has evaluated wetland studies, stream determinations, and mitigation plans submitted to the City of Duvall as part of numerous proposed development applications, including assessment and review for the City's Public Works Department. • Aaron Booy Page 2 Relevant Experience (Continued) Washington State Ferries, Hydrologic Monitoring and Modeling, Anacortes, WA. Project Scientist. ESA developed and implemented a detailed hydrologic monitoring plan for two significant wetland systems that surround the Washington State Ferries - Anacortes Terminal. Monitoring includes the installation of 12 piezometer nests, four continuous recording pressure transducers, and 2 continuous recording rain gauges. Aaron assists in conducting bi-monthly monitoring of the wetland system, which is currently in progress. Everett Riverfront Development, WA. Biologist. ESA was contracted by the City of Everett to conduct an environmental study in support of the Everett Riverfront Development project, in the City of Everett. Aaron is a biologist for the large development project along the Snohomish River in the City of Everett, Washington covering over 100 acres. The project involved the delineation, rating, and functional assessment for over 20 wetlands and several streams, including Bigelow Creek. Ongoing work has included hydrologic monitoring and modeling of the wetland and stream systems in the project area. Union Hill Road Phase II Project, Redmond, WA. Project Manager. ESA was contracted by the City of Redmond and INCA Engineers, Inc. to conduct an environmental study in support of the Union Hill Phase II Project, in the City of Redmond. The proposed road improvements will occur near Bear Creek, a is Washington Department of Fish and Wildlife listed priority habitat. Aaron served as the Project Manager on the Union Hill - Phase II Project, which included client communication. He served as the primary author for the Mitigation Plan, SEPA Checklist, and the Permits Matrix. Aaron assisted in the field study as a biologist, which included a stream and wetlands survey and an assessment of fish and wildlife habitat. City of Auburn SMP Update, WA. Project Scientist. Aaron assisted in the update of the City of Auburn's Shoreline Master Program. He authored chapters on freshwater shoreline natural resources for the Shoreline Inventory and Characterization Report, including wetlands, instream and riparian habitats, and critical wildlife habitat and species. Cathcart Custodial Transfer Site and Bunk Foss Road Site Wetland and Stream Reconnaissance, Snohomish County, WA. Project Scientist. Aaron assisted in conducting a wetland and stream reconnaissance on the 60 total acre Woodinville Sites, the 200-acre Custodial Transfer Site and the 12-acre Bunk Foss Road Site in Snohomish County, Washington. The purpose of the study was to assist Snohomish County with future site planning. Aaron prepared the technical memos detailing the findings of the wetland and stream reconnaissance for the Woodinville Sites and Bunk Foss Road Site. • PAUL ADAMUS Adamus Resource Assessment, Inc. Dr. Paul Adamus is the author of ORWAP, the new tool of the Department of State Lands that assesses the relative capacity of wetlands to remove nitrate, as well as 15 other functions and values. While developing this he applied it to 220 wetlands throughout Oregon, including several he visited in the Upper Deschutes study area. For DSL, he has trained nearly 100 agency personnel and consultants in the use of ORWAP, and previously developed both of DSL's "hydrogeomorphic" (HGM) methods for assessing wetlands. In 2008 OWEB competitively selected Dr. Adamus to conduct ecological audits of their wetland projects in the Willamette Valley, for which he applied ORWAP and surveyed vegetation and soils at 60 sites. He has comprehensively assessed wetlands for Crater Lake National Park; for the Corvallis Natural Features Inventory; for Juneau, Alaska; and for Island County, Washington, where he drafted a local wetlands protection ordinance (subsequently adopted) that has been cited nationally for its innovative approach to buffer width determinations. He also designed and established the County's 5-year program for monitoring nitrate contamination of surface waters and statistically analyzed those data. He has twice been invited to testify on wetland matters to the U.S. Congress, and was chosen as the sole expert witness on major wetlands case in Michigan. He is best known as the author of WET (Wetland Evaluation Technique), developed originally for the Federal Highway Administration in the early 1980's, and used widely by federal agencies in the decade that followed. Over the past 35 years he has authored over 100 publications, many during the 10 years he was part of EPA's National Wetlands Research Program based in Corvallis. His research for EPA focused on cumulative impacts and the effects of excessive nutrients on wetland biological communities. Education Ph.D. Wildlife Science, Oregon State University, Corvallis M.S. Biology (Aquatic), University of Utah, Salt Lake City B.S. Wildlife Science, University of Maine, Orono Current Positions Adamus Resource Assessment, Inc., Corvallis, Oregon. Principal. 1997-present. Oregon State University, Corvallis, Oregon (2002-present) College of Oceanographic and Atmospheric Sciences, Assistant Professor (Courtesy) Environmental Sciences Graduate Program (Water Resources) Wetland Program Consultations State/Tribe Wetland Program Consultation: North Carolina (Dept. Environmental Management) Illinois (Dept. of Conservation) Maine (State Planning Office) Washington (Dept. of Ecology) Oregon (Dept. Environmental Quality, Department of State Lands) Oklahoma Michigan is Confederated Tribes of the Umatilla Indian Reservation Regional Wetland Functional Assessment Projects: • Klamath Region (Lassen Volcanic & Crater Lakes National Parks) Oregon Coast: HGM data collection, model development, and application Willamette Valley, Oregon: HGM data collection, model development, and application Juneau, Alaska: Wetlands Management Plan (the second such plan approved in the U.S.) New Jersey (Hackensack Meadowlands, Raritan Estuary) Salt Lake City, Utah: Wetlands Advanced Identification Project Southern Maine: Wetlands Advanced Identification Project Washington (Mill Creek Watershed): Special Area Management Plan Washington (Puget Sound - Island County) Selected Publications Adamus, P., J. Morlan, and K. Verble. 2009. Oregon Rapid Wetland Assessment Protocol (ORWAP): calculator spreadsheet, databases, and data forms. Oregon Dept. of State Lands, Salem, OR. http://oregonstatelands.us/DSL/WETLAND/or wet prot.shtml Willamette Partnership, Parametrix, and P.R. Adamus. 2009. Crediting and Debiting of Ecosystem Services. Counting on the Environment Project: http://www.willamettepartnership.or,g/ongoing_projects-and-activities/nres- conservation-innovations-grant-1 /nres-conservation-innovations-grant Adamus, P.R. and C.L. Bartlett. 2008. Wetlands of Crater Lake National Park: An Assessment of Their Ecological Condition. Natural Resource Technical Report NPS/KLMN/NRTR-2008/115. National Park Service, Fort Collins, CO. httl2://science.nature.nps.gov/im/units/klmn/Inventories/Adamus Wetland/Adamus Wetland.cfm Adamus, P.R. 2007. Best Available Science for Wetlands of Island County, Washington: Review of Published • Literature. Report to Island County Dept. of Planning & Community Development, Coupeville, WA. Internet: htip://www.islandcoun!y.net/planning/criticalareas/wetlands/ Adamus, P.R., J. Burcar, K. Hanna, C. Luerkens, A. Boscolo, J. Coleman, and M. Kershner. 2006. Wetlands of Island County, Washington: Profile of Characteristics, Functions, and Health. Report to Island County Dept. of Planning & Community Development, Coupeville, WA.Internet: http://www islandcounty net/planninp/criticalareas/wetlands/Phasel Complete-doc ndf Adamus, P.R. 2004. Classification, Assessment, Monitoring, and Evaluation of Riverine and Palustrine Wetland Ecosystems. Chapter 12 In: M. McKinstry(ed.). Wetland and Riparian Areas of the Intermountain West. University of Texas Press. http://www.utexas.edu/utpress/books/mckwet.htmi Windham, L. and P.R. Adamus. 2004. Analysis of nitrogen processing and other water qualityfunctions of Phragmitis australis wetlands of the Raritan Estuary during summer 2003. Report to PSS, Inc. Adamus, P.R., J. Webster, C. Shippentower, S. O'Daniel, D.E. Williams, and S. Minthorn. 2002. Umatilla River Floodplain and Wetlands: A Quantitative Characterization, Classification, and Restoration Concept. Confederated Tribes of the Umatilla Indian Reservation, Pendleton, OR. httn://www.umatilla.nsn.us/database/wetlands • EDUCATION: B.S. Environmental Science, Alessandra E. Capretti, WPIT WETLAND SPECIALIST Portland State University, Minor, Environmental Engineering Ms. Capretti is a wetland scientist and natural resource specialist with WORK HISTORY: expertise in environmental permitting, wetland delineation, compensatory Total Years of Experience: 9 mitigation, habitat enhancement and restoration. She also manages Years with HHPR: 6 multidisciplinary projects involving Endangered Species Act and National Historic Preservation Act components. She is actively involved in all aspects PROFESSIONAL of fieldwork and uses the latest technology. Ms. Capretti provides knowledge and experience in supervising landscape contractors; developing AFFILIATIONS: erosion control measures; inspecting plant material; preparing monitoring Member of the Society of Wetland and maintenance plans, as well as site monitoring. In addition, she has Scientists (SWS) experience in preparing Phase I Environmental Site Assessments in the states of Oregon and Washington. Ms. Capretti actively keeps abreast of the Member of American Society of Civil latest local, state and federal rules and regulations affecting her work and Engineers has an excellent reputation of working with clients and agency representatives in providing creative, cost effective solutions to CERTIFICATIONS: environmental, regulatory and permitting challenges. . Wetland Professional in Training Ms. Capretti is currently completing the coursework needed for her (WPIT) environmental engineering degree. • Professional Certificate in Wetland Mitigation & Restoration, CONTINUING EDUCATION: Portland State University • GIS & Field GIS • Professional Certificate in Wetland Delineation • Basic Wetland Delineation • • NEPA AREA OF EXPERTISE: • Hydrogeomorphic Wetland Classification • Wetland Delineation/Permitting • ESA I & ESA II • Natural Resource Assessment • Wetland Mitigation, Const. & Installation • Environmental Review • Mitigation Planning • Advanced Soils & Hydrology for Delineators . Permitting • Basic Water Rights • Agency Consultation • Wetland Plants of the Pacific Northwest • Environmental Compliance: Integration, Project Permits • Wetland Regulations & Mitigation Compliance • Arid Western Regional Supplement Training • Oregon Rapid Wetland Assessment Protocol (ORWAP)Training • HP QUALIFICATIONS / PROJECT EXPERIENCE: Founded in Portland in 1990, HHPR currently has offices in Bend, Clackamas, and Portland, Oregon; and Vancouver, Washington. HHPR's staff of over 75 employees includes licensed Professional Engineers, Landscape Architects, Environmental Specialist and Surveyors in addition to Certified Planners and Project Managers, Engineers-in-Training, Designers/CAD Specialists, and office support. Many of our staff have public sector experience combined with successful years of providing consulting services. This balance of experience assures knowledge of what is required to provide efficient consulting services with an understanding of what is needed by our public clients. Qualifications: Ms. Capretti has managed environmental projects throughout the Pacific Northwest, from the Pacific Coast to the High Desert Region in Oregon, providing consulting services and developing compliance programs for public and private clients. These projects have included performing wetland delineations/determinations and compensatory mitigation plans for school districts, industrial sites, commercial properties, county and city road widening projects. Ms. Capretti has written numerous Natural Resources Assessments for public and private entities for projects ranging in size from less than an acre to 80 acres. Ms. Capretti has recent experience utilizing Army Corps of Engineers (LISACE) 1987 Wetland Delineation Manual: Arid Western Region Supplement. HHPR was contracted by Deschutes Valley Water District (DVWD) to perform a wetland delineation on the proposed crossing of Willow Creek for the installation of a 20 inch transmission waterline. Ms. Capretti performed all the fieldwork for the delineation of Willow Creek. Directed the mapping and surveying of the project creek crossing. She prepared exhibits and a report for submittal to DSL and ACOE. Ms. Capretti continuing education pursuits within wetland delineation, permitting and field investigations results in accurate, consistent establishment of sensitive are boundaries based on current guidelines to obtain concurrence by permitting authorities. • r~ HP • South Deschutes County Local Wetland Inventory Report E APPENDIX C: WETLAND DETERMINATION FORMS 0 ESA Adolfson June 2011 Appendix C WETLAND DETERMINATION DATA FORM - Arid West Region Project/Site: DESCHUTES LWI City/County: WILD RIVER/DESCHUTES Sampling Date:, 03-May-10 Applicant/Owner: DESCHUTES COUNTY_ State: OR _ Sampling Point: SP 1 • Investigator(s): ALISON SIGLER, SARAH HARTUNG Section, Township, Range: S 23 T 21 S R 9 E Landform (hillslope, terrace, etc.): Floodplain Local relief (concave, convex, none): concave Slope: 0.0% / 0.0 ° Subregion (LRR): LRR B Lat.: 43.7434 Long.: -121.6076 Datum: NAD 83 Soil Map Unit Name: Not available NWI classification: Are climatic/hydrologic conditions on the site typical for this time of year? Yes 0 No ❑ (If no, explain in Remarks.) Are Vegetation ❑ , Soil ❑ , or Hydrology ❑ significantly disturbed? Are "Normal Circumstances" present? Yes * No ❑ AreVegetation ❑ , Soil ❑ , or Hydrology ❑ naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transects, important features, etc. Hydrophytic Vegetation Present? Yes 0 No ❑ Hydric Soil Present? YES ~ NO 0 Is the Sampled Area Yes No ❑ Wetland Hydrology Present? Yes * No ❑ within a Wetland? Remarks: ONSITE AT WILD RIVER VEGETATION - Use scientific names of plants. Dominant _ Species? Absolute Rel.Strat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: ) % Cover Cover Status ❑ Number of Dominant Species 1. 0 0.0% That are OBL, FACW, or FAC: 3 (A) 0 3 0 ❑ 0 0% Total Number of Dominant . . (B) Species Across All Strata: 311-1 4. 0 ❑ o.o% 1 o =Total Cover Percent of dominant Species 100 0% (A/13) Sapling/Shrub Stratum (Plot size: ) . That Are OBL, FACW, or FAC: 1. Spiraea douglasii 15 U 100.0% FACWa Prevalence Index worksheet: 2• 0 0.0% Total % Cover of: Multiply.by...._ 3• 0 ❑ 00% 08L species 10 x 1 = 10 4. 0 ❑ 0.0% FACW species 55 x 2 = 110 5. 0 ❑ 0.0% FAC species 40 x 3 = 120 15 = Total Cover FACU species 10 x q _ 40 Herb Stratum (Plot size: 0 J ff 35 ❑ 35 0% C UPL species x 5 = 1. uncus e usus . FA W Column Totals : 115 (A) 280 (e) 2. Taraxacum officinale 10 El 1o.0% FACU 3. Veronica americana 10 ❑ 10.0% OBL Prevalence Index = B/A = 2.435 4Poa palustris 25 25.0% FAC Hydrophytic Vegetation Indicators: 5. Salix sp. 5 _ ❑ 5.0% FACW d❑ Dominance Test is > so% Agrostis sp ^15 El 15.0% FAC ✓ Prevalence Index is <_3.0 1 7. 0 ❑ 0.0% - 1 . provide supporting Morphological Adaptations 1 8,. 0 ❑ 0.0% , data in Remarks or on a separate sheet) 9. 0 L r l o.0%, ❑ Problematic Hydrophytic Vegetation 1 (1 :plain) 10, 0 ❑ 0.0% 11. 0 ❑ 0.0% 100 = Total Cover Woody Vine Stratum (Plot size: ) 1. -0-111 Ell I 2. 0 ❑ 0.o% 0 = Total Cover % Bare Ground in Herb Stratum: 0 % Cover of Biotic Crust 0 • Remarks: Salix sp. assumed FACW. Salix sp. and Agrostis sp. assumed FAC. 1 Indicators of hydric soil and wetland hydrology must be present, unless disturbed or problematic. Hydrophytic Vegetation Present? Yes 0 No ❑ *Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS. US Army Corps of Engineers Arid West - Version 2 Oct. 2008 Soil Sampling Point: SP 1 Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Depth Matrix Redox Features (inches) Color (moist) % Color (moist) % Type Loc. Texture Remarks • 0-3 10YR 3/2 100% Sand 80% SAND WITH 20% SILT 3-6 10YR 3/2 70% Silt Loam 30% SAND - 1 Type: C=Concentration. D=Depletion. RM=Reduced Matrix, CS=Covered or Coated Sand Grains 21-ocation: PL=Pore Lining. M=Matrix Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils3 ❑ Histosol (Al) ❑ Sandy Redox (S5) ❑ 1 cm Muck (A9) (LRR C) ❑ Histic Epipedon (A2) ❑ Stripped Matrix (S6) ❑ 2 cm Muck (A10) (LRR B) ❑ Black Histic (A3) ❑ Loamy Mucky Mineral (Fl) ❑ Reduced Vertic (1`18) ❑ Hydrogen Sulfide (A4) ❑ Loamy Gleyed Matrix (F2) ❑ Red Parent Material (TF2) ❑ Stratified Layers (AS) (LRR C) ❑ Depleted Matrix (F3) d❑ Other (Explain in Remarks) ❑ 1 cm Muck (A9) (LRR D) ❑ Redox Dark Surface (F6) ❑ Depleted Below Dark Surface (All) ❑ Depleted Dark Surface (F7) ❑ Thick Dark Surface (A12) ❑ Sandy Muck Mineral (Sl) ❑Redox depressions (F8) 3 Indicators of hydrophytic vegetation and ❑ Sandy Gleyed Matrix (S4) ❑ Vernal Pools (F9) wetland hydrology must be present. Restrictive Layer (if present): - Type: Depth (inches): Hydric Soil Present? Yes C No Remarks: SOILS ARE HYDRIC BASED ON PERSISTENT SATURATION Hydrology Wetland Hydrology Indicators: Primary Iri i tors (minimum_gf one required, check all that apply) Secondary Indicators (2 or more required) ❑ Surface Water (Al) ❑ Salt Crust (Bll) ❑ Water Marks (Bl) (Riverine) High Water Table (A2) ❑ Biotic Crust (B12) ❑ Sediment Deposits (B2) (Riverine) V Saturation (A3) ❑ Aquatic Invertebrates (B13) ❑ Drift Deposits (B3) Riverine) ❑ Water Marks (BI) (Nonriverine) ❑ Hydrogen Sulfide Odor (Cl) ❑ Drainage Patterns (B10) ❑ Sediment Deposits (B2) (Nonriverine) ❑ Oxidized Rhizospheres along Living Roots (0) ❑ Dry Season Water Table (C2) r 11 Drift deposits (B3) (Noneriverine) ❑ Presence of Reduced Iron (C4) ❑ Crayfish Burrows (C8) ❑ Surface Soil Cracks (B6) ❑ Recent Iron Reduction in Plowed Soils (C6) ❑ Saturation Visible on Aerial Imagery (C9) ❑ Inundation Visible on Aerial Imagery (B7) ❑ Thin Muck Surface (0) ❑ Shallow Aquitard (D3) ❑ Water-Stained Leaves (B9) a Other (Explain in Remarks) ❑ FAC-neutral Test (D5) Field Observations: Surface Water Present? Yes 0 No Depth (inches): Water Table Present? Yes No 0 Depth (inches): 4~ ? Yes No Saturation Present? (includes capillary fringe) Yes No 0 Wetlan Depth (inches): 0 d Hydrology Present Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available: Remarks: - - - - - SURFACE WATER WITHIN 2 FEET OF PLOT US Army Corps of Engineers Arid West - Version 2 Oct. 2008 WETLAND DETERMINATION DATA FORM - Western Mountains, Valleys, and Coast Region Project/Site: DESCHUTES LWI City/County: SUNRIVER/DESCHUTES Sampling Date: 21-Jun710 • Applicant/Owner DESCHUTES COUNTY State: OR Sampling Point: SP 01A Investigator(s) ALISON SIGLER SARAH HARTUNG Section, Township, Range: S 18 T 21 S R 11 E Landform (hillslope, terrace, etc.): Valley bottom Local relief (concave, convex, none): concave Slope: 2.0% Subregion (1.1111): LRR A Lat.: 43.7543 Long.: -121.4672 Datum: NAD83 Soil Map Unit Name: 144A; _SV_n,river sandy loam. 0 0,3 QerSent 51Q 5 NWI classification: PE A _ Are climatic/ hydrologic conditions on the site typical for this time of year? Yes No 0 (If no, explain in Remarks.) Are Vegetation ❑ , Soil ❑ , or Hydrology ❑ significantly disturbed? Are "Normal Circumstances" present? Yes 0 No 0 Are Vegetation ❑ , Soil ❑ , or Hydrology ❑ naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transects, important features, et Hydrophytic Vegetation Present? Yes No Hydric Soil Present? Yes ~ No ❑ Is the Sampled Area within a Wetland? Yes * No 0 Wetland Hydrology Present? Yes C NO 0 Remarks: OFF-SITE DETERMINATION VEGETATION - Use scientific names of plants. Dominant Species? Absolute Rel.Strat. Indicator Tree Stratum (Plot size: ) % Cover Cover Status 0 ❑ 0.0% 2,. 0 ❑ 0.0% 3. ❑ _o.o%o 4. ❑ 0.0% 0 = Total Cover Sapling/Shrub Stratum (Plot size: ) 14 . _ 0 ❑ 0.0% 2. 0 ❑ 0.o% 3. o ❑ o.o% 4. o ❑ 0.0% 5. 0 ❑ 0 = Total Cover Herb Stratum (Plot size: ) ~ 1. Carex sp. 10 ❑ 1o.0% FACW 2. Juncus balticus 88 ❑ 88.0% FACW TYpha latifolia 3 2 ❑ 2.0% OBL . 4, ❑ o.o% 0 ❑ 0.0% 0-1- ❑ o.o% 7. 0 ❑ o.o°io 8. ❑ 0.0% 9. o ❑1 0.0% 10. _ 0 ❑ o.o°io 11. 0 ❑ 0.0% 100 = Total Cover Woody Vine Stratum (Plot size: ) 1. 0 ❑ 0.0% 2. 0 L l 0.0% 0 = Total Cover Bare Ground in Herb Stratum: 0 Dominance Test worksheet: Number of Dominant Species That are OBL, FACW, or FAC: 1 (A) Total Number of Dominant Species Across All Strata: (B) Percent of dominant Species That Are OBL, FACW, or FAC: 100.0% (A/B) Prevalence Index worksheet: Total % Cover-of:, Multi I b OBL species 2 x 1 = 2 FACW species 98._ x 2 = 196 FAC species 0 x 3 = FACU species 0 x 4 = 0 UPL species 0. x 5 - column Totals: 100 (A) 198 (B) Prevalence Index = B/A = 1.980 Hydrophytic Vegetation Indicators: Dominance Test is > 50% Prevalence index is :53.01 Morphological Adaptations 1(Provide supporting data in Remarks or on a separate sheet) ❑ Wetland Non-Vascular Plantsl ❑ Problematic Hydrophytic Vegetationl (Explain) 1Indicators of hydric soil and wetland hydrology must be present, unless disturbed or problematic. Hydrophytic Vegetation Yes0 No 0 Present. E Carex sp. assumed to be FACW. Remarks: *Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version Soil Sampling Point: SP 01A Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Depth Matrix Redox Features j (inches) Color (moist) % Color (moist) % TypeI Lot= Texture Remarks E • I 1Type: C=Concentration. D=Depletion. RM=Reduced Matrix, CS=Covered or Coated Sand Grains 'Location: PL=Pore Lining. M=Matrix Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils:3 - Histosol (Al) L J Sandy Redox (S5) 2 cm Muck (A10) Histic Epipedon (A2) -1 Stripped Matrix (S6) I Red Parent Material (TF2) ❑ Black Histic (A3) LL Loamy Mucky Mineral (Fl) (except in MLRA 1) F Other (Explain in Remarks) V Hydrogen Sulfide (A4) ❑ Loamy Gleyed Matrix (F2) Depleted Below Dark Surface (All) Depleted Matrix (F3) Thick Dark Surface (A12) Redox Dark Surface (F6) 3 Indicators of hydrophytic vegetation and _ Sandy Muck Mineral (Sl) - Depleted Dark Surface (F7) wetland hydrology must be present, j Sandy Gleyed Matrix (S4) Redox depressions (F8) unless disturbed or problematic. Restrictive Layer (if present): Types _ Depth (inches): Hydric Soil Present? Yes ! No Remarks: I Hydrology Wetland Hydrology Indicators: Primary Indicators (minimum of one required; check all that apply) Secondary Indicators (minimum of two required) u Surface Water (Al) LL Water-Stained Leaves (B9) (except MLRA Water-Stained Leaves (B9) (MLRA 1, 2, High Water Table (A2) 1, 2, 4A, and 4B) 4A, and 4B) Saturation (A3) 1 Salt Crust (Bil) r Drainage Patterns (B10) Water Marks (BI) Aquatic Invertebrates (813) L_I Dry Season Water Table (C2) ❑ Sediment Deposits (B2) Hydrogen Sulfide Odor (Cl) E J Saturation Visible on Aerial Imagery (C9) Drift deposits (63) Oxidized Rhizospheres on Living Roots (0) ❑ Geomorphic Position (132) Algal Mat or Crust (B4) ❑ Presence of Reduced Iron (C4) Shallow Aquitard (D3) Iron Deposits (B5) LJ Recent Iron Reduction in Tilled Soils (C6) FAC-neutral Test (D5) c Surface Soil Cracks (B6) L J Stunted or Stressed Plants (Dl) (LRR A) Raised Ant Mounds (D6) (LRR A) Inundation Visible on Aerial Imagery (B7) [ Other (Explain in Remarks) Frost Heave Hummocks (D7) I Sparsely Vegetated Concave Surface (B8) i Field Observations: Surface Water Present? Yes No U Depth (inches): L i Water Table Present? Yes No Depth (inches): Saturation Present? - Yes' NO Wetla Depth (inches): 1 nd Hydrology Present? Yes NO E r (includes capillary frinqe) Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available: Aerial photo Remarks: i i US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version • WETLAND DETERMINATION DATA FORM - Arid West Region Project/Site: DESCHUTES LWI City/County: Sunriver/Deschutes Sampling Date: 03-May-10 Applicant/Owner: DESCHUTES COUNTY State: OR Sampling Point: SP 2 Investigator(s): ALISON SIGLER, SARAH HARTUNG Section, Township, Range: S 31 T 20 S R 10E Landform (hillslope, terrace, etc.): Valley bottom Local relief (concave, convex, none). concave Slope: 0.0% / 0.0 ° Subregion (LRR): LRR B Lat.: 43.7978 Long.: -121.5722 Datum: NAD 83 Soil Map Unit Name: 115A: Shanahan loamy coarse sand, 0 to 3 percent slopes NWI classification: / y ogic conditions on the site typical for this time of year. Yes 0- NO If no, explain in Remarks.) Are climatic/ hydrologic drol Are Vegetation ❑ Soil ❑ , or Hydrology ❑ significantly disturbed? Are "Normal Circumstances" present? Yes * No O Are Vegetation ❑ , Soil ❑ , or Hydrology ❑ naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transects, important features, etc. Hydrophytic Vegetation Present? Yes 0 No ❑ Hydric Soil Present? Yes 0 No Is the Sampled Area Yes * No O Wetland Hydrology Present? Yes C No ❑ within a Wetland? Remarks: On-site determination. VEGETATION - Use scientific names of plants Tree Stratum (Plot size: ) 1. Salix sp. 2. 3. 4. • Sapling/Shrub Stratum (Plot size: ) 1.. 2. 3. 4. 5. Herb Stratum (Plot size: ) 1. Carex aquatilis 2. 3. 4. 7. 8. 9. 10. 11. Woody Vine Stratum (Plot size: ) Dominant - Species? Absolute Rel.Strat. Indicator Dominance Test worksheet: % Cover Cover Status . , . _ . Number of Dominant Species 20 ❑ 100.0% FACW That are OBL, FACW, or FAC: 2 (A) 0 ❑ 0.0% 0 0% ❑ 0 Total Number of Dominant - . Species Across All Strata: 2 (B) 0 ❑ 0.0% 20 =total Cover Percent of dominant Species 100 0% (A/B) . That Are OBL, FACW, or FAC: Prevalence Index worksheet: 0 ❑ o.o% Total % Cover of: Multi y -by: 0 ❑ o.o% OBL species 85 x 1 = 85 0 ❑ 11- o. 0% FACW species 20 x 2 = 40 0 ❑ 0.0% FAC species 0 x 3= 0 0 = Total Cover FAcu species x 4 = _ 0 85 0% OBL i ❑ 100 UPL species x 5 = . column Totals: 105 (A) 125 (B) o El 0.0% 0 ❑ 0.o% Prevalence Index = B/A = 1.190 0 ❑ 0.0% Hydrophytic Vegetation Indicators: 0 ❑ 0.0% d❑ Dominance Test is > so% 0 ❑ 0.o% ❑ Prevalence Index is <_3.0 1 0 ❑ o.o% ❑ Morphological Adaptations 11- -rovide supporting 0 o.o% data in Remarks or on a separate sheet) 0 ❑ 0.o°r° - ❑ Problematic Hydrophytic Vegetation 1(1 :plain) 0 ❑ 0.0% 0 ❑ 0.0% 1 Indicators of hydric soil and wetland hydrology must 85 =Total Cover - - be present, unless disturbed or problematic. 1. 0 ❑ 0.0% 2. 0 ❑ 0.o% Hydrophytic Vegetation 0 = Total Cover Present? Yes No ❑ % Bare Ground in Herb Stratum: 15 % Cover of Biotic Crust 0 Remarks: • Salix sp. assumed FACW. *Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS. US Army Corps of Engineers Arid West - Version 2 Oct. 2008 Soil Sampling Point: SP 2 Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Depth pth Matrix Redox Features (inches).,,. Color (moist) % Color (moist) % Type I Lox= Texture Remarks 0-3 10YR 3/2 95% 10YR 4/6 5% C PL Loamy Sand 3-20 10YR 4/1 100% Loam 1 Type. C=Concentration. D=Depletion. RM=Reduced Matrix, CS=Covered or Coated Sand Grains 2Location: PL=Pore Lining. M=Matrix Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils3 ❑ Histosol (Al) ❑ Sandy Redox (S5) ❑ 1 cm Muck (A9) (LRR C) ❑ Histic Epipedon (A2) ❑ Stripped Matrix (S6) ❑ 2 cm Muck (A10) (LRR B) ❑ Black Histic (A3) Hydrogen Sulfide (A4) ❑ Loamy Mucky Mineral (FI) ❑ Reduced Vertic (1`18) ❑ Stratified Layers (AS) (LRR C) ❑ Loamy Gleyed Matrix (F2) ❑ Depleted Matrix (9) ❑ Red Parent Material (TF2) ❑ Other (Explain in Remarks) ❑ 1 cm Muck (A9) (LRR D) ❑ Redox Dark Surface (F6) ❑ Depleted Below Dark Surface (All) ❑ Thick Dark Surface (A12) ❑ Depleted Dark Surface (F7) I ❑ Sandy Muck Mineral (Sl) ❑ Redox depressions (F8) ❑ Vernal Pools (F9) 3 Indicators of hydrophytic vegetation and ❑ Sandy Gleyed Matrix (S4) wetland hydrology must be present. Restrictive Layer (if present): Type Depth (inches): Hydric Soil Present? Yes * No ❑ I Remarks: i Hydrology Wetland Hydrology Indicators: Primary I,rldicatprs (minimum of one required;_check-alhthat apply)_, Secondary Indicators (2 or more required) ❑ Surface Water (Ai) ❑ Salt Crust (B1 I) ❑ Water Marks (Bl) (Riverine) ❑ High Water Table (A2) ❑ Biotic Crust (B12) ❑ Sediment Deposits (B2) (Riverine) • Saturation (A3) ❑ Aquatic Invertebrates (B13) ❑ Drift Deposits (B3) Riverine) ❑ Water Marks (Bl) (Nonriverine) ❑ Hydrogen Sulfide Odor (CI) ❑ Drainage Patterns (B10) I ❑ Sediment Deposits (B2) (Nonriverine) ❑ Oxidized Rhizospheres along Living Roots (0) ❑ Dry Season Water Table (C2) ❑ Drift deposits (B3) (Nonriverine) ❑ Presence of Reduced Iron (C4) ❑ Crayfish Burrows (C8) ❑ Surface Soil Cracks (B6) ❑ Recent Iron Reduction in Plowed Soils (C6) ❑ Saturation Visible on Aerial Imagery (C9) ❑ Inundation Visible on Aerial Imagery (B7) ❑ Thin Muck Surface (C7) ❑ Shallow Aquitard (D3) ❑ Water-Stained Leaves (B9) ❑ Other (Explain in Remarks) ❑ FAC-neutral Test (D5) Field Observations: Surface Water Present? Yes ❑ No 0 Depth (inches): i Water Table Present? Yes NO ❑ Depth (inches): Yes NO ❑ Saturation Present? a Yes No ❑ Wetland H Depth (inches): Eo 1 ydrology Present? I (includes capillary fringe) - Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if avai lable: I Remarks: US Army Corps of Engineers Arid West - Version 2 Oct. 2008 WETLAND DETERMINATION DATA FORM - Western Mountains, Valleys, and Coast Region Project/Site: DESCHUTES LWI City/County: SUNRIVER/DESCHUTES Sampling Date: 21-Jun-10 Applicant/Owner: DESCHUTES COUNTY State: OR Sampling Point: SP 2A Investigator(s): ALISON SIGLER, SARAH. HARTUNG_ v Section, Township, Range: S 18 T 21 S R 11 E Landform (hillslope, terrace, etc.): Valley bottom Local relief (concave, convex, none): concave Slope: 0.0% / 0.0 ° Subregion (LRR): LRR A Lat.: 43.7543 Long.: -121.4665 Datum: NAD83 Soil Map Unit Name: 2. A [1[ 9U, II q_tQ 5 rQQnt.$1Q42Q,£ NWI classification: P~(1A.__... Are climatic/ hydrologic conditions on the site typical for this time of year? m Yes No ❑ (If no, explain in Remarks.) Are Vegetation ❑ , Soil ❑ , or Hydrology ❑ significantly disturbed? Are "Normal Circumstances" present? Yes * No ❑ Are Vegetation ❑ , Soil ❑ , or Hydrology L_I naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transects, important features, et • Hydrophytic Vegetation Present? Yes 0 No ❑ Hydric Soil Present? Yes 0 No ❑ Wetland Hydrology Present? Yes No ❑ Remarks: OFF-SITE DETERMINATION 0 ❑ 0.o% 0 ❑ 0.0% 0 = Total Cover VEGETATION - Use scientific names of plants. Dominant Species? Absolute Rel.Strat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: ) % Cover Cover Status ❑ Number of Dominant Species 1. 0 0.0% That are OBL, FACW, or FAC: 2 (A) 2. 0 ❑ 0.0% 3 0 ❑ 0 0% Total Number of Dominant j . . Species Across All Strata: 2 (B) 4. o [.7 0.0% Percent of dominant Species Sapling/Shrub Stratum (Plot size: ) 0 = Total Cover That Are OBL, FACW, or FAC: o 100.0 /o (A/B) Woody Vine Stratum (Plot size: ) 1. 2 1, 0 ❑ 0.0% Prevalence Index worksheet: 2. _ 0 ❑ 0.0% Total % Cover of Mul ly_by 3. o ❑ 0.o% 08L species 0 x 1= 0 4. 0 ❑ 0.0% FACw species 100 x 2 = x 200 5. 0 ❑ 070% FAC species 0 x 3= 0 0 = Total Cover 0 0 FACU species x 4 Herb Stratum (Plot size: ) 0 0 C 20 V 20 0% FACW x 5 - = UPL species 1 arex sp. . 2. Juncus balticus 80 0 80.0% FACW 100 Column Totals: .___.(A) 200 (B) ; 3 0 ❑ 0.0% Prevalence Index = B/A = 27000 4. 0 0.0% Hydrophytic Vegetation Indicators: 5. 0 ❑ 0.0% ❑d Dominance Test is > 5o% 6. 0 ❑ 0.0% _ 0 Prevalence Index is :53.01 7. 0 ❑ 0.0% 1 ❑ Morphological Adaptations (Provide supporting 8 0 ❑ 0.0% data in Remarks or on a separate sheet) 9• 0 ❑ 0.o% _ ❑ Wetland Non-Vascular Plantsl 10• ❑ 0% - ❑ Problematic Hydrophytic Vegetationl (Explain) 11. _ 0 ❑ 0.0% 1Indicators of hydric soil and wetland hydrology must 100 - = T otal Cover be present, unless disturbed or problematic. % Bare Ground in Herb Stratum: 0 Remarks: Carex sp. assumed to be FACW. *Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version Hydrophytic Vegetation Yes* No ❑ • Present. Is the Sampled Area within a Wetland? Yes 0 No ❑ Soil Sampling Point: SP 2A Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Depth Matrix Redox Features- Color (moist) % (inches) F Color (moist) % Type 1 Loc2 Texture Remarks i 1Type: C=Concentration. D=Depletion. RM=Reduced Matrix, CS=Covered or Coated Sand Grains zLocation. PL=Pore Lining. M=Matrix Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils 3 ❑ Histosol (Al) ❑ Sandy Redox (S5) ❑ 2 cm Muck (A10) ❑ Histic Epipedon (A2) ❑ Stripped Matrix (S6) ❑ Red Parent Material (TF2) ❑ Black Histic (A3) ❑ Loamy Mucky Mineral (Fl) (except in MLRA 1) EVI Other (Explain in Remarks) ❑ Hydrogen Sulfide (A4) ❑ Loamy Gleyed Matrix (F2) ❑ Depleted Below Dark Surface (All) ❑ Depleted Matrix (F3) ❑ Thick Dark Surface (A12) Redox Dark Surface (F6) 3 Indicators of hydrophytic vegetation and ❑ Sandy Muck Mineral (Si) L _ Depleted Dark Surface (F7) wetland hydrology must be present, ❑ Sandy Gleyed Matrix (S4) Redox depressions (F8) unless disturbed or problematic. Restrictive Layer (if present): Type Depth (inches): Hydric Soil Present? Yes No ❑ E Remarks: SOILS ASSUMED HYDRIC BY SATURATION I Hydrology Wetland Hydrology Indicators: Primary Indicators (minimum of one required; check all that apply) Secondary Indicators (minimum of two required) ' LJ Surface Water (Al) ❑ Water-Stained Leaves (B9) (except MLRA ❑ Water-Stained Leaves (B9) (MLRA 1, 2, ❑ High Water Table (A2) 1, 2, 4A, and 4B) 4A, and 4B) ❑ Saturation (A3) ❑ Salt Crust (Bll) ❑ Drainage Patterns (B10) ❑ Water Marks (Bl) Aquatic Invertebrates (B13) ❑ Dry season water Table (C2) ❑ Sediment Deposits (B2) ❑ Hydrogen Sulfide Odor (Cl) ❑ Saturation Visible on Aerial Imagery (C9) ❑ Drift deposits (B3) LJ Oxidized Rhizospheres on Living Roots (0) ❑ Geomorphic Position (D2) ❑ Algal Mat or Crust (B4) ❑ Presence of Reduced Iron (C4) ❑ Shallow Aquitard (D3) ❑ Iron Deposits (B5) ❑ Recent Iron Reduction in Tilled Soils (C6) ❑ FAC-neutral Test (D5) ❑ Surface Soil Cracks (B6) ❑ Stunted or stressed Plants (Dl) (LRR A) ❑ Raised Ant Mounds (D6) (LRR A) j Inundation Visible on Aerial Imagery (B7) ❑ Other (Explain in Remarks) ❑ Frost Heave Hummocks (D7) " ❑ Sparsely Vegetated Concave Surface (B8) Field Observations: Surface Water Present? Yes ❑ No Depth (inches): ! Water Table Present? Yes O No Depth (inches): l ? Yes No ❑ l P Saturation Present? Yes 0 No O and Hydro ogy resent ~ Wet Depth (inches): ~V J (includes capillary fringe) Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available: Aerial photo - Remarks: US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version • WETLAND DETERMINATION DATA FORM - Western Mountains, Valleys, and Coast Region Project/Site: DESCHUTES LWI City/County: SUNRIVER/DESCHUTES Sampling Date: 21-Jun-10 • Applicant/ Owner: DESCHUTES COUNTY State: OR Sampling Point: SP 3A Investigator(s). ALISON _SIGLERi SARAH HARTUNG Section, Township, Range: S 13 T 21 S R 10 E Landform (hillslope, terrace, etc.): Shoreline Local relief (concave, convex, none): concave Slope: 0.0% / 0.0 ° Subregion (LRR): LRR A Lat.: 43.7550 Long.: -121.4862 Datum: NAD83 Soil Map Unit Name: 29Aw.C..rwgvQll k9 3 percent I9p2 NWI classification: Are climatic/ hydrologic conditions on the site typical for this time of year? Yes No ❑ (If no, explain in Remarks.) Are Vegetation ❑ , Soil ❑ , or Hydrology ❑ significantly disturbed? Are "Normal Circumstances" present? Yes C No ❑ Are Vegetation ❑ Soil , or Hydrology naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transects, important features, et Hydrophytic Vegetation Present? Yes No ❑ j Is the Sampled Area Hydric Soil Present? Yes No ❑ Yes 0- No ❑ Wetland Hydrology Present? Yes C No ❑ within a Wetland? Remarks: On-site determination. VEGETATION - Use scientific names of plants. Dominant i Absolute es? Spec Rel.Strat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: ) % Cover Cover Status ❑ Number of Dominant Species 0 0.0% That are OBL, FACW, or FAC: 3 (A) 3 0 ❑ 0 0% Total Number of Dominant • . Species Across All Strata: 3 (B) 4. 0 ❑ 0.0% 0 = Total Cover Percent of dominant Species 100 0% (A/B) Sapling/Shrub Stratum (Plot size: ) ~ FACW, or FAC: That Are OBL , - . SaIix exi ua 1. 9 20 100.0% OBL - - Prevalence Index worksheet: 2. 0 ❑ 0.0% Total % Cover, oof: Multiply by: 3.1-1 0 ❑ 0.0% oBL species 70 x 1 = 70 4. 0 i 0.0% FACW species 45 x 2 = 90 5. 0 ❑ 0.0% pAC species 0 x 3= 0 20 - - = Total Cover 0 0 FACU species x 4 = Herb Stratum (Plot size: ) 0 1 Carex nebrascensis 50 [ 52.6% OBL - x 5 UPL species 2.Juncus nevadensis 30 u 31.6% FACW Column Totals: 115 (q) 160 _ (B) 3 Rumex occidentalis 10 10.5% FACW Prevalence Index = B/A = 1.391 4 Potentilla sp. 6 5.3% FACW Hydrophytic Vegetation Indicators: 5. __0 ❑ o.o% . Dominance Test is > 50% 6. ❑ 0.0% W L f Prevalence index is :53.01 'J, 0 ❑ o.o% ❑ Morphological Adaptations 1 Provide supporting ( 0 ❑ 0.o% data in Remarks or on a separate sheet) 9. 0 ❑ 0.0% ❑ Wetland Non-Vascular Plantsl 10. 0 0 ❑ 0.0 /o ❑ Problematic Hydrophytic Vegetationl (Explain) 11. 0 ❑ 0.0% 95 = Total Cover 1Indicators of hydric soil and wetland hydrology must d l - be present, unless disturbed or problematic. - - - - - - y Vine Stratum (P ot size: ) Woo - - - 1 • 0 ❑ 0.0% 2. 0 ❑ 0.0% Hydrophytic - 0 = Total Cover Vegetation Present? Yes * No ❑ % Bare Ground in Herb Stratum: 5 Remarks: • Potentilla sp. assumed FACW. *Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version Soil Sampling Point: 3A Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Depth Matrix Redox Features (inches) Color (moist) % Color (moist) % Type 1 Loc2 Texture Remarks 0-12 2.SYR 3/1 950/0 10YR 4/4 5% C M Silt Loam 5% small rocks; dense roots 12-14 2.SYR 3/1 900/0 10YR 3/4 100/6 C M Sandy Clay Loam w/silts and gravel TType: C=Concentration. D=Depletion. RM=Reduced Matrix, CS=Covered or Coated Sand Grains zLocation: PL=Pore Lining. M=Matrix Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils 3 Histosol (Al) Sandy Redox (55) 1 L ] 2 cm Muck (A10) r] Histic Epipedon (A2) i__J Stripped Matrix (S6) ]I Red Parent Material (TF2) ❑ Black Histic (A3) Loamy Mucky Mineral (Fl) (except in MLRA 1) ] Other (Explain in Remarks) Hydrogen Sulfide (A4) r Loamy Gleyed Matrix (F2) Depleted Below Dark Surface (All) Depleted Matrix (F3) Thick Dark Surface (A12) Lv ~ Redox Dark Surface (F6) 3Indicators of hydrophytic vegetation and i- J Sandy Muck Mineral (Sl) Depleted Dark Surface (F7) wetland hydrology must be present, Sandy Gleyed Matrix (S4) Redox depressions (F8) unless disturbed or problematic. Restrictive Layer (if present): Type: jeXtrprne. saturation Depth (inches): 14 Hydric Soil Present? Yes 0' No Remarks: - Hydrology Wetland Hydrology Indicators: Primary Indicators (minimum of one required; check all that apply) Secondary Indicators (minimum of two required) le Surface Water (Al) L-1 Water-Stained Leaves (B9) (except MLRA Water-Stained Leaves (B9) (MLRA 1, 2, FVI High Water Table (A2) 1, 2, 4A, and 4B) 4A, and 4B) Saturation (A3) Salt Crust (Bll) ❑ Drainage Patterns (B10) Water Marks (B1) ❑ Aquatic Invertebrates (613) Dry season water Table (C2) Sediment Deposits (B2) Hydrogen Sulfide Odor (Cl) Saturation Visible on Aerial Imagery (C9) ] Drift deposits (B3) Oxidized Rhizospheres on Living Roots (0) a Geomorphic Position (D2) ❑ Algal Mat or Crust (B4) L _I Presence of Reduced Iron (C4) Shallow Aquitard (D3) Iron Deposits (B5) _ Recent Iron Reduction in Tilled Soils (C6) FAC-neutral Test (D5) Surface Soil Cracks (B6) Stunted or Stressed Plants (Dl) (LRR A) - Raised Ant Mounds (D6) (LRR A) Inundation Visible on Aerial Imagery (B7) I Other (Explain in Remarks) Frost Heave Hummocks (D7) Sparsely Vegetated Concave Surface (B8) Field Observations: Surface Water Present? Yes L NO ~ Depth (inches): ~ 1 Water Table Present? Yes No Depth (inches): l W ? Yes No d H l P Saturation Present? Yes No et an ydro ogy resent - Depth (inches): 0 L (includes capillary_ fringe) i Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available: Remarks: - US Army Corps of Engineers Western Mountains, Valleys, and Coast Region - Interim version WETLAND DETERMINATION DATA FORM - Arid West Region Project/Site: DESCHUTES LWI City/County: Sunriver/Deschutes Sampling Date: 03-May-10 Applicant/Owner: DESCHUTES COUNTY State: OR Sampling Point: SP 4 Investigator(s): ALISON SIGLER, ROSEMARY BAKER Section, Township, Range: S 31 T 20S R 10 E Landform (hillslope, terrace, eta): Valley bottom Local relief (concave, convex, none): concave Slope: 0.0% / 0.0 ° Subregion (LRR): LRR B Lat.: 43.7950 Long.: -121.5856 Datum: NAP 83 Soil Map Unit Name: 114C: Shanahan loamy coarse sand, 0 to.,15 percent slopes.. _ NWI classification: Are climatic/ hydrologic conditions on the site typical for this time of year? Yes 0 No ❑ (If no, explain in Remarks.) Are Vegetation ❑ , Soil ❑ , or Hydrology ❑ significantly disturbed? Are "Normal Circumstances" present? Yes C' No ❑ Are Vegetation ❑ , Soil E_ , or Hydrology ❑ naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transects, important features, etc. Hydrophytic Vegetation Present? Yes J-) No ❑ Is the Sampled Area Hydric Soil Present? Yes ~ NO ❑ Yes 00 No ❑ Wetland Hydrology Present? Yes NO ❑ within a Wetland? Remarks: On-site determination. VEGETATION - Use scientific names of plants. Dominant Species? _ Absolute Rel.Strat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: ) /Cover Cover ~ Status Number of Dominant Species 1, 0 ❑ That are OBL, FACW, or FAC: 2. 0 ❑ 0.0% 3 ❑ Total Number of Dominant . 0 0.o% Species Across All Strata: 4. o ❑ o.o% 2 (A) 2 (B) Percent of dominant Species 0 =Total Cover That Are OBL, FACW, or FAC: 100.0% (A/B) Sapling/Shrub Stratum (Plot size ) 1. 2. 3. 4. 5. Herb Stratum (Plot size: ) 1. Carex aquatilis 2. Salix sp. 3. Poa sp. 4 Fragaria virginiana 6.__ . 7, 9. 10. 11. 0 0.0% Prevalence Index worksheet: 0 ❑ 0.0% Total % Cover of: Multiply by: 0 6 ❑ 0.0% OBL species 70 x 1 = 70 _0 ❑ 0.0% FACW species 20 x 2 40 0 ❑ 0.0% FAC species 8 x 3 = 24 0 = Total Cover FACU species 2 x 4= 8 70 ❑ 70 0% OBL UPL species 0 x 5 = 0 . Column Totals: 100 (A) 142 (B) 20 E-4 20.0% FACW 8 1 ❑ - s.0% FAC Prevalence Index = B/A = 1.420 2 2.0°1" FACU Hydrophytic Vegetation Indicators: 0 ❑ 0.0% ❑d Dominance Test is > 50% 0 ❑ 0.0 /o ❑d prevalence Index is <_3.0 1 0 ❑ 0.0% ❑ Morphological Adaptations i _ rovide supporting 0 ❑ 0.0% data in Remarks or on a separate sheet) 0 ❑ a 0.0% _ _ ❑ Problematic Hydrophytic Vegetation 1 (1 :plain) o ❑ o.o% o ❑ o.o°io 1 Indicators of hydric soil and wetland hydrology must 100 =T otal Cover be present, unless disturbed or problematic. Woody Vine Stratum (Plot size: ) 1, 0 ❑ 0.0% 2. 0 ❑ 0.0% Hydrophytic Vegetation 0 =Total Cover Present? Yes No ❑ % Bare Ground in Herb Stratum: 0 % Cover of Biotic Crust 0 Remarks: • Salix sp. assumed FACW. Poa sp. assumed FAC. *Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS. US Army Corps of Engineers Arid West - Version 2 Oct. 2008 Soil Sampling Point: SP 4 Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Depth Matrix _ Redox Fea tures _ (inches) Color (moist) % Color (moist) % Type I Loci Texture Remarks 0-6 10YR 2/2 100% Sandy Loam DENSE ROOTS 6-18 10YR 2/2 100% Sandy Loam WITH GRAVEL, SATURATED 1 Type: C=Concentration. D=Depletion. RM=Reduced Matrix, CS=Covered or Coated Sand Grains 21-ocation: PL=Pore Lining. M=Matroc Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Solls3 ❑ Histosol (Al) ❑ Sandy Redox (S5) ❑ 1 cm Muck (A9) (LRR C) ❑ Histic Epipedon (A2) ❑ Stripped Matrix (S6) ❑ 2 cm Muck (A10) (LRR B) ❑ Black Histic (A3) ❑ Loamy Mucky Mineral (Fl) ❑ Reduced Vertic (FIB) ❑ Hydrogen Sulfide (A4) ❑ Stratified Layers (AS) (LRR C) ❑ Loamy Gleyed Matrix (F2) ❑ Red Parent Material (TF2) ❑ 1 cm Muck (A9) (LRR D) ❑ Depleted Matrix (F3) Other (Explain in Remarks) ❑ Redox Dark Surface (F6) El Depleted Below Dark Surface (All) El Depleted Dark Surface (F7) ❑ Thick Dark Surface (A12) ❑Redox depressions (F8) io ❑ Sandy Muck Mineral (Sl) ❑ Vernal Pools 3 Indicators of hydrophytic vegetation and El Sandy Gleyed Matrix (S4) wetland hydrology must be present. Restrictive Layer (if present): Type: Depth (inches): Hydric Soil Present? Yes a No Remarks: `SOILS HYDRIC BY SATURATION Hydrology Wetland Hydrology Indicators: _t rimarv Indicators (minimum of Qne required; check all that apply) Secondary Indicators (2 or more required) Surface Water (Al) C Salt Crust (Bli) U Water Marks (Bl) (Riverine) High Water Table (A2) ❑ Biotic Crust (B12) ❑ Sediment Deposits (B2) (Riverine) Saturation (A3) ❑ Aquatic Invertebrates (B13) ❑ Drift Deposits (B3) Riverine) U Water Marks (BI) (Nonriverine) ❑ Hydrogen Sulfide Odor (Cl) ❑ Drainage Patterns (B10) ❑ Sediment Deposits (B2) (Nonriverine) ❑ Oxidized Rhizospheres along Living Roots (0) ❑ Dry Season Water Table (C2) ❑ Drift deposits (B3) (Noneriverine) ❑ Presence of Reduced Iron (C4) ❑ Crayfish Burrows (C8) ❑ Surface Soil Cracks (B6) ❑ Recent Iron Reduction in Plowed Soils (C6) ❑ Saturation Visible on Aerial Imagery (C9) ❑ Inundation Visible on Aerial Imagery (B7) ❑ Thin Muck Surface (C7) ❑ Shallow Aquitard (D3) ❑ Water-Stained Leaves (B9) ❑ Other (Explain in Remarks) FAC-neutral Test (D5) ^Field Observations: Surface Water Present? Yes ❑ No Depth (inches): Water Table Present? Yes * No 0 Depth (inches): j 5 Yes No 0 Saturation Present? Yes 00 No 0 Wetlan Depth (inches): 0 d Hydrology Present? } (includes capillaryfringe) Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available: i Remarks: I I US Army Corps of Engineers Arid West - Version 2 Oct. 2008 WETLAND DETERMINATION DATA FORM - Western Mountains, Valleys, and Coast Region Project/Site: DESCHUTES LWI City/County: SUNRIVER/DESCHUTES Sampling Date: 21-Jun-10 • Applicant/ Owner: DESCHUTES COUNTY State: OR Sampling Point SP 4A Investigator(s): ALISON SIGLER, SARAH HARTUNG, Section, Township, Range: S 14 T 21 S R 10 E Landform (hillslope, terrace, etc.): Valley bottom Local relief (concave, convex, none): concave Slope: 0.0% / 0.0 ° Subregion (1.1111): LRR A Lat.: 43.7606 Long.: -121.4890 Datum: NAD83 Soil Map Unit Name: 29A: Crvagll91l5,. Q tQ 3 percent slopes NWI classification: PEMA_., Are climatic/ hydrologic conditions on the site typical for this time of year? Yes U No ❑ (If no, explain in Remarks.) Are Vegetation ❑ , Soil V , or Hydrology ❑ significantly disturbed? Are "Normal Circumstances" present? Yes No ❑ Are Vegetation ❑ , Soil ❑ , or Hydrology ❑ naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transects, important features, et r~ Hydrophytic Vegetation Present? Yes 0 No ❑ ? Yes* No ❑ d i il Is the Sampled Area Hy r c So Present Yes 0* NO ❑ Wetland Hydrology Present? Yes* No ❑ within a Wetland? Remarks: WETLAND WITH PROBLEM SOILS. FILL MATERIAL WITHIN WETLAND IN SEVERAL POCKETS. SOILS COLOR VARIABLE THROUGHOUT IT, HEAVILY GRAZED AND TRAMPLED BY HORSES On-site determination. VEGETATION - Use scientific names of plants. Dominant Species? Absolute Rel.Strat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: ) % Cover Cover Status Number of Dominant Species 1. 0 ❑ 0.0% That are OBL, FACW, or FAC: 2 _ (A) 2. 0 ❑ 0.0% _m 0 ❑ 0 0% Total Number of Dominant 3, . Species Across All Strata: (B) 4. 0 ❑ o.o°r° Percent of dominant Species - Total Cover FAC Th t A OBL FACW 100.0 /o (A/B) ° Sapling /Shrub Stratum (Plot size ) or re , : a Woody Vine Stratum (Plot size: ) 1. _ 2. 4,Carex sp. 60 60.0%0 FACW Hydrophytic Vegetation Indicators: 5. Q,._ 0.0% W Dominance Test is > So% 6. 0 ❑ 0.0% Wl Prevalence index is 53.01 7 0 0.0% ❑ Morphological Adaptations 1 (Provide supporting 8 0 ❑ o.0% data in Remarks or on a separate sheet) 9 0 ❑ 0.0% ❑ Wetland Non-Vascular Plantsl 10. ❑ Problematic Hydrophytic Vegetationl (Explain) 11. 0 1:1 0.0ro 100 =Total Cover 1Indicators of hydric soil and wetland hydrology must be present, unless disturbed or problematic. w 1 0 ❑ 0.0% Prevalence Index worksheet: 2. ❑ o.o%. Total % Cover of:_. _ Multiply by: _ 3• 0 ❑ 0.0% OBL species 0 x 1 = 0 4. 0 ❑ o.0% FACW species 70 x 2 = 140 5. 0 ❑ 0.o% FAC species 30 x 3 = 90 0 - = Total Cover 0 FACU species x 4 = 0 Herb Stratum (Plot size: ) ° ~ 0 1 Potentilla sp. 10 ❑ 10.0% FACW UPL species - - x 5 = - Column Totals: (A) Z30 2. Poa sp. 25 ❑1 25.0% FAC 3 Trifolium repens 5 ❑ 5.0% FAC Prevalence Index = B/A = 2.3 00 (B) 0 El. 1 0.0% 0 ❑ 0.0% Hydrophytic 0 =Total Cover Vegetation Present? Yes * No ❑ % Bare Ground in Herb Stratum: 0 Remarks: • Poa sp. assumed FAC. Carex sp. and Potentilla sp assumed FACW. *Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version soil Sampling Point: 4A ._Y_..__ _ Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Depth Matrix Redox Features (inches) Color (moist) % Color (moist) % TypeI LOC2 Texture Remarks 0-7 10YR 2/1 100% Sandy silt loam DENSE ROOTS, VERY MOIST 7-16 10YR 5/2 95% 10YR 4/6 5% C PL Sand I E. _ 1 lType: C=Concentration. D=Depletion. RM=Reduced Matrix, CS=Covered or Coated Sand Grains zLocation: PL=Pore Lining. M=Matrix Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils:3 ❑ Histosol (Al) ❑ Sandy Redox (S5) ❑ 2 cm Muck (A10) ❑ Histic Epipedon (A2) ❑ Stripped Matrix (S6) ❑ Red Parent Material (TF2) ❑ Black Histic (A3) ❑ Loamy Mucky Mineral (Fl) (except in MLRA 1) EVI Other (Explain in Remarks) ❑ Hydrogen Sulfide (A4) ❑ Loamy Gleyed Matrix (F2) Depleted Below Dark Surface (All) ❑ Depleted Matrix (F3) El Thick Dark Surface (A12) El Redox Dark Surface (F6) ❑ De leted Dark Surface (F7) 3Indicators of hydrophytic vegetation and ❑ Sandy Muck Mineral (Sl) p wetland hydrology must be present, ❑ Sandy Gleyed Matrix (S4) ❑ Redox depressions (F8) unless disturbed or problematic. E Restrictive Layer (if present): i Type _ Depth (inches): _ Hydric Soil Present? Yes • No s Remarks: - PROBLEM SOIL. THERE ARE POCKETS OF FILLED MATERIAL IN WETLAND. t Hydrology f3 t Wetland Hydrology Indicators: Primary Indicators (minimum of one required; check all that apply) Secondary Indicators (minimum of two required) i ❑ Surface Water (Al) ❑ Water-Stained Leaves (B9) (except MLRA Water-Stained Leaves (B9) (MLRA 1, 2, ❑ High Water Table (A2) 1, 2, 4A, and 4B) 4A, and 4B) ❑ Saturation (A3) ❑ Salt Crust (Bll) ❑ Drainage Patterns (B10) El Water Marks (Bl) ❑ Aquatic Invertebrates (B13) ❑ Dry season water Table (C2) ❑ Sediment Deposits (B2) El Hydrogen Sulfide Odor (Cl) ❑ Saturation Visible on Aerial Imagery (C9) ❑ Drift deposits (B3) ❑ Oxidized Rhizospheres on Living Roots (0) ❑ Geomorphic Position (D2) ❑ Algal Mat or Crust (B4) ❑ Presence of Reduced Iron (C4) ❑ Shallow Aquitard (D3) ❑ Iron Deposits (B5) ❑ Recent Iron Reduction in Tilled Soils (C6) ❑ FAC-neutral Test (D5) ❑ Surface Soil Cracks (B6) ❑ Stunted or Stressed Plants (Dl) (LRR A) i ❑ Raised Ant Mounds (D6) (LRR A) 1 ❑ Inundation Visible on Aerial Imagery (B7) -1 Other (Explain in Remarks) El Frost Heave Hummocks (D7) ❑ Sparsely Vegetated Concave Surface (B8) Field Observations: Surface Water Present? Yes 0 No Depth (inches): Water Table Present? Yes No 0 Depth (inches): 15 Saturation Present? Wetland Hydrology Present? Yes 0 No 0 I (includes capillary fringe) Yes No 0 Depth (inches): 11 Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available: Remarks: • • US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version • WETLAND DETERMINATION DATA FORM - Arid West Region Project/Site: DESCHUTES LWI City/County: Sunriver/Deschutes Sampling Date: 03-May-10 Applicant/Owner: DESCHUTES COUNTY State: OR Sampling Point SP 5 Investigator(s): ALISON SIGLER, ROSEMARY BAKER Section, Township, Range: S 24 T 20S R 10E Landform (hillslope, terrace, etc): Floodplain Local relief (concave, convex, none): concave Slope: 0.0% / 0.0 ° Subregion (LRR): LRR B Lat.: 43.8312 Long.: -121.4737 Datum: NAD 83 Soil Map Unit Name: 29A: Cryaouo115 0 to 3 percent slopes NWI classification R2UBH. Are climatic/hydrologic conditions on the site typical for this time of year? Yes NO ❑ (If no, explain in Remarks.) Are Vegetation ❑ , Soil ❑ , or Hydrology ❑ significantly disturbed? Are "Normal Circumstances" present? Yes No ❑ Are Vegetation ❑ , Soil , or Hydrology ❑ naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transects, important features, etc. Hydrophytic Vegetation Present? Yes * NO ❑ Is the Sampled Area Hydric Soil Present? Yes 0 NO ❑ Yes 0 No ❑ Wetland Hydrology Present? Yes 0 No ❑ within a Wetland? Remarks: On-site determination. VEGETATION - Use scientific names of plants. Dominant Species? Absolute Rel.Strat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: ) % Cover Cover Status Number of Dominant Species 1. 0 ❑ 0.0% That are OBL, FACW, or FAC: 2 (A) 2. 0 El o.00/- ° Total Number of Dominant 3• ❑ 0.0 /o m _ Species Across All Strata: 2_ (B) 4. 0 ❑ 0.0% 0 = Total Cover Percent of dominant Species o Sapling/Shrub Stratum (Plot size: ) That Are OBL, FACW, or FAC: 10070 /o (A/B) 1. 0 ❑ 0.o% Prevalence Index worksheet: 2. 0 ❑ o.0% Total % Cover of; Multiply by: 3. 0 ❑ 0.0% !OBL species 50 x 1 = 50 4. 0 ❑ 0.0% FACW species 0 x 2= 0 5. 0 ❑ 0.0°i° IFAC species 25 x 3 75 0 =Total Cover FACU species x 4 = Herb Stratum (Plot size: ) 1. Carex aquatilis 50 66.7% OBL UPL species 0 x 5 = Column Totals: 75 (A) 125 (B) 2. Equisetum arvense 25❑ 33.3% FAC 3. 0 ❑ 0.o% Prevalence Index = B/A = 1.667 4 0 ❑ 0.0% Hydrophytic Vegetation Indicators: 5. ❑y 0.0% Dominance Test is > 50% 6. ❑ o.o°ro_ 1 Prevalence Index is 53.0 7. 0 ❑ 0.0% 1 ❑ Morphological Adaptations 1 -rovide supporting 8. ❑ ..Oct%_ data in Remarks or on a separate sheet) 9, 0 ❑ 0.0% 1 _a ❑ Problematic Hydrophytic Vegetation 1 ( :plain) 10. o ❑ 0.0% 11. o ❑ 0.0% 75 = Total Cover 1 Indicators of hydric soil and wetland hydrology must be present, unless disturbed or problematic. Woody Vine Stratum (Plot size: ) L 0 ❑ o.o% 2. 0 ❑ 0.0% Hydrophytic Vegetation 0 = Total Cover Present? Yes 0 No % Bare Ground in Herb Stratum: 25 % Cover of Biotic Crust 0 Remarks: - *Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS. US Army Corps of Engineers Arid West - Version 2 Oct. 2008 Soil Sampling Point: SP 5 Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Depth ._._.__Matrix Redox Features (inches) Color (moist) % Color (moist) % Type 1 Loo= Texture Remarks 0-3 10YR 2/2 100% Loam DENSE ROOTS i 3-20 10YR 4/2 85% 7.5YR 4/6 15% C M Silty Clay Loam Type: C=Concentration. D=Depletion. RM=Reduced Matrix, CS=Covered or Coated Sand Grains 2Location: PL=Pore Lining. M=Matroc I Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils3 ❑ Histosol (AS) ❑ Sandy Redox (S5) ❑ 1 cm Muck (A9) (LRR C) ❑ Histic Epipedon (A2) ❑ Stripped Matrix (S6) ❑ 2 cm Muck (A10) (LRR B) ❑ Black Histic (A3) ❑ Hydrogen Sulfide (A4) ❑ Loamy Mucky Mineral (FS) ❑ Reduced Vertic (F18) ❑ Stratified Layers (AS) (LRR C) ❑ Loamy Gleyed Matrix (F2) ❑ Red Parent Material (TF2) ❑ 1 cm Muck (A9) (LRR D) ❑ Depleted Matrix (F3) ❑ Other (Explain in Remarks) ❑ Depleted Below Dark Surface (All) ❑ Redox Dark Surface (F6) ❑ Thick Dark Surface (A12) ❑ Depleted Dario Surface (F7) ❑ Sandy Muck Mineral (Si) ❑ Redox depressions (F8) ❑ Vernal Pools (F9) 3 Indicators of hydrophytic vegetation and ❑ Sandy Gleyed Matrix (S4) wetland hydrology must be present. Restrictive Layer (if present): Type Depth (inches): - Soil Present? Yes NO i Remarks: Remarks: Hydrology Wetland Hydrology Indicators: y I Primary .Indicators (minimum of one_required; check all that apply) Secondary Indicators (2 or more required) ❑ Surface Water (Al) ❑ Salt Crust (B11) ❑ Water Marks (BI) (Riverine) 0 High Water Table (A2) ❑ Biotic Crust (B12) ❑ Sediment Deposits (B2) (Riverine) • Saturation (A3) ❑ Aquatic Invertebrates (B13) ❑ Drift Deposits (B3) Riverine) ❑ Water Marks (BI) (Nonriverine) ❑ Hydrogen Sulfide Odor (Cl) ❑ Drainage Patterns (B10) ❑ Sediment Deposits (B2) (Nonriverine) ❑ Oxidized Rhizospheres along Living Roots (0) ❑ Dry season water Table (C2) i ❑ Drift deposits (B3) (Nonriverine) ❑ Presence of Reduced Iron (C4) ❑ Crayfish Burrows (C8) ❑ Surface Soil Cracks (B6) ❑ Recent Iron Reduction in Plowed Soils (C6) ❑ Saturation Visible on Aerial Imagery (C9) ❑ Inundation Visible on Aerial Imagery (B7) ❑ Thin Muck Surface (C7) ❑ Shallow Aquitard (D3) ❑ Water-Stained Leaves (B9) El Other (Explain in Remarks) L FAC-neutral Test (D5) Field Observations: _ Surface Water Present? Yes ❑ No Depth (inches): Water Table Present? Yes No O Depth (inches): 12 Saturation Present? Wetland Hydrology Present? Yes * No 1 (includes capillary fringe) Yes No ❑ Depth (inches): Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available: Remarks: _ l US Army Corps of Engineers Arid West - Version 2 Oct. 2008 • • • WETLAND DETERMINATION DATA FORM - Western Mountains, Valleys, and Coast Region Project/Site: DESCHUTES LWI City/County: SUNRIVER/DESCHUTES Sampling Date: 21-Jun-10 • Applicant/Owner DES CHUTES COUNTY State: OR Sampling Point SP 5A Investigator(s) ALISON SIGLER, SARAH HARTUNG Section, Township, Range: S 14 T 21 S R 10 E Landform (hillslope, terrace, etc.): Valley bottom Local relief (concave, convex, none): concave Slope: 0.0% / 0.0 ° Subregion (LRR): LRR A Lat.: 43.7526 Long.: -121.4962 Datum: NAD83 Soil Map Unit Name: 144A: SUnrivpr spn& loam,, 0 to 3 pe.rpen I m NWI classification: Are climatic/ hydrologic conditions on the site typical for this time of year? Yes ! No (If no, explain in Remarks.) Are Vegetation , Soil , or Hydrology significantly disturbed? Are "Normal Circumstances" present? Yes No Are Vegetation , Soil L , or Hydrology naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transects, important features, et Hydrophytic Vegetation Present? Yes NO ❑ Is the Sampled Area Hydric Soil Present? Yes No within a Wetland? Yes -l No Wetland Hydrology Present? Yes No Remarks: - On-site determination. VEGETATION - Use scientific names of plants. Dominant Species? Absolute Rel.Strat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: ) % Cover Cover Status ' j i Number o Dominant Species 1. Pinus contorta 5 100.0% FAC That are OBL, FACW, or FAC: 2 (A) _ 3 0 ❑ 0.0% Total Number of Dominant , _ Species Across All Strata: _ 2 (B) 4. o ❑ 0.0% Percent of dominant Species Sapling/Shrub Stratum (Plot size: ) 5 = Total Cover ° That Are OBL, FACW, or FAC: 1010.9% (A/B) 1, 0 0.0% Prevalence Index worksheet: 2• 0 ❑ 0.0% Total % Cover of: Multiply by 3. 0 1 ..0.0% OBL species 0 x 1= 0 4. o f o.o°r° FACW species 70 x 2 = 140, . 5. 0 ❑ 0.0% FAC species 27 x 3 _ 81 0 = Total Cover 2 8 FACII species x 4 = Herb Stratum (Plot size: ) 0 ~ Juncussp. 1 70 74.5% FACW UPL species - x 5 . E ilobium s _ 5 ❑ 5.3 /o FAC Column Totals: _ 99 (A) 229 (B) i 3 Iris douglasiana 5 ] 5.3% FAC Prevalence Index = B/A = 2.313 4. Poa palustris - 10 ❑ 10.6% FAC Hydrophytic Vegetation Indicators: 5. Trifolium sp. 2 L l 2.1% FAC rdl Dominance Test is > 50% j 6 Sidalcea sp. 2 2.1% FACU I U Prevalence index is :53.01 7• 0 ❑ 0.o% L i Morphological Adaptations 1 (Provide supporting 8 0 ❑ 0.9% data in Remarks or on a separate sheet) 9, 0 ❑ _0.0% Wetland Non-Vascular Plantsl 10 El F_ Problematic Hydrophytic Vegetationl (Explain) 11. 0 0.0/o ° 94 = Total Cover 1Indicators of hydric soil and wetland hydrology must - be present, unless disturbed or problematic. - Woody Vine Stratum (Plot size: ) 1 0 ❑ 0.0% 2. 0 0.0% Hydrophytic 0 = Total Cover Vegetation Present? Yes No - % Bare Ground in Herb Stratum: 6 Remarks: • Trilfolium sp. assumed FAC. Sidalcea sp. assumed FACU. *Indicator suffix = National status or professional decision assigned because Regional status not de fined by FWS US Army Corps of Engineers Wester n Mountains, Valleys, and Coast Region Interim version Soil Sampling Point: 5A Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Depth Matrix (inches) Color (moist) % Redox Features Color (moist) % Type1 Locz • Texture Remarks 0-11 IOYR 2/1 100% Silt Loam 11-18 IOYR 3/1 100% Silty Clay 1Type: C=Concentration. D=Depletion. RM=Redu ced Matrix, CS=Covered or Coated Sand Grains 21-ocation: PL=Pore Lining. M=Matrix Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils:3 ❑ Histosol (Al) ❑ Sandy Redox (S5) ❑ 2 cm Muck (A10) ❑ Histic Epipedon (A2) L Stripped Matrix (S6) ❑ Red Parent Material (TF2) ❑ Black Histic (A3) ❑ Loamy Mucky Mineral (Fl) (except in MLRA 1) ❑ Other (Explain in Remarks) ❑ Hydrogen Sulfide (A4) ❑ Loamy Gleyed Matrix (F2) ❑ Depleted Below Dark Surface (All) Depleted Matrix (F3) ❑ Thick Dark Surface (A12) E' Redox Dark Surface (F6) 3Indicators of hydrophytic vegetation and ❑ Sandy Muck Mineral (Si) L_j Depleted Dark Surface (F7) wetland hydrology must be present, n 1-4,, rio...1 near,., rca) LJ Redox depressions (F8) unless disturbed or problematic. Restrictive Layer (if present): Depth (inches): Hydric Soil Presents • Type: Yes O No Remarks: I Hydrology i Wetland Hydrology Indicators: Primary Indicators (minimum of one required; check all that apply) Secondary Indicators (minimum of two required) ❑ Surface Water (A1) ❑ Water-Stained Leaves (B9) (except MLRA ❑ Water-Stained Leaves (B9) (MLRA 1, 2, ❑ High Water Table (A2) 1, 2, 4A, and 4B) 4A, and 4B) ❑ Saturation (A3) ❑ Salt Crust (Bll) ❑ Drainage Patterns (B10) ❑ Water Marks (BI) ❑ Aquatic Invertebrates (B13) ❑ Dry season water Table (C2) ❑ Sediment Deposits (B2) ❑ Hydrogen Sulfide Odor (Cl) ❑ Saturation Visible on Aerial Imagery (C9) ❑ Drift deposits (B3) ❑ Oxidized Rhizospheres on Living Roots (0) ❑ Geomorphic Position (D2) ❑ Algal Mat or Crust (B4) ❑ Presence of Reduced Iron (C4) ❑ Shallow Aquitard (D3) I ❑ Iron Deposits (B5) ❑ Recent Iron Reduction in Tilled Soils (C6) ❑ FAC-neutral Test (D5) ❑ Surface Soil Cracks (B6) ❑ Stunted or stressed Plants (Dl) (LRR A) ❑ Raised Ant Mounds (D6) (LRR A) ❑ Inundation Visible on Aerial Imagery (B7) ❑ Other (Explain in Remarks) ❑ Frost Heave Hummocks (D7) ❑ Sparsely vegetated Concave Surface (B8) Field Observations: Surface Water Present? Yes 0 No Depth (inches): Water Table Present? Yes 0 No Depth (inches): Saturation Present? Wetland Hydrology Present? Yes 0 No (includes capillary fringe) Yes 0 No Depth (inches): Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available: Remarks: US Army Corps of Engineers Western Mountains, Valleys, and Coast Region - Interim version • WETLAND DETERMINATION DATA FORM - Arid West Region Project/Site: DESCHUTES LWI City/County: Sunriver/Deschutes Sampling Date:,-"-- . _ Applicant/owner: 05-May-10 DESCHUTES COUNTY State: OR Sampling Point: SP 6 Investigator(s) ALISON SIGLER, ROSEMARY BAKER Section, Township, Range: S 24 T 20 S R 10 E Landform (hillslope, terrace, etc.): Floodplain Local relief (concave, convex, none): concave Slope: 0.0% / 0.0 ° Subregion (LRR): LRR B Lat.: 43.8323 Long.: -121.4704 Datum: NAD 83 Soil Map Unit Name: 29A: Gyaquolls, 0 to 3 percent slopes,___ NWI classification: PEMC Are climatic/hydrologic conditions on the site typical for this time of year? Yes 0 No O (If no, explain in Remarks.) Are Vegetation Soil ❑ , or Hydrology ❑ significantly disturbed? Are "Normal Circumstances" present? Yes 0 NO O Are Vegetation F-I , Soil ❑ , or Hydrology ❑ naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transects, important features, etc. Hydrophytic Vegetation Present? Yes 0 No Hydric Soil Present? Yes '0 No Is the Sampled Area Yes * NO 0 Wetland Hydrology Present? Yes 0 NO O within a Wetland? Remarks: - - - On-site determination. VEGETATION - Use scientific names of plants. Dominant Species? Absolute Rel.Strat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: ) % Cover Cover Status a, Number of Dominant Species 1•. , 0 ❑ 0.0% That are OBL, FACW, or FAC: 1 (A) 2. 0 ❑ 0.0% 3 0 ❑ 0 0% Total Number of Dominant . . Species Across All Strata: 1 (B) 4. o ❑ o.o°r° o =Total Cover ercent of dominant Species Sapling/Shrub Stratum (Plot size: [P hat Are OBL, FACW, or FAC: 100.0%1.1 (A/B) 1. 0 ❑ 0.0% Prevalence Index worksheet: 2. o ❑ 0.0%- Total % Cover of: Multiply 1by. 3. 0 ❑ 0.o% OBL species 70 x 1 = 70 4. 0 El 0.0% FACW species 2 x 2= 4 0 ❑ 0.0% FAC species x 3 = 15 0 Total Cover = Fspecies _0 x 4 = .0 Herb Stratum (Plot size: ) 0 0 1 Carex aquatilis 70 ❑ 90.9% OBL UPL species x 5 = . I 77 Column totals: (A) 9 (e) 2. Ranunculus repens 2 El 2.6% FACW , 3. Rumex crispus 5 ❑ 6.5% FAC Prevalence Index = B/A = 1.156 4. 0 ❑ 0.00( Hydrophytic Vegetation Indicators: 5 . 0 0 El 0.0% Dominance Test is > 90% 6. 0 ❑ 0.0% LV Prevalence Index is <_3.0 1 7. 0 0.0% % ❑ ❑ Morphological Adaptations 1 i. Irovide supporting 0 0.0 data in Remarks or on a separate sheet) 9. 0 El 0.0% ❑ Problematic Hydrophytic Vegetation 1 (1 :plain) 10. 0 - ❑ 0.0% 11. 0 ❑ o.o% 1 Indicators of hydric soil and wetland hydrology must 77 - = Total Cover be present, unless disturbed or problematic. Woody Vine Stratum (Plot size: ) - - 1. 0 ❑ 0.0% 2. 0 ❑ 0.0% Hydrophytic 0 = Total Cover Vegetation Present? Yes 0 No O % Bare Ground in Herb Stratum: 23 '/o Cover of Biotic Crust 0 1 • Remarks: RUMEX ROOTS, VEGETATIVE NOT PRESENT - E t *Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS. US Army Corps of Engineers Arid West - Version 2 Oct. 2008 Soil Sampling Point: SP 6 Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Depth Matrix Redox Features (inches) Color (moist) % Color (moist) % Type 1 Loc= Texture Remarks 0-2 10YR 2/2 100% Silt Loam 2-20 10YR 3/2 82% 10YR 4/6 10% C M Silt Loam 2 types of redox 10YR 5/6 2% C M C` 1 Type: C=Concentration. D=Depletion. RM=Reduced Matrix, CS=Covered or Coated Sand Grains 21-ocation: PL=Pore Lining. M=Matrix Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) j Indicators for Problematic Hydric Soils3 I ❑ Histosol (Al) ❑ Sandy Redox (S5) ❑ 1 cm Muck (A9) (LRR C) ❑ Histic Epipedon (A2) ❑ Stripped Matrix (S6) ❑ 2 cm Muck (A10) (LRR B) ❑ Black Histic (A3) ❑ Loamy Mucky Mineral (FS) ❑ Reduced Vertic (F18) j ❑ Hydrogen Sulfide (A4) ❑ Loamy Gleyed Matrix (F2) ❑ Red Parent Material (TF2) El Stratified Layers (AS) (LRR C) ❑ Depleted Matrix (F3) ❑ Other (Explain in Remarks) ❑ 1 cm Muck (A9) (LRR D) Redox Dark Surface (F6) El Depleted Below Dark Surface (All) ❑ Depleted Dark Surface (F7) ❑ Thick Dark Surface (A12) ❑ Redox depressions (F8) ❑ Sandy Muck Mineral (Sl) ❑ Vernal Pools (F9) 3 Indicators of hydrophytic vegetation and ❑ Sandy Gleyed Matrix (S4) wetland hydrology must be present. Restrictive Layer (if present): Type: Depth (inches): Hydric Soil Present? Yes NO 0 Remarks: • Hydrology Wetland Hydrology Indicators: Primarv Indicators,(minimum of one required;_check all that apply) Secondary Indicators (2 or more required) ❑ Surface Water (Al) ❑ Salt Crust (Bll) ❑ Water Marks (Bl) (Riverine) ❑ High Water Table (A2) ❑ Biotic Crust (B12) ❑ Sediment Deposits (B2) (Riverine) Saturation (A3) ❑ Aquatic Invertebrates (B13) ❑ Drift Deposits (B3) Riverine) ❑ Water Marks (Bl) (Nonriverine) ❑ Hydrogen Sulfide Odor (Cl) ❑ Drainage Patterns (B10) ❑ Sediment Deposits (B2) (Nonriverine) ❑ Oxidized Rhizospheres along Living Roots (0) ❑ Dry Season Water Table (C2) ❑ Drift deposits (B3) (Nonriverine) ❑ Presence of Reduced Iron (C4) Crayfish Burrows (C8) ❑ Surface Soil Cracks (B6) ❑ Recent Iron Reduction in Plowed Soils (C6) ❑ Saturation Visible on Aerial Imagery (C9) ❑ Inundation Visible on Aerial Imagery (B7) ❑ Thin Muck Surface (0) ] Shallow Aquitard (D3) ❑ Water-Stained Leaves (B9) ❑ Other (Explain in Remarks) ❑ FAC-neutral Test (D5) Field Observations: Surface Water Present? Yes 0 No Depth (inches): F Water Table Present? Yes 0 No O Depth (inches): Saturation Present? Yes 0 Wetland Hydrology Present? NO 0 Depth (inches): E ° J (includes capillary fringe) Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available: - Remarks: - Yes No 0 j i US Army Corps of Engineers Arid West - Version 2 Oct. 2008 WETLAND DETERMINATION DATA FORM - Western Mountains, Valleys, and Coast Region Project/Site: DESCHUTES LWI City/County: SUNRNER/DESCHUTES Sampling Date: 21-Jun-10 • Applicant/Owner: DESCHUTES COUNTY State: OR Sampling Point: SP 6A Investigator(s): ALISON SIGLER, SARAH HARTUNG Section, Township, Range. S 14 T 21 S R 10 E Landform (hillslope, terrace, etc.): Lowland Local relief (concave, convex, none): flat Slope: 2.0% / 1.1 ° Subregion (LRR): LRR A Lat.: 43.7485 Long.: -121.4932 Datum: NAD83 Soil Map Unit Name:_29A;-_CryagiQll >0 3CCntIQp~ _ NWI classification: Are climatic/ hydrologic conditions on the site typical for this time of yeas'? Yes No O (If no, explain in Remarks.) Are Vegetation ❑ , Soil ❑ , or Hydrology ❑ significantly disturbed? Are "Normal Circumstances" present? Yes 0 No ❑ Are Vegetation ❑ , Soil ❑ , or Hydrology ❑ naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transects, important features, et • Hydrophytic Vegetation Present? Yes No ❑ Is the Sampled Area Hydric Soil Present? Yes 0 No ❑ within a Wetland? Yes ❑ No ❑ Wetland Hydrology Present? Yes O No ❑ Remarks: On-site determination. Woody Vine Stratum (Plot size: ) 1. 0 ❑ 0.0% 2. 0 ❑ 0.0% 0 = Total Cover VEGETATION - Use scientific names of plants. Dominant _ Species? Absolute Rel.Strat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: ) % Cover Cover Status ❑ Number of Dominant Species 1,.._ _ 0 0.0% That are OBL, FACW, or FAC: 3 (A) 0 ❑ 0.0°ro 3 _ 0 ❑ 0 0% Total Number of Dominant • _ _ . Species Across All strata: 3 (B) 4. o ❑ o.o% 0 = Total Cover Percent of dominant Species o 100.0 /o (A/13) Sapling/ Shrub Stratum (Plot size: That Are OBL, FACW, or FAC: _ 1. Salix exigua _70- ❑ 100.0% OBL___.. Prevalence Index worksheet: 2. 0 ❑ 0.0% Total % Cover of: Multiply by: 3. 0- ❑ 0.0% OBL species 70 x 1 = 70 4. 0 ❑ 0.0% FACW species 85 x 2 = 170 5. 0 ❑ 0.0% FAC species Q x 3 0_ 70 = Total Cover FACU species 0 x 4 = 0 Herb Stratum (Plot size: l i J b 50 ❑ 58 8% CW UPL species - - - x 5 = uncus 1. a t cus . FA . 2. Carex sp. 30 n 35.3% FACW Column Totals: _155 _ (A) 240 (B) 3 Rumex occidentalis 5 L J 5.9% FACW Prevalence Index = B/A = 17548 4. 0 ❑ 0.0% Hydrophytic Vegetation Indicators: 5. 0 ❑ 0.0% LVI Dominance Test is > 50% 6. 0 o ❑ 0.0 /o - Prevalence index is :53.01 7 0 ❑ 0.0% Morphological Adaptations' (Provide supporting 8 0 ❑ 0.0% data in Remarks or on a separate sheet) 9, _ 0 ❑ 0.0% ❑ Wetland Non-Vascular Piantsl 10. 0 ❑ 0.0% Problematic Hydrophytic Vegetation' (Explain) El 0 0 El 0.0% 85 =Total Cover 'Indicators of hydric soil and wetland hydrology must be present, unless disturbed or problematic. % Bare Ground in Herb Stratum: 15 Hydrophytic Vegetation Present? Yes* No ❑ Remarks: • Carex sp. assumed to be FACW. _ *Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version Soil Sampling Point: 6A Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) € Depth Matrix Redox Features , (inches) Color (moist) % Color (moist) % Type 1 Locz Texture Remarks 0-2 IOYR 2/1 100% muck 2-20 IOYR 3/1 20% peat mixed matrix, 2 layers 10YR 3/2 80% peat mixed matrix 1Type: C=Concentration. D=Depletion. RM=Redu i ced Matrix, CS=Covered or Coated Sand Grains zLocation: PL=Pore Lining. M=Matrix Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils:3 ❑ Histosol (Al) ❑ Sandy Redox (SS) ❑ 2 cm Muck (A10) ❑ Histic Epipedon (A2) ❑ Stripped Matrix (S6) ❑ Red Parent Material (TF2) ❑ Black Histic (A3) ❑ Loamy Mucky Mineral (Fl) (except in MLRA 1) ❑ Other (Explain in Remarks) ❑ Hydrogen Sulfide (A4) ❑ Loamy Gleyed Matrix (F2) ❑ Depleted Below Dark Surface (All) ❑ Depleted Matrix (F3) ❑ Thick Dark Surface (A12) Redox Dark Surface (F6) g Indicators of hydrophytic vegetation and ❑ Sandy Muck Mineral (Sl) ❑ Depleted Dark Surface (F7) wetland hydrology must be present, ❑ Sandy Gleyed Matrix (S4) ❑ Redox depressions (F8) unless disturbed or problematic. I Restrictive Layer (if present): Type: Depth (inches): Hydric Soil Present? Yes NO ❑ Remarks: Hydrology Wetland Hydrology Indicators: Primary Indicators (minimum of one required; check all that apply) Secondary Indicators (minimum of two required) ❑ Surface Water (A1) ❑ Water-Stained Leaves (B9) (except MLRA ❑ Water-Stained Leaves (B9) (MLRA 1, 2, V High Water Table (A2) 1, 2, 4A, and 4B) 4A, and 4B) 0 Saturation (A3) ❑ Salt Crust (BIl) ❑ Drainage Patterns (B10) ❑ Water Marks (Bl) ❑ Aquatic Invertebrates (B13) ❑ Dry Season Water Table (C2) ❑ Sediment Deposits (B2) ❑ Hydrogen Sulfide Odor (Cl) ❑ Saturation Visible on Aerial Imagery (C9) ❑ Drift deposits (B3) ❑ Oxidized Rhizospheres on Living Roots (0) ❑ Geomorphic Position (D2) ❑ Algal Mat or Crust (B4) ❑ Presence of Reduced Iron (C4) ❑ Shallow Aquitard (D3) ❑ Iron Deposits (B5) ❑ Recent Iron Reduction in Tilled Soils (C6) ❑ FAC-neutral Test (D5) ❑ Surface Soil Cracks (B6) ❑ Stunted or stressed Plants (Dl) (LRR A) ❑ Raised Ant Mounds (D6) (LRR A) ❑ Inundation Visible on Aerial Imagery (B7) ❑ Other (Explain in Remarks) ❑ Frost Heave Hummocks (D7) ❑ Sparsely vegetated concave Surface (B8) Field Observations: _ Surface Water Present? Yes ❑ No Depth (inches): Water Table Present? Yes No ❑ Depth (inches): 12 'Saturation Present? Wetiand Hydrology Present? Yes 0 No ❑ (includes capillary fringe) Yes NO ❑ Depth (inches): Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available: Remarks: • • US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version 0 WETLAND DETERMINATION DATA FORM - Arid West Region Project/Site: DESCHUTES LWI City/County: Sunriver/Deschutes Sampling Date: 05-May-10 ,Applicant/owner: DESCHUTES COUNTY State: OR Sampling Point: SP 7 Investigator(s):_ALISON SIGLER, ROSEMARY BAKER Section, Township, Range: S 13 T 20 S R 10 E Landform (hillslope, terrace, etc.): Floodplain Local relief (concave, convex, none): concave Slope: 0.0% / 0.0 ° Subregion (LRR): LRR B Lat.: 43.8341 Long.: -121.4745 Datum: NAD 83 Soil Map Unit Name: 144A: Sunriver sand loam , 0 to 3 percent slopes__ NWI classification: R2UBH._, a. Are climatic/hydrologic conditions on the site typical for this time of year? Yes' No (If no, explain in Remarks.) Are Vegetation , Soil ❑ , or Hydrology D significantly disturbed? Are "Normal Circumstances" present? Yes No (-1 Are Vegetation L_--I , soil L J , or Hydrology J naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transects, important features, etc. Hydrophytic Vegetation Present? Yes NO IS the Sampled Area Hydric Soil Present? Yes No . ~P a Wetland? Yes No Wetland Hydrology Present? Yes NO within On-site determination. VEGETATION - Use scientific names of plants. Dominant _..Species? Absolute Rel.Strat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: ) % Cover Cover Status 1. _ 0- L 0.0% Number of Dominant Species That are OBL, FACW, or FAC: 1 (A) 2• 0 0.0% Total Number of Dominant 3 ° . 0 0.0 ro Species Across All Strata: 1 (B) 4. 0 ❑ o.0% 0 Total Cover Percent of dominant Species ° 100.0% (A/B) Sapling/Shrub Stratum (Plot size: ) That Are OBL, FACW, or FAC: 1• 0 0.0% Prevalence Index worksheet: 2. 0 L 0.0% Total % Cover of: Multiply by: , 3• 0 0.0% x l = 80 IOBL species 80 4. 0 0.0% _ I FACW species 0 x 2= 0 5• 0 FAC species 0___ x 3 = 0 0 =Total Cover Fspecies x 4 = 0 Herb Stratum (Plot size: ) 0 0 C b i 75 93 8% OBL UPL species x 5 = arex ne rascens s . I Column Totals: 80 (A) 80 (B) 2• Carex aquatilis 5 i 6.3% OBL 3 0 h 0.0 /o Prevalence Index = B/A = 1.000 4. o 0. Hydrophytic Vegetation Indicators: 5. 0.0% Dominance Test is > SO% 6. 0 0.0% _ Prevalence index is 53.0 i 7, 0 Ll 0.0% i ~ Morphological Adaptations 1 _ provide supporting 8• 0 -1 0.0% _ , data in Remarks or on a separate sheet) 9• 0 _ 0 0.0 /o Problematic Hydrophytic Vegetation 1 (t :plain) 10. _ 0 11. o _7 o.o°ro Woody Vine Stratum (Plot size: ) 1. 2. % Bare Ground in Herb Stratum: 20 • Remarks: i 80 = Total Cover t Indicators of hydric soil and wetland hydrology must be present, unless disturbed or problematic. 0 LJ 0.0% 0 El 0.0% Hydrophytic Vegetation 0 = Total Cover Present? Yes No % Cover of Biotic Crust 0 *Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS. US Army Corps of Engineers Arid West - Version 2 Oct. 2008 Soil Sampling Point: SP 7 Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) • Matrix Depth Redox Features (inches) Color (moist) '/o Color (moist) % Type Loc2 Texture Remarks i 0-6 10YR 3/2 100% Silt 6-13 10YR 4/2 100% Silt 13-20 10YR 3/2 95% 7.5YR 4/4 5% C PL Silt i 1 Type: C=Concentration. D=Depletion. RM=Reduced Matrix, CS=Covered or Coated Sand Grains 2Location: PL=Pore Lining. M=Matrbx Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils3 ❑ Histosol (Al) ❑ Sandy Redox (S5) ❑ 1 cm Muck (A9) (LRR C) ❑ Histic Epipedon (A2) ❑ Stripped Matrix (S6) ❑ 2 cm Muck (A10) (LRR B) ❑ Black Histic (A3) ❑ Loamy Mucky Mineral (Fl) ❑ Reduced Vertic (F18) ❑ Hydrogen Sulfide (A4) ❑ Loamy Gleyed Matrix (F2) ❑ Red Parent Material (TF2) ❑ Stratified Layers (AS) (LRR C) ❑ Depleted Matrix (F3) G Other (Explain in Remarks) ❑ 1 cm Muck (A9) (LRR D) ❑ Redox Dark Surface (F6) ❑ Depleted Below Dark Surface (All) ❑ Depleted Dark Surface (F7) ❑ Thick Dark Surface (A12) ❑ Redox depressions (F8) ❑ Sandy Muck Mineral (Sl) ❑ Vernal Pools (F9) 3 Indicators of hydrophytic vegetation and ❑ Sandy Gleyed Matrix (S4) wetland hydrology must be present. Restrictive Layer (if present): Type: Depth (inches): Hydric Soil Present? Yes * No O Remarks: HYDRIC SOILS ASSUMED BASED ON WETLAND HYDROLOGY INDICATORS. HAS CHARCOAL IN TRACE AMOUNTS THROUGH ENTIRE PROFILE. Hydrology Wetland Hydrology Indicators: Primary Indicators (minimum of one required: check all that,a I Secondary Indicators (2 or more required) ❑ Surface Water (Al) ❑ Salt Crust (BI I) ❑ Water Marks (Bl) (Riverine) ❑ High Water Table (A2) ❑ Biotic Crust (B12) ❑ Sediment Deposits (B2) (Riverine) 0 Saturation (A3) ❑ Aquatic Invertebrates (B13) ❑ Drift Deposits (B3) Riverine) ❑ Water Marks (Bl) (Nonriverine) ❑ Hydrogen Sulfide Odor (Cl) ❑ Drainage Patterns (B10) ❑ Sediment Deposits (B2) (Nonriverine) ❑ Oxidized Rhizospheres along Living Roots (0) ❑ Dry Season Water Table (C2) ❑ Drift deposits (B3) (Nonriverine) ❑ Presence of Reduced Iron (C4) ❑ Crayfish Burrows (CS) ❑ Surface Soil Cracks (B6) ❑ Recent Iron Reduction in Plowed Soils (C6) ❑ Saturation Visible on Aerial Imagery (C9) ❑ Inundation Visible on Aerial Imagery (B7) ❑ Thin Muck Surface (C7) ❑ Shallow Aquitard (D3) ❑ Water-Stained Leaves (B9) ❑ Other (Explain in Remarks) ❑ FAC-neutral Test (D5) Field Observations: Surface Water Present? Yes O NO Depth (inches): F Water Table Present? Yes NO ❑ 12 Depth (inches): L Saturation Present? Wetland Hydrology Present? Yes O NO ❑ (includes capillary fringe) Yes U NO ❑ Depth (inches): Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available: Remarks: US Army Corps of Engineers • • Arid West - Version 2 Oct. 2008 WETLAND DETERMINATION DATA FORM - Western Mountains, Valleys, and Coast Region Project/Site:_DESCHUTES LWI City/County: SUNRIVER/DESCHUTES Sampling Date: 21-Jun-10 • Applicant/Owner: DESCHUTES COUNTY State: OR Sampling Point: SP 7A Investigator(s):_ALISON SIGLER, SARAH HARTUNG Section, Township, Range: S 35 T 2.0 S R 10 E Landform (hillslope, terrace, etc.): Floodplain Local relief (concave, convex, none): flat Slope: 1.0% / 006 ° Subregion (LRR): LRR A Lat.: 43.7968 Long.: -121.5008 Datum: NAD83 Soil Map Unit Name: Wpter NWI classification: pEMF _ Are climatic/ hydrologic conditions on the site typical for this time of year? Yes * No ❑ -(If no, explain in Remarks.) Are Vegetation ❑ , Soil ❑ , or Hydrology ❑ significantly disturbed? Are "Normal Circumstances" present? Yes * No ❑ Are Vegetation ❑ , Soil ❑ , or Hydrology ❑ naturally problematic? (If needed, explain any answers in Remarks.) Aa__V ~h.,...:..n c=mnlinn nnint Incations. transects, important features, et JY11111101 y V■ 111~"~~7v ...~r . Hydrophytic Vegetation Present? Yes No ❑ Is the Sampled Area Hydric Soil Present? Yes No ❑ within a Wetland? Yes * No ❑ Wetland Hydrology Present? Yes No ❑ Remarks: DIRT ROADS BLOCKED; COULD NOT ACCESS. OFF-SITE DATA PLOT VEGETATION - Use scientific names of plants. Dominant Species? Absolute Rel.Strat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: ) % Cover _ Cover Status Number of Dominant Species 30 100.0% FAC That are OBL, FACW, or FAC: 1 Pinus contorts - 0 ❑ O.o% - Total Number of Dominant 3 0 ❑ 0.0% Species Across All Strata: 0 ❑ 0. Percent of dominant Species 30 = Total Cover BL FACW r FAC• Saplmg/Shrub Stratum (Plot size: 1 • 1 Salix exigua 10 100.0% OBL C~ 2 0 El 0.0% 3 0 ❑ 0.0% _ 4. 0 E-1 0.00/0 5. ° 10 =Total Cover Herb Stratum (Plot size: ) 1 Juncus balticus 50 50.0% FACW Carex nebrascensis 10 ❑ 10.0% OBL 3 Carexaquatilis_ 40 40.0% OBL 0 ❑ 0.00/0 4 0 0 El 0 ❑ 0.0% 6 0 0.0% 7P 0 El 0.0% 9. 0 ❑ 0.0%._ 0 ❑ 0.0% 100 = Total Cover i Woody Vine Stratum (Plot size: ) 1• 0 El 0.o% 2 0 El 0.0% _0 = Total Cover O/o Bare Ground in Herb Stratum: 0 Remarks: • That Are 0 , , o 4 - (A) 4 (B) 100.0% (A/B) Prevalence Index worksheet: Total % Cover of: Multiply by: W OBL species 60-- x 1 = _ 60 - FACw species ~50 x 2 = 100 FAC species --30- x 3 = _ 90 _ FACU species _0___ x 4 = -0-- 0 UPL species - x 5 = Column Totals: .140 (A) _ _250_ Prevalence Index = B/A = _ 1.786 Hydrophytic Vegetation Indicators: V Dominance Test is > 50% Prevalence Index is :53.01 ❑ Morphological Adaptations 1 (Provide supporting data in Remarks or on a separate sheet) ❑ Wetland Non-Vascular Plantsl ❑ Problematic Hydrophytic Vegetationl (Explain) 1Indicators of hydric soil and wetland hydrology must be present, unless disturbed or problematic. Hydrophytic Vegetation Yes No ❑ Present. *Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version (B) Soil Sampling Point: 7A Prome np on: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Depth Matrix Redox Features (inches) Color (moist) % Color (moist) % TypeI LOC2 Texture Remarks Type: C=Concentration. D=Depletion. RM=Reduced Matrix, CS=Covered or Coated Sand Grains xLocation: PL=Pore Lining. M=Matrix y c Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) LJ Histo l Al Indicators for Problematic Hydric Soils 3 so ( ) Histic Epipedon (A2) L_ 1 Sandy Redox (S5) 71 Stripped Matrix (56) I j 2 cm Muck (A10) D Red Parent Material (TF2) ❑ Black Histic (A3) Hydrogen Sulfide (A4) ] Loamy Mucky Mineral (Fl) (except in MLRA 1) L-I Loamy Gleyed Matrix (F2) Lj Other (Explain in Remarks) ❑ Depleted Below Dark Surface (Ali) - Depleted Matrix (F3) Thick Dark Surface (A12) LJ Sandy Muck Mineral (Si) Redox Dark Surface (F6) Depleted Dark Surface (F7) 3Indicators of hydrophytic vegetation and 'L 1 Sandy Gleyed Matrix (S4) Redox depressions (F8) wetland hydrology must be present, unless disturbed or problematic. Restrictive Layer (if present): Type: Depth (inches): Hydric Soil Present? Yes (I, NO Remarks: SSUMED HYDRIC SOILS BASED ON HYDROLOGY Wetland Hydrology Indicators: v _ Primary Indicators (minimum of one required; check all that apply) VI Surface Water (A1) High Water Table (A2) Water-Stained Leaves (B9) (except MLRA 1, 2, 4A, and 4B) L~ Saturation (A3) L J Salt Crust (Bll) Water Marks (B1) r Aquatic Invertebrates (B13) LJ Sediment Deposits (B2) Ll Hydrogen Sulfide Odor (Cl) Drift deposits (B3) i Oxidized Rhizospheres on Living Roots (0) CI Algal Mat or Crust (B4) E-1 Presence of Reduced Iron (C4) Iron Deposits (B5) F J Recent Iron Reduction in Tilled Soils (C6) J Surface Soil Cracks (B6) L- Stunted or Stressed Plants (D1) (LRR A) L Inundation Visible on Aerial Imagery (B7) Other (Explain in Remarks) - Sparsely Vegetated Concave Surface (B8) I Secondary Indicators (minimum of two required) 'Water-Stained Leaves (B9) (MLRA 1, 2, 4A, and 4B) Drainage Patterns (B10) L_L Dry Season Water Table (C2) Saturation Visible on Aerial Imagery (C9) U Geomorphic Position (D2) I Shallow Aquitard (D3) FAC-neutral Test (DS) Raised Ant Mounds (D6) (LRR A) E Frost Heave Hummocks (D7) j Field Observations: Surface Water Present? Yes No Depth (inches): ~ 1 J Water Table Present? Yes No (4~" Depth (inches): F Saturation Present? - Wetland Hydrology Present? Yes NO (includes capillary fringe) Yes - NO Depth (inches): 0 Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available: Remarks: SURFACE WATER ALONG WETLAND EDGE • • US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version 0 WETLAND DETERMINATION DATA FORM - Arid West Region Project/Site: DESCHUTES LWI City/County: Sunriver/Deschutes Sampling Date: 05-May-10 Applicant/Owner: DESCHUTES COUNTY State: FoR Sampling Point: SP .8 • Investigator(s): ALISON SIGLER, ROSEMARY BAKER _ Section, Township, Range: S 24 T 20 S R 10 E Landform (hilislope, terrace, etc.): Floodplain Local relief (concave, convex, none): convex Slope: 0.0% / 0.0 ° Subregion (LRR): LRR B Lat.: 43.8235 Long.: -121.4766 Datum: NAD 83 Soil Map Unit Name. 29A: Cryaq_uolls, 0 to 3 percent slopes NWI classification: PEMF.._ Are climatic/ hydrologic conditions on the site typical for this time of year? Yes * No ❑ (If no, explain in Remarks.) Are Vegetation ❑ , Soil ❑ , or Hydrology ❑ significantly disturbed? Are "Normal Circumstances" present? Yes 0 No ❑ Are Vegetation ❑ , Soil ❑ , or Hydrology Pi naturally problematic? (If needed, explain any answers in Remarks.) Csirmmnrv of Finrlinnc - attach site man showing sampling point locations, transects, important features, etc. Hydrophytic Vegetation Present? Yes No ❑ Is the sampled Area Hydric Soil Present? Yes No ❑ within a Wetland? Yes No ❑ Wetland Hydrology Present? Yes No ❑ Remarks: On-site determination VEGETATION - Use scientific names of plants. Dominant Species? Absolute ReLStrat. Indicator Dominance Test worksheet: i Tree Stratum (Plot size: ) % Cover Cover Status Number of Dominant Species 0 ❑ o.o% That are OBL, FACW, or FAC: 1 2. - - - 0 ❑ o.0% Total Number of Dominant 3 0 ❑ 0.0% Species Across All Strata: Percent of dominant Species 0 = Total Cover That Are OBL, FACW, or FAC: Sapling/Shrub Stratum (Plot size: ) 2. 3. 4 5. Herb Stratum (Plotsize: ) Carex aquatilis 2. 3. 5. 6. 9. Woody Vine Stratum (Plot size: ) 0 El o.o% - r Prevalence index worksheet: 0 ❑ 0.0°i° Total % Cover of: multjplyby; 0 ❑ 0.00/,o OBL species 100 x 1 = 100 0 ❑ FACIN species 0 x 2 = .01- 0 ❑ 0.0% FAC species 0 x 3= 0 0 = Total Cover ! FAcu species x 4 = I UPL species 0... x 5 0 100 100.0% OBL Column Totals: 100 (A) 100 (B) o ❑ 0.0% 0 ❑ ° 0.0% 1.00 Prevalence Index = B/A = - _ 0 ❑ 0.0% E1/1 Dominance Test is > SO% 0 ❑ o.o% Prevalence Index is <_3.0 1 0 ❑ _ 0.0% 1 F1 Morphological Adaptations 1 ,.'rovide supporting 0 El 0.0% data in Remarks or on a separate sheet) 0 _ ❑ 0.0% Problematic Hydrophytic Vegetation 1 (1 :plain) 0 ❑ o.0% o ❑ o.0°r° 1 indicators of hydric soil and wetland hydrology must 100 Total Cover q = be present, unless disturbed or problematic. 0 ❑ 0.0% 2 0 ❑ 0.0% 0 v 0 = Total Cover % Bare Ground in Herb Stratum: 0 Remarks % Cover of Biotic Crust 0 Hydrophytic Vegetation Present? Yes 0 No 0 1... _ (A) l 1_.. (B) 100.0% (A/B) *Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS. US Army Corps of Engineers Arid West - Version 2 Oct. 2008 Soil Sampling Point: SP 8 Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Depth Matrix Redox Features (inches) Color (moist) % Color (moist) Loc= Texture Remarks 012 10YR 3/2 100% Silt 12-20 10YR 4/2 95% lOYR 5/6 5% C PL Silt 1 Type: C=Concentration. D=Depletion. RM=Reduced Matrix, CS=Covered or Coated Sand Grains 2Location: PL=Pore Lining. M=Matr oc y ric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) ❑ Histosol (Al) ❑ Sandy Redox (SS) Indicators for Problematic Hydric Soils3 ❑ Histic Epipedon (A2) ❑ Black Histic (A3) ❑ j Stripped Matrix (S6) ❑ 1 cm Muck (A9) (LRR C) ❑ 2 cm Muck (A10) (LRR B) ❑ Hydrogen Sulfide (A4) ❑ Loamy Mucky Mineral (Fl) El Reduced Vertic (1`18) ❑ Stratified Layers (AS) (LRR C) ❑ Loamy Gleyed Matrix (F2) ❑ Red Parent Material (TF2) 1 cm Muck ; ❑ (A9) (LRR D) ❑ Depleted Matrix (9) ❑ Redox Dark Surface (F6) ~ Other (Explain in Remarks ) ❑ Depleted Below Dark Surface (All) El Thick Dark Surface (A12) ❑ Depleted Dark Surface (F7) ~ ❑ Sandy Muck Mineral (Si) ❑ Sand Gle ed Matri 54 ❑Redox depressions (F8) ❑ Vernal Pools io 3 Indicators of hydrophytic vegetation and wetland h drolo t b y y x ( ) y gy mus e present. Restrictive Layer (if present): Type: C Depth (inches) .,v.. Hydric Soil Present? Yes 0 NO ❑ Remarks: - HYDRIC SOILS BY SATURATION s Hydrology Wetland Hydrology Indicators: Prima-rx Indicators (minimum of one required ❑ Surface Water (Al) check all that applYl,_ ❑ Salt Crust (Bll) Secondary Indicators (2 or more required) ❑ High Water Table (A2) ❑ Biotic Crust (B12) ❑ Water Marks (Bl) (Riverine) ❑ Sediment Deposits (62) (Riverine) Saturation (A3) ❑ Aquatic Invertebrates (B13) ❑ Drift Deposits (B3) Riverine) ❑ Water Marks (Bl) (Nonriverine) ❑ Hydrogen Sulfide Odor (Cl) ❑ Drainage Patterns (BIO) ❑ Sediment Deposits (B2) (Nonriverine) ❑ Oxidized Rhizospheres along Living Roots (0) ❑ Dry Season Water Table (C2) ❑ Drift deposits (B3) (Nonriverine) ❑ Presence of Reduced Iron (C4) ❑ Crayfish Burrows (CS) ❑ Surface Soil Cracks (B6) ❑ Recent Iron Reduction in Plowed Soils (C6) ❑ Saturation Visible on Aerial Imagery (C9) ❑ Inundation Visible on Aerial Imagery (B7) ❑ Thin Muck Surface (C7) ❑ Shallow Aquitard (D3) ❑ Water-Stained Leaves (B9) ❑ Other (Explain in Remarks) ❑ FAC-neutral Test (D5) Field Observations: - i Surface Water Present? Yes ❑ No _ Depth (inches): ~ Water Table Present? Yes No ❑ ~ Depth (inches): 0 I Saturation Present? (includes capillary fringe) Yes ❑ No ❑ Wetland Hydrology Present? Yes No ❑ Depth (inches): Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available: Remarks: i i I US A C f rmy orps o Engineers Arid West - Version 2 Oct. 2008 WETLAND DETERMINATION DATA FORM - Western Mountains, Valleys, and Coast Region Project/Site: DESCHUTES LWI City/County: SUNRIVER/DESCHUTES Sampling Date: 22-Jun-10 • Applicant/Owner: DESCCHUTES COUNTY State: OR Sampling Point: SP 8A Investigator(s): ALISON SIGLER, SARAH HARTUNG Section, Township, Range: S 3 T 211-S- R 10 E Landform (hillslope, terrace, etc.): Shoulder slope Local relief (concave, convex, none): concave Slope: 0.0% / 0.0 ° Subregion (LRR): LRR A Lat.: 43.7801 Long.: -121.5122 Datum: NAD83 Soil Map Unit Name: 29A: Crya4uolls,. Q_to 3 Portent 5lppe$ _ NWI classification: PS5C Are climatic/ hydrologic conditions on the site typical for this time of year? Yes 0 No ❑ (If no, explain in Remarks.) Are Vegetation ❑ , Soil ❑ , or Hydrology ❑ significantly disturbed? Are "Normal Circumstances" present? Yes * No ❑ Are Vegetation ❑ , Soil ❑ , or Hydrology ❑ naturally problematic? (If needed, explain any answers in Remarks.) summary of Findinas - Attach site map showing sampling point locations, transects, important features, et • Hydrophytic Vegetation Present? Yes * No ❑ Is the Sampled Area Hydric Soil Present? Yes C No ❑ Yes O No ❑ within a Wetland? Wetland Hydrology Present? Yes ❑ NO ❑ Remarks: OFF-SITE DETERMINATION VEGETATION - Use scientific names of plants. Dominant Species? Absolute Rel.Strat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: ) % Cover Cover Status Number of Dominant Species 1. Pinus contorta 10 100.0% FAC That are OBL, FACW, or FAC: 4 w (A) 2 0 ❑ 0.0% . ❑ Total Number of Dominant 3. _0 0.0%_ - _ Species Across All Strata: 4 (B) 4. 0 El 0.0% Percent of dominant Species 10 Total Cover = That Are OBL, FACW, or FAC: 100.0/o (A/13) ° Sapling/Shrub Stratum (Plot size: ) Herb Stratum (Plot size: ) 1 Carex aquatilis 2. Poa sP. 3 Juncus sp. 4, 5. 7. _ 8. 9. 10: 1, Salix exigua 2. 4. 5. 15 d❑ 100.0% OBL _ 0 ❑ 0.0% o ❑ 0.0% 0 ❑ _ 0.0% 0 ❑ 0.0% 15 = Total Cover 5 ❑ 5.0% OBL 65 ❑ 65.0% FAC 30 [V 30.0% FACW 0 ❑ 0.0% 0 ❑ "0.0%0 0 ❑ 0.0% 0 ❑ o.o% 0 ❑ 0.0% 0 ❑ 0.0% 0 ❑ 0.0% 0 ❑ 0.0% 100 = Total Cover Woody Vine Stratum (Plot size: ) 1. ° 2. 0 ❑ 0.0% ` _ 0 = Total Cover % Bare Ground in Herb Stratum: 0 Prevalence Index worksheet: Total %q Cover of: Multiply by: OBL species 20 x 1 = 20 FACW species 30 x 2 = 60. FAC species _ 75 x 3 = 225 FACU species --0 x 4 = - " UPL species x S = °0 Column Totals: 125 (A) 305 (B) Prevalence Index = B/A = 2.440 Hydrophytic Vegetation Indicators: Dominance Test is > so% 0 Prevalence index is <_3.01 ❑ Morphological Adaptations t (Provide supporting data in Remarks or on a separate sheet) ❑ Wetland Non-Vascular Plantsl ❑ Problematic Hydrophytic Vegetationl (Explain) 11ndicators of hydric soil and wetland hydrology must be present, unless disturbed or problematic. Hydrophytic Vegetation Present? Yes 0 No Remarks: • Poa sp. assumed FAC and Juncus sp. assumed FACW. i *Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version Soil Sampling Point: 8A Profile Description. (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Depth Matrix Redox Features • (inches) Color (moist) % Color (moist) % Type' Loc2 Texture Remarks 'Type: C= concentration. D=Depletion. RM=Reduced Matrix, CS=Covered or Coated Sand Grains zLocation: PL=Pore Lining. M=Matrix Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils:3 ❑ Histosol (Al) ❑ Sandy Redox (S5) ❑ 2 cm Muck (A10) ❑ Histic Epipedon (A2) ❑ Black Histic (A3) ❑ Stripped Matrix (56) ❑ Loamy Mucky Mineral (Fi) (except in MLRA 1) ❑ Red Parent Material (TF2) ❑d Other (Explain in Remarks) ❑ Hydrogen Sulfide (A4) Loamy Gleyed Matrix (F2) ❑ Depleted Below Dark Surface (Ail) ❑ Depleted Matrix (F3) ❑ Thick Dark Surface I (A12) El Redox Dark Surface (F6 ) 3Indicators of hydrophytic vegetation and y El Sandy Muck Mineral (Sl) ❑ Sandy Gleyed Matrix (S4) Depleted Dark Surface (F7) El ❑ Redox depressions (F8) wetland hydrology must be present, j unless disturbed or problematic. Restrictive Layer (if present): - - Type: Depth (inches): Hydric Soil Present? Yes U No O Remarks: HYDRIC BASED ON HYDROLOGY Hydro logy Wetland Hydrology Indicators: - Primary Indicators (minimum of one required; check all that apply) Secondary Indicators (minimum of two required) U Surface Water (Ai) ❑ water-Stained Leaves (B9) (except MLRA ❑ Water-Stained Leaves (B9) (MLRA 1 2 ❑ High Water Table (A2) 1, 2, 4A, and 4B) , , 4A, and 4B) Saturation (A3) ❑ Salt Crust (Bli) ] Drainage Patterns (B10) ❑ Water Marks (BI) ❑ Aquatic Invertebrates (B13) ❑ Dry Season Water Table (C2) ❑ Sediment Deposits (B2) ❑ Hydrogen Sulfide Odor (Cl) ❑ Saturation Visible on Aerial Imagery (C9) ❑ Drift deposits (B3) ❑ Oxidized Rhizospheres on Living Roots (0) ❑ Geomorphic Position (D2) ❑ Algal Mat or Crust (B4) ❑ Presence of Reduced Iron (C4) ❑ Shallow Aquitard (D3) ❑ Iron Deposits (B5) ❑ Recent Iron Reduction in Tilled Soils (06) ❑ FAC-neutral Test (D5) ❑ Surface Soil Cracks (B6) ❑ Stunted or Stressed Plants (Dl) (LRR A) ❑ Raised Ant Mounds (D6) (LRR A) ❑ Inundation Visible on Aerial Imagery (B7) _ Other (Explain in Remarks) ❑ Frost Heave Hummocks (D7) ❑ Sparsely Vegetated Concave Surface (B8) Field Observations: Surface Water Present? Yes * No O Depth (inches): F 1 Water Table Present? Yes O No Depth (inches): Saturation Present? Yes No O (includes capillary fringe) Depth (inches): 0 Wetland Hydrology Present? Yes No O Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if ava ilable: Aerial photo - - Remarks: I - i US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version • WETLAND DETERMINATION DATA FORM - Arid West Region Project/Site: DESCHUTES LWI City/County: Sunriver/Deschutes Sampling Date:_05-May-10 Applicant/Owner D- I __ES COUNTY _ _ State: j Sampling Point: SP 9 • Investigator(s): ALISON SIGLER ROSEMARY BAKER Section, Township, Range: S 24 T 20 S R 10 E Landform (hillslope, terrace, etc.): Valley bottom Local relief (concave, convex, none): concave Slope: 0.0 ° Subregion (LRR): LRR B Lat.: 43.8259 Long.: -121.4767 Datum: NAD 83 Soil Map Unit Name: 29A: Cryag4Qlls, 0 to 3 percent slopes NWI classification: pggF Are climatic/hydrologic conditions on the site typical for this time of year? Yes' No ` (If no, explain in Remarks.) Are Vegetation Soil L , or Hydrology significantly disturbed? Are "Normal Circumstances" present? Yes No Are Vegetation Soil or Hydrology naturally problematic? (If needed, explain any answers in Remarks.) ciirrmmnrv of Findinac - Attach site mall showing sampling point locations, transects, important features, etc. Hydrophytic Vegetation Present? Yes % No is the Sampled Area Hydric Soil Present? Yes No within a Wetland? Yes No - Wetland Hydrology Present? Yes No Remarks: LARGE IRRIGATION COMPLEX On site determination VEGETATION - Use scientific names of plants. Dominant Species? _ . , _ Absolute Rel.Strat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: ) % Cover Cover Status Number of Dominant Species 0 0.0% That are OBL, FACW, or FAC: 1 (A) 1. 2 - - 0 - - 0.0% Total Number of Dominant 3 0 0.0% Species Across All Strata: 1 (B) 4. 0 o.o Percent of dominant Species 0 = Total Cover 100.0% (A/B) That Are OBL, FACW, or FAC: - Sapling/Shrub Stratum (Plot size: ) • , 1 0 0.0% Prevalence Index worksheet: 2 0 0.0% Total % Cover of: MUltiply_by: 3. 0 0.0% OBL species 90 x 1 = 90 4. o 0.0% FACw species 0 x 2 = Q 5. 0.0% FAC species 0 x 3 = 0 0 = Total Cover I FAcu species x 4 = 0- Herb Stratum (Plotsize: ) 0 0 UPL species x 5 = Carex a uatilis 1. 4 90 VI 100.0% OBL 90 column Totals: 90 (A) (B) 0 0.0% 2. 0 0 00/1 Prevalence Index = B/A = 1.000 3_ . 4 0 Hydrophytic Vegetation Indicators: 5. 0 ~ /o 0.0 ( T h/ Dominance Testis > SO% 0 0.0% Prevalence Index is <_3.0 1 7. 01 1___0.0°/o _ . Morphological Adaptations 11_-rovide supporting . 8 0 1 0.0% data in Remarks or on a separate sheet) 9. o 0.0%p Problematic Hydrophytic Vegetation 1 (1 :plain) 10. 0 0.0% 11. o 0.0% 1 Indicators of hydric soil and wetland hydrology must 9o = Total Cover be present, unless disturbed or problematic. Woody Vine Stratum (Plot size: ) o L o.o% 2 0 _:1 0.0% Hydrophytic . Vegetation 0 = Total Cover I Present? Yes No % Bare Ground in Herb Stratum: 10 % Cover of Biotic Crust p } Remarks: • : I *Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS. Arid West - Version 2 Oct. 2008 US Army Corps of Engineers Soil Sampling Point: SP 9 Profile Description: (Describe to the depth needed to document the indicator or co f th b n i rm e a sence of indicators.) Depth Matrix Redox Features 0 (inches) Color (moist) /o Color (moist) % Type 1 Loc2 Texture Remarks • 0-3 10YR 2/2 100% Silt DENSE ROOTS 3-18 7.5YR 2.5/1 100% Muck 1 Type: C=Concentration. D=Depletion RM=Reduced Matrix, CS=Covered or Coated Sand Grains 21-ocation. PL=Pore Lining. M=Matrix Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) ' Histo l EVI AS Indicators for Problematic Hydric Soils3 so ( ) I L1 Histic Epipedon (A2) El Sandy Redox (SS) 1:1 Stripped Matrix (S6) El 1 cm Muck (A9) (LRR C) ❑ Black Histic (A3) L J Loamy Mucky Mineral (Fl) ❑ 2 cm Muck (A10) (LRR B) ❑ Hydrogen Sulfide (A4) ❑ Reduced Vertic (F18) ❑ Stratified Layers (AS) (LRR C) ❑ Loamy Gleyed Matrix (F2) El Red Parent Material (TF2) ❑ 1 cm Muck (A9) (LRR D) ❑ Depleted Matrix (F3) ❑ Other (Explain in Remarks) ❑ Depleted Below Dark Surface (All) ❑ Redox Dark Surface (F6) ❑ Thick Dark Surface (A12) ❑ Depleted Dark Surface (F7) ❑ Sandy Muck Mineral (Sl) ❑ Redox depressions (F8) ❑ Vernal Pools (F9) 3 Indicators of hydrophytic vegetation and ❑ Sandy Gleyed Matrix (S4) wetland hydrology must be present. Restrictive Layer (if present): Type: Depth inches): " Hydric Soil Present? Yes * No ❑ Remarks. 1I u 1 . Hydrology Wetland Hydrology Indicators: Prim .In i Aprs. (minimum _ f one required; check all that apply) ❑ Surface Water (Al) Secondary Indicators (2 or more required) -1 _ . . ❑ High Water Table (A2) L-1 Salt Crust (Bll) ❑ Biotic Crust (B12) ❑ Water Marks (BI) (Riverine) ❑ S di Saturation (A3) ❑ Aquatic Invertebrates (B13) e ment Deposits (B2) (Riverine) ❑ Drift Deposits (83) Riverine) ❑ Water Marks (Bl) (Nonriverine) ~ ❑ Hydrogen Sulfide Odor (CS) ❑ Drainage Patterns (BSO) i ❑ Sediment Deposits (B2) (Nonriverine) j ❑ Drift deposits (B3) (Nonriverine) ❑ Oxidized Rhizospheres along Living Roots (0) ❑ Presence of Reduced Iron (C4) Dry Season Water Table (C2) ❑ C f j ❑ Surface Soil Cracks (66) ❑ Recent Iron Reduction in Plowed Soils (C6) ray ish Burrows (C8) i ❑ Saturation Visible on Aerial Imagery (C9) ❑ Inundation Visible on Aerial Imagery (B7) ❑ Thin Muck Surface (0) ❑ Shallow Aquitard (D3) ❑ Water-Stained Leaves (69) ❑ Other (Explain in Remarks) El FAC-neutral Test (D5) Field Observations: - Surface Water Present? Yes ❑ No Depth (inches)• C Water Table Present? Yes O No ❑ Depth (inches): 1 i Saturation Present? e - Wetland Hydrology Present? Yes No ❑ I (includes es capillary fringe) Yes No ❑ Depth (inches): 0 Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available: _ Remarks: LARGE AREA OF SURFACE WATER ABOUT 15 FT AWAY E US Army Corps of Engineers Arid West - Version 2 Oct. 2008 WETLAND DETERMINATION DATA FORM - Western Mountains, Valleys, and Coast Region Project/Site:-DESCHUTES LWI City/County: SUNRNER/DESCHUTES Sampling Date: -22-Jun-1'0.---- Applicant/Owner: DESCHUTES COUNTY _ State:, OR Sampling Point: SP 9A Investigator(s): ALISON SIGLER, SARAH HARTUNG Section, Township, Range: S 3 T 21 S R 10 E Landform (hillslope, terrace, etc.): Valley bottom Local relief (concave, convex, none): concave Slope: 0.0% /_0.0 ° Subregion (LRR): LRR A Lat.: 43.7797 Long.: -121.5108 Datum: NAD83 Soil Map Unit Name: j40® gggllc n rq r Pn> NWI classification: p$ Are climatic/ hydrologic conditions on the site typical for this time of year? Yes * No U (If no, explain in Remarks.) Are Vegetation ❑ , Soil ❑ , or Hydrology ❑ significantly disturbed? Are "Normal Circumstances" present? Yes * NO Are Vegetation ❑ , Soil ❑ , or Hydrology ❑ naturally problematic? (If needed, explain any answers in Remarks.) r , ..40 c: ..A;- - - A++m, h cito rnnn chnwina camnlina point locations, transects, important features, et Hydrophytic Vegetation Present? Yes No ❑ Is the Sampled Area Hydric Soil Present? Yes No ❑ Yes O No ❑ within a Wetland? Wetland Hydrology Present? Yes No ❑ Remarks: WETLAND DITCHED THROUGHOUT SITE, SEVERAL UPLAND AREAS INCLUDED AT ABOUT 10% On-site determination. VEGETATION - Use scientific names of plants. Dominant ) Tree Stratum (Plot size: Cove Pmus contorts _ 3. 0 El 0.0% . 4•. 0 El- 0.0% Sapling/Shrub Stratum (Plot size: 1 Salix exiqua 0 i - - 3.-- 4. 5. Herb Stratum (Plot size: ) 1 Carex sp. Lu inus s 4, 5- 6. 7 1~.-- - Woody Vine Stratum (Plot size 1 Absolute Indicator Rel.Strat. Dominance Test worksheet: r - - St~atus - Cover umber of Dominant Species SO ❑ .0% FAC 100 That are OBL, FACW, or FAC: - ❑ Total Number of Dominant 0 0.0% Species Across All Strata: Percent of dominant Species 10 = Total Cover That Are OBL, FACW, or FAC: 20 0 0 --0-- 0 20 50 10 40 0 0 -0- 0 0 ^0 0 0 100 ❑ 100.0% 0131- 0.0% ❑ 0.0% ❑ 0.0% 0.0% = Total Cover [VI 50.00% FACW ❑ 10.0% FAC_ 40.0% FAC ❑ 0.0% ❑ o.o% ❑ 0.0% ❑ 0.0% ❑ ❑ 0.0°ro._ = Total Cover -_4 (A) ! -4 - (B) I v 100.0% (A/B) Prevalence Index worksheet: - Total % Cover of: _ Multiply bY. 1 20 OBL species 20 x = FACW species 50 x 2 = 100 FAC species 60 x 3 = 180 FACU species x 4 = _._._0 0 UPL species x 5 - - Column Totals: _ 130 (A) - 300 (B) Prevalence Index = B/A = 2.308 Hydrophytic Vegetation Indicators: W Dominance Test is > 50% -v Prevalence Index is :53.01 ❑ Morphological Adaptations 1 (Provide supporting data in Remarks or on a separate sheet) ❑ Wetland Non-Vascular Plantsl ❑ Problematic Hydrophytic Vegetationl (Explain) 1Indicators of hydric soil and wetland hydrology must be present, unless disturbed or problematic. 0 ❑ 0.0% 0 El 0.0% Hydrophytic - _ Vegetation 0 = Total Cover Present? Yes * No ❑ % Bare Ground in Herb Stratum: 0 - Remarks: Carex sp. assumed to be FACW; Lupinus sp. and Poa sp. assumed FAC. *Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version Soil Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Depth Matrix Redox Features winches Color (moist) % tlColor (moist) o Type' Locz Texture 0-20 IOYR 2/1 100% peat Sampling Point: 9A Remarks 'Type: C=Concentration. D=Depletion. RM=Reduced Matrix, CS=Covered or Coated Sand Grains Location: PL=Pore Lining. M=Matrix 1 Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) j Histosol (Al) ❑ Sa d R d SS Indicators for Problematic Hydric Soils} I I ❑ Histic Epipedon (A2) n y e ox ( ) ❑ Stripped Matrix (S6) ❑ 2 cm Muck (A10) 1 ❑ Red Parent Material (TF2) ❑ Black Histic (A3) ❑ Hydrogen Sulfide (A4) ❑ Loamy Mucky Mineral (Fl) (except in MLRA 1) ❑ Loamy Gleyed Matrix (F2) ❑ Other (Explain in Remarks) j ❑ Depleted Below Dark Surface (All) ❑ Depleted Matrix (F3) ❑ Thick Dark Surface (A12) ❑ Sandy Muck Mineral (Sl) 1:1 Redox Dark Surface (F6 ❑ ) Depleted Dark Surface (F7) 3Indicators of hydrophytic vegetation and I ❑ Sandy Gleyed Matrix (S4) I ❑ Redox depressions (F8) - wetland hydrology must be present, unless disturbed or problematic. I Restrictive Layer (if present): - Type: Depth (inches): Hydric Soil Present? Yes No ❑ Remarks: Wetland Hydrology Indicators: Primary Indicators (minimum of one required; check all that apply) Secondary Indicators (minimum of two re uired) ❑ Surface Water (Al) ❑ High Water Table (A2) ❑ Water-Stained Leaves (B9) (except MLRA 1, 2, 4A, and 4B) q ❑ Water-Stained Leaves (B9) (MLRA 1, 2, 4A d 4B Saturation (A3) ❑ Salt Crust (Bll) , an ) ❑ Drainage Patterns (B10) ❑ Water Marks (Bl) ❑ Sediment Deposits (B2) ❑ Aquatic Invertebrates (B13) ❑ Hydrogen Sulfide Odor (Cl) ❑ Dry season water Table (C2) ❑ Saturation Visible on Aerial Imagery (C9) ❑ Drift deposits (B3) ❑ Oxidized Rhizospheres on Living Roots (0) ❑ Geomorphic Position (D2) ❑ Algal Mat or Crust (B4) [7j Presence of Reduced Iron (C4) ❑ Shallow Aquitard (D3) ❑ Iron Deposits (B5) ! ❑ Surface Soil Cracks (B6) ❑ Recent Iron Reduction in Tilled Soils (C6) ❑ Stunted or Stressed Plants (Dl) (LRR A) ❑ FAC-neutral Test (D5) 1 ❑ Raised Ant Mounds (D6) (LRR A) ❑ Inundation Visible on Aerial Imagery (B7) ❑ Other (Explain in Remarks) ❑ Frost Heave Hummocks (D7) ❑ Sparsely vegetated Concave Surface (B8) Field Observations: Surface Water Present? Yes ❑ No Depth (inches): r 1 Water Table Present? Yes ❑ No O Depth (inches): Saturation Present? (includes capillary fringe) Yes ❑ NO ❑ Wetland Hydrology Present? Yes U No ❑ Depth (inches): C 0- 6 Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available: RCI I I'll US Army Corps of Engineers • • Western Mountains, Valleys, and Coast Region Interim version • WETLAND DETERMINATION DATA FORM - Arid West Region Project/Site: DESCHUTES LWI City/County: Sunriver/Deschutes Sampling Date:_05-May-10 Applicant/Owner: DESCHUTES COUNTY State: OR J Sampling Point: SP 10 m • Investigator(s): ALISON SIGLER, ROSEMARY BAKER _ Section, Township, Range: S 24 T 20 S R 10 E Landform (hillslope, terrace, etc.): Floodplain Local relief (concave, convex, none): flat Slope: 0.0% / 0.0 ° Subregion (LRR): LRR B Lat.: 43.8258 Long: -121.4754 Datum: NAD 83 Soil Map Unit Name: 144A, Sunriver sandy loam, 0, to 3 percent slopes _ NWI classification: PEMC Are climatic/hydrologic conditions on the site typical for this time of year? Yes 0 No ❑ (If no, explain in Remarks.) Are Vegetation ❑ , Soil ❑ , or Hydrology ❑ significantly disturbed? Are "Normal Circumstances" present? Yes No ❑ Are Vegetation ❑ , Soil ❑ , or Hydrology ❑ naturally problematic? (If needed, explain any answers in Remarks.) c....,. !%r o%f Finrlinnc - Attach site man showin4 sampling point locations, transects, important features, etc. Hydrophytic Vegetation Present? Yes 0 No ❑ Is the Sampled Area Hydric Soil Present? Yes 0 No ❑ within a Wetland? Yes CO) No Wetland Hydrology Present? Yes * No ❑ Remarks: OFF-SITE INVESTIGATION VEGETATION - Use scientific names of plants. Dominant Species? Absolute Rel.Strat Indicator Dominance Test worksheet: Tree Stratum (Plot size: ) % Cover Cover - -Status Number of Dominant Species - 0 ❑ 0.0% i That are OBL, FACW, or FAC: 1 (A) 1 2 0 ❑ 0.0% . 3 0 ❑ 0.0% Total Number of Dominant Species Across All Strata: 1 (B) 4 o ❑ 0.01% . Percent of dominant Species 0 - - = Total Cover 100.0% (A/B) That Are OBL FACW or FAC: - - - - Sapling/Shrub Stratum (Plot size: ) Herb Stratum (Plot size: ) 1 Carex aquatilis 4, 5. 7. 8. 9. 10. 11. 1. _ 3. 4. 5. Woody Vine Stratum (Plot size 0 0.0% ~revalence Index worksheet: 0 ❑ 0.0% Total % Cover of;, _ Multiply by: 0 ❑ 0.0% _ OBL speci es 100 x 1 = -100-- 0 ❑ 0.0%0 _ FACW species 0 x 2= 0 M 0 ❑ 0.0% 0 FAC species 0 x 3= 0 = Total Cover FAcu species x 4 = _ 0, UPL species 0' x 5 = 0 100 F41 100.0% OBL ~ column Totals: 100 (A) 100 (e) 0 El 0.0% 0 El 0.0% Prevalence Index = B/A = 1.000 0 ❑ 0.0% _ Hydrophytic Vegetation Indicators: 0 M ❑ 0.0% Dominance Test is > 50"h o ❑ o.0% - [41 Prevalence index is:53.0 1 0 ❑ 0 0.0 /o ❑ Morphological Adaptations 11-Irovide supporting 0 ❑ 0.0% data in Remarks or on a separate sheet) 0 ❑ 0.0% ❑ Problematic Hydrophytic vegetation 1 (1 :plain) o ❑ 0.0% 1 Indicators of hydric soil and wetland hydrology must 10o = Total Cover be present, unless disturbed or problematic. 1. 0 ❑ 0.0% 2 0 ❑ 0.0% 0 = Total Cover % Bare Ground in Herb Stratum: 0 % Cover of Biotic Crust 0 Remarks: Hydrophytic Vegetation Yes 00 No ❑ Present? *Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS. US Army Corps of Engineers Arid West - Version 2 Oct. 2008 Soil Sampling Point: SP 10 Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Depth Matrix Redox Features • (inches) Color (moist) % Color (moist) % Type 1 Loc= Texture Remarks Type: C=Concentration. D=Depletion. RM=Reduced Matrix, CS=Covered or Coated Sand Grains zLocation: PL=Pore Lining. M=MatriX I Hydric Soil Indicators: (Applicable to all LRRS, unless otherwise noted.) ❑ Histosol (Al) ❑ S d Indicators for Problematic Hydric Soils3 ❑ Histic Epipedon (A2) an y Redox (SS) ❑ Stripped Matrix (S6) ❑ 1 cm Muck (A9) (LRR C) ❑ Black Histic (A3) ❑ Hydrogen Sulfide (A4) Loamy Mucky Mineral (Fl) Ell El 2 cm Muck (A10) (LRR B) ❑ Reduced Vertic (1`18) El Stratified Layers (AS) (LRR C) El Loamy Gleyed Matrix (F2) ❑ Depleted Matrix (F3) El Red Parent Material (TF2) ' ❑ 1 cm Muck (A9) (LRR D) ❑ Depleted Below Dark Surface (All) ❑ Redox Dark Surface (F6) W Other (Explain in Remarks) ❑ Thick Dark Surface (A12) ❑ Depleted Dark Surface (F7) ❑ Sandy Muck Mineral (Sl) El Sand Gle ed M t i 54 ❑ Redox depressions (F8) ❑ Vernal Pools (F9) 3 Indicators of hydrophytic vegetation and wetland h d l y y a r x ( ) - ro y ogy must be present. Restrictive Layer (if present): - - - TYpe I Depth (inches): Hydric Soil Present? Yes C No I Remarks: i HYDRIC SOILS BY SATURATION Hydrology Wetland Hydrology indicators: _ Primary In icetors_(minimum of one_required; ,check all that apply) ❑ Surface Water (Al) ❑ Salt Crust (BlI) Secondary Indicators (2 or more required) ❑ High Water Table (A2) ❑ Biotic Crust (B12) ❑ Water Marks (Bl) (Riverine) ❑ Sediment Deposits (B2) (Riverine) Saturation (A3) ❑ Aquatic Invertebrates (B13) ❑ Drift Deposits (B3) Riverine) ❑ Water Marks (Bl) (Nonriverine) ❑ Hydrogen Sulfide Odor (Cl) ❑ Drainage Patterns (B10) I ❑ Sediment Deposits (B2) (Nonriverine) ❑ Drift de osits (B3 N i i ❑ Oxidized Rhizospheres along Living Roots (0) ❑ ❑ Dry Season Water Table (C2) p ) ( oner ver ne) ❑ Surface Soil Cracks (B6) Presence of Reduced Iron (C4) ❑ Recent Iron Reduction in Plowed Soils (C6) ❑ Crayfish Burrows (C8) ❑ Saturation Visible on Aerial Imagery (C9) ❑ Inundation Visible on Aerial Imagery (B7) ❑ Thin Muck Surface (C7) ❑ Shallow Aquitard (D3) El Water-Stained Leaves (B9) IL Other (Explain in Remarks) El FAC-neutral Test (D5) Field Observations: - - Surface Water Present? Yes ❑ No C Depth (inches): j Water Table Present? Yes ❑ No O Depth (inches): i Saturation Present? a Wetland Hydrology Present? Yes * No 0 (includes capillary fringe) Yes * No 0 Depth (inches): [ 0 J Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available: Remarks: US Army Corps of Engineers Arid West - Version 2 Oct. 2008 WETLAND DETERMINATION DATA FORM - Western Mountains, Valleys, and Coast Region Project/Site: DESCHUTES LWI City/County: SUNRIVER/DESCHUTES Sampling Date: 22-Jun-10 Applicant/Owner: DESCHUTES COUNTY. State: OR Sampling Point: SP 10A Investigator(s): ALISON SIGLERSARAH HARTUNG Section, Township, Range: S 3 T 21S R 10 E Landform (hilislope, terrace, etc.): Valley bottom Local relief (concave, convex, none): flat Slope: 1.0% / 0.6 ° Subregion (LRR): LRR A Lat.: 43.7794 Long.: -121.5119 Datum: NAD83 NWI classification: Soil Map Unit Name: 29q:Crrya, II;;,,Q_t4 Are climatic/ hydrologic conditions on the site typical for this time of year? Yes JNO V (If no, explain in Remarks.) Are Vegetation ❑ , Soil ❑ , or Hydrology ❑ significantly disturbed? Are "Normal Circumstances" present? Yes * No ❑ Are Vegetation ❑ , Soil ❑ , or Hydrology ❑ naturally problematic? (If needed, explain any answers in Remarks.) Caim ,arv of Findinas - Attach site maD showing sampling point locations, transects, important features, et Hydrophytic Vegetation Present? Yes 0 NO ❑ Is the Sampled Area Hydric Soil Present? Yes No ❑ . Yes * No ❑ within a Wetland? Wetland Hydrology Present? Yes No Remarks: On-site determination. VEGETATION - Use scientific names of plants. Dominant Species? Absolute t. Indicator ReLStr Dominance Test worksheet: ) Tree Stratum (Plot size: Cover /o ° _ a I Status Number of Dominant Species 1. 0 ❑ 0.-0-% That are OBL, FACW, or FAC: 3 (A) E1__ o.'0% Total Number of Dominant 3 0 ❑ 0.0% Species Across All Strata: 3 _ (B) o ❑ o. of dominant Species IPlercent o =Total Cover L 100.0% (A/13) hat Are OBL, FACW, or FAC: Sapling/Shrub Stratum (Plot size: ) • 1 0 ❑ 0.0% Prevalence Index worksheet: 2 0 ❑ o.o% Total % Cover _of Multiply _ 3 0 ❑ 0.0% OBL species 50 x 1 = 50 4. 0 ❑ 0.0% FACW species 40 x 2 = 80 5. 0, ❑ o.0% FAC species 0 x 3 = 0 _ _ 0 = Total Cover FACU species 0 x 4 = 0__.1 Herb Stratum (Plot size: ) UPL species 0.__ x 5 0 Juncuspeffusus 1 20 [ 20.00 FACW 90 130 (B) (A) Column Totals : Juncus balticus 2 20 EI/I 20.0% FAC. . Carex sp. 10 ❑ 10.0% Prevalence Index = B/A = 1.444 3 4 Carex aquatilis 50 .-50.0% OBL Hydrophytic Vegetation Indicators: 0 ❑ EVI Dominance Test is > 50% 5 0 ❑ 0.0% [ Prevalence index is 53.01 6 7 ❑ 0.0% Morphological Adaptations 1 (Provide supporting . 0 ❑ 0.0% data in Remarks or on a separate sheet) 8 0 ❑ 0.0% ❑ Wetland Non-Vascular Plantsl 10 0 0.0% El Problematic Hydrophytic Vegetationl (Explain) 0 El 0.0% lIndicators of hydric soil and wetland hydrology must ~ 100 =Total Cover be present, unless disturbed or problematic. Woody Vine Stratum (Plot size: ) 0 ❑ 0.0%__ 2 0 ❑ 0.0% Hydrophytic . _ Vegetation Yes No ❑ 0 = Total Cover Present? % Bare Ground in Herb Stratum: 0 _ Remarks: *Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS Western Mountains, Valleys, and Coast Region Interim version US Army Corps of Engineers Soil Sampling Point: 10A Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Depth _-Matrix Redox Features (inches) Color (moist) % Color (moist) % Type 1 Locz Texture Remarks r ~0-4 10YR 2/1 100% peaty loam - 4-14 10YR 2/1 100% Silty Clay Loam 14-20 10YR 3/1 100% Clay Loam I TType: C=Concentration. D=Depletion. RM=Reduced Matrix, CS=Covered or Coated Sand Grains 'Location: PL=Pore Lining. M=Matrix Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic H dric Soils:3 ❑ Histosol (Al) ~ ❑ Sand Redox (SS) Y ) ❑ 2 cm Muck (A10) ❑ Histic Epipedon (A2) S ❑ Black Histic (A3) ❑ Stripped Matrix (S6) ❑ Loamy Mucky Mineral (Fl) (exce t in MLRA 1) ❑ Red Parent Material (TF2) ❑ Hydrogen Sulfide (A4) p ❑ Loamy Gleyed Matrix (F2) 1011 Other (Explain in Remarks) ❑ Depleted Below Dark Surface (All) ❑ Depleted Matrix (F3) ❑ Thick Dark Surface (A12) ❑ Sandy Muck Mineral (S1) ❑ Redox Dark Surface (F6) ❑ Depleted Dark Surface (F7) 3Indicators of hydrophytic vegetation and tl d h d ❑ Sandy Gleyed Matrix (S4) ❑ Redox depressions (F8) we an y rology must be present, unless disturbed or problematic. Restrictive Layer (if present): - Type: Depth (inches): Hydric Soil Present? Yes O No O Remarks: - - - - IASSUMED HYDRIC BASED ON PERSISTENT SATURATION I Hydrology Wetland Hydrology Indicators: Primary Indicators (minimum of one required; check all that apply) Secondary Indicators (minimum of two required) ❑ Surface Water (Ai) ❑ Water-Stained Leaves (B9) (except MLRA ❑ Water-Stained Leaves (B9) (MLRA 1 2 ❑ High Water Table (A2) 1, 2, 4A, and 4B) , , 4A, and 4B) 1/01 Saturation (A3) ❑ Salt Crust (Bil) ❑ Drainage Patterns (B10) ❑ Water Marks (Bl) ❑ Sediment Deposits (B2) ❑ Aquatic Invertebrates (B13) ❑ Hydrogen Sulfide Odor (Cl) ❑ Dry season water Table (C2) ❑ Saturation Visible on Aerial Imagery (C9) ❑ Drift deposits (B3) ❑ Oxidized Rhizospheres on Living Roots (C3) ❑ Geomorphic Position (D2) ❑ Algal Mat or Crust (B4) ❑ Presence of Reduced Iron (C4) ❑ Shallow Aquitard (D3) ❑ Iron Deposits (B5) ❑ Recent Iron Reduction in Tilled Soils (C6) ❑ FAC-neutral Test (D5) I ❑ Surface Soil Cracks (B6) ❑ Inundation Visible on Aerial Ima er B7 ❑ Stunted or stressed Plants (Dl) (LRR A) ❑ Raised Ant Mounds (D6) (LRR A) g y ( ) ❑ Other (Explain in Remarks) ❑ Frost Heave Hummocks (D7) ❑ Sparsely Vegetated Concave Surface (B8) Field Observations, Surface Water Present? Yes O No O Depth (inches): Water Table Present? Yes No O Depth (inches): E 13 j Saturation Present? (includes capillary fringe) Yes O No O Wetland Hydrology Present? Yes 0 No O Depth (inches): E-0 Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available: Remarks: i - ditching along northern boundary, running east-west i E US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version • WETLAND DETERMINATION DATA FORM - Arid West Region Project/Site: DESCHUTES LWI City/County: Sunriver/Deschutes Sampling Date: 06-May-10 Applicant/Owner: DESCHUTES COUNTY State: OR Sampling Point, SP 11 • Investigator(s): ALISON SIGLER, ROSEMARY BAKER Section, Township, Range: S 24 T 20 S R 10E Landform (hillslope, terrace, etc.): Floodplain Local relief (concave, convex, none): flat Slope: 0.0% / 0.0 ° Subregion (LRR): LRR B Lat.: 43.8258 Long.: -121.4754 Datum: NAD 83 Soil Map Unit Name: 144A: Sunriver sandv loam, 0 to 3 percent slopes _ NWI classification: PEMF _ Are climatic/hydrologic conditions on the site typical for this time of year? Yes a No ❑ (If no, explain in Remarks.) Are Vegetation ❑ , Soil ❑ , or Hydrology ❑ significantly disturbed? Are "Normal Circumstances" present? Yes * No ❑ Are Vegetation ❑ , Soil ❑ , or Hydrology D naturally problematic? (If needed, explain any answers in Remarks.) summary of Findinas - Attach site map showing sampling point locations, transects, important features, etc. Hydrophytic Vegetation Present? Yes C' No ❑ Is the Sampled Area • Hydric Soil Present? Yes 0 No ❑ ❑ • ~ within a Wetland? Yes No Wetland Hydrology Present? Yes ❑ No L- Remarks: OFF-SITE INVESTIGATION VEGETATION - Use scientific names of plants. Dominant species? Absolute Rel.Strat. Indicator Dominance Test worksheet: ) Tree Stratum (Plot size: Cover % Cover Status umber of Dominant Species N 1 00% That are OBL, FACW, or FAC: 1 (A) 2 0 ❑ 0.o% . ❑ Total Number of Dominant 3. 0._. . 0.0% Species Across All Strata: 1 _ (B) 4, o ❑ 0.0% Percent of dominant Species 0 = Total Cover 100.0% That Are OBL, FACW, or FAC: (A/B) Sapling/Shrub Stratum (Plot size: ) 1 0 ❑ 0.0% Prevalence Index worksheet: 2 _ _ 0 ❑ o.o% I Total % Cover of:e Mul ly _ - 3. 0 El OBL species 100 x 1 = 100- 4. 0 ❑ 0.0% FACW species 0 x 2 = -0, 5. 0 ❑ 0.0%_. FAC species 0 x 3 0 0 = Total Cover FACU species 9- x 4 = _0 Herb Stratum (Plot size: ) _ 0 0 UPL species x 5 = Carex aquatilis _ 1 loo _ 1 100.0% OBL 00 (A) 100 (B) Column Totals: 1 , 0 0% ❑ 0 Prevalence Index = B/A = 1.000 3. . 4 0 ❑ 0.0% Hydrophytic Vegetation Indicators: 5 0 L] 0.0% Dominance Test is > so% ❑ 0.0% Prevalence index is <_3.0 1 7. 0 ❑ 0. ❑ Morphological Adaptations i 1.'rovide supporting 8 0 ❑ 0.0% data in Remarks or on a separate sheet) 9 0 ❑ 0.0% ❑ Problematic Hydrophytic Vegetation 1 (1 tplain) ❑ o.o% 11 o ❑ o.o°io . Indicators of hydric soil and wetland hydrology must 100 = Total Cover be present, unless disturbed or problematic. Woody Vine Stratum (Plot size: ) 1. 0 ❑ 0.0% 2. 0 ❑ o.o% Hydrophytic Vegetation 0 = Total Cover Present? % Bare Ground in Herb Stratum: 0 % Cover of Biotic Crust 0 Remarks: • *Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS. US Army Corps of Engineers Yes * No Arid West - Version 2 Oct. 2008 Soil Sampling Point: SP 11 F Profile Description: (Describe to the depth ne eded to document the indicator or confirm the a bsence of indicators.) Depth _ Matrix (inches) Color (moist) % I~ Redox Features Color (moist) % Type 1 Loc= Texture Remarks Type: C=Concentration. D=Depletion. RM=Reduced Matrix, CS=Covered or Coated Sand Grains zLocation: PL=Pore Lining. M=Matrix Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) ❑ Histosol (Al) ❑ Sandy Redox (S5) Indicators for Problematic Hydric Soils3 ❑ Histic Epipedon (A2) ❑ Black Histic (A3) ❑ Stripped Matrix (S6) ❑ 1 cm Muck (A9) (LRR C) ❑ 2 cm Muck (A10) (LRR B) I El Hydrogen Sulfide (A4) ❑ Loamy Mucky Mineral (Fl) ❑ Reduced Vertic (F18) ❑ Stratified Layers (AS) (LRR C) ❑ Loamy Gleyed Matrix (F2) ❑ Red Parent Material (TF2) El 1 cm Muck (A9) (LRR D) ] Depleted Matrix (F3) 0 Other (Explain in Remarks) ❑ Depleted Below Dark Surface (All) Redox Dark Surface (F6) ❑ El Thick Dark Surface (A12) El Depleted Dark Surface (F7) ❑ Sandy Muck Mineral (Sl) ❑ Redox depressions (F8) El Vernal Pools (F9) 3 Indicators of hydrophytic vegetation and ❑ Sandy Gleyed Matrix (S4) - wetland hydrology must be present. Restrictive Layer (if present): - - Type: I Depth (inches): Hydric Soil Present? Yes NO ❑ Remarks: HYDRIC SOIL BY SATURATION k k E Hydrology I Wetland Hydrology Indicators: Primary Indica,tors_(minimum_of one required; _ check all thatap ) y_ _ Secondary Indicators (2 or more required) ❑ Surface Water (Al) ❑ Salt Crust (Bil) ❑ Water Marks (Bl) (Riverine) ❑ High Water Table (A2) ❑ Saturation (A3) ❑ Biotic Crust (B12) ❑ Sediment Deposits (B2) (Riverine) ❑ Aquatic Invertebrates (B13) ❑ Drift Deposits (B3) Riverine) Water Marks (BI) (Nonriverine) ❑ Hydrogen Sulfide Odor (Cl) ❑ Drainage Patterns (B10) ❑ Sediment Deposits (B2) (Nonriverine) ❑ Oxidized Rhizospheres along Living Roots (0) ❑ Dry Season Water Table (C2) ❑ Drift deposits (B3) (Noneriverine) ❑ Presence of Reduced Iron (C4) ❑ Crayfish Burrows (C8) ❑ Surface Soil Cracks (B6) ❑ Recent Iron Reduction in Plowed Soils (C6) ❑ Saturation Visible on Aerial Imagery (C9) ❑ Inundation Visible on Aerial Imagery (B7) ] Thin Muck Surface (C7) ❑ Shallow Aquitard (D3) ❑ Water-Stained Leaves (B9) ❑ Other (Explain in Remarks) ❑ FAC-neutral Test (D5) i Field Observations: Surface Water Present? Yes ❑ No Depth (inches): Water Table Present? Yes ❑ No 0 Depth (inches): Saturation Present? I- includes capillary fringe) Yes * NO ❑ - Wetland Hydrology Present? Yes ] No Depth (inches): 0 - - Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections) if available: Remarks: - - - - US A i rmy Corps of Engineers Arid West - Version 2 Oct. 2008 WETLAND DETERMINATION DATA FORM - Western Mountains, Valleys, and Coast Region Project/Site:, DESCHUTES LWI City/County: SUNRIVER/DESCHUTES Sampling Date: 22-Jun-10 • Applicant/Owner: DESCHUTES COUNTY State: OR Sampling Point: SP 11A Investigator(s). ALISON SIGLER~SARA H HARTUNG Section, Township, Range: S 3 T 21 S R 10 E Landform (hillslope, terrace, etc.). Floodplain Local relief (concave, convex, none): concave Slope: 0.0% Subregion (LRR): LRR A Lat.: 43.7781 Long.: -121.5169 Datum: NA983 Soil Map Unit Name: 29A:_CryQgQQll6, tQ.3 percent sloDeS NWI classification: P5K- Are climatic/ hydrologic conditions on the site typical for this time of yeas? Yes 0 No ❑ (If no, explain in Remarks.) Are Vegetation ❑ , soil ❑ , or Hydrology ❑ significantly disturbed? Are "Normal Circumstances" present? Yes O No ❑ Are Vegetation ❑ , Soil ❑ , or Hydrology ❑ naturally problematic? (If needed, explain any answers in Remarks.) %iimmarv of Findinas - Attach site maD showing sampling point locations, transects, important features, et Hydrophytic Vegetation Present? Yes NO ❑ Is the Sampled Area Hydric Soil Present? Yes No ❑ Yes No ~ within a Wetland? Wetland Hydrology Present? Yes ❑ No ❑ - Remarks: On-site determination. VEGETATION - Use scientific names of plants. Absolute Dominant Species? Rel.Strat. Indicator Dominance Test worksheet: € Tree Stratum (Plot size: ) 1 2. 3 % Cover 0 0 0 Cover ❑ 0.0% ❑ 0.0°ro ❑ 0.0% Status Number of Dominant Species _ That are OBL, FACW, or FAC: 1 (A) Total Number of Dominant Species Across All Strata: 1 (B) 4. 0 ❑ o.o°r° 0 = Total Cover 100.0% (A/B) That Are 013L, FACW, or FAC: Sapling/Shrub Stratum (Plot size: ) - - - - _ 1 _ • 0 ❑ 0.0% Prevalence Index worksheet: 2 0 ❑ 0.0% _Total_% Cover of Multiply by: 3. 0 ❑ o.0% OBL species 65 x 1 = 65 4. 0 ❑ 0.0% FACW species 0 x 2 = Q,.. 5. 0 _ ❑ 0.0% FAC species 15 x 3 = 45 0 =Total Cover FACU species 0--- x 4= 0 Herb Stratum (Plot size: ) 0 0 l1PL species x 5 = 1. Carex aquatilis 65 ❑ 813% pOBL 80 110 (B) column Totals: (A) 2 ]uncus balticus 15 L] 18.8% FAC _ 0 0.0% Prevalence Index = B/A = 1.375 3 - - 4r 0 ❑ 0.0 /o Hydrophytic Vegetation Indicators: 0 ❑ 0.0% d❑ Dominance Test is > 50% 5. _ ( _ ❑ 0.0°r° Prevalence index is :53.01 . 7 0 ❑ _ 0.0% i morphological Adaptations 1 (Provide supporting 0 El 0.0% data in Remarks or on a separate sheet) 8. - 0 . ❑I o.0% [ Wetland Non-Vascular Plantsl - 10 0 ❑ 0.0% ❑ Problematic Hydrophytic Vegetation' (Explain) . 0 0.0% 11 1Indicators of hydric soil and wetland hydrology must 801 Total Cover be present, unless disturbed or problematic. Woody Vine Stratum (Plot size: ) - 1. 0_. ❑ 0.0°ro_ 2 0 ❑ 0.o% Hydrophytic Vegetation * No ❑ Y 0 = Total Cover Percent of dominant Species es Present? % Bare Ground in Herb Stratum: 20 Remarks: *Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version Soil Sampling Point: 11A Profile Description: (Describe to the depth needed to document the indicator or confirm th b f i e a sence o ndicators.) Depth Matrix y Redox Features j (inches) Color (moist) % Color (moist) % Typel Loc= Texture Remarks 0-6 10YR 3/2 100% peat includes some duff 6-20 10YR 2/1 30 peat 2 matrix colors 10YR 3/2 70% IOYR 3/4 10% C PL Clay Loam Type: C=Concentration. D=Depletion. RM=Red uced Matrix, CS=Covered or Coated Sand Grains zLocation: PL=Pore Lining. M=Matrix Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils:3 ❑ Histosol (Al) ❑ Sandy Redox (SS) ❑ 2 cm Muck (A10) ❑ Histic Epipedon (A2) ❑ Black Histic (A3) ❑ Stripped Matrix (S6) ❑ Loamy Mucky Mineral (Fi) (except in MLRA 1) ❑ Red Parent Material (TF2) ❑ Other (Explain in Remarks) ❑ Hydrogen Sulfide (A4) ❑ Loamy Gleyed Matrix (F2) ❑ Depleted Below Dark Surface (All) ❑ Depleted Matrix (F3) ❑ Thick Dark Surface (A12) ❑ Sandy Muck Mineral (Sl) El Redox Dark Surface (F6) ❑ Depleted Dark Surface (F7) 3Indicators of hydrophytic vegetation and l ❑ Sandy Gleyed Matrix (S4) ❑ Redox depressions (F8) wet and hydrology must be present, unless disturbed or problematic. - Restrictive Layer (if present): - i Type: Depth (inches): Hydric Soil Present? Yes 0 No ❑ Remarks: Hydrology ---H,- n._.- _ Wetland Hydrology Indicatore: Primary Indicators (minimum of one required; check all that apply) Secondary Indicators (minimum of two required) Surface Water (Al) ❑ Water-Stained Leaves (B9) (except MLRA ❑Water-Stained Leaves (B9) (MLRA 1 2 ❑ High Water Table (A2) 1, 2, 4A, and 4B) , , 4A, and 4B) %ll Saturation (A3) Ll Salt Crust (Bll) ❑ Drainage Patterns (B10) ❑ Water Marks (Bl) ❑ Aquatic Invertebrates (B13) ❑ Dry Season Water Table (C2) ❑ Sediment Deposits (B2) ❑ Hydrogen Sulfide Odor (CI) ❑ Saturation Visible on Aerial Imagery (C9) ❑ Drift deposits (B3) ❑ Oxidized Rhizospheres on Living Roots (0) ❑ Geomorphic Position (D2) ❑ Algal Mat or Crust (B4) ❑ Presence of Reduced Iron (C4) ❑ Shallow Aquitard (D3) ❑ Iron Deposits (B5) ❑ Recent Iron Reduction in Tilled Soils (C6) ❑ FAC-neutral Test (D5) ❑ Surface Soil Cracks (B6) ❑ Stunted or stressed Plants (Dl) (LRR A) ❑ Raised Ant Mounds (D6) (LRR A) E ❑ Inundation Visible on Aerial Imagery (B7) El Other (Explain in Remarks) ❑ Frost Heave Hummocks (D7) ❑ Sparsely Vegetated Concave Surface (B8) i Field Observations: Surface Water Present? Yes ❑ NO 0 Depth (inches): E Water Table Present? Yes ❑ No O Depth (inches): J I Saturation Present? Wetland Hydrology Present? YeS O No ❑ ❑ : 6 ) e No Depth (inches) (includes capillary fringe Yes Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available: i Remarks: - - US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version • WETLAND DETERMINATION DATA FORM - Arid West Region Project/Site: DESCHUTES LWI _ City/County: Sunriver/Deschutes Sampling Date: 06-May-10 Applicant/Owner: DESCHUTES COUNTY State: OR Sampling Point: SP 12 • Investigator(s): ALISON SIGLER, ROSEMARY BAKER Section, Township, Range: S 26 T 20 S R 10E Landform (hillslope, terrace, etc.): Floodplain Local relief (concave convex, none): concave Slope: 0.0% / 0.0 ° Subregion (LRR): LRR B Lat.: 43.8175 Long.: -121.4896 Datum:- NAD 83 - " Soil Map Unit Name: Not available NWI classification: Are climatic/ hydrologic conditions on the site typical for this time of year? Yes C No (If no, explain in Remarks.) Are Vegetation ❑ , Soil ❑ , or Hydrology ❑ significantly disturbed? Are "Normal Circumstances" present? Yes No ❑ Are Vegetation ❑ , Soil ❑ , or Hydrology ❑ naturally problematic? (If needed, explain any answers in Remarks.) Summarv of Findinas - Attach site map showing sampling point locations, transects, important features, etc. Hydrophytic Vegetation Present? Yes * No ❑ Is the Sampled Area Hydric Soil Present? Yes O No ❑ Yes O No ❑ O ~ within a Wetland? Wetland Hydrology Present? Yes No Remarks: OFF-SITE INVESTIGATION, COULD NOT ACCESS LOT FROM LAND VEGETATION - Use scientific names of plants. Absolute Dominant Species? Rel.Strat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: 2. 3. Cover 0 _0 0._.. Cover Status ❑ 0.0% ❑ 0.0% ❑ 0.0% Number of Dominant Species That are OBL, FACW, or FAC: Total Number of Dominant Species Across All Strata: 1 (A) 2 (B) _ 4• o - El Total Cover Percent of dominant Species That Are OBL FACW, or FAC: 50.0% (A/B) m-- Sapling/Shrub Stratum (Plot size: ) • 1 Salix geyeriana 15 100. o Prevalence Index worksheet. 2 0 ❑ 0.0°° Total % Cover Multiply by. 3 ❑ 0.0% OBL species 85 x 1 = 85 4 0 ❑ 0.0% FACW species 0 x 2= 0 5. ❑ 0.070/4 m _ i FAC species x 3 = 0 _ 15 = Total Cover FACU species 0 x 4 = _ 0 _ Herb Stratum (Plot size: ) i 0 x 5= 0 UPL species - Carex aquatilis L 85 100.0% OBL 85 (e) Column Totals: 85 (A) 2 0 ❑ 0.0% 0 ❑ 0.0% Prevalence Index = B/A = 1.000 3 4__ 0 ❑ 0.0% Hydrophytic Vegetation Indicators: 5 0 ❑ OA% ❑ Dominance Test is > so% 6. 0 E] 0.0% Prevalence index is <_3.0 1 7. _0 El . 0.00/o ❑ Morphological Adaptations 1 1. Irovide supporting 8 0 ❑ om_ data in Remarks or on a separate sheet) 9 0 ❑ 0.0% F vrnhl -matie Hvdroohvtic Vegetation 1 l1 :plain) 10 0 ❑ 0.0% 11. o ❑ o.o°io 85 = Total Cover Woody Vine Stratum (Plot size: ) 1. 0 ❑ _.0.0% 2. 0 ❑ 0.0% 0 = Total Cover % Bare Ground in Herb Stratum: 15 % Cover of Biotic Crust 0 Remarks: • i 1 Indicators of hydric soil and wetland hydrology must be present, unless disturbed or problematic. Hydrophytic Vegetation Present? Yes 0 No ❑ *Indicator suffix National status or professional decision assigned because Regional status not defined by FWS. US Army Corps of Engineers Arid West - Version 2 Oct. 2008 SOIL Sampling Point: SP 12 Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Depth Matrix_.. Redox Features (inches) Color (moist) % Color (moist) % Type 1 Loc= Texture Remarks I Type. C=Concentration. D=Depletion. RM=Reduced Matrix, CS=Covered or Coated Sand Grains 2Location: PL=Pore Lining. M=Matrix Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) ❑ Histosol (Al) ❑ Sandy Redox (S5) Indicators for Problematic Hydric Soils3 ❑ Histic Epipedon (A2) ❑ Black Histic (A3) ❑ Stripped Matrix (S6) ❑ 1 cm Muck (A9) (LRR C) ❑ 2 cm Muck (A10) (LRR B) Hydrogen Sulfide (A4) ❑ Loamy Mucky Mineral (FS) ❑ Reduced Vertic (F18) Stratified Layers (AS) (LRR C) ❑ ❑ Loamy Gleyed Matrix (F2) El Depleted Matrix (F3) ❑ Red Parent Material (TF2) 1 cm Muck (A9) (LRR D) ❑ Redox Dark Surface (F6) 0 Other (Explain in Remarks) ❑ Depleted Below Dark Surface (All) ❑ Depleted Dark Surface (F7) ❑ Thick Dark Surface (A12) ❑ Sandy Muck Mineral (Si) ❑ Redox depressions (F8) 3 I di t f h ❑ Sandy Gleyed Matrix (S4) ❑ Vernal Pools (F9) n ca ors o ydrophytic vegetation and wetland hydrology must be present. Restrictive Layer (if present): Type. Depth (inches): Hydric Soil Present? Yes * No ❑ Remarks: HYDRIC SOILS BY SATURATION Hydrology Wetland Hydrology Indicators: Prime Indicators minimum Qf one. regq redt .Cheq all_that a ly1_. ❑ Surface Water (Al) ❑ Salt Crust (Bll) ❑ High Water Table (A2) ❑ Biotic Crust (B12) ❑ Saturation (A3) ❑ Aquatic Invertebrates (B13) ❑ Water Marks (Bl) (Nonriverine) ❑ Hydrogen Sulfide Odor (Cl) ❑ Sediment Deposits (B2) (Nonriverine) ❑ Oxidized Rhizospheres along Living Roots (0) ❑ Drift deposits (B3) (Nonriverine) ❑ Presence of Reduced Iron (C4) ❑ Surface Soil Cracks (B6) ❑ Recent Iron Reduction in Plowed Soils (C6) ❑ Inundation Visible on Aerial Imagery (B7) ❑ Thin Muck Surface (C7) ❑ Water-Stained Leaves (B9) ❑ Other (Explain in Remarks) Field Observations: Surface Water Present? Yes ❑ No O Depth (inches): Water Table Present? Yes ❑ No 0 Depth (inches): - Secondary Indicators (2 or more required) ❑ Water Marks (Bl) (Riverine) ❑ Sediment Deposits (B2) (Riverine) ❑ Drift Deposits (B3) Riverine) ❑ Drainage Patterns (B10) ❑ Dry Season Water Table (C2) ❑ Crayfish Burrows (C8) ❑ Saturation Visible on Aerial Imagery (C9) ❑ Shallow Aquitard (D3) ❑ FAC-neutral Test (D5) No ❑ Saturation Present? a J Wetland Hydrology Present? Yes (includes capillary fringe) Yes ❑ No ❑ Depth (inches): 0 Describe Recorded Data (stream gauge, monitor well aerial photos, previous inspections), if available: Remarks: US Army Corps of Engineers Arid West - Version 2 Oct. 2008 WETLAND DETERMINATION DATA FORM - Western Mountains, Valleys, and Coast Region Project/Site:_DESCHUTES LWI _ City/County: SUNRIVER/DESCHUTES Sampling Date: 22-Jun-10 • Applicant/Owner: DESCHUTES COUNTY State: OR Sampling Point: SP 12A Investigator(s): ALISON SIGLER SARAH HARTUNG _ Section, Township, Range: S 3 T 21 S R 10 E Landform (hillslope, terrace, etc.): Flat Local relief (concave, convex, none): none Slope: 1.0% / 0.6 ° Subregion (LRR): LRR A Lat.: 43.7780 Long.: -121.5086 Datum: NAD83 Soil Map Unit Name: 2qA: CryagWQ115, O to p9rSa11t5l9p95 _ NWI classification: p$$C Are climatic/ hydrologic conditions on the site typical for this time of year? Yes No ❑ (If no, explain in Remarks.) Are Vegetation ❑ , Soil ❑ , or Hydrology ❑ significantly disturbed? Are "Normal Circumstances" present? Yes * No ❑ Are Vegetation ❑ , Soil ❑ , or Hydrology ❑ naturally problematic? (If needed, explain any answers in Remarks.) crrmm:%rv of Findinas - Attach site maD showing sampling point locations, transacts, important features, et Hydrophytic Vegetation Present? Yes * No ❑ Twithin s the Sampled Area Hydric Soil Present? Yes O No ❑ yes No ❑ ~ Yes ~ No ❑ a Wetland? Wetland Hydrology Present. Remarks: On-site determination. VEGETATION - Use scientific names of plants. Dominant Species? Absolute Rel.Strat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: ) % Cover Cover Status Number of Dominant Species 1 0 ❑ 0.0% _ That are OBL, FACW, or FAC: (A) 2 0 ❑ 0.0% . _ _ , % ❑ Total Number of Dominant 2 B 3. 0 0.0 ( ) Species Across All Strata: 4 0 ❑ o.0% . Percent of dominant Species 0 - Total Cover = 100.0% (A/B) LT hat Are OBL, FACW, or FAC: ) Sapling/Shrub Stratum (Plot size: - • 1. Salix exigua 10 ❑ 100.0% OBL Prevalence Index worksheet: 2 0 ❑ 0.0% Total % Cover of , _ Multipj_by: _ 3 0 ❑ m0.0% oBL species 10, x 1 = 10 4. 0 ❑ 0.o% FACW species 75 x 2 = 150 5• r . 0.0% FAC species _ 10 x 3 = 30 10, = Total Cover FACU species 0 x 4 = 0 Herb Stratum (Plot size: ) IIpL species 'Jo- x 5 = 1_ Lupinus sp. _ 1Q ❑ 10.5% FAC (B) Column Totals: 105 (A) 240 Potentilla anserina ssp.pacifca 2 10 ❑ 10.5% UPL . 9% FACW 0 78 Prevalence Index = B/A = 2.286 3 Juncus balticus 75 . .11 4 0 ❑ 0.0% Hydrophytic Vegetation Indicators: 0 F1 0.0% d❑ Dominance Test is > 500/. 5 0 ❑ 0.0% 9/1 Prevalence index is :53.01 6. 7 0 _ ❑ 0.0% ❑ Morphological Adaptations I (Provide supporting , 0 ❑ 0.o% data in Remarks or on a separate sheet) 8 _ 0 ❑ 0.0% El Wetland Non-Vascular Plants) 9...._.. Y 10 0 ❑ 0.o% ❑ Problematic Hydrophytic Vegetationl (Explain) 0 ❑ 0.0% 11. - 1Indicators of hydric soil and wetland hydrology must 95 =Total Cover be present, unless disturbed or problematic. Woody Vine Stratum (Plot size: ) 1. . 0 ❑ o.0% , _ 2 0 ❑ o.o% Hydrophytic Vegetation Yes ~ No ❑ 0 =Total Cover Present? Bare Ground in Herb Stratum: 5 % Remarks: • ~ Lupinus sp. assumed FAC. *Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS Valleys, and Coast Region Interim version Western Mountains US Army Corps of Engineers , SOII Sampling Point: 12A Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Depth Matrix Redox Features • (inches Color (moist) % Color (moist) % Typel LoC= Texture Remarks 0 s 10YR 3/1 100% peat 5-20 10YR 2/1 100% Silty Clay 1Type: C=Concentration. D=Depletion. RM=Reduced Matrix, CS=Covered or Coated Sand Grains _ 21-ocation: PL=Pore Lining. M=Matrix Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) y ❑ Histosol (Al) ❑ Sa d R d S5 Indicators for Problematic Hydric Soils:3 { ❑ Histic Epipedon (A2) n y e ox ( ) ❑ Stripped Matrix (S6) ❑ 2 cm Muck (A10) ❑ Red Parent Material (TF2) ❑ Black Histic (A3) ❑ Hydrogen Sulfide (A4) ❑ Loamy Mucky Mineral (Fl) (except in MLRA 1) ❑ Loamy Gleyed Matrix (F2) V Other (Explain in Remarks) ❑ Depleted Below Dark Surface (Ali) ❑ Depleted Matrix (9) ❑ Thick Dark Surface (A12) ❑ Sandy Muck Mineral (Si) ❑ Redox Dark Surface (F6) ❑ Depleted Dark Surface (F7) 3Indicators of hydrophytic vegetation and l ❑ Sandy Gleyed Matrix (S4) ❑ Redox depressions (F8) wet and hydrology must be present, unless disturbed or problematic. Restrictive Layer (if present): - Type: Depth (inches):_ Hydric Soil Present? Yes * No ❑ i Remarks: ;top peat layer not thick enough to be A2 but exhibits primary characteristics of an A2 profile. Assumed hydric based on hydrology indicators I Hydrology Wetland Hydrology Indicators: Primary Indicators (minimum of one required; check all that apply) Secondary Indicators (minimum of two required) I❑ Surface Water (Al) ❑ Water-Stained Leaves (B9) (except MLRA ❑ Water-Stained Leaves (B9) (MLRA 1 2 ❑ High Water Table (A2) 1, 2, 4A, and 4B) , , 4A, and 4B) Saturation (A3) ❑ Salt Crust (Bll) ❑ Drainage Patterns (B10) ❑ Water Marks (BI) ❑ Aquatic Invertebrates (613) ❑ Dry season water Table (C2) ❑ Sediment Deposits (B2) j ❑ Drift deposits (B3) ❑ Hydrogen Sulfide Odor (Cl) ❑ Oxidized Rhizospheres on Living Roots (0) ❑ Saturation Visible on Aerial Imagery (C9) ❑ Geomorphic Position (D2) ❑ Algal mat or crust (B4) ❑ Presence of Reduced Iron (C4) ❑ Shallow Aquitard (D3) ❑ Iron Deposits (BS) ❑ Recent Iron Reduction in Tilled Soils (C6) ❑ FAC-neutral Test (DS) ❑ Surface Soil Cracks (B6) ❑ Inundation Visible on Aerial Imagery (B7) ❑ Stunted or Stressed Plants (Dl) (LRR A) ❑ Other (Explain in Remarks) ❑ Raised Ant Mounds (D6) (LRR A) ❑ Frost Heave Hummocks (D7) ❑ sparsely vegetated Concave Surface (BS) Field Observations: Surface Water Present? Yes ❑ No 0 Depth (inches): Water Table Present? Yes ❑ No 0 Depth (inches): Saturation Present? Wetland Hydrology Present? Yes No n I (includes capillary fringe) Yes No ❑ Depth (inches): 4 Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available: - 'Remarks: US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version • WETLAND DETERMINATION DATA FORM - Arid West Region Project/Site: _DESCHUTES LWI City/County: Sunriver/Deschutes Sampling Date: 06-May-10 Applicant/owner: DESCHUTES COUNTY State: OR Sampling Point: SP 13 • Investigator(s): ALISON SIGLER, ROSEMARY BAKER Section, Township, Range: S 23 T 20 S R 10 E Landform (hilislope, terrace, etc.): Floodplain Local relief (concave, convex, none): convex Slope: 0.0% / 0.0 ° Subregion (LRR): LRR B Lat.: 43.8220 Long.: -121.4889 Datum: NAD 83 Soil Map Unit Name: Not available NWI classification: PEMF Are climatic/ hydrologic conditions on the site typical for this time of year? Yes * No O (If no, explain in Remarks.) Are Vegetation ❑ , Soil ❑ , or Hydrology ❑ significantly disturbed? Are "Normal Circumstances" present? Yes NO AreVegetation ] , Soil ❑ , or Hydrology ❑ naturally problematic? (If needed, explain any answers in Remarks.) Summarv of Findinas - Attach site mao showin4 sampling point locations, transects, important features, etc. Hydrophytic Vegetation Present? Yes No Is the Sampled Area Hydric Soil Present? Yes No O Yes O No O within a Wetland? ~ Wetland Hydrology Present? Yes No O Remarks: On-site determination. VEGETATION - Use scientific names of plants. Dominant Species? Absolute Rel.Strat. Indicator I Dominance Test worksheet: Tree Stratum (Plot size: ) % Cover - Cover Status - Number of Dominant Species 0 ❑ 0.0% That are OBL, FACW, or FAC: (A) 2 0 ❑ 0.0%_ Total Number of Dominant 3• 0 0.0% Species Across All Strata: 21 (B) 4. o ❑ °r o.o° Percent of dominant Species _0_._ = Total Cover 100%0% (A/B) That Are OBL, FACW, or FAC: Sapling/Shrub Stratum (Plot size: ) 1, Salix geyeriana 1 ❑ 100.0% FACW Prevalence Index worksheet: 2. 0 ❑ 0.0% Total % Cover of: MultI by; 3. 0 ❑ 0.0% OBL species 85 x 1 = 85 4. 0 ❑ 0.0% FACW species 16 x 2 = 32 5• 0 ❑ 0.0°ro FAC species 0 x 3 = 0 1 = Total Cover Fspecies 0 _ x 4 = 0 Herb Stratum (Plot size: ) 0 x 5 0 UPL species 1. Carex aquatilis 85 _ EV 85.0% OBL (A) 117 (B) Column Totals: 101 2. Juncus effusus 15 ❑ 15.0% FACW 0 o% ❑ o Prevalence Index = B/A = 1.158 3 . 4 0 ❑ 0.0% Hydrophytic Vegetation Indicators: 5 0 ❑ 0.0% d❑ Dominance Test is > 50% 6, __0 ❑ 0.0% Prevalence Index is 53.0 1 7. - 0 ❑ 0.0% Morphological Adaptations 1 ! _ ,rovide supporting 8 0 ❑ 0.0% data in Remarks or on a separate sheet) 9. _ 0 ❑ 0.0% ❑ Problematic Hydrophytic Vegetation 1 (1 :plain) 10. _ 0 ❑ 0.0% 11 0 ❑ 0.0% . [ndicators of hydric soil and wetland hydrology must 100 =Total Cover be present, unless disturbed or problematic. Woody Vine Stratum (Plot size: ) 1. 0 ❑ o.0% 2. 0 ❑ 0.0% Hydrophytic Vegetation Yes No O 0 = Total Cover Present? % Bare Ground in Herb Stratum: 0 % Cover of Biotic Crust 0 Remarks: *Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS. US Army Corps of Engineers Arid West - Version 2 Oct. 2008 Soil Sampling Point: SP 13 Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Depth Matrix Redox Features . _ _ • (inches) Color (moist) oist) % % Color (moist) % Type I Loc= Texture Remarks s: 0-6 10YR 4/2 100% Silt 6-20 10YR 3/2 85% 10YR 4/6 5% C PL Silt L 2 t es of redox 5YR 3/4 10% CS oam YP M pockets of sand 1 Type: C=Concentration. D=Depletion. RM=Reduced Matrix, CS=Covered or Coated Sand Grains 21-ocation: PL=Pore Lining. M=Matrix _ Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils3 ❑ Histosol (Al) ❑ Histc Epipedon (A2) ❑ Sandy Redox (S5) ❑ Stri ed Matrix (S6) ❑ 1 cm Muck (A9) (LRR C) ❑ Black Histic (A3) El Hydrogen Sulfide (A4) pp El Loamy Mucky Mineral (Fl) ❑ 2 cm Muck (A10) (LRR B) El Reduced Vertic (F18 ) ❑ Stratified Layers (AS) (LRR C) El Loamy Gleyed Matrix (F2) ❑ Red Parent Material (TF2) ❑ 1 cm Muck (A9) (LRR D) ❑ Depleted Matrix (F3) ❑ Other (Explain in Remarks) ❑ Depleted Below Dark Surface (All) d❑ Redox Dark Surface (F6) El Depleted Dark Surface (F7) ❑ Thick Dark Surface (A12) ❑ Redox depressions (F8) r ❑ Sandy Muck Mineral (Si) ❑ Vernal Pools (F9) 3 Indicators of hydrophytic vegetation and ❑ Sandy Gleyed Matrix (S4) wetland hydrology must be resent. p i Restrictive Layer (if present): Type: Depth (inches): Hydric Soil Present? Yes * No I Remarks: Hydrology Wetland Hydrology Indicators: Primary Indi tors„(minimum of qne required check q(I that @pply~, _ Secondary Indicators (2 or more required) ❑ Surface Water (Al) ❑ Salt Crust (B11) ❑ Water Marks (Bl) (Riverine) High Water Table (A2) ❑ Biotic Crust (B12) ❑ Sediment Deposits (B2) (Riverine) ❑d Saturation (A3) ❑ Aquatic Invertebrates (B13) ❑ Drift Deposits (B3) Riverine) ❑ Water Marks Bl Nonriverine ( ) ( ) ❑ Hydrogen Sulfide Odor (Cl) ❑ Drainage Patterns (B10) ❑ Sediment Deposits (B2) (Nonriverine) ❑ Oxidized Rhizospheres along Living Roots (0) ❑ Dry Season Water Table (C2) ❑ Drift deposits (B3) (Noneriverine) ❑ Presence of Reduced Iron (C4) ❑ Crayfish Burrows (C8) ❑ Surface Soil Cracks (B6) ❑ Recent Iron Reduction in Plowed Soils (C6) ❑ Saturation Visible on Aerial Imagery (C9) ❑ Inundation Visible on Aerial Imagery (B7) ❑ Thin Muck Surface (C7) ❑ Shallow Aquitard (D3) ❑ Water-Stained Leaves (B9) ❑ Other (Explain in Remarks) ❑ FAC-neutral Test (D5) Field Observations: Surface Water Present? Yes O No Depth (inches): C-~ Water Table Present? Yes No Depth (inches): 12 Saturation Present? (includes capillary fringe) Yes OO No O Wetland Hydrology Present? Yes O No O Depth (inches): 7 Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if avai -'--i lable: Remarks: i US Army Corps of Engineers Arid West - Version 2 Oct. 2008 WETLAND DETERMINATION DATA FORM - Western Mountains, Valleys, and Coast Region Project/Site: DESCHUTES LWI City/County: SUNRNER/DESCHUTES Sampling Date: 22-Jun-10 Applicant/Owner: DESCHUTES COUNTY State: OR Sampling Point: SP 13A Investigator(s): ALISON SIGLER, SARAH HART UNG Section, Township, Range: S 12 T 21S R 10 E Landform (hilislope, terrace, etc.): Floodplain Local relief (concave, convex, none): concave Slope: 2.0% / 1.1 ° Subregion (LRR): LRR A Lat.: 43.7714 Long.: -121.4795 Datum: NAD83 Soil Map Unit Name: 144A:, nriver sandy loam, 0 to 3_percent slopes . NWI classification: PEMC- Are climatic/ hydrologic conditions on the site typical for this time of year? Yes C No ❑ (If no, explain in Remarks.) Are Vegetation El , Soil ❑ , or Hydrology ❑ significantly disturbed? Are "Normal Circumstances" present? Yes O No ❑ Are Vegetation ❑ , Soil ❑ , or Hydrology ❑ naturally problematic? (If needed, explain any answers in Remarks.) Summarv of Findinas - Attach site map showing sampling point locations, transects, important features, et Hydrophytic Vegetation Present? Yes 0 No Is the Sampled Area Hydric Soil Present? Yes No ❑ Yes O No ❑ Wetland Hydrology Present. Yes NO ❑ within a Wetland? ~ ~ Remarks: Off-site determination. VEGETATION - Use scientific names of plants. Dominant Species? Absolute Rel.Strat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: ) "/o Cover - Cover Status Number of Dominant Species 1 0 ❑ 0.0% That are OBL, FACW, or FAC: (A) 2 0 ❑ 0.0% ❑ Total Number of Dominant 3. 0 0.0% Species Across All Strata: 2 (B) 4. o C~ o.o°io Percent of dominant Species Woody Vine Stratum (Plot size: ) 2. 0 _ ❑ 0.o% 0 = Total Cover 0 =Total Cover That Are OBL, FACW, or FAC: 100.0% (A/B) m Sapling/Shrub Stratum (Plot size: 1 0 ❑ 0.o% Prevalence Index worksheet: 2. 0 ❑ o.o°io Total % Cover.of:_. Multiply by,.,,. 3. 0 ❑ 0.0% OBL species 40 x 1 = 40 _ 4' 0 ❑ ..0.0% FACW species ..._45__. x 2 = _ 90...... 5• 0 ❑ 0.0% FAC species _7 x 3 = __21 011 = Total Cover FACU species 0 x 4 = 0', - Herb Stratum (Plot size: ) _ 0 0 OPL species x 5 1 Carex aquatilis 40 ❑ 43.5% OBL 51 Column Totals: 92 (A) (B) Col 2luncusbalticus 35 38.0% FACW 3 Poa trivialis 10 ❑ 10.9% FACW Prevalence Index = B/A = 1.641 4 Sidalcea sp. 5 ❑ 5.4% FAC Hydrophytic Vegetation Indicators: 5. Lupinus sp. _2 ❑ 2.2% FAC Dominance Test is > 500%, 6 0 ❑ 0.0% Prevalence index is 53.01 7. m 01 El 0 0.0% Morphological Adaptations 1 (Provide supporting 8 0 ❑ 0.0% data in Remarks or on a separate sheet) 9 0 ❑ 0.0% ❑ Wetland Non-Vascular Plantsl 10 0 0 0.0 /o El Problematic Hydrophytic Vegetationl (Explain) 0 ~.J 0.0% lIndicatom of hydric soil and wetland hydrology must 92 = Total Cover ha nresent. unless disturbed or Droblematic. Bare Ground in Herb Stratum: E Hydrophytic Vegetation Present? Yes 0 No ❑ Remarks: is Lupinus sp. and Sidalcea sp. assumed FAC. _ _ _ _ _._T...._ _ .___m 11 1 _ ----1 ) *Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version Soil Sampling Point: 13A Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Depth Matrix Redox Features inches) Color (moist) % Color (moist) % Type 1 Locz Texture Remarks 0-9 10YR 2/1 100% Silt Loam 9-20 10YR 4/2 60% IOYR 3/1 40% D M Clay Loam 1Type: C=Concentration. D=Depletion. RM=Reduced Matrix, CS=Covered or Coated Sand Grains 2Location: PL=Pore Lining. M=Matrix Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils3 ❑ Histosol (Al) ❑ Sandy Redox (S5) ❑ 2 cm Muck (A10) ❑ Histic Epipedon (A2) ❑ Stripped Matrix (S6) ❑ Red Parent Material (TF2) ❑ Black Histic (A3) ❑ Hydrogen Sulfide (A4) ❑ Loamy Mucky Mineral (Fl) (except in MLRA 1) ❑ Loamy Gleyed Matrix (F2) ❑ Other (Explain in Remarks) Depleted Below Dark Surface (All) ❑ Depleted Matrix (F3) ❑ Thick Dark Surface (A12) ❑ Sandy Muck Mineral (Si) ❑ Redox Dark Surface (F6) ❑ Depleted Dark Surface (F7) 3Indicators of hydrophytic vegetation and l d h ❑ Sandy Gleyed Matrix (S4) ❑ Redox depressions (F8) wet an ydrology must be present, unless disturbed or problematic. Restrictive Layer (if present): Type: Depth (inches): dric Soil Present? • ~ HY Yes No 0 Remarks: 4 Hydrology Wetland Hydrology Indicators: Primary Indicators (minimum of one required; check all that apply) Surface Water (Al) ❑ Water-Stained Leaves (B9) (except MLRA High Water Table (A2) 1, 2, 4A, and 4B) 0 Saturation (A3) ❑ Salt Crust (Bll) ❑ Water Marks (BI) U Aquatic Invertebrates (B13) ❑ Sediment Deposits (B2) ❑ Hydrogen Sulfide Odor (Cl) ❑ Drift deposits (B3) ❑ Oxidized Rhizospheres on Living Roots (0) ❑ Algal Mat or Crust (B4) ❑ Presence of Reduced Iron (C4) ❑ Iron Deposits (B5) ❑ Recent Iron Reduction in Tilled Soils (C6) ❑ Surface Soil Cracks (B6) ❑ Stunted or Stressed Plants (Dl) (LRR A) ❑ Inundation Visible on Aerial Imagery (B7) ❑ Other (Explain in Remarks) ❑ Sparsely Vegetated Concave Surface (B8) • • Secondary Indicators (minimum of two required) Water-Stained Leaves (B9) (MLRA 1, 2,- 4A, and 4B) ❑ Drainage Patterns (B10) ❑ Dry Season Water Table (C2) ❑ Saturation Visible on Aerial Imagery (C9) Geomorphic Position (D2) ❑ Shallow Aquitard (D3) ❑ FAC-neutral Test (D5) ❑ Raised Ant Mounds (D6) (LRR A) i ❑ Frost Heave Hummocks (D7) Field Observations: ! Surface Water Present? Yes ❑ No 0 Depth (inches): Water Table Present? Yes No ❑ Depth (inches): 12~ Saturation Present? Wetland Hydrology Present? Yes * NO ❑ (includes capillary frinqe) Yes No ❑ Depth (inches): j Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available: Remarks: i US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version • WETLAND DETERMINATION DATA FORM - Arid West Region Project/Site: DESCHUTES LWI City/County: Sunriver/Deschutes Sampling Date: 06-May-10 Applicant/Owner: DESCHUTES COUNTY State: OR Sampling Point: SP 14 • Investigator(s): ALISON SIGLER, ROSEMARY BAKER _ Section, Township, Range: S 25 T 20S R 10E Landform (hillslope, terrace, etc): Valley bottom Local relief (concave, convex, none). concave Slope: 0.0% / 0.0 ° Subregion (LRR): LRR B Lat., 43.8157 Long.: -121.4797 Datum: NAD 83 Soil Map Unit Name: 115A Shanahan loamy coarse sand,, 0-to 3 percent slopes,. NWI classification: . Are climatic/ hydrologic conditions on the site typical for this time of year? Yes 0 NO ❑ (If no, explain in Remarks.) Are Vegetation ❑ , Soil ❑ , or Hydrology ❑ significantly disturbed? Are "Normal Circumstances" present? Yes * No ❑ Are Vegetation ❑ , Soil ❑ , or Hydrology ❑ naturally problematic? (If needed, explain any answers in Remarks.) -ss. nnrv of Fintlinne - attach site man showing sampling point locations, transacts, important features, etc. Hydrophytic vegetation Present? Yes C NO ❑ Is the Sampled Area Hydric Soil Present? Yes No ❑ within a Wetland? Yes * No ❑ Wetland Hydrology Present? Yes NO ❑ Remarks: OFF-SITE INVESTIGATION VEGETATION - Use scientific names of plants. Dominant "Species? Absolute ReLStret. Indicator ~ Dominance Test worksheet: , % Cover Cover Status Tree Stratum (Plot size. Number of Dominant Species 0 ❑ 0.0% That are OBL, FACW, or FAC: 2 _ (A) 1, 2 0 ❑ mm . % ❑ Total Number of Dominant 2 (B) 3 0 0.0 Species Across All Strata: 4. 0 ❑ o.o%io Percent of dominant Species 0 Total cover - That Are OBL, FACW, or FAC 100.0% - (A/B) Sapling/Shrub Stratum (Plot size: ) _ - - 1• Salix sp. • 30 U 10040% FACW Prevalence Index worksheet: 2. 0 ❑ o.o% Total %_Cover of Multiply by:- 3• 0 El 0.0% OBL species 75 x 1 = 75 4. 0 ❑ 0.o% FAcw species 30 x 2 = _ 60 5. _ 0 ❑ 0.0% I FAC species 0 x 3 = 0 30 = Total Cover FACU species 0 x 4 = 0_.__. Herb Stratum (Plot size: ) ~ 0 UPL species x 5 = 0 Care x aquatilis 1. 75 D 100.0% OBL column Totals: 105 (A) 135 (B) 0 El 0.0% _ 2._ 1.286 0 ❑ 0.0% Prevalence Index = B/A = 0 ❑ 0.0% Hydrophytic Vegetation Indicators: 4 5. 0 ❑ 010% W1 Dominance Test is > SO% 6. 0 ❑ _0.0% n Prevalence index is <_3.0 1 7, 0.0% _ ❑ Morphological Adaptations 1 I.,rovide supporting 8 0 ❑ 0.0% data in Remarks or on a separate sheet) 9 0 0.0% ❑ problematic Hydrophytic Vegetation 1(1 :plain) 10. 0 ❑ 0.0% 0 ❑ 0.0% _ ~ Indicators of hydric soil and wetland hydrology must 75 =Total Cover be present, unless disturbed or problematic. Woody Vine Stratum (Plot size: ) 2 % Bare Ground in Herb Stratum: 0 • Remarks: 25% open water, Salix sp. assumed FACW 0 ❑ 0 ❑ 0.o% 0 = Total Cover % Cover of Biotic Crust 0 Hydrophytic Vegetation Yes 0 No ❑ Present. *Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS. US Army Corps of Engineers Arid West - Version 2 Oct. 2008 Soil Sampling Point: SP 14 Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) I Depth _ Matrix Redox Features (inches) Color (moist) % Color (moist) % Type 1 Lox2 Texture Remarks Type: C=Concentration. D=Depletion. RM=Reduced Matrix, CS=Covered or Coated Sand Grains 21-ocation: PL=Pore Lining. M=Matrix Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) ❑ Histosol (Al) ❑ Sandy Redox (SS) Indicators for Problematic Hydric Soils3 ❑ Histic Epipedon (A2) ❑ Stripped Matrix (S6) El 1 cm Muck (A9) (LRR C) El Black Histic (A3) E ❑ Hydrogen Sulfide (A4) ❑ Loamy Mucky Mineral (Fl) ❑ 2 cm Muck (A10) (LRR B) ❑ Reduced Vertic (F18) El Stratified Layers (AS) (LRR C) ❑ Loamy Gleyed Matrix (F2) El Red Parent Material (TF2) ❑ 1 cm Muck (A9) (LRR D) El Depleted Matrix (F3) D Other (Explain in Remarks) ❑ Depleted Below Dark Surface (All) ❑ Redox Dark Surface (F6) El Thick Dark Surface (A12) ❑ Depleted Dark Surface (F7) i ❑ Sandy Muck Mineral (Sl) S d El Redox depressions (F8) ❑ Vernal Pools (F9) 3 Indicators of hydrophytic vegetation and an y Gleyed Matrix (S4) wetland hydrology must be present. Restrictive Layer (if present): Type: Depth (inches) Hydric Soil Present? Yes No 0 Remarks: HYDRIC SOIL BY SATURATION I Hydrology Wetland Hydrology Indicators: s Primary Indicators (minimum 4f onq_regl.lired• check all that apply),_ L VI W t Al _ Secondary Indicators (2 or more required) a er ( ) ❑ High Water Table (A2) ❑ Salt Crust (Bll) ❑ Biotic Crust (B12) ❑ Water Marks (BI) (Riverine) ❑ Sediment Deposits (B2) (Riverine) Saturation (A3) EVI ❑ Aquatic Invertebrates (B13) ❑ Drift Deposits (B3) Riverine) ❑ Water Marks (BS) (Nonriverine) ❑ Hydrogen Sulfide Odor (Cl) ❑ Drainage Patterns (B10) ❑ Sediment Deposits (B2) (Nonriverine) ❑ Oxidized Rhizospheres along Living Roots (0) ❑ Dry Season Water Table (C2) E ❑ Drift deposits (B3) (Noneriverine) ❑ Presence of Reduced Iron (C4) ❑ Crayfish Burrows (C8) I ❑ Surface Soil Cracks (B6) ❑ Recent Iron Reduction in Plowed Soils (C6) ❑ Saturation Visible on Aerial Imagery (C9) ❑ Inundation Visible on Aerial Imagery (B7) ❑ Thin Muck Surface (C7) ❑ Shallow Aquitard (D3) ❑ Water-Stained Leaves (B9) ❑ Other (Explain in Remarks) l- _J FAC-neutral Test (D5) Field Observations: Surface Water Present? Yes 0 No ❑ Depth (inches): Cl Water Table Present? Yes ❑ No 0 Depth (inches): Saturation Present? (includes capillary fringe) Yes G NO ❑ Wetland Hydrology Present? Depth (inches): Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available: I Aerial photo Remarks: I Yes C No ❑ i i • • US Army Corps of Engineers Arid West - Version 2 Oct. 2008 WETLAND DETERMINATION DATA FORM - Western Mountains, Valleys, and Coast Region Project/Site: DESCHUTES LWI City/County: SUNRIVER/DESCHUTES Sampling Date: 22-Jun-10 Applicant/Owner: DESCHUTES COUNTY State: OR Sampling Point: SP 14A • Investigator(s): ALiSON SIGLER, SARAH HARTUNG Section, Township, Range: S 23 T 21 S R 10 E Landform (hillslope, terrace, etc.): Floodplain Local relief (concave, convex, none): flat Slope: 1.0% / 0.6 ° Subregion (LRR): LRR A Lat.: 43.7405 Long.: -121.4917 Datum: NAD83 Soil Map Unit Name: 29A:,,CryagpollS, Q to 3 percent slopes NWI classification: pA Are climatic/ hydrologic conditions on the site typical for this time of year? Yes No ❑ (If no, explain in Remarks.) Are Vegetation E] , Soil ❑ , or Hydrology ❑ significantly disturbed? Are "Normal Circumstances" present? Yes No ❑ Are Vegetation ❑ , Soil ❑ , or Hydrology ❑ naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transects, important features, et u Hydrophytic Vegetation Present? Yes * No ❑ Is the Sampled Area Hydric Soil Present? Yes C No ❑ Yes 0 No ❑ within a Wetland? Wetland Hydrology Present? Yes NO ❑ Remarks: On-site determination. VEGETATION - Use scientific names of plants. Dominant Species? Absolute Rel.Strat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: ) % Cover. - Cover Status Number of Dominant Species 1. 0 ❑ 0.0% That are OBL, FACW, or FAC 2 (A) 2 0 ❑ -0.0% _ . ❑ Total Number of Dominant 3. 0 0.0% Species Across All Strata: 2, (B) 4. 0 ❑ o.o% Percent of dominant Species 0 = Total Cover That Are OBL, FACW, or FAC: 100.0% (A/B) Sapling/Shrub Stratum (Plot size: 1, Salix exigua 30 FV_1 100.0% OBL Prevalence Index worksheet: 2. 0 ❑ 0._00i6 _ Total % Cover of: Multiply. by: _ 3. 0 ❑ 0.0% OBL species 120 x 1 = 120 4. 0 ❑ 0.0% FACw species 10 x 2 = 20 5• 0 ❑ 0.0% _ FAC species 0 _ x 3 = 0 30 = Total Cover FACU species 0 x 4 = _Q Herb Stratum (Plot size: ) 0 x 5 = 0 - - 10 0% OBL -1 10 uPL species 1 Mentha pulegium. _ . 130 column Totals: (A) 140 (B) 2 Carex aquatilis 80 80.0% OBL 10 L 10.0% FACW Prevalence Index = B/A = 1.077 Woody Vine Stratum (Plot size: ) 2. % Bare Ground in Herb Stratum: 0 Remarks: 0 ❑ 0.0% 0 ❑ 0.0% 0 ❑ 0.0% 0 ❑ 0.o% 0 ❑ 0.0% 0 ❑ 0.0% 0 ❑ 0.0% 0 L, 0.0% 100 = Total Cover 0 ❑ 0.0% 0 ❑ 0.0°i° 0 = Total Cover Hydrophytic Vegetation Indicators: ❑d Dominance Test is > so% Prevalence index is :53.01 ❑ Morphological Adaptations 1 (Provide supporting data in Remarks or on a separate sheet) ❑ Wetland Non-Vascular Plantsl ❑ Problematic Hydrophytic Vegetationl (Explain) 1Indicators of hydric soil and wetland hydrology must ho nrnsent_ unless disturbed or problematic. Hydrophytic Vegetation Present? Yes* No ❑ *Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version Soil Sampling Point: 14A Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Depth _ Matrix Redox Features (inches) Color (moist) % Color (moist) % Types Loc2 Texture Remarks 0-6 IOYR 3/2 100% Clay Loam 6-20 10YR 4/1 60% SYR 4/6 38% C PL Sandy Loam 2 types of redox features 10YR 3/1 2% D M tType• C=Concentration. D=Depletion. RM=Reduced Matrix, CS=Covered or Coated Sand Grains zlocation: PL=Pore Lining. M=Matrix Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils:3 LL Histosol (Al) ❑ Sandy Redox (S5) ❑1 2 cm Muck (A10) _ Histic Epipedon (A2) ❑ Stripped Matrix (S6) [71 Red Parent M t i l TF2 L-1 Black Histic (A3) - Loamy Mucky Mineral (Fl) (except in MLRA 1) a er a ( ) [ Other (Explain in Remarks) ❑ Hydrogen Sulfide (A4) Loamy Gleyed Matrix (F2) Depleted Below Dark Surface (All) Depleted Matrix (9) ❑ Thick Dark Surface (A12) ❑ Sandy Muck Mineral (Sl) IL i Redox Dark Surface (F6) -1 Depleted Dark Surface (F7) 3Indicators of hydrophytic vegetation and l d h l Sandy Gleyed Matrix (S4) Redox depressions (F8) wet an ydro ogy must be present, unless disturbed or problematic. Restrictive Layer (if present): Type: _ Depth (inches): Hydric Soil Present? Yes (~s,' No Remarks: Hydrology j Wetland Hydrology Indicators: Primary Indicators (minimum of one required; check all that apply) Secondary Indicators (minimum of two required) L Surface Water (AS) ❑ Water-Stained Leaves (B9) (except MLRA i Water-Stained Leaves (B9) (MLRA 1, 2, High Water Table (A2) 1, 2, 4A, and 4B) 4A, and 4B) Saturation (A3) J Salt Crust (Bll) Drainage Patterns (B10) Water Marks (BI) L Aquatic Invertebrates (B13) J Dry Season Water Table (C2) L_ Sediment Deposits (B2) J Drift d it B3 L_-i Hydrogen Sulfide Odor (Cl) Saturation Visible on Aerial Imagery (C9) epos s ( ) I Oxidized Rhizospheres on Living Roots (0) ❑ Geomorphic Position (D2) Algal Mat or Crust (B4) Presence of Reduced Iron (C4 - ) L Shallow Aquitard (D3) E J Iron Deposits (BS) Recent Iron Reduction in Tilled Soils (C6) r ! FAC-neutral Test (D5) ❑ Surface Soil Cracks (B6) [ Stunted or Stressed Plants (Dl) (LRR A) ❑ Raised Ant Mounds (136) (LRR A) ❑ Inundation Visible on Aerial Imagery (B7) - ! Other (Explain in Remarks) Frost Heave Hummocks (D7) F li Sparsely Vegetated Concave Surface (B8) Field Observations: 1 Surface Water Present? Yes No Depth (inches): F- Water Table Present? Yes ❑ No Depth (inches): _ Saturation Present? - Yes No 7 Wetland Hydrology Present? Yes No L' Depth (inches): ~ L (includes capillary fringe) Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available: Remarks: E j US Army Corps of Engineers Western Mountains, Valleys, and Coast Region - Interim version • WETLAND DETERMINATION DATA FORM - Arid West Region Project/Site: DESCHUTES LWI City/County: Sunriver/Deschutes Sampling Date: 06-May-10 Applicant/Owner: DESCHUTES COUNTY State: OR ] Sampling Point: SP 15 • Investigator(s): ALISON SIGLER, ROSEMARY_BAKER Section, Township, Range: S 25 T 20 S R 10E Landform (hillslope, terrace, etc.): Valley bottom Local relief (concave, convex, none): concave Slope: 04% / 0.0 ° Subregion (LRR): LRR B Lat., 43.8121 Long.: -121.4851 Datum: NAD 83 Soil Map Unit Name: 144A Sunnv_er sandy loam 0 to 3 percent slopes NWI classification: pFOA Are climatic/hydrologic conditions on the site typical for this time of year? Yes * NO ❑ (If no, explain in Remarks.) Are Vegetation ❑ , Soil ❑ , or Hydrology ❑ significantly disturbed? Are "Normal Circumstances" present? Yes No O Are Vegetation ❑ , Soil ❑ , or Hydrology ❑ naturally problematic? (If needed, explain any answers in Remarks.) e•.. Y Y_.-. -9 C:...I:w..~. _ Af+~~I% Sao mnn chnwine camnlina noint locations, transects, important features, etc. Hydrophytic Vegetation Present? Yes C No ❑ Is the Sampled Area Hydric Soil Present? Yes U No ❑ Wetland Hydrology Present? Yes * NO ❑ Yes 0 No ❑ within a Wetland? Remarks: PFO IN AN AREA THAT IS CURRENTLY BEING DRAINED BY SEVERAL DITCH LINES FOR FUTURE DEVELOPMENT ON-SITE DETERMINATION VEGETATION - Use scientific names of plants. Dominant Absolute Rel.Strat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: ) % Cover - Cover S-tatus - - Number of Dominant Species 1 Pinus contorts 15 ❑ 100.0% FAC That are OBL, FACW, or FAC: 3.__ (A) 2 - - 0 ❑ 0.0% Total Number of Dominant 3 0 ❑ Species Across All Strata: 4 (B) 4. o ❑ o.o°io _ Percent of dominant Species 15 =Total Cover 75.0% (A/B) That Are OBL, FACW, or FAC: Sapling/Shrub Stratum (Plot size: ) 1, Spiraea douglasii _ 2 ❑ 6.3% FACW _ ; prevalence Index worksheet: 2. Salix geyeriana 20 ✓ 62.5% Total %,Cover of.. Multiply by:, y. 3. Betula glandulosa 10 [V1-31.3% OBL Ospecies 10 x 1 = 10 4 0 ❑ 0.0% FACw species 67 x 2 = 134 0 0.0% FAC species _ 17._ x 3 = 51 32 = Total Cover FACU species 5 x 4 20 Herb Stratum (Plot size: ) UPL species - x 5 = 0 1 Juncus sp. _ 65 _ E-/1 90.3% FACW (A) 215 (B) Column Totals: 99 2. Fragaria virginiana 5 ❑ 6.9% FACU _ 172 2 2 ❑ 2.8°i° FAC . Prevalence Index = B/A 3 Equisetum arvense 4. 0 ❑ 0.0% Hydrophytic Vegetation Indicators: 5, 0 El 0.0% EV Dominance Test is > 50% 6. 0 ❑ 0.o% Prevalence index is 53.0 i 7. . ❑ 0.0% o _ ❑ Morphological Adaptations 1 i-'rovide supporting 8 0 ❑ 0.0% data in Remarks or on a separate sheet) 9. _ 0 0 ❑ 0.0% _ ❑ Problematic Hydrophytic Vegetation 1 (I :plain) 10. 0 ❑ 0.0% 11, 0 ❑ 0.0% i Indicators of hydric soil and wetland hydrology must 72 = Total Cover be present, unless disturbed or problematic. Woody Vine Stratum (Plot size: ) 1. 0 ❑ 0.0% 2 0 ❑ 0.0% Hydrophytic . Vegetation Yes No ❑ p = Total Cover Present? % Bare Ground in Herb Stratum: 28 % Cover of Biotic Crust 0 Remarks-. • Juncus sp. assumed FACW. *Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS. Arid West - Version 2 Oct. 2008 US Army Corps of Engineers Soil Sampling Point: SP 15 I Profile Description: (Describe to the depth needed to doc t th ' d' umen e n rcator or confirm the absence of indicators.) Depth Matrix Redox Features (inches) Color (moist) % Color (moist) % Type 1 LOCI Texture Remarks 0-3 10YR 2/2 100% Loam 3-18 10YR 3/1 70% 7.5YR 4/4 10% C _ M Silty Clay Loam AATo iN IIES~,o~ AND IOYR 7/1 20% D _ M GRAVELS I Type: C=Concentration D =Depletion. RM=Reduced Matrix, CS=Covered or Coated Sand Grains zLocation: PL=Pore Lining. M=Matrnc Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils3 Histosol (Al) Hi i E rJ Sandy Redox (S5) - i _ 1 cm Muck (A9) (LRR C) st c pipedon (A2) L Black Histic (A3) Stripped Matrix (S6) 2 cm Muck (A10) (LRR B) Loamy Mucky Mineral (FS) R d d V i F Hydrogen Sulfide (A4) Loamy Gleyed Matrix (F2) e uce ert c ( 18) Stratified Layers (AS) (LRR C) L I Depleted Matrix (F3) -D Red Parent Material (TF2) 1 cm Muck (A9) (LRR D) LI/i Redox Dark Surface (F6) L Other (Explain in Remarks) Depleted Below Dark Surface (Ali) - ❑ Thick Dark Surface (A12) 1 1 Depleted Dark Surface (F7) J Redox depressions (F8) _i Sandy Muck Mineral (Sl) Vernal Pools (F9) 3 Indicators of hydrophytic vegetation and l Sandy Gleyed Matrix (S4) wet and hydrology must be present. Restrictive Layer (if present): - Type: Depth (inches): - Hydric Soil Present? Yes No Remarks: - - Hydrology Wetland Hydrology Indicators: - Primary,In cators (minimum of one_._required check.all t t "ly)_„ Secondary Indicators (2 or more required) Surface Water (Al) Salt Crust (Bl1) Water Marks (BI) (Riverine) High Water Table (A2) Biotic Crust (B12) Sediment Deposits (B2) (Riverine) Saturation (A3) Aquatic Invertebrates (B13) Drift Deposits (B3) Riverine) L-I Water Marks (Bl) (Nonriverine) L Hydrogen Sulfide Odor (Cl) Drainage Patterns (B10) Sediment Deposits (B2) (Nonriverine) Oxidized Rhizospheres along Living Roots (0) Dry Season Water Table (C2) L -L Drift deposits (B3) (Noneriverine) F j Presence of Reduced Iron (C4) J Crayfish Burrows (C8) - Surface Soil Cracks (B6) L Recent Iron Reduction in Plowed Soils (C6) Saturation Visible on Aerial Imagery (C9) Inundation Visible on Aerial Imagery (B7) Thin Muck Surface (C7 ) F _I Shallow Aquitard (D3) L Water-Stained Leaves (B9) Other (Explain in Remarks) _ J FAC-neutral Test (D5) Field Observations: Surface Water Present? Yes No Depth (inches): I Water Table Present? Yes No Depth (inches): 12 Saturation Present? Wetland Hydrology Present? Yes NO = (includes capillary fringe) Yes No Depth (inches): 0 1 Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available: - - Remarks: SURFACE WATER ABOUT 4FT FROM PLOT • • US Army Corps of Engineers Arid West - Version 2 Oct. 2008 WETLAND DETERMINATION DATA FORM - Western Mountains, Valleys, and Coast Region Project/Site: DESCHUTES LWI City/County: SUNRIVER/DESCHUTES Sampling Date: 22-Jun-10 • Applicant/Owner: DESCHUTES COUNTY State: xOR_ Sampling Point: SP 15A Investigator(s): ALISON SIGLER, SARAH HARTUNG Section, Township, Range: S 23 T 21 S R 10 E Landform (hillslope, terrace, etc.): Valley bottom Local relief (concave, convex, none): flat Slope: 1.0% / 0.6 ° Subregion (LRR): LRR A Lat.: 43.7400 Long.: -121.4987 Datum: NAD83 Soil Map Unit Name: 144A.,Sunriv r 6an_d[_loam, 0 (O, rcen$ Slopes - NWI classification: PEMA Are climatic/ hydrologic conditions on the site typical for this time of year? Yes 0 No ❑ (If no, explain in Remarks.) Are Vegetation ❑ , Soil ❑ , or Hydrology ❑ significantly disturbed? Are "Normal Circumstances" present? Yes No ❑ Are Vegetation ❑ , Soil ❑ , or Hydrology ❑ naturally problematic? (If needed, explain any answers in Remarks.) summarv of Findinas - Attach site map showing sampling point locations, transects, important features, et • Hydrophytic Vegetation Present? Yes NO ❑ Is the Sampled Area Hydric Soil Present? Yes O No ❑ Yes O No ❑ Wetland Hydrology Present? Yes ❑ No ❑ within a Wetland? Remarks: OFF-SITE DETERMINATION VEGETATION - Use scientific names of plants. Dominant Species? Absolute Rel.Strat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: ) % Cover Cover Status Number of Dominant Species 1 0 ❑ 0.0% That are OBL, FACW, or FAC: 3 (A) 2. - - - 0 ❑ 0.0% " ~ Total Number of Dominant 3. o__ ❑ 0.0% Species Across All Strata: 3. (B) 4. o_ ❑ o ' Percent of dominant Species 4. , 0 = Total Cover or FAC: FACW t Are OBL Th 100.0% (A/B) Sapling/Shrub Stratum (Plot size: ) , , a 1. 0 ❑ 0.0% Prevalence Index worksheet: 2 0 ❑ o.o% _ ly by__ Total % Cover of,: _ Mult IP, 3 0 ❑ 0.0% OBL species 20 x 1 = 20 4. 0 ❑ 0.0% FACW species 60 x 2 = 120 5. 0 ❑ 0.0% FAC species 20 x 3 = 60 0 = Total Cover FACU species 0 x 4 = Herb Stratum (Plot size: ) 0 UPL species x 5 = 0 1 luncus balticus _ 60 60.0% FACW (A) column Totals: 100 200 (e) 2 Carex aquatilis 20 0 20.0% OBL , 20 ❑ 0% FAC 20 Prevalence Index = B/A = 2.000 3 Iris sp. . 0 ❑ 0.0% 0 ❑ 0.0% 0 ❑ 0.0% 0 ❑1 o.0% 0 _ ❑ 0.0% 0 ❑ 0.0% 0 ❑ 0.0% 0 ❑ 0.0% 100 - = Total Cover Woody Vine Stratum (Plot size: ) 1. _ 0 ❑ 0.0% 2. 0 ❑ 0.0% 0 = Total Cover % Bare Ground in Herb Stratum: 0 Hydrophytic Vegetation Indicators: 0 Dominance Test is > 50% d❑ Prevalence index is :53.01 ❑ Morphological Adaptations 1 (Provide supporting data in Remarks or on a separate sheet) ❑ Wetland Non-Vascular Plants' ❑ Problematic Hydrophytic Vegetation' (Explain) 1Indicators of hydric soil and wetland hydrology must be present, unless disturbed or problematic. Hydrophytic Vegetation Present? Yes * No ❑ Remarks: Iris sp. assumed FAC. *Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version Soil Sampling Point: 15A _ Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Depth Matrix Redox Features _Sinches~ Color (moist) % Color (moist) oist) % Type1 Loci Texture Remarks IType: C=Concentration. D=Depletion. RM=Reduced Matrix, CS=Covered or Coated Sand Grains zLocation: PL=Pore Lining. M=Matrix Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils:3 ❑ Histosol (Al) ❑ Histic Epipedon (A2) ❑ Sandy Redox (S5) ❑ Stripped Matrix (S6) ❑ 2 cm Muck (A10) ❑ Black Histic (A3) ❑ Loamy Mucky Mineral (Fl) (except in MLRA 1) ❑ Red Parent Material (TF2) Other (Explain in Remarks) I ❑ Hydrogen Sulfide (A4) ❑ Loamy Gleyed Matrix (F2) ❑ Depleted Below Dark Surface (All) ❑ Depleted Matrix (F3) ❑ Thick Dark Surface (A12) ❑ Sandy Muck Mineral (Sl) ❑ Redox Dark Surface (F6) ❑ Depleted Dark Surface (F7) 3Indicators of hydrophytic vegetation and l ❑ Sandy Gleyed Matrix (S4) ❑ Redox depressions (F8) wet and hydrology must be present, unless disturbed or problematic. Restrictive Layer (if present): t Type Depth (inches): Hydric Soil Present? Yes NO ❑ Remarks: ASSUMED HYDRIC BASED ON HYDROLOGY IN I DICATORS. Hydrology Wetland Hydrology Indicators: Primary Indicators (minimum of one required; check all that apply) Secondary Indicators (minimum of two required) ❑ Surface Water (Al) ❑ Water-Stained Leaves (B9) (except MLRA ❑ Water-Stained Leaves (139) (MLRA 1 2 i ❑ High Water Table (A2) 1, 2, 4A, and 4B) , , 4A, and 4B) ❑ Saturation (A3) ❑ Salt Crust (Bli) ❑ Drainage Patterns (B10) ❑ Water Marks (BI) ❑ Aquatic Invertebrates (B13) ❑ Dry season water Table (0) ❑ Sediment Deposits (B2) ❑ Hydrogen Sulfide Odor (Cl) [VI Saturation Visible on Aerial Imagery (C9) ❑ Drift deposits (B3) ❑ Oxidized Rhizospheres on Living Roots (0) EVI Geomorphic Position (D2) ❑ Algal Mat or Crust (64) ❑ Presence of Reduced Iron (C4) ❑ Shallow Aquitard (D3) ❑ Iron Deposits (B5) ❑ Recent Iron Reduction in Tilled Soils (C6) ❑ FAC-neutral Test (D5) ❑ Surface Soil Cracks (B6) ❑ Stunted or Stressed Plants (Dl) (LRR A) ❑ Raised Ant Mounds (D6) (LRR A) ❑ Inundation Visible on Aerial Imagery (B7) ❑ Other (Explain in Remarks) ❑ Frost Heave Hummocks (D7) ❑ Sparsely vegetated concave Surface (B8) s Field Observations: Surface Water Present? Yes ❑ NO Depth (inches): Water Table Present? Yes ❑ No O Depth (inches): Saturation Present? Yes ❑ No O Wetland Hydrology Present? Yes No ❑ Depth (inches): (includes capillary frinqe) Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available: - Remarks: I - - US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version • WETLAND DETERMINATION DATA FORM - Arid West Region Project/Site: DESCHUTES LWI City/County: Sunriver/Deschutes Sampling Date: 06-May-10 Applicant/Owner: DESCHUTES COUNTY State: OR Sampling Point: SP 16 • Investigator(s): ALISON SIGLER, ROSEMARY BAKER Section, Township, Range: S 25 T 205-1- R 10 E Landform (hillslope, terrace, etc.). Valley bottom Local relief (concave, convex, none): concave Slope: 0.0% / 0.0 ° Subregion (LRR): LRR B Lat.: 43.8099 Long.: -121.4862 Datum: NAD 83 Soil Map Unit Name: _144A: Sunriver sandy loam, 0 to 3 percent,slope$ _ NWI classification: Are climatic/hydrologic conditions on the site typical for this time of year? Yes No U (If no, explain in Remarks.) Are Vegetation ❑ , Soil ❑ , or Hydrology ❑I significantly disturbed? Are "Normal Circumstances" present? Yes 0 No Are Vegetation ❑ , Soil ❑ , or Hydrology ❑ naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transects, important features, etc. Hydrophytic Vegetation Present? Yes 0 No ❑ IS the Sampled Area Hydric Soil Present? Yes 0 No ❑ Yes No ❑ Yes 0 No within a Wetland? Wetland Hydrology Present? Remarks: On-site determination. VEGETATION - Use scientific names of plants. Dominant Species? Absolute Rel.Strat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: ) % Cover Cover Status Number of Dominant Species 1, Pinus contorts 10 ❑ 100.0% FAC That are OBL, FACW, or FAC: 4 (A) 2. 0 ❑ 0.0% _ ❑ Total Number of Dominant 3•__.., 0 0.0% _ Species Across All Strata: _ 4 (B) Percent of dominant Species Sapling/Shrub Stratum (Plot size: ) 10 = Total Cover That Are OBL, FACW, or FAC: 100.0% (A/B) 1. Betula glandulosa 10 ❑ 52.6% OBL Prevalence Index worksheet: 2. Spiraea douglasii 5 L VI 26.3% FACW Total % Cover of: Multiply by: 3. Rosa woodsii 2 ❑ 10.5% FACU OBL species 10 x 1 = 10 4. Ribes bracteosum 2 ❑ 10.5% FAC FACW species 7 x 2 = 14 5. 0 ❑ 0.0% FAC species 109 x 3 = 327 19 = Total Cover FACU species x 4 8 Stratum (Plot size: H ~ 1 Y 0/ FAC ❑ 98 ° UPL species . x 5 = _ Poa sp 97 . o ;Column Totals: 128 (A) 359 (B) 2 Geum macrophyllum 2 ° ❑ 2.0% FACW 3 El 0.0% Prevalence Index = B/A = 2.805 4. „ 0 ❑ 0.0% Hydrophytic Vegetation Indicators: 5 0 ❑ 0.0% d❑ Dominance Test is > 50% 6. _ __0_ ❑ 01.9%,_. ❑d Prevalence index is :53.0 1 7. 0 ❑ 0.0% - ❑ Morphological Adaptations 1 provide supporting 8• 0 _ ❑ 0.0% data in Remarks or on a separate sheet) 9, 0 ❑ 0.0% ❑ Problematic Hydrophytic Vegetation 1 (1 :plain) 10. 0 ❑ 0.0%0 11. o ❑ 0.0% 1 Indicators of hydric soil and wetiand hydrology must 99 = Total Cover be present, unless disturbed or problematic. !,Woody Vine Stratum (Plot size: 1. 0 ❑ 0.0% 2. 0 ❑ 0.0% Hydrophytic Vegetation 0 = Total Cover Present? Yes 0 No ❑ % Bare Ground in Herb Stratum: 0 % Cover of Biotic Crust 0 Remarks: • Poa sp. assumed FAC. *Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS. US Army Corps of Engineers Arid West - Version 2 Oct. 2008 Soil Sampling Point: SP 16 Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Depth Matrix Redox Features (inches) Color (moist) % Color (moist) % Type t Loc= Texture Remarks 0-3 10YR 3/2 100% Loam Duff layer w/grit & roots I 3-20 l0YR 3/1 100% Silty Clay t Type: C=Concentration. D=Depletion. RM=Reduced Matrix, CS=Covered or Coated Sand Grains 2Location: PL=Pore Lining. M=Matroc H dric Soil Indicators: (Applicable to all LR Rs, unless otherwise noted.) Indicators for Problematic Hydric Soils3 ❑ Histosol (Al) Sandy Redox (S5) L1 cm Muck (A9) (LRR C) I Histic Epipedon (A2) L I Stripped Matrix (S6) [ 2 cm Muck (A10) (LRR B) v Black Histic (A3) n Hydrogen Sulfide (A4) J Loamy Mucky Mineral (Fl) ['I Reduced Vertic (1`18) Stratified Layers (AS) (LRR C) Loamy Gleyed Matrix (F2) Red Parent Material (TF2) ❑ 1 cm Muck (A9) (LRR D) _J Depleted Matrix (F3) R do D k S rfa F6 Other (Explain in Remarks) ~ ~ e x ar u ce ( ) ❑ Depleted Below Dark Surface (All) ]Depleted Dark Surface (F7) Thick Dark Surface (A12) Redox depressions (F8) Sandy Muck Mineral (Sl) 3 Indicators of hydrophytic vegetation and Sandy Gleyed Matrix (54) Vernal Pools (F9) wetland hydrology must be present. I~~I Restrictive Layer (if present): Type: Depth (inches): Hydric Soil Present. Yes No Remarks: Hydric soils assumed based on saturation • Hydrology Wetland Hydrology Indicators: Primary Indicators (minimum of one required c check_All th ( apps _ Secondary Indicators (2 or more required) Secondary ❑ Surface Water (Al) Salt Crust (Bll) I Water Marks (Bl) (Riverine) High Water Table (A2) Biotic Crust (B12) Sediment Deposits (82) (Riverine) Saturation (A3) _l Aquatic Invertebrates (B13) Drift Deposits (B3) Riverine) I_I Water Marks (Bl) (Nonriverine) [ j Hydrogen Sulfide Odor (Cl) Drainage Patterns (B10) Ll Sediment Deposits (B2) (Nonriverine) C_ Oxidized Rhizospheres along Living Roots (0) Dry Season Water Table (C2) Drift deposits (B3) (Nonriverine) Presence of Reduced Iron (C4) Crayfish Burrows (C8) Surface Soil Cracks (B6) l Recent Iron Reduction in Plowed Soils (C6) Saturation Visible on Aerial Imagery (C9) _ Inundation Visible on Aerial Imagery (B7) Thin Muck Surface (C7) F 1 Shallow Aquitard (D3) Water-Stained Leaves (B9) 11 Other (Explain in Remarks) FAC-neutral Test (D5) Field Observations: Surface Water Present? Yes No Depth (inches): j~ Water Table Present? Yes !i No ! Depth (inches): L 6 _ Saturation Present? Yes No - Wetland Hydrology Present? Yes' NO Depth (inches): L 0 (includes capillary fringe) Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available: Remarks: appears to be a perched water table I I US Army Corps of Engineers Arid West - Version 2 Oct. 2008 WETLAND DETERMINATION DATA FORM - Western Mountains, Valleys, and Coast Region Project/Site: DESCHUTES LWI City/County: SUNRIVER/DESCHUTES Sampling Date: 22-.1un-10 • Applicant/ Owner: DESCHUTES COUNTY State: OR Sampling Point: SP 16A Investigator(s): ALISON SIGLER, SARAH HARTUNG Section, Township, Range: S 26 T 21 S R 10 E Landform (hillslope, terrace, etc.): Shoulder slope Local relief (concave, convex, none): flat Slope: 0.0% / 0.0 ° Subregion (LRR): LRR A Lat.: 43.7255 Long.: -121.4971 Datum: NAD83 Soil Map Unit Name: 144A: $Unriv r pndy l0 m Q_to 3 percent Slppg NWI classification: PEMA_ Are climatic/ hydrologic conditions on the site typical for this time of year? Yes No ❑ (If no, explain in Remarks.) Are Vegetation ❑ , Soil ❑ , or Hydrology ❑ significantly disturbed? Are "Normal Circumstances" present? Yes * No ❑ or Hydrology El naturally problematic? (If needed, explain any answers in Remarks. Are Vegetation [__1 , Soil ❑ , ) Summary of Findings - Attach site map showing sampling point locations, transects, important features, et Hydrophytic Vegetation Present? Yes 0 No ❑ Is the Sampled Area Hydric Soil Present? Yes ❑ No O Yes ❑ No Yes ❑ No within a Wetland? Wetland Hydrology Present? i~ Remarks: LAWN, PLANTED WITH PINUS CONTORTA, MOWED VERY SHORT On-site determination. VEGETATION - Use scientific names of plants. Dominant Species? Absolute Re1.Strat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: ) % Cover Cover Status Number of Dominant Species 1. Pinus contorts SO ❑ 100.0% FAC That are OBL, FACW, or FAC: 2 0 ❑ 0.0% . ❑ Total Number of Dominant 3. 0 0.o% _ Species Across All Strata: 4. _0 ❑ 0.0% Percent of dominant Species 10 =Total Cover That Are OBL, FACW, or FAC: Sapling/Shrub Stratum (Plot size: Woody Vine Stratum (Plot size: ) 1. 0 ❑ 0.0% 2. 0 ❑ 0.0% 0 = Total Cover 1. 0 ❑ 0.0% Prevalence Index worksheet: 2. 0 ❑ o.o% Total % Cover of: Multiply by: 3. 0 ❑ 0.00% OBL species 0 x 1= 0 4. 0 ❑ 0.0% FACW species 45 x 2 = 90 5• 0 ❑ 0.0% FAC species 10 x 3 = 30 0 = Total Cover FACU species 20...-- x 4 _ 80 Herb Stratum (Plot size: ) UPL species 0 X 5 -O 1. Juncus sp. 45 ❑ _69.2% FACW 75 200 (e) Column Totals: (A) 2. Festuca idahoensis 20 30.8% FACU 3 Trifolium sp. 0 ❑ 0.0% FAC Prevalence Index = B/A = 2.667 4. 0 ❑ 0.0% Hydrophytic Vegetation Indicators: 5. 0 ❑ 0-0%1-,,- - _ ❑ Dominance Test is > 50% 6. 0 ❑ 0.0% Prevalence index is:53.01 7. _ _0 0 0.0 /o ❑ Morphological Adaptations 1 (Provide supporting 8. 0 ❑ 0.o% data in Remarks or on a separate sheet) 9 0 0 ❑ 0.0% - _ ❑ Wetand Non-Vascular Plantst 10 0 0 0./o 0 . ❑ Problematic Hydrophytic Vegetationl (Explain) 11 0 ❑ 0.0% - 11ndicators of hydric soil and wetland hydrology must 65 - = Total Cover be present, unless disturbed or problematic. % Bare Ground in Herb Stratum: 35 I E 2 (A) - 3 _ (B) 66.7% (A/B) Hydrophytic t'~~on Present. Yes* No ❑ Presen Remarks: Juncus sp. assumed FACW and Trifolium sp. assumed FAC. *Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version Soil _ Sampling Point: 16A Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Depth Matrix Redox Features (inches) Color (moist) % Color (moist) % Type l Loc' Texture Remarks 0-20 10YR 2/2 100% Silt Loam - - 1Type: C=Concentration. D=Depletion. RM=Reduced Matrix, CS=Covered or Coated Sand Grains 21-ocation: PL=Pore Lining. M=Matrix Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils-3 ❑ Histosol (Al) ❑ Sandy Redox (S5) ❑ 2 cm Muck (A10) ❑ Histic Epipedon (A2) ❑ Stripped Matrix (S6) ❑ Red Parent Material (TF2) ❑ Black Histic (A3) ❑ Loamy Mucky Mineral (Fl) (except in MLRA 1) ❑ Other (Explain in Remarks) ❑ Hydrogen Sulfide (A4) ❑ Loamy Gleyed Matrix (F2) ❑ Depleted Below Dark Surface (All) ❑ Depleted Matrix (F3) El Thick Dark Surface (A12) El Redox Dark Surface (F6) 3Indicators of hydrophytic vegetation and ❑ Sandy Muck Mineral (Sl) ❑ Depleted Dark Surface (F7) wetland hydrology must be present, ❑ Sandy Gleyed Matrix (S4) ❑ Redox depressions (F8) unless disturbed or problematic. Restrictive Layer (if present): Type: I Depth (inches): Hydric Soil Present? Yes ❑ No C i Remarks: 'dry, no moisture Hydrology Wetland Hydrology Indicators: Primary Indicators (minimum of one required; check all that apply) Secondary Indicators (minimum of two required) e ❑ Surface Water (Al) ❑ Water-Stained Leaves (B9) (except MLRA L J Water-Stained Leaves (B9) (MLRA 1, 2, ❑ High Water Table (A2) 1, 2, 4A, and 4B) 4A, and 4B) ❑ Saturation (A3) ❑ Salt Crust (Bll) ❑ Drainage Patterns (B10) ❑ Water Marks (Bl) ❑ Aquatic Invertebrates (B13) ❑ Dry Season Water Table (C2) ❑ Sediment Deposits (B2) ❑ Hydrogen Sulfide Odor (Cl) ❑ Saturation Visible on Aerial Imagery (C9) ❑ Drift deposits (B3) ❑ Oxidized Rhizospheres on Living Roots (0) ❑ Geomorphic Position (D2) ❑ Algal Mat or Crust (B4) ❑ Presence of Reduced Iron (C4) ❑ Shallow Aquitard (D3) ❑ Iron Deposits (BS) ❑ Recent Iron Reduction in Tilled Soils (C6) ❑ FAC-neutral Test (D5) ❑ Surface Soil Cracks (B6) ❑ Stunted or stressed Plants (Dl) (LRR A) ❑ Raised Ant Mounds (D6) (LRR A) ❑ Inundation Visible on Aerial Imagery (B7) ❑ Other (Explain in Remarks) ❑ Frost Heave Hummocks (D7) ❑ Sparsely vegetated concave Surface (B8) i Field Observations: Surface Water Present? Yes ❑ No O Depth (inches): Water Table Present? Yes ❑ No O Depth (inches): Saturation Present? Yes ❑ NO Wetland Hydrology Present? Yes ❑ Nci De th (inches): (includes capillary fringe) p Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available: Remarks: US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version • WETLAND DETERMINATION DATA FORM - Arid West Region Project/Site: DE CHUTES LWI City/County: Sunriver/Deschutes Sampling Date: 07-May-10 Applicant/Owner: DESCHUTES COUNTY State: OR Sampling Point: SP 17 • Investigator(s): ALISON SIGLER, ROSEMARY BAKER Section, Township, Range: S 26 T 20 S R 10E Landform (hillslope, terrace, etc.): Valley bottom Local relief (concave, convex, none): concave Slope: 0.0% / 0.0 ° Subregion (LRR): LRR B Lat.: 43.8119 Long: -121.4927 Datum: NAD 83 Soil Map Unit Name: Not available _ NWI classification: PEMC Are climatic/ hydrologic conditions on the site typical for this time of year? Yes * No 0 (If no, explain in Remarks.) El Soil El or Hydrology El significantly disturbed? Are "Normal Circumstances" present? Yes NO Are Vegetation O Are Vegetation 1 , Soil ❑ , or Hydrology ❑ naturally problematic? (If needed, explain any answers in Remarks.) c...,,.,,~..., r%f Finrilinnc - Attach site man showing sampling point locations, transects, important features, etc. Hydrophytic Vegetation Present? Yes * NO 0 Is the Sampled Area Hydric Soil Present? Yes 0 No O within a Wetland? Yes C No O Wetland Hydrology Present? Yes NO Remarks: On-site determination. VEGETATION - Use scientific names of plants. Dominant w._ _ . Species? Absolute ReLStrat. Indicator , Dominance Test worksheet: ' Tree Stratum (Plot size: ) % Cover Cover Status Number of Dominant Species 5 D 100.0% FAC That are OBL, FACW, or FAC: 4-11 (A) 1. Pinus contorta 2. 0 ❑ 0.0% Total Number of Dominant 3 „ 0 w ❑ OA% Species Across All Strata: 4 (B) 4. 0 ❑ 0.0% Percent of dominant Species b Stratum (Plot size: ) Sh li 5 =Total Cover 100.0% (A/B) That Are OBL, FACW, or FAC: ru ng/ Sap - - - - 1. Betula glandulosa • 10 EI/I 33.3% OBL Prevalence Index worksheet: 2. Salix geyeriana 20 ❑ 66.7% FACW Total % Cover of: Multiply by: 3. 0 ❑ _ 0.0% OBL species 110 x 1 = 110 4. 0 0.0% ❑ FACw species _ 20x 2 = 40 5 _ 0 El 0.0% Fspecies 5 _ x 3 = 30 =Total Cover I FACU species Q._ x 4 Herb Stratum (Plot size: ) , 0,.._ x 5 = U UPL species Carex nebrascensis 1. 100 100.0% OBL 165 (B) 135 (A) Column Totals: 0 ❑ 0.0% _ 2.. 0 L] o.0% Prevalence Index = B/A = 1.222 4 0 L~ 0.0% Hydrophytic Vegetation Indicators: . 5 0 ❑ 0.0% Dominance Test is > 50% 6. El 0.0% V Prevalence index is <_3.0 1 7. 0 o El 0.0% L1 Morphological Adaptations 1 i.'rovide supporting 0 ❑ 0.0 /o data in Remarks or on a separate sheet) 8 9 0 ❑ 0.0% ❑ Problematic Hydrophytic Vegetation 1 (1 :plain) 0 ❑ 0.0% 10. _ . 11. 0 ❑ 0.0% 100 Total Cover 1 indicators of hydric soil and wetland hydrology must = be present, unless disturbed or problematic. Woody Vine Stratum (Plot size: ) El 0.0 x 2 0 ❑ 0.0% Hydrophytic Vegetation p = Total Cover Present? Yes No % Bare Ground in Herb Stratum: 0 % Cover of Biotic Crust Q Remarks: • "Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS. I US Army Corps of Engineers Arid West - Version 2 Oct. 2008 Soil Profile Description: (Describe to the depth needed to document the indic t Sampling Point: SP 17 a or or confirm the absence of indicators.) Depth Matrix Redox Features i _ (Inches) Color (moist) % Color (moist) % Type 1 Loc2 Texture Remarks 0-3 IOYR 2/2 100% Silt Loam 3-8 10YR 3/3 100% Peat 8-20 SOYR 2/1 50% Silt Loam some sand, 2 matrices I 10YR 2/2 50% i Type C=Concentration D=Depletion. RM=Reduce d Matrix, CS=Covered or Coated Sand Grains zLocation: PL=Pore Lining. M=Matrix Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) IJ Histosol (Al) Sandy Redox (SS) Indicators for Problematic Hydric Soils3 F Histic Epipedon (A2) Black Histic (A3) Stripped Matrix (S6) ❑ 1 cm Muck (A9) (LRR C) ❑ 2 cm Muck (A10) (LRR B) ❑ Hydrogen Sulfide (A4) ❑ Loamy Mucky Mineral (Fl) Loamy Gleyed Matrix (F2) Reduced Vertic (F18) ❑ Stratified Layers (AS) (LRR C) L- Red Parent Material (TF2) El 1 cm Muck (A9) (LRR D) Depleted Matrix (F3) Other (Explain in Remarks) ❑ Depleted Below Dark Surface (All) Redox Dark Surface (F6) k _ Depleted Dark Surface (F7) u Thick Dark Surface (A12) ~ ❑ Sandy Muck Mineral (Sl) Redox depressions (F8) 3 L I Sandy Gleyed Matrix (S4) _ Vernal Pools (F9) Indicators of hydrophytic vegetation and wetland hydrology must be present. Restrictive Layer (if present): - i Type: Depth (inches) Hydric Soil Present? Yes No C I Remarks: HYDRIC SOILS BY SATURATION. j • Hydrology Wetland Hydrology Indicators: - - Prim onerequired;ch - imum of gck all.that apgly)__ Surface Wat Al Secondary Indicators (2 or more required) er ( ' ❑ Salt Crust (611) Water Marks (Bl) (Riverine) High Water A2) Imo ( Saturation (A3) l Biotic Crust (B12) [J Sediment Deposits (B2) (Riverine) J Water Marks (BI) (Nonriverine) _ Aquatic Invertebrates (613) Hydrogen Sulfide Odor (Cl) [1 Drift Deposits (B3) Riverine) J' Sediment Deposits (B2) (Nonriverine) I _I Oxidized Rhizospheres along Living Roots (C3) L Drainage Patterns (B10) [ Dry Season Water Table (C2) j ❑j Drift deposits (B3) (Nonriverine) ❑ Presence of Reduced Iron (C4) Crayfish Burrows (C8) Surface Soil Cracks (B6 I ) I J Recent Iron Reduction in Plowed Soils (C6) I Saturation Visible on Aerial Imagery (C9) Inundation Visible on Aerial Imagery (B7) Water-Stained Lea e B9 Thin Muck Surface (C7) j Shallow Aquitard (D3) v s ( ) J Other (Explain in Remarks) ] FAC-neutral Test (D5) Field Observations: - - Surface Water Present? Yes NO ' P! Depth (inches): F- Pre Water Table nt. Yes No Depth (inches) : 10 p ry (Sndudtiioon resentfringe) Ye s No - ~ Wetiand Hydrology Present? YES ~ NO - Depth (inches): 0 1 - - Describe Recorded Data (stream gauge, monitor well aerial photos previous ins ectio s if il bl , , p n ) a va a e: Remarks: SURFACE WATER ABOUT 2 INCHES DEEP AND 3 FT FROM PLOT. I US Arm Cor s of En i y p g neers Arid West - Version 2 Oct. 2008 WETLAND DETERMINATION DATA FORM - Western Mountains, Valleys, and Coast Region Project/Site: DE CHUTES LWI City/County: SUNRNER/DESCHUTES Sampling Date:??-Jun-10 Applicant/Owner: DESCHUTES COUNTY, State: OR Sampling Point: SP 17A Investigator(s):,ALISON SIGLER{ SARAH HARTUNG Section, Township, Range: S 35 T 21S R 10 E Landform (hillslope, terrace, etc.): Floodplain Local relief (concave, convex, none): flat _ Slope: 0.0% / 0.0 ° Subregion (LRR): LRR A Lat.: 43.7142 Long.: -1214951 Datum: NAD83 Soil Map Unit Name: 29A: ry oll ,tQ3, r n .5 NWI classification: P$Sry_ „ -pet Are climatic/ hydrologic conditions on the site typical for this time of year? Yes 0 No ❑ (If no, explain in Remarks.) Are Vegetation ❑ , Soil ❑ , or Hydrology ❑ significantly disturbed? Are "Normal Circumstances" present? Yes * NO ❑ Are Vegetation ❑ , Soil El , or Hydrology ❑ naturally problematic? (If needed, explain any answers in Remarks.) crrmmarv of Findinas - Attach site man showing sampling point locations, transects, important features, et Hydrophytic Vegetation Present? Yes 0 NO ❑ Is the Sampled Area Hydric Soil Present? Yes* NO within a Wetland? Yes * NO ❑ Wetland Hydrology Present? Yes * No ❑ Remarks: On-site determination. VEGETATION - Use scientific names of plants. Dominant Absolute Rel.Strat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: Cover - - Cover Status Number of Dominant Species 1 0 ❑ 0.o% _ That are OBL, FACW, or FAC: 3(A) 2 0 ❑ ""0.0% . 0% ❑ Total Number of Dominant 3 B 3 0 0. ( ) Species Across All Strata: 4 0 ❑ o.o°i° Percent of dominant Species 0 Total Cover = 100.0% That Are OBL, FACW, or FAC: (A/13) ) Sapling/Shrub Stratum (Plot size: • 1 Salix exigua 20 © 100.0% OBL Prevalence Index worksheet: 2. 0 ❑ 0.0% Total % Cover of. -_a Multiply by 3. 0 ❑ 0.0% OBL species 40 x 1 = 40 4 0 ❑ 0.0% FACw species 80 x 2 = 160 5. 0 _ ❑ 0.0% 0 x 3= 0 FAC species 20 = Total Cover FACU species 9- x 4 = 0 Herb Stratum (Plot size: ) 0 0 UPL species x 5 = Phalaris arundinacea 1. 70 0 70.0% FACW 120 (A) 200 (B) column Totals: Carex aquatilis 2 20 20.0% OBL . 0% FA(W ❑ 10 Prevalence Index = B/A = 1.667 3 ]uncus balticus 10 . 4 0 ❑ 0.0% Hydrophytic Vegetation Indicators: 0 ❑ 0.0% ~ Dominance Test is > 500/o 5. 0 ❑ 0.0% L] Prevalence index is <_3.01 6 7 ❑ 0.0 /o - ❑ Morphological Adaptations 1 (Provide supporting . 0 ❑ 0.0% data in Remarks or on a separate sheet) 8 9 0 - ❑ o.0% _ wenand Non-Vascular Plantsl . 10 0 ❑ 0.0% ❑ Problematic Hydrophytic Vegetationl (Explain) . 0 ❑ 0.0% 11 1Indicators of hydric soil and wetland hydrology must 100 = Total Cover be present, unless disturbed or problematic. Woody Vine Stratum (Plot size: ) 1. 0 ❑ 0.0% 2 0 ❑ 0.0% Hydrophytic . i Vegetation Yes 0 No C 0 = Total Cover Present? % Bare Ground in Herb Stratum: 0 Remarks: *Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS Valleys, and Coast Region Interim version Western Mountains US Army Corps of Engineers , soil Profile Description: (Describe to the depth needed to docume t th i di Sampling Point: 17A n e n cator or confirm the absence of indicators.) Depth Matrix Redox Features inches) Color (moist) _ % Color (moist) % Type t Loci Texture Remarks 0-4 IOYR 3/2 100% organics and loam 4-8 IOYR 3/1 90% 10YR 4/6 10% C PL Loam w/ organics- 8-9 10YR 3/1 100% Sand 9-19 10YR 3/1 70% 10YR 4/6 30% C M Sandy Loam w/ organics 11 1Type: C=Concentration. D=Depletion. RM=Reduced Matrix, CS=Covered or Coated Sand Grains zLocation: PL=Pore Lining. M=Matrix Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) ❑ Histosol (Al) ❑ Sa d R d S5 Indicators for Problematic Hydric Soils:3 ❑ ❑ Histic Epipedon (A2) n y e ox ( ) ❑ Stripped Matrix (S6) 2 cm Muck (A10) ❑ Red Parent Material (TF2) ❑ Black Histic (A3) ❑ Hydrogen Sulfide (A4) ❑ Loamy Mucky Mineral (Fl) (except in MLRA 1) ❑ Loamy Gleyed Matrix (F2) ❑ Other (Explain in Remarks) ❑ Depleted Below Dark Surface (All) ❑ Depleted Matrix (9) ❑ Thick Dark Surface (A12) ❑ Sandy Muck Mineral (Sl) EV Redox Dark Surface (F6) ❑ Depleted Dark Surface (F7) 3Indicators of hydrophytic vegetation and ❑ Sandy Gleyed Matrix (S4) ❑ Redox depressions (F8) wetland hydrology must be present, unless disturbed or problematic. Restrictive Layer (if present): Type: Depth (inches): Hydric Soil Present? Yes CD No Remarks: Hydrology Wetland Hydrology Indicators; Primary Indicators (minimum of one required; check all that apply) ❑ Surface Water (Al) ❑ Water-Stained Leaves (B9) (except MLRA ❑ High Water Table (A2) 1, 2, 4A, and 4B) Saturation (A3) ❑ Salt Crust (B11) ❑ Water Marks (BI) ❑ Aquatic Invertebrates (B13) ❑ Sediment Deposits (B2) ❑ Hydrogen Sulfide Odor (Cl) ❑ Drift deposits (B3) ❑ Oxidized Rhizospheres on Living Roots (0) ❑ Algal Mat or Crust (B4) ❑ Presence of Reduced Iron (C4) ❑ Iron Deposits (B5) ❑ Surface Soil C k B6 ❑ Recent Iron Reduction in Tilled Soils (C6) rac s ( ) ❑ Stunted or Stressed Plants (Dl) (LRR A) ❑ Inundation Visible on Aerial Imagery (B7) ❑ Other (Explain in Remarks) ❑ Sparsely Vegetated Concave Surface (B8) Secondary Indicators (minimum of two required) ❑ Water-Stained Leaves (B9) (MLRA 1, 2, 4A, and 4B) ❑ Drainage Patterns (B10) ❑ Dry Season Water Table (C2) ❑ Saturation Visible on Aerial Imagery (C9) ❑ Geomorphic Position (D2) ❑ Shallow Aquitard (D3) ❑ FAC-neutral Test (D5) ❑ Raised Ant Mounds (D6) (LRR A) ❑ Frost Heave Hummocks (D7) Field Observations: Surface Water Present? Yes ❑ No 0 Depth (inches): Water Table Present? Yes O No ❑ Depth (inches): 14 Saturation Present? a Wetland Hydrology Present? Yes * No ❑ (includes capillary fringe) Yes No ❑ Depth (inches): 0 Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available: KemarKs: i E • US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version 0 WETLAND DETERMINATION DATA FORM - Arid West Region Project/Site: DESCHUTES LWI City/County: Sunriver/Deschutes Sampling Date: 07-May-10 Applicant/Owner: DESCHUTES COUNTY State: OR Sampling Point: SP is Investigator(s): ALISON SIGLER, ROSEMARY BAKER _ Section, Township, Range: S 26 T 20 S R 10 E Landform (hillslope, terrace, etc.): Floodplain Local relief (concave, convex, none): concave Slope: 0.0% / 0.01 Subregion (1-1111): LRR B Lat 43.8115 Long: 121.4966 Datum: NAD 83 - - NWI classification: PEMC Soil Map Unit Name: Not available Are climatic/ hydrologic conditions on the site typical for this time of year? Yes 0 No ❑ (If no, explain in Remarks.) Are Vegetation ❑ , Soil ❑ , or Hydrology ❑ significantly disturbed? Are "Normal Circumstances" present? Yes 0 No ❑ Are Vegetation ❑ , Soil ❑ , or Hydrology ❑ naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transects, important features, etc. Hydrophytic Vegetation Present? Yes 0 No ❑ Is the Sampled Area Hydric Soil Present? Yes O No ❑ Yes O No ❑ ~ within a Wetland? Wetland Hydrology Present? Yes No ❑ Remarks: OFFSITE INVESTIGATION VEGETATION - Use scientific names of plants. Dominant Species? Absolute Rel.Strat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: ) % Cover - - Cover Status Number of Dominant Species 1 0 ❑ 0.0% That are OBL, FACW, or FAC: _ 2 (A) 2 0 ❑ 0.0% ' ❑ Total Number of Dominant 3. 0 0.0% Species Across All Strata: 3(B) 4. o ❑ o.o% _ Percent of dominant Species • 0 _ =Total Cover That Are OBL, FACW, or FAC: 66.7% (A/B) Sapling/Shrub Stratum (Plot size: 1, Salix geyeriana 10 0 100.0% Prevalence Index worksheet. 2. 0 ❑ 0.o% Total % Cover of: Multiplyab_y:, 3, 0 ❑ 0.0% OBL species 90 x 1 = 90 4. 0 ❑ 0.0 /o FACW species 0 x 2 = 0 5. _0 ❑ 0.0% FAC species ~..0x 3 = 10 = Total Cover _ I FACU species 0 x 4 = --0 Herb Stratum (Plot size: ) 0 0 UPL species x 5 1, Carex aquatilis 65 72.2% OBL (A) 90 (B) Column Totals: 90 Carex nebrascensis 25 EVI 27.8% OBL 3 0 ❑ 0.0% Prevalence Index = B/A = 1.000 4 0 ❑ 0.0% Hydrophytic Vegetation Indicators: 5. 0 ❑ 0.0% Dominance Test is > 50% 6. - ❑ 0.0% ~ Prevalence index is <_3.0 1 7.. 0 ❑ 0.0% ❑ Morphological Adaptations 1 1_ provide supporting 0 ❑ 0.0/o ° data in Remarks or on a separate sheet) 9. _ _ -0, ❑ 0.0% ❑ Problematic Hydrophytic Vegetation 1 (1 :plain) 10. 0 ❑ 0.0%_ 11 0 ❑ 0.0% . Indicators of hydric soil and wetland hydrology must 9p =Total Cover be present, unless disturbed or problematic. Woody Vine Stratum (Plot size: ) 1. 0 ❑ 0.0% 2. 0 ❑ 0.0% Hydrophytic Vegetation Yes No ❑ 0 = Total Cover Present? No Bare Ground in Herb Stratum: 10 % Cover of Biotic Crust0 • Remarks: *Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS. US Army Corps of Engineers Arid West - Version 2 Oct. 2008 Soil Sampling Point: SP 18 • Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Matrix Depth n_ Redox Features I (inches) Color (moist) % _d_.. _ Color (moist) % Type Loc2 Texture Remarks i 1 type: C=Concentration. D=Depletion. RM=Reduced Matrix, CS=Covered or Coated Sand Grains 21-ocation: PL Pore Lining. M=Matrix i Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils3 ❑ Histosol (Al) ❑ Sandy Redox (S5) ❑ 1 cm Muck (A9) (LRR C) ❑ Histic Epipedon (A2) ❑ Black Histic (A3) ❑ Stripped Matrix (S6) El 2 cm Muck (ASO) (LRR B) ❑ Hydrogen Sulfide (A4) ❑j Loamy Mucky Mineral (Fl) ❑ Reduced Vertic (F18) ! I ❑ Stratified Layers ( (LRR C) ❑ Loamy Gleyed Matrix (F2) ❑ Red Parent Material (TF2) ❑ 1 cm Muck (A9) (LR LRR D) ❑ Depleted Matrix (F3) L✓ Other (Explain in Remarks) i ❑ Depleted Below Dark Surface (All) ❑ Redox Dark Surface (F6) ❑ Thick Dark Surface (A12) ❑ Depleted Dark Surface (F7) ❑ sandy Muck Mineral y (Si) ❑ Redox depressions (F8) ❑ Vernal Pools (F9) 3 Indicators of hydrophytic vegetation and i ❑ Sandy Gleyed Matrix (S4) wetland hydrology must be present. Restrictive Layer (if present). Type: . • Depth (inches): Hydric Soil Present? Yes No ❑ Remarks: t HYDRIC SOIL BY SATURATION Hydrology _ Wetland Hydrology Indicators: im _j icator6 (m im m of one r_eouired; j check all that apply) Secondary Indicators (2 or more required) ❑ Surface Water (Al) Salt Crust (BlI) Water-Marks_ (Bl) (Rive-•---_rin..e._)-. El High Water Table (A2) ❑ Biotic Crust (B12) ❑ Sediment Deposits (B2) (Riverine) V Saturation (A3) ❑ Aquatic Invertebrates (B13) ❑ Drift Deposits (B3) Riverine) ❑ Water Marks (Bl) (Nonriverine) E] Hydrogen Sulfide Odor (Cl) ❑ Drainage Patterns (B10) ❑ Sediment Deposits (B2) (Nonriverine) ❑ Oxidized Rhizospheres along Living Roots (0) ❑ Dry Season Water Table (C2) ❑ Drift deposits (B3) (Nonriverine) ❑ Presence of Reduced Iron (C4) ❑ Crayfish Burrows (C8) ❑ Surface Soil Cracks (B6) ❑ Recent Iron Reduction in Plowed Soils (C6) ❑ Saturation Visible on Aerial Imagery (C9) ❑ Inundation Visible on Aerial Imagery (B7) ❑ Thin Muck Surface (0) ❑ Shallow Aquitard (D3) ❑ Water-Stained Leaves (B9) ❑ Other (Explain in Remarks) FAC-neutral Test (D5) Field Observations: Surface Water Present? Yes ❑ No Depth (inches): f Water Table Present? Yes ❑ No O Depth (inches): f Saturation Present? I (includes capillary fringe) Yes 0 No ❑ Wetland Hydrology Present? Yes No ❑ Depth (inches): Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available: i Aerial photo Remarks. Saturation visible from offsite and from aerial photo WETLAND DETERMINATION DATA FORM - Western Mountains, Valleys, and Coast Region Project/Site: DESCHUTES LWI City/County: SUNRIVER/DESCHUTES Sampling Date: _22-Jun-10 Applicant/ Owner: DESCHUTES COUNTY State: OR Sampling Point: SP 18A • _ Investigator(s). ALISON SIGLER, SARAH HARTUNG Section, Township, Range: 5 27 T 21 S R 10 E Landform (hillslope, terrace, etc.): Valley bottom Local relief (concave, convex, none): convex Slope: 0.0 ° Subregion (LRR): LRR A Lat.: 43.7237 Long.: -121.5088 Datum: NAD83 Soil Map Unit Name: 144A:_unriver SandYm,_Q. Q 3 Percent Slgpg5„ NWI classification: pA Are climatic/ hydrologic conditions on the site typical for this time of year? Yes * No ❑ (If no, explain in Remarks.) Are Vegetation ❑ , soil ❑ , or Hydrology ❑ significantly disturbed? Are "Normal Circumstances" present? Yes ❑ No 0 AreVegetation lI , Soil ❑ , or Hydrology ❑ naturally problematic? (If needed, explain any answers in Remarks.) Summarv of Findinas - Attach site map showing sampling point locations, transects, important features, et Hydrophytic Vegetation Present? Yes *j No ❑ Is the Sampled Area Hydric Soil Present? Yes ❑ No* Yes ❑ No 0 Yes ❑ • No Within a Wetland? ❑ Wetland Hydrology Present? Remarks: HEAVILY GRAZED BY RESIDENT CATTLE On-site determination. VEGETATION - Use scientific names of plants. Dominant Species? _ Absolute Rel.Strat. Indicator Tree Stratum (Plot size: ) % Cover Cover. Status Z.. _ 0 ❑ 0.0% 2,_ 0 ❑ 0.0% 3 o r 0.0% 4. 0 ❑ 0.0% 9 = Total Cover Sapling/Shrub Stratum (Plot size: ) _ _ • 1. 0 ❑ 0.0% 2. 0 ❑ 0.0% 3. o ❑ o.o% 4. o ❑ q1._q% 5. 0 ❑ 0.0% 0 = Total Cover Herb Stratum (Plot size: ) 1. Gnaphalium sp. 10 ❑ 13.3% FAC 2.Juncus sp 20 EI/I 26.7% FACW 3. Festuca sp. 40 ❑ 53.3% FAC 4_Poa sp. 5 ❑ 6.7%, FAC 5. 0 ❑ 0.0% 0 ❑ o.0% o ❑ 0 0 % 7, . - 0 El 0.0% 8 . 0 ❑ o.o% 9 0 F1 0.0% _ ZO . o ❑ o.o% 11. 75 = Total Cover Woody Vine Stratum (Plot size: ) 1. 0 ❑ 0.00 2. 0 ❑ 0.0%0 0 = Total Cover % Bare Ground in Herb Stratum: 25 Dominance Test worksheet: Number of Dominant Species That are OBL, FACW, or FAC: 2 (A) Total Number of Dominant Species Across All Strata: 2 (B) Percent of dominant Species That Are OBL, FACW, or FAC: 100.0% (A/B) Prevalence Index worksheet: Total % Cover of. Multoly by, OBL species 0 x 1 = 0, FACW species 20 x 2 = 40 FAC species x 3 = 165 FACU species 0 x 4 = 0 UPL species I x 5 = 0 column Totals: 75 (A) 205 (B) Prevalence Index = B/A = 2.733 Hydrophytic Vegetation Indicators: ❑d Dominance Test is > 50% ❑d Prevalence index is :53.01 Morphological Adaptations 1 (Provide supporting data in Remarks or on a separate sheet) ❑ Wetland Non-Vascular Plantsl ❑ Problematic Hydrophytic Vegetationl (Explain) 1Indicators of hydric soil and wetland hydrology must be present, unless disturbed or problematic. Hydrophytic Vegetation Yes C NO Present? Remarks: Poa sp., Gnaphalium sp. and Festuca sp. assumed FAC. Juncus sp. assumed FACW. *Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version Soil Sampling Point: 18A Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Depth Matrix Redox Features (inches) Color (moist) % Color (moist) mm % Type1 Loci Texture Remarks 0-11 10YR 2/1 100% Loam 11-20 10YR 4/1 100% Sand 1Type: C=Concentration. D=Depletion. RM=Reduced Matrix, CS=Covered or Coated Sand Grains 21-ocation: PL=Pore Lining. M=Matrix i Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils:3 ❑ Histosol (Al) ❑ Sandy Redox (S5) ❑ 2 cm Muck (A10) ❑ Histic Epipedon (A2) ❑ Black Histic (A3) ❑ Stripped Matrix (S6) ❑ Loamy Mucky Mineral (Fl) (except in MLRA 1) ❑ Red Parent Material (TF2) ❑ Other (Explain in Remarks) ❑ Hydrogen Sulfide (A4) ❑ Loamy Gleyed Matrix (F2) ❑ Depleted Below Dark Surface (All) ❑ Depleted Matrix (F3) ❑ Thick Dark Surface (A12) ❑ Sandy Muck Mineral (Sl) ❑ Redox Dark Surface (F6) ❑ Depleted Dark Surface (F7) 3Indicators of hydrophytic vegetation and tl d h l ❑ Sandy Gleyed Matrix (S4) ❑ Redox depressions (F8) we an ydro ogy must be present, unless disturbed or problematic. Restrictive Layer (if present): i Type: Depth (inches): a Hydric Soil Present? Yes ❑ No 0 Remarks: i • Hydrology Wetland Hydrology Indicators: _ Primary Indicators (minimum of one required; check all that apply) Secondary Indicators (minimum of two required) ❑ Surface Water (Al) ❑ Water-Stained Leaves (B9) (except MLRA ❑ Water-Stained Leaves (B9) (MLRA 1, 2 ❑ High Water Table (A2) 1, 2, 4A, and 4B) , 4A, and 4B) ❑ Saturation (A3) ❑ Salt Crust (Bll) ❑ Drainage Patterns (B10) ❑ Water Marks (BI) ❑ Aquatic Invertebrates (B13) ❑ Dry Season Water Table (C2) ❑ Sediment Deposits (B2) ❑ Hydrogen Sulfide Odor (Cl) F] Saturation Visible on Aerial Imagery (C9) ❑ Drift deposits (B3) ❑ Oxidized Rhizospheres on Living Roots (0) ❑ Geomorphic Position (D2) ❑ Algal Mat or Crust (B4) ❑ Presence of Reduced Iron (C4) ❑ Shallow Aquitard (133) t ❑ Iron Deposits (B5) ❑ Recent Iron Reduction in Tilled Soils (C6) ❑ FAC-neutral Test (DS) ❑ Surface Soil Cracks (B6) ❑ Stunted or Stressed Plants (Dl) (LRR A) ❑ Raised Ant Mounds (D6) (LRR A) ❑ Inundation Visible on Aerial Imagery (B7) ❑ Other (Explain in Remarks) ❑ Frost Heave Hummocks (137) ❑ Sparsely vegetated Concave Surface (B8) Field Observations: Surface Water Present? Yes ❑ No O Depth (inches): J Water Table Present? Yes ❑ No 0 Depth (inches): Saturation Present? Yes ❑ No Wetland Hydrology Present? Yes ❑ No C Depth (inches): (includes capillary fringe) Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available: i i Remarks: US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version • WETLAND DETERMINATION DATA FORM - Western Mountains, Valleys, and Coast Region Project/Site: DESCHUTES LWI _ City/County: SUNRIVER/DESCHUTES Sampling Date: 22-Jun-10 • Applicant/ Owner: DESCHUTES COUNTY State: OR Sampling Point: SP 19A Investigator(s): ALISON SIGLER, SARAH HARTUNGp Section, Township, Range: S 2 T 22S R 10 E Landform (hillslope, terrace, etc.): Valley bottom Local relief (concave, convex, none): concave Slope: 0.0% / 0.0 ° Subregion (LRR): LRR A Lat.: 43.7031 Long.: -121.5032 Datum:, NAD83 Soil Map Unit Name: 144A. $upCiv~r SanoyJQAm.Q. t9.3 Dlirgent Slope$_ NWI classification: Are climatic/ hydrologic conditions on the site typical for this time of year? Yes ~ NO ❑ (If no, explain in Remarks.) Are Vegetation ❑ , Soil ❑ , or Hydrology ❑ significantly disturbed? Are "Normal Circumstances" present? Yes * No ❑ Are Vegetation ❑ , Soil ❑ , or Hydrology ❑ naturally problematic? (If needed, explain any answers in Remarks.) ..F c:-Aron, - el+arh citp man showina samDlinA point locations, transects, important features, et Hydrophytic Vegetation Present? Yes O No ❑ Is the Sampled Area Hydric Soil Present? Yes C No ❑ Yes 0 No ❑ within a Wetland? Wetland Hydrology Present? Yes C No ❑ Remarks: On-site determination. VEGETATION - Use scientific names of plants. Dominant Species? Absolute Rel.Strat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: ) % Cover Cover Status _ Number of Dominant Species 1 0 ❑ 0.0% That are OBL, FACW, or FAC: _ (A) _ _ 2 0 o 0.0 /o Total Number of Dominant _ 3. 0 ❑ _ 0.0% Species Across All Strata: (B) _ 4 o ❑ o.o% Percent of dominant Species 0 _ - Total Cover = ° (A/B) Nm - That Are 013L, FACW, or FAC: 100.0 /o ) Sapling/Shrub Stratum (Plot size: 60 100.0% OBL Prevalence Index worksheet: • 1, Salix exigua 0 o°i° ❑ o Multly: Total % Cover of. 2 _e . _ 3. 0 0.0% OBL species 60 x 1 = 60 4. 0 ❑ 0.0% T FACW species 100 x 2 = 200 _ 5 0 0.0% ❑ FAC species 0_ x 3= 0 _ 60 = Total Cover FACU species x 4 = 0 Herb Stratum (Plot size: ) 0 0 UPL species x 5 = " 1 Carex sp. 100 V 100.0% FACW 160 260 CB) (A) - Column Totals: 2 0 El 0.0% _ . 0 ❑ o.o% Prevalence Index = B/A = 1.625 0 ❑ 0.0% Hydrophytic Vegetation Indicators: 0 0.0% ❑d Dominance Test is > s0% 5. 0 ❑ 0.0% _ Prevalence Index is :53.01 6 0 ❑ _ O.0% Ll Morphological Adaptations 1 (Provide supporting 0 ❑ 0.0% data in Remarks or on a separate sheet) 0 0 ❑ 0 0% [l Wetland Non-Vascular Plantsl 9. 0 ❑ 0.o% _ ❑ Problematic Hydrophytic Vegetationl (Explain) 10 0 ❑ 0.0% 11. - - - lIndicators of hydric soil and wetland hydrology must 100 =Total Cover be present, unless disturbed or problematic. Woody Vine Stratum (Plot size: ) 1 0 ❑ 0.0% 2 0 ❑ 0.0% Hydrophytic . Vegetation Yes 0 No ❑ 0 =Total Cover Present? % Bare Ground in Herb Stratum: 0 Remarks: Carex sp. assumed to be FACW. ned because Regional status not defined by FWS n assi i i i l d f ec s o ona ess *Indicator suffix = National status or pro g Western Mountains, Valleys, and Coast Region Interim version US Army Corps of Engineers Soil Sampling Point: 19A Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Depth Matrix Redox Features_ (inches) Color (moist) % Color (moist) % Type' ~LOC= Texture Remarks 0-6 lOYR 3/2 100% peat 6-20 lOYR 2/1 100% Silty Clay 11 'Type: C=Concentration . D=Depletion. RM=Reduced Matrix, CS=Covered or Coated Sand Grains zLocation: PL=Pore Lining. M=Matrix i Hydric Soil Indicators: (Applicable to all ❑ Histo l Al LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils-3 ( so ) ❑ Histic Epipedon (A2) ❑ Sandy Redox (S5) ❑ St i d ❑ 2 cm Muck (A10) ❑ Black Histic (A3) ppe r Matrix (S6) ❑ Loamy Mucky Mineral (Fl) (except in MLRA 1) ❑ Red Parent Material (TF2) Other (Ex lain in Rem k E ❑ Hydrogen Sulfide (A4) ❑ Loamy Gleyed Matrix (F2) p ar s) ❑ Depleted Below Dark Surface (All) ❑ Depleted Matrix (9) ❑ Thick Dark Surface (A12) ❑ Redox Dark Surface (F6) 3 ❑ Sandy Muck Mineral(Sl) ❑ Depleted Dark Surface (F7) In e of hydrophytic vegetation and ❑ Sandy Gleyed Matrix (S4) ❑ Redox depressions (F8) w tland d hydro logy must be present, unless disturbed or problematic. Restrictive Layer (if present): Type: Depth (inches): Hydric Soil Present? Yes * No ❑ Remarks: - HYDRIC SOILS ASSUMED BASED ON PERSISTENT SATURATION. NOT THICK ENOUGH TO BE A HISTOSOL Hydrology Wetland Hydrology _ indicators: Primary Indicators (minimum of one required; check all that apply) Surface Water (Al) ❑ Water-Stained Leaves (B9) (except MLRA High Water Table (A2) 1, 2, 4A, and 4B) Saturation (A3) ❑ Water Marks (B1) ❑ Salt Crust (Bll) ❑ Aquatic Invertebrates (B13) ❑ Sediment Deposits (B2) ❑ Hydrogen Sulfide Odor (Cl) ❑ Drift deposits (B3) ❑ Oxidized Rhizospheres on Living Roots (0) ❑ Algal Mat or Crust (B4) ❑ Presence of Reduced Iron (C4) ❑ Iron Deposits (B5) ❑ Recent Iron Reduction in Tilled Soils (C6) ❑ Surface Soil Cracks (B6) ❑ Stunted or stressed Plants (Dl) (LRR A) ❑ Inundation Visible on Aerial Imagery (B7) ❑ Other (Explain in Remarks) ❑ Sparsely Vegetated Concave Surface (B8) Secondary Indicators (minimum of two required) ❑ Water-Stained Leaves (B9) (MLRA 1, 2, 4A, and 4B) ❑ Drainage Patterns (B10) ❑ Dry Season Water Table (C2) ❑ Saturation Visible on Aerial Imagery (C9) ❑ Geomorphic Position (D2) ❑ Shallow Aquitard (D3) L--i FAC-neutral Test (DS) ❑ Raised Ant Mounds (D6) (LRR A) ❑ Frost Heave Hummocks (D7) Field Observations: Surface Water Present? Yes ❑ No 0 Depth (inches): Water Table Present? Yes No ❑ Depth (inches): IF 12 Saturation Present? a r Wetland Hydrology Present? Yes 0 No ❑ (includes capillary fringe) Yes ❑ No ❑ Depth (inches): Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available: !Remarks: - - E US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version • • • WETLAND DETERMINATION DATA FORM - Western Mountains, Valleys, and Coast Region Project/Site: DESCHUTES LWI City/County: SUNRNER/DESCHUTES Sampling Date: 2374un-10 • Applicant/ Owner: DESCHUTES COUNTY State: OR Sampling Point: SP 20A Investigator(s) ALISON SIGLER, SARAH HARTUNG Section, Township, Range: S 34 T 21 S R 10 E Landform (hillslope, terrace, etc.): Lowland Local relief (concave, convex, none): concave Slope: 1.0% / 0.6 ° Subregion (LRR): LRR A Lat.: 43.7120 Long.: -121.5160 Datum: NAD83 Soil Map Unit Name: 144A: Sunrivor sandy Ioam,,Qto 3 pen;eni $)op25._ NWI classification: PEMA Are climatic/ hydrologic conditions on the site typical for this time of year? Yes 0 NO 0 (If no, explain in Remarks.) Are Vegetation ❑ , Soil ❑ , or Hydrology ❑ significantly disturbed? Are "Normal Circumstances" present? Yes 0 No 0 Are Vegetation ❑ , Soil ❑ , or Hydrology ❑ naturally problematic? (If needed, explain any answers in Remarks.) Summarv of Findinas - Attach site man showing sampling point locations, transects, important features, et Hydrophytic Vegetation Present? Yes 0 No 0 Is the Sampled Area Hydric Soil Present? Yes 0 No Yes 0 No ~ within a Wetland? Wetland Hydrology Present? Yes 0 No ❑ Remarks: off-site; right of way; heavily grazed - horse pasture; PRAIRIE DOG BURROWS IN FIELD VEGETATION - Use scientific names of plants. Dominant Species? Absolute Rel.Strat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: ) % Cover Cover Status Number of Dominant Species 0 ❑ 0.)% That are OBL, FACW, or FAC: 2 0 ❑ 0.0% . . ❑ Total Number of Dominant 3 0 0.0% Species Across All Strata: 4. o ❑ o.o% Percent of dominant Species Sapling/Shrub Stratum (Plot size: ) o = Total Cover That Are OBL, FACW, or FAC: Woody Vine Stratum (Plot size: ) 1. 0 _ ❑__0.0% 2. 0 ❑ 0.0% 0 = Total Cover % Bare Ground in Herb Stratum: 0 1. 0 ❑ 0.0% _ Prevalence Index worksheet: 2. 0 ❑ 0.0% Total % Cover of. _ Multip _by: 3 0 ❑ 0.0% OBL species 30 x 1 = 30 4. 0 ❑ 0.0% FACW species 20 x 2 = 40 _ 5• 4_. x_.0.0% FAC species _ 50 x 3 = 150 0 = Total Cover FACU species 0 x 4 = 0 - Herb Stratum (Plot size: ) 0 0 UPL species - _ x 5 = 1 Carex aquatilis 30 V 30.0% OBL column Totals: 100 (A) 220 (B) 2Poa trivialis 20 20.0% FACW C 3 Unidentified pasture grasses 50 141 50.0% FAC Prevalence Index = B/A = 2.200 4. _ 0 El 0.0% _ Hydrophytic Vegetation Indicators: 0 ❑ 0.0% EVI Dominance Test is > 50% 0 ❑ 0.0% W1 Prevalence index is 53.01 7. 0._ ❑0.0 /o _ ❑ Morphological Adaptations 1 (Provide supporting 8 0 ❑ 0.0% data in Remarks or on a separate sheet) 0 ❑ 0.0% ❑ Wetland Non-Vascular Plantsl 10 0 ❑ 0.0% ❑ problematic Hydrophytic Vegetationl (Explain) 11 lIndicators of hydric soil and wetland hydrology must 100 . =Total Cover _ be present, unless disturbed or problematic. 3 (A) 3 (B) 100.0% (A/B) Hydrophytic Vegetation Present? Yes 0 No 0 Remarks: • Carex sp. likely due to road run-off. Unidentified pasture grasses assumed FAC. *Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version soil Sampling Point: 20A Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Depth Matnx~ Redox Features (inches) Color (moist) % Color (moist) % Typel Loc= Texture Remarks 0-20 IOYR 3/2 100% Loam 'Type: C=Concentration. D=Depletion. RM=Red uced Matrix, CS=Covered or Coated Sand Grains zLoca tion: PL=Pore Lining. M=Matrix Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) ❑ Histosol (Al) ❑ Indicators for Problematic Hydric Soils-3 I ❑ Histic Epipedon (A2) Sandy Redox (S5) ❑ Stripped Matrix (S6) ❑ 2 cm Muck (A10) ❑ Red Parent Material (TF2) ❑ Black Histic (A3) ❑ Loamy Mucky Mineral (Fl) (except in MLRA 1) ❑ Other (Explain in Remarks) ❑ Hydrogen Sulfide (A4) ❑ Loamy Gleyed Matrix (F2) ❑ Depleted Below Dark Surface (All) ❑ Depleted Matrix (9) ❑ Thick Dark Surface (A12) ❑ Sandy Muck Mineral (Sl) ❑ Redox Dark Surface (F6) ❑ Depleted Dark Surface (F7) 3Indicators of hydrophytic vegetation and l h ❑ Sandy Gleyed Matrix (S4) ❑ Redox depressions (F8) wet and ydrology must be present, unless disturbed or problematic. Restrictive Layer (if present): Type Depth (inches): _ Hydric Soil Present? Yes ❑ No 0 Remarks: Hydrology Wetland Hydrology Indicators: Primary Indicators (minimum of one required; check all that apply) Secondary Indicators (minimum of two required)' ❑ Surface Water (Al) ❑ Water-Stained Leaves (B9) (except MLRA ❑ Water-Stained Leaves (B9) (MLRA 1 2 ❑ High Water Table (A2) 1, 2, 4A, and 4B) , , 4A, and 4B) ❑ Saturation (A3) ❑ Salt Crust (Bll) ❑ Drainage Patterns (B10) ❑ Water Marks (BS) ❑ Aquatic Invertebrates (B13) ❑ Dry season water Table (C2) ❑ Sediment Deposits (B2) ❑ Drift de it B3 ❑ Hydrogen Sulfide Odor (Cl) ❑ Saturation Visible on Aerial Imagery (C9) pos s ( ) ❑ Oxidized Rhizospheres on Living Roots (C3) ❑ Geomorphic Position (D2) ❑ Algal Mat or Crust (B4) ❑ Presence of Reduced Iron (C4) ❑ Shallow Aquitard (D3) ❑ Iron Deposits (B5) ❑ Recent Iron Reduction in Tilled Soils (C6) ❑ FAC-neutral Test (D5) ❑ Surface Sail Cracks (B6) ❑ Stunted or Stressed Plants (Dl) (LRR A) ❑ Raised Ant Mounds (D6) (LRR A) ❑ Inundation Visible on Aerial Imagery (B7) ❑ Other (Explain in Remarks) ❑ Frost Heave Hummocks (D7) ❑ Sparsely Vegetated Concave Surface (B8) Field Observations: Surface Water Present? Yes ❑ No Depth (inches): Water Table Present? Yes ❑ No O Depth (inches): C Saturation Present? (includes capillary fringe) Yes ❑ No O _ Wetland Hydrology Present? Yes ❑ No Depth (inches): Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if ava ilable: i Remarks: - US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version • WETLAND DETERMINATION DATA FORM - Western Mountains, Valleys, and Coast Region Project/Site: DESCHUTES LWI _ _ . City/County: SUNRNER/DESCHUTES Sampling Date: 23-Jun-10 Applicant/Owner: DESCHUTES COUNTY _ State: OR_,a Sampling Point: SP 21A • Investigator(s): ALISON SIGLER, SARAH HARTUNG Section, Township, Range: S 9 T 22S R 10 E Landform (hillslope, terrace, etc.): Floodplain Local relief (concave, convex, none): Concave Slope: 2.0% / 1.1 ° Subregion (LRR): LRR A Lat.: 43.6745 Long.: -121.5436 Datum: NAD83 Soil Map Unit Name: 1+4 . $Wnriyer5,@ndv IOam..,,4,to 3 Percent 51QQe NWI classification: Are climatic/ hydrologic conditions on the site typical for this time of year? Yes No ❑ (If no, explain in Remarks.) Are Vegetation ❑ , soil ❑ , or Hydrology ❑ significantly disturbed? Are "Normal Circumstances" present? Yes C No ❑ Are Vegetation ❑ Soil [:71 , or Hydrology ❑ naturally problematic? (If needed, explain any answers in Remarks.) Qimmarv of Findinas - Attach site maD showing sampling point locations, transects, important features, et • Hydrophytic Vegetation Present? Yes 0 No ❑ Fis the Sampled Area Hydric Soil Present? Yes C No Yes No l within a Wetland? 00 NO ❑ Wetland Hydrology Present? Yes Remarks: On-site determination. 0 ❑ o.o°° 4 _ 0 ❑ 0.0% 0 El o.0% 6. _ 0 ❑ 0.o% 0 0% ❑ 0 8 o . 0 ❑ o.o% 9 0 0.0% ❑ 10 - . 0 ❑ 0.0 % 11 1 100 = Total Cover VEGETATION - Use scientific names of plants. Dominant -Species Absolute Rel.Strat Indicator Dominance Test worksheet: Tree Stratum (Plot size: ) % Cover _ Cover Status - Number of Dominant Species 0 ❑ 0.0% That are OBL, FACW, or FAC: 2 (A) 2 o ❑ 0.0% i t f _ - ❑ Dom nan Total Number o B 3 0 Species Across All Strata: ) ( 4 0 ❑ 0.0% . Percent of dominant Species ' Sapling/Shrub Stratum (Plot size: 0 - - =Total Cover That Are OBL, FACW, or FAC: 100.0% - - (A/B) 1, Salix exigua 20 100.0% OBL Prevalence Index worksheet: 2 0 ❑ o.o°io Total % Cover of;_ Multiply by:_ 3. o.o% OBL species 120 x 1 = 120 4 0 ❑ 0.0% FACW species Q x 2= 5. o ❑ 0.0%,- FAC species 0 x 3 20 =Total Cover FACU species x 4 = U-- Herb Stratum (Plot size: ) 0 UPL species x 5 = 0 _ Carex aquatilis 1. 100 V] 100.0% OBL 120 Column Totals: (A) 120 (B) 2 0 ❑ o.o% . 3 0 ❑ 0.0% Prevalence Index = B/A = 1.000 Hydrophytic Vegetation Indicators: d❑ Dominance Test is > 50% 0 Prevalence index is :53.01 ❑ Morphological Adaptations 1 (Provide supporting data in Remarks or on a separate sheet) ❑ Wetland Non-Vascular Plantsl ❑ Problematic Hydrophytic Vegetationl (Explain) 'Indicators of hydric soil and wetland hydrology must be present, unless disturbed or problematic. Hydrophytic Vegetation Present? Yes* No ❑ Woody Vine Stratum (Plot size: ) 1. 0 ❑....0.0% 2. 0 ❑ _ 0.0%- 0 = Total Cover % Bare Ground in Herb Stratum: 0 Remarks: *Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version Soil Sampling Point: 21A Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Depth Matrix Redox Features (inches) color, (moist) % Color (moist) % Type I Loc2 Texture Remarks 0-8 IOYR 2/1 85% IOYR 3/4 15% C M Sandy Loam 8-20 7.5YR 3/1 90% 7.5YR 3/4 10% C M Clay Loam i tType: C=Concentration. D=Depletion. RM=Red uced Matrix, CS=Covered or Coated Sand Grains 'Location: PL=Pore Lining. M=Matrix Hydric Soil Indicators: (Applicable to all LRRS, unless otherwise noted.) Indicators for Problematic Hydric Soils-3 ❑ Histosol (Al) ❑ Sandy Redox (S5) ❑ 2 cm Muck (A10) I ❑ Histic Epipedon (A2) ❑ Stripped Matrix (S6) ❑ Red Parent Material (TF2) ❑ Black Histic (A3) ❑ Hydrogen Sulfide (A4) J Loamy Mucky Mineral (Fl) (except in MLRA 1) ❑ Loamy Gleyed Matrix (F2) ❑ Other (Explain in Remarks) ❑ Depleted Below Dark Surface (All) ❑ Depleted Matrix (F3) ❑ Thick Dark Surface (A12) ❑ Redox Dark Surface (F6) 3Indicators of hydrophytic vegetation and ❑ Sandy Muck mineral (51) ❑ Depleted Dark Surface (F7) wetland hydrology must be present ❑ Sandy Gleyed Matrix (S4) ❑ Redox depressions (F8) , unless disturbed or problematic. Restrictive Layer (if present): Type: I Depth (inches):_ Hydric Soil Present? Yes 0 No O I Remarks: _ is i i Hydro logy Wetland Hydrology Indicators: Primary Indicators (minimum of one regwred; -check all that apply) Secondary Indicators (minimum of two required) , Surface Water (Al) ❑ Water-Stained Leaves (B9) (except MLRA ❑ Water-Stained Leaves (B9) (MLRA 1 2 ❑ High Water Table (A2) 1, 2, 4A, and 4B) , , 4A, and 4B) Saturation (A3) ❑ Salt Crust (BlI) ❑ Drainage Patterns (B10) ❑ Water Marks (51) ❑ Aquatic invertebrates (613) ❑ Dry Season Water Table (C2) ❑ Sediment Deposits (B2) ❑ Drift deposits (B3) D Hydrogen Sulfide Odor (Cl) ❑ Oxidized Rhizospheres on Living Roots (0) ❑ Saturation Visible on Aerial Imagery (C9) ❑ Geomorphic Position (132) ❑ Algal Mat or Crust (B4) ❑ Presence of Reduced Iron (C4) ❑ Shallow Aquitard (133) ❑ Iron Deposits (B5) ❑ Recent Iron Reduction in Tilled Soils (C6) ❑ FAC-neutral Test (135) ❑ Surface Soil Cracks (B6) ❑ Stunted or Stressed Plants (Dl) (LRR A) ❑ Raised Ant Mounds (136) (LRR A) ❑ Inundation Visible on Aerial Imagery (B7) ❑ Other (Explain in Remarks) ❑ Frost Heave Hummocks (D7) ❑ Sparsely Vegetated Concave Surface (68) Field Observations: Surface Water Present? Yes O No O Depth (inches): Water Table Present? Yes No O Depth (inches): 14 Saturation Present? g Wetland Hydrology Present? Yes 0 No O (includes capillary fringe) Yes NO O Depth (inches): Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available: `Remarks: I US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version • WETLAND DETERMINATION DATA FORM - Western Mountains, Valleys, and Coast Region Project/Site: DE CHUTES LWI City/County: SUNRIVER/DESCHUTES Sampling Date: 23-Jun-10 is Applicant/Owner: DESCHUTES COUNTY State: OR,rn_ Sampling Point: SP 22A Investigator(s): ALISON SIGLER, SARAH HARTUNG Section, Township, Range: S 15 T 22 S R 10 E Landform (hillslope, terrace, etc.): Valley bottom Local relief (concave, convex, none): convex Slope: 0.0% / 0.0 ° Subregion (1.1111): LRR A Lat.: 43.6671 Long.: -121.5107 Datum: NAD83 Soil Map Unit Name: 29A: Crydq!1 I , O to. p€r4ri 519pe NWI classification: PEMC _ Are climatic/ hydrologic conditions on the site typical for this time of year? Yes 0 NO ❑ (If no, explain in Remarks.) Are Vegetation ❑ , Soil ❑ , or Hydrology ❑ significantly disturbed? Are "Normal Circumstances" present? Yes O No ❑ Are Vegetation ❑ , Soil ❑ , or Hydrology ❑ naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transects, important features, et t E Hydrophytic Vegetation Present? Yes * No ❑ Is the Sampled A. Hydric Soil Present? Yes O No ❑ Yes 0 No Yes * No ❑ within a Wetland? Wetland Hydrology Present? Remarks: IN RIGHT OF WAY, WETLAND IN GRAZED HORSE PASTURE Off-site determination. VEGETATION - Use scientific names of plants. Dominant Species? Absolute Rel.Strat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: ) % Cover Cover Status Number of Dominant Species 0 ❑ 0.0% That are OBL, FACW, or FAC: 1 (A) ❑ 0.0% ❑ Total Number o Dominant 3. 0 0.0% Species Across All Strata: (B) 4. 0 ❑ 0.0% Percent of dominant Species 0 =Total Cover That Are OBL, FACW, or FAC: 100.0% (A/B) Sapling/Shrub Stratum (Plot size: ) 1 0 ❑ 0.0% Prevalence Index worksheet: 2. 0 ❑ o.o°io Total %_Cover of: Mult!I?ly by';_ 3. 0 ❑ 0.0% 08L species 5 x 1= 5 4, 0 ❑ 0.0% FACW species 57 x 2 = 1114- 5. 0 ❑ 0.0% FAC species 10 x 3 = 30_ _ 0 = Total Cover FACU species 15..-- x 4 = 60 Herb Stratum (Plot size: ) 25 5 0 9% FAC ❑ 10 . x 5 = UPL species 1 Claytonia perfoliata 1 . 234 (B) 92 2 Capsella bursa pastors 15 ❑ 16.3% FACU (A) Column Totals: 3 Carex sp. 55 FV11 59.8% FACW Prevalence Index = B/A = 2.543 4 Carex nebrascensis 5 ❑ 5.4% OBL Hydrophytic Vegetation Indicators: 5 Verbascum thapsus 5 ❑ 5.4% UPL Dominance Test is > so% Myosotis sp. ❑.,__2.2% FACW Prevalence Index is 53.01 7. , 0 ❑ 0.0%_ ❑ Morphological Adaptations I (Provide supporting 8 0 0.0% data in Remarks or on a separate sheet) 9. 011 ❑ 0.0 /o ❑ Wetland Non-Vascular Plantsl 1o. _0 o 0'0% Problematic Hydrophytic Vegetation' (Explain) 11. _ 0 ❑ 0.0% 11ndicators of hydric soil and wetland hydrology must 92 = Total Cover he present. unless disturbed or Droblematic. Woody Vine Stratum (Plot size: ) 1. 0._. ❑ 0.0% 0- El 2. ° 0 = Total Cover O/o Bare Ground in Herb Stratum: 8 Hydrophytic Vegetation Yes 0 No ❑ Present? Remarks: Carex sp. and Myosotis sp. assumed to be FACW. *Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS *Indicator US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version Soil Sampling Point: 22A Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Depth Matrix Redox Features (inches) Color (moist) o{o Color (moist) % Typel Loc- Texture Remarks 0-9 10YR 2/1 100% MUCKY PEAT 9 20 10YR 2/1 100% Silty Clay Loam 1Type: C=Concentration. D=Depletion. RM=Reduced Matrix, CS=Covered or Coated Sand Grains 2Location: PL=Pore Lining. M=Matrix Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils:3 s ❑ Histosol (Al) ❑ Sandy Redox (S5) ❑ 2 cm Muck (A10) Histic Epipedon (A2) ❑ Stripped Matrix (S6) ❑ Red Parent Material (TF2) ❑ Black Histic (A3) ❑ Loamy Mucky Mineral (Fl) (except in MLRA 1) ❑ Other (Explain in Remarks) ❑ Hydrogen Sulfide (A4) ❑ Loamy Gleyed Matrix (F2) ❑ Depleted Below Dark Surface (All) ❑ Depleted Matrix (F3) ❑ Thick Dark Surface (A12) ❑ Sand Muck Mineral (Sl) ❑ Redox Dark Surface (F6) ❑ Depleted Dark Surface (F7) 3Indicators of hydrophytic vegetation and tl d h l d t b y ❑ Sandy Gleyed Matrix (S4) ❑ Redox depressions (F8) we an y ro ogy mus e present, unless disturbed or problematic. I Restrictive Layer (if present): Type' Depth (inches): Hydric Soil Present? Yes * No ❑ Remarks: Hydrology Wetland Hydrology Indicators: Primary Indicators (minimum of one required; check all that apply) Secondary Indicators (minimum of two required) ❑ Surface Water (Al) ❑ Water-Stained Leaves (B9) (except MLRA ❑ Water-Stained Leaves (B9) (MLRA 1, 2, ❑ High Water Table (A2) 1, 2, 4A, and 4B) 4A, and 4B) Saturation (A3) ❑ Salt Crust (811) ❑ Drainage Patterns (B10) ❑ Water Marks (Bl) ❑ Aquatic Invertebrates (B13) ❑ Dry Season Water Table (C2) ❑ Sediment Deposits (B2) ❑ Hydrogen Sulfide Odor (CI) L _I Saturation Visible on Aerial Imagery (C9) ❑ Drift deposits (B3) ❑ Oxidized Rhizospheres on Living Roots (0) ❑ Geomorphic Position (D2) ❑ Algal Mat or Crust (B4) ❑ Presence of Reduced Iron (C4) ❑ Shallow Aquitard (D3) ❑ Iron Deposits (B5) ❑ Recent Iron Reduction in Tilled Soils (C6) ❑ FAC-neutral Test (DS) ❑ Surface Soil Cracks (B6) ❑ Stunted or Stressed Plants (Dl) (LRR A) ] Raised Ant Mounds (D6) (LRR A) ❑ Inundation Visible on Aerial Imagery (B7) ❑ Other (Explain in Remarks) ❑ Frost Heave Hummocks (137) ❑ Sparsely vegetated concave Surface (B8) Field Observations: Surface Water Present? Yes ❑ No Depth (inches): Water Table Present? Yes 0 No ❑ Depth (inches): Saturation Present? Wetland Hydrology Present? Yes * No ❑ Yes * No ❑ Depth (inches): (includes capillary frinqe) Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available: Remarks: • US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version • WETLAND DETERMINATION DATA FORM - Western Mountains, Valleys, and Coast Region Project/Site: DESCHUTES LWI City/County: SUNRIVER/DESCHUTES Sampling Date: _23-Jun-10 • Applicant/ Owner: DESCHUTES COUNTY State: OR Sampling Point: SP 23A Investigator(s). ALISON SIGLER, SARAH HARTUNG Section, Township, Range: S 16 T 22 S R 10 E 11 Landform (hillslope, terrace, etc.): Valley bottom Local relief (concave, convex, none): concave Slope: 0.0% / 0.0 ° Subregion (LRR): LRR A Lat.: 43.6727 Long.: -121.5380 Datum: NAD83 „ Soil Map Unit Name: 144A: $4inriv r.sPn Ism Q r n .$_1Qpe NWI classification: PFOA Are climatic/ hydrologic conditions on the site typical for this time of year? _ Yes No (If no, explain in Remarks.) Are Vegetation , Soil or Hydrology ❑ significantly disturbed? Are "Normal Circumstances" present? Yes No Are Vegetation , Soil , or Hydrology _J naturally problematic? (If needed, explain any answers in Remarks.) summarv of Findinas - Attach site map showing sampling point locations, transects, important features, et u • Hydrophytic Vegetation Present? Yes No Is the Sampled Area Hydric Soil Present? Yes No ' No e within a Wetland? Yes Wetland Hydrology Present? Yes NO Remarks: On-site determination. VEGETATION - Use scientific names of plants. Dominant Species? Absolute Rel.Strat. Indicator Dominance Test worksheet Tree Stratum (Plot size: ) % Cover Cover Status Number of Dominant Species 1. Pinus contorta 60 100.0% FAC That are OBL, FACW, or FAC: 3 . (A) 2 0° I I 0.0% . ❑ Total Number of Dominant 3. __0 0.0% Species Across All Strata: 5 (e) 4. o ❑ 0.0% Percent of dominant Species 60 - = Total Cover That Are OBL, FACW, or FAC: 60.0% (A/B) Sapling/Shrub Stratum (Plot size: 1 Woody Vine Stratum (Plot size: ) 2. 4.Poa sp. 5. Spiraea sp. li Taraxacum officinale 7. 8 9. 10. 1. Amelanchier alnifolia 10 66.7% FACU Prevalence index worksheet: 2. Rosa sp. 5 33.3% FAC Total % Cover of: Multiply by: 3. 0.0% OBL species 0 x 1 = 0 4. 0 0.0% FACW species 10 x 2 = 20 5._ ❑ 0.0% FAC species 120_._ x 3 = 360 15 = Total Cover FACU species 36 x 4 = 14,4 Herb Stratum (Plot size: ) 0 x 5 = 0 1. Equisetum sp. 5.5% FAC uPL species 166 column Totals : CA) 524 Trifolium sp. 2 10 11.0% FAC . U 2 5% FACU Prevalence Index = B/A = 3.1 6 3 Frageria sp. 25 7. 40 44.0% FAC 10 ❑ 11.0% FACW 1 1.1% FACU 0 ❑ 0.0% o ❑ 0.0% 0 ❑ 0.o% o ❑ o.o% 0 0.0% 91 = Total Cover (B) Hydrophytic Vegetation Indicators: l,k4 Dominance Test is > SO% ❑ Prevalence index is :53.01 Morphological Adaptations 1(Provide supporting data in Remarks or on a separate sheet) Wetland Non-Vascular Plantsl Problematic Hydrophytic Vegetationl (Explain) 1Indicators of hydric soil and wetland hydrology must be present, unless disturbed or problematic. 0 ❑ 0.0% 0 0.0% Hydrophytic Vegetation 0 = Total Cover Present? Yes No Bare Ground in Herb Stratum: 9 Remarks: Rosa sp., Equisetum sp., Trifolium sp. and Poa sp. assumed FAC. Spiraea sp. assumed FACW. Fragaria sp. assumed FACU. *Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version son Sampling Point: 23A Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Depth _w Matrix Redox Features (inches) Color (moist) % Color (moist) % Type' Loci Texture Remarks 0-3 10YR 2/1 100% sandy silt loam 3-5 10YR 3/1 100% _ Clay Loam 5-20 2.5Y 6/4 80% Sy 6/6 _ 20% C PL Sandy Clay 'Type: C=Concentration. D=Depletion. RM=Reduced Matrix, CS=Covered or Coated Sand Grains zLocation: PL=Pore Lining. M=Matrix Hydr c Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils} Histosol (Al) 1 1 ] Histic E edon (A2) Sandy Redox (S5) Stripped Matrix (56) L! 2 cm Muck (A10) i 1 Red Parent Material (TF2) Black Histic (A3) Loamy Mucky Mineral (Fl) (except in MLRA 1) - 1 Other (Explain in Remarks) Hydrogen Sulfide (A4) L 1 Loamy Gleyed Matrix (F2) EI Depleted Below Dark Surface (All) F1 Depleted Matrix (F3) J Thick Dark Surface (A12) Sandy Muck Mineral (Sl) Redox Dark Surface (F6) i~ Depleted Dark Surface (F7) 3Indicators of hydrophytic vegetation and l d h Sandy Gleyed Matrix (S4) l Redox depressions (F8) wet an ydrology must be present, unless disturbed or problematic. Restrictive Layer (if present): Type: Depth (inches): Hydric Soil Present? Yes No Remarks: Soils assumed hydric based on hydrology indicator. • E Hydrology -1011U nyarvwOgy LHUICacorS: Primary Indicators (minimum of one required; check all that apply) Secondary Indicators (minimum of two required)' u Surface Water (AS) L_ Water-Stained Leaves (B9) (except MLRA Water-Stained Leaves (B9) (MLRA 1 2 E High Water Table (A2) 1, 2, 4A, and 4B) , , 4A, and 4B) Saturation (A3) Salt Crust (Bll) [J Drainage Patterns (B10) L_ Water Marks (Bl) L- Aquatic Invertebrates (B13) Dry Season Water Table (C2) J Sediment Deposits (82) n Hydrogen Sulfide Odor (Cl) Saturation Visible on Aerial Imagery (C9) _ Drift deposits (B3) ❑ Algal Mat or Crust (B4) L-- Oxidized Rhizospheres on Living Roots (0) F-1 Presence of Reduced Iron (C4) Geomorphic Position (D2) L Shallow Aquitard (D3) 7 Iron Deposits (B5) C J Surface Soil Cracks (B6) L Recent Iron Reduction in Tilled Soils (C6) 1-Stunted or Stressed Plants (Dl) (LRR A FAC-neutral Test (D5) - Inundation Visible on Aerial Imagery (B7) ) iNOther (Explain in Remarks) - I Raised Ant Mounds (D6) (LRR A) r I Frost Heave Hummocks (D7) Sparsely Vegetated Concave Surface (B8) Field Observations: Surface Water Present? Yes No Depth (inches): Water Table Present? Yes NO Depth (inches): - Saturation Present? Wetland Hydrology Present? Yes No L~ (includes capillary fringe) Yes No Depth (inches): Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available: E- - - i Remarks: Landowner confirms there is early spring hydrology on-site. i US Army Corps of Engineers Western Mountains, valleys, and Coast Region Interim version • WETLAND DETERMINATION DATA FORM - Western Mountains, Valleys, and Coast Region Project/Site: DESCHUTES LWI City/County: SUNRIVER/DESCHUTES Sampling Date: 23-Jun-10 Applicant/Owner: DESCHUTES COUNTY State: OR Sampling Point: SP 24A Investigator(s). ALISON SIGLER, SARAH HARTUNG Section, Township, Range: S 17 T 22 S R 10 E Landform (hillslope, terrace, etc.): Floodplain Local relief (concave, convex, none): convex Slope: 0.0% / 0.0 ° Subregion (LRR): LRR A Lat.: 43.6701 Longs -121.5544 Datum: NAD83 Soil Map Unit Name: 29A: Crvaauolls, 0 to 3 percent slopes NWI classification: P5$C Are climatic/ hydrologic conditions on the site typical for this time of year? Yes * No (If no, explain In Remarks.) Are Vegetation ❑ , Sail ❑ , or Hydrology ❑ significantly disturbed? Are "Normal Circumstances" present? Yes C) No Are Vegetation , Soil , or Hydrology F-1 naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transects, important features, et • Hydrophytic Vegetation Present? Yes No 0 IS the Sampled Area Hydric Soil Present? Yes No -i) ~ - within a Wetland? Yes No Wetland Hydrology Present? Yes ` No - Remarks: On-site determination. Y 0 ❑ 0.0% 2. 0 1-1 0.0% 0 = Total Cover VEGETATION - Use scientific names of plants. Dominant Species? Absolute Rel.Strat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: ) % Cover Cover Status ❑ ° Number of Dominant Species 1. 0 0.0 k That are 013L, FACW, or PAC: 3 (A) 2. 0 ❑ 0.0% 3 0 U 0 o% Total Number of Dominant , . Species Across All Strata: 3 (B) 4. 0 0.0% 0 = Total Cover Percent of dominant Species 100.0°/13 (A/8) Sapling/Shrub Stratum (Plat size: ) That Are OBL, FACW, or FAC: 1, Salix exigua 65 U 81.3°h OBL Prevalence Index worksheet: 2. Spiraea sp. 15 ❑ 18.8°h FACW Total % Cover of: Multiply by: 3. 0 ❑ 0.0% 0131- species 65 x 1 - 65 4. .0 0.0°ra PACw species 80 x 2 - 160......... 5. 0 ❑ 0.0% FAC species 5 x 3 - 15 80 = Total Cover FACU species 0 x 4 = 0 Herb Stratum (Plot size: ) 5 25 C 45 U 60 0% FACW x 5 uPL species 1. arex sp. . 2. Equisetum arvense 5 ❑ 6.7% FAC Column Totals: 155 (A) Z65 (B) 3 Stellaria longifolia 20 n 26.7% FACW Prevalence Index = B/A = 1.710 Galeopsis tetrahit 4. 5 ❑ 6.7% UPL Nydrophytic Vegetation indicators: 5. 0 ❑ 0.0% n Dominance Test is n SO% 6.. 0 L 0.0% Prevalence Index is 53.01 0 ❑ 0.o% Morphological Adaptations I (Provide supporting 8 0 ❑ 0.0% data in Remarks or on a separate sheet) 9 0 ❑ 0.0% Wetland Non-Vascular Plantsl 10, 0 ❑ 0.0% ❑ problematic Hydrophytic Vegetationl (Explain) 17 . 0.. ~ I 0.0% . 75 =Total Cover 1lndicators of hydric soil and wetland hydrology must be present, unless disturbed or problematic. Wood Vine Stratum (Plot size: ) - Hydrophytic Vegetation Present? Yes C',' No % Bare Ground In Herb Stratum: 0 Remarks: 50% HERB LAYER 15 BARE GROUND AND OPEN WATER, Carex sp. and Spiraea sp. assumed FACW. *Indicator suffix = National status or professional decision asstgne d because Regional status not defined by FWS US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version Soil Sampling Point: 24A Profile Description; (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Depth Matrix Redox Features (inches) Color (moist) 0/0 Color (moist) % Type 1 Loc2 Texture Remarks 0-7 lOYR 3/2 100% Peat 7-20 2Y 3/1 85% I 10YR 4/6 15% C M Sandy Loam TType: C=Concentration. D=Depletion. RM=Reduced Matrix, CS=Covered or Coated Sand Grains zLocation: PL=Pore Lining. M=Matrix ~ Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils:3 Histosol (Al) I I Sandy Redox (S5) 1 1 2 cm Muck (A10) ~N Histic Epipedon (A2) ❑ Stripped Matrix (S6) I_I Red Parent Material (TF2) r Black Histic (A3) ❑ Loamy Mucky Mineral (FS) (except in MLRA 1) ❑ Other (Explain in Remarks) ❑ Hydrogen Sulfide (A4) Loamy Gleyed Matrix (F2) ❑ Depleted Below Dark Surface (All) ❑ Depleted Matrix (F3) I_I Thick Dark Surface (A12) ❑ Redox Dark Surface (F6) 3Indicators of hydrophytic vegetation and ❑ Sandy Muck Mineral (Sl) ❑ Depleted Dark Surface (177) wetland hydrology must be present, ❑ Sandy Gleyed Matrix (S4) Redox depressions (F8) unless disturbed or problematic. Restrictive Layer (If present): Type: Depth (inches): Hydric Soil Present? Yes * No 0 Remarks: Hydrology Wetland Hydrology Indicators: Primary Indicators (minimum of one required; check all that apply) Secondary Indicators (minimum of two required) Surface Water (Al) ❑ Water-Stained Leaves (B9) (except MLRA Water-Stained Leaves (B4) (MLRA 1, 2, High Water Table (A2) 1, 2, 4A, and 4B) 4A, and 4B) Saturation (A3) ❑ Salt Crust (BS 1) Drainage Patterns (Blo) ❑ Water Marks (Bl) ❑ Aquatic Invertebrates (B13) ❑ Dry Season Water Table (C2) ❑ Sediment Deposits (B2) Hydrogen Sulfide Odor (CI) ❑ Saturation Visible on Aerial Imagery (C9) ❑ Drift deposits (B3) Oxidized Rhizospheres on Living Roots (0) ] Geomorphic Position (132) ~ .1 Algal Mat or Crust (84) Presence of Reduced Iron (C4) Shallow Aquitard (D3) Iron Deposits (B5) ❑ Recent Iron Reduction in Tilled Soils (C6) FAC-neutral Test (D5) Surface Soil Cracks (B6) [ Stunted or Stressed Plants (Dl) (LRR A) Raised Ant Mounds (D6) (LRR A) ❑ Inundation Visible on Aerial Imagery (B7) ❑ Other (Explain in Remarks) ❑ Frost Heave Hummocks (D7) Sparsely Vegetated Concave Surface (58) Field Observations: Surface Water Present? Yes No Depth (inches): r Water Table Present? Yes No 0 Depth (inches): 11 Saturation Present? - 0 Wetland Hydrology Present? Yes No • - (includes capillary fringe) Yes No Depth (inches): Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available: Remarks: STANDING WATER ABOUT 4 FT AWAY U5 Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version WETLAND DETERMINATION DATA FORM - Western Mountains, Valleys, and Coast Region Project/Site: DESCHUTES LWI City/County: SUNRIVER/DESCHUTES Sampling Date: 23-Jun-10 , Applicant/Owner: DESN CHUTES SIGLER, COUNTY SARAH HARTUNG Section, Township Range: S 1State: OR Sampling Point: SP 25A Investigator(s): 7 T 215 R 10 E Landform (hillslope, terrace, etc.): valley bottom Local relief (concave, convex, none): Concave Slope: 0.0% / 0.0 ° Subregion (LRR): LRR A Lat.: 43.6733 Long.: -121.5535 Datum: NAD83 Son Map Unit Name: 144A: Sunrlver sandy loam, O,to 3, percent slopes NWI classification: PEMA Are climatic/ hydrologic conditions on the site typical for this time of year? Yes No (If no, explain In Remarks.) Are Vegetation ❑ , Soil ❑ , or Hydrology ❑ significantly disturbed? Are "Normal Circumstances" present? Yes * No ) Are Vegetation I i , Soil I I , or Hydrology l ~ naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transects, important features, et • Hydrophytic Vegetation Present? Yes NO 0 Is the sampled Area Hydric Soil Present? YLS No 0 YeS No Wetland Hydrology Present? Yes (T) No - j within a Wetland? Remarks: On-site determination. VEGETATION - Use scientific names of plants. Dominant Species? Absolute Rel.Strat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: ) % Cover Cover Status Number of Dominant Species 1. Pinus contorta 10 100.0% FAC_ That are OBL, FACW, or FAC: 4 (A) 2. 0 ❑ 0.0% 3 0 0% ❑ 0 Total Number of Dominant . . Species Across All Strata: 5 (B) 4. 0 I 0.0% 10 = Total Cover Percent of dominant Species ° 80.0 (A/B) Sapling/Shrub Stratum (Plot size: ) That Are OBL, FACW, or FAC: 1. 0 1 0.0% Prevalence Index worksheet: 2. 0 [7J 0.0% Total °/a Cover of Multiply by: 3. 0 0.0% OBL species 40 x 1 - 40 4. o r 0.0% FACw species 20 x 2 a 40. 5. 0 ❑ 0.0% FAC species 15 x 3 = 45 0 = Total Cover FACU species .5 x 4 = 20 Herb Stratum (Plot size: ) 10 50 x 5 ~ UPL species 1 Achillea millefollum 5 6.3°h FACU . 2. Trifolium sp. 5 ❑ 6.3% FAC Column Totals : 40 (A) 195 (B) g Carex aquatilis 40 n 50.0% OBL Prevalence Index = B/A = 2.167 ]uncus balticus 4. 10 ❑ 12,5% FACW Hydrophytic Vegetation indicators: 5 Galeopsis tetrahit 10 n 12.5% UPL n Dominance Test is n 50% Stellaria longifolia 10 12.5% FACW L1 Prevalence Index is 53.0t 7 o El a.a°° , L[ Morphological Adaptations 1 (Provide supporting 8 0 0.0% data in Remarks or on a separate sheet) 9. 0 0.0% Wetland Non-Vascular Plantsl 10• o ~-1 0.0% ❑ Problematic Hydrophytlc Vegetatlonl (Explain) 11. o ❑ o.o% 80 =Total Cover 'Indicators of hydric soil and wetland hydrology must W od VI St t (PI t be present, unless disturbed or problematic. . . o y ne ra um o size. ) 1. 0 ❑ 0.0% 2. 0 ❑ 0.0% Hydrophytic Vegetation 0 = Total Cover Present? Yes No C ) % Bare Ground In Herb Stratum: 20 Remarks: Trifolium sp. assumed to be FAC. *Indicator Suffix = National status or professional decision assigned because Regional status not defined by FWS US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version Soil sampling point: SP 25A Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of Indicators.) Matrix Depth Redox Features ) ( ) % (inches) Color mo st color (moist) % Typal Loc1 C Texture Remarks a~ 0-13 o 1 100 Clay Loam 13-20 7 SYR 3/1 80% 10YR 4/1 20% D M Clay Loam 1Type: C=Concentration. D=Depletion. RM=Reduced Matrix, CS=Covered or Coated Sand Grains 21-ocation: PL=Pore Lining. M=Matrix Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric 5oils:3 ❑ Histosol (Al) Sandy Redox (S5) ❑ 2 cm Muck 010) ❑ Histic Epipedon (A2) ❑ Shipped Matrix (S6) ❑ Red Parent Material (72) I_I Black Histic (A3) ❑ Loamy Mucky Mineral (Fl) (except in MLRA 1) n Other (Explain in Remarks) I_I Hydrogen Sulfide (A4) ❑ Loamy Gleyed Matrix (F2) ❑ Depleted Below Dark Surface (All) ❑ Depleted Matrix (F3) ❑ Thick Dark Surface (A12) ❑ Redox Dark Surface (F6) 3Indicators of hydrophytic vegetation and Ll Sandy Muck Mineral (Sl) ❑ Depleted Dark Surface (F7) wetland hydrology must be present, ❑ Sandy Gleyed Matrix (S4) ❑ Redox depressions (F8) unless disturbed or problematic. Restrictive Layer (if present)- Type: Depth (inches): Hydric Soil Present? Yes No Remarks: ASSUMED HYDRIC SOILS BASED ON HYDROLOGY Hydrology wetland Hydrology Indicators: Primary Indicators (minimum of one required; check all that apply) Secondary Indicators (minimum of two required) Surface Water (Al) ❑ Water-stained Leaves (69) (except MLRA ❑ Water-Stained Leaves (B9) (MLRA 1, 2, High Water Table (A2) 1, 2, 4A, and 4B) 4A, and 4B) Saturation (A3) Salt Crust (B11) ❑ Drainage Patterns (B10) ❑ Water Marks (81) ❑ Aquatic Invertebrates (813) ❑ Dry Season Water Table (C2) Sediment Deposits (82) ❑ Hydrogen Sulfide Odor (Cl) 7/1 Saturation Visible on Aerial Imagery (C9) ❑ Drift deposits (B3) 1 Oxidized Rhizospheres on Living Roots (0) Vi Geomorphic Position (132) Algal Mat or Crust (64) 1 Presence of Reduced Iron (C4) ❑ Shallow Aquitard (D3) ❑ Iron Deposits (85) ❑ Recent Iron Reduction in Tilled Soils (C6) ❑ FAC-neutral Test (DS) ❑ Surface Soil Cracks (B6) ❑ Stunted or Stressed Plants (Dl) (LRR A) ❑ Raised Ant Mounds (06) (LRR A) ❑ Inundation Visible on Aerial Imagery (137) 7 Other (Explain in Remarks) ❑ Frost Heave Hummocks (D7) ❑ Sparsely Vegetated Concave Surface (68) Field Observations: Surface Water Present? Yes 0 No Depth (inches): Water Table Present? Yes No ! Depth (inches): Saturation Present? wetland Hydrology Present? Yes 4) No C-) Yes No ! Depth (inches): (includes capillary fringe) Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available: Remarks: SOIL IS SOMEWHAT MOIST US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version 40 WETLAND DETERMINATION DATA FORM - Western Mountains, Valleys, and Coast Region SUNRIVER/DESCHUTES Sampling Date: 23-Jun-10 Project/Site: DESCHUTES LWI City/County: Applicant/ Owner: DESCHUTES COUNTY State: OR Sampling Point: SP 26A Investigator(s): ALISON SIGLER, SARAH FARTUNG Section, Township, Range: 5 17 T.22 S R 10 E Landform (hiilslope, terrace, etc.): Valley bottom Local relief (concave, convex, none): convex Slope: 0.0% / 0.0 Subregion (LRR): LRR A Lat.: 43.6721 Long.: -121.5551 Datum: NAD83 Soil Map Unit Name: 144A: $wn,river.sandy loam, 0 to 3 percent slopes NWI classification: PFQA Are climatic/ hydrologic conditions on the site typical for this time of year? Yes C No (If no, explain in Remarks.) Are Vegetation ❑ , Soil or Hydrology ❑ significantly disturbed? Are "Normal Circumstances" present? Yes * No Are Vegetation _ , Soil ❑ , or Hydrology L naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transects, important features, et C7 Hydrophytic Vegetation Present? Yes NO Is the Sampled Area Hydric Soil Present? Yes No within a Wetland? Yes NO Wetland Hydrology Present? Yes ` No Remarks: On-site determination. VEGETATION - Use scientific names of plants. Dominant Species? Absolute Rel.Strat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: Cover Cover Status Number of Dominant Species 1 0 1 .J 0.0% That are OBL, FACW, or FAC: ..2. (A) n Total Number of Dominant 3. 0 0.0% Species Across All Strata: 2 (B) 4. 0 ❑ 0.0% Percent of dominant Species 0 = Total Cover 100.0% That Are OBL, FACW, or FAC: (A/B) Sapling/Shrub Stratum (Plot size: ) 1, Salix exigua 45 100.0/° OBL Prevalence Index worksheet: 2• 0 0.0°% Total Cover of: Multiply by: 3. 0 0.0% OBL species 45 x 1 - 45 4. 0 ❑ o.0% FACW species 98 x 2 = 196 5. 0 0.0% FAC species U x 3 - 0. 45 = Total Cover FACU species 0 x 4 - 0 Herb Stratum (Plot size: ) 0 0 Carex sp. 1 98 k 100.0°k FACW 0 x 5 - UPL species . 0 ❑ 0 column Totals: 143 (A) 241 (B) 2. 3 0 ❑ 0.0% Prevalence Index = 8/A = 1.685 4. 0 L. J 0.0% Hydrophytlc Vegetation Indicators: 5. 0 1 .1 0.0% U Dominance Test is > 500% 6. 0 ❑ 0.0°h Prevalence index is 53.01 7. 0 r 0.0% ❑ Morphological Adaptations 1(Provide supporting 8 o F l 0.0°% ° data In Remarks or on a separate sheet) 9 0 ° ❑ 0.0 ❑ Wetland Non-Vascular Plantsl 10. 0 ❑ 0.0% ❑ Problematic Hydrophytic Vegetationl (Explain) 11 ° 0 T ° . C lIndicators of hydric soil and wetland hydrology must 98 over ot a be present, unless disturbed or problematic. Woody Vine Stratum (Plot size 1. 0 ❑ 0.0% 2. 0 ❑ 0.0% Hydrophytic Vegetation 0 = Total Cover Present? Yes No % Bare Ground in Herb Stratum: 2 Remarks: Carex sp. assumed to be FACW. *Indicator suffix - National status or professional decision assigned because Regional status not defined by FWS US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version 1 Sampling point: ygA Profile Description: Describe to the depth needed to document the indicator or confirm ( the absence of Indicators.) ~ Depth Matrix Redox Features (inches) Color (moist) % Color (moist) % Type I Loc2 Texture Remarks 0-7 laYR 2/1 100% Clay Loam 7-10 10YR 4/2 90% ° lOYR 2/1 10% C M Silty Clay Mn SOFT MASSES 10-12 2.SY 3/2 100% Sand 12-16 2.5Y 5/3 100% GRAVEL SMALL BREAKS APART WHEN CRUSHED IType: C=Concentration. D=Depletion. RM=Reduced Matrix, CS=Covered or Coated Sand Grains 21-ocation: PL=Pore Lining. M=Matrix Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils:3 Histosol (Al) Sandy Redox (55) 2 cm Muck (Ala) Histic Epipedon (A2) Stripped Matrix (S6) Red Parent Material (TF2) ] Black Histic (A3) Loamy Mucky Mineral (Fl) (except in MLRA 1) ~i Other (Explain in Remarks) Hydrogen Sulfide (A4) Loamy Gleyed Matrix (F2) -I Depleted Below Dark Surface (All) Depleted Matrix (F3) Thick Dark Surface (A12) Redox Dark Surface (F6) Depleted Dark Surface (F7) 3Indicators of hydrophytic vegetation and 1 Sandy Muck Mineral (Sl) J Sandy Gleyed Matrix (S4) ] Redox depressions (F8) wetland hydrology must be present, unless disturbed or problematic, Restrictive Layer (if present): Type: ROCK Depth (inches): 16 Hydric Soil Present? Yes No Remarks: HYDRIC SOILS ASSUMED BASED ON HYDROLOGY. Hydrology . Wetland Hydrology Indicators: Primary Indicators (minimum of one required; check all that apply) Secondary Indicators (minimum of two required) Surface Water (Al) Water-Stained Leaves (B9) (except MLRA Water-Stained Leaves (B9) (MLRA 1, 2, ] High Water Table (A2) 1, 2, 4A, and 4B) 4A, and 4B) Saturation (A3) I Salt Crust (Bl1) F Drainage Patterns (B10) Water Marks (Bl) Aquatic Invertebrates (B13) 1 1 Dry Season Water Table (C2) Sediment Deposits (B2) ] Hydrogen Sulfide Odor (Cl) L . Saturation visible on Aerial Imagery (C9) J Drift deposits (B3) Oxidized Rhizospheres on Living Roots (0) ❑ Geomorphic Position (D2) Algal Mat or Crust (B4) L Presence of Reduced iron (0) Shallow Aquitard (D3) Iron Deposits (B5) Recent Iron Reduction in Tilled Soils (C6) FAC-neutral Test (DS) Surface Soil Cracks (B6) Stunted or Stressed Plants (Dl) (LRR A) Raised Ant Mounds (D6) (LRR A) L. Inundation Visible on Aerial Imagery (B7) Other (Explain in Remarks) Frost Heave Hummocks (137) Sparsely Vegetated Concave Surface (B8) Field Observations: Surface Water Present? Yes No ~0? Depth (inches): Water Table Present? Yes • No Depth (inches): 16 Saturation Present? - Wetland Hydrology Present? Yes No r (includes capillary frinqe) Yes No Depth (inches): 3 Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available: Remarks: US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version WETLAND DETERMINATION DATA FORM - Western Mountains, Valleys, and Coast Region Project/Site: DESCHUTES LWI City/County: SUNRIVER/DESCHUTES Sampling Date: 237Jun-10 A licant/Owner: DESCHUTES COUNTY State: OR Sampling Point: SP 27A ALS50N $IGLER, SARAN HARTUNG Section, Township, Range: S 25 T 22 S R 9 E Investigator(s): Landform (hillslope, terrace, etc.): Floodplain Local relief (concave, convex, none): convex Slope: 0.0% / 0.01 Subregion (LRR): LRR A Lat.: 43.6453 Long.: -121.5919 Datum: NAD83 Soil Map Unit Name: 29q; Crya0u011% Q...kp 3. percent 5Iop05. NWI classification: PSSC Are climatic/ hydrologic conditions on the site typical for this time of year? Yes (i No (If no, explain in Remarks.) Are Vegetation I I , Soil I I , or Hydrology I I significantly disturbed? Are "Normal Circumstances" present? Yes O No (J Are Vegetation ❑ , soil ❑ , or Hydrology ❑ naturally problematic? (If needed, explain any answers In Remarks.) Summary of Findings - Attach site map showing sampling point locations, transects, important features, et Hydrophytic Vegetation Present? Yes Np Is the Sampled Area Hydric Soil Present? Yes NO Yes ) No Wetland Hydrology Present? Yes No within a Wetland? Remarks: Off-site determination. VEGETATION - Use scientific names of plants. Dominant species? Absolute Rel.Strat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: ) a/a Cover Cover Status ' ❑ Number of Dominant Species 1. 0 0.0% That are OBL, FACW, or FAC: 3 (A) 2 0 % . 3 0 ❑ 0 0% Total Number of Dominant 4• 0 . 0.0% ! Species Across All Strata: 3 (B) 0 =Total Cover 1 Percent of dominant Species a 100.0 /o (A/13) Sapling/Shrub Stratum (Plot size: ) That Are OBL, FACW, or FAC: Salix exi g a 1 . 25 .4% 013L U 71 Preva a Index worksheet: p Spi raea 5 2 . 10 ❑ 28.6% total % Cover of: Multiply by: 3. 0 ❑ O.o% o6L species 25 x 1 = 25 4. 0 0.0% FACW species 90 x 2 = 180 5. 0 f. _l 0.0% FAC species 0 . x 3 - U 35 = Total Cover FACU species 0 x 4 - 0 Herb Stratum (Plot size: ) ~ ~ x 5 - UPL Species 1 Phalarisarundinacea 5 6.3% FACW . Carex sp. 2 75 n 93.8% FACW Column Totals: 115 (A) 205 (e) 3. 0 0.0% Prevalence Index = B/A = 1.783 4. 0 ❑ 0.00/0 Hydrophytic Vegetation indicators: 5. 0 0.0% n Dominance Test is n 50% 6. 0 ❑ o.0% y_ Prevalence Index is 53.01 7. 0 0.0% ❑ Morphological Adaptations' (Provide supporting 8. 0 ❑ 0.0% data in Remarks or on a separate sheet) 9. 0 0.0% Wetland Non-Vascular Plants' 10. ❑ 0.0% ❑ Problematic Hydrophytic Vegetation' (Explain) 11. o ❑ o.o% 80 =Total Cover 'Indicators of hydrlc soil and wetland hydrology must be present, unless disturbed or problematic. Woody Vine Stratum (Plot size: ) 1 0 ❑ 0.o% 2, 0 0,0% Hydrophytic 0 = Total Cover Vegetation Present? Yes No - % Bare Ground in Herb Stratum: 20 Remarks: Carex Sp. and Spiraea sp. assumed to be FACW. *Indicator suffix = National status or professional decision assigned beca use Regional status not defined by FWS US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version Soil Sampling point: 27A Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Depth M~trlx Redox Features (inches) Color (mol ) olor (moist) "/o TypeI Loci C Texture Remarks • 0-4 OYR 3/2 1% Silty Sand 4-20 IOYR 3/ 1 80% 7.SYR 3J1 20% C M Sandy Clay Loam 'Type: C=Concentration. D=Depletion. RM=Reduced Matrix, CS=Covered or Coated Sand Grains zLocation: PL=Pore Lining. M=Matrix Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils? Histosol (Ai) Sandy Redox (SS) 2 cm Muck (A10) F1 Histic Epipedon (A2) Stripped Matrix (S6) Red Parent Material (TF2) ❑ Black Histic (A3) Loamy Mucky Mineral (Fl) (except in MLRA 1) Other (Explain in Remarks) 1 Hydrogen Sulfide (A4) ❑ Loamy Gleyed Matrix (F2) ❑ Depleted Below Dark Surface (All) ❑ Depleted Matrix (F3) ❑ Thick Dark Surface (A12) Redox Dark Surface (F6) 3 Indicators of hydrophytic vegetation and ❑ Sandy Muck Mineral (Sl) Depleted Dark Surface (F7) wetland hydrology must be Sandy Gleyed Matrix (S4) ❑ Redox depressions (FB) unless disturbed or problematic. Restrictive Layer (if present): Type: . Depth (inches): Hydric Soil Present? Yes * No Remarks Hydrology Hydrology Indicators; Wetland Primary Indicators (minimum of one required; check all that apply) Secondary Indicators (minimum of two required) ❑ Surface Water (A1) ❑ Water-Stained Leaves (B9) (except MLRA Water-Stained Leaves (89) (MLRA 1, 2, High Water Table (A2) 1, 2, 4A, and 48) 4A, and 4B) V11 Saturation (A3) ❑ Salt Crust (811) ❑ Drainage Patterns (B10) ❑ Water Marks (Bl) ❑ Aquatic Invertebrates (B13) ❑ Dry Season Water Table (C2) Sediment Deposits (B2) Hydrogen Sulfide Odor (Cl) ❑ Saturation visible on Aerial Imagery (C9) ❑ Drift deposits (B3) J Oxidized Rhizospheres on Living Roots (0) Geomorphic Position (D2) ❑ Algal Mat or Crust (B4) ❑ Presence of Reduced iron (0) LJ Shallow Aquitard (133) ❑ Iron Deposits (B5) ❑ Recent Iron Reduction in Tilled Soils (06) ❑ FAC-neutral Test (135) ❑ Surface Soil Cracks (B6) ❑ Stunted or Stressed Plants (D1) (LRR A) ❑ Raised Ant Mounds (D6) (LRR A) Inundation Visible on Aerial Imagery (B7) J Other (Explain in Remarks) Frost Heave Hummocks (137) ❑ Sparsely Vegetated Concave Surface (B8) Field Observations: Surface Water Present? Yes 0 No J) _ Depth (inches): Water Table Present? Yes C) No J) Depth (inches): Yes No ~ Saturation Present? - Yes No - Wetland Hydrology Present? Depth (inches): 0~ (includes capillary fringe) Describe Recopied Data (stream gauge, monitor well, aerial photos, previous inspections), if available: Remarks: US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version WETLAND DETERMINATION DATA FORM - Western Mountains, Valleys, and Coast Region Project/Site: DESCHUTES LWI City/County: SUNRIVER/DESCHUTES Sampling Date: 23-Jun-10 Applicant/ Owner: DESCHUTES COUNTY State: OR Sampling Point: SP 28A Investigator(s): ALISON SIGLER, SARAH HARTUNG Section, Township, Range: 5 24 T 22 S R 9 E Landform (hlllslope, terrace, etc.): Floodplain Local relief (concave, convex, none): concave Slope: 2.0% / 1.1 ° Subregion (LRR): LRR A Lat.: 43.6455 Long.: -121.5918 Datum: NAD83 Soil Map Unit Name: 29A: CrvaQuoils. 0 to 3 perGgnt SloooS NWI classification: PEM..C Are climatic/ hydrologic conditions on the site typical for this time of year? Yes NO (If no, explain in Remarks.) AreVegetation , Soil , or Hydrology ❑ significantly disturbed? Are "Normal Circumstances" present? Yes * No Are Vegetation ❑ , Soil ❑ , or Hydrology ❑ naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transects, important features, et r~ u Hydrophytic Vegetation Present? Yes No Is the Sampled Area Hydric Soil Present? Yes NO J!) within a Wetland? Yes ~ No ~ Wetland Hydrology Present? Yes No Remarks: OFF-SITE DETERMINATION 1 2. VEGETATION - Use scientific names of plants. Dominant Species? Absolute Rel.Strat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: ) % Cover Cover Status 1 Pinus contorta 10 100.0% FAC Number of Dominant Species That are OBL, FACW, or FAC: 4 (A) 2 ❑ 0.0% . 3 0' ' ❑ 0 0% Total Number of Dominant . . Species Across All Strata: 4 (B) 4. 0 1 1 0.0% 10 = Total Cover Percent of dominant Species 100-00/0 (4/13) Sapling/Shrub Stratum (Plot size: ) That Are OBL, FACW, or FAC: 1. Salix exi4ua 75 ~ 100 ,0% OBL Prevalence . Index worksheet: 2. 0 ° [1 o„or° ° Total /q Cover of: Multiply by: 3. o ❑ o.o°i° 08L species 95 x 1 - 95 4. 0 0.0% PACW species 80 x 2 - 160 5. 0 0.0% FAC species 10 x 3 = 30 75 = Total Cover FACU species 0 x 4 0 Herb Stratum (Plot size: ) (1 Phalaris arundinacea 1 80 ~ 80 .0% PACW UPL species X 5 = a uatilis 2. Carex q 20 ] 20.0 % OBL column Totals: 185... (A) 285 (8) 3 0 ❑ 0.0% Prevalence Index = B/A = 1.541 4. 0 ❑ 0.0% Hydrophytic Vegetation Indicators: 5. 0 L 0.o% Dominance Test is n 5001. 6. 0 ❑ 0.0% Prevalence index is 53.0t 7 0 ❑ 0.0°k ❑ Morphological Adaptations I (Provide supporting 8. 0 ❑ D.0% data in Remarks or on a separate sheet) 9, 0 ❑ 0.0% ] Wetland Non-Vascular Plantsl 10. 0 ❑ 0.00% Problematic Hydrophytic Vegetationl (Explain) 11 o ❑ a.a°r°. . 1Indicators of hydric soil and wetland hydrology must 100 =Total Cover be present, unless disturbed or problematic. Woody Vine Stratum (Plot size: ) % Bare Ground in Herb Stratum: 0 Remarks: 0 ❑ 0.0% 0 ❑ 0.0% Hydrophytic Vegetation 0 = Total Cover Present? Yes No *Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS U5 Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version Soil Sampling Point: 28A Profile Description: (Describe to the depth needed to document the Indicator or confirm the absence of indicators.) Depth (inches) Color (moist) Matrix % Color (moist) Redox % tureType t Loc= Texture Remarks i 'Type: C=Concentration. D=Depletion. RM=Reduced Matrix, CS=Covered or Coated Sand Grains zLocation: PL=Pore Lining. M=Matrix Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils-3 Histosol (Al) Sandy Redox (S5) 2 cm Muck (A10) L Histic Epipedon (A2) I Stripped Matrix (S6) [I Red Parent Material (TF2) L~ Black Histic (A3) Loamy Mucky Mineral (F1) (except in MLRA 1) LV' Other (Explain in Remarks) Hydrogen Sulfide (A4) Loamy Gleyed Matrix (F2) Depleted Below Dark Surface (All) Depleted Matrix (F3) Thick Dark Surface (A12) Redox Dark Surface (F6) 3Indicators of hydrophytic vegetation and _I Sandy Muck Mineral (Sl) I Depleted Dark Surface (F7) wetland hydrology must be present, Sandy Gleyed Matrix (S4) Redox depressions (F8) unless disturbed or problematic. Restrictive Layer (if present): Type: Depth (inches). Hydric Soil Present? Yes No i . Remarks: ASSUMED HYDRIC SOILS BASED ON HYDROLOGY Hydrology Wetland Hydrology Indicators: Primary Indicators (minimum of one required; check all that apply) Secondary Indicators (minimum of two required) ,Vi Surface Water (A1) L. Water-Stained Leaves (B9) (except MLRA I J Water-Stained Leaves (B9) (MLRA 1, 2, ] High Water Table (A2) 1, 2, 4A, and 4B) 4A, and 4B) Saturation (A3) ] Salt Crust (811) Drainage Patterns (810) Water Marks (BI) r Aquatic Invertebrates (813) Dry Season Water Table (C2) Sediment Deposits (B2) Hydrogen Sulfide Odor (Cl) Saturation visible on Aerial Imagery (C9) Drift deposits (B3) Oxidized Rhizospheres on Living Roots (0) Geomorphic Position (D2) [ Algal Mat or Crust (B4) Presence of Reduced Iron (C4) Shallow Aquitard (D3) Iron Deposits (B5) Recent Iron Reduction in Tilled Solis (C6) L FAC-neutral Test (D5) Surface Soil Cracks (B6) Stunted or Stressed Plants (DI) (LRR A) Raised Ant Mounds (D6) (LRR A) Inundation Visible on Aerial Imagery (137) I Other (Explain in Remarks) Frost Heave Hummocks (D7) Sparsely vegetated Concave Surface (88) Field Observations: Surface Water Present? Yes No Depth (inches): 2 lip, Water Table Present? Yes No Depth (inches): Saturation Present? wetland Hydrology Present? Yes No (includes capillary fringe) Yes No Depth (inches): D Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available: Remarks; Assumed there was 2 inches of surface water at sample plot based on close visual field observations of wetland. 1~i US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version 0 WETLAND DETERMINATION DATA FORM - Western Mountains, Valleys, and Coast Region City/County: SUNRIVER/DESCHUTES Sampling Date: 24-Jun-10 Project/Site: Applicant/ Owner: DESCHUTES COUNTY State: OR Sampling Point: 5 . Investigator(s): ALISON SIGLER, SARAH HARTUNG Section, Township, Range: S 24 T 22 S R 9 E P 29A Landform (hillslope, terrace, etc.): Floodplain Local relief (concave, convex, none): Concave Slope: 1.0% / 0.6 ° D83 Subregion (LRR): LRR A Lat.: 43.6455 Long.: -121.5918 Datum: NA Soil Map Unit Name: 29A; rrYaQuolls, 0 t0 3 Percent slopes. NWI classification: PEMC Are climatic/ hydrologic conditions on the site typical for this time of year? Yes No 3 (If no, explain in Remarks.) Are Vegetation , Soil L.. , or Hydrology significantly disturbed? Are "Normal Circumstances" present? Yes No C) Are Vegetation , Soil , or Hydrology naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transects, important features, et Hydrophytic Vegetation Present? Yes No Is the Sampled Area Hydric Soil Present? Yes No within a Wetland? YES (No C Wetland Hydrology Present? Yes No Remarks: On-site determination. VEGETATION - Use scientific names of plants. Dominant Species? Absolute Rel.Strat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: ► "/o Cover Cover Status Number of Dominant Species 1, Pinus contorts 2 IVI 100.0% FAC That are OBL, FACW, or FAC: 5 (A) 2, 2. 0 0.0% 0 ❑ 0 0% Total Number of Dominant . Species Across All Strata: 5 (13) 4. 0 0.0% 2 = Total Cover Percent of dominant Species ° 100.0% (A/B) Sapling/Shrub Stratum (Plot size: ) That Are OSL, FACW, or FAC: 1. Salix exigua 5 k 1100.0% 013E Prevalence Index worksheet: 2. 0 ❑ 0.0% Total % Cover of Multiply by: 3. 0 l..J 0.0% oBL species 35 x 1 - 35 4. 0 0.0% FACW species 70 x 2 . 140 5. 0 0.0% FAC species 2 x 3 6 5 = Total Cover FACU species 0 x 4 0 Herb Stratum (Plot size: ) 0 0 Ph l i di 0 FA U UPL species x 5 = a ar s arun nacea 1. 5 50.0% CW 2. Myosotis laxa 5 L 5.0°h 0131 column totals: 107 (A) 181 (s) 3 Alopecurus pratensis 20 n 20.0% FACW Prevalence Index = B/A = 1.692 Carex aquatilis 4. 25 n 25.0% 013E Hydrophytic Vegetation indicators: 5 0 U 0.0% n Dominance Test is 7 50% 6. 0 I_I 0.0% 41 prevalence index is 53.01 7 0 IL 0.o% [J Morphological Adaptations I (Provide supporting g 0 L 0.o% data in Remarks or on a separate sheet) 9, 0 r... 0,0°k Wetland Non-Vascular Plantss 10, L Problematic Hydrophytic Vegetations (Explain) 11. 0 17 0.0% 100 = Total Cover 'indicators of hydric soil and wetland hydrology must be present, unless disturbed or problematic. Woody Vine Stratum (Plot size: ) - - 1. 0 0.0% 2. 0 ❑ 0.0% Hydrophytit 0 = Total Cover Vegetation Yes No % Bare Ground in Herb Stratum: 0 Remarks: *Indicator suffix = National status or professional decision assigned beca use Regional status not de fined by FWS US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version Soil Sampling Point: 29A Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Depth Matrix edox Features R ) Color (moist) ( Color (moist) % Type 1 Loc2 Texture Remarks 0-e 3/l 90 a . 3/4 10% C PL Loam 10-20 10YR 4/1 75°k lOYR 3/6 25% C M Silt Loam w/ 20% fine sand tType: C=Concentration. D=Depletion. RM=Reduced Matrix, CS=Covered or Coated Sand Grains =Location: PL=Pare Lining. M=Matrix Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils-3 Histosol (Al) Sandy Redox (S5) n 2 cm Muck (A10) Histic Epipedon (A2) Stripped Matrix (S6) Red Parent Material (TF2) n Black Histic (A3) Loamy Mucky Mineral (Fl) (except in MLRA 1) L-i Other (Explain in Remarks) n Hydrogen Sulfide (A4) L Loamy Gleyed Matrix (F2) U Depleted Below Dark Surface (All) L Depleted Matrix (F3) Thick Dark Surface (A12) L Redox Dark Surface (F6) 3Indicators of hydrophytic vegetation and U Sandy Muck Mineral (51) L Depleted Dark Surface (F7) wetland hydrology must be present, LJ Sandy Gleyed Matrix (S4) n Redox depressions (FB) unless disturbed or problematic. Restrictive Layer (if present): Type: Depth (inches): Hydric Soil Present? Yes ! Nor) Remarks: - - profile at 10-20 inches has concentrations in the pore linings too. Hydrology Wetland Hydrology Indicators: Primary Indicators (minimum of one required; check all that apply) Secondary Indicators (minimum of two required) i. surf ace Water (Al) L Water-Stained Leaves (59) (except MLRA L Water-Stained Leaves (B9) (MLRA 1, 2, High Water Table (A2) 1, 2, 4A, and 4B) 4A, and 4B) Saturation (A3) n Salt Crust (Bll) ❑ Drainage Patterns (B10) Water Marks (Bl) Aquatic Invertebrates (B13) F-1 Dry Season Water Table (C2) Sediment Deposits (B2) Hydrogen Sulfide Odor (Cl) Saturation Visible on Aerial Imagery (C9) Drift deposits (B3) Oxidized Rhizospheres on Living Roots (0) Geomorphic Position (132) n Algal Mat or Crust (84) Presence of Reduced Iron (C4) Shallow Aquitard (133) Iron Deposits (B5) Recent Iron Reduction in Tilled Soils (C6) J FAC-neutral Test (D5) L.J Surface Soil Cracks (B6) Stunted or Stressed Plants (Dl) (LRR A) L Raised Ant Mounds (D6) (LRR A) L Inundation Visible on Aerial Imagery (B7) Other (Explain in Remarks) Ll Frost Heave Hummocks (D7) Sparsely Vegetated Concave Surface (B8) Field Observations: Surface Water Present? Yes No • Depth (inches): Water Table Present? Yes C) No J) Depth (inches): Saturation Present? 10 Wetland Hydrology Present? C No Depth (inches): ~ includes capillary fringe) Yes - - Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available: Remarks: Yes i•'> No r~ US Army Corps of Engineers Western Mountains, valleys, and Coast Region Interim version WETLAND DETERMINATION DATA FORM - Western Mountains, Valleys, and Coast Region Project/Site: DESCHUTES LWI City/County: SUNRIVER/DESCHUTES Sampling Date: 24-Jun-10 Applicant/ Owner: DE H T COUNTY State: OR Sampling I vestigator(s): ALISON SIGLER, SARAH HARTUNG Section, Township, Range: S 18 T 22 5 ?ling Point: SP 30A R 10 E Landform (hillslope, terrace, etc.): Swale Local relief (concave, convex, none): flat Slope: 0.0% / 0.0 ° Subregion (LRR): LRR A Lat.: 43.6688 Long.: -121.5714 Datum: NAD83 Soil Map Unit Name: 1.140: Shanahan loamy coarse .°.eand, Q tQ 1..5 perrmnt sigDes. NWI classification: Are climatic/ hydrologic conditions on the site typical for this time of year? Yes No ( (If no, explain in Remarks.) Are Vegetation ❑ , Soil ❑ , or Hydrology ❑ significantly disturbed? Are "Normal Circumstances" present? Yes No - Are Vegetation I Soil I I , or Hydrology naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transacts, important features, et Sapling/Shrub Stratum (Plot size 1. 2. 3. 4. 5. Herb Stratum (Plot size: 1. Phalaris arundinacea 2. Poa sp. 3 ]uncus balticus 4. 5. 6. 7 Dominant Species? Absolute Rel.Strat. Indicator Dominance Test worksheet: o Cover a ova status l ° Number of Dominant Species loo.Dr% AC That are OBL, FACW, or FAC: 4 (A) o I l 0.0% , Total Number of Dominant 0 ❑ 0.0% Species Across All Strata: 4 (B) 0 0.0% 5 = Total Cover Percent of dominant Species 100.0°/% (A/B) That Are OBL, FACW, or FAC: 0 ❑ 0.0%/0 Prevalence index w worksheet: 0 % ❑ 0.0 r% , Total % Cover of: Multiply by; 0 L 1 0.00r% oBL species 0 x 1- 0 . 0 i 0.0°/% x 2 _ 160 FACW species 80 0 ❑ 0.0% FAC species 25 x 3 - 75 = Total Cover 0 0 FACU species x 4 - 60 0% FACW U 60 UPL species 0 x 5= 0 20 . 20.0% FAC column Totals: 105 (A) 235 (B) 20 11/1 20.0°/% FACW Prevalence Index = B/A = 2.238 0 ❑ 0.0°h Hydrophytic Vegetation Indicators: 0 ❑ 0.0% 7 Dominance Test is n 50% 0 ❑ 0.0% !VI Prevalence index is 53.01 a L__1 o.o%r° ❑ Morphological Adaptations I (Provide supporting 0 ❑ 0.0°r% data in Remarks or on a separate sheet) 0 ❑ 0.0% Wetland Non-Vascular Plantsl 0 0.0% Problematic Hydrophytic Vegetationl (Explain) 0 0.0°k (Indicators of hydric soil and wetland hydrology must 100 = Total Cover be present, unless disturbed or problematic. 0 ❑ 0.0% 0 0.00% Hydrophytic Vegetation - 0 = Total Cover Present? Yes J) No ) CI Hydrophytic Vegetation Present? Yes No Is the Sampled Area Hydrlc Soil Present? Yes No - - Wetland Hydrology Present? Yes No 0 within a Wetland? Yes No ) Remarks: Off-site sample plot VEGETATION - Use scientific names of plants Tree Stratum (Plot size: ) 1. Pinus contorts 2. 3. 4. % Bare Ground in Herb Stratum: 0 Remarks: Poa sp. assumed FAC. *Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version Soil Sampling Point: 30A Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Depth Matrix Redox Features (inches) Color (moist) % Color (moist) % Type I LOC2 Texture Remarks 1Type: C=Concentration. D=Depletion, RM=Reduced Matrix, CS=Covered or Coated Sand Grains zLoca tion: PL=Pore Lining. M=Matrix Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils:3 ❑ Histosol (Al) ❑ Sandy Redox (S5) 2 cm Muck (A10) Histic Epipedon (A2) ❑ Stripped Matrix (S6) Red Parent Material (TF2) Black Histic (A3) ❑ Loamy Mucky Mineral (Fl) (except in MLRA 1) F] Other (Explain in Remarks) ❑ Hydrogen Sulfide (A4) ❑ Loamy Gleyed Matrix (F2) ❑ Depleted Below Dark Surface (All) ❑ Depleted Matrix (F3) ❑ Thick Dark Surface (A12) [ Redox Dark Surface (F6) 3Indicators of hydrophytic vegetation and * Sandy Muck Mineral (S1) Depleted Dark Surface (F7) wetland hydrology must be present, ❑ Sandy Gleyed Matrix (S4) ❑ Redox depressions (F8) unless disturbed or problematic. Restrictive Layer (if present): Type: Depth (inches): Hydric Soil Present? Yes No L Remarks: ASSUMED HYDRIC BASED ON HYDROLOGY I Hydrology Wetland Hydrology Indicators: Primary Indicators (minimum of one required; check all that apply) Secondary Indicators (minimum of two required) ❑ Surface Water (Al) ❑ Water stained Leaves (B9) (except MLRA 7 Water Stained Leaves (B9) (MLRA 1, 2, ❑ High Water Table (A2) 1, 2, 4A, and 4B) 4A, and 4B) Saturation (A3) Salt Crust (Bl1) ❑ Drainage Patterns (B10) Water Marks (Bl) ❑ Aquatic Invertebrates (B13) ❑ Dry Season Water Table (C2) ❑ Sediment Deposits (82) ❑ Hydrogen Sulfide Odor (Cl) V1 Saturation Visible on Aerial Imagery (Cg) J Drift deposits (B3) 1. 1 Oxidized Rhizospheres on Living Roots (0) Geomorphic Position (D2) Algal Mat or Crust (84) 1 1 Presence of Reduced Iron (C4) L] Shallow Aquitard (D3) Iron Deposits (B5) ❑ Recent Iron Reduction in Tilled Soils (C6) L] FAC-neutral Test (D5) ] Surface Soil Cracks (B6) I I Stunted or Stressed Plants (Dl) (LRR A) ❑ Raised Ant Mounds (D6) (LRR A) L] Inundation Visible on Aerial Imagery (B7) i 1 Other (Explain in Remarks) Frost Heave Hummocks (D7) [ Sparsely Vegetated Concave Surface (B8) Field Observations: Surface Water Present? Yes No Depth (inches): Water Table Present? Yes No Depth (inches): Y N 0 Saturation Present? Yes No es o Wetland Hydrology Present? Depth (inches (includes capillary fringe) _ - Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available: Remarks: ASSUME SATURATION BASED ON ROBUST AND VIBRANT GREEN GRASS C~ • US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version WETLAND DETERMINATION DATA FORM - Western Mountains, Valleys, and Coast Region Project/Site: DESCHUTES LWI City/County: SUNRIVER/DESCHUTES Sampling Date:, 24-Jun-10 Applicant/Owner: DE HUTE COUNTY State: OR Sampling Point: SP 31A Investigator(s): ALISON SIGLER, SARAH HARTUNG Section, Township, Range: S 10 T 21 S R 10 E Landform (hillslope, terrace, etc.): Floodplain Local relief (concave, convex, none): flat Slope: 0.0% / 0.01 Subregion (LRR): LRR A Lat.: 43.7703 Long.: -121.5249 Datum: NAD83 Soll Map Unit Name: 144A: $unriver sandy loam, p to 3 PerCQnt slopes. NWI classification: PEMC. Are climatic/ hydrologic conditions on the site typical for this time of year? Yes (No (If no, explain in Remarks.) Are Vegetation ] , Soil ❑ , or Hydrology El significantly disturbed? Are "Normal Circumstances" present? Yes No Are Vegetation L , soil it I , or Hydrology F1 naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transects, important features, et • • Hydrophytic Vegetation Present? Yes ` No Is the Sampled Area Hydric Soil Present? Yes ! No within aWetland? Yes NO 0 Wetland Hydrology Present? Yes J') No Remarks: On-site, located in state park, no digging allowed without a state cultural resource permit VEGETATION - Use scientific names of plants. Dominant Species? Absolute Rel.Strat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: ) a/o Cover Cover Status Number of Dominant Species 1. 0 1 1 0.0% That are OBL, FACK or FAC: 2. 0 n 0.0% 3 D ❑ 0 0% Total Number of Dominant , . Species Across All Strata: 4. 0 L o.o% 0 = Total Cover Percent of dominant Species Sapling/Shrub Stratum (Plot size: ) That Are OBL, FACW, or FAC: 1. Salix exigua 40 ~J 100.0% OBL Prevalence index worksheet: 2. 0 . LJ 0.0% Total % Cover of: Multiply by 3. 0 LJ 0.0% oBL species 40 x 1 = 40 4. 0 LL 0.0°h FACW species 100 x 2 - 200 5. 0 1 .I 0.0% FAC species 0 x 3- 0 40 = Total Cover FACD 0 4 0 Herb Stratum (Plot size: ) 1. Carex sp. 2. Veratrum californicum 3. 4. 5. 6. 7. R Bare Ground in Herb Stratum: 0 Remarks: Carex sp. assumed to be FACW. 80 80.0% FACW 20 n 20.0% FACW 0.0% 0 1 0.0% 0 ~i 0.0% 0 L...J 0.0% 0 n 0.0% o L J 0.0% 0 0.0% 0 0.0% .0 LJ 0.0% 100 = Total Cover 0 LL o.o% 0 I 0.0% 0 = Total Cover 3 (A) 3 (B) 100.0% (A/8) species x - UK species U x 5 0........... Column Totals: 140 (A) 240 (B) Prevalence Index = B/A = 1.714 . Hydrophytic Vegetation Indicators: ❑ Dominance Test is n 50% Prevalence index is 53.01 L Morphological Adaptations I (Provide supporting data in Remarks or on a separate sheet) Wetland Non-Vascular Plantsl L Problematic Hydrophytic Vegetationl (Explain) (Indicators of hydric soil and wetland hydrology must be present, unless disturbed or problematic. Hydrophytic Vegetation Present? Yes * No C_1 *Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version soil Sampling Point: 31A Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of Indicators.) Depth Matrix Redox Features (inches) Color (moist) % Color (moist) "/o Type 1 Loc' Texture Remarks 1Type: C=Concentration. D=Depletion. RM=Reduced Matrix, CS-Covered or Coated Sand Grains 2Loca tion: PL=Pore Lining. M=Matrix Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Solls 3 J Histosol (Al) ❑ Sandy Redox (SS) I 1 2 cm Muck (A10) ❑ Histic Epipedon (A2) Stripped Matrix (S6) ❑ Red Parent Material (TF2) Black Histic (A3) Loamy Mucky Mineral (Fl) (except in MLRA 1) d Other (Explain in Remarks) ❑ Hydrogen Sulfide (A4) ❑ Loamy Gleyed Matrix (F2) ❑ Depleted Below Dark Surface (All) ❑ Depleted Matrix (F3) ❑ Thick Dark Surface (A12) ❑ Redox Dark Surface (F6) 3Indicators of hydrophytic vegetation and ❑ Sandy Muck Mineral (Sl) ❑ Depleted Dark Surface (F7) wetland hydrology must be present, ❑ Sandy Gleyed Matrix (S4) ❑ Redox depressions (FB) unless disturbed or problematic. J Restrictive Layer (If present): Type: Depth (inches): Hydric Soil Present? Yes C4) No - Remarks: ASSUMED HYDRIC HYDRICS BASED ON HY DROLOGY Hydrology Wetland Hydrology Indicators: Primary Indicators (minimum of one required; check all that apply) Secondary Indicators (minimum of two required) VI Surface Water (Al) ❑ Water-Stained Leaves'(B9) (except MLRA Water-Stained Leaves (B9) (MLRA 1, 2, High Water Table (A2) 1, 2, 4A, and 4B) 4A, and 48) Saturation (A3) E] Salt crust (Bll) ❑ Drainage Patterns (B10) ❑ Water Marks (Bl) Aquatic Invertebrates (B13) F Dry season water Table (C2) Sediment Deposits (62) ❑ Hydrogen Sulfide Odor (CI) L I Saturation Visible on Aerial Imagery (C9) Drift deposits (83) ❑ Oxidized Rhizospheres on Living Roots (0) J Geomorphic Position (D2) II Algal Mat or Crust (84) Presence of Reduced Iron (C4) ❑ Shallow Aquitard (D3) Iron Deposits (B5) ] Recent Iron Reduction in Tilled Soils (C6) ❑ FAC-neutral Test (D5) F_ ~ Surface Soil Cracks (B6) Stunted or Stressed Plants (Dl) (LRR A) I I Raised Ant Mounds (D6) (LRR A) Inundation Visible on Aerial Imagery (87) Other (Explain in Remarks) 11 Frost Heave Hummocks (D7) Sparsely Vegetated Concave Surface (BB) Field Observations: Surface Water Present? Yes * No C.) Depth (inches): 1 Water Table Present? Yes 0 No Depth (Inches): Saturation Present? - Wetland Hydrology Present? Yes No (includes capillary fringe) Yes No Depth (inches): Lo Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available: Remarks: • is US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version 0 WETLAND DETERMINATION DATA FORM - Western Mountains, Valleys, and Coast Region Project/site: DESCHUTES LWI City/County: SUNRIVER/DESCHUTES Sampling Date: 24-Jun-10 „ Applicant/Owner: DES Investigator(s): ALISON H State: OR Sampling Point: SP 32A IGLER, SARAN HARTUNG Section Township, Range: S 10 T 21S R 10E Landform (hillslope, terrace, etc.): Floodplain Local relief (concave, convex, none): flat Slope: 0.0% / 0.0 ° Subregion (LRR): LRR A Lat.: 43.7703 Long.: -121.5248 Datum: NAD83 Soil Map Unit Name: 29A: CrydgUQllg, 0 to 3 Percent .51.gpes NWI classification: P$SC Are climatic/ hydrologic conditions on the site typical for this time of year? Yes * NO (If no, explain in Remarks.) Are Vegetation I.....I , soil ❑ , or Hydrology ❑ significantly disturbed? Are "Normal Circumstances" present? Yes 4) No C) Are Vegetation ❑ , Soil ❑ , or Hydrology ❑ naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transects, important features, et Hydrophytic Vegetation Present? Yes * No Hydric Soil Present? Yes NO Wetland Hydrology Present? Yes No Remarks: OFF-SITE DETERMINATION Is the Sampled Area within a Wetland? Yes * No C j VEGETATION - Use scientific names of plants. Dominant Species? Absolute Rel.Strat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: ) % Cover Cover Status . Number of Dominant Species 1. Pinus contorta 5 n 100.0% FAC That are 08L, FACW, or FAC: 4 (A) 2. o ❑ o.o% 3 0 ~ ~ 0 0% Total Number of Dominant , . . Species Across All Strata: 4 (B) 4. 0 0.0% 5 = Total Cover Percent of dominant Species o 100.0% (A/B) Sapling/Shrub Stratum (Plot size: ) That Are OBL, FACW, or FAC: 1, Salix exigua 10 100.0% 08L Prevalence Index worksheet: 2. 0 ❑ 0.o% Total % Cover of: Multiply by: 3. 0 ❑ 0.0%0 08L species 10 x 1 = 10 4. 0 0.0% FACw species 100 x Z = 200 5. o ❑ 0.0% FAC species S x 3 = 15 10 = Total Cover FACU species 0 x 4 - 0 Herb Stratum (Plot size: ) 0 0 ' C so U 80 0% FACW uPL species x 5 - ( arex sp. . 2, ]uncus balticus 20 ~ 20.0% FACW (B] column Totals: 115 (A) 225 3. 0 ❑ 0.0% Prevalence Index = B/A = 1.957 4, 0 ❑ 0,0% Mydrophytic Vegetation indicators: 5. 0 LJ 0.o% n Dominance Test is a 50% 6. 0 ❑ 0.0%o IV] Prevalence Index is 53.01 7 0 ❑ 0.0% Morphological Adaptations' (Provide supporting 0 ❑ 0.0% data in Remarks or on a separate sheet) 9. 0 0.0% ❑ i Wetland Non-Vascular Plantsl 10. 0 ~ 17 0.0° Problematic Hydrophytic Vegetation' (Explain) 11. 0 I LJ 0.0% lindicators of hydric soil and wetland hydrology must 100 = Total Cover be present, unless disturbed or problematic. Woody Vine Stratum (Plot size: ) 1. 0 ❑ 0.0% 2. 0 ❑ o.0% Hydrophytic 0 =Total Cover Vegetation Yes No Present? % Bare Ground in Herb Stratum: 0 Remarks: Carex sp. assumed to be FACW. *Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version Soil Sampling Point: 32A Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Matrix Features Redox ost) % (inches) Color ( Color (moist) Type Loc2 % Texture Remarks 'Type: C=Concentration. D=Depletion. RM=Reduced Matrix, CS=Covered or Coated Sand Grains xLoca n: PL=Pore Lining. M=Matrix tio Hydrlc Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils:3 ❑ Histosol (Al) ❑ Sandy Redox (S5) 2 cm Muck (A10) ❑ Histic Epipedon (A2) Stripped Matrix (S6) Red Parent Material (TF2) ❑ Black Histic (A3) Loamy Mucky Mineral (Fl) (except in MLRA 1) ~I Other (Explain in Remarks) L Hydrogen Sulfide (A4) Loamy Gleyed Matrix (F2) ❑ Depleted Below Dark Surface (Ail) ❑ Depleted Matrix (F3) El Thick Dark Surface (A12) Redox Dark Surface (F6) 3Indicators of hydrophytic vegetation and Sandy Muck Mineral (Sl) ❑ Depleted Dark Surface (F7) wetland hydrology must be present, ❑ Sandy Gleyed Matrix (S4) Redox depressions (F8) unless disturbed or problematic. Restrictive Layer (If present): Type: Depth (inches): Hydric Soil Present? Yes No Remarks: ASSUMED HYDRIC SOILS BASED ON HYDROLOGY Hydrology Wetland Hydrology Indicators: Primary Indicators (minimum of one required; check all that apply) Secondary Indicators (minimum of two required) ❑ Surface Water (A1) Water-Stained Leaves (139) (except MLRA ❑ Water-Stained Leaves (B9) (MLRA 1, 2, ❑ High Water Table (A2) 1, 2, 4A, and 4B) 4A, and 4B) ❑ Saturation (A3) ❑ Salt Crust (BI 1) ❑ Drainage Patterns (B10) Water Marks (BI) ❑ Aquatic Invertebrates (B13) ❑ Dry Season Water Table (C2) ❑ Sediment Deposits (132) ❑ Hydrogen Sulfide Odor (Cl) Saturation Visible on Aerial Imagery (C9) Drift deposits (133) Oxidized Rhizospheres on Living Roots (0) 1%4 Geomorphic Position (D2) ❑ Algal Mat or Crust (64) Presence of Reduced Iron (C4) Shallow Aquitard (133) Iron Deposits (BS) ❑ Recent Iron Reduction in Tilled Soils (C6) ❑ FAC-neutral Test (135) Surface Soil Cracks (B6) Stunted or Stressed Plants (Dl) (LRR A) ❑ Raised Ant Mounds (136) (LRR A) ❑ Inundation Visible on Aerial Imagery (87) ❑ Other (Explain in Remarks) ❑ Frost Heave Hummocks (137) Sparsely Vegetated Concave Surface (B8) Field Observations: Surface Water Present? Yes > No Depth (inches): Water Table Present? Yes No Depth (inches): r Yes No 0 Saturation Present. Present? ! Yes No Wetland Hydrology Present? Depth (inches): ...(includes capillary fringe) Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available: Remarks: US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version WETLAND DETERMINATION DATA FORM - Western Mountains, Valleys, and Coast Region Project/Site: DESCHUTES LWI City/County: SUNRIVER/DESCHUTES Sampling Date: 24-Jun-10 Investigator(s): ALDH GLER, OARAN HARTUNG Section, Township, Range: State: OR Sampling Point: SP 33A ISON I • S 10 T21S R10E Landform (hillslope, terrace, etc.): Floodplain Local relief (concave, convex, none): flat Slope: 0.0% / 0.0 ° Subregion (LRR): LRR A Lat.. 43.7723 Long.: -121.5183 Datum: NAD83 Soil Map Unit Name: 144A: SUnriver sandy Ioam..0.to 3 percent Slopes NWI classification: P$5c Are climatic/ hydrologic conditions on the site typical for this time of year? Yes No (If no, explain In Remarks.) Are Vegetation ! ' , Soil 1 I , or Hydrology significantly disturbed? Are "Normal Circumstances" present? Yes ' No - Are Vegetation , Soil I I , or Hydrology naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transects, important features, et • • Hydrophytic Vegetation Present? Yes No Is the Sampled Area Hydnc Soil Present? Yes NO 7 within a Wetland? Yes No Wetland Hydrology Present? Yes No Remarks- Off-site determination. No digging allowed without a state cultural resource permit. 1. 0 0.0% 2. 0 0.0% 0 = Total Cover Bare Ground in Herb Stratum: 0 Remarks: VEGETATION - Use scientific names of plants. Dominant Species? Absolute Rel.Strat. Indicator Tree Stratum (Plot size: ► % Cover Cover Status 1. Pinus contorta 5 1/1 100.0% FAC 2. 0 0.0% 3. o 010% 4. 0 0.0% 5 = Total Cover Sapling/Shrub Stratum (Plot size: ) 1. Salix exigua 60 IV 100.0% OOL 2. 0 r 0.0% 3. 0 0.0% 4. 0 0.0% 5. 0 0.00 60 = Total Cover Herb Stratum (Plot size: ) 1. Carex aquatilis 70 I1/I 70.0% OBL 2. ]uncus balticus 30 l-1 30.0% FACW 3. 0 1 10.0% 4. 0 h 0.0% 5. 0 0.0% 6. 0 0.0% 7 0 L o.o% 8 0 LJ 0.0% 9. 0 F 1 0.0% 10. 0 J o.0% 11. 0 L 0.0% 100 = Total Cover Woody Vine Stratum (Plot size: ) Dominance Test worksheet: Number of Dominant Species That are OBL, FACW, or FAC: 4 (A) Total Number of Dominant Species Across All Strata: 4 (B) Percent of dominant Species That Are OBL, FACW, or FAC: 100.0% (A/B) Prevalence Index worksheet: Total % Cover of: Multiply by: OBL species 130 x 1 = 130 FACW species 30 x 2 = 60 FAC species 5 x 3 = 15 FACU species 0 x 4 = 0 UPL species 0 x 5 = 0 column Totals: 165 (A) 205 (13) Prevalence Index = B/A = 1.242 . Hydrophytic Vegetation Indicators: Dominance Test is > 50% ~I Prevalence Index is 53.01 Morphological Adaptations 1(Provide supporting data In Remarks or on a separate sheet) Wetland Non-Vascular Plants' Problematic Hydrophytic Vegetation' (Explain) 'Indicators of hydric soil and wetland hydrology must be present, unless disturbed or problematic. Hydrophytic Vegetation Present? Yes i• No *Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version Soil Sampling Point: 33A Profile Description: (Describe to the depth needed to document the Indicator or confirm the absence of Indicators.) Depth Matrix Redox Features (inches) Color (moist) % Color (moist) % Type 1 Loc2 Texture Remarks Type: C=Concentration. D=Depletion. RM=Reduced Matrix, CS=Covered or Coated Sand Grains =Location: PL=Pore t Lining. M=Matrix Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils:3 ❑ Histosol (Al) ❑ Sandy Redox (55) ❑ 2 cm Muck (A10) ❑ Histic Epipedon (A2) ` ] Stripped Matrix (S6) ❑ Red Parent Material (TF2) L Black Histic (A3) ❑ Loamy Mucky Mineral (Fl) (except in MLRA 1) [I Other (Explain in Remarks) ❑ Hydrogen Sulfide (A4) ❑ Loamy Gleyed Matrix (F2) ❑ Depleted Below Dark Surface (All) ❑ Depleted Matrix (F3) ❑ Thick Dark Surface (A12) Redox Dark Surface (F6) 3 Indicators of hydrophytic vegetation and ❑ Sandy Muck Mineral (SS) Depleted Dark Surface (F7) wetland hydrology msent, Sandy Gleyed Matrix (S4) ❑ Redox depressions (FS) unless disturbed or problematic. Restrictive Layer (if present): Type: Depth (Inches): Hydric Soil Present? Yes No U Remarks: ,ASSUMED HYDRIC SOILS BASED ON HYDROLOGY Hydrology Wetland Hydrology Indicators: Primary Indicators (minimum of one required; check all that apply) ❑ Surface Water (Al) ❑ Water-stained Leaves (139) (except MLRA ❑ High Water Table (A2) 1, 2, 4A, and 413) n Saturation (A3) Salt Crust (1311) Water Marks (Bl) ❑ Aquatic Invertebrates (813) ❑ Sediment Deposits (132) ❑ Hydrogen Sulfide Odor (Cl) Drift deposits (133) ❑ Oxidized Rhizospheres on Living Roots (0) F I Algal Mat or Crust (84) Presence of Reduced Iron (C4) Iron Deposits (135) ❑ Recent Iron Reduction in Tilled Soils (C6) Surface Soil Cracks (156) ] Stunted or Stressed Plants (Dl) (LRR A) Inundation Visible on Aerial Imagery (137) ❑ Other (Explain in Remarks) ❑ Sparsely Vegetated Concave Surface (138) Secondary Indicators (minimum of two required) Water-Stained Leaves (89) (MLRA 1, 2, 4A, and 48) ❑ Drainage Patterns (1310) ❑ Dry Season Water Table (C2) Saturation Visible on Aerial Imagery (C9) ❑ Geomorphic Position (D2) Shallow Aquitard (D3) FAC-neutral Test (DS) Raised Ant Mounds (136) (LRR A) Frost Heave Hummocks (137) Field Observations: Surface Water Present? Yes No i•'> Depth (inches): J Water Table Present? Yes No Depth (inches): Saturation Present? Yes - No - Wetland Hydrology Present? Depth (inches): J L 0 (includes capillary fringe) - Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available: Remarks: Yes J') No • US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version WETLAND DETERMINATION DATA FORM - Western Mountains, Valleys, and Coast Region Project/Site:,DESCHUTES LWI City/County: SUNRIVER/DESCHUTES Sampling Date: 24-Jun-10 Applicant/Owner:H State: OR Sampling Point: 5P 35A Investigator(s): ALISON IGLER, SARAH HARTUNG Section, Township, Range: S 0 T215 810E Landform (hillslope, terrace, etc.): Floodplain Local relief (concave, convex, none): flat Slope: 0.0% / 0.01 Subregion (LRR): LRR A Lat.: 43.7732 Long.: -121.5246 Datum: NAD83 Soil Map Unit Name: 144A: Sunriyer sandy ipam,..Q.to 3 percent slopes NWI classification: R2UBH Are climatic/ hydrologic conditions on the site typical for this time of year? Yes 4) No (3 (If no, explain in Remarks.) Are Vegetation , Soil , or Hydrology significantly disturbed? Are "Normal Circumstances" present? Yes * No ( . Are Vegetation ❑ , Soil ❑ , or Hydrology ❑ naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transects, important features, et C7 Hydrophytic Vegetation Present? Yes No C) Is the Sampled Area Hydric Soil Present? Yes No - within a Wetland? Yes NO Wetland Hydrology Present? Yes - No Remarks: OFF-SITE DETERMINATION 1. 0 ❑ 0.0% 2. 0 l 0.0% Hydrophytlc Vegetation 0 = Total Cover Present? Yes No % Bare Ground In Herb Stratum: 0 Remarks: VEGETATION - Use scientific names of plants. Dominant Species? Absolute Rel.Strat. Indicator I Dominance Test worksheet: Tree Stratum (Plot size: ) % Cover Cover Status ❑ Number of Dominant Species 2 1. 0 o.o% (A) That are OBL, FACW, or FAC: 2, 0 0.0% Total Number of Dominant 2 . (B) Species Across All Strata: 4. 0 ❑ o.o°r° Percent of dominant Species Sapling/Shrub Stratum (Plot size: ) 0 Total Cover = 100.0° ro (q/B) That Are OBL, FACW, or FAC: 1. Salix exigua 2 100.0% OBL Prevalence Index worksheet: 2. 0 0.0% Total % Cover of: Multiply by: 3. 0 ❑ 0.0% oaL species 102 x 1 = 102 4. 0 ❑ 0.0% FACW species 0 x 2 - 0„ 5. 0 _.i 0.0% FAC species 0 x 3- 0 2 = Total Cover FACU species 0 x 4= 0 Herb Stratum (Plot size: ) 0 Carex aquatilis 1 lOD n 100.0°k 08L uPL species x 5 - . 2. 0 ❑ 0.0% Column Totals: 102 (A) 102 (IS) 3. 0 L o.o% Prevalence Index = B/A = 1.000 4. 0 LJ 0.0% Hydrophytic Vegetation Indicators: 5 0 ❑ 0.0% Dominance Test is a 50% 6. 0 1 . l 0.0% n Prevalence index is 53.01 7• o L_I o.o°i° Morphological Adaptations' (Provide supporting 8 0 1 1 0.0% data in Remarks or on a separate sheet) 9. 0 ❑ o.o% ❑ wetland Non-Vascular Plantsl ~ o ❑ 0.0% ❑ Problematic Nydrophytic Vegetation) (Explain) 100 =Total Cover 'Indicators of hydric soil and wetland hydrology must be present, unless disturbed or problematic. Woody Vine Stratum (Plot size: ) Indicator suffix = National status o.. * r professional decision assigned because Regional status not defined by FWS US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version Soil Sampling point: 35A Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Matrix Redox Features (inches) Color (moist) % % Types Loc= Color (moist) Texture Remarks IType: C=Concentration. D=Depletion, RM=Reduced Matrix, CS=Covered or Coated Sand Grains 21-oca tion: PL=Pare Lining. M=Matrix Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Solls3 ❑ Histosol (Al) ❑ Sandy Redox (SS) ❑ 2 cm Muck 010) ❑ Histic Epipedon (A2) ! Stripped Matrix (S6) ❑ Red Parent Material (TF2) ❑ Black Histic (A3) ❑ Loamy Mucky Mineral (Fl) (except in MLRA 1) Other (Explain in Remarks) ❑ Hydrogen Sulfide (A4) ❑ Loamy Gleyed Matrix (F2) ❑ Depleted Below Dark Surface (Ali) ❑ Depleted Matrix (F3) ❑ Thick Dark Surface (A1Z) Redox Dark Surface (F6 ) 3Indicators of hydrophytic vegetation and ❑ Sandy Muck Mineral (SS) ❑ Depleted Dark Surface (F7) wetland hydrology must be present, Sandy Gleyed Matrix (54) Redox depressions (F8) unless disturbed or problematic. Restrictive Layer (if present): Type: Depth (inches): - Hydric Soil Present? Yes ! No Remarks: ASSUMED HYDRIC SOILS BASED ON HYDROLOGY Hydrology Wetland Hydrology Indicators: Primary Indicators (minimum of one required; check all that apply) Secondary Indicators (minimum of two required) V1 Surface Water (Al) Water-Stained Leaves (B9) (except MLRA ❑ Water-Stained Leaves (B9) (ML RA 1, 2, 1-1 High Water Table (A2) 1, 2, 4A, and 4B) 4A, and 4B) U Saturation (A3) ❑ Salt Crust (Bll) ❑ Drainage Patterns (B10) Ll Water Marks (BI) ] Aquatic Invertebrates (B13) ❑ Dry Season Water Table (C2) ❑ Sediment Deposits (B2) Hydrogen Sulfide Odor (Cl) Saturation Visible on Aerial Imagery (C9) ❑ Drift deposits (B3) ❑ Oxidized Rhizospheres on Living Roots (0) Geomorphic Position (D2) ❑ Algal Mat or Crust (134) ~J Presence of Reduced Iron (C4) ❑ Shallow Aquitard (D3) ❑ Iron Deposits (B5) ❑ Recent Iron Reduction in Tilled Soils (C6) ❑ FAC-neutral Test (D5) ❑ Surface Soil Cracks (B6) ❑ Stunted or Stressed Plants (Dl) (LRR A) ❑ Raised Ant Mounds (D6) (LRR A) ❑ Inundation Visible on Aerial Imagery (B7) ❑ Other (Explain in Remarks) ❑ Frost Heave Hummocks (D7) Sparsely vegetated concave Surface (B8) Field Observations: Surface Water Present? Yes ! No Depth (inches): 0.25 . Water Table Present? Yes 0 No C*) Depth (inches): Saturation Present? - Wetland Hydrology Present? Yes * No (Includes capillary fringe) Yes No - Depth (inches): Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available: Remarks: SURFACE WATER ALONG WETLAND EDGE US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version • WETLAND DETERMINATION DATA FORM - Western Mountains, Valleys, and Coast Region Project/Site: DESCHUTES LWI City/County: SUNRNER/DESCHUTES Sampling Date: 24-Jun-10 A licant/Owner: Investigator(s): ALISON DESCHUTES SIGLER, COUNTY SARAH HARTUNG Section, Township, State: OR Sampling Point: SP 36A is Range: S 10 t 21 5 R 10 E Landform (hillslope, terrace, etc.): Floodplain Local relief (concave, convex, none): flat Slope: 0.0% / 0.0 ° Subregion (LRR): LRR A Lat.: 43.7739 Long.: -121.5238 Datum: NAD83 Soil Map Unit Name: 144A: Sunriver sandy loam, 0 to 3 percent slopes NWI classification: P$SG Are climatic/ hydrologic conditions on the site typical for this time of year? Yes * No (If no, explain in Remarks.) Are Vegetation n , Soil n , or Hydrology ❑ significantly disturbed? Are "Normal Circumstances" present? Yes No Are Vegetation , Soil , or Hydrology naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transects, important features, et Hydrophytic Vegetation Present? Yes No Is the Sampled Area Hydric Soil Present? Yes No within a Wetland? Yes * NO Wetland Hydrology Present? Yes No 0 Remarks: On-site determination. No digging allowed without a state cultural resource permit. VEGETATION - Use scientific names of plants. Dominant Species? Absolute Rel.Strat, Indicator Dominance Test worksheet: Tree Stratum (Plot size: ) "/o Cover Cover Status Number of Dominant Species 1. 0 0.0% That are OBL, FACW, or FAC: 5 (A) 2. 0 LJ 0.0% 3 0 D D% Total Number o Dominant , . Species Across All Strata: 5 (D) 4. 0 n 0.0% Percent of dominant Species Sapling/Shrub Stratum (Plot size: ) U =Total Cover That Are OBL, FACW, or FAC: 100.0% (A/6) . l xigua 20 n 66.70 OBL Prevalence Index worksheet: 2. Ppus a 10 ~1 33.30% FAC Total % Cover of: Multiply by 3. o ° O,a r° 08L species 60 x 1 - 60 4. 0 ❑ 0.0% FACW species 40 x 2 m 80 5. 0 0.0% FAC species 30 x 3 - 90 30 = Total Cover FACU species 0 x 4 - 0 Herb Stratum (Plot size: ) 0 0 1 Smilacina a~ 20 FAC 7V 0 l1PL species x 5 - - , Carex a uatilis 4 0 OBL U 40.0% 130 230 column Totals: (A) (B) 3 3uncus balticus 20 IV 20.0% FACW Prevalence Index = B/A = 1.769 4 Poa trivialis 10 10.0% FACW Hydrophytic Vegetation Indicators: 5 Spiraea douglasii 10 10.0% FACW U Dominance Test Is 7 50% 6 0 n 0.0% [ Prevalence index is 53.01 7 o 0.0% ~ Morphological Adaptations 1(Provide supporting 8. 0 0.0% data in Remarks or on a separate sheet) 9 0 LJ 0.0 h 7, Wetland Non-Vascular Plants' 10. 0 1 1 0.0°r° Problematic Hydrophytic Vegetation' (Explain) 11. 0 1.1 0.0% 1Inditators of hydric soil and wetland hydrology must 100 = Total Cover be present, unless disturbed or problematic. Woody Vine Stratum (Plot size: ) 1. 0 n 0.0% 2. 0 0.0% Hydrophytic 0 = Total Cover Vegetation Present? Yes * No (J Bare Ground in Herb Stratum: 0 Remarks: *Indicator suffix = National status or professional decision assigned because Regional status not de fined by FWS US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils:3 Histosol (Al) L Sandy Redox (S5) ❑ 2 cm Muck (A10) ❑ Histic Epipedon (A2) _ ] Stripped Matrix (S6) ❑ Red Parent Material (TF2) ❑ Black Histic (A3) ❑ Loamy Mucky Mineral (Fl) (except in MLRA 1) Other (Explain in Remarks) ❑ Hydrogen Sulfide (A4) ❑ Loamy Gleyed Matrix (F2) Depleted Below Dark Surface (All) ❑ Depleted Matrix (F3) ❑ Thick Dark Surface (A12) ❑ Redox Dark Surface (F6) ❑ 3Indicators of hydrophytic vegetation and ❑ Sandy Muck Mineral (51) Depleted Dark Surface (F7) wetland hydrology must be present, ❑ Sandy Gleyed Matrix (S4) [ Redox depressions (F8) unless disturbed or problematic. Restrictive Layer (it present): Type: Depth (Inches): _ Hydric Soil Present? Yes J) No Remarks: ASSUMED HYDRIC BASED ON HYDROLOGY Hydrology Wetland Hydrology Indicators: Primary Indicators (minimum of one required; check all that apply) Secondary Indicators (minimum of two required) ❑ Surface Water (Al) ❑ Water-Stained Leaves (B9) (except MLRA ❑ Water-Stained Leaves (B9) (MLRA 1, 2, ❑ High Water Table (A2) 1, 2, 4A, and 4B) 4A, and 4B) * Saturation (A3) Salt Crust (B11) ❑ Drainage Patterns (1310) 71 Water Marks (Bl) L Aquatic Invertebrates (B13) ❑ Dry Season Water Table (C2) ❑ Sediment Deposits (B2) ❑ Hydrogen Sulfide Odor (Cl) Saturation visible on Aerial Imagery (Cg) Drift deposits (B3) ❑ Oxidized Rhizospheres on Living Roots (0) - ❑ Geomorphic Position (D2) ❑ Algal Mat or Crust (B4) ❑ Presence of Reduced Iron (C4) Shallow Aquitard (D3) Iron Deposits (85) ❑ Recent Iron Reduction in Tilled Soils (C6) ❑ FAC-neutral Test (D5) Surface Soil Cracks (B6) ❑ Stunted or Stressed Plants (DI) (LRR A) ❑ Raised Ant Mounds (D6) (LRR A) ❑ Inundation Visible on Aerial Imagery (B7) ❑ Other (Explain in Remarks) Frost Heave Hummocks (D7) Sparsely Vegetated Concave Surface (B8) Field Observations: Surface Water Present? Yes No ! Depth (inches): Water Table Present? Yes C. NO Depth (inches): r Wetland Hydrology Present? Yes Saturation Present? No - _cludes capillary fringe) Yes No C Depth (inches ) 0 in-_ - Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available: Remarks: US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version WETLAND DETERMINATION DATA FORM - Western Mountains, Valleys, and Coast Region Project/Site: DESCHUTES LWI City/County: SUNRIVER/DESCHUTES Sampling Date: 24-Jun-10 • Applicant/ Owner: DESCHUTES COUNTY State: OR Sampling Point: SP 37A Investigator(s): ALISON SIGLER, SARAH HARTUNG Section' Township, Range: S 10 T 21 S R 10 E Landform (hillslope, terrace, etc.): Floodplain Local relief (concave, convex, none): flat Slope: 0.0% / 0.0 ° Subregion (LRR): LRR A lat.: 43.7746 long.: -121.5260 Datum: NAD83 Soil Map Unit Name: 144A: 5unrivQr sandy 10am,.Q to 3 percent sl9pes NWI classification: PFOC/PEMC Are climatic/ hydrologic conditions on the site typical for this time of year? Yes No (If no, explain in Remarks.) Yes C') No Are Vegetation ❑ , soil ❑ , or Hydrology ❑ significantly disturbed? Are "Normal Circumstances" present? Are Vegetation I ...J , Soil I I , or Hydrology naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transects, important features, et Hydrophytic Vegetation Present? Yes ! No 0 Is the Sampled Area H dric Soil Present? Yes No y Yes No Wetland Hydrology Present? Yes ` NO within a Wetland? Remarks: OFF-SITE DETERMINATION VEGETATION - Use scientific names of plants. Dominant Species? Absolute Rel.Strat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: ) % Cover Cover Status ' Number of Dominant Species 1. Pinus contorts 20 100.0% FAC That are OBL, FACW, or FAC: 4 (A) 2 0 n 0.0% . 3 0 ❑ 0 0% Total Number of Dominant . . Species Across All Strata: 4 (B) 4. 0 LJ 0.0% Percent of dominant Species Sapling/Shrub Stratum (Plot size: ) 20 = Total Cover ° That Are OBL, FACW, or FAC: 100.0 /o (A/a) • Salix exi9ua 1. to ~ 100.0 k OBL Prevalence index worksheet: 2. 0 ° 0.0% Total /o o Cover Cover of Multiply by: 3. o ❑ 0.0% OBL species 10 x 1 - 10 4. 0 LJ 0.o% FACW species 100 x 2 - 200 5. 0 1 1 0.00/. FAC species 20 x 3 - 60 10 = Total Cover 0 0 FACU species x 4 = Herb Stratum (Plot size: 0 0 C 80 80 0% FACW x 5 T uPL species arex sp. 1 . 2. Juncus balticus 20 L ] 20.01/o FACW Column Totals: 130 (A) 270 (B) 3. 0 n 0.0°i° Prevalence Index = B/A = 2.077 4. 0 LJ 0.0% Hydrophytic Vegetation Indicators: 5 0 n 0.0%° U Dominance Test is 7 so% 6 0 n 0.0% Prevalence index is 53.01 7• 0 n 0.0/ Morphological Adaptations 1(Provide supporting S. 0 n 0.0% data in Remarks or on a separate sheet) 9 0 0 LJ 0.0 h n Wetland Non-Vascular Plantsl 10. 0 L 0.0% Problematic Hydrophytic Vegetatlonl (Explain) 11. o ❑ 0.0% 11ndicators of hydric soil and wetland hydrology must 100 =Total Cover be present, unless disturbed or problematic. Woody Vine Stratum (Plot size: ) 1 . 0 n 0.0% 2. D ❑ 0.0% Hydrophytic 0 = Total Cover Vegetation Present? Yes * No 016 Bare Ground in Herb Stratum: 0 Remarks: Carex sp, assumed to be FACW. Indicator suffix = National status or professional decision assigned because Regional status not de fined by FWS US Army Corps of Engineers Wester n Mountains, Valleys, and Coast Region Interim version Soil Sampling Point: 37A Profile Description: (Describe to the depth needed to document the Indicator or conflrm the absence of Indicators.) x Features Depth (inches) Color (moist) Matrix % Color (moist) Redo % Type 1 Loc= Texture Remarks (nc I Type: Ion. D=Depletion. RM=Reduced Matrix, CS=Covered or Coated Sand Grains 2Location: PL=Pore Lining. M=Matrix Type. C-Concentrat Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric SoilS:3 ❑ Histosol (At) Sandy Redox (SS) ❑ 2 cm Muck (A10) ❑ Histic Epipedon (A2) Stripped Matrix (56) Red Parent Material (TF2) ❑ Black Histic (A3) Loamy Mucky Mineral (Fl) (except in MLRA 1) V/ Other (Explain in Remarks) ❑ Hydrogen Sulfide (A4) L Loamy Gleyed Matrix (F2) ❑ Depleted Below Dark Surface (All) L Depleted Matrix (F3) ❑ Thick Dark Surface (A12) L- Redox Dark Surface (F6) 3Indicators of hYdroPhYtis vegetation and ❑ Sandy Muck Mineral (Sl) i j Depleted Dark Surface (F7) wetland hydrology must be present, ❑ Sandy Gleyed Matrix (S4) ❑ Redox depressions (F8) unless disturbed or problematic. Restrictive Layer (if present): Type: Depth (inches):. Hydric Soil Present? Yes No (D Remarks: ASSUMED HYDRIC BASED ON HYDROLOGY . . Hydro logy Wetland Hydrology Indicators: Primary Indicators (minimum of one required; check all that apply) Secondary Indicators (minimum of two required) SJ Surface Water (At) Water-Stained Leaves (139) (except MLRA ❑ Water-Stained Leaves (B9) (MLRA 1, 2, ❑ High Water Table (A2) 1, 2, 4A, and 4B) 4A, and 48) Saturation (A3) ❑ Salt Crust (Bll) Drainage Patterns (B10) ❑ Water Marks (Bl) ❑ Aquatic Invertebrates (813) ❑ Dry season water Table (C2) L Sediment Deposits (132) Hydrogen Sulfide Odor (Cl) L Saturation Visible on Aerial Imagery (Cg) Drift deposits (83) ,J Oxidized Rhizospheres on Living Roots (0) ❑ Geomorphic Position (D2) ❑ Algal Mat or Crust (B4) ❑ Presence of Reduced Iron (C4) r Shallow Aquitard (D3) ❑ Iron Deposits (BS) Recent Iron Reduction in Tilled Soils (C6) FAC-neutral Test (DS) Surface Soil Cracks (86) Stunted or Stressed Plants (DS) (LRR A) Raised Ant Mounds (D6) (LRR A) Inundation Visible on Aerial Imagery (87) Other (Explain in Remarks) ❑ Frost Heave Hummocks (D7) Sparsely Vegetated Concave Surface (B8) Field Observations: Surface Water Present? Yes No Depth (inches): 5 Water Table Present? Yes C) No Depth (inches): Saturation Present? Yes ' No - Wetland Hydrology Present? Yes No - Depth (inches): F 00--i (includes capillary fringe) - Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available: Remarks: US Army Corps of Engineers . Western Mountains, Valleys, and Coast Region Interim version . WETLAND DETERMINATION DATA FORM - Western Mountains, Valleys, and Coast Region Project/Site: DESCHUTES LWI City/County: SUNRIVER/DESCHUTES Sampling Date: 24-Jun-10 Applicant/Owner: G Section State: OR Sampling Point: SP 38A Investigator(s): ALISON SIGLER, , Township, Range: S 9 T 21S R 10 E SARAH , HARTUN Landform (hillslope, terrace, etc.): Floodplain Local relief (concave, convex, none): flat Slope: 0.0% / 0.0 ° Subregion (LRR): LRR A Lat.: 43.7755 Long.: -121.5301 Datum: NAD83 ell SLopgS NWY classification: PFOA Soil Map Unit Name: 1140: Shanahan loamy coarse gano, 01o• 15 perC Are climatic/ hydrologic conditions on the site typical for this time of year? Yes C~) No (If no, explain in Remarks.) Are Vegetation , Soil , or Hydrology ❑ significantly disturbed? Are "Normal Circumstances" present? Yes * No Are Vegetation , Soil , or Hydrology naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transects, important features, et Hydrophytic Vegetation Present? Yes No r_ Is the Sampled Area Hydric Soil Present? Yes No C-) * No within a Wetland? Yes ( ) Wetland Hydrology Present? Yes C~) No C-) Remarks: On-site determination. No digging allowed without a state cultural resource permit. VEGETATION - Use scientific names of plants. Dominant Species? Absolute Rel.Strat. Indicator Dominance Test worksheet: lot size: Stratum T °/a Cover Cover S at s Number of Dominant Species Pinus o That are OBL, FACW, or FAC: 3 (A) 2. 0 n D.0°k 3 0.. ❑ D D% Total Number of Dominant , . Species Across All Strata: 3 (8) 4. D f 10.0% 2 = Total Cover Percent of dominant Species a 100.0 /o (A/B) Sapling/Shrub Stratum (Plot size: ) That Are OBL, FACW, or FAC: 1. Alnus incana 10 ❑ 16.7% FACW Prevalence Index worksheet: 2. Salix exigua SO U 83.3M ° OBL Total % Cover of: Multiply by: 3, 0 U 0.0% oBL species 50 x 1 = 50 4. 0 1 1 0.0% FACW species 90 x 2 . 180 5. 0 ❑ 0.0% FAC species 22 x 3 = 66 60 = Total Cover FACU species 0 x 4 = 0 Herb Stratum (Plot size: ) C 70 U 70 0% FACW DPL species x 5 = 1. arex sp. . . 2. Equisetum arvense S 5.0h ° FAC ❑ column Totals: 162 (A) 296 (B) 3 Rumex unonatus ltl 10.00/a FACW ❑ Prevalence Index = B/A = 1.827 Poa sp. 4. 15 ❑ 15.0% FAC Nydrophytic Vegetation Indicators: 5 0 ❑ 0.0% n Dominance Test is > 50% 6. 0 LJ 0.0% d Prevalence Index is 53.01 7. 0 1 0.0"/° ❑ Morphological Adaptations 1 (Provide supporting S 0 ° I 0.0% data in Remarks or on a separate sheet) 9. ❑ 0.0% Wetland Non-Vascular Plantsl 10. D I 0.0% ❑ Problematic Hydrophytic Vegetationl (Explain) 11. 0 0.0°/a 100 = Total Cover 'Indicators of hydric soil and wetland hydrology must be present, unless disturbed or problematic. Woody Vine Stratum (Plot size: ) 1. 0 ❑ 0.0% 2. 0 U o.0% Hydrophytic 0 - Total Cover - Vegetation Present? Yes No % Bare Ground In Herb Stratum: 0 Remarks: Carex sp. assumed FACW. Poa sp. assumed FAC.. *Indicator suffix = National status or professional decision assigned because Regional status not de fined by FWS US Army Corps of Engineers Wester n Mountains, Valleys, and Coast Region Interim version Soil Sampling Point: 38A Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Depth Matrix Redox Features (inches) Color (moist) a/o Color (moist) "/o Type I Loc2 Texture Remarks ,Type: C=Concentration. D=Depletion. RM=Reduced Matrix, CS=Covered or Coated Sand Grains 2Loca tion: PL=Pore Lining. M=Matrix Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils :3 F. ] Histosol (Al) Sandy Redox (SS) J 2 cm Muck (A10) ❑ Histic Epipedon (A2) ❑ Stripped Matrix (S6) ❑ Red Parent Material (TF2) L_] Black Histic (A3) ❑ Loamy Mucky Mineral (Fl) (except in MLRA 1) DI/ Other (Explain in Remarks) ❑ Hydrogen Sulfide (A4) ❑ Loamy Gleyed Matrix (F2) ❑ Depleted Below Dark Surface (All) ❑ Depleted Matrix (F3) ❑ Thick Dark Surface (A12) Redox Dark Surface (F6) 3Indicators of hydrophytic vegetation and ❑ Sandy Muck Mineral (51) ❑ Depleted Dark Surface (F7) wetland hydrology must be present, ❑ Sandy Gleyed Matrix (S4) ] Redox depressions (F8) unless disturbed or problematic. Restrictive Layer (if present): Type I Depth (inches): Hydric Soil Present? Yes No - Remarks: ASSUMED HYDRIC SOILS BASED ON HYDROLOGY Hydrology Wetland Hydrology Indicators: Primary Indicators (minimum of one required; check all that apply) Secondary Indicators (minimum of two required) ] Surface Water (Al) Water-Stained Leaves (89) (except MLRA water-Stained Leaves (89) (MLRA 1, 2, ❑ High Water Table (A2) 1, 2, 4A, and 4B) 4A, and 4B) ❑ Saturation (A3) Salt Crust (511) ❑ Drainage Patterns (B10) ❑ Water Marks (Bl) L Aquatic Invertebrates (B13) i._.] Dry Season Water Table (C2) ] Sediment Deposits (B2) ❑ Hydrogen Sulfide Odor (Cl) Saturation Visible on Aerial Imagery (C9) 1 Drift deposits (53) ❑ Oxidized Rhizospheres on Living Roots (0) Geomorphic Position (D2) ❑ Algal Mat or Crust (B4) L-' Presence of Reduced Iron (C4) ❑ Shallow Aquitard (D3) ❑ Iron Deposits (B5) Recent Iron Reduction in Tilled Soils (C6) ❑ FAC-neutral Test (D5) ❑ Surface Soil Cracks (B6) ❑ Stunted or Stressed Plants (DS) (LRR A) Raised Ant Mounds (D6) (LRR A) ❑ Inundation Visible on Aerial Imagery (B7) Other (Explain in Remarks) Frost Heave Hummocks (D7) ❑ Sparsely Vegetated Concave Surface (BS) Field Observations: Surface Water Present? Yes No Depth (inches): Water Table Present? Yes 0 No Depth (inches): F 1 Y N Saturation Present? - Yes No ! es o Wetland Hydrology Present? Depth (inches): (includes capillary fringe) Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available: Remarks; US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version WETLAND DETERMINATION DATA FORM - Western Mountains, Valleys, and Coast Region Project/Site: DESCHUTES LWI City/County: SUNRNER/DESCHUTES Sampling Date: 24-Jun-10 Applicant/Owner: State: OR Sampling Point: SP 39A Investigator(s): ALISON SGLER SARAH HARTUNG Section, Township, Range: S 9 T 21 S R 10 E Landform (hillslope, terrace, etc.): Floodplain local relief (concave, convex, none): flat Slope: 0.0% / 0.00 Subregion (LRR): LRR A lat.: 43.7752 Long.: -121.5299 Datum: NAD83 Soil Map Unit Name: 1.44A; $.Unriver,5andy loam. Q.to 3 perG0[..it 51ope5 NWI classification: P$$C/PFOA Are climatic/ hydrologic conditions on the site typical for this time of year? Yes (No (If no, explain in Remarks.) Are Vegetation ❑ , Soil ❑ , or Hydrology ❑ significantly disturbed? Are "Normal Circumstances" present? Yes (4) NO - Are Vegetation , Soil , or Hydrology naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transacts, important features, et r~ E Hydrophytic Vegetation Present? Yes ! No 0 Is the Sampled Area Hydric Soil Present? Yes ! No 0 within a Wetland? Yes > No Wetland Hydrology Present? Yes No ( ~ Remarks: OFF-SITE DETERMINATION VEGETATION - Use scientific names of plants. Dominant Species? Absolute Rel.Strat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: % Cover Cover Status n Number of Dominant Species Pinus contorts 5 100.0% FAC That are OBL, FACW, or FAC: 2 0 0.0°r° . 3 0 LL 0 0% Total Number of Dominant , . Species Across All Strata: 4. 0 1 0.0% 5 = Total Cover Percent of dominant Species Sapling/Shrub Stratum (Plot size: ) That Are OBL, FACW, or FAC: 1. Alnus incana 2. Salix exigua 3. 4. 5. Herb Stratum (Plot size: ) 1. Carex aquatilis 2. )uncus balticus 3. 4. 5. 6. 7. 8. 9. 10. 11. Woody Vine Stratum (Plot size: ) 1. 2. 0/6 Bare Ground in Herb Stratum: 0 Remarks: *Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version 10 1. 1 16.7% FACW 50 ❑ 83.3% OBL 0 J 0.0°% 0 0.0% 0 n 0.0% 60 = Total Cover BO L l 80.0% OBL 20 ❑ 20.0% FACW 0 n 0.0% 0 J 0.0% 0 n 0.0% 0 LL 0.0% 0 LL o.o% 0 0.0% 0 n 0.0% o (L o.o% 0 0.0% 100 = Total Cover 0 LL 0.0% 0 ❑ 0.0% 0 = Total Cover 4 (A) 4 (B) 100.0% (A/B) worksheet: Prevalence % Cover of: Multiply by: Total ro Cover of: Multiply by: oBL species 130 x 1 - 130 FACW species 30 x 2 = 60 FAC species 5 x 3 = 15 FACU species 0 x 4 = 0. UPL species 0 - x 5 = 0 column Totals: 165 (A) 205 (B, Prevalence Index = B/A = 1.242 Hydrophytic Vegetation Indicators: ~Y.I Dominance Test is n 50% !-4 Prevalence Index is 53.01 L_ Morphological Adaptations 1(Provide supporting data in Remarks or on a separate sheet) Wetland Non-Vascular Plantsl LL Problematic Hydrophytic Vegetationl (Explain) 1Indicators of hydric soil and wetland hydrology must be present, unless disturbed or problematic. Hydrophytic Vegetation Present? Yes * No SOLI Sampling Point: 39A Profile Description: (Describe to the depth needed to document the Indicator or confirm the absence of Indicators.) Depth i X ture s Redox F (inches) Color (mo st) % Color (moist) Typet Loc2 % Texture Remarks ,Type: C=Concentration. D=Depletion. RM=Red uced Matrix, CS=Covered or Coated Sand Grains 21-oca tion: PL=Pore Lining. M=Matrix Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils:3 ❑ Histosol (Al) ❑ Sandy Redox (S5) ❑ 2 cm Muck (A10) ❑ Histic Epipedon (A2) ❑ Stripped Matrix (S6) ❑ Red Parent Material (TF2) ❑ Black Histic 03) ❑ Loamy Mucky Mineral (Fl) (except in MLRA 1) J Other (Explain in Remarks) ❑ Hydrogen Sulfide (A4) ❑ Loamy Gleyed Matrix (F2) ❑ Depleted Below Dark Surface (All) ❑ Depleted Matrix (F3) 7 Thick Dark Surface (A12) Redox Dark Surface (F6) 3Indicators of hydrophytic vegetation and ❑ Sandy Muck Mineral (Si) Depleted Dark Surface (F7) wetland hydrology must be present, Sandy Gleyed Matrix (S4) r ❑ Redox depressions (F8) unless disturbed or problematic. Restrictive Layer (if present): Type. Depth (inches): Hydric Soil Present? Yes No C ) Remarks: ASSUMED HYDRIC SOILS BASED ON HYDROLOGY Hydrology Wetland Hydrology Indicators: Primary Indicators (minimum of one required; check all that apply) Secondary Indicators (minimum of two required) 1-/I Surface Water (Al) ❑ Water-Stained Leaves (89) (except MLRA Ll Water-Stained Leaves (139) (MLRA 1, 2, High Water Table (A2) 1, 2, 4A, and 413) 4A, and 4B) n Saturation (A3) LJ' Salt Crust (1311) _i Drainage Patterns (Blo) ❑ Water Marks (BS) ❑ Aquatic Invertebrates (B13) LJ Dry Season Water Table (C2) ❑ Sediment Deposits (132) Hydrogen Sulfide Odor (Cl) ❑ Saturation Visible on Aerial Imagery (C9) ❑ Drift deposits (B3) _ Oxidized Rhizospheres on Living Roots (0) Geomorphic Position (D2) Algal Mat or Crust (134) Presence of Reduced Iron (C4) Shallow Aquitard (D3) L_L Iron Deposits (B5) Recent Iron Reduction in Tilled Soils (C6) FAC-neutral Test (D5) ❑ Surface Soil Cracks (136) Stunted or Stressed Plants (Dl) (LRR A) Raised Ant Mounds (D6) (LRR A) ❑ Inundation Visible on Aerial Imagery (137) ❑ Other (Explain in Remarks) ❑ Frost Heave Hummocks (137) Sparsely Vegetated Concave Surface (138) Field Observations: Surface Water Present? Yes No Depth (Inches): 2 Water Table Present? Yes No Depth (inches): Saturation Present? Wetland Hydrology Present? Depth (inches): p (Includes capllary f ringe)_-. Yes J') No O Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available: Remarks: SURFACE WATER ALONG WETLAND EDGE Yes No • US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version WETLAND DETERMINATION DATA FORM - Western Mountains, Valleys, and Coast Region Project/Site: DESCHUTES LWI City/County: SUNRIVER/DESCHUTES Sampling Date: 24-Jun-10 Applicant/ Owner: DESCHUTES COUNTY 55 te: OR Sampling Point: SP 40A Investigator(s): ALISON SIGLER, SARAH HARTUNG Section, Township, Range: 3 T 21 S R 10 E Landform (hillslope, terrace, etc.): Floodplain Local relief (concave, convex, none): flat Slope: 0.0% / 0.0 ° Subregion (LRR): LRR A Lat.: 43.7772 Long.: -121.5142 Datum: NAD83 Soil Map Unit Name: 29A; Cryaquolls, 0 to 3 percent slopes NWI classification: PEMG/PSSC, Are climatic/ hydrologic conditions on the site typical for this time of year? Yes No (If no, explain in Remarks.) Are Vegetation , Soil i I , or Hydrology ❑ significantly disturbed? Are "Normal Circumstances" present? Yes No Are Vegetation __1 , Soil ❑ , or Hydrology naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transacts, important features, et Hydrophytic Vegetation Present? Yes No Is the Sampled Area Hydric Soil Present? Yes (P) No within a Wetland? Yes No Wetland Hydrology Present? Yes Ji) No Remarks: OFF-SITE DETERMINATION VEGETATION - Use scientific names of plants. Dominant Species? Absolute Rel.Strat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: Cover Cover Status Number of Dominant Species 1. 0 0.0% That are 08L, FACW, or FAC: 3 (A) 2. a f I o.o% 3 0 El o 0% Total Number o Dominant , . Species Across All Strata: 3 (8) 4. a ❑ o.o% Percent of dominant Species 0 = Total Cover u or FAC: 100.0 (A/8) That Are OBL FACW Sapling/Shrub Stratum (Plot size: ) , , 1. Alnus incana SO 7 19.6% FACW Prevalence Index worksheet: 2. Pinus contorta 1 L 2.0% FAC Total % Cover of: Multiply by: 3. Salix exigua 40 78.4% OBL oBL species 120 x 1 - 120 4. 0 . 0.0% FACW species 10 x 2 - 20 5. 0 ❑ 0.0% FAC species 21 x 3 - 63 51 = Total Cover FACU species 0 x 4 = 0 Herb Stratum (Plot size: ) Carex aquatilis 1 80 U 80.0/° 08L UPL species x 5 . 2_ Poa sp. 20 U 20.0% FAC column Totals: 151 (A) 203 (B) 3. 0 ❑ 0.0% Prevalence Index = B/A = 1.344 4 0 ❑ 0.0% Hydrophytic Vegetation indicators: 5. 0 ❑ 0.0% n Dominance Test is a 50% 6. 0 ❑ 0.0% d prevalence Index is 53.01 0 ~.J 0.0% LJ Morphological Adaptations I (Provide supporting 8 0 ❑ 0.0% data in Remarks or on a separate sheet) 9. 0 ❑ 0.0% ~L Wetland Non-Vascular Plantsl 10~ o ❑ 0.a°% ° ❑ Problematic Hydrophytic Vegetatlonl (Explain) 11. o ❑ o.o% 100 =Total Cover 1Indicators of hydric soil and wetland hydrology must be present, unless disturbed or problematic. Woody Vine Stratum (Plot size: ) . 1. 0 ❑ o.o% 2. 0 1 0,0% Hydrophytic 0 = Total Cover Vegetation Present? Yes No Bare Ground in Herb Stratum: 0 Remarks: Poa sp. assumed FAC. *Indicator suffix = National status or professional decision assigned because Regional status not de fined by FWS US Army Corps of Engineers Wester n Mountains, Valleys, and Coast Region Interim version Soil Sampling Point: 40A Profile Description: (Describe to the depth needed to document the Indicator or confirm the absence of Indicators.) Depth Matrix Redox Features (inches) Color (moist) % Color (moist) % Type I Loc= Texture Remarks . tType: C=Concentration. D=Depletion. RM=Reduced Matrix, CS=Covered or Coated Sand Grains 2Loca tion: PL=Pore Lining. M=Matrix dric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Hy Indicators for Problematic Hydric Solls:3 I I L Histosol (Al) Sandy Redox (S5) ❑ 2 cm Muck (A10) ❑ Histic Epipedon (A2) ❑ Stripped Matrix (S6) ❑ Red Parent Material (TF2) Black Histic (A3) Loamy Mucky Mineral (Fl) (except in MLRA 1) ❑ Other (Explain in Remarks) ❑ Hydrogen Sulfide (A4) L Loamy Gleyed Matrix (F2) Depleted Below Dark Surface (All) ❑ Depleted Matrix (F3) Thick Dark Surface (A12) ❑ Redox Dark Surface (F6) 3Indicators of hydrophytic vegetation and ❑ Sandy Muck Mineral (Sl) ❑ Depleted Dark Surface (F7) wetland hydrology must be present, ❑ Sandy Gleyed Matrix (S4) ❑ Redox depressions (F8) unless disturbed or problematic. Restrictive Layer (if present): Type: Depth (inches): Hydric Soil Present? Yes ' No Remarks: SOILS ASSUMED HYDRIC BY SATURATION Hydrology Weiland Hydrology Indicators: Primary Indicators (minimum of one required; check all that apply) Secondary Indicators (minimum of two required) Surface Water (Al) Water-Stained Leaves (B9) (except MLRA Water-Stained Leaves (89) (MLRA 1, 2, High Water Table (A2) 1, 2, 4A, and 4B) 4A, and 4B) V Saturation (A3) ❑ Salt Crust (Btl) ❑ Drainage Patterns (1310) ❑ Water Marks (BS) Aquatic Invertebrates (813) Dry season water Table (C2) Sediment Deposits (B2) ❑ Hydrogen Sulfide Odor (Cl) -J Saturation Visible on Aerial Imagery (C9) Drift deposits (83) ❑ Oxidized Rhizospheres on Living Roots (0) ❑ Geomorphic Position (D2) ❑ Algal Mat or Crust (134) ❑ Presence of Reduced Iron (0) ❑ Shallow Aquitard (D3) ❑ Iron Deposits (135) I.1 Recent Iron Reduction in Tilled Soils (C6) ❑ FAC-neutral Test (D5) Surface Soil Cracks (136) ❑ Stunted or stressed Plants (Dl) (LRR A) ❑ Raised Ant Mounds (D6) (LRR A) Inundation Visible on Aerial Imagery (137) Other (Explain in Remarks) Frost Heave Hummocks (D7) Sparsely Vegetated Concave Surface (138) Field Observations: Surface Water Present? Yes 0 No Depth inches : Water Table Present? Yes C-) No Depth (inches): I Saturation Present? Yes No - - Wetland Hydrology Present? Yes ! No Depth (inches): 0 _(includes capillary fringe) Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available: Remarks: SATURATION SEEN WITH BINOCULARS US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version WETLAND DETERMINATION DATA FORM - Western Mountains, Valleys, and Coast Region Project/Site: DESCHUTES LWI City/County: SUNRIVER/DESCHUTES Sampling Date: 24-Jun-10 Applicant/Owner: DESCHUTES COUNTY State: OR Sampling Point: SP 41A Investigator(s): ALISON SIGLER, SARAH HARTUNG Section, Township, Range: S 3 T 21 S R 10 E Landform (hlilslope, terrace, etc.): Floodplain Local relief (concave, convex, none): flat Slope: 0.0% / 0.0 ° Subregion (LRR): LRR A Lat.: 43.7834 Long.. -121.5141 Datum: NAD83 Soil Map Unit Name: Z9A; t ryaggp,llS, 0 tq 3 plucent slopes , NWI classification: PEMA/P$$Q`PFQA Are climatic/ hydrologic conditions on the site typical for this time of year? Yes No ( (If no, explain in Remarks.) Are Vegetation Soil , or Hydrology I__] significantly disturbed? Are "Normal Circumstances" present? Yes * No (L Are Vegetation Soil ❑ , or Hydrology n naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transects, important features, et Hydrophytic Vegetation Present? Yes No Is the Sampled Area Hydric Soil Present? Yes J) No )L j YeS ! No Wetland Hydrology Present? Yes J) No O within a Wetland? Remarks: OFF-SITE DETERMINATION VEGETATION - Use scientific names of plants. Dominant Species? Absolute Rel-Strat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: ) % Cover Cover Status ❑ Number of Dominant Species 4 1. 0 0.0% That are OBL, FACW, or FAC: , (A) 2. 0 . 0.0% 3 0 0 0% Total Number of Dominant • . Species Across All Strata: 4 (e) 4. 0 I 0.0% 0 = Total Cover Percent of dominant Species u 0 /o (A/B) 100 Sapling/Shrub Stratum (Plot size: ) . That Are OBL, FACW, or FAC: 1, Alnus incana 10 1/1 25.0% FACW Prevalence Index worksheet: 2. Salix exigua 30 U 75.0% OBL Total % Cover of; Multiply by: 3. 0 ❑ 0.0% ORL species 110 x 1 - 110 4. 0 n 0.0°/n FACW species 10 x 2 = 20 5. 0 I. J 0.0% FAC species 20 x 3 60 40 = Total Cover FACU species 0 . x 4 = 0 Herb Stratum (Plot size: ) 0 1 Carex aquatilis 80 n 80.0% OBL uPL species x 5 = . 2. Poa sp. 20 L ~ 20.0% FAC column Totals; 140 (A) 190 (B) g 0 LJ 0.0% Prevalence Index = B/A = 1.357 4 0 l J 0.0°/n Hydrophytlc Vegetation indicators: 5 0 0.0% Dominance Test Is 7 50% 6. 0 7 0,0% n Prevalence index is S3.0t 7. 0 1 1 0,0°h 1 Morphological Adaptations (Provide supporting S 0 0.0% data in Remarks or on a separate sheet) 9. 0 L 0,0% ❑ Wetland Non-Vascular Plants' 10 0 n 0.00/. ❑ Problematic Hydrophytic Vegetation' (Explain) 11: 0 F7 0.0% 'Indicators of hydric soil and wetiand hydrology must 100 =Total Cover be present, unless disturbed or problematic. Woody Vine Stratum (Plot size: ) 1. 0 L 0.0% 2. 0 L] 0.0% Hydrophytic 0 - Total Cover Vegetation Present? Yes No Bare Ground in Herb Stratum: 0 - Remarks: oa sp. assume FAC.. . , , *Indicator suffix = National status or professional decision assigned because Regional status not de fined by FWS US Army Corps of Engineers Wester n Mountains, Valleys, and Coast Region Interim version Soil Sampling Point: 41A Profile Description: (Describe to the depth needed to document the Indicator or confirm the absence of Indicators.) Depth Matrix Redox Features Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils:3 ❑ Histosol (Al) ❑ Sandy Redox (S5) ❑ 2 cm Muck (A10) Histic Epipedon (A2) LI Stripped Matrix (S6) Red Parent Material (TF2) Black Histic (A3) Loamy Mucky Mineral (F1) (except in MLRA 1) n Other (Explain in Remarks) ❑ Hydrogen Sulfide (A4) L Loamy Gleyed Matrix (F2) ❑ Depleted Below Dark Surface (Ali) Depleted Matrix (F3) ❑ Thick Dark Surface (A12) r Redox Dark Surface (F6) 3Indicators of hydrophytic vegetation and Sandy Muck Mineral (Si) Depleted Dark Surface (F7) wetland hydrology must be present, ❑ Sandy Gleyed Matrix (S4) L~ Redox depressions (F8) unless disturbed or problematic. Restrictive Layer (if present): Type: Depth (inches): Hydric Soil Present? Yes J) No Remarks: SOILS ASSUMED HYDRIC BY SATURATION • Hydrology Wetland Hydrology indicators: Primary Indicators (minimum of one required; check all that apply) Secondary Indicators (minimum of two required)' . ❑ Surface Water (Al) ❑ Water-Stained Leaves (69) (except MLRA Water-Stained Leaves (89) (MLRA 1, 2, ❑ High Water Table (A2) 1, 2, 4A, and 4B) 4A, and 4B) n Saturation (A3) ~_..J Salt Crust (Bl1) ❑ Drainage Patterns (BIO) ❑ Water Marks (BS) ❑ Aquatic Invertebrates (B13) 11 Dry season water Table (C2) ❑ Sediment Deposits (82) ❑ Hydrogen Sulfide Odor (Cl) 1 _J Saturation Visible on Aerial Imagery (C9) ❑ Drift deposits (83) Oxidized Rhizospheres on Living Roots (0) ❑ Geomorphic Position (D2) Algal Mat or Crust (84) Presence of Reduced Iron (C4) ❑ Shallow Aquitard (133) ❑ Iron Deposits (BS) Recent Iron Reduction in Tilled Soils (C6) ! FAC-neutral Test (135) Surface Soil Cracks (136) [ Stunted or Stressed Plants (Dl) (LRR A) ❑ Raised Ant Mounds (D6) (LRR A) Inundation Visible on Aerial Imagery (137) ❑ Other (Explain in Remarks) ( Frost Heave Hummocks (1)7) Sparsely Vegetated Concave Surface (BB) Field Observations: Surface Water Present? Yes No Depth (inches): Water Table Present? Yes No Depth (inches): Y N ~ Saturation Present? - - Yes No es o - Depth (inches); 0 i Wetland Hydrology Present? (includes capillary fringe) Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available: Aerial photo Remarks: SATURATION SEEN WITH BINOCULARS US Army Corps of Engineers Western Mountains, Valleys, and Coast Region - Interim version WETLAND DETERMINATION DATA FORM - Western Mountains, Valleys, and Coast Region Project/Site: DESCHUTES LWI City/County: SUNRIVERMESCHUTES Sampling Date: 24-Jun-10 ALISON COUNTY SARAH HARTUNG Section Township, Range State: OR Sampling Point: SP 42A investigator(s): S 35 T20S R l0E Landform (hillslope, terrace, etc.): Valley bottom Local relief (concave, convex, none): concave Slope: 0.0% / 0.0 ° Subregion (LRR): LRR A Lat.: 43.8046 Long.: -121.4956 Datum: NAD83 Soil Map Unit Name: 29A: GrYaau411S, 0 to.3 perSent $19.pes NWI classification: KM Are climatic/ hydrologic conditions on the site typical for this time of year? Yes * No (D (If no, explain in Remarks.) Are Vegetation ❑ , Soil ❑ , or Hydrology ❑ significantly disturbed? Are "Normal Circumstances" present? Yes * No Are Vegetation , Soil , or Hydrology [-7 naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transects, important features, et Hydrophytic Vegetation Present? Yes=) No - ) Hydric Soil Present? Yes IS the Sampled Area No Yes No 0 Wetland Hydrology Present? Yes within a Wetland? No ( ) Remarks: On-site determination. VEGETATION - Use scientific names of plants. Dominant Species? Absolute Rel.Strat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: ) 0/6 Cover Cover Status Number of Dominant Species 1. Pinus contorta 50 100.0% FAC That are D6L, FACW, or FAC: 3 (A) 2. 0 % 3 0 0 0 Total Number of Dominant , . Species Across All Strata: 4 (8) 4. 0 0.0% 50 = Total Cover Percent of dominant Species u 75.0% (A/B) Sapling/Shrub Stratum (Plot size: ) That Are OBL, FACW, or FAC: 1. Rosa gymnocarpa 0 ❑ 0.0% FACU Prevalence Index worksheet: 2, salix exigua 20 0 100.0% OBL Total % Cover of; Multiply by: 3. 0 ❑ 0.0% oBL species 20 x 1 = 20 4. 0 Ll o.0% FACW species 0 x 2= 0 5. o 71 0.0°r° FAt species 60 x 3 = 180.. 20 = Total Cover 5 20 FACU species x 4 = Herb Stratum (Plot size: ) 0 1 Fragaria virginiana 5 141 33.3% FACU UPL species x 5 = • 2. Trifolium repens 10 n 66.7% FAC Column Totals: 85 (A) 220 (B) 3. 0 ❑ 0.0% Prevalence Index = B/A = 2.588 4• 0 ❑ 0.0"/0 Hydrophytic Vegetation indicators: 5 0 L] 0.0% n Dominance Test is 7 50% 6 0.. o Ll 0.0% d~ Prevalence index is 53.01 7. 0 ❑ o.o% 1 Morphological Adaptations 1 (Provide supporting ~ 8 0 ❑ 0.0% . data in Remarks or on a separate sheet) 9 0 ❑ 0.0% Wetland Non-Vascular Plantsl 10. 0 ❑ o.0%° Problematic Hydrophytic Vegetationl (Explain) 11. o ❑ o.o0r° 15 =Total Cover 1Indicators of hydric soil and wetland hydrology must be present, unless disturbed or problematic. Woody Vine Stratum (Plot size: ) 1. 0 ❑ 0.0% 2. 0 0.0% Hydrophytic 0 Total Cover Vegetation Yes No ( ) Present? Bare Ground in Herb Stratum: 85 Remarks: "Bare ground" was duff/leaf lit t er. *Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version SOII Sampling Point: 42A Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Depth Matrix Redox Features (inches) Color (moist) % Color (moist) "/o Type I Loc2 Texture Remarks 0-310YR 3/2 100% Loam 3-6 10YR 5/1 90% 10YR 314 SO% C M Loam 6-8 10YR 8/2 80% 10YR 5/6 20% C M Clay Loam 8-20 10YR 7/2 60% IOYR 5/6 40% C M Loamy Sand 'Type: C=Concentration. D=Depletion, RM=Redu ced Matrix, CS=Covered or Coated Sand Grains 2Location: PL=Pore Lining. M=Matrix Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric soils:3 ❑ Histosol (Al) ❑ Sandy Redox (SS) [ 1 2 cm Muck (A10) Histic Epipedon (A2) ❑ Stripped Matrix (S6) ❑ Red Parent Material (TF2) Black Histic (A3) ❑ Loamy Mucky Mineral (Fl) (except in MLRA 1) ❑ Other (Explain in Remarks) Hydrogen Sulfide (A4) ❑ Loamy Gleyed Matrix (F2) ❑ Depleted Below Dark Surface (All) ❑ Depleted Matrix (F3) [ Thick Dark Surface (A12) ❑ Redox Dark Surface (F6) 3Indicators of hydrophytic vegetation and Sandy Muck Mineral (Sl) ❑ Depleted Dark Surface (F7) wetland hydrology must be present, ❑ Sandy Gleyed Matrix (S4) Redox depressions (FS) unless disturbed or problematic. f Restrictive Layer (If present): Type, Depth (inches): Hydric Soil Present? Yes No i•_ Remarks: Hydrology Wetland Hydrology Indicators: Primary Indicators (minimum of one required; check all that apply) Surface Water (Al) i. l Water-Stained Leaves (B9) (except MLRA High Water Table (A2) 1, 2, 4A, and 4B) Saturation (A3) ❑ Salt Crust (Bll) ❑ Water Marks (BS) L_L[ Aquatic Invertebrates (B13) Sediment Deposits (B2) L J Hydrogen Sulfide Odor (CS) ❑ Drift deposits (83) ❑ Oxidized Rhizospheres on Living Roots (0) Algal Mat or Crust (B4) L] Presence of Reduced Iron (C4) ❑ Iron Deposits (B5) ❑ Recent Iron Reduction in Tilled Soils (C6) ❑ Surface Soil Cracks (B6) [ Stunted or Stressed Plants (Dl) (LRR A) ❑ Inundation Visible on Aerial Imagery (B7) ~ Other (Explain in Remarks) ❑ Sparsely Vegetated Concave Surface (B8) Field Observations: Surface Water Present? Yes 0 No Depth (inches): Water Table Present? Yes No Depth (inches): Saturation Present? Wetland Hydrology Present? Yes * No (includes capillary fringe) Yes No Depth (inches): - Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available: Remarks: LANDOWNER SAYS AREA IS SATURATED EARLIER IN SPRING AND SURFACE WATER IS PRESENT WHEN SNOWFALL IS GREATER. AREA HAS BEEN GETTING DRIER DUE TO LODGEPOLE PINE GROWTH AND PROLIFERATION. Secondary Indicators (minimum of two required) Water-Stained Leaves (B9) (MLRA 1, 2, 4A, and 4B) ❑ Drainage Patterns (B10) ❑ Dry Season Water Table (C2) Saturation Visible on Aerial Imagery (C9) ❑ Geomorphic Position (D2) ❑ Shallow Aquitard (D3) ❑ FAC-neutral Test (135) ❑ Raised Ant Mounds (136) (LRR A) ❑ Frost Heave Hummocks (D7) • US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version 0 WETLAND DETERMINATION DATA FORM - Western Mountains, Valleys, and Coast Region Project/Site: DESCHUTES LWI City/County: SUNRIVER/DESCHUTES Sampling Date: 25-Jun-10 ppnNa DESCHUTES COUNTY SIGEER, SARAH HARTUNG Section, Township, Range: g State: OR T Sampling Point: SP 43A 20S R l0E Investigator(s): Landform (hillslope, terrace, etc.): Floodplain Local relief (concave, convex, none): flat Slope: 0.0% / 0.0 ° Subregion (LRR): LRR A Lat.: 43.7995 Long.: -121.5009 Datum: NAD83 Soil Map Unit Name: Not available NWI classification: Are climatic/ hydrologic conditions on the site typical for this time of year? Yes * No 0 (If no, explain in Remarks.) Are Vegetation ❑ , Soil ❑ , or Hydrology ❑ significantly disturbed? Are "Normal Circumstances" present? Yes No - AreVegetation J , Soil , or Hydrology I I naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transects, important features, et • E Hydrophytic Vegetation Present? Yes No Is the Sampled Area Hydric Soil Present? Yes NO Wetland Hydrology Present? Yes No - within a Wetland? Yes No Remarks: OFF-SITE DETERMINATION VEGETATION - Use scientific names of plants. Dominant Species? Absolute Re1.Strat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: ) % Cover Cover Status N b f D i t S i 1. 0 0.0°k um er o om nan pec es That are OBL, FACW, or FAC: 2 (A) 2. 0 ❑ 0.0% 3 0 ❑ 0 0% Total Number of Dominant , . Species Across All Strata: 2 (B) 4. 0 0.0% 0 = Total Cover Percent of dominant Species o 0% (A/B) 100 Sapling/Shrub Stratum (Plot size: ) . That Are OBL, FACW, or FAC: 1 Salix exigua 60 85.7% 08L Prevalence index worksheet: 2, Alnus incana 10 ❑ 14.3 FACW Total % Cover of: Multiply by: 3. o., ❑ 0.0% oBL species 130 x 1 = 130 4. 0 1 1 0.0% FACW species 30 x 2 = 60 5. 0 ❑ 0.0% - U FAC species 0 x 3 - Total Cover 5 20 FACU species x 4 = Herb Stratum (Plot size: ) 0 Carex aquatllis 1 70 J 73.7% 0131- - UPL species x S = . 2. luncus sp. 15 1_J 15,80k FACW column Totals: 165 (A) 210 (B) 7araxacum officinale 3 5 ❑ 5.3% FACU Prevalence Index = B/A = 1.273 . 4 Ranunculus sp. 5 5.3% FAC1N Hydrophytic Vegetation Indicators: 5 0 0.0% ~J Dominance Test is a 50% 6 0 ❑ 0.0% d Prevalence Index is $3.01 7, 0 ❑ 0.0% ` Morphological Adaptations 1 (Provide supporting El 8 0 0.0% data in Remarks or on a separate sheet) 9. 0 ❑ 0.0% 1 ~ Wetland Non-Vascular Plantsl 70. 0 IL I 0.0% ❑ Problematic Nydrophytic Vegetations (Explain) 11. o ❑ o.o% 95 =Total Cover 11ndicators of hydric soil and wetland hydrology must be present, unless disturbed or problematic. Woody Vine Stratum (Plot size: ) 1. 0 LJ 0.0% 2. 0 0.0% Hydrophytic 0 = Total Cover Vegetation Yes No Present? % Bare Ground in Herb Stratum: 0 Remarks: ]uncus sp. and Ranunculus sp. assumed FACW. *Indicator suffix = National status or professional decision assigned because Regional status not defined by FW S US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version soil Sampling point. 43A Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Depth Matrix Redox Features (inches) Color (moist) % 1 Color (moist) % Type Loc_ Texture Remarks„ tType: C=Concentration. D=Depletion. RM=Reduced Matrix, CS=Covered or Coated Sand Grains =Loca tion: PL=Pore Lining. M=Matrix Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils:3 ❑ Histosol (Al) ❑ Sandy Redox (S5) ❑ 2 cm Muck 010) ❑ Histic Epipedon (A2) ❑ Stripped Matrix (S6) ❑ Red Parent Material (TF2) [.J Black Histic (A3) ❑ Loamy Mucky Mineral (Fl) (except in MLRA 1) Other (Explain in Remarks) ❑ Hydrogen Sulfide (A4) ❑ Loamy Gleyed Matrix (F2) ❑ Depleted Below Dark Surface (All) ❑ Depleted Matrix (F3) F Thick Dark Surface (A12) Redox Dark Surface (F6) 3Indicators of hydrophytic vegetation and ❑ Sandy Muck Mineral (Sl) LJ Depleted Dark Surface (F7) wetland hydrology must be present, [ ] Sandy Gleyed Matrix (S4) ❑ Redox depressions (F8) unless disturbed or problematic. Restrictive Layer (if present): Type: Depth (inches): Hydric Soil Present? Yes No C-) Remarks: SOILS ASSUMED HYDRIC BY SATURATION Hydrology Wetland Hydrology Indicators: Primary Indicators (minimum of one required; check all that apply) Secondary Indicators (minimum of two required) L Surface Water (Al) ❑taater-Stained Leaves (B9) (except MLRA ❑taater-Stained Leaves (89) (MLRA 1, 2, ❑ High Water Table (A2) 1, 2, 4A, and 4B) 4A, and 4B) ❑ Saturation (A3) ❑ Salt Crust (Bll) ❑ Drainage Patterns (B10) Water Marks (Bl) ❑ Aquatic Invertebrates (B13) ❑ Dry Season Water Table (C2) Sediment Deposits (B2) ❑ Hydrogen Sulfide Odor (Cl) ❑ Saturation Visible on Aerial Imagery (0) ❑ Drift deposits (83) ❑ Oxidized Rhizospheres on Living Roots (0) ❑ Geomorphic Position (132) ❑ Algal Mat or Crust 04) Presence of Reduced Iron (C4) Shallow Aquitard (D3) ❑ Iron Deposits (B5) ❑ Recent Iron Reduction in Tilled Soils (C6) `l FAC-neutral Test (DS) Surface Soil Cracks (B6) [ . Stunted or Stressed Plants (Dl) (LRR A) ~ _.1 Raised Ant Mounds (136) (LRR A) ❑ Inundation Visible on Aerial Imagery (B7) ❑ Other (Explain in Remarks) ❑ Frost Heave Hummocks (D7) ❑ Sparsely Vegetated Concave Surface (B8) Field Observations: Surface Water Present? Yes C-) No * Depth (inches): Water Table Present? Yes 0 No C~) Depth (inches): Saturation Present? Wetland Hydrology Present? Yes No (includes capillary frinqe) Yes ('P) No Depth (inches); 0 - Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available: Aerial photo Remarks: SATURATION SEEN WITH BINOCULARS US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version WETLAND DETERMINATION DATA FORM - Western Mountains, Valleys, and Coast Region Project/site: DESCHUTES LWI City/County: SUNRIVER/DESCHUTES Sampling Date: 25-Jun-lo Applicant/owner: DESCHUTES COUNTY State: OR Sampling Point: SP 45A Investigator(s): ALISON SIGLER, SARAH HARTUNG Section, Township, Range: S 26 T 20 S R 10 E Landform (hillslope, terrace, etc.): Floodplain Local relief (concave, convex, none): concave Slope: 0.0% / 0.09 Subregion (LRR): LRR A Lat.: 43.8094 Long.: -121.4946 Datum. NAD83 Soil Map Unit Name: Not available. NWI classification: PSSC Are climatic/ hydrologic conditions on the site typical for this time of year? Yes No (If no, explain In Remarks.) Are Vegetation Soil F_ or Hydrology F1 significantly disturbed? Are "Normal Circumstances" present? Yes 4) No U , Are Vegetation , Soil 1_1 , or Hydrology ❑ naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transects, important features, et [7 • Hydrophytic Vegetation Present? Yes n No0 Is the Sampled Area Hydric Soil Present? Yes ' No Yes * No Wetland Hydrology Present? Yes No within a Wetland? Remarks: OFF-SITE DETERMINATION VEGETATION - Use scientific names of plants. Dominant Species? Absolute Rel.Strat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: ► % Cover Cover Status ❑ Number of Dominant Species 1. 0 0.0% That are 08L, FACW, or FAC: 3 (A) 3 0 0 ❑ 0 Total Number of Dominant • . Species Across All Strata: 3 (8) 4. 0 1 0.0% Percent of dominant Species Sapling/Shrub Stratum (Plot size: ) 0 Total Cover - That Are OBL, FACW, or FAC: 100.0% (A/13) 1. Alnus incana 5 1/1 25.001. FACW Prevalence Index worksheet: 2. Salix exigua 15 V 75.0% OBL Total % Cover of: Multiply by 3. o ❑ 0.0% OBL species 15 x 1 - 15 4. 0 ❑ 0.0% = 8 0 FACw species 90 x 2 1, 5. 0 0.0% FAC species 0 x 3 0 20 = Total Cover 0 0 FACU species x 4 = ) Herb Stratum (Plot size: 1 Carex sp. 75 ~V1 88.2% FACW uPL species x 5 - • 2. Phalaris arundinacea 10 ❑ 11.8% FACW Column Totals: 105 (A) 195 (B) 3. 0 ❑ o.o% Prevalence Index = B/A = 1.857 4 0 0.0% Hydro p h 0 c Vegetation indicators: 5. 0 ❑ 0.0% n Dominance Test is a so% 6. 0 ❑ 0.0% Prevalence Index is 53.01 2 0 1 1 0.0% L J Morphological Adaptations 1(Provide supporting 8 0 l._.L 0.0% data In Remarks or on a separate sheet) 9. 0 I_I 0,0% ❑ wetland Non-Vascular Plantsl 10 0 ❑ 0.0% J Problematic Hydrophytic Vegetatlonl (Explain) 11. 0 0.0% 1Indicators of hydric soil and wetland hydrology must I 85 =Total Cover be present, unless disturbed or problematic. Woody Vine Stratum (P of size. ) 1. 0 ❑ 0.0% 2. 0 ❑ 0.0% Hydrophytlc t?on Total ,Cover Present. 0 Yes COQ No ( ) Presen "/o Bare Ground In Herb Stratum: 0 Remarks: Carex sp. assumed to be FACW. *Indicator suffix = National status or professional decision assigned because Regional status not defined by F WS US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version OI Sampling Point: 45A , Profile Description: (Describe to the depth needed to document the Indicator or confirm the absence of indicators.) Depth Matrix Redox Features (inches) Color (moist) "/o Color (moist) % Type1 Loc' Texture Remarks lType: C=Concentration. D=Depletion. RM=Reduced Matrix, CS=Covered or Coated Sand Grains 'Location: PL=Pore Lining, M=Matrix Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils:3 n Histosol (Al) 1-1 Sandy Redox (S5) 71 2 cm Muck (A10) F I Histic Epipedon (A2) Stripped Matrix (S6) I I Red Parent Material (TF2) ❑ Black Histic (A3) Loamy Mucky Mineral (Fl) (except in MLRA 1) C Other (Explain in Remarks) U Hydrogen Sulfide (A4) n Loamy Gleyed Matrix (F2) n Depleted Below Dark Surface (All) ❑ Depleted Matrix (F3) U Thick Dark Surface (A12) Redox Dark Surface (F6) ❑ De leted Dark Surface (F7) 3Indicators of hydrophytic vegetation and n Sandy Muck Mineral (Sl) p wetland hydrology must be present, Sandy Gleyed Matrix (S4) U Redox depressions (178) unless disturbed or problematic. Restrictive Layer (if present): Type: Depth (inches): Hydric Soil Present? Yes * No Remarks: SOILS ASSUMED HYDRIC BY SATURATION Hydrology Wetland Hydr ology Indicators: Primary Indicators (minimum of one required; check all that apply) Secondary Indicators (minimum of two required) U Surface Water (Al) ❑ Water-Stained Leaves (Bg) (except MLRA Water-Stained Leaves (B9) (MLRA 1, 2, n High Water Table (A2) 1, 2, 4A, and 4B) 4A, and 4B) Saturation (A3) ❑ Salt Crust (Bll) U Drainage Patterns (B10) U Water Marks (BS) Aquatic Invertebrates (B13) ❑ Dry Season Water Table (C2) ❑ Sediment Deposits (B2) F7 Hydrogen Sulfide Odor (Cl) L~ Saturation Visible on Aerial Imagery (C9) LJ Drift deposits (83) Oxidized Rhizospheres on Living Roots (0) [ ] Geomorphic Position (D2) Algal Mat or Crust (84) Presence of Reduced Iron (C4) F] Shallow Aquitard (133) Iron Deposits 05) Recent Iron Reduction in Tilled Soils (C6) FAC-neutral Test (D5) Surface Soil Cracks (B6) Stunted or Stressed Plants (DI) (LRR A) Raised Ant Mounds (D6) (LRR A) Inundation Visible on Aerial Imagery (B7) ❑ Other (Explain in Remarks) Frost Heave Hummocks (137) Sparsely Vegetated Concave Surface (88) Field Observations: Surface Water Present? Yes C) No Depth (inches): Water Table Present? Yes 0 No Depth (inches): Saturation Present? Wetland Hydrology Present? Yes * No . (includes capillary fringe) Yes No Depth (inches): 0 Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available: Remarks: US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version • WETLAND DETERMINATION DATA FORM - Western Mountains, Valleys, and Coast Region Project/Site: DESCHUTES LWI City/County: SUNRIVER/DESCHUTES Sampling Date: 25-Jun-10 41 Applicant/ Owner: DESCHUTES COUNTY State: OR Sampling Point: SP 46A Investigator(s): ALISON SIGLER, SARAH HARTUNG Section, Township, Range: 5 26 T 20.5 R 10 E Landform (hlllslope, terrace, etc.): Floodplain Local relief (concave, convex, none): flat Slope: 010% / 0.0 ° D3 Subregion (LRR): LRR A Lat.: 43.$044 Long.: -121.4946 Datum: NA Soil Map Unit Name: Not available NWI classification: PEM ime of year? Yes NO (If no, explain in Remarks.) Are climatic/ hydrologic conditions on the site typical for this t P Are Vegetation , Soil , or Hydrology significantly disturbed? pre "Normal Circumstances" present? Yes No Are Vegetation ',-l , Soil ❑ , or Hydrology ❑ naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transects, important features, et Hydrophytlc Vegetation Present? Yes No i Is the Sampled Area Ye No Hydr c Soil Present? s Yes J) No Wetland Hydrology Present? within a Wetland? Yes (i) No C) Remarks: OFF-SITE DETERMINATION VEGETATION - Use scientific names of plants. Dominant Species? Absolute Rel.Strat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: ) % Cover Cover Status Number of Dominant Species 1. 0 ❑ 070% That are OBL, FACW, or FAC: 1 (A) 2. 0 ❑ 0.0% 3 . 0 ❑ 0 0% Total Number of Dominant • . Species Across All Strata: 1.. (B) 4. 0 L-1 0.0% Percent of dominant Species Sapling/Shrub Stratum (Plot size: 0 ) = Total Cover ° That Are OBL, FACW, or FAC: 100.0 /a (A/8) 1. 0 ❑ 0.0% Prevalence Index worksheet-:- 2. 0 ❑ 0.0% Total % Cover of Multiply by: 3. 0 ❑ 0.0% oBL species 0 x 1= 0 4. 0 0.0% FAC, species 75 x 2 = 150 5. 0 ❑ 0.0% FAC species 10 x 3 = 30 0 = Total Cover 0 0 FACU species x 4 = Herb Stratum (Plot size: 0 0 1 Carex sp. 65 .5% FACW 76 x 5 UPI species . 10 11.8% FAC ❑ column Totals: 85 (A) 180 (B) 3. Juncus sp. 1o L-I 11.8% FACW Prevalence Index = B/A = 2.118 0 1 1 0.0% Hydrophytic Vegetation Indicators: 0 ❑ 0.0 h n Dominance Test is n 50% 0 0 ❑ 0.0 [~/f prevalence Index Is 53.0t 0 ❑ 0.0% Morphological Adaptations I (Provide supporting 8. 0 ❑ 0.0% data in Remarks or on a separate sheet) 0 ❑ 0.0% Wetland Non-Vascular Plantsl 10. 0 0 .0°h ❑ Problematic Hydrophytic Vegetation' (Explain) 0 ~ D ~ .0 85 =Total Cover 'Indicators of hydric soil and wetland hydrology must be present, unless disturbed or problematic. Woody Vine Stratum (Plot size: ) 1. D f 1 0.0% 2. 0 ( 0.00% Hydrophytic 0 - Total Cover Present? Vegetation Yes JO) No - • % Bare Ground in Herb Stratum: 0 Remarks: Carex sp, and Juncus sp. assumed to be FACW. Poa sp. assumed FAC. *Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version Spit Sampling Point: 46A Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Matrix Depth a ox Features (inches) Color (moist) % Color (moist) 0/6 Typel LOC2 Texture Remarks 1Type: C=Concentration, D=Depletion. RM=Reduced Matrix, CS=Covered or Coated Sand Grains =Loca tion: PL=Pore Lining. M=Matrix Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils:3 n Histosol (Al) F-1 Sandy Redox (55) 1 2 cm Muck (A10) Histic Epipedon (A2) JJ Stripped Matrix (S6) ~.._.f Red Parent Material (TF2) ❑ Black Histic (A3) Loamy Mucky Mineral (Fl) (except in MLRA 1) 1/1 Other (Explain in Remarks) ❑ Hydrogen Sulfide (A4) LJ Loamy Gleyed Matrix (F2) U Depleted Below Dark Surface (All) FJ Depleted Matrix (F3) n Thick Dark Surface (A12) Redox Dark Surface (F6) 3 Indicators of hydrophytic vegetation and Sandy Muck Mineral (Sl) Depleted Dark Surface (F7) wetland hydrology must be present, ❑ Sandy Gleyed Matrix (S4) ❑ Redox depressions (FB) unless disturbed or problematic. Restrictive Layer (if present): Type: Depth (inches): Hydric Soil Present? Yes No C) Remarks: SOILS ASSUMED HYDRIC BY SATURATION Hydrology Wetland Hydrology Indicators: Primary Indicators (minimum of one required; check all that apply) Secondary Indicators (minimum of two required) Surface Water (Al) ❑ Water-Stained Leaves (Bg) (except MLRA J Water-Stained Leaves (Bg) (MLRA 1, 2, ❑ High Water Table (A2) 1, 2, 4A, and 4B) 4A, and 4B) n Saturation (A3) [J Salt Crust (Bll) U Drainage Patterns (B10) Water Marks (Bl) ❑ Aquatic invertebrates (813) ❑ Dry Season Water Table (C2) ❑ Sediment Deposits (B2) n Hydrogen Sulfide Odor (Cl) ❑ Saturation Visible on Aerial Imagery (C9) I[ Drift deposits (B3) Oxidized Rhizospheres on Living Roots (0) Geomorphic Position (D2) Algal Mat or Crust (B4) Presence of Reduced Iron (C4) Shallow Aquitard (133) Iron Deposits (B5) Recent Iron Reduction in Tilled Soils (C6) J FAC-neutral Test (D5) ] Surface Soil Cracks (B6) Stunted or Stressed Plants (Dl) (LRR A) L.] Raised Ant Mounds (D6) (LRR A) U Inundation Visible on Aerial Imagery (B7) Other (Explain in Remarks) ❑ Frost Heave Hummocks (D7) Sparsely Vegetated Concave Surface (B8) Field Observations: Surface Water Present? Yes No Depth (inches): Water Table Present? Yes No Depth inches : Saturation Present? - - Wetland Hydrology Present? Yes NO Depth (inches); 0 (includes capillary fringe) Yes * No C) Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available Aerial photo SATURATION SEEN WITH BINOCULARS • • US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version WETLAND DETERMINATION DATA FORM - Western Mountains, Valleys, and Coast Region Project /Site: DESCHUTES LWI City/County: SUNRIVER/DESCHUTES Sampling Date: 09-Aug-10 . Applicant/Owner: DESCHUTES COUNTY State: OR Sampling Point: SP 47A Investigator(s): ndra Capretti Section, Township, Range: S 15 T 22S R.10 E Landform (hillslope, terrace, etc.): Valley bottom Local relief (concave, convex, none): flat Slope: 1.0% / 0.6 ° Subregion (LRR): LRR A Lat.: 43.6603 Long.: -121.5117 Datum: NAD83 Soil Map Unit Name:,29k Cryacipolls, Q to 3.mrcent slopes, NWI classification: PEMC Are climatic/ hydrologic conditions on the site typical for this time of year? Yes No 0 (If no, explain in Remarks.) Are Vegetation , Soil , or Hydrology I I significantly disturbed? Are "Normal Circumstances" present? Yes No 0 Are Vegetation ❑ , Soil ❑ , or Hydrology ❑ naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transacts, important features, et Hydrophytic Vegetation Present? Yes (P) No ( ) Is the Sampled Area Hydric Soil Present? Yes No . - Wetland Hydrology Present? Yes No within a Wetland? Yes * No ~ Remarks: OFF-SITE DETERMINATION, SOIL PIT EXCAVATED IN THE ROAD RIGHT-OF-WAY AND REPRESENTS SITE CONDITIONS. VEGETATION - Use scientific names of plants. Dominant Species? Absolute Rel.Strat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: ) % Cover Cover Status ❑ Number of Dominant Species 1, 0 0,0% That are OBL, FACW, or FAC: 1 (A) 2, 0 L.I 0.0% I 3 0 0 0% Total Number of Dominant • . ° Species Across All Strata: 1 (B) 4. 0 0.0% Percent of dominant Species Sapling/Shrub Stratum (Plot size: ) 0 = Total Cover ° That Are OBL, FACW, or FAC: 100.0% (A/B) 1 • 0 0.0% prevalence Index worksheet: 2. 0 L l 0.0% Total % Cover of: Multiply by 3. 0 71 0.0% o6L species 0 x 1- 0 4. o 17 0..0% FACW species 0 X 2 - 0 5. 0 i.. 0.0% FAC species 100 x 3 - 300 0 = Total Cover 0 0 FACU species x 4 - Herb Stratum (Plot size: ) 0 0 R i 10 ❑ 10 0% FAC , x 5 - UPL species umex cr spus 1 . 2. Hordeum Iubatum 10 ❑ 10.0% FAC Column Totals: 100 (q) 300 (B) mus cinereus 3. EIy 80 n 80.00/° FAC Prevalence Index - - 8 A - 3.000 / - 4 0 0.0%° Hydrophytic Vegetation Indicators: 5. 0 ❑ 0.0% U Dominance Test is n 50% 6. 0 ❑ 0.0% Prevalence Index is 53.01 7. 0 ❑ 0.0% 0 Morphological Adaptations I (Provide supporting 8 0 F 0.0% data in Remarks or on a separate sheet) 9. 0 I_I 0.0% ] Wetland Non-Vascular Plants' 10: 0 f. _l 0.e% Hydrophytic Vegetation' (Explain) 11. ❑ ° 0.0 % 'Indicators of hydric soil and wetland hydrology must Pl d i S i 100 = Total Cover be present, unless disturbed or problematic. tratum ( Woo y V ne at s ze: ) 0 . 7 0.0% 2, 0 ❑ 0.0% Hydrophytic 0 Total Cover Vegetation Present? Yes No % Bare Ground in Herb Stratum: 0 _ Remarks: *Indicator suffix = National status or professional decision assigned because Regional status not de fined by FWS US Army Corps of Engineers Wester n Mountains, Valleys, and Coast Region Interim version SP 47A Soil Sampling Point: . Profile Depth Description- (Describe Matrix the depth needed to document the indicator or confirm the absence of indicators.) Redox Features (inches) Color (moist) o/v color (moist) % Types Loc2 Texture Remarks lOYR 3/2 100/° Silt Loam root mass 0-6 6-18 10YR 3/2 100% Silty Clay Loam IType: C=Concentration. D=Depletion. RM=Reduced Matrix, CS=Covered or Coated Sand Grains zLocation: PL=Pore Lining. M=Matrix Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils:3 ❑ Histosol (Al) ❑ Sandy Redox (S5) ❑ 2 cm Muck (A10) Histic Epipedon (A2) ❑ Stripped Matrix (S6) ❑ Red Parent Material (TF2) Black Histic (A3) ❑ Loamy Mucky Mineral (Fl) (except in MLRA 1) U Other (Explain in Remarks) ❑ Hydrogen Sulfide (A4) ❑ Loamy Gleyed Matrix (F2) ❑ Depleted Below Dark Surface (All) LJ Depleted Matrix (F3) Ll Thick Dark Surface (A12) ❑ Redox Dark Surface (F6) ❑ De leted Dark Surface (F7) 3Indicators of hydrophytic vegetation and Sandy Muck Mineral (51) p wetland hydrology must be present, Sandy Gleyed Matrix (S4) Redox depressions (F8) unless disturbed or problematic. Restrictive Layer (if present): Type: Depth (inches): Hydric Soil Present? Yes No Remarks: ASSUMED HYDRIC SOILS BASED ON PRIMARY WETLAND INDICATOR AND HYDROPHYTIC VEGETATION. Hydrology wetland Hydrology Indicators: Primary Indicators (minimum of one required; check all that apply) Secondary Indicators (minimum of two required) Surface Water (Al) A Water-Stained Leaves (89) (except MLRA ~ Water-Stained Leaves (139) (MLRA 1, 2, High Water Table (A2) 1, 2, 4A, and 4B) 4A, and 4B) Saturation (A3) ❑ Salt Crust (811) ❑ Drainage Patterns (1310) 1/1 Water Marks (B1) Aquatic Invertebrates (813) ❑ Dry Season Water Table (C2) ❑ Sediment Deposits (132) i 1 Hydrogen Sulfide Odor (0) ❑ Saturation visible on Aerial Imagery (C9) ❑ Drift deposits (133) 1 Oxidized Rhizospheres on Living Roots (0) Geomorphic Position (132) Algal Mat or Crust (134) I_I Presence of Reduced Iron (C4) Shallow Aquitard (D3) ❑ Iron Deposits (135) Recent Iron Reduction in Tilled Soils (C6) ❑ FAC-neutral Test (D5) ❑ Surface Soil Cracks (136) L. f Stunted or Stressed Plants (Dl) (LRR A) ❑ Raised Ant Mounds (136) (LRR A) ❑ Inundation Visible on Aerial Imagery (137) Other (Explain in Remarks) ❑ Frost Heave Hummocks (07) ❑ Sparsely Vegetated Concave Surface (138) Field Observations: Surface Water Present? Yes - No Depth (inches): Water Table Present? Yes C) No Depth (inches): Saturation Present? - Wetland Hydrology Present? Yes No (includes capillary fringe)-.. Yes - No Depth (Inches): Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available: Remarks: WATER MARKS ON VEGETATION • US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version WETLAND DETERMINATION DATA FORM - Western Mountains, Valleys, and Coast Region Project/Site: DESCHUTES LWI City/County: SUNRIVER/DESCHUTES Sampling Date: 10-Aug-10 State: OR Sampling Point: 5P 49A Applicant/Owner: COUNTY n, Towns Investigator(s): Alessandro Capreto Section, Township, Range: S 27 T 22 S R 10 E Landform (hillslope, terrace, etc.): Valley bottom Local relief (concave, convex, none): flat Slope: 0.0% / 0.0 ° Subregion (LRR): LRR A Lat.: 43.6326 Long.: -121.5146 Datum: NAD83 Soil Map Unit Name: 29A: CryaQu0115, ,0 to 3 percent 519pe5 NWI classification: P~MF . . Are climatic/ hydrologic conditions on the site typical for this time of year? Yes 4) No (If no, explain in Remarks.) Are Vegetation ❑ , Soil ❑ , or Hydrology ❑ significantly disturbed? Are "Normal Circumstances" present? Yes * No Are Vegetation ❑ , Soil ❑ , or Hydrology naturally problematic? (If needed, explain any answers In Remarks.) Summary of Findings - Attach site map showing sampling point locations, transects, important features, et r~ • Hydrophytic Vegetation Present? Yes NO Is the Sampled Area Hydric Soil Present? Yes No C.) within a Wetland? Yes * NO Wetland Hydrology Present? Yes No 0 Remarks: OFF-SITE DETERMINATION, SOIL PIT EXCAVATED IN THE ROAD RIGHT-OF-WAY AND REPRESENTS SITE CONDITIONS. 1, 0 ❑ 0.0% 2. 0 ❑ 0.0% Hydrophytlc Vegetation 0 = Total Cover Present? Yes * No VEGETATION - Use scientific names of plants. Dominant Species? Absolute Rel.Strat. Indicator I Dominance Test worksheet: Tree Stratum (Plot size: ) % Cover Cover Status Number of Dominant Species 1. 0 ❑ o.o% That are 08L, FACW, or FAC: 1 (A) 2. 0 ❑ 0.0% Total Number of Dominant 3, 0 . 0.0% Species Across All Strata: 1 (B) 4. 0 0.0% o - Total Cover - Percent o Species 100 0 % (A113) Sapling/Shrub Stratum (Plat size: ) . That Are OBL, FACW, or FAC: 1_ 0 ❑ 0.0% Prevalence Index worksheet: 2. 0 ❑ 0.0% Total % Cover of: Multiply by: 3. 0 ❑ 0.0% ORL species 0 x 1- 0 4. 0 ❑ 0,0% FACW species 0 x 2- 0 5. 0 0.0% FAC species 100 x 3 = 300 o. = Total Cover 0 0 FACU species x 4 Herb Stratum (Plot size: ) 0 0 R i 10 ❑ 10 0% FAC x 5 = UPL species 1 umexcr spus , - 100 300 (a) 2. Hordeum jubatum 10 ❑ 10.0% FAC (A) Column Totals: Elymus cinereus 80 n 80.0% FAC Prevalence Index = B/A = 3.000 4. 0 0.0°h Hydrophytic Vegetation Indicators: 5 0 0.0%° U Dominance Test is a 504/0 6. 0 ❑ 0.0% L VI Prevalence index is 53.01 7. 0 [ ..._I 0.0% ~ Morphological Adaptations' (Provide supporting ~ 8• 0 El 0.0°% n data in Remarks or on a separate sheet) 9. 0 1 I 0.0% ❑ Wetland Non-Vascular Plants' 1~• a L] o.o°° ❑ Problematic Hydrophytic Vegetation' (Explain) 11, o ❑ o.o°r° 'Indicators of hydriC soil and wetland hydrology must 100 = Total Cover be present, unless disturbed or problematic. Woody Vine Stratum (Plot size: ) % Bare Ground in Herb Stratum: 0 Remarks: *Indicator suffix = National status or professional decision assigned because Regional status not defined by FW5 US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version Soil Sampling Point: SP 49A Profile Description: (Describe to the d i epth needed to document the indicator or confirm the absence of indicators.) Matrix Depth Redox Features (inc ) hes Color (moist) G/o I Color (moist) °/a Type Loci Texture Remarks u 0-8 10YR 3/1 100/o Silt Loam 8-12 lOYR 3/2 100% Silty Clay Loam 12-18 10YR 3/2 100% Silty Clay Loam IType: C=Concentration. D=Depletion. RM=Redu ced Matrix, CS=Covered or Coated Sand Grains zLoca tion: PL=Pore Lining. M=Matrix Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Solls:3 Histosol (Al) ❑ Sandy Redox (S5) 2 cm Muck (A10) ❑ Histic Epipedon (A2) ❑ Stripped Matrix (S6) Red Parent Material (TF2) ❑ Black Histic (A3) ❑ Loamy Mucky Mineral (F1) (except in MLRA 1) ] Other (Explain in Remarks) ❑ Hydrogen Sulfide 04) ❑ Loamy Gleyed Matrix (F2) ❑ Depleted Below Dark Surface (All) ❑ Depleted Matrix (173) Thick Dark Surface A12 ( ) ❑ Redox Dark Surface (F6) 3 Indicators of hydrophytic vegetation and ❑ Sandy Muck Mineral (SS) ❑ Depleted Dark Surface (F7) wetland hydrology must be present, Sandy Gleyed Matrix (S4) Redox depressions (F8) unless disturbed or problematic. Restrictive Layer (if present): Type: Depth (inches): Hydric Soil Present? Yes * No Remarks: ASSUME HYDRIC SOILS BASED ON WETLAND HYDROLOGY AND HYDROPHYTIC VEGETATION. Hydrology Wetland Hydrology Indicators: Primary Indicators (minimum of one required; check all that apply) Secondary Indicators (minimum of two required) dl Surface Water (Al) ❑Water-Stained Leaves (69) (except MLRA ❑Water-Stained Leaves (89) (MLRA 1, 2, W High Water Table (A2) 1, 2, 4A, and 413) 4A, and 4B) Saturation (A3) ❑ Salt crust (BSI) ❑ Drainage Patterns (B10) Water Marks (Bl) Aquatic Invertebrates (B13) ❑ Dry Season Water Table (C2) ❑ Sediment Deposits (B2) _ Hydrogen Sulfide Odor (Cl) ❑ Saturation Visible on Aerial Imagery (C9) Drift deposits (B3) ❑ Oxidized Rhizospheres on Living Roots (0) ❑ Geomorphic Position (D2) ❑ Algal Mat or Crust (84) ~J Presence of Reduced Iron (C4) Shallow Aquitard (D3) [ 7 Iron Deposits (BS) !J Recent Iron Reduction in Tilled Soils (C6) ❑ FAC-neutral Test (135) Surface Soil Cracks (B6) I ~ Stunted or Stressed Plants (Dl) (LRR A) Raised Ant Mounds (D6) (LRR A) Inundation Visible on Aerial Imagery (B7) ❑ Other (Explain in Remarks) Frost Heave Hummocks (137) ❑ Sparsely Vegetated Concave Surface (B8) Field Observations: Surface Water Present? Yes No Depth (inches): Water Table Present? Yes NO Depth inches : 9 Wetland Hydrology Present? Yes No Saturation Present? LOLL (includes capillary fringe) Yes No C) Depth (inches): Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available: Remarks; WATER IN CHANNELS US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version WETLAND DETERMINATION DATA FORM - Western Mountains, Valleys, and Coast Region Project/Site: DESCHUTES LWI City/County: SUNRIVER/DESCHUTES Sampling Date: 10-Aug-10 Applicant/Owner: DESCHUTES COUNTY State: OR Sampling Point: SP SOA • Investigator(s): Alessandra Capretti Section, Township, Range: S 27 T 22 5 R 10 E Landform (Y 1.0% / 0.6 ° hillslope, terrace, etc.): Valley bottom Local relief (concave, convex, none): flat Slope: Subregion (LRR) Datum: NAD83 : LRR A Lat.. 43.6436 Long.: 121.5201 Soil Map Unit Name: 29A; CrvaQU9tls, 0 to 3 Percent slopes NWI classification: PIMA . Are climatic/ hydrologic conditions on the site typical for this time of year? Yes * No (If no, explain in Remarks.) Are Vegetation ❑ , Soil , or Hydrology ❑ significantly disturbed? Are "Normal Circumstances" present? Yes No AreVegetation , Soil or Hydrology ~ I naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transacts, important features, et Hydrophytic Vegetation Present? Yes J-) No 0 Is the Sampled Area Hydric Soil Present? Yes No within a Wetland? Yes • No Wetland Hydrology Present? Yes No C ) Remarks: Two 8 inch culverts under highway and running water. Soil disturbed from road construction and past filling events. On-site determination. VEGETATION - Use scientific names of plants. Dominant Species? Absolute ReLStrat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: ) % Cover - Cover Status Number of Dominant Species 1. 0 , 0.0% That are OBL, FACW, or FAC: 3 . (A) 2 0 0.0% . ❑ Total Number of Dominant 3. 0 0.0% Species Across All Strata: 3 (B) 4. 0 [ 0.0% Percent of dominant Species = Total Cover 100.0% (A/B) That Are 08L, FACW, or FAC: Sapling/Shrub Stratum (Plot size: ) 1. Salix geyeriana 5 100.09% FACW ksheet Prevalence 2. 0 [7. 0.0% / Cover o Multiply by: 3. 0 ❑ 0.0% 08L species 0 x 1= 0 4. 0 0.0% FACW species 60 x 2 = 120 5. 0 [ 0.0% FAC species 20.. x 3 = 60 5 = Total Cover FACU species 10 x 4 - 40 Herb Stratum (Plot size: ) UPL species 10 x 5 - 50 1. ]uncus effusus 40 F/I 42.1% FACW Column totals: 100 (A) 270 (e) 2. Equisetum hyemale 15 ❑ 15.8% FACW 3 Daucus carota 10 1 1 10.5% UPL Prevalence Index = B/A = 2.700 4 Elymus cinereus 20 U 21.1% FAC Hydrophytic Vegetation Indicators: 5 Festuca idahoensis 10 1 10.5% FACU 0 U Dominance Test is 7 50% 6 0 0% Prevalence index is 53.01 0 0 ❑ 0.0% l Morphological Adaptations I (Provide supporting 8 0 A i 0.0% data in Remarks or on a separate sheet) 9 0 1 1 0.0% _ ❑ Wetland Non-Vascular Plantsl . 10, 0 0.0% F ❑ Problematic Hydrophytic Vegetations (Explain) 0 u 0.0% 'Indicators of hydrlc soil and wetland hydrology must 95 = Total Cover be present, unless disturbed or problematic. Woody Vine Stratum (Plot size: ) - - 1. 0 0.0% 2. 0 0.0° ❑ Hydrophytic Vegetation Yes No 0 - Total Cover Present? Bare Ground in Herb Stratum: 5 Remarks: * Indicator suffix = National status or professional decision assigned because Regional status not d efined by FWS US Army Corps of Engineers Wester n Mountains, Valleys, and Coast Region Interim version Soil Sampling Pant: SP 50A. i Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Matrix Redeox Features Depth (inches) Color „ (mat) % Color (most) o " Type1 Loc= Texture Remarks 0- 18 IOYR 3/3 100% Silt Loam mostly road fill I Type: C=Concentration. D=Depletion. RM=Reduced Matrix, CS=Covered or Coated Sand Grains xLocation: PL=Po t re Lining. M=Matrix Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils:3 ❑ Histosol (Al) i. ~ Sandy Redox (S5) 2 cm Muck (A10) ❑ Histic Epipedon (A2) ❑ Stripped Matrix (S6) i Red Parent Material (TF2) L_1 Black Histic (A3) ❑ Loamy Mucky Mineral (FS) (except in MLRA 1) I'll Other (Explain in Remarks) ❑ Hydrogen Sulfide (A4) ❑ Loamy Gleyed Matrix (F2) ❑ Depleted Below Dark Surface (All) ❑ Depleted Matrix (F3) L_l Thick Dark Surface (A12) ❑ Sandy Muck Mineral (Sl) ❑ Redox Dark Surface (F6) 1. 1 Depleted Dark Surface (F7) 3Indicators of hydrophytic vegetation and etl nd h d l ❑ Sandy Gleyed Matrix (S4) ❑ Redox depressions (F8) w a y ro ogy must be present, unless disturbed or problematic. Restrictive Layer (If present): Type: ~ Depth (inches Hydric Soil Present? Yes * No ~ Remarks: Assume hydric soils based on wetland hydrology Hydrology Wetland Hydrology indicators: rs: Primary indicators (minimum of one required; check all that apply) Secondary Indicators (minimum of two required) V1 Surface Water (Ai) Ir ~ Water-Stained Leaves (89) (except MLRA I f Water-Stained Leaves (89) (MLRA 1, 2, U High Water Table (A2) 1, 2, 4A, and 4B) 4A, and 4B) Saturation (A3) Salt Crust (Bil) ❑ Drainage Patterns (B10) ❑ Water Marks (BI) _ Aquatic Invertebrates (B13) ❑ Dry season water Table (C2) ❑ Sediment Deposits (B2) Hydrogen Sulfide Odor (Cl) ❑ Saturation visible on Aerial Imagery (C9) ❑ Drift deposits (B3) ❑ Oxidized Rhizospheres on Living Roots (0) ❑ Geomorphic Position (D2) ❑ Algal Mat or Crust (B4) ❑ Presence of Reduced Iron (C4) ❑ Shallow Aquitard (D3) Iron Deposits (B5) I Recent Iron Reduction in Tilled Soils (06) FAC-neutral Test (DS) ❑ Surface Soil Cracks (86) Stunted or stressed Plants (D1) (LRR A) Raised Ant Mounds (D6) (LRR A) Inundation Visible on Aerial Imagery (B7) Other (Explain in Remarks) ❑ Frost Heave Hummocks (D7) ❑ Sparsely Vegetated Concave Surface (158) Field Observations: Surface Water Present? Yes (i) No U Depth (Inches): 6 Water Table Present? Yes No 0 Depth (inches): L 0 Saturation Present? Wetland Hydrology Present? Yes No (.L (includes capillary fringe) Yes NO Depth (inches): Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available: Remarks: WATER IN ROAD SIDE DITCH. DITCH RECEIVES OVERLAND FLOW/RUNOFF FROM ROAD. US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version WETLAND DETERMINATION DATA FORM - Western Mountains, Valleys, and Coast Region Project/Site: DESCHUTES LWI City/County: SUNRIVER/DESCHUTES Sampling Date: 10-Aug-10 Applicant/Owner: DESCHUTES COUNTY State: OR Sampling Point: SP 51A Investigator(s): Alessandra Capretti Section, Township, Range. S 27 T 22 S R 10 E Landform (hillslope, terrace, etc.): Valley bottom Local relief (concave, convex, none): flat Slope: 1.0% / 0.6 ° Subregion (LRR): LRR A Lat.: 43.6434 Long.: -121.5204 Datum: NAD83 Soil Map Unit Name: 29A: Cryao.U4119. 0 to 3 gerCent S.IQP25. NWI classification: PEMA Are climatic/ hydrologic conditions on the site typical for this time of year? Yes NO (If no, explain in Remarks.) Are Vegetation ! , Soil , or Hydrology significantly disturbed? Are "Normal Circumstances" present? Yes No Are Vegetation , Soil , or Hydrology naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transects, important features, et • .7 Hydrophytic vegetation Present? Yes NO Is the Sampled Area Hydric Soil Present? Yes NO ; 41) within a Wetland? Yes No Wetland Hydrology Present? Yes No Remarks: OFF-SITE DETERMINATION, SOIL PIT EXCAVATED IN THE ROAD RIGHT-OF-WAY TO REPRESENT NON-WETLAND CONDITIONS SOUTHWEST OF ROADWAY. VEGETATION - Use scientific names of plants. Dominant Species? Absolute Rel.Strat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: ) % Cover Cover Status Number of Dominant Species 1, ICI Pinus contorts 20 25.0% FAC 'That are 0131., FACW, or FAC: 2. Salix geyeriana 60l 75.0% FACW 4 (A) 3. 0 L 0.0% Total Number of Dominant Species Across All Strata: 5 (8) 4. 0 0.0% 80 = Total Cover Percent of dominant Species ° Sapling/Shrub Stratum (Plot size: ) That Are OBL, FACW, or FAC: 80.0 /o (A/13) 1. Salix geyeriana 2. Pinus contorta 3. 4. 5. Herb Stratum (Plot size: 1. Festuca idahoensis 2. 3. 4. 5. 6. 7. 8. 9. 10. 11. 5 71,4% FACW 2 28.6% FAC 0 0.0% .0 0.0% 0 C..1 0.0% 7 ) = Total Cover Woody Vine Stratum (Plot size: ) 1. % Bare Ground in Herb Stratum: p Remarks: 15 I1/I 100.0% FACU 0 L 0.0% 0 1 0.0% 0 =I 0.0% 0 . 0.0% 0 0.0% 0 0.0% 0 0.0% 0 0.0% 0 h 0.0% 0 _ 0.0% 15 = Total Cover 0 1 0.0% 0 0.0% 0 = Total Cover Prevalence Index worksheet: Total % Cover of: Multiply by; 0131. species 0 x 1 = 0 FACW species 65 x 2 = 130 FAC species 22 x 3 = 66 FACU species 15 x 4 = 60 UPL sped eS 0- - x 5 0 column Totals: 102 (A) 256 (13) Prevalence Index = 8/A = 2.510 Hydrophytic Vegetation Indicators: Dominance Test is n 50% Prevalence index is 53.01 Morphological Adaptations' (Provide supporting data in Remarks or on a separate sheet) _ Wetland Non-Vascular Plantsl -i Problematic Hydrophytic Vegetation' (Explain) 'Indicators of hydric soil and wetland hydrology must be present, unless disturbed or problematic. Hydrophytic Vegetation - Present? Yes' No' *Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version Soil Sampling Point: SP 51A Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Depth Matrix edox Features . (inches) Color (moist) % Color (moist) . % Type I Loc . Texture Remarks 3 10YR 3/3 10% Silt Loam with gravels 3-18 IOYR 3/3 100% Silt Loam with gravels 1Type: C=Concentration. D=Depletion. RM=Reduced Matrix, CS=Covered or Coated Sand Grains =Location: PL=Pore Lining. M=Matrix Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Solls:3 A Histosol (Al) F1 Sandy Redox (S5) F 1 2 cm Muck (A10) Histic Epipedon (A2) ❑ Stripped Matrix (S6) ❑ Red Parent Material (TF2) Black Histic (A3) ❑ Loamy Mucky Mineral (Fl) (except in MLRA 1) Other (Explain in Remarks) Hydrogen Sulfide (A4) ❑ Loamy Gleyed Matrix (F2) ❑ Depleted Below Dark Surface (All) ❑ Depleted Matrix (F3) ❑ Thick Dark Surface (A12) ❑ Redox Dark Surface (F6) 3Indicators of hydrophytic vegetation and ❑ Sandy Muck Mineral (Sl) L.J Depleted Dark Surface (F7) wetland hydrology must be present, Sandy Gleyed Matrix (S4) ❑ Redox depressions (F8) unless disturbed or problematic. Restrictive Layer (if present): Type: Depth (inches): Hydric Soil Present? Yes No Remarks: Hydrology Wetland Hydrology Indicators: Primary Indicators (minimum of one required; check all that apply) Secondary Indicators (minimum of two required) Surface Water (Al) Water-Stained Leaves (B9) (except MLRA ❑ Water-Stained Leaves (B9) (MLRA 1, 2, ❑ High Water Table (A2) 1, 2, 4A, and 4B) 4A, and 4B) ❑ Saturation (A3) ❑ Salt Crust (B11) ❑ Drainage Patterns (B10) ❑ Water Marks (Bl) Aquatic Invertebrates (B13) ❑ Dry Season Water Table (C2) Sediment Deposits (B2) Hydrogen Sulfide Odor (Cl) [ ] Saturation Visible on Aerial Imagery (C9) ❑ Drift deposits (B3) ❑ Oxidized Rhizospheres on Living Roots (0) Geomorphic Position (D2) ❑ Algal Mat or Crust (B4) J Presence of Reduced Iron (C4) J Shallow Aquitard (D3) ❑ Iron Deposits (BS) ❑ Recent Iron Reduction in Tilled Soils (C6) ❑ FAC-neutral Test (D5) r Surface Soil Cracks (B6) (_f Stunted or Stressed Plants (DS) (LRR A) ❑ Raised Ant Mounds (D6) (LRR A) ( J Inundation Visible on Aerial Imagery (B7) Other (Explain in Remarks) Frost Heave Hummocks (D7) ❑ Sparsely Vegetated Concave Surface (B8) Field Observations: Surface Water Present? Yes U No Depth (inches): Water Table Present? Yes No Depth (inches): ~ - Saturation Present? Yes No ! - Wetland Hydrology Present? Yes (2 No Depth (inches): (includes capillary fringe) Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available: Remarks: US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version WETLAND DETERMINATION DATA FORM - Western Mountains, Valleys, and Coast Region Project/Site: DESCHUTES LWI City/County: SUNRIVERZ/DESCHUTES Sampling Date: 10-Aug-10 40 Applicant/ Owner: DESCHUTES COUNTY State: OR Sampling Point- SP 52A Investigator(s): Alessandra Capretti Section, Township, Range: 5 27 T 22S R 10 E Landform (hillslope, terrace, etc.): Valley bottom Local relief (concave, convex, none): flat slope: 1.0% / 0.6 ° Datum. N Subregion (LRR): LRR A Lat.: 43.6354 Long.: -121.5161 AD83 Soil Map Unit Name: ZqA; Cryaouglls, 0. to 3 percent, sl9paS NWI classification: PA5,Fx Are climatic/ hydrologic conditions on the site typical for this time of year? Yes * No 0 (If no, explain in Remarks.) Are Vegetation ❑ , Soil , or Hydrology F -I significantly disturbed? Are "Normal Circumstances" present? Yes NO - Are Vegetation , Soil ] , or Hydrology LL naturally problematic? (If needed, explain any answers In Remarks.) Summary of Findings - Attach site map showing sampling point locations, transects, important features, et Hydrophytic Vegetation Present? Yes No (P) Is the Sampled Area Hydric Soil Present? Yes No within a Wetland? Yes - NO Wetland Hydrology Present? Yes NO Remarks: OFF-SITE DETERMINATION, SOIL PIT EXCAVATED IN ROAD RIGHT-OF-WAY. VEGETATION - Use scientific names of plants. Dominant Species? Absolute Rel.Strat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: % C er Status Cover ecies t S N b f D i a ov O 0°~ p um er o om n n That are OBL, FACW, or FAC: 0 (A) 2 0 L 1 0.0°ro . D 0 Total Number of Dominant 3 0 0.0 /u Species Across All Strata: 1. (B) 4. 0 11 0.0% Percent of dominant Species 0 = Total Cover 0.0% That Are OBL, FACW, or FAC: (A/6) Sapling/Shrub Stratum (Plot size: ) 1 0 ~ 0.0% - pre evalence Index x worksheet: 2, 0 0.0%.. Total % Cover of: Multiply by: 3, 0 n 0.0% OBL species 0 x 1= 0 4. 0 0.0% FACW species 0 x 2= 0 5. 0 0.0% FAC species 0 x 3 = 0. 0 = Total Cover FACU species 100 x 4 - 400 Herb Stratum (Plot size: ) 0 0 Festuca idahoensis 1 100 U 100.0%° FACU - x - UPIL . LL column Totals: 100 (A) ) 400 (a) column 2 . 0 o.o% 3. 0 7 0,0°r° Prevalence Index = B/A - 4.000 - 4. 0 n 0.0% Hydrophytic Vegetation Indicators: 5. 0 L~ 0.0% LL Dominance Test is 7 501/a 6 0 LL 0.0% Prevalence index is 53,01 7 0 f 0.0% LL Morphological Adaptations 1 (Provide supporting 8, 0 LL 0.0% data in Remarks or on a separate sheet) 9. 0 0 0.0 /o Wetland Non-Vascular Plantsl 10. 0 0 0.0% Problematic Hydrophytic Vegetation) (Explain) 71 LL O. . ° . 'Indicators of hydric soil and wetland hydrology must 100 =Total l Cover be present, unless disturbed or problematic. Woody Vine Stratum (Plot size: ) 1, 0 ❑ 0.0% 2 0 LL 0.o% Hydrophytic , 0 =Total Cover Vegetation . . Present? Yes No Q') % Bare Ground in Herb Stratum: 0 Remarks: is Pasture with horse and cattle grazing. Assessment area also looks like it is used as a hay crop. *Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version Soil Sampling Point: SP 52A Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Depth Matrix Redox Features (inches) Color (moi Color (moral) NO Type1 Loc2 Texture Remarks 3/2 1% 0-4 OYR . root mass Silt Loam I 4-18 10YR 3/2 100% Silt Loam TType: C=Concentration, D=Depletion. RM=Reduced Matrix, CS=Covered or Coated Sand Grains zLocation: PL=Pore Lining. M=Matrix Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils :3 ❑ Histosol (Al) n Sandy Redox (S5) ❑ 2 cm Muck (A10) ❑ Histic Epipedon (A2) ~.J Stripped Matrix (S6) ❑ Red Parent Material (TF2) ❑ Black Histic (A3) Loamy Mucky Mineral (Fl) (except in MLRA 1) Other (Explain in Remarks) ❑ Hydrogen Sulfide (A4) ❑ Loamy Gleyed Matrix (F2) ❑ Depleted Below Dark Surface (All) ❑ Depleted Matrix (F3) Thick Dark Surface (A12) Redox Dark Surface (F6) 3Indicators of hydrophytic vegetation and ❑ Sandy Muck Mineral (Sl) ❑ Depleted Dark Surface (F7) wetland hydrology must be present, Sandy Gleyed Matrix (S4) Redox depressions (FS) unless disturbed or problematic. Restrictive Layer (if present): Type: Depth (inches); Hydric Soil Present? Yes No Remarks: ASSUMED HYDRIC BASED ON HYDROLOGY Hydrology Wetland Hydrology Indicators: Primary Indicators (minimum of one required; check all that apply) Secondary Indicators (minimum of two required) . ILI Surface Water l) ❑ Water-stained Leaves (89) (except MLRA n Water-Stained 2 ater- ed Leaves (139) (MLRA 1 El H Table 4Aand 45) , , 413) n Saturation (A3) ❑ Salt Crust (811) ❑ Drainage Patterns (810) Water Marks (BI) L~ Aquatic Invertebrates (1313) ❑ Dry Season Water Table (C2) ❑ Sediment Deposits (132) n Hydrogen Sulfide Odor (Cl) ❑ Saturation Visible on Aerial Imagery (C9) Drift deposits (133) 1 1 Oxidized Rhizospheres on Living Roots (0) 1 1 Geomorphic Position (132) ❑ Algal Mat or Crust (134) 1 Presence of Reduced Iron (C4) I I Shallow Aquitard (D3) ❑ Iron Deposits (B5) I Recent Iron Reduction in Tilled Soils (06) ❑ FAC-neutral Test (DS) Surface Soil Cracks (136) Stunted or Stressed Plants (DS) (LRR A) ❑ Raised Ant Mounds (D6) (LRR A) ❑ Inundation Visible on Aerial Imagery (137) ❑ Other (Explain in Remarks) ❑ Frost Heave Hummocks (D7) Sparsely Vegetated Concave Surface (88) Field Observations: Surface Water Present? Yes C') No 0 Depth (inches): F:~ 6] Water Table Present? Yes NO (4') Depth inches : Saturation Present? Yes No i- Wetland Hydrology Present? Yes No 0 Depth (inches): (includes capillary fringe) Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available: Remarks: WATER IS DITCHED AND MOST LIKELY PIPED/ DITCHFD IN MOST PARTS OF THE ASSESSMENT AREA. US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version • WETLAND DETERMINATION DATA FORM - Western Mountains, Valleys, and Coast Region Project/Site: DESCHUTES LWI City/County: SUNRNER/DESCHUTES Sampling Date: 10-Aug-10 Applicant/Owner: DESCHUTES COUNTY State: OR Sampling Point: SP 53A Investigator(s): Alessandra Capretti Section, Township, Range: S 27 T 22S R 10 E Landform (hillslope, terrace, etc.): Valley bottom Local relief (concave, convex, none): flat Slope: 0.0% / 0.0 ° Subregion (LRR): LRR A Lat.: 43.6343 Long: -121.5156 Datum: NAD83 Soli Map Unit Name: 29A; CryapllolIs, Q.ts13 percent SloDe9 NWI classification: PEMC AlVege'taton hydrologic coil ionL~s on the sHydrology lt pfolr~this significantly I year? Yes No O (If no, explain in Remarks.) disturbed? Are "Normal Circumstances" present? Yes No 0 Are Are Vegetation , Soil [_.i or Hydrology [ ] naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transects, important features, et Hydrophytic Vegetation Present? Yes No Is the Sampled Area Hydric Soil Present? Yes No within a Wetland? Yes No Wetland Hydrology Present? Yes No Remarks: OFF-SITE DETERMINATION, SOIL PIT EXCAVATED IN THE ROAD RIGHT-OF-WAY AND REPRESENTS SITE CONDITIONS. VEGETATION - Use scientific names of plants. Dominant Species? Absolute Rel.Strat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: ) % Cover Cover Status Number of Dominant Species 1. 0 1 0.0% That are OBL, FACW, or FAC: 2 (A) 2 0 F-1 0.0% . 0 0% Total Number of Dominant 3. 0 . Species Across All Strata: 3 (B) 4. 0 ..I 0.0% Percent of dominant Species D Total Cover = , That Are OBL, FACW, or FAC: 66.7% (A/B) Sapling/Shrub Stratum (Plot size: ) . 1 0 0.0% Prevalence Index worksheet: 2. 0 U om% Total % Cover of: Multiply by: 3 a , 0.0% oBL species 0 x 1- 0 4. 0 l..~ 0.0% FACw species 50 x2- 100 5. 0 0.0% FAC species 20 x 3 - 60 0 = Total Cover FACU species 20 x 4 - 80 Herb Stratum (Plot size: ) 0 0 luncuseffusus 1 5o L I 55.6% FAC,W x 5 = uPL species 9 . 2. Festuca idahoensis 20 V1 22.2% FACU 0 (A) 240 (B) Column Totals: 3 Elymus cinereus 20 V] 22.2% FAC Prevalence Index = B/A = 2.667 4. 0 n 0,00% Hydrophytic Vegetation indicators. 5. 0 0.0% n Dominance Test is n 500% 6. 6 D 0.0% Prevalence Index is 53.01 f J 7. 0 0.0% ` Morphological Adaptations I (Provide supporting 0 L 0.0% - data in Remarks or on a separate sheet) 9 0 0.0% Wetland Non-Vascular Plants' 10. 0 ° o.o L] Problematic Hydrophytic Vegetatlonl (Explain) 11 0 1 0.0% . 'Indicators of hydric soil and wetland hydrology must 90 = Total Cover be present, unless disturbed or problematic. Woody Vine Stratum (Plot size: ) 1. 0 LJ 0.0% 2. 0 0.0°k Hydrophytic Vegetation No ( ) Yes 0 = Total Cover Present? Bare Ground in Herb Stratum: 10 Remarks: *Indicator suffix = National status or professional decision assigned because Regional status not d efined by FW5 US Army Corps of Engineers Wester n Mountains, Valleys, and Coast Region Interim version soil Sampling Point: $P 53A Profile Description. (Describe to the depth needed to document the Indicator or confirm the absence of indicators.) Matrix Depth Redox features /o (inches) Color (moist) o Types Lac= Color (moist) % ) Texture Remarks s / 100% Silt Loam roots 4-18 lOYR 3/1 100% with gravels Silt Loam IType: C=Concentration. D=Depletion. RM=Reduced Matrix, CS=Covered or Coated Sand Grains 2Location: PL=Pore Lining. M=Matrix Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Solls:3 Histosol (Al) Sandy Redox (SS) 12 cm Muck (A10) Histic Epipedon (A2) ❑ Stripped Matrix (S6) ❑ Red Parent Material (TF2) Black Histic (A3) ❑ Loamy Mucky Mineral (Fl) (except in MLRA 1) LVI Other (Explain in Remarks) Hydrogen Sulfide (A4) ❑ Loamy Gleyed Matrix (F2) ❑ Depleted Below Dark Surface (All) ❑ Depleted Matrix (F3) ❑ Thick Dark Surface (A12) ❑ Redox Dark Surface (F6) 3Indicators of hydrophytic vegetation and Sandy Muck Mineral (Sl) ❑ Depleted Dark Surface (F7) wetland hydrology must be present, Sandy Gleyed Matrix (S4) Redox depressions (F8) unless disturbed or problematic. Restrictive Layer (if present): Type: Depth (inches): Hydric Soil Present? Yes * No ) Remarks: ASSUMED HYDRIC SOILS BASED ON WETLAND HYDROLOGY INDICATORS AND HYDROPHYTIC VEGETATION Hydrology Wetland Hydrology Indicators: Primary Indicators (minimum of one required; check all that apply) Secondary Indicators (minimum of two required) Surface Water (Al) ❑ Water-Stained Leaves (B9) (except MLRA Water-Stained Leaves (B9) (MLRA 1, 2, n High Water Table (A2) 1, 2, 4A, and 48) 4A, and 48) Saturation (A3) ❑ Salt Crust (811) Drainage Patterns (B10) I ~ Water Marks (BI) ❑ Aquatic Invertebrates (B13) ❑ Dry Season Water Table (C2) ❑ Sediment Deposits (B2) ❑ Hydrogen Sulfide Odor (Cl) Saturation Visible on Aerial Imagery (Cg) Drift deposits (B3) ❑ Oxidized Rhizospheres on Living Roots (0) Geomorphic Position (D2) ❑ Algal Mat or Crust (84) ❑ Presence of Reduced Iron (C4) Shallow Aquitard (D3) ❑ Iron Deposits (BS) Recent Iron Reduction in Tilled Soils (C6) FAC-neutral Test (DS) ❑ Surface Soil Cracks (B6) ❑ Stunted or Stressed Plants (Dl) (LRR A) ❑ Raised Ant Mounds (D6) (LRR A) 7 Inundation Visible on Aerial Imagery (B7) ❑ Other (Explain in Remarks) ❑ Frost Heave Hummocks (D7) F-1 Sparsely Vegetated Concave Surface (B8) Field Observations: Surface Water Present? Yes (t) No Depth (inches): - Water Table Present? Yes r'> No C) Depth (inches): 0 Saturation Present? Wetland Hydrology Present? Yes No (includes capillary-fringe) Yes No ( Depth (Inches): Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available: Remarks: US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version WETLAND DETERMINATION DATA FORM - Western Mountains, Valleys, and Coast Region Project/Site: DESCHUTES LWI City/County: SUNRIVER/DESCHUTES Sampling Date: 10-Aug-10 . State: OR Sampling Point: SP 54A Applicant/ Owner: DESCHUTES COUNTY Investigator(s): Alessandra Capretti Section, Township, Range: S 27 T 22 S R 10 E Landform (hillslope, terrace, etc.): Valley bottom Local relief (concave, convex, none): flat slope: 1.0% / 0.6 ° Subregion (LRR): LRR A Lat.: 43.6333 Long.: -121.5151 Datum: NAD83 Soil Map Unit Name: 29A: Cncaguolls. 0 to 3 Percent slippers NWI classification: PEMF gni~ocfyan~ar?eS Are "Normal (If no, explain in Remarks.) AArelVegeita Vegetation conditions ion j on the sl forthistime or Hydrology sl y disturbed? Circumstances" present? Yes No 0 Are Vegetation I I , Soil or Hydrology I ~ naturally problematic? (If needed, explain any answers in Remarks.) Summarv of Findinas - Attach site map showing sampling point locations, transects, important features, et • • Hydrophytic Vegetation Present? Yes * NO - Is the Sampled Area Hydric Soil Present? Yes J) No - within a Wetland? Yes No Wetland Hydrology Present? Yes No 0 Remarks: OFF-SITE DETERMINATION, SOIL PIT EXCAVATED IN THE ROAD RIGHT-OF-WAY AND REPRESENTS SITE CONDITIONS. VEGETATION - Use scientific names of plants. Dominant Species? Absolute Rel.Strat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: ) °k cover Cover Status " Number of Dominant Species 1 0 ❑ 0.0°/o That are OBL, FACW, or FAC: 2 (A) 2 0 0.0% . Total Number of Dominant 3. 0 J 010% Species Across All Strata: 2 (B) 4. 0 ❑ 0.0% Percent of dominant Species 0 = Total Cover 100.0% That Are OBL, FACW, or FAC: (A/B) Sapling/Shrub Stratum (Plot size: ) 1 0 ❑ 0.0% Prevalence Index worksheet: 2. 0 ❑ o.00% Total % Cover of: Multiply by: 3 0 ❑ 0.0% oaL species 0 x 1- 0 4. 0.. ❑ 0.0% FACW species 0 x 2 - 0 5. 0 I 0.0% FAC species 100 x 3 = 300 0 = Total Cover FACU species 0 x 4- 0 Herb Stratum (Plot size: ) UPL species 0 x 5 - 1. Rumex crispus 10 ° ❑ 10.0% FAC 100 300 (a) Column Totals: (A) 2. Hordeum jubatum 20 20,0% AC 3 Elymus cmereus 70 F U 70.0% AC Prevalence Index = B/A = 3,000 4 0 ❑ 0.0% Hydrophytic Vegetation Indicators: 5. 0 [ 0.0°M n Dominance Test is n 50% 6. 0 ❑ 0.0% 1VJ Prevalence Index is 53.01 7 0 0.0% LJ Morphological Adaptations' (Provide supporting 8 0 71 0.0% data in Remarks or on a separate sheet) 0 J_L 0.0% Wetland Non-Vascular Plants' 10. 0 ❑ 0.0% L] Problematic Hydrophytic Vegetation' (Explain) 11 0 0.0% L . 'Indicators of hydric soil and wetland hydrology must 100 Total Cover be present, unless disturbed or problematic. Woody Vine Stratum (Plot size: ) 1. 0 ❑ 0.0% 2 0 71 0,0% Hydrophytic . Vegetation * N 0 = Total Cover o Present? Yes % Bare Ground in Herb Stratum: 0 Remarks: Active grazing. ' Indicator suffix - National status or professional decision assigned because Regional status not defined by FWS US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version Soil Sampling Point: 54A, . Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of Indicators.) Depth Matrix Redox Features (inc es) t Color ( oi % Color (moist) % Type' „Loci . Texture..... Remarks 0-B 3 /l OYR 100% 5 Silt Loam B-12 10YR 3/2 100"/v Silty Clay Loam . 12-18 10YR 3/2 100% Silty Clay Loam WITH COBBLES 'Type: C=Concentration. D=Depletion. RM=Reduced Matrix, CS=Covered or Coated Sand Grains zLocation: PL=Pore Lining. M=Matrix Hydric Soil Indicators: (Applicable to all LRRS, unless otherwise noted.) Indicators for Problematic Hydric Soils:3 L_I Histosol (Al) ❑ Sandy Redox (SS) 2 cm Muck (A10) Histic Epipedon (A2) L Stripped Matrix (S6) Red Parent Material (TF2) Black Histic (A3) n Loamy Mucky Mineral (Fl) (except in MLRA 1) Other (Explain in Remarks) Hydrogen Sulfide (A4) n Loamy Gleyed Matrix (F2) Depleted Below Dark Surface (All) Depleted Matrix (F3) ❑ Thick Dark Surface (A12) n Sandy Muck Mineral (Sl) Redox Dark Surface (F6) Depleted Dark Surface (F7) 3Indicators of hydrophytic vegetation and tl d h d l ❑ Sandy Gleyed Matrix (S4) ❑ Redox depressions (FB) we an y ro ogy must be present, unless disturbed or problematic. Restrictive Layer (if present): Type: Depth (inches): Hydric Soil Present? Yes * No ) Remarks: ASSUMED HYDRIC BASED ON WETLAND HYDROLOGY INDICATORS AND HYDROPHYTIC VEGETATION Hydrology Wetland r Hydrology Indicators: Primary Indicators (minimum of one required; check all that apply) U Surface Water (Al) n Water-Stained Leaves (B9) (except MLRA ❑ High Water Table (A2) 1, 2, 4A, and 4B) n Saturation (A3) n Salt Crust (B1 1) Water Marks (131) Aquatic Invertebrates (B13) ❑ Sediment Deposits (B2) ❑ Hydrogen Sulfide Odor (Cl) Drift deposits (B3) Oxidized Rhizospheres on Living Roots (0) L~ Algal Mat or Crust (B4) LJ Presence of Reduced Iron (C4) Iron Deposits (85) Recent Iron Reduction in Tilled Solis (C6) Surface Soil Cracks (B6) Stunted or stressed Plants (Dl) (LRR A) Inundation Visible on Aerial Imagery (B7) n Other (Explain in Remarks) n Sparsely Vegetated Concave Surface (BB) Secondary Indicators (minimum of two required) Water-Stained Leaves (B9) (MLRA 1, 2, 4A, and 4B) n Drainage Patterns (B10) Dry Season Water Table (C2) 'I Saturation Visible on Aerial Imagery (C9) Geomorphic Position (D2) ❑ Shallow Aquitard (D3) ❑ FAC-neutral Test (D5) ❑ Raised Ant Mounds (D6) (LRR A) ❑ Frost Heave Hummocks (D7) Field Observations: Surface Water Present? Yes No Depth (inches): L 6 Water Table Present? Yes NO Depth (inches): L_ 3 Saturation Present? Wetland Hydrology Present? Yes No (inclC_) Yes No Depth (inches): 0 udes capillary fringe) - _ Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available: • US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version 40 WETLAND DETERMINATION DATA FORM - Western Mountains, Valleys, and Coast Region Project/Site: DESCHUTE5 LWI City/County: SUNRIVER/DESCHUTES sampling Date: 10-Aug-10 Applicant/ Owner: DESCHUTES COUNTY State: OR Sampling Point: SP SSA • tnvestigator(s): Alessandra Capretti Section, Township, Range: 5 34 T 22S R 10 E Landform (hillslope, terrace, etc.): Valley bottom Local relief (concave, convex, none): flat slope: 1.0% / 0.6 0 Subregion (LRR): LRR A Lat.: 43.6290 Long.: -121.5129 Datum: NAD83 Soil Map Unit Name: 115A: Shanahan loamy CoorW Sand, low, o to 3 perCent slQpv5 NWI classification: PEMA Are climatic/ hydrologic conditions on the site typical for this time of year? Yes (P) No l) (If no, explain in Remarks.) Are Vegetation J , Soil Ll , or Hydrology significantly disturbed? Are "Normal Circumstances" present? Yes No Are Vegetation ❑ , Soil ❑ , or Hydrology JJ naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map s howing sampling point locations, transects, important features, et Hydrophytic Vegetation Present? Yes No (J) Is the Sampled Area Hydric Soil Present? Yes No Yes 0 No l.') Yes C) NO within a Wetland? Wetland Hydrology Present? Remarks: ESSIVE DOGS NEARBY MADE IT DIFFICULT TO ASSESS SAMPLE PLOT. LODGEPOLE PINES FORMED A DENSE G R OFF-SITE DETERMINATION. AG PATCH. VEGETATION - Use scientific names of plants. Dominant Species? for Dominance Test worksheet: Absolute Re l Strat Ind Tree Stratum (Plot size: I s 0 /o Cover Cover Status Number of Dominant Species 1. Pinus contorts 71/ 100.0% 20 AC . That are OBL, FACW, or FAC: 1 . (A) 2, ❑ 0.0% 0 ❑ Total Number of Dominant 1 3. 0.o% . . 0 Species Across All Strata: (B) 4. ° D / Percent of dominant Species 20 Cover Tota That Are OBL, FACW, or FAC 10.0% (A/13) 'Sapling/Shrub Stratum (Plot size: 1 1 0 ❑ D.00° Prevalence Index worksheet: 2 D ❑ 0.0 Po Total Cover of Multiply by: 3. 0 ❑ .0.0°Po OBL species 0 x 1- 0 4. 0 0.0% FACw species 0 x z 0 5. 0 ❑ 0.0%v FAC species 20 x 3 - 60 0 = Total Cover FACU species 0 x 4- 0 Herb Stratum (Plot size: ) 0 0 UPL species x 5 = 1. 0.0% D f.J 0°Po ❑ D column Totals: 20,. (A) 60 (B) 2 . o . o ❑ 0.0% Prevalence Index = B/A = 3.000 3. 4 0 ❑ 0.0% Hydrophytic Vegetation Indicators: . 5. 0 ❑ 0.0% k Dominance Test is > 500% 6 0 ❑ 0.0% JJ Prevalence index is 53.0t . 7 v 0 L 0.0 Morphological Adaptations t (Provide supporting 0 ❑ 0.0% data In Remarks or on a separate sheet) 8 9 0 ❑ 0.0% Wetland Non-Vascular Plantst . 10. 0 JJ 0.0% - Problematic Hydrophytic Vegetationl (Explain) 11 ] 0.0% a r 11ndicators of hydric soil and wetland hydrology must 0 = Total Cover be present, unless disturbed or problematic. E100% LEAF LITTER. Woody Vine Stratum (Plot size: i 1. 2, % Bare Ground in Herb Stratum: 100 Remarks: D ❑ 0.0% 0 ❑ 0.0% 0 = Total Cover Hydrophytic Vegetation Yes No Present? *Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version Soil Sampling Point- SP 55A Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Depth Matrix Redox Features (Inches) Color (moist) 9k i Color (most) % Type I Locz Texture Remarks . . . tType: C=Concentration. D=Depletion. RM=Reduced Matrix, CS=Covered or Coated Sand Grains 21-ocation: PL=Pore Lining, M=Matrix Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) U Hi t l Al Indicators for Problematic Hydric Soils:3 s oso ( ) ❑ Histic Epipedon (A2) ❑ Sandy Redox (S5) Stripped Matrix (S6) 2 cm Muck (A10) U Black Histic (A3) Loamy Mucky Mineral (Fl) (except in MLRA 1) Red Parent Material (TF2) Other (Explain in Remarks) U Hydrogen Sulfide (A4) Loamy Gleyed Matrix (F2) I Depleted Below Dark Surface (All) ❑ Depleted Matrix (F3) ❑ Thick Dark Surface (A12) Redox Dark Surface (F6) 3Indicators of hydrophytic vegetation and n Sandy Muck Mineral (Sl) ❑ Sandy Gleyed Matrix (S4) Depleted Dark Surface (F7) U Redox depressions (F8) wetland hydrology must be present, unless disturbed or problematic. Restrictive Layer (if present): Type: Depth (inches): Hydric Soil Present? Yes U No Remarks: NO PIT DUG IN THE RIGHT OF WAY, ANGRY DOGS NEARBY. Hydrology Wetland Hydrology indicators: Primary Indicators (minimum of one required; check all that apply) Secondary Indicators (minimum of two required) LI Surface Water (Al) L Water-Stained Leaves (B9) (except MLRA Water-Stained Leaves (Bg) (MLRA 1 2 ❑ High Water Table (A2) 1, 2, 4A, and 4B) , , 4A, and 4B) I .J Saturation (A3) U Salt Crust (Bll) L Drainage Patterns (Blo) _1 Water Marks (BS) ❑ Aquatic Invertebrates (B13) Dry Season Water Table (C2) U Sediment Deposits (B2) n Hydrogen Sulfide Odor (Cl) L..~ Saturation Visible on Aerial Imagery (Cg) L Drift deposits (B3) Oxidized Rhizospheres on Living Roots (0) Geomorphic Position (D2) n Algal Mat or Crust (B4) L_.l Presence of Reduced Iron (C4) [ I Shallow Aquitard (D3) J Iron Deposits (B5) ❑ Recent Iron Reduction in Tilled Soils (C6) ❑ FAC-neutral Test (DS) n Surface Soil Cracks (B6) n Stunted or Stressed Plants (Dl) (LRR A) n Raised Ant Mounds (D6) (LRR A) Inundation Visible on Aerial Imagery (87) ❑ Other (Explain in Remarks) I I Frost Heave Hummocks (D7) Sparsely Vegetated Concave Surface (B8) Field Observations: Surface Water Present? Yes No ' Depth (inches): Water Table Present? Yes - No Depth (inches): Saturation Present? - ! Wetland Hydrology Present? Yes No --(includes caplllary fringe) Yes No Depth (inches); Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available: Remarks: US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version WETLAND DETERMINATION DATA FORM - Western Mountains, Valleys, and Coast Region Project/Site: DESCHUTES LWI City/County: SUNRIVER/DESCHUTES Sampling Date: 10 AUg-10 . A licant/Owner: Investigator(s): Alessandra DESCHUTES Capretti COUNTY Section, Township, Range: S State: 34 OR T 22 S~mpl'R 10 E Point: SIP 56A Landform (hlllslope, terrace, etc.): Valley bottom Local relief (concave, convex, none): flat Slope: 1.0% / 0.6 ° Subregion (LRR): LRR A Lat.: 43.6286 Long.: -121.5127 Datum: NAD83 Soil Map Unit Name: 115A: Shanahan loamy cParSe Sand, low, 4 to.3. n rGel II .SIQp@S NWI classification: Are climatic/ hydrologic conditions on the site typical for this time of year? Yes ! No (If no, explain in Remarks.) Are Vegetation , Soil , or Hydrology I I significantly disturbed? Are "Normal Circumstances" present? Yes * No - Are Vegetation ❑ Soil ❑ , or Hydrology ❑ naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transects, important features, et Hydrophytic Vegetation Present? Yes No '12 Is the Sampled Area Hydric Soil Present? Yes No within a Wetland? Yes 0 No Wetland Hydrology Present? Yes No Remarks: OFF-SITE DETERMINATION, LIMITED PUBLIC VIEWING ACCESS. VEGETATION - Use scientific names of plants Tree Stratum (Plot size: ) 1. Pinus contorts 2. 3. 4. 0 Sapling/Shrub Stratum (Plot size: ) 1. 2. 3. 4. 5. Woody Vine Stratum (Plot size: ) 1. 2. % Bare Ground in Herb Stratum: 0 Remarks: Dominant Absolute Species Rel.Strat. Indicator i Dominance Test worksheet: % Cover Cover Status 15 W 100.0% Number of Dominant Species FAC That are OBL, FACW, or FAC: 1 (A) 0 L l o,o% Total Number of Dominant 0 0.0% Species Across All Strata: 1 0 ❑ 0.0% Percent of dominant Species 15 = To tal Cover That Are OBL, FACW, or FAC: u 100.0% 0 L_1 0.0% Pr evalenc e Index worksheet: 0 ❑ 0.0% Total % Cover of: Multiply by: 0 0.00% 0131- species 0 x 1- 0 0 ❑ 0.0%. FACW species 0 x 2- 0 0 ❑ 0.0% FAC species 15 x 3 - 45 0 = Total Cover FACU species 0. x 4 = „ 0 0 ❑ 0.0% 0 ❑ 0.0% 0 ❑ 0.0%0 0 L .I 0.0% 0 ❑ 0.0% 0 71 0.0% 0 1 1 0.0% 0 ❑ o.o% . 0 u 0.0% 0 l.. 0.0%° 0 ❑ 0.0% 0 = Total Cover (B) (A/8) UPL species 0 x 5 - 0 column Totals: . 15 (A) 45 (a) Prevalence Index = B/A = 3.000 . Hydrophytlc Vegetation Indicators: n Dominance Test is 7 50% Prevalence Index is 53.01 L J Morphological Adaptations I (Provide supporting data in Remarks or on a separate sheet) Wetland Non-Vascular Plantsl Problematic Hydrophytic Vegetationl (Explain) lIndicators of hydric soil and wetland hydrology must be present, unless disturbed or problematic. 0 0.0% 0 ❑ 0.0% Hydrophytic Vegetation 0 = Total Cover Present? Yes * No *Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version • Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric SOIIs:3 Histosol (Al) ❑ Sandy Redox (S5) ❑ 2 cm Muck (A10) ❑ Histic Epipedon (A2) ❑ Stripped Matrix (S6) ❑ Red Parent Material (TF2) ❑ Black Histic (A3) Loamy Mucky Mineral (Fl) (except in MLRA 1) ❑ Other (Explain in Remarks) ❑ Hydrogen Sulfide (A4) ❑ Loamy Gleyed Matrix (F2) ❑ Depleted Below Dark Surface (All) J Depleted Matrix (9) ❑ Thick Dark Surface (A12) Redox Dark Surface (F6) 3 Indicators of hydrophytic vegetation and ❑ Sandy Muck Mineral (SI) Depleted Dark Surface (F7) wetland hydrology must be present, ❑ Sandy Gleyed Matrix (S4) ❑ Redox depressions (F8) unless disturbed or problematic. Restrictive Layer (if present): Type: Depth (inches): Hydric Soil Present? Yes No Remarks: LIMITED ACCESS, COULD NOT DIG PIT IN RIGHT OF WAY Hydrology Wetland Hydrology Indicators: Primary Indicators (minimum of one required; check all that apply) Secondary Indicators (minimum of two required) ❑ Surface water (Al) ❑ Water-stained Leaves (B9) (except MLRA water-stained Leaves (B9) (MLRA 1, 2, ❑ High Water Table (A2) 1, 2, 4A, and 4B) 4A, and 4B) ❑ Saturation (A3) [ Salt Crust (811) ❑ Drainage Patterns (B10) ❑ Water Marks (Bl) L Aquatic Invertebrates (B13) I _ .I Dry season water Table (C2) ❑ Sediment Deposits (B2) ❑ Hydrogen Sulfide Odor (Cl) ❑ Saturation Visible on Aerial Imagery (C9) ❑ Drift deposits (83) Oxidized Rhizospheres on Living Roots (C3) ❑ Geomorphic Position (D2) Algal Mat or Crust (B4) Presence of Reduced Iron (C4) ❑ Shallow Aquitard (133) I J Iron Deposits (BS) ❑ Recent Iron Reduction in Tilled Soils (C6) FAC-neutral Test (DS) ❑ Surface Soil Cracks (B6) Stunted or Stressed Plants (Dl) (LRR A) Raised Ant Mounds (D6) (LRR A) ❑ Inundation Visible on Aerial Imagery (B7) ❑ Other (Explain in Remarks) A Frost Heave Hummocks (D7) Sparsely Vegetated Concave Surface (B8) Field Observations: Surface Water Present? Yes No _ Depth (inches): Water Table Present? Yes No Depth (inches): Wetland Hydrology Present? Yes No Saturation Present? (includes capillary fringe) Yes > NO Depth (inches): Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available: Remarks: US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version WETLAND DETERMINATION DATA FORM - Western Mountains, Valleys, and Coast Region . Project/Site: DESCHUTES LWI City/County: SUNRIVER/DESCHUTES Sampling Date: 10-Aug-1.0. • Applicant/ o rr((ss) A DESlessaCHUTESP OUNTY State: OR Sampling Point: SP 57A Investigatondra Ca retti Section, Township, Range: S 14 T 21S R 10 E Landform (hillslope, terrace, etc.): Flat Local relief (concave, convex, none): concave slope: 3.0% / 1.7 ° Subregion (LRR): LRR A Lot- 43.7488 Long.: -121.4997 Datum: NAD83 Soil Map Unit Name: 115A: Shanahan loamy coarse.$.and, low, 0 to 3 percent Slopes NWI classification: PEMA. Are climatic/ hydrologic conditions on the site typical for this time of year? Yes No (If no, explain in Remarks.) Are Vegetation Soil or Hydrology significantly disturbed? Are "Normal Circumstances" present? Yes (Ii!) No 0 Are Vegetation ❑ , Soil . _ , or Hydrology ❑ naturally problematic? (If needed, explain any answers in Remarks.) Summarv of Findings - Attach site map showing sampling point locations, transects, important features, et Hydrophytic Vegetation Present? Yes No Is the Sampled Area Hydric Soil Present? Yes 3 No Wetland Hydrology Present? Yes No within a Wetland? Yes NO Remarks: OFF-SITE DETERMINATION VEGETATION - Use scientific names of plants. Dominant Species? Absolute Rel.Strat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: 1 % Cover. Cover Status - Number of Dominant Species 1. 0 . 71 0.00% That are 08L, FACW, or FAC: 1. (A) 2 0 ❑ 0.0°k . - - ❑ 0 0% Total Number of Dominant 1 3. 0 . (B) Species Across All Strata: 4. 0 f 1 0.0% Percent of dominant Species 0 Total Cover 100.0% (A/B) 0 Sapling/Shrub Stratum (Plot size: ► 1. 2. 3. 4. 5. Herb Stratum (Plot size: 1 1 Unidentified pasture grasses Woody Vine Stratum (Plot size: ► 1. 2. % Rare Ground in Herb Stratum: 20 Remarks: Unidentified pasture grasses assumed FAC. Pastured land. That Are OBL, FACW, or FAC. 0 0.0% Prevalence index worksheet: 0 ❑ 0.o% Total % Cover of. Multiply by: 0 ❑ 0.0% ORL species 0 x 1= 0 0. ❑ 0.0% FACIN species 0 x 2 = 0 0 0.0%° FAC species $0 x 3 = 240 0.. . Total Cover FACU species 0 x 4 = 0 80 LV 100.0% FAC uPL species 0.... - x 5 - 0 column Totals: 80 (A) 240 (a) 0 ❑ 0.0% 0 ❑ o.o% Prevalence Index = B/A = 3.000 0 1 0.0% Hydrophytic Vegetation indicators: 0 ❑ 0.0% n Dominance Test is a 500% 0 ❑ 0.0% Prevalence Index is 53.01 0 ❑ D.o% ❑ Morphological Adaptations 1(Provide supporting 0 1 0.0% data In Remarks or on a separate sheet) D ❑ 0.0% ❑ Wetland Non-Vascular Plantsl 0 0.0%0 ❑ Problematic Hydrophytic Vegetationl (Explain) 0 L.J 0.0% 'Indicators of hydric soil and wetland hydrology must BO _ - Total Cover be present, unless disturbed or problematic. o J 0.0% D 0.0% Hydrophytic Vegetation Y ' N 0 = T otal Cover es o Present? *.Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version soil . sampling Point: SP 57A Profile Description. (Describe to the depth needed to document ' the indicator or confirm the absence of indicators.) I. i Depth x Redox Features (inches) Color (moist) % Color (moist) 9/o Typel Lot= 6 Texture Remarks a-l no soil, root "M V s ayes 1-6 10YR 3/3 100% Loamy Sand with silt and pebbles 1....8 10YR 3/3 100% 6.... Loamy Sand with silt and pebbles tType: C=Concentration. D=Depletion. RM=Reduced Matrix, CS=Covered or Coated Sand Grains z Location: PL=Pore Lining. M-Matrix ~ Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils:3 Histosol (Al) Sandy Redox (SS) I 12 cm Muck (A10) Histic Epipedon (A2) 1 Stripped Matrix (56) L] Red Parent Material (TF2) Black Histic (A3) Loamy Mucky Mineral (Fl) (except in MLRA 1) Other (Explain in Remarks) L] Hydrogen Sulfide (A4) Loamy Gleyed Matrix (F2) F7 Depleted Below Dark Surface (All) Depleted Matrix (F3) Thick Dark Surface (A12) Redox Dark Surface (F6) }Indicators of hydrophytic vegetation and ] Sandy Muck Mineral (51) Depleted Dark Surface (F7) wetland hydrology must be present, Sandy Gleyed Matrix (S4) Redox depressions (F8) unless disturbed or problematic. Restrictive Layer (If present): Type: Depth (inches): Hydric Soil Present? Yes No Remarks: Hydrology Wetland Hydrology Indicators: Primary Indicators (minimum of one required; check all that apply) Secondary Indicators (minimum of two required) Surface Water (Al) L ]Water -Stained Leaves (Bg) (except MLRA Water-stained Leaves (Bg) (MLRA 1, 2, J High Water Table (A2) 1, 2, 4A, and 4B) 4A, and 45) L ] Saturation (A3) ] Salt Crust (511) [J Drainage Patterns (B10) Water Marks (Bl) r Aquatic Invertebrates (B13) ] Dry Season Water Table (C2) Sediment Deposits (B2) L Hydrogen Sulfide Odor (Cl) [ I Saturation Visible on Aerial Imagery (C9) Drift deposits (B3) Oxidized Rhizospheres on Living Roots (0) Geomorphic Position (D2) Algal mat or crust (B4) Presence of Reduced Iron (C4) Shallow Aquitard (D3) Iron Deposits (55) Recent Iron Reduction in Tilled Soils (C6) FAC-neutral Test (DS) ] Surface Soil Cracks (B6) Stunted or Stressed Plants (Dl) (LRR A) J Raised Ant Mounds (D6) (LRR A) Inundation Visible on Aerial Imagery (B7) Other (Explain in Remarks) Frost Heave Hummocks (D7) Sparsely Vegetated Concave Surface (B8) . Field Observations: - Surface Water Present? Yes No Depth (inches): L L Water Table Present? Yes _ No Depth (inches): f (Saturates caPresent? fringe) _ Yes No I _ Wetland Hydrology Present? Yes No Depth (Inches): Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available; Remarks: I US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version WETLAND DETERMINATION DATA FORM - Arid West Region Project/Site: Deschutes County LWI City/County: Sunriver/Deschutes Sampling Date: 03-May-10 Applicant/Owner: DESCHUTES COUNTY State: OR _ Sampling Point: SP 100 Investigator(s): A. Booy, R. Baker, J. Gordon Section, Township, Range: 5 13 T 20S R 10 E Landform (hillslope, terrace, etc.): Valley bottom Local relief (concave, convex, none): none Slope: 0.0% / 0.0 ° Subregion (LRR): LRR B Lat.: 43.8383 Long: -121.4740 Datum: NAD 83 Soil Map Unit Name: W: Water NWI classification: PEMC Are climatic/ hydrologic conditions on the site typical for this time of year? Yes' No - ' (If no, explain in Remarks.) Are Vegetation , Soil , or Hydrology significantly disturbed? Are "Normal Circumstances" present? Yes No l AreVegetation , Soil L , or Hydrology L naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transects, important features, etc. Hydrophytic Vegetation Present? Yes No Is the Sampled Area Hydric Soil Present? Yes NO Wetland Hydrology Present? Yes No within a Wetland? Yes NO I Remarks: On-site determination. VEGETATION - Use scientific names of plants. Dominant Species? Absolute Rel.5trat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: ) 1. % Cover 0 Cover 0.0% Status Number of Dominant Species That are OBL, FACW, or FAC: 2 (A) 2 0 0.0% . 3. 0 010% Total Number of Dominant Species Across All Strata: 2 (B) 4. 0 0.0% 0 = Total Cover Percent of dominant Species o 100.0 /o (A/e) Sapling/Shrub Stratum (Plot size: That Are OBL, FACW, or FAC: . 1. Salix sp. 10 N 100.0% FACW Prevalence Index worksheet: 2. 0 0.0% Total Cover of: Multiply by: 3. 0 0.0% 013L species 0 x 1= 0 4. 0 . 0.0% FACW species 108 x 2 = 216 5. 0 0.0% FAC species. x 3 - 10 = Total Cover I FACU species 0 x 4= 0 Herb Stratum (Plot size: ) 30 2 1 Carex sp. 96 IV 96.0% FACW x 5 = UPL species . Column Totals: 110 (A) 226 (B) 2. Geum macroPhyIlum 1 1.0% FACW 3. Rumex acetosa 2 2.0% UPL ~ Prevalence Index = B/A = 2.055 ]uncus balticus 4. 1 I 1.0% FACW Hydrophytic Vegetation Indicators: 5. 0 ] 0.0% /11 Dominance Test Is 7 50% 6. 0 0.0% Prevalence index is 53.0 1 0 0.00/1 Morphological Adaptations 1 ~.'rovide supporting g 0 0.0% data in Remarks or on a separate sheet) 9. 0 0.0% Problematic Hydrophytic Vegetation 1(1 :plain) 10. 0 0.0% 11 0 0.0% . 1 Indicators of hydric soil and wetland hydrology must 100 = Total Cover be present, unless disturbed or problematic. Woody Vine Stratum (Plot size: ) ] 0 0.0% 2. 0 0.0% Hydrophytic 0 Total Cover = Vegetation ' Present? Yes No % Bar e Gr ound in Herb Stratum: 0 % Cover of Biotic Crust 0 Remarks: Salix sp. and Carex sp. assumed FACW. *Indicator Suffix National status or professional decision assigned because Regional status not defined by FWS. US Army Corps of Engineers Arid West - Version 2 Oct. 2008 Soil Sampling Point: SP 100 Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Depth Matrix - . Redox Features inches Color moist % Color (moist) 0% Type 1 Loc2 Texture Remarks 0 5 2/ 2 100% Silt Loam 5-12 10YR 2/2 70% Muck 2 different soils 5-12 10YR 4/3 30% Clay Loam 12-21 10YR 2/2 100% Muck Type: C=Concentration. D-De , 1 - pletion. RM=Reduced Matrix, CS=Covered or Coated Sand Grains i zLocatlon: PL=Pore Lining. M=Matroc Hydric Soil Indicators: (Applicable to all LR Rs, unless otherwise noted.) Indicators for Problematic Hydric SoilsP '/i Histosol (Al) Sandy Redox (SS) , 1 cm Muck (A9) (LRR C) Histic Epipedon (A2) Stripped Matrix (S6) r 2 cm Muck (A10) (LRR 8) Black Histic (A3) t Loamy Mucky Mineral (Fi ) Reduced Ver[ic (F18) i Hydrogen Sulfide (A4) JI Loamy Gleyed Matrix (F2) ; R d P t M i l TF2 Stratified Layers (AS) (LRR C) Depleted Matrix (F3) e aren ater ( a ) ` 1 cm Muck (A9) (LRR D) i Other (Explain in Remarks) Redox Dark Surface (F6) Depleted Below Dark Surface (All) Depleted Dade Surface (F7) I L! Thick Dark Surface (A12) Sandy Muck Mineral (Sl) Redox depressions (F8) 3 Indicators of hydrophytic vegetation and Sandy Gleyed Matrix (54) Vernal Pools (F9) wetland hydrology must be present. Restrictive Layer (if present): Type: Depth (inches): Hydric Soil Present? Yes i•' No Remarks: • Hydrology Wetland Hydrology Indicators: Primarv Indicators (minimum of one required; check all that apply) Secondary indicators (2 or more required) Surface Water (Al) J Salt Crust (Bll) Water Marks (Bl) (Riverine) High Water Table (A2) Biotic Crust (B12) Sediment Deposits (B2) (Riverine) Saturation (A3) Aquatic Invertebrates (B13) i Drift Deposits (B3) Riverine) Water Marks (BS) (Nonriverine) Hydrogen Sulfide Odor (Cl) Drainage Patterns (B10) Sediment Deposits (82) (Nonriverine) Oxidized Rhizospheres along Living Roots (0) i Dry Season Water Table (C2) Drift deposits (B3) (Noneriverine) Presence of Reduced Iron (C4) Crayfish Burrows (C8) Surface Soil Cracks (B6) Recent Iron Reduction in Plowed Soils (C6) Saturation Visible on Aerial Imagery (C9) Inundation Visible on Aerial Imagery (B7) Thin Muck Surface (C7) 11 Shallow Aquitard (D3) Water-Stained Leaves (B9) Other (Explain in Remarks) [ FAC-neutral Test (D5) Field observations: Surface Water Present? Yes No Depth (inches): _ Water Table Present? Yes p' No Depth (inches): 22 Saturation Present? Yes No Wetland H 12 Depth (inches): L ydrology Present? Yes No (includes capillary fringe) _ Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if avai lable: Remarks: - . _ _ , WATER TABLE AT 22 INCHES, HOWEVER EVIDENCE OF HIGHER WATER TABLE OBSERVED BY WATER MARKS AND OXIDIZED ROOTS US Army Corps of Engineers Arid West - Version 2 Oct. 2008 WETLAND DETERMINATION DATA FORM - Arid West Region Project/Site: Deschutes County LWI City/County: Deschutes Sampling Date: 03-may-10 Applicant/Owner: DESCHUTES COUNTY State: OR Sampling Point: SP 101 Investigator(s): ABp/AM/]G/RB Section, Township, Range: S 1ne): none slope: 0.0% / 0.0 ° Landform hillslo a terrace, etc.): flat Local relief concave, convex, non 7 20S R 10E Subregion (LRR): LRR B Lat.: 45.8422 Long.: -121.4749 Datum: NAD 83 Soil Map Unit Name: 144A: Sunriver Sandy loam, 0 to 3 percent Slopes NWI classification: pS..SC Are climatic/hydrologic conditions on the site typical for this time of year? Yes No (If no, explain in Remarks.) _i Are Vegetation soil I , or Hydrology significantly disturbed? Are "Normal Circumstances" present? Yes ` No Are Vegetation , Soil I_-I , or Hydrology naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transects, important features, etc. Hydrophytic Vegetation Present? Yes No IS the Sampled Area Hydric Soil Present? Yes ( No (~1 within a Wetland? Yes No Wetland Hydrology Present? Yes No Remarks: On-site determination. VEGETATION - Use scientific names of plants. Dominant Species? Absolute Rel.5trat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: ) % Cover Cover Status i Number of Dominant Species 1. Pinus contorts 15 100.09% FAC That are OBL, FACW, or FAC: 1 (A) 2 0 0. 0% . - . Total Number of Dominant 3. 0 0.0% Species Across All Strata: 2 (B) 4. 0 0.0%° Percent of dominant Species 15 = Total Cover ° Sapling/Shrub Stratum (Plot size: ) I , 1, Prunus sp. 40 VfI 50.0% FACU Prevalence Index worksheet: 2. Salix sp. 40 50.0% FACW Total % Cover of: Multiply by: 3, 0 0.0% oBL species 0 x 1- 0 4. 0 0.0% FACw species 40x 2 = 80 5. 0 0.0% FAC species 15 x 3 = 45 80 = Total Cover I FACU species 40 x 4 - 160 Herb Stratum (Plot size: ► 0 0 uPL species x 5 - 1. 0 0.0% ColUmn Totals: 95 (A) 285 (B) 2. 0 0.0% 3 0 0.0% Prevalence Index = B/A = 3.000 4. 0 i 0.0% Hydrophytic Vegetation Indicators: 5. 0 I 0.0% Dominance Test is n 50% 6. 0 J 0.0% Prevalence Index Is 53.0 1 7. 0 1- 0.0% Morphological Adaptations 1 1_'rovide supporting 8. 0 1 0 0% _ data in Remarks or on a separate sheet) 0 ° 0.0% J Problematic Hydrophytic Vegetation 1 (1 :plain) 10. 0 0.0% 11 0 0.0% . Indicators of hydric soil and wetland hydrology must p . =Total Cover be present, unless disturbed or problematic. Woody Vine Stratum (Plot size: ) or FAC: 50.0 /o (AJB) That Are OBI FACW 1 0 1 0.0% 2. 0 0.0% Hydrophytic Vegetation 0 = Total Cover Present? Bare Ground in Herb Stratum: 10Pinus contortaP % Cover of Biotic Crust 0 Remarks: prunus sp. assumed FACU and Salix sp. assumed FACW. *Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS. US Army Corps of Engineers Yes No ' . Arid West - Version 2 Oct. 2008 SOiI Sampling Point: SP 101 Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of Indicators.) matrix Redox Features . % (inches) Co for (moist... LOC= Color (moist) 0% Types Texture Remarks 0-4 lOYR 2/2 100% p ROOTS M POSED W00 Silt 4-8 10YR 3/1 100%... UNpECp Silt ROOTS, MATERIApp L SED VEG 8-18 10YR 2/2 100% Silt Loam SAND POCKETS, CHARCOAL PLANT MATERIAL I Type: C=Concentration. D=Depletion, RM=Reduced Matrix, CS=Covered or Coated Sand Grains 'Location: PL=Pore Lining. M=Matra Hydric Soil Indicators: (Applicable to all LRRs unless otherwise noted.) Indicators for Problematic Hydric Soils- e Histosol (Al) _J Sandy Redox (S5) 1 cm Muck (A9) (LRR C) L F1 Histic Epipedon (A2) Stripped Matrix (S6) i 2 cm Muck (A10) (LRR B) L., Black Histic (A3) Hydrogen Sulfide I Loamy Mucky Mineral (Fi) 17 Reduced Vertic (F18) L ~ tifi d Loamy Gleyed Matrix (F2) Red Parent Material (72) Layers ers (AS) ) (LRR C) Stra e 1 cm Muck (A9) (LRR D) Depleted Matrix (F3) Other (Explain in Remarks) [I Depleted Below Dark Surface (All) Redox Dark Surface (F6) Depleted Dark Surface (F7) 11 Thick Dark Surface (A12) Redox depressions (FS) F1 Sandy Muck Mineral (Sl) Vernal Pools (F9) 3 Indicators of hydrophytic vegetation and Sandy Gleyed Matrix (54) wetland hydrology must be present. Restrictive Layer (if present): Type: Depth (inches): Hydric Soil Present? Yes NO Remarks; "U ndecom posed" means the structure of the organic material is fibrous or una ltered. The lowest layer (8-18") contains slow ly decaying and burnt organic material. Hydrology Wetland Hydrology Indicators: Primary indicators (minimum of one required.; check all that apply) Secondary Indicators (2 or more required) Surface Water (Ai) i Salt Crust (BIl ) I I Water Marks (Bl) (Riverine) ~i High Water Table (A2) Biotic Crust (B12) Sediment Deposits (B2) (Riverine) IV' Saturation (A3) JI Aquatic Invertebrates (613) Drift Deposits (B3) Riverine) Water Marks (Bl) (Nonriverine) I Hydrogen Sulfide Odor (Cl) Drainage Patterns (B10) Sediment Deposits (B2) (Nonriverine) " Oxidized Rhizospheres along Living Roots (0) Dry Season Water Table (C2) Drift deposits (B3) (Nonriverine) Presence of Reduced Iron (C4) Crayfish Burrows (C8) L I Surface Soil Cracks (B6) Recent Iron Reduction in Plowed Soils (C6) Saturation Visible on Aerial Imagery (C9) Inundation Visible on Aerial Imagery (137) _ Thin Muck Surface (C7) I Shallow Aquitard (D3) Water-Stained Leaves (89) .I Other (Explain in Remarks) FAC-neutral Test (D5) Field observations: Surface Water Present? Yes ` NO Depth (inches): Water Table Present? Yes No ' Depth (inches : 12 I - Saturation Present? Yes e1 NO ` Depth (r,uches) 4 - Wetland Hydrology Present? Yes No includes capillary fringe) Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available: Remarks: SATURATION AT 4 INCHES, WATER TABLE AT 12 INCHES US Army Corps of Engineers Arid West -Version 2 Oct. 2008 WETLAND DETERMINATION DATA FORM - Arid West Region Project/Site: Deschutes LWI City/County: Deschutes Sampling Date: 04-May-10 Applicant/Owner: DESCHUTES COUNTY State: OR 2 Investigator(s): John Gordon, Adam Merrill Section, Township, Range: S 24 T 20 Sampling R10 E Point: SP 10 Landform (hillslope, terrace, etc.): Floodplain Local relief (concave, convex, none): flat Slope: 0.0% / 0.0 ° Subregion (LRR): LRR B Lat.: 43.8285 Long.: -121.4729 Datum: NAD 83 Soil Map Unit Name: 29A: Cryaquolls, 0 to 3 percent slopes NWI classification: PEMF Are climatic/ hydrologic conditions on the site typical for this time of year? Yes No (If no, explain in Remarks.) Are Vegetation , Soil , or Hydrology significantly disturbed? Are "Normal Circumstances" present? Yes No( Are Vegetation , Soil , or Hydrology naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transects, important features, etc. Hydrophytic Vegetation Present? Yes No Is the Sampled Area Hydric Soil Present? Yes No, within Wetland Hydrology Present? YES NO a Wetland? Yes NO Remarks: On-site determination. VEGETATION - Use scientific names of plants. Dominant Species? Absolute ReLStrat. Indicator Dominance Test worksheet: Tree Stratum (Plat size: ) % Cover Cover Status Number of Dominant Species 1. 0 ❑ 0.00/. That are OBL, FACW, or FAC: 2. (A) 2. 0 0.0% 3 0 0 0% Total Number of Dominant . . - Species Across All Strata: 2 (e) 4. 0 ..I 0.0% 0 = Total Cover Percent of dominant Species u sapling/Shrub Stratum (Plot size: ) That Are OBL, FACW, or FAC: 100.0% (A/B) 1. 0 0.0% Prevalence Index worksheet: 2. 0 7 0.0% Total % Cover of: , Multiply by: 3. 0 1 0.0% OBL species 60 x 1 60 4. 0 0.0% FACW species 40 x 2 = 80 5. 0 ° 0.0k FAC species 0 x 3= 0 0 = Total Cover FACU species 0 x 4 0 Herb Stratum (Plot size: ) 0 5cirpusamericanus 1 60 60.0% OBL uPL species x 5 . 2. Juncus balticus 40 ' vfI 40.0% FACW column Totals: 100 (q) 140 (a) 3. 0 0.0% Prevalence Index = B/A = 1.400 4. D 0.0°/. Hydrophytic Vegetation Indicators: 5. 0 0.0% Dominance Test is a so% 6. D 0.0% N Prevalence Index is 53.0 1 7. 0 I 0.0% L morphological p I- Irovide supporting d t 8. 0 0.0% a separate sheet) data in Remarks or n 9. 0 ~ O.D°/° 71 Problematic Hydrophytic Vegetation 1(1 :plain) 1.0. 0 0.0% 7 1. o ~ 0.0% . 1 Indicators of hydric soil and wetland hydrology must 100 Total Cover = ! be present, unless disturbed or problematic. Woody Vine Stratum (Plot size: ) 1. 0 J o.0% 2. 0 L 0.0% Hydrophytic 0 =Total Cover Vegetation Present? Yes • No % Bare Ground in Herb Stratum: 0 % Cover of Biotic Crust 0 Remarks: *Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS. US Army Corps of Engineers Arid West - version 2 Oct. 2008 1 type: C=Concentration. D=Depletion. RM=Reduced Matrix, CS=Covered or Coated Sand Grains 21-ocation: PL=Pore Lining. M=Matra Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric SoilO ❑ Histosol (Al) ❑ Sandy Redox (S5) ❑ 1 cm Muck (A9) (LRR C) W Histk Epipedon (A2) ❑ Stripped Matrix (S6) I 12 cm Muck (A10) (LRR B) ❑ Black Histic (A3) Hydrogen Sulfide (A4) I .I Loamy Mucky Mineral (FI) ❑ Reduced Vertic (1`18) . ❑ Stratified Layers (A5) (LRR C) ❑ Loamy Gleyed Matrix (172) ❑ Depleted Matrix (F3) I J Red Parent Material (72) ❑ Other (Explain in Remarks) 1 cm Muck (A9) (LRR D) Redox Dark Surface (F6) Depleted Below Dark Surface (All) ❑ Depleted Dark Surface (F7) Thick Dark Surface (A12) Redox depressions (F8) ❑ Sandy Muck Mineral (Sl) ❑ Vernal Pools (F9) 3 Indicators of hydrophytic vegetation and ❑ Sandy Gleyed Matrix (S4) - - wetland hydrology must be present. - - - - Restrictive Layer (if present): - TYPe; Depth (inches); Hydric Soil Present? Yes * No - Remarks: ~i Hydrology Weiland Hydrology Indicators: Primary Indicators (minimum of one required, check all that apply) Secondary Indicators (2 or more required) ❑ Surface Water (Al) ❑ Salt Crust (B11) ❑ Water Marks (81) (Riverine) High Water Table (A2) ❑ Biotic Crust (B12) Sediment Deposits (B2) (Riverine) U Saturation (A3) ❑ Aquatic Invertebrates (B13) ❑ Drift Deposits (0) Riverine) Water Marks (Bl) (Nonriverine) Hydrogen Sulfide Odor (Cl) I I Drainage Patterns (B10) ❑ Sediment Deposits (B2) (Nonriverine) ❑ Oxidized Rhizospheres along Living Roots (0) ❑ Dry Season Water Table (C2) Drift deposits (B3) (Noneriverine) Presence of Reduced Iron (C4) I I Crayfish Burrows (C8) ❑ Surface Soil Cracks (B6) ❑ Recent Iron Reduction in Plowed Soils (C6) ❑ Saturation Visible on Aerial Imagery (C9) I*/~ Inundation Visible on Aerial Imagery (B7) Thin Muck Surface (0) Shallow Aquitard (D3) 71 Water-Stained Leaves (B9) ❑ Other (Explain in Remarks) ( FAC-neutral Test (D5) Field Observations: Surface Water Present? Yes 0 NO ~ i Depth (inches): Water Table Present? Yes ! No Depth (inches): lfi H W No ( ) l P t? Yes Saturation Present? Yes J> No 0 eiland Depth (inches): v resen ydro ogy (includes capillary fringe) . Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if avai lable: Remarks: US Army Corps of Engineers Arid West - Version 2 Oct. 2008 WETLAND DETERMINATION DATA FORM - Arid West Region Project/Site: Deschutes LWI City/County: Sunriver/Deschutes Sampling Date: 04-May-10 Applicant/Owner: DE5CHUTE5 COUNTY State: OR Sampling Point: SP 103 Investigator(s): John Gordon, T205 R10E Landform (hilisloP e, terrace, 4 etc.): Shoreline Local r relief (concave convex none): flat Slope: 0.0% / 0.0 ° Subregion (LRR): LRR B Lat.: 43.7934 Long.: -121.5352 Datum: NAD 83 Soil Map Unit Name: 29A; Crvaouolls, 0 to 3 percent slopes NWI classification: Are cl lmatic/ hydrologic conditions on the site typical for this time of year? Yes * No (If no, explain in Remarks.) Are Vegetation ❑ , Soil n , or Hydrology hI significantly disturbed? Are "Normal Circumstances" present? Yes No - AreVegetation , Soil L_ , or Hydrology .....1 naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transacts, important features, etc. Hydrophytic Vegetation Present? Yes No Is the Sampled Area Hydric Soil Present? Yes No 0 Wetland Hydrology Present? Yes No - within a Wetland? Yes * No Remarks: On-site determination. VEGETATION - Use scientific names of plants. Dominant Species? Absolute Rel.Strat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: ) % Cover Cover Status u - Number of Dominant Species 1. Pinus contorts 5 ~ 100.0% FAC - That are OBL, FACW, or FAC: 3 (A) 2. 0 ❑ 0.0% 3 n 0 0% Total Number of Dominant . 0. . Species Across All Strata: 4 (B) 4. 0 f 0..0% 5 =Total Cover Percent of dominant Species 75.0% (A/B) Sapling/Shrub Stratum (Plot size: ) That Are OBL, FACW, or FAC: 1„ Salix geyeriana 40 88.9% Prevalence Index worksheet: 2. Betula glandulosa 5 11.1% OBL Total % Cover of: Multiply by: 3. o _J 0.0% IoBI_ species 55 x 1 - 55 4. 0 0.0% FACw species 50 x 2 - 100 5. ° 0.0% FAC species 5 x 3 = 15 5 - Total Cover FACU species 0 x 4 = 0 Herb Stratum (Plot size: ) 0 0 C tili 50 n 50 0% OBL x 5 - UPL species arex aqua s 1. . 2. ]uncus ensifolius 50 ~ 5D.0% FACW Column Totals; 110 (q) 170 (e) 3. 0 ❑ 0.0% Prevalence Index = B/A = 1.545 4. 0 0.0% Hydrophytic Vegetation indicators: 5 0 ❑ o.ook 1-/1 Dominance Test is a s0% 6. 0 I 1 0.0% 1 Prevalence Index is 53.0 7. o ❑ 0.0% 1 ❑ Morphological Adaptations i ,.'rovide supporting 8. 0 0.0% data in Remarks or on a separate sheet) 9. 0 U 0.0% [ Problematic Hydrophytic Vegetation 1(1 :plain) 10. 0 ❑ 0.0% 11. 0 ❑ 0.0% Indicators of hydric soil and wetland hydrology must 100 = Total Cover be present, unless disturbed or problematic. Woody Vine Stratum (Plot size: ) 1. 0 ❑ 0.0% 2. 0 ❑ 0.0% Hydrophytic 0 = Total Cover Vegetation * No Present? Yes % Bare Ground in Herb Stratum: p % Cover of Biotic Crust 0 Remarks: Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS US Army Corps of Engineers Arid West - Version 2 Oct. 2008 Soil Sampling Point: SP 103 Profile Description: (Describe to the depth needed to document the Indicator or confirm the absence of indicators.) Depth matrix Redox Features (inches) Color (moist Color (moist) /o u Type 1 Loci Texture Remarks I 0-20 lOYR 3/3 100% i Type: C=Concentration. D=Depletion. RM=Reduced Matrix, CS=Covered or Coated Sand Grains 'Location: PL=Pore Lining. M=Matrix Hydric Soil Indicators: (Applicable to all LRRS, unless otherwise noted.) Indicators for Problematic Hydric Soils ❑ Histosol (Al) ❑ Sandy Redox (S5) ❑ 1 cm Muck (A9) (LRR C) Histic Epipedon (A2) ❑ Stripped Matrix (S6) I 12 em Muck (A10) (LRR B) ❑ Black Histic (A3) Loamy Mucky Mineral (Fl) ❑ Reduced Vertic (1`18) J Hydrogen Sulfide (A4) J Loamy Gleyed Matrix (F2) Red Parent Material (TF2) ❑ Stratified Layers ( (LRR C) [ Depleted Matrix (F3) EWI Other (Explain in Remarks) . ] 1 cm Muck (A9) (LR R D) Redox Dark Surface (F6) I ~ Depleted Below Dark Surface (All) ~ Depleted Dark Surface (F7) Thick Dark Surface (A12) ~ Redox depressions (F8) sio 71 Sandy Muck Mineral (Si) Vernal Pools 3 Indicators of hydrophytic vegetation and L Sandy Gleyed Matrix (S4) wetland hydrology must be present. Restrictive Layer (if present): ' Type: Depth (inches): Hydric Soil Present? Yes * No Remarks: aquic moisture regime Hydrology Wetland Hydrology Indicators: Primary Indicators (minimum of one required; check all that apply) Secondary Indicators (2 or more required) . Surface Water (Al) I I Salt Crust (Bll) ❑ Water Marks (Bl) (Riverine) High Water Table (A2) ❑ Biotic Crust (1312) I I Sediment Deposits (132) (Riverine) Saturation (A3) Aquatic Invertebrates (813) ❑ Drift Deposits (B3) Riverine) ❑ Water Marks (131) (Nonriverine) ❑ Hydrogen Sulfide Odor (Cl) Drainage Patterns (810) ❑ Sediment Deposits (132) (Nonriverine) oxidized Rhizospheres along Living Roots (0) ❑ Dry Season Water Table (C2) ❑ Drift deposits (83) (Nonriverine) ❑ Presence of Reduced Iron (C4) Crayfish Burrows (C8) ❑ Surface Soil Cracks (B6) Recent Iron Reduction in Plowed Soils (C6) ❑ Saturation Visible on Aerial Imagery (C9) Inundation Visible on Aerial Imagery (B7) 11 Thin Muck Surface (C7) Shallow Aquitard (D3) Water-Stained Leaves (69) ❑ Other (Explain in Remarks) ❑ FAC-neutral Test (D5) Field Observations: Surface Water Present? Yes No Depth (inches): Water Table Present? Yes No - Depth (inches): 10 7 Y 4) N Saturation Present? Yes J!) No Depth (inches): 0 1 Wetland H es o ydrology Present? (includes capillary fringe), . Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if avai lable: Remarks: US . . , Army Corps of Engineers Arid West - Version 2 Oct. 2008 WETLAND DETERMINATION DATA FORM - Arid West Region Project/Site: Deschutes County LWI City/County: Sunriver/Deschutes Sampling Date: 06-may-10 Applicant/Owner: DESCHUTES COUNTY State: OR Sampling Point: SP 104 investigator(s)- John Gordon, Adam Merrill Section, relief Range: convex, none T 20S R 10, E Landform (hlllslope, terrace, etc.): floodplain Lo (contave concave Slope: 0.0% / 0.0 ° Lat.: 43.7921 Long.: -121.5196 Datum: NAD 83 Subregion (LRR): LRR B Soil Map Unit Name: 29A: Crvaquolls, 0 to 3 percent slopes NWI classification: 82UBH Are climatic/hydrologic conditions on the site typical for this time of year? Yes No (If no, explain in Remarks.) • Are Vegetation , Soil , or Hydrology significantly disturbed? Are "Normal Circumstances" present? Yes' No' Are Vegetation Soil , or Hydrology naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transects, important features, etc. Hydrophytic Vegetation Present? Yes P NO Is the Sampled Area Hydric Soil Present? Yes No' within a Wetland? Yes' NO Wetland Hydrology Present? Yes No Remarks: Fall River site. On-site determination. VEGETATION - Use scientific names of plants. Dominant Species? AbsoluteCover rat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: 1 cY6 Number of Dominant Species 1. Pinus contorts 10 100.0% FAC That are OBL, FACW, or FAC: 4 (A) 2. 0 I 0.0°/a Total Number of Dominant 3. 0 0.0% Species Across All Strata: 4 (B) 4. 0 0.0% 10 = Total Cover Percent of dominant Species 100.0% (A/B) Sapling/Shrub Stratum (Plot size: That Are OBL, FACW, or FAC: 1•Salixgeyeriana 2. Betula glandulosa 3. 4. 5. Woody Vine Stratum (Plot size: 1. 2. % Bare Ground in Herb Stratum: 0 Remarks: about 10% openwater 15 60.0% FACW . rksheet Prevalence Index 10 ° 40.0% OBL ° Cover Multiply by: of: Total /o e 0 l 0.0% OBL species 100 x 1 = 100 0 0.0% FACW species 15 x 2 = 30 0 0.0% FAC species 10 x 3 = 30 25 = Total Cover FACU species 0 x 4 - 0 0 9% OBL 1/ 88 UPL species 0 x 5 = U 8 . Column Totals: 125 (A) 160 (B) 10 11.1% OBL 0 I 0.0% Prevalence Index = B/A = 1.280 0 0.0% Hydrophytic Vegetation Indicators: 0 0.0% Dominance Test is > 50% 0 0.0% Prevalence Index is 53.0 1 0 0.0% Morphological Adaptations 1 ;.'rovide supporting 0 J 0.00% data In Remarks or on a separate sheet) 0 0.0% Problematic Hydrophytlc Vegetation 1 (1 :plain) 0 0.0% 0 0.0% r 1 Indicators of hydric soil and wetland hydrology must g0 = Total Cove be present, unless disturbed or problematic. 0 0.0% 0 o.0% Hydrophytic - Vegetation - 0 = Total Cover Present? Yes No - % Cover of Biotic Crust 0 *Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS. US Army Corps of Engineers Arid West - Version 2 Oct. 2008 SOII Sampling Point: SP 104 Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Depth Matrix Redox Features (inches) Color (m) s/o Color (moist) a/o Type I Loci Texture Remarks i 0 14 . 7.5YR 2.5/1 100% organic 100% organic 14-20 7 SYR 3/z.,.. 1 Type: C=Concentration. D=DePletion. RM=Reduced Matrix, CS=Covered or Coated Sand Grains 2Location: PL= -Pore Lining. M=Matra Hydric Soll Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils3 Histosol (Al) Histic Epipedon (A2) Sandy Redox (S5) 1 cm Muck (A9) (LRR C) Stripped Matrix (S6) ] 2 cm Muck (A10) (LRR B) Black Histic (A3) Loamy Mucky Mineral (Fl) ^ Reduced Vertic (F18) Hydrogen Sulfide (A4) Loamy Gleyed Matrix (F2) Red Parent Material (TF2) L i Stratified Layers AS R C Depleted Matrix (F3) _ ( LI 1 cm Muck A9 LRR D Redox Dark Surface (F6) Other (Explain in Remarks) IL Depleted Below Dark Surface (Ali) Depleted Dark Surface (F7) Thick Dark Surface (A12) Redox depressions (F8) Sandy Muck Mineral (Sl) Vernal Pools (F9) 3 Indicators of hydrophytic vegetation and _.I Sandy Gleyed Matrix (S4) wetland hydrology must be present. Restrictive Layer (if present): Type: Depth (inches): Hydric Soil Present? Yes No Remarks: Depths approximate; soil very wet and unconsolidated except 0-14" is very full of roots making extraction of sample difficult Hydrology Wetland Hydrology Indicators: Primarv.Indicators (minimum of one required; check all that apply) Secondary Indicators (2 or more required) Surface Water (Al) Salt Crust (B11) Water Marks (Bl) (Riverine) Vi High Water Table (A2) I Biotic Crust (B12) Sediment Deposits (B2) (Riverine) Saturation (A3) Aquatic Invertebrates (B13) Drift Deposits (133) Riverine) Water Marks (BI) (Nonriverine) _ Hydrogen Sulfide Odor (Cl) Drainage Patterns (B10) Sediment Deposits (62) (Nonriverine) Oxidized Rhizospheres along Living Roots (0) r j Dry Season Water Table (C2) Drift deposits (83) (Nonriverine) J Presence of Reduced iron (C4) Crayfish Burrows (C8) Surface Soil Cracks (66) Recent Iron Reduction in Plowed Soils (C6) r Saturation Visible on Aerial Imagery (C9) Inundation Visible on Aerial Imagery (B7) Thin Muck Surface (0) Shallow Aquitard (D3) I Water-Stained Leaves (B9) Other (Explain in Remarks) FAC-neutral Test (DS) Field Observations: Surface Water Present? Yes NO Depth (inches): 1 Water Table Present? Yes P' NO ' Depth (inches): j 0 Saturation Present? Yes ~i NO - Wetland Hydrology Present? Yes No' Depth (inches): 0 (includes cap n fringe) Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available: Remarks: Surface water varies, to 2 inches deep to 1 inc h near pit. US Army Corps of Engineers Arid West - Version 2 Oct. 2008 • • WETLAND DETERMINATION DATA FORM - Arid West Region Project/Site: Deschutes LWI City/County: Sunriver/Deschutes Sampling Date: 06-May-10 Applicant/Owner: Deschutes County OR State: OR Sampling Point: SP lOG I ( P P Merrill Section, 35 T 20 S R 10 E Ladform hi Islo l a terrace, etc.): valley bottom Local relief (concave, convex none): Flat Slope: 0.0% / 0.0 ° Subregion (LRR): LRR B Lat.: 43.8007 Long.: -121.5055 Datum: NAD 83 Soil Map Unit Name: Not available NWI classification: Are climatic/hydrologic conditions on the site typical for this time of year? Yes Ci% No (If no, explain in Remarks.) AreVegetation I I , Soil , or Hydrology ❑ significantly disturbed? Are "Normal Circumstances" present? Yes * No Are Vegetation ❑ , Soil , or Hydrology L .I naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transects, important features, etc. Hydrophytic Vegetation Present? Yes No - _ Is the Sampled Area Hydric Soil Present? Yes No within a Wetland? Yes No Wetland Hydrology Present? Yes NO C-) Remarks: On-site determination. VEGETATION - Use scientific names of plants. Dominant Species? Absolute Rel.Strat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: ) % Cover Cover Status Number of Dominant Species 1. 0 ❑ 0.0% That are 0111, FACW, or FAc: 4. (A) 2. 0 ❑ 0.0%. % Total Number of Dominant 3. 0 E] 0 0 Species Across All Strata: 4 (11) . 0% Percent of dominant Species 0 = Total Cover 100.0% (A/11) Sapling/Shrub Stratum (Plot size: ) a re , , o 1. Salix geyenana 25 100.0% FACW Prevalence index worksheet: 2. 0 I_I 0.o% Total % Cover of: Multiply by: 3. 0 I_I 0.0% oBL species 80 x 1 = 80 4. 0 ❑ 0.0% ! FAcw species 45 x 2 = 90 5. 0.,. ❑ O.D% I FAc species 0 x 3 0 25, = Total Cover IFACU species _0 x 4 = 0 Herb Stratum (Plot size: ) 0 0 C b 40 40 0% OBL x 5 = uP1 species 1, arex ne rascensis . column Totals: 125 (A) 170 (B) 2. Carex aquatilis 40 ❑ 40.0% 011L 3. ]uncus balticus 20 d❑ 20.0% FACW Prevalence Index = B/A = 1.360 4. 0 0.0% I Hydrophytic Vegetation indicators: 5. a, ❑ 0.0% ! n Dominance Test is > 50% 6. 0 ❑ 0.0°/° U Prevalence Index Is $3.0 1 7, 0 0 1 I 0.0% ❑ 0 0% ❑ 1 ! Morphological Adaptations 1 provide supporting 8 . data in Remarks or on a separate sheet) g, 0 0.0% Problematic Hydrophytit Vegetation 1 (1 :plain) 10. 0 ❑ 0.0% 11 o I I o.o°o . 1 indicators of hydric soil and wetland hydrology must 100 =Total Cover be present, unless disturbed or problematic. Woody Vine Stratum (Plot size: r FAC: Th t A OBL FACW 1. 2. % Bare Ground in Herb Stratum: 0 Remarks: 40 0 ❑ 0.0% ❑ 0.0% 0 = Total Cover % Cover of Biotic Crust 0 Hydrophytic Vegetation Yes NO Present? not defined by FWS. *Indicator suffix = National status or professional decision assigned because Regional status US Army Corps of Engineers Arid West - Version 2 Oct. 2008 SOLI Sampling Point: sp106 Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Depth Matrix Redox Features (inches) Color (moist) n o Color (moist) % Type 1 Loci Texture Remarks 0-4 OYR3 80% 2.5YR 4/6 20% C M Silt Loam root mass 4-10 10YR 3/3 80% 2.5YR 4/6 20% C M Silt Loam 10-14 10YR 3/1 80% 2.5YR 4/6 20% C M Loam 14-20 10YR 3/3 80% 2.SYR 4/6 20% C M Silt Loam Type: C=Concentration. D=Depletion. RM=Reduced Matrix, CS=Covered or Coated Sand G ~ rains =Location; PL=Pore Lining. M=Matrix Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Solls3 n Histosol (A1) ❑ Sandy Redox (SS) 1 cm Muck (A9) (LRR C) ❑ Histic Epipedon (A2) [_-f Stripped Matrix (S6) ❑ 2 cm Muck (A10) (LRR B) Black Histic (A3) ❑ Loamy Mucky Mineral (Fl) ( f Reduced Vertic (F18) Hydrogen Sulfide (A4) [ Loamy Gleyed Matrix (F2) ❑ Red Parent Material (TF2) ❑ Stratified Layers (AS) (LRR C) ❑ Depleted Matrix (F3) U Other (Explain in Remarks) 1 cm Muck (A9) (LRR D) Redox Dark Surface (F6) ❑ Depleted Below Dark Surface (All) ❑ Depleted Dario Surface (F7) ❑ Thick Dark Surface (A12) Redox depressions (F8) Sandy Muck Mineral (Si) ❑ Vernal Pools (F9) 3 Indicators of hydrophytic vegetation and Sandy Gleyed Matrix (S4) wetland hydrology must be present. Restrictive Layer (if present): Type: Depth (inches): Hydric Soil Present? Yes O No ) Remarks: HYDRIC SOILS ASSUMED BASED ON HYDROLOGY INDICATORS AND WETLAND VEGETATION . . Hydrology Wetland Hydrology Indicators: Primary. Indicators (minimum of one required; Check all that apply) Secondary indicators (2 or more required) 71 Surface Water (Al) ❑ Salt crust (Bll) Water Marks (Bl) (Riverine) ❑ High Water Table (A2) Biotic Crust (B12) Sediment Deposits (62) (Riverine) U Saturation (A3) ❑ Aquatic Invertebrates (B13) L. J Drift Deposits (B3) Riverine) ❑ Water Marks (BI) (Nonriverine) ❑ Hydrogen Sulfide Odor (Cl) ❑ Drainage Patterns (B10) ❑ Sediment Deposits (B2) (Nonriverine) ❑ Oxidized Rhizospheres along Living Roots (0) ❑ Dry Season Water Table (C2) ❑ Drift deposits (B3) (Noneriverine) ❑ Presence of Reduced Iron (C4) Crayfish Burrows (CB) ❑ Surface Soil Cracks (B6) 1 Recent Iron Reduction in Plowed Soils (C6) ❑ Saturation Visible on Aerial Imagery (C9) Inundation Visible on Aerial Imagery (B7) ❑ Thin Muck Surface (C7) Shallow Aquitard (13) J Water-Stained Leaves (B9) ❑ Other (Explain in Remarks) FAC-neutral Test (DS) Field Observations: Surface Water Present? Yes No Depth (inches): Water Table Present? Yes No Depth (inches): =16 l d Y N d l (D Saturation Present? Yes No - Wet an H Depth (inches): 12 y ogy Present? es o ro includes capillary fringe Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if avai lable: Remarks: . . US Army Corps of Engineers Arid West - Version 2 Oct. 2008 WETLAND DETERMINATION DATA FORM - Arid West Region Project/Site: Deschutes LWI City/County: Sunriver/Deschutes Sampling Date: 06-May 10 Applicant/owner: Deschutes County State: OR Sampling Point: SP 107 • Investigator(s): Alessandra Capretti, Adam Merrill Section, Township, Range: S 35 T 205 R 10E Landform (hilislope, terrace, etc.): Valley bottom Local relief (concave, convex, none): flat Slope: 0.0% / 0.0 ° Subregion (LRR): LRR B Lat.: 43.7978 Long: -121.5029 Datum: NAD 83 NWI classification: _ Soil Map Unit Name: ry/q Are climatic/hydrologic conditions on the site typical for this time of year? Yes * No 0 (If no, explain in Remarks.) Are Vegetation ❑ , Soil ❑ , or Hydrology I 1 significantly disturbed? Are "Normal Circumstances" present? Yes * No AreVegetation , Soil L , or Hydrology ❑ naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transects, important features, etc. Hydrophytic Vegetation Present? Yes J•) No - Is the Sampled Area Hydric Soil Present? Yes ` No - Yes No Yes within aWetland? No Wetland Hydrology Present? Remarks: On-site determination. VEGETATION - Use scientific names of plants. Dominant . Species? Absolute Rel.5trat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: ) % Cover - Cover Status Number of Dominant Species 0 ❑ 0.0% - That are 06L, FACW, or FAC: 3 (A) 2 0 ❑ 0.0% . Total Number of Dominant 3. 0 1 1 0.0% _ Species Across All Strata: 3 (8) 4. 0 f l 0.0% Percent of dominant Species p =Total Cover 100.0% (A/e) Sapling/Shrub Stratum (Plot size: 1. Salix geyeriana ) 10 [VI 100.0% FACW , , - J Prevalence Index worksheet: 2. 0 ❑ 0.0% i Total % Cover of: Multiply by: 3, 0 ❑ 0.0% OBL species 100 x 1 - 100 4. o. 0.o% FACW species 10 . x 2 = 20 5. 0 ❑ 0.0% FAC species 0 x 3= 0 10 = Total Cover FACU species 0 x 4 - 0 Herb Stratum (Plot size: ) 1 0 0 UPL species x S - 1. Carex a9uatilis 80 F 80.0% 013E Column Totals: 110 (A) 120 (B) 2. Carex nebrascensis 20 20.0% OBL 3. 0 ❑ 0.0% Prevalence Index = B/A = 1.091 4. 0 ❑ 0.0% Hydrophytic Vegetation Indicators: 5. 0 ❑ 0.00k V Dominance Test is a 50% 6. 0 ❑ o.0% n Prevalence Index is $3.0 1 7. 0 0,0% ❑ Morphological Adaptations 11 _ Irovide supporting 8 0 ❑ 0.0% data in Remarks or on a separate sheet) 9. 0 ❑ 0.0% ' ❑ Problematic Hydrophytic Vegetation 1 (1 plain) 10. 0 0.0% 11 a I I 0.0% . 1 Indicators of hydric soil and wetland hydrology must 100 =Total Cover be present, unless disturbed or problematic. Woody Vine Stratum (Plot size: ) 1 0 I_I 0.0% 2 0 0.0% L. 1 Hydrophytic . p , Total Cover Vegetation Present? Yes * No - % Bare Ground in Herb Stratum: 0 % Cover of Biotic Crust 0 Remarks: FACW or FAC That Are OBE *Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS. US Army Corps of Engineers Arid West - Version 2 Oct. 2008 Soil Sampling Point: SP 107 Profile Description: (Describe to the depth needed to document the indicator or conflrm the absence of Indicators.) Depth Matrix Redox Features (inches) Color (moist) N. Color (moist) % Type Loc= Texture Remarks 0-6 10YR 3/4 100% Silt Loam gravelly, Thick root mass , 100% .........6-20............ lOYR 3/2 Silty Clay.... gravelly 1 Type: C_ Concentration. D=Depletion. RM=Reduced Matrix, CS=Covered or Coated Sand Grains Location: PL=Pore Lining. M=Mats N dric soil Indicators: (Applicable to all LRRS, unless otherwise noted.) Indicators for Problematic Hydric Soils:3 Histosol (Al) Sandy Redox (S5) I - . 1 cm Muck (A9) (LRR C) Histic Epipedon (A2) Stripped Matrix (S6) 2 cm Muck (A10) (LRR B) H Black Histic (A3) Hydrogen Sulfide (A4) Loamy Mucky Mineral (Fl) L I Reduced Vertic (F18) Stratified Layers (AS) (LRR C) _ Loamy Gleyed Matrix (F2) Red Parent Material (TF2) Depleted Matrix (F3) E VI Other (Explain in Remarks) 1 cm Muck (A9) (LRR D) J Redox Dark Surface (F6) Depleted Below Dark Surface (All) Depleted Dark Surface (F7) Thick Dark Surface (A12) - Sandy Muck Mineral (Sl) Redox depressions (F8) Vernal Pools (F9) 3 Indicators of hydrophytic vegetation and I I. I Sandy Gleyed Matrix (54) wetland hydrology must be present. Restrictive Layer (if present): Type: Depth (inches): Hydric Soil Present? Yes No Remarks: peraquic moisture regime Hydrology Wetland Hydrology Indicators: Prlmart' Indicators (minimum of one required.; Check all that apply) Secondary Indicators (2 or more required) 1 Surface Water (Al) Salt Crust (1311) 1 Water Marks (131) (Riverine) [vI High Water Table (A2) _I Biotic Crust (1312) Sediment Deposits (B2) (Riverine) 1/I Saturation (A3) Aquatic Invertebrates (B13) [ Drift Deposits (B3) Riverine) i i I Water Marks (Bl) (Nonriverine) Hydrogen Sulfide Odor (Cl) Drainage Patterns (1310) _1 Sediment Deposits (132) (Nonriverine) Oxidized Rhizospheres along Living Roots (0) ! Dry Season Water Table (C2) [ Drift deposits (133) (Noneriverine) Presence of Reduced Iron (C4) Crayfish Burrows (C8) Surface Soil Cracks (B6) _ Recent Iron Reduction in Plowed Soils (C6) [ saturation Visible on Aerial Imagery (C9) Inundation Visible on Aerial Imagery (137) Thin Muck Surface (0) Shallow Aquitard (133) Water-Stained Leaves (B9) Other (Explain in Remarks) FAC-neutral Test (DS) Field Observations: Surface Water Present? Yes NO Depth (inches): Water Table Present? Yes NO - Depth (inches): 2 Saturation Present? - Yes NO - - Wetland Hydrology Present? Yes No' Depth (inches): L 0 (includes ca ilia fringe) Describe Recorded Data stream gauge, monitor well, aerial photos, previous inspections), if available: - Remarks: - - E 1-1 US Army Corps of En ineers 9 Arid West -Version 2 Oct. 2008 WETLAND DETERMINATION DATA FORM - Arid West Region Project/Site: Deschutes LWI City/County: Sunriver/Deschutes Sampling Date. 06-May-10 Applicant/Uwner: Deschutes County State: `OR J Sampling Point: SP 10$ Investigator(s): Alessandra Capretti, Adam Merrill Section, Township, Range: S 35 T 20 S R 10E Landform (hillslope, terrace, etc.): Valley bottom Local relief (concave, convex, none). flat slope: 0.0% / 0.0 ° Subregion (LRR): LRR B Lat.: 43.7445 Long.: -121.5034 Datum: NAD 83 Soil Map Unit Name: 29A: Cryaquolls, 0. to 3 percent slopes NWI classification: PSSC Are climatic/hydrologic conditions on the site typical for this time of year? Yes No - (If no, explain In Remarks.) Are Vegetation , Soil , or Hydrology ~ I significantly disturbed? Are "Normal Circumstances" present? Yes * No Are Vegetation , Soil i , or Hydrology F1 naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transects, important features, etc. Hydrophytic Vegetation Present? Yes No _ ) Is the Sampled Area Hydric Soil Present? Yes No Yes ! No within a Wetland? Wetland Hydrology Present? Yes No Remarks: On-site determination. VEGETATION - Use scientific names of plants. Dominant Species? Absolute Rel.Strat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: ) % Cover Cover Status Number of Dominant Species 1. Pinus contorts 10 7 100.0% FAC That are OBL, FACW, or FAC: 5 (A) 2. 2 0 ❑ 0.0% ❑ % Total Number of Dominant . 0 0.0 0'.0% Species Across All Strata: 5 (B) 4. o ❑ 0.o°r° 10 = Total Cover Percent of dominant Species 1D0 0% (A/B) Sapling/Shrub Stratum (Plot size: ) That Are OBL, FACW, or FAC: . 1. Betulaglandulosa 1 O - Prevalence Ind : he 2. Salix geyeriana 0 ❑ 0 o% F ACW Total % Co err of: Multiply by. 3. 0 L] 0.0% OBL species 55 x 1 - 55 4. 0 I_I 0.o% FACW species 50 x Z = 100 5. 0 1 I 0.0% ° FAC species 10 x 3 30 = 5... = Total Cover FACU species 0 . x 4 - 0 Herb Stratum (Plot size: ) 0 0 l b lti 50 ~ 50 0% FACW OPL species x S uncus a cus 1. . 2. carex aquatilis 30 IVI 30.0%° OBL i column Totals: 115 (A) 185 (e) Carex nebrascensis g. 20 LJ 20.0% OBL Prevalence Index = B/A = 1.609 4. 0 l 0.0% Hydrophytic Vegetation Indicators: 5. 0,.. 0.00k d Dominance Test is 7 so,,/. 6. .0 0.0%.. U Prevalence Index is 53.0 7. 0 ❑ 0.0% 1 1 Morphological Adaptations 1 1_ Irovide supporting 8. 0 0.0% data in Remarks or on a separate sheet) 9. 0 % ° Problematic Hydrophytic Vegetation 1 (1 :plain) 10. 0 . ❑ 0.0% 11. o ❑ o.o% 1 indicators of hydric soil and wetland hydrology must 100 1.0. 0 =Total Cover present, unless disturbed or problematic. Woody Vine Stratum (Plot size: ) 1. 0 ❑ 0.0% 2. 0 ❑ 0.o% Hydrophytic 0 = Total Cover Vegetation Present? Yes ' No % Bare Ground In Herb Stratum: 0 % Cover of Biotic Crust 0 Remarks: `Indicator suffix = National status or professio nal decision assigned because Regional status not defined by FWS. US Army Corps of Engineers Arid West - Version 2 Oct. 2008 Soil Sampling Point: 5P 108 Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Depth Matrix Redox Features...... ) (inches color (moist) Color (moi) 0/0 Type 1 Loci Texture Remarks 0-4 10YR 3/3 80°i° 2.5YR 20% M root mass 4-10 10YR 3/3 80% 2.5YR 4/6 20% C M 10-20 10YR 3/1 80% 2.SYR 4/6 20% C M 1 Type: C=Concentration. D=Depletion. RM=Reduced Matrix, CS=Covered.......,. . or Coated Sand Grains 'Location: PL=Pore Lining. M=Mats Hydrlc Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric SoilsP Histosol (AS) ❑ Sandy Redox (S5) ❑ 1 cm Muck (A9) (LRR C) ❑ Histic Epipedon (A2) Stripped Matrix (S6) 2 cm Muck (A10) (LRR B) Black Histic (A3) ❑ Loamy Mucky Mineral (Fi) ❑ Reduced Vertic (F18) n Hydrogen Sulfide (A4) ❑ Stratified Layers (AS) (LRR C) J Loamy Gleyed Matrix (F2) Red Parent Material (TF2) n 1 cm Muck (A9) (LRR D) ❑ Depleted Matrix (F3) Other (Explain in Remarks) J Redox Dark Surface (F6) Depleted Below Dark Surface (Ali) [7 Depleted Dario Surface (F7) n Thick Dark Surface (A12) J Redox depressions (F8) Sandy Muck Mineral (Sl) ❑ Vernal Pools (F9) 3 Indicators of hydrophytic vegetation and n Sandy Gleyed Matrix (S4) wetland hydrology must be present. Restrictive Layer (if present): Type: Depth (inches). Hydric Soil Present? Yes l.~) No Remarks: HYDRIC SOILS ASSUMED BASED ON HYDROLOGY INDICATORS. Hydrology Wetland Hydrology Indicators: Primary . Indicators (minimum of one required; check all that apply) Secondary Indicators (2 or more required) Surface Water (Al) ❑ Salt Crust (B11) Water Marks (Bl) (Riverine) ❑ High Water Table (A2) I I Biotic Crust (B12) J Sediment Deposits (B2) (Riverine) U Saturation (A3) Aquatic Invertebrates (B13) a Drift Deposits (B3) Riverine) [ Water Marks (BS) (Nonriverine) Hydrogen Sulfide Odor (Cl) Drainage Patterns (Bl0) J Sediment Deposits (B2) (Nonriverine) n Oxidized Rhizospheres along Living Roots (0) ❑ Dry Season Water Table (C2) Drift deposits (B3) (Noneriverine) ❑ Presence of Reduced Iron (C4) L. I Crayfish Burrows (C8) ❑ Surface Soil Cracks (B6) !_I Recent Iron Reduction in Plowed Soils (C6) ❑ Saturation Visible on Aerial Imagery (C9) Inundation Visible on Aerial Imagery (B7) a Thin Muck Surface (C7) Shallow Aquitard (D3) ❑ Water-Stained Leaves (B9) Other (Explain in Remarks) [ FAC-neutral Test (DS) Field Observations: Surface Water Present? Yes 0 No Depth (inches): Water Table Present? Yes No Depth (inches): Yes No ) Saturation Present? - s ca ilia fnn Yes' No (include-tea 9e) Wetland Hydrology Present? Depth (inches): 12 Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if avai lable: Remarks........ US Army Corps of Engineers Arid West - Version 2 Oct. 2008 WETLAND DETERMINATION DATA FORM - Arid West Region Project/Site: Deschutes LWI City/County: Sunriver/Deschutes Sampling Date: 06-May-10 Appllcant/owner: Deschutes County State: lOR Sampling Point: SP 109 Investigator(s): Alessandra Capretti, Adam Merrill Section, Township, Range: S 34 T 20 S R 10 E Landform (hillslope, terrace, etc.): Valley bottom Local relief (concave, convex, none): flat Slope: 0.0% / 0.0 ° Subregion (LRR): LRR B Lat.: 43.7947 Long.: -121.5082 Datum: NAD 83 Soil Map Unit Name: 29A: Cryaquolls, 0 to 3 percent slopes NWI classification: pSSC Are climatic/ hydrologic conditions on the site typical for this time of year? Yes * No (If no, explain in Remarks.) Are Vegetation ❑ , Soil ❑ , or Hydrology ❑ significantly disturbed? Are "Normal Circumstances" present? Yes * No 0 Are Vegetation , Soil , or Hydrology naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transects, important features, etc. Hydrophytic Vegetation Present? Yes No C-) Hydric Soil Present? Yes Is the Sampled Area No Yes No Wetland Hydrology Present? Yes within a Wetland? No (D Remarks: On-site determination. VEGETATION - Use scientific names of plants. Dominant species? Absolute Rel.Strat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: ) % Cover Cover Status Number of Dominant Species 1. 0 [ I 0.0°k That are OBL, FACW, or FAC: 2 (A) 2. 0 ❑ 0.0% 3. 0 0.0% Total Number of Dominant Species Across All Strata: 2 (B) 4. 0 [_.J 0.0% 0 = Total Cover Percent of dominant Species ° 100 0 /o (A/e) Sapling/Shrub Stratum (Plot size: ) . That Are OBL, FACW, or FAC: 1. 0 Prevalence Index worksheet: 2. 0 ] 0.0°/. Total % Cover of: Multiply by; . . 3. 0 ❑ 0.0% ospecies 100 x 1 - 100 4. 0 ❑ 0.o% FACW species 0 x 2= 0 5. 0 J 0.0% FAC species 0 x 3= 0 0 = Total Cover I FACU species 0 x 4= 0 Herb Stratum (Plot size: ) 0 0 1 Carex nebrascensis 50 50.0% OBL x 5 UPL species , (B) Column Totals: 100 (A) 100 Carex aGuatilis 2. 50 ° ❑ 50. 0/° OBL 3. 0 , ❑ 0.0% Prevalence Index = B/A = 1.000 4. I] 0.0% Hydrophytic Vegetation Indicators: 5. 0 [.J 0.0% Idl Dominance Test is 7 so% 6, 0 1 0.0% U Prevalence Index is 53.0 1 0 ❑ 0.0./. _ 7 [ Morphological Adaptations 1 ;.'rovide supporting 8. 0 ❑ o.o% data In Remarks or on a separate sheet) 9. 0 [ 0.0% Problematic Hydrophytic Vegetation 1 (1 :plain) 10. 0 ❑ 0.0% 11. 0 10.0% 1 Indicators of hydric soil and wetland hydrology must 100 = Total Cover be present, unless disturbed or problematic. Woody Vine Stratum (Plot size: ) 1. 0 i I 0.0% 2. 0 7 0.0°k Hydrophytic Vegetation - - 0 - Total Cover iPresent? Yes No 0/6 Bare Ground In Herb Stratum: 0 % Cover of Biotic Crust 0 Remarks: `Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS. US Army Corps of Engineers Arid West - Version 2 Oct. 2008 Soil Sampling Point: SP 109 i Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Depth Redox Features (inches) for (moist) 0 Pe , Loci Color (moist) Texture Remarks O /l 100% Silt Loam I 1 Type: C_ Concentration. D=Depletion. RM=Reduced Matrix, CS=Covered or Coated Sand Grains ?Location.: PL=Pore Lining M=Matra Hydric Soil Indicators: (Applicable to all LRRS, unless otherwise noted.) Indicators for Problematic Hydric SoilsP ❑ Histosol (Al) ❑ Sandy Redox (S5) 1 cm Muck (A9) (LRR C) ❑ Histic Epipedon (A2) ❑ Stripped Matrix (S6) 2 cm Muck (A10) (LRR B) ❑ Black Histic (A3) ❑ Loamy Mucky Mineral (Fl) ❑ Reduced Vertic (Fi8) ~J Hydrogen Sulfide (A4) ❑ Loamy Gleyed Matrix (F2) J Red Parent Material (TF2) Stratified Layers (AS) (LRR C) Depleted Matrix (F3) [i Other (Explain in Remarks) 1 cm Muck (A9) (LRR D) ❑Redox Dark Surface (F6) ❑ Depleted Below Dark Surface (All) I ~ Depleted Dark Surface (F7) Thick Dark Surface (A12) TLI Redox depressions (F8) Sandy Muck Mineral (Sl) Vernal Pools (F9) 3 Indicators of hydrophytic vegetation and ❑ Sandy Gleyed Matrix (S4) wetland hydrology must be present. Restrictive Layer (if present): Type: Depth (inches): Hydric Soil Present? Yes (i) No ( ) Remarks: HYDRIC SOILS ASSUMED BASED ON PERSISTANT SATURATION (AQUIC MOISTURE REGIME). Hydrology Wetland Hydrology Indicators: Primary Indicators (minimum of one required; check all that awly) Secondary Indicators (2 or more required) ❑ Surface Water (Ai) Salt Crust (1311) ❑ Water Marks (81) (Riverine) I I High Water Table (A2) ❑ Biotic Crust (B12) Sediment Deposits (B2) (Riverine) n Saturation (A3) ❑ Aquatic Invertebrates (B13) U Drift Deposits (B3) Riverine) ❑ Water Marks (Bl) (Nonriverine) ❑ Hydrogen Sulfide Odor (Cl) I I Drainage Patterns (B10) Sediment Deposits (B2) (Nonriverine) 7 Oxidized Rhizospheres along Living Roots (0) ❑ Dry Season Water Table (C2) [ El Drift deposits (B3) (Noneriverine) ❑ Presence of Reduced Iron (C4) ! Crayfish Burrows (C8) Surface Soil Cracks (B6) Recent Iron Reduction in Plowed Soils (C6) _ i Saturation Visible on Aerial Imagery (C9) ❑ Inundation Visible on Aerial Imagery (B7) ❑ Thin Muck Surface (C7) Shallow Aquitard (D3) ❑ Water-Stained Leaves (B9) ❑ Other (Explain in Remarks) FAC-neutral Test (D5) Field Observations: Surface Water Present? Yes No Depth (inches): Water Table Present? Yes No Depth (inches): _ Y N ` ) Saturation Present? Yes No es o - Depth (inches): Wetland Hydrology Present? 0~ (includes capillary fringe) Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available: Remarks: U5 Army Corps of Engineers Arid West -Version 2 Oct. 2008 WETLAND DETERMINATION DATA FORM - Arid West Region Project/Site: Deschutes LWI City/County: Sunriver/Deschutes Sampling Date: 06-May-10 Applicant/Owner: Deschutes County State: IOR Sampling Point: SP 110 Investigator(s): Alessandra Capretti, Adam Merrill Section, Township, Range: S 34 T 20 S R 10 E Landform (hilislope, terrace, etc.): Valley bottom Local relief (concave, convex, none): flat Slope: 0.0% / 0.0 ° Subregion (LRR): LRR B Lat.: 43,7917 Long: -121.5096 Datum: NAD 83 Soil Map Unit Name: 29A: Cryaquolls, 0 to 3 Percent slopes NWI classification: PSSC Are climatic/ hydrologic conditions on the site typical for this time of year? Yes * No > (If no, explain in Remarks.) Are Vegetation , Soil , or Hydrology significantly disturbed? Are "Normal Circumstances" present? Yes No Are Vegetation n , Soil n , or Hydrology n naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transects, important features, etc. Hydrophytic Vegetation Present? Yes No Hydric Soil Present? Is the Sampled Area Yes ' No Yes * No Wetland Hydrology Present? - Yes No within a Wetland? ~ Remarks: On-site determination. VEGETATION - Use scientific names of plants, Dominant Species? Absolute Rel-Strat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: ) % Cover Cover Status Number of Dominant Species 1. 0 ❑ 0.0% i That are 013L, FACW, or FAC: 3 (A) 2. 0 ❑ 0.0% 3, 0 ❑ 0.0°/n Total Number of Dominant Species Across All Strata: 3 (13) 4. 0 ❑ 0.0% 0 Total Cover Percent of dominant Species o 100.0% (A/B) Sapling/Shrub Stratum (Plot size: ) That Are OBL, FACW, or FAC: 1. Salix geyeriana 30 7 100.0% FACW Prevalence index worksheet: 2, 0 n 0.0% Total % Cover of: Multiply by: 3. 0 n 0.0% 0species 100 x 1 = 100 4. 0 F I 0.0% FACW species 0 x2- 60 5. 0 n 0.0% I O0 FAC species x 3 = 30 = Total Cover FACU species 0 x 4 = 0 Herb Stratum (Plot size: 0 0 C tili 60 [VI 60 0% OBL UPL species x 5 - arex aqua s 1. . Column Totals: 130 (A) 160 (B) 2, Carex nebrascensis 40 U 40.00% 0131- 3. 0 ❑ 0.0% Prevalence Index = B/A = 1.231 4. 0 0.0% Hydrophytic Vegetation Indicators: 5 0 0.0% d~ Dominance Test is 7 s0% 6, 0 L] 0.0% ~i Prevalence index is 53.0 1 7. 0 ❑ 0.0% ~ I Morphological Adaptations 11. ,'rovide supporting 8_ 0 ° 1 I 0.0% data in Remarks or on a separate sheet) 9. 0 LJ 0.0% ❑ Problematic Hydrophytic Vegetation 1 (1 cplain) 10. 0 LJ o.o% 77 . o ❑ o.o% . 1 indicators of hydric soil and wetland hydrology must 100 =Total Cover be present, unless disturbed or problematic. Woody Vine Stratum (Plot size: ) 1, 0 n 0.0% 2. o n 0.0% Hydrophytic - Total Cover 0 Vegetation Present? Yes No O/o Bare Ground in Herb Stratum: 0 % Cover of Biotic Crust 0 Remarks: • *Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS. US Army Corps of Engineers Arid West - Version 2 Oct. 2008 Soil sampling Point: SP 110 Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Depth Matrix Redox Features (inches) Color (moist) % Color (moist) % Type 1 LoC2 Texture Remarks 0-7 10YR 2/1 100% Silt dense root mass 7-10 10YR 2/1 60% 2.5YR 3/6 40% C M Silt 10-20 5Y 7/3 70% 10YR 4/6 30% C M Silty Clay 1 T C=Concentration. D-De letion. RM=Reduced Matrix, CS=Covered o Type: - p or Coated Sand Grains ZLocation: PL=Pore Lining. M=Mats Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydrlc Solls3 ❑ Histosol (Al) Sandy Redox (S5) ❑ 1 cm Muck (A9) (LRR C) ❑ Histic Epipedon (A2) ❑ Stripped Matrix (S6) 2 cm Muck (A10) (LRR B) ❑ Black Histic (A3) Hydrogen Sulfide (A4) Loamy Mucky Mineral (Fl) ❑ Reduced Vertic (1`18) Stratified Layers (A5) (LRR C) ❑ Loamy Gleyed Matrix (F2) Red Parent Material (TF2) ❑ 1 cm Muck (Ag) (LRR D) ❑ Depleted Matrix (F3) ❑ Other (Explain in Remarks) L Redox Dark Surface (F6) Depleted Below Dark Surface (All) ❑ Depleted Dark Surface (F7) ❑ Thick Dark Surface (A12) Sandy Muck Mineral (Sl) ❑ Redox depressions (F8) 3 Indicators of hydrophytic vegetation and ❑ Sandy Gleyed Matrix (S4) ❑ Vernal Pools (F9) wetland hydrology must be present. Restrictive Layer (if present): Type: Depth (inches): Hydric Soil Present? Yes (tl No Remarks: HYDRIC SOILS ASSUMED BASED ON HYDROLOGY INDICATOR. Hydrology Wetland Hydrology Indicators: Primary Indicators (minimum of one required; check all that apply) Secondary Indicators (2 or more required) Surface Water (Al) ❑ Salt Crust (Bll) I I Water Marks (Bl) (Riverine) ❑ High Water Table (A2) ❑ Biotic Crust (B12) Ll Sediment Deposits (B2) (Riverine) V1 Saturation (A3) ❑ Aquatic Invertebrates (B13) Drift Deposits (B3) Riverine) ❑ Water Marks (Bl) (Nonriverine) ❑ Hydrogen Sulfide Odor (Cl) ❑ Drainage Patterns (B10) ❑ Sediment Deposits (B2) (Nonriverine) L Oxidized Rhizospheres along Living Roots (0) _ Dry Season Water Table (C2) Drift deposits (B3) (Noneriverine) ❑ Presence of Reduced Iron (C4) ❑ Crayfish Burrows (C8) Surface Soil Cracks (B6) ❑ Recent Iron Reduction in Plowed Soils (C6) Saturation Visible on Aerial Imagery (Cg) El Inundation Visible on Aerial Imagery (B7) Thin Muck Surface (C7) Shallow Aquitard (D3) F Water-Stained Leaves (B9) Other (Explain in Remarks) FAC-neutral Test (D5) Field Observations: Surface Water Present? Yes C) No ' Depth (inches): Water Table Present? Yes 0 No Depth (inches): J Saturation Present? i) O 10 Wetland Hydrology Present? (includes capillary fringe) Yes - No Depth (inches) Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available: U5 Army Corps of Engineers Arid West - Version 2 Oct. 2008 • Yes No 0 • WETLAND DETERMINATION DATA FORM - Arid West Region Project/Site: Deschutes LWI City/County: Sunriver/Deschutes Sampling Date:. 06-May-10 Applicant/Owner: Deschutes County State: LOR Sampling Point: SP 111 Investigator(s): Alessandra Capretti, Adam Merrill Section, Township, Range: 5 3 T 215 R 10E Landform (hillslope, terrace, etc.): Valley bottom Local relief (concave, convex, none): flat Slope: 0.0% / 0.0 ° Subregion (LRR): LRR B Lat.: 43.7795 Long.: -121.5162 Datum: NAD 83 Soil Map Unit Name: 29A: CryagUOlis, 0 to 3 percent slopes NWI classification: pEMC Are climatic/ hydrologic conditions on the site typical for this time of year? Yes No ( (If no, explain in Remarks.) Are Vegetation , Soil ] , or Hydrology I i significantly disturbed? Are "Normal Circumstances" present? Yes C4) No AreVegetation , Soil ❑ , or Hydrology L-.l naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transects, important features, etc. Hydrophytic Vegetation Present? Yes No C_) Hydric Soil Present? Is the Sampled Area Yes No Yes No C) Wetland Hydrology Present? within a Wetland? Yes ! No Remarks: On-site determination. VEGETATION - Use scientific names of plants. Dominant Species? Absolute Rel.Strat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: ) % Cover Cover Status 1, Pinus contorts 5 ❑ 100.09% i Number of Dominant Species FAC That are OBL, FACW, or FAC: 3 (A) 2. 0 ❑ 0.0% 3. 0 ❑ 0.0% Total Number of Dominant Species Across All Strata: 3 (e) 4. 0 ❑ 0.0% 5 = Total Cover Percent of dominant Species 1000°/ AB Sapling/Shrub Stratum (Plot size: ) 1, Salix geyeriana 2. 3. 4. 5. Woody Vine Stratum (Plot size: 1. 2. Bare Ground in Herb Stratum: 0 Remarks: Agrostis sp. assumed FAC. That Are OBL, FACW, or FAC: ° > 20 v'❑ 100.0% FACW Prevalence Index worksheet: 0 0.0% Total. % Cover of: Multiply by: , 0 ❑ 0.00% OBL species 90 x 1 - 90 0 . 0. 0 %0 species CW 0 0.0% 10 x 3 30 FA species 20 = Total Cover FACU species 0 x 4 = 0 80 U 84 20% OBL UPL species 0 x 5 - 0 . Column Totals: 120 (A) 160 (B) 10 LJ 10.5o/. 013L 5 ❑ 5.3% FAC Prevalence Index = B/A = 1.333 0 0.0% Hydrophytic Vegetation Indicators: 0 ❑ 0.0% U Dominance Test is a 50% 0 ❑ 0.0% Prevalence Index Is 53.0 1 0 0.0% Morphological Adaptations 1 - rovide supporting 0 ❑ 0.0% . data In Remarks or on a separate sheet) 0 0.0% Problematic Hydrophytic Vegetation 1(1 :plain) 0 0.0% 0 ❑ 0 .0% . Indicators of hydric soil and wetland hydrology must 95 = T otal Cover i be present, unless disturbed or problematic. 0 ❑ 0.0% 0 ❑ 0.0% Hydrophytic Vegetation - 0 = Total Cover Present? Yes * No (2 % Cover of Biotic Crust 0 `Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS. US Army Corps of Engineers Arid West - Version 2 Oct. 2008 Soil Sampling Point: $P111 Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Depth . _ _ Matrix Redox Features (inches) Color (moist) % Color (moist) % Type 1 Loc= Texture Remarks 0-8 10YR 2/1 100% Silty Clay ROOT MASS 8-11 10YR 2/1 1000/0 Silty Clay 11-20 2.5Y 7/4 70% 2.5YR 4/8 30% C M Silty Clay I Type: C-Concentration. D=Deple tion. RM=Reduced Matrix, CS-Covered or Coated Sand Grains zLocation: PL=Pore Lining. M=Matra Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils:3 ❑ Histosol (Al) ❑ Sandy Redox (SS) ❑ 1 cm Muck (A9) (LRR C) I l I Histic Epipedon (A2) ❑ Stripped Matrix (S6) ❑ 2 cm Muck (A10) (LRR B) ❑ Black Histic (A3) Loamy Mucky Mineral (Fl) I Reduced Vertic (F18) Hydrogen Sulfide (A4) ❑ Loamy Gleyed Matrix (F2) ❑ Red Parent Material (TF2) 7 Stratified Layers (AS) (LRR C) ❑ Depleted Matrix (6) Other (Explain in Remarks) 1 cm Muck (A9) (LRR D) ❑ Redox Dark Surface (F6) [ Depleted Below Dark Surface (All) ❑ Depleted Dark Surface (F7) Thick Dark Surface (A12) ❑ ~ Redox depressions (F8) r Sandy Muck Mineral (Sl) . ❑ Vernal Pools (F9) 3 Indicators of hydrophytic vegetation and Sandy Gleyed Matrix (S4) wetland hydrology must be present. Restrictive Layer (if present): Type: Depth (inches): Hydric Soil Present? Yes No Remarks: HYDRIC SOILS ASSUMED BASED ON PERSISTANT SATURATION (AQUIC MOISTURE REGIME). Hydrology Wetland Hydrology Indicators: Primary. Indicators (minimurn of one required: check all that apply) Secondary Indicators (2 or more required) ❑ Surface Water (Al) ❑ Salt Crust (BlI) ❑ Water Marks (Bl) (Riverine) ❑ High Water Table (A2) Biotic Crust (B12) Sediment Deposits (82) (Riverine) W Saturation (A3) [J Aquatic Invertebrates (B13) ❑ Drift Deposits (B3) Riverine) ❑ Water Marks (Bl) (Nonriverine) L Hydrogen Sulfide Odor (Cl) ❑ Drainage Patterns (B10) ❑ Sediment Deposits (B2) (Nonriverine) Oxidized Rhizospheres along Living Roots (0) Dry Season Water Table (C2) Drift deposits (B3) (Nonriverine) ❑ Presence of Reduced Iron (C4) ❑ Crayfish Burrows (CS) ❑ Surface Soil Cracks (B6) Recent Iron Reduction in Plowed Soils (C6) Saturation Visible on Aerial Imagery (C9) ❑ Inundation Visible on Aerial Imagery (87) a Thin Muck Surface (C7) [ Shallow Aquitard (D3) ❑ Water-Stained Leaves (B9) ii Other (Explain in Remarks) FAC-neutral Test (135) Field Observations: Surface Water Present? Yes 0 No ! Depth (inches): - Water Table Present? Yes No Depth (inches): I1 18~ Saturation Present? Yes No Wetland Hydrology Present? Depth (inches): 0~ (includes capillary fringe)___. _ Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available: Remarks: Yes * No • • US Army Corps of Engineers Arid West - Version 2 Oct. 2008 WETLAND DETERMINATION DATA FORM - Arid West Region Project/Site: Deschutes LWI City/County: Sunriver/Deschutes Sampling Date: 08 May-10 Applicant/Owner: Deschutes County State: LOR Sampling Point: SP 112 • Investigator(s): Alessandra Capretti, Adam Merrill Section, Township, Range: 5 3 T 215 R 10 E Landform (hillslope, terrace, etc): Valley bottom Local relief (concave, convex, none): hummocky Slope: 0.0% / 0.0 ° Subregion (LRR): LRR B Lat.: 43.7866 Long.: -121.5143 Datum: NAD 83 Soil Map Unit Name: 29A: Crydquoll5, 0 to 3 percent slopes NWI classification: PEMC Are climatic/ hydrologic conditions on the site typical for this time of year? Yes * No (If no, explain in Remarks.) Are Vegetation I , Soil I I , or Hydrology significantly disturbed? Are "Normal Circumstances" present? Yes * No Are Vegetation 1- , Soil ❑ , or Hydrology ❑ naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transects, important features, etc. Hydrophytic Vegetation Present? Yes 4) No - _ Is the Sampled Area Hydric Soil Present? Yes NO - i within a Wetland? Yes No Wetland Hydrology Present? Yes No - Remarks: On-site determination VEGETATION - Use scientific names of plants. Dominant Species? Absolute Rel.Strat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: ) % Cover Cover Status Number of Dominant Species 1. 0 0.0% That are OBL, FACW, or FAC: 3 (A) 2. 0 0.0% 3 0 0 0% Total Number of Dominant . . Species Across All Strata: 3 (B) 4. 0 ❑ 0.0% 0 Total Cover = Percent of dominant Species Sapling/Shrub Stratum (Plot size: ) That Are OK, FACW, or FAC: 100.0% (A/13) 1. Salix geyeriana 5 100.0% FACW Prevalence Index worksheet: 2. 0 ❑ 0.0% Total % over of. Multiply by: /o C, 3. o _.1 0.0% obi. species 60 x 1 = 60 4. 0 . 0.0% FACW species 5 x Z - 10 5. 0 0.0% FAC species 40 x 3 = 120 5 = Total Cover FACU species 0, x 4 = 0 , Herb Stratum (Plot size: 0 0 Ca e a uatilis 60 DV 60 0% OBL = x 5 UPL species 1. r x q . Column Totals: 105 (A) 190 (B) 2. Agrostis 5p. 40 U 40.00/a FAC 3. 0 ❑ o.o% Prevalence Index = B/A = 1.810 4. 0 ❑ 0.o% Hydrophytic Vegetation Indicators: 5. 0 1---1 0.0% Dominance Test is > 50% 6. 0. ❑ o.0% Prevalence Index is 53.0 1 7. 0. 0 r 0.0% ❑ 0 0% ] Morphological Adaptations 1 ;.1rovide supporting 8. . data in Remarks or on a separate sheet) 9. 0 J 0.0% ❑ Problematic Hydrophytic Vegetation 1 (1 :plain) 10. 0 0.0% 11. 0 ❑ 0-mo 1 Indicators of hydric soil and wetland hydrology must 100 = Total Cover be present, unless disturbed or problematic. Woody Vine Stratum (Plot size: ) 7 . 0 1 7 0.0% 2. 0 ❑ 0.0% Hydrophytic Vegetation 0 = Total Cover present? Yes * No % Bare Ground In Herb Stratum: 0 % Cover of Biotic Crust 0 Remarks: *Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS. US Army Corps of Engineers Arid West - Version 2 Oct. 2008 Soil Sampling Point: SP 112 Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of Indicators.) Depth Matrix Redox Features t C (inches) Color (mois Color (moist) % Type I Loc2 Texture Remarks 3 o l2 100k 0 S OYR Silt Loam root mass 5-10 IOYR 2/1 100% Silt Loam 10-20 10YR 3/2 100% Silt Loam I Type: C=Concentration. D=Depletion. RM=Red. . duced Matrix, CS=Covered or Coated Sand Grains xLocation: PL=Pore Lining. M=Matrbc ~ Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric SoilsP ❑ Histosol (Al) ❑ Sandy Redox (55) 1 cm Muck (A9) (LRR C) ❑ Histic Epipedon (A2) El Stripped Matrix (S6) ❑ 2 cm Muck 010) (LRR B) ❑ Black Histic (A3) I I Loamy Mucky Mineral (Fl) ❑ Reduced Vertic (1`18) Hydrogen Sulfide (A4) ❑ Loamy Gleyed Matrix (F2) ❑ Red Parent Material (TF2) Stratified Layers (A5) (LRR C) ❑ Depleted Matrix (F3) n Other (Explain in Remarks) ❑ 1 cm Muck (A9) (LRR D) Redox Dark Surface (F6) Depleted Below Dark Surface (All) ❑ Depleted Dark Surface (F7) ❑ Thick Dark Surface (A12) ;Redox depressions (F8) Sandy Muck mineral (51) ❑ Vernal Pools (F9) 3 Indicators of hydrophytic vegetation and Sandy Gleyed Matrix (54) ❑ wetland hydrology must be present. Restrictive Layer (If present): Type: Depth (inches): Hydric Soil Present? Yes No C' Remarks: aquic moisture regime Hydrology Wetland Hydrology Indicators: Primary. Indicators (minimum. of one required; check all that apply) Secondary Indicators (2 or more required) ❑ Surface Water (Al) Salt Crust (1311) ❑ Water Marks (Bl) (Riverine) ❑ High Water Table (A2) El Biotic Crust (812) Sediment Deposits (82) (Riverine) n Saturation (A3) ❑ Aquatic Invertebrates (B13) Drift Deposits (B3) Riverine) ❑ Water Marks (Bl) (Nonriverine) 17 Hydrogen Sulfide Odor (Cl) ❑ Drainage Patterns (810) ❑ Sediment Deposits (132) (Nonriverine) ❑ Oxidized Rhizospheres along Living Roots (0) ` J Dry Season Water Table (C2) Drift deposits (83) (Nonriverine) Presence of Reduced Iron (C4) ❑ Crayfish Burrows (CS) ❑ Surface Soil Cracks (66) ❑ Recent Iron Reduction in Plowed Soils (C6) ❑ Saturation Visible on Aerial Imagery (C9) Inundation Visible on Aerial Imagery (87) Thin Muck Surface (C7) I ] Shallow Aquitard (D3) ❑ Water-Stained Leaves (B9) ❑ Other (Explain in Remarks) ❑ FAC-neutral Test (D5) Field Observations: Surface Water Present? Yes No J) Depth (inches): Water Table Present? Yes 0 No J) Depth (inches): J Yes No > Saturation Present. Yes No Depth (inches): 0 Wetlan - d Hydrology Present? Sincludes capillary fringe) Describe Recorded Data (stream gauge, moni tor well, aerial photos, previous inspections), i available: i Remarks: - US Army Corps of Engineers Arid West - Version 2 Oct. 2008 WETLAND DETERMINATION DATA FORM - Arid West Region Project/Site: Deschutes LWI City/County: Sunriver/Deschutes Sampling Date: 07-May-10 Applicant/Owner: Deschutes County State: OR Sampling Point: SP 113 Investigator(s): Lan Alessandra Capretti, Adam Merrill Section, Township, Range: T 20S R 10E dform (hillsope, terrace etc.): Valley bottom Local relief (concave, convex, none): hummocky Slope: 0.0% / 0.0 ° Subregion (LRR): LRR B Lat.: 43.7908 Long.: -121.5039 Datum: NAD 83 Soil Map Unit Name: W; Water NWI classification: Are climatic/hydrologic conditions on the site typical for this time of year? Yes * No > (If no, explain in Remarks.) Are Vegetation 1 Soil Hydrology El significantly disturbed? Are "Normal Circumstances" present? Yes No - , L , or Are Vegetation l , Soil ❑ , or Hydrology ❑ naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transects, important features, etc. Hydrophytic Vegetation Present? Yes No Is the Sampled Area Hydric Soil Present? Yes No within a Wetland? Yes * No ~ Wetland Hydrology Present? Yes No Remarks: On-site determination. VEGETATION - Use scientific names of plants. Dominant Species? Absolute Rel.Strat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: ) % Cover Cover Status Number of Dominant Species 1. 0 ❑ 0.0% That are OBL, FACW, or FAC: 2 (A) 2. 0 ❑ o.0% 3 ❑ Total Number of Dominant . 0 0.0% Species Across All Strata: 3 (B) 4. 0 ❑ 0.0°r° 0 = Total Cover Percent of dominant Species ° Sapling/Shrub Stratum (Plot size: ) that Are OBL, FACW, or FAC: 1. Salix geyerIana 10 ❑ 100.0% Prevalence Index worksheet: 2. 0 0.0% Total % Cover of: Multiply by: 3. 0 0.0% oBL species 90 x 1 - 90 4. 0 [ 0.0% FACW species 10 x z = 20 0 0.0% FAC species 0 x 3= 0 10 = Total Cover I FACU species 0 x 4 - 0 Herb Stratum (Plot size: ) 0 C b i 30 0 0% n uPL species x 5 = arex nee rascens s . 3 O8L Column Totals: 100 (A) 110 (a) Carex a uatilis 2. 60 ❑ 60.0% OBL 3 ]uncus balticus 10 ❑ 10.0% FACW Prevalence Index = B/A = 1.100 0 ❑ 0.0% Hydrophytic Vegetation Indicators: 5. 0 0.0% V1 Dominance Test is 7 so% 6. 0 ~ 0.0% U Prevalence index is 53.0 1 0 ❑ 0.0% ❑ ❑ Morphological Adaptations 1 ~.'rovide supporting 8. 0 0.0% data In Remarks or on a separate sheet) 9. 0 ❑ o.o% Problematic Hydrophytic Vegetation 1(1 :plain) 10. o 0.0% 11. o ❑ 0.0% Indicators of hydric soil and wetland hydrology must 100 = Total Cover be present, unless disturbed or problematic. Woody Vine Stratum (Plot size: ) 1 0 ❑ 0.0% 2. 0 [ 0.0% Hydrophytic 0 = Total Cover Vegetation Present? Yes J No % Bare Ground in Herb Stratum: 0 % Cover of Biotic Crust 0 Remarks: *Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS. US Army Corps of Engineers 66.7 /o (A/131 Arid West - Version 2 Oct. 2008 Soil Sampling Point: sp113 Profile Descri to the depth needed to document the Indicator or confirm the absence of Indicators.) ption- (Describe De~ Matrix Redox Features (inches) Color (moist) ° Color (moist) °7o Types Locz Texture Remarks 0-3 OYR2 10 /a Silty Clay Loam thick root mass 3-8 10YR 3/2 100% Silty Clay Loam B-20 IOYR 1 100% Silty Clay Loam 1 Type: C=Concentration. D=Depletion, RM=Reduced Matrix, CS=Covered or Coated Sand Grains zLocation: PL=Pore Lining. M=Matrix Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils:3 ❑ Histosol (Ai) Sandy Redox (S5) 1 cm Muck (A9) (LRR C) ❑ Histic Epipedon (A2) ❑ Stripped Matrix (S6) ❑ 2 cm Muck (A10) (LRR B) ❑ Black Histic (A3) Lj Hydrogen Sulfide (A4) I Loamy Mucky Mineral (FS) I - I Reduced VertiC (FIB) ❑ Stratified Layers (AS) (LRR C) ❑ Loam Gle ed Matrix (F2 Y Y ) ❑ Red Parent Material (TF2) 1 cm Muck (A9) (LRR D) ❑ Depleted Matrix (F3) ~J Other (Explain in Remarks) ❑ Redox Dark Surface (F6) ❑ Depleted Below Dark Surface (All) I I Depleted Dark Surface (F7) F I Thick Dark Surface (A12) ❑ Redox depressions (FB) ❑ Sandy Muck Mineral (Sl) Vernal Pools (F9) 3 Indicators of hydrophytic vegetation and Sandy Gleyed Matrix (S4) - wetland hydrology must be present. Restrictive Layer (if present): TYpe Depth (inches): Hydric Soil Present? Yes No ) Remarks: HYDRIC SOILS ASSUMED BASED ON HYD ROLOGY INDICATORS. Hydrology Wetland Hydrology Indicators: Primary indicators .(minimum. Qf one required, check all that apply) Secondary indicators (2 or more required) ❑ Surface Water (Al) Salt Crust (BSS) Water Marks (BI) (Riverine) L l High Water Table (A2) ❑ Biotic Crust (612) ❑ Sediment Deposits (62) (Riverine) k Saturation (A3) ❑ Aquatic Invertebrates (B13) Drift Deposits (B3) Riverine) Water Marks (BS) (Nonriverine) ❑ Hydrogen Sulfide odor (Cl) ❑ Drainage Patterns (B10) ❑ Sediment Deposits (B2) (Nonriverine) Oxidized Rhizospheres along Living Roots (0) ❑ Dry Season Water Table (C2) Drift deposits (B3) (Noneriverine) ❑ Presence of Reduced Iron (C4) ❑ Crayfish Burrows (C8) ❑ Surface Soil Cracks (B6) Recent Iron Reduction in Plowed Soils (C6) Saturation Visible on Aerial Imagery (C9) Inundation Visible on Aerial Imagery (87) ❑ Thin Muck Surface (C7) ❑ Shallow Aquitard (D3) Water-Stained Leaves (69) ❑ Other (Explain in Remarks) FAC-neutral Test (D5) Field Observations: Surface Water Present? Yes ( No Depth (inches): Water Table Present? Yes No C-) Depth (inches): 16 J Yes NO 0 Saturation Present? Yes No Wetland H Depth (inches): 8 ydrology Present? (includes capillary fringe) Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if avai lable: Remarks: • u 11 US Army Corps of Engineers Arid West - Version 2 Oct. 2008 WETLAND DETERMINATION DATA FORM - Western Mountains, Valleys, and Coast Region Project/Site: DESCHUTES LWI City/County: SUNRIVER/DESCHUTES ..m__. ..-.mm , Sampling Pate: 17 Nov_1.0...... Applicant/Owner: COUNTY State: OR Sampling Point: SP 114 Investigator($):Sarah Hartung Section, Township, Range: S 2 T 21 S R 10 E Landform (hllislope, terrace, etc.): Valley bottom Local relief (concave, convex, none): concave Slope. 0.0% 0 ° / 0.0 ° Subregion (LRR): LRR A Lat.: 43.7873 Long.: -121.5066 Datum: NAD83 Soil Map Unit Name:.2.2A;..CryNidS21I5...Q.SQ..J NWI classification: PS$ Are climatic/ hydrologic conditions on the site typical for this time of year? Yes No 0 (If no, explain in Remarks.) Are Vegetation , Soil , or Hydrology significantly disturbed? Are "Normal Circumstances" present? Yes No ) Are Vegetation . , Soil , or Hydrology naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transects, important features, et Hydrophytic Vegetation Present? Yes (O) No Is the Sampled Area Hydric Soil Present? Yes CP', No within a Wetland? Yes No Wetland Hydrology Present? Yes No i L_ Remarks: On-site determination. T 10. _ Dominant Species? Absolute ReI.Strat. Indicator Dominance Test worksheet: % Cover Cover Status Number of Dominant Species 40 U 100 0% FAC That are OBL, FACW, or FAC: 3 (A) o Total Number of Dominant 0 [ 0.0% Species Across All Strata: 3 (B) 0 El 0 0% 'i Percent of dominant Species 40 Tot I Cover That Are OBL, FACW, or FAC: 0.0% (A/B) 30 n 100.0% FACW Prevalence Index worksheet: j 0 0.0% Total % Cover of Multil?~Y by ORL species 0 x 1 - 0 1]-_0-.0..%.. FACW species 30 x 2 - 60 [J 0.0% _ 420 140 FAC species x 3 - --30- = Total Cover 0 _ 0 FACU species x 4 100 n 100 0% FAC x g j UPL species 0_._.... = 0 . U Column Totals:.... (A) 4 Ce) 0 0.0% 0 .0% Prevalence Index = B/A = 0.000 U U•0% Hydrophytic Vegetation Indicators: O -0% U Dominance Test Is n 50% ~ 0 n _ 0.00k Prevalence Index is 53 01 0 n 0.0% . Morphological Adaptations 1 (Provide supporting 0 U 010% data In Remarks or on a separate sheet) 0 U 0.0% Wetland Non-Vascular Plantsl ° Problematic Hydrophytic Vegetatlonl (Explain) f 0 0.0% 100 'Indicators of hydric soil and wetland hydrology must - = Total Cover be present, unless disturbed or problematic. 0 n 0.0% 0 0.0% Hydrophytic U ` - Total Cover Vegetation Present? Yes * No "Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version • 1Type: C_ Concentration. D=Depletion. RM=Reduced Matrix, CS=Covered or Coated Sand Grains 2Locatiom PL=Pore Lining. M=Matrix i Nydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric $gils:3 Histosol (Al) Sandy Redox (SS) 2 CM Muck (A10) Histic Epipedon (A2) Stripped Matrix (S6) ! Red Parent Material (TF2) ~I Black Histic (A3) Loamy Mucky Mineral (Fl) (except in MLRA 1) 3el Other (Explain in Remarks) I Hydrogen Sulfide (A4) Loamy Gleyed Matrix (F2) N Depleted Below Dark Surface (All) Depleted Matrix (F3) Thick Dark Surface (A12) Redox Dark Surface (F6) 3Indicators of hydrophytic vegetation and Sandy Muck Mineral (Sl) Depleted Dark Surface (F7) wetland hydrology must be present, Sandy Gleyed Matrix (S4) Redox depressions (FS) unless disturbed or problematic. Restrictive Layer (if present): Type: _ Depth (inches) , Hydric Soil Present? Yes No Remarks: Hydric soils assumed based on persistent saturation. Wetland Hydrology Indicators: minimum of one required; check a tat Primary Indicators apply) ry Indicators minimum of two required) Surface Water (Al) Water- Leaves (B9) (except MLRA Stained Water-Stained Leaves (B9) (MLRA 1, 2, ~ High Water Table (A2) 1, 2, 4A, and 4B) 4A, and 4B) Saturation (A3) Salt Crust (Bll) Drainage Patterns (Blo) d L_ Water Marks (Bl) E I Aquatic Invertebrates (B13) ! Dry Season Water Table (C2) R Sediment Deposits (132) Hydrogen Sulfide Odor (Cl) Saturation Visible on Aerial Imagery (C9) _ Drift deposits (B3) Oxidized Rhizospheres on Living Roots (0) Geomorphic Position (D2) Algal Mat or Crust (84) Presence of Reduced Iron (C4) Shallow Aquitard (D3) Iron Deposits (B5) I Recent Iron Reduction in Tilled Soils (C6) FAC-neutral Test (D5) Surface Soil Cracks (B6) Stunted or Stressed Plants (Dl) (LRR A) Raised Ant Mounds (D6) (LRR A) Inundation Visible on Aerial Imagery (B7) I Other (Explain in Remarks) Frost Heave Hummocks (137) Sparsely Vegetated Concave Surface (BB) Field Observations: Surface Water Present? Yes ' No Depth (inches): Water Table Present? Yes No > Depth (inches): 15 Saturation Present? ~i Wetland Hydrology Present? Yes P' NO Yes No Depth (inches): 0 (includes capillary fringe). Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available: Q Remarks: i • US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version 0 WETLAND DETERMINATION DATA FORM - Arid West Region Project/Site: Deschutes County LWI City/County: Sunriver/Deschutes Sampling Date: 04-May-10 Applicant/Owner: DFSCHUTFS COUNTY State: OR Sampling Point: SP 201 Investigator(s): Sarah Hartung, Aaron BooY Section, Township, Range: S 7 T 20S R 11 E Landform (hillslope, terrace, etc.): Floodplain Local relief (concave convey, none): concave slope: 1.0% / 0.6 ° Subregion (LRR): LRR B Lat.: 43.8632 Long.: -121.4536 Datum: NAD 83 . Soil Map Unit Name: 29A; Cryoquolls, 0 to 3 percent slppes NWI classification: pSS.C. Are climatic/hydrologic conditions on the site typical for this time of year? Yes No (If no, explain in Remarks.) 1 , Are Vegetation I Soil L , or Hydrology significantly disturbed? Are "Normal Circumstances" present? Yes ' No AreVegetation , Soil L , or Hydrology naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transects, important features, etc. r , . _ T Hydrophytic Vegetation Present? Yes No Is the Sampled Area Hydric Soil Present? Yes No within a Wetland? Yes 'e NO Wetland Hydrology Present? Yes No Remarks: Off-site determination. VEGETATION - Use scientific names of plants Tree Stratum (Plot size: ) 1. 2. 3. 4. Sapling/Shrub Stratum (Plot size: ) 1, Salix 9eyerlana 2. 3. 4. 5. Dominant Species? Absolute Re1.5trat. Indicator Dominance Test worksheet: % Cover Cover Status Number of Dominant Species 0 0.0% That are 08L, FACW, or FAC: 2 (A) o I o.o% Total Number of Dominant 0 0.0% Species Across All Strata; 2 (B) 0 0.0°r° 0 = Total Cover Percent of dominant Species ° 100 0 (A/B) 15 INI 100.0% FACW 0 0.0% 0 . 0.0% 0 . J 0.0% 0 i 0.0% 15 = Total Cover 85 -/I 85.0% 0131- 5 1 5.0% 0131 10 1 10.0% FACW o F- 0.0% 0 1! 7 0.0% 0 _..I 0,0% 0 0.0% 0 0.0% 0 1 0.0% .0 0.0% 0 0.0% 100 = Total Cover Woody Vine Stratum (Plot size: ) 1. 0 0.0% That Are OBL, FACW, or FAC. Prevalence Index worksheet: Total %,.Cover of: Multiply by: )6L species 90 x 1 = 90 'ACW species 25 x 2 - 50 'AC species 0 x 3 = 0 -Acu species 0 x 4 = 0 IPL species 0 x 5 - 0 :olumn Totals: 115 (A) 140 (s) Prevalence Index = B/A = 1.217 iydrophytic Vegetation Indicators: lV; Dominance Test is a 50% Prevalence Index is S3.0 1 Morphological Adaptations 1 1.1rovide supporting data in Remarks or on a separate sheet) Problematic Hydrophytic Vegetation 1 (1 :plain) 1 Indicators of hydric soil and wetland hydrology must be present, unless disturbed or problematic. 2. 0 0.0% Hydrophytic 0 Total Cover Vegetation Yes NO Present. % Bare Ground in Herb Stratum: 0 % Cover of Biotic Crust 0 Remarks: *Indicator suffix = National status or professional decision assigned because Regional status not define d by FWS. US Army Corps of Engineers Arid West - Version 2 Oct. 2008 Soil Sampling Point: SP 201 Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Matrix Depth eatures Redox F ' (inches) Color (moist) . ) % Type I Loc= Color (moist Texture Remarks o 0-4 10YR 2/l 100/o Silt Loam 4-10 lOYR 2/1. 100/a.. , Clay Loam . 10-22 10YR 2/1 80% 10YR 3/4 20% C M Clay Loam I T. C=Concentration. D= Depletion. RM=Reduced Matrix, CS= Covered ype: Covered or Coated Sand Grains zLocation: PL= Pore Lining. M=Mats Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils:3 ❑ Histosol (At) ❑ Sandy Redox (S5) ❑ 1 cm Muck (A9) (LRR C) ❑ Hisbc Epipedon (A2) ❑ Stripped Matrix (S6) 2 cm Muck (A10) (LRR B) ❑ Black Histic (A3) Loamy Mucky Mineral (Fl) ❑ Reduced Vertic (F18) Hydrogen Sulfide (A4) F7 Loamy Gleyed Matrix (F2) ❑ Red Parent Material(TF2) ❑ Stratified Layers (AS) (LRR C) ❑ Depleted Matrix (F3) n Other (Explain in Remarks) ❑ 1 cm Muck 09) (LRR D) ❑ Redox Dark Surface (F6) Depleted Below Dark Surface (Ail) L 7 Depleted Dark Surface (F7) ❑ Thick Dark Surface (A12) ❑ Redox depressions (FS) ❑ Sandy Muck Mineral (SS) Vernal Pools (F9) 3 and vegetation Indicators of hydrophytic 17 Sandy Gleyed Matrix (54) hydrology must be present. wetland Restrictive Layer (if present): Type: Depth (inches): - - Hydric Soil Present? Yes No Remarks: ASSUME HYDRIC SOILS BASED ON PERSISTENT SATURATION. Hydrology Wetland Hydrology Indicators: primary ,)ndirators j.min. m.um of one required; check all that apply) Secondary Indicators (2 or more required) Surface Water (Al) i. J Salt Crust (Bit) I _1 Water Marks (Bl) (Riverine) ❑ High Water Table (A2) ❑ Biotic Crust (B12) ❑ Sediment Deposits (B2) (Riverine) U Saturation (A3) ❑ Aquatic Invertebrates (B13) Drift Deposits (B3) Riverine) ❑ Water Marks (Bl) (Nonriverine) ❑ Hydrogen Sulfide Odor (Cl) ❑ Drainage Patterns (B10) ❑ Sediment Deposits (B2) (Nonriverine) L l Oxidized Rhizospheres along Living Roots (0) L_J Dry Season Water Table (C2) Drift deposits (B3) (Noneriverine) ❑ Presence of Reduced Iron (C4) 7 Crayfish Burrows (C8) ❑ Surface Soil Cracks (B6) Recent Iron Reduction in Plowed Soils (C6) L I Saturation Visible on Aerial Imagery (C9) Inundation Visible on Aerial Imagery (B7) ❑ Thin Muck Surface (C7) ❑ Shallow Aquitard (D3) Water-Stained Leaves (B9) Other (Explain in Remarks) FAG-neutral Test (D5) Field Observations: Surface Water Present? Yes O No Depth (inches): Water Table Present? Yes No ' Depth (inches): - i -7] Saturation Present? Wetland Hydrology Present? Yes No - Sincludes capillary fringe) Yes No Depth (inches): 55 Describe Recorded Data (stream gauge, monitor well photos, P p aerial previous ins actions if available: WETLAND DETERMINATION DATA FORM - Arid West Region Project/Site: Deachutes County LWI City/County: Sunriver/Deschutes Sampling Date: 04-May-10 Applicant/Owner: DESCHUTES COUNTY State: OR Sampling Point: SP 202 Investigator(s): Sarah Hartung, Aaron BooY Sectionr Township, Range: S 12 T 20 S R 10 E Landform (hillslope, terrace, etc.): Flat Local relief (concave, convex, none): flat Slope: 1.0% / 0.6 ° Subregion (LRR): LRR B Lat.: 43.8537 Long.: -121.4812 Datum: NAD 83 Soil Map Unit Name: 29A: Cryacluolls, 0 to 3 percent slopes NWI classification: PEMA Are climatic/hydrologic conditions on the site typical for this time of year? Yes ' No ( (If no, explain in Remarks.) Are Vegetation ❑ , Soil ❑ , or Hydrology ❑ significantly disturbed? Are "Normal Circumstances" present? Yes * No Are Vegetation ❑ , Soil ❑ , or Hydrology ❑ naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transects, important features, etc. Hydrophytic Vegetation Present? Yes No C'!) Is the Sampled Area Hydric Soil Present? Yes - No - Wetland Hydrology Present? Yes - No ' within a Wetland? Yes No Remarks: On-Site determination. VEGETATION - Use scientific names of plants. Dominant Species? Absolute Re1.Strat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: ) % Cover Cover Status Number of Dominant Species 1. 0 ❑ 0.0% That are OBL, FACW, or FAC: 1 (A) 2. 0 ❑ 0.0% 3 El Total Number of Dominant . 0 0.0% Species Across All Strata: 2 (B) 4. 0 0.0% . . . . . . . . . . . . . . 0 = Total Cover ! Percent of dominant Species Sapling/Shrub Stratum (Plot size: ) That Are OBL, FACW, or FAC: 1. 0 ❑ 0.0% 'Prevalence index worksheet: 2. o 0.0% Total % Cover of: Multiply-by:, 3. 0 0.0% oBL species 0 x 1- 0 4. 0 ❑ 0.0% ',FACw species 0 x 2 0 5. 0 0.0% ° ~ FAC species 55 x 3 = 165 0 = Total Cover FgCU species 45 x 4 180 Herb Stratum (Plot size: ) 0 0 il ea millefnlium 1 0 lve~ 40.0% AC u uPL species x 5 - s . ~a 2. P. 55 o ~ 55,0% F Ac column Totals: 100 (q) 345 (B) 3. Taraxacum officinale 5 ❑ s.o% FACU Prevalence Index = B/A = 3.450 4 0 ❑ 0.0% - Hydrophytic Vegetation Indicators: - - 5. 0 F l 0.0% . f-..[ Dominance Test is a So% 6. 0 1 .1 0.0°ro 1 ❑ Prevalence index is 53.0 7. 0 ❑ 0.0% Morphological Adaptations 11 _ provide supporting 8. 0 0.0% data In Remarks or on a separate sheet) 9, 0 [ 0.0% Problematic Hydrophytic Vegetation 1(1 cplain) 10. 0 0.0% 11. 0 ❑ 0.0% 50.0% (A/B) Woody Vine Stratum (Plot size: ) 1. 2. 100 = Total Cover 1 Indicators of hydric soil and wetland hydrology must be present, unless disturbed or problematic. 0 ❑ 0.0% 0 ❑ 0.0% Hydrophytic Vegetation 0 = Total Cover present? Yes C) No % Bare Ground in Herb Stratum: 0 % Cover of Biotic Crust 0 Remarks: Poa sp, assumed FAC. *Indicator Suffix - National status or professional decision assigned because Regional status not defined by FWS. US Army Corps of Engineers Arid West - Version 2 Oct. 2008 Soil Sampling Point: SP 202 Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Depth Matrix Redox Features Color (moist) /o (inches) Loc1 Color (moist) % Type 1 Texture Remarks 0 8 7.SYR 2.52 100% Loam 8-20 lOYR 2 100% 2~..,. i Sandy Clay y Y,. , I Type: C-Concentration. D=Depletion, RM=Reduced Matrix, CS=Covered or Coated Sand Grains 21-ocation: PL=Pore Lining. M= Matrix Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils:3 ❑ Histosol (Al) ❑ Sandy Redox (S5) ❑ 1 cm Muck (A9) (LRR C) ❑ Histic Epipedon (A2) ❑ Stripped Matrix (S6) 2 cm Muck (A10) (LRR B) ❑ Black Histic (A3) ❑ Loamy Mucky Mineral (Fl) Y ❑ Reduced Vertic (1`18) ❑ Hydrogen Sulfide (A4) ❑ Loamy Gleyed Matrix (F2) ❑ Red Parent Material (TF2) ❑ Stratified Layers (A5) (LRR C) ❑ Depleted Matrix (F3) [ Other (Explain in Remarks) ❑ 1 cm Muck (A9) (LRR D) ❑ Redox Dark Surface (F6) Depleted Below Dark Surface (All) [ i Depleted Dark Surface (F7) ❑ Thick Dark Surface (A12) ❑ Redox depressions (F8) ❑ Sandy Muck Mineral (Sl) Vernal Pools (F9) 3 Indicators of hydrophytic vegetation and ❑ Sandy Gleyed Matrix (54) wetland hydrology must be present. Restrictive Layer (if present): Type: Depth (Inches): Hydric Soil Present? Yes - No Remarks: i Hydrology Wetand Hydrology Indicators: Primary., Indicators ,(,minimum. of one required.; check all that apply) Secondary Indicators (2 or more required) Surface Water (Al) ❑ Salt Crust (Bll) Water Marks (Bl) (Riverine) ❑ High Water Table (A2) LI Biotic Crust (B12) ❑ Sediment Deposits (B2) (Riverine) Saturation (A3) ❑ Aquatic Invertebrates (B13) Drift Deposits (B3) Riverine) [1 Water Marks (Bl) (Nonriverine) ❑ Hydrogen Sulfide Odor (Cl) ❑ Drainage Patterns (B10) ❑ Sediment Deposits (B2) (Nonriverine) L Oxidized Rhizospheres along Living Roots (0) ❑ Dry Season Water Table (C2) I_I Drift deposits (B3) (Noneriverine) ❑ Presence of Reduced Iron (C4) I I Crayfish Burrows (C8) ❑ Surface Soil Cracks (B6) ' 1 Recent Iron Reduction in Plowed Soils (C6) ❑ Saturation Visible on Aerial Imagery (C9) -J Inundation Visible on Aerial Imagery (B7) 1 Thin Muck Surface (C7) Shallow Aquitard (D3) ❑ Water-Stained Leaves (B9) I_I Other (Explain in Remarks) ❑ FAC-neutral Test (D5) Field Observations: Surface Water Present? Yes No • Depth (inches): Jj Water Table Present? Yes N0 I Depth (inches); J Yes NO Saturation Present? Yes No Wetland Hydrology Present? Depth (inches): (includes capillary fringe) Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available: Remarks: • • US Army Corps of Engineers Arid West - Version 2 Oct. 2008 WETLAND DETERMINATION DATA FORM - Arid West Region Project/Site. Deschutes County LWI City/County: Sunriver/Deschutes Sampling Date: 05-May-10 r Applicant/Owner: DESCHUTES COUNTY State: !OR Sampling Point: SP 203 Investigator(s): Sarah Hartung, Aaron Booy Section, Township, Range: S 7 T 20 S R 11 E Landform (hillslope, terrace, etc.): Swale Local relief (concave, convex, none): concave Slope: 2.0% ° Subregion (LRR): LRR B Lat.: 43.8627 Long.: -121.4600 Datum: NAD 83 Soil Map Unit Name: 144A: Sunriver sandy loam, 0 to 3 percent slopes NWI classification: Are climatic/ hydrologic conditions on the site typical for this time of year? Yes No (If no, explain in Remarks.) Are Vegetation , Soil or Hydrology significantly disturbed? Are "Normal Circumstances" present? Yes NO Are Vegetation , Soil or Hydrology naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transects, important features, etc. Hydrophytic Vegetation Present? Yes No Is the Sampled Area Hydric Soil Present? Yes No within a Wetland? Yes No Wetland Hydrology Present? Yes No I Remarks: On-site determination. VEGETATION - Use scientific names of plants. Dominant Species? Absolute ReLStrat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: ) % Cover Cover Status Number of Dominant Species 1, 0 0.0% That are OBL, FACW, or FAC: 3 (A) 2. 0 I 0.0% 3 0 0 0% Total Number of Dominant . . Species Across All Strata: 3 (B) 4. 0 0.0% 0 = Total Cover Percent of dominant Species Sapling/Shrub Stratum (Plot size: ) That Are OBL, FACW, or FAC: 100.0% (A/13) 1• Salix geyeriana 2. Spiraea douglash 3. 4. 5. 50 62.5% FACW Prevalence index worksheet: 30 37.5% FACW Total % ,Cover of: Multiply by: 0 0.0% 08L species 40 x 1 - 40 0 0.0% FACW species 80 x 2 = 160 D 0.0 % ii FAC species 0 x 3= 0 80 = Total Cover I FACU species 0 x 4 - 0 40 100.0 100.0% OBL UPL species 0 x Column Totals: 120 (A) 200 (8) 0 0.0% 0 0.0°11 Prevalence Index = B/A = 1.667 0 (l.0% Hydr ophytic Vegetation Indicators: 0 0.0% Dominance Test is a 509/0 0 ] 0.0% Prevalence Index Is 55.0 1 0 ~ 0.0% h l i l d i ' id i 0 0.0% Morp o og A aptat ons 1 _ rov e support ng ca data in Remarks or on a separate sheet) ° Problematic Hydrophytic Vegetation 1 (1 :plain) 0 .0 0% 0 010% 1 Indicators of hydric soil and wetland hydrology must 0 4 . • = T otal Cover be bl ti Woody Vine Stratum (Plot size: ) 1. 0 0.0% 2. 0 0.0% 0 = Total Cover % Bare Ground in Herb Stratum: 0 % Cover of Biotic Crust 0 Remarks: 60% SURFACE WATER resent unIes Asst urbed or p, s pro ema c. Hydrophytic Vegetation Present? Yes• No i *Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS. US Army Corps of Engineers Arid West - Version 2 Oct. 2008 I Type. C=Concentration. D=Depletion. RM=Reduced Matrix, CS=Covered or Coated Sand Grains 21-ocation: PL=Pore Lining. M=Matrix Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils3 Histosol (Al) Sandy Redox (S5) 1 cm Muck (A9) (LRR C) Histic Epipedon (AZ) Stripped Matrix (S6) [ 2 cm Muck (A10) (LRR 8) Black Histic (A3) Loamy Mucky Mineral (Fl) r Reduced Vertic (F18) Hydrogen Sulfide (A4) Loamy Gleyed Matrix (F2) 1 .1 Red Parent Material (TF2) Stratified Layers ( (LRR C) _ Depleted Matrix (F3) F7 Other (Explain in Remarks) 1 cm Muck (A9) (LR R D) Redox Dark Surface (F6) `i Depleted Below Dark Surface (All) Depleted Dada Surface (F7) Thick Dark Surface (A12) Sandy Muck Mineral (Sl) Redox depressions (F8) 3 Indicators of hydrophytic vegetation and L: Sandy Gleyed Matrix (S4) Vernal Pools (F9) wetland hydrology must be present. Restrictive Layer (If present): Type: Depth (inches): Hydric Soil Present? Yes NO Remarks: Hydrology Wetland Hydrology Indicators: PrimaryIno.icators (.minimum of one required; Check all that. apply) Secondary indicators (2 or more required) ] Surface Water (Al) Salt Crust (811) I Water Marks (BI) (Riverine) ./I High Water Table (A2) Biotic Crust (B12) [ Sediment Deposits (B2) (Riverine) V1 Saturation (A3) J Aquatic Invertebrates (B13) Drift Deposits (B3) Riverine) Water Marks (Bl) (Nonriverine) Hydrogen Sulfide Odor (CI) Drainage Patterns (810) Sediment Deposits (B2) (Nonriverine) [ Oxidized Rhizospheres along Living Roots (0) Dry Season Water Table (C2) [ [ Drift deposits (B3) (Nonriverine) Presence of Reduced Iron (C4) Crayfish Burrows (C8) [ Surface Soil Cracks (B6) Recent Iron Reduction in Plowed Soils (C6) Saturation Visible on Aerial Imagery (C9) [ Inundation Visible on Aerial Imagery (57) Thin Muck Surface (C7) F Shallow Aquitard (D3) Water-Stained Leaves (B9) Other (Explain in Remarks) FAC-neutral Test (135) Field Observations: Surface Water Present? Yes NO Depth (inches): 1 Water Table Present? Yes NO Depth (inches): 0 Yes No Saturation Present? Yes No - Wetland H Depth (inches): 0 ydrology Present? includes capillary frin a Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if avai lable: Remarks: US Army Corps of Engineers Arid West - Version 2 Oct. 2008 P_.~ WETLAND DETERMINATION DATA FORM - Arid West Region Project/Site: Deachutes County LWI City/County: Sunriver/Deschutes Sampling Date: 05-May-10 Applicant/Owner: DESCHUTES COUNTY State: LOR - 1 Sampling Point: SP 205 Investigator(s): Sarah Hartung, Aaron Booy Section, Township, Range: S 6 T 20S R 11 E . . . . . . . . . . . Landform (hillslope, terrace, etc.): Floodplain local relief (concave, convex, none): flat Slope: 0.0% / 0.0 ° Subregion (LRR): LRR B tat.: 43.8695 Long: -121.4610 Datum: NAD 83 Soil Map Unit Name: Not available NWI classification: PE.MC . Are climatic/hydrologic conditions on the site typical for this time of year? Yes No (If no, explain in Remarks.) Are Vegetation , Soil , or Hydrology significantly disturbed? Are "Normal Circumstances" present? Yes * No 0 Are Vegetation Soil or Hydrology ❑ naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transects, important features, etc. Hydrophytic Vegetation Present? Yes (i.) No C Is the Sampled Area Hydric Soil Present? Yes * No ~ within a Wetland? Yes No ~ Wetland Hydrology Present? Yes * No Remarks: Off-site determination. VEGETATION - Use scientific names of plants. Dominant Species? . Absolute Rel.Strat. Indicator Dominance Test worksheet: Stratum (Plot size: ) Tree % Cover Cover Status Number of Dominant Species 1. ❑ 0.0% That are OBL, FACW, or FAC: 1 (A) 2. ❑ 0.0% Total Number of Dominant 3. ❑ 0.0% Species Across All Strata: 1 (B) 4. 0 ❑ 0.0% 0 = Total Cover Percent of dominant Species o Sapling/Shrub Stratum (Plot size: l That Are OBL, FACW, or FAC: 100.0% (A/B) 1, 0 ❑ 0.00" i Prevalen rksheet: 2. 0 0.0% e Total % Cover of: Multiply by: 3. 0 0.0% qaL species 95 x 1 - 95 4. 0 . 0.0% FACW species 5 x 2 = 10 5. 0 0.0°h FAC species 0 x 3= 0 0 = Total Cover FACU species 0 . x 4 - 0 Herb Stratum (Plot size: l 0 0 Carex aquatilis 1 90 [ ~ 90.0% 0131 = x 5 UPL species . column Totals: 100 (A) 106 (B) 2.luncusbalticus 5 Li s.D% FACW i 3. Typha latifolia 5 ❑ 5.0% OBL Prevalence Index = B/A = 1.050 4. 0 1 I 0.0% Hydrophytic Vegetation Indicators: 5. 0 ❑ 0.0% V1 Dominance Test is 7 so% 6. 0 ❑ 0.0% 'k/i prevalence Index is 53.0 1 7. 0 D 0.0% ❑ 0 0% Morphological Adaptations 1 ;.'rovide supporting . data in Remarks or on a separate sheet) 9. 0 0.0% Problematic Hydrophytic Vegetation 1 (1 :plain) 10. o . ❑ 0.0% 11. 0 ❑ 0.0% r 1 Indicators of hydric soil and wetland hydrology must 100 = Total Cove be present, unless disturbed or problematic. Woody Vine Stratum (Plot size: l 1. 0 ❑ 0.0% 2. 0 ❑ 0.0o/. % Bare Ground in Herb Stratum: 0 0 = Total Cover % Cover of Biotic Crust 0 Remarks: Carex dominant through majority of wetland, small clumps dominated by other two species Hydrophytlc Vegetation Present? Yes No 0 Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS. US Army Corps of Engineers Arid West - Version 2 Oct. 2008 soil Sampling Point: SP 205 Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) I Depth Matrix Redox Features O (inches) Color (moist). /o Color (moist) O/o Type I Loc1 Texture Remarks i Type: C=Concentration. D=Depletion. RM=Red uced Matrix, CS=Covered or Coated Sand Grains zLocation: PL=Pore Lining. M=Matrb( Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils J Histosol (Al) ~_J Sandy Redox (55) 1 cm Muck (A9) (LRR C) Histic Epipedon (A2) ❑ Stripped Matrix (S6) ❑ 2 cm Muck (A10) (LRR B) ❑ Black Histic (A3) ❑ Loamy Mucky Mineral (Fl) 1 Reduced Vertic (F18) L ~ ❑ Hydrogen Sulfide (A4) Loamy Gleyed Matrix (F2) i - F Red Parent Material (TF2) Stratified Layers (A5) (LRR C) ❑ Depleted Matrix (9) U Other (Explain in Remarks) ❑ 1 cm Muck (A9) (LRR D) Redox Dark Surface (F6) Depleted Below Dark Surface (All) L1 Depleted Dark Surface (F7) Thick Dark Surface (A12) ❑ Redox depressions (F8) ❑ Sandy Muck Mineral (SS) ❑ Vernal Pools (F9) 3 Indicators of hydrophytic vegetation and ❑ Sandy Gleyed Matrix (S4) wetland hydrology must be present. Restrictive Layer (if present): TYPe Depth (Inches): Hydric Soil Present? Yes * No Remarks: no access - hydric soils assumed based on OBL dominant veg. Hydrology Wetland Hydrology Indicators: Primary Indicators (minimum of one required; check all that apply) Secondary Indicators (2 or more required) 1 Surface Water (Al) ❑ Salt Crust (BlI) Water Marks (Bl) (Riverine) ❑ High Water Table (A2) I 7 Biotic Crust (B12) Sediment Deposits (B2) (Riverine) ❑ Saturation (A3) ❑ Aquatic Invertebrates (B13) Drift Deposits (133) Riverine) ❑ Water Marks (Bl) (Nonriverine) 7 Hydrogen Sulfide Odor (Cl) ❑ Drainage Patterns (B10) ❑ Sediment Deposits (B2) (Nonriverine) ❑ Oxidized Rhizospheres along Living Roots (0) Dry Season Water Table (C2) ❑ Drift deposits (B3) (Noneriverine) Presence of Reduced Iron (C4) ❑ Crayfish Burrows (CB) Surface soil cracks (B6) LJ Recent Iron Reduction in Plowed Soils (C6) Saturation Visible on Aerial Imagery (C9) ❑ Inundation Visible on Aerial Imagery (B7) Thin Muck Surface (0) Shallow Aquitard (D3) ❑ Water-Stained Leaves (B9) ❑ Other (Explain in Remarks) Wl FAC-neutral Test (DS) Field Observations: Surface Water Present? Yes No Depth (inches): Water Table Present? Yes (3 No Depth (inches): I - Y N Saturation Present? - (includes capillary fringe) Yes NO - Wetiand H Depth (inches): 1 - es o ydrology Present? - Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if avai lable: Aerial hoto p s • Remarks: no access - hydrology assumed based on aerial photo, landscape position, and observations of adjacent river elevation [approx. At wetland elevation) US Army Corps of Engineers Arid West - Version 2 Oct. 2008 WETLAND DETERMINATION DATA FORM - Arid West Region Project/Site: Deschutes County LWI City/County: Sunriver/Deschutes Sampling Date: 05-May-10 Applicant/Owner: DESCHUTES COUNTY State: OR 1 Sampling Point: SP 206 Investigator(s): Sarah Hartung, Aaron Booy Section, Township, Range: S 6 T 20 5 R 11 E Landform (hillslope, terrace, etc.): Floodplain Local relief (concave, convex, none): flat Slope: 1.0% / 0.6 ° Subregion (LRR): LRR 8 Lat.: 43.8764 Long.: -121.4601 Datum: NAD 83 Soil Map Unit Name: 29A: Cryap .olls, 0 to 3 percent slopes NWI classification: PSSC Are climatic/hydrologic conditions on the site typical for this time of year? Yes * No (If no, explain in Remarks.) Are Vegetation ❑ , Soil ❑ , or Hydrology ❑ significantly disturbed? Are "Normal Circumstances" present? Yes No ( ) AreVegetation I I , Soil L L , or Hydrology ❑ naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transects, important features, etc. Hydrophytic Vegetation Present? Yes No 0 Is the Sampled Area Hydric Soil Present? Yes No within a Wetland? Yes * No Wetland Hydrology Present? Yes No' Remarks: Off-site determination. Area contains hydrophytic veg, wetland hydrology observed from aerial photos and veg., hydric soils assumed [no access] VEGETATION - Use scientific names of plants. Dominant Species? Absolute Rel.Strat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: ) % Cover Cover Status I Number of Dominant Species 1. 0 ❑ 0.0% That are OBL, FACW, or FAC: 2 (A) 2. 0 ❑ 0.0% 3 D 1 11 0 Total Number of Dominant . .0% Species Across All Strata: 2 (B) 4. o I I 0.0% P t f do in t S i o Total Cover = ercen o m an pec es o 1000% (A/B) ACW, or FAC: Sapling/Shrub Stratum (Plot size: ) That Are OBL, F 1, 0 0.0% Prevalence index worksheet: 2. o ❑ 0.0% Total % Cover of: Multiply by: 3. 0 ❑ 0.0% OBL species 95 x 1 - 95 4. 0 ❑ o.0% FACW species 5 x 2 - 10 5. 0 ❑ 0.0% I FAC species 0 x 3= 0 0 = Total Cover FACU species 0 x 4 = 0 Herb Stratum (Plot size: ) 0 0 Carex aquatilis 1 65 IVI 65.0% 0131- UPL species x 5 - . 2, Typha latifolia 30 11.1 30.0% OBL column Totals: 100 (A) 105 (B) 3. ]uncus balticus 5 LL s.o% FACw Prevalence Index = B/A = 1.050 4. 0 1. I 0.0% - Hydrophytic Vegetation indicators: 5. 0 L 0.0% Dominance Test Is 7 50% 6, 0 ❑ 0.0% N Prevalence Index is 53.0 1 2, 0 ~..L 0.0% ❑ Morphological Adaptations 11 Irovide supporting 8. 0 ❑ 0.0% _ data in Remarks or on a separate sheet) 9. o 0.0% El Problematic Hydrophytic Vegetation 1 (1 :plain) 10. o 0.0% I I 77. o ❑ o.o% 1 indicators of hydric soil and wetland hydrology must 00 = Total Cover be present, unless disturbed or problematic. Woody Vine Stratum (Plot size: ) 1. 0 ❑ 0.0% 2. 0 ❑ 0.0% Hydrophytic o = Total Cover Vegetation Present? Yes No (L % Bare Ground in Herb Stratum: 0 % Cover of Biotic Crust 0 Remarks: Carex and Typha dominated, patches of Salix throughout. Mostly on edges. *Indicator suffix = National status or profess ional decision assigned because Regional status not defined by FWS. US Army Corps of Engineers Arid West - Version 2 Oct. 2008 Soil Sampling Point: SP 206 Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) t Depth Redox Features. ) /o (inches) Color (moist) mois c r moist 2 Color % ~ Loc (moist) Texture Remarks I 1 Type: C=Concentration. D=Depletion. RM=Reduced Matrix, CS=Covered or Coated Sand Grains 21-ocation: PL=Pore Lining. M=Matrix Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric SoilsP ❑ Histosol (Al) ❑ Sandy Redox (SS) ❑ 1 cm Muck (Ag) (LRR C) ❑ Histic Epipedon (A2) Stripped Matrix (S6) El 2 cm Muck (A10) (LRR B) Black Histic (A3) 7 Loamy Mucky Mineral (FS) ❑ Reduced Vertic (F18) ❑ Hydrogen Sulfide (A4) ❑ Loamy Gleyed Matrix (F2) ❑ Red Parent Material (TF2) ❑ Stratified Layers (AS) (LRR C) ❑ Depleted Matrix (F3) U Other (Explain in Remarks) I cm Muck (A9) (LRR D) ❑I Redox Dark Surface (F6) ❑ Depleted Below Dark Surface (Ail) ❑ Depleted Dark Surface (F7) ❑ Thick Dark Surface (A12) Redox depressions (F8) ❑ Sandy Muck Mineral (Sl) ❑ Vernal Pools (F9) 3 Indicators of hydrophytic vegetation and ~ Sandy Gleyed Matrix (54) wetland hydrology must be present. Restrictive Layer (if present): Type: Depth (inches) , _ ( Hydric Soil Present? . Yes No Remarks: no access - hydric soils assumed based on OBL dominant veg. • Hydrology Wetland Hydrology Indicators: Primary.I.ndicators (minimum of one required; check all that apply) Secondary Indicators (2 or more required) ❑ Surface Water (Al) Salt Crust (B11) ❑ Water marks (Bl) (Riverine) L I High Water Table (A2) Biotic Crust (B12) i I Sediment Deposits (B2) (Riverine) ❑ Saturation (A3) ❑ Aquatic Invertebrates (B13) ❑ Drift Deposits (83) Riverine) ❑ Water Marks (Bl) (Nonriverine) Hydrogen Sulfide Odor (Cl) I I Drainage Patterns (B10) ❑ Sediment Deposits (B2) (Nonriverine) ❑ Oxidized Rhizospheres along Living Roots (0) ❑ Dry Season Water Table (C2) ❑ Drift deposits (B3) (Noneriverine) ❑ Presence of Reduced Iron (C4) F. I Crayfish Burrows (C8) ❑ Surface Soil Cracks (B6) ❑ Recent Iron Reduction in Plowed Soils (C6) Saturation Visible on Aerial Imagery (C9) Inundation Visible on Aerial Imagery (B7) Thin Muck Surface (C7) Shallow Aquitard (D3) ❑ Water-Stained Leaves (B9) ❑ Other (Explain in Remarks) kf FAC-neutral Test (DS) Field Observations: Surface Water Present? Yes 0 No Depth (inches): Water Table Present? Yes 0 No Depth (inches): Yes NO 0 Saturation Present? Yes NO Wetland Hydrology Present? Depth (inches): includes ca illa fringe) Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if avai lable: Aerial ph oto Remarks: no access - hydrology assumed based on aeria l photo, landscape position, and observations of adjacent river elevation [wetland outlet near river elevation wetland elevation] • US Army Corps of Engineers Arid West - Version 2 Oct. 2008 WETLAND DETERMINATION DATA FORM - Arid West Region Project/Site: DESCHUTES LWI City/County: Sunriver/Deschutes Sampling Date: 05 May-10 Applicant/Owner: DESCHUTES COUNTY State: OR Sampling Point: 5P 207 Investigator(s): Sarah Hartung, Aaron Booy Section, Township, Range: S 6 T 20S R 11 E Landform (hilislope, terrace, etc.): Floodplain Local relief (concave, convex, none): flat Slope: 0.5% / 0.3 ° Subregion (LRR) 83 : LRR B Lat.: 43.8769 Long.: -121.4628 Datum: A Soil Map Unit Name: Not available NWI classification: PSSC Are climatic/ hydrologic conditions on the site typical for this time of year? Yes ' No (If no, explain in Remarks.) Are Vegetation , Soil , or Hydrology significantly disturbed? Are "Normal Circumstances" present? Yes * No AreVegetation Soil n , or Hydrology n naturally problematic? (If needed, explain any answers In Remarks.) Summary of Findings - Attach site map showing sampling point locations, transects, important features, etc. Hydrophytic Vegetation Present? Yes NO IS the Sampled Area Hydric Soil Present? Yes ! No - Wetland Hydrology Present? Yes No within a Wetland? Yes ( No Remarks: Off-site determination. Area contains hydrophytic veg, wetland hydrology observed from aerial photos and veg., hydric soils assumed [no access]. VEGETATION - Use scientific names of plants. Dominant Species? . Absolute Rel.Strat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: ) % Cover Cover Status 0 0.0% Number of Dominant Species That are OBL, FACW, or FAC: 2 (A) 0 ❑ 0.0% 0-.0% Total Number of Dominant Species Across All Strata: 2 (B) 4. o ❑ 0.0% = Sapling /Shrub Stratum (Plot size: ) That Are OBL, FACW, or FAC: 1. Salix geyeriana SDO ❑ 100.0% FACW Prevalence Index worksheet: 2. 0 0.0% Total % Cover of: Multiply by: 3. 0 LL 0.0% j OBL species 100 x 1 - 100 4. 0 0.0% FACW species 100 x 2 = 200 5. 0 0.0%. FAC species x 3 = 0 100 = Total Cover FACU species 0 x 4 = 0 Herb Stratum (Plot size: ) 0 0 1 Carex aquatilis 100 k 100.0% OBL uPL species - X S - . Column Totals: 200 (A) 300 (s) . 2. 0 El o.o% 3, 0 LL o.0% Prevalence Index = B/A = 1.500 4. 0 0.0% H - - ydrophytic Vegetation Indicators: 5, 0.. 0.0% , dI Dominance Test is 7 so"/° 6, 0 0.0% . [L Prevalence index is 53.0 1 7. 0 n D.o% Morphological Adaptations 1 _ rovide supporting 0 0.0°~ data in Remarks or on a separate sheet) 9 . o .o n o Problematic Hydrophytic Vegetation 1 (1 :plain) 10. 0 0 .0°i ° E] 11. 0 n 0.0% 1 Indicators of hydric soil and wetland hydrology must 100 = Total Cover be present, unless disturbed or problematic. Woody Vine Stratum (Plot size: ) 0 Total Cover Percent of dominant Species o 100.0 /o (A/B) 1. 0 LL o.o% 2. 0 ❑ 0.0% 0 = Total Cover % Bare Ground in Herb Stratum: 0 % Cover of Biotic Crust 0 Remarks: Several lone pines observed, however PSS is Salix dominated. Hydrophytic Vegetation - Present? Yes * No *Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS. US Army Corps of Engineers Arid West - Version 2 Oct. 2008 Soil Sampling Point: 5P 207 Profile Description: (Describe to the depth needed to document the Indicator or confine the absence of indicators.) Matrix I nc Redox Features hes) Color (moist) % (i Color (moist) % Type 1 Loc' Texture Remarks 1 Type: C=Concentration. D=Depletion. RM=Red uced Matrix, CS=Covered or Coated Sand Grains zLocation: PL=Pore Lining. M=Matrix I Hydrlc Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric 5oils3 U Histosol (Al) Sandy Redox (S5) ❑ 1 cm Muck (A9) (LRR C) Histic Epipedon (A2) Stripped Matrix (S6) I J 2 cm Muck (A10) (LRR B) ❑ Black Histic 03) ❑ Loamy Mucky Mineral (Fl) ❑ Reduced Vertic (F18) ❑ Hydrogen Sulfide (A4) J Loamy Gleyed Matrix (F2) Red Parent Material (72) ❑ Stratified Layers ( (LRR C) ] Depleted Matrix (F3) n Other (Explain in Remarks) 1 cm Muck (A9) (LR R D) Redox Dark Surface (F6) Depleted Below Dark Surface (All) ❑ Depleted Dark Surface (F7) ❑ Thick Dark Surface (A12) ❑ Sandy Muck Mineral (SS) 7 Redox depressions (F8) 3 Indicators of hydrophytic vegetation and ❑ Sandy Gleyed Matrix (S4) Vernal Pools (F9) wetland hydrology ology must be present. Restrictive Layer (if present): Type: Depth (inches): Hydric Soil Present? Yes No r.> Remarks: no access - hydric soils assumed based on FAC and wetter dominant veg. Hydrology Wetland Hydrology Indicators: Primary Indi4ato rs (minimum of one required; check all that apply) Secondary Indicators (2 or more required) ❑ Surface Water (Al) Salt Crust (Bll) ❑ Water Marks (Bl) (Riverine) High Water Table (A2) Biotic Crust (B12) L I Sediment Deposits (B2) (Riverine) ❑ Saturation (A3) Aquatic Invertebrates (B13) ❑ Drift Deposits (B3) Riverine) Water Marks (Bl) (Nonriverine) ❑ Hydrogen Sulfide Odor (Cl) ❑ Drainage Patterns (B10) ❑ Sediment Deposits (82) (Nonriverine) Oxidized Rhizospheres along Living Roots (0) ❑ Dry Season Water Table (C2) ❑ Drift deposits (B3) (Noneriverine) ❑ Presence of Reduced Iron (C4) ❑ Crayfish Burrows (C8) Surface Soil Cracks (B6) Recent Iron Reduction in Plowed Soils (C6) ~v/1 Saturation Visible on Aerial Imagery (C9) ❑ Inundation Visible on Aerial Imagery (B7) ❑ Thin Muck Surface (C7) ❑ Shallow Aquitard (D3) Water-Stained Leaves (89) Other (Explain in Remarks) J FAC-neutral Test (D5) Field Observations: Surface Water Present? Yes No Depth (inches): j Water Table Present? Yes NO Depth (inches): t? Yes No C P Saturation Present? Yes N0 Wetland H Depth (inches): resen ydrology (includes capillary fringe) Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if avai lable: Aerial photo Remarks: no access - hydrology assumed based on aerial photo, landscape position, and observations of adjacent river elevation [approx. At wetland elevation] US Army Corps of Engineers Arid West - Version 2 Oct. 2008 WETLAND DETERMINATION DATA FORM - Arid West Region Project/Site: Deachutes Count`/ LWI City/County; Sunriver/Deschutes Sampling Date: 05-May-10 Applicant/Owner: DESCHUTE8 COUNTY State: OR __L_] Sampling Point: SP 208 Investigator(s): Sarah Hartung, Aaron Booy Section, Township, Range: S 1 T 20 5 R 10 E Landform hillslo a terrace, etc,): Local relief (concave, convex, none): flat Slope: 1.0% / 0.6 ° Subregion (LRR): LRR B Lat.: 43.8694 Long.: -121.4691 Datum: NAD 83 Soil Map Unit Name: Not.available NWI classification: PEMC Are climatic/hydrologic conditions on the site typical for this time of year? Yes (P) No C..) (If no, explain in Remarks.) Are Vegetation ❑ , Soil F i , or Hydrology ❑ significantly disturbed? Are "Normal Circumstances" present? Yes NO Are Vegetation ❑ , soil . , or Hydrology -J naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transacts, important features, etc. Hydrophytic Vegetation Present? Hydric Soil Present? Wetland Hydrology Present? Remarks: Off-site determination. Yes No() Yes No(.-) Yes ! No C_) Is the Sampled Area within a Wetland? VEGETATION - Use scientific names of plants. Dominant Species? Absolute Re1.Strat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: ) % Cover Cover Status C~ ° Number of Dominant Species 1. Pinus contorts 2 1D0.0/o FAC That are OBL, FACW, or FAC: 3 (A) 2. 0 ❑ 0.0% 3 D ❑ C 0% Total Number of Dominant . . Species Across All Strata: 3 (B) 4. 0 ❑ 0.0% = Total Cover Percent of dominant Species Sapling/Shrub Stratum (Plotsize: ) ° That Are OBL, FACW, or FAC: 100.0% (A/13) 1, Salix ana 60 ❑ 100.0% FACW Prevalence index worksheet: 2. 0 .J 0.0% Total % Cover of: Multiply by: 3. o. 1 0.0% OBL species 80 x I = 80 4. D 0.0% x z 120 FACW species 60 5. 0 0.0% FAC species 2 x 3- 6 60 = Total Cover ! FACU species 0 x 4 .0 HerbStratum (Plotsize: ) 0 0 1. Carex aquatilis 80 100.0% OBL UPL species x 5 = column Totals: 142 (A) 206 (B) 2. 0 El 0.0% 3. 0 ❑ 0.0% Prevalence Index = B/A = 1.451 4. o L.J D.o% Hydrophytic Vegetation indicators: 5. .0 ❑ 0.0o% 7 Dominance Test is a So% 6. 0 0.0% Prevalence Index is 53.0 1 7. 0 ❑ 0.0% ❑ Morphological Adaptations 1 rovide supporting 0 0.0°j° data in Remarks or on a separate sheet) 9, 0 I_I 0.00% li Problematic Hydrophytlc vegetation 1 (1 :plain) 10. D .0. Ll o 11. 0 ❑ o.o% 80 = Total Cover 1 Indicators of hydric soil and wetland hydrology must be present, unless disturbed or problematic. Woody Vine Stratum (Plot size: ) 1. 0 ❑ 0.0°k 1 2. 0 0.0% Hydrophytic 0 = Total Cover Vegetation Present? Yes No % Bare Ground in Herb Stratum: 20 % Cover of Biotic Crust 0 Remarks: Several lone pines observed, however PSS wetland is Salix dominated w/ Carex dominant herb layer Yes No *Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS. US Army Corps of Engineers Arid West - Version 2 Oct. 2008 1 Type - Matrix, CS=Covered or Coated Sand Grains zLocation: PL=Pore Lining. M=Matroc 1 C=Concentration. D=Depletion. RM-Reduced `Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils3 ❑ Histosol (Al) ❑ Sandy Redox (S5) 1 Cm Muck (A9) (LRR C) Histic Epipedon (A2) ❑ Stripped Matrix (S6) ❑ 2 cm Muck (A10) (LRR B) ❑ Black Histic (A3) ❑ Loamy Mucky Mineral (FI) L Reduced Vertic (F18) ❑ Hydrogen Sulfide (A4) ❑ Loamy Gleyed Matrix (F2) ❑ Red Parent material (72) F Stratified Layers (AS) (LRR C) ❑ Depleted Matrix (F3) [1 Other (Explain in Remarks) ❑ 1 cm Muck (A9) (LRR D) Redox Dark Surface (F6) Depleted Below Dark Surface (Al I) n Depleted Dark Surface (F7) Thick Dark Surface (A12) ❑ Redox depressions (FB) Sandy Muck Mineral (Si) El Vernal Pools (F9) 3 Indicators of hydrophytic vegetation and F Sandy Gleyed Matrix (S4) - wetland hydrology logy must be present. Restrictive Layer (if present): Type: Depth (i riches Hydric Soil Present? Yes No Remarks: no access - hydric soils assumed based on FAC and wetter dominant veg. Hydrology Wetland Hydrology Indicators: Primary indicators (minimum.of one required; check all that apply) Secondary indicators (2 or more required) Surface Water (Al) ❑ Salt Crust (B11) ❑ Water Marks (BI) (Riverine) ❑ High Water Table (A2) L I Biotic Crust (B12) Sediment Deposits (B2) (Riverine) L._J Saturation (A3) ❑ Aquatic Invertebrates (B13) ❑ Drift Deposits (B3) Riverine) n Water Marks (Bl) (Nonriverine) ❑ Hydrogen Sulfide Odor (Cl) Drainage Patterns (B10) ❑ Sediment Deposits (B2) (Nonriverine) Oxidized Rhizospheres along Living Roots (0) ❑ Dry Season Water Table (C2) n Drift deposits (B3) (Noneriverine) ❑ Presence of Reduced Iron (C4) Crayfish Burrows (CS) Surface Soil Cracks (B6) ❑ Recent Iron Reduction in Plowed Soils (C6) EI Saturation Visible on Aerial Imagery (C9) ❑ Inundation Visible on Aerial Imagery (B7) Thin Muck Surface (C7) ❑ Shallow Aquitard (D3) Water-Stained Leaves (B9) ❑ Other (Explain in Remarks) FAC-neutral Test (D5) Field Observations: Surface Water Present? Yes No I Depth (inches): _J Water . Table pt (inches): Yes No 0 7 Saturation Present? Yes O No Depth (inches): Wetlan d Hydrology Present? includes capillary fringe) Data (stream gauge, monitor well aerial photos, previous inspections), if available: Describe Recorded Aerial photo Remarks: no access - hydrology assumed based on aerial photo, landscape position, and observations of adjacent channel elevation [approx. At wetland elevation] US Army Corps of Engineers Arid West - Version 2 Oct. 2008 WETLAND DETERMINATION DATA FORM - Arid West Region Project/Site: Deachutes County LWI City/County: Sunriver/Deschutes Sampling Date: 05-May-10 Applicant/Owner: DESCHUTES COUNTY State: L R Sampling Point: SP 209 Investigator(s):Lanhterrace, etc.): Booy Section, Township, Range: S 7 T.20 S R 11 E dform (hiIslope odplain local relief (concave, convex, none): flat Slope: 1.0% / 0.6 ° Subregion (1-1111): LRR B Lat.: 43.8571 Long.: -121.4574 Datum: NAD 83 Soil Map Unit Name: 29A: Crvaquolls, 0 to 3 percent slopes NWI classification: pEMC Are climatic/ hydrologic conditions on the site typical for this time of year? Yes * No (If no, explain in Remarks.) AreVegetation , Soil ❑ , or Hydrology I I significantly disturbed? Are "Normal Circumstances" present? Yes No( Are Vegetation L , soil , or Hydrology L-1 naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transects, important features, etc. Hydrophytic Vegetation Present? Yes • No 0 Is the Sampled Area Hydric Soil Present? Yes ! No ( - within aWetland? Yes NO C-) Wetland Hydrology Present? Yes No • Remarks: Offsite determination. VEGETATION - Use scientific names of plants. Dominant Species? Absolute Rel.Strat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: ) % Cover Cover Status - - Number of Dominant Species 1• Pinus contorta 3 [4 100.0% FAC That are 08L, FACW, or FAC: 3 (A) 2 0 ❑ om% El ° Total Number of Dominant 3. 0 p 0 r° Species Across All Strata: 3 (S) 4. 0 ❑ 0.0°r° 3 =Total Cover Percent of dominant Species 100.0% (A/B) Sapling/Shrub Stratum (Plot size: ) That Are OBL, FACW, or FAC: • 1. Salix geyeriana 5... 100.09r° FACW Prevalence index worksheet: 2• 0 1 1 0.0% Total % Cover of: Multiply by: 3• 0 7 0.0% . 0131- species 100 x 1. = 100 4. o o.o% ❑ FACW species 5 x 2 10 5. 0. 1 1 0.0% FAC species 3 x 3= 9 5 = Total Cover Fspecies U x 4 0 Herb Stratum (Plot size: D x 5 0 i Carex aquatilis 1 90 L I 90.0% O8L uP1- spec es . Column Totals: 108 (A) 119 (13) 2. Carex nebrascensis 1.0 L 10.0%o OBL 3 0 ❑ 0.o% Prevalence Index = 6/A = 1.102 4. 0 0.0% j Hydrophytic Vegetation Indicators: 5. 0 ❑ 0.0% 7 Dominance Test is a 50% 6. 0 0.0°r° U prevalence index is 53.0 7. 0 i 0.0°r° Morphological Adaptations 1 ;.'rovide supporting 0 0.o% data in Remarks or on a separate sheet) 9 0 ❑ 0.o°r° i ~ Problematic Nydrophytic Vegetation 1 ( cplain) 10, 0 ❑ 0.0%° 11. o ❑ o.o% . ~ Indicators of hydric loll and wetland hydrology must 100 =Total Cover be present, unless disturbed or problematic. Woody Vine Stratum (Plat size: ) 1 0 . ❑ 0.0% 2. 0 ❑ 0.o% Hydrophytic 0 = Total Cover Vegetation Present? Yes No ( ) % Bare Ground in Herb Stratum: 0 % Cover of Biotic Crust 0 Remarks: Carex dominant through majority of wetland, individual Salix and Pinus as well. *Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS. US Army Corps of Engineers Arid West - Version 2 Oct. 2008 Soil Sampling Point: SP 209 Profile Description: (Describe to the depth needed to document the Indicator or confirm the absence of Indicators.) Matrix Redox Feat res Depth (inches) Color (moist) % u Color (moist) % Type 1 Loc= Texture Remarks i I Type. C=Concentration. D=Depletion. RM=Reduced Matrix, CS=Covered or Coated Sand Grains 21-ocation. PL-Pore Lining. M=Ma trIX Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils:3 ❑ Histosol (Al) Sandy Redox (SS) I❑ 1 cm Muck (A9) (LRR C) ❑ Histic Epipedon (A2) ❑ Black Histic (A3) Stripped Matrix (S6) I 2 cm Muck (A10) (LRR B) [ I Hydrogen Sulfide (A4) L Loamy Mucky Mineral (Fl) ❑ Reduced Vertic (F18) ❑ Stratified Layers (AS) (LRR C) Loamy Gleyed Matrix (F2) Red Parent Material (TF2) [ 1 Cm Muck (A9) (LRR D) ❑ Depleted Matrix (F3) ❑ Other (Explain in Remarks) . ❑ Depleted Below Dark Surface (All) ❑Redox Dark Surface (F6) l Depleted Dark Surface (F7) r Thick Dark Surface (A12) Redox depressions (F8) ❑ Sandy Muck Mineral (Sl) vernal Pools (F9) 3 Indicators of hydrophytic vegetation and ❑ Sandy Greyed Matrix (54) wetland hydrology must be present. Restrictive Layer (if present): Type: , Depth (inches); Hydric Soil Present? Yes No ~ Remarks: no access - hydric soils assumed based on OBL dominant veg. • Hydrology Wetland Hydrology Indicators: Primary indicators (minimum. of one required; check all that apply) Secondary Indicators (2 or more required) ❑ Surface Water (Al) Salt Crust (Bll) Water Marks (Bl) (Riverine) High Water Table (A2) ❑ Biotic Crust (B12) ❑ Sediment Deposits (B2) (Riverine) ❑ Saturation (A3) Aquatic Invertebrates (B13) Drift Deposits (B3) Riverine) ❑ Water Marks (BI) (Nonriverine) ❑ Hydrogen Sulfide Odor (Cl) ❑7 Drainage Patterns (810) Sediment Deposits (B2) (Nonriverine) Oxidized Rhizospheres along Living Roots (0) ❑ Dry Season Water Table (C2) Drift deposits (B3) (Noneriverine) Presence of Reduced Iron (C4) Crayfish Burrows (CB) Surface Soil Cracks (136) ❑ Recent Iron Reduction in Plowed Soils (C6) Saturation Visible on Aerial Imagery (C9) ❑ Inundation Visible on Aerial Imagery (87) Thin Muck Surface (C7) Shallow Aquitard (D3) ~J Water-Stained Leaves (B9) Other (Explain in Remarks) iv/1 FAC-neutral Test (DS) Field Observations: Surface Water Present? Yes O No Depth (inches): Water Table Present? Yes ( % No Depth (inches): J tl W d H Y N Saturation Present? - - (includes capillary fringe) Yes No ! e an Depth (inches): ydrology Present? es O Describe Recorded Data stream gauge, monitor well, aerial photos, previous inspections), if avai lable rial photo Aerial photo ........ri . . Remarks: no access - hydrology assumed based on aerial photo, landscape position, and observations of adjacent river elevation [approx. At wetland elevation) US Army Corps of Engineers Arid West - Version 2 Oct. 2008 E WETLAND DETERMINATION DATA FORM - Arid West Region Project/Site: Deachutes County LWI City/County: Sunriver/Deachutes Sampling Date: O6-May-10 Applicant/Owner: DESCHUTES COUNTY State: OR Sampling Point: SP 210 investigator(s): Sarah Hartung, Aaron Boo Section, Township, Range: S 7 T 20S R 11 E Landform (hi (slope, terrace, etc.: Floodplain Local relief (concave, convex, none) concave Slope: 1.0% / 0.6 ° • Subregion (LRR): LRR B Lat.: 43.8599 Long.: -121.4570 Datum: NAD 83 Soil Map Unit Name: W: Water NWI classification: PEMC Are climatic/ hydrologic conditions on the site typical for this time of year? Yes * No - (If no, explain in Remarks.) Are Vegetation I I , Soil I I , or Hydrology ❑ significantly disturbed? Are "Normal Circumstances" present? Yes (il!) No Are Vegetation L , Soil ❑ , or Hydrology -i naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transects, important features, etc. Hydrophytic Vegetation Present? Yes ' No C-) Is the Sampled Area Hydric Soil Present? Yes ' No within aWetland? Yes * No Wetland Hydrology Present? Yes No Remarks: On-site determination. VEGETATION - Use scientific names of plants. Dominant Species? Absolute Re1.Strat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: i % Cover Cover Status Number of Dominant Species 1. 0 0.0% That are OBL, FACW, or FAC: 1 (A) 2 0 % . Total Number of Dominant 3. 0 0.0 Species Across All Strata: 1.. (B) 4. 0 0.0% 0 Total Cover = Percent of dominant Species 100 0% (A/13) Sapling/Shrub Stratum (Plot size: ) . That Are OBL, FACW, or FAC: 1. 0 I 0.0% 'prevalence Index worksheet: 2. 0 ❑ o.ooi° Total % Cover of; Multiply by: 3. 0 ❑ 0.0% OsL species 100 x 1 - 100 4. 0 f o.0% FACW species 0 x 2- D . 5. 0 E 0.00% FAC species 0 x 3= 0 0 = Total Cover FACU species 0 x 4= 0 Herb Stratum (Plot size: 1 0 0 Carex aquatilis 1 100 n 100.0% OBL UPL species x 5 = . El lColumn Totals: 100 (A) 100 (a) 2. 0 o.0% 3. 0 . ❑ 0.0% Prevalence Index = B/A = 1.000 i 4. 0 0.0% Hydrophytic Vegetation Indicators: 5. 0 I_I 0.0% W Dominance Test is a 50% 6. ❑ o.0% LV Prevalence Index is 53.0 1 7, 0 0 o 0.0 /o ❑ 0 00% Morphological Adaptations 11. Irovide supporting 8. . data in Remarks or on a separate sheet) 9 Problematic Hydrophytic Vegetation 1 (1 :plain) 10. 0 ❑ 0.0 ~ 11 0 ❑ o.o% . 1 Indicators of hydric soil and wetland hydrology must 100 = Total Cover be present, unless disturbed or problematic. Woody Vine Stratum (Plot sae: 1. 0 ❑ 0.0% 2. 0 0.0% Hydrophytic O. = Total Cover Vegetation - - Present? Yes No % Bare Ground in Herb Stratum: 0 % Cover of Biotic Crust D Remarks: *Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS. US Army Corps of Engineers Arid West - Version 2 Oct. 2008 Soil Sampling Point: SP 210 Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Depth Matrix Redox Features . , (Inches C olor (moist) ) Color (moist) % "k Type 1 Color (moist) Loc_ Texture Remarks , . o 100/a 5 0 10YR 2/2 w/ roots Silt Loam 5-20 10YR 2/1 100% Silt type. C=Concentrabon. D=Depletion. RM=Reduced Matrix, CS-Covered or Coated Sand Grains Location: PL =Pore =Pore Lining. M=Matroc Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric 5oils3 ❑ Histosol (Al) I _ Sandy Redox (SS) f 1 cm Muck (A9) (LRR C) Histic Epipedon (A2) ❑ Stripped Matrix (S6) ❑ 2 cm Muck (A10) (LRR B) ❑ Black Histic (A3) ❑ Hydrogen Sulfide (A4) Loamy Mucky Mineral (Fl) ❑ Reduced Vertic (1`18) ❑ Stratified Layers (AS) (LRR C) ❑ Loamy Gleyed Matrix (F2) ❑ Red Parent Material (TF2) ❑ 1 cm Muck (A9) (LRR D) Depleted Matrix (F3) ❑ Other (Explain in Remarks) ❑ Redox Dark Surface (F6) Depleted Below Dark Surface (Ail) Depleted Dark Surface (F7) ❑ Thick Dark Surface (A12) ❑ Redox depressions (F8) Sandy Muck Mineral (Sl) Vernal Pools (F9) 3 Indicators of hydrophytic vegetation and Sandy Gleyed Matrix (S4) wetland hydrology must be present. Restrictive Layer (if present): Type: Depth (inches). Hydric Soil Present? Yes NO Remarks: HYDRIC SOILS ASSUMED BASED ON PERSISTANT SATURATION Hydrology Wetland Hydrology Indicators: i?r mart' Indicators (minimum of one required; check all that apply) Secondary Indicators (2 or more required) ❑ Surface Water (Al) I I Salt Crust (Bil) ❑ Water marks (Bl) (Riverine) U High Water Table (A2) ❑ Biotic Crust (B12) Sediment Deposits (B2) (Riverine) W Saturation (A3) ❑ Aquatic invertebrates (813) ❑ Drift Deposits (B3) Riverine) ❑ Water Marks (Bl) (Nonriverine) ❑ Hydrogen Sulfide Odor (Cl) ❑ Drainage Patterns (B10) Sediment Deposits (B2) (Nonriverine) ❑ Oxidized Rhizospheres along Living Roots (0) 1 Dry Season Water Table (C2) Drift deposits (B3) (Noneriverine) I I Presence of Reduced Iron (C4) ❑ Crayfish Burrows (C8) Surface Soil Cracks (B6) ❑ Recent Iron Reduction in Plowed Soils (C6) Saturation Visible on Aerial Imagery (0) ❑ Inundation Visible on Aerial Imagery (B7) Thin Muck Surface (0) ❑ Shallow Aquitard (D3) ❑ Water-Stained Leaves (89) ❑ Other (Explain in Remarks) FAC-neutral Test (D5) Field Observations: Surface Water Present? Yes - No Depth (inches): Water Table Present? Yes No - Depth (Inches): 10 Yes No Saturation Present? Yes I!~ No (includes capillary fringe) Wetland H Depth (inches): ydrology Present? Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if avai lable: Remarks: ~I US Army Corps of Engineers Arid West - Version 2 Oct. 2008 • WETLAND DETERMINATION DATA FORM - Arid West Region Project/Site: Deachutes County LWI City/County: Sunriver/Deschutes Sampling Date: 06-May-10 Applicant/owner: DESCHUTES COUNTY State: IOR J Sampling Point: SP 212 Investigator(s)- Sarah Hartung, Aaron BooY Section, Township. Range: S 7 T 20 S R 11 E Landform (hillslope, terrace, etc.): Floodplain Local relief (concave, convex none): flat Slope: 1.0% / 0.6 ° Subregion (LRR): LRR B Lat.: 43.8538 Long: -121,4587 Datum: NAD 83 Soil Map Unit Name: 29A: Cryaouolls, 0 to 3 percent slopes NWI classification: PEMF Are climatic/ hydrologic conditions on the site typical for this time of year? Yes No' • (If no, explain in Remarks.) Are Vegetation ! I , Soil I , or Hydrology significantly disturbed? Are "Normal Circumstances" present? Yes 0; No AreVegetation , soil L , or Hydrology naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transects, important features, etc. Hydrophytic Vegetation Present? Yes i4' NO Is the Sampled Area Hydric Soil Present? Yes No Wetland Hydrology Present? Yes No within a Wetland? Yes No Remarks: Off-site determination. VEGETATION - Use scientific names of plants. Dominant Species? Absolute Rel.Strat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: ) o /o Cover Cover Status I Number of Dominant Species 0 J L 0.0% I That are OBL, FACW, or FAC: 2 (A) 2, 0 I 0.0% 3 0 0 0°k Total Number of Dominant , . Species Across All Strata: 2 (B) 4. 0 0.0% T t l C Percent of dominant Species 0 = o a over o Sapling/Shrub Stratum (Plot size: ) That Are OBL, FACW, or FAC: 1 • 0 0.0% Prevalence index worksheet: 2. 0 0.0% Total % Cover of: Multiply by: 3. 0 0.0% i06L species 80 x 1 = 80 4, 0 L! 0.0% FACW species 20 x 2 = 40 5. 0 0.0% FAC species 0 x 3= 0 0 = Total Cover FACU species 0 x 4- 0 Herb Stratum (Plot size: ) 0 0 Carex q 1 % 013E x 5 UPL species . 2. ]uncus balticus 20 JI 20.0% FACW 100 (A) 120 (B) column Totals; 3. 0 0.0% Prevalence Index = B/A = 1.200 4• 0 FI 0.0% Hydrophytic Vegetation Indicators: 5. 0 0.0% V Dominance Test is > 50% 6. 0 U.0% N Prevalence Index is $3.0 1 7. 0 0 0.0% • 0 0% 1 I Morphological Adaptations 1 provide supporting 8. _ . data in Remarks or on a separate sheet) 9. 0 0.0% Problematic Hydrophytlc Vegetation 1 (1 cplain) 10. 0 1 0.0% 11. 0 0.0% 1 Indicators of hydric soil and wetland hydrology must 1 00 Total Cover = 100.0 /o (A/13) be rose t, un ~ less d'sturbed or roblematic Woody Vine Stratum (Plot size: ) 1. 0 0.0% 2. 0 _ 0.0% % Bare Ground in Herb Stratum: 0 Remarks: 0 = Total Cover % Cover of Biotic Crust 0 p n p I Hydrophytic Vegetation Present? Yes • No *Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS. US Army Corps of Engineers Arid West - Version 2 Oct. 2008 Soil Sampling Point: SP 212 Profile Description; (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Matrix Depth (inches) Color (moist) Color (moist) % Type 1 LOC= Texture Remarks I Type: C=Concentration. D=Depletion. RM=Reduced Matrix, CS=Covered or Coated Sand Grains 21-ocation: PL=Pore Lining. M=Matrix Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils:3 Histosol (Al) Sandy Redox (S5) 1 cm Muck (A9) (LRR C) Histic Epipedon (A2) Stripped Matrix (56) 2 cm Muck (A10) (LRR B) Black Histic (A3) r _i Loamy Mucky Mineral (Fl) Reduced Vertic (1`18) Hydrogen Sulfide (A4) Loamy Gleyed Matrix (F2) Red Parent Material (TF2) Stratified Layers (A5) (LRR C) Depleted Matrix (F3 ) IVI Other (Explain in Remarks) 1 cm Muck (A9) (LRR D) Redox Dark Surface (F6) I Depleted Below Dark Surface (All) Depleted Dark Surface (F7) Thick Dark Surface (A12) M ck Min l Sl nd S Redox depressions (F8) 3 Indicators of h droph tic ve etation and u ( ) era a y 'Vernal Pools (F9) y y g wetland hydrology must be present. L., Sandy Gleyed Matrix (S4) Restrictive Layer (If present): Type: Depth (inches): Hydric Soil Present? Yes No Remarks; HYDRIC SOILS BASED ON PERSISTANT SATURATION Hydrology Wetland Hydrology Indicators: PrimaryIndicators (minimum of one required; check all that apply) Secondary indicators (2 or more required) i I Surface Water (Al) Salt Crust (Bll) Water Marks (Bl) (Riverine) High Water Table (A2) Biotic Crust (812) Sediment Deposits (B2) (Riverine) Saturation (A3) Aquatic Invertebrates (B13) Drift Deposits (B3) Riverine) Water Marks (Bi) (Nonriverine) Hydrogen Sulfide Odor (Cl) Drainage Patterns (B10) Sediment Deposits (92) (Nonriverine) Oxidized Rhizospheres along Living Roots (0) Dry Season Water Table (C2) Drift deposits (B3) (Nonriverine) Presence of Reduced Iron (C4) Crayfish Burrows (C8) Surface Soil Cracks (B6) Recent Iron Reduction in Plowed Soils (C6) r Saturation Visible on Aerial Imagery (C9) Inundation Visible on Aerial Imagery (87) Thin Muck Surface (C7) I Shallow Aquitard (D3) Water-Stained Leaves (B9) Other (Explain in Remarks) FAC-neutral Test (D5) Field Observations: Surface Water Present? Yes ` No Depth (inches): Water Table Present? Yes - No • Depth (inches): Saturation Present? Yes No Wetland Hydrology Present? Yes No Depth inches : 0 (includes capillary fringe) Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available: i Remarks: US Army Corps of Engineers Arid West - Version 2 Oct. 2008 WETLAND DETERMINATION DATA FORM - Arid West Region Project/Site: eachutes County LWI City/County: Sunriver/Deschutes Sampling Date: 06-May-10 Applicant/owner: DESCHUTES COUNTY State: OR Sampling Point SP 213 Investigator(s). Sarah Hartung, Y Section, Township, Range: T 205 Slope: R 11 E Landform (hillslope, terrace, etc)n Floodplain Local relief (concave, convex, none): flat 1.0% / 0.6 „ Subregion (LRR): LRR B Lat.: 43.$529 Long.: -121.4592 Datum: NAD 83 Soil Map Unit Name: 29A: Cryaauolls, 0 to 3 percent slopes NWI classification: PEMF Are climatic/hydrologic conditions on the site typical for this time of year? Yes No (If no, explain in Remarks.) Are Vegetation ❑ , Soil ❑ , or Hydrology ❑ significantly disturbed? Are "Normal Circumstances" present? Yes • No U Are Vegetation I-...I , soil L , or Hydrology ❑ naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transects, important features, etc. Hydrophytic Vegetation Present? Yes • No Is the Sampled Area Hydric Soil Present? Yes ! No within a Wetland? Yes ( ) No Wetland Hydrology Present? Yes No C-) Remarks: Off-site determination. VEGETATION - Use scientific names of plants. Dominant Species? Tree Stratum (Plot size: I 1. Absolute % Cover 0 Rel.Strat. Cover ❑ 0.0% Indicator Dominance Test worksheet: Status Number of Dominant Species That are OBL, FACW, or FAC: 1 (A) 2. 0 ❑ 0.0% 3. o ❑ 0.0% Total Number of Dominant Species Across All Strata: 1 (B) 4. o I l o.o°% ° = Total Cover Percent of dominant Species Sapling/Shrub Stratum (Plot size: . That Are OBL, FACW, or FAC: . 1, 0 ❑ o.0% Prevalence Index worksheet: 2. 0 0.0% Total % Cover of: Multiply by: 3. 0 0.0% ospecies 100 x 1 = 100 4. 0 I 0.0% FACW species 0 x 2= 0 5. 0 o.o% FAC species 0 x 3 0 0 = Total Cover FACU species U x 4- 0 Herb Stratum (Plot size: 0 0 x 5 = UPI_ species 1 Typha latifolia 10 :10.0 0131- . a % Column Totals: 100 (A) 100 (s) 2 . Carex 90 90.0 OBL 3. 0 ❑ o.o% Prevalence Index = B/A = 1.000 4. 0 0.0% Hydrophytic Vegetation Indicators: 5, 0 0.0% IVf Dominance Test is n 50% 6. 0 0.0°r° 1 n Prevalence Index Is 53.0 7, 0 ❑ 0.0°k . 1 Morphological Adaptations 1 - Irovide supporting 8. 0 0.0% , data in Remarks or on a separate sheet) 9. .0 ❑ 0.0% Problematic Hydrophytic Vegetation 1 (1 ;plain) 10. 0 ❑ o.o% 11. 0 ❑ 0.0°r° 1 Indicators of hydric soil and wetland hydrology must 100 = Total Cover be present, unless disturbed or problematic. Woody Vine Stratum (Plot size: ) 7 . o ❑ 0.0% 2. 0 ❑ 0.0°rc Hydrophytic 0 = Total Cover Vegetation Present? Yes No % Bare Ground in Herb Stratum: 0 % Cover of Biotic Crust p - Remarks: *Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS. US Army Corps of Engineers 0 100 0% (A1131 Arid West - Version 2 Oct. 2008 Soil Sampling Point: 5P 213 Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) ; Depth Matrix.. Redox Features (inches) Color (moist) a/a Color (moist) % Type 1 LOC2 Texture Remarks 1 Type: C=Concentration.... . p=Depletion. PM=Reduced Matrix, CS_ -Covered or r Coated Sand Grains zLocation: PL=Pore Lining. M-Matra Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Solls3 ❑ Histosol (Al) ❑ Sandy Redox (SS) ❑ 1 cm Muck (A9) (LRR C) Histic Epipedon (A2) ❑ Stripped Matrix (S6) 2 cm Muck (A10) (LRR B) Black Histic (A3) ❑ Loamy Mucky Mineral (Fl) ❑ Reduced Vertic (1`18) ❑ Hydrogen Sulfide (A4) J Loamy Gleyed Matrix (F2) ❑ Red Parent Material (TF2) ❑ Stratified Layers (AS) (LRR C) ❑ Depleted Matrix (F3) ~d Other (Explain in Remarks) ❑ 1 cm Muck (Ag) (LRR D) ❑Redox Dark Surface (F6) Depleted Below Dark Surface (All) Depleted Dark Surface (F7) Thick Dark Surface (A12) ❑ Redox depressions (F8) ❑ Sandy Muck Mineral (Si) Vernal Pools (F9) 3 Indicators of hydrophytic vegetation and Sandy Gleyed Matrix (54) ~ wetland hydrology must be present. Restrictive Layer (if present): Type. Depth (inches): Hydric Soil Present? Yes (i) No (l) Remarks: J ASSUME HYDRIC SOILS BASED ON AERIAL MAP AND LANDSCAPE POSITION HYdrologY Wetland Hydrology Indicators: Primary. Indicators (minimum of one required;, check all that apply) Secondary Indicators (2 or more required) ❑ Surface Water (Al) Salt Crust (B11) Water Marks (Bl) (Riverine) 1 1 High Water Table (A2) ❑ Biotic Crust (B12) ❑ Sediment Deposits (B2) (Riverine) ❑ Saturation (A3) _ Aquatic Invertebrates (B13) Drift Deposits (0) Riverine) Water Marks (Bl) (Nonriverine) ❑ Hydrogen Sulfide Odor (Cl) ❑ Drainage Patterns (B10) ❑ Sediment Deposits (B2) (Nonriverine) ❑ Oxidized Rhizospheres along Living Roots (0) L_._I Dry Season Water Table (C2) Drift deposits (B3) (Nonriverine) ❑ Presence of Reduced Iron (C4) ❑ Crayfish Burrows (CS) Surface Soil Cracks (B6) Recent Iron Reduction in Plowed Soils (C6) L/~ Saturation Visible on Aerial Imagery (C9) Inundation Visible on Aerial Imagery (B7) L_l Thin Muck Surface (C7) ❑ Shallow Aquitard (D3) ❑ Water-Stained Leaves (B9) Other (Explain in Remarks) d FAC-neutral Test (p5) Field Observations: Surface Water Present? Yes - No Depth (inches): Water Table Present? Yes No Depth (inches): J Yes No 0 Saturation Present? Yes No Wetlan Depth (inches): d Hydrology Present? (includes capillary fringe) Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available: Aerial Photo Remarks: ASSUME HYDROLOGY BASED ON LOW ELEVATION AND PROXIMITY TO THE RIVER US Army Corps of Engineers Arid West - Version 2 Oct. 2008 11 • WETLAND DETERMINATION DATA FORM - Arid West Region Project/Site: Deachutes County LWI City/County: Sunriver/Deschutes Sampling Date: 06-May-10 ,ApplicantlOwner: DESCHUTES COUNTY State: OR Sampling Point: SP 214 Investigator(s): Sarah Hartung, Aaron Booy Section, Township, Range: S 18 T 20S R 11 E Landform (hillslope, terrace, etc.): Floodplain Local relief (concave, convex, none): flat Slope: 1.0% / 0.6 ° Subregion (LRR): LRR 8 Lat.: 43.8464 Long.: -121.4595 Datum: NAD 83 Soil Map Unit Name: 144A: Sunriver sandy loam, 0 to 3 percent slopes NWI classification: PEMC. Are climatic/ hydrologic conditions on the site typical for this time of year? Yes No (If no, explain in Remarks.) Are Vegetation , Soil or Hydrology significantly disturbed? Are "Normal Circumstances" present? Yes NO Are Vegetation _ , Soil , or Hydrology I_I naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transects, important features, etc. Hydrophytic Vegetation Present? Yes No Is the Sampled Area Hydric Soil Present? Yes No within a wetland? Yes No Wetland Hydrology Present? Yes No Remarks: On-site determination. VEGETATION - Use scientific names of plants. Dominant Species? Absolute Rel.Strat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: ) % Cover Cover Status Number of Dominant Species 1. 0 0.0% That are OBL, FACW, or FAC: 2 (A) 2. o I o.o°r° Total Number of Dominant 3, 0 1 0.0% Species Across All Strata: 3 (B) 4. 0 C' 0.0°r° 0 = Total Cover Percent of dominant Species 66.7% (A/B) That Are OBL, FACW, or FAC: • Sapling/Shrub Stratum (Plot size: ) i 1. Salix geyeriana 2. 3. 4. 5. Woody Vine Stratum (Plot size: ) 10 100.0% Prevalence worksheet. o 0.0% Total %Coerr of: Multiply by: 0 0.0% oBL species 60 x 1 - 60 0 0 .0% FACW species 40 x Z = 80 ~I 0 .0 /n 0 ° 0 x 3- 0 FAC Species 10 = Total Cover FACU species 0. x 4 - 0 60 60 0% OBL uPL species 0 x 5 - 0. . [olumn Totals: 100 (q) 140 (s) 40 40.0% FACW 0 0.00/0 Prevalence Index = B/A = 1.400 0.0% Hydrophytic Vegetation indicators: 0 0.0% INI Dominance Test is n 50% 0 0.0°/o k Prevalence Index is 53.0 1 0 J 0.0% Morphological Adaptations 1 1-Irovide supporting 0 0.0% data in Remarks or on a separate sheet) 0 0.0% Problematic Hydrophytic Vegetation 1 (1 :plain) 0 0.0% 0 0.0% 1 indicators of hydric soil and wetland hydrology must 100 = Total Cover be present, unless disturbed or problematic. 0 0.0% Hydrophytic 2. 0 0.0% % Bare Ground In Herb Stratum: 0 Remarks: Vegetation No 0 = Total Cover Present? Yes No % Cover of Biotic Crust 0 *Indicator suffix National status or professional decision assigned because Regional status not defined by FWS. US Army Corps of Engineers Arid West - Version 2 Oct. 2008 SOII . Sampling Point: SP 214 Profile Description. ( Describe to the depth needed to document the indicator or confirm the absence of indicators.) Depth Matrix V Redox Features (inches) Color (moist) % Color (moist) % Type 1 Locz Texture Remarks 0-2 10YR 3/2 100% Loam duff 2-8 10YR 3/2 100% Silt decaying sedge material 8-20 10YR 3/1 80% lOYR 3/4 20% C PL Clay Loam I Type: C=Concentration. D=Depletion. RM=Reduced Matrix, CS=Covered or Coated Sand Grains xLOCation: PL=Pore Lining. M=Matroc Hydric Soil Indicators: (Applicable to all LR Rs, unless otherwise noted.) Indicators for Problematic Hydric SoilsP 1 Histosol (Al) Sandy Redox (S5) [ ! 1 cm Muck (A9) (LRR C) L Histic Epipedon (A2) ❑ Stripped Matrix (S6) ❑ 2 M k A10 LRR B Black Histic (A3) Loamy Mucky Mineral (FS) cm uc ( ) ( ) Reduced Vertic (1`18) Hydrogen Sulfide 71 Loamy Gleyed Matrix (F2) L7 Red Parent Material (TF2) Stratified Layers (ASS) (LRR C) ❑ Depleted Matrix (F3) Other (Ex lain in Remarks) 1 cm Muck (A9) (LRR D) Redox Dark Surface (F6) p ❑ Depleted Below Park Surface (All) ❑ Depleted Dark Surface (F7) Thick Dark Surface (A12) l Redox depressions (1`8) L ❑ Sandy Muck Mineral (Sl) . J Vernal Pools (F9) 3 Indicators of hydrophytic vegetation and ❑ Sandy Gleyed Matrix (S4) wetland hydrology must be present. Restrictive Layer (if present): Type: Depth (inches): Hydric Soil Present? Yes No Remarks: Hydrology Wetland Hydrology Indicators: Primary Indpatpr5 (minimum of one required; Check all that apply) Secondary Indicators (2 or more required) ❑ Surface Water (Al) ❑ Salt Crust (Bll) ❑ Water Marks (BI) (Riverine) High Water Table (A2) L Biotic Crust (1312) Sediment Deposits (B2) (Riverine) k] Saturation (A3) ❑ Aquatic Invertebrates (B13) ❑ Drift Deposits (133) Riverine) I ] Water Marks (Bl) (Nonriverine) L Hydrogen Sulfide Odor (Cl) Drainage Patterns (B10) ❑ Sediment Deposits (B2) (Nonriverine) ~ Oxidized Rhizospheres along Living Roots (0) L l Dry Season Water Table (C2) Drift deposits (B3) (Noneriverine) ❑ Presence of Reduced Iron (C4) i .1 Crayfish Burrows (C8) ❑ Surface soil cracks (B6) Recent Iron Reduction in Plowed Soils (C6) ❑ Saturation Visible on Aerial Imagery (C9) J Inundation Visible on Aerial Imagery (B7) Thin Muck Surface (0) 1 .J Shallow Aquitard (D3) ❑ Water-Stained Leaves (139) ❑ Other (Explain in Remarks) [ FAC-neutral Test (D5) Field Observations: Surface Water Present? Yes 0 No Depth (inches): Water Table Present? Yes No ! Depth (inches): Saturation Present? Yes No ^ 1 Wetland Hydrology Present? Yes No ~ ~ Depth (inches): (includes capillary fringe) Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if avai lable: Remarks: SATURATION AT SURFACE US Army Corps of Engineers Arid West - Version 2 Oct. 2008 WETLAND DETERMINATION DATA FORM - Arid West Region Project/Site: Deachutes County LWI City/County: Sunriver/Deschutes Sampling Date: 08-May-10 ,Applicant/owner: DESCHUTES COUNTY State: LOR Sampling Point: SP 217 Investigator(s): Sarah Hartung, Aaron Booy Section Township, Range: S 1 T 20 S R 11 E Landform hlllslo a terrace, etc.): Floodplain Local relief (concave, convex, none) convex Slope: 2.0% / 1.1 ° Subregion (LRR): LRR B Lat.: 43.8323 Long: -121.4481 Datum: NAD 83 Soil Map Unit Name: 29A: Cryaquolls, 0 to 3 percent slopes NWI classification: PS..SC Are climatic/ hydrologic conditions on the site typical for this time of year? Yes * No (If no, explain in Remarks.) Are Vegetation ❑ , Soil , or Hydrology L significantly disturbed? Are "Normal Circumstances" present? Yes * No Are Vegetation ❑ , Soil , or Hydrology naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transects, important features, etc. Hydrophytic Vegetation Present? Yes ' No Is the Sampled Area Hydric Soil Present? Yes ! No within a Wetland? Yes 'No Wetland Hydrology Present? Yes No Remarks: Off-site determination. VEGETATION - Use scientific names of plants. Dominant Species? Absolute Rel.Strat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: ) % Cover over Status Number of Dominant Species O ° 0.0/o That are OBL, FACW, or FAC: 1 (A) 2 0 0.0% . 0 ° 0 / 0 I Total Number of Dominant 3. ° . Species Across All Strata: 2 (B) 4. o [ ] 0.0% Percent of dominant Species 50.0% (A/B) 0 -Total Cover o • Sapling/shrub Stratum (Plot size: ) That Are OBL, FACW, or FAC 1. Salix geyeriana 2. 3. 4. 5. Herb Stratum (Plot size: 1 Carex aquatilis Woody Vine Stratum (Plot size: ) 1. 50 100.0% heet: Pr e val d 0 0.0% Multiply by: Coverr of: Total °o 0 0.0% 001- species 90 x 1 = 90 0 0.0% FACW species 0 x 2 - 0. 0, 0.0% FAC species 0 x 3 = 0. 50 = Total Cover FACU species 0 x 4 = 0 9 0 d❑ 100.0% OBL UPL species 0 x 5- 0 column Totals; 90 (A) 90 (B) 0 ❑ 0.0% 0 ❑ 0.0% Prevalence Index = B/A = 1.000 U% Hydrophytic Vegetation Indicators: 0 L 0.0% Dominance Test is n 50% 0 0.o% Prevalence Index is 53.0 1 0 ❑ 0 o.o ❑ Morphological Adaptations 1 i.'rovide supporting 0 0.0% data in Remarks or on a separate sheet) 0 0.0% 1 ..1 Problematic Hydrophytic Vegetation 1(1 :plain) 0 ❑ 0.0% 0 ❑ 0.0% 1 Indicators of hydric soil and wetland hydrology must go . Total Cover be present, unless disturbed or problematic. I 0 ❑ 0.0% 2. 0 ❑ 0.0% Hydrophytic _ Vegetation 0 - Total Cover Present? Yes No % Bare Ground in Herb Stratum: 0 % Cover of Biotic Crust 0 Remarks: *Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS. US Army Corps of Engineers Arid West - Version 2 Oct. 2008 Soil Sampling Point: SP 217 profile Description: (Describe to depth needed to document the indicator or confirm the absence . . the of indicators.) . Matrix Depth Redo' Features (Inches) Color (moist) ~D " Color (moist) % Type 1 LOC2 Texture Remarks 1 Type; C=Concentration. D=Depletion. RM=Red uced Matrix, CS=Covered or Coated Sand Grains 'Location: PL=Pore Lining. M=Matra Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils:3 ❑ Histosol (Al) ❑ Sandy Redox (S5) ❑ 1 cm Muck (A9) (LRR C) ❑ Histic Epipedon (A2) ❑ Stripped Matrix (S6) [ ] ❑ Black Histic (A3) ❑ Hydrogen Sulfide (A4) Loamy Mucky Mineral (Fl) 2 cm Muck (A10) (LRR B) ❑ Reduced Vertic (F18) ❑ Stratified Layers (A5) (LRR C) Loamy Gleyed Matrix (F2) Red Parent Material (TF2) ❑ 1 cm Muck (A9) (LRR D) ❑ Depleted Matrix (9) 1 Other (Explain in Remarks) [ Depleted Below Dark Surface (All) Redox Dark Surface (F6) ❑ Thick Dark Surface (A12) ❑ Depleted Dark Surface (F7) [ Sandy Muck Mineral (51) I Redox depressions (F8) ❑ Vernal Pools (F9) 3 Indicators of hydrophytic vegetation and ❑ Sandy Gleyed Matrix (54) wetland hydrology must be present. Restrictive Layer (if present): Type: Depth (inches): Hydric Soil Present? Yes * No Remarks; ASSUME HYDRIC SOILS BASED ON HYDROLOGY INDICATOR Hydrology Wetland Hydrology Indicators: Primary Lndicators (minimum of one required; check all that apply) Secondary Indicators (2 or more required) ❑ Surface Water (Al) Salt Crust ( ll) L ❑ Water Marks (Bl) (Riverine) High Water Table (A2) ` I Biotic Crust 812) Sediment Deposits (82) (Riverine) Saturation (A3) [ ] Aquatic invertebrates (813) Drift Deposits (B3) Riverine) ❑ Water Marks (Bl) (Nonriverine) Hydrogen Sulfide Odor (CI) ❑ Drainage Patterns (B10) Sediment Deposits (B2) (Nonriverine) ❑ Oxidized Rhizospheres along Living Roots (0) I I Dry Season Water Table (C2) ❑ Drift deposits (B3) (Noneriverine) 1 Presence of Reduced Iron (C4) U Crayfish Burrows (C8) [_J Surface Soil Cracks (B6) ❑ Recent Iron Reduction in Plowed Soils (C6) J Saturation Visible on Aerial Imagery (C9) ❑ Inundation Visible on Aerial Imagery (B7) I I Thin Muck Surface (C7) Shallow Aquitard (D3) Water-Stained Leaves (B9) ❑ Other (Explain in Remarks) FAC-neutral Test (D5) Field Observations: Surface Water Present? Yes No ' Depth (inches): J Water Table Present? Yes No Depth (inches): Saturation Present? Yes J!) No % Depth (inches): 0 Wetland Hydrology Present? Yes No - (includes capillary fringe) Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if avai lable: Aerial photo Remarks: Saturation was visually observed off-site and was based on the observation of water glisten ing on the surface by the naked eye and/or with the aid of binoculars. US Army Corps of Engineers Arid West - Version 2 Oct. 2008 • WETLAND DETERMINATION DATA FORM - Arid West Region Project/Site: Deachutes County LWI City/County, Sunriver/Deschutes Sampling Date: 08-May-10 Applicant/owner: DESCHUTES COUNTY State: 1 Sampling Point: SP 218 Investigator(s): Landform(hillslope, Sarah Hartung, etc.): Aaron Boo Floodplain Local Section, relief Township, concave, Range: convex 5 19 none : T convex 20S Slope: i e: 2.0 Subregion (LRR): LRR B Lat.: 43.8320 Long.: -121.4481 Datum: NAD 83 Soil Map Unit Name: 29A: CryaQuolls, 0 to 3 percent slopes NWI classification: pSSC Are climatic/hydrologic conditions on the site typical for this time of year? Yes * No (If no, explain in Remarks.) Are Vegetation ❑ , Soil , or Hydrology ❑ significantly disturbed? Are "Normal Circumstances" present? Yes No Are Vegetation soil 71 , or Hydrology naturally problematic? (If needed, explain any answers In Remarks.) Summary of Findings - Attach site map showing sampling point locations, transacts, important features, etc. Hydrophytic Vegetation Present? Yes No Is the Sampled Area Hydric Soil Present? Yes No within a Wetland? Yes * No Wetland Hydrology Present? Yes No - Remarks: Off-site determination. VEGETATION - Use scientific names of plants. Dominant Species? Absolute Rel.Strat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: ) % Cover Cover Status Number of Dominant Species 1 0 L-1 0.0% i That are OBL, FACW, or FAC: 2 (A) 2 0 El 0.0% . U Total Number of Dominant 3, 0 0.0% Species Across All Strata: 2 (B) 4. 0 ❑ 0.0% Percent of dominant Species Total Cover That Are OBI FACW or FAC• 10010% (A/B) Sapling/Shrub Stratum (Plot size: ) 1, Salix geyeriana 2, Spiraea douglasii 3. 4. 5. 30 85.7% FACW i Prevalence Index worksheet: 5 14.3% FACW Total % Cover of: Multiply by: 0 i 0.0% oBL species 50 x 1 = 50 0 ❑ 0.00% FACW species 35 x 2 = 70 0 0.0% FAC species 0 x 3- 0 35 = Total Cover FACU species 0 x 4 .0 50 100.0% 0131 UPL species 0 x 5 = 0 column Totals: 85 (A) 120 (B) 0 o.o% 0 0.0% Prevalence Index = B/A = 1.412 0 u 0.0% Hydrophytlc Vegetation Indicators: 0 ❑ 0.0°k Dominance Test is a 50% 0 U 0.0% Prevalence index is 53.0 1 ° 0 0.0/o L] Morphological Adaptations 1 I_ provide supporting O 0.0% data In Remarks or on a separate sheet) 0 .0.0% ❑ Problematic Hydrophytic Vegetation 1 (1 :plain) 0 LI 0.0% 11. o I I 0.0% 1 Woody Vine Stratum (Plot size: 1. 2. E % Bare Ground in Herb Stratum: 50 Remarks: 50 = Total Cover indicators of hydric soil and wetland hydrology must be present, unless disturbed or problematic. 0 n 0.0% 00.0% Hydrophytic Vegetation 0 = Total Cover Present? Yes ' No - % Cover of Biotic Crust 0 ~ or professional decision assigned because Regional status not defined by FWS. Indicator suffix = National status US Army Corps of Engineers Arid West - Version 2 Oct. 2008 Soil Sampling Point: SP 218 Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Depth Matrix Redox Features inches Color (moist) % Color (moist) % Type I L..ocz Texture Remarks 1 type: C=Concentration. D=Depletion. RM=Reduced Matrix, CS=Covered or Coated Sand Grains I z - Location: PL-Pore Lining. M=Mafia Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Sollsp ❑ Histosol (Al) ❑ Sandy Redox (S5) 1 cm Muck (A9) (LRR C) Histic Epipedon (A2) ❑ Stripped Matrix (S6) El 2 cm Muck (A10) (LRR e) ❑ Black Histic (A3) J Hydrogen Sulfide (A4) Loamy Mucky Mineral (FS) Reduced Vertic (1`18) ❑ Stratified Layers (AS) (LRR C) ❑ Loamy Gleyed Matrix (F2) ❑ Red Parent Material (TF2) 1 cm Muck (A9) (LRR D) f Depleted Matrix (F3) Other (Explain in Remarks) ❑ Redox Dark Surface (F6) t. Depleted Below Dark Surface (Al I) ❑ Depleted Dank Surface (F7) ❑ Thick Dark Surface (A12) Redox depressions (F8) Sandy Muck Mineral (Sl) ❑ Vernal Pools (F9) 3 Indicators of hydrophytic vegetation and Sandy Gleyed Matrix (S4) wetland hydrology must be present. Restrictive Layer (if present): Type: Depth (inches): Hydrlc Soil Present? Yes * No Remarks: ASSUME HYDRIC SOILS BASED ON HYDROLOGY INDICATORS Hydrology Wetland Hydrology Indicators: Primary )nplcators (minimum.of one required; check all that apply) ❑ Surface Water (Ai) Salt Crust (B11) Secondary Indicators (2 or more required) Water Marks (Bl) (Riverine) ❑ High Water Table (A2) ❑ Biotic Crust (612) Sediment Deposits (B2) (Riverine) Saturation (A3) ❑ Aquatic Invertebrates (B13) ❑ Drift Deposits (83) Riverine) ❑ Water Marks (BI) (Nonriverine) Hydrogen Sulfide Odor (Cl) Drainage Patterns (B10) Sediment Deposits (B2) (Nonriverine) ~i Oxidized Rhizospheres along Living Roots (0) ❑ Dry Season Water Table (C2) ❑ Drift de posits (63) (Noneriverine) Presence of Reduced Iron (C4 ) ~ Crayfish Burrows (CS) _ Surface Soil Cracks (B6) ❑ Recent Iron Reduction in Plowed Soils (C6) U Saturation Visible on Aerial Imagery (C9) ❑ Inundation Visible on Aerial Imagery (B7) - Thin Muck Surface (C7) Shallow Aquitard (133) 1 Water-Stained Leaves (B9) F ❑ Other (Explain in Remarks) FAC-neutral Test (D5) Field observations: Surface Water Present? Yes No Depth (inches): Water Table Present? Yes No Depth (inches): Saturation Present? - Wetland Hydrology Present? Yes No includes capillary fringe) Yes U No Depth (inches): L _ 1 Describe Recorded. Data (stream gauge, monitor well, aerial photos, previous inspections), if available: Aerial photo Remarks: US Army Corps of Engineers Arid West - Version 2 Oct. 2008 WETLAND DETERMINATION DATA FORM - Arid West Region Project/Site: Deachutes County LWI City/County: Sunriver/Deschutes Sampling Date: 07-May-10 A F.._..... pplitant/Owner: DESCHUTES COUNTY State: OR Sampling Point: SP 221 • I La dfoam r() Sarah terrace Hartung, Aaron Y etc): Swale Local Section, relief (concave, Range: convex, none): T 20 S R 11 E (hillslope flat Slope: 0.0% / 0.0 ° Subregion (LRR): LRR B Lat.: 43.8016 Long: -121.4593 Datum: NAD 83 Soil Map Unit Name: 144A: Sunriver sandy loam, 0 to 3 percent slopes NWI classification: PEMC Are climatic/ hydrologic conditions on the site typical for this time of year? Yes * No - (If no, explain in Remarks.) Are Vegetation I i , Soil ❑ , or Hydrology I I significantly disturbed? Are "Normal Circumstances" present? Yes * No 0 Are Vegetation L , soil I , or Hydrology L naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transects, important features, etc. Hydrophytic Vegetation Present? Yes NO Is the Sampled Area Hydric Soil Present? Yes ' No within a Wetland? Yes * No Wetland Hydrology Present? Yes No Remarks: Off-site determination. VEGETATION - Use scientific names of plants. Dominant species? Absolute ReLStrat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: ) % Cover Cov er Status Number of Dominant Species ] O ❑ 0 0 ° 1 That are 0131., FACW, or FAC: (A) 2. 0 ❑ 0.0% Total Number of Dominant 3. 0 0.0% . Species Across All Strata: 2 (B) 4. 0 L~ 0.0% Percent of dominant Species Sapling/Shrub Stratum (Plot size: ) o =Total Cover That Are OBL, FACW, or FAC: 50.0% (A/6) 1. Salix geyeriana 2. 3. 4. 5. Herb Stratum (Plot size: ) 1. Carex aquatilis 7 Juncus balticus Woody Vine Stratum (Plot size: 1. 2. Bare Ground in Herb Stratum: 0 Remarks: 2 -1 100.0°k Preval worksheet: d 0 I 0.0% Multiply by Coverr of Total% 0 I_I 0.0°i° . 08L species 95 x 1 = 95 0 0.0% FAcw species 5 x 2 = 10 0 0.0% FAC species 0 x 3- 0 2 Total Cover FACU species 0 x 4- 0 ° BL 5 UPL species 0 x 5 = 0 % column Totals: 100 (A) 105 (a) 5 ❑ 5 0 FACW 0 ❑ 0.0% Prevalence Index = B/A = 1.050 0.0°i° Hydrophytic Vegetation indicators: 0 0.o% IL Dominance Test is 7 50% 0 1. 0.0% n Prevalence Index is 53.0 1 0 0 I I 0.00/1, 0 0% Morphological Adaptations 19 _ Irovide supporting _ . data in Remarks or on a separate sheet) 0 0.0% ❑ problematic Hydrophytic Vegetation 1(1 :plain) 0 o.o% . 0 0.0%0 1 indicators of hydric soil and wetland hydrology must 100 = T otal Cover be present, unless disturbed or pro blematic. 0 ❑ 0.0% 0 J 0.0% 0 = Total Cover 0/6 Cover of Biotic Crust 0 Hydrophytlc Vegetation Yes ' No - Present? *Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS. US Army Corps of Engineers Arid West - Version 2 Oct. 2008 Soil Sampling Point: SP 221 Profile Description: (Describe to the depth needed to document the Indicator or confirm the absence of indicators.) Depth Matrix Redox Features , Inches Color moist % Color (moist) % Type I Loc2 Texture Remarks II I Type. C=Concentration. D=Depletion. RM=Reduced Matrix, CS=Covered or Coated Sand Grains 'Locati on: PL-Pore Lining. M=Matroc PL= Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils3 7 Histosol (Al) J Sandy Redox (S5) I I 1 cm Muck (A9) (LRR C) ❑ Histic Epipedon (A2) ❑ Stripped Matrix (S6) El 2 cm Muck (A10) (LRR B) ❑ Black Histic (A3) L] Hydrogen Sulfide (A4) Loamy Mucky Mineral (FS) F1 Reduced Vertic (1`18) ❑ Loamy Gleyed Matrix (F2) ❑ Red Parent Material (TF2) I Stratified Layers (AS) (LRR C) ❑ 1 cm Muck (A9) (LRR D) Depleted Matrix (F3) I%el Other (Explain in Remarks) Depleted Below Dark Surface (Ali) ❑Redox Dark Surface (F6) Depleted Dark Surface (F7) Thick Dark Surface (A12) i Redox depressions (F8) L Sandy Muck Mineral (Sl) ~ Vernal Pools (F9) 3 Indicators of hydrophytic vegetation and ❑ Sandy Gleyed Matrix (54) wetland hydrology must be present. Restrictive Layer (if present): Type: Depth (inches): Hydric Soil Present? Yes i.!) No U Remarks: ASSUME HYDRIC SOILS BASED ON WETLAND HYDROLOGY INDICATORS AND HYDROPHYTIC VEGETATION. Hydrology Wetland Hydrology Indicators: Primary Indicators (minimum of one required; check all that apply) Secondary Indicators (2 or more required) ❑ Surface Water (Al) Salt Crust (811) i .J Water Marks (Bl) (Riverine) ❑ High Water Table (A2) ❑ Biotic Crust (B12) ❑ Sediment Deposits (B2) (Riverine) ❑ Saturation (A3) Aquatic Invertebrates (B13) 1 Drift Deposits (B3) Riverine) ❑ Water Marks (BI) (Nonriverine) I Hydrogen Sulfide Odor (Cl) Id❑ Drainage Patterns (B10) Sediment Deposits (B2) (Nonriverine) ❑ Oxidized Rhizospheres along Living Roots (0) Dry Season Water Table (0) ❑ Drift deposits (B3) (Noneriverine) I Presence of Reduced Iron (C4) ❑ Crayfish Burrows (C8) Surface Soil Cracks (B6) ❑ Recent Iron Reduction in Plowed Soils (C6) U Saturation Visible on Aerial Imagery (C9) ❑ Inundation Visible on Aerial Imagery (B7) Thin Muck Surface (0) ❑ Shallow Aquitard (133) ❑ Water-Stained Leaves (B9) Other (Explain in Remarks) V FAC-neutral Test (DS) Field Observations: Surface Water Present? Yes 0 No Depth (inches): Water Table Present? Yes C) No Depth (inches): Saturation Present? Yes 0 No Wetland Hydrology Present? Yes * No - Depth (inches): L Includescapillary fringe) - Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available: Remarks: US Army Corps of Engineers Arid West - Version 2 Oct. 2008 WETLAND DETERMINATION DATA FORM - Arid West Region Project/Site: Deachutes County LWI City/County: Sunriver/Deschutes Sampling Date: 07-May-10 Applicant/Owner: DESCHUTES COUNTY State: OR Sampling Point: 5P 222 Investigator(s): Sarah Hartung, Aaron Booy Section, Township, Range: S 31 T 20 S R 11 E Landform (hillslope, terrace, etc.): Valley bottom Local relief (concave, convex, none): flat Slope: 0.0% / 0.0 ° Subregion (LRR): LRR B Lat.: 43.8014 Long.: -121.4588 Datum: NAP 83 Soil Map Unit Name: 29A.: Cryaquolls, 0 to 3 percent slopes NWI classification: PEMC Are climatic/hydrologic conditions on the site typical for this time of year? Yes * NO (If no, explain in Remarks.) Are Vegetation I , Soil ❑ , or Hydrology I I significantly disturbed? Are "Normal Circumstances" present? Yes * No C) Are Vegetation L-] , Soil F1 , or Hydrology ❑ naturally problematic? (If needed, explain any answers In Remarks.) Summary of Findings - Attach site map showing sampling point locations, transects, important features, etc. Hydrophytic Vegetation Present? Yes NO Is the Sampled Area Hydric Soil Present? Yes No within a Wetland? Yes No, Wetland Hydrology Present? Yes No Remarks: On-site determination. VEGETATION - Use scientific names of plants. Dominant species? Absolute Rel.Strat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: ) % Cover Cover Status Number of Dominant Species 1 0 ❑ 0.0% . That are OBL, FACW, or FAC: 2 (A) 2. 2. 0 ❑ 0.0% ❑ Total Number of Dominant 0 0.0% Species Across All Strata: 3 _ (B) 4. o ❑ 0.0 r° Percent of dominant Species 0 Total Cover FACW, or FAC: That Are OBL 66.7% ° (A/B) Sapling/Shrub Stratum (Plot size: ) , 10 1. 0 0.0% Prevalence Index worksheet: 2, 0 ❑ 0.o% Total % Cover of: Multiply by: 3. 0 ❑ 0.0% I OBL species 0 x 1= 0 4. 0 Li o.o% FACw species 20 x 2 - 40 5. 0 ❑ 0.0% FAC species 50 x 3 = 150 0 = Total Cover FACU species 30 x 4 = 120 Herb Stratum (Plot size: ) 0 0 - ° 50 0 FAC x 5 = UPL species 1. Poa sp. 50 . Coumn Totals: 100 (A) 310 (B) l Achill a millefolium 2, 20 ❑ 20.0% FACU , 3. luncus balticus 20 SV] 20.00% FACW Prevalence Index = B/A = 3.100 4 Taraxacum officinale 10 10.0% FACU Hydrophytic vegetation Indicators: 5,. 0 0.0% Dominance Test is a 50% 6 0 ❑ 0.00/0 ❑ Prevalence Index Is S3.0 1 7. 0 I 0.0°/° Morphological Adaptations 1 provide supporting [ 8 0 ❑ o.o% data in Remarks or on a separate sheet) 9. 0 0.0% 1 ❑ Problematic Hydrophytic Vegetation 1 ( :plain) lo. 0 0.0% 11. o f I 0.0°i° i Indicators of hydnit soil and wetland hydrology must 100 =Total Cover ha nra nt. unlace diehirhad nr nrnhinmatie. Woody Vine Stratum (Plot size: ) 1. 0 ❑ 0.0% 2. 0 0.0% % Bare Ground in Herb Stratum: 0 Remarks: • Poa sp. assumed FAC. 0 = Total Cover % Cover of Biotic Crust 0 Hydrophytic Vegetation Present? Yes No 0 decision assigned because Regional status not defined by FWS. *.Indicator suffix = National status or professional. US Army Corps of Engineers Arid West - Version 2 Oct. 2008 Soil Sampling Point: SP 222 Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Matrix Depth Redox Features......... . („Inches) Color (moist), "/o Color (moist) 9/0 Type I Loc2 Texture Remarks 0-20 10YR 3/2 100% Silt Loam I Type. C=Concentration. D=Depletion. RM=Reduced Matrix, CS=Covered or Coated Sand Grains xLocati on: PL=Pore Lining. M=Matrix ~I Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils:3 ❑ Histosol (Al) ❑ Sandy Redo. (55) ❑ 1 cm Muck (A9) (LRR C) ❑ Histic Epipedon (A2) ❑ Stripped Matrix (S6) ❑ 2 cm Muck (A10) (LRR B) Black Histic (A3) ❑ Hydrogen Sulfide (A4) ] Loamy Mucky Mineral (Fl) 1 I Reduced Vertic (1`18) j Stratified Layers (A5) (LRR C) ❑ Loamy Gleyed Matrix (F2) ❑ Red Parent Material (TF2) ❑ 1 cm Muck (A9) (LRR D) Depleted Matrix (F3) Other (Explain in Remarks) ~ ❑ Redox Dark Surface (F6) Depleted Below Dark Surface (All) J Depleted Dark Surface (F7) ❑ Thick Dark Surface (A12) ❑ Redox depressions (F8) Sandy Muck Mineral (Sl) Vernal Pools (F9) 3 Indicators of hydrophytic vegetation and ❑ Sandy Gleyed Matrix (54) wetland hydrology must be present. Restrictive Layer (if present): Type: Depth (inches);, - - Hydric Soil Present? Yes NO Remarks: Hydrology Wetland Hydrology Indicators: Prmary,(ndicatprsfminimum of one required; check all that applYl Secondary Indicators (2 or more required) Surface Water (Al) ❑ Salt Crust (811) Water Marks (B1) (Riverine) ❑ High Water Table (A2) ^I Biotic Crust (B12) ❑ Sediment Deposits (82) (Riverine) I._! Saturation (A3) Aquatic Invertebrates (813) Drift Deposits (133) Riverine) ❑ Water Marks (BS) (Nonriverine) ❑ Hydrogen Sulfide Odor (Cl) ❑ Drainage Patterns (B10) Sediment Deposits (B2) (Nonriverine) Oxidized Rhizospheres along Living Roots (0) ❑ Dry Season Water Table (C2) ❑ Drift deposits (B3) (Nonriverine) ❑ Presence of Reduced Iron (C4) ❑ Crayfish Burrows (C8) Surface Soil Cracks (B6) ❑ Recent Iron Reduction in Plowed Soils (C6) ❑ Saturation Visible on Aerial Imagery (C9) ❑ Inundation Visible on Aerial Imagery (B7) Thin Muck Surface (0) Shallow Aquitard (D3) [ Water-Stained Leaves (B9) L Other (Explain in Remarks) FAC-neutral Test (D5) Field Observations: Surface Water Present? Yes No Depth (inches): Water Table Present? Yes--1 No Depth (inches): 1 Saturation Present? Yes No i - - Wetland Hydrology Present? Yes No Depth (inches): (includes capillary fringe) _ Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available: Remarks: US Arm Corps of Engineers Arid West - Version 2 Oct 2008 WETLAND DETERMINATION DATA FORM - Arid West Region Project/Site: Deachutes County LWI City/County: Deschutes Sampling Date: 07-May-10 Applicant/owner: DESCHUTES COUNTY State: FR- J Sampling Point: 223 • Investigator(s): Sarah Hartung, Aaron Booy Section, Township, Range: S 31 T 20S R 11 E Landform (hillslope, terrace, etc.): Floodplain Local relief (concave, convex, none convex Slope: 1.0% / O6 0 Subregion (LRR): LRR B Lat.: 43.8000 Long: -121.4545 Datum: NAD 83 Soil Map Unit Name: 29A: Crvaquolls, 0 to 3 percent slopes NWI classification: p$$C Are climatic/ hydrologic conditions on the site typical for this time of year? Yes (.4) No - (If no, explain In Remarks.) Are Vegetation U , Soil I I , or Hydrology significantly disturbed? Are "Normal Circumstances" present? Yes * No > Are Vegetation , Soil L-1 , or Hydrology n naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transacts, important features, etc. Hydrophytic Vegetation Present? Yes No 0 IS the Sampled Area Hydric Soil Present. Yes • No Yes * No within a Wetland? Yes Cl!~ No C Wetland Hydrology Present? Remarks: On-site determination. VEGETATION - Use scientific names of plants. Dominant Species? Absolute Re1.Strat. Indicator ! Dominance Test worksheet: Tree Stratum (Plot size: Cover Cover Status Number of Dominant Species 1. 0 0.0% That are OBL, FACW, or FAC: 3. (A) 2 0 0.0% . Total Number of Dominant 3. 0 0.0% Species Across All Strata: 3 (B) 4. 0 0.0% Percent of dominant Species p =Total Cover That Are OBL, FACW, or FAC: 100.0% (A/B) • Sapling /Shrub Stratum (Plot size: ) 1. Salix geyeriana 2. 3. 4. 5. Herb Stratum (Plot size: 1 Carex aquatilis 9. 10. 11. Woody Vine Stratum (Plot size: ) 1., 50 ICI 100.0% FACW eet' Prevalent Index 0 0.0% k Coverr of: Multiply by: Total . . % 0 L. 0.0% Ospecies 100 x 1 = 100 10 species . W 0 L 0.o% 0 Species FAC z 3 50 = Total Cover ' FACU species 0 x 4 = 0 . . 60 W 60 0% OB L IUPL species 0 x 5 = 0 . column Totals: 150 (A) 200 (B) 40 ❑ ° 40.0k OB L 0 1 0.0% Prevalence Index = B/A = 1.333 0 U 0.0% Hydrophytic Vegetation Indicators: 0 LL q0% EVJ Dominance Test is a 50% 0 0.0% n Prevalence Index is 53.0 1 0 0.0% Morphological Adaptations 11- Irovide supporting l 0 LJ 0.0% - data in Remarks or on a separate sheet) 0 l i - 0.0% problematic Hydrophytic Vegetation 1(1 :plain) 0 r ~ 0.0% o 7 o.o% r 1 Indicators of hydric soil and wetland hydrology must 1.9-0. =T otal Cove be present, unless disturbed or problematic. 0... L..1 0.0% 2. 0 0.0% Hydrophytic % Bare Ground in Herb Stratum: 0 Remarks: Vegetation 0 = Total Cover Present? Yes * No % Cove r of Biotic Crust 0 *Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS. US Army Corps of Engineers Arid West - Version 2 Oct. 2008 Soil Sampling Point: 223 Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) x Depth i Redox Features (inches) Color (mo st) % Color (moist) % Type 1 LoC= Texture Remarks 0-7 10YR 3/2 80% 7.SYR 4/6 20% C M Loam 7-20 10YR 3/1 70% 7.5 YR 4/6 30% C M Clay Loam 1 Type: C=Concentrabon. D-Depletion. RM-Redu D= Depletion. ced Matrix, CS-Covered or Coated Sand Grains sLocation: PL=Pore Lining. M=Matroc Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils? _I Histosol (Al) ❑ Sandy Redox (S5) 1 cm Muck (A9) (LRR C) ❑ Histic Epipedon (A2) Stripped Matrix (S6) ❑ 2 cm Muck (A10) (LRR B) ❑ Black Histic (A3) Hydrogen Sulfide (A4) ❑ Loamy Mucky Mineral (FI) U Reduced Vertic (F18) ❑ Stratified Layers (AS) (LRR C) Loamy Gleyed Matrix (F2) ❑ Red Parent Material (TF2) 1 cm Muck (A9) (LRR D) ❑ Depleted Matrix (F3) ❑ Other (Explain in Remarks) U Redox Dark Surface (F6) Depleted Below Dark Surface (All) ❑ Thick Dark Surface (A12) Depleted Dark Surface (F7) ❑ Redox depressions (F8) Sandy Muck Mineral (Sl) Vernal Pools (F9) 3 Indicators of hydrophytic vegetation and ❑ Sandy Gleyed Matrix (54) wetland hydrology must be present. Restrictive Layer (if present): Type: Depth (inches): Hydric Soil Present? Yes No Remarks: • Hydrology Wetland Hydrology Indicators: Primary Indicators .(minimum. of one required. Check all that apply) Secondary Indicators (2 or more required) ❑ Surface Water (Al) Salt Crust (BlI) ❑ Water Marks (Bl) (Riverine) ❑ High Water Table (A2) ❑ Biotic Crust (B12) Sediment Deposits (B2) (Riverine) ❑ Saturation (A3) Aquatic Invertebrates (B13) ❑ Drift Deposits (133) Riverine) ❑ Water Marks (Bl) (Nonriverine) ❑ Hydrogen Sulfide Odor (Cl) Drainage Patterns (B10) ❑ Sediment Deposits (B2) (Nonriverine) Oxidized Rhizospheres along Living Roots (0) ❑ Dry Season Water Table (C2) J Drift deposits (B3) (Noneriverine) Presence of Reduced Iron (C4) L-~ Crayfish Burrows (C8) Surface Soil Cracks (86) Recent Iron Reduction in Plowed Soils (C6) Saturation Visible on Aerial Imagery (C9) Inundation Visible on Aerial Imagery (B7) ❑ Thin Muck Surface (C7) Shallow Aquitard (D3) ❑ Water-Stained Leaves (B9) i [ Other (Explain in Remarks) C FAC-neutral Test (D5) Field Observations: Surface Water Present? Yes No Depth (inches): Water Table Present? Yes ( ) No ` Depth (inches): ~J Saturation Present? _ Wetland Hydrology Present? includes capillary fringe) Yes No Depth (inches): Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available: Remarks: US Army Corps of Engineers Yes * No Arid West - Version 2 Oct . 2008 WETLAND DETERMINATION DATA FORM - Arid West Region Project/Site: Deschutes County LWI City/County: Sunriver/Deschutes Sampling Date: 06-May-10 Applicant/Owner: DESCHUTES COUNTY State: _R Ll Sampling Point: SP 400 • Investigator(s): dform Wn hretc.): oxbow Section, T (nship, Range: 5 34e 20S R 10E (hillslope, terrace, Local relief concave, convex none): concave Slope: 0.0% / 0.0 ° Subregion (ERR): LRR B Lot.: 43.7908 Long.; -121.5198 Datum: NAD 83 Soil Map Unit Name: 144A: Sunriver sandy loam, 0 to 3 percent slopes NWI classification: Are climatic/hydrologic conditions on the site typical for this time of year? Yes * No (If no, explain in Remarks.) Are Vegetation ❑ , Soil L_J , or Hydrology El significantly disturbed? Are "Normal Circumstances" present? Yes ! No ) Are Vegetation LJ , Soil I I , or Hydrology LJ naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transacts, important features, etc. Hydrophytic Vegetation Present? Yes No Is the Sampled Area O No C_> N dric Soil Present? Yes y within a Wetland? Yes No Wetland Hydrology Present? Yes No Remarks: In oxbow south of Fall River. On-site determination. VEGETATION - Use scientific names of plants. Dominant Species? Absolute Rel.St at. Indicator worksheet: Dominance Test Tree Stratum Plot size: ) ( % Cover Cover Stet Number of Domin Dominant Species ort a 1 P' 10 100.0 _ ° FAC That are OBL, FACW, or FAC: 4 (A) 2. 0.0% ❑ Total Number of Dominant 3. 0 Species Across All Strata: 4 (e) 4. 0 ❑ 0.0°/a 10 = Total Cover Percent of dominant Species 100.0% A/B) Sapling/Shrub Stratum (Plot size: ) That Are OBL, FACW, or FAC: 1, Salix g e 15 ❑ 50.00% FACW Index worksheet: Prevalence landulosa 2, Betula 10 41 40.0% OBL 0 Total oCover of: Multiply by; 3. Q, ❑ 0.0% OsL species 100 x 1 - 100 4. 0 7 0.0% 30 FACW species 15 x 7 = . 5. 0 1 1 0.0% 1 FAC species 10 x 3- 30 25 = Total Cover - FACU species 0 x 4 0. Herb Stratum (Plot size: ) UPL species _0 x 5 0. ~ 1. Carex aquatilis 80 vie1 88.9% OBL I Calumn Totals: 125 (A) 160 (s) z. Carex nebrascensis 10 ❑ 11,.,1% OBL 3. 0 LJ o.0% Prevalence Index = B/A = .1.280 4, o L I o.o% Hydrophytic Vegetation Indicators: 5. 0. 0.0% NI Dominance Test is n 50% 6. 0 , 0.0%. Prevalence Index is 53.0 1 0 ❑ 0.0% Morphological Adaptations 1 1- Irovide supporting g 0 0.0% _ data in Remarks or on a separate sheet) 9. 0 ° ❑ 0.0 Problematic Nydrophytit Vegetation 1 (1 :plain) 10. 0 ❑I 0.0% 11. 0 LJ o.o% Indicators of hydric soil and wetland hydrology must 90 = Total Cover be present, unless disturbed or problematic. Woody Vine Stratum (Plot size: ) 1. 0 ❑ o.0% 2. 0 ❑ o.o°i0 Hydrophytic 0 = Total Cover Vegetation _ Present? Yes No % Bare Ground in Herb Stratum: 0 % Cover of Biotic Crust 0 Remarks: about 10% openwater * ndicator suffix = National status or professional decision ass igned beca use Regional status not defined by FWS. US Army Corps of Engineers Arid West - Version 2 Oct. 2008 Soil Sampling Point: SP 400 Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of Indicators.) Depth Matrix Redox Features (moist) 0/0 Color l (moist) o/o Type I Lot: Color Texture Remarks o 0 14 7.SYR /1 100% . organic . , , 14-20 7.5YR 3/2 100% organic I Type: C=Concentranon ion. . D=Depletion, RM=Reduced Matrix, CS=Covered or Coated Sand Grains ZLocation: PL=Pore Lining. M=Mats Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric SoilsP ❑ Histosol (Al) Sandy Redox (SS) ❑ 1 cm Muck (A9) (LRR C) J Histic Epipedon (A2) ❑ Stripped Matrix (S6) 2 cm Muck (A10) (LRR B) ❑ Black Histic (A3) ❑ Hydrogen Sulfide (A4) Loamy Mucky Mineral (Fl) ❑ Reduced Vertic (F18) Stratified Layers (A5) (LRR C) ❑ Loamy Gleyed Matrix (F2) ❑ Red Parent Material (TF2) 1 cm Muck (A9) (LRR D) ❑ Depleted Matrix (9) ❑ Other (Explain in Remarks) ❑ Depleted Below Dark Surface (Ail) Redox Dark Surface (F6) ❑ Thick Dark Surface (A12) Depleted Dark Surface (F7) Sandy Muck Mineral (Sl) ❑ Redox depressions (F8) Vernal Pools (F9) 3 Indicators of hydrophytic vegetation and Sandy Gleyed Matrix (54) wetland hydrology must be present. Restrictive Layer (if present): Type: Depth (inches): Hydric Soil Present? Yes (.~1 No Remarks: Depths approximate; soil very wet and unconsolidated except 0-14" is very full of roots making extraction of sample difficult Hydrology Wetland Hydrology Indicators: Primary Indicators .(minimum of one required; check all that apply) Secondary Indicators (2 or more required) LJ Surface Water (Al) ❑ Salt Crust (1311) Water Marks (131) (Riverine) High Water Table 02) Biotic Crust (812) Sediment Deposits (B2) (Riverine) Saturation (A3) ❑ Aquatic Invertebrates (B13) ❑ Drift Deposits (B3) Riverine) Water Marks (Bl) (Nonriverine) Hydrogen Sulfide Odor (Cl) Drainage Patterns (1310) ❑ Sediment Deposits (132) (Nonriverine) ❑ Oxidized Rhizospheres along Living Roots (0) ❑ Dry season water Table (C2) f Drift deposits (B3) (Noneriverine) ❑ Presence of Reduced Iron (C4) Crayfish Burrows (CB) ❑ Surface Soil Cracks (B6) ❑ Recent Iron Reduction in Plowed Soils (C6) ❑ Saturation Visible on Aerial Imagery (C9) Inundation Visible on Aerial Imagery (137) Thin Muck Surface (C7) ❑ Shallow Aquitard (D3) ❑ Water-stained Leaves (139) ❑ Other (Explain in Remarks) FAC-neutral Test (D5) Field Observations: Surface Water Present. Yes No - Depth (inches): L- 1 1 Water Table Present? Yes NO 0 Depth (inches): V Saturation Present? Yes J) No 0 Wetland Hydrology Present? Yes No 0 Depth (inches): includes capillary fringe)_ - - - Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available: Remarks: Surface water varies, to 2 inches deep to 1 inch near pit. US Army Corps of Engineers Arid West - Version 2 Oct. 2008 WETLAND DETERMINATION DATA FORM - Arid West Region Project/Site: Deschutes County LWI City/County: Sunriver/Deschutes Sampling Date: 06-May-10 Applicant/Owner: DESCHUTES COUNTY State: OR __-J Sampling Point: SP 402 Investigator(s): John Gordon Section, Township, Range: S 30 T 20 S R 11E Slope: 1.0% / 0.6 ° Landform (hillslope, terrace, etc.): Floodplain Local relief (concave, convex, none): concave Subregion (ERR): LRR B Lat.: 43.8169 Long.: -121.4514 Datum: NAD 83 Soil Map Unit Name: 29A: Cryaou..olls, O to 3 percent slopes NWI classification: PSSC. Are climatic/ hydrologic conditions on the site typical for this time of year? Yes * No (If no, explain in Remarks.) Are Vegetation ❑ , soil , or Hydrology L.._1 significantly disturbed? Are "Normal Circumstances" present? Yes J!) No Are Vegetation i I , Soil , or Hydrology ❑ naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transects, important features, etc. Hydrophytic Vegetation Present? Yes No - Is the Sampled Area Hydric Soil Present? Yes ! No Yes No Wetland Hydrology Present? Yes C4) NO C-) within a Wetland? Remarks: On-site determination. VEGETATION - Use scientific names of plants. Dominant Species? Absolute Rel.Strat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: ) % Cover Cover Status Number of Dominant Species 1. 0 I 0.0% That are OBL, FACW, or FAC: 2 (A) 2 0 ❑ 0.0% . 0 0% Total Number of Dominant 3, 0 . Species Across All Strata: 2 (B) 4. 0 0.0% Percent of dominant Species 0 = Total Cover 1000% (A/B) Sapling/Shrub Stratum (Plot size: ) 1. Salix geyeriana 2. 3. 4. 5. Woody Vine Stratum (Plot size: 1. _ 2. That Are OBL, FACW, or FAC: 30 CW 100.0/o FA Prevalence Index worksheet: 0 r 0.0% Total % Cover of: Multiply by: 0 ❑ 0.0% 08L species 80 x 1 = 80 0 ❑ .O:o°k FACw species 30 x2- 60 . 0.. ❑ 0.0% FAC species 0 x 3 - 30 = Total Cover FACw species x 4 = 0 I 0 0 75 N 93 8% OBL x 5 = UPL species . column Totals: 110 (A) 140 (6) 5 6.3% 013E ( 0 ❑ 0.0% Prevalence Index = B/A = 1.273 0 ❑ 0.00% Hydrophytic Vegetation Indicators: 0 ❑ 0.0% 7 Dominance Test is > 50% 0 ❑ 0.00% Prevalence index is 53.0 i 0 ❑ 0.0% ❑ Morphological Adaptations 1 i.'rovide supporting 0 7 0.0% data in Remarks or on a separate sheet) 0 0.0% ❑ Problematic Hydrophytic Vegetation 1(1 :plain) 0 0.0% 0.0% 1 indicators of hydric soil and wetland hydrology must 80 =T otal Cover be present, unless disturbed or problematic. 0 L_.] 0.0% 0 L._l 0.0% Hydrophytic vegetation - 0 Total Cover Present? Yes ! No % Bare Ground in Herb Stratum: 20 Cover of Biotic Crust 0 Remarks: Bare soil covered with litter. About 5% unvegetated open water in small patches. *Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS. US Army Corps of Engineers Arid West - Version 2 Oct. 2008 Soil Sampling Point: SP 402 Profile Description: (Describe to the depth needed to document the indicator or confine the absence of indicators.) Depth x ox Features R~ (moist) (i 3 ) Color ~ Color (moist) % Type 1 Lot= Texture Remarks SY 0 R 2.5/2 100% Sandy Loam many roots 3-12 7.5YR 3/2 100% Silt 12-20 7.5YR 3/1 95% 7.5YR 3/3 5% C PL Sandy Loam f Type: C=Concentration. D=Depletion. RM=Reduced Matrix, CS=Covered or Coated Sand Grains 2L : PL=Pore Lining. M=Matra - . . Hydric Soil indicators: (Applicable to all LRRs, unless otherwise noted.) . Indicators for Problematic Hydric Soils3 L~ Histosol (Al) Sandy Redox (S5) 1 cm Muck (A9) (LRR C) Histic Epipedon (A2) Stripped Matrix (56) 2 cm Muck (A10) (LRR B) J Black Histic (Aid L Hydrogen Sulfide Loamy Mucky Mineral (Fl) Reduced Vertic (F16) n Stratified Layers (S) (LRR C) Loamy Gleyed Matrix (F2) Red Parent Material (TF2) 71 Depleted Matrix (F3) Other (Explain in Remarks) 1 cm Muck (A9) (LR R p) Redox Dark Surface (F6) 1 Depleted Below Dark Surface (All) Depleted Dario Surface (F7) Thick Dark Surface (A12) ~ Redox depressions (F8) ~.i Sandy Muck Mineral (Sl) Vernal Pools (F9) 3 Indicators of hydrophytic vegetation and Sandy Gleyed Matrix (S4) wetland hydrology must be present. Restrictive Layer (if present): Type: Depth (inches): Hydric Soil Present? Yes No . Remarks: ASSUME HYDRIC SOILS BASED PERSISTENT SATURATION. Hydrology Wetland Hydrology Indicators: Primary Indicators (minimum of one .required. ; check all.khal; apply) Secondary Indicators (2 or more required) Surface Water (Al) Salt Crust (B11) Water Marks (Bl) (Riverine) Vi High Water Table (A2) Biotic Crust (B12) Sediment Deposits (B2) (Riverine) ~i Saturation (A3) Aquatic Invertebrates (813) Drift Deposits (B3) Riverine) r Water Marks (BI) (Nonriverine) Hydrogen Sulfide Odor (Cl) Drainage Patterns (1510) Sediment Deposits (B2) (Nonriverine) ` Oxidized Rhizospheres along Living Roots (0) Dry Season Water Table (C2) Drift deposits (B3) (Noneriverine) i Presence of Reduced Iron (C4) F. I Crayfish Burrows (C8) Surface Soil Cracks (B6) I Recent Iron Reduction in Plowed Soils (C6) Saturation Visible on Aerial Imagery (C9) Inundation Visible on Aerial Imagery (B7) Thin Muck Surface (C7) Shallow Aquitard (D3) Water-Stained Leaves (B9) Other (Explain in Remarks) FAC-neutral Test (D5) Field Observations: Surface Water Present? Yes N0 (i Depth (inches): - _ fl Water Table Present? Yes r" No Depth (inches): 6 ' saturation Present? Yes No _ Wetland Hydrology Present? Yes '•e' No Depth (inches): L 0 I (includes capillary fringi Describe Recorded Data (stream gauge, monitor well aerial photos, previous inspections), if available: Remarks: Surface water with a depth of 6 inches was located several feet south of pit. US Army Carps of Engineers Arid West - Version 2 Oct. 2008 WETLAND DETERMINATION DATA FORM - Arid West Region Project/Site: Deschutes County LWI City/County: Sunriver/Deschutes Sampling pate: 06-May-10 Appllcant/Owner: DESCHUTES COUNTY State: LqR Sampling Point: SP 403 Investigator (s): John Gordon Section, Township, Range: S 30 T 20 S R 11 0.0% / 0.0 ° Landform hilislope, terrace, etc..) Local relief concave, convex, none): Slope: 1 Subregion (LRR): LRR B Lat.: 43.8178 Long.: -121.4564 Datum: NAD 83 Soil Map Unit Name: 144A: Sunriver sandy loam, 0 to 3 percent slopes NWI classification: Are climatic/ hydrologic conditions on the site typical for this time of year? Yes No (If no, explain in Remarks.) Are Vegetation , Soil , or Hydrology significantly disturbed? Are "Normal Circumstances" present? Yes r No', Are Vegetation , Soil , or Hydrology naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transects, important features, etc. Hydrophytic Vegetation Present? Yes No IS the Sampled Area Hydric Soil Present? Yes No within a Wetland? Yes No Wetland Hydrology Present? Yes No • Remarks: No access to wetland to the west. Vegetation community is similar, except it has large patches of Juncus balticus. On-site determination. VEGETATION - Use scientific names of plants. Dominant Species? Absolute Rel.Strat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: ) % Cover Cover Status Number of Dominant Species 1. 0 _ 0.0% That are OBL, FACW, or FAC: 1 (A) 2. 0 i 0.0% Total Number of Dominant 3. p 0.0% Species Across All Strata: 2 (e) 4. 0 0.0% 0 = Total Cover Percent of dominant Species 50.0% A (/8) Sapling/Shrub Stratum (Plot size: ) That Are OBL, FACW, or FAC: • 1. 0 0.0% Prevalence Index worksheet: 2, 0 0.0% Total % Cover of; Multiply by: 3. 0 0.0% oBL species 0 x 1= 0 4. 0 0.0% 35 Facw species x 2 70 5. 0 0.0% FAC species 25 x 3 = 75 0 = Total Cover FACU species 30 x 4 = 120 Herb Stratum (Plot size: ) 0 0 35 38 9% FACW Y x 5 - uPL species 1. Juncus balticus , . 265 (B) 90 (A) Column Totals: 2 Achillea millefolium 20 d 22.2% FACU 3 Poa sp. 15 16.7% FAC Prevalence Index = B/A = 2.944 4, Taraxacum officinale 10 11.1% FACU Hydrophytic Vegetation Indicators: 5. Agropyron repens 10 11.1% FAC Dominance Test is a 500/6 6. 0 0.0% /I Prevalence Index is 53.0 t 7. 0 ° 0.0% Morphological Adaptations 1 rovide supporting 8 0 0.0% data in Remarks or on a separate sheet) 9. 0 010% Problematic Hydrophytic Vegetation 1 (t :plain) 10. 0 0.0% 11. p I 0,0°r° 1 indicators of hydric soil and wetland hydrology must 9p =Total Cover be present, unless disturbed or problematic. Woody Vine Stratum (Plot size: ) 1 0 0.0% 2. 0 0.0% Hydrophytic 0 = Total Cover Vegetation Present? Yes NO % Bare Ground in Herb Stratum: 10 % Cover of Biotic Crust 0 Remarks: • Poa sp. assumed FAC. Pinus contorta adjacent are not included. SP is for meadow/grassland community on this lot and adjacent lot to the west. *Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS. US Army Corps of Engineers Arid West - Version 2 Oct. 2008 Soil Sampling Point: SP 403 Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Depth Matrix Redox Features (Inches) Color (moist) % Color (moist) % Type 1 L oc= Texture Remarks Colo 2/2 100 Sand 4-8 10YR 4/2 100% Sand 8-20 10YR 6/2 Sand 1 Type: C=Concentration. D=Dep - letion. RM-Reduced Matrix, CS=Covered or Coated Sand Grains 'Locati on: PL=Pore Lining. M=Mats Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils:3 ❑ Histosol (Al) Sandy Redox (SS) ❑ 1 cm Muck (A9) (LRR C) ❑ Histic Epipedon (A2) Stripped Matrix (S6) 2 cm Muck (A10) (LRR B) Black Histic (A3) ~ I Hydrogen Sulfide (A4) ❑ Loamy Mucky Mineral (Fl) _ ❑ Reduced Vertic (F18) j Stratified Layers (AS) (LRR C) Loamy Gleyed Matrix (F2) [ Red Parent Material (TF2) 1 cm Muck (A9) (LRR D) ❑ Depleted Matrix (F3) L: Other (Explain in Remarks) ❑ Depleted Below Dark Surface (All) L-1 Redox Dark Surface (F6) ❑ Thick Dark Surface (A12) [ Depleted Dark Surface (F7) ❑ Sandy Muck Mineral (Sl) L....i Redox depressions (F8) Vernal Pools (F9) 3 Indicators of hydrophytic vegetation and [.J Sandy Gleyed Matrix (S4) wetland hydrology must be present. Restrictive Layer (if present): Type: Depth (inches): Hydric Soil Present? Yes No Remarks Hydrology Wetland Hydrology Indicators: PumarY Indicators (minimum of one required; check all that. apply) Secondary Indicators (2 or more required) Surface Water (Al) I I Salt Crust (Bll) ( Water Marks Bl Riverine) High Water Table (A2) ❑ Biotic Crust (B12) J Sediment Deposits (B2) (Riverine) ❑ Saturation (A3) Aquatic Invertebrates (B13) Drift Deposits (B3) Riverine) Water Marks (81) (Nonriverine) ❑ Hydrogen Sulfide Odor (Cl) ❑ Drainage Patterns (B10) Sediment Deposits (B2) (Nonriverine) J Oxidized Rhizospheres along Living Roots (0) ❑ Dry Season Water Table (C2) ❑ Drift deposits (B3) (Nonriverine) ] Presence of Reduced Iron (C4) Crayfish Burrows (C8) ❑ Surface Soil Cracks (B6) I Recent Iron Reduction in Plowed Soils (C6) ❑ Saturation Visible on Aerial Imagery (C9) ❑ Inundation Visible on Aerial Imagery (B7) L Thin Muck Surface (0) ❑ Shallow Aquitard (D3) ❑ Water-Stained Leaves (B9) ❑ Other (Explain in Remarks) L_[ FAC-neutral Test (D5) Field Observations: Surface Water Present? Yes (J No Depth (inches): Water Table Present? Yes C) No Depth (Inches): Saturation Present? - - Yes No Wetland Hydrology Present? Yes (D )No Depth (inches): (includes capilla frin a Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available: Remarks: Soil is very well drained, porous, slightly moist. I US Army Corps of Engineers Arid West -Version 2 Oct. 2008 WETLAND DETERMINATION DATA FORM - Arid West Region Project/Site: Deschutes County LWI City/County: Sunriver/Deschutes Sampling Date: 07-May-10 Applicant/Owner: DESCHUTES COUNTY State: OR Sampling Point: SP 404 Investigator(s): lohn Gordon Section, Township, Range: S 6 T 21 S R 11 E Landform (hillslope, terrace, etc.): Floodplain Local relief (concave, convex, none): Concave Slope: 1.0% / 0.6 ° ( ) 9•: -121.4623 Datum: NAD 83 Subregion LRR : LRR B Lat.: 43.7895 Lon Soil Map Unit Name: 2.9A: Cryaquolls, 0 to.3 percent slopes. NWI classification: pSSC Are climatic/ hydrologic conditions on the site typical for this time of year? Yes No (If no, explain In Remarks.) Are Vegetation ❑ , Soil ❑ , or Hydrology significantly disturbed? Are "Normal Circumstances" present? Yes No Are Vegetation [._J , soil ❑ , or Hydrology ❑ naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transects, important features, etc. Hydrophytic Vegetation Present? Yes No Hydric Soil Present? Yes No is the Sampled Area ' Wetland Hydrology Present? Yes No ( within a Wetland? Yes NO Remarks: On-site determination, VEGETATION - Use scientific names of plants. Dominant Species? Absolute Re1.5trat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: Cover Cover Status Number of Dominant Species 1. 0 ❑ 0.0% That are OBL, FACW, or FAC: 2 (A) 2. 0 0.0% 3 ❑ Total Number of Dominant . 0 0.0% 0-.0% Species Across All Strata: 2 (S) 4. 0 ❑ 0.0% 0 Total Cover = Percent of dominant Species /o 100 (A/8) 0° Sapling/shrub Stratum (Plot size: ) . . That Are 013L, FACW, or FAC: 1. Salix geyeriana 30 ❑ 100.0% FACW Prevalence Index worksheet: 2. 0 0.0% Total % Cover of: Multiply by: 3. 0 0,0% oeL species 70 x 1 - 70 4. 0 ❑ 0,0% FACw species 30 x 2 = 60 5. 0. 0.0% FAC species 0 x 3- 0 30 = Total Cover FACU species 0. x 4 - 0 Herb Stratum (Plot size: ) Carex aquatilis 1 70 U 100.0% OBL species m UPL e . Totals: 100 (A) 130 (s) Column 2. . 0 L 0.0% . 3. 0 . . ❑ 0.0% Prevalence Index = B/A = 1.300 4. 0 1 0.0% Nydrophytic Vegetation Indicators: 5. 0 0.0% IVl Dominance Test is 7 so% 6. 0 ❑ 0.0°/o L Prevalence Index is 53.0 1 7. 0, ❑ 0.0% t [ ] Morphological Adaptations 1 .'rovide supporting g, 0 n 0.% . ~ data in Remarks or on a separate sheet) 9. 0 LJ 0.o0% Problematic Hydrophytlc Vegetation 1 (1 :plain) 10. a o.o% ❑ 11. 0 ❑ o.o% Indicators of hydric soil and wetland hydrology must 70 = Total Cover be present, unless disturbed or problematic. Woody Vine Stratum (Plot size: ► 7 , 0 ❑ o.0% 2. 0 ❑ 0.00/. Hydrophytic 0 = Total Cover Vegetation - Present? Yes No % Bare Ground in Herb Stratum: 30 % Cover of Biotic Crust 0 Remarks: *Indicator suffix = National status or professio nal decision assigned because Regional status not defined by FWS. US Army Corps of Engineers Arid West - Version 2 Oct. 2008 Soil Sampling Point: SP 404 Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) R ox Features (inches) Color (oZst) u I LP 2 % Ty Colo (moist) Texture Remarks 0-4 7.5Y / 95% C 3/3 5% L Sand 4-9 7.5YR 2.5/1 95% 7.5YR 3/3 5% C PL Sand 9-20 7.5YR 2.5/1 100% Sand i Type: C=Concentration. D=Depletion. RM=Reduced Matrix, CS=Covered or Coated Sand Grains zLocation: PL=Pore Lining. M=Matrix Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils) ❑ Histosol (Al) Sandy Redox (S5) ❑ 1 cm Muck (A9) (LRR C) ❑ HistiC Epipedon (A2) Stripped Matrix (S6) 2 cm Muck (A10) (LRR B) ❑ Black Histic (A3) Loamy Mucky Mineral (Fl) ❑ Reduced Vertic (FIB) L Hydrogen Sulfide (A4) ❑ Stratified Layers (A5) (LRR C) ❑ Loamy Gleyed Matrix (F2) ❑ Red Parent Material (TF2) ❑ 1 cm Muck (A9) (LRR D) Depleted Matrix (F3) ❑ Other (Explain in Remarks) ❑ Redox Dark Surface (F6) Depleted Below Dark Surface (All) Depleted Dark Surface (F7) ❑ Thick Dark Surface (A12) ❑ Redox depressions (F8) Sandy Muck Mineral (Sl) Vernal Pools (F9) vegetation and 3 Indicators of hydrophytic ❑ Sandy Gleyed Matrix (S4) i . wetland hydrology ology must be present. must Restrictive Layer (if present): Type: Depth (inches): - Hydric Soil Present? Yes No . Remarks: Hydrology J Wetland Hydrology Indicators: Primary Indicators .(minimum of one required; check all that apply) Secondary Indicators (2 or more required) Surface Water (Al) Salt Crust (Bil) ❑ Water Marks (BI) (Riverine) High Water Table (A2) ❑i Biotic Crust (B12) F -I Sediment Deposits (B2) (Riverine) Saturation (A3) ❑ Aquatic Invertebrates (B13) ❑ Drift Deposits (B3) Riverine) ❑ Water marks (Bi) (Nonriverine) ❑ Hydrogen Sulfide Odor (Cl) L. _I Drainage Patterns (B10) 1 Sediment Deposits (B2) (Nonriverine) _ Oxidized Rhizospheres along Living Roots (0) ❑ Dry Season Water Table (C2) ❑ Drift deposits (B3) (Noneriverine) ❑ Presence of Reduced Iron (C4) Ll Crayfish Burrows (C8) Surface soil Cracks (B6) Recent Iron Reduction in Plowed Soils (C6) ❑ Saturation Visible on Aerial Imagery (C9) ❑ Inundation Visible on Aerial Imagery (B7) ❑ Thin Muck Surface (0) Shallow Aquitard (D3) L J Water-Stained Leaves (B9) ` ❑ Other (Explain in Remarks) FAC-neutral Test (DS) Field Observations: Surface Water Present? Yes No Depth (inches): Water Table Present? Yes No Depth (inches): j 12 J t? Yes No P Saturation Present? Yes No - Wetlan Depth (inches): L 0 resen d Hydrology includes capillary fringe) Describe Recorded Data (stream gauge, moni tor well, aerial photos, previous inspections), if available: Remarks: Water table still rising when pit closed. Surface water is present in nearby parts of oxbow. US Army Corps of Engineers Arid West - Version 2 Oct. 2008 WETLAND DETERMINATION DATA FORM - Arid West Region Project/Site: Deschutes County LWI City/County: Sunriver/Deschutes Sampling Date: 12-May-10 Applicant/Owner: DESCHUTES COUNTY State: OR Sampling Point: SP 405 Investigator(s): John Gordon Section, Township, Range: S 24 T 20S R 10E Landform (hillslope, terrace, etc.): Terrace Local relief (concave, convex, none): flat Slope: 010% / 0.0 ° Subregion (1-1111): LRR B Lat.: 43.8202 Long.: -121.4668 Datum: NAD 83 Soil Map Unit Name: 115A: Shanahan loamy coarse sand, 0 to 3 percent slopes NWI classification: Are climatic/ hydrologic conditions on the site typical for this time of year? Yes (.t) No (if no, explain In Remarks.) Are Vegetation ❑ , Soil ❑ , or Hydrology ❑ significantly disturbed? Are "Normal Circumstances" present? Yes * No Are Vegetation , Soil I I , or Hydrology I I naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transects, important features, etc. Hydrophytic Vegetation Present? Yes L) No ~ is the Sampled Area Hydric Soil Present? Yes No - r within a Wetland? Yes No 'S) Wetland Hydrology Present? Yes NO ` Remarks: Offsite determination. No visual or physical access. Determination based on aerial photos, NWI, soil maps and project experience. VEGETATION - Use scientific names of plants. Dominant Species? Absolute Rel.Strat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: Cover Cover Status Number of Dominant Species 1. 0 .0% 1 That are OBL, FACW, or FAC: 0 (A) 2• 0 1 0 .09/a 3 0 0 0% Total Number of Dominant . . Species Across All Strata: 0 (13) 4. o I 1 0.0% 0 = Total Cover Percent of dominant Species 0 0 0% Sapling/Shrub Stratum (Plot size: ) . (A/B) That Are OBL, FACW, or FAC: 1• 0 ❑ 0.0% Prevalence Index worksheet: 2. 0 0.0% Total % Cover of: Multiply by: 3. 0 0.0% 06L species 0 x 1- 0 4. 0 0.0% FACW species 0 x 2 0 5. o ❑ 0.0% FAC species 0 x 3= 0 0 = Total Cover FACU species U , x 4 - 0 Herb Stratum (Plot size: ) 0 0 . x 5 = Upl species 1 Carexsp. 0 0.0% FACW _ icolumn Totals: 0 (A) 0 (e) 2. 0 0.0% 3. 0 010% Prevalence Index = B/A = 0.000 4 0 ❑ 0.0% Hydrophytic Vegetation Indicators: 5. 0 ❑ 0.0% ❑ Dominance Test is n 50% 6. 0 ❑ 0.0% Prevalence Index is 53.0 1 7. 0 0.0% LJ Morphological Adaptations 11. Irovide supporting 8.. 0 [ ] 0.0% data in Remarks or on a separate sheet) 9. 0 0.0% - ❑ Problematic Hydrophytic Vegetation 1 (1 plain) 10. 0 . 0.0% 11. o ❑ o.o% 1 Indicators of hydric soil and wetland hydrology must 0 . Total Cover be present, unless disturbed or problematic. Woody Vine Stratum (Plot size: ) - 1. 0 10.0% 2. 0 ❑ 0.0% Hydrophytic 0 Cover Total - Vegetation O Present? Yes No % Bare Ground in Herb Stratum: 0 % Cover of Biotic Crust 0 Remarks: Vegetatoin appears similar to vegetation in floodplain and oxbow wetla nds in study area. Predominant emergent group is Carex. Carex sp. assumed FACW. *Indicator suffix = National status or professional decision assigned because Regional status no not defined by FVVS. US Army Corps of Engineers Arid West - Version 2 Oct. 2008 Soil Sampling Point: SP 405 Profile Description. (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Matrix n Redox Features (i ches) Color (moist) % Color (moist) % Type I Loc= Texture Remarks C= Concentration. RM=Reduced Matrix, C5=Covered or Coated Sand Grains 2Locatipn: PL- -Pore Lining. M-Matrix I Type: C-Concentration. D=Depletion. . Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric SoilsP ❑ Histosol (Al) Sandy Redox (SS) L 1 cm Muck (A9) (LRR C) Histic Epipedon (A2) Stripped Matrix (S6) 12 cm Muck (A10) (LRR B) Black Histic (A3) ❑ Loamy Mucky Mineral (Fi) L Reduced Vertic (F18) Hydrogen Sulfide (A4) L Loamy Gleyed Matrix (F2) I I Red Parent Material (TF2) El Stratified Layers (AS) (LRR C) ❑ Depleted Matrix (F3) F' Other (Explain in Remarks) J 1 cm Muck (A9) (LRR D) ❑ Redox Dark Surface (F6) ❑ Depleted Below Dark Surface (All) Depleted Dark Surface (F7) Thick Dark Surface (A12) ❑ Redox depressions (F8) ❑ Sandy Muck Mineral (Si) l Vernal Pools (F9) 3 Indicators of hydrophytic vegetation and Sandy Gleyed Matrix (54) wetland hydrology must be present. Restrictive Layer (if present): Type; Depth (inches): Hydric Soil Present? Yes No ( ) Remarks; Landscape position and vegetation indicate hydric conditions. Hydrology Wetland Hydrology Indicators: Primary_Indicators (minimum of one required; check all that apply) Secondary indicators (2 or more required) ❑ Surface Water (Al) I I Salt Crust (Bll) ❑ Water Marks (Bi) (Riverine) High Water Table (A2) Li Biotic Crust (612) I J Sediment Deposits (B2) (Riverine) ❑ Saturation (A3) ❑ Aquatic Invertebrates (B13) ❑ Drift Deposits (B3) Riverine) Water Marks (Bl) (Nonriverine) L Hydrogen Sulfide Odor (Cl) ❑ Drainage Patterns (B10) ❑ Sediment Deposits (B2) (Nonriverine) [ . I Oxidized Rhizospheres along Living Roots (0) [J Dry Season Water Table (C2) L Drift deposits (B3) (Noneriverine) ❑ Presence of Reduced Iron (C4) Crayfish Burrows (CB) ❑ Surface Soil Cracks (B6) Recent Iron Reduction in Plowed Soils (C6) J Saturation Visible on Aerial Imagery (C9) Inundation Visible on Aerial Imagery (B7) ❑ Thin Muck Surface (C7) Shallow Aquitard (D3) Water-Stained Leaves (Bg) Other (Explain in Remarks) FAC-neutral Test (DS) Field Observations: Surface Water Present? Yes No Depth (inches): Water Table Present? Yes No ` Depth (inches): IL r - Yes No ` Saturation Present? - Yes No 1 • • - Wetland Hydrology Present? Depth (inches): L includes capillary fringe) Describe Recorded Data (stream gauge, moni tor well, aerial photos, previous inspections), if available: Remarks: Vegetation indicates wetland hydrology is present, based on vegetation consistent with oxbow wetlands nearby. US Army Corps of Engineers Arid West - Version 2 Oct. 2008 WETLAND DETERMINATION DATA FORM - Arid West Region Project/Site: DESCHUTES LWI City/County: Sunriver/Deschutes Sampling Date: 07-May-10 Applicant/Owner: DESCHUTES COUNTY State: OR Sampling Point: SP 408 Investigator(s): ALISON SIGLER, ROSEMARY BAKER Section, Township, Range: S 26 T 20S R 10 E Landform (hillslope, terrace, etc.): Flat Local relief (concave, convex, none): concave Slope: 0.0% / 0.0 ° Subregion (LRR): LRR B Lat.: 43.8105 Long.: -121.4888 Datum: NAD 83 Soil Map Unit Name: Not available NWI classification: PEMA Are climatic/ hydrologic conditions on the site typical for this time of year? Yes * No (If no, explain in Remarks.) Are Vegetation , Soil , or Hydrology ❑ significantly disturbed? Are "Normal Circumstances" present? Yes Ci) No Are Vegetation ❑ , Soil ❑ , or Hydrology ❑ naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transects, important features, etc. Hydrophytic Vegetation Present? Yes No - Is the Sampled Area Hydric Soil Present? Yes ! No within aWetland? Yes * No ( Wetland Hydrology Present? Yes ' No Remarks: On-site determination. VEGETATION - Use scientific names of plants. Dominant Species? Absolute Rel.Strat. Indicator ! Dominance Test worksheet: Tree Stratum (Plot size: ) % Cover Cover Status Number of Dominant Species 1. Pinus contorts 20 IVI 100.0% FAC That are OBL, FACW, or FAC: 2. 0 ❑ 0.0% 4 (A) 3. 0 ❑ 0.0% Total Number of Dominant Species Across All Strata: 5 (B) 4. 0 ❑ 0.0% = Total Cover Percent of dominant Species ° 2~. That Are OBL, FACW, or FAC: 80.0 /o (A/B) Sapling/Shrub Stratum (Plot size: ) 1. Spiraea douglasii 2. 3. 4. 5. Woody Vine Stratum (Plot size: 7. 2. % Bare Ground In Herb stratum: 55 Remarks: 5 ❑ 50.0% FACW Prevalence Index worksheet: 0.0% Total % Cover, of: Multiply by: 5 U 50.09/b Ospecies 0 x 1- 0 0 ❑ 0.0% FACw species 15 x 2 - 30 0 ❑ o.o% FAC species 50 x 3 = 150 10 = Total Cover FACU species 5 x 4 = 20 10 n 22 2% FACW UPL species 0 x 5 = 0. . (Column Totals: 70 (A) 200 (B) 30 ❑ 66.7% FAC 5 ❑ 11.1% FACU Prevalence Index = B/A = 2.857 0 Hydrophytic Vegetation Indicators: 0 ❑ 0.0% Dominance Test is n so% 0 ❑ 0.0% Prevalence index Is 53.0 1 ° d p 0 0.0% Morphological A aptations 1 - rovide supporting data In Remarks or on a separate sheet) a ❑ 0.0% Problematic Hydrophytic Vegetation 1 (1 :plain) 0 ❑ 0.0% 0 71 0.0% 1 Indicators of hydric soil and wetland hydrology must 45 = Total Cover be present, unless disturbed or problematic. 0 ❑ 0.0% 0 7 0.0% Hydrophytic Vegetation 0 = Total Cover Present? Yes ' No % Cover of Biotic Crust 0 *Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS. US Army Corps of Engineers Arid West - Version 2 Oct. 2008 D= Depletion. Matrix, CS=Covered or Coated Sand Grains xLOCation: PL=Pore Lining. M=Matrbc Type: C=Concentration. D-Depletion. RM Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric SoilsP ❑ Histosol (Al) ❑ Sandy Redox (S5) 1 Cm Muck (A9) (LRR C) L Histic Epipedon (A2) Stripped Matrix (S6) ❑ 2 cm Muck (A10) (LRR B) Black Histic (A3) Hydrogen Sulfide (A4) ❑ Loamy Mucky Mineral (Fl) L Reduced Vertic (1`18) L Stratified Layers (A5) (LRR C) Loamy Gleyed Matrix (F2) n Red Parent Material (TF2) 1 cm Muck (A9) (LRR D) El Depleted Matrix (9) Other (Explain in Remarks) U Redox Dark Surface (F6) ❑ Depleted Below Dark Surface (All) F7 Depleted Dark Surface (F7) n Thick Dark Surface (A12) ❑ Redox depressions (F8) ❑ Sandy Muck Mineral (Si) Vernal Pools (F9) 3 Indicators of hydrophytic vegetation and Sandy Gleyed Matrix (S4) n wetland hydrology must be present. Restrictive Layer (if present): Type: Depth (inches): - Hydric Soil Present? Yes No 0 Remarks: Hydrology Wetand Hydrology Indicators: Primary Indicators (minimum of one required; check all that apply) Secondary Indicators (2 or more required) Surface Water (Al) ❑ Salt Crust (BlI) F I Water Marks (BI) (Riverine) d❑ High Water Table (A2) I I Biotic Crust (1312) ,.J Sediment Deposits (B2) (Riverine) Saturation (A3) LJ Aquatic Invertebrates (B13) I I Drift Deposits (B3) Riverine) ❑ Water Marks (B1) (Nonriverine) Hydrogen Sulfide Odor (Cl) ❑ Drainage Patterns (B10) ❑ Sediment Deposits (82) (Nonriverine) F. ] Oxidized Rhizospheres along Living Roots (0) L Dry Season Water Table (C2) Drift deposits (B3) (Noneriverine) L- Presence of Reduced Iron (C4) Crayfish Burrows (C8) Surface Soil Cracks (136) ❑ Recent Iron Reduction in Plowed Soils (C6) L Saturation Visible on Aerial Imagery (C9) ❑ Inundation Visible on Aerial Imagery (B7) Thin Muck Surface (C7) LJ Shallow Aquitard (D3) L Water-Stained Leaves (B9) U Other (Explain in Remarks) [vfI FAC-neutral Test (D5) Field Observations: Surface Water Present? Yes No Depth (inches): C. Water Table Present? Yes No Depth (inches): 7~ Y ' N ` Y Present? - Saturation Yes No es O • - es Wetland Hydrology Present? Depth (inches): (includes ca ills _ fringe) Recorded Data (stream gauge, monitor well aerial photos, previous inspections), if available: Remarks: US Army Corps of Engineers Arid West - Version 2 Oct. 2008 WETLAND DETERMINATION DATA FORM - Western Mountains, Valleys, and Coast Region Project/Site: DESCHUTES LWI City/County: SUNRIVER/DESCHUTES Sampling Date: 17-Nov-10 Investigator(s): Applicant/Owner: Sarah Hartun9„ Section, Township, Range: S 19 m T 20 S phR Point SP 600 im R 11 F Landform (hillslope, terrace, etc) Valley bottom Local relief (concave, convex, none) sl!q t concave m.. Slope: 1.0% / OA ° Subregion (LRR): LRR A Lat.: 43,7402 Long.: -121.4654 Datum: NAD83 C I NWI classification: i Map Unit Name:.2~f{, Are climatic/ hydrologic conditions on the site typical for this time of year? Yes (01 No` . (If no, explain in Remarks.) Are Vegetation , Soil , or Hydrology Imo' significantly disturbed? Are "Normal Circumstances" present? Yes No Are Vegetation [ , Soil , or Hydrology L naturally problematic? (If needed, explain any answers In Remarks.) Summary of Findings - Attach site map showing sampling point locations, transects, important features, et 0 = Total Cover Percent of dominant Species 100 0°/ VEGETATION - Use scientific names of plants. Dominant 5pecies7 Absolute Rel.5trat Indicator Dominance Test worksheet: Tree Stratum (Plot size: ) % Cover Cover Status - - Number of Dominant Species 1. 0 ~.0%. That are 08L, FACW, or FAC:.._. (A) 2 0 0.0% , , 3 0 - 0 0% Total Number of Dominant , . Species Across All Strata: 2 (B) 4, 0 0.0% Hydrophytic Vegetation Present? Yes No ` Is the Sampled Area Hydric Soil Present? Yes NO No Yes Wetland Hydrology Present? Yes No ` - within a Wetland? Remarks: Site is normally irrigated, but has not been irrigated in the past 3-4 years.On-site determination. Sapling/Shrub Stratum (Plot size: ) _ Herb. S-tratu-m (Plot size: 9.- 10.- 1L Woody Vine Stratum (Plot size: ) 1. 2. • % Bare Ground in Herb Stratum: 0 Remarks: Poa spp. assumed FAC. 0 I_I 0.0% [711.0,01%.-1 .0% 0 El D. _ 0 = Total Cover 75 75.0% FACW 20 20.0% FAC 5.0% PL 0 0.0% 0 D.0 0 0.0% U _ 0.0% 0 0.0% 100 = Total Cover 0 0.0% 0 0.0% 0 = Total Cover That Are OBL, FACW, or FAC: (p✓B) Prevalence Index worksheet: i Total % Cover-of M Iti lY bY;_.____._.. 06L species 0 x 1 = 0 FACW species x 2 - 150 FAC species 20..... x 3 - i 60 FACU species .....0.,....,.. x 4 = _0....... 5 25 UPL species x 5 Column Totals: 100_m (A) 235..._ (B) i Prevalence Index = B/A = 2.350 Hydrophytic Vegetation Indicators: Dominance Test is 7 So% GGG Prevalence index is 53.01 i Morphological Adaptations' (Provide supporting data In Remarks or on a separate sheet) Wetland Non-Vascular Plants' Problematic Hydrophytic Vegetation' (Explain) i 'Indicators of hydric soil and wetland hydrology must be present, unless disturbed or problematic. Hydrophytic Vegetation Present? Yes Na i ' *Indicator suffix = National status or professional decision assigned because Regional 5t _ _ atus not defined by FWS US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version Soil document the indicator or confirm the absence of Indicators.) Profile Description: Descr a to the to depth needed (Describe Depth Redox Features inches ast .Co..._lnr ms h Color _T Texture (moist) pet Locz moo 3 0 ..0YR 3/2 100% . y Sandy Loam . 3-4 10YR 2/2 100% loam oamy duff 4-8 10YR 4/2 100% Sandy Loam B-20 lOYR 4/3 lo 0% Loamy Sand Sampling Point: SP 600 Remarks dense many composite colors many composite.. colors many composite colors IT-ype: C=Concentration. D=Depletion. RM=Reduced Matrix, CS=Covered or Coated Sand Grains 2Location: PL=Pore Lining. M=Matrix Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils.-3 L Histosol (Al) F Sandy Redox (S5) I 2 cm Muck (A10) Histic Epipedon (A2) ] Stripped Matrix (S6) - I Red Parent Material (TF2) f Black Histic (A3) rLoamy Mucky Mineral (Fl) (except in MLRA 1) N', Other (Explain in Remarks) [._I Hydrogen Sulfide (A4) Loamy Gleyed Matrix (F2) I I Depleted Below Dark Surface (All) [J Depleted Matrix (F3) I 71i Thick Dark Surface (A12) Redox Dark Surface (F6) 3Indicators of hydrophytic vegetation and I [ Sandy Muck Mineral (Sl) L J Depleted Dark Surface (F7) wetland hydrology must be present, ~ ] Sandy Gleyed Matrix (S4) Redox depressions (F8) unless disturbed or problematic. Restrictive Layer (if present): Depth Type. (inches) - Hydric Soil Present? Yes ' No Remarks: Hydric soils assumed based on irrigated conditions. Site receives overflow from irrigation channels. I Hydrology Primary Indicators (minimum of one required; • check all that apply) I Indicators (minimum of two required) , Secondary L Surface Water (Al) Water-Stained Leaves (69) (except MLRA Water-Stained Leaves (B9) (MLRA 1, 2, ] High Water Table (A2) 1, 2, 4A, and 4B) 4A, and 4B) I Saturation (A3) I Salt Crust (811) Drainage Patterns (810) F'^I Water Marks (BI) Aquatic Invertebrates (813) Dry Season Water Table (C2) Sediment Deposits (B2) Hydrogen Sulfide Odor (Cl) [v Saturation Visible on Aerial Imagery (C9) Drift deposits (133) Oxidized Rhizospheres on Living Roots (C3) Geomorphic Position (D2) Algal Mat or Crust (64) [ 1 Presence of Reduced iron (0) Shallow Aquitard (D3) Iron Deposits (85) Recent Iron Reduction in Tilled Soils (C6) ~ FAC-neutral Test (DS) i Surface Soil Cracks (B6) Stunted or Stressed Plants (Dl) (LRR A) Raised Ant Mounds (D6) (LRR A) i Inundation Visible on Aerial Imagery (67) V1 Other (Explain in Remarks) Frost Heave Hummocks (D7) Sparsely Vegetated Concave Surface (BS) Field Observations: Surface Water Present? Yes No Depth (inches): Water Table Present? Yes NO Depth (inches): Saturation Present? Wetland Hydrology Present? Yes No ` (includes capillary fringe) Yes - No Depth ( gauge, p coons), if available: Describe Recorded Data stream monitor well, aerial (inches): hotos, previous inspe Remarks: Saturation present in early part of growing season. Very moist at 0.5", sand layer moist 8-13" but no saturation, lots of organic decaying. - - - - - • US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version 0 WETLAND DETERMINATION DATA FORM - Western Mountains, Valleys, and Coast Region Project/Site: DESCHUTES LWI City/County: SUNRNER/DESCHUTES Sampling Date: ._I7 Nov-10... .H . Sampling E Applicant/ Investigator(s): wner.Sarah, .ar DE HUTE tung COUNTY Section, Township, Ran State: OR 4 T 21 5 R R 10 Point SP 601 Landform (hlllslope, terrace, etc.): Flat Local relief (concave, convex, none): none Slope: 1.0 /o Subregion (LRR): LRR A Lat.: 43.7413 Long.: -121.4689 Datum: NAD83 Soil Map Unit Name:_1.1.5A.Shi1naban j_QaMY 4di ~~n.S ,_1QW S?.tQ. .R CDS,.S1.417CS..... NWI classification: Are climatic/ hydrologic conditions on the site typical for this time of year? Yes ' No l.- (If no, explain in Remarks.) Are Vegetation n , Soil n , or Hydrology n significantly disturbed? Are "Normal Circumstances" present? Yes No Are Vegetation I I , Soil I I , or Hydrology naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transects, important features, et Hydrophytic Vegetation Present? Yes - No * Is the Sampled Area Hydric Soil Present? Yes - NO Wetland Hydrology Present? Yes - No within a Wetland? Yes No Remarks: On-site determination. VEGETATION - Use scientific names of plants. Dominant Absolute ReI..Strat. Indicator Dominance Test worksheet: Tree Stratum (Plot size: ) % Cover er Co Status v _ . Number of Dominant Species 2 1 - ~ That are OBL, FACW, or FACT (A) 2 tl I 0.0 /o . 3 % Tots Number o Dominant , Species Across All Strata: 4 (B) 4. 0 n o Percent of dominant Species 0- - Total Cover 00% or FAC: (A/B) ~ That Are 013L FACW size: ) Sapling/Shrub Stratum (Plot 0 0. n 0°~ . , , Prevalence Index worksheet: h 2 0 0°r° n D. Total % Cover of , _Multiply_bY ° 3. 0 0.0% _ 0131. sp e 0 x1- 0 4 0 n 0.0% 0 FACW species 20 x 2 = .0% 120........_. FAC species 40.., x 3 = 0 =Total Cover FACU species x Herb Stratum (Plot size: ) 20 00 1 ]uncus balticus 10 n 10.0% FACW = x 5 UPL species n 100 340 e column Totals. A ( ) ( ) 2 Carex sP 10 10.0% FACW 3 Tnfolium re ens- 20 /I-20,0% FAC Prevalence Index = B/A = 3.400 4 Taraxacum officinale ZQ vO', 200% FACU Hydrophytic Vegetation Indicators: 5. Thinopyrum intermedium 20... ~Vl- 20.0% UPL Dominance Test is 7 50% 6 Poa sPr. 20 170120.0% FAC Prevalence Index is 53.01 7 0 0.0% J Morphological Adaptations I (Provide supporting 8 0 L 0.0°k data In Remarks or on a separate sheet) 9 D.... n 0.0% L-l Wetland Non-Vascular Plantsl 10. _ ._...0_ _ 0.0% Problematic Hydrophytic Vegetationl (Explain) 11. 0 n 0.0% 100 =Total Cover lIndicators of hydric soil and wetland hydrology must - - be present, unless disturbed or problematic. Woody Vine Stratum (Plot size: ) 1. --.9__. 0.0_%_.. 2. 0 0.0% Hydrophytic 0 - Total Cover Vegetation Present? Yes No % Bare Ground in Herb Stratum: 0 Remarks: Carex sp. assumed FACW and Poa sp. assumed FAC. *Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version Soil Sampling Point: SP 601 Profile Descri ption: (Describe to the depth needed to document the Indicator or confirm the absence of Indicators.) t x a ox F~ atures C3 s Color (moist) s Color or (moist) Type 1 LoC' Texture Remarks - O OYR3 - 100% Bandy Loam _ _ dense roots 0-8.5 lOYR 3 /2 100% Sandy Loam 8.5-20 10YR 5/4 50% Sand mixed colors 10YR 4/4 50% Sand no redox Type: C=Concentration. D=Depletion. RM=Reduced Matrix, CS=Covered or Coated Sand Grains sLocab t on: PL=Pore Lining. M=Matrix Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils:3 Histosol (Al) Sandy Redox (5S) 2 cm Muck (A10) Histic Epipedon (A2) Stripped Matrix (S6) I Red Parent Material (TF2) Black Histic (A3) Loamy Mucky Mineral (Fl) (except in MLRA 1) Other (Explain in Remarks) Hydrogen Sulfide (A4) L Loamy Gleyed Matrix (F2) _I Depleted Below Dark Surface (All) Depleted Matrix (9) Thick Dark Surface (A12) Redox Dark Surface (F6) 3Indicators of hydrophytic vegetation and Sandy Muck Mineral (Sl) Depleted Dark Surface (F7) wetland hydrology must be present, Sandy Gleyed Matrix (S4) Redox depressions (FS) unless disturbed or problematic. Restrictive Layer (if present): Type: Depth inches),__ Hydric Soil Present? Yes No Remarks: Hydrology _ Wetland Hydrology Indicators: Primary Indicators (minimum of one required; check all that apply) Secondary Indicators (minimum of two required) . I Surface Water (Al) 1 Water-Stained Leaves (B9) (except MLRA 2, Water-Stained Leaves (B9) (MLRA 1, I J , I High Water Table (A2) 1, 2, 4A, and 4B) 4A, and 4B) Saturation (A3) Salt Crust (Bll) - Drainage Patterns (810) E Water Marks (BS) Aquatic Invertebrates (B13) J Dry Season Water Table (C2) Sediment Deposits (82) 7 Hydrogen Sulfide Odor (Cl) L_ Saturation Visible on Aerial Imagery (Cg) J Drift deposits (B3) Oxidized Rhizospheres on Living Roots (0) Geomorphic Position (132) L Algal Mat or Crust (B4) Presence of Reduced Iron (C4) Shallow Aquitard (D3) Iron Deposits (B5) I Recent Iron Reduction in Tilled Soils (C6) FAC-neutral Test (DS) Surface Soil Cracks (B6) I Stunted or Stressed Plants (Dl) (LRR A) Raised Ant Mounds (D6) (LRR A) 7 Inundation Visible on Aerial Imagery (87) Other (Explain in Remarks) Frost Heave Hummocks (D7) Sparsely Vegetated Concave Surface (BB) Field Observations: Surface Water Present? Yes No Depth (inches): Water Table Present? Yes No `P Depth (inches). _ Saturation Present? - - Wetland Hydrology Present? Yes No (includes capillary fringe) Yes No •P Depth (inches): - Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available: Remarks: somewhat moist US Army Corps of Engineers • • Western Mountains, Valleys, and Coast Region Interim version 0 WETLAND DETERMINATION DATA FORM - Western Mountains, Valleys, and Coast Region Project/Site: DESCHUTES LWI _ _ City/County: SUNRIVER/DESCHUTES Sampling Date: _17 Nov-10 • PP _ _ P g Point: SP 602 10 E Investigator(s) rSarah Hartuny COUNTY Section, Township, Range: State: OR T Z1 S Sampling Landform (hillslopa, terrace etc.): Flat Local relief (concave convex, none): none slope: 1.0% / 0.0 ° Subregion (LRR): LRR A Lat 43.7453 Long.: -121.4694 Datum NAD83 Soil Map Unit Name: ...L44A_SMiY0ras RI,Qto 3 percent slopes NWI classification: P~Mf~.......W_ Are climatic/ hydrologic conditions on the site typical for this time of year? Yes No 0 (If no, explain in Remarks.) Are Vegetation I I , Soil I I , or Hydrology F significantly disturbed? Are "Normal Circumstances" present? Yes No Are Vegetation ❑ , soil ❑ , or Hydrology I.... I naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transects, important features, et Hydrophytic Vegetation Present? Yes No J) j Is the Sampled Area Hydric Soil Present? Yes No 0 - within aWetland? Yes (•P> No ( Wetland Hydrology Present? Yes No 0 Remarks: On-site determination. VEGETATION - Use scientific names of plants. Dominant Snecles? Tree Stratum (Plot size: z, 3. 4. . Absolute Rel.Strat. Indicator Dominance Test worksheet: Number of Dominant Species That are OBL, FACW, or FAC: Total Number of Dominant Species Across All Strata: Percent of dominant Species That Are OBL, FACW, or FAC: 2 (A) ~ /Shrub Stratum (Plot size Sa hn_ 2. 3 4. 5 % Cover Cover Status 0 ❑ 0.0% 0 0.0% 0 u ❑ 0.0 /o 0 JJ o.o%- 0 = Total Cover 0 _ 0.0% 0 LJ o.0% ❑ o.o°,° 0.0% 0 0.0% 0 = Total Cover 60 . W 60.0% FACW . 30 JJ FA 30.0% C 5 J 5.0% FAC 5 5.0% FACU 0 CJ 0.0% 0% 0% 0 ❑ 0.0% 0 0.0% - f T -9.0% o 1-1- 10% 100 = Total Cover 0 ❑ 0.0% 0 = Total Cover 0.0% (A/6) Prevalence Index worksheet: I_ / Cover of:_.-Multply-by_ Tots ° 08L species 0 x 1 - 0 FACW species 60.... x z = 120 FAC species 35. x 3 = 105 FACU species 5.._......... x 4 = 20 UPL species x 5 - column Totals: (A) 245 (e) Prevalence Index = B/A = 2.450 Hydrophytic Vegetation Indicators: Dominance Test is n 50% JJ Prevalence Index is 53.01 J Morphological Adaptations 1 (Provide supporting data in Remarks or on a separate sheet) L Wetland Non-Vascular Plantsl ❑ Problematic Hydrophytic Vegetatlonl (Explain) 'Indicators of hydric soil and wetland hydrology must be present, unless disturbed or problematic. Hydrophytic Vegetation Yes ' No Present? Remarks: *Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version Soil Sampling Point: - Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Depth ~ Matrix _Re ox Features (inch eS~. Color moist ~o 0 Color (_-moist) k Type 1 ~z exture Remarks 3 .w. . YR 5 u 100k T Loam _ . 40% organic k 3-6 3 3/2 lOYR lOD% Loamy Sand 6-18 10YR 4/3 80% Sand 20% silts 10YR 5/6 20% Sand no streaking SP 602 _ yp P I' =Matrix 1T e: C=Concentration. D-De letion . RM=Reduced Matrix, C5- Covered or Coated Sand Grains _Location. PL Pore Lining. MW 3 Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for ProblemAIC Hydric Soils. i Histosol (Al) Sandy Redox (S5) 2 cm Muck (A10) I Histic Epipedon (A2) Stripped Matrix (S6) I Red Parent Material (TF2) j 17 Black Histic (A3) a Loamy Mucky Mineral (Fl) (except in MLRA 1) j~ Other (Explain in Remarks) 71 Hydrogen Sulfide (A4) Loamy Gleyed Matrix (F2) U Depleted Below Dark Surface (All) _ Depleted Matrix (F3) Thick Dark Surface (A12) Redox Dark Surface (F6) 3Indicators of hydrophytic vegetation and Sandy Muck Mineral (Sl) Depleted Dark Surface (F7) wetland hydrology must be present, d Sandy Gleyed Matrix (S4) Redox depressions F8 unless disturbed or problematic. Restrictive Layer (if present): Type: Depth (inches): Hydric Soil Present? Yes No I Remarks: Hydric soils assumed based on hydrology indicators. j I Hydrology _ Hydrology Indicators: Wetland g s ( heck all that aPPIY) Primary ~ Indicators mimmum of one required; C _ Secondary Indicators „ (minimum of two required T..m._ Surface Water (Al) L 1 Water-Stained Leaves B9) (except MLRA ( Water-Stained Leaves (89) (ML (MLRA 1, 2, High Water Table (A2) 1, 2, 4A, and 4B) 4A, and 4B) j_ Saturation (A3) Salt Crust (Bll) Drainage Patterns (B10) Water Marks (Bl) L Aquatic Invertebrate (813) Dry Season Water Table (C2) I Sediment Deposits (B2) ❑ Hydrogen Sulfide Odor (Cl) Saturation Visible on Aerial Imagery (C9) a Drift deposits (83) Oxidized Rhizospheres on Living Roots (0) Geomorphic Position (D2) L Algal mat or crust (84) Presence of Reduced Iron (C4) Shallow Aquitard (D3) ] Iron Deposits (B5) Recent Iron Reduction in Tilled Soils (C6) FAC-neutral Test (DS) Surface Soil Cracks (B6) r'. Stunted or Stressed Plants (Dl) (LRR A) Raised Ant Mounds (136) (LRR A) Inundation Visible on Aerial Imagery (B7) Iii Other (Explain in Remarks) Frost Heave Hummocks (D7) j Sparsely Vegetated Concave Surface (BB) Ii E Field Observations: Surface Water Present? Yes No i~ Depth (inches): J Water Table Present? Yes No Depth (inches): I _ Saturation Present? Wetland Hydrology Present? Yes '•a' No (includes capillary fringe) Yes NO i Describe Recorded Data (stream gauge, monitor Depth (inches): well, aerial photos, previous inspections), if available: Remarks: Landowner information about irrigating the site in the spring. C, • US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version 0 WETLAND DETERMINATION DATA FORM - Western Mountains, Valleys, and Coast Region Project/Site: DESCHUTES LWI City/County: SUNRIVER/DESCHUTES Sampling Date:-03Deo-10 Applicant/Owner: artunS COUNTY = _ ^ State: OR . Sampling Point 5P 603 SardhH q Section, Township, Range: S T R Investigator(s): Landform (hillslope, terrace, etc.): Swale Local relief (concave, convex, none): concave Slope: 010% / 0.0 ° Subregion (LRR): LRR A Lat.: Long.: Datum: NAD83 Soil Map Unit Name: NWI classification: Are climatic/ hydrologic conditions on the site typical for this time of ear? Yes No If no, explain in Remarks.) Are Vegetation ❑ , Soil ❑ , or Hydrology L.] significantly disturbed? Are "Normal Circumstances" present? Yes No Are Vegetation Soil ❑i , or Hydrology ❑ naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transects, important features, et Hydrophytic Vegetation Present? Yes No 1. 1 Hydric Soil Present? Yes No - Is the Sampled Area Yes NO Wetland Hydrology Present? Yes No within a Wetland? Remarks: On-site determination. VEGETATION - Use scientific names of plants. Dominant Species? Absolute Rel.Strat. Indicator Dominance Test worksheet: ot size Tree Stratum C ver Cover Status I P o Number of Dominant Species 1 ° .0/° _ That are OBL, FACW, or FAC: o ❑ 0 0 / ° Total Number o Dominant . o _ Species Across All Strata: 4. 0 0.0% 0 = Total Cover Percent of dominant Species Sapling/Shrub Stratum (Plot size: That Are OBL, FACW, or FAC: 1 Salix geyeriana tl.... 0.0% FACW Prevalence index worksheet: 2• 0_... 0.0°/. tI . Total _%Cover of: - MUIy_~ 3. .._0.. f. . 0.0% OBL species 0 x 1 - 0 4. 0 070% FACW species 0 x 2- 0 5 0 ❑ 0.0% FAC species 0..._. x 3- 0 = Cover Total 0 0 FACU species x 4 = ) Herb Stratum (Plot size: Carexa uatilis 70 70.0% FACW UPL species - _ x 5 - 2, Veronica americana 10 ❑ 10.0% OBL Column Totals: (A) (a) 3 Poa sp. 10 I_I 1o.o% FAc Prevalence Index = B/A = 0.000 A rostis sp. -1.0. 711 10.0% FAC Hydrophytic Vegetation Indicators: 5. 0.. 1..]. _.0:0% ❑ Dominance Test is 7 50% 6. - 0 . ❑ .0.00k ❑ Prevalence Index Is 53.01 7, . 0 ❑ 0.0/ ~ ~ Morphological Adaptations 1(Provide supporting o....,..,. L] ° 0.0 /o data In Remarks or on a separate sheet) 9. 0-..... F 070%.. Wetland Non-Vascular Plantsl 10. 0.... - ❑ r 0.0% - Problematic Hydrophytic Vegetatipnl (Explain) 11- 0 0.0% 'indicators of hydric soil and wetland hydrology must 100 = T otal Cover be present, unless disturbed or problematic. 0 0.0% 0 = Total Cover 1....... (g) (A/B) Hydrophytlc Vegetation Present? Yes * No *Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version Soil Sampling Point: SP 603 _ r or confirm the absence of indicators.) to the depth needed to document the Profile Description: (Describe tI Depth . . -1 Fetures Inches). Color (moist) o _ ~0 COlpr (moist) % rType l ,L.oc2 Texture Remarks _ 0-6 IOYR 2/2 100% - . - - _ _ - ...M. _ • peat 3/1 6-18 10YR 90% 3/3 10% C M 10YR Clay Loam I - - - - - 1 Llning. M=Matrix Dep letion. RM=Reduced Matrix, CS=Covered or d Sand Grains zLocation PL=Pore Type: C=Concentration. D ( N dric Soil Indicators Applicable to all LRRs, unless otherwise noted.) for Problematic Hydric Soils 3 Indicators Histosol (Al) r Sandy Redox (S5) 2 cm Muck (A1D) i Histic Epipedon (A2) Stripped Matrix (S6) I Red Parent Material (TF2) Black Histic (A3) Loamy Mucky Mineral (Fl) (except in MLRA 1) 1 11 Other (Explain in Remarks) Hydrogen Sulfide (A4) Loamy Gleyed Matrix (F2) ~I Depleted Below Dark Surface (All) Depleted Matrix (F3) ~I Thick Dark Surface (A12) Redox Dark Surface (F6) 3Indicators of hydrophytic vegetation and J Sandy Muck Mineral (Sl) Depleted Dark Surface (F7) wetland hydrology must be present, Sandy Gleyed Matrix (S4) Redox depressions (F8) unless disturbed or problematic. Restrictive Layer (if present): Type Depth (inches) Nydric Soil Present? Yes No Remarks: Hydrology Wetland Hydrology Indicators: Primarv Indicators (minimum of one required; check all that apply) Se of two I Secondary _L_ Surface water ( (Al) ) Water-Stained Leaves (B9) (except MLRA Stained Leaves (B9) (MLRA 1, 2, High Water Table (A2) 1, 2, 4A, and 4B) 4A, and 4B) I~ Saturation (A3) J Salt Crust (B11) Drainage Patterns (1310) Water Marks (Bl) Aquatic invertebrates (513) Dry Season Water Table (C2) Sediment Deposits (132) Hydrogen Sulfide Odor (Cl) Saturation Visible on Aerial Imagery (Cg) Drift deposits (B3) Oxidized Rhizospheres on Living Roots (0) Geomorphic Position (D2) Cl Algal Mat or Crust (84) Presence of Reduced Iron (C4) Shallow Aquitard (D3) Iron Deposits (BS) Recent Iron Reduction in Tilled Soils (C6) _ FAC-neutral Test (135) Surface Soil Cracks (B6) Stunted or Stressed Plants (Dl) (LRR A) Raised Ant Mounds (D6) (LRR A) L Inundation Visible on Aerial Imagery (B7) 141 Other (Explain in Remarks) Frost Heave Hummocks (D7) Sparsely Vegetated Concave Surface (B8) I I Field Observations: Surface Water Present? Yes No Depth (inches): i Water Table Present? Yes No I Depth (inches): C 16 Wetland Hydrology Present? Saturation Present? (includes capillary fringe) Yes No Depth (inches): 12 - Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available: Yes No I . Remarks: Saturation along ped surfaces. Best professional judgement- expect saturation iin upper part during early growing season. US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version 0 WETLAND DETERMINATION DATA FORM - Western Mountains, Valleys, and Coast Region Project/Site: DESCHUTES LWI _ City/County: SUNRIVER/DESCHUTES Sampling Date. ..17 Nov-10 Applicant/Owner: DESCHUTESgCOUNTY - 40 _ State: OR Sampling Point SP 604 Investigator(s): Sarah Hartun Section,. _ _ Township, Range. S 2 T 21S R 10 E Landform (hlllslope, terrace, etc.): Valley bottom Local relief (concave, convex, none): concave Slope: 2.0% / 0.0 ° Subregion (LRR): LRR A Lat.: 43.7892 Long.: -121.5030 Datum: NAD83 Soil Map Unit Name: 4~_(Q NWI classification: pA Are climatic/hydrologic conditions on the site typical for this time of year? Yes * No (If no, explain In Remarks.) Are Vegetation , Soil ❑ , or Hydrology J significantly disturbed? Are "Normal Circumstances" present? Yes No Are Vegetation Soil or Hydrology ❑ naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transects, important features, et Hydrophytic Vegetation Present? Yes NO Is Soil Present? Yes No 0 the Sampled Area Wetland Hydrology Present? Yes ! No within a Wetland? Yes No Remarks: On-site determination. Sapling/Shrub Stratum (Plot size ) 1 _ 4 5. Dominant Species? Absolute Rel.Strat. Indicator Dominance Test worksheet: % Cover Cover Status 0 U 0 0% Number of Dominant Species . That are OBL, FACW, or FAC: 1 (A) 0 i._ 0 .0 % 0 _ _ 0 0% Total Number of Dominant . Species Across All Strata: 0 0.0% 0 = Total Cover Percent of dominant Species % (A/B) That Are OBL, FACW, or FAC: 0.0 0 ❑ 0.0% Prevalence Index worksheet: 0 T_otal_ Coyer of: _ Multiply by_ 0.0% OBL species 80 x 1 80 ❑ 0.0% FACw species ..10.... x 2 = ......20 0.. 0.0% FAC species -.40. . x 3 = 30 0 = Total Cover 0 0 FACU species x 4 = 80 n UPL species 0_W...... x S -0.._..,. 10 80.0% OBL n 10.0% FACW Column Totals: m,,,•, 100 (A) 130 (B) 10 0° FAC Prevalence Index = B/A = 1.300 0 0.0°k - Hydrophytic Vegetation Indicators D 0.0% j Dominance Test is > 50% 0 117, 0.00/0 I I Prevalence index is 53.0t 0 - [J J Morphological Adaptations I (Provide supporting 0 0.0% data in Remarks or on a separate sheet) L 0.0% r [ Wetland Non-Vascular Plantst 0 J Problematic Hydrophytic Vegetationl (Explain) 0 0.0% 100 - Total Cover 11ndicators soil and wetiand hydrology must n r be Present less disturbed or problem tic. *Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version Soil Sampling Point: - SP 604 Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) (inches oist) x - "A° Color (moist) Redox ~satureT Color ( Ype1 l.oc' _ Texture... Remarks 0-6 10YR 2/2 100% peat s .6-20 10YR 3/1 60% ..._..10YRT 4/1 30% D M Silty , m... , ' Ity Clay Loam I IType: C=Concentration. D=Depletion. RM=Reduced Matrix, CS=Covered or Coated Sand Grains zLocation. PL=Pore Lining. M=Matrix f Hydric Soil Indicators: (Applicable to all LRRS, unless otherwise noted.) Indicators for Problematic Hydric Soils:3 Histosol S 2 Muck (A10) I p p ( ) Histc E ipedon A2 (S6) Striped Matrix Red d Parent Material (TF2) Ej Black Histic (A3) Loamy Mucky Mineral (Fl) (except in MLRA 1) [ Other (Explain in Remarks) j Hydrogen Sulfide (A4) _ Loamy Gleyed Matrix (F2) - Depleted Below Dark Surface (All) Depleted Matrix (F3) _ Thick Dark Surface (A12) Redox Dark Surface (F6) 3Indicators of hydrophytic vegetation and I Sandy Muck Mineral (SS) Depleted Dark Surface (F7) wetland hydrology must be present, Sandy Gleyed Matrix (54) Redox depressions (F8) unless disturbed or problematic. Restrictive Layer (if present): Type i Depth (Inches): Hydric 5011 Present? Yes ' Na ` . . Remarks: i i i Hydrology Wetiand Hydrology indicators: - - 4 I that apply) Pr of one required; check al Indicators (minimum Primary Secondary Indicators (minimum of two required) T. ^ _ _1 Surface Water (Al) 7 Water-Stained Leaves (B9) (except MLRA Water-Stained Leaves (B9) (MLRA 1, 2, */J High Water Table (A2) 1, 2, 4A, and 48) 4A, and 4B) 3~I Saturation (A3) Salt Crust (1311) Drainage Patterns (B10) L Water Marks (BI) Aquatic Invertebrates (B13) 1 Dry Season Water Table (C2) Sediment Deposits (B2) Hydrogen Sulfide Odor (Cl) Saturation Visible on Aerial Imagery (C9) Drift deposits (B3) Oxidized Rhizospheres on Living Roots (0) L Geomorphic Position (D2) Algal Mat or Crust (84) Presence of Reduced iron (0) i Shallow Aquitard (133) -i Iron Deposits (B5) Recent Iron Reduction in Tilled Soils (C6) [ FAC-neutral Test (D5) Surface Soil Cracks (B6) Stunted or Stressed Plants (Di) (LRR A) Raised Ant Mounds (D6) (LRR A) Inundation Visible on Aerial Imagery (87) Other (Explain in Remarks) Frost Heave Hummocks (D7) r Sparsely Vegetated Concave Surface (B8) Field Observations: Surface Water Present? Yes No Depth (inches): L Water Table Present? Yes ` No Depth (inches C 11 Present? f Wetland Hydrology Present? Yes P' No Saturation Yes I (Includes capillary fringe) No Depth (inches): 6 Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available: Remarks: • US Army Corps of Engineers Western Mountains, valleys, and Coast Region Interim version 0 WETLAND DETERMINATION DATA FORM - Western Mountains, Valleys, and Coast Region Project/Site: DESCNUTES LWI City/County: SUNRIVER/DESCNUTES Sampling Date: 17-Nov-10 APPlicant/Owner DE„ OUNTY State: OR....... m.._. Sampling Point: SP 605 investigator(s): ara... Na rtun C Section, Township, Range: S 2 T 20 S R 10 E tandform (hillslope, terrace, etc.): Swale, valley bottom Local relief (concave, convex, none): concave Slope: 210/o / 0..0 Subregion (LRR): LRR A tat.: 43.7864 tong.: -121.5067 Datum: NAD83 Soil Map Unit Name: 14L.11[]f1Y.1<C..Sdfl4(.Y..11adO]. 4.4..~ti[SI:II~ SISaP~S .......W........ . _w.... _ m.. NWI classlflcation:_pIMPl Are climatic/ hydrologic conditions on the site typical for this time of year? Yes * No _ (If no, explain in Remarks.) Are Vegetation I I , Soil I I , or Hydrology significantly disturbed? Are "Normal Circumstances" present? Yes No (D Are Vegetation LL , Soil L , or Hydrology naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transects, important features, et Hydrophytic Vegetation Present? Yes No H dric Soil Present? y Yes NO - Is the Sampled Area Yes No C-) Wetland Hydrology Present? Yes ! No within a Wetland? Remarks- On-site determination. VEGETATION - Use scientific names of plants. Dominant Absolute ReLStrat. Indicator Dominance Test worksheet: p (Plot size: ) Stratum Tree % Cover Cover Status 9 Number of Dominant Species P ontorta _ 1. . 30.. FAC 1.00.9. That are OBL, FACW, or FAC: (A) 0 0.0% CL 3 O.. O_ D% Total Number of Dominant . . Species Across All Strata: _3...._... (B) 4. o 17 0.0°r° 30 - Total Cover Percent of dominant Species 0 0% (A/8) rub Stratum (Plot size: ) Sapling/Shrub . That Are OBL, FACW, or FAC: 1 9 Salix ?yenana 50 ICI 1000/° A F Prevalence Index worksheet: 0 0.0% Total % Cover of: Mult!p bY... 3 0 0.0% . oeL species 10 x 1 = 10 0.0% FACW species 55 x 2 - 110 LL o.0°/ 115 x 3 345.. . FAC species 50 - - Total Cover 0 0 p _ FACU 5 eCl e5 X 4 Herb Stratum (Plot size: ) 0 0 s e 1 Geum maCrophyllum 5 ~ S.00% FAC1N _ mencana 2 e _ 10 LL 10.0% 08L 465 (B) Column TOtals: (A) A rost s s 75 75.0% FAC Prevalence Index - B/A - 0.000 i 4, eromus sp 10 S0'0%-- FAC Hydrophytic Vegetation Indicators: 5, 0.__ U . 0.0% - _ . ❑ Dominance Test Is a 50% 6 0. ❑ 0.0% LL Prevalence Index is 53.01 7, D LL o.o% LL Morphological Adaptations 1 (Provide supporting 8 0 0.0% . data in Remarks or on a separate sheet) 9. 0.0 k ° Wetland Non-Vascular Plantsl 0 LL D.0°r° Problematic Hydrophytic Vegetatlonl (Explain) 17 1 100 =Total Cover 1ndicators of hydric soil and wetland hydrology must be present, unless disturbed or problematic. Woody Vine Stratum (Plot size: 1 0 LL o.o% 2. 0 0.0% Hydrophytic 0 = Total Cover Vegetation Present? Yes No C Bare Ground in Herb Stratum: 0 Remarks: Agrostis sp. and Bromus sp, assumed FAC. _._....1 *Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS US Army Corps of Engineers Western Mountains, ValleyS, and Coast Region Interim version Sampling Point: SP 605 Remarks mixed matrix - ins ZLocation, PL-Pore Umng. M=Matrix IType: C=Concentration. D-Depletion. RM=Reduced Matrix, CS=Covered or Coated Sand Gra Hydric Soll Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric Soils:3 Histosol (AS) Sandy Redox (55) 2 cm Muck (A10) _ Histic Epipedon (A2) Stripped Matrix (56) 1 I Red Parent Material (TF2) i Black Histic (A3) Loamy Mucky Mineral (Fl) (except in MLRA 1) Other (Explain in Remarks) L _ Hydrogen Sulfide (A4) Loamy Gleyed Matrix (F2) [J Depleted Below Dark Surface (All) Depleted Matrix (9) Thick Dark Surface (A12) Redox Dark Surface _ (F6) 3Indicators of hydrophytic vegetation and Sandy Muck Mineral (S1) _ Depleted Dark Surface (F7) wetland hydrology must be present, Sandy Gleyed Matrix (S4) Redox depressions (F8) unless disturbed or problematic. Restrictive Layer (If present): Type _ Depth (inches):___ Hydric Soil Present? Yes • No Remarks: Hydric soils assumed based on hydrology i ndicators. Hydrology Wetland Hydrology Indicators: - Primary Indicators _ (minimum of one required; check all that apply) Secondary Indicators (minimum of two required) JI j Surface Water (Al) Water-Stained Leaves (139) (except MLRA Water-Stained Leaves (89) (MLRA 1, 2, High Water Table (A2) 1, 2, 4A, and 413) 4A, and 413) ` Saturation (A3) J Salt Crust (BSS) J Drainage Patterns (B10) Water Marks (61) r Aquatic Invertebrates (613) i Dry Season Water Table (C2) Sediment Deposits (132) Hydrogen Sulfide Odor (Cl) L , Saturation Visible on Aerial Imagery (C9) Drift deposits (133) Oxidized Rhizospheres on Living Roots (0) Geomorphic Position (132) _ Algal Mat or Crust (B4) Presence of Reduced Iron (C4) Shallow Aquitard (D3) Iron Deposits (135) 1 Recent Iron Reduction in Tilled Soils (C6) FAC-neutral Test (135) Surface Soil Cracks (136) Stunted or Stressed Plants (Dl) (LRR A) - Raised Ant Mounds (136) (LRR A) L Inundation Visible on Aerial Imagery (B7) d Other (Explain in Remarks) Frost Heave Hummocks (D7) Sparsely Vegetated Concave Surface (B8) I Field Observations: Surface Water Present? Yes No '•'i Depth (inches): L - j Water Table Present? Yes No Depth (inches): Saturation Present? Yes - No - Wetland Hydrology Present? Yes No Depth (inches): (includes capillary fringe) (stream gauge, g / photos, previous Describe Recorded Data stream au a monitor well, aerial hotos, revious inspections), if available: i Remarks: Very moist 0-9", Best professional judgement indicates area would be saturated for at least 2 weeks during the growing season. US Army Corps of Engineers • • Western Mountains, Valleys, and Coast Region Interim version 0 WETLAND DETERMINATION DATA FORM - Western Mountains, Valleys, and Coast Region Project/Site:_DESCHUTES LWI City/County: SUNRIVER/DESCHUTES Sampling Date: 17 Nov-10 A licant/Onr: DESCHUTESgCOUNTY _ State: OR Sampling Point: 5P 606 • Invests ator s .Sarah Halton - = Section, Township, Range: S 2 T 21 S R 10 E Landform (hillslope, terrace, etc.): bottom of slope Local relief (concave convex, none): fl ° ° at slope:... 2.0/°/ , 0.0 - Subregion (LRR): LRR A Lat.: 43.7856 Long.: -121.5067 Datum: NAD83 Soil Map Unit NWI classification: PFQA.....- Are climatic/ hydrologic conditions on the site typical for this time of year? Yes ' No (If no, explain in Remarks.) Are Vegetation L , Soil L , or Hydrology I . J significantly disturbed? Are "Normal Circumstances" present? Yes No ( ) Are Vegetation 71 , Soil ❑ , or Hydrology Ll naturally problematic? (If needed, explain any answers in Remarks.) Summary of Findings - Attach site map showing sampling point locations, transects, important features, et • is Hydrophytic Vegetation Present? Yes NO - Hydrlc Soil Present? Yes No Is the Sampled Area - - Yes ~ No Wetland Hydrology Present? Yes No ( within a Wetland? Remarks: On-site determination. VEGETATION - Use scientific names of plants. Dominant Species? Absolute Rel.Strat. Indicator Dominance Test worksheet: Tree Stratum (Plot Size: % Cover Cover Status N b f D i t S i 1 Pinus contorta 50 U 100.0% FAC um er o om nan pec es That are OBL, FACW, or FAC: 3 (A) 2 0 o.o%° , 3 0 0 0% I-i Total Number o Dominant • . _ Species Across All Strata: 3 4. 0...... L-1 0.0% Percent of dominant Species Sapling/Shrub Stratum (Plot size: ) so = Total Cover 0.0% (A/13) That Are OBL, FACW, or FAC: Prevalence Index worksheet: 0 - _0.0°h Total % Cover of: MultiplY._by 3. 0 I 0.0% ORL species 0 x 1= 0 4 0 n 0.0% FACW species _ 0 x 2= 0 5 o U o.o°i m „ x 3 _ 360 FAC species 120.. ver Total 48 U s H Ize: u ) 0 0 shilea millefoium 1 A 2 71 2% FACU _ x 5 uPL species Fra n vv meana 2. S.a_... 10 ° 1 10.9% FACU 8 40-._.-. Cs) column Totals: .._..13.2 (A) p Carex s p. 3 43 3 5 FAC 00 Prevalence Index - 8/A - 0 0 4 Poa sp. 30 IV] 32.6% FAC Hydrophytic Vegetation Indicators: - ' 5. Unknown herb 10 1 10.9% L Dominance Test is n 500/6 6, 0 _ .0.0% ❑ Prevalence index is 53.0' 7, 0 0.0% L Morphological Adaptations L~ porting . S 0 J 0.0% or n a separate sheet) data In i 9 0 . L J 0.0% n Wetland Non-Vascular Plants' 10. U L ..o.o% Problematic Hydrophytic Vegetationl (Explain) 11. 0 71 0,0% 92 = Total Cover 11ndicators of hydric soil and wetland hydrology must - - - be present, unless disturbed or problematic. Woody Vine Stratum (Plot size: 2. 0 D_0% Hydrophytic 0 = Total Cover Vegetation Yes No Present. i % Bare Ground in Herb Stratum: 8 Remarks: 1 Carex sp. and Poa sp. assumed to be FAC. C(C *Indicator suffix = National status or professional decision assigned because Regional status not defined by FWS US Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version Soil Sampling Point: SP 606 Profile Desch Ion: Describe to the depth needed to document the indicator or Confirm the absence of indicators pt ( Depth -.-.---.-Matrix__ Redox Features- (inches (inches) Color (moist) % Color (moist) % Type t Loc2 Texture Remarks - - J - - v It Loam i with 30% duff/organics 3-10 lOYR 4/1 90% 10YR 4/4 10% C M Clay Loam 10-20 10YR 6/2 80% lOYR 4/4 20% C M Sand streaking in sand 1Type; C=Concentration. D=Deplehon. RM- -Red - uced Matrix, CS-Covered or Coated Sand Grains zLocation, PL-Pore Lining. M=Mat rix Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.) Indicators for Problematic Hydric SOIIs:3 ] Histosol (Al) Sandy Redox (S5) 2 cm Muck (A10) ] Histic Epipedon (A2) _ Stripped Matrix (S6) Li Red Parent Material (TF2) 1_] Black Histic (A3) Loamy Mucky Mineral (Fl) (except in MLRA 1) r 1 Other (Explain in Remarks) Hydrogen Sulfide (A4) Loamy Gleyed Matrix (F2) LI Depleted Below Dark Surface (All) 1/' Depleted Matrix (F3) Thick Dark Surface (A12) Redox Dark Surface (F6) 3Indicators of hydrophytic vegetation and ] Sandy Muck Mineral (51) _ Depleted Dark Surface (F7) wetland hydrology must be present, ~~..J Sandy Gleyed Matrix (54) Redox depressions (F8) unless disturbed or problematic. Restrictive Layer (If present): Type: f Depth (inches). Hydric Soil Present? Yes No I Remarks: Hydrology _ Welland f I Primary Indicators (minimum of one required; check all that apply) m of two required) Secondary Indicators m Surface Water r ( I) ' Water-Stained eaves (69) (except MLRA 9 Mm Leaves B9) ( ( LRA 1, 2, Water-Stained Table (A2) High Water A 4A d and 4B) and 48) Saturation (A3) ] Salt Crust (1311) Drainage Patterns (B10) Water Marks (BI) Aquatic Invertebrates (813) Dry Season Water Table (C2) Sediment Deposits (B2) Hydrogen Sulfide Odor (Cl) _ Saturation Visible on Aerial Imagery (C9) Drift deposits (B3) Oxidized Rhizospheres on Living Roots (0) Geomorphic Position (D2) Algal Mat or Crust (84) Presence of Reduced Iron (C4) Shallow Aquitard (03) hh Iron Deposits (BS) i ]Recent Iron Reduction in Tilled Soils (C6) FAC-neutral Test (D5) Surface Soil Cracks (86) Stunted or Stressed Plants (Dl) (LRR A) Raised Ant Mounds (136) (LRR A) I Inundation Visible on Aerial Imagery (137) 1111 Other (Explain in Remarks) Frost Heave Hummocks (D7) Sparsely Vegetated Concave Surface (B8) i Field Observations: Surface Water Present? Yes ' No Depth (inches): I i Water Table Present? Yes No Depth (inches): j Saturation Present? - - Wetland Hydrology Present? Yes •P` No (includes capillary fringe) Yes No Depth (inches); Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspections), if available; F Remarks: Saturation in spring based on landowner information. Springs located at base of the hill provide hydrology for the area. Water ponds on nearby roads throughout spring. • U5 Army Corps of Engineers Western Mountains, Valleys, and Coast Region Interim version 0 South Deschutes County Local Wetland Inventory Report C, APPENDIX D: WETLAND SUMMARY SHEETS rI • ESA Adolfson June 2011 Page D-1 • 0 E r~ r~ • South Deschutes County Local Wetland Inventory Wetland Summary Sheet - Date(s) of Field Verification: 5/5/2010 Wetland Mapping Code: 1 Investigator(s): Sarah Hartung, Aaron Booy Size (acres): 3.5 Data Sheet Numbers: SP 207 Location Legal: T20 S R 11E S 6 BB Nearest Town: Sunriver Other: Located on the west side of the Deschutes Latitude: 43.8769 River, west and parallel to the airport Longitude: -121.4628 Basin: Deschutes River Soils Mapped Series: Not available Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Riverine Flow-Through Dominant Vegetation and Comments Cowardin Classification(s): PSSE Vegetation: Shrubs: Salix geyeriana (Geyer willow), Herbs: Carex aquatilis (Water sedge) Comments: Off-site determination. Low-lying area along the Deschutes River, open space. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 10 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included adjoining open water and an island. Percent (approx.) of the Wetland Visited: 0, viewed from opposite shoreline. Percent (approx.) of the AA Visited: 2, included the Deschutes River shoreline. Month & Year of ORWAP Training Attended by Investigator(s): 8/2009 and 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 3 Goal 6 Water Quality Resource: No Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom Project Number: 209554 South Deschutes County Local Wetland Inventory - Wetland Summary Sheet Date(s) of Field Verification: 5/5/2010 Wetland Mapping Code: 2 Investigator(s): Sarah Hartung, Aaron Booy Size (acres): 1.0 Data Sheet Numbers: SP 206 Location Legal: T20 S R 11 E S 6 BB Nearest Town: Sunriver Other: West of airport, east side of Deschutes River Latitude: 43.8743 and slightly east of channel Longitude: -121.4617 Basin: Deschutes River Solls Mapped Series: 29A: Gryaquolls, 0 to 3 percent slopes Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Slope Valley Dominant Vegetation and Comments Cowardin Classification(s): PEMY Vegetation: Herbs: Carex aquatilis (Water sedge), Typha latifolia (Broadleaf cattail) Comments: Off-site determination. In undeveloped area adjacent to the airport. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 8 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included the larger wetland that extends outside of the study area. Percent (approx.) of the Wetland Visited: 0, viewed from public trail. Percent (approx.) of the AA Visited: 0 Month S Year of ORWAP Training Attended by Investigator(s): 8/2009 and 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 3 Goal 6 Water Quality Resource: No Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom r~ • Project Number: 209554 • • South Deschutes County Local Wetland Inventory - Wetland Summary Sheet - Date(s) of Field Verification: 5/5/2010 Wetland Mapping Code: 3 Investigator(s): Sarah Hartung, Aaron Booy Size (acres): 12.7 Data Sheet Numbers: SP 205 LLocation Legal: T 20 S R 11 E S 6 AC, BC, CB Nearest Town: Sunriver Other: West and southwest of airport on west side of Latitude: 43.8701 Deschutes River, near confluence with Spring River Longitude: -121.4619 Basin: Deschutes River Soils Mapped Series: Not available LHydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Riverine Flow-Through Dominant Vegetation and Comments Cowardin Classification(s): PEME Vegetation: Herbs: Carex aquatilis (Water sedge) Comments: Off-site determination. In open space, undeveloped area south of confluence of Spring River and Deschutes River. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 16 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included adjoining open water. Percent (approx.) of the Wetland Visited: 0, viewed from opposite shoreline. Percent (approx.) of the AA Visited: 2, included the Deschutes River shoreline. Month & Year of ORWAP Training Attended by Investigator(s): 8/2009 and 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 3 Goal 6 Water Quality Resource: Yes Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom Project Number: 209554 South Deschutes County Local Wetland Inventory - Wetland Summary Sheet - Date(s) of Field Verification: 5/5/2010 Wetland Mapping Code: 4 Investigator(s): Sarah Hartung, Aaron Booy Size (acres): 2.2 Data Sheet Numbers: SP 208 Location Legal: T20 S R 10 E S 1 AD Nearest Town: Sunriver Other: Southwest of airport on the east side of Spring Latitude: 43.8684 River, west of Deschutes River Longitude: -121.4699 Basin: Deschutes River Soils Mapped Series: Not available Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Riverine Flow-Through Dominant Vegetation and Comments Cowardin Classification(s): PEMY Vegetation: Trees: Pinus contorta (Lodgepole pine), Shrubs: Salix geyeriana (Geyer willow), Herbs: Carex aquatilis (Water sedge) Comments: Off-site determination. Narrow, convoluted wetland along Spring River and unnamed tributary to Spring River. In undeveloped area, open space. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 4 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included adjoining open water in Spring River. Percent (approx.) of the Wetland Visited: 0 Percent (approx.) of the AA Visited: 0 Month & Year of ORWAP Training Attended by Investigator(s): 8/2009 and 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 3 Goal 6 Water Quality Resource: No Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom E • • Project Number: 209554 n u E E South Deschutes County Local Wetland Inventory - Wetland Summary Sheet - Date(s) of Field Verification: 5/7/2010 Wetland Mapping Code: 5 Investigator(s): Sarah Hartung, Aaron Booy Size (acres): 8.0 Data Sheet Numbers: SP 201 I Location Legal; T 20 E R 11 E S 6 DC, CD Nearest Town: Sunriver Other: North of Spring River Road, west side of Latitude: 43.8684 Deschutes River Longitude: -121.4699 Basin: Deschutes River Soils Mapped Series: 29A: Cryaquolls, 0 to 3 percent slopes, W: Water Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification (s): Riverine Flow-Through Dominant Vegetation and Comments Cowardin Classification(s): PEME, PSSE Vegetation: Shrubs: Salix geyeriana (Geyer willow), Herbs: Carex aquatilis (Water sedge) Comments: Off-site determination. In undeveloped area along the Deschutes River. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 10.5 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included adjoining open water in the Deschutes River. Percent (approx.) of the Wetland Visited: 0, viewed from right-of-way. Percent (approx.) of the AA Visited: 0, viewed from right-of-way. Month & Year of ORWAP Training Attended by Investigator(s): 8/2009 and 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 3 Goal 6 Water Quality Resource: No Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom Project Number: 209554 South Deschutes County Local Wetland Inventory - Wetland Summary Sheet - Date(s) of Field Verification: 5/5/2010 Wetland Mapping Code: 6a-b Investigator(s): Sarah Hartung, Aaron Booy Size (acres): 0.6 Data Sheet Numbers: SP 203 (6a-b) Location Legal: T 20 S R 11 E S 7 AB, T 20 S R 11 E S 6 DC Nearest Town: Sunriver Other: West of Lunar Dr along Spring River Rd Latitude: a. 43.8627 b. 43.8630 Basin: Deschutes River Longitude: a. -121.4600 b. -121.4591 ISoils Mapped Series: 144A: Sunriver sandy loam, 0 to 3 percent slopes Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Depressional Outflow (6a-b) Dominant Vegetation and Comments Cowardin Classification(s): PSSF (6a), PSSC (6b) Vegetation: Salix geyeriana (Geyer willow), Spiraea douglasii (Douglas spirea), Herbs: Carex aquatilis (Water sedge), Comments: On-site determination. 6a-b surrounded by residential development and along busy road (Spring River Rd). Fill activities have reduced size of 6a, only a few residences nearby and adjacent to woodland. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 0.6,same size as wetland areas. AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. For 6a-b, the AA's were the same size as the wetland polygons. Percent (approx.) of the Wetland Visited: a. 20 b.10 Percent (approx.) of the AA Visited: a. 20 b. 10 Month & Year of ORWAP Training Attended by Investigator(s): 8/2009 and 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 2 Goal 6 Water Quality Resource: No Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom • • Project Number. 209554 • • • South Deschutes County Local Wetland Inventory - Wetland Summary Sheet - Date(s) of Field Verification: 5/6/2010 Wetland Mapping Code: 7 Investigator(s): Alison Sigler, Rosemary Baker Size (acres): 0.7 Data Sheet Numbers: SP 210 Location Legal: T 20 S R 11 E S 7 AB, DB Nearest Town: Sunriver Other: East of Lunar Rd, south of Spring River Rd on Latitude: 43.8599 west side of Deschutes River Longitude: -121.4570 Basin: Deschutes River Soils Mapped Series: 144A: Sunriver sandy loam, 0 to 3 percent slopes, W: Water Hydrology Primary Hydrology Source(s): Flooding Hydro-geomorphic (HGM) Classification(s): Riverine Flow-Through Dominant Vegetation and Comments Cowardin Classification(s): PEME Vegetation: Carex aquatilis (Water sedge) Comments: On-site determination. Narrow wetland along Deschutes River, residential waterfront. Two polygons less than 100 feet apart on same side of Deschutes River; considered one unit due to small size of polygons and close proximity. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 2 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included adjoining open water in the Deschutes River. Percent (approx.) of the Wetland Visited: 20 Percent (approx.) of the AA Visited: 6 Month & Year of ORWAP Training Attended by Investigator(s): 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 2 Goal 6 Water Quality Resource: No Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom Project Number: 209554 South Deschutes County Local Wetland Inventory - Wetland Summary Sheet - Date(s) of Field Verification: 5/5/2010 Wetland Mapping Code: 8 Investigator(s): Alison Sigler, Rosemary Baker Size (acres): 1.1 Data Sheet Numbers: SP 209 Location Legal: T20 S R 11 E S 7 DB Nearest Town: Sunriver Other: East of Lunar Rd, east side of Deschutes River Latitude: 43.8570 Basin: Deschutes River Longitude: -121.4574 Soils Mapped Series: 44A: Sunriver sandy loam, 0 to 3 percent slopes, 29A Cryaquolls, 0 to 3 percent slopes Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Riverine Flow-Through Dominant Vegetation and Comments Cowardin Classification(s): PEME Vegetation: Trees: Pinus contorta (Lodgepole pine), Shrubs: Salix geyeriana (Geyer willow), Herbs: Carex aquatilis (Water sedge) Comments: Off-site determination. Undeveloped land along the Deschutes River. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 2.5 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included adjoining open water in the Deschutes River. Percent (approx.) of the Wetland Visited: 0, viewed from opposite shoreline. Percent (approx.) of the AA Visited: 1, included shoreline of Deschutes River. Month & Year of ORWAP Training Attended by Investigator(s): 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 2 Goal 6 Water Quality Resource: No Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PFM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom • • Project Number: 209554 • South Deschutes County Local Wetland Inventory - Wetland Summary Sheet - Date(s) of Field Verification: 5/7/2010 Wetland Mapping Code: 9 Investigator(s): Sarah Hartung, Aaron Booy Size (acres): 6.8 Data Sheet Numbers: N/A Location Legal: T 20 S R 11 E S 7 CD Nearest Town: Sunriver Other: Immediately south of the confluence of Little Latitude: 43.8514 Deschutes and Deschutes River; west of Canoe Camp Longitude: -121.4524 Dr Basin: Deschutes River Soils Mapped Series: 29A: Cryaquolls, 0 to 3 percent slopes, 144A: Sunriver sandy loam, 0 to 3 percent slopes Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Slope Valley I Dominant Vegetation and Comments Cowardin Classification(s): PEMC, PFOC Vegetation: From aerials and vegetation in vicinity: Carex sp. (sedges); grasses (unknown species); Pinus contorta (Lodgepole pine) Comments: Not able to view in field due to lack of property access and lack of public roads, therefore no data sheet was created. Wetland is in undeveloped forested area; exclusive residences and golf course to the east Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 15 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included the larger wetland extending north of the study area and adjoining open water in the Deschutes River and Little Deschutes River. Percent (approx.) of the Wetland Visited: 0, not able to view in field due to lack of property access and lack of public roads. Percent (approx.) of the AA Visited: 0 Month & Year of ORWAP Training Attended by Investigator(s): 8/2009 and 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 3 Goal 6 Water Quality Resource: No Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom Project Number: 209554 South Deschutes County Local Wetland Inventory - Wetland Summary Sheet - Date(s) of Field Verification: 5/6/2010 Wetland Mapping Code: 10 Investigator(s): Sarah Hartung, Aaron Booy Size (acres): 9.2 Data Sheet Numbers: SP 212 Location Legal: T 20 S R 11 E S 7 AC, BC, CC, DC Nearest Town: Sunriver Other: South of the intersection of Meteor and Latitude: 43.8539 Elsinore, west side of Deschutes River Longitude: -121.4614 Basin: Deschutes River ISoils Mapped Series: 29A: Cryaquolls, 0 to 3 percent slopes, 144A: Sunriver sandy loam, 0 to 3 percent slopes Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Slope Valley Dominant Vegetation and Comments Cowardin Classification(s): PEMF, PSSE, PFOA Vegetation: Herbs: Carex aquatilis (Water sedge), Juncus balticus (Baltic rush) Comments: Off-site determination. Old Oxbow of Deschutes River; surrounded by residential development. Viewed from public trail. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 9.2 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. Percent (approx.) of the Wetland Visited: 0, viewed from public trail. Percent (approx.) of the AA Visited: 0 Month & Year of ORWAP Training Attended by Investigator(s): 8/2009 and 512010 Number of Wetlands Assessed by Investigators Using ORWAP: 3 Goal 6 Water Quality Resource: Yes Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom r~ u r~ u • Project Number: 209654 • • • South Deschutes County Local Wetland Inventory Wetland Summary Sheet Date(s) of Field Verification: 5/5/2010 Wetland Mapping Code: 11 Investigator(s): Sarah Hartung, Aaron Booy Size (acres): 3.8 Data Sheet Numbers: SP 213 Location Legal: T 20 S R 11 E S 7 AC, DC Nearest Town: Sunriver Other: East of Eclipse on the east side of the Latitude: 43.8523 Deschutes River Longitude: -121.4594 Basin: Deschutes River Soils Mapped Series: 29A: Cryaquolls, 0 to 3 percent slopes Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification (s): Riverine Flow-Through Dominant Vegetation and Comments Cowardin Classification(s): PEMF Vegetation: Carex aquatilis (Water sedge) Comments: Off-site determination. Low-lying area on a bend of the Deschutes River. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 5 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included adjoining open water in the Deschutes River. Percent (approx.) of the Wetland Visited: 0, viewed from opposite shoreline. Percent (approx.) of the AA Visited: 1, included the Deschutes River shoreline. Month & Year of ORWAP Training Attended by Investigator(s): 8/2009 and 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 3 Goal 6 Water Quality Resource: No Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom Project Number: 209554 South Deschutes County Local Wetland Inventory Wetland Summary Sheet - Date(s) of Field Verification: 5/5/2010 Wetland Mapping Code: 12 Investigator(s): Sarah Hartung, Aaron Booy Size (acres): 2.2 Data Sheet Numbers: SP 214 Location Legal: T20 S R 11 E S 18 AB, BB Nearest Town: Sunriver Other: South of Guss Way on the west side of Latitude: 43.8468 Deschutes River Longitude: -121.4619 Basin: Deschutes River Soils Mapped Series: 144A: Sunriver sandy loam, 0 to 3 percent slopes Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Riverine Flow-Through Dominant Vegetation and Comments Cowardin Classification(s): PEME, PSSE Vegetation: Saiix geyeriana (Geyer willow), Herbs: Carex aquatilis (Water sedge), Juncus balticus (Baltic rush) Comments: On-site determination. Narrow fringe along the Deschutes River, residential waterfront. Several docks and boat slips constructed in wetland. Wetland includes previous DSL determination WD2009-0042. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 4 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included adjoining open water in the Deschutes River. Percent (approx.) of the Wetland Visited: 5 Percent (approx.) of the AA Visited: 1 Month & Year of ORWAP Training Attended by Investigator(s): 8/2009 and 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 3 Goal 6 Water Quality Resource: No Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom • Project Number: 209554 11 C7 • South Deschutes County Local Wetland Inventory - Wetland Summary Sheet - Date(s) of Field Verification: 5/3/2010 Wetland Mapping Code: 13a-d Investigator(s): John Gordon, Rosemary Baker Size (acres): 0.7 Data Sheet Numbers: SP 101 Location Legal: T 20 S R 10 E S 13 CA Nearest Town: Three Rivers Other: Running northwest to southeast from Norwalk Latitude: 43.8403 continuing south of Pasadena Longitude: -121.4734 Basin: Deschutes River Soils Mapped Series: 144A: Sunriver sandy loam, 0 to 3 percent slopes Hydrology Primary Hydrology Source(s): Overland Flow Hydro-geomorphic (HGM) Classification(s): Slope Headwater Dominant Vegetation and Comments Cowardin Classification(s): PSSE, PFOE Vegetation: Trees: Pinus contorta (Lodgepole pine), Shrubs: Prunus sp. (cherry), Salix sp. (willow) Comments: On-site determination. Surrounded by residential development. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 0.7 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA was the same size as the wetland. Percent (approx.) of the Wetland Visited: 25 Percent (approx.) of the AA Visited: 25 Month 8r Year of ORWAP Training Attended by Investigator(s): 8/2009 and 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 3 Goal 6 Water Quality Resource: Yes Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom Project Number- 209554 South Deschutes County Local Wetland Inventory - Wetland Summary Sheet - Date(s) of Field Verification: 5/3/2010 Wetland Mapping Code: 14 Investigator(s): John Gordon, Adam Merrill Size (acres): 9.8 Data Sheet Numbers: SP 100 Location Legal: T20 S R 3 E S 13 AD, BD, AG, T20 S R 3 E S Nearest Town: Three Rivers 18 BC Latitude: 43.8394 Other: South of Pasadena Rd, north of Milky Way Longitude: -121.4714 Basin: Deschutes River ISoils Mapped Series: 144A: Sunriver sandy loam, 0 to 3 percent slopes, W: Water Hydrology Primary Hydrology Source(s): Flooding Hydro-geomorphic (HGM) Classification(s): Riverine Flow-Through Dominant Vegetation and Comments Cowardin Classification(s): PEMC, PSSC Vegetation: Shrubs: Saiix sp., Herbs: Carex sp., Geum macrophyllum (Largeleaf avens), Rumex acetosa (Garden sorrel), Juncus balticus (Baltic rush) Comments: On-site determination. Old oxbow of Deschutes River surrounded by residential development. Wetland includes previous DSL determination W02007-0154. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 15 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included adjoining open water. Percent (approx.) of the Wetland Visited: 10 Percent (approx.) of the AA Visited: 4 Month & Year of ORWAP Training Attended by Investigator(s): 8/2009 and 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 3 Goal 6 Water Quality Resource: No Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom • • Project Number: 209554 11 • South Deschutes County Local Wetland Inventory - Wetland Summary Sheet - Date(s) of Field Verification: 5/5/2010 Wetland Mapping Code: 15 Investigator(s): Alison Sigler, Rosemary Baker Size (acres): 4.3 Data Sheet Numbers: SP 7 Location Legal: T 20 S R 10 E S 13 CD, DD, T 20 S R11 ES Nearest Town: Three Rivers 18 CC, T 20 S R 10 E S 24 BA Latitude: 43.8360 Other: South of Upland Rd and Milky Way, on the west Longitude: -121.4710 side of Deschutes River Basin: Deschutes River Soils Mapped Series: 144A: Sunriver sandy loam, 0 to 3 percent slopes, W: Water Hydrology Primary Hydrology Source(s): Overland Flow Hydro-geomorphic (HGM) Classification(s): Riverine Flow-Through Dominant Vegetation and Comments Cowardin Classification(s): PEME Vegetation: Carex nebrascensis (Nebraska sedge), Carex aquatilis (Water sedge) Comments: On-site determination and includes previous delineation WD1995-0148. Narrow fringe along the Deschutes River, residential waterfront. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 10 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included adjoining open water in the Deschutes River. Percent (approx.) of the Wetland Visited: 4 Percent (approx.) of the AA Visited: 1 Month & Year of ORWAP Training Attended by Investigator(s): 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 2 Goal 6 Water Quality Resource: No Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom Project Number: 209554 South Deschutes County Local Wetland Inventory - Wetland Summary Sheet - Date(s) of Field Verification: 5/5/2010 Wetland Mapping Code: 16 Investigator(s): Alison Sigler, Rosemary Baker Size (acres): 2.0 Data Sheet Numbers: SP 6 Location Legal: T20 S R 10 E S 24 AA, BA Nearest Town: Three Rivers Other: Northwest of Wood Duck and Osprey Latitude: 43.8324 intersection on the west side of the Deschutes River Longitude: -121.4702 Basin: Deschutes River Solis Mapped Series: 29A: Cryaquolls, 0 to 3 percent slopes, 144A: Sunriver sandy loam, 0 to 3 percent slopes Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Riverine Flow-Through Dominant Vegetation and Comments Cowardin Classification(s): PEME Vegetation: Herbs: Carex aquatilis (Water sedge) Comments: On-site determination. Peninsula at bend in Deschutes River. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 5 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included adjoining open water. Percent (approx.) of the Wetland Visited: 10 Percent (approx.) of the AA Visited: 2 Month S Year of ORWAP Training Attended by Investigator(s): 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 2 Goal 6 Water Quality Resource: No Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom • t • Project Number: 209554 • E South Deschutes County Local Wetland Inventory - Wetland Summary Sheet - Date(s) of Field Verification: 5/3/2010 Wetland Mapping Code: 17 Investigator(s): Alison Sigler, Rosemary Baker Size (acres): 2.5 Data Sheet Numbers: SP 5 Location 7-771 Legal: T 20 S R 10 E S 24 BA, DA Nearest Town: Three Rivers Other: West and parallel to Wood Duck, on the west Latitude: 43.8306 side of Deschutes River Longitude: -121.4739 Basin: Deschutes River Soils Mapped Series: 29A: Cryaquolls, 0 to 3 percent slopes, 144A: Sunriver sandy loam, 0 to 3 percent slopes Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Riverine Flow-Through Dominant Vegetation and Comments Cowardin Classification(s): PEME, PFOA Vegetation: Herbs: Carex aquatilis (Water sedge), Equisetum arvense (Field horsetail) Comments: On-site determination. Low-lying area along the Deschutes River. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 6 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included adjoining open water. Percent (approx.) of the Wetland Visited: 5 Percent (approx.) of the AA Visited: 1 Month & Year of ORWAP Training Attended by Investigator(s): 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 2 Goal 6 Water Quality Resource: No Wetland Classificatlon Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom Project Number: 209554 South Deschutes County Local Wetland Inventory - Wetland Summary Sheet - Date(s) of Field Verification: 5/5/2010 Wetland Mapping Code: 18 Investigator(s): Alison Sigler, Rosemary Baker Size (acres): 10.7 Data Sheet Numbers: SP 9,102 Location Legal: T 20 S R 10 E S 24 CB, CA, BD, AC, DB Nearest Town: Three Rivers Other: South of Sharp on west side of Deschutes Latitude: 43.8285 River, includes area in drainage field Longitude: -121.4729 Basin: Deschutes River Soils Mapped Series: 29A: Cryaquolls, 0 to 3 percent slopes, 144A: Sunriver sandy loam, 0 to 3 percent slopes Hydrology Primary Hydrology Source(s): Flooding Hydra-geomorphic (HGM) Classification(s): Riverine Flow-Through Dominant Vegetation and Comments Cowardin Classification(s): PEMF Vegetation: Herbs: Carex aquatilis (Water sedge), Scirpus americanus (Chairmaker's bulrush), Juncus balticus (Baltic rush) Comments: On-site determination of previous delineations, WD1993-0294 and WD2001-0398. Backwater slough connected to the Deschutes River. Oregon Rapid Wetland Assessment Protocol (ORWAP) 71 Approximate Size of the Assessment Area (AA) in acres: 12 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included adjoining open water in the Deschutes River. Percent (approx.) of the Wetland Visited: 3 Percent (approx.) of the AA Visited: a 1 Month & Year of ORWAP Training Attended by Investigator(s): 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 2 Goal 6 Water Quality Resource: No Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom • • C Project Number: 209554 • South Deschutes County Local Wetland Inventory - Wetland Summary Sheet - Date(s) of Field Verification: 5/5/2010 Wetland Mapping Code: 19 Investigator(s): Alison Sigler, Rosemary Baker Size (acres): 2.3 Data Sheet Numbers: SP 10 Location Legal: T 20 S R 10 E S 24 AD, BD Nearest Town: Three Rivers Other: West of the end of Chief Paulina on the west Latitude: 43.8241 side of Deschutes River Longitude: -121.4718 Basin: Deschutes River Soils Mapped Series: 9A: Cryaquolls, 0 to 3 percent slopes, 144A: Sunriver sandy loam, 0 to 3 percent slopes, W: Water Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Riverine Flow-Through Dominant Vegetation and Comments Cowardin Classification(s): PEMC Vegetation: Carex aquatilis (Water sedge) Comments: Off-site determination. Undeveloped land along the Deschutes River, adjacent to upland forest. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 5 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included adjoining open water. Percent (approx.) of the Wetland Visited: 0 Percent (approx.) of the AA Visited: 0 Month & Year of ORWAP Training Attended by Investigator(s): 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 2 Goal 6 Water Quality Resource: No • Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom Project Number: 209554 South Deschutes County Local Wetland Inventory - Wetland Summary Sheet - Date(s) of Field Verification: 5/6/2010 Wetland Mapping Code: 20 Investigator(s): Alison Sigler, Rosemary Baker Size (acres): 3.7 Data Sheet Numbers: SP 11 Location Legal: T 20 S R 10 E S 24 BD Nearest Town: Three Rivers Other: South of Big River/Century Rd, on the east Latitude: 43.8252 bank of the Deschutes River Longitude: -121.4741 Basin: Deschutes River Soils Mapped Series: 29: Cryaquolls, 0 to 3 percent slopes, W: Water Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Riverine Flow-Through Dominant Vegetation and Comments Cowardin Classification(s): PEME Vegetation: Carex aquatilis (Water sedge) Comments: Off-site determination. Undeveloped land along the Deschutes River, adjacent to upland forest. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 7 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included adjoining open water in the Deschutes River. Percent (approx.) of the Wetland Visited: 0, viewed from opposite shoreline. Percent (approx.) of the AA Visited: 1 Month & Year of ORWAP Training Attended by Investigator(s): 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 2 Goal 6 Water Quality Resource: No Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom • C7 • Project Number: 209554 • • E South Deschutes County Local Wetland Inventory - Wetland Summary Sheet - Date(s) of Field Verification: 5/6/2010 Wetland Mapping Code: 21 Investigator(s): Alison Sigler, Rosemary Baker Size (acres): 7.8 Data Sheet Numbers: N/A Location Legal: T20 S R 10 E S 24 AD, DD, CD Nearest Town: Three Rivers Other: North of Big River/Century Rd, east of Latitude: 43.8203 Fountainebleau and south of Deschutes River Longitude: -121.4724 Basin: Deschutes River Soils Mapped Series: 115A: Shanahan loamy coarse sand, 0 to 3 percent slopes, 144A: Sunriver sandy loam, 0 to 3 percent slopes Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Riverine Flow-Through Dominant Vegetation and Comments Cowardin Classification(s): PABF, PEME, PEMH, PSSC, PFOA Vegetation: From aerial image and vegetation in vicinity: grasses, sedges, and Pinus contorta (Lodgepole Pine) Comments: Off-site determination. No visual access. Old oxbow of Deschutes River surrounded by low density residential and forest. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 7.84 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA was the same size as the wetland. Percent (approx.) of the Wetland Visited: 0 Percent (approx.) of the AA Visited: 0 Month & Year of ORWAP Training Attended by Investigator(s): 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 2 Goal 6 Water Quality Resource: Yes Wetland Classificatlon Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom Project Number- 209554 South Deschutes County Local Wetland Inventory Wetland Summary Sheet - Date(s) of Field Verification: 5/5/2010 Wetland Mapping Code: 22 Investigator(s): Alison Sigler, Rosemary Baker Size (acres): 4.5 Data Sheet Numbers: SP 8 Location Legal: T 20 S R 10 E S 24 BD, AC, DC Nearest Town: Three Rivers Other: South of the end of Cone, on the west side of Latitude: 43.8227 the Deschutes River Longitude: -121.4781 Basin: Deschutes River Soils Mapped Series: 29A: Cryaquolls, 0 to 3 percent slopes Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Riverine Flow-Through Dominant Vegetation and Comments Cowardin Classification(s): PEME Vegetation: Carex aquatilis (Water sedge) Comments: On-site determination. Low-lying area adjacent to Deschutes River. Buffer is upland forest and low density residential. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 7 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included adjoining open water. Percent (approx.) of the Wetland Visited: 5 Percent (approx.) of the AA Visited: 1 Month & Year of ORWAP Training Attended by Investigator(s): 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 2 Goal 6 Water Quality Resource: No Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom • • C Project Number: 209564 • South Deschutes County Local Wetland Inventory - Wetland Summary Sheet - Date(s) of Field Verification: 5/6/2010 Wetland Mapping Code: 23 Investigator(s): Alison Sigler, Rosemary Baker Size (acres): 1.1 Data Sheet Numbers: NIA Location Legal: T20 S R 10 E S 24 AC, BC Nearest Town: Three Rivers Other: North of Gatehouse Ln, on the east side of the Latitude: 43.8239 Deschutes River Longitude: -121.4826 Basin: Deschutes River Soils Mapped Series: 29A: Cryaquolls, 0 to 3 percent slopes, 144A: Sunriver sandy loam, 0 to 3 percent slopes Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Riverine Impounding LDominant Vegetation and Comments Cowardin Classification(s): PABF Vegetation: From aerial image and vegetation in vicinity: sedges, and Pinus contorta (Lodgepole Pine) Comments: Off-site determination and no public access viewing. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 1.1 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA was the same size as the wetland. Percent (approx.) of the Wetland Visited: 0 Percent (approx.) of the AA Visited: 0 Month & Year of ORWAP Training Attended by Investigator(s): 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 2 Goal 6 Water Quality Resource: Yes Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom Project Number: 209554 South Deschutes County Local Wetland Inventory Wetland Summary Sheet - Date(s) of Field Verification: 5/6/2010 Wetland Mapping Code: 24 Investigator(s): Alison Sigler, Rosemary Size (acres): 3.0 Data Sheet Numbers: SP 13 Location Legal: T20 S R 10 E S 23 D Nearest Town: Three Rivers Other: North of Big River Rd on the east side of the Latitude: 43.8220 Deschutes River Longitude. -121.4889 Basin: Deschutes River Soils Mapped Series: Not available Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Riverine Flow-Through Dominant Vegetation and Comments Cowardin Classification(s): PEMF Vegetation: Shrubs: Salix geyeriana (Geyer willow), Herbs: Carex aquatilis (Water sedge) Comments: On-site determination. Low-lying area adjacent to Deschutes River. Residential development upslope. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 5 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included adjoining open water in the Deschutes River. Percent (approx.) of the Wetland Visited: 10 Percent (approx.) of the AA Visited: 2 Month & Year of ORWAP Training Attended by Investigator(s): 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 3 Goal 6 Water Quality Resource: No Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom • • Project Number: 209554 • rI South Deschutes County Local Wetland Inventory Wetland Summary Sheet - Date(s) of Field Verification: 5/6/2010 Wetland Mapping Code: 25 Investigator(s): Alison Sigler, Rosemary Baker Size (acres): 5.0 Data Sheet Numbers: SP 12 Location Legal: T 20 S R 10 E S 23 DD, T 20 S R 10 E S 26 Nearest Town: Three Rivers AA Latitude: 43.8184 Other: Southeast of Wagon Master on the west side of Deschutes River Longitude: -121.4906 Basin: Deschutes River Soils Mapped Series: Not available Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Riverine Flow-Through Dominant Vegetation and Comments Cowardin Classification(s): PEME Vegetation: Shrubs: Salix geyeriana (Geyer willow), Herbs: Carex aquatilis (Water sedge) Comments: Off-site determination. Low-lying area adjacent to Deschutes River. Residential development upslope, beyond forest buffer, Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 7 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included adjoining open water in the Deschutes River. Percent (approx.) of the Wetland Visited: 0, viewed from opposite shoreline. Percent (approx.) of the AA Visited: 1 Month 8r Year of ORWAP Training Attended by Investigator(s): 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 2 Goal 6 Water Quality Resource: No Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom Project Number.- 209554 South Deschutes County Local Wetland Inventory - Wetland Summary Sheet - Date(s) of Field Verification: 5/6/2010 Wetland Mapping Code: 26a-b Investigator(s): Alison Sigler, Rosemary Size (acres): 2.5 Data Sheet Numbers: SP 14 Location Legal: T 20 S 10 E S 25 AS, DB, CB Nearest Town: Three Rivers Other: North and south of Century Rd, to the east of Latitude: 43.8157 Seevers Longitude: -121.4797 Basin: Deschutes River Soils Mapped Series: 115A: Shanahan loamy coarse sand, 0 to 3 percent slopes, 144A: Sunriver sandy loam, 0 to 3 percent slopes Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Depressional Closed Nonpermanently Flooded Dominant Vegetation and Comments Cowardin Classification(s): PEMA, PSSA, PFOA Vegetation: Shrubs: Salix sp., Herbs: Carex aquatilis (Water sedge) Comments: Off-site determination. Near residential uses and forest land. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 2.5 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA was the same size as the wetland. Percent (approx.) of the Wetland Visited: 0, viewed from right-of-way. Percent (approx.) of the AA Visited: 0 Month & Year of ORWAP Training Attended by Investigator(s): 512010 Number of Wetlands Assessed by Investigators Using ORWAP: 2 Goal 6 Water Quality Resource: Yes Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = paiustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom • • is Project Number: 209554 South Deschutes County Local Wetland Inventory - Wetland Summary Sheet - Date(s) of Field Verification: 5/6/2010 Wetland Mapping Code: 27a-c Investigator(s): Alison Sigler, Rosemary Baker Size (acres): 12.1 Data Sheet Numbers: SP 15 LLocation Legal: T20 S RIO E S25 BB Nearest Town: Three Rivers Other: East of Heierman Dr and south of S Century Dr Latitude: 43.8121 Basin: Deschutes River Longitude: -121.4851 Soils Mapped Series: 144A: Sunriver sandy loam, 0 to 3 percent slopes, 115A:Shanahan loamy coarse sand, 0 to 3 percent slopes Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Depressional Closed Nonpermanently Flooded Dominant Vegetation and Comments • Cowardin Classification(s): PFOY Vegetation: Pinus contorta (Lodgepole pine), Shrubs: Spiraea douglasii (Douglas spirea), Salix geyeriana (Geyer willow), Betula grandulosa (resin birch), Herbs: Juncus sp., Fragaria virginiana (Virginia strawberry), Equisetum arvense (Field horsetail) Comments: On-site determination. Wetland/Upland Mosaic located in a forested, undeveloped residential area that has uneven terrain from extensive on-site ditching and previous earth moving work, creating pockets of upland areas throughout wetland. This wetland sits to the west of the base of a slope. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 12,1 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA was the same size as the wetland. Percent (approx.) of the Wetland Visited: 10 Percent (approx.) of the AA Visited: 10 Month & Year of ORWAP Training Attended by Investigator(s): 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 2 Goal 6 Water Quality Resource: Yes Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom Project Number: 209554 South Deschutes County Local Wetland Inventory - Wetland Summary Sheet - Date(s) of Field Verification: 5/6/2010 Wetland Mapping Code: 28a-b Investigator(s): Alison Sigler, Rosemary Baker Size (acres): 1.8 Data Sheet Numbers: SP 16 Location Legal: T 20 S R 10 E S 25 BC Nearest Town: Three Rivers Other: West of Heierman Dr, north and south of Gross Latitude: 43.8099 Dr Longitude: -121.4862 Basin: Deschutes River Mapped Series: 144A, Sunriver sandy loam, 0 to 3 percent slopes Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Depressional Closed Nonpermanently Flooded Dominant Vegetation and Comments Cowardin Classification(s): PFOY Vegetation: Shrubs: Betula glandulosa (Resin birch), Spiraea douglasii (Douglas spirea), Herbs: Poa sp. Comments: On-site determination. Wetland/Upland Mosaic located in a forested, undeveloped residential area that has uneven terrain from extensive on-site ditching and previous earth moving work, creating pockets of upland areas. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 1.8 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA was the same size as the wetland. Percent (approx.) of the Wetland Visited: 10 Percent (approx.) of the AA Visited: 10 Month & Year of ORWAP Training Attended by Investigator(s): 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 2 Goal 6 Water Quality Resource: Yes Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom • C: Project Number: 209554 I South Deschutes County Local Wetland Inventory - Wetland Summary Sheet Date(s) of Field Verification: 5/6/2010 Wetland Mapping Code: 29a-c Investigator(s): Alison Sigler, Rosemary Baker Size (acres): 5.8 Data Sheet Numbers: SP 408 Location Legal: T 20 S R 10 E S 26 DA, AD Nearest Town: Three Rivers Other: South and west of Heierman Dr Latitude: 43.8105 Basin: Deschutes River Longitude: -121.4888 Soils Mapped Series: 144A: Sunriver sandy loam, 0 to 3 percent slopes Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Depressional Closed Nonpermanently Flooded Dominant Vegetation and Comments Cowardin Classification(s): PFOY, PEMY Vegetation: Trees: Pinus contorta (Lodgepole pine), Shrubs: Spiraea douglasii (Douglas spirea), Herbs: Juncus sp., Poa sp., Fragaria virginiana (Virginia strawberry) Comments: On-site determination. Wetland/Upland Mosaic due to uneven terrain and areas of upland vegetation creating numerous upland hummocks. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 5.8 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA was the same size as the wetland. Percent (approx.) of the Wetland Visited: 5 Percent (approx.) of the AA Visited: 5 Month & Year of ORWAP Training Attended by Investigator(s): 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 2 Goal 6 Water Quality Resource: Yes E Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom Project Number: 209554 South Deschutes County Local Wetland Inventory I 0 - Wetland Summary Sheet - Date(s) of Field Verification: 5/7/2010 Wetland Mapping Code: 30 Investigator(s): Alison Sigler, Rosemary Baker Size (acres): 1.7 Data Sheet Numbers: SP 17 Legal: T 20 S R 10 E S 26 BD Nearest Town: Three Rivers Other: North of Big River Rd, west of Casper and east Latitude: 43.8119 of Deschutes River Longitude: -121.4927 Basin: Deschutes River Mapped Series: Not available Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Depressional Closed Nonpermanently Flooded Dominant Vegetation and Comments Cowardin Classification(s): PEME, PSSE, PFOE Vegetation: Trees: Pinus contorta (Lodgepole pine), Shrubs: Betula glandulosa (Resin birch), Salix geyeriana (Geyer willow), Herbs: Carex nebrascensis (Nebraska sedge) Comments: On-site determination. Wetland/Upland Mosaic, part of an old river oxbow including non-wetland hummocks. This wetland extends out of study area and is adjacent to the Deschutes River. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 1.7 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA was the same size as the wetland. Percent (approx.) of the Wetland Visited: 5 Percent (approx.) of the AA Visited: 5 Month & Year of ORWAP Training Attended by Investigator(s): 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 2 Goal 6 Water Quality Resource: No Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom Project Number: 209554 • • South Deschutes County Local Wetland Inventory - Wetland Summary Sheet Date(s) of Field Verification: 5/7/2010 Wetland Mapping Code: 31 Investigator(s): Alison Sigler, Rosemary Baker Size (acres): 0.8 Data Sheet Numbers: SP 18 Location Legal: T 20 S R 10E S 26 BD Nearest Town: Three Rivers Other: Northwest of Big River Rd on east side of Latitude: 43.8118 Deschutes River Longitude: -121.4963 Basin: Deschutes River ISoils Mapped Series: Not available Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Riverine Flow-Through Dominant Vegetation and Comments Cowardin Classification(s): PEME Vegetation: Shrubs: Salix geyeriana (Geyer willow), Herbs: Carex aquatilis (Water sedge), Carex nebrascensis (Nebraska sedge) Comments: Off-site determination. Low-lying area along the Deschutes River. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 2 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included adjoining open water. Percent (approx.) of the Wetland Visited: 0, viewed from adjacent parcel. Percent (approx.) of the AA Visited: 0 Month & Year of ORWAP Training Attended by Investigator(s): 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 2 Goal 6 Water Quality Resource: No Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub R8B = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom Project Number: 209554 South Deschutes County Local Wetland Inventory Wetland Summary Sheet - Date(s) of Field Verification: 6/25/2010 Wetland Mapping Code: 32 Investigator(s): Alison Sigler, Sarah Hartung Size (acres): 1.4 Data Sheet Numbers: SP 45A Location Legal: T 20 S R 10 E S 26 BD Nearest Town: Three Rivers Other: Northwest of Meadow, on the west side of Latitude: 43.8096 Deschutes River Longitude: -121.4955 Basin: Deschutes River Soils Mapped Series: Not available Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Riverine Flow-Through Dominant Vegetation and Comments Cowardin Classification(s): PEMY, PSSC, R2UBH Vegetation: Shrubs: Alnus incana (Gray alder), Salix exigua (Narrowleaf willow), Herbs: Carex sp., Phalaris arundinacea (Reed canary grass) Comments: Off-site determination. Peninsula in bend of Deschutes River. A couple residences nearby but mainly upland forest in vicinity. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 3 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included adjoining open water. Percent (approx.) of the Wetland Visited: 0, viewed from opposite shoreline. Percent (approx.) of the AA Visited: 0 Month & Year of ORWAP Training Attended by Investigator(s): 8/2009 and 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 3 Goal 6 Water Quality Resource: No Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom • • Project Number: 209554 C~ C7 • South Deschutes County Local Wetland Inventory Wetland Summary Sheet - Date(s) of Field Verification: 6/25/2010 Wetland Mapping Code: 33 Investigator(s): Alison Sigler, Sarah Hartung Size (acres): 3.7 Data Sheet Numbers: SP 46A Location Legal: T 20 S R 10 E S 26 BD, CD Nearest Town: Three Rivers Other: South of Meadow, on the east side of Latitude: 43.8084 Deschutes River Longitude: -121.4953 Basin: Deschutes River Solis Mapped Series: Not available Hydrology Primary Hydrology Source(s): Flooding Hydro-geomorphic (HGM) Classification (s): Riverine Flow-Through Dominant Vegetation and Comments Cowardin Classification(s): PEMC, PFOC Vegetation: Herbs: Carex sp., (sedge), Poa sp., (grass), Juncus sp. (rush), Trees: Pinus contorts (Lodgepole Pine) Comments: Off-site determination. Wetland is part of an old oxbow of Deschutes River. A few residences nearby but mainly forest land. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 15 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included the off-site wetland to the south and adjoining open water in the Deschutes River. Percent (approx.) of the Wetland Visited: 0 Percent (approx.) of the AA Visited: 0 Month & Year of ORWAP Training Attended by Investigator(s): 8/2009 and 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 3 Goal 6 Water Quality Resource: No Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom Project Number: 209554 South Deschutes County Local Wetland Inventory - Wetland Summary Sheet - Date(s) of Field Verification: 6/24/2010 Wetland Mapping Code: 34 Investigator(s): Alison Sigler, Sarah Hartung Size (acres): 4.3 Data Sheet Numbers: SP 42A Location Legal: T 20 S R 20 E S 35 AA, BA Nearest Town: Three Rivers Other: West of Foster Rd, north and south of Gray Latitude: 43.8046 Wolf Longitude: -121.4956 Basin: Deschutes River ISoils Mapped Series: Not available Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Slope Valley Dominant Vegetation and Comments Cowardin Classification(s): PFOA Vegetation: Trees: Pinus contorta (Lodgepole pine), Shrubs: Rosa gymnocarpa (Dwarf rose), Salix exigua (narrowleaf willow), Herbs: Fragaria virginiana (Virginia strawberry), Trifolium repens (White clover) Comments: On-site determination. Wetland/Upland Mosaic due to relict oxbow with uneven terrain and pockets of upland vegetation. Wetland extends out of study area, two polygons united by "off-site" wetland area. Surrounded by forested land; south and higher elevation than old oxbow (Wetland 33). Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 9 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included off-site wetland area to the north. Percent (approx.) of the Wetland Visited: 5 Percent (approx.) of the AA Visited: 1 Month & Year of ORWAP Training Attended by Investigator(s): 8/2009 and 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 3 Goal 6 Water Quality Resource: No Wetland Classiflcatlon Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom E • Project Number: 209554 • C7 • South Deschutes County Local Wetland Inventory - Wetland Summary Sheet - Date(s) of Field Verification: 5/6/2010 Wetland Mapping Code: 35 Investigator(s): Alessandra Capretti, Adam Merrill Size (acres): 2.5 Data Sheet Numbers: SP 106 Location Legal: T 20 S R 10 E S 35 BB, CB Nearest Town: Three Rivers Other: Southeast of the intersection of Carrington and Latitude: 43.8007 Forest on the west side of Deschutes River Longitude: -121.5055 Basin: Deschutes River Soils Mapped Series: Not available Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Riverine Flow-Through I Dominant Vegetation and Comments Cowardin Classification(s): PEMC, R2UBH Vegetation: Shrubs: Salix geyeriana (Geyer willow), Herbs: Carex nebrascensis (Nebraska sedge), Carex aquatilis (Water sedge), Juncus balticus (Baltic rush) Comments: On-site determination. Residential waterfront along Deschutes River. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 4.5 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included adjoining open water. Percent (approx.) of the Wetland Visited: 5 Percent (approx.) of the AA Visited: 2 Month & Year of ORWAP Training Attended by Investigator(s): 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 2 Goal 6 Water Quality Resource: No Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom Project Number: 209554 South Deschutes County Local Wetland Inventory - Wetland Summary Sheet - Date(s) of Field Verification: 5/7/2010 Wetland Mapping Code: 36 Investigator(s): Alison Sigler, Rosemary Baker Size (acres): 2.4 Data Sheet Numbers: SP 43A Location Legal: T 20 S R 10 E S 35 CB, DBO Nearest Town: Three Rivers Other: Northeast of Mallard Dr, on west side of Latitude: 43.7990 Deschutes River Longitude: -121.5023 Basin: Deschutes River Soils Mapped Series: Not available Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Riverine Flow-Through Dominant Vegetation and Comments Cowardin Classification(s): PEMC, PSSC Vegetation: Shrubs: Salix exigua (narrowleaf willow), Herbs: Carex aquatilis (Water sedge) Comments: Off-site determination. Low-lying area along the Deschutes River. Low density residential, forest land. Oregon Rapid Wetland Assessment Protocol (ORWAP) 71 Approximate Size of the Assessment Area (AA) in acres: 5 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included adjoining open water. Percent (approx.) of the Wetland Visited: 0, viewed from opposite shoreline. Percent (approx.) of the AA Visited: 0 Month & Year of ORWAP Training Attended by Investigator(s): 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 2 Goal 6 Water Quality Resource: Yes Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom • Project Number: 209554 • • South Deschutes County Local Wetland Inventory - Wetland Summary Sheet - Date(s) of Field Verification: 5/6/2010 Wetland Mapping Code: 37 Investigator(s): Alessandra Capretti, Adam Merrill Size (acres): 1.9 Data Sheet Numbers: SP 107 Location Legal: T 20 S R 10 E S 35 AC, BC, CB, DB Nearest Town: Three Rivers Other: East of Mallard, on west side of Deschutes Latitude: 43.7978 River Longitude: -121.5029 Basin: Deschutes River ISoils Mapped Series: 29A: Cryaquolls, 0 to 3 percent slopes, 115A: Shanahan loamy coarse sand, low, 0 to 3 percent slopes, W: Water Hydrology Primary Hydrology Source(s): Flooding Hydro-geomorphic (HGM) Classification(s): Riverine Flow-Through Dominant Vegetation and Comments Cowardin Classification(s): PEMC, PSSC, R2UBH Vegetation: Shrubs: Salix geyeriana (Geyer willow), Herbs: Carex aquatilis (Water sedge), Carex nebrascensis (Nebraska sedge) Comments: On-site determination. Complex of low-lying wetland areas along the Deschutes River. Wetland extends outside of the study area. SP 107 is representative of wetland 37 although it is located outside of study area, it characterizes the same wetland. Two polygons united by "off-site" wetland area. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 14 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included adjoining open water, wetlands outside of study area, peninsula and island to the north. Percent (approx.) of the Wetland Visited: 5 Percent (approx.) of the AA Visited: 1 Month & Year of ORWAP Training Attended by Investigator(s): 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 2 Goal 6 Water Quality Resource: No Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom Project Number: 209554 South Deschutes County Local Wetland Inventory - Wetland Summary Sheet - Date(s) of Field Verification: 6/21/2010 Wetland Mapping Code: 38 Investigator(s): Sarah Hartung, Alison Sigler Size (acres): 2.3 Data Sheet Numbers: SP 7A Location Legal: T 20 S R 10 E S 35 BC, AC Nearest Town: Three Rivers Other: South of Beaver Dr; east side of Deschutes Latitude: 43.7948 River Longitude: -121.5023 Basin: Deschutes River Solls Mapped Series: 29A: Cryaquolls, 0 to 3 percent slopes, W: Water Hydrology Primary Hydrology Source(s): Flooding Hydro-geomorphic (HGM) Classification(s): Riverine Flow-Through Dominant Vegetation and Comments Cowardin Classification(s): PEMH, R2UBH Vegetation: Trees: Pinus contorta (Lodgepole pine), Shrubs: Salix exigua (narrowleaf willow), Herbs: Juncus balticus (Baltic rush), Carex aquatilis (Water sedge) Comments: Off-site determination. Low-lying area along river; adjacent to national forest. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 5 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included adjoining open water. Percent (approx.) of the Wetland Visited: Percent (approx.) of the AA Visited: Month & Year of ORWAP Training Attended by Investigator(s): 8/2009 and 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 3 Goal 6 Water Quality Resource: No Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom • Ll E Project Number: 209554 • • E South Deschutes County Local Wetland Inventory - Wetland Summary Sheet - Date(s) of Field Verification: 5/6/2010 Wetland Mapping Code: 39 Investigator(s): Alessandra Capretti, Adam Merrill Size (acres): 1.8 Data Sheet Numbers: SP 108 Location Legal: T 20 S R 10 E S 35 BC, CC Nearest Town: Three Rivers Other: North of the end of Silver Fox, on the west side Latitude: 43.7945 of the Deschutes River Longitude: -121.5034 Basin: Deschutes River Soils Mapped Series: 29A Cryaquolls, 0 to 3 percents slopes, W: Water Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Riverine Flow-Through Dominant Vegetation and Comments Cowardin Classification(s): PSSC Vegetation: Trees: Pinus contorta (Lodgepole pine), Shrubs: Betula grandulosa (Resin birch), Herbs: Juncus balticus (Baltic rush), Carex aquatilis (Water sedge), Carex nebrascensis (Nebraska sedge) Comments: On-site determination. Undeveloped peninsula in bend of Deschutes River. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 6 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included adjoining open water and the east end of the wetland that extends off-site. Percent (approx.) of the Wetland Visited: 5 Percent (approx.) of the AA Visited: 1 Month & Year of ORWAP Training Attended by Investigator(s): 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 2 Goal 6 Water Quality Resource: No Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom Project Number: 209554 South Deschutes County Local Wetland Inventory - Wetland Summary Sheet - Date(s) of Field Verification: 5/6/2010 Wetland Mapping Code: 40 Investigator(s): Alessandra Capretti, Adam Merrill Size (acres): 3.5 Data Sheet Numbers: SP 109 Location Legal: T 20 S R 10 E S 35 BC, T 20 S R 10 E S 34 Nearest Town: Three Rivers AD, DD Latitude: 43.7947 Other: South of Mallard, east of Forest on west side of Longitude: -121.5082 Deschutes River Basin: Deschutes River Soils Mapped Series: 29A Cryaquolls, 0 to 3 percents slopes, W: Water Hydrology Primary Hydrology Source(s): Flooding Hydra-geomorphic (HGM) Classification(s): Riverine Flow-Through Dominant Vegetation and Comments Cowardin Classification(s): PEMC, PSSC Vegetation: Herbs: Carex nebrascensis (Nebraska sedge), Carex aquatilis (Water sedge) Comments: On-site determination. Low-lying area along the Deschutes River. Low density residential to the west. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 6 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included adjoining open water. Percent (approx.) of the Wetland Visited: 5 Percent (approx.) of the AA Visited: 1 Month & Year of ORWAP Training Attended by Investigator(s): 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 2 Goal 6 Water Quality Resource: No Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom • • • Project Number 209554 • • • South Deschutes County Local Wetland Inventory - Wetland Summary Sheet - Date(s) of Field Verification: 5/7/2010, 11/17/2010 Wetland Mapping Code: 41 Investigator(s): A. Capretti, A. Merrill, S. Hartung Size (acres): 34.0 Data Sheet Numbers: SP 113 Location Legal: T20 S R 10 E S 34 DD, T20 S R 10 E S 35 Nearest Town: Three Rivers BC, CC,T21SR10ES2B6 Latitude: 43.7892 Other: South of Mallard Dr, northwest of Silver Fox Dr Longitude: -121.5030 on east side of Deschutes River Basin: Deschutes River Soils Mapped Series: 29A: Cryaquolls, 0 to 3 percent slopes, 114C: Shanahan loamy coarse sand, 0 to 15 percent slopes, W: Water Hydrology Primary Hydrology Source(s): Flooding, seeps from forested hillside to the east, and overland flow. Roads in area often flooded in spring according to landowner information. Hydro-geomorphic (HGM) Classification(s): Riverine Flow-Through Dominant Vegetation and Comments Cowardin Classification(s): PEME, PSSE, PFOE Vegetation: Pinus contorta (Lodgepole pine), Salix geyeriana (Geyer willow), Herbs: Carex nebrascensis (Nebraska sedge), Carex aquatilis (Water sedge), Poa sp. (grass) Comments: On-site determination (41). Wetland/Upland Mosaic hummocks of slightly higher elevation and upland vegetation included in wetlands. A large island (included in wetland) in the Deschutes River created the excavation of a channel at the southeast end of the island. Portions of wetland are in a low-lying area at base of forested hill. Platted for residential development, but not fully built. Wetland includes previous DSL determination WD1994-0072. Three polgons assessed as one unit, all formerly united prior to excavation of cut-off channels. A log jam is obstructing the cut-off channel at the base of the northern polygon, according to nearby landowner information. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 39 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included adjoining open water in the Deschutes River. Percent (approx.) of the Wetland Visited: 2 Percent (approx.) of the AA Visited: 1 Month & Year of ORWAP Training Attended by Investigator(s): 8/2009 and 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 3 Goal 6 Water Quality Resource: No Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom Project Number: 209554 South Deschutes County Local Wetland Inventory - Wetland Summary Sheet - Date(s) of Field Verification: 5/6/2010 Wetland Mapping Code: 42 Investigator(s): A. Capretti, A. Merrill Size (acres): 34.8 Data Sheet Numbers: SP 110 Location Legal: T20 S R 10 E S 34 DD, T20 S R 10 E S 35 Nearest Town: Three Rivers BC, T 21 S R 10 E S 3 AA, T 21 S R 10 E 3 2 BB Latitude: 43.7917 Other: East of Forest Ln on the west side of Deschutes Longitude: -121.5096 River, includes large island Basin: Deschutes River Soils Mapped Series: 9A Cryaquolls, 0 to 3 percents slopes, W: Water Hydrology Primary Hydrology Source(s): Overland Flow Hydro-geomorphic (HGM) Classification(s): Riverine Flow-Through • Dominant Vegetation and Comments Cowardin Classification(s): PEMC, PSSC, PFOC, R2UBH . Vegetation: Shrubs: Salix exigua (narrowleaf willow), Herbs: Carex aquatilis (Water sedge), Carex nebrascensis (Nebraska sedge) Comments: On-site determination. Wetland/Upland Mosaic due to uneven terrain and dynamic floodplain conditions that have created uneven topography resulting in non-wetland/upland hummocks. Wetland includes large island formed by river meander. Four polygons assessed as one, united by a large oxbow west of Deschutes River main channel. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 45 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included adjoining open water and large island. Percent (approx.) of the Wetland Visited: 3 Percent (approx.) of the AA Visited: 1 Month & Year of ORWAP Training Attended by Investigator(s): 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 2 Goal 6 Water Quality Resource: Yes Wetland Classification Codes PFO = palustrine forested PS5 = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom • Project Number: 209554 C~ r~ • South Deschutes County Local Wetland Inventory - Wetland Summary Sheet - Date(s) of Field Verification: 5/7/2010, 11/17/2010 Wetland Mapping Code: 43a-e Investigator(s): A. Sigler, R. Baker, S. Hartung Size (acres): 32.3 Data Sheet Numbers: SP 114, 603, 604, 605, 606 Location Legal: T 21 S R 10 E S 3 AA, T 21 S R 10 E S 2 BB Nearest Town: Three Rivers Other: Northwest of Silver Fox Dr on east side of Latitude: 43.7873 Deschutes River Longitude: -121.5066 Basin: Deschutes River ISoils Mapped Series: 29A: Cryaquolls, 0 to 3 percent slopes, 144A: Sunriver sandy loam, 0 to 3 percent slopes, W: Water Hydrology Primary Hydrology Source(s): Groundwater, seeps from forested hillside to the east, and overland flow. Hydro-geomorphic (HGM) Classification(s): Slope Valley Dominant Vegetation and Comments Cowardin Classification(s): PEMA, PFOA, PFOE Vegetation: Pinus contorta (Lodgepole pine), Betula glandulosa (bog birch), Salix geyeriana (Geyer willow), Herbs: Carex aquatilis (Water sedge),Agrostis sp. (bentgrass), Poa sp. (bluegrass) Comments: On-site determination and review of previous delineations WD2001-0365, WD2007-0620 and WD2003-0034. Low lying area along the Deschutes River. Residential use adjacent to wetland. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 35 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included adjoining open water. Percent (approx.) of the Wetland Visited: 5 Percent (approx.) of the AA Visited: 2 Month & Year of ORWAP Training Attended by Investigator(s): 8/2009 and 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 5 Goal 6 Water Quality Resource: No Wetland Classiflcation Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom Project Number: 209554 South Deschutes County Local Wetland Inventory - Wetland Summary Sheet Date(s) of Field Verification: 5/6/2010 Wetland Mapping Code: 44 Investigator(s): John Gordon, Adam Merrill Size (acres): 12.3 Data Sheet Numbers: N/A Location Legal: T 21 S R 10 E S 3 AA, BA Nearest Town: Three Rivers Other: South of Forest Ln on the west side of Latitude: 43.7872 Deschutes River Longitude: -121.5124 Basin: Deschutes River ISoils Mapped Series: 29A: Cryaquolls, 0 to 3 percent slopes, W: Water Hydrology Primary Hydrology Source(s): Flooding Hydro-geomorphic (HGM) Classification(s): Riverine Flow-Through Dominant Vegetation and Comments Cowardin Classification(s): PEMC, PSSC, PFOC, R2UBH Vegetation: From aerial and landscape in vicinity: Salix sp. (willow), Herbs: Carex sp. (sedge) Comments: Off-site determination. No visual access. Low-lying area south of confluence of Fall River and Deschutes River. Mapped as occurring in two different drainages, but assessed as if in Deschutes River drainage Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 16 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included adjoining open water. Percent (approx.) of the Wetland Visited: 0 Percent (approx.) of the AA Visited: 0 Month & Year of ORWAP Training Attended by Investigator(s): 8/2009 and 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 3 Goal 6 Water Quality Resource: No Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom • • rI Project Number: 209554 • C, South Deschutes County Local Wetland Inventory - Wetland Summary Sheet - Date(s) of Field Verification: 5/6/2010 Wetland Mapping Code: 45 Investigator(s): Alessandra Capretti, Adam Merrill Size (acres): 21.0 Data Sheet Numbers: SP 112 Location Legal: T 21 S R 10 E S 3 BA, CA, DA Nearest Town: Three Rivers Other: West of Mule Deer and Red Bear, east side of Latitude: 43.7866 Deschutes River Longitude: -121.5143 Basin: Deschutes River Soils Mapped Series: 29A Cryaquolls, 0 to 3 percents slopes, W: Water, 144A: Sunriver sandy loam, 0 to 3 percent slopes Hydrology Primary Hydrology Source(s): Overland Flow Hydro-geomorphic (HGM) Classification(s): Riverine Flow-Through Dominant Vegetation and Comments Cowardin Classification(s): PEME, PSSC Vegetation: Salix geyeriana (Geyer willow), Herbs: Carex aquatilis (Water sedge), Agrostis sp. Comments: On-site determination. Wetland/Upland Mosaic includes an old oxbow and has upland hummocks throughout the wetland. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 25 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included adjoining open water. Percent (approx.) of the Wetland Visited: 5 Percent (approx.) of the AA Visited: 1 Month & Year of ORWAP Training Attended by Investigator(s): 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 2 Goal 6 Water Quality Resource: No Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom Project Number: 209554 South Deschutes County Local Wetland Inventory Wetland Summary Sheet - Date(s) of Field Verification: 6/24/2010 Wetland Mapping Code: 46 Investigator(s): Sarah Hartung, Alison Sigler Size (acres): 25.3 Data Sheet Numbers: SP 41A Location Legal: T 21 S R 10 E S 3 AB, DB, BA, DA, AC Nearest Town: Three Rivers Other: Northwest of Blacktail, west side of Deschutes Latitude: 43.7843 River, south of Fall River Longitude: -121.5163 Basin: Deschutes River ISoils Mapped Series: 29A Cryaquolls, 0 to 3 percent slopes, W: Water, 144A: Sunriver sandy loam, 0 to 3 percent slopes Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Riverine Flow-Through Dominant Vegetation and Comments Cowardin Classification(s): PEMC, PSSC, PFOC Vegetation: Shrubs: Alnus incana (Gray alder), Salix exigua (narrowleaf willow), Herbs: Carex aquatilis (Water sedge), Poa sp. (bluegrass) Comments: Off-site determination. Wetland/Upland Mosaic due to dynamic floodplain conditions that have created uneven topography resulting in non-wetland hummocks. Low-lying area along the Deschutes River. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 32 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included adjoining open water and island to the south. Percent (approx.) of the Wetland Visited: 0, viewed from opposite shoreline Percent (approx.) of the AA Visited: 0 Month & Year of ORWAP Training Attended by Investigator(s): 8/2009 and 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 3 Goal 6 Water Quality Resource: No Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom • • E Project Number: 209654 r~ E • South Deschutes County Local Wetland Inventory - Wetland Summary Sheet - Date(s) of Field Verification: 6/21/2010 Wetland Mapping Code: 47 Investigator(s): Sarah Hartung, Alison Sigler Size (acres): 2.8 Data Sheet Numbers: N/A Location Legal: T21 SR 10 E S 3 AC, BD Nearest Town: Three Rivers Other: Parallel to the intersection of White Tail Ln and Latitude: 43.7820 Silver Fox Dr on the west side of Deschutes River Longitude: -121.5173 Basin: Deschutes River ISoils Mapped Series: 29A Cryaquolls, 0 to 3 percents slopes, W: Water Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Riverine Flow-Through Dominant Vegetation and Comments Cowardin Classification(s): PEMC, PSSC Vegetation: From aerial and landscape in vicinity: Salix sp. (willow), Herbs: Carex sp. (sedge) Comments: Off-site determination with no visual access. Peninsula at bend in river. Wetland/Upland Mosaic due to uneven terrain. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 5 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included adjoining open water. Percent (approx.) of the Wetland Visited: 0 Percent (approx.) of the AA Visited: 0 Month & Year of ORWAP Training Attended by Investigator(s): 8/2009 and 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 3 Goal 6 Water Quality Resource: No Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom Project Number: 209554 South Deschutes County Local Wetland Inventory Wetland Summary Sheet - Date(s) of Field Verification: 5/6/2010 Wetland Mapping Code: 48 Investigator(s): Alessandra Capretti, Adam Merrill Size (acres): 27.4 Data Sheet Numbers: SP 111 Location Legal: T 21 S R 10 E S 3 BD, CD, AC, CA Nearest Town: Three Rivers Other: Parallel to the intersection of White Tail Ln and Latitude: 43.7795 Silver Fox Dr on the east side of Deschutes River Longitude: -121.5162 Basin: Deschutes River ISoils Mapped Series: 9A Cryaquolls, 0 to 3 percents slopes, W: Water, 144A: Sunriver sandy loam, 0 to 3 percent slopes Hydrology Primary Hydrology Source(s): Flooding Hydro-geomorphic (HGM) Classification(s): Riverine Flow-Through Dominant Vegetation and Comments Cowardin Classification(s): PEME, PSSE Vegetation: Trees: Pinus contorta (Lodgepole pine), Shrubs: Salix geyeriana (Geyer willow), Herbs: Carex aquatilis (Water sedge) Comments: On-site determination. Wetland/Upland Mosaic due to hummocks. Low-lying area along the Deschutes River; a few residences to the south and east. Two polygons assessed as one, formerly united prior to excavation of a cut-off channel at east end of island. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 32 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included adjoining open water. Percent (approx.) of the Wetland Visited: 5 Percent (approx.) of the AA Visited: 1 Month & Year of ORWAP Training Attended by Investigator(s): 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 2 Goal 6 Water Quality Resource: No Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom • • • Project Number: 209554 • • South Deschutes County Local Wetland Inventory - Wetland Summary Sheet - Date(s) of Field Verification: 6/22/2010 Wetland Mapping Code: 49 Investigator(s): Alison Sigler, Sarah Hartung Size (acres): 1.5 Data Sheet Numbers: SP 8A Location Legal: T21 S R 10 E S 3 AD Nearest Town: Three Rivers Other: North of Big Buck Ln and east of Silver Fox Dr Latitude: 43.7801 Basin: Deschutes River Longitude: -121.5122 Soils Mapped Series: 29A Cryaquolls, 0 to 3 percents slopes, 144A: Sunriver sandy loam, 0 to 3 percent slopes Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Slope Valley I Dominant Vegetation and Comments Cowardin Classification(s): PFOY Vegetation: Trees: Pinus contorta (Lodgepole pine), Shrubs: Salix exigua (narrowleaf willow), Herbs: Poa sp. (bluegrass), Juncus sp. (rush) Comments: Off-site determination. Adjacent to low density residential use and forest land. Higher in elevation than Wetland 48. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 1.5 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA was the same size as the wetland. Percent (approx.) of the Wetland Visited: 0, viewed from right-of-way. Percent (approx.) of the AA Visited: 0 Month & Year of ORWAP Training Attended by Investigator(s): 8/2009 and 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 3 Goal 6 Water Quality Resource: No Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom Project Number: 209554 South Deschutes County Local Wetland Inventory - Wetland Summary Sheet - Date(s) of Field Verification: 6/22/2010 Wetland Mapping Code: 50a-c Investigator(s): Alison Sigler, Sarah Hartung Size (acres): 14.8 Data Sheet Numbers: SP 9A Location Legal: T 21 S R 10 E S 3 DD, T 21 S R 10 E S 2 CC, T Nearest Town: Three Rivers 21 S R 10 E S 10 AA Latitude: 43.7797 Other: South of Big Buck Ln, east and west of Caribou Longitude: -121.5108 Dr and north and south of Silver Fox Dr Basin: Deschutes River ISoils Mapped Series: 29A Cryaquolls, 0 to 3 percents slopes, 114C: Shanahan loamy coarse sand, 0 to 15 percent slopes Hydrology Primary Hydrology Source(s): Groundwater Hydra-geomorphic (HGM) Classification(s): Slope Valley Dominant Vegetation and Comments Cowardin Classification(s): PEMY, PFOY Vegetation: Trees: Pinus contorta (Lodgepole pine), Shrubs: Salix exigua (narrowleaf willow), Herbs: Poa sp., (bluegrass), Carex sp. (sedge) Comments: On-site determination. Wetland/Upland Mosaic with upland areas at about 10%, wetland ditched throughout site. At base of slope, a few residences in area and upland forest. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 14.8 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA was the same size as the wetland. Percent (approx.) of the Wetland Visited: 5 Percent (approx.) of the AA Visited: 1 Month & Year of ORWAP Training Attended by Investigator(s): 8/2009 and 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 3 Goal 6 Water Quality Resource: No Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom • Project Number: 209554 11 • South Deschutes County Local Wetland Inventory - Wetland Summary Sheet - Date(s) of Field Verification: 6/22/2010 Wetland Mapping Code: 51 Investigator(s): Alison Sigler, Sarah Hartung Size (acres): 3.4 Data Sheet Numbers: SP 12A Location Legal: T21 SR 10 E S 3 DD Nearest Town: Three Rivers Other: South of Fisher Ln and east of Silver Fox Dr Latitude: 43.7780 Basin: Deschutes River Longitude: -121.5086 Soils Mapped Series: 29A Cryaquolls, 0 to 3 percents slopes Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Slope Valley Dominant Vegetation and Comments Cowardin Classification(s): PEMY, PFOY Vegetation: Shrubs: Salix exigua (narrowleaf willow), Herbs: Juncus balticus (Baltic rush) Comments: On-site determination. At base of slope, a few residences in area and upland forest. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 3.4 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA was the same size as the wetland. Percent (approx.) of the Wetland Visited: 5 Percent (approx.) of the AA Visited: 1 Month & Year of ORWAP Training Attended by Investigator(s): 8/2009 and 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 3 Goal 6 Water Quality Resource: No Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom Project Number.' 209554 South Deschutes County Local Wetland Inventory Wetland Summary Sheet - Date(s) of Field Verification: 6/22/2010 Wetland Mapping Code: 52 Investigator(s): Alison Sigler, Sarah Hartung Size (acres): 2.4 Data Sheet Numbers: SP 11A Location Legal: T 21 S R 10 E S 3 AC, DC, CDO Nearest Town: Three Rivers Other: East of Moose Dr on the west side of the Latitude: 43.7781 Deschutes River Longitude: -121.5169 Basin: Deschutes River Soils Mapped Series: 29A Cryaquolls, 0 to 3 percents slopes, W: Water Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Riverine Flow-Through Dominant Vegetation and Comments Cowardin Classification(s): PEMY, PFOY Vegetation: Carex aquatilis (Water sedge) Comments: On-site determination. Narrow wetland along the river; low density residential Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 5 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included adjoining open water. Percent (approx.) of the Wetland Visited: 5 Percent (approx.) of the AA Visited: 1 Month & Year of ORWAP Training Attended by Investigator(s): 8/2009 and 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 3 Goal 6 Water Quality Resource: No Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom • rI Project Number: 209554 • r~ • South Deschutes County Local Wetland Inventory - Wetland Summary Sheet - Date(s) of Field Verification: 6/24/2010 Wetland Mapping Code: 53 Investigator(s): Alison Sigler, Sarah Hartung Size (acres): 4.2 Data Sheet Numbers: SP 40A Location Legal: T 21 S R 10 E S 3 CD, T 21 S R 10 E S 10 BA Nearest Town: Three Rivers Other: East of Lynx Dr on the west side of Deschutes Latitude: 43.7770 River Longitude: -121.5134 Basin: Deschutes River Soils Mapped Series: 29A Cryaquolis, 0 to 3 percents slopes, W: Water Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Riverine Flow-through Dominant Vegetation and Comments Cowardin Classification(s): PEME, PSSE Vegetation: Shrubs: Salix exigua (narrowleaf willow), Herbs: Carex aquatilis (Water sedge), Poa sp. (bluegrass) Comments: Off-site determination. Peninsula formed by river bend. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 8 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included adjoining open water. Percent (approx.) of the Wetland Visited: 0, viewed from opposite shoreline. Percent (approx.) of the AA Visited: 0 Month & Year of ORWAP Training Attended by Investigator(s): 8/2009 and 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 3 Goal 6 Water Quality Resource: No Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom Project Number: 209554 South Deschutes County Local Wetland Inventory - Wetland Summary Sheet - Date(s) of Field Verification: 6/22/2010 Wetland Mapping Code: 54 Investigator(s): Alison Sigler, Sarah Hartung Size (acres): 36.8 Data Sheet Numbers: SP 10A Location Legal: T21 S R 10 E S 3 DD, CD, T 21 S R 10 E S 10 Nearest Town: Three Rivers AN BA River Latitude: 43.7794 Other: Northwest of Bench Leg Rd and southwest of Longitude: -121.5119 Silver Fox Dr on east side of Deschutes River Basin: Deschutes River Soils Mapped Series: 29A Cryaquolls, 0 to 3 percents slopes, 114C: Shanahan loamy coarse sand, 0 to 15 percent slopes Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Slope Valley Dominant Vegetation and Comments .1 1 Cowardin Classification(s): PEMY, PSSY, PFOY Vegetation: Juncus effusus (Common rush), Juncus balticus (Baltic rush), Carex aquatilis (Water sedge) Comments: On-site determination and review of previous delineation WD2007-0398 and WD1995-0062. At base of forested slope along the river. Wetland/Upland Mosaic consisting of uneven, mostly forested with with some uneven terrain and pockets of upland vegetation interwined within the wetland. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 38 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included a portion of adjoining open water. Percent (approx.) of the Wetland Visited: 5 Percent (approx.) of the AA Visited: 1 Month & Year of ORWAP Training Attended by Investigator(s): 8/2009 and 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 3 Goal 6 Water Quality Resource: No Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom • t Project Number: 209554 • • South Deschutes County Local Wetland Inventory - Wetland Summary Sheet - Date(s) of Field Verification: 6/24/2010 Wetland Mapping Code: 55 Investigator(s): Alison Sigler, Sarah Hartung Size (acres): 4.0 Data Sheet Numbers: SP 33A Location Legal: T21 S R 10 E S 10 BA, CA, AB, DB Nearest Town: Three Rivers Other: Northeast of the end of LaPine State Recreation Latitude: 43.7725 Rd in the park on the west side of Deschutes River Longitude: -121.5164 Basin: Deschutes River Soils Mapped Series: 144A: Sunriver sandy loam, 0 to 3 percent slopes, W: Water Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Riverine Flow-through Dominant Vegetation and Comments Cowardin Classification(s): PEME, PSSE, PFOE Vegetation: Trees: Pinus contorta (Lodgepole pine), Shrubs: Salix exigua (Narrowleaf willow), Herbs: Juncus balticus (Baltic rush), Carex aquatilis (Water sedge) Comments: On-site determination. Wetland/Upland Mosaic due to dynamic floodplain conditions that have created uneven topography and resulting in non-wetland hummocks. Peninsula in bend of river, adjacent to forest land. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 6 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included adjoining open water. Percent (approx.) of the Wetland Visited: 0, viewed from opposite shoreline. Percent (approx.) of the AA Visited: 0 Month & Year of ORWAP Training Attended by Investigator(s): 8/2009 and 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 3 Goal 6 Water Quality Resource: No Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom Project Number: 209554 South Deschutes County Local Wetland Inventory - Wetland Summary Sheet - Date(s) of Field Verification: 6/24/2010 Wetland Mapping Code: 56 Investigator(s): Alison Sigler, Sarah Hartung Size (acres): 8.5 Data Sheet Numbers: SP 32A Location Legal: T 21 S R 10 E S 10 AB, BB, CB, T 21 S R 10 E Nearest Town: Three Rivers S 9 DA Latitude: 43.7717 Other: North of LaPine State Recreation Rd in the park Longitude: -121.5229 on the east side of Deschutes River Basin: Deschutes River Solls Mapped Series: 29A Cryaquolls, 0 to 3 percents slopes, 144A: Sunriver sandy loam, 0 to 3 percent slopes, W: Water Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Riverine Flow-Through Dominant Vegetation and Comments Cowardin Classification(s): PEME, PSSE Vegetation: Trees: Pinus contorta (Lodgepole pine), Shrubs: Salix exigua (Narrowleaf willow), Herbs: Juncus balticus (Baltic rush), Carex sp. Comments: Off-site determination. No soil excavation allowed in LaPine State Park. Wetland/Upland Mosaic located on an island in river bend with uneven topography and upland vegetation. Wetland includes shoreline to the east of the island. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 13 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included adjoining open water. Percent (approx.) of the Wetland Visited: 0 Percent (approx.) of the AA Visited: 1 Month & Year of ORWAP Training Attended by Investigator(s): 8/2009 and 512010 Number of Wetlands Assessed by Investigators Using ORWAP: 3 Goal 6 Water Quality Resource: No Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom • • Project Number 209554 rI 11 • South Deschutes County Local Wetland Inventory - Wetland Summary Sheet - Date(s) of Field Verification: 6/24/2010 Wetland Mapping Code: 57 Investigator(s): Alison Sigler, Sarah Hartung Size (acres): 0.9 Data Sheet Numbers: SP 31A Location Legal: T 21 S R 10 E S 10 CB Nearest Town: Three Rivers Other: North of LaPine State Recreation Rd in the park Latitude: 43.7703 on the east side of Deschutes River Longitude: -121.5249 Basin: Deschutes River Soils Mapped Series: 144A: Sunriver sandy loam, 0 to 3 percent slopes, W: Water Hydrology Primary Hydrology Source(s): Flooding Hydro-geomorphic (HGM) Classification (s). Riverine Flow-through Dominant Vegetation and Comments Cowardin Classification(s): PEME Vegetation: Shrubs: Salix exigua (Narrowleaf willow), Herbs: Carex sp., Veratrum californicum (California false hellebore) Comments: On-site determination but no digging was allowed in the park. Narrow wetland at base of steep slope in LaPine State Park. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 3 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included adjoining open water. Percent (approx.) of the Wetland Visited: 20 Percent (approx.) of the AA Visited: 10 Month & Year of ORWAP Training Attended by Investigator(s): 8/2009 and 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 3 Goal 6 Water Quality Resource: No Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom Project Number: 209554 South Deschutes County Local Wetland Inventory - Wetland Summary Sheet - Date(s) of Field Verification: 6/24/2010 Wetland Mapping Code: 58 Investigator(s): Alison Sigler, Sarah Hartung Size (acres): 0.9 Data Sheet Numbers: SP 35A Location Legal: T 21 S R 10 E S 10 BB, CB Nearest Town. Three Rivers Other: North of LaPine State Recreation Rd in the park Latitude: 43.7724 on the west side of the island in Deschutes River Longitude: -121.5247 Basin: Deschutes River Soils Mapped Series: 144A: Sunriver sandy loam, 0 to 3 percent slopes, W: Water Hydrology Primary Hydrology Source(s): Flooding Hydro-geomorphic (HGM) Classification(s): Riverine Flow-Through Dominant Vegetation and Comments Cowardin Classification(s): PEME Vegetation: Shrubs: Salix exigua (Narrowleaf willow), Herbs: Carex aquatilis (Water sedge) Comments: Off-site determination. Narrow fringe along an island in bend of river of state park. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 3 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included adjoining open water. Percent (approx.) of the Wetland Visited: 0 Percent (approx.) of the AA Visited: 1 Month $ Year of ORWAP Training Attended by Investigator(s): 8/2009 and 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 3 Goal 6 Water Quality Resource: No Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom C-l • Project Number: 209554 • • South Deschutes County Local Wetland Inventory - Wetland Summary Sheet - Date(s) of Field Verification., 6/24/2010 Wetland Mapping Code: 59 Investigator(s): Alison Sigler, Sarah Hartung Size (acres): 2.2 Data Sheet Numbers: SP 36A Location Legal: T21 S R 10 E S 101313 Nearest Town: Three Rivers Other: North of LaPine State Recreation Rd in the park Latitude: 43.7739 on the east side of Deschutes River Longitude: -121.5238 Basin: Deschutes River Soils Mapped Series: 144A: Sunriver sandy loam, 0 to 3 percent slopes, W: Water Hydrology Primary Hydrology Source(s): Flooding Hydro-geomorphic (HGM) Classification(s): Riverine Flow-Through Dominant Vegetation and Comments Cowardin Classification(s): PEME, PSSE Vegetation: Shrubs: Salix exigua (Narrowleaf willow), Pinus contorta (Lodgepole pine), Herbs: Smilacena stellata (Starry false lily of the valley), Carex aquatilis (Water sedge), Juncus balticus (Baltic rush) Comments: On-site determination but no digging was allowed in the park. Peninsula in Deschutes River. Wetland/Upland Mosaic due to uneven terrain. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 4 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included adjoining open water. Percent (approx.) of the Wetland Visited: 50 Percent (approx.) of the AA Visited: 10 Month & Year of ORWAP Training Attended by Investigator(s): 8/2009 and 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 3 Goal 6 Water Quality Resource: No Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom Project Number: 209554 South Deschutes County Local Wetland Inventory Wetland Summary Sheet - Date(s) of Field Verification: 6/24/2010 Wetland Mapping Code: 60 Investigator(s): Alison Sigler, Sarah Hartung Size (acres): 3.9 Data Sheet Numbers: SP 37A Location Legal: T21 S R 10 E S 10 BB, T21 S R 10 E S 9 AA Nearest Town: Three Rivers Other: Southwest of the end of Mountain Sheep Ln in Latitude: 43.7749 LaPine State Park on the north side of Deschutes River Longitude: -121.5254 Basin: Deschutes River Soils Mapped Series: 144A: Sunriver sandy loam, 0 to 3 percent slopes, W: Water Hydrology Primary Hydrology Source(s): Flooding Hydro-geomorphic (HGM) Classification(s): Riverine Flow-Through Dominant Vegetation and Comments Cowardin Classification(s): PEME, PFOE, R2UBH Vegetation: Trees: Pinus contorta (Lodgepole pine), Shrubs: Salix exigua (Narrowleaf willow), Herbs: Carex sp., Juncus balticus (Baltic rush) Comments: Off-site determination. Low-lying area along the Deschutes River; includes small island to the east. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 6 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included adjoining open water. Percent (approx.) of the Wetland Visited: 0, viewed from opposite shoreline. Percent (approx.) of the AA Visited: 1 Month & Year of ORWAP Training Attended by Investigator(s): 8/2009 and 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 3 Goal 6 Water Quality Resource: No Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom 11 • Project Number: 209554 r~ u • South Deschutes County Local Wetland Inventory - Wetland Summary Sheet - Date(s) of Field Verification: 6/24/2010 Wetland Mapping Code: 61 Investigator(s): Alison Sigler, Sarah Hartung Size (acres): 2.1 Data Sheet Numbers: SP 38A Location Legal: T 21 S R 10 E S 9 AA, T 21 S R 10 E S 4 DD Nearest Town: Three Rivers Other: North of LaPine State Recreation Rd in the park Latitude: 43.7755 on the east side of Deschutes River Longitude: -121.5301 Basin: Deschutes River Soils Mapped Series: 14C: Shanahan loamy coarse sand, 0 to 15 percent slopes, W: Water Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Riverine Flow-Through Dominant Vegetation and Comments Cowardin Classification(s): PEME, PSSE, PFOE Vegetation: Trees: Pinus contorts (Lodgepole pine), Shrubs: Salix exigua (Narrowleaf willow), Herbs: Carex sp. Comments: On-site determination but no digging was allowed in the state park. Peninsula in bend of river. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 3 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included adjoining open water. Percent (approx.) of the Wetland Visited: 50 Percent (approx.) of the AA Visited: 10 Month & Year of ORWAP Training Attended by Investigator(s): 8/2009 and 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 3 Goal 6 Water Quality Resource: No Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom Project Number: 209554 South Deschutes County Local Wetland Inventory Wetland Summary Sheet - Date(s) of Field Verification: 6/24/2010 Wetland Mapping Code: 62 Investigator(s): Alison Sigler, Sarah Hartung Size (acres): 3.1 Data Sheet Numbers: SP 39A Location Legal: 21 S R 10 E S 9 AA Nearest Town: Three Rivers Other: West of LaPine State Recreation Rd in the state Latitude: 43.7742 park on the west side of Deschutes River Longitude: -121.5299 Basin: Deschutes River ISolls Mapped Series: 144A: Sunriver sandy loam, 0 to 3 percent slopes, W: Water Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Riverine Flow-Through Dominant Vegetation and Comments Cowardin Classification(s): PEME, PSSE, PFOE Vegetation: Trees: Pinus contorta (Lodgepole pine), Shrubs: Salix exigua (Narrowleaf willow), Herbs: Carex aquatilis (Water sedge), Juncus balticus (Baltic rush) Comments: Off-site determination. Wetland/Upland Mosaic has dynamic floodplain conditions that have created uneven topography resulting in non-wetland hummocks. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 5 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included adjoining open water. Percent (approx.) of the Wetland Visited: 0 Percent (approx.) of the AA Visited: 0 Month & Year of ORWAP Training Attended by Investigator(s): 8/2009 and 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 3 Goal 6 Water Quality Resource: No Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom • • Project Number: 209554 11 • South Deschutes County Local Wetland Inventory - Wetland Summary Sheet - Date(s) of Field Verification: 5/6/2010 Wetland Mapping Code: 63 Investigator(s): John Gordon, Adam Merrill Size (acres): 10.4 Data Sheet Numbers: SP 104 Location Legal: T20 S R 10 E S 34 CC, DC, T21 S R 10 E S 3 Nearest Town: Three Rivers AB,DB,T21 SR10ES3BA Latitude: 43.7921 Other: South of Forest Ln, east of FS Road 4360; Longitude: -121.5196 along Fall River near confluence with Deschutes River Basin: Deschutes River Soils Mapped Series: 29A: Cryaquolls, 0 to 3 percent slopes, 115A: Shanahan loamy coarse sand, low, 0 to 3 percent slopes Hydrology Primary Hydrology Source(s): Flooding Hydro-geomorphic (HGM) Classification(s): Riverine Flow-Through Dominant Vegetation and Comments Cowardin Classification(s): PSSC, PFOC Vegetation: Trees: Pinus contorta (Lodgepole pine), Shrubs: Salix geyeriana (Geyer willow), Betula glandulosa (Resin birch), Herbs: Carex aquatilis (Water sedge) Comments: On-site determination. Wetland/Upland Mosaic due to dynamic floodplain conditions that have created uneven topography resulting in non-wetland hummocks. Complex of wetland on both sides of the Fall River; adjacent to undeveloped forest land. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 15 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included adjoining open water of the Fall River, Percent (approx.) of the Wetland Visited: 5 Percent (approx.) of the AA Visited: 1 Month S Year of ORWAP Training Attended by Investigator(s): 8/2009 and 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 3 Goal 6 Water Quality Resource: Yes Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom Project Number. 209554 South Deschutes County Local Wetland Inventory - Wetland Summary Sheet - Date(s) of Field Verification: 5/6/2010 Wetland Mapping Code: 64 Investigator(s): John Gordon Size (acres): 2.0 Data Sheet Numbers: SP 400 Location Legal: T20 S R 10 E S 34 DC, T21 S R 10 E S 3 AB Nearest Town: Three Rivers Other: West of Forest Ln on the Fall River Latitude: 43.7908 Basin: Deschutes River Longitude: -121.5198 Soils Mapped Series: 29A: Cryaquolls, 0 to 3 percent slopes, 144A: Sunriver sandy loam, 0 to 3 percent slopes Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Riverine Impounding Dominant Vegetation and Comments Cowardin Classification(s): PEMC, PSSC Vegetation: Trees: Pinus contorta (Lodgepole pine), Shrubs: Salix geyeriana (Geyer willow), Betula glandulosa (Resin birch), Herbs: Carex aquatilis (Water sedge) Comments: On-site determination. Old oxbow of Fall River adjacent to undeveloped forest land. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 2.0 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included adjoining open water. Percent (approx.) of the Wetland Visited: 10 Percent (approx.) of the AA Visited: 2 Month & Year of ORWAP Training Attended by Investigator(s): 8/2009 and 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 2 Goal 6 Water Quality Resource: Yes Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom • • Project Number: 209554 • C~ E South Deschutes County Local Wetland Inventory - Wetland Summary Sheet - Date(s) of Field Verification: 5/5/2010 Wetland Mapping Code: 65 Investigator(s): John Gordon, Adam Merrill Size (acres): 0.7 Data Sheet Numbers: N/A Location Legal: T20 S R 10 E S 34 BC Nearest Town: Three Rivers Other: East of FS Road 4360 on the Fall River Latitude: 43.7961 Basin: Deschutes River Longitude: -121.5260 Soils Mapped Series: 29A: Cryaquolls, 0 to 3 percent slopes, W: Water Hydrology Primary Hydrology Source(s): Flooding Hydro-geomorphic (HGM) Classification(s): Riverine Flow-Through Dominant Vegetation and Comments Cowardin Classification(s): PSSC Vegetation: Trees: Pinus contorta (Lodgepole pine), Shrubs: Salix geyeriana (Geyer willow), Betula glandulosa (Resin birch), Herbs: Carex sp. (sedge) Comments: Off-site determination. Low-lying area along undeveloped peninsula in the Fall River. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 1 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included adjoining open water in the Fall River. Percent (approx.) of the Wetland Visited: 0 Percent (approx.) of the AA Visited: 0 Month & Year of ORWAP Training Attended by Investigator(s): 8/2009 and 512010 Number of Wetlands Assessed by Investigators Using ORWAP: 3 Goal 6 Water Quality Resource: Yes Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom Project Number: 209554 South Deschutes County Local Wetland Inventory - Wetland Summary Sheet - Date(s) of Field Verification: 5/5/2010 Wetland Mapping Code: 66 Investigator(s): John Gordon, Adam Merrill Size (acres): 1.4 Data Sheet Numbers: N/A Location Legal: T 20 S R 10 E S 34 ACO Nearest Town: Three Rivers Other: East of FS Road 4360 on the north bank of the Latitude: 43.7957 Fall River Longitude: -121.5266 Basin: Deschutes River Soils Mapped Series: 29A Cryaquolls, 0 to 3 percents slopes, 115A: Shanahan loamy coarse sand, low, 0 to 3 percent slopes Hydrology Primary Hydrology Source(s): Flooding Hydro-geomorphic (HGM) Classification(s): Riverine Flow-Through Dominant Vegetation and Comments Cowardin Classification(s): PSSC Vegetation: Trees: Pinus contorta (Lodgepole pine), Shrubs: Salix geyeriana (Geyer willow), Betula glandulosa (Resin birch), Herbs: Carex sp. (sedge) Comments: On-site determination. Adjacent to undeveloped forest land, signage in area indicates public access is allowed. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 2 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included adjoining open water in the Fall River. Percent (approx.) of the Wetland Visited: 1 Percent (approx.) of the AA Visited: 1 Month R Year of ORWAP Training Attended by Investigator(s): 8/2009 and 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 3 Goal 6 Water Quality Resource: Yes Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom • • C, Project Number: 209554 rI • South Deschutes County Local Wetland Inventory Wetland Summary Sheet - Date(s) of Field Verification: 5/5/2010 Wetland Mapping Code: 67 Investigator(s): John Gordon, Adam Merrill Size (acres): 0.8 Data Sheet Numbers: N/A Location Legal: T 20 S R 10 E S 33 AD, DD Nearest Town: Three Rivers Other: East of FS Road 4360 on the Fall River Latitude: 43.7932 Basin: Deschutes River Longitude: -121.5288 Soils Mapped Series: 29A: Cryaquolls, 0 to 3 percent slopes, W: Water Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Riverine Flow-Through Dominant Vegetation and Comments Cowardin Classification(s): PFOC Vegetation: Trees: Pinus contorta (Lodgepole pine), Shrubs: Salix geyeriana (Geyer willow), Betula glandulosa (Resin birch), Herbs: Carex sp. (sedge) Comments: Off-site determination. Peninsula in Fall River adjacent to undeveloped forest land. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 1.5 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included adjoining open water. Percent (approx.) of the Wetland Visited: 0 Percent (approx.) of the AA Visited: 0 Month & Year of ORWAP Training Attended by Investigator(s): 8/2009 and 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 3 Goal 6 Water Quality Resource: Yes Wetland Classification Codes PFO = palustrine forested PS5 = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom Project Number: 209554 South Deschutes County Local Wetland Inventory Wetland Summary Sheet - Date(s) of Field Verification: 5/5/2010 Wetland Mapping Code: 68 Investigator(s): John Gordon, Adam Merrill Size (acres): 0.3 Data Sheet Numbers: N/A Location Legal: T 20 S R 10 E S 33 AD, DDO Nearest Town: Three Rivers Other: East of FS Road 4360, south side of Fall River Latitude: 43.7939 Basin: Deschutes River Longitude: -121.5295 Soils Mapped Series: 29A: Cryaquolls, 0 to 3 percent slopes, W: Water Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Riverine Flow-Through Dominant Vegetation and Comments Cowardin Classification(s): PSSC Vegetation: Trees: Pinus contorta (Lodgepole pine), Shrubs: Salix geyeriana (Geyer willow), Betula glandulosa (Resin birch), Herbs: Carex sp. (sedge) Comments: Off-site determination. Narrow wetland along the Fall River; undeveloped forest land. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 0.5 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included adjoining open water. Percent (approx.) of the Wetland Visited: 0 Percent (approx.) of the AA Visited: 0 Month & Year of ORWAP Training Attended by Investigator(s): 8/2009 and 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 3 Goal 6 Water Quality Resource: Yes Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom • • r~ u Project Number: 209554 • South Deschutes County Local Wetland Inventory - Wetland Summary Sheet Date(s) of Field Verification: 5/4/2010 Wetland Mapping Code: 69 Investigator(s): John Gordon, Adam Merrill Size (acres): 39.1 Data Sheet Numbers: SP 103 Location Legal: T 20 S R 10 E 33 BD, CD, DD, T 20 S R 10 E S Nearest Town: Three Rivers 33AC,BC,CC,DC,T20SR10ES33CBT20SR 10 E S 33 CB, T 20 S R 10 E S 32 DA, T 20 S R 10 E Latitude: 43.7934 S 32 AD, BD, CD, DD. Longitude: -121.5352 Other: South of S Century Dr, mostly east of FS Road 4360 on both sides of the Fall River Basin: Deschutes River Soils Mapped Series: 29A: Cryaquolls, 0 to 3 percent slopes, 115A: Shanahan loamy coarse sand, low, 0 to 3 percent slopes, 144A: Sunriver sandy loam, 0 to 3 percent slopes, W: Water Hydrology Primary Hydrology Source(s): Flooding Hydro-geomorphic (HGM) Classification (s): Riverine Flow-Through Dominant Vegetation and Comments Cowardin Classification(s): PEMC, PSSC, PSSF, PFOC, R2UBH Vegetation: Trees: Pinus contorts (Lodgepole pine), Shrubs: Salix geyeriana (Geyer willow), Betula grandulosa (Resin birch), Herbs: Carex aquatilis (Water sedge), Juncus ensifolius (Swordleaf rush) Comments: On-site determination. Wetland/Upland Mosaic due to dynamic floodplain conditions that have created uneven topography resulting in non-wetland hummocks. Signage in area indicates public access allowed. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 60 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included adjoining open water in the Fall River. Percent (approx.) of the Wetland Visited: a 1 Percent (approx.) of the AA Visited: < 1 Month & Year of ORWAP Training Attended by Investigator(s): 8/2009 and 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 3 Goal 6 Water Quality Resource: Yes Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom Project Number: 209554 South Deschutes County Local Wetland Inventory - Wetland Summary Sheet - Date(s) of Field Verification: 5/3/2010 Wetland Mapping Code: 70 Investigator(s): Alison Sigler, Sarah Hartung Size (acres): 0.6 Data Sheet Numbers: SP 2 Location Legal: T 20 S R 10 S 31 BD Nearest Town: Three Rivers Other: South of South Century Dr, northeast of the fish Latitude: 43.7978 hatchery on the north bank of a side channel of the Fall Longitude: -121.5722 River Basin: Deschutes River Soils Mapped Series: 115A: Shanahan loamy coarse sand, low, 0 to 3 percent slopes Hydrology Primary Hydrology Source(s): Overland Flow Hydro-geomorphic (HGM) Classification(s): Riverine Flow-Through Dominant Vegetation and Comments Cowardin Classification(s): PSSF Vegetation: Trees: Salix sp., Herbs: Carex aquatilis (Water sedge) Comments: On-site determination. Low-lying area at base of slope along a side channel of Fall River. Side channel modified for fish hatchery operations. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 1 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included adjoining open water in side channel of Fall River. Percent (approx.) of the Wetland Visited: 50 Percent (approx.) of the AA Visited: 40 Month & Year of ORWAP Training Attended by Investigator(s): 8/2009 and 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 3 Goal 6 Water Quality Resource: No Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom is E Project Number: 209554 • • South Deschutes County Local Wetland Inventory - Wetland Summary Sheet - Date(s) of Field Verification: 5/3/2010 Wetland Mapping Code: 71a-b Investigator(s): Alison Sigler, Rosemary Baker Size (acres): 0.5 Data Sheet Numbers: SP 4 Location Legal: T 20 S R 10 E S 31 BC, CC Nearest Town: Three Rivers Other: North and south of S Century Dr on Indian Latitude: 43.7950 Creek Longitude: -121.5856 Basin: Deschutes River Soils Mapped Series: 114C: Shanahan loamy coarse sand, 0 to 15 percent slopes Hydrology Primary Hydrology Source(s): Overland Flow Hydro-geomorphic (HGM) Classification(s): Riverine Flow-Through Dominant Vegetation and Comments Cowardin Classification(s): PEMH Vegetation: Herbs: Carex aquatilis (Water sedge), Salix sp., Poa sp., Fragaria virginiana (Virginia strawberry) Comments: On-site determination and review of previous DSL delineation WD2004-0061. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 0.5 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA was the same size as the wetland. Percent (approx.) of the Wetland Visited: 10 Percent (approx.) of the AA Visited: 10 Month & Year of ORWAP Training Attended by Investigator(s): 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 2 Goal 6 Water Quality Resource: No Wetland Classification Codes PFO = paiustrine forested PSS = paiustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = paiustrine open water RUB = riverine unconsolidated bottom Project Number: 209554 South Deschutes County Local Wetland Inventory Wetland Summary Sheet - Date(s) of Field Verification: 5/3/2010 Wetland Mapping Code: 72 Investigator(s): Alison Sigler, Sarah Hartung Size (acres): 0.9 Data Sheet Numbers: SP 1 Location Legal: T21 S R 9 E S 23 AA, BA Nearest Town: Three Rivers Other: West of Kokanee Way on the east side of Latitude: 43.7434 Deschutes River; Pringle Falls; downstream from Longitude: -121.6076 Burgess Rd Bridge Basin: Deschutes River Soils Mapped Series: Not available Hydrology Primary Hydrology Source(s): Overland Flow Hydro-geomorphic (HGM) Classification(s): Riverine Flow-Through Dominant Vegetation and Comments Cowardin Classification(s): PSSF Vegetation: Herbs: Juncus effusus (Common rush), Poa palustris (Fowl bluegrass) Comments: On-site determination. Braided side channels of upper Deschutes River through wetland; surrounded by small housing development. Wetland/Upland Mosaic located within and near stream channel where hummocks with upland vegetation are located throughout the wetland. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 2 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included adjoining open water. Percent (approx.) of the Wetland Visited: 50 Percent (approx.) of the AA Visited: 40 Month & Year of ORWAP Training Attended by Investigator(s): 8/2009 and 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 3 Goal 6 Water Quality Resource: No Wetland Classlflcation Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom • is Project Number: 209554 South Deschutes County Local Wetland Inventory - Wetland Summary Sheet - Date(s) of Field Verification: 5/6/2010 Wetland Mapping Code: 73 Investigator(s): Sarah Hartung, Aaron Booy Size (acres): 46.8 Data Sheet Numbers: SP 217 Location Legal: T20 S R 11 E S 18 AD, DD, T20 S R 11 E S Nearest Town: Three Rivers 17 BC, CC,T20SR11 ES 19 AA,T20SR11 ES 20 BB Latitude: 43.8373 Other: East of Hashknife Rd, west of School House Longitude: -121.4482 Rd, Little Deschutes River, north of bridge Basin: Deschutes River Soils Mapped Series: 29A: Cryaquolls, 0 to 3 percent slopes, 114C: Shanahan loamy coarse sand, 0 to 15 percent slopes, 144A: Sunriver sandy loam, 0 to 3 percent slopes, W: Water Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Riverine Flow-Through Dominant Vegetation and Comments Cowardin Classification(s): PEME, PSSE, PFOE, R2UBH Vegetation: Shrubs: Salix geyeriana (Geyer willow), Herbs: Carex aquatilis (Water sedge) Comments: Off-site determination. Wetland/Upland Mosaic due to dynamic floodplain conditions that have created uneven topography resulting in non-wetland hummocks. Wetland is within an exclusive, low density residential development. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 55 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included adjoining open water. Percent (approx.) of the Wetland Visited: 2 Percent (approx.) of the AA Visited: < 1 Month & Year of ORWAP Training Attended by Investigator(s): 8/2009 and 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 3 Goal 6 Water Quality Resource: No Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom Project Number: 209554 South Deschutes County Local Wetland Inventory Wetland Summary Sheet - Date(s) of Field Verification: 5/6/2010 Wetland Mapping Code: 74a-c Investigator(s): Sarah Hartung, Aaron Booy Size (acres): 94.9 Data Sheet Numbers: SP 218 Location Legal: T 20 S R 11 E S 18 AD, DD, T 20 S R 11 ES Nearest Town: Three Rivers 17 BC, CC, T 20 S R 11 E S 19 AA, T 20 S R 11 E S Latitude: 43.8261 20 BB Other: East of Hashknife Rd, west of School House Longitude: -121.4453 Rd, Little Deschutes River Basin: Deschutes River Soils Mapped Series: 29A: Cryaquolls, 0 to 3 percent slopes, 114C: Shanahan loamy coarse sand, 0 to 15 percent slopes, 144A: Sunriver sandy loam, 0 to 3 percent slopes, W: Water Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Riverine Flow-Through Dominant Vegetation and Comments Cowardin Classification(s): PABF, PEME, PSSE, PFOE Vegetation: Shrubs: Salix geyeriana (Geyer willow), Herbs: Carex aquatilis (Water sedge) Comments: Off-site determination. Wetland/Upland Mosaic due to dynamic floodplain conditions that have created uneven topography resulting in non-wetland hummocks. Wetland along private camping facility; undeveloped land. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 115 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included adjoining open water in the Little Deschutes River. Percent (approx.) of the Wetland Visited: 1 Percent (approx.) of the AA Visited: <1 Month S Year of ORWAP Training Attended by Investigator(s): 8/2009 and 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 3 Goal 6 Water Quality Resource: No Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom • • Project Number: 209554 • • • South Deschutes County Local Wetland Inventory - Wetland Summary Sheet - Date(s) of Field Verification: 5/7/2010 Wetland Mapping Code: 75 Investigator(s): Sarah Hartung, Aaron Booy Size (acres): 0.7 Data Sheet Numbers: N/A Location Legal: T 20 S R 11 E S 19 BD Nearest Town: Three Rivers Other: North of S Century Dr, east of Snow Good Rd Latitude: 43.8 and west of the Little Deschutes River Longitude: -121.4 Basin: Deschutes River Soils Mapped Series: 144A: Sunriver sandy loam, 0 to 3 percent slopes Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Depressional Closed Nonpermanently Flooded. Dominant Vegetation and Comments Cowardin Classification(s): PEME Vegetation: Herbaceous plants (unknown species) Comments: Off-site determination. No visual access. In private camp facility; undeveloped forest land. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 0.7 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA was the same size as the wetland. Percent (approx.) of the Wetland Visited: 0 Percent (approx.) of the AA Visited: 0 Month & Year of ORWAP Training Attended by Investigator(s): 8/2009 and 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 3 Goal 6 Water Quality Resource: Yes Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom Project Number: 209554 South Deschutes County Local Wetland Inventory - Wetland Summary Sheet - Date(s) of Field Verification: 5/6/2010 Wetland Mapping Code: 76 Investigator(s): Sarah Hartung, Aaron Booy Size (acres): 72.7 Data Sheet Numbers: 5P 402 Location Legal: T20 S R 11 E S 30 AA, BA, CA, DA, T20 S R Nearest Town: Three Rivers 11 E S 19 DD, CD, T 20 S R 11 E S 30 AD, BD, CD Latitude: 43.8169 Other: East of Lazy River Rd, south of S Century Rd, Longitude: -121.4514 west of Huntington Rd on the Little Deschutes River Basin: Deschutes River Solls Mapped Series: 29A: Cryaquolls, 0 to 3 percent slopes, 115A:Shanahan loamy coarse sand, low, 0 to 3 percent slopes Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Riverine Flow-Through Dominant Vegetation and Comments Cowardin Classification(s): PABF, PEME, PSSE, PFOE Vegetation: Shrubs: Salix geyeriana (Geyer willow), Herbs: Carex aquatilis (Water sedge), Carex nebrascensis (Nebraska sedge) Comments: On-site determination of previous DSL delineations WD2009-0454, WD1993-0251. Wetland/Upland Mosaic due to dynamic floodplain conditions that have created uneven topography resulting in non-wetland hummocks. Wetland located in low-density residential area mixed with natural land. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 80 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included adjoining open water. Percent (approx.) of the Wetland Visited: 1 Percent (approx.) of the AA Visited: a 1 Month & Year of ORWAP Training Attended by Investigator(s): 8/2009 and 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 3 Goal 6 Water Quality Resource: No Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom • E Project Number: 209554 • C7 • South Deschutes County Local Wetland Inventory - Wetland Summary Sheet - Date(s) of Field Verification: 5/7/2010 Wetland Mapping Code: 77 Investigator(s): Sarah Hartung, Aaron Booy Size (acres): 23.4 Data Sheet Numbers: SP 223 Location Legal: T20 S R 11 E S 31 BA, AA, CA, T20 S R 11 E Nearest Town: Three Rivers S 30 BD, DD Latitude: 43.8033 Other: East of Lazy River Rd, northeast of Log Bridge Longitude: -121.4538 Rd, west of Huntington Rd Basin: Deschutes River Soils Mapped Series: 29A: Cryaquolls, 0 to 3 percent slopes, 115A:Shanahan loamy coarse sand, low, 0 to 3 percent slopes Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Riverine Flow-Through Dominant Vegetation and Comments Cowardin Classification(s): PABF, PEME, PSSE, PFOE Vegetation: Shrubs: Salix geyeriana (Geyer willow), Herbs: Carex aquatilis (Water sedge), Carex nebrascensis (Nebraska sedge) Comments: On-site determination and review of previous DSL delineation WD2002-0612. Wetland/Upland Mosaic due to due to dynamic floodplain conditions that have created uneven topography resulting in non-wetland hummocks. Wetland located in rural residential area along the Little Deschutes River. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 28 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included adjoining open water. Percent (approx.) of the Wetland Visited: 1 Percent (approx.) of the AA Visited: < 1 Month & Year of ORWAP Training Attended by Investigator(s): 8/2009 and 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 3 Goal 6 Water Quality Resource: No Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom Project Number: 209554 South Deschutes County Local Wetland Inventory Wetland Summary Sheet - Date(s) of Field Verification: 517/2010 Wetland Mapping Code: 78 Investigator(s): Sarah Hartung, Aaron Booy Size (acres): 0.5 Data Sheet Numbers: SP 221 Location Legal: T 20 S R 11 E S 31 AB Nearest Town: Three Rivers Other: North of Lazy River Dr, south of Lodgepole Ln Latitude: 43.8016 and east of JackPine Wy Longitude: -121.4593 Basin: Deschutes River Soils Mapped Series: 144A: Sunriver sandy loam, 0 to 3 percent slopes Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Slope Valley Dominant Vegetation and Comments Cowardin Classification(s): PEMB Vegetation: Shrubs: Salix geyeriana (Geyer willow), Herbs: Carex aquatilis (Water sedge) Comments: Off-site determination. Rural residential area. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 0.5 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. Percent (approx.) of the Wetland Visited: 0 Percent (approx.) of the AA Visited: 0 Month & Year of ORWAP Training Attended by Investigator(s): 8/2009 and 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 3 Goal 6 Water Quality Resource: No Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom • • rI Project Number: 209554 r~ C South Deschutes County Local Wetland Inventory - Wetland Summary Sheet Date(s) of Field Verification: 5/7/2010 Wetland Mapping Code: 79 Investigator(s): John Gordon Size (acres): 142.2 Data Sheet Numbers: SP 404 Location Legal: T 20 S R 11 E S 31 BD, CA, AC, BC, CC, DC, T Nearest Town: Three Rivers 21 SR11 E S 6 AB, BB, CB, T 21 SR10ES1 DAT 21 S R 11 E S 6 BC. Latitude: 43.7895 Other: :West of Huntington Rd, south of Old Bridge Rd Longitude: -121.4623 on the Little Deschutes River Basin: Deschutes River Soils Mapped Series: 29A: Cryaquolls, 0 to 3 percent slopes, 115A:Shanahan loamy coarse sand, low, 0 to 3 percent slopes, 144A: Sunriver sandy loam, 0 to 3 percent slopes Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Riverine Flow-Through Dominant Vegetation and Comments Cowardin Classification(s): PABF, PEME, PSSE, PFOE Vegetation: Shrubs: Salix geyeriana (Geyer willow), Herbs: Carex aquatilis (Water sedge) Comments: On-site determination. Wetland/Upland Mosaic due to dynamic floodplain conditions that have created uneven topography resulting in non-wetland hummocks. Wetland includes DSL determination WD2009-0055. Wetland is in rural residential area and undeveloped forest land along the Little Deschutes River. Large wetland on both side of Little Deschutes River assessed as one despite occuring in two USGS sub-watersheds, Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 155 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included adjoining open water. Percent (approx.) of the Wetland Visited: ¢ 1 Percent (approx.) of the AA Visited: < 1 Month & Year of ORWAP Training Attended by Investigator(s): 8/2009 and 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 2 Goal 6 Water Quality Resource: No Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom Project Number: 209554 South Deschutes County Local Wetland Inventory Wetland Summary Sheet Date(s) of Field Verification: 6/22/2010 Wetland Mapping Code: 80 Investigator(s): Sarah Hartung, Aaron Booy Size (acres): 91.6 Data Sheet Numbers: SP 13A Location Legal: T21 S R 10 E S 12 DB, T 21 S R 10 E S 12 Nearest Town: Three Rivers AC, BC, DC, CC, T 21 S R 10 E S 12 CA T 21 S R 10 Latitude: 43.7660 ES 12 BD, CD Other: South of La Pine State Recreation Rd Longitude: -121.4776 Basin: Deschutes River ISoils Mapped Series: 29A: Cryaquolls, 0 to 3 percent slopes, 115A:Shanahan loamy coarse sand, low, 0 to 3 percent slopes, 144A: Sunriver sandy loam, 0 to 3 percent slopes Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Riverine Flow-Through Dominant Vegetation and Comments Cowardin Classification(s): PEMF, PSSF, PFOC Vegetation: Herbs: Carex aquatilis (Water sedge), Juncus balticus (Baltic rush). Wetland/Upland Mosaic; includes uneven terrain and small islands of non-wetlands along old oxbows. Adjacent to undeveloped forest land and scrub-shrub. Comments: Off-site determination. Wetland/Upland Mosaic includes hummocks, upland vegetated pockets, and old oxbows encompassing both sides of the river. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 95 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included adjoining open water in the Little Deschutes River. Percent (approx.) of the Wetland Visited: < 1 Percent (approx.) of the AA Visited: r 1 Month & Year of ORWAP Training Attended by Investigator(s): 8/2009 and 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 3 Goal 6 Water Quality Resource: No Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom • • Project Number. 209554 • • • South Deschutes County Local Wetland Inventory - Wetland Summary Sheet - Date(s) of Field Verification: 6/21/2010 Wetland Mapping Code: 81 Investigator(s): Alison Sigler, Sarah Hartung Size (acres): 17.3 Data Sheet Numbers: N/A Location Legal: T 21 S R 10 E S 13 BA, DA, CA, T 21 S R 10 E Nearest Town: Three Rivers S 13 AB, T 21 S R 10 E S 12 DC, T 21 S R 10 E S Latitude: 43.7599 12 CD Other: South of La Pine State Recreation Rd, west and Longitude: -121.4732 north of Huntington Rd Basin: Deschutes River Soils Mapped Series: 29A: Cryaquolls, 0 to 3 percent slopes, 115A:Shanahan loamy coarse sand, low, 0 to 3 percent slopes, 144A: Sunriver sandy loam, 0 to 3 percent slopes, W: Water Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Slope Valley Dominant Vegetation and Comments Cowardin Classification(s): PEME Vegetation: Herbaceous plants (unknown species) Comments: Off-site determination with limited visual access. Undeveloped land along Paulina Creek. Wetland/Upland Mosaic located on large, open field with hummocks. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 19 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included adjoining area in Paulina Creek. Percent (approx.) of the Wetland Visited: 0 Percent (approx.) of the AA Visited: 0 Month & Year of ORWAP Training Attended by Investigator(s): 8/2009 and 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 3 Goal 6 Water Quality Resource: Yes Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom Project Number: 209554 South Deschutes County Local Wetland Inventory - Wetland Summary Sheet Date(s) of Field Verification: 6/21/2010 Wetland Mapping Code: 82 Investigator(s): Alison Sigler, Sarah Hartung Size (acres): 10.4 Data Sheet Numbers: SP 2A Location Legal: T21 SIR 10 E S 13 DA Nearest Town: Three Rivers Other: South of La Pine State Recreation Rd, west and Latitude: 43.7557 north of Huntington Rd Longitude: -121.4694 Basin: Deschutes River Soils Mapped Series: 29A: Cryaquolls, 0 to 3 percent slopes, 144A: Sunriver sandy loam, 0 to 3 percent slopes, W: Water Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Slope Valley Dominant Vegetation and Comments Cowardin Classification(s): PEMY Vegetation: Herbs: Carex sp., Juncus balticus (Baltic rush) Comments: Off-site determination. Wetland/Upland Mosaic. No site access, but impoundment appears to be an earthen berm, possibly for vehicle access and/or agricultural purposes. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 10.4 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. Percent (approx.) of the Wetland Visited: 0 Percent (approx.) of the AA Visited: 0 Month & Year of ORWAP Training Attended by Investigator(s): 8/2009 and 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 3 Goal 6 Water Quality Resource: Yes Watland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom • • • Project Number: 209554 • • South Deschutes County Local Wetland Inventory - Wetland Summary Sheet - Date(s) of Field Verification: 6/21/2010, 11/17/2010 Wetland Mapping Code: 83 Investigator(s): Alison Sigler, Sarah Hartung Size (acres): 93.7 Data Sheet Numbers: SP 1A, 601, 602 Location Legal: T 21 S R 10 E S 13 DA, DD, T 21 S R 11 E S Nearest Town: Three Rivers 18 BC, CC, T 21 S R 10 E S 24, AA, DA T 21 S R 11 E Latitude: 43.7508 S 18 BC, CC. Other: South of La Pine State Recreation Rd, west, Longitude: -121.4687 south and north of Huntington Rd Basin: Deschutes River Soils Mapped Series: 115A:Shanahan loamy coarse sand, low, 0 to 3 percent slopes, 144A: Sunriver sandy loam, 0 to 3 percent slopes Hydrology Primary Hydrology Source(s): Groundwater, overland flow - irrigation ditches diverted from Paulina Creek. Hydro-geomorphic (HGM) Classification(s): Slope Valley Dominant Vegetation and Comments Cowardin Classification(s): PEMY Vegetation: Herbs: Juncus balticus (Baltic rush), Trifolium repens (White clover), Poa sp. (bluegrass), Carex sp. (sedge) Comments: On-site determination with landowner and DSL present. Pasture land for cattle surrounded by rural residential and upland forests. Wetland/Upland Mosaic due to hummocks along the irrigation ditches; uneven excavation of ditches. Site heavily irrigated in the spring. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 93.7 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. Percent (approx.) of the Wetland Visited: 20 Percent (approx.) of the AA Visited: 20 Month & Year of ORWAP Training Attended by Investigator(s): 8/2009 and 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 3 Goal 6 Water Quality Resource: Yes Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom Project Number: 209554 South Deschutes County Local Wetland Inventory - Wetland Summary Sheet - Date(s) of Field Verification: 6/21/2010 Wetland Mapping Code: 84 Investigator(s): Alison Sigler, Sarah Hartung Size (acres): 7.9 Data Sheet Numbers: N/A Location Legal: T 21 S R 11 E S 18 BC, CC, DC, T 21 S R 11 E Nearest Town: Three Rivers S 19 BB Latitude: 43.7506 Other: Northwest of Highway 97, north of intersection Longitude: -121.4634 of Pine Crest Ln and Hwy 97, along Paulina Creek Basin: Deschutes River Soils Mapped Series: 29A: Cryaquolls, 0 to 3 percent slopes Hydrology Primary Hydrology Source(s): Groundwater, overland flow in some years but Paulina Creek dry for most of the season due to irrigation withdrawals Hydro-geomorphic (HGM) Classification(s): Slope Valley Dominant Vegetation and Comments Cowardin Classification(s): PEMY Vegetation: Herbaceous plants (unknown species) Comments: Off-site determination. Adjacent to pasture land not recently irrigated. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 7.9 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. Percent (approx.) of the Wetland Visited: 0 Percent (approx.) of the AA Visited: 0 Month & Year of ORWAP Training Attended by Investigator(s): 8/2009 and 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 3 Goal 6 Water Quality Resource: Yes Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom • E Project Number: 209554 E • South Deschutes County Local Wetland Inventory Wetland Summary Sheet - Date(s) of Field Verification: 6/21/2010, 11/17/2010 Wetland Mapping Code: 85 Investigator(s): Alison Sigler, Sarah Hartung Size (acres): 32.0 Data Sheet Numbers: SP 600 Location Legal: T21 S R 11 E S 19 AB, BB, CB, DB, T21 S R Nearest Town: La Pine 11 E S 19 AC, BC, CC, DC Latitude: 43.7398 Other: Southeast of Hwy 97, west of Paulina Lake Rd Longitude: -121.4652 Basin: Deschutes River Soils 77771 Mapped Series: 29A: Cryaquolls, 0 to 3 percent slopes, 115A:Shanahan loamy coarse sand, low, 0 to 3 percent slopes, 144A: Sunriver sandy loam, 0 to 3 percent slopes Hydrology Primary Hydrology Source(s): Groundwater, overland flow and diversions from Paulina Creek. Hydra-geomorphic (HGM) Classification(s): Slope Valley Dominant Vegetation and Comments Cowardin Classification(s): PEMY Vegetation: Juncus sp. (rush), Poa sp. (bluegrass), Thinopyrum intermedium (Intermediate wheatgrass) Comments: On-site determination with DSL present. Accessed easement on-site with adjacent landowner (Mr. Hatcher). Site manipulated due to excavation of irrigation ditches. ODOT excavated a ditch on-site parallel to Hwy 97 to prevent roadway flooding in the spring. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 32.0 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. Percent (approx.) of the Wetland Visited: 2 Percent (approx.) of the AA Visited: 2 Month & Year of ORWAP Training Attended by Investigator(s): 8/2009 and 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 3 Goal 6 Water Quality Resource: No Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom Project Number: 209654 South Deschutes County Local Wetland Inventory - Wetland Summary Sheet - Date(s) of Field Verification: 6/21/2010 Wetland Mapping Code: 86 Investigator(s): Alison Sigler, Sarah Hartung Size (acres): 95.2 Data Sheet Numbers: N/A Location Legal: T21 S R 11 E S 30 AB, BB, T21 S R 11 E S Nearest Town: La Pine 30, BA, CA, T 21 S R 11 E S 19, CC Latitude: 43.7291 Other: East of Hwy 97, South of Paulina Lake Rd, west Longitude: -121.4533 of Newberry Rd Basin: Deschutes River Soils Mapped Series: 29A: Cryaquolis, 0 to 3 percent slopes, 115A:Shanahan loamy coarse sand, low, 0 to 3 percent slopes, 144A: Sunriver sandy loam, 0 to 3 percent slopes Hydrology Primary Hydrology Source(s): Groundwater, overland flow Hydro-geomorphic (HGM) Classification(s): Slope Valley Dominant Vegetation and Comments Cowardin Classification(s): PEMY Vegetation: Poa sp. (bluegrass), Thinopyrum intermedium (Intermediate wheatgrass) Comments: Off-site determination. Wetland/Upland Mosaic; upland hummocks along ditches. Site disturbed from ditching, diverting water from Paulina Creek, and past grazing activities. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 95.2 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. Percent (approx.) of the Wetland Visited: 0, viewed from adjacent gravel road. Percent (approx.) of the AA Visited: 0 Month & Year of ORWAP Training Attended by Investigator(s): 8/2009 and 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 3 Goal 6 Water Quality Resource: No Wetland Classiflcation Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom • • Project Number: 209554 • t E South Deschutes County Local Wetland Inventory Wetland Summary Sheet --r- Date(s) of Field Verification: 6/21/2010 Wetland Mapping Code: 87a-b Investigator(s): Alison Sigler, Sarah Hartung Size (acres): 41.1 Data Sheet Numbers: N/A Location Legal: T 21 S R 11 E S 30 AA, DA, T 21 S R 11 E S 29 Nearest Town: La Pine CB, DB, T 21 S R 11 E S 29, AC, BC, DC T 21 S R 11 Latitude: 43.7255 E S 29 AD, BD, CD Other: South of Paulina Lake Rd, east of Newberry Rd Longitude: -121.4446 and north of USFS 9745 Rd Basin: Deschutes River Soils Mapped Series: 114C, Shanahan loamy coarse sand, 0 to 15 percent slopes, 115A:Shanahan loamy coarse sand, low, 0 to 3 percent slopes, 144A: Sunriver sandy loam, 0 to 3 percent slopes Hydrology Primary Hydrology Source(s): Groundwater, overland flow in some years from Paulina Creek Hydro-geomorphic (HGM) Classification(s): Slope Valley Dominant Vegetation and Comments Cowardin Classification(s): PEMY Vegetation: Poa sp. (bluegrass), Juncus sp. (rush), Agropyron repens (quackgrass) Comments: Off-site determination. Wetland/Upland Mosaic due to uneven terrain, small islands of non-wetland along the stream channels. Site disturbed from ditching, diverting water from Paulina Creek, and past grazing activities. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 45 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included adjoining area in Paulina Creek. Percent (approx.) of the Wetland Visited: 0 Percent (approx.) of the AA Visited: 0 Month & Year of ORWAP Training Attended by Investigator(s): 8/2009 and 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 3 Goal 6 Water Quality Resource: No Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom Project Number: 209554 South Deschutes County Local Wetland Inventory - Wetland Summary Sheet - Date(s) of Field Verification: 6/21/2010 Wetland Mapping Code: 88 Investigator(s): Alison Sigler, Sarah Hartung Size (acres): 1.4 Data Sheet Numbers: SP 4A Location Legal: T 21 S R 10 E S 14 AA Nearest Town: La Pine Other: Northwest of Pine Grove Rd and Shadow Ct Latitude: 43.7603 Basin: Deschutes River Longitude: -121.4895 Soils Mapped Series: 29A: Cryaquolls, 0 to 3 percent slopes, 144A: Sunriver sandy loam, 0 to 3 percent slopes Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Slope Valley Dominant Vegetation and Comments Cowardin Classification(s): PEMB Vegetation: Poa sp. (bluegrass), Carex sp. (sedge) Comments: On-site determination. Horse pasture in rural residential area; golf course nearby Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 1.4 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. Percent (approx.) of the Wetland Visited: 20 Percent (approx.) of the AA Visited: 20 Month & Year of ORWAP Training Attended by Investigator(s): 8/2009 and 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 3 Goal 6 Water Quality Resource: Yes Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom • C, • Project Number: 209554 C7 11 • South Deschutes County Local Wetland Inventory - Wetland Summary Sheet - Date(s) of Field Verification: 6/21/2010 Wetland Mapping Code: 89 Investigator(s): Alison Sigler, Sarah Hartung Size (acres): 85.0 Data Sheet Numbers: SP 3A Location Legal: T 21 S R 10 E S 12 CC, DC, T21 S R 10 E S Nearest Town: La Pine 14 AA, DA,T21 S R 10 E S 13 AB, BB, CB Latitude: 43.7567 Other: East of Pine Grove Rd, south of Bridge Dr Longitude: -121.4853 Basin: Deschutes River Soils Mapped Series: 29A: Cryaquolls, 0 to 3 percent slopes, 115A:Shanahan loamy coarse sand, low, 0 to 3 percent slopes, 144A: Sunriver sandy loam, 0 to 3 percent slopes Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Riverine Flow-Through Dominant Vegetation and Comments Cowardin Classification(s): PABF, PEMB, PEMC, PEMF, PEMY, PSSC, PSSF, PFOC, PFOF, R2UBH Vegetation: Shrubs: Salix exigua (Narrowleaf willow), Herbs: Carex nebrascensis (Nebraska sedge), Juncus nevadensis (Sierra rush) Comments: On-site determination. Wetland/Upland Mosaic. Site includes old oxbows and small islands of non- wetland due to uneven terrain. Rural residential area with undeveloped natural land. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 95 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included adjoining open water in the Little Deschutes River. Percent (approx.) of the Wetland Visited: 1 Percent (approx.) of the AA Visited: a 1 Month & Year of ORWAP Training Attended by Investigator(s): 8/2009 and 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 3 Goal 6 Water Quality Resource: No Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom Project Number: 209554 South Deschutes County Local Wetland Inventory - Wetland Summary Sheet - Date(s) of Field Verification: 6/21/2010 Wetland Mapping Code: 90 Investigator(s): Alison Sigler, Sarah Hartung Size (acres): 65.5 Data Sheet Numbers: SP 6A Location Legal: T21 SR 10 E S 14 AD, CD, DD, T 21 S R 10E Nearest Town: La Pine S 13 BC, T 21 S R 10 E S 13 CB, T 21 S R 10 E S 23 Latitude: 43.7512 AA Other: South of Bridge Dr, north of Riverview Dr Longitude: -121.4872 Basin: Deschutes River Soils Mapped Series: 29A: Cryaquolls, 0 to 3 percent slopes, 115A:Shanahan loamy coarse sand, low, 0 to 3 percent slopes Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Riverine Flow-Through Dominant Vegetation and Comments Cowardin Classification(s): PABF, PEMY, PSSY, PFOY, R2UBH Vegetation: Shrubs: Salix exigua (Narrowleaf willow), Herbs: Juncus balticus (Baltic rush), Carex sp. (sedge) Comments: On-site determination; includes previous delineation WD2007-0442. Wetland/Upland Mosaic. Site includes old oxbows and small islands of non-wetland due to uneven terrain. Rural residential area and undeveloped natural land. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 75 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included adjoining open water in the Little Deschutes River. Percent (approx.) of the Wetland Visited: 1 Percent (approx.) of the AA Visited: < 1 Month & Year of ORWAP Training Attended by Investigator(s): 8/2009 and 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 3 Goal 6 Water Quality Resource: No Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom • • C Project Number: 209554 • • rI South Deschutes County Local Wetland Inventory - Wetland Summary Sheet - Date(s) of Field Verification: 8/9/2010 Wetland Mapping Code: 91 Investigator(s): Alessandra Capretti Size (acres): 2.9 Data Sheet Numbers: N/A Location Legal: T 21 S R 10 F S 23 AB, BA Nearest Town: La Pine Other: West of Bridge Dr, south of Sprague Loop Latitude: 43.7456 Basin: Deschutes River Longitude: -121.4968 ISoils Mapped Series: 115A: Shanahan loamy coarse sand, low, 0 to 3 percent slopes, 144A: Sunriver sandy loam, 0 to 3 percent slopes Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Slope Valley Dominant Vegetation and Comments Cowardin Classification(s): PEMY Vegetation: Herbaceous plants Comments: Off-site determination. A few rural residences in area but mainly undeveloped land Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 2.9 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. Percent (approx.) of the Wetland Visited: 0 Percent (approx.) of the AA Visited: 0 Month & Year of ORWAP Training Attended by Investigator(s): 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 1 Goal 6 Water Quality Resource: No Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom Project Number: 209554 South Deschutes County Local Wetland Inventory - Wetland Summary Sheet - Date(s) of Field Verification: 6/22/2010 Wetland Mapping Code: 92a-b Investigator(s): Alison Sigler, Sarah Hartung Size (acres): 48.8 Data Sheet Numbers: SP 15A, 57A Location Legal: T21 S R 10 E S 23 AB, DB, T 21 S R 10 E S 23 Nearest Town: La Pine AC, DC, T 21 S R 10 E S 23 CA, T 21 S R 10 E S 23 Latitude: 43.7400 CDT21 SR 10ES23BID. Other: West of Bridge Dr, south of Buena Vista Dr Longitude: -121.4987 Basin: Deschutes River Soils Mapped Series: 115A:Shanahan loamy coarse sand, low, 0 to 3 percent slopes, 144A: Sunriver sandy loam, 0 to 3 percent slopes Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Slope Valley Dominant Vegetation and Comments Cowardin Classification(s): PEMY Vegetation: Trees: Pinus contorta (Lodgepole pine), Herbs: Juncus sp., Festuca idahoensis (Idaho fescue) Comments: Off-site determination. Wetland/Upland Mosaic due to uneven terrain. Rural residential area; pasture land. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 48.8 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. Percent (approx.) of the Wetland Visited: 0 Percent (approx.) of the AA Visited: 0 Month & Year of ORWAP Training Attended by Investigator(s): 8/2009 and 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 3 Goal 6 Water Quality Resource: No Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom • • Project Number: 209554 • • C South Deschutes County Local Wetland Inventory - Wetland Summary Sheet - Date(s) of Field Verification: 6122/2010 Wetland Mapping Code: 93a-b Investigator(s): Alison Sigler, Sarah Hartung Size (acres): 340.06 Data Sheet Numbers: SP 14A Location Legal: T 21 S R 10 E S 23 AA, BA, CA, DA, T 21 S R Nearest Town: La Pine 10 E S 23 AD, BD, CD, DD, T 21 S R 10 E S 26 AA, BA,CAT21 SR 10ES26DA,T21 SR10ES26 Latitude: North end: 43.7472 AD, BD, CD, DD, T 21 S R 10 E S 35 AA, BA, T 21 S R South end: 43.7146 10 E S 14 CD, DD. Longitude: North end: -121.4923 Other: Mostly east of Bridge Dr, west of Riverview Dr, along the Little Deschutes River South end: -121.4955 Basin: Deschutes River I5olls Mapped Series: 29A: Cryaquolls, 0 to 3 percent slopes, 115A:Shanahan loamy coarse sand, low, 0 to 3 percent slopes, 144A: Sunriver sandy loam, 0 to 3 percent slopes Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Riverine Flow-Through Dominant Vegetation and Comments Cowardin Classification(s): PABF, PABH, PEMY, PSSY, PFOY, R2UBH Vegetation: Shrubs: Salix exigua (Narrowleaf willow), Herbs: Carex aquatilis (Water sedge) Comments: On-site determination and review of previous delineation WD2009-0208. Wetland/Upland Mosaic due to uneven terrain creating many non-wetland islands. Site includes numerous old oxbows of the Little Deschutes River. Rural residential area. Wetland 93a is one of the larger polygons because of the broad, continuous floodplain on the east side of the Little Deschutes River. Division between Wetlands 93a and 94 is based on a change from PSSY at the south end of Wetland 93 to PEME and PSSC at north end of Wetland 94. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 360 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included adjoining open water in the Little Deschutes River. Percent (approx.) of the Wetland Visited: < 1 Percent (approx.) of the AA Visited: a 1 Month 8r Year of ORWAP Training Attended by Investigator(s): 8/2009 and 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 3 Goal 6 Water Quality Resource: Yes Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub R5B = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom Project Number: 209554 South Deschutes County Local Wetland Inventory - Wetland Summary Sheet Date(s) of Field Verification: 6/22/2010 Wetland Mapping Code: 94 Investigator(s): Alison Sigler, Sarah Hartung Size (acres): 104.14 Data Sheet Numbers: SP 17A Location Legal: T 21 S R 10 E S 35 AA, BA, CA, DA, T 21 S R Nearest Town: La Pine 10 ES 35DB,T21 S R 10 E S 35 AC, CC, DC T 21 S R 10 E S 35 BD, CD. Latitude: North end: 43.7146 Other: North of Burgess Rd, west of Huntington Rd, South end: 43.7037 along the Little Deschutes River Longitude: North end: -121.4955 Basin: Deschutes River South end: -121.4993 Soils Mapped Series: 29A: Cryaquolls, 0 to 3 percent slopes, 115A:Shanahan loamy coarse sand, low, 0 to 3 percent slopes, 144A: Sunriver sandy loam, 0 to 3 percent slopes Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Riverine Flow-Through Dominant Vegetation and Comments Cowardin Classification(s): PABF, PEMC, PSSC Vegetation: Shrubs: Salix exigua (Narrowleaf willow), Herbs: Phalaris arundinacea (Reed canary grass), Carex aquatilis (Water sedge) Comments: On-site determination. Wetland/Upland Mosaic due to uneven terrain creating many non-wetland islands. Site includes many old oxbows of the Little Deschutes River. Rural residential area and undeveloped forest land. Division between Wetlands 93a and 94 is based on a change from PSSY at the south end of Wetland 93 to PEME and PSSC at north end of Wetland 94. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 120 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included adjoining open water in the Little Deschutes River. Percent (approx.) of the Wetland Visited: < 1 Percent (approx.) of the AA Visited: r 1 Month & Year of ORWAP Training Attended by Investigator(s): 8/2009 and 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 3 Goal 6 Water Quality Resource: No Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom • • Project Number: 209554 • C, South Deschutes County Local Wetland Inventory - Wetland Summary Sheet - Date(s) of Field Verification: 6/22/2010 Wetland Mapping Code: 95 Investigator(s): Alison Sigler, Sarah Hartung Size (acres): 69.1 Data Sheet Numbers: SP 19A Location Legal: T21 S R 10 E S 35 CC, DC, T22 S R 10 E S 2 Nearest Town: La Pine AB, BB, CB, DB Latitude: 43.7010 Other: South of Burgess Rd, east of Arctic Dr and west Longitude: -121.5018 of Glenwood Dr, along the Little Deschutes River Basin: Deschutes River Soils Mapped Series: 29A: Cryaquolls, 0 to 3 percent slopes, 115A:Shanahan loamy coarse sand, low, 0 to 3 percent slopes, 144A: Sunriver sandy loam, 0 to 3 percent slopes Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Riverine Flow-Through Dominant Vegetation and Comments Cowardin Classification(s): PABF, PEMC, PFOC Vegetation: Shrubs: Salix exigua (Narrowleaf willow), Herbs: Carex sp. Comments: On-site determination. Wetland/Upland Mosaic due to uneven terrain creating many non-wetland islands. Rural residential area and undeveloped natural land. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 80 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included adjoining open water in the river. Percent (approx.) of the Wetland Visited: < 1 Percent (approx.) of the AA Visited: a 1 Month & Year of ORWAP Training Attended by Investigator(s): 8/2009 and 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 3 Goal 6 Water Quality Resource: No Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom Project Number: 209554 South Deschutes County Local Wetland Inventory - Wetland Summary Sheet - Date(s) of Field Verification: 6/22/2010 Wetland Mapping Code: 96 Investigator(s): Alison Sigler, Sarah Hartung Size (acres): 82.3 Data Sheet Numbers: N/A Location Legal: T 22 S R 10 E S 2 CB, BC, CC, DC, T 22 S R Nearest Town: La Pine 10 E S 3 AD, DD Latitude: North end: 43.6964 Other: West of Huntington Rd, south of Burgess South end: 43.6893 Rd/Frontage Rd Basin: Deschutes River Longitude: North end: -121.5036 South end: -121.5031 ISoils Mapped Series: 29A: Cryaquolls, 0 to 3 percent slopes, 115A: Shanahan loamy coarse sand, low, 0 to 3 percent slopes, 144A, Sunriver sandy loam, 0 to 3 percent slopes, W: Water Hydrology Primary Hydrology Source(s): Groundwater Hydra-geomorphic (HGM) Classification(s): Riverine Flow-Through Dominant Vegetation and Comments Cowardin Classification(s): PABF, PEMC, PSSC Vegetation: Shrubs: Salix exigua (Narrowleaf willow), Herbs: Carex sp. Comments: Off-site determination. Wetland/Upland Mosaic due to uneven terrain creating many non-wetland islands. Rural residential area and undeveloped natural land. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 95 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included adjoining open water. Percent (approx.) of the Wetland Visited: 0 Percent (approx.) of the AA Visited: 1 Month & Year of ORWAP Training Attended by Investigator(s): 8/2009 and 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 3 Goal 6 Water Quality Resource: No Wetland Classification Codes PPO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom 11 • Project Number: 209554 C7 • South Deschutes County Local Wetland Inventory - Wetland Summary Sheet - Date(s) of Field Verification: 6/22/2010 Wetland Mapping Code: 97 Investigator(s): Alison Sigler, Sarah Hartung Size (acres): 64.3 Data Sheet Numbers: N/A Location Legal: T 22 S R 10 ES 10 AA, BA, CA, T 22 S R 10 E Nearest Town: La Pine S 2 CC, T 22 S R 10 E S 11 BB Latitude: 43.6873 Other: West of Huntington Rd and Caldwell Dr, along Longitude: -121.5048 the Little Deschutes River Basin: Deschutes River Soils Mapped Series: 29A: Cryaquolls, 0 to 3 percent slopes, 115A: Shanahan loamy coarse sand, low, 0 to 3 percent slopes, 144A: Sunriver sandy loam, 0 to 3 percent slopes, W: Water Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Riverine Flow-Through Dominant Vegetation and Comments Cowardin Classification(s): PEMC, PSSC, PFOC, R2UBH Vegetation: Herbaceous plants (various spp.), Salix sp. (willow) Comments: Off-site determination. Wetland includes DSL delineation WD1995-0280. Wetland/Upland Mosaic due to uneven terrain creating many non-wetland islands. Rural residential area and undeveloped natural land and pasture land. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 70 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included adjoining open water in the Little Deschutes River. Percent (approx.) of the Wetland Visited: r 1 Percent (approx.) of the AA Visited: < 1 Month & Year of ORWAP Training Attended by Investigator(s): 8/2009 and 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 3 Goal 6 Water Quality Resource: No Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom Project Number: 209554 South Deschutes County Local Wetland Inventory - Wetland Summary Sheet Date(s) of Field Verification: 6/22/2010 Wetland Mapping Code: 98 Investigator(s): Alison Sigler, Sarah Hartung Size (acres): 7.7 Data Sheet Numbers: N/A Location Legal: T22 S R 10 E S 10 AA, BA, CA, T22 S R 10 E Nearest Town: La Pine S 2 CC, T 22 S R 10 E S 11 BB Latitude: 43.6856 Other: West of Huntington Rd and Caldwell Dr Longitude: -121.5232 Basin: Deschutes River Soils Mapped Series: 29A: Cryaquolls, 0 to 3 percent slopes, 115A: Shanahan loamy coarse sand, low, 0 to 3 percent slopes, 144A: Sunriver sandy loam, 0 to 3 percent slopes, W: Water Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Slope Valley Dominant Vegetation and Comments Cowardin Classification(s): PEMA Vegetation: Herbaceous plants (unknown species). Comments: Off-site determination with no public viewing access. Rural residential area; fallow pasture. Wetland includes DSL delineation WD1995-0280. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 7.7 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. Percent (approx.) of the Wetland Visited: 0 Percent (approx.) of the AA Visited: 0 Month & Year of ORWAP Training Attended by Investigator(s): 8/2009 and 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 3 Goal 6 Water Quality Resource: Yes Wetland Classiflcation Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom r~ C, E Project Number: 209554 rI C7 South Deschutes County Local Wetland Inventory - Wetland Summary Sheet - Date(s) of Field Verification: 6/23/2010 Wetland Mapping Code: 99 Investigator(s): Alison Sigler, Sarah Hartung Size (acres): 232.7 Data Sheet Numbers: SP 21A Location Legal: T 22 S R 10 E S 17 AA, T 22 S R 10 E S 8 DD, Nearest Town: La Pine T 22 S R 10 E S 9 AC,CC, DC, T 22 S R 10 ES 16 AB, Latitude: North end: 43.6844 BB T 22 S R 10 E S 9 AD, BD, CD, CD, T 22 S R 10 E S 9 DA, T 22 S R 10 E S 10 CB, DB, T 22 S R 10 E S South end: 43.6726 10 BC, T 22 S R 10 E S 10 CA Longitude: North end: -121.5147 Other: North of Jackpine Rd, south of Rim Or and Davis Ave, along the Little Deschutes River South end: -121.5472 Basin: Deschutes River Soils Mapped Series: 29A: Cryaquolls, 0 to 3 percent slopes, 144A: Sunriver sandy loam, 0 to 3 percent slopes Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Riverine Flow-Through Dominant Vegetation and Comments Cowardin Classification(s): PABF, PEMY, PSSY, PFOY, R2UBH Vegetation: Shrubs: Salix exigua (Narrowleaf willow), Herbs: Carex aquatilis (Water sedge) Comments: On-site determination. Wetland/Upland Mosaic due to dynamic floodplain conditions that have created uneven topography resulting in non-wetland hummocks. Rural residential area. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 245 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included adjoining open water in the Little Deschutes River. Percent (approx.) of the Wetland Visited: < 1 Percent (approx.) of the AA Visited: a 1 Month & Year of ORWAP Training Attended by Investigator(s): 8/2009 and 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 3 Goal 6 Water Quality Resource: No Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom Project Number.' 209554 South Deschutes County Local Wetland Inventory - Wetland Summary Sheet - Date(s) of Field Verification., 6/23/2010 Wetland Mapping Code: 100a-b Investigator(s): Alison Sigler, Sarah Hartung Size (acres): 15.0 Data Sheet Numbers: SP 23A Location Legal: T 22 S R 10 E S 9 CD, T 22 S R 10 E S 16 Nearest Town: La Pine BA, T 22 S R 10 E S 16 AB Latitude: 43.6725 Other: Northwest of Ash Rd, North of Jackpine Rd, Longitude: -121.5368 east of Riverland Ave Basin: Deschutes River Soils Mapped Series: 144A: Sunriver sandy loam, 0 to 3 percent slopes Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Slope Valley Dominant Vegetation and Comments Cowardin Classification(s): PEMA, PFOA Vegetation: Trees: Pinus contorta (Lodgepole pine), Shrubs: Amelanchier alnifolia (Saskatoon serviceberry), Rosa sp., Herbs: Fragaria sp. (strawberry), Poa sp. (bluegrass) Comments: On-site determination. Residential area. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 15.0 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. Percent (approx.) of the Wetland Visited: 1 Percent (approx.) of the AA Visited: 1 Month & Year of ORWAP Training Attended by Investigator(s): 8/2009 and 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 3 Goal 6 Water Quality Resource: Yes Wetland Classification Codes PPO = palustrine forested PSS = palustrine scrub-shrub RS6 = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom • • • Project Number. 209554 C, • South Deschutes County Local Wetland Inventory - Wetland Summary Sheet - Date(s) of Field Verification: 6/23/2010 Wetland Mapping Code: 101 Investigator(s): Alison Sigler, Sarah Hartung Size (acres): 1.2 Data Sheet Numbers: SP 25A Location Legal: T22 S R 10 E S 17 BA Nearest Town: La Pine Other: South of Deer Ave, north of Cascade Dr Latitude: 43.6732 Basin: Deschutes River Longitude: -121.5532 ISoils Mapped Series: 144A: Sunriver sandy loam, 0 to 3 percent slopes Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Slope Valley Dominant Vegetation and Comments Cowardin Classification(s): PEMA, PFOA Vegetation: Trees: Pinus contorta (Lodgepole pine), Herbs: Achillea millefolium (Common yarrow), Trifolium sp., Carex aquatilis (Water sedge), Juncus balticus (Baltic rush), Stellaria longifolia (Longleaf starwort), Galeopsis tetrahit (Brittlestem hempnettle) Comments: On-site determination. Rural residential area and undeveloped natural land. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 1.2 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included adjoining open water. Percent (approx.) of the Wetland Visited: 10 Percent (approx.) of the AA Visited: 10 Month & Year of ORWAP Training Attended by Investigator(s): 8/2009 and 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 3 Goal 6 Water Quality Resource: No Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom Project Number: 209554 South Deschutes County Local Wetland Inventory - Wetland Summary Sheet - Date(s) of Field Verification: 6/23/2010 Wetland Mapping Code: 102 Investigator(s): Alison Sigler, Sarah Hartung Size (acres): 2.28 Data Sheet Numbers: SP 26A Location Legal: T 22 S R 10 E S 17 AB, T 22 S R 10 E S 17 BA Nearest Town: La Pine Other: North of Cascade Dr, south of Deer Ave, along Latitude: 43.6722 Little Deschutes River Longitude: -121.5549 Basin: Deschutes River Soils Mapped Series: 144A: Sunriver sandy loam, 0 to 3 percent slopes Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Slope Valley Dominant Vegetation and Comments Cowardin Classification(s): PEMY, PFOY Vegetation: Shrubs: Salix exigua (Narrowleaf willow), Herbs: Carex sp. (sedge) Comments: On-site determination.This wetland is on a gentle slope, slightly higher in elevation than south of the roadway and is in a rural residential area. Assessed separately from Wetland 103 due to difference in slope and elevation. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 2.28 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included adjoining open water. Percent (approx.) of the Wetland Visited: 2 Percent (approx.) of the AA Visited: 2 Month & Year of ORWAP Training Attended by Investigator(s): 8/2009 and 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 3 Goal 6 Water Quality Resource: Yes Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom • E Project Number- 209554 • • • South Deschutes County Local Wetland Inventory - Wetland Summary Sheet - Date(s) of Field Verification: 6/23/2010 Wetland Mapping Code: 103a-b Investigator(s): Alison Sigler, Sarah Hartung Size (acres): 200.4 Data Sheet Numbers: SP 24A Location Legal: T 22 S R9 E S 24 AA, T 22 S R 10 ES 18 CC, Nearest Town: La Pine DC, T 22 S R 10 E S 18 AD, CD, DD T 22 S R 10 E S Latitude: 43.6695 17 AB, CB, DB, T 22 S R 10 E S 17 AA, BA, CA Other: Mostly north of Pierce Rd, along the Little Longitude: -121.5574 Deschutes River Basin: Deschutes River Soils Mapped Series: 29A: Cryaquolls, 0 to 3 percent slopes, 114C: Shanahan loamy coarse sand, 0 to 15 percent slopes, 144A: Sunriver sandy loam, 0 to 3 percent slopes Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Riverine Flow-Through Dominant Vegetation and Comments Cowardin Classification(s): PEMC, PSSC, PFOC, R2UBH Vegetation: Shrubs: Salix exigua (Narrowleaf willow), Herbs: Carex sp., Stellaria longifolia (Longleaf starwort) Comments: On-site determination. Wetland/Upland Mosaic due to uneven terrain. Rural residential area; open space. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 220 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included adjoining open water in the Little Deschutes River. Percent (approx.) of the Wetland Visited: < 1 Percent (approx.) of the AA Visited: r 1 Month & Year of ORWAP Training Attended by Investigator(s): 8/2009 and 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 3 Goal 6 Water Quality Resource: Yes Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom Project Number: 209554 South Deschutes County Local Wetland Inventory - Wetland Summary Sheet - Date(s) of Field Verification: 6/24/2010 Wetland Mapping Code: 104a-b Investigator(s): Alison Sigler, Sarah Hartung Size (acres): 1.2 Data Sheet Numbers: SP 30A Location Legal: T 22 S R 10 E S 18 CA Nearest Town: La Pine Other: Southwest of Deer Ave Latitude: 43.6683 Basin: Deschutes River Longitude: -121.5715 Soils Mapped Series: 114C, Shanahan loamy coarse sand, 0 to 15 percent slopes, 144A: Sunriver sandy loam, 0 to 3 percent slopes Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Slope Valley Dominant Vegetation and Comments Cowardin Classification(s): PEMB Vegetation: Herbs: Phalaris arundinacea (Reed canary grass), Poa sp., Juncus balticus (Baltic rush) Comments: Off-site determination. Undeveloped forest land. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 1.2 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. Percent (approx.) of the Wetland Visited: 0 Percent (approx.) of the AA Visited: 0 Month & Year of ORWAP Training Attended by Investigator(s): 8/2009 and 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 3 Goal 6 Water Quality Resource: No Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom • • Project Number: 209554 rI • • South Deschutes County Local Wetland Inventory Wetland Summary Sheet - Date(s) of Field Verification: 6/23/2010 Wetland Mapping Code: 105 Investigator(s): Alison Sigler, Sarah Hartung Size (acres): 97.2 Data Sheet Numbers: SP 28A Location Legal: T22 S R 9 E S 24 AA, BA, CA, DA, T22 S R 9 Nearest Town: La Pine E S 24 AD, BD, CD, T 22 S R 9 E S 24 DC T 22 S R 9 Latitude: 43.6546 E S 25 BA. Other: Mostly north of Masten Rd, along the Little Longitude: -121.5888 Deschutes River Basin: Deschutes River ISoils Mapped Series: 29A: Cryaquolis, 0 to 3 percent slopes, 114C, Shanahan loamy coarse sand, 0 to 15 percent slopes, 144A: Sunriver sandy loam, 0 to 3 percent slopes Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Riverine Flow-Through Dominant Vegetation and Comments Cowardin Classification(s): PEMC, PSSC Vegetation: Trees: Pinus contorta (Lodgepole pine), Shrubs: Salix exigua (Narrowleaf willow), Herbs: Phalaris arundinacea (Reed canary grass), Carex aquatilis Comments: Off-site determination. Wetland/Upland Mosaic due to uneven terrain. Rural residential area. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 110 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included adjoining open water in the river. Percent (approx.) of the Wetland Visited: 0 Percent (approx.) of the AA Visited: 0 Month & Year of ORWAP Training Attended by Investigator(s): 8/2009 and 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 3 Goal 6 Water Quality Resource: Yes Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom Project Number: 209554 South Deschutes County Local Wetland Inventory Wetland Summary Sheet - Date(s) of Field Verification: 6/23/2010 Wetland Mapping Code: 106 Investigator(s): Alison Sigler, Sarah Hartung Size (acres): 159.3 Data Sheet Numbers: SP 27A Location Legal: T22 S R 9 E S 25 BA, CA, T22 S R 9 E S 25 Nearest Town: La Pine AB, DB, T 22 S R 9 E S 25 AC T 22 S R 9 E S 25 AD, Latitude: 43.6453 BD, CD, DD, T 22 S R 9 E S 25 AC, T 22 S R 9 E S 36 AA, BA. Longitude: -121.5919 Other: South and east of Masten Rd, along the Little Deschutes River Basin: Deschutes River Soils Mapped Series: 29A: Cryaquolls, 0 to 3 percent slopes, 114C, Shanahan loamy coarse sand, 0 to 15 percent slopes, 144A: Sunriver sandy loam, 0 to 3 percent slopes Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Riverine Flow-Through Dominant Vegetation and Comments Cowardin Classification(s): PEMC, PSSC, PFOC, R2UBH Vegetation: Shrubs: Salix exigua (Narrowleaf willow), Spiraea sp., Herbs: Carex sp. (sedge) Comments: Off-site determination. Wetland/Upland Mosaic due to uneven terrain resulting in many non-wetland islands. Rural residential. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 170 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included adjoining open water. Percent (approx.) of the Wetland Visited: ¢ 1 Percent (approx.) of the AA Visited: r 1 Month & Year of ORWAP Training Attended by Investigator(s): 8/2009 and 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 3 Goal 6 Water Quality Resource: Yes Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom • Project Number: 209554 • • • South Deschutes County Local Wetland Inventory Wetland Summary Sheet Date(s) of Field Verification: 6/24/2010 Wetland Mapping Code: 107 Investigator(s): Alison Sigler, Sarah Hartung Size (acres): 100.4 Data Sheet Numbers: SP 29A Location Legal: T22 S R 9 E S 36 BA, CA, T22 S R 9 E S 36 Nearest Town: La Pine AB, DB, T 22 S R 9 E S 36 AC, BC, CC, DC T 22 S R 9 Latitude: 43.6455 E S 36 BD, CD. Other: West of Wagon Trail Rd and east of Masten Rd, Longitude: -121.5918 along the Little Deschutes River Basin: Deschutes River Soils Mapped Series: 29A: Cryaquolls, 0 to 3 percent slopes, 1140, Shanahan loamy coarse sand, 0 to 15 percent slopes, 144A: Sunriver sandy loam, 0 to 3 percent slopes Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Riverine Flow-Through Dominant Vegetation and Comments Cowardin Classification(s): PEMC, PSSC, PFOC, R2UBH Vegetation: Trees: Pinus contorts (Lodgepole pine), Shrubs: Salix exigua (Narrowleaf willow), Herbs: Phalaris arundinacea (Reed canary grass), Alopecurus pratensis (Meadow foxtail), Carex aquatilis (Water sedge) Comments: On-site determination. Wetland/Upland Mosaic due to uneven terrain. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 120 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. In this case, the AA included adjoining open water in the Little Deschutes River. Percent (approx.) of the Wetland Visited: r 1 Percent (approx.) of the AA Visited: < 1 Month & Year of ORWAP Training Attended by Investigator(s): 8/2009 and 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 3 Goal 6 Water Quality Resource: No Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom Project Number: 209554 South Deschutes County Local Wetland Inventory - Wetland Summary Sheet - Date(s) of Field Verification: 6/23/2010 Wetland Mapping Code: 108 Investigator(s): Alison Sigler, Sarah Hartung Size (acres): 48.0 Data Sheet Numbers: SP 22A Location Legal: T22 S R 10 E S 15 CD, DD, T 22 S R 10 E S Nearest Town: La Pine 22 BA Latitude: 43.6671 Other: South of 6th St, northwest of Hwy 97 Longitude: -121.5107 Basin: Deschutes River Soils Mapped Series: 29A: Cryaquolls, 0 to 3 percent slopes, 144A, Sunriver sandy loam, 0 to 3 percent slopes, 153A: Tutni loamy coarse sand, 0 to 3 percent slopes Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Slope Valley Dominant Vegetation and Comments Cowardin Classification(s): PEMY, PFOY Vegetation: Claytonia perfoliata (Miner's lettuce), Carex sp. (sedge) Carex nebrascensis (Nebraska sedge) Comments: Off-site determination. Wetland includes wetland polygon from the La Pine/Wickiup Junction LWI. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 48.0 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. Percent (approx.) of the Wetland Visited: 0, viewed from right-of-way Percent (approx.) of the AA Visited: 0 Month & Year of ORWAP Training Attended by Investigator(s): 8/2009 and 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 3 Goal 6 Water Quality Resource: No Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom C t Project Number- 209554 C1 • South Deschutes County Local Wetland Inventory - Wetland Summary Sheet - Date(s) of Field Verification: 8/9/2010 Wetland Mapping Code: 109 Investigator(s): Alessandra Capretti Size (acres): 112.8 Data Sheet Numbers: SP 47A Location Legal: T 22 S R 10 E S 22 BA, CA, DA, T 22 S R10 E Nearest Town: La Pine S 22 AD, BD, DD, T 22 S R 10 E S 23 BC, CC T 22 S Latitude: 43.6603 R10ES15CD. Other: Southeast of Hwy 97 and west of Huntington Longitude: -121.5117 Rd Basin: Deschutes River Soils Mapped Series: 115A, Shanahan loamy coarse sand, low, 0 to 3 percent slopes, 153A: Tutni loamy coarse sand, 0 to 3 percent slopes, 29A: Cryaquolls, 0 to 3 percent slopes,144A: Sunriver sandy loam, 0 to 3 percent slopes Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Slope Valley Dominant Vegetation and Comments Cowardin Classification(s): PEMC, PFOC Vegetation: Leymus cinereus (Basin wildrye) Comments: Off-site determination. Undeveloped, open space. Wetland includes wetland polygon from the La Pine/Wickiup Junction LWI. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 112.8 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. Percent (approx.) of the Wetland Visited: 0 Percent (approx.) of the AA Visited: 0 Month & Year of ORWAP Training Attended by Investigator(s): 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 1 Goal 6 Water Quality Resource: Yes Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom Project Number: 209554 South Deschutes County Local Wetland Inventory - Wetland Summary Sheet - Date(s) of Field Verification: 8/9/2010 Wetland Mapping Code: 110 Investigator(s): Alessandra Capretti Size (acres): 221.10 Data Sheet Numbers: SP 49A, SP 50A, SP 51A* Location Legal: T 22 S R 10 E S 22 AD, CD, DD, T 22 S R 10 E Nearest Town: La Pine S 27 AA, BA, CA, DA, T 22 S R 10 E S 27 AB, DB Latitude: 43.6326 Other: Northeast of Hwy 31 Longitude: -121.5146 Basin: Deschutes River Soils Mapped Series: 29A: Cryaquolls, 0 to 3 percent slopes, 115A: Shanahan loamy coarse sand, 0 to 3 percent slopes, 144A: Sunriver sandy loam, 0 to 3 percent slopes ,153A: Tutni loamy coarse sand, 0 to 3 percent slopes H F ydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Slope Valley Dominant Vegetation and Comments Cowardin Classification(s): PABF, PEMC, PFOC Vegetation: Leymus cinereus (Basin wildrye) Comments: Off-site determination. Undeveloped, open space. *SP 51A describes non-wetland conditions (i.e. no hydrology) on the southwest side of the road to demonstrate that Wetland 110 does not extend under the road. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres., 221.10 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. Percent (approx.) of the Wetland Visited: 0 Percent (approx.) of the AA Visited: 0 Month & Year of ORWAP Training Attended by Investigator(s): 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 1 Goal 6 Water Quality Resource: No Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom • • • Project Number: 209554 • • South Deschutes County Local Wetland Inventory - Wetland Summary Sheet Date(s) of Field Verification: 8/10/2010 Wetland Mapping Code: 111 Investigator(s): Alessandra Capretti Size (acres): 8.6 Data Sheet Numbers: SP 52A Location Legal: T 22 S R 10 E S 27 DB, T 22 S R 10 E S 27 AC Nearest Town: La Pine Other: Northeast of Hwy 31 Latitude: 43.6354 Basin: Deschutes River Longitude: -121.5161 Soils Mapped Series: 29A: Cryaquolls, 0 to 3 percent slopes Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Slope Valley Dominant Vegetation and Comments Cowardin Classification(s): PEMC, PFOC Vegetation: Herbs: Festuca idahoensis (Idaho fescue) Comments: Off-site determination. Wetland includes previous DSL delineation WD2006-0415. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 8.6 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. Percent (approx.) of the Wetland Visited: 0 Percent (approx.) of the AA Visited: 0 Month & Year of ORWAP Training Attended by Investigator(s): 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 1 Goal 6 Water Quality Resource: Yes Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom Project Number: 209654 South Deschutes County Local Wetland Inventory - Wetland Summary Sheet - Date(s) of Field Verification: 8/10/2010 Wetland Mapping Code: 112 Investigator(s): Alessandra Capretti Size (acres): 15.3 Data Sheet Numbers: SP 53A Location Legal: T 22 S R 10 E S 27 AC, DC, T 22 S R 10 E S Nearest Town: La Pine 34 AB Latitude: 43.6343 Other: Southeast of Hwy 31 Longitude: -121.5156 Basin: Deschutes River Soils Mapped Series: 29A: Cryaquolls, 0 to 3 percent slopes, 153A: Tutni loamy coarse sand, 0 to 3 percent slopes Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Riverine Flow-Through Slope Valley Dominant Vegetation and Comments Cowardin Classification(s): PEMC, PFOC Vegetation: Herbs: Juncus efPusus (Common rush), Festuca idahoensis (Idaho fescue), Leymus cinereus (Basin wildrye) Comments: Off-site determination. Agricultural use. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 15.3 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. Percent (approx.) of the Wetland Visited: 1 Percent (approx.) of the AA Visited: 1 Month & Year of ORWAP Training Attended by Investigator(s): 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 1 Goal 6 Water Quality Resource: No Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom 0 11 Project Number: 209554 • • E South Deschutes County Local Wetland Inventory Wetland Summary Sheet - Date(s) of Field Verification: 8/10/2010 Wetland Mapping Code: 113 Investigator(s): Alessandra Capretti Size (acres): 78.0 Data Sheet Numbers: SP 54A Location Legal: T22 S R 10 E S 27 CD, T22 S R 10 E S 34 Nearest Town: La Pine BA, CA, T 22 S R 10 E S 34 AB, DB, T 22 S R 10 E S Latitude: 43.6254 34 AC Other: Northeast of Hwy 31 Longitude: -121.5166 Basin: Deschutes River ISoils Mapped Series: 29A: Cryaquolls, 0 to 3 percent slopes, 115A: Shanahan loamy coarse sand, low, 0 to 3 percent slopes, 153A: Tutni loamy coarse sand, 0 to 3 percent slopes Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Slope Valley Dominant Vegetation and Comments Cowardin Classification(s): PEMF, PFOA, PFOC Vegetation: Herbs: Hordeum jubatum (Foxtail barley), Leymus cinereus (Basin wildrye) Comments: Off-site determination. Rural residential, agricultural use. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 78.0 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. Percent (approx.) of the Wetland Visited: ¢ 1 Percent (approx.) of the AA Visited: < 1 Month & Year of ORWAP Training Attended by Investigator(s): 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 1 Goal 6 Water Quality Resource: Yes Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PFM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom Project Number: 209554 South Deschutes County Local Wetland Inventory - Wetland Summary Sheet - Date(s) of Field Verification: 8/10/2010 Wetland Mapping Code: 114 Investigator(s): Alessandra Capretti Size (acres): 31.0 Data Sheet Numbers: N/A Location Legal: T 22 S R 10 E S 34 AC, BC, DC Nearest Town: La Pine Other: West of Huntington Rd Latitude: 43.6201 Basin: Deschutes River Longitude: -121.5210 ISoils Mapped Series: 29A: Cryaquolls, 0 to 3 percent slopes, 115A: Shanahan loamy coarse sand, low, 0 to 3 percent slopes, 153A: Tutni loamy coarse sand, 0 to 3 percent slopes Hydrology Primary Hydrology Source(s): Groundwater Hydro-geomorphic (HGM) Classification(s): Slope Valley Dominant Vegetation and Comments Cowardin Classification(s): PEMC, PFOC Vegetation: Herbs: Hordeum jubatum (Foxtail barley), Leymus cinereus (Basin wildrye) Comments: Off-site determination. Rural residential, agricultural use. Oregon Rapid Wetland Assessment Protocol (ORWAP) Approximate Size of the Assessment Area (AA) in acres: 31.0 AA as Percent of the Entire Wetland: NA. This question was intended for cases where the AA is smaller than wetland. Percent (approx.) of the Wetland Visited: 0 Percent (approx.) of the AA Visited: 0 Month $ Year of ORWAP Training Attended by Investigator(s): 5/2010 Number of Wetlands Assessed by Investigators Using ORWAP: 1 Goal 6 Water Quality Resource: No Wetland Classification Codes PFO = palustrine forested PSS = palustrine scrub-shrub RSB = riverine streambed (intermittent) PEM = palustrine emergent POW = palustrine open water RUB = riverine unconsolidated bottom • t Project Number: 209554 • 0 CL m O C N 7 C 7 •J Z" c O O U E CD cli 0 0 LO LO O O ro 0 0 m m N N O O O Q N N 0 0 0 0 0 0 0 0 0 0 0 0 0 0 N N Q Q l2 0 0 0 0 0 0 0 P, 0 0 0 0 0 0 0 co co co m co co m n r• r• r• r• r• r• 0 0 0 0 0 0 0 O O O O O Q Q N N N N 04 104 N O O m Q U 0 a N Cl) N d O LO 0 0 0 4 ~ O Q O 0 0 0 0 0 0 0 0 0 0 O 0 co 0 m 0 m 0 co 0 co 0 co P, r-_ rn rn rn rn o o ~ o 0 Q 0 0 0 0 0 N N N N N N O O co ~ 0 0 U 0 cD rD Q Q O O N N Q M O O R CD 0 O O N O Q Q M O a N O O O O N 4 0 0 tD co Q Q O O N N Q (DD O O r CD Q O O N J E x 7 z G (0 N (D Z' (0 E E a ym 7 E Z O J x co r x m a n a tf O n (O O C N 7 C C O O U S S S S Q S d 0 S S 0 O 0 d 0 d 0 O 6 0 6 0 d 0 T T 0 O 0 0 0 0 d 0 O 0 0 0 0 O 0 0 0 0 0 0 O 0 d 0 O 0 0 a 0 0 0 0 0 0 0 0 0 a 0 a 0 Q a 4 a a O 0 x Q 0 4 0 a 4 V n N m a0 O M m r N T m r ~ M T O d M N c C r M r a r M Cl) r V O f O n O Cl) m lf] CS m n co m CO fp M N N 1. ~ p O 0 O 0 O d r 0 d 0 r 0 0 0 0 0 d 0 O 0 r 0 O 0 O 0 r 0 O 0 O 0 N 0 M 4 0 N 0 M 0 S o D S T S T S Q S N S m M S r S 7 S p S S S O S n S S S M 0 Q 0 N 6 N 0 0 0 0 r O U O U O ❑ O ❑ O ❑ O U a U 0 U 0 ❑ 0 U a U 0 U 0 ❑ 0 U 0 U 0 ❑ 0 ❑ 0 ❑ 0 ❑ Q O Q ❑ a ❑ ❑ ❑ in 0 ❑ ❑ 0 © 4 ❑ ❑ ❑ ❑ ❑ C] ❑ ❑ ❑ ❑ ❑ ❑ ❑ ❑ ❑ ❑ ❑ m M co m Cl) Cl) Cl) M Cl) Cl) M Cl) M M Cl) M M M M Cl) M M M M M M co Cl) m m M co M M M M M m Cl) M Cry m C! 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For further information about Cowardin class, water regime and special modifiers refer to Classification of Wetlands and Deepwater Habitats of the United States document (Cowardin et al., 1979). Table E-1. Cowardin Wetland Habitat Classes and Water Regimes found in the South Deschutes County Local Wetland Inventory Labeled Feature on Cowardin Class Water Regime Special Modifier Map PABF PAB: Palustrine F: Semipermanently Aquatic Bed Flooded PABFx PAB: Palustrine F: Semipermanently x: excavated Aquatic Bed Flooded PABH PAB: Palustrine H: Permanently - Aquatic Bed Flooded PEMA PEM: Palustrine A: Temporarily Emergent Flooded PEMB PEM: Palustrine B: Saturated Emergent PEMC PEM: Palustrine C: Seasonally Flooded Emergent PEMCx PEM: Palustrine C: Seasonally Flooded x: Excavated Emergent PEME PEM: Palustrine E: Seasonally Emergent Flooded/Saturated PEMF PEM: Palustrine F: Semipermanently Emergent Flooded PEMH PEM: Palustrine H: Permanently Emergent Flooded PEMY PEM: Palustrine Y: Saturated/Semi- Emergent permanently/ Seasonally Flooded PFOA PFO: Palustrine A: Temporarily Forested Flooded PFOB PFO: Palustrine B: Saturated Forested PFOC PFO: Palustrine C: Seasonally Flooded Forested PFOE PFO: Palustrine E: Seasonally Forested Flooded/Saturated ESA Adoson Page E-1 June 2011 South Deschutes rI .7 E South Deschutes County Local We{land lnv_entoq Repgrt r~ • • Labeled Feature on Cowardin Class Water Regime Special Modifier Map PFOY PFO: Palustrine Y: Saturated/Semi- Forested permanently/ Seasonally Flooded PSSA PSS: Palustrine A: Temporarily Scrub-shrub Flooded PSSC PSS: Palustrine C: Seasonally Flooded Scrub-shrub PSSE PSS: Palustrine E: Seasonally Scrub-shrub Flooded/Saturated PSSY PSS: Palustrine Y: Saturated/Semi- Scrub-shrub permanently/ Seasonally Flooded PUBF PUB: Palustrine F: Semipermanently Unconsolidated Flooded Bottom PUBFh PUB: Palustrine F: Semipermanently h: Diked/Impounded Unconsolidated Flooded Bottom PUBFx PUB: Palustrine F: Semipermanently x: Excavated Unconsolidated Flooded Bottom PUSHh PUS: Palustrine H: Permanently Unconsolidated Shore Flooded PUSCx PUS: Palustrine C: Seasonally Flooded x: Excavated Unconsolidated Shore R2UBH R2UB: Riverine H: Permanently Upper Perennial Flooded Unconsolidated Bottom R2UBHx R2UB: Riverine H: Permanently x: Excavated Lower Perennial Flooded Unconsolidated Bottom R4SBC R4SB: Riverine C: Seasonally Streambed Flooded R4SBCx R4SB: Riverine C: Seasonally x: Excavated Streambed Flooded Page E-2 ESA Adolfson June 2011 South Deschutes County Local Wetland Inventory Report Palustrine System Definition.The Palustrine System includes all nontidal wetlands dominated by trees, shrubs, persistent emergents, emergent mosses or lichens, and all such wetlands that occur in tidal areas where salinity due to ocean-derived salts is below 0.5 percent. It also includes wetlands lacking such vegetation, but with all of the following four characteristics: (1) area less than 8 ha (20 acres); (2) active wave-formed or bedrock shoreline features lacking; (3) water depth in the deepest part of basin less than 2 m at low water; and (4) salinity due to ocean-derived salts less than 0.5 percent. Limits. The Palustrine System is bounded by upland or by any of the other four Systems. Description. The Palustrine System was developed to group the vegetated wetlands traditionally called by such names as marsh, swamp, bog, fen, and prairie, which are found throughout the United States. It also includes the small, shallow, permanent or intermittent water bodies often called ponds. Palustrine wetlands may be situated shoreward of lakes, river channels, or estuaries; on river floodplains; in isolated catchments; or on slopes. They may also occur as islands in lakes or rivers. The erosive forces of wind and water are of minor importance except during severe floods. • The emergent vegetation adjacent to rivers and lakes is often referred to as "the shore zone" or the "zone of emergent vegetation" (Reid and Wood 1976), and is generally considered separately from the river or lake. As an example, Hynes (1970:85) wrote in reference to riverine habitats, "We will not here consider the long list of emergent plants which may occur along the banks out of the current, as they do not belong, strictly speaking, to the running water habitat. " There are often great similarities between wetlands lying adjacent to lakes or rivers and isolated wetlands of the same class in basins without open water. Subsystems. None. Classes. Rock Bottom, Unconsolidated Bottom, Aquatic Bed, Unconsolidated Shore, Moss-Lichen Wetland, Emergent Wetland, Scrub-Shrub Wetland, and Forested Wetland. Unconsolidated Bottom Definition. The Class Unconsolidated Bottom includes all wetland and deepwater habitats with at least 25 percent cover of particles smaller than stones, and a vegetative cover less than 30 percent. Water regimes are restricted to subtidal, permanently flooded, intermittently exposed, and semipermanently flooded. Description. Unconsolidated Bottoms are characterized by the lack of large stable surfaces for plant and animal attachment. They are usually found in areas with lower energy than Rock Bottoms, and may be very unstable. Exposure to wave and current action, temperature, salinity, and light penetration determines the composition and distribution of organisms. ESA Adolfson Page E-3 June 2011 South Deschutes County Local Wetland Inventory Report Most macroalgae attach to the substrate by means of basal holdfast cells or discs; in sand and mud, however, algae penetrate the substrate and higher plants can successfully root if wave action and currents are not too strong. Most animals in unconsolidated sediments five within the substrate, e.g., Macoma and the amphipod Melita. Some, such as the polychaete worm Chaetopterus, maintain permanent burrows, and others may live on the surface, especially in coarse-grained sediments. In the Marine and Estuarine Systems, Unconsolidated Bottom communities are relatively stable. They vary from the Arctic to the tropics, depending largely on temperature, and from the open ocean to the upper end of the estuary, depending on salinity. Thorson (1957) summarized and described characteristic types of level-bottom communities in detail. In the Riverine System, the substrate type is largely determined by current velocity, and plants and animals exhibit a high degree of morphologic and behavioral adaptation to flowing water. Certain species are confined to specific substrates and some are at least more abundant in one type of substrate than in others. According to Hynes (1970:208), "The larger the stones, and hence the more complex the substratum, the more diverse is the invertebrate fauna." In the Lacustrine and Palustrine Systems, there is usually a high correlation, within a given water body, between the nature of the substrate and the number of species and individuals. For example, in the profundal bottom of eutrophic lakes where light is absent, oxygen content is low, and carbon dioxide concentration is high, the sediments are ooze-like organic materials and species diversity is low. Each substrate type typically supports a relatively distinct community of organisms (Reid and Wood 1976:262). Aquatic Bed Definition. The Class Aquatic Bed includes wetlands and deepwater habitats dominated by plants that grow principally on or below the surface of the water for most of the growing season in most years. Water regimes include subtidal, irregularly exposed, regularly flooded, permanently flooded, intermittently exposed, semipermanently flooded, and seasonally flooded. Emergent Wetland Definition. The Emergent Wetland Class is characterized by erect, rooted, herbaceous hydrophytes, excluding mosses and lichens. This vegetation is present for most of the growing season in most years. These wetlands are usually dominated by perennial plants. All water regimes are included except subtidal and irregularly exposed. Description. In areas with relatively stable climatic conditions, Emergent Wetlands maintain the same appearance year after year. In other areas, such as the prairies of the central United States, violent climatic fluctuations cause them to revert to an open water phase in some years (Stewart and Kantrud 1972). Emergent Wetlands are found throughout the United States and occur in all Systems except the Marine. Emergent Wetlands are known by many names, including marsh, meadow, fen, prairie pothole, and Page E-4 ESA Adolfson June 2011 South Deschutes County Local Wetland Inventory Report slough. Areas that are dominated by pioneer plants which become established during periods of low water are not Emergent Wetlands and should be classified as Vegetated Unconsolidated Shores or Vegetated Streambeds. Shrub-Scrub Wetland Definition. The Class Scrub-Shrub Wetland includes areas dominated by woody vegetation less than 6 m (20 feet) tall. The species include true shrubs, young trees, and trees or shrubs that are small or stunted because of environmental conditions. All water regimes except subtidal are included. Description. Scrub-Shrub Wetlands may represent a successional stage leading to Forested Wetland, or they may be relatively stable communities. They occur only in the Estuarine and Palustrine Systems, but are one of the most widespread classes in the United States (Shaw and Fredine 1956). Scrub-Shrub Wetlands are known by many names, such as shrub swamp (Shaw and Fredine 1956), shrub carr (Curtis 1959), bog (Heinselman 1970), and pocosin (Kologiski 1977). For practical reasons we have also included forests composed of young trees less than 6 m tall. Forested Wetland Definition. The Class Forested Wetland is characterized by woody vegetation (i.e., trees) that is 6 m tall or taller. All water regimes are included except subtidal. Description. Forested Wetlands are most common in the eastern United States and in those sections of the West where moisture is relatively abundant, particularly along rivers and in the mountains. They occur only in the Palustrine and Estuarine Systems and normally possess an overstory of trees, an understory of young trees or shrubs, and a herbaceous layer. Forested Wetlands in the Estuarine System, which include the mangrove forests of Florida, Puerto Rico, and the Virgin Islands, are known by such names as swamps, hammocks, heads, and bottoms. These names often occur in combination with species names or plant associations such as cedar swamp or bottom. Streambed Definition. The Class Streambed includes all wetland contained within the Intermittent Subsystem of the Riverine System and all channels of the Estuarine System or of the Tidal Subsystem of the Riverine System that are completely dewatered at low tide. Water regimes are restricted to irregularly exposed, regularly flooded, irregularly flooded, seasonally flooded, temporarily flooded, and intermittently flooded. Description. Streambeds vary greatly in substrate and form depending on the gradient of the channel, the velocity of the water, and the sediment load. The substrate material frequently changes abruptly between riffles and pools, and complex patterns of bars may form on the convex side of single channels or be included as islands within the bed of braided streams (Crickmay 1974). In mountainous areas the entire channel may be cut through bedrock. In most cases streambeds are not vegetated because of the scouring ESA Adolfson Page E-5 June 2011 South Deschutes County Local Wetland Inventory Report effect of moving water, but, like Unconsolidated Shores, they may be colonized by "pioneering" annuals or perennials during periods of low flow or they may have perennial emergents and shrubs that are too scattered to qualify the area for classification as Emergent Wetland or Scrub-Shrub Wetland. Unconsolidated Shore Definition. The Class Unconsolidated Shore includes all wetland habitats having three characteristics: (1) unconsolidated substrates with less than 75 percent areal cover of stones, boulders, or bedrock; (2) less than 30 percent areal cover of vegetation other than pioneering plants; and (3) any of the following water regimes: irregularly exposed, regularly flooded, irregularly flooded, seasonally flooded, temporarily flooded, intermittently flooded, saturated, or artificially flooded. Intermittent or intertidal channels of the Riverine System and intertidal channels of the Estuarine System are classified as Streambed. Description. Unconsolidated Shores are characterized by substrates lacking vegetation except for pioneering plants that become established during brief periods when growing conditions are favorable. Erosion and deposition by waves and currents produce a number of landforms such as beaches, bars, and flats, all of which are included in this Class. Unconsolidated Shores are found adjacent to Unconsolidated Bottoms in all Systems; in the Palustrine and Lacustrine Systems, the Class may occupy the entire basin. As in Unconsolidated Bottoms, the particle size of the substrate and the water regime are . the important factors determining the types of plant and animal communities present. Different substrates usually support characteristic invertebrate fauna. Fauna] distribution is controlled by waves, currents, interstitial moisture, salinity, and grain size (Hedgpeth 1957; Ranwell 1972; Riedl and McMahan 1974). Aquatic Bed Description. Aquatic Beds represent a diverse group of plant communities that requires surface water for optimum growth and reproduction. They are best developed in relatively permanent water or under conditions of repeated flooding. The plants are either attached to the substrate or float freely in the water above the bottom or on the surface. Water Regime Modifiers Precise description of hydrologic characteristics requires detailed knowledge of the duration and timing of surface inundation, both yearly and long-term, as well as an understanding of groundwater fluctuations. Because such information is seldom available, the water regimes that, in part, determine characteristic wetland and deepwater plant and animal communities are described here in only general terms. Water regimes are grouped under two major headings, Tidal and Nontidal. Tidal Water Regime Modifiers are used for wetlands and deepwater habitats in the Estuarine and Marine Systems and Nontidal Modifiers are used for all nontidal parts of • Page E-h ESA Adolfson June 2011 South Deschutes County Local Wetland Inventory Report the Palustrine, Lacustrine, and Riverine Systems. The Tidal Subsystem of the Riverine System and tidally influenced parts of the Palustrine and Lacustrine Systems require careful selection of Water Regime Modifiers. We designate subtidal and irregularly exposed wetlands and deepwater habitats in the Palustrine, Riverine, and Lacustrine Systems as permanently flooded-tidal rather than subtidal, and Palustrine, Riverine, and Lacustrine wetlands regularly flooded by the tide as regularly flooded. If Palustrine, Riverine, and Lacustrine wetlands are only irregularly flooded by tides, we designate them by the appropriate nontidal Water Regime Modifier with the word tidal added, as in seasonally f looded-tidal. Though not influenced by oceanic tides, nontidal water regimes may be affected by wind or seiches in lakes. Water regimes are defined in terms of the growing season, which we equate to the frost-free period (see the U.S. Department of Interior National Atlas 1970:110-111 for generalized regional delineation). The rest of the year is defined as the dormant season, a time when even extended periods of flooding may have little influence on the development of plant communities. Permanently Flooded. Water covers the land surface throughout the year in all years. Vegetation is composed of obligate hydrophytes. Intermittently Exuosed. Surface water is present throughout the year except in years of extreme drought. Semipermanently Flooded. Surface water persists throughout the growing season in most years. When surface water is absent, the water table is usually at or very near the land surface. Seasonally Flooded. Surface water is present for extended periods especially early in the growing season, but is absent by the end of the season in most years. When surface water is absent, the water table is often near the land surface. Saturated. The substrate is saturated to the surface for extended periods during the growing season, but surface water is seldom present. Temporarily Flooded. Surface water is present for brief periods during the growing season, but the water table usually lies well below the soil surface for most of the season. Plants that grow both in uplands and wetlands are characteristic of the temporarily flooded regime. Intermittently Flooded. The substrate is usually exposed, but surface water is present for variable periods without detectable seasonal periodicity. Weeks, months, or even years may intervene between periods of inundation. The dominant plant communities under this regime may change as soil moisture conditions change. Some areas exhibiting this regime do not fall within our definition of wetland because they do not have hydric soils or support hydrophytes. Artificially Flooded. The amount and duration of flooding is controlled by means of pumps or siphons in combination with dikes or dams. The vegetation growing on these ESA Adolfron Page E-7 June 2011 South Deschutes County Local Wetland Inventorrv Report • areas cannot be considered a reliable indicator of water regime. Examples of artificially flooded wetlands are some agricultural lands managed under a rice-soybean rotation, and wildlife management areas where forests, crops, or pioneer plants may be flooded or dewatered to attract wetland wildlife. Neither wetlands within or resulting from leakage from man-made impoundments, nor irrigated pasture lands supplied by diversion ditches or artesian wells, are included under this modifier and hardwoods. Special Modifiers Many wetlands and deepwater habitats are man-made, and natural ones have been modified to some degree by the activities of man or beavers. Since the nature of these modifications often greatly influences the character of such habitats, special modifying terms have been included here to emphasize their importance. The following Modifiers should be used singly or in combination wherever they apply to wetlands and deepwater habitats. Excavated Lies within a basin or channel excavated by man. Impounded Created or modified by a barrier or dam which purposefully or unintentionally obstructs the outflow of water. Both man-made dams and beaver dams are included. Diked Created or modified by a man-made barrier or dike designed to obstruct the inflow of water. Partly Drained The water level has been artificially lowered, but the area is still classified as wetland because soil moisture is sufficient to support hydrophytes. Drained areas are not considered wetland if they can no longer support hydrophytes. • Farmed The soil surface has been mechanically or physically altered for production of crops, but hydrophytes will become reestablished if farming is discontinued. Artificial Refers to substrates classified as Rock Bottom, Unconsolidated Bottom, Rocky Shore, and Unconsolidated Shore that were emplaced by man, using either natural materials such as dredge spoil or synthetic materials such as discarded automobiles, tires, or concrete. Jetties and breakwaters are examples of Artificial Rocky Shores. Page E-8 ESA Adolfson June 2011 South Deschutes County Local Wetland Inventory Report APPENDIX F: ORWAP RAW DATA ESA Adolfson Appendix F June 2011 0- • • i A O I W t W 00 W J W ~ W U W A W W W N W r W 0 N ~D N OD N J N 01 N to N A N W N N N N O ~D r 00 J ~ r U A W N - O J U A W N ~ O O O O ~ ~ p Ui A W N D a Z N fn N O O O ~ Z 0 O d 4 N m m N ~1 p O ' m m ~ m d n~ ID ° o - r - nl d - ~ ° o < < T O a d O ~ j ~ N N ~ R N d ~ D ~ ~ l ~ W ~ ~ b7 N Ip O H O O .-O n O' N g m° x m V m g' N S o A v, ~ m ~ J o + o n p rr `5. j W o c o j 3 a' V m Ut o N S o A cn m o 0 0 0 ° 3 `5. o y o n2 m ° ~ ' a a o 0 H o m m a v o o° _ a °0 4 o m m 3 o o a, p m a o 0 N m o _ ° 0 o 0 2 m o P P o Y' 3 o' m y< m ? Q 3 w o -a m v m y o y° y z m n m y a o n m p ~o o rn o 0 0 o m m o m o o $ p o y N Ei 0 o S w 0 2 3 k'n _ m N cn o 0 m a F n d o ~o o o N 0 c? n m F m p- n' y - p o H. m Dy n' d o m yy z 0 o DD pC O a N N f ° ° e m m N O O d O (D O y E Y? m w O D O O O p w n 3 O o O e e rJ N t0 p y G O O O) O p 3 N a N nl ~ C p, < ~ ~p ? D ~ - ° O D n1 (0 D 3_ y N x y N 3 T_ - N g m 3 o_ N A y O N a ° o y^ tj C 3 5?. ] y o o m (D ( 'f S2 m e~ o N j c 3 A i ' f~ O o a m C N< N m y y ~ c Ni ~ ° a m m o n Er o M v' N d m O 4 O v Gr O j N N N 0: d u a d G D S o tl 00 N GG O " n N a y - H d O~ A p° - d = N N N y G y ~ ~p (p t0. O O' O y d o C y ~ C g N O f~ O N 'Z m 3 3 D H° J m v ? o° . 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O O O o 0 O O O O O O O 0 0 O O O O O O O O O O O O O (.Il O O O O O O O O O O O O O O O O O O O O O O O O O O N Q r O O O O O O O O O O O O O O O O O O O O O O O O O O J O O O O O O O 0 0 O O O O O O O O O O O O 0 0 O O O OD 0 0 0 0 0 0 0 00 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 o m C' 0 0 0 0 0 0 0 00 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 z O O O O O O O O O O O O O O O O O O O O O O O O O O IV Q O O O O O O O O O O O O 0 0 0 0 O O O O O O O O O O lp n ^p O 0 0 O O O O O O O O O 0 0 O O O O O O O O O O O O ? O O O O O O O 0 0 O O O 0 0 O O O O O O O O O O O O N lJ O O O 0 0 O O O O O O O O O O O O O O O O O O O O O ~ !n O O O O O O 0 0 O O O O O O O O O O O O O O O O O O O ~ O O O O O O O O O O O O O O 0 0 O O O O O O O O O O aD O O O O O O O O O O O O O O O O O O O O O O O O O O ~ O O O O O O O O O O O O O O O O O O O O O O O O O O p O 0 0 O O O O 0 0 O O O O O O O O O O O O 0 0 O O O N 1 XI O O O O O O O O O O O O O O O O O O O O O 0 0 0 0 O ~j O O O O O O O O O O O O O O 0 0 O O O O O O O O O O W N O O O O O O O O O O O O O O O O O O O O O O O O O O p O O O 0 0 O O O O O O O O O 0 0 O O O O O O O O O O N WWW O O O O O O O O O O O O O O O O O O O O O O O O O O N d O O O O O O O O O O O O O O O O O O O O O o 0 0 o O d g C9 O O O O O O O O O O O O O O O O O O O O O O O O O O N d Q CCC~~~111 N O O O O O O O O O O O O O O 0 0 O 0 0 O O O O O O O p01 ~ Q O 0 0 0 0 0 0 0 0 0 0 O 0 0 0 0 0 0 0 0 0 O 0 0 0 0 O 0 a O 0 0 0 0 p p p p 0 0 O 0 0 0 0 0 0 0 0 0 O 0 0 0 0 O ...JJ O O p p p p p p p 0 0 O O p p p p p p 0 0 O 0 0 0 0 O N a O O p p p p p p p 0 0 O O p p p p p p 0 0 O 0 0 0 0 O W w O 0 0 0 0 p p p p O O O O O p p 0 0 0 0 O O 0 0 0 0 O ( w O O p p p p p p p O O O O O p p 0 0 0 0 0 O 0 0 0 0 O !w)1 O O p p p 0 0 0 0 O O O O p p p 0 0 0 0 0 O 0 0 0 0 O rn O O p p p p p p p O O O O O p p p p p p p O 0 0 0 0 O V O O p p p p p p p O O O O p p p p p p p p O 0 0 0 0 O m a 0 O O p p p p p p p O O O O p p p p p p p p O 0 0 0 0 O W O O p p p p p p p 0 0 O O 0 0 0 p p p p p O 0 0 0 0 O ~ a O O O O O O O O O O O O O O O O O O O O O O O O O O O A O O O O O O O O O O O O O 0 0 0 O O O O O O O O O O O N J A J W J N J O O~ K) T CA CT J O~ Q\ a\ U A a W Q a N~ aO ~D CA JU Q\U U A W N ~ O A ~D A CA A J A CT A U AA A A W A N AII 1 0 0 0 o v v OY (n A W N ,D n x a d y~ ° n 3 ~ ~ c ~ x 3 ~ ~ n m ni d ~ o Q' ~ nri sa 0 o m n nom' y v m - n Z c of ~ n a ~ d d n ? - m a- ~ b7 d ¢ y N ~ d N d n G H N O ~ '00 m b b d O C c~ 8 o N O N N C F O 0 0 0 O C 9 d 0 0 0 N d O F O N p P 0 d t~ n O C O O C 00 00 00 O A N N j y C _ Q n y O 0 C d N W O = a CP ° CT O O O o (0 p T d fG C. to O d f~ N N C J 0 N 0 O 0 91 i fD D y d O a S c-~ O d fC O l Z O r O G - N n 0~ 3 N J ~ A J 1_ d D n O n f0 O O C O d N A c c 0 0 = 0 4Ci J O ' N H N S^ O O a = N O CY f~ 0 N 0 N N <0 0 ID = ti N 0 0 S O O C (a N O O CS N O O ((pp O O N O O fC O i C . d O a t n F o m T rS S S o w o ? C) O F o < m m y -p m a" O 3 N A m y v O d N F Q F ac c °i = F, n F m o m o o a N a fn 3 o < N O rn d = n O F m S O g 0 3 _ n ~D T m c 0) = N S S N S 0 n m N N a rn c C N lc y = m N m ^ o C N = O N yy O Q c _ < D O C a N a A ni 3 °o o. C n N m CY 0 j (0 „ n ~ N E o 0 . c C 3 a y D y O N o. N O n N 8 N~ = C O Ol . n ~ d n v, ' O a O, H ] Gt O O . W = O y (0 n. = y N < a (D O .O-. O tt~Y f O O 3 a (0 0 fD (D N d ? 0 CS ° C f0 a O Oc_Y N C N' y o m n N n O m N j d 3 j 7 O v N » a ? n m m 3 ry CT o m y o m a m a 3 f~ - F n m N S O m 3 m m m ° 0 3. H a G? d T m o- y . ° 3 can a Cs' m o a m S ° C7 d D N n O O 4 1 ~S CC'~~ S j f0 " d+ N O N F O ° 0. f D ~ ~5 p Ol N N oY f . O O S _ , t7'') t y C f0 G S N 'O y (D 4i O O c C 0 N COY C Y . 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N N N <u o> F x o- p fp .d. j j j O m< o y . d o ~ m 3 = F 91 0 0_ d ~ a a s d A O o . 7 CY . y ~ n d d U. y ~ ~ , 3 d n o 0 0~ m a a a d F< m d o o d o ~.~g ° n i m ~a g n N ~~.~dg so o 0 ~y3g ~d n o~ ~ y m O O >>~d o n N N ~ F y o- < 3 O d 0 a ~a 0- ° x(^ da~a~d ~ `z m N N N n o d ~,~ax c ~D. d ~ T ° m Q y f/ O tp ~ ° y (D ~ F- x m f O fG f/i fD N N x° m a ~ = j O c 3 d d d O a° d m ~ a~ ~ F T G p O y ~ m c vii ° . N a -do ? fnD F n n~ n tD ? ~ d a n o a° m N m x N x N x b N N d ~ y x n< C m m ~ p_ Ci ° C d g ° 3 o d a o- o a n i ? n m ~p 9 m 0 a y a n n ip d o. o d o. c o m c d C1C rn C n ut C n A d o o m c H d a d ° N n o ~ c~ w d o T F p o c p H d f~ o~< y m f 3 ° F o~ c cn ~ n~ ° o, y o o _ f m 7 ~ ~ F c d H d m 3 'm _ m n " o m~ m D v ~G a O p 0 0 n y c m Vl VI ~ 4i o ° dOj 0 m O' Sl O 7' w .0.. N C O y 0 ^Cc ? O O y p°j O O T O - W ~ y~ d y. 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O ?5j. .d. d `0.. d ~ X 0 " m F ° d m v y 3 O J N d fV0 (7 T 4i p d N 7 y - x 41 O X d° G N A O N ~ O C d n \ N N fD o d y d n y o m' o S . y . p C n m < m n~ a g .C ( d o o° ` G o TI O T m F 3 m m 8 m y m n m fD o 'o 3 y o a c a n 3- n x v+ v d n v n Q m N N n C O N O y O ° N O fD .Q V C y lp 0L ? n D O' y y d 3 (D d N N 0 0 0 0 0 0 0 0 0 0 0 0 0 0 ~ C7 O O O O O O O O O 0 0 0 O O N O O O O O O O O O O O O O O W ']7 O O O O O O O O O O O O O O A O o O O O O o O O O O O O o f.n O O O O O O O O O O O O O O O) d Q rti O O O O O O O O O O O O O O V O O O O O O O O O O O O O O m 0 0 0 0 0 0 0 0 0 0 0 0 0 0 C' 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 z O O O O O O O O O 0 0 0 O O IV Q 0 0 0 0 0 0 0 0 0 0 0 0 0 o q`"'i a b O O O O O O O O O O O O O O p O O O O O O O O O O O O O O ~ 'A O O O O O O O O O O O O O O p~ (n O O O O O O O O O O O O O O V O O O O O O O O O O O O O O ap [ O O O O O O O O O O O O O O ~ O O O O O O O O O O O O O O p 0 0 0 0- o 0 0 0 0 0 0 0 0 0 k 0 0 0 0 0 0 0 0 0 0 0 0 0 0 ~ 0 0 0 0'-a,~ 0 0 0 0 0 0 0 0 0 o W ~ 7 O O O O O O O O O O O O O O p ' p C O O O O O O O O O O O O O O ~ W WW O O O O O O O O O O O O O O N d a V O O O O O O O O O O O O O O N d a ~ O O O O O O O O O O O O O O N d O O O O O O O O O O O O O O N d Q 0 0 0 0 ° o 0 0 ° o ° o o ° O O O O O O O O O O O O O O N O O O O O O O O O O O O O O fwia O O O O O O O O O O O O O O ? 'D O O O O O O O O O O O O O O ~ C ' O O O O O O O O O O O O O O ~ y O O O O O O O O O O O O O O V 'D o ° o 0 0 0 0 ° o ° o o O o ~ a 0 0 0 ° O o ° o 0 0 0 0 0 0 ° o a O O O OO O O O O O O O O O N ~ • • • to A to W ~ U O N ~ oAO J tAii A w N A A O ~ ~D w 00 W J w a W to W A W I II O O O O O a o o m o o 0 0 o o Q ~ m m `D m < v i o m~ = d m Q o a no • vci T c~ m m n a ID 0 W j~ o o c~ n ~ n n a ~ a m m ° O p o f ? O S n v~+ ~O ~ y O D O O N O m" n m° o °F o ° = m y O y S 3 0 rs S < O D O _21 ° o m e F ~ o 0 c m O S ~ 3° y a G O D O a O N y 0 ~ o° o m c ° _ ~ m o 3 F y, fn S m ~o ~ y 3 S O D vi n n O L O N ° c o m ° o~ 0 y °F 3 to O O S m 3 G O cDi 0° g o m m iv ° m ° c=~ o c a s o In y m_ ~o g O 3 m d y m o m IV = ~ c a o h a m fp o 3 m m o w m N O c n m n m fo a - m m- o iv F c o ? a. c 3 m o _ o- N v+ N ~ ' ? c o a pia W O d j w tP Q O O (00 S y O y D 3c o a O ? o S d o~ Q (C(ppS t0 O" J N 4 O ~ n N N F QO G N N O O A ` duo- 0 0 O O ~l g N f N 09 O tD S V - fD S ~O d y n~ O ~ c o J C.> W _ m d m y ° 4+ O iv GOi (O N O' 3 _ N y y J z FD N y 3 ( - (D n _ ^ (D O t/~ S 1 1 y N w' O m t° S 3 c O ' - d C a N O m O S N y O N (D z N^ N 0 3 CIl 3 N N O y O y T (D S N N rJ z N O O' N = d N N O (D O y O F O m 3 m O m O x m o m 3 F y 0 > o m 0 o-f° x n - o M 3 a o m m - m O vo 3 g o F p1 m a x ni m 0 m m y v~ a o g f 3 o ~ ' c m m 0 3 c m 3 z a c m 0 a v' 3 3 N j m 2 c m N 3 ° a 3 o d c s 3 ~ o ° c o 3 ° ~ d c ~ z m . o m - ° f ° a 3 < n o 3 ' m o^ 3 ID m vi 3 Q m ° N 3 1 d c v m 3 in y N 3 n O X 3 n d . N a o w r ii 3 y 0 y X 3 - T c 3 ' Q m 3 k SR i r o ii ° c O O 3 3 Ot y S m 3 N N m K 1 f m O m X j N p~ f F a a 0- O x ° o m y (p A n 0 0 ' j Np 1 O- O X O o m N ° Q y y 0 y Q j J N d° X o m ? O y, O - Q a o p y 1 ° X K 3 Ul N i A d o d o C] m m 3 c d O ^ m v c D m 2 c, o m o c D o m o m m , T o 3 m o y m 3 3 0 n c y o F O' y m o F 3 n n N N y ID d a N y o m N F 3 z N y fD d O a d i c n o O q y 3 Z m N F y Q y N z c o y y F y m 3 y y N n gi 0 fp Lg 0 N A O p ° m tD O' O v, n 3.9 a w O' o z N ° n O' O /1 3 d o 0 O O 0 ° ? Q, - 3 y d o N N O c Q H ' ? 3 9 d O . IV Q o m E o a l (D y O_ y N c Q 00 p N N - m 0 y m o d N y 52. n y - _ - l1 tD ' y N ° O y y f~ v+ d y N y v 3 m z m N E{ N - m - m ¢ O ° N H y o m F - o b' ° m N F - 3 fO d ~ y m n m y 3 m(p d f9 n y 3 O' O . N O O o 3 = n T `G y n O y 0 < o 3 y S ~G y C d N a o S y y C ( O O 0 ID ( n y y O j O N 0 d N N d= O N° 0 O F y. N J O 0 5P fD O N y O N J ~ 7 0 fD d 0 . O N a y F 2 fD _ v ( ] - 0 a 5. 2 y ° o 0 ' y F m 3 m a F m o . 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F o M y 3 m o D 0 . m d o ~ H 3 m 0 0 0 0 0 0 0 0 0 0 0 0 0 ~ C7 O O O O O O O O O O O O O N [Sf O O O O O O O O O O O O O W '1] O O O O O O O O O O O O O A O O O O O O O O O O O O O O N O O O O O O O O O O O O O O) N Q ^ O O O O O O O O O O O O O V O O O O O O O O O O O O O 00 O O O O O O O O O O O O O c0 O O O O O O O O O O O O O p O O O O O O O O O O O O O , z O O O O O O O O O O O O O N O O O O O O O O O O O O O O Qt d b O O O O O O O O O O O O O p O O O O O O O O O O O O O U O O O O O O O O O O O O O ~ V] O O O O O O O O O O O O O v r-] O O O O O O O O O O O O O Qp L•' O O O O O O O O O O O O O ~ O O O O O O O O O O O O O ~ O O O O O O O O O O O O O ~ 'X O O O O O O O O O O O O O ~j 0 0 0 0 0 0 0 0 0 0 0 0 o W N O O O O O O O O O O O O O p ' p C O O O O O O O O O O O O O ~ ' y 'D O O O O O O O O O O O O O N y a Q 0 0 0 0 0 0 0 0 0 0 0 0 o a m t7 O O O O O O o O O O O O O N N Q C~1 O O O O O O O O O O O O O N y 0 0 0 0 0 0 0 0 0 o O o o W a o 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Cl 0 0 0 0 0 0 0 o O N Y O o o O o 0 o O o 0 0 0 o w 0 0 o O O O O o 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 o O O o 0 0 0 0 0 0 0 0 0 m 0 0 0 0 0 0 0 o O O O O o ~ .IDS 0 0 0 o O O O O O O O O O W a 0 0 0 0 0 0 0 0 o O o 0 0 ~ a ro 0 0 0 0 0 0 0 0 0 0 0 0 o g a 0 0 0 0 0 0 0 0 0 0 0 0 0 ~ 0 0 0 0 0 0 0 0 0 0 0 o O N a • • • ~ J J D 00 J J J ~ J U J A J W r N J J O T ~O Q\ 00 T J O~ 01 Q~ O\ U A W p~ N O ~D OO J ~ v o v v o m m o ~ o ° y ~ n o c ay ~ g d ~ U ~ d d g o ~n m d m ° ~ o > > m n ay ° g" m n H O < m m n m n m d ° O o r n O m o D d O O = O O m m ° yo d P m o j D O C= N N o o m c 3 ° ~ c ° 0 F = ~D N O a o m g F D OC = N O- O o o m c = o? o F = Q o< F ~D O O a= N ° dc o m n o m C 3 m O a 0= T o _ c m f f n s m H g = n a_ 0 N d P o= d N m n a O N d Q C yy P o i D n m ° - . o Ih a l n° c m m =o H m N d a? 3 m m o o In m d m c w N ~p C O C m° n S to "^S O y H f. S n N N a 7C = d m n w O- n O C i - n = ma y m n o C --o o o- O' 0 0 N d F o- O J m o- ° N c_ d o l n_ o- ? N O = O= d- 0 _ N ° m y @ cn7 _ o m N N c . O= n O ° O G~ d (D a ° Q C a n m n 3 d O fn = ~S m N O O - g m 2 N - d O d m c a m o c o N O o m m N EF O~ O N 2 m N N O _ O O ' H O N -^S _ Or 2 m H s? m 2 0 < m a ci a n -i 3 d d ~p d = S> G c d ° d S m S T N d 0 m= = N m f0 N' N N O O 3 C = m y _ d O O O O S d - N° 3 m y y 9~ O O O O a a T m C= n d N m m d O fn a m N = d D f_ N = y° d O 3 P F O = m n c 3 O m X O n= 3 a o N a O n ~D c 3 2 N. X m tC j a F o n '0 c O O F a _ O G N F f< d fD N= . D d S N Q N o = N 4i N O^ 3 N C y' N C O C " l0 = N 4i F F m = H° ° m - n n c ° N a a o 9 n - o g° m o! K o 0 3 g Qi o° m m o 2 N° T m a b' o" m ° a 3 m° Q m o0 0 n n _ n i d u t~/ j j ~O d t0 m ao d m d o N fD ~S P 3 o -^S C, n 3 m `3 d o ° O h N m 0 c 2 O- o m o d o o g m m 2 0 N- p -.0 ° i n a F _ d m 3 d o ~o o m m o n x v° m ° w c D m 3 Z N m _ o y c D H m Z n = n o a~ ~ c = m S F N m Q n S m d 3 C - N d n d y d a n a °F O N O m= F. - y d ~ Er 41 N d O y 3. .o c ^ w o o v 0 0? N m N m d O d 3 y a ^ o m x ° 3 m w y D= . f0 n y m F d = f0 n `5. 4i = o c O ~ d d vi `3 (p p, N _ N O m °o n m m~ o mo 4. w T o , d m ~ ID L~. ~i D r. T m ° o m m a 3 m m . m? cWn v o a 4 o ~ o ° y 3 c o^ o- m o' T y S c o- ° 3 0 3 m° m 3 v 3 w F m H o v ° ? 3 0 F N 3 . o c `z °i o o o y m o - - . 0 N f S m m d m 3 = a O = m - 3 m m n m m m N m ` ~ d 3 0 ° m - n m 1 m N m o D N 3 0 2 y~ F ~ m x D n O n fn° n d 0 0 0 0 0 0 0 0 0 0 0 0 0 0 ~ C7 O O O O O O O O O O O O O O N [rJ O O O O O O O O O O O O O O W 'Sf O O O O O O O O O O O O O A O O O O O O O O O O O O O O Ol i~^ O O O O O O O O O O O O O O d Q r-y O O O O O O O O O O O O O O V O O O O O O O O O O O O O O Oo 0 0 0 0 0 0 0 0 0 0 0 0 0 0 o co t" 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 z O O O O O O O O O O O O O O N Q O O O O O O O O O O O O O O W n ^~J O O O O O O O O O O O O O O 'A O O O O O O O O O O O O O O (T O O O O O O O O O O O O O O ~ (/J 0 0 0 0 0 0 0 0 0 0 0 0 0 0 ~ y 0 0 0 0 0 0 0 0 0 0 0 0 0 o m ~ 0 0 0 0 0 0 0 0 0 0 0 0 0 0 ~ C O O O O O O O O O O O O O O N O O O O O O O O O O O O O O O , k O O O O O O O O O O O O O O ~j r~ 0 0 0 0 0 0 0 0 0 0 0 0 0 o w N 0 0 0 0 0 0 0 0 0 0 0 0 0 o a 0 0 0 0 0 0 0 0 0 0 0 0 0 0 ~ 0 0 0 0 0 0 0 0 0 0 0 0 0 o N m c C] 0 0 0 0 0 0 0 0 0 0 0 0 0 0 m O O O O O O O O 0 0 O O O O N y Q O O O O O O O O O O O O O O N y ~ Q 0 0 0 o O O o 0 0 0 0 o O o Y x 0 0 0 0 0 0 0 0 0 0 0 0 0 o N Y 0 0 0 0 0 0 0 0 0 0 0 0 0 0 W o O O o o O O O o 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 ~ 0 0 0 0 0 0 0 0 0 o O o 0 0 ~ 0 o O o 0 0 o O O O o 0 0 0 ~ 0 0 0 0 0 0 0 0 0 0 0 0 0 0 ~ D 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 ~ 0 0 0 0 0 0 0 0 0 0 0 0 0 o Ao Y 0 0 0 0 0 0 0 0 0 0 0 0 0 0 ~ ~ O O O O O O O O O O O O O O N ~ • • • N N O O ~ to N O A N O w N O N N O N O O ~O ~O ~D oo ~O J ~D D, ~O U ~O A ~p w ~p N [p O pp b pp oo pp v pp o~ ~ ~ ~ A ~ w ~ N ~ ~ o ~ ~ ° p w co p w ao O w v p ~ a g j o m ~ m C a D C J o 7 J 00 J N D c d N - cn O c p O c~ 3 m O c m m a O N a v° fD ° J m y N C N N N g ~ fD (D p J D p (G ~ ~ J ~ g g m y 'o J ~D 3 x' m H 3 y s 3 o 3 0 << m (D J o ~J H n w o 8° fD m J m o ° o v m fD ' y m o ° fo ' o S 3. m g F a o m m Q S t O S C J n a o n 0 m m m + d n m o o S C J n d, J ° w d o c J- m O O- O m m c y O g m m y o _ c N O C - c m ° u - o a N v, - z j U ' m o - . J N l~D y o c O (D D N n D m J fD o '0 m m m J o tn' J o J d m " o- ° S x m 3 2 °m ° o ~n v, J 3 w J o 4 c m q O w w J c ~D- ~ ~ 2 m a m o J u~ J n ~c ° c o d n c H r o o m , o o o 0 0- rn m o J o a a 'o m° o y. o rn 3 n J - o f ~ o~ O n n n on o n o m o s m o3 J n a m c c o ^ y ° m o o m n °1 o m o- ° ° ` 0- ° J o m c y o m n fo H m n y m m m m - c o c~' g o m g g m o t'n 3 o D a C) a' o ~ F v o J m [p F m y N y N O _ N " F g O n N y °.1 m c R O F N F o n O N y? d o d n m o m g m n vi ° f0 v g .d. n N m ~<o- mi u N D J O f o v' 3 m= O^ c o N 3 m ~ ° n 3 m ° o m y m c 3 n . >1 m ' ° _ x o g o n m< Q (7 n o D c a, o < n ° 3 n o - an cn 6 3 o n Er (n 3 m f n o g m g °c m" N &Z f °f n m m J° m °w H -L m-- 2L m w o o y o o F m o m m fD rs m J° d m a 2L " D J 1 n J O J --4 m D° m 3 m 3 x a , D m g m a m f A o g o F J d m f7 RE F m y n o cs Fo F y° n No m g u E5- m m o m n m m g° m n ~ U1 J ° Q r F v° D N O > O > N fD a m o ur S n N p1 m n w ry y n N n J C o o o D y F y N ur O- Q S J m N C n J j ` N y y C x m m c C O ( (p N 41 d N ? (n N ~ y m _ `m ~o N ID ~ N O n F 4 N n n d d t~/i (O N f0 O pOj N y 3 3 H 0 S o n S H n m m i y o ur n vl m f- w H F 'D o a J E O ur n co J o '<n J 3 5 m o m o ° g F ° n o m° J n H a c m N no a° O m .g F, 3 = o c a lp „F--~ mA °c v o y c m o n --I o n m D . a 3 N~ N n C f9 ~ ~ F~ ° l~ y 0 d N N N J N O ? O d D mo N N .C.. ` G N JJ O 41 ~ d m O O O O 5 0 O ~ O O S O O ~ 0 0 0 ~ O ~ ❑ O O O C O 5 ` 0 O ~ O O S O O ~ O O O ~ O N [i7 O O O O ~ O O r 5 ` O O S O O ~ O O O G ` O W 17 O O O O O r ` 0 O ~ O O O O ~ O O O ~ O A C) C O O O O ~ O O ~ O O S ` ° O S ` O O O S ` O (T "y" O O O O 5 ` 0 O ~ O O ~ ` O O ~ O O O ~ O ` O O O O ~ O O ~ O O ~ O O ~ O O O ~ O V ~_.i ~ O O O O S ` O O ~ O O S ` O O ~ O O O ~ O Oo 0 0 0 0 ~ o o ~ o o ~ o o ~ o 0 o S ` o 0 0 0 0 ~ o o ~ o o ~ o o ~ o 0 0 ~ o o 0 0 0 0 ~ o o ~ o o ~ o o ~ o 0 0 ~ o z ~ O O O O 5 0 O S ` O O S O O ~ O O O ~ O I V O C C O O O O ~ O O ~ O O S O O ~ O O O ~ O n "d O 0 0 0 S ` O O ~ O O S O O ~ O O O ~ O p ` O O O O ~ O O ~ O O S ` ° O ~ O O O S ` O ~ ~ ` O O O O 5 0 O ~ O O ~ O O ~ O O O ~ O ~ V1 ~ O O O O 5 0 O G ` O O S ` ° O S ` O O O S ` O V y O O O O 5 ` 0 O ~ O O ~ O O ~ O O O ~ O pp [ C O O O O ~ O O ~ O O S O O ~ O O O ~ O ~ O O O O C O O ~ O O 5 0 O ~ O O O S ` O ~ O O O O ~ O O ~ O O 5 0 O ~ O O O ~ O , C O O O O ~ O O ~ O O 5 0 O ~ O O O ~ O ~j ~ ` O O O O 5 ` 0 O S O O ~ O O ~ O O O ~ O W N C J ` O O O O ~ O O 5 ` O O ~ ` O O ~ O O O ~ O p ~ O O O O 5 0 O ~ ` O O ~ O O ~ O O O ~ O ~ O O O O 5 0 O ~ O O S O O C O O O ~ O d n O O O O ~ O O C ~ O C O C O O ~ O O C O S O N a O O O O ~ O O ~ ` O O 5 0 O ~ 0 0 0 ~ O N Q ICT+I] C J O O O O 5 0 O ~ O O S O O ~ O O O ~ O N S CC) O O O O 5 ` O O ~ O O S O O C ` O O O ~ O O O O O ~ O O ~ O O 5 O O ~ O O O ~ O N O O O O ~ O O ~ O O ~ O O 5 O O O ~ O W O O O ~ O O O 5 ` O O 5 0 O ~ O O O 5 ` O p O 0 0 C 0 5 0 O ~ O O 5 0 O ~ O O O ~ O ~ C O O O O ` ` O O ~ ` O O 5 0 O ~ O O O ~ O ~ O O O O ~ O O 5 ` O O 5 ` O O ~ O O O S ` O V / y C O O O O S O O ~ O O ~ O O ~ O O O ~ O pwp O ` ` ~ O O O O S O O G O O S ° O ~ O O O 5 O ~ 'aV ` O O O O ~ O O ~ O O 5 0 O ~ O O O ~ O N ~ • • • N ~ N A N A N A N A N A N A N A N A N A N A N W N W N N N W N w N W N W N NN NN N N N N N N N N N N N N N N N O ~D oD J ~ to A W N O \D 00 J 4\ U A W N ^ O \O GD J C\ In A W N O ^ l0 OD J D, to A W N ^ O R 000 J ' ^ II cA0 NA O T CAT O ? O W O N Y pNj y C o0 O O 1 ~ ~ p o m :i7 ~ d .Z7 d O ~ ~ O N ~ x d ~ d ~ Z F c o 0 O 0 a ~1 N ~ ~ n j 0 p 2 ° O ° T o d n ~ r p1 ° ~ o ~ fJ o 0 W n O O w W N o 3 V ° 3 ri O O O F S O S o ~1 ° S o S S F g -1 o V J N ow o j a D o Z Z p Z y f W 3 > > o oD Z N £o 5 - n N d ll T O o ~ m m a C .y+ f~0 N d cfD x 0 d a 0 O A (D fD ^ O O D A N y a V V V 0 V N O p p O ' O S Z O S T D c rS y ' C y p o o ' f0 d W w O_ d 3 d O 5' d ~ O y m S' 3 c w m m 9 n O 3 3 o N O O a. a d T T d O d g m fo C ° C _ d b ] q o y y, F O m m S o O 3 J fD d (dy W o F^ O W A o y ooh O w~p A y md O n N m da S fD v+ ~ n ~ y 'o _ O ° o~ _ m _ p an m . . N 3 b' d d.° d c n o o O Q m ~ N c 3 > 7 S O c3 (7 < C 1 m O N d N •1 N d O N N N N O H n N Q d d 0 0 d 3 O N 3 N 3 S , d Q ; < N N d Q 0 N N U d y - 0 N ' m O n N N n , SD S d 3 c n m ° ` p v N w N tl I' N N m N 0 m N d m A N o N N A j g ' m u ° o 3 3 d m - c ° v ~O d v > o > m rn + m o an d d m m m m d < c m n d o O - m , ' m m an , > p m = F w m ° m a ^ m ~ ° 3 V ° m o m ~ n d m m d . m o 0 o = d O d y O T 8 y c m D ^ m o n D y o o • c n . o i y ' O ~ m x 2 ° rn ° D c °c o c b O m y n 3 n y > > ° n d 3 S m o c G d m o n c O d m A. O d c Cl) O ° n d a c o i o n y 0 ° 3 o p O m fii f y ° c m a F n O O r m d Z7 C CJ o o- s x y c 1 F - cp y d o < d m° n c ° n m , m o d c° n p o y m m m o o F v m m < o F d $ y o m T o x ~D an c d m d m N m N n w nd ? c? F x C ~c C ~x C 1 m o a v d a 3 °i `c p1 y 3 a' d O o 3 C o o 3 Q. p o d c m GSA CNC d ? a d O O N N `2 d 3 y' 9 N . Q= N N = Q C N C N N O ~ F ° m a m -°1 m 3 n o o ' D T n 7q N t p D r o n m r > ~ ? N n d x d ~ d n ry o m y N y ~ o ~ ° o v = F~ v = v ~ ~i D o ~ _ y y y y D yy S S yy S v d O d j n m ~ g m d 0 0 0 0 0 0 0 0„ O 0 0 O 0 0 0 0 0 0 0 0 o O O o o O 0 0 0 d 0 0 0 0 0 O O O O O O O O O O O O O O O O O O O O O O O O N ~rJ 0 0 0 0 0 '+~:G i,* O O O O O O O O O 0 0 0 0 0 O O O O O O O O O O W 'a7 O O O O y*. O O O OO O O O O O O O O O O O O O O O O O O O O A O 0 0 0 0 0 0 0 O O O O O O O 0 0 O O O O O O O O O O O O O CT 0 0 0 0 0 0 O O O 4 O O O O O O O O O O O O O O O O O O O O N ~ o o o o oh` 0 , 0 . 0 oN 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 o O 0 0 o V 0 0 0 0 0 '0 0 0 o 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 m 7C 0 0 0 0 0 o 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 m o o o o o 0 0 0 O 0 0 O 0 0 0 0 0 0 0 0 o O O o 0 0 0 0 0 0 y - 0 0 0 0 0 +%!d o 0 0 O o 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 o O o o Z O O O O O'I.. O O O O O O O O O 0 0 0 0 0 O O O O O O O O O O N O O O O O O 0 0 O O O O O O O O O O O O O O O O O O O O O O 9) n "0 0 0 0 0 0 0 O O O O O O O O O O O O O O O O O O O O O O O A 0 0 0 0 0 O O O ' O O O O O O O O O O O O O O O O O O O O O ~ ',L O O O O O ;~1 O O O` O O O O O O O O O O O O O O O O O O O O O !n O O O O O O J O V O O O O O O O O O O O O O O O O O O O O O O V O O O O O O O O O 0 0 O O O O O O O O O O O O O O O 0 0 0 O0 C" 0 0 0 0 yy 0 ~~~i' O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O N O 0 0 H -1 - 0 1 0 O y,T O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 o O o 0 0 0 0 0 w N O O O O O O O O O O O O O O O O O O O O O O O O O O O O O p O O O O O O O O O 0 0 O O O O O O O O O O O O O O O O O O N CT 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 N m c n 0 0 0 0 0 0 0 O ~O 0 0 O 0 0 0 0 0 0 0 O O O O O O O 0 0 0 d 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 N m 6- Y ~ O O O O O O O O O O O O O O O O O O O O O O O O O O O O O N d Q 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 o O o o c a 0 0 0 0 0 _ o 0 0 .,tip o 0 o O O O o o c o o 0 0 0 0 0 o O O O O O O O O O =4„ A~. O O O ~ O 0 0 O 0 0 O O O O O O O O O O O O O O O W N D F-i O O O O O O O O O O O O O O O O O O O O O O O O O O O o 0 W W O O O O O O O O O O O O 0 0 O O 0 0 0 O O O O O O O O O O p L O O O O O 0 0 O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O v 0 0 0 0 0 0 0 0 O O O O O o 0 0 0 0 0 O o o O o O O 0 0 0 Y O 0 0 0 0 0 0 0 0 O o 0 o O O o 0 0 0 0 0 0 0 0 0 0 0 O o o 0 0 0 0 0 0 0 o O o 0 o O O o 0 0 0 0 0 o O o 0 o O O O O o a O O O O O a O O O O O O O O O O O O O O O O O O O O O O O O A 0 0 0 0 0 O O O O O O O O O O O O O O O O O O O O O O O O N D • • • A O W ~O W 00 W J W ~ W U W A W W W N W W O N ~D N 00 N J N O~ N U N A N W N N N N O ~O r 00 J 01 U A + W N r 0 ~ W J Q\ U A W N r o v c° v m v rn v v v y Y m H o o v m z n m c m jp ~ ~ n ° ° ' o m o H m m d r r Z @ m ~ n r n n °1 = o- _ ° ~ o S (7 C1 g n T 0 o m o ~ S ~ ° x, ~ m m T n m m D m N m = 4 o ~ = m° d m d x 3 g N m 0 0 cnii N ~o o ° N o "0 3 3' v O0 u, N 0 0 c.n n U~ - v (p 0 o+ 0 ' 0 o 3 of m m F od m = 3 m° c ° N O a O fD ID o a 0 0 o 0 S o o O + O N O C _S N O d 'O N O N N - 6o O e 0 C W O O O O 3 J j (p y< N N U p- 3 f0 N O V} y O' fD ° S y ( p d (D 2 N n o ~0 = y m p co rn o 0 o N 0 o = ° m o O m o O d i R N v_ m m m 50 o O o C'~ N O 0 ? FD n ° W (n o o O n C d 3' cn O O N + 3 m m a FC = w Q F a m . N. = y =m = o d O t-i D C ~ D ° yy "O"' D c N C O N 3_ Cf ° ° O N j N o 0 y i N 0 y p (D N O p ~ o y O~ = 3 e o -e ~ Er N t0 CJ ' o S o O rn O m y i d p C n, O N= fD 3 + fp o y 3 3_ v O y H f ii x o c o 3 ~D ° , ui < o 3 3 m y o y o y D ~ ~ o o 03 ° 3 m Yn rs= m m o m o m= m d Q n- f maa?; m = o- 3_ ' c a y c m N d = ~S m m N = n N N y ID y N N D o F n c . , n ° . = a g m 3 D 0' .L O' y 4 O _ C (p < N m m p = y o t O ° m tD d O1 0' p1 d n m N a - D S o d o t0 m o N °0 5'i N .p. G a m 3 N m a S _ Q N n^ ` O tD d tD t m a2 ° o p an d m co y w as ny o 0-~ 9 y am y m w Y'a'm o y $ya F o ~ ' ° m m n m= n ° El m aa m fo o O r i Q . y c ~ d F 3 N i N = m N O n ~ d m . y vi c ( m e N E ' O n J ~ ? v = Np1 0 so rS p c 3 y 3i m 3 (D 5. N Q q m ff fD ~ ~O p C o = o II N C 0 3 u ~ p d E = O a ryi d J fD d d ° tD N 3 C tD O ° tD fp U i d a D 9] H= y N o ~o °m o o m N d m d m y D c° Fo ? y m ° - n> y d ¢ o~ 3 c 3 x O F n O N tD o = m O O= II o N o n m N y II o- m m S r D m = Q ~c n m j n N n~ yy m D m m F r = m m o X F a a F `G m m m ~ ~ d ~ s n ~ e c a ~ o a m g 3o a ~ ° m 0 oy^i o = ~ ~ ~ m a ~ D d O d n = C f0 9l z N 3 ~ ~ .y.. N o j d '0 0 G fIl ° o 0 n ° m In o ' o ~ ' v o m ? a o a c . N m < m m - F m . = _ y F~ y g N g °g ~y@~ =-sue a a y p T S = f° D D = O `G ~ O ~ ° ~ N~ y p D n it fD m A O O o 0 0 0 0 0 0 0 o O O O O O 0 0 0 0 0 O o 0 0 o O d a f0 O O O O O 0 0 0 0 O O O O 0 0 0 O O O O O O O O O O O p D 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 ~ C 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 ~ 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 ~ 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 I T 0 0 0 0 0 0 0 0 o w Y O O O O O O O O O O O O O O O O O O O O O O O O O O A O IIVV 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 o O O O o 0 0 0 0 0 o w Y a 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 W m O O O O O 0 0 O O O O O O O O O O O O O O O O O O O O N O O O O O O O O O O O O O O O O 0 0 0 O O O O O O O O W d O O O O O 0 0 0 0 O O O O O O O O O O O O O O O O O O A ~ O O O O O O O O O O O O O O O O O O O O O O O O O O O ~ ~ O O O O O O O O O O O O O O O O O O O 0 o O O O O O O °~j O O 0 0 0 O O O O O O O O O O O O O O O O O O O O O O V x 0 0 0 0 0 0 0 0 0 0 0 0 o c c c o 0 0 0 0 0 0 0 0 0 o m W 0 0 0 0 0 0 0 0 0 0 0 0 o O O O o 0 0 0 0 0 0 o O O o 0 o O o 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 o O O o o ~ 0 0 0 0 0 0 0 0 0 0 0 0 o O o o 0 0 0 0 0 0 0 0 0 0 0 W r 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 N O O O O O O O O O O O O O O O O O O O O O O O O O O O °j z o O 0 0 0 0 0 0 0 O O O O o 0 o O O O O O O o o O O o ? ~ Q O O + 0 0 0 0 + 0 0 0 0 O O O O + 0 0 0 0 0 0 0 0 + O O O O O O ~ W b O O + 0 0 0 0 + 0 0 0 0 O O O 0 + 0 0 0 0 0 0 0 0 + O O O O O O ~ O O + 0 0 0 0 + 0 0 0 0 O O O O + 0 0 0 0 0 0 0 0 + O O O O O O ~ W O O O O O O + O 0 0 0 0 o O O O O 0 0 0 0 0 O O O 0 0 O pp ~ O O 0 0 0 0 O O O O O O O O O O O O 0 0 O O O O O ~ O O O O O O O O O O O O O O O O O O O O O O O O O O O O V O lA O O O O O O O O O O O O O O O O O O O O O O O O O O O O V d Q C O O 0 0 0 0 O O O O O O O O O O O O O O O O O O O O O O N O O O O O 0 0 0 0 O O O 0 0 O O O O O O O O O O O O V W X O O O O O O O O O O O O O O V d O O O O O O O O O O O O o O 0 0 O O O O O O O O O O O 0 0 O O O O O O O O O O ~ I N 'd 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Cl 0 0 0 0 0 0 0 0 0 ~ Y o O O O O 0 0 0 0 0 o O o 0 0 0 0 0 0 0 o O O o 0 0 ~ C1 W O o 0 0 0 0 0 0 0 0 o O o 0 0 0 0 0 0 0 0 0 o ~ ~ O o o 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 o m f7 v 0 0 0 0 0 0 0 0 0 O O o 0 0 0 0 0 0 0 0 0 0 0 0 0 0 o mo n 0 0 0 0 0 0 0 0 0 0 0 0 o O o o 0 0 0 0 0 0 0 0 0 0 0 C7 ~n 0 0 0 0 0 0 o O O O o 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 N ("1 O O O O O O O O O O O O O O O O O O O O O O O O O O W x O O O O O O O O O O O O O O O O O O O O O O O O O O p n O O 0 0 0 O O O O O O O O O O O O O O O O O O O O O O ~ • • • J A w J N J C J O Ot l0 D\ 00 a J D\ Q\ D, U A D\ W a O, N a O U ~O U 00 U U J O\ U U to A to W N cn ~ to O A ~D A 00 A J A O\ A A A W A A f O p 0 O O p O) Ol A W N Y o ~ C7 or O [n a G X 3 U = Z~ O x n m ~ o 3 m p F° y n r ~ ~ d r m ~ Z c m m a c uri y ~ n y m c7 0 n 0 m o °o o° o ° m o ° ° can m 3 m O x m m m y m ° m o o' g g fD c o ~ 3 o c S ° a m ~ o g g m m m ui Z = o~ C f o-dy o o _ o a C d 0oc~ a o w o cn a N oo c o d C m Z 2 d rt7 n~ ~ N r ~ N n ' m~ _g m ° O O ~ o o> l d m > x~mm o a, 4 d ' a o N N ~ a, o ° o 0 0 ~ m 9l O O O N ' f o O N O y c . 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N p O p - p w a 5 cn _ wc) n ~ d ~a 2 h G o uz ° 0 m o m m d y f0 Ro ° O o = ~I co f0 ~ O O 5 Z y- n Z fD 4. a D y m v D g ° o ~ m cn m m d 4 o D c m g= ° N Sy., m nt ? 3 to ° m 3 3 m F 3 5' o c= n d g F y F o C1 n ° d c 3 c m °d = H w H o- m f o c x n= (p C m° S ? m m< . d m m m O d N . m O N ° ~ 3 m m O d d c''~ tU a d of D f ry_. n 'O D n o O S< O m » ~c = S VI d = = y m . = 3 n m (p d = _ ° d m o d m d (p 3 (7 m ~ < o g n y N n D 0 N< d g d a ° y g i y ° = , ~ 0 d d N = . j d Q o° c O e y - m 3 o a a- F n V n= d m o- N N 0 m g 0 g 0 g a 2° d 0 3 C t0 v; f N F Q y o ? H= m n o i c o n ~ d n ~ < o? 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O o 0 0 0 0 0 0 0 0 m m O O O O ''.'.Y~ O O O O O O O O O O ~ 0 0 0 0 0 0 0 0 0 0 0 0 0 m o n 0 0 0 0 0 0 0 0 0 0 0 0 0 0 ~ b7 x 0 0 0 0 0 0 0 0 0 0 0 0 0 o m m 0 0 0 0 0 0 0 0 0 0 0 0 0 0 m 0 0 0 0 o 0 0 0 0 0 0 0 0 o c Utl 0 0 0 0 - o 0 0 0 0 0 0 0 0 0 ~ r O O O O O O O O O ~ O O O O O N y O O O O O O O O O O O O O O W z O O O O O O O O O O O O O O 0 O O O O O O O O O ~ 0 0 0 O~ O ~ ~ b O O O O - O O O O O - + O O O O~ O ~ ~ O O O O O O O O O~ 0 0 0 O + O ~ - O O O O O O O O 0 0 0 0 O O m O O O O O O O O O O O O O ~ O O O O O O O O O O O O O V O O O O O O O O O O O O O O O O V d Q < O O O O O O O W O O 0 0 0 O O N 0 0 0 0 0 0 0 0 ~ 0 0 0 0 0 o w k O O O O O O O O 5 O O O O V d ~ O O A O O O O O O O O O O O O O O N ~ N 0 0 0 0 o 0 0 0 0 0 0 0 0 o rn Y 0 0 0 0 ~ o 0 0 0 0 o o O O o ~ ("1 o~ 0 0 0 0 0 0 0 0 o c o o 0 o m n ( ] 0 0 0 0 o 0 0 0 0 0 0 0 0 ~ A 0 v 0 0 0 0 o o O o 0 0 0 0 0 0 m ("1 l ot o m 0 0 o a ti-- ~ o 0 0 0 0 0 0 0 0 0 'psi O O O C ~ ' O O O O O O O O N ~ ~ ^ M O O n O O O O O O O OO O O O O O O 5 ( J O O O O 7" 71 O O O O O O O O 0 0 p C~ O O O O ~ti~ O O O O O O O O O O ~ n • • • U A A A A A A A A A ~ w w w 1..+ F A o ° 0 y cnz nz na 3 on < 0 0 m ~ n o e o ~ o o n Q y ° c ~ on ~ ~ n a ~ N o m o o ~cn o F o y m ~3 R- m m 0 0 o O p o f C 0 Q n w O D O O N O p n o o O N m o o m o f m N, O S ty'1 3 0 o < O D O N O' ° n o 0 o c o' m e O S S 3° L O D O d N ok ° o o 1. 0 3 rJ N S 3 N 3 g O D o O G N 0 3 = N O O m 3 , o g ^ O 2 ry bi d co' a n C o in f/i f0 n 8 S O 3 N m H m N N IV a C~ o in a ~p (D N N m o fOi~ tU N - . _ C('11 O. 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A 00 A J A A ~ A A W A N A I f 0 0 0 o v o 07 (T A W N rD O O V y Z m O ~ o. 3 y o . m m ° R° m 2i o o ~ n ° n z r m 0 v ~ m n ~ a Z ~ m c n n > j a' r W w a m ^ on N ~ m n 0 d n d m C~ o C) 0 m m n 0 n o_ m n~S ° m F X o o 0 0 08 So ~ 0 o a m 0 c m o o 0 o o wc^ o e m~ o a- o y F z 0 z m m _ m s m ~ ~ m o^m` m ~ ° o o'o 4 ~ o ~ m m m = n o c o o °c f 3 o m .o O m ~~l ° 8 a c m < 0 m ° ° c ° ° ° ° b s o m 5° m m Ll c Q n y E3 o S 0 a o c o- Fli, w e w cn N o o m c ° d m i m m m a m o 0 ° o m _ m m g m - 0 m = w n o m w ' t o - o o i o o o = ~ n ~s' m m m ° 3 m A - n m . < m n tC 0 °p o C 0= n y m ° c=i w o c m n 0 0 H 2 o Q m = o m y m m n Q p a' u, m o y m y . ° y o _ o o o 0 0 m H ' o a d = o o T m y o ~n 8 3 o m - 0 n n F o^ m m o - ~ o ' o ° 3 d c F o m v ° o < y T = d n m_ a 3 n g n' o v°i m w a m o Q o~ m F. F n w = m f. y o m o N c m 3 F n m o < m 'o <n m o F d m Sa 3 m a , > m m T SO o N fc m > CD yy a°i =p1 w a N o o ° ° m g > n . ° ° 0 r o ui y ? m o . -.D ti F o ~D c n c 3 o N m g m o m a c m. n c N c ° m ' m ° y n m o m Q° 8 o u i 3 8 n a = $ ~ n ° H T ' o m ° N S L~ 'O T a < c i N a? F i ° < C ~ 2 d F a _ m d m n~ 8 3 o m o _ N J m 3 C n d N so 3 O c n m n ¢ g 3 m , a° ^ a` o N N 3 N Oc n -v S n m o m 3 3 " m N O N n y N N N N _ (p N C _ O ^ N 0= N S N V C UI T l i _ O S f0 fp h O n N ~S = N V O ° d ^ n g 9l ~ G O ~ a 0 f0 N ~ (/i N O~ f0 2 j 'y d a 4j S 3 (D y Er fD O v° N C~ O ~ N C Gl C n g f0 p d S A N ~ m m v+ m m° m m m 2j = n n D o C a m m a s o o y g g y a m R d 5- 0 f'l N Q N d d y a = x j O^ o m ^S m&= = F Q C7 F y c Q fC (D A F F a o m = N d o n y m o d = ° 4 o F m y D y y D c m m o a m 3 = m so ° 2 o a m m a y m ° ^ v iT y o1 in H a myy H - my n ~y S c~ ^ m~ n - m e Q m - m v ~ -So o. 0 H n D m° r D o n m H< m 2 m c m N m y < m f° N N N F. O O O Q (D N N ti n n ~ (D ate, = y g, a N D N d O O O O O O O O O O O O O O O O O O O O O Qo O O O) O O O O O O O O O O O O O O O O O O O O O O O W n J r O O O O O O O O O O O O O O O O O O y O O O O O W O O O 0 0 0 O O O O O O O O O O O O O O O O O ~ z O O O O O O O O O O o O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O ~ ~ rp O O O O O O O O O O O O O O O O O O 0 0 O O O O N O- O O O O O O O O O O O O O O O O O O O O O O O 0 d ~ Q O O O O O O O O O O O O O O O O O O O O O O O p ~ O O O O O O O O O O O O 0 0 O O O O O O O O O O n V• y O O O O O O O O O O O O O O O O O O O O O O O ~ ~ O O O O O O O O O O O O O O O O O O O O O O ~ O < O O O O O O O O O O O 0 0 0 O C O O O O O O O O O OD O O O O O O O O O O O O O O O O O O O O O O ~ k O O O O O O O O O O O O O O O O O O O O O O O O ~ Q 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 o N 0 0 0 0 0 0 O O O O O 0 0 0 O O O O 0 0 0 0 0 N a 0 0 0 0 0 0 O O O O 0 0 0 O O O O 0 0 0 0 0 d ~ 0 0 0 0 0 0 O O O O 0 0 0 0 O O O O 0 0 O p p ~ o 0 0 0 0 0 0 O O O 0 0 0 0 O O O O 0 0 0 0 0 ~ o 0 0 0 0 0 0 O O O 0 0 0 0 O O O O 0 0 0 0 0 O v 0 0 0 0 0 0 O O O 0 0 0 0 O O O O 0 0 0 0 0 V d 0 0 0 O p p O O O O O 0 0 0 O O O O 0 0 0 0 0 0 0 0 0 0 0 O O O O 0 0 0 0 O O O O 0 0 0 0 0 O v O p p 0 0 0 O O O O O 0 0 0 O O O O 0 0 0 0 0 o d 0 0 0 0 0 0 O O O O O 0 0 0 O O O O 0 0 0 0 v O O O O O O O O O O O O O O O O O O O O O O X IV O O O O O O O O O O O O O O O O O O O O O O W O O O 0 0 0 O O O O O O O O O O O O ` O O O O A y rte. • • O \O 0- I O ? °W N O r, O O ~ W b J b 01 b to A W b N ~...b . O Oo ~O W 00 00 00 J O~ 00 to 00 A 00 W 00 N 00 00 O J ~O J 0o J J J O~ J to ~ 0 0 0 0 0 - N O ~ ~ ~ a Z m aC n m o a n cn a° ° v o D o m ° cn (A m m ° 3 ~ m d' C G C d fD ~ X -0 _ 3 x ~ x 3 m m ° 4 N j N O N C N N C O p p O^ 0 ° _ ~p N N O w_ O C O n N ( Vii p3 t VJ~ (n 30 N o o w w N O C W W (^l~ (A T m< m< o~ f m a° m rn fD oo a o o v ° m m' N a m ° m 3 a oo g y 3 3 3 m z n 3a 3 ° d m o H °o o° o0 Q ° °o °o o n m ~'.m 3 o 0 0 o o 0 e o 0 ° m m O d ~ C2~ m N O N m 0 O 0 O m m O N m N j C j o 0 ~ N < N m ~ N N m N it 41 m H 91 m m y N m N p N 0 0 O 0 O ~ G ~ N n n 0 ° ° . r m m ~c~ = o> A n `2 Coo _ 3 H 0 o o ' m y c; m F n i3 y D m m n . S. o o _ ° a x n ' f 3 o o c F 3 n m n m o o S S m m n G n c C7 n O N N N ~y . - O N O m m N N N O O O' d o O O m n m n m 0 m 4. 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( a O O O 0 0 -1 -1 0 0 0 0 0 O O O O O O O O O O O O O O A G • • • N W O N ~O N 00 N J N N U N A N W N N N N O ~ ~O r Oo r J r T r to r A r W r N O O p w a ~cn ~ ~ 3 c o a m n = m x ti c o uzi o m e Q+ ~ o ° ~ a b7 d N = ~ d n ti lA O G Z O fD O S a D iD C y v D Q (D A . d$° No C t"l N 3 D s= f0 (D O $ f m e O S 3 lC x 3 °D 3 d C f 3 b a^ d.. d= d 3 $ f d F o m C .O. T O O 'o m = N m N m N m m m f° C tp d. x C d j j N Z A . m m ° J o°i p1 m p j m m`' o Si S 3= m m ° a n d $ n y d f g g m A o m < o m T' `e 7 m ° emu, m y _ = o~ m 3 n v m ° m o a S ' ^ . . m m < m = i c) d m < d n g m m y y n a D 3 y Si m D ' y n w 3 D = . v f=c d y m = m ' a o n O (n ° G 3 W A ° v° F n C _ d Z c N' n m N d N _ o c C ° 3 m = m Q O < ~j N O = O t0 % j ID N (D ~ f O d N O f0 = fD O fp N d f, O ° 4i S= N O ~ d° n O N C N n c a ' y-. n O' O d v Q S p 0. y~~ ~G N d n N _ T C S~ N Q n n C 0 _ ~ j d N Q d O N n a $ N 2 0 ( 2 0 ( S N d fD N 2 d N N n (D O fD < N &'j 0- N ° = c d~ N 3 ~ ' = v ,2 ~ p- ~ ° a 'G (p S n m rs, o- ~p o O a y m m m N p n o n 3 ~ d n < $ u 3 n t 0 d - d ~ o z ° _ - ' ~ o d ~ a ,2 c o m C rn C cni, C a C ~ d ° m n m p a m m v d 3° d O m m ° F a - ff f ° $ 3 i c , w n o . o, m c° m ° ° ~ m y m 3< m DV m n o W= ? d N 00 (/I VI N O o d= 7 ~ c fD N y tp d O N U 0 (D ^ N N w n fp j Z u fp Ip (0 x= N- Z CJ a m D o~ !o a 8 a = H° 3 o _ m m o o n x ~y p S 3 = o o n E, F - m o- ~ = 3_ ° a= ° o m m m o ~Z- n H m o y m W D a m o c n ~D m o m c = 'G = fD o . °m n 3 3 m ~ o 3 m = o p1 ° n d a F y ~ ° a d< _ ~ ° `n 3 3 m z n n n d 'a d m m T 3 a n D vi O O= iV N d fn O O .d.. 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O n W n -3 @ m o o O o O O c _ < coo O- N m o. m d f < c m = , O 3 N fG m y 3 O ~p d m o m H d n o' o- V n m m n m fp x w n ? a n m F y d n - c d m N 3? o v a ~ a c S' - v C H o 0 o m D Q N N O (D O H n .=i j N C') d N f0 N O O O O O O O O O O O O O m O O O O O O O O O O O O O O O ~ r 0 0 0 0 0 0 0 0 0 0 0 0 0 0 ~ 0 0 0 0~ 0 0 0 0 0 0 0 0 0 o O° ("I z O o 0 o O o 0 0 0 0 0 0 0 0 o f7 0 O o o O o o O o o 0 0 0 0 o m C] 0 0 0 0 0 0 0 0 0 0 0 0 0 o m o_ C] O O O oE o O O o O O O O o o m O O O O O O O O O O O O O O p O O O O O O O O O O O O O O ~ n y O) O O O y` O O O O O O O O O O O ~ C O O O O O O O O O O O O O O ~O O) C O O O O ~ ry' O O O O O O O O O O ~ k O O O O~ O O O O O O O O O O ~ Q O O O O O O O O O O O O O O O N ~ O O O O O O O O O 0 0 0 O O N a O O O O T I- Q O O O O O O O O O O O O O O Q O O O O ' O O O O O O O O 0 0 0 . ~ O O O O }rf O O O O O O O O O O T d O O O O O O O O O O O O 0 0 d v O O O 3'• O rtk O o O O O o 0 o O O , ~ O O O O O O O O O O O O O O ~ O O O O >M1' O O O O O O O O O O ~ O O O O O ,.~,y, O O O O O O O O O O ~ d O O O O O O O O O O O O O O N O O O O O O O O O 0 0 0 O O W O O O O O O O O O O O O O O O ? y • • • r A U W r ~ N O A \O A 00 A J A ~ A U A A A W A A A N O r ~D L W 00 W J W ~ w U W A W W v o co p p m v m a a"' o o m o~ o ~ 0 0 m 2 cp a: j Q o ° ~ °^l. ~ ~ m d n ion T C'7 A a~ ry o n n ~ H C7 C'7 ~ N Q O m N m m H o. o o f Q S n m U n D C°'! C O N O° m o o t' o f o c o c o m y O ~y,~ S 3 o f° < O a n° ° c o O N n- 'o m o O' O = F O y O S m o m ° s G O a O a O N ° n n m o m c °F " ° c° c o tn, $ y 3 m c - y 3 S O D n O .C N _ o m o' y e °F 3 = to O O S m 3 ~c ^ S :5, O D o o 9 b' N m n f'o o n ^ m y H N O _a m Fp 3' ° o O m IV `Z n m m o N O O c a d N C m m N (D f 3 (D S W w_ O n i.> w O .0.. Q > c o o 0 S O y n m (D 0 0 p 3 rn O 0>> o y O ' .O. S o° O N O o N 0 a F O' y o " rn N C9 d Dl O 0 > n G " m o 0 0 0 c4 g y O N J ^ 0 Vl (°p o n 41 ^ , o o N J S O w O w p n t'- 9 N d (JSI y O p 4=i N (D O (D y_ O N R^ _ (D d (?(pp. O Or. y N ° F N ry fn Z ry^ N O" O . ° ~ ° a f0 O N C ° d _ ~ y O fD y O O F a Z N^ O 3 ' d -(DU 0 N O y ° N O E-r N N y z O O . O O" N C'1 - N O (D O y F OT N Qi t' 3 3 0 O° O X m H <3 3 - o ° O' N 3 F m m C N m m 0 m ' (D O c 3 S _ x (D 3 ° m o m o x N y (D y ? O ° m X c (n g `G m F d 3 m s3 fD H c H o 3 0 g N o Q 3 F ~c _ o ^ 0 SR m m m c v 3 c ? n c 3 o o m 2 a c m y 3 ° n n o _ o y n c m 2 a 3 n° 3 w ° y n d a° 3 o m 2 v c o c m m < o 0° m a m ° y m ° a 3 l'1 o n o 0 3 y ° m 3 ^ y 3 ? rn °0 0 3 y ' c N RL m 3 - > m y o m y 3 , n y 3 N O N S c y 3 C c= l f0 X v' ~ 3 t'3 y n c- l y o~ o ~ ° D F m C] S N° y N J NN n N n° d 0 X y i 0 y ~p~ 00 X N 9 n° 0 y y N 9 00 Q X 7~ p N 1 ~ d X ~ y Q y' ° Q N j NN d p X x y ~i (.Il y , n O K n ( > . .d ° fD d o ° o 0 a N n f o d O N ° n o o° O y T o° p 3 n ^ y° c n F y y 3 n y m m m m F n m 3 y m m z 0 n n o d m o w y 3 z m F o (D 41 fp z o- Q m D a m F y y 3 i ( A n y m d N F °c o y C°Y ~ N N o H n O' ~ ~ ~ n N o- O < N 2 m ~ y O' N _ 3 y~ A O V O ~ O < _ d O" y~ ~ 3 N N f O fU ~n(pp. Q p ? y 3 V n O (~1 V 2 " N < y Q C ry a y l _ y J m m ° N O m Q O c o n 1~ . m N d d Ut O (O m o o O d~ , , m m_ ^ ~ N. y N ' tT n N? 4i y 41 ~ (D . d m D. ~ ~ m co ° j y 0 y N (D d d O y y F (D d N F O" C 3 c Q <p fD y° N y O y C 3 O ~ `G O" p° m F j n, S C O 3 l° O D N p y y C F o- 3 N f0 n N Q z 0~ n ^S c° y (yp 3 ° o y .c ° m v o c 3 o F 5 8 w n o o ° n y m o n o o b 0 H y c o c n o 5. m m v+ 0 8 F b' o y b' H 3 ~ fD O C d °F m O m e O F N 3 t' m y O O N m m g p H° o ~ ,g m f m w W ? ry V o o c . j g m = O c ° ° 3 O ' ° N _ O 3 y = fD 0 N n n o m n d m ` G (D m 0 0 0 0 0 0 0 0 0 0 0 0 o rn ~ 0 0 0 0 0 0 0 0 0 0 0 0 0 ° ° ('1 r r 0 0 0 0 0 0 0 o O o 0 0 o m 0 0 0 0 0 0 o O O O O O o ~ Z O o 0 0 0 0 0 0 o O o 0 0 0 (1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 ~D C7 b 0 0 0 0 0 0 0 0 0 0 0 0 o m o_ f7 0 0 0 0 0 0 0 0 0 0 0 0 o m Q ~ O O O O O O O O O O O O O p O O O O O O O O O O O O O (O O O O O O O O O O O O O O ~ O O O O O O O O O O O O O V < O O O O O O O O ~O O O O O O Oo O O O O O O O O O O O O O ~ k O O O O O O O O O O O O O n O N O' 0 0 0 0 0 0 0 0 0 0 0 0 0 o N o O O O O o 0 0 0 o O O o o ~ Y 0 0 0 0 o O o 0 0 0 0 0 0 ~ ° m 0 0 0 0 0 0 0 0 0 0 0 0 0 ~ d 0 o O o 0 0 0 0 o O O O o ~ ° o 0 0 0 0 o O o 0 0 - o 0 0 o rn O O O o 0 0 0 0 0 0 0 0 0 0 o O O o 0 0 0 0 0 0 0 0 0 0 0 0 ~ m 0 0 0 0 0 0 0 0 o o O O o ~ x O O O O O o 0 o O O O O o o d o O o 0 0 o O O o o O O o d O O O O O O O O O O O O O N O O O O O O O O O O O O O W O O O O O O O O O O v O O O ? • ~ J J J O 00 J J D\ ~ U J A J W J N J r -1 O 10 0o J ~ O, ~ a\ ut A ~ w N O ~D U U J U U a\ to o ~ o 0 o a d~ o o ~ o n m cn ~ ~ f o j O i m m ~ m ~ ~ n ~ o o 0 9: m m b o i S j y n ~ N n N n. ~ > S > • O cDi b1 P H ^ : Z 0 z < d < n m O m Q Z ' O ° "S On O O g m "S O n '0 d S 0 m O On o O S m P O N D O n m 'o m c F 0 3 m N O O m d O C tD n C°9 C O N n m O C F m ~J O ? ° D o A C O N m C _ o ° a M N 0 O ~~pp d N H N g a N 9l m m C O N d d Q n O a g (D a ~~aQ 3 A, N f ° C O ~aa C ~p O ,~~o ~ O O N O C° a a ' n ° o N m F N m F F° = d v vo m d o C o v° ° CL m n o m_ N ° O. o n c O O" N N J n n m o o O N J n> > N N O n Q ° o o lOD n o y c - Q1 m n ~ = n f° Q ^ O ~ N o S O c o O d y m H m O j N v n C o o n m p -w Q o o Q g 5. O_ f m m ? O S m N. o S tD O N Ul a m o C o° ? - fD m O 7 . N o° m v, O 9 P g d Fn' m o O ` C d m d N 3 d - O 00 L 3 =O m J w 3 O d o a m> j 5. l 3° N Z N o N e 3 o m O fp c n m= 3 N d O S FD m° n O 3 m f0 Q o B 2 FD O, N ? m N ~o+ ° g EL a 20 ~D c° m m n m n m o w u~ u`"'i m m m o g m F ~yD ° o N l y m 3 o m H m o g n m c g 3 o m o ~c n o 3 ~D m a ~o i° w o n m c " 3 0 2 Pc' ° _ O r° w m c y o F y ~c a c ° T > a ° ° o n y e c m ' "s m D a- 4 F. f° ? m 2 a c v; 3 w o o 3 y 3 umi m 3 3 m 2 H F d F o m H S m H n S F > o m , m g m m o n n j m o n ° ° n m n fn n o 3 n m ~i m o y y m 0 o 3 m n H ~ c n H m o c o m n > m F m m m m 3 ° ~'o m ° r'° m ° o v m c N m v rs c, m n o n~ o 3 - c n o a 3 m . m > > o m 3 c i y m o m m m a o n r: 3 o ~p ~ . - m m 2 o 0 m a a o vi o, o m 3 ] f uZ D m m m n v F m y F d m m ~D m 3 m m n y m ° ; a n o ~c m m n N H m o o 7c A m o c D m F 3 Z - v m n c 2 o c n o " m y m F o g c m 3 H D z 0 m n o ° o a o v o c g F m 3 H n ° m 3 c m n a m o n n o a H o m° v ° y O d v m o o v m fn m m o o v w m m °n m d m m ° ` m ° H . ? O m g 3_ v n c m ' o ° o? ° m ° m 3. a o. ' ` ° m H m x ' ° 3. v n 3 ' D° f° m n fc N F O O ' 5_. N H O ' N o "O O O N ~ , N O O o O ? m ~ G O O < 0 H. 3 m ° y D N N S ry y j p O O O tD d N N N W m 0: O N ° N C ` 3 O O' O ° O O y C SG y O . ° 3 O y C N y 3 DDD z o v o o O o a 3 F iv m 3 3 O 3 n `G o c G o o o o O F M Sn. m g `n m 3 O N o N m d° o o m F ID S m y F N (n m o m cNi 3 o o m , °o m ~ g 3' o m o m , a m m m F _ m y d m H o o m F y 3 a T ° - ° 'o m F ' N n ° ' y ° t° ° 3 ` ' - m o m D N ry~ ~ N n O _ d N ~ J m d N 0 0 0 0 0 0 0 0 0 0 0 0 0 0 o rn ®r) 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 ~ C] r 0 0 0 0 0 0 0 0 0 0 0 0 0 0 ~ 0 0 0 0 0 0 0 0 0 0 0 0 0 o m z 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 (7 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 C7 ^o 0 0 0 0 0 0 0 0 0 0 0 0 0 o 0 m Q C7 0 0 0 0 0 0 0 0 0 0 0 0 0 o m m ~ c O O O O O O O O O O O O O O O ? O O O O O O O O O O O O O O O ~ O O O O O O O O O O O O O O O f0 O O O O O O O O O O O O O O O ~ < O O O O O O O O O O C O O O O O m 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 ~ ( 7 k 0 0 0 0 0 0 0 0 0 0 0 0 0 0 y o Q K 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 o N 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 o O N O O O O O O O O O O O O O O O ~ Q O O O O O O O O O O O O O O O ~ d Q O O O O O O O O O O O O O O O O ~ O O O O O O O O O O O O O O O ~ O O O O O O O O O O O O O O O O d O O O O O O O O O O O O O O C) O O O O O O O O O O O O O O ~ O O O O O O O O O O O O O O O C O O O O O O O O O O O O O O O O O O O O O O O O O O O O O N O O O O O O O O O O O O O O d w O O O O O O O O O ~ O O O O O A y N N • • • 0 ~ 0 U 0 l A a- h" 0 r 00 ~D ~ Q\ U A W N O ~O Oo -J ~ ~ U ~A W ~ ~ N O O O m ~ ~ V O rn Y = o j m ° m N H O ~ = N~ o 4 m n~i ~ a U1 o ~ O" ~ m O c ~ O ~ o 3 ~ ~D n ti ~ ~0 n i _ d C n i 2 4 o m y CO y C u N = N N N (D O tO7 = (D 5 5 m ~ c = to S N m m `2 2. N (D N ~ ° Z j m a S 3° X ? ff 0 o d O m 5= S O CS - ~ y 0 3 ° y S= S° 3 0-3' D G < 91 = p 'O r o o N N m O 8 O O (D 3 n O v O CNT ^ ' v a N ~ r D N - 0 N O n n n Q u. d O d p N H = ' O= d n= f0 N r 0 (D n O d N ~ d n ~ O N S O N h 1 ~ 3= = N d n fD ' O r ~ C C N N j O O c S O O' f~ a$ (D O S C< (D n n N O S = C ~ n O t0 tD .d.. ~ N - C F C N f0 e - O o IV Cn N = a f0 O f ~ ~ N~ tG p ' d F° = _ N g d O ti. n ~ N N= Q S N fD W = = ^ t0 j 3. O o = " m Sl O' o C K m N 3 C N N = ~ (/N(/11 ° 0 0 VI 3. 3 w = o 4 . c d » (p S J S j C ta/1 n m a, o m N N p) = d v j O C^ l N S r O S o c v c o F c y 0 ° ° O Vj Cl _ o ° O O _ _ O y y N 0 O 3 m S O O N =o n n 0 m w n c m o m o ' ~ m 3 o n ~ n m F c ~0 m y Q ~ m o e m G m v = = a m ° y n m~ ~ o m~ m = m ° o d 9 c a ° y m~ m a y m G' m n m v ~ m m c ° = ° c o= e g o : m o ~ o a o ~ 3~ D m~ C7 m o a t/ F ~ = m H c N a n o j m m H to N n m < = ai- o N w m 4 f 0 m o n m _ = N o F m ° w o d a m N n ° m^ O m O G N Fn D= o_ w3 O O d 0 3 m m N ~O m 3 n m N d o m v 3 . O N X O a 3 ° m 3 (7 F C O d m= (D t~/ m^ T a . p~ <p N m m C7 ~ O D D C O O. c a, c m m e N F o N w a m co m = 23 ` I - y ' m 5 o c m n m o v 3 o o-O m m ° n F H - - o = n o m m fD g N n m o u^i < nm m= D F m w --m ° x nm S F n 9' o m m g n F m t-'1 n m f n P. E? m m H 41 n o F° ~D m^ ^ O a n F O0 o- o o o > l m ~D O= 3 N r N N F 'O (1 tV 3 tD Cl (D C a (D O N N O (D f0 y O y n y' a O f = a N • S C7 J O S O D y F es N d tD ° O J Gt d d N> 2D O S d .C 1{~1 ~N O _ O N ~ H d dJ~.' d y y O N O~ N n. O ° 3 C d " n 6 F N C f0 O S O N ID N C O~ O - ° o w o 3 otDi N ~ _ ~1 3 (n m `2 F G O N N y a. N m y = m N~ o N C N F ~ = d a _ n o = d N N _ (Il [O O m N N 3 3 N' N (n ° 3 w m m H m F N F o a a m 'a o n ~ x ov , H m y 25 o m o $ o m- H c a m T F y c m n r c n m m 0 o m a o m ° o n `G c c = c m G c o o n v N = m o m D m p 3 3 - _ 0 S o s o ~ 0 0 0 0 0 ~ o o ~ o o ~ o o ~ o 0 0 ~ o ~ o ~ 0 0 0 0 0 ~ o o ~ o o ~ o o ~ o 0 0 ~ o °V° n., r o o 0 0 0 0 o o o o o o o 0 0 o o ~ 0 0 0 0 0 ~ o o ~ o o ~ o o ~ o 0 0 ~ o ~ Z o ~ 0 0 0 0 0 ~ o o ~ o o ~ o o ~ o 0 0 ~ o o O o 0 0 0 o O o o o o o o o 0 0 o ~O „nti o ~ 0 0 0 0 0 ~ o o ~ o o ~ o o ~ o 0 0 ~ o m C1 o 0 0 0 0 0 o o o o o o o 0 0 o 9 O ~ O 0 0 0 O ~ O O ~ O O ~ O O ~ O O O 5 ` O A ~ O ~ O O O O O ~ O O ~ O O ~ O O 5 0 0 0 ~ O ~ ~ ` ` O ~ O O O O O ~ O O 5 O O ~ O O ~ O O O 5 O ~ ` ` ` O ~ O O O O O J O O ~ O O ~ O O ~ O O O 5 O V ` ` < O J O O O O O ~ O O ~ O O ~ O O ~ O O O ~ O ~ C ` ` O ~ O O O O O ~ O O 5 O O S O O O O O O ~ X ` ` ` G ` G ` O ~ O O O O O ~ O O J O O ~ O O ~ O O O ~ O ~ O ~ O O O O O ~ O O ~ O OJ O O ~ O O O ~ O O N ` O O O O O O r J O O 5 O O 5 O O 0 0 0 O N ` ` D O O O O O O ~ O O 5 O O ~ O O O O O O N tz S O ~ O O O O O ~ O O ~ O O ~ O O ~ O O O ~ O ~ n Q O ~ O O O O O ~ O O 5 p O 5 O O ~ O O O ~ O ` ` ` ` O ~ O O O O O ~ O O 5 O O 5 O O ~ O O O ~ O ~ d ` ` O ~ O O O O O ~ O O 5 ` O O ~ O O ~ O O O 5 ` O O O ~ O O O O O C O O ~ O O ~ O O ~ O O O ~ O ~ ` O ~ O O O O O ~ O O ~ O O 5 O O O O O O ~ .d . ` ` G ` G ` om O J ` O O O O O ~ O O ~ O O ~ O O ~ O O O ~ O ~ D O ~ O O O O O ~ O O ~ O O ~ O O ~ 0 0 0 ~ ` O ~ d O J O O O O O J O O ~ O O ~ O O ~ O O O ~ O N ` O ~ O O O O O ~ O O ~ O O ~ O O ~ O O O ~ O W 0 ` O ~ O 0 0 0 O ~ O O 5 O O 5 O O ~ O O O S O A ~y • • • N N A N A N A N A N N A A N A N A N N A A N W N W N N N W N W N w w N W N w N N N N N N N N N N N N N N N N N N N N N .N- N N y ~ N y N N N O l0 00 J Q\ U A W N O r ~O 00 J O~ to A W N O ~D 00 J 0\ U A W N O ~D 00 J ~ U A w N O b W J r o pv o v v v v o T C o0 O v 1 m d ~ m ~ O o x m x = m o o o v ~ ~ z - v " 0 c W a 2 ~ d m ~ d n - ~ r O n 0 o ~ m O o o w n 0 v 0 A ° T o V N> >1 3 c o T. m m y v 3 n 0 ' e g d m o 0 0 0 0~ m m o- o- o S ~ F Dyy o v A o N W P ~ a D m z z 0 0 `5. d y p ~ z m o m m oz _ o> > 3' w o D o m S ' 0 n y d - m Vl C f~ V C d 3 m o- O 3 d D 3 O DD 3 A (D O 3 _ O OD 3 A m - N y V J A V f0 N o G~ O Z J T Q T J m yD y o C o O m 3 y O d m ' O m 3 fn' d m O y W O N w d d O W y N O n a O A m o y 0 O v m 3 y g o m F ~ d o m n 0 O O O ~ n O Z. ^ 3 ' ~ O N n aD N 00 N p fo d y N S y S N O. O d O n~p N O m N O N o j^ d 3 3 o f~ d d O' C O d 2 O m y 0 - y y y N m _ . < C y 41 O y n 0 m m y m y > O Q (/i O O y n m d o m K m 3 y O d 3 S ' O O d S d d X d m m r O < m m m Q o O fD O N y m m m d G 0 O (Il H m m = ( < O t~ 0 m y m f0 N m m o N < (D m n o C ^1 d 8 3 < m ? a. o,< ~ S d O m c 3 0 n S' ? m- ~m d ~a m m m m o m d d m o d n ? rs C o m S 7 o 2 3 c m c> d 3 '0 0 G d o 0 m m o> o o > v rn d N o m d d m m m m y m < a m a g d = o o p v b' = m d > o m > y > 45 d o d O m o. F m H O d S n H. m n o- N g J ? m j = m> O n O d d d d . Q. U) ? N D O G1 o O d O d C T p o O .y-. O x c O C m n D o n 3 O O C S f0 O S > O - (U JC p O O O ( O . m C C O m o O m Q d m w S ° ' > > n o 3> > K m o b n m ? O c y m d d m 3 0 0 6i Gi o c - - 9 c ~ a a, f ~n ^s C n OQ r ~ m o i v ~ < Oo o- ~ m m o y 6i c d a - ~ ~ d a d r~~ m m ~ ^ C] n m m Q m m m umi °c o v g o $ m g T o v D 3 d m F H y m d y a d d< m c d N C 3 C > N o C 3 1 m v o d a c > > G1 v d tx m d g y 3 a, O 0 o ? 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' y ~ m ' _°-F o y o ? ~p1 e y m. F y nyFi d d y ' ° - 00 m d o m m O ' S S 6 (D ~p N s _ m ~o d y rmn m y m - . H u~Di 5` O F = d - o o y n y m - °c 3 y m F a o 0 0 0 0 5' - a o 5 o o o . m ~c' e' ~n y m ~ o = D D ~ o v, m m o m m m c y ^ ~ a 8 b' b' b' m 3 y o 8 b' b' b' b' 'm chi c o o m F = m Fn f° m r°'i, m y m Q m m° d m E6, o - ° o y n m o m m-i < ° _ m p E5, 0 5' Z w m m m m m m m m o y m F, F y m m m m e = 3° 3 m °c m °c m c m F a 3 u, m c° m c n y m o H u y g » o o m m . o y m ni o F S'i - n v s m =m u i m m m m m F m , o m ~ m m a, m e. m m m nFi 9' ~ c23 ° ni = m O ~ Yn' y m N g o. 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O O O O O O O O O O O O O O O O O O 0 0 t F O O O O O O w o L ` o o 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 O ~ O O O O O O O O O o 0 0 0 O O 0 0 O O O O O O O O o 0 O N 0 0 N O O O O 0 0 0 0 0 0 0 O O O O O C ~ 0 0 0 0 0 0 0 0 0 0 0 0 0 o A O 5 0 0 A O O O O O O O O O O 0 0 0 0 0 0 0 0 0 0 0 0 0 O O O O O N N O 5 ` A 0 0 O O O O O O O O O O O O O O O O O O O O O O 0 0 0 O ~ _.N O 0 0 O O O O O O O O 0 0 0 O 0 0 O O O O 5 ` O A 0 0 0 O o 0 0 0 O O o 0 0 O O O O O 0 0 0 0 0 0 0 O O o 0 0 0 m ~ ` O A O O O O O O O O 0 0 0 0 0 0 0 O O O O S _ ~ N O O O O O O O O O r O 0 0 0 0 O 0 0 0 O 0 0 0 O O 0 0 0 G ` O O - 0 0 0 0 O O O - O O O O 1 - H O O O O - 0 0 O O O 5 ` - - O O O O O O O O - O O O O - O O O O O O O O O O O 0 0 0 O O 0 0 O N O 5 ` O O ~ O + O 0 0 O O ~ O O O 0 0 0 0 O O O O O 0 0 O O - - O ~ 5 O O O O ni 0 0 0 .a O O O O + O O O O O O O O O O O O O O- O O - O p + o o o o o o o o o o o o O o o o - 0 0 0 0 0 0 o oo - o o o» o m u o ~ o o o o o o o 0 0 0 0 0 0 0 0 0 0 0 00 -.0 0 0 ~ - o o- ~ o o o o - o o 0 0 0 0 0 0 0 0 0 0 0 00 - o. - o ~ G o o r o o o 0 0 0 0 0 0 0 0 0 0 0 0 o oo : o m o G o o - - - - - - o o o o o -a 0 0 0 0 0 0 0 0 0 0 0 0 0 00 . o o - -o ~ o G o o o« o o o 0 0 o o o o o ".a o o 0 0 0 o 0 0 0 0 0 0 0 o c « oo o 0 o V 1 7 1 0 0 0 0 0 0 - 0 0 0 00 0 0 o O 5 ` O O O - C - O O O O O O O O O - O O O O O O O O O O O O O O C- = 0 0 O O N O 5 p 0 O O O - 0 0 - 0 0 0 0 - O C + a 0 0 W O O - p 0 O H O O O O O O C ~ O O O O O ~iy `y O ~ 0 0 O N O O O O C - +v. O O O O r+ O O O O K 0 0 0 0 O 0 0 0 0 0 O 'w O O 0 0 0 O O J O 5 O f0 O O O O O O O O O - O O O O O O 0 0 O O O 0 0 0 O - ~ O O C 4 N O o .M O 0 0 0 O O O o O O O O 5 ` O O O O O O O O O O O O 0 0 0 0 0 O O O O O O O O O O O O O O O O O 0 0 0 0 0 0 O O O J O O 5 ` C +t N C O 0 0 0 - O O O O O 0 0 0 0 r O O O O _ O + j O ~ ~ - - - _ _ O + - O O O O r O O O O C R O Q 5 0 0 - N - o o O O O O O O 0 0 O O O ~ O H O O O 5 O O O - _ N O O O O O O O O O O O O O O O O O O O O O ~ O O O O O ao N 5 N o O + 0 0 X 0 0 O O O O O O O 5 - _ _ O O ~ 0 0 0 O O O 0 0 0 O 0 0 ~ * O p O - - N O - 0 0 O O O O O - 0 0 O O O O O O O O O O O O O fOn N C - - - 0 - - - 0 0 0 0 0 0 0 0 0 0-. +oo o o ~ o ~ 4{. N o 0 0 o 0 0 0 0 0 0 0 0 0 0 0 o 0 0 0 0 0 V° 0 O 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 O 0 0 0 0 0 0 0 0 0 o 0 5 w .r - O O 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 - 0 0 o O 5 - - - O O `3r, o 0 0 0 - ~ o o O O O . 0 0 `O • T m N T N T A N W N N N N O + p 22 QO d m m -°m ° y n D a S d y m Q O N g o m' m tpE O N g m' m (7 3 a = ~ 0 0 0 0 c'i 3 Ci m = o m m n m m s ~ 0 F = f 3 » F n o o ° 0 ° 0 m m m m m o c~ 3' = oFi c~ m m m F m nmi n m = y cni o cNi, N can o e " D 3 a cn'i~ <n o v e ° cni~ x vNi N' ° w op F D m 4 'm o F m 8 c m ° 8 m ° 8 3 Pn 0 3 x y 8 o o- _m c o 6 3 o o o= ' i° 3 m °i m a F s z m z fD a ~n v T m m c o °p °o " ° o o ?S c m o m ~ s d m ^ o = m y 3 m o• m o ° e = a o 0 o= 0 ° ° o ° o° w ^ my m F y y l c f c m in o 3 n ° m m m o o y . y 3 y m m m o 0 F o o m x w v pi o 3 ° m o w m m v W C m N eFi m m m m F m F = p1' a3i m - w o n° 8 m m m m o 0 ° d v 0 3 O N n y 0 3 O N = S N= ' g 2 m ~ d a ,Q - m 'O , 2 F o ma _ A d o d Q D < ' O y p F . - m y c ` m y °i 3 m 3 3 > D d c o y m - m 1"n m Fo m 3 3 of 3 = m Q m C-F m c < m 8 8 c m y c m c m c p1 o a f ~ m m ° ^ m ° = j d m n m = - F a d w m " o 3 ° m m ° m m Q a u S. o m o° - o D F g o °s G gs m= ° o. _ c y 3 ^ ~ o y , = 8 y~ m ' ~.a»~y y D 9 m o yy rs D yy j D 8 m a Q m n m 'a y y a o ° = - v > - F y n w m o y o o m o m " O = of o 3 c m G _ = ° m= 'b' o m - ° y 8 = m F °g c o 0 m m m m 3 m m = o m w > m > j y $ = a H c m In 3 ° F 8 oFi m m 8 , r Fr < m m _ m ' = _ g = m n~° c m v c _ c m n c a - m ° o m= d a y o - n c m m m g y 8' » N d A 3 m m ° y io m a m o 5F 3 m o' 5 3 y mG»i s 3 c F ° y ' S m = d N - y =m m f m $ = m o m m 8 'm o = 3 m= m = o o m m _ m C °o Q . . io N ? i 3' 0 F `n . F o I O N m fU m Si = 3 ~ 3 ~ N g m G o ~ P' ° w o F z C ^ 3 m ° 2 w N • = . = A Ci f='f 00 m A N m - y N = f < (U N P j = A 6 C = N F ~ ,y y m d = _ . q Q. m . m w O m Aa = m N ^ p w = y m l D y N {p N m F L~. m m m ^ M tD F C c o N F 6 F O A °1 G», : o ~n m o o _ F. m O ° < w C-r m m y N m ° Si N 8' m ° Si _ m m m m n w o m d o m a ' n d ~ ' p m w D - m i 3 . d O y 2 y H ? m W°o m = fO n d 4 g m g 3 m X? » - K= » y 'm m^ y g 8 =n m m d w m , am O d = m 23 y y s m D _ " = V w m N m ° y Ci m ° m ~ D n O - N m ~ m n N n ~ Gyzl ff y C y = n m n c n 3 N ~ G m f O N = ~ = o t0 T m' y F f=c D m y ~ - - y - o- c 3 o y y m Fo ~ w n w m y ° o o F z 8 m O n 2 ° ~x. ~ g ° : LT T N m m N m m o'ci o 5 . m» vmi m a ~ m ~ F $ ~ o m a m m d o o' ° $ m E a o m ° y 8 so rte. n$ w o 0 3 v m _ y AT -a o c y ~ F ~ 3 `e y m o a ° 3 o ,a 3 m o o v m e 25 p1 o n m o m d n °i m m C ~ m ~ N n y = c ~ = N d ~ ~ - ~ ~ ti. C. N d ° ~ ~ y yO n = - y sf y G ~ m = ~ - ~ y 9 m Q O ~ C~ ~ m [D 3 j Cn N N ~ = ^ R y _ ~ m O N N ~ N fD m N N Ip 0 m ~ ~ O A N N _ _ 12 ° 4 y N _ a' m y _ w m m _ m O O O O O O ~ ` O O O O O O ° 0 0 0 0 O O 0 0 O O O O O 5 ` 0 0 0 0 ~ O O v 0 0 0 0 O O S ` O O 0 0 0 O O O O O O O O O O O O O O O ~ ` O 0 0 0 ~ O O ~ 0 0 0 0 O O 5 ` O O O O O O 0 0 0 O O O 0 0 0 O O O O O S ` O O 5 ` O O O 5 ` O O ~ 0 0 0 0 O O 5 O O O O O O 0 0 0 O O O O O O O O O O O 5 O O ~ O O O 5 O O ~ O O O 5 ` O O O O O O O I F O 5 ` 5 ` 0 5 ` 0 O ~ 0 0 O O O O ~ O O 0 0 0 O O O O O O O O O O O O O O O ~ O ~ O O O O O N 0 0 O O O O ~ O O 0 0 0 O O O O O O 0 0 0 O O O O O O ~ O 0 0 0 5 ` O O W 0 0 O o O O ~ ` O O O o 0 o O O O O O O o 0 o O o O O O S ` O ~ o ` 0 0 ~ O O A 0 0 0 0 O O S ` O O O O O O O O O O O 0 0 O O O O O O O S ` O 5 O ` O O 5 L O O N 0 0 0 0 O O 5 ` O O O O O O O 0 0 0 0 O O O O O O O O O ~ O 5 O ` O O 5 ` O O ~ 0 0 0 0 O O ` S O O O O O O O O O O O O O O O O O O O O 5 O 5 0 0 O 5 O O ~ O O O 5 ` O O O O O O O O O O O O G ` O 5 O ` O S ` O O ~ O O O O O O 5 O O O O O O O O O O O O O O O O O O O O 5 O 5 O O ` 5 O ~ ` O - - 0 O O O O S O _ p O O O O ? , +f O O 5 p~ C 0 0 0 O O O O O O 0 0 4 O O O +i O O - O - ~ T~- - O S O O O r 5 - Y: O 0 0 O O O ~ O - ~ O O O O + 0 0 O O O O O O J+ 5 ` O 0 0 0 . 5 ` - O N O O O O , O O ~ O- O 0 0 0 O O O + O O O O O - + 0 0 O + O O O O ~ O 5 0 0 0 5 O W O O O O 3 k O O S O - + O O O O O 0 0 O O O O O O O O O O O O O O O O C O O 5 0 0 0 - S - O O O O O i O O 5 p w O C = 0 0 0 0 O O O O O+ 0 0 + O + O O O O ~ 'Y O 0 0 0 - C - V O N 0 0 0 O + O O 5 O - + O - - - - - - - - - - - - - - ~ O G ~ ~ D7 0 0 0 0 7, ~ O O ~ O - O C = 0 0 O O - 0 0 0 0 0 - O O O 5 C C C C V O O O O L M O O O 1 0 0 0 0 0 O O - - - - O O - + O + O O O O 5 0 ` 0 0 - ` ` - y:. 0 0 O O S O . + O O O O O O O - O O 5 .JY .r O ~ O 5 - O O O 5 ` - O O O r 0 0 0 0 + O O O 5 ` _ . 5 0 ` 5 ` _ t I 5 - O 0 0 0 0 0 0 0 0 0 o S 5 0 5 o pj Q O O O O ~ O O 5 ` O + O O O O O O + O O O 0 0 0 0 .a O O O - ~ 5 0 ` 0 0 Y ~ - O V 0 0 O O O 5 O+ O o .ia O O O O O O O O O O O ~ 5 f~ O 5 0 0 0 5 - ~ O ~ 0 0 _ O O S O - 0 0 O p p p p C c r O 5 p - 5 - - p V y 0 0 0 0 O O C ` O 0 0 0 0 0 0 - - - - - - - 0 0 0 O O O 0 0 5 0 0 O G 0 0 0 5 O O CVI~ - O _ O p+ - + p p O C O C _a O G O G G C _O 0 0 0 0 + o o G o^ x. o o o o o o o o o o o oo o + o + o 0 0 0 C o G o o o C o M o V V O O O O O O O O O 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 O O O O O S J O O 5 O O S O O ~ 0 0 0 0 < O 0 5 0 0 - 0 0 0 0 O O - 0 0 0 0 0 0 0 +i O J O O O O + 5 - S O O O C - O V 0 0 0 0 O ~ O- O r O O O O - = 0 0 0 0 0 0 0 0 r O + O O O - ` O 5 0 ` 0 0 5 = O p O O O O O 5 LL p O O O O O O .5 0 0 O + O G L - ~ O ` = o O m 0 0 0 0 + 1? i-( O O 5 ~ O O O O O O O O O O O O O 0 0 O + O O > O O L 5 - O ~ O O O G S O O 0 0 0 0 . O O O O + O O O O 0 0 + 0 0 0 0 0 - + O O O ~ O O O O L S O O ~ 0 0 - O 5 O - r O ~ O O O 5 + O O O O O O O O O 5 O ` p 5 ` C O p O 1 O O S - O O + 0 0 O ~ O 5 O ` O O ~ . O N 0 0 0 0 O O 5 ` O O O O O O O O O O O O O O O O + O O u O O ~ . 5 O O O r C C O ~ _ O O O O O O ~ - O O O O O O O O O O O O O O O O + O O O O ~ O 0 0 0 5 O - O r O O O O O O O O ~ 0 0 0 0 0 0 0 0 0 0 0 0 0 0 O O O O O O O ~ O O ~ O O O ~ O O O m O O O - O O S p 0 0 0 0 0 O S O 5 O 5 O - o - o O 5 O o o O o 5 _ r 5 O S - O O O O O O 5 0 O O O O O 0 0 0 0 O O O O O O O 0 0 5 • • • A A A N A O fp Oo V T IT.1 Ur W A tTJ W N W m O m~ a cfna2 Q y m a ' °i 0[n2 o m , o• . 0mz2 o o m m m = m m C7H ~ o ° 0 3 m2 m ° ~ cw o- D c O(n fn o D ~ os,g cn o D o ~ ~ ~<D{p wv1 m m c ~ c ° Z o t n --I _0 m n ~ DDZ c 3 m ~ a ~ a m 6 y^ ~ PD y y 8 o t o '0 8 [n ' z m m " m? ^1 ~ ~ . n c m ° 3 m n m `n n e . 1 o 0 0 _ 0 ib y = a ml \ = ° o o H c 'm-' a c o N o m ° 3 ° a m= o ` ^ 3 ° ° m e N o coil n a c a y °i c=V ~ °rf. S'i 'o m m ° y mD m a, m ro m I ^2 m° ^ m S o a m 8 m o o g m m 3 i n o m a m N x m ° ' m C. . p m e o S , " N y _ O o p ' m w a o o - m° rn N m ° - - om l o g e O o o o o o o o , c c ro p a i F m , 3 A F 3 m °1 m C O m < 8 0 J o 0 D - d c m n 1 m c N g m D D 43 4 . y . m m - = 3 7c 3 3 3 - . 3 9 3 . Er ° s m 8 m o o° c o y y D y m c m o o - `m' 8 m u • ^ ^ H m° _ y? p $a y c o m m = m i° m m 8 a o• d D D m ~1 F o ~o' w C N < m w m N V o p m A J V 3 ° N @ = c m ~i m m m Si < m m m m y o _ m i~ = @. m y = m N G p• ` a, m ' ff' a, m m n D 3 z o m °o S F m w y m c- 0 c ~ m ? m' m o fU m 4 3 n S n m - g 'a m °1 m m m n m o y m y 'm rn 0 8 y c N " e o w ' o ~ o 8 o o 8 y m ° (nom' m 4n o o 3, ° d ' o m o. 6i ° Ei n m o. ~ d N p1 ~ 8 . y to " 4 fn < m to D m F y F' ~ F c~ F ~ Ge g' u, m ~ o w c e 3 ~ 3 °m = x =o m y m ? N g o m m y m 3 - m on n m m m o' J j 0 m 6i 3 8 a m rn _ m c m < p o a m d m m n Vl v 3 ' y y ° m' " w 3 d m 1 e n i m m - = In o vi m° 3 w? p o g F m m - o H= N m 7 w ° = gy F. m tp 1p n m ~ d ~ ~ m fm 1D m rs h y m 4. > > < m 3 O a' < 00 \ m m y ~ O O p ~ m (A ~ j m ~ y m g H m m N m 'm d m °1 N m m ~ > N > m m ' m ~F = - Z m m " C - ~ ~ ~ , , d m m m = p ~ c m m' l~D m 3 ^ D D o3 m m 8 ~ umi c o, , _ e 8 D yy m m yy m ~ 3 o m g ° = 3 y " p, - ~c o m y m D o ~ m y m F N m 3 ~ o o yo m ~e ° n F m m F ~ m F a og 3 a m D g g D m ro 3 m m - m H o pp m Das d ~ = o dd m - R 8 y m = 8 m c y O o $ y °c o o c n o 8 fc 8 3 m m < D 3 m d = w 3 3 d _ y [n a m o m c y a m m ~ o y ` y N o H m y u1 f - m m 0 ' a m D n m ~ 8 ~ m, x n < _ N d O` o J N c F N a c 3 o V G o ° N a N V ? a N y ? m y m 8 m m f c c C o, ' d d ° m O o - - y 3 O o O ° s PD = ma O- o 3 ~ _ m m p d~ f° 3 m N " x N N N p H N ~ N d ~ - N tLC''~~f mi~ d V 'O ° ~ O - O O N o, N ~ m (n D < ~ T 10 C H F ~ N ~l ~ y m N J w j y Q o d y d - Q y y ~ N O N ° ~ m N g g n m 8 O 8 y 2 v ' T 2 4 d m F g m o m o m so m m n m' 45 > A o m y D < 8 m =a y 3' a m m o n a ° 0 1s a 8 r D D F F m m o m ° m m m n 8 y $ F m a m 7 5 a $ = = m o m p q. p m D D v c o m o m °a1 c m m a m T 3 m x H n o H G m " o m m o m o H m m m of a m m 3 m a m °i c a m m g o a m 3 3 Id c m d s a y y y r o 3 a m e m" ~d m F o _ a a n m cn ° j ? < m n ci m p1 m m m m 52. o y o c m _ 3 ? n g? m_ m m A 8 ° y m c m c° ~ m y ti ° ~ o ro m _ ~ FD $ > > m ~ m ° ~ ~ o m ° m F ~ y ~ m a1 ° H f m m ~ m \ o wn ° n = 1D c f ~ " ~ o_ y 0o d N ~ N O °O y ~ ~ u 0 m N n m J v < El 2L o m O O O O O O O O O O O O O O 0 0 0 0 0 0 0 0 0 0 O O O O J O O o O O O o 0 0 0 0 0 O O O o 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 O O o O O O o O A W O O 0 o O O O O O O O O O O O O O 0 0 0 O O O O O O O O O O O O O ~ O O O O O O O O O O O O O O O O O O O O O O O O O O O G O O O O O 0 0 0 O O O O O O O O O O O O O O O O O o 0 0 0 0 0 0 O O O O O O ~ O O O O o O O O O O O O O O O O O O O O O o 0 0 O O O O O O o N O O O O O O O O O O O O O O O O O O O 0 0 0 0 0 0 0 O O O O O O O W O O O O O O O o 0 0 0 O O O O o 0 0 O O O o 0 0 0 0 O O O O O A O O O O O O O O O O O O o 0 0 O O O O ~ 411 O O O O O O O O O O O O O O O O O O O O O O O O 0 0 0 0 O O O O O O O ~ O O O O O O O 0 0 O O O O O O O O O O O O O O O O O O O O O O O V O O O O O O O O O O O 0 0 O O O O O O O O O O f.tt O O O O O O O O O O O O O O O O O O O O 0 0 0 0 0 O O O O O ~ O O O 0 0 O O O O O O O O O 0 0 - 0 0 0 C + O + O O O O O O 0 O O O t 0 0 O O 0 0 0 O O O O O 0 0 0 O O O O + 0 0 O O O c . 0 O r J 0 0 O O °1 O O O t y~. ..t J O O O O O O - O O O O O + O O B O O O O O O - O O O - O - O r- O O O O O O N O O O J O O O O O O - Y l - 'l - O O O O O O O O O + O O O O J O O O O O - O O O - O O ~ O O _"-~'K O µ J 0 O O O O O O O O + O O O O O O O O O O - 0 0 0 0 0 0 0 0 0 0 O 'J O O O O p O O O ~Y J O O O O O O + O O O O O O O 0 0 0 ~ = 0 0 0 0 O ^ O O O O O ~ tit{, O O O O O O O O O O O O O + O O O O - J O O O O O O O O ~ O O O J O O O O O O O O O O O O O O - O + O O O O ~ O O ~'i.,L1 J O O O O O O + 0 0 + 0 0 o O O O O o 0 0 0 0 J O O O O O - O O °1 O O O ' r J O O O O O O O 0 0 0 - O O ~:nry1 - 0 0 0 - 0 0 0 0 0 0 0 o O o 0 0 - _ _ - O O ~ O O O _ ~i - O O O -1 Y O ~1 + 0 0 0 O O O O O O O O O O O O O - - - - 0 0 O - O O O ~ O O ~ N O O 1 O : -iii ~ J O O O O O O - - O O O O O O O O O O O X 0 0 O O _ - - - - O ~ O r 0 O O W O O O ~ O O O O O O O w O w O O O O O O O O O O O O - 0 0 O O ~ 4 1r, - + O O ~ O O O O O V y n 0 0 0 0 0 0 0 0 0 0 - }r o o o o 0 0 0 0 0 0 0 0 0 0 0 0 -~~~-~`:aid >?i - c J o 0 0 0 0 0 0 0 0 o N I LI - F- O O O - O O 0 0 0 - O + 0 0 0 O O O 0 0 O O O + 0 0 O O o 0 0 0 O + O O O v V 0 0 0 0 O O O O 0 0 0 - O O O O O O O - 0 0 0 0 0 0 0 - ~ y O O O O O O O O O O O C J O O O O O O O O O O O O o 0 0 O H O O O O O O O O a! - J O O O O O O - 0 0 0 0 - O O O O O + 0 0 0 0 - - 0 0 - O O O O Cv ~ O '.t~, M1 J O O O O O O + O O O O - O O O -w O - 0 0 O O O - O O O O O O N O O O ~F^ .J O O O O O O ~ O O O O O O o j. a1-. O O O O O O O O W O O~ O •';YR J O O 0 0 0 - O O O O O O } 'J O O O O O O p O O O - - O O O O O O + O O O O O O O O O O O O O 0 0 O O O 0 0 O O N + 0 0 O O 0 0 0 0 0 0 O J O O ~ 0 l 0 o o 0 0 0 0 0 0 - o o o o 0 0 0 o o o o o o o o o - 0 0 0 0 0 0 0 0 0 0 0 ~ 0 0 t~'•CT. o - - ~ 0 0 0 0 o -Y O o o o u o 0 0 o o +t o o o 0 0 0 o o c J ~ 0 0 0 0 0 0 ~ 0 0 0 0 0 0 0 0 v. - o 0 0 0 0 o f'±~JL_ o o o o o o o 0 0 0 - - 0 0 0 0 0 0 `O • • • U f.l~ ~ ~ VTi N N O tA° OAO V ~ A U1 a m O m 3. 6' m 2 o y o o m ' m -2 n T C7 O N 8 C 9 U) a 8 c' 00 fn fn 3 P o y g `m p S m g r 0 3~~ d °C. O C1 F y N~ `Z f0/~ 9c _ ~ 1 O W y~ O m O g n N l N n ~ f0 3 d m w 3 3- m m n g ^s a o m SL ' y c 0. _ S -V ~.n o N o N v ° + 6 + O n o n o rs m N ° v VJi o n N tr fNl~ n o m r n m n m n 4. n m n m ^ n Q. m n m n Q. m - n a o m N m d - ° tD < 3 $ 3 $ ° N o A n H m n_ C c~ ° F C s N can o 4Ni Cn o a m ~ c~i~ 0 4Ni cNi. N o <O u. n~ ° - m. 5" o ? o' a o m n n n d= 8 m o F = d y m 3 o 3 o y ° o 0 0 ' o ' y~ ~ m ° o o ° ' = F ° m n e m n °c m c ° _ m e . m o m a m Q ° = c cn c v, _ m w m in w a m c n n F m ~i o e o o e o o _ a ° o ° o o 0 o e ° ~ n ~ o ^ ~ y m c ~ m C1 ~ o °i ° y N l 3 m o =m o =m " G D O~. o =m m < ° S v ~ w v ~ = m ~ y m N p fD w a tD A u ~ m' 'm w y , ~ ^s m ° o m 3 S ° ao O ° 00 O 3 3 3. = i O n n N ' N N ? f~ m ^s m o F lD m N a. °1 ~ m < fD ^s m o N "s N m° N m m ° ? m N D D m G 3 O 'm m ~ y O' d a N 3 m m ~ m y y 3 - + o. di, o. ti - a 3 d d m c i ~ y ° w' °1 ^ ~ F _ c y . o c C Q° _ m = ° _ v m m y _ m g y c a $ ~ w m 'm ~ m m °1 F nFi m 6, m < ° Ci m m m m 3 ? m o Yn' c ° ti ~o o x w y m = m w m F m n m m m 'm m °i m m = a m - ° 6i R ? - m m^ iy ^ a 3 3 to m y 3 m m m rn rn l m m m ° - N o' $ e o . w o ° D m' m c H a- ° F _ F . 9 _ n D ay n n n ° y o H n 3? N PD °3 0 0 8 m x °c 3 n v, o m m = n _ n 8 3 w ° < ° 0 ? = 3. n c Q ? + o° o a D y D y y D d _ ~ O H 3 a w N O ~ C N m m c d D D ~ ~ d c3i } N DD D o c~v ~ cva x v o 3 ~ 3 v' m ~ u, S y ~ w m d < ~ Er d m uni ~ o . H F y o o o °^s, T n ° m y o 6 Q 3 < o^ ° o^ ° = y m m m m a - = T 3 m m 8 m m y N m ° a m °o ° n m c °m a' 3 m = ° > a° > O a S m o m ° y^ 5i m D 8 m = O 3 m m o o u~°i w w nFi g + °i c 3 _ 3 m c > = ~ a m - A mo o Fo o 5. ff o m m ' Q 3 Q m o w m ~ m Z w f7° a S y m 5 ~ F F > 3 1° y wLl ? c n o } c °i n o o ~0 m N d ? ' any .r m O A ~ y ~ m ~ 3 3 ? c m m m m > > a in x m m w m 3 m, ~ ~ ~ ~ m 0 ' m 3 m n~ m 3 m n ~ ~ m ^s m ~ F D D m ' m a ~ ~ ~ ~ ~ g w ~n ~ °1 0 3 o 3 ~ o o S 0 - o ~ y ~ y m m < m on n _ O o m y ° c m N m m fD F F = m a 8 C, Q° ' w m P 03 -S 8 m o 0 oc o m G j e N m v a si m (n y D~ o n = ~ ~ F a n m F °1 o F 5: F o n o m F D D a m o o m o o 3 Si F 5i o O m - c ~ m F n m ~ e e m o m a~ ~ n i y ' o 0 u m ~i m m 3 n y ° m o ^ o rn ~ » o_ a a o n 0 3 `C, n n = n m on o ' 3 E 9: . m 8 = 3 ~ j m o N L. m m N m m c 5 ' ti o 3 c ~ ° g g m s w m c o- m an d ~ o w d ~ ~ o - 0 8 ~ ~ o ~ d d N _ ' 8 3 m o o ni 3 m n Z m ay r° m - e 'o v o a n = m i F = ~ ~ m d n~ y O O 0 0 0 0 0 0 0 0 O o 0 0 0 0 0 0 0 O O 0 0 0 0 O O O O O O O O A J ° O ° 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 O ° ° O O 0 0 0 0 ° ° O O O ° 0 0 0 A m O O O O 0 0 0 0 O O O O O O O O 0 0 O O O O 0 0 0 0 O O O O O O O O O A b O O O O O O O O O O O O O O O O O O O O O O O 0 0 0 O O O O w 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 O O O 0 0 0 0 O O O O 0 0 0 0 0 0 0 0 O o O O O o 0 0 O O O 0 0 0 N O O O O O O O O O O O O O O 0 0 0 0 0 O O O O O O O O O O 0 0 O O O O O W o O o ° ° ° o 0 o ° 0 0 0 0 0 0 0 0 0 0 0 0 0 0 ° ° ° ° 0 0 0 0 O ° ° o 0 ? 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O O O I5. - 0 0 O O 0 0 O 0 0 0 O O O 0 0 0 0 O O O O 0 0 0 0 0 O O O r p O O O O O ~ • • • V V ° °Ti O ~ OD T V OTi °f OTi (I~ °Ti A m W °Ti N T O ~ T Oho T V pU1j O H y N a C j < y m (iCi Q h ~D d O n H° O d° n G m c n A w m o z u c m T 3 G1 m Fo G) m c O a 0 (n 3 7 C c m 0~ m c y y o ~ ~ Q ° a ~n ~ o ~ `2 y m m = r3 ~ D 31 ~ a 3 3~ m n a m o N ? n v X~ n - m a 0 m m ~ - a~ - y a m m o ~ - o = ~ o °F' Fo 3 F f 'p° o m m = o y ° m o ~ ti on m > - > - 8 > S > 0 = = o cn~ir yNi c_n c m g m 3 SS ~ < g 0 co 3 T m N in rn » ~ o ~ m = m N'm F m f si W W T F U m' o o y d o A fi ° b' ° 3-'(> n o r- o 3 N D o m g m o o 3 m i 3 3 m o y< m m- 3 m a m 3 o 3 ? ? 0 3 o m` c g ^ ° o o ° = 3 x n~i yy = f0 3 m = m n o o 1 3 a _ ° o = o m y ° m 3 0 F ° = m o ❑ < m m c - m F m 3 -c ° ' f o = m S'' m S'' o- ° in E ~ m ° c o a D m < a ° d' m m s m - n= ' m " m _ 3 N _ ^ y i° w 'n m w o a ? m 3 o N _ m $ Q~ y m m o m 'm m > g 3 _ ? Ef F o g cb o= m o m o _ y ' 3y'c DND n n - m a m c y o- fD m ° ° i° ~DD N a m - y m _ m m F o m a w m m ° o = : n d m ? = y D o > m j 3 m o ' c m y = 3 a c3 ° y o o m S = n n 2 o n -o o o ? m m ` n ° 5 Si N a o o- ° 3 y 3 3 0 n , c o n a EL L c j a H . m 0 m 6 w o 3 m F S O 1 °1 H - y m 3 cZ. L2 o= y T. ° 'm , m F c c cFi a m N a m o m 3 ' ° N o 0 o ° ~ 0 mn ° m m o n o i x d S 3 = o 3 Q 3' o m o o 3 p1 m ^ m g - F v a w d _ d 'r o m m o °1 y f o m o m g m n o m m g ° " H o3 - o a o m 3 g ^ _ rn m ° - f m m m d - o g d _ 5 A 91 a m- N - a = o - - d g ° d~ 8 ~ m a 5 5 _ ° s od 0 ° 5~. w a „ m d yy ' a a = d am ' ' m 3 0 y H - ? N o< p m \ 3 3 » a m j 3 m N m d °i i c F _ ~a F D d m 3 m - F ~ 3 c m ~g o m a o a y D _ m o y 0- m m °y m g a m m o d d w ~ ~ n m o £o no N o o f _ y ° 3 m n m o W nn~ m m 0 3 w ' m 3 y n 0 » m e ga a n S N o- 3. y 3 er a, c~ P. n o = d 2 5 w m m yy o m FD F m m m ~o»' 55 a rf ° m 12 Yn' o y n m v ui 3 Q $ Q a 0 a 3 y Er m 1-2 H N o- F = m 7 m c g m w ri* H 3 3 = S y n m n m w S• ~ m m e H _ c° ~ - ' m is ~ < ~ n o = - a m ° m o. ? m m a v m > D 3 C a ° a o m 3 0 al y c°i 3 o a °1 = c m m o a v H n a° o N H y F o, 'm H n w d ~ d N N _ ° 2~ N = d d J = ~ d d N w a 6i ~ Q y ni m° ~=c 3~ f° _ m c A _ m ° = D n ~ D O 0 0 O O O O O O O O o O o O O O O O O O O O 5 p J O O O O O O O O O O O o 0 0 O O 0 0 0 0 O p p 0 O O O ~ O ~ ` O O o 0 0 o p 0 O O O O O O p p p ~ A b 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 ~ o w 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 ~ o 0 0 0 0 0 0 0 0 O O O O O O O O N O O O O O O O O o O O O O O O O O O O O O 5 c O o o o O o p p p ° p C c A O 0 0 0 0 0 0 0 0 0 0 0 O O O 0 0 O O O O N O O O O O O O O O O O O O O O O O O O O O S O N O O 0 0 O 0 0 0 0 0 O 0 0 0 O O O O O O O v O O O O O O O O O O O O O O O 0 0 0 O O O O O O O ~ O N O O 0 0 0 0 0 O O - H O O O O O O C o ~ O o - - p p 0 0 0 ~ O - - O O O C ~ O ~ ° O O O 0 0 0 0 0 - O O O 0 0 _ _ O _ O O c O O O O C - - O 5 ` p 0 O O 0 0 0 0 O - _ _ O O O O - = o o = 0 0 4 - 0 5 5 ` ` O N O O O O O - _ - 0 0 O O ~ o O O _ _ _ _ C c p W O O O O 0 0 0 = 11 O O O 0 0 _ O o - - - O + ~ 4 ^ 0 0 - - _ O O S ` p O O O O O O _~4 `Zr,~.: ~ O O O O O = - 0 0 O O O~ p C 0 = O O ` O O U O O O O O O ~ O O O O O _ - 0 0 O O ° - 0 0 0^ _ O O S p 0 0 0 0 0 - ~r O O O O - - - - O o 0 o O O O- O O O ' - - O O C c J O O X 0 0 0 0 - O O O O - - O o 0 o O O 0 0 0 - O O C c O O - O o o O O O c _ I O O 5 ` O 0 0 0 - = O O O O o A p o o ^ + O O O C c . O O o Q ° 0 0 0 0 O = O O O o p o 0 0 O p : O p p - ~ ` O N O 0 0 O Y- O O O O -1 _ ^ O o 1 o O O O C - O - + p - _ _ p C C c 0 0 0 o a o o o o o » o o _ - o c o _ o o o- _ - ~iz o ~ o a m 0 0 0 - o ' o o - M- 0 0 0 0 - ~ 1 -1 - o+ + o o o o o + o o ° 0 0 0 0 ~ o o o o ~ ~ o ~o - 0 0 0 o ~ o 0 5 o rn 0. 1. o.w o 0 0 0 o 0 0 0 0 o o o > o o ~ o --0 0 0 0 - -mo o o ` o V o o 0 o p p ;~,K r 0 0 0 0 0 0 0 0 0 0- ` O ~ O F - 0 0 0 0 r 0 0 1 -1 - O _ 0 0 r+ O C. _ ..l O + O O O O ~ - O O 5 LL 0 O O O O O O O _ 0 0 O O o 0 0 4 ~ i O O O O O = O O 5 ` O ~ O e - - O O - O o O --a O 0 0 0 ~ - O O 5 0 0 0 O - 0 0 0 O o O O O O O O O O + O X 0 0 0 O 5 O N O 0 0 0 O O = O o 0 0 O O O O O ~ . 0 0 0 = ~ ` O ~ O O O O O O O O O o O O O X 0 0 0 ~ O p O - - - O O ^ O O O 4 - 5 O O O O O O O O O O O o O O o O O +i O O 0 0 0 o 5 O O 0 0 X 0 0 O O O O O o O O O O -s O O -a O O p p W + - O S ` O m - o o ~ p m o O O p O o p o 0 0 0 0 0 - O S p ` 0 0 0 0 0 - o 0 0 O O o _i O o 0 0 ~ O 0 0 0- O O S p ~ • • • O m tV0 V O V V m O V l U T V t A J N Q c a o v m N- a CA m m N ao ~ m D O m m m ? o m d m 0 z m m - ' d d m D~ m ~3 'o° C w v o ~ tc1 G N n m D N n o m < D y O p v 3 a 0 3 m - N o m a m ~ pi - O 3 A m i o - o D c _ n m n R - o ~ m c o m N c m N O F O a m 3 y m o q n ~ ° o m n 3 o. „ u, N O y y a E, o 3 m 0 F m ~d - m ~D f° o 3 l m j n oFi 9 m 3 m n j a g \ o _ N ut c f~l1 o O J U V N o y rS N o 3 0 ~ n fD n m ~ w H g~ o~ O O m m - 3 m (o ~ ~ n m W O O \ o e 0 o' PD o S° m N H ~ n D m ~ ~ ~ v c n ~ 6 x g c m m o y O 7 'n ° m y- = o D c y m d n : N N = y H d i ° F o d m y .3_ ? = n ~ ~ y F C i - < n L' m o o d ry z m a n c y _ n 3 O c m ' -F'° m s m O o- n 3p C? a o o F c d n~ c n g _ w p1 o _ . u N O 0 O 0. 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O O O O O O O O O O w O O o 0 0 0 - p _ _ + 0 0 O - 0 0 O N 0 0 0 0 0 + O 0 0 0 0 w O o 0 0 - O - - O O O = 0 0 0 0 - O O 0 0 0 ~ O O - - O O O O O O O O O o - O o o O O _ - 0 0 0 . a O o p d O O O O O O 0 0 _ O p 0 0 O N 0 0 0 0 O O 0 0 0 0 + - ~ O O o V - - O o o O O ~ 0 0 0 0 O O - O O O O O O O O O O - o O O - O O « 0 0 0 ~ 0 0 - C - - 0 0 O O o O O O - - - - O Q O +M 0 0 O O O 0 0 0 0 + -1 -1 - 0 O . -1 -1 - - - - 0 0 o m O O 0 0 0 + 0 0 - ~ 0 0 0 0 0 w O O O o O O O w O o p O O O w O O O - ~ O O O N O + O O o 0 0 + O O O O o O O O - - - O O O O O O - • 0 0 - O O o p O O 0 0 0 O O o 0 0 0 O O o O O o p O 0 0 o N O O O O O 0 0 0 0 o _ O O - • O O o - ~ O 0 0 O O O 0 0 0 o O 0 0 O O + 0 0 0 TN -a OD i.: 0 0 0 0 - - - a O O O O 0 0 0 ~ O O O O O O O - 0 0 0 - O - 0 0 - 0 0 0 ~ O ~ 0 0 0 0 O O + O O O O O ~ti: O O o ~ O o 0 u O O o b 0 0 0 T T 4TH A T N _T m c m chi m m m ° m F ° m 'c m ~ 3 _ m » 11 V-1 o= El 3 j' md °Z N IS F 'm 3 g o C 8 rs c° (n m N c o 8 n ~ 0 8 0 ' 8 o 8 O^ c mi nn o m o ' D DD y ~ e ~ N ro C~n o cn o u, v m e v z z N c y 6 o `z m o m e W m ~ x w Fo c o f. ~ 3 N o < 0 Pi c= - y c c 8 m= c - i m _ o ozi C w c x m w c~~ m .Q ° ~ Go d° O. tO D -~o D m~ z D z ~ ~ O r n o ~ C F ~ O y C-F 3 » c a o ? N a c o o c w ° m m 3 g g 3 c d o o o ^ m ° ° e o ° " ° o ° m g ac n o a n 3 - ° m m wa u, _ c S ' d - m ? , m ° c ° m x~ v O° of ' o y° n T m is m m c 5 ? o oa » ~ m g ? mmy m g ? w o~ c N c ' m c -y ' m d dd 0 0 ^ ~yy ~ ~ m g n _ c: < m m ' b ° o m o = d d o df A ad so f~ v. _ c. - ~°d m o aag o y~ f < w ~a g D 3 m oo D m u' 3 N y y c n° m S m o m = R 0- m .=m_,. m D > g D g < m n i n o- m - ~F ° a m y m n n o o R m m ' 0 = 0 0 o m m y ' ° 4 n ~ s Q. S 6' m 8 3 Ei _ o. m > ' 8 S a m m n m y cf S. B? m m o& y D - n » y o u=n ° w y= a = u a o C7 " m m n m 3 m t'~ m£ n m 3 - D k- . i - ' n y °1 o. ° > - c = o. o ~ ° o m ° m ~ 8 m e a - F ° _ a ' m- m m = o a $ m o - _ o w m ~ d d 8- ~ o d - a - = F° m - a' n u°-, - w y m m y c s m c m a ° d m 4 = y, S m m' S m ~p 3 a 3 N n ~ v a g= x c ~ m w p m - 8 y m' o o ~ m a m a m~ _ m ~ , - c m m 8 m ' m <m R - 5. o V, o ~ v. ° a m ro 0 F - 8 = S: = ° ma yy m D y m 8 'm F ? n m= F ? a 'm F F A ~ ni 4 M m y o _ , ~ ~ m m m y" y y v m ~ m Q °1 ~ = w - o m' m d fD 2 3 o 'o m = ~ = ~ ~ < m o d m - ~c H N m ~ n y y m ai F m s s° m m m m f m m o= c3 a c < z 2 n ~ ~ o rs Fyny D d n m an y no- 'z °:a m a ni a n m a ui n m Fo 8 gn. F m 8 y m n u, Q H = _ -0 d ~ ? np1 ? y nc o c n °1 a g ? ' a'y o m F m m O°-' a w o m m Oy 3 o n F m ~y m o a - m t° ~ j 8 E » 8 G m n; E F 3 3 o u°, ° x m y m Q a m m m ? = y n n m a m ° m ° c = m m c' ti m o n F ~ c' m n ~ w i + uu 0 c N 4 ~ c 'w a a y m a. ~ a u, ' g i u~ ? mon. m nm 2 y a ~.m oa o ET m as 3 a m n < o = S m < f me 8 a m ~ ~0 n, y c g~-oy bi ~0 H ao° 3" p8 o m F u7 ~'o v A 1 m 'o m v 'c n n ~ i c m c ° w m oFi m ^ `5°. o , 3 8 F , 3 . = d ~ nFi _ ~ m n 'a ~ _ m m m w m m m n y c mi y n _ i o 'a ~ : 'o c n m ma ~ o ~ o- ? v' c 3 H 3 n m 3 `z n o " E3 ru F m m n F o ° m - y m - = m o- w n S. d ~ B-9 - 5 o a n a m v d y F F n n + 0 ° o' ' c g m » y d =w c m a _ c 2, m m s 2 L y' y~ ~ m n v m m m = v~ g d a m a x m N' m u H m d m ^ a a c y m n n m c c 3 E T m f° w D y F m m o y o m m `D N sd n 8o ~d s ° o m a d a~ F d g~ cn y ~g H d 3. a dj i m gd'? y D o m d~ m f d PD o a n m v f F c } a$ m y ° m .z m n y m f m m o m p1 . y -o_ p 75 3 o m m 8 -5 5. m m m m a ° o 3 8 £ v O o m' F m- m o 3 m m ° m d m n3i o ~ vi n m g n O g °a ° m o o 3 » 3 m ' ° m , _a T m o 8 m'_ c 3 ° o 3 F 'm ' ° m " m a = . ~ ' = c . m oV o 3 H c < w m = a 8 . rn 8 o ~ m m m o m m o °m o m ° m m Z n m o- c n' m n m m m ° v an d o - 3. n ° m' 3 = - 6 T nFi = o 8 8 a ` m - c 8 a g g m m o m o. ~ D o' Y m m . ~ n m ~ ? v ? ~ o o < m u lo C; . m 0 0 - O O O O O O O X 0 0 0 0 0 O O O O O O O O ~ O O 5 N y Q O O O O _ O y- O O O O O ` 0 0 0 0 0 + O O O O O O O O O O O O ` O O O 5 y {i O 0 0 O p O o S ` 0 0 O O o O O O O O O O O 5 ` v O O o 5 p 0 0 O O - O O O O ~ 0 0 0 0 0 O O O O O O O O O O O O ~ + O O O S ~ O O 0 0 ~ O O O p O O O ` 0 0 0 0 0 O O O O O O O O O O O O ~ O O O 5 ~ O O 0 0 ~ O O O O O O O ~ O O O O O O O O O o ~ ` _ O ~ ` ~ ;~Y O O O O O O ` O O O O O O O O ~ ` p ~ O 0 0 + O O O O O O ~ ` 0 0 O O O O O O O O O O ~ O p S ` 0 0 0 ~ 0 0 0 0 0 o p ° p ~ p C c w 0 0 0 0 0 0 ~ o 0 0 0 0 0 0 0 0 0 0 0 . o o ° ~ o 0 0 0 0 0 0 ~ o o ~ o N 0 4F 0 0 - O O O O O r 0 0 0 0 0 O O O O O O O O O O ~ ` O O ~ O 0 0 0 0 0 0 0 ~ 0 0 0 0 0 0 0 0 0 0 0 0 ~ o o ~ w c 0 0 0 0 a: 0 0 0 0 0 0 0 ~ o 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 ~ 0 0 0 ~ o 0 0 0 0 rj 0 0 0 0 0 0 S o o ~ - rn +,w 0 0 0 0 0 0 0 0 ~j ` 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 ~ - 0 0 0 ~ o 0 0 0 0 0 0 0 5 ` 0 0 0 0 0 0 0 0 0 0 0 0 0 0 ~ 0 0 0 0 0 D o c o o ~ 0 0 0 0 0 0 0 0 0 0 0 ~ o o ~ o + 0 0 0 0 ~ o 0 0 0 0 0 0 ~ o O C ~ O O O x 0 0 0 0 0 O O O ~ ` O p 5 ` N O O O O C O O O O O O ` 0 0 0 0 O O O O O O O O O O O ~ O O O ~ ` W 0 0 O O c O O O o ~ 0 0 0 O O O O O O ~ O O O ~ ? • • • r V r Of ~ r A ~ i N ~ T ~ T G7 _ O = ate O a O O ~a O 7] T (A - f/1 O 8 ~gy fn (/1 O ddogy a, w -0 T d F p y n 3: m o - 8 o O o y w ? 12 N C N 3 N lD c ° N lD y d O F !L j g m z 6< lU O ~S S O y 6 m N 3 'm 3 N 3 N v z 0 N 0 N O A + N N O) = A O ut + W W m O O -ci m - r N N Y' P V (~D s m c ? p = N N - r N F V m m m O N 7 a. Z Z ° ' r N N o V N O w A U1 N N n N o, - N a A o. ~ a ~ m n m = s n n n = ~ » m m ~ " % H 3 b'i a a _ = o ~ ue \ fee ° H °1 ~ 3 o 9 o 0 cn 0 0 o \ y » m o, m 3, 0 ° 0 o <.n o e ° c a o 0 O 0 o O G ~ _ m m m % m y g m w m m= m r ~ 8 ° ° y » m m °m =o ~ > > m y = 9 o _ 0 ' = 0 8 c ° 0 0 F x S 8 o s _ o s _ o 8 s d m y m m S: o ~ y ~ , ° g ~ m m z n o s m ~o m mI ` F 8 y m m c 3 m m= 88 _ = s _ = _ = ~ ° ~ - `c' a ci _ = n ~s„ o m o m g D g D g g ; m" ° g g ai n 5' o a w y ° chi o 3 m m m a m m m m a o n u~ d = m n m s' m ' m fii 3 m m m m= n 27 j n 0 a m 3 nm _ 3< a d s = m O R 3 m m y m m f y m ° 3; m y n o 0 n 0 y = F ~0 w o - ~ u ° . n ET n 0 n 0 n o v cFi T o n ~ ` ° v m ° i ° ? A N " i C'1 O ~G N y o fii n y S O- m y fD V N N H w cmo N o ? S S = r N 3 o = S S lD y .8 N ' d g N O m m 'z n - F m m m a v ' m - 0 3>> F o o m m n> L m w > _ > > m R! m x m _ m y o 8 H m m 3 m m fo w p, 5i n y m y , = y m m ai Q m m 3 m fy~ m s a g m nFi dm- mul v m s'° _ x m g w s F N a. ~ F d n F F o = m o m D D° d 2 N y F y F y f o s o 3w o- m N o F_ m m o° o °c ? 'n m u, m " w 3 3 n a _ 3 y m _ F m ° m `n 0 _ 0 _ 0 = o b' ° o _ o - o o s, n= v m d H w m - y ea m ° ` ' _ y =~mO° a y e _ ~ ~ 8 8 8 8 ~d ~ s s s s g yd~ i o d b'i m m _ mm w y m m °n d 'S m ° m m c c c c m o c « c m w m < m m y m _ s F m 5 m F < y m m y ° m S S 3 a F m y °c y °c y °c ° `5. o v m 3 F y oc w l oc y ' c o n = m d y f S' F n S'i o- w m ° °1 , y P m m m °i a P m m m m d m o x, ° o n m m m c$i 3 n y i = 'o fO v = m m ~lr u m= v e yy m o, m m.. m F ^ p F m ° y m m H y PD 21 o m a _ o m m m S'i ? ~ n ~ 3 3°'~ m= g - ~ ~ ~ m d m m ~ g y m °i m m m cFi b' g~ ~n - y~~ F d } H 6i 3 m m g = m uFi c`OO ~ in ~ w y R uFi m ~ o ~ ~ m 3 ii ~ E r g ~ d N ~ N ~ ~ H ~ m FD tmii A ~ d G N o U1 ° o y d _ ~ ' ~ \ A = d d _T ~ ~ a i m AV y ~ °i m ° ° fD } m 7 m 4 4 m f tU O a » F = m j o j o d ? 6 O g w a ° nn O ~ n o , o \ g c m m o o ° 119 f~ = g - m o oo - o - o s E N oo - s - o y ~ a 3 m x H O m F m o y a s m m m m i n 3 0 3 ~m m = y m ~ ~ m~ a, m ~ 3 g~~y - m a m o o m ° so o ~ y ~ m m- m " c ~ ~ uDi m v a y $ n o n » y ° w _ ; 91 N 3. 3 , o m o = o f° = m 3 m D ~ m s L 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 o y 7 o _ Q, o o a. o 0 0 0 - c - o 0 0 0 0 0 0 o o o D o c - o o o o y - O O O - O r O O o - O p p 0 ..F O O O O O C 0 0 0 O O p 0 0 0 O p p p O ` - _ N 0 0 O O r o O O O O O O - p O O O O -w O O O O O O O - p p 0 O r 'J ~ O ~ ` -w 1 .w N O O O O 1 p O o - O O p 0 J O 0 0 p 0 -w O O O O O O O O ~ ~ O ~ LL M N O O _ J O O O O O O O O ryl O O O O O O 0 0 0 0 + O O O - 0 0 0 O O ~ J O ~ _ - - O O O O O O O O O X 0 0 0 O O O 0 0 ~ S o 0 o O p ~ » 0 0 ~ O O O O r 0 0 O O O - O O O 0 0 0 O p 0 0 0 O O O O O O O 0 0 0 0 0 0 0 O O Q 0 0 0 O p 0 0 0 O O O O O O O O O O O O O O O O O O O O p O O O r 0 O O O O O O .a O O O O 0 0 0 O O O O O O p N O ` O (p O O - N O O O O r 0 0 - O O O O O = O O O O O 5 O = - 0 0 0 O o 0 0 0 0 0 0 0 O 0 0 0 O 0 0 0 0 0 0 0 0 0 A w Q 0 G K -.mo o 0 0 O + o 0 0 0 0 0 0 0 0 0 0 - 0 0 0 0 0 0 0 0 0 0 o .a. o o 0 5 N = _ c o o o o o r o 0 0 0 0 0 0 0 0 - o o o o o o o o o o o o o p rn o ~ ~ .r - o o o o o 0 0 0 0 o p ~ O 5 O ft. N = 0 0 p - - 0 0 0 O O O O O O O O O O O O O O O O r O ~ O p W 5 O N _ 4Y O O o - 0 0 0 O > 0 0 0 0 0 0 0 ~ O O O O C 0 0 O O p O O _ - O w O O O O O 0 0 0 O O 0 0 - O O O O 0 0 Si O O O O O O r 5 0 0 r + 0 0 0 O O O O O O O O 0 0 + O O O r r - - O O O O O O O O O p O O O O O 0 0 0 0 0 0 0 N O F- = N O O + O O O -i 0 0 O O O O O O 0 0 0 0 + O O O O O O O - O O O O C -r O S + O N O O O O O O O O O O + O O O O O O O r O O O O O O O O + O O O O C 'A • • • T N T N N T A N N N N T O T T QO m m m o y n' :E D o g ~ti m m mC n D~ N< ° ro ' ~m oN < - to ' 0 S! ° OO OO m f ' n m y m ~ m m °1 m m 3 0 o » O = „ 3 ' m 3 I o ° E m o ~T m a n ~ m F ~ o f ~ £ o 8 °o 8.1 ° _m= o= m ° = o O D m o 0 F = a = a. m cn O N V1 o 3 - N e o cNn ° ° O m 'rs m 0 m= $ m y$ 3 ? H 3 % $ o ° N m ° 3 O d 3 nmi N F A Z 2 m rn v g N N C 3 o• O o I o O ° m ° ^ _ o j F m I m m f m m = O ? = rn 3 3 Q F OT 5= a o 0 0 ° o 2 m -`n m o H ° = 0 0 Ce 3 o x 00 o m > D m 3 c m j m °1 n 3 m m m y T ° o ' ° o o + 3 m S -m " y `e . y m m 3 m m o - w F 1 m F S m , S m ° F c g S y _ 3 m o n m N o = m = m w ? _ m y o o ° N a 0 3 = a H 3' 3 . F m= m c c c °i m c + A - 0 c rs . m _ • m - o F F w w ? w ? rn c w n c 3 F m 3 3 o g c o N F N m m cFi m cFi m m 3 m 3 m 7, c • $ 'm" $ ~ ° $ m o m , c o y m c m m n u-I o - m m v7 m ° = m m m n o v nFi m 2 'o A n 3 ° m m o m m g = m F ro H e o o m n . g s yc g = in o m rs a m y. D =m ° n ayc m m F $ m 3 ~ o m m Q _ m m m F o d a m o m F m m W = m c vi < m m ~ `n 0 ° m " m 0 q o m o o ff a ~ 3 y y o m ~ m m c = g > ? D w o d S. c ° o m m ~ m p1 N c m n g °c y o m m m= y _ ~ H y ' 3$ °c N ° m H O o g ~ a r G _ ~ ' 3 o a a b' _ o ~ g y ~ y cc' d o °n ? ~ y$ ? ? vo, z. cb ' 3 3 % m w In 3 n ° c o m f m S'i Fo' m_, S~ $ m ~ o - ? _ c~' = a m m ° ° m m ~ m _ ma - ' m m 3 v m c $ m ? m n y o n y F nl rn m y S g - rn m rn 3 ~ m m ' ~D 3 0 n ~ - v g 3 3 3 m m m m s c _ ' n $ c w ~ o ~ _ o - - o c c°i $ m ? o o °i o m i ° m o Io y o a $ F Q~ I°'il c 3 o " m m y rs m ' f m m' m o+ 3 ° _ = = 3 m H : _ on $ g m '0 F m 3 $ x ' ' _ to o ° o 2< S O m N ? N p1 3 ~1 f0 s = A d ~ o F m w mw t~ ° p d m y N 3 o O S O m ^ w d d N = N F < m m ~ - o O d d m O m c y o ~ v -O m a n F Aso m ^ v o in m = m __"s F w o o d m ~ m m ' m m w m p c~ rn m S A m m ° a = F ~ c nm ~ " n m ' m' ~ ~ ,y m m-"'c y a ' w OO m ? o m rs m yy m o m y o' = o m c o m m c ° o S „ m r o y a ~ m `O E'r 3 m m g y o a R. m 2S , y 3 -0 a sca = m g n - y y° a n m n hni u a F3 m i3 H < m F 0 T ° ° O ~O oFi o a 9 d o- 3 0 ° m to o F m o ca a oFi~ - y o o ? ~ M m o cd o 5 m m c as w 0 c 0 ~ m ~ m° o m m y m o f ° w o o $ f ~ 8 c S c m m n o 3 m ~ vi* m "d m w m F c ~ w o n ~ n o m no o y r 0 m F a u1 3 m D y o 3 eL. o n F ma 5 m 52 m ^ n d m m m m o y m m n °o ~ n a 3 F o G m u Inc 7c a ° n o o m d m N 3 3 , m w fo m m ' o ' m 3 m o a T ' m ¢ F a y o a m c o N F D N a m y m o - y = m r' o a m v° m m y" v `~y' o n a m a ° A m m x m m c m - a, _ m > > o m m = n 3 _ m 0 0 0 0 0 0 0 0 0 0 o p O p p o 0 o p O o o O o O p o 0 0 0 0 0 0 ~ 0 0 0 ~ o 0 0 0 ~ o 0 o y c o - 0 0 0 0 0 G ` 0 + o p p p o 0 o O p a o 0 0 0 o ` ` O O_ O c~ ` _ O O > 0 0 0 - O O O O O 0 0 0 0 + o o 5 n ' ew o S O o o _ . S _ O A O O O O + O O 5 O O > 0 0 0 O O O O O O O O O O O + O O O O - ~ O O O - - 5 ` _ p Vii 0 0 O ~ - 0 0 0 O + O O O O O O O O 5 - 5 0 0 0 - - 5 - ~ O O - 1- H O O ~ - O - - - - - - . . . . . . O O O C O ` ` ` p ~O O O O O O O ` > O O O O O + O 0 0 0 0 p 0 O O O O O 0 0 O O O O O ` O O O ` S - r O O O ~ - O O O O O O O M O O O 5 O 5 o ~ _ `O O O O O O O O O ` 5 O O 0 0 O O O O 0 0 0 0 0 0 0 0 0 O O O O O O O O O ~ 0 0 G 5 O O O 5 O O ~ S 0 0 0 0 0 0 ~ o 0 0 0 0 0 0 0 ° 0 0 0 0 0 ` ` 0 0 0 ~ o o ~ p ° o o O 5 ` C o 5 ` 0 o N 0 0 0 O +4 O O S O O + 0 0 0 O O O O O O O O O o + O + O O ,yy O O ~ ~ ~ -i O G O O O ~ 5 ` - + O O 0 0 0 0 0 0 0 0 G o 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 G ~ o o G o 0 0 0 5 v 0 o w c 0 0 0 0 o o G ~ o o o 0 0 0 0 0 0 0 0 0 0 0 0 o + o o o o ~ , ~ o ~ o 0 0 - ~j c o p 0 00 0 o o '~c ~ - o - o 0 0 0 0 o .a o ~ ,Y: s `G o o c - - ~ _ o J O O O O O S O O > 0 0 > 0 0 0 0 0 O O +T O .a O O O S _ S c O O O ~ - - O p W O 0 0 0 O O 5 O O ~ -y Y l - O O C O O w O O 5 ~ O O O 5 0 ~ O. o. O o - ' O. O, o. o, ~ O O O J± O O o I 0 0 ~ - O O O O S ` + O + O 0 0 0 O 0 0 0 0 0 0 O O O O O O O O O O O O 5 ` O O 5 0 0 + O 5 ` ` < O O ~ vi O O + 0 0 0 0 - 0 0 0 0 0 O O O - O O O O > O O 5 r 0 55 0 0 0 - ~ 5 1 p N O O 0 0 O O S ` i p O + 0 0 0 0 O ~ 0 0 O O O O O ~ O O -F O O 0 0 C , 5 ` 0 0 G r • C - O 0 0 - O ` x- O 0 0 O MT O O + O O 5 j`*. O , S O O O + 5 O ~ • • C A T W T N A O two T r Owl (Jwi T W tTJ N W T O m~ o o ° ctnvx o- y m a o• ^ ornx o m 3 i' m 0zzx o o m . a m 0 G7 o < T mx Flo cm a G orncn 3 C c~- < vi N N C <a [n D °c w T c m ° ' ° c o m n~i n _ Q c '2 m m m O y m m H o 0 3 'o ° w c Z m m c y o o ,p ? < m m o 3 n° r o N o a m 3 m y c+ c o g m °c ° m m m 3 n o + o _ g m m m c~ N m s m = o fD m ~ m o H 0 ~ 3 H c 3 H c 0 0 T m A~ < ? m ~ ' 3 0 ~ ~ 3 $ = 3 ° = 0 m m 3 n ce e ~n °Ni o N o u, ~ cn n e ° m 3 3 w m m m H m m D m = 3 N '0 ~ m O n ~ w 3 3 3 m° c 3 o = m m n o cn nv cn " cn O u+ ~ ' o V~ D ~ m O c m- O m o x O a, m- $ an ° a d ~ o ~ ~ ~a ? ~ 5r j m _ m cs m Q y y ~ m m m a, <u m m m' Z ~ w 2 O O m ° fD 8 'm ~ m O O 0 ° m 3 ° IP ° A 3 x 3 3 3 °1 3 3 O m m O [ m m [n m o _ m < ^ ~ e c o- v 3 F 3 m° 3 m m m m ° ' F m m c ,c c .0.. m £ - ' w o- o 0 m < m yy D ° . N v m ° w m c _ ° - o o o a - 3 _ m 3 o - 3 m < S m m fO c $ < g m °p w-o w D < o_ ° m o - Z `m-^. c m m m u G o H m < ' 3 - m g m w v m m g c m ° o m ur ~ or g F g ° m g 12. w m w ° m -e < m v m $ o m n' 'o v _ a v A ° m _ ° 3 ' m i m m 6i m m 6i m 'm m : m o s - - m ~ H m = a m = m z. m H Er E m F < o T tn d a, m m H m m ~o' a ° D 3 Om w o °o F - m Q °1 I _ 0 m ~ < fD v m m o < ° v L. mi 3 ^ 6 $ S a g y - o S n~ m a o m 'o 8 m y m m m ~ ' ~ ° ° g O m \ ' 4° o 3 ° m m m N m N ~ ^ ~ w $ a < £ m $ n$i s F s R d 0 o - 1on m c 3 m 3 m o' d umi d y go m n 3 ? ° n m o g ^ g 3 m 8 3 m 3 Q. vm m m 52 m m < m o a m d o ? o w m } o h o m m o m o D 3 3 y m m o w $ ie' w 3 ° m m m w m m m - m, o m 3 w o ° _ 30 m s o m = < m y y F H ° ° > m 3 y m o 'o ? o' m 3 y _ m p o m m g m 4 m m 5 m 4 w w D y m y m m N 3 m m' m m w y < - u s m ? y m F F m» _ y a_ c ~c A y D o m° c m p1 Zn x m 3 °1 £o g ° g m 8 ° so m < ° o ^ 8 o DD D D D Fn 3 $ o m m $ - 3 m c n m x oo H m y o D o' c F N m 3 o o f°o s ' m ° ` m Q 5. m 3 m ' d m F a O f° r3 3 a v H a m o cn A ° p1 m x ° 3 = v ° m 3 m " g c o o ° 8 5= m° 8 o ? y d n o ni o m ' m < - m m' H c m m n F m m o < s y w m m N H n n o w ° ' o 3 $ ? 3 m v ° 3 ~ £ m y m 3 8 3 y y m o p1 m m o > o ° + F o u. o ° o H w ° Yn- w m c 3 i u u + o ` m o. m o n m m $_c g 8 m y _ c c $ v n N Er u m m - m y p1 ' m 0 'm m 'm m c n m - m m' m m m m ° N m 3o m m' ti ° m o m ° o+ c 3 'm w m m m o " ' m v ~ $ 8 8 o 8 ? w m O r a 'm ~ m w ti < g m ~ i H m ' y <m v a m o~ m m 'c 4 o m ~ < of ? a g m ~ g g m g H m £ H m £ ~ y m ~ m m n y F m 8 x ~ 8 ? ? ~ vo m ~ y ° ^ ~ i o i u m m y 8 m n y ° m % a s o o o m m n f w so m 3 2L 3~ m ~D° 3 ? ~ a m n _ m m o ~i 3 o m 3 a c ° -n m o m F m n o 'm c m g m a v y CD o w °1 $ 5 m m ? T n ' 5 Q N o $ y ° m m c ~ o £ F $ m H (n o c $ o° vm m oci v m O m (n c a - - a m o y' Fr m~ _ m o T y o' m ~ m f F ~ 3 ~ o c m ° , v y o m d o gs y o m = D G 3 n o- o x _ m o m' m O O 7i~ri. Y. 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PD V QD On CO 00 Cb A A A A A A A A A a a -o -o PO (D L,o 0o CO ~O (O CO ~O ~ o o o o o o o u, <n ~ cn cn cn cn cn co co v v v v v v v 0 0 0 0 0 0 o D N CD N 3 CD m d O O A O O w O w A w O O O - O w Q N A A 0 0 U N A A 0 0 N A A O O J W N W N O N O 00 N w A N O O N A A w O O N w A N N w A w N W N A w O A South Deschutes County Local Wetland Inventory Report • APPENDIX G: ORWAP SUMMARY SCORES - TABLES G1 TO G4 0 ESA Adolfson June 2011 Appendix G E • • 0 0 N y CO b Q C O V C a W 0. 3 O w° C O C~ i a~ L ,R r~ V a H c O + Q N ~ °6 a) m cn CD cu N U) 06 c O D of c N .9 o can' c O N : `O L O_ o a D N otf Co O E z O 6 rn 2 o E N c `6 N M es U) c O d 0 X W ca 2 c o~ 0 o _ .0+ N a) > 0 7 ¢ o 11- = N LL O = E O N ¢ cu = c LL w O E o c c z a = (D Q O of ° ¢ o _ L o a - = N Z L E E N 06 O m of m co ° - U = o M _ a ° ~ N O > c d N z v can m z v o ? 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U y a~ a~ a 3 W 0 C 0 C a w C 0 BCD W W O t~ R U' e~ E4 13 IL c2 X X X X x x X , „ X J 0 ,n Q X X X X X X X CL LO m X X X X X X X X , LO d z m N , X , , , , , , X X X , . . X X d V L d a LL m C . . . . . . . X X X X X x x w a c m c p X X Q c U. = LL X X X X X m w 3 > z w . , , , , , , , X X X X X X _ LO rn V OC) ~ . , , , , , , , X X X X N N v, X c U) o X X X X X ri i x o c y nl m .fir R N C 'a V c G> _ R7 O ta c:.~ = •-oa a 4) c W N M (D Lo CO 1- co 17, D N M Ch O O O Cl> t0 CD GO CO co O aD 00 OO O) M 0 ~ N W E • 0 South Deschutes Coun Local Wetland Inventory Report • APPENDIX H: OVERVIEW OF GROUNDWATER QUALITY 0 ESA Adolfson June 2011 Appendix H • C7 South Deschutes County Local Wetland Inventory Report • ESA Adolfson performed a brief analysis of groundwater issues in South Deschutes County based upon existing information. In general, the water quality in the shallow aquifer of Deschutes County is threatened by nitrate contamination from widespread use of septic systems. The effluent from these conventional septic wastewater systems has been shown to contribute to nitrate levels in the upper 100 feet of the shallow aquifer. The contaminated groundwater not only affects the local water supply wells, it also impacts water quality of the Deschutes and Little Deschutes Rivers in areas where the groundwater discharges into the river. Groundwater in this region occurs in most of the fractured bedrock as well as the alluvial deposits, which consist of shallow fine to coarse sand, fine to coarse gravel and cinder fluvial deposits. Most wells in the study area are screened in these fluvial deposits. Less permeable silts and clays comprise much of the lacustrine deposits but overall the shallow aquifer is considered unconfined. Many of these soils are derived from pumice deposits which are relatively low in organic matter and have high porosity. The soils in the region are highly permeable with no intervening layer protecting the aquifer. The high permeability allows for swift downward migration of water from precipitation and septic effluent. The water table generally ranges in depth from less than two feet to about thirty feet below ground surface. Groundwater velocities are generally low and oxic (oxygen rich or at least containing oxygen) near the water table surface (Rich, 2005). However, at depths ranging from near is zero to more than fifty feet below the water table, groundwater becomes suboxic (low in oxygen) where conditions are conducive to denitrification. Denitrification is the microbially facilitated geochemical process where nitrates are reduced or removed through a process which results in the production of harmless molecular nitrogen (Nz) through a series of intermediate gaseous nitrogen products. Denitrification helps limit nitrate contamination in the groundwater, but requires anaerobic (without oxygen) conditions; therefore, any oxic portions of an aquifer remain vulnerable to nitrate contamination. • In a study conducted by the USGS, an attempt was made to better understand the relationship of oxic and suboxic conditions in the aquifer near La Pine Oregon (USGS, 2007). While the distribution of oxic and suboxic conditions varies widely throughout the region, the findings of the La Pine study determined that oxic groundwater tended to be present near the outside edge of a river meander bend (edge closest to the margin of the valley floor) (USGS, 2007). However, not all outside edges were oxic. In areas where the width of the riparian environment adjacent to an outside edge was relatively narrow, oxic groundwater conditions were found. Groundwater samples taken from the center of riparian zones were always suboxic (USGS, 2007). Therefore, the relatively narrow wetlands identified in the project area such as Wetlands 15, 14, 72, and 52 or the wetlands located near the outside edge of a river meander bend such as Wetlands 10, 29a- c combined with 28 a-b and 27a-c, and 35 are likely the last defenses against nitrate contributions to the Deschutes and Little Deschutes rivers. The ORWAP scores for these examples vary; however as noted above, the scores do not account for overall size of the wetland and the underlying groundwater conditions. A more thorough examination in ESA Adolfson Page H-1 June 201 South Deschutes County Local Wetland Inventory Report • light of the findings of the USGS study may offer more guidance in interpreting the value scores of the identified wetlands and making determinations for Goal 6 Water Quality Resources. LITERATURE CITATIONS Rich, Barbara et. al., in collaboration with Deschutes County Environmental Health Division, Oregon Department of Environmental Quality and US Geological Survey. Undated. La Pine National Decentralized Wastewater Treatment Demonstration Project, 1999 - 2005. U.S. Geological Survey (USGS). 2007. Ground Water Redox Zonation near La Pine, Oregon: Relation to River Position within the Aquifer-Riparian Zone Continuum, Scientific Investigations Report 2007-5239, • Page H-2 ESA Adolfson June 2011 South Deschutes County Local Wetland Inventory Report • ATTACHMENT 1: SOUTH DESCHUTES COUNTY LOCAL WETLAND INVENTORY MAPS ESA Adol(son June 2011 Attachment 1 • 0 ~0~;~3o I I I rr -t- 1 9qg~--I-1-1-N, a a s -r -1 -i o I I I I I C131V`dNN~I a-iWdNv I I I I i~ s I I M °°oN= I I I T o o v -1- -I--,- --Its -~T`~--i --T-I- - 1 N 11 I I 1 I AME I - I_ I_ I~ I ° a x o I 1 I_ I_ I I_I I_ Ilei 2. a < ID m ° m Q ° _ •1-1-1 1-~ ~~~--1 1--1 NNA ED I I I ti l I; I I I I I _ I_ I I I_ I~ ~n-cnm°" ° ~ II 3 N ° 00 off 1-1- 1-71 m - -1 -I 1e~~ -1 11 Nca~,, 03 I I /I I I I' I `'T1 I I I ~I I- I I I I tiyy I I gU ~N~m'0 IV m D a m u, =a C V7 1 1 1- 1 1 1-T1 -l 11 'cy i K O ° s m I I I I lae~~is~ I I I I I I FS 414'0 I co mI I I I I~ .l- <<s I m ° ° < v TI O 1- -1- --~~--1--1-,- 1 -1 o a s m I I I~ I A I I I I I (I 22 I I ~I ti9 I C9 I L O ° 0- < c 3 0 0 N - --I- -TI ^ Z C--C9 m m v v° l a I~11 I "sue / I I I I I l I U) c. 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