Loading...
HomeMy WebLinkAboutChenega Bay Hydroelectric Wetlands Study - Dec 2011 - REF Grant 7030010environmental research & services 12 December 2011 TO: Robin Reich, Solstice Alaska FROM: Wendy Davis, ABR Inc. RE: Chenega Bay Preliminary Jurisdictional Determination and Functional Assessment ABR, Inc. was contracted by Solstice Alaska on behalf of Hatch to perform a preliminary wetlands determination in support of a Section 404 Wetlands Permit sought for a small scale hydroelectric project. The proposed project is located adjacent to Chenega Creek in the village of Chenega Bay, Prince William Sound, Alaska (Figure 1). Wetlands in the area were previously mapped and described by HDR, Inc. (HDR Inc. 2009) and National Wetland Inventory (NWI) maps also exist for the area. The NWI maps show extensive saturated emergent and scrub wetlands within the study area, but the maps are not at a fine enough scale for the purposes of a 404 permit application. HDR, Inc. performed more detailed mapping, but the effort was office based; thus, a field survey was necessary to verify and finalize the map. The project comprises 13.5 acres and includes the lower reaches of Chenega Creek and an access road to an existing dam upstream (Figure 2). The legal description is Township 1 S, Range 8E, Sections 23 and 26, Seward Meridian, Seward quadrangle A-3, centered on Latitude/Longitude (WGS84) 60.070 °N, 148.017 °W (Figure 1). The study area generally slopes steeply toward the coastline and is composed of mature Sitka spruce/hemlock forests and organic fen wetland complexes common throughout the Prince William Sound area. Routine wetland determinations were made at 9 locations throughout the study area on October 5 and 6, 2011. The determinations were performed using the Army Corps of Engineers three parameter approach (USACE 1987, 2007a) (Appendix A). This method uses observations of vegetation, hydrology, and hydric soil indicators to determine the wetland status of an area. To be classified as a wetland, a site must be dominated by wetland plants (hydrophytes), have wet (hydric) soils, and have wetland hydrology (saturation of sufficient duration). Indicator status of dominant plants was determined using the National List of Plant Species that Occur in Wetlands (Reed 1988) Classification of upland/wetland communities followed guidelines outlined in the Classification of Wetlands and Deepwater Habitats of the United States (Cowardin et al. 1979). Taxonomic nomenclature followed Hulten (1968) with the exception of willows (Salix spp.), which followed Viereck and Little (2007). Soil color was described using Munsell soil color charts (2009). Photos of the vegetation and soils were taken at each site (Appendix B). Verifications were completed at 3 plots, which are rapid on -site assessments of areas already described with a full wetland determination (Appendix A). Corporate Headquarters Anchorage, Alaska Pacific Northwest Northeastern U.S. P.O. Box 80410 P.O. Box 240268 P.O. Box 249 15 Bank Street, Suite B Fairbanks, AK 99708 Anchorage, AK 99524 Forest Grove, OR 97116 Greenfield, MA 01301 907.455.6777 907.344.6777 503.359.7525 413.774.5515 907.455.6781 (fax) 907.770.1443 (fax) 503.359.8875 (fax) 413.774.5514 (fax) e-mail: info@abrinc.com website: www.abrinc.com Page 12 Mapping was completed by digitizing polygon boundaries on -screen using high resolution digital orthophotography obtained 6/28/2005 (provided by Hatch) and ArcGIS 10.0 software. Polygons were digitized based on results of field data and photo interpretation of vegetation communities. Polygons were coded using the National Wetland Inventory (NWI) system based on Cowardin et al. (1979). Acreages were calculated and are summarized in Table 1. A functional assessment for the wetlands and waters mapped in the study area was conducted using a rapid assessment procedure based on the Literature Review and Evaluation Rationale of the Wetland Evaluation Technique (Adamus et al. 1991), the Rapid Procedure for Assessing Wetland Functional Capacity (Magee 1998), and recommendations summarized in a recent Regulatory Guidance Letter (RGL 09-01) (USACE 2009). The USACE guidance includes recommendations and a dataform for objectively evaluating wetland functions and values, using hydrogeomorphic (HGM) principles (Appendix Q. The procedure facilitates a rapid assessment of the many landscape functions that wetlands provide for overall ecosystem maintenance, including hydrology, water quality, primary productivity, wildlife and fisheries habitat, and providing for public needs such as subsistence. The functions performed by wetlands and waters in the project area were qualitatively ranked depending on the extent to which various wetland functions were occurring and/or site characteristics were present. The relative rankings are used to determine compensation ratios should wetland mitigation be required. Both waters of the U.S. and wetlands occur in the study area, comprising 5 NWI classes. Chenega Creek is a water of the U.S. and was classified as an Upper Perennial Stream (R3UBH, 0.48 acres) and connects directly to Traditional Navigable Waters (Sawmill Bay) (Figure 2, Table 1). The channel is a shallow permanently flooded feature with variable depths and gradients along the reach in question. The majority of wetlands within the study area boundaries are part of an interconnected series of hillside organic fens. The fens are all gently sloping features made up of a complex of 3 NWI types. Palustrine Seasonally Flooded/Saturated Emergent Meadow (PEMIE) and Palustrine Seasonally Flooded/Saturated Emergent-Needleleaf Evergreen Meadow (PEMI/SS4E) together account for 3.26 acres. These wetlands are characterized by a thick saturated moss peat layer. Common emergent plant species include Eriophorum angustifolium (narrow -leaf cotton -grass), Calamagrostis canadensis var. langsdorfii (bluejoint grass), Fauria crista-galli (deer cabbage), Erigeron pergrinus (wandering fleabane), Geum macrophyllum (large -leaf avens) and Lysichiton americanum (American skunk cabbage). PEMI/SS4E commonly support more dwarf and low shrub species including Harimanella stellariana (Alaska moss heath), Tsuga mertensiana (mountain hemlock) and Alnus sinuata (Sitka alder). Numerous small intermittent streams (R4SBC, 0.18 acres) flow through the organic fen communities and are often difficult to separate in mapping from the wetland complex. The intermittent streams are generally in the form of beaded streams that may be actively flowing or a series of stagnant pools. Pools of surface water within the hillside fen complexes may also support obligate aquatic plants such as Potamageton sp. (pondweed). One small area of Palustrine Saturated Needleleaf Evergreen Forest was identified near the Chenega Bay community power plant. The area is a small topographic depression at the headwaters of a small intermittent drainage connecting to Chenega Creek. The site does not meet the hydrophytic vegetation criteria because of the high cover of the overstory facultative upland tree species Picea sitchensis (Sitka spruce). The area was still classified as wetland, however, due to strong hydric soil and hydrology indicators and the presence of obligate emergent species such as Lysichiton americanum. ABR, Inc.—Chenega Bay Study Page 13 All of the waters and wetlands in the study area were assigned an overall functional category of III (moderate to low functioning). None are unique to the area and are in close proximity to existing local disturbance that surrounds the community of Chenega Bay. The highest value wetlands in the area are the Organic Fens (PEM1E, PEM1/SS4E and R4SBC) because of their importance in supporting hydrologic and water quality functions. The emergent fen plant communities also score relatively high with respect to plant species richness. The Upper Perennial Stream (R3UBH) was ranked high for fish habitat based on the presence or absence of spawning and rearing habitat; however, this ranking does not take into account physical barriers to fish traveling upstream. The ADF&G online database identifies Sockeye salmon presence (ADF&G 2011) well above the first anadromous fish barrier identified by HDR (HDR, Inc. 2009). The fish habitat scoring of high for Chenega Creek may be reduced, pending confirmation that anadromous fish are not present within the study area boundaries. The Saturated Forested (PFO4B) wetlands were very limited in extent and had the lowest relative functional performance scores across all categories. The southern edge of the study area is 0.3 river miles along Chenega Creek from the nearest section 10 TNW (Sawmill Bay) (USACE 2011). Chenega Creek is a permanently flooded waterway and is considered to be a relatively permanent water (RPW). The Intermittent Streams in the area should also be considered RPWs on the basis of having a surface water connection throughout most of the growing season and detectable flow, occurring seasonally for at least 2 consecutive weeks (USACE 2007b). The Intermittent Streams can be considered tributaries to Chenega Creek and connect directly at numerous locations along the lower reaches. On the basis of the hydrologic connection described above we suggest that all waters of the U.S. and wetlands mapped within the study area are jurisdictional. Uplands dominate the study area and include existing disturbances such as the placement of fill, steep slopes supporting mature Sitka spruce/hemlock forests and rarely, small convex features within the hillside organic fens where the underlying bedrock is close to the surface. The mature Sitka spruce/hemlock forests have 40-80% cover of Picea sitchensis and Tsuga heterophylla (western hemlock). Common understory shrubs include Vaccinium alaskaense (Alaska blueberry), Menziesia ferruginea (mock -azalea), and Rubus spectabilis (salmonberry). Forbs are also common and include Blechnum spicant (deer fern), Coptis asplenifolia (spleenwort-leaf goldthread) and Rubus pedatus (strawberry -leaf raspberry). My acreage estimates for Upland (fill) are conservative because the 2005 imagery used for the mapping does not include two new disturbances to the area since the photography was taken. These include a new gravel pad expansion to the north of the existing powerplant and brush clearing and excavation along the access road to the water tank. I do not believe any wetlands were disturbed in association with these two new disturbances. ABR, Inc.—Chenega Bay Study Page 14 References Cited Alaska Department of Fish and Game (ADF&G) 2011. ADF&G Fish Distribution Database: Interactive mapper. [Online] Available http://gis.sfadfg.state.ak.us/AWC_IMS/viewer.htm. October 2011. Adamus, P. R., L.T. Stockwell, E. J. Clairain, Jr., M. E. Morrow, L. P. Rozas, and R. D. Smith. 1991. Wetland Evaluation Technique (WET); Vol. 1: Literature Review and Evaluation Rationale. Technical Report WRP-DE-2. U. S. Army Corps of Engineers Waterways Experiment Station, Vicksburg, MS. Cowardin, L. M., V. Carter, F. C. Golet, and E. T. LaRoe. 1979. Classification of wetlands and deepwater habitats of the United States. U. S. Fish and Wildl. Serv., Office of Biol. Serv., Washington, DC. 103 PP. HDR, Inc. 2009. Chenega Bay Hydroelectric Feasibility Study: Reconnaissance Report. Report prepared for Chenega Corporation, Anchorage, AK. 29pp. + Appendices. Hult6n, E. 1968. Flora of Alaska and neighboring territories. Stanford Univ. Press, Stanford, CA. 1008 PP. Magee, D. W. and G. G. Hollands. 1998. A rapid procedure for assessing wetland functional capacity based on Hydrogeomorphic Classification. Report prepared for Association of State Wetland Managers. 177 pp. Municipality of Anchorage (MOA). 1996. Anchorage wetlands management plan. Department of Community Planning and Development, Municipality of Anchorage, Alaska. 220 pp. Munsell Soil Color Charts. 2009. Revised edition. Kollmorgen Instruments Corporation, Baltimore, MD. Reed, P. B., Jr. 1988. National list of plant species that occur in wetlands: national summary. U.S. Fish and Wildlife Service, Washington, D.C. Biological Report 88 (24). 244 pp. U.S. Army Corps of Engineers (USACE) Environmental Laboratory. 1987. Corps of Engineers Wetlands Delineation Manual. Technical Report Y-87-1, U.S. Army Engineer Waterway Experiment Station, Vicksburg, MS. 90 pp + appendices. U.S. Corps of Engineers (USACE). 2007a. Supplement to the Corps of Engineers Wetland Delineation Manual: Alaska Region Version 2.0. Wetlands Regulatory Assistance Program, U.S. Army Engineer Research and Development Center, Vicksburg, MS. 72 pp. + appendices. U.S. Corps of Engineers (USACE). 2007b. U.S. Army Corps of Engineers Jurisdictional Determination Form Instructional Guidebook USACE and Environmental Protection Agency. 60pp. U.S. Corps of Engineers (USACE). 2009. Alaska District Regulatory Guidance Letter on Implementation of the Federal Rule on Compensatory Mitigation. RGL ID No. 09-01. U.S. Army Corps of Engineers (USACE). 2011. USACE, Alaska District, Navigable Waters List. [Online] http://www.poa.usace.anny.mil/reg/NavWat.htm. October 2011. U.S. Environmental Protection Agency (EPA). 2011. The Anchorage Debit -Credit Method: A Procedure for Determining Development Debits and Compensatory Mitigation Credits for Aquatic Areas in Anchorage, Alaska. Revised Document, Heather Dean, April 2011. 33pp. + Appendices. Viereck, L. A., and E. L. Little. 2007. Alaska trees and shrubs. Agriculture Handbook No. 410. U.S. Dept. Agric., Washington, D.C. 265 pp. ABR, Inc.--Chenega Bay Study Table 1. Acreages of NWI wetland types found within the study area of the proposed small scale hydroelectric project on Chenega Creek, Chenega Bay, AK. NWI code Description Acres Waters of the U.S. R3UBH Upper Perennial Stream R4SBC Intermittent Stream Total Waters of the U.S. Wetlands PEM1E Palustrine Seasonally Flooded/Saturated Emergent Meadow PEM1/SS4E Palustrine Seasonally Flooded/Saturated Emergent-Needleleaf Evergreen Meadow PFO4B Palustrine Saturated Needleleaf Evergreen Forest Uplands U Us Total Area Upland Upland (Fill) Total Wetlands Total Water and Wetlands Total Uplands 0.48 0.18 0.66 0.35 2.91 0.15 3.41 4.07 8.00 1.39 9.39 13.46 ABR, Inc.—Chenega Bay Study 5 Table 2. Functional performance of wetlands and waters within the study area, Chenega Creek Hydroelectric project, Alaska. NWI wetland types are grouped into similar functional groupings. Wetland/ Water Upper Perennial Stream (R3UBH) Saturated Forested Wetland (PF04B) Organic Fensa, (PEM1E, PEMl/SS4B, R4SBCb) Overall Functional Category III III III Flood Flow Regulation High High High Sediment, Nutrient, & Toxicant Removal Low Low -Moderate High Erosion Control and Shoreline Stabilization N/A Moderate High Organic Matter Production & Export Low Low -Moderate High General Habitat Suitability Low Low Moderate Fish Habitat High N/A Low Native Plant Richness Low Low High Subsistence/ Recreational/ Educational Value High Low Low -Moderate Uniqueness & Special Status Low Low Low a Confined to hillside in study area. b These intermittent drainages are functionally part of the fen complexes and thus, cannot be evaluated separately even though they do not directly support some wetland functions. ABR, Inc.—Chenega Bay Study 1ursc rr run u•n r�nry . •._ - _ ii _ 1 y: R r. } s (AWe yr•�;. a i� r l iM1 4 .: Chenega C4VS r r' 7,Siif say _C t r ilw. .r (ri71� Ism 7V leer $ I ► Bak b�� • i '� S>ari ;,lean i � .� ��� � ` cM i. H �: V Figure 1. Chenega Bay w f{��%' Project Location Map, E s Approximate Scale 1.5 Kiiomeb 0.25 0.5 0.75 1 IVi9I@&� 1dA°d'W .- Evans Island, Alaska � Seward Quadran Ia A-3, Towns hi IS, 9 P ° Ranges 8E, Sections 23 and 26, Seward Meridian jr�,, - wrrprrr�mlGr: 1I 7� j 66ecem6e<20'1 ABR file: Chenega Bay_L-VSGS -111.rr•xd 1dA•9W Idfl°I1W t67°P ABR, Inc.—Chenega Bay Study 7 ABR, Inc.—Chenega Bay Study Appendix A. Wetland Determination Data and Verification Forms ABR, Inc.—Chenega Bay Study WETLAND DETERMINATION DATA FORM - Alaska Region Project/Site: CHENEGA HYDRO Borough/City: CHENEGA BAY Sampling Date: Applicant/Owner: HATCH/SOLSTICE Investigator(s): WAD, NMT Local relief (concave, convex, none): concave Sampling Point: Landform (hillside, terrace, hummocks etc.): Flat Slope: 0.0 % / 0.0 o Elevation: Subregion: Southeast Alaska Lat.: Long.: Soil Map Unit Name: NWI classification: PF04E Are climatic/hydrologic conditions on the site typical for this time of year? Yes U No U (If no, explain in Remarks.) Are Vegetation ❑ Soil ❑ , or Hydrology ❑ significantly disturbed? Are "Normal Circumstances" present? Yes OO No O Are Vegetation ❑ Soil ❑ , or Hydrology ❑ naturally problematic? (If needed, explain any answers in Remarks.) 05-Oct-11 CH 11-01 Datum: WGS84 SUMMARY OF FINDINGS - Attach site map showing sampling point locations, transects, important features Hydrophytic Vegetation Present? Yes O No Is the Sampled Area Hydric Soil Present? Yes No ❑ � within a Wetland? Yes * NO Wetland Hydrology Present? Yes No O Remarks: Very few forested sites in the area showed clear wetland soils and hydrology similar to this site. Although this area does not meet the hydrophytic vegetation criteria we have identified it as a forested wetland for the limited concave area that it occupies. VEGETATION Use scientific names of plants. List all species in the plot. Absolute Dominant Indicator Dominance Test worksheet: Tree Stratum % Cover Species? Status Number of Dominant Species 1 Picea sitchensis 80 d❑ FACU That are OBL, FACW, or FAC: 3 _ (A) 2 Tsuga heterophylla 15 ❑ FAC Total Number of Dominant 0 ❑ Species Across All Strata: 6 (B) p El Percent of dominant Species 4 0 ❑ That Are OBL, FACW, or FAC: 50.0% (A/B) 5 Prevalence Index worksheet: Total Cover: 95 Sapling/Shrub Stratum 50% of Total Cover: 47.5 20% of Total Cover: 19 Total % Cover of: Multiply by: Oplopanaxhorridus 20 91 FACU OBL species 30 x 1 = 30 1 2 Vaccinium ovalifolium 3 ❑ FAC FACW species 0 x 2= 0 3. Rubusspectabilis 15 d❑ FACU FAC species 39 x 3 = 117 4 Alnus sinuata 10 d❑ FAC FACU species 115 x 4 = 460 5 0 ❑ UPL species 0 x 5= 0 6 0 ❑ rnlumn Tntals- 184 (A) 607 (B) 7. 0 ❑ Prevalence Index = B/A = 3.299 8. 0 ❑ Hydrophytic Vegetation Indicators: 0 ❑ 9 0 ❑ ❑ Dominance Test is > 500/o 10. Total Cover: 48 ❑ Prevalence Index is :53.0 50% of Total Cover: 24 20% of Total Cover: 9.6 ❑ Morphological Adaptations 1 (Provide supporting Herb Stratum data in Remarks or on a separate sheet) 1 Lysichiton americanum 30 66 OBL ❑ Problematic Hydrophytic Vegetation 1 (Explain) 2. Rubus pedatus 10 0 FAC i Indicators of hydric soil and wetland hydrology must 3. Tiarella trifoliata 1 El FAC be present, unless disturbed or problematic. 4. 0 ❑ ❑❑ 5. 0 Plot size (radius, or length x width) 6. 0 ❑ % Cover of Wetland Bryophytes 10 7 (Where applicable) $ 0 ❑ % Bare Ground 0 9. 0 ❑ Total Cover of Bryophytes 10 10. — 0 ❑ Hydrophytic Total Cover: 41 Vegetation 50% of Total Cover: 20.5 20% of Total Cover: 8.2 Present? Yes O No with skunk cabbage, alder and devils club and Remarks: Mature Sitka spruce hemlock patch, patchy vegetation types in understory, low microsites limited high microsites with mature sitka spruce, few understory species. US Army Corps of Engineers Alaska Version 2.0 SOIL Sampling Point: CH11-01 Profile Description: Describe to depth needed to document the presence or absence of indicators Depth Matrix Redox Features (inches) Color (moist) % Color (moist) % Type' Loci 0-2 10YR 2/1 100 Peat 2-4 10YR 3/3 100 Peat 4-5 10YR 2/1 100 Peat 5-19 2.5Y 3/1 Texture Remarks oe Oi oe Peat Oa, sand and silt content 'Type: C=Concentration D=Depletion RM=Reduced Matrix 2Location: PL=Pore Lining RC=Root Channel M=Matrix Hydric Soil Indicators: Indicators for Problematic Hydric Soils:' ❑d Histosol or Histel (Al) 4 ❑ Alaska Color Change (TA4) ❑ Alaska Gleyed Without Hue 5Y or Redder ❑ Histic Epipedon (A2) ❑ Alaska Alpine swales (TA5) Underlying Layer ❑ Hydrogen Sulfide (A4) Alaska Redox With 2.5Y Hue ❑ Other (Explain in Remarks) ❑ Thick Dark Surface (Al2) ❑ Alaska Gleyed (A13) 3 One indicator of hydrophytic vegetation, one primary indicator of wetland hydrology, ❑ Alaska Redox (A14) and an appropriate landscape position must be present ❑ Alaska Gleyed Pores (A15) 4 Give details of color change in Remarks Restrictive Layer (if present): Type: frost Hydric Soil Present? Yes OO No 0 Depth (inches): 19 Remarks: HYDROLOGY Wetland Hydrology Indicators: Primary Indicators (any one is sufficient) ❑ Surface Water (Al) ❑ Inundation Visible on Aerial Imagery (671, ❑� High Water Table (A2) ❑ Sparsely Vegetated Concave Surface (138; ❑� Saturation (A3) ❑ Marl Deposits (615) ❑ Water Marks (131) ❑ Hydrogen Sulfide Odor (Cl) ❑ Sediment Deposits (132) ❑ Dry -Season Water Table (C2) ❑ Drift Deposits (133) ❑ Other (Explain in Remarks) ❑ Algal Mat or Crust (64) ❑ Iron Deposits (135) ❑ Surface Soil Cracks (136) Field Observations: Surface Water Present? Yes 0 No Depth (inches): 0 Secondary Indicators (two or more are required) ❑ Water Stained Leaves (139) W Drainage Patterns (1310) ❑ Oxidized Rhizospheres along Living Roots (0) ❑ Presence of Reduced Iron (C4) ❑ Salt Deposits (C5) ❑ Stunted or Stressed Plants (131) 0 Geomorphic Position (132) ❑ Shallow Aquitard (D3) ❑ Microtopographic Relief (134) ❑ FAC-neutral Test (D5) Water Table Present? Yes * No 0 Depth (inches): 7 Wetland Hydrology Present? Yes * No 0 Saturation Present? Yes 0 No* Depth (inches): 0 (includes cagillary fringe) Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspection) if available: Remarks: U.S. Army Corps of Engineers Alaska Version 2.0 WETLAND DETERMINATION DATA FORM - Alaska Region Project/Site: CHENEGA HYDRO Borough/City: CHENEGA BAY Sampling Date: 05-Oct-11 Applicant/Owner: HATCH/SOLSTICE Sampling Point: CHII-02 Investigator(s): WAD, NMT Landform (hillside, terrace, hummocks etc.): Toeslope Local relief (concave, convex, none): concave Slope: 0.0 % / 0.0 ° Elevation: Subregion : Southeast Alaska Lat.: 60.0681033333333 Long.:-148.016026666667 Datum: WGS84 Soil Map Unit Name: NWI classification: PEM1E Are climatic/hydrologic conditions on the site typical for this time of year? Yes U No U (If no, explain in Remarks.) Are Vegetation ❑ , Soil ❑ , or Hydrology ❑ significantly disturbed? Are "Normal Circumstances" present? Yes O 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 Hydrophytic Vegetation Present? Yes O No O Is the Sampled Area Hydric Soil Present? Yes O NO O within a Wetland? Yes * No U Wetland Hydrology Present? Yes NO O Remarks: Flooded area potentially toeslope accumulation or stream headwater photos 374-378 VEGETATION Use scientific names of plants. List all species in the plot. Absolute Dominant Indicator Dominance Test worksheet: Tree Stratum % Cover Species? Status Number of Dominant Species 1 ❑ That are OBL, FACW, or FAC: 2 (A) 2 El Total Number of Dominant ❑ Species Across All Strata: 2 (B) 3. ❑ Percent of dominant Species 4. ❑ That Are OBL, FACW, or FAC: 100.0% (A/B) 5 Prevalence Index worksheet: Total Cover: 0 Sapling/Shrub Stratum SO%of Total Cover: 0 20% of Total Cover: 0 Total % Cover of: Multiply by: ❑ OBL species 55 x 1 = 55 1 ❑ FACW species 0 x 2= 0 2.3. ❑ FAC species 0 x 3 = 0 4. ❑ FACU species 0 x 4 = 0 5 ❑ UPL species 10 x 5 = 50 6 ❑ rnlumn Tntalse 65 (p) 105 (B) ❑❑ 7. Prevalence Index = B/A = 1.615 Hydrophytic Vegetation Indicators: 9. ❑ ❑ e Dominance Test is > 50% 10. Total Cover: 0 ?] Prevalence Index is <_3.0 SO% of Total Cover: 0 20% of Total Cover: 0 ❑ Morphological Adaptations 1 (Provide supporting Herb Stratum data in Remarks or on a separate sheet) 1 Carex lyngbyei 35 OBL ❑ Problematic Hydrophytic Vegetation 1 (Explain) 2 Calamagrostis canadensis var. langsdorfii 10 ❑ UPL 1 Indicators of hydric soil and wetland hydrology must 3. Juncus mertensianus 5 ElOBL be present, unless disturbed or problematic. 4 Cinna latifolia 15 OBL 0 ❑ 5. Plot size (radius, or length x width) 6. o s % Cover of Wetland Bryophyte 7 (Where applicable) $ 0 ❑ % Bare Ground 9. 0 ❑ Total Cover of Bryophytes 10. 0 ❑ Hydrophytic Total Cover: 65 Vegetation SO% of Tota I Cover: 32.5 20% of Total Cover: 13 Present? Yes O No O Remarks: potomageton unidentified OBL 15, unidentified forb 5 US Army Corps of Engineers Alaska Version 2.0 SOIL Sampling Point: CH11-02 Profile Description: Describe to depth needed to document the presence or absence of indicators Depth Matrix Redox Features % Color (moist) (inches) Color (moist) t) % Type' Loci Texture 'Type: C=Concentration D=Depletion RM=Reduced Matrix 2Location: PL=Pore Lining RC=Root Channel M=Matrix Remarks Hydric Soil Indicators: Indicators for Problematic Hydric Soils:' ElHistosol or Histel (Al) ElAlaska Color Change (TA4) ❑ Alaska Gleyed Without Hue 5Y or Redder ❑ Histic Epipedon (A2) ❑ Alaska Alpine swales (TA5) Underlying Layer ❑ Hydrogen Sulfide (A4) ❑ Alaska Redox With 2.5Y Hue ❑ Other (Explain in Remarks) ❑ Thick Dark Surface (Al2) ❑ Alaska Gleyed (A13) 3 One indicator of hydrophytic vegetation, one primary indicator of wetland hydrology, and an appropriate landscape position must be present ❑ Alaska Redox (A14) ❑ Alaska Gleyed Pores (A15) 4 Give details of color change in Remarks Restrictive Layer (if present): Type: Depth (inches): Remarks: no pit permanently innundated HYDROLOGY Wetland Hydrology Indicators: Primary Indicators (any one is sufficient) ❑� Surface Water (Al) ❑ Inundation Visible on Aerial Imagery (671, ❑ High Water Table (A2) ❑ Sparsely Vegetated Concave Surface (138; ❑ Saturation (A3) ❑ Marl Deposits (615) ❑ Water Marks (131) ❑ Hydrogen Sulfide Odor (Cl) ❑ Sediment Deposits (132) ❑ Dry -Season Water Table (C2) ❑ Drift Deposits (133) ❑ Other (Explain in Remarks) ❑ Algal Mat or Crust (64) ❑ Iron Deposits (135) ❑ Surface Soil Cracks (136) Field Observations: Surface Water Present? Yes No 0 Depth (inches): 2 Hydric Soil Present? Yes O No 0 Secondary Indicators (two or more are required) ❑ Water Stained Leaves (139) ❑ Drainage Patterns (1310) ❑ Oxidized Rhizospheres along Living Roots (0) ❑ Presence of Reduced Iron (C4) ❑ Salt Deposits (C5) ❑ Stunted or Stressed Plants (131) ❑ Geomorphic Position (132) ❑ Shallow Aquitard (D3) ❑ Microtopographic Relief (134) ❑� FAC-neutral Test (D5) Water Table Present? Yes* No 0 Depth (inches): Wetland Hydrology Present? Yes * No 0 Saturation Present? Yes 0 No 0 Depth (inches): (includes cagillary fringe) Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspection) if available: Remarks: flooded area at toeslope, ditch drainages from side near pad U.S. Army Corps of Engineers Alaska Version 2.0 WETLAND DETERMINATION DATA FORM - Alaska Region Project/Site: CHENEGA HYDRO Borough/City: CHENEGA BAY Sampling Date: 05-Oct-11 Applicant/Owner: HATCH/SOLSTICE Sampling Point: CHII-03 Investigator(s): WAD, NMT Landform (hillside, terrace, hummocks etc.): Flat Local relief (concave, convex, none): convex slope: 0.0 % / 0.0 ° Elevation: Subregion : Southeast Alaska Lat.: 60.0680316666667 Long.:-148.016558333333 Datum: WGS84 Soil Map Unit Name: NWI classification: Upland Are climatic/hydrologic conditions on the site typical for this time of year? Yes U No U (If no, explain in Remarks.) Are Vegetation ❑ Soil ❑ , or Hydrology ❑ significantly disturbed? Are "Normal Circumstances" present? Yes UO 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 Hydrophytic Vegetation Present? Yes O NO Is the Sampled Area Hydric Soil Present? Yes O NO within a Wetland? Yes 0 No Wetland Hydrology Present? Yes * No O UO Remarks: just at edge of sapling sitka spruce, alnus growing on old patch of fill photos 380-383 VEGETATION Use scientific names of plants. List all species in the plot. Absolute Dominant Indicator Dominance Test worksheet: Tree Stratum % Cover Species? Status Number of Dominant Species 1 Picea sitchensis 2 d❑ FACU That are OBL, FACW, or FAC: 2 (A) 2 0 ❑ Total Number of Dominant 0 ❑ Species Across All Strata: 5 (B) p El Percent of dominant Species 4 0 ❑ That Are OBL, FACW, or FAC: 40.0% (A/B) 5 Total Cover: 2 Prevalence Index worksheet: Sapling/Shrub Stratum 50% of Total Cover: 1 20% of Total Cover: 0.4 Total % Cover of: Multiply by: 0 FACU OBL species 5 x 1 = 5 Picea sitchensis 85 2. Tsuga heterophylla 10 ❑ FAC FACW species 0 x 2 = 0 3 Alnuscrispa 10 ❑ FAC FAC species 23 x 3 = fi9 4 Rubus spectabilis 5 ❑ FACU FACU species 92 x 4 = 368 5 0 ❑ UPL species 2 x 5= 10 6. 0 ❑ rnlumn Tntals- 122 (A) 452 (B) 7. 0 ❑ Prevalence Index = B/A = 3.705 8. 0 ❑ Hydrophytic Vegetation Indicators: 0 ❑ 9 0 ❑ ❑ Dominance Test is > 500/o 10. Total Cover: 110 ❑ Prevalence Index is :53.0 50% of Total Cover: 55 20% of Total Cover: 22 ❑ Morphological Adaptations 1 (Provide supporting Herb Stratum data in Remarks or on a separate sheet) 1. Lysichiton americanum 5 66 OBL ❑ Problematic Hydrophytic Vegetation 1 (Explain) 2 Calamagrostis canadensis var. langsdorfii 2 d❑ UPL 1 Indicators of hydric soil and wetland hydrology must 3. Athyrium filix-femina 2❑ - FAC be present, unless disturbed or problematic. 4 Blechnum spicant 1 ❑ FAC U ❑ 5. ❑❑ Plot size (radius, or length x width) 6. 0 % Cover of Wetland Bryophytes 7 (Where applicable) $ 0 ❑ % Bare Ground 9. 0 ❑ Total Cover of Bryophytes 10. 0 ❑ Hydrophytic Total Cover: 10, Vegetation SO% of Total Cover: 5 20% of Total Cover: 2 Present? Yes O No O Remarks: US Army Corps of Engineers Alaska Version 2.0 SOIL Sampling Point: CH11-03 Profile Description: Describe to depth needed to document the presence or absence of indicators Depth Matrix Redox Features % Color (moist) (inches) Color (moist) t) % Type' Loci 0-16 10YR 2/1 100 Peat Texture 'Type: C=Concentration D=Depletion RM=Reduced Matrix 2Location: PL=Pore Lining RC=Root Channel M=Matrix Remarks with sand and big hunks of woody debris thro Hydric Soil Indicators: Indicators for Problematic Hydric Soils:' ElHistosol or Histel (Al) ElAlaska Color Change (TA4) ❑ Alaska Gleyed Without Hue 5Y or Redder ❑ Histic Epipedon (A2) ❑ Alaska Alpine swales (TA5) Underlying Layer ❑ Hydrogen Sulfide (A4) ❑ Alaska Redox With 2.5Y Hue ❑ Other (Explain in Remarks) ❑ Thick Dark Surface (Al2) ❑ Alaska Gleyed (A13) 3 One indicator of hydrophytic vegetation, one primary indicator of wetland hydrology, and an appropriate landscape position must be present ❑ Alaska Redox (A14) ❑ Alaska Gleyed Pores (A15) 4 Give details of color change in Remarks Restrictive Layer (if present): Type: Depth (inches): Remarks: HYDROLOGY Wetland Hydrology Indicators: Primary Indicators (any one is sufficient) ❑ Surface Water (Al) ❑� High Water Table (A2) ❑� Saturation (A3) ❑ Water Marks (131) ❑ Sediment Deposits (132) ❑ Drift Deposits (133) ❑ Algal Mat or Crust (64) ❑ Iron Deposits (B5) ❑ Surface Soil Cracks (136) Field Observations: Surface Water Present? Yes O No ❑ Inundation Visible on Aerial Imagery (67; ❑ Sparsely Vegetated Concave Surface (138; ❑ Marl Deposits (615) ❑ Hydrogen Sulfide Odor (Cl) ❑ Dry -Season Water Table (C2) ❑ Other (Explain in Remarks) Depth (inches): Hydric Soil Present? Yes O No O Secondary Indicators (two or more are required) ❑ Water Stained Leaves (139) ❑ Drainage Patterns(B10) ❑ Oxidized Rhizospheres along Living Roots (0) ❑ Presence of Reduced Iron (C4) ❑ Salt Deposits (C5) ❑ Stunted or Stressed Plants (131) ❑ Geomorphic Position (132) ❑ Shallow Aquitard (D3) ❑ Microtopographic Relief (134) ❑ FAC-neutral Test (D5) Water Table Present? Yes* No O Depth (inches): 17 Wetland Hydrology Present? Yes * No O Saturation Present? Yes 0 No O Depth (inches): (includes cagillary fringe) Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspection) if available: Remarks: saturated at surface but only because of heavy rain at the time of sampling. U.S. Army Corps of Engineers Alaska Version 2.0 WETLAND DETERMINATION DATA FORM - Alaska Region Project/Site: CHENEGA HYDRO Borough/City: CHENEGA BAY _ Sampling Date: 06-Oct-11 Applicant/Owner: HATCH/SOLSTICE Sampling Point: CHII-04 Investigator(s): WAD, NMT Landform (hillside, terrace, hummocks etc.): ditch Local relief (concave, convex, none): concave Slope: 1.7 % / 1.0 ° Elevation: Subregion : Southeast Alaska Lat.: 60.0676516666667 Long.:-148.016783333333 Datum: WGS84 Soil Map Unit Name: NWI classification: 114SBC Are climatic/hydrologic conditions on the site typical for this time of year? Yes U No U (If no, explain in Remarks.) Are Vegetation ❑ Soil ❑ , or Hydrology ❑ significantly disturbed? Are "Normal Circumstances" present? Yes UO 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 Hydrophytic Vegetation Present? Yes No Is the Sampled Area Hydric Soil Present? Yes No within a Wetland? Yes * No O Wetland Hydrology Present? Yes No O Remarks: ditch running around power plant pad. running water silt fence. VEGETATION Use scientific names of plants. List all species in the plot. Absolute Dominant Indicator Dominance Test worksheet: Tree Stratum % Cover Species? Status Number of Dominant Species 1 ❑ That are OBL, FACW, or FAC: 2 (A) 2 El Total Number of Dominant ❑ Species Across All Strata: 3 (B) 3. — ❑ Percent of dominant Species 4 ❑ That Are OBL, FACW, or FAC: 66.7% (A/B) 5 Total Cover: 0 Prevalence Index worksheet: Sapling/Shrub Stratum 50% of Total Cover: 0 20% of Total Cover: 0 Total % Cover of: Multiply by: 10 9❑ FACU OBL species 10 x 1 = 10 Rubusspectabilis 1' 2 Alnus crisps 5 ❑ FAC FACW species 0 x 2 = 0 3 0 ❑ FAC species 5 x 3= 15 4 0 ❑ FACU species 10 x 4 = 40 5 0 ❑ UPL species 0 x 5= 0 6 0 ❑ rnlumn Tntalse 25 (A) 65 (B) 7. 0 ❑ Prevalence Index = B/A = 2.600 8. 0 ❑ Hydrophytic Vegetation Indicators: 0 ❑ 9 0 El❑� Dominance Test is > 50% 10. Total Cover: — 15 Prevalence Index is <_3.0 50% of Total Cover: 7.5 20% of Total Cover: 3 ❑ Morphological Adaptations 1(Provide supporting Herb Stratum data in Remarks or on a separate sheet) 1 Cinna latifolia 10 66 OBL ❑ Problematic Hydrophytic Vegetation 1 (Explain) 2 0 ❑ 1 Indicators of hydric soil and wetland hydrology must 3. 0 Elbe present, unless disturbed or problematic. 4. 0 ❑ 5. 0 El Plot size (radius, or length x width) 6. 0 ❑ % Cover of Wetland Bryophytes 7 (Where applicable) $ 0 ❑ % Bare Ground 9. 0 ❑ Total Cover of Bryophytes 10. 0 ❑ Hydrophytic Total Cover: 10, Vegetation SO% of Total Cover: 5 20% of Total Cover: 2 Present? Yes O No O Remarks: channel with overhanging shrubs US Army Corps of Engineers Alaska Version 2.0 SOIL Sampling Point: CH11-04 Profile Description: Describe to depth needed to document the presence or absence of indicators Depth Matrix Redox Features % Color (moist) (inches) Color (moist) t) % Type' Loci Texture 'Type: C=Concentration D=Depletion RM=Reduced Matrix 2Location: PL=Pore Lining RC=Root Channel M=Matrix Remarks Hydric Soil Indicators: Indicators for Problematic Hydric Soils:' ElHistosol or Histel (Al) ElAlaska Color Change (TA4) ❑ Alaska Gleyed Without Hue 5Y or Redder ❑ Histic Epipedon (A2) ❑ Alaska Alpine swales (TA5) Underlying Layer ❑d Hydrogen Sulfide (A4) ❑ Alaska Redox With 2.5Y Hue ❑ Other (Explain in Remarks) ❑ Thick Dark Surface (Al2) ❑ Alaska Gleyed (A13) 3 One indicator of hydrophytic vegetation, one primary indicator of wetland hydrology, and an appropriate landscape position must be present ❑ Alaska Redox (A14) ❑ Alaska Gleyed Pores (A15) 4 Give details of color change in Remarks Restrictive Layer (if present): Type: Depth (inches): Remarks: no pit, saturated HYDROLOGY Wetland Hydrology Indicators: Primary Indicators (any one is sufficient) ❑d Surface Water (Al) ❑� High Water Table (A2) ❑� Saturation (A3) ❑ Water Marks (131) ❑ Sediment Deposits (132) ❑ Drift Deposits (133) ❑ Algal Mat or Crust (64) ❑ Iron Deposits (135) ❑ Surface Soil Cracks (136) Field Observations: Surface Water Present? Yes No 0 ❑ Inundation Visible on Aerial Imagery (67; ❑ Sparsely Vegetated Concave Surface (138; ❑ Marl Deposits (615) ❑ Hydrogen Sulfide Odor (Cl) ❑ Dry -Season Water Table (C2) ❑ Other (Explain in Remarks) Depth (inches): 4 Hydric Soil Present? Yes O No 0 Secondary Indicators (two or more are required) U Water Stained Leaves (139) ❑ Drainage Patterns (1310) ❑ Oxidized Rhizospheres along Living Roots (0) ❑ Presence of Reduced Iron (C4) ❑ Salt Deposits (C5) ❑ Stunted or Stressed Plants (131) ❑ Geomorphic Position (132) ❑ Shallow Aquitard (D3) ❑ Microtopographic Relief (134) ❑ FAC-neutral Test (D5) Water Table Present? Yes* No 0 Depth (inches): Wetland Hydrology Present? Yes * No 0 Saturation Present? Yes 0 No 0 Depth (inches): (includes cagillary fringe) Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspection) if available: Remarks: U.S. Army Corps of Engineers Alaska Version 2.0 WETLAND DETERMINATION DATA FORM - Alaska Region Project/Site: CHENEGA HYDRO Borough/City: CHENEGA BAY Sampling Date: Applicant/Owner: HATCH/SOLSTICE Investigator(s): WAD, NMT Local relief (concave, convex, none): PLANAR Sampling Point: Landform (hillside, terrace, hummocks etc.): Ravine Slope: 99.9 % / 45.0 ° Elevation: Subregion: Southeast Alaska Lat.: Long.: Soil Map Unit Name: NWI classification: Uplan( Are climatic/hydrologic conditions on the site typical for this time of year? Yes U No ❑ (If no, explain in Remarks.) Are Vegetation ❑ Soil ❑ , or Hydrology ❑ significantly disturbed? Are "Normal Circumstances" present? Yes OO No ❑ Are Vegetation ❑ Soil ❑ , or Hydrology ❑ naturally problematic? (If needed, explain any answers in Remarks.) 06-Oct-11 CH 11-05 Datum: WGS84 SUMMARY OF FINDINGS - Attach site map showing sampling point locations, transects, important features Hydrophytic Vegetation Present? Yes * No Is the Sampled Area Hydric Soil Present? Yes ❑ No within a Wetland? Yes 0 NO OO Wetland Hydrology Present? Yes * No O Remarks: Steep ravine sideslope down to creek photos 395 399 VEGETATION Use scientific names of plants. List all species in the plot. Tree Stratum 1. 2. 3. 4. 5. Tsuga heterophylla Sapling/Shrub Stratum 1 Vaccinium alaskaense Absolute Dominant % Cover Species? 65 d❑ 0 ❑ 0 ❑ 0 ❑ 0 ❑ Total Cover: 65 50% of Total Cover: 32.5 20% of Total Cover: 2 Menziesia ferruginea 3 Harrimanella stelleriana 4 Tsuga heterophylla 5 Phyllodoce aleutica 6. 7. 8. 9. _ 10. Total Cover Herb Stratum 50% of Total Cover: 1 Blechnum spirant 2 Coptis aspleniifolia 3. Fauria crista-galli 4 Rubus pedatus 5 Calamagrostis canadensis var. langsdorfii 6. 7. 8. 9. 1n 30 0 50 66 5 ❑ 5 ❑ 3 ❑ 0 ❑ 0 ❑ 0 ❑ 0 ❑ 0 ❑ 93 46.5 20% of Total Cover: 10 d❑ 5 d❑ 5 d❑ 2 ❑ 5 d❑ 0 ❑ 0 ❑ 0 ❑ 0 ❑ 0 ❑ Total Cover: 27 50% of Total Cover: 13.5 20% of Total Cover: Remarks: unknown graminoid, thin leaved sedge Indicator Status 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: 5 7 71.4% (A) (B) (A/B) FAC 13 Prevalence Index worksheet: Total % Cover of: OBL species 0 FACW species 10 FAC species 117 FACU species 0 UPL species 58 rnlumn Tntals- 185 Multiply x 1 = x 2 = x 3 = x 4 = x 5 = (A) by: 0 20 351 0 290 661 (B) FAC UPL FACW FAC UPL Prevalence Index = B/A = 3.573 Hydrophytic Vegetation Indicators: ❑d Dominance Test is > 50% ❑ Prevalence Index is :53.0 18.6 ❑ Morphological Adaptations 1 (Provide supporting data in Remarks or on a separate sheet) FAC ❑ Problematic Hydrophytic Vegetation 1 (Explain) FAC 1 Indicators of hydric soil and wetland hydrology must FACW be present, unless disturbed or problematic. FAC UPL Plot size (radius, or length x width) Cover of Wetland Bryophytes 0 (Where applicable) Bare Ground Total Cover of Bryophytes 30 Hydrophytic Vegetation 5.4 Present? Yes * No O US Army Corps of Engineers Alaska Version 2.0 SOIL Sampling Point: CH11-05 Profile Description: Describe to depth needed to document the presence or absence of indicators Depth Matrix Redox Features (inches) Color (moist) % Color (moist) % Type' Loci 0-5 10YR 2/1 100 Peat 5-8 2.5Y 4/1 95 10YR 4/6 5 C PL Loamy Sand 8-9 Texture 'Type: C=Concentration D=Depletion RM=Reduced Matrix 2Location: PL=Pore Lining RC=Root Channel M=Matrix Remarks oe 90 coarse FRAGMENTS bedrock Hydric Soil Indicators: Indicators for Problematic Hydric Soils:' ElHistosol or Histel (Al) ElAlaska Color Change (TA4) ❑ Alaska Gleyed Without Hue 5Y or Redder ❑ Histic Epipedon (A2) ❑ Alaska Alpine swales (TA5) Underlying Layer ❑ Hydrogen Sulfide (A4) ❑ Alaska Redox With 2.5Y Hue ❑ Other (Explain in Remarks) ❑ Thick Dark Surface (Al2) ❑ Alaska Gleyed (A13) 3 One indicator of hydrophytic vegetation, one primary indicator of wetland hydrology, ❑ Alaska Redox (A14) and an appropriate landscape position must be present ❑ Alaska Gleyed Pores (A15) 4 Give details of color change in Remarks Restrictive Layer (if present): Type: bedrock Hydric Soil Present? Yes 0 No OO Depth (inches): 8 Remarks: HYDROLOGY Wetland Hydrology Indicators: Primary Indicators (any one is sufficient) ❑ Surface Water (Al) ❑ High Water Table (A2) ❑� Saturation (A3) ❑ Water Marks (131) ❑ Sediment Deposits (132) ❑ Drift Deposits (B3) ❑ Algal Mat or Crust (64) ❑ Iron Deposits (135) ❑ Surface Soil Cracks (136) Field Observations: Surface Water Present? Yes 0 No ❑ Inundation Visible on Aerial Imagery (67; ❑ Sparsely Vegetated Concave Surface (138; ❑ Marl Deposits (615) ❑ Hydrogen Sulfide Odor (Cl) ❑ Dry -Season Water Table (C2) ❑ Other (Explain in Remarks) Depth (inches): Secondary Indicators (two or more are required) ❑ Water Stained Leaves (B9) ❑ Drainage Patterns(B10) ❑ Oxidized Rhizospheres along Living Roots (0) ❑ Presence of Reduced Iron (C4) ❑ Salt Deposits (C5) ❑ Stunted or Stressed Plants (131) ❑ Geomorphic Position (132) ❑ Shallow Aquitard (D3) ❑ Microtopographic Relief (134) ❑ FAC-neutral Test (D5) Water Table Present? Yes 0 No* Depth (inches): Wetland Hydrology Present? Yes * No 0 Saturation Present? Yes* No 0 Depth (inches): (includes cagillary fringe) Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspection) if available: Remarks: Saturated at the surface, but its due to heavy rain. U.S. Army Corps of Engineers Alaska Version 2.0 WETLAND DETERMINATION DATA FORM - Alaska Region Project/Site: CHENEGA HYDRO Borough/City: CHENEGA BAY _ Sampling Date: 06-Oct-11 Applicant/Owner: HATCH/SOLSTICE Sampling Point: CHII-06 Investigator(s): WAD, NMT Landform (hillside, terrace, hummocks etc.): Gulch or Gully Local relief (concave, convex, none): concave Slope: 46.6 % / 25.0 ° Elevation: Subregion : Southeast Alaska Lat.: 60.0722 Long.:-148.018816666667 Datum: WGS84 Soil Map Unit Name: NWI classification: pEM1E Are climatic/hydrologic conditions on the site typical for this time of year? Yes U No ❑ (If no, explain in Remarks.) Are Vegetation ❑ Soil ❑ , or Hydrology ❑ significantly disturbed? Are "Normal Circumstances" present? Yes OO 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 Hydrophytic Vegetation Present? Yes No Is the Sampled Area Hydric Soil Present? Yes No ❑ within a Wetland? Yes * No O Wetland Hydrology Present? Yes No O Remarks: finger of wet bog extending downslope to creek. drainage feature. photos 400-404 VEGETATION Use scientific names of plants. List all species in the plot. Absolute Dominant Indicator Dominance Test worksheet: Tree Stratum % Cover Species? Status Number of Dominant Species 1 ❑ That are OBL, FACW, or FAC: 4 (A) 2 El Total Number of Dominant ❑ Species Across All Strata: 6 (B) 3. — ❑ Percent of dominant Species 4 ❑ That Are OBL, FACW, or FAC: 66.7% (A/B) 5 Total Cover: 0 Prevalence Index worksheet: Sapling/Shrub Stratum 50% of Total Cover: 0 20% of Total Cover: 0 Total % Cover of: Multiply by: Cornuscanadensis d❑ FACU OBL species 20 x 1 = 20 1 5 2 Harrimanella stelleriana 2 d❑ FACW FACW species 46 x 2 = 92 3 Rubusarcticus 2 d❑ FAC FAC species 2 x 3= 6 4 Menziesia ferruginea 1 ❑ UPL FACU species 5 x 4 = 20 5 0 ❑ UPL species 11 x 5 = 55 6. 0 ❑ rnlumn Tntals- 84 (A) 193 (B) 7. 0 ❑ Prevalence Index = B/A = 2.298 8. 0 ❑ Hydrophytic Vegetation Indicators: 0 ❑ 9 0 El❑� Dominance Test is > 50% 10. Total Cover: — 10 Prevalence Index is <_3.0 50% of Total Cover: 5 20% of Total Cover: 2 ❑ Morphological Adaptations 1(Provide supporting Herb Stratum data in Remarks or on a separate sheet) 1 Eriophorum angustifolium 10 d❑ OBL ❑ Problematic Hydrophytic Vegetation 1 (Explain) 2 Calamagrostis canadensis var. langsdorfli 10❑ UPL 1 Indicators of hydric soil and wetland hydrology must 3. Gentian douglasiana 2 — ❑ FACW be present, unless disturbed or problematic. 4 Carex pluriflora 5 ❑ OBL 5. Geum macrophyllum 5 El FACW length ❑ Plot size (radius, or x width) 6. Lysichiton americanum 5 OBL %Cover of Wetland Bryophytes 50 7. Fauria crista-galli 2 ❑ FACW (Where applicable) 8. Erigeron peregrinus 35 0 FACW % Bare Ground 9. 0 ❑ Total Cover of Bryophytes 50 10. 0 ❑ Hydrophytic Total Cover: 74 Vegetation SO% of Total Cover: 37 20% of Total Cover: 14.8 Present? Yes O No O Remarks: US Army Corps of Engineers Alaska Version 2.0 SOIL Sampling Point: CH11-06 Profile Description: Describe to depth needed to document the presence or absence of indicators Depth Matrix Redox Features (inches) Color (moist) % Color (moist) % Type' Loci 0-3 10YR 4/6 100 Peat 3-5 10YR 5/6 100 Peat 5-16 10YR 3/6 100 Peat Texture Remarks of of of 'Type: C=Concentration D=Depletion RM=Reduced Matrix 2Location: PL=Pore Lining RC=Root Channel M=Matrix Hydric Soil Indicators: Indicators for Problematic Hydric Soils:' ❑d Histosol or Histel (Al) 4 ❑ Alaska Color Change (TA4) ❑ Alaska Gleyed Without Hue 5Y or Redder ❑ Histic Epipedon (A2) ❑ Alaska Alpine swales (TA5) Underlying Layer ❑ Hydrogen Sulfide (A4) ❑ Alaska Redox With 2.5Y Hue ❑ Other (Explain in Remarks) ❑ Thick Dark Surface (Al2) ❑ Alaska Gleyed (A13) 3 One indicator of hydrophytic vegetation, one primary indicator of wetland hydrology, ❑ Alaska Redox (A14) and an appropriate landscape position must be present ❑ Alaska Gleyed Pores (A15) 4 Give details of color change in Remarks Restrictive Layer (if present): Type: Hydric Soil Present? Yes OO No 0 Depth (inches): Remarks: HYDROLOGY Wetland Hydrology Indicators: Primary Indicators (any one is sufficient) ❑d Surface Water (Al) ❑� High Water Table (A2) ❑� Saturation (A3) ❑ Water Marks (61) ❑ Sediment Deposits (132) ❑ Drift Deposits (133) ❑ Algal Mat or Crust (64) ❑ Iron Deposits (65) ❑ Surface Soil Cracks (136) Field Observations: Surface Water Present? Yes No 0 ❑ Inundation Visible on Aerial Imagery (67; ❑ Sparsely Vegetated Concave Surface (138; ❑ Marl Deposits (615) ❑ Hydrogen Sulfide Odor (Cl) ❑ Dry -Season Water Table (C2) ❑ Other (Explain in Remarks) Depth (inches): Secondary Indicators (two or more are required) U Water Stained Leaves (139) ❑ Drainage Patterns(810) ❑ Oxidized Rhizospheres along Living Roots (0) ❑ Presence of Reduced Iron (C4) ❑ Salt Deposits (C5) ❑ Stunted or Stressed Plants (131) ❑ Geomorphic Position (132) ❑ Shallow Aquitard (D3) ❑ Microtopographic Relief (134) ❑� FAC-neutral Test (D5) Water Table Present? Yes* No 0 Depth (inches): Wetland Hydrology Present? Yes * No 0 Saturation Present? Yes 0 No 0 Depth (inches): (includes cagillary fringe) Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspection) if available: Remarks: surface water in patches, small beaded stream U.S. Army Corps of Engineers Alaska Version 2.0 WETLAND DETERMINATION DATA FORM - Alaska Region Project/Site: CHENEGA HYDRO Borough/City: CHENEGA BAY _ Sampling Date: 06-Oct-11 Applicant/Owner: HATCH/SOLSTICE Sampling Point: CHII-07 Investigator(s): WAD, NMT Landform (hillside, terrace, hummocks etc.): Hillside Local relief (concave, convex, none): concave Slope: 8.7 % / 5.0 ° Elevation: Subregion : Southeast Alaska Lat.: Long.: Datum: WGS84 Soil Map Unit Name: NWI classification: PEM1/SS4E Are climatic/hydrologic conditions on the site typical for this time of year? Yes U No O (If no, explain in Remarks.) Are Vegetation ❑ Soil ❑ , or Hydrology ❑ significantly disturbed? Are "Normal Circumstances" present? Yes OO 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 Hydrophytic Vegetation Present? Yes No O Is the Sampled Area Hydric Soil Present? Yes No O within a Wetland? Yes OO No O Wetland Hydrology Present? Yes No O Remarks: Bog patch centerline of proposed trench. Beaded stream runs around edge of bog photos 415-420 VEGETATION Use scientific names of plants. List all species in the plot. Absolute Dominant Indicator Dominance Test worksheet: Tree Stratum % Cover Species? Status Number of Dominant Species 1 ❑ That are OBL, FACW, or FAC: 6 (A) 2 El Total Number of Dominant ❑ Species Across All Strata: 6 (B) 3. — ❑ Percent of dominant Species 4 ❑ That Are OBL, FACW, or FAC: 100.0% (A/B) 5 Total Cover: 0 Prevalence Index worksheet: Sapling/Shrub Stratum 50% of Total Cover: 0 20% of Total Cover: 0 Total % Cover of: Multiply by: El OBL species 13 x 1 = 13 1 Tsuga mertensiana 5 2 Cornus suecica 5 ❑ FAC FACW species 30 x 2 = 60 3. Harrimanella stelleriana 15 d❑ FACW FAC species 18 x 3 = 54 4. Alnus sinuata 1 ❑ FAC FACU species 0 x 4 = 0 5 0 ❑ UPL species 0 x 5= 0 6. 0 ❑ rnlumn Tntals- 61 (A) 127 (B) 7. 0 ❑ Prevalence Index = B/A = 2.082 8. 0 ❑ Hydrophytic Vegetation Indicators: 0 ❑ 9 0 El❑� Dominance Test is > 50% 10. Total Cover: — 26 Prevalence Index is <_3.0 50% of Total Cover: 13 20% of Total Cover: 5.2 ❑ Morphological Adaptations 1(Provide supporting Herb Stratum data in Remarks or on a separate sheet) 1. Eriophorum angustifolium 5 d❑ OBL ❑ Problematic Hydrophytic Vegetation 1 (Explain) 2 Carex pluriflora 5 d❑ OBL 1 Indicators of hydric soil and wetland hydrology must 3. Geum macrophyllum 5 d❑ FACW be present, unless disturbed or problematic. 4. Lycopodium annotinum 2 El FAC 5. ]uncus stygius 3 ElOBL length Gentians douglasiana ❑ FACW Plot size (radius, or x width) 6. 3 %Cover of Wetland Bryophytes 30 7. Fauria crista-galli 2 ❑ FACW (Where applicable) 8. Rubus arcticus 5❑ FAC % Bare Ground 9. Erigeron peregrinus 5❑ FACW Total Cover of Bryophytes 30 10. 0 ❑ Hydrophytic Total Cover: 35 Vegetation 50% of Total Cover: 17.5 20% of Total Cover: 7 Present? Yes O No O Remarks: US Army Corps of Engineers Alaska Version 2.0 SOIL Sampling Point: CH11-07 Profile Description: Describe to depth needed to document the presence or absence of indicators Depth Matrix Redox Features % Color (moist) (inches) Color (moist) t) % Typel Loci 0-16 10YR 3/2 100 Peat 16-21 10YR 2/1 100 Texture of Peat oe 'Type: C=Concentration D=Depletion RM=Reduced Matrix 2Location: PL=Pore Lining RC=Root Channel M=Matrix Remarks Hydric Soil Indicators: Indicators for Problematic Hydric Soils:' 4 ❑d Histosol or Histel (Al) ❑ Alaska Color Change (TA4) ❑ Alaska Gleyed Without Hue 5Y or Redder ❑ Histic Epipedon (A2) ❑ Alaska Alpine swales (TA5) Underlying Layer ❑ Hydrogen Sulfide (A4) ❑ Alaska Redox With 2.5Y Hue ❑ Other (Explain in Remarks) ❑ Thick Dark Surface (Al2) ❑ Alaska Gleyed (A13) 3 One indicator of hydrophytic vegetation, one primary indicator of wetland hydrology, and an appropriate landscape position must be present ❑ Alaska Redox (A14) ❑ Alaska Gleyed Pores (A15) 4 Give details of color change in Remarks Restrictive Layer (if present): Type: Depth (inches): Remarks: HYDROLOGY Wetland Hydrology Indicators: Primary Indicators (any one is sufficient) ❑d Surface Water (Al) ❑� High Water Table (A2) ❑� Saturation (A3) ❑ Water Marks (131) ❑ Sediment Deposits (132) ❑ Drift Deposits (133) ❑ Algal Mat or Crust (64) ❑ Iron Deposits (135) ❑ Surface Soil Cracks (136) Field Observations: Surface Water Present? Yes No ❑ ❑ Inundation Visible on Aerial Imagery (67; ❑ Sparsely Vegetated Concave Surface (138; ❑ Marl Deposits (615) ❑ Hydrogen Sulfide Odor (Cl) ❑ Dry -Season Water Table (C2) ❑ Other (Explain in Remarks) Depth (inches): 5 Hydric Soil Present? Yes O No O Secondary Indicators (two or more are required) U Water Stained Leaves (139) ❑ Drainage Patterns (1310) ❑ Oxidized Rhizospheres along Living Roots (0) ❑ Presence of Reduced Iron (C4) ❑ Salt Deposits (C5) ❑ Stunted or Stressed Plants (131) ❑ Geomorphic Position (132) ❑ Shallow Aquitard (D3) ❑ Microtopographic Relief (134) ❑� FAC-neutral Test (D5) Water Table Present? Yes* No O Depth (inches): 13 Wetland Hydrology Present? Yes * No O Saturation Present? Yes 0 No O Depth (inches): (includes cagillary fringe) Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspection) if available: Remarks: surface water in patches U.S. Army Corps of Engineers Alaska Version 2.0 WETLAND DETERMINATION DATA FORM - Alaska Region Project/Site: CHENEGA HYDRO Borough/City: CHENEGA BAY Sampling Date: 06-Oct-11 Applicant/Owner: HATCH/SOLSTICE Sampling Point: CHII-08 Investigator(s): WAD, NMT Landform (hillside, terrace, hummocks etc.): Channel (active) Local relief (concave, convex, none): concave Slope: 8.7 % / 5.0 ° Elevation: Subregion : Southeast Alaska Lat.: Long.: Datum: WGS84 Soil Map Unit Name: NWI classification: R4SBC Are climatic/hydrologic conditions on the site typical for this time of year? Yes U No U (If no, explain in Remarks.) Are Vegetation ❑ , Soil ❑ , or Hydrology ❑ significantly disturbed? Are "Normal Circumstances" present? Yes O 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 Hydrophytic Vegetation Present? Yes O No O Is the Sampled Area Hydric Soil Present? Yes O NO O within a Wetland? Yes * No U Wetland Hydrology Present? Yes NO O Remarks: beaded stream runs at edge of bog photos 426-428 VEGETATION Use scientific names of plants. List all species in the plot. Absolute Dominant Indicator Dominance Test worksheet: Tree Stratum % Cover Species? Status Number of Dominant Species 1 ❑ That are OBL, FACW, or FAC: 0 (A) 2 El Total Number of Dominant ❑ Species Across All Strata: 0 (B) 3. ❑ Percent of dominant Species 4. ❑ That Are OBL, FACW, or FAC: 0.0% (A/B) 5 Prevalence Index worksheet: Total Cover: 0 Sapling/Shrub Stratum SO%of Total Cover: 0 20% of Total Cover: 0 Total % Cover of: Multiply by: ❑ OBL species 0 x 1 = 0 1 ❑ FACW species 0 x 2= 0 2. 3. ❑ FAC species 0 x 3 = 0 4 ❑ FACU species 0 x 4= 0 5 ❑ UPL species 0 x 5= 0 6. ❑ [nlumn Tntals, 0 fnl 0 (B) ❑❑ 7. Prevalence Index = B/A = 0.000 Hydrophytic Vegetation Indicators: 9. ❑ ❑ ❑ Dominance Test is > 50% 10. ❑ Prevalence Index is <_3.0 Total Cover: 0 50% of Total Cover: 0 20% of Total Cover: 0 ❑ Morphological Adaptations 1 (Provide supporting Herb Stratum data in Remarks or on a separate sheet) 1 . 0 ❑ ❑ Problematic Hydrophytic Vegetation 1 (Explain) 2. 0 ❑ 1 Indicators of hydric soil and wetland hydrology must 3. 0 ❑ be present, unless disturbed or problematic. 4. a ❑ 0 5. Plot size (radius, or length x width) 6. 0 ❑ % Cover of Wetland Bryophytes 0 7 (Where applicable) $ 0 ❑ % Bare Ground 9. 0 ❑ Total Cover of Bryophytes 0 10. 0 ❑ Hydrophytic Total Cover: 0 Vegetation SO% of Tota I Cover: 0 20% of Total Cover: 0 Present? Yes O No O Remarks: potamageton in channel 3% US Army Corps of Engineers Alaska Version 2.0 SOIL Sampling Point: CH11-08 Profile Description: Describe to depth needed to document the presence or absence of indicators Depth Matrix Redox Features % Color (moist) (inches) Color (moist) t) % Type' Loci Texture 'Type: C=Concentration D=Depletion RM=Reduced Matrix 2Location: PL=Pore Lining RC=Root Channel M=Matrix Remarks Hydric Soil Indicators: Indicators for Problematic Hydric Soils:' ElHistosol or Histel (Al) ElAlaska Color Change (TA4) ❑ Alaska Gleyed Without Hue 5Y or Redder ❑ Histic Epipedon (A2) ❑ Alaska Alpine swales (TA5) Underlying Layer ❑ Hydrogen Sulfide (A4) ❑ Alaska Redox With 2.5Y Hue ❑ Other (Explain in Remarks) ❑ Thick Dark Surface (Al2) ❑ Alaska Gleyed (A13) 3 One indicator of hydrophytic vegetation, one primary indicator of wetland hydrology, and an appropriate landscape position must be present ❑ Alaska Redox (A14) ❑ Alaska Gleyed Pores (A15) 4 Give details of color change in Remarks Restrictive Layer (if present): Type: Depth (inches): Remarks: no pit saturated HYDROLOGY Wetland Hydrology Indicators: Primary Indicators (any one is sufficient) ❑d Surface Water (Al) ❑ Inundation Visible on Aerial Imagery (671, ❑� High Water Table (A2) ❑ Sparsely Vegetated Concave Surface (138; ❑� Saturation (A3) ❑ Marl Deposits (615) ❑ Water Marks (131) ❑ Hydrogen Sulfide Odor (Cl) ❑ Sediment Deposits (132) ❑ Dry -Season Water Table (C2) ❑ Drift Deposits (133) ❑ Other (Explain in Remarks) ❑ Algal Mat or Crust (84) ❑ Iron Deposits (135) ❑ Surface Soil Cracks (136) Field Observations: Surface Water Present? Yes No 0 Depth (inches): 12 Hydric Soil Present? Yes O No 0 Secondary Indicators (two or more are required) ❑ Water stained Leaves (139) ❑ Drainage Patterns (1310) ❑ Oxidized Rhizospheres along Living Roots (0) ❑ Presence of Reduced Iron (C4) ❑ Salt Deposits (C5) ❑ Stunted or Stressed Plants (131) ❑ Geomorphic Position (132) ❑ Shallow Aquitard (D3) ❑ Microtopographic Relief (134) ❑ FAC-neutral Test (D5) Water Table Present? Yes* No 0 Depth (inches): Wetland Hydrology Present? Yes * No 0 Saturation Present? Yes 0 No 0 Depth (inches): (includes cagillary fringe) Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspection) if available: Remarks: beaded stream with deep pools and saturated edges U.S. Army Corps of Engineers Alaska Version 2.0 WETLAND DETERMINATION DATA FORM - Alaska Region Project/Site: CHENEGA HYDRO Borough/City: CHENEGA BAY _ Sampling Date: 06-Oct-11 Applicant/Owner: HATCH/SOLSTICE Sampling Point: CHII-09 Investigator(s): WAD, NMT Landform (hillside, terrace, hummocks etc.): Hillside Local relief (concave, convex, none): planar Slope: 70.0 % / 35.0 ° Elevation: Subregion : Southeast Alaska Lat.: Long.: Datum: WGS84 Soil Map Unit Name: NWI classification: Upland Are climatic/hydrologic conditions on the site typical for this time of year? Yes U No ❑ (If no, explain in Remarks.) Are Vegetation ❑ Soil ❑ , or Hydrology ❑ significantly disturbed? Are "Normal Circumstances" present? Yes OO 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 Hydrophytic Vegetation Present? Yes O NO Is the Sampled Area Hydric Soil Present? Yes O NO Wetland Hydrology Present? Yes O No within a Wetland? Yes NO Remarks: steep hillside above disturbance. Still some small drainages through here, but too small to map photos 433-439 VEGETATION Use scientific names of plants. List all species in the plot. Absolute Dominant Indicator Dominance Test worksheet: Tree Stratum % Cover Species? Status Number of Dominant Species 1 Picea sitchensis 15❑ FACU That are OBL, FACW, or FAC: 3 (A) 2 Tsuga heterophylla 10 FAC Total Number of Dominant 0 ❑ Species Across All Strata: 6 (B) p El Percent of dominant Species 4 0 ❑ That Are OBL, FACW, or FAC: 50.0% (A/B) 5 Total Cover: 25 Prevalence Index worksheet: Sapling/Shrub Stratum 50% of Total Cover: 12.5 20% of Total Cover: 5 Total % Cover of: Multiply by: ferruginea ElUPL OBL species 1 x 1 = 1 1. Menziesia 5 2. Vaccinium ovalifolium 15 d❑ FAC FACW species 0 x 2 = 0 3. Rubusspectabilis 10 ❑ FACU FAC species 55 x 3 = 165 4 Alnus sinuata 5 ❑ FAC FACU species 51 x 4 = 204 5 Cornuscanadensis 25❑ FACU UPL species 35 x 5 = 175 6 Oplopanax horridus 1 ❑ FACU rnlumn Tntals- 142 (A) 545 (B) 7. 0 ❑ Prevalence Index = B/A = 3.838 8. 0 ❑ Hydrophytic Vegetation Indicators: 0 ❑ 9 0 ❑ ❑ Dominance Test is > 500/o 10. Total Cover: 61 ❑ Prevalence Index is :53.0 50% of Total Cover: 30.5 20% of Total Cover: 12.2 ❑ Morphological Adaptations 1 (Provide supporting Herb Stratum data in Remarks or on a separate sheet) 1. Calamagrostis canadensis var. langsdorfii 30❑ UPL ❑ Problematic Hydrophytic Vegetation 1 (Explain) 2. Athyrium filix-femina 20 FAC i Indicators of hydric soil and wetland hydrology must 3. Lysichiton americanum 1 - El OBL be present, unless disturbed or problematic. 4 Coptis aspleniifolia 5 ❑ FAC U ❑ 5. ❑❑ Plot size (radius, or length x width) 6. 0 % Cover of Wetland Bryophytes 0 7 (Where applicable) $ 0 ❑ % Bare Ground 9. 0 ❑ Total Cover of Bryophytes 0 10. 0 ❑ Hydrophytic Total Cover: 56 Vegetation 50% of Total Cover: 28 20% of Total Cover: 11.2 Present? Yes O No Remarks: US Army Corps of Engineers Alaska Version 2.0 SOIL Sampling Point: CH11-09 Profile Description: Describe to depth needed to document the presence or absence of indicators Depth Matrix Redox Features (inches) Color (moist) % Color (moist) % Type' Loci 0-8 10YR 2/1 100 Peat Texture 8-13 2.5Y 4/2 95 10YR 4/3 5 C PL Silt Loam 'Type: C=Concentration D=Depletion RM=Reduced Matrix 2Location: PL=Pore Lining RC=Root Channel M=Matrix oe Remarks Hydric Soil Indicators: Indicators for Problematic Hydric Soils:' ElHistosol or Histel (Al) ElAlaska Color Change (TA4) ❑ Alaska Gleyed Without Hue 5Y or Redder ❑ Histic Epipedon (A2) ❑ Alaska Alpine swales (TA5) Underlying Layer ❑ Hydrogen Sulfide (A4) ❑ Alaska Redox With 2.5Y Hue ❑ Other (Explain in Remarks) ❑ Thick Dark Surface (Al2) ❑ Alaska Gleyed (A13) 3 One indicator of hydrophytic vegetation, one primary indicator of wetland hydrology, and an appropriate landscape position must be present ❑ Alaska Redox (A14) ❑ Alaska Gleyed Pores (A15) 4 Give details of color change in Remarks Restrictive Layer (if present): Type: rock Depth (inches): 13 Remarks: HYDROLOGY Wetland Hydrology Indicators: Primary Indicators (any one is sufficient) ❑ Surface Water (Al) ❑� High Water Table (A2) ❑� Saturation (A3) ❑ Water Marks (131) ❑ Sediment Deposits (132) ❑ Drift Deposits (133) ❑ Algal Mat or Crust (64) ❑ Iron Deposits (135) ❑ Surface Soil Cracks (136) Field Observations: Surface Water Present? Yes O No ❑ Inundation Visible on Aerial Imagery (67; ❑ Sparsely Vegetated Concave Surface (138; ❑ Marl Deposits (615) ❑ Hydrogen Sulfide Odor (Cl) ❑ Dry -Season Water Table (C2) ❑ Other (Explain in Remarks) Depth (inches): Hydric Soil Present? Yes O No O Secondary Indicators (two or more are required) ❑ Water Stained Leaves (139) ❑ Drainage Patterns (1310) ❑ Oxidized Rhizospheres along Living Roots (0) ❑ Presence of Reduced Iron (C4) ❑ Salt Deposits (C5) ❑ Stunted or Stressed Plants (131) ❑ Geomorphic Position (132) ❑ Shallow Aquitard (D3) ❑ Microtopographic Relief (134) ❑ FAC-neutral Test (D5) Water Table Present? Yes* No O Depth (inches): 10 Wetland Hydrology Present? Yes * No O Saturation Present? Yes 0 No O Depth (inches): 2 (includes cagillary fringe) Describe Recorded Data (stream gauge, monitor well, aerial photos, previous inspection) if available: Remarks: Pit filled with water despite steep slope. May be due to heavy rain. U.S. Army Corps of Engineers Alaska Version 2.0 Appendix B. Site Photos ABR, Inc.—Chenega Bay Study 29 SITE PHOTOGRAPHS g" . y CH11-01: Palustrine Saturated Needle -leaf Evergreen Forest Hydrology: High water table, saturation NWI Class: PF04B Soils: Histosol CHII-02: Palustrine Seasonally Flooded/Saturated Emergent Meadow NWI Class: PEM1E CHII-03: Upland NWI Class: U Hydrology: Surface water Soils: Inundated Hydrology: Saturation, high water table Soils: Histic epipedon aak�, �i_ J�17 ey •.. � Y - fit, ��` 'i.. hR r ' '� Aw AL CH11-07: Palustrine Seasonally Flooded/Saturated Emergent- Hydrology: Surface water, saturation, high water table Needleaf Evergreen Meadow NWI Class: PEM1/SS4E Soils: Histosol CH11-08: Intermittent Stream NWI Class: R4SBC CH11-09: Upland NWI Class: U Hydrology: Running water Soils: Inundated Hydrology: Saturation at surface due to heavy rain Soils: Organics over silt loam CHV11-01: Upland NWI Class: U CHV11-03: Upland NWI Class: U CHV11-02: Upland NWI Class: U Appendix C. Functional Assessment Forms ABR, Inc. Chenega Bay Study 35 Wetland Functions Data Form -Alaska Regulatory Best Professional Judgment Characterization (Modified by ABR, Inc. -Environmental Research & Services; March 2009) File #:Chenega Bay Date:12/1/2011 Wetland:PF04B PM/RS: WAD A. Flood Flow Regulation (Storage and Desynchronization) Likely or not likely to Provide (Y or N): Y Rating: HIGH 1. Wetland is capable of retaining much higher volumes of water during 1. Y storm events than under normal rainfall conditions. 2. N 2. Wetland is a closed (depressional) system subject to flooding or 3. N shows evidence of flooding. 4. Y 3. If flow -through, wetland has constricted outlet with signs of fluctuating 5. Y water levels, algal mats, and/or lodged debris. 6. Y 4. Wetland has dense (>40% cover) woody vegetation. 5. Wetland receives floodwater from an adjacent water course at least once every 10 years. > 4 attributes (Y)-High Function 6. Floodwaters enter and flow through wetland predominantly as sheet 2-3 attributes (Y)-Moderate Function flow rather than channel flow. 0-1 attributes (Y)-Low Function B. Sediment, Nutrient (N and P), Toxicant Removal Likely or not likely to Provide (Y or N): N Rating: LOW -MODERATE 1. Sediment, nutrients and/or toxicants (from tillage, mining, 1. Y construction or other sources of pollution) appear to be or are likely to 2' N 3. N be entering the wetland. 4. N 2. Slow -moving or still water is present or occurs during flooding that 5. N happens at least once every 10 years. 6. Y 3. Dense (>50% cover) herbaceous vegetation is present. 4. At least moderate interspersion of vegetation and water is present or occurs during flooding that happens at least once every 10 years. > 4 attributes (Y)-High Function 5. Sediment deposits are present (evidence of deposition during floods). 2-3 attributes (Y)-Moderate Function 6. Thick surface organic horizon and/or abundant fine organic litter is 0-1 attributes (Y)-Low Function present. C. Erosion Control and Shoreline Stabilization Likely or not likely to Provide (Y or N): Y (Only assess if directly abuts permanent or relatively permanent water) Rating: MODERATE 1. Wetland has dense, energy absorbing vegetation (trees, shrubs) 1.Y bordering the water course and no evidence of erosion. 2.N 2. An at least moderately dense herbaceous layer is present. 1-2 attributes (Y)-High Function None -Low Function D. Production of Organic Matter and its Export Likely or not likely to Provide (Y or N): Y Rating: LOW -MODERATE 1. Wetland has at least 30% cover of herbaceous vegetation. 1. Y 2. Woody plants in wetland are mostly deciduous. 2. N 3. High degree of plant community structure, vegetation density, and 3. N species richness present. 4. N 5. Y 4. Interspersion of vegetation and water is at least moderate. 6. N 5. Wetland is flooded at least once every 10 years. 6. A more than minimal amount of organic matter is flushed from the wetland by water flow at least once every 10 years. >_ 4 attributes (Y)-High Function 2-3 attributes (Y)-Moderate Function 0-1 attributes (Y)-Low Function If Function 5 or 6 is N, then automatically low function E. General Habitat Suitability Likely or not likely to Provide (Y or N): N Rating: LOW 1. Wetland is not fragmented by development. 1.N 2. Upland surrounding wetland is undisturbed. 2. N 3. Diversity (evenness of cover) of plant species is moderately high (>_5 3. N species with at least 10% cover each). 4. Y 4. Plant community has two or more strata, with at least two of those 5. N strata having >10% total cover. 6. N 5. Wetland has at least a moderate degree of Cowardin Class interspersion. 6. Evidence of wildlife use (e.g., nests, tracks, scat, gnawed stumps, > 5 attributes (Y)-High Function survey data) is present. 2-4 attributes (Y)-Moderate Function 0-1 attributes (Y)-Low Function F. General Fish Habitat (must be associated with a fish -bearing Likely or not likely to Provide (Y or N): N/A stream) Rating: 1. Wetland has perennial or intermittent surface water connection to a 1. fish -bearing water body. 2. 2. Wetland has sufficient size and depth of open water so as not to 3. freeze completely during winter. 4. 3. Fish are present or are known to be present. 5. 4. Herbaceous and/or woody vegetation is present in wetland and/or 6. buffer to provide cover, shade, and/or detrital matter. 5. Spawning areas are present (aquatic vegetation and/or gravel beds >_ 5 attributes (Y)-High Function 6. Juvenile rest areas present (e.g. pools with organic debris or 3-4 attributes (Y)-Moderate Function overhanging vegetation). 0-2 attributes (Y)-Low Function G. Native Plant Richness Likely or not likely to Provide (Y or N): N Rating: LOW 1. At least 20 native plant species occur in the wetland 1. N 2. Wetland contains two or more Cowardin Classes. 2. N 3. Wetland has three or more strata of vegetation with at least 10% 3. N cover in each stratum. >_ 2 attributes (Y)-High Function 1 attribute (Y)-Moderate Function None -Low Function H. Educational, Scientific, Recreational, or Subsistence Use Likely or not likely to Provide (Y or N): N Rating: LOW 1. Site has documented scientific or educational use. 1. N 2. Wetland is in public ownership. 2. Y 3. Accessible trails are available. 3. Y 4. Wetland supports subsistence activities (e.g., hunting, fishing, berry 4. N picking). >_ 2 attributes (Y)-High Function 1 attribute (Y)-Moderate Function None -Low Function I. Uniqueness and Special Status Likely or not likely to Provide (Y or N): N Rating: LOW 1. Wetland contains documented occurrence of a state or federally 1. N listed threatened or endangered species. 2. N 2. Wetland contains documented critical habitat, high quality 3. N ecosystems, or priority species, respectively designated by the U.S. 4. N Fish and Wildlife Service 3. Wetland has biological, geological, or other features that are >_ 2 attributes (Y)-High Function determined to be rare. 1 attribute (Y)-Moderate Function 4. Wetland has been determined significant because it provides None -Low Function functions scarce for the area. If attribute 1 is Y, then automatically High Function Wetland Functions Data Form -Alaska Regulatory Best Professional Judgment Characterization (Modified by ABR, Inc. -Environmental Research & Services; March 2009) File #:Chenega Bay Date:12/1/2011 Wetland:PEM1E, PEM/SS4E, R4SBC PM/RS: WAD A. Flood Flow Regulation (Storage and Desynchronization) Likely or not likely to Provide (Y or N): Y Rating: HIGH 1. Wetland is capable of retaining much higher volumes of water during 1. Y storm events than under normal rainfall conditions. 2. N 2. Wetland is a closed (depressional) system subject to flooding or 3. Y shows evidence of flooding. 4. Y 3. If flow -through, wetland has constricted outlet with signs of fluctuating 5. N water levels, algal mats, and/or lodged debris. 6. Y 4. Wetland has dense (>40% cover) woody vegetation. 5. Wetland receives floodwater from an adjacent water course at least once every 10 years. > 4 attributes (Y)-High Function 6. Floodwaters enter and flow through wetland predominantly as sheet 2-3 attributes (Y)-Moderate Function flow rather than channel flow. 0-1 attributes (Y)-Low Function B. Sediment, Nutrient (N and P), Toxicant Removal Likely or not likely to Provide (Y or N): Y Rating: HIGH 1. Sediment, nutrients and/or toxicants (from tillage, mining, 1. Y construction or other sources of pollution) appear to be or are likely to 2' Y 3. Y be entering the wetland. 4. Y 2. Slow -moving or still water is present or occurs during flooding that 5. Y happens at least once every 10 years. 6. Y 3. Dense (>50% cover) herbaceous vegetation is present. 4. At least moderate interspersion of vegetation and water is present or occurs during flooding that happens at least once every 10 years. > 4 attributes (Y)-High Function 5. Sediment deposits are present (evidence of deposition during floods). 2-3 attributes (Y)-Moderate Function 6. Thick surface organic horizon and/or abundant fine organic litter is 0-1 attributes (Y)-Low Function present. C. Erosion Control and Shoreline Stabilization Likely or not likely to Provide (Y or N): Y (Only assess if directly abuts permanent or relatively permanent water) Rating: HIGH 1. Wetland has dense, energy absorbing vegetation (trees, shrubs) 1. N bordering the water course and no evidence of erosion. 2.Y 2. An at least moderately dense herbaceous layer is present. 1-2 attributes (Y)-High Function None -Low Function D. Production of Organic Matter and its Export Likely or not likely to Provide (Y or N): Y Rating: HIGH 1. Wetland has at least 30% cover of herbaceous vegetation. 1. Y 2. Woody plants in wetland are mostly deciduous. 2. N 3. High degree of plant community structure, vegetation density, and 3. N species richness present. 4. Y 5. Y 4. Interspersion of vegetation and water is at least moderate. 6. Y 5. Wetland is flooded at least once every 10 years. 6. A more than minimal amount of organic matter is flushed from the wetland by water flow at least once every 10 years. >_ 4 attributes (Y)-High Function 2-3 attributes (Y)-Moderate Function 0-1 attributes (Y)-Low Function If Function 5 or 6 is N, then automatically low function E. General Habitat Suitability Likely or not likely to Provide (Y or N): Y Rating: MODERATE 1. Wetland is not fragmented by development. 1. N 2. Upland surrounding wetland is undisturbed. 2. N 3. Diversity (evenness of cover) of plant species is moderately high (>_5 3. Y species with at least 10% cover each). 4. N 4. Plant community has two or more strata, with at least two of those 5. Y strata having >10% total cover. 6. N 5. Wetland has at least a moderate degree of Cowardin Class interspersion. 6. Evidence of wildlife use (e.g., nests, tracks, scat, gnawed stumps, > 5 attributes (Y)-High Function survey data) is present. 2-4 attributes (Y)-Moderate Function 0-1 attributes (Y)-Low Function F. General Fish Habitat (must be associated with a fish -bearing Likely or not likely to Provide (Y or N): N stream) Rating: LOW 1. Wetland has perennial or intermittent surface water connection to a 1.Y fish -bearing water body. 2.N 2. Wetland has sufficient size and depth of open water so as not to 3.N freeze completely during winter. 4.N 3. Fish are present or are known to be present. 5.N 4. Herbaceous and/or woody vegetation is present in wetland and/or 6.Y buffer to provide cover, shade, and/or detrital matter. 5. Spawning areas are present (aquatic vegetation and/or gravel beds >_ 5 attributes (Y)-High Function 6. Juvenile rest areas present (e.g. pools with organic debris or 3-4 attributes (Y)-Moderate Function overhanging vegetation). 0-2 attributes (Y)-Low Function G. Native Plant Richness Likely or not likely to Provide (Y or N): Y Rating: HIGH 1. At least 20 native plant species occur in the wetland 1. Y 2. Wetland contains two or more Cowardin Classes. 2. Y 3. Wetland has three or more strata of vegetation with at least 10% 3. N cover in each stratum. >_ 2 attributes (Y)-High Function 1 attribute (Y)-Moderate Function None -Low Function H. Educational, Scientific, Recreational, or Subsistence Use Likely or not likely to Provide (Y or N): N Rating: LOW -MODERATE 1. Site has documented scientific or educational use. 1. N 2. Wetland is in public ownership. 2. Y 3. Accessible trails are available. 3. Y 4. Wetland supports subsistence activities (e.g., hunting, fishing, berry 4. N picking). >_ 2 attributes (Y)-High Function 1 attribute (Y)-Moderate Function None -Low Function I. Uniqueness and Special Status Likely or not likely to Provide (Y or N): N Rating: LOW 1. Wetland contains documented occurrence of a state or federally 1. N listed threatened or endangered species. 2. N 2. Wetland contains documented critical habitat, high quality 3. N ecosystems, or priority species, respectively designated by the U.S. 4. N Fish and Wildlife Service 3. Wetland has biological, geological, or other features that are >_ 2 attributes (Y)-High Function determined to be rare. 1 attribute (Y)-Moderate Function 4. Wetland has been determined significant because it provides None -Low Function functions scarce for the area. If attribute 1 is Y, then automatically High Function Wetland Functions Data Form -Alaska Regulatory Best Professional Judgment Characterization (Modified by ABR, Inc. -Environmental Research & Services; March 2009) File #:Chenega Bay Date:12/1/2011 Wetland:R3UBH PM/RS:WAD A. Flood Flow Regulation (Storage and Desynchronization) Likely or not likely to Provide (Y or N): Y Rating: HIGH 1. Wetland is capable of retaining much higher volumes of water during 1. Y storm events than under normal rainfall conditions. 2. N 2. Wetland is a closed (depressional) system subject to flooding or 3. Y shows evidence of flooding. 4. N 3. If flow -through, wetland has constricted outlet with signs of fluctuating 5. Y water levels, algal mats, and/or lodged debris. 6. Y 4. Wetland has dense (>40% cover) woody vegetation. 5. Wetland receives floodwater from an adjacent water course at least once every 10 years. > 4 attributes (Y)-High Function 6. Floodwaters enter and flow through wetland predominantly as sheet 2-3 attributes (Y)-Moderate Function flow rather than channel flow. 0-1 attributes (Y)-Low Function B. Sediment, Nutrient (N and P), Toxicant Removal Likely or not likely to Provide (Y or N): N Rating: LOW 1. Sediment, nutrients and/or toxicants (from tillage, mining, 1. Y construction or other sources of pollution) appear to be or are likely to 2' N 3. N be entering the wetland. 4. N 2. Slow -moving or still water is present or occurs during flooding that 5. Y happens at least once every 10 years. 6. N 3. Dense (>50% cover) herbaceous vegetation is present. 4. At least moderate interspersion of vegetation and water is present or occurs during flooding that happens at least once every 10 years. > 4 attributes (Y)-High Function 5. Sediment deposits are present (evidence of deposition during floods). 2-3 attributes (Y)-Moderate Function 6. Thick surface organic horizon and/or abundant fine organic litter is 0-1 attributes (Y)-Low Function present. C. Erosion Control and Shoreline Stabilization Likely or not likely to Provide (Y or N): N/A (Only assess if directly abuts permanent or relatively permanent water) Rating: 1. Wetland has dense, energy absorbing vegetation (trees, shrubs) 1. bordering the water course and no evidence of erosion. 2. 2. An at least moderately dense herbaceous layer is present. 1-2 attributes (Y)-High Function None -Low Function D. Production of Organic Matter and its Export Likely or not likely to Provide (Y or N): N Rating: LOW 1. Wetland has at least 30% cover of herbaceous vegetation. 1. N 2. Woody plants in wetland are mostly deciduous. 2. N 3. High degree of plant community structure, vegetation density, and 3. N species richness present. 4. N 5. Y 4. Interspersion of vegetation and water is at least moderate. 6. N 5. Wetland is flooded at least once every 10 years. 6. A more than minimal amount of organic matter is flushed from the wetland by water flow at least once every 10 years. >_ 4 attributes (Y)-High Function 2-3 attributes (Y)-Moderate Function 0-1 attributes (Y)-Low Function If Function 5 or 6 is N, then automatically low function E. General Habitat Suitability Likely or not likely to Provide (Y or N):Y Rating: LOW 1. Wetland is not fragmented by development. 1. Y 2. Upland surrounding wetland is undisturbed. 2. N 3. Diversity (evenness of cover) of plant species is moderately high (>_5 3. N species with at least 10% cover each). 4. N 4. Plant community has two or more strata, with at least two of those 5. N strata having >10% total cover. 6. N 5. Wetland has at least a moderate degree of Cowardin Class interspersion. 6. Evidence of wildlife use (e.g., nests, tracks, scat, gnawed stumps, > 5 attributes (Y)-High Function survey data) is present. 2-4 attributes (Y)-Moderate Function 0-1 attributes (Y)-Low Function F. General Fish Habitat (must be associated with a fish -bearing Likely or not likely to Provide (Y or N): Y stream) Rating: HIGH 1. Wetland has perennial or intermittent surface water connection to a 1.Y fish -bearing water body. 2.N 2. Wetland has sufficient size and depth of open water so as not to 3.Y freeze completely during winter. 4.Y 3. Fish are present or are known to be present. 5.Y 4. Herbaceous and/or woody vegetation is present in wetland and/or 6.Y buffer to provide cover, shade, and/or detrital matter. 5. Spawning areas are present (aquatic vegetation and/or gravel beds >_ 5 attributes (Y)-High Function 6. Juvenile rest areas present (e.g. pools with organic debris or 3-4 attributes (Y)-Moderate Function overhanging vegetation). 0-2 attributes (Y)-Low Function G. Native Plant Richness Likely or not likely to Provide (Y or N): N Rating: LOW 1. At least 20 native plant species occur in the wetland 1. N 2. Wetland contains two or more Cowardin Classes. 2. N 3. Wetland has three or more strata of vegetation with at least 10% 3. N cover in each stratum. >_ 2 attributes (Y)-High Function 1 attribute (Y)-Moderate Function None -Low Function H. Educational, Scientific, Recreational, or Subsistence Use Likely or not likely to Provide (Y or N): Y Rating: HIGH 1. Site has documented scientific or educational use. 1. N 2. Wetland is in public ownership. 2. Y 3. Accessible trails are available. 3. Y 4. Wetland supports subsistence activities (e.g., hunting, fishing, berry 4. Y picking). >_ 2 attributes (Y)-High Function 1 attribute (Y)-Moderate Function None -Low Function I. Uniqueness and Special Status Likely or not likely to Provide (Y or N): N Rating: LOW 1. Wetland contains documented occurrence of a state or federally 1. N listed threatened or endangered species. 2. N 2. Wetland contains documented critical habitat, high quality 3. N ecosystems, or priority species, respectively designated by the U.S. 4. N Fish and Wildlife Service 3. Wetland has biological, geological, or other features that are >_ 2 attributes (Y)-High Function determined to be rare. 1 attribute (Y)-Moderate Function 4. Wetland has been determined significant because it provides None -Low Function functions scarce for the area. If attribute 1 is Y, then automatically High Function