4.7. Wetlands, Riparian, and Littoral Resources

4.7. Wetlands, Riparian, and Littoral Resources

PRE-APPLICATION DOCUMENT 4.7. Wetlands, Riparian, and Littoral Resources 4.7.1. Introduction This section describes the wetlands, riparian, and littoral habitat areas surrounding, and potentially affected by, the Project and conforms to the content requirements of 18 CFR § 5.6(d)(3)(vi). The assessment area includes potential effects, both direct and indirect, caused by access road and transmission-line corridors; hydrologic changes, including flooding of terrestrial areas; dam facilities; and filled areas. The information presented in this section relies heavily on the findings of studies conducted for the APA Project in the early 1980s, as summarized in the reports cited below and in the draft amended FERC license application (APA 1985). Additional information is incorporated from the terrestrial wildlife data-gap analysis completed for the Project (ABR 2011). 4.7.1.1. Wetlands and Littoral Habitats A cooperative agreement between the APA and the USFWS in the 1980s resulted in the production of a preliminary wetlands map of the APA Project area at a scale of 1:63,360, through the National Wetlands Inventory (NWI) program (USFWS 1984). The NWI maps for the APA Project area were based on the vegetation mapping done by McKendrick et al. (1982), and incorporated additional modifications from stereoscopic interpretation of aerial photos. The original vegetation classes were converted into wetland classes using the classification scheme of Cowardin et al. (1979). Although the APA Project differs from the currently proposed Project, wetlands constituted <10 percent of the project area habitats for the original APA Project (APA 1985). Wetland types in the project area consisted of Riverine (rivers, creeks, and gravel bars) and Palustrine wetlands (bogs, marshes, forested lowlands, shrublands, and meadows) and open waters (ponds), but were dominated by Palustrine forested and scrub–shrub and Riverine habitats. No lakes (and therefore, littoral habitats) were considered likely to be impacted directly by the APA Project. Because mapping was not finalized by the time the amended license application (APA 1985) was submitted to FERC, a table of wetland classes identified during the APA Project study was prepared and is reproduced here as the best summary of wetlands occurrence in the area of the proposed Project (Table 4.7-1).The plant species most commonly found in wetlands in the project area are listed in Table 4.7-1 and descriptions of wetland vegetation types are provided in Section 4.6 (Botanical Resources). An update of mapping of existing wetlands has not been conducted yet for the Project. Figures 4.7-1 and 4.7-2 provide an indication of the occurrence of wetland habitats in areas potentially affected by the project. Susitna-Watana Hydroelectric Project Alaska Energy Authority FERC Project No. 14241 Page 4-226 December 2011 PRE-APPLICATION DOCUMENT Table 4.7-1. Wetlands (NWI classes1) mapped for the APA Susitna Hydroelectric Project (adapted from USFWS 1984). NWI Class / NWI Code Description Lacustrine (Lakes) L1UBH Permanently flooded, open-water areas greater than 8.1 hectares (20 ac) in size. The water depth usually exceeds 2 m (6.6 ft). Riverine (Rivers and Streams) R3UBH (formerly R3OWH) Permanently flooded, open-water channels of upper perennial rivers and streams. R3USC Seasonally flooded river flats and bars within upper perennial river channels. Palustrine (Ponds) PUBH (POWH) Permanently flooded, small open waterbodies (ponds). Vegetation is generally lacking within the open-water area, but aquatic beds or emergents may provide sparse cover (<30 percent) along the pond edge. PUB/AB3H (formerly Permanently flooded ponds supporting aquatic (floating- leaved) vegetation. POW/AB3H) Dominant plants include yellow pond lily (Nuphar polysepala) and pondweed (Potamogeton spp.). Palustrine Wetlands PEM1B Saturated, emergent, bog-type wetlands in depressions below the tree line, and high-elevation sedge–grass tundra areas on poorly drained soils. Common emergent species include cottongrass (Eriophorum spp.), sedges (Carex spp.), and bluejoint (Calamagrostis canadensis). PEM1C Seasonally flooded emergent marshes occurring in the floodplain of small streams and on the periphery of ponds and lakes. Surface water is present in these areas for 1–2 months during the growing season. Species of primary importance include sedges, cottongrass, bluejoint, and horsetails (Equisetum spp.). PEM1F Semipermanently flooded emergent marshes. These marsh areas usually exhibit standing water throughout the growing season in most years. This wetland type usually occurs in wetter portions of typical emergent and shrub bog situations, and along the periphery of ponds and lakes. Dominant vegetation includes water sedge (Carex aquatilis), marsh horsetail (Equisetum palustre), buckbean (Menyanthes trifoliata), marsh cinquefoil (Potentilla palustris), and rushes (Juncus spp.). PEM1H Permanently flooded emergent marshes. These areas exhibit standing water throughout the year in all years. The dominant vegetation consists of water sedge, horsetails, and buckbean. Palustrine Scrub–Shrub Wetlands PSS1A Temporarily flooded, dense shrub areas on river and stream floodplains consisting primarily of willows (Salix spp.) and alders (Alnus spp.). This wetland type often occurs on riverbars that have become stable enough to Susitna-Watana Hydroelectric Project Alaska Energy Authority FERC Project No. 14241 Page 4-227 December 2011 PRE-APPLICATION DOCUMENT NWI Class / NWI Code Description support persistent woody vegetation. PSS1/USA Temporarily flooded areas on river and stream floodplains consisting of a mix of shrubs and unvegetated riverine flats. Shrub species are primarily willows and alders. PSS1B Saturated, dense shrub wetlands usually occurring in seepage areas on slopes. Tall willow and alder are the most common species. PSS1/EM1B Saturated bogs and moist tundra areas on poorly drained soil with 30 percent or more of the canopy consisting of low broad-leaved deciduous shrubs. The remaining portion of the canopy consists of persistent emergent vegetation. Common shrub species include dwarf birch (Betula nana), resin birch (B. glandulosa), willows, bog blueberry (Vaccinium uliginosum), Labrador tea (Ledum groenlandicum), crowberry (Empetrum nigrum), bog rosemary (Andromeda polifolia), and bearberry (Arctostaphylos spp.). Dominant emergent species include cottongrass, sedges, and bluejoint. PSS1/EM1C Seasonally flooded areas occurring on floodplains in stream and creek corridors. These wetlands are characterized by a mixture of broad-leaved deciduous shrubs and emergent vegetation. Common shrubs include tall willow and alder. Emergent species of primary importance include sedges, cottongrass, bluejoint, and horsetails. PSS1/EM1F Patterned bogs (string bogs and reticulate bogs) and other semipermanently flooded complexes of emergents and broad-leaved deciduous shrubs. This wetland type is sometimes found in areas influenced by beaver activity. In patterned bog areas, the shrub species include those described for PSSI/EMIB wetlands. Dominant emergent species include sedges, horsetails, marsh cinquefoil, buckbean, and rushes. PSS4B Saturated, closed-canopy black spruce (Picea mariana) scrub wetlands. The black spruce in these areas is less than 6 m in height. PSS4/EM1B Saturated, open-canopy black spruce scrub wetlands with an emergent understory. PSS4/1B Saturated, open-canopy black spruce scrub wetlands with a dense deciduous shrub understory. The deciduous shrub species include dwarf birch, Labrador tea, bog blueberry, and willows. Palustrine Forested Wetlands PFO4B Saturated, black spruce forested wetlands. These areas are characterized by a closed canopy of black spruce. PFO4/SS1B Saturated, open-canopy black spruce forested wetlands with an understory of broad-leaved deciduous shrubs. The areal coverage of the black spruce is between 30 percent and 50 percent. PFO4/SS4B Saturated, open-canopy black spruce forested wetland with an understory of scrub black spruce. PFO4/SS1A Temporarily flooded wetlands adjacent to streams and rivers that are a complex of black spruce on higher terraces and deciduous shrubs on lower terraces. Willows and alders are the common shrub species. Susitna-Watana Hydroelectric Project Alaska Energy Authority FERC Project No. 14241 Page 4-228 December 2011 PRE-APPLICATION DOCUMENT NWI Class / NWI Code Description PFO4/EM1B Saturated, open-canopy black spruce forested wetlands with an emergent understory. PFO4/1B Saturated, closed-canopy forested wetlands consisting of a mix of broad- leaved deciduous and needle-leaved evergreen trees. Black cottonwood (Populus trichocarpa) and balsam poplar (P. balsamifera) are the dominant deciduous species. Black spruce is the dominant evergreen species. PFO1A Temporarily flooded, deciduous forest wetlands occurring on river floodplains. Balsam poplar and black cottonwood are the common trees on these sites. PFO1/SS1A Temporarily flooded wetlands on river and stream floodplains consisting of a mix of broad- leaved deciduous forest and broad-leaved deciduous shrubs. Dominant tree species are balsam poplar and black cottonwood. Willows and alders are the dominant species in the shrub areas. PFO5C Seasonally flooded, dead-tree forested wetlands generally found along streams and small rivers. The dead trees usually result from beaver activity. 1 NWI = National Wetland Inventory (based on the Classification of Wetlands and Deepwater Habitats of the United States, Cowardin et al. 1979). NWI codes

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