Laserfiche WebLink
Vantage to Pomona Heights Chapter 4 <br />230 kV Transmission Line Project FEIS Environmental Consequences <br /> PAGE 4-79 <br />Twenty-six special status species have been documented to occur within the Project study area, with one <br />or more locations occurring in every route segment. Impacts related to these occurrence areas and RDFs <br />to minimize impacts are described in Section 4.3.3.5 State-listed and Other Special Status Species and in <br />Section 4.3.4 Impacts Specific to Route Segments. <br />The Action Alternatives do not pass through any special management areas, but one or more special <br />management areas occur within one mile of each Action Alternative—the Columbia National Wildlife <br />Refuge (at Route Segment 3c), Hanford Reach National Monument (at Route Segment 3c), Columbia <br />Basin State Wildlife Area (at Route Segments 3b and 3c), and Wenas Wildlife Area (at Route Segment <br />NNR-3). Impacts to Special Management areas are discussed in Section 4.6 Special Management Areas. <br />4.3.4 Impacts Specific to Route Segments <br />Impacts to habitat and species are discussed below for each route segment. Digital element occurrence <br />records for PHS documented within the analysis area were obtained from WDFW in June 2014 (WDFW <br />2014). A map showing special status wildlife locations and management areas is included in Appendix A; <br />however, due to the sensitive nature of location information, certain locations (such as nest locations) are <br />not shown and this map is presented at a small-scale (WDFW 2011b; Guggenmos 2012). <br />4.3.4.1 Route Segment 1a/NNR-1 <br />Approximately 3.5 acres of long-term and 9.2 acres of short-term disturbance would occur through the <br />construction of Route Segment 1a/NNR-1. The majority of disturbance for this route segment would <br />occur in habitat that has been disturbed in the past and is currently dominated by rabbitbrush <br />(Chrysothamnus viscidiflorus and Ericameria nauseosa; 4.8 acres long-term disturbance), exotic annual <br />grasses (0.3 acre long-term and 1.3 acres short-term), and developed areas, such as agricultural and <br />residential areas (0.4 acre long-term and 2.2 acres short-term; Table 4.3-4). The remaining 3.7 acres of <br />long-term disturbance would occur within areas classified as sagebrush/perennial grassland. RDFs would <br />be implemented to minimize further habitat degradation, as described in Section 4.3.3.1. Impact levels to <br />habitat are expected to be low for 1.7 miles and moderate for 0.7 mile (sagebrush/perennial grassland). <br />The presence of new transmission line structures, which could provide additional perch and/or nesting <br />sites for avian predators, could negatively impact nearby prey species such as small mammals and avian <br />species, particularly when the new structures are built in an area where perching opportunities currently <br />do not exist (i.e., greater than 0.25 mile from existing structures or trees). Construction of Route Segment <br />1a/NNR-1 would require an estimated 31 structures in a landscape dominated by low growing grasses and <br />shrubs. An estimated 14 new structures would be located greater than 0.25 mile from an existing <br />transmission line or trees (Table 4.3-5). <br />Within one mile of Route Segment 1a/NNR-1, potentially suitable habitat is present for 54 special status <br />wildlife species that are possible, likely, or known to occur (Tables 3.3-2, 3.3-3, and 3.3-7). Potential <br />impacts and RDFs to address them are discussed in Sections 4.3.3.1 and 4.3.3.2. Species or wildlife <br />resources that have been documented at specific locations within one mile of Route Segment 1a/NNR-1 <br />include bull trout critical habitat, steelhead critical habitat (Middle Columbia River DPS), a bald eagle <br />nest, and the Selah Waterfowl Concentration Area/Selah Gravel Pit Wetlands. <br />Critical habitat for bull trout occurs within one mile of Route Segment 1a/NNR-1 in the Yakima River. <br />Bull trout are not known to spawn within streams within the Project area because the streams are too <br />small and not cold enough over a long enough time period to provide suitable spawning and rearing <br />habitat; however, bull trout could use streams for short periods for foraging (AECOM Environmental <br />2010). No structure or road construction work would occur directly within the Yakima River. Erosion <br />would be minimized by applying and maintaining standard erosion and sediment control methods. The