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Vantage to Pomona Heights Chapter 4 <br />230 kV Transmission Line Project FEIS Environmental Consequences <br /> <br /> PAGE 4-97 <br />degradation, as described in Section 4.3.3.1. Impact levels to habitat are expected to be low for 16.5 miles <br />and moderate for 5.2 miles (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 />3b would require an estimated 181 structures, of which 160 structures would be located greater than 0.25 <br />mile from an existing transmission line (Table 4.3-5). <br />Within 1.0 mile of Route Segment 3b, potentially suitable habitat is present for 66 special status wildlife <br />species that are possible, likely, or known to occur (Tables 3.3-2, 3.3-3, and 3.3-7). Potential impacts and <br />RDFs to address them are discussed in Sections 4.3.3.1 and 4.3.3.2. Species or wildlife resources that <br />have been documented at specific locations within 1.0 mile of Route Segment 3b include critical habitat <br />for bull trout, Chinook salmon, and steelhead; occurrences of striped whipsnake, night snake, sagebrush <br />lizard, loggerhead shrike, American white pelican, black-tailed jackrabbit, pallid bat, and regular <br />concentrations of chukar, mule deer, waterfowl, and common loons; and a breeding colony of black- <br />crowned night herons and great blue herons. Basalt cliffs and bluffs provide nesting substrates for raptors <br />and several nests of golden eagles, peregrine falcons, and prairie falcons. Bald eagles nest and winter <br />within one mile of the route segment. <br />The Hanford Reach supports the larger of the only two remaining healthy naturally spawning fall <br />Chinook salmon populations in the Columbia River System (Nugent et al. 2002). Route Segment 3b <br />parallels the Hanford Reach for 2.7 miles to the Priest Rapids Dam. No structure or road construction <br />work would occur directly within the Columbia River. For the Columbia River crossing the structures <br />would be approximately 200 foot tall lattice steel structures for the up to 2,800 foot crossing. Impacts to <br />Chinook salmon from the construction of Route Segment 3b could include increased erosion, <br />sedimentation and elevated turbidity. The potential for impacts would be minimized by implementing <br />RDFs that apply and maintain standard erosion and sediment control methods. Specific erosion and <br />sediment control measures and locations would be specified in the SWPPP. These may include straw <br />wattles, straw bale barriers, and silt fencing which would be placed at construction boundaries. The <br />implementation of RDFs is anticipated to be effective at minimizing impacts. Impact levels are expected <br />to be low for the entire route segment. <br />Critical habitats for bull trout, the Columbia River Chinook salmon ESU, and the Upper Columbia River <br />steelhead DPS occur within 1.0 mile of Route Segment 3b in the Columbia River. Tributaries of the <br />Columbia River in and near the Project area are not part of the Upper Columbia River Spring Run <br />Chinook salmon ESU; they are part of the Mid-Columbia River Spring Run Chinook salmon ESU which <br />is not listed under the ESA (NOAA 2013). Aside from the Columbia River, it is unlikely that spawning <br />occurs in streams within the Project area. Bull trout and Chinook salmon are not known to spawn within <br />streams within the Project area because the streams are too small and not cold enough over a long enough <br />time period to provide suitable spawning and rearing habitat; however, bull trout could use streams for <br />short periods for foraging (AECOM Environmental 2010). No structure or road construction work would <br />occur directly within the Columbia River. Erosion would be minimized by applying and maintaining <br />standard erosion and sediment control methods. The implementation of RDFs is anticipated to be <br />effective at minimizing impacts to all three species. No identifiable impacts to the three species or their <br />habitats are anticipated to occur through construction, operation, and maintenance of the proposed <br />Project. <br />Striped whipsnake, night snake, and sagebrush lizard have been documented within one mile of Route <br />Segment 3b. Potential impacts to these three species include direct habitat loss, indirect habitat loss or