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Vantage to Pomona Heights Chapter 4 <br />230 kV Transmission Line Project FEIS Environmental Consequences <br /> <br /> PAGE 4-100 <br />for 6.5 miles, impact levels on golden eagles are anticipated to be moderate for 2.3 miles, and impact <br />levels on prairie falcons are expected to be moderate for 10.2 miles. <br />Route Segment 3b also crosses 10.2 miles of JBLM YTC’s Bald Eagle Protection Area and 0.6 mile of <br />WDFW’s Bald Eagle Management Zone. Bald eagles are known to winter along the Columbia River’s <br />western edge. Roosting bald eagles have been documented within one mile of Route Segment 3b at <br />Borden Springs, Hanson Creek, and Alkali Canyon Creek. Habitat in Borden Springs and Alkali Canyon <br />has been altered by fires occurring in 1996. Two suitable roost trees remained and were utilized at Borden <br />Springs following the fire, while no evidence of roosting at Alkali Canyon Creek has been documented <br />since the fire. Bald eagles wintering in the area have been observed foraging along Priest Rapids <br />Reservoir during the day. Wintering bald eagles are typically present from between November and April, <br />with peak abundance occurring in February (JBLM YTC 2002). Noise from construction equipment and <br />general construction activities could disturb and displace wintering bald eagles. It is anticipated that no <br />large trees suitable for roosting, perching and nesting would be removed. As described in Sections 4.3.3.1 <br />and 4.3.3.2, RDFs would be implemented to reduce short- and long-term impacts and include avoidance <br />of bald eagle winter roost areas between 8 am and 5 pm during the winter roosting season. With the <br />implementation of RDFs, the impact on wintering eagles is anticipated to include 10.5 miles of moderate <br />and 11.2 miles of low impacts. <br />The majority of the habitat disturbance associated with Route Segment 3b would be located within the <br />Regularly Occupied Habitat MU for Sage-Grouse (107.9 acres) with the remainder of disturbance within <br />Occasionally Occupied Habitat MU (20.5 acres). Construction activities would disturb less than one <br />percent of Regularly Occupied Habitat (Table 4.3-7). Anticipated ground disturbance includes 26.9 acres <br />of suitable Sage-Grouse habitat, 8.0 acres of marginal habitat, and 72.9 acres of unsuitable habitat (Table <br />4.3-8). With the implementation of RDFs (Sections 4.3.3.1 and 4.3.3.2), the scale of disturbance and <br />degradation to Sage-Grouse habitat is anticipated to be low for 18.4 miles and moderate for 3.3 miles. <br />Construction of Route Segment 3b would require an estimated 181 new structures, of which 160 (88 <br />percent) would be located greater than 0.25 mile of an existing transmission line (Table 4.3-5). <br />The estimated Sage-Grouse population range does not overlap the Route Segment 3b ROW. <br />Approximately seven percent (14,616 acres) of the JBLM YTC 95 percent population range is within four <br />miles of Route Segment 3b (Figure 3.3-4). No active leks are known to occur within four miles of Route <br />Segment 3b (Table 4.3-6). One inactive lek is located approximately 3.9 miles west of Route Segment 3b. <br />This lek was last occupied in 2007. With the implementation of RDFs (Sections 4.3.3.1 and 4.3.3.2), <br />impacts to lekking Sage-Grouse associated with the construction of Route Segment 3b is anticipated to be <br />moderate for the 0.6 miles that are within four miles of the inactive lek. <br />4.3.4.10 Route Segment 3c <br />Approximately 74.3 acres of long-term and 45.9 acres of short-term disturbance would occur through the <br />construction of Route Segment 3c. Most of the permanently disturbed areas would be sagebrush/perennial <br />grassland (49.6 acres) and agriculture/disturbed ground (32.1 acres). Short-term disturbance would <br />primarily be on agriculture/disturbed land (32.1 acres) and annual grassland (11.5 acres; Table 4.3-4). <br />Riparian/wetland habitat occurs along Lower Crab Creek and estimated disturbance to these areas would <br />be 0.3 acres of long-term and 1.3 acres of short-term disturbance, though this disturbance would be <br />avoided if possible by spanning the riparian area. RDFs would be implemented to minimize habitat loss <br />and degradation, as described in Section 4.3.3.1. Impact levels to habitat are expected to be low for 14.5 <br />miles and moderate for 10.7 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