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Vantage to Pomona Heights Chapter 4 <br />230 kV Transmission Line Project FEIS Environmental Consequences <br /> <br /> PAGE 4-29 <br />Hairy Bugseed <br />Hairy bugseed is a Washington Sensitive Species. This species is found in Colorado, Minnesota, <br />Missouri, Montana, Nebraska, Nevada, North Dakota, Wisconsin, Wyoming, most Canadian provinces, <br />and Grant County, Washington (NatureServe 2015). At the regional level, three populations occupying <br />approximately 1,267 acres are known to occur. Threats are not documented but are presumed to be similar <br />to sensitive species in sandy habitats, including OHV use, increased weed invasions, changes in sand <br />deposition, and agricultural conversion. WNHP indicates that hairy bugseed occurrences intersect a 0.6- <br />mile section of Route Segment 3c. These locations include large buffers, so it is difficult to accurately <br />determine whether these occurrences truly intersect the ROW corridor. For the proposed Project, direct <br />and indirect impacts to hairy bugseed are similar to those described above for Nuttall’s sandwort. Nearly <br />all potential habitat on federal and state lands was surveyed, so it is unlikely hairy bugseed occurs within <br />Route Segment 3c. With the implementation of RDFs described above and the assumption that <br />occurrences would be spanned and avoided, Project construction, operation, and maintenance activities <br />could impact individuals or habitat (moderate impact), but would not contribute a trend toward federal <br />listing. <br />Hoover’s Desert-Parsley <br />Refer to Route Segment 3b for information on Hoover’s desert-parsley. WNHP and BLM GeoBOB data <br />indicates that Hoover’s desert-parsley may intersect Route Segment 3c for 2.1 miles. These locations <br />include large buffers; therefore, it is difficult to accurately determine whether these occurrences truly <br />intersect the ROW corridor. Impacts from the proposed Project are similar to those described above for <br />Route Segment 3b. Nearly all potential habitat on federal and state lands was surveyed, so it is unlikely <br />Hoover’s desert-parsley occurs in Route Segment 3c. With the implementation of RDFs described above <br />and the assumption that potential occurrences would be spanned and avoided, Project construction, <br />operation, and maintenance activities could impact individuals or habitat (moderate impact), but would <br />not contribute a trend toward federal listing. <br />4.2.4.11 Route Segment NNR-2 <br />General Vegetation <br />Route Segment NNR-2 parallels an existing JBLM YTC fire break road, existing roads, and an existing <br />transmission line. Construction of Route Segment NNR-2 would result in long-term disturbance of <br />approximately 8.7 acres of vegetation. Disturbance would occur in 1.0 acre of annual grasses and noxious <br />weeds, 0.4 acre of perennial grassland, 0.3 acre of rabbitbrush annual grassland, 2.4 acres of sagebrush <br />annual grassland, 4.4 acres of sagebrush perennial grassland, and 0.2 acre of trees (Table 4.2-4). Short- <br />term disturbance would occur to approximately 9.2 acres of vegetation. General vegetation impacts are <br />similar to those described above for Route Segment 1a/NNR-1 and Impacts Common for All Route <br />Segments (Section 4.2.3). Disturbance would be minimized by RDFs designed to reduce impacts to <br />vegetation resources. RDFs include using existing public roads to access structure sites, minimizing <br />blading and disturbance to plant communities, revegetating following construction, and implementing a <br />Noxious Weed and Invasive Plant Management Plan. Refer to Section 2.3 - Required Design Features <br />Common to Action Alternatives for a complete list and description of RDFs. <br />With the implementation of RDFs, long-term impact levels for Route Segment NNR-2 include 1.5 miles <br />of no identifiable, 2.4 miles of low, and 1.3 miles of moderate impacts. <br />Special Status Species and Priority Ecosystem <br />WNHP data indicate that basalt daisy (Erigeron basalticus), Hoover’s desert-parsley, and pauper <br />milkvetch (Astragalus misellus var. pauper) are known to occur within one mile of Route Segment NNR- <br />2 (Table 4.2-5). None of these species were documented during the special status plant surveys for Route <br />Segment NNR-2; however, Hoover’s desert-parsley and Pauper milkvetch were documented within the