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Vantage to Pomona FEIS Index 34
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12. December
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2018-12-18 10:00 AM - Commissioners' Agenda
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Vantage to Pomona FEIS Index 34
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Last modified
12/13/2018 1:49:29 PM
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12/13/2018 1:34:21 PM
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Meeting
Date
12/18/2018
Meeting title
Commissioners' Agenda
Location
Commissioners' Auditorium
Address
205 West 5th Room 109 - Ellensburg
Meeting type
Regular
Meeting document type
Supporting documentation
Supplemental fields
Alpha Order
a
Item
Conduct a Closed Record Meeting to consider the Hearing Examiner's Recommendation for the Vantage to Pomona Transmission Line Conditional Use Permit (CU-18-00001)
Order
1
Placement
Board Discussion and Decision
Row ID
50108
Type
Conduct closed record hearing
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Vantage to Pomona Heights Chapter 3 <br />230 kV Transmission Line Project FEIS Affected Environment <br /> PAGE 3-61 <br />approximately five miles, though movements of up to 20 miles have been recorded for adult females in <br />Washington. Sage-Grouse in the YTC population are non-migratory with only localized movements <br />between seasonal use areas, whereas some birds in the Mansfield Plateau/Moses Coulee population <br />exhibit migratory patterns (Robb and Schroeder 2012). <br />The WHCWG completed a statewide connectivity analysis (WHCWG 2010) and a Columbia Plateau <br />connectivity analysis (WHCWG 2012), including a species-specific connectivity analysis for Sage- <br />Grouse (Robb and Schroeder 2012). <br />Sage-Grouse-specific WHCWG analyses identified four Habitat Concentration Areas (HCA) within <br />Washington. These include the YTC and Mansfield Plateau/Moses Coulee populations already mentioned <br />and two reintroduced populations, one in the northern Crab Creek drainage in Lincoln County and one on <br />the Yakama Indian Reservation in Yakima County. Sage-Grouse were translocated to the Yakama Indian <br />Reservation in 2006, but, as of 2012, there were no confirmed observations of breeding activity (Robb <br />and Schroeder 2012). <br />The WHCWG analyzed connectivity among the four HCAs by assigning resistance values to various land <br />covers and anthropogenic features along potential routes that Sage-Grouse may take if they attempted to <br />travel from one HCA to another. The resistance values relied upon published literature and the <br />professional judgment of biologists and expert reviewers. Resistance values for anthropogenic features <br />ranged from 0 (e.g., 1,640 to 3,280-foot buffer of 230 kV transmission line) to 99 (housing with less than <br />10 acres/dwelling unit). Transmission lines were given a resistance value of 7 for single 230 kV line and 3 <br />for 1,640-foot buffer. For two adjacent 230 kV lines the resistance values were not doubled, but increased <br />by approximately 25 percent (9 for double line; 4 for 1,640-foot buffer; 1 for 0.6-mile buffer; Robb and <br />Schroeder 2012). <br />The WHCWG analysis identified the linkage between the YTC HCA and the Mansfield Plateau/Moses <br />Coulee HCA as “fairly good” (see Figure 3.3-3). Much of the habitat along this corridor is shrub-steppe <br />that is protected within state-owned wildlife areas. Impediments to this linkage include the relative <br />steepness of the terrain, disturbance associated with I-90, several existing transmission lines, and two <br />wind energy developments. Conditions for movement are best in the central portion of the linkage, but <br />there are areas of concern at both ends. Near its northern end, the modeled corridor is constricted as it <br />crosses the Columbia River near Rock Island Dam. Near the southern end, north of I-90 and the proposed <br />Project, the linkage is constricted by two wind energy developments (Robb and Schroeder 2012). <br />Sage-Grouse Population Range Estimates <br />Based on location data provided by JBLM YTC, including telemetry data and incidental observations, it <br />is apparent that within the JBLM YTC, some areas are more heavily used by Sage-Grouse than others <br />(Figure 3.3-2). To generate a clearer picture of relative density of use by the YTC Sage-Grouse <br />population, a fixed kernel density analysis was conducted using telemetry data. The methodology is <br />explained in detail in Appendix B-5 Sage-Grouse Technical Report. <br />The kernel density method is commonly used to compute probabilistic estimates of utilization distribution <br />within individual animal home ranges, using random location data consisting of discrete points (Fuller et <br />al. 2005). While most often used to estimate distribution of use for individuals, the method has also been <br />used to estimate utilization distribution for populations (Coates et al. 2013). To yield easily interpretable <br />metrics, 95 percent and 80 percent isopleths were generated in our analysis. Areas within the isopleths <br />represent probabilities of utilization. The 95 percent isopleth encompasses 95 percent of the predicted <br />distribution of all grouse habitat use for the YTC population; for the lay reader, this concept can be <br />roughly understood in the following way: on an “average” day, 95 percent of the grouse would be <br />expected to occur within the 95 percent isopleth, or alternatively the “average” grouse spends 95 percent
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