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Vantage to Pomona Heights Chapter 3 <br />230 kV Transmission Line Project FEIS Affected Environment <br /> PAGE 3-69 <br />In the southern portion of the Project study area, Sage-Grouse 80 percent core and 95 percent population <br />range substantially overlaps the other route segments associated with Alternatives A-G. Route Segment <br />2a is entirely within the core population range. Route Segment 2b has the next highest proportion of <br />overlap with the core and 95 percent population ranges (41 percent in core, 84 percent in population <br />range) followed by Route Segments 1b (18 and 73 percent) and 1c (14 and 73 percent), 2c (25 and 59 <br />percent), and 2d (four and 14 percent). Acreages of core population range and 95 percent population <br />range within the ROW and eight-mile wide analysis area are shown in Table 3.3-4 and described for each <br />route segment (Section 3.3.5). <br />A time-series of the three study periods reveals a southeastward shift in the YTC Sage-Grouse population <br />range and core population range since 1989. It is beyond the scope of this document to speculate at length <br />on possible causes of the shift, but it should be noted that the existing Pomona-Wanapum 230 kV <br />transmission line was built in the early 1970s, more than 15 years before the earliest available Sage- <br />Grouse location data. An examination of fire history at JBLM YTC (see Figure 3.3-6) does not suggest a <br />relationship between fire history and the shift in Sage-Grouse distribution. The formerly occupied area <br />suffered minimal burns relative to areas within the current core population range. The shift in Sage- <br />Grouse distribution may have been influenced by JBLM YTC training maneuvers. Most of the Sage- <br />Grouse range shift occurred during the 1993 to 1999 period in JBLM YTC Training Areas (TA)-15 and <br />TA-16. According to JBLM YTC (personal communication, JBLM YTC 2014a), there was a period of <br />heavy training maneuvers during the mid-1990s, with particularly high activity levels in TA-16. It is also <br />possible that the population shift was not a response to any change in habitat or disturbance levels, but <br />merely a response to population declines, such that if the TA-15 and TA-16 areas held inherently lower <br />quality habitat to begin with relative to the core area, they simply may have been the first areas to be <br />abandoned as the population declined from over 300 birds during the 1989-1993 period to approximately <br />200 birds during the most recent period. <br />The population range during the most recent period (2012-2014) provides the most useful information for <br />predicting Project impacts on the current grouse population. Nevertheless, the historic population ranges <br />might be indicative of areas likely to be reoccupied in the future if the YTC Sage-Grouse population <br />recovers and expands into currently unoccupied areas. Future occupancy is speculative in nature and <br />would depend on a number of factors including wildfire occurrence, military training activities, and future <br />habitat condition. <br />Sage-Grouse Leks <br />Active, inactive, and historical leks are shown in Table 3.3-5 and discussed in Section 3.3.4 for each route <br />segment. Leks are classified by JBLM YTC as: 1) active - a lek with at least two male grouse observed <br />displaying on at least two different days during the previous two years or, if not checked in the past two <br />years, was active during the last year checked; 2) inactive - has been active sometime during the previous <br />10 years, but was not active during the past two years or in the last year checked; or 3) historical - a <br />formerly active lek site in which no activity has been observed for the previous 10 years (JBLM YTC <br />2014b; SEE 2013). <br />Lek complexes are defined as active leks within 1.8 miles of each other and have been used to estimate <br />the YTC Sage-Grouse population size and trends (SEE 2013; Schroeder et al. 2000). Fifteen (15) lek <br />complexes are known to occur within JBLM YTC, containing approximately 22 leks. Of the 15 lek <br />complexes, two have not been attended by male Sage-Grouse since the early 1990s. Lek surveys are <br />conducted on JBLM YTC on a yearly basis with priority given to areas with prior Sage-Grouse sightings <br />during the breeding period and active, inactive and historic lek locations. It is unlikely that an <br />undocumented major lek exists on JBLM YTC in searchable areas. Additional leks may be present on <br />JBLM YTC in unsearchable areas (i.e., Central Impact Area) and on adjacent private lands (SEE 2015).