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Supplemental Final Environmental Impact Statement I Federal Coal Lease Modifications COC -1362& COC -67232 <br />as the primary factor contributing to vehicle -wildlife collisions (Gunther et al. 1998). Neither is considered <br />to be a factor for this project due to the lack of suitable habitat in the project area. There are no landscape <br />linkage areas in or near the project area or any travel routes associated with the project. <br />The Recovery Outline (USDI FWS 2005) identifies core areas, secondary areas and peripheral areas, <br />based on historical and current occurrence records, as well as confirmed breeding. The Southern Rockies <br />(Colorado and Wyoming) were identified as a Provisional Core Area. This designation was identified <br />because this area contains a reintroduced population. Reproduction has been documented but it is too <br />early to determine whether a self-sustaining population will result. A total of 37 dens and 116 kittens had <br />been located in Colorado prior to the 2009 breeding season (CPW 2009). <br />In November 2005, the FWS proposed critical habitat for lynx (USDI FWS 2005a). In 2006 Critical Habitat <br />for the lynx was designated, with none occurring in the Southern Rockies (USDI FWS, 2006). A revised <br />critical habitat designation which does not include lands within Colorado has been proposed (USDI FWS, <br />2008). On September 12, 2014, the USDI FWS revised Endangered Species Act (ESA) protections for <br />the contiguous United States distinct population segment (DPS) of Canada lynx The Service finalized <br />both a revised critical habitat designation for the lynx DPS and a revised definition for what constitutes <br />the range of the DPS — the portion of the species' North American range in which lynx are protected by <br />the Act.(USDI 2014) None of the critical habitat occurs in Colorado. See bottom of section for reference. <br />Extensive stands of pure aspen may not provide quality hare (primary prey) habitat due to deficiencies <br />in winter habitat characteristics. However, when mixed with spruce/fir, aspen (especially younger stands) <br />may substantially contribute to prey productivity (Ruediger et al. 2000). Lynx transplanted into Colorado <br />were frequently located in well-developed riparian and valley wetland shrub habitats of the upper <br />montane and subalpine zones. These ecotones may provide quality foraging habitat for lynx. <br />Lynx Standards and Guidelines from the GMUG Forest Plan are shown in Table 6 of the Biological <br />Assessment found in the Project File. <br />3.10.1.3 Alternative 1 (No Action) Environmental Effects <br />The direct and indirect impacts of the no action alternative would not change current habitat or population <br />conditions of Canada lynx in the short term. Long-term changes would continue to be dependent on <br />existing conditions, current succession of vegetative types, and other actions within the project area, as <br />indicated in the cumulative effects tables and discussions in this analysis. The ongoing aspen decline <br />may result in both short- and long-term loss of aspen at a landscape scale in this area. <br />3.10.1.4 Alternative 3 (Proposed Action) Environmental Effects <br />WLAU boundary and acreage has changed but the effects have not. Still the same disturbance and <br />habitat alteration as discussed in the BA and still the same not -reaching -threshold -we -consulted -on, even <br />if the acres were revised to reflect a better fit to suitable habitat <br />Under Alternative 3, the Forest Service would consent to and BLM would modify the leases with <br />stipulations outlined in Section 2.2 including those related to Canada Lynx and TES species. For this <br />analysis, all lease stipulations are considered to be in effect. <br />Mining may result in subsidence of surface topography as coal is removed from below ground. This <br />subsidence has resulted in landslides and other surface changes on unstable and steep slopes in other <br />portions of the Forest in which such mining has occurred. Such disturbance, however, has been limited <br />to steep and unstable ground and has not been widespread in undermined areas. Most surface <br />subsidence has been relatively uniform across the landscape and in most areas, does not visibly alter <br />surface features or vegetation. <br />189 <br />