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2008-06-12_GENERAL DOCUMENTS - C1980007 (3)
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2008-06-12_GENERAL DOCUMENTS - C1980007 (3)
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Last modified
5/26/2020 1:45:00 PM
Creation date
6/13/2008 2:26:34 PM
Metadata
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Template:
DRMS Permit Index
Permit No
C1980007
IBM Index Class Name
General Documents
Doc Date
6/12/2008
Doc Name
Mining Plan Decision Document COC-67232
From
OSM
Permit Index Doc Type
Other Permits
Email Name
TAK
Media Type
D
Archive
No
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Southern Rocky Mountains Region (Colorado, SE Wyoming) - Colorado represents the <br />extreme southern edge of the range of the lynx. The southern boreal forest of Colorado and <br />southeastern Wyoming is isolated from boreal forest in Utah and northwestern Wyoming by the • <br />Green River Valley and the Wyoming basin (Findley and Anderson 1956). These areas likely <br />reduce opportunities for immigration from the Northern Rocky Mountains/Cascades Region and <br />Canada (Halfpenny et al. 1982; Koehler and Aubry 1994). Although habitats in the Southern <br />Rockies are far from source populations and more isolated, it is still possible that dispersers <br />could arrive in the Southern Rocky Mountains during extreme highs in the population cycle. <br />The majority of historic lynx occurrence records in Colorado and southeastern Wyoming are <br />associated with the "Rocky Mountain Conifer Forest" type. The occurrences in the Southern <br />Rockies were generally at higher elevations (8,000-12,000 feet) than were all other occurrences <br />in the West (Ruediger et al. 2000). Canada lynx occur primarily in spruce-fir and lodgepole pine <br />forests, at elevations between 8,000 and 12,000 feet (2,450 to over 3,650 meters) (Ruggiero et al. <br />2000). Quaking aspen (Popultes tremidoides) stands and forest edges, as well as open grass <br />meadows and forest ecotones, may also support high numbers of hares and Canada lynx. On a <br />landscape scale, Canada lynx habitat includes a mosaic of early seral stages that support <br />snowshoe hare populations and late seral stages of dense old growth forest that provide ideal <br />denning and security habitat. <br />Records of lynx occurrence are available from throughout most of the Southern Rocky <br />Mountains. The last specimens of lynx taken in the Southern Rockies were from the late 1960s <br />and early 1970s. In 1969, three lynx specimens were taken in adjacent counties in the central <br />core of the Southern Rockies. One was shot along the Fryingpan River in Pitkin County, another <br />on Vail Mountain (Eagle County), and a third was trapped south of Leadville in Lake County (G. <br />Byrne, pers. comm. 1999). In 1971, the State of Colorado closed the season on lynx, making it <br />illegal to take this species. Since then, only a few specimens have been obtained. In 1972, a <br />lynx was trapped on Guanella Pass and another caught in a snow slide east of Bakerville, <br />Colorado, both in Clear Creek County. During the 1973-74 winter, a pair of lynx was illegally <br />trapped within Vail Ski Area boundaries (Thompson and Halfpenny 1989). No lynx specimens <br />are available since those last illegal takes. <br />The Canada lynx has been classified by the State of Colorado as a State endangered species since <br />1976. In 2000, the Service classified the lynx as a federally threatened species. Since 1978, <br />there have been 14 investigations into naturally occurring lynx presence in Colorado conducted <br />by the CDOW and other private and public conservation groups. <br />Recovery Outline <br />We developed a recovery outline for lynx in the contiguous United States (Service, 2005). The <br />purpose of the outline is to serve as an interim strategy to guide recovery efforts until a draft <br />recovery plan has been completed. The Southern Rockies (Colorado and southern Wyoming) is <br />identified as a provisional core area, along with 6 other core areas. The Southern Rockies was <br />identified as a provisional "core area" because it meets the criteria for evidence of historical <br />populations of lynx, has recent evidence that reproduction can be supported, and appears to <br />contain sufficient quantity and quality of habitat to support both lynx and snowshoe hare. <br />However, because the population had declined to the point that it was not believed to be self- <br />sustaining (CDOW 2002), a reintroduction was initiated. While the reintroduction appears to be • <br />very promising, it is too early to tell if a self-sustaining population will be achieved. Until that <br />12
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