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<br />In Montana, the Montana Rivers Information System (MRIS) was updated in 1994 for westslope <br />cutthroat. This database contains many of the components of the questionnaire, therefore the <br />database was queried for information on this subspecies. The questionnaire was completed by Errol <br />Claire, Oregon Department of Fish and Wildlife, for westslope cutthroat populations in the John Day <br />River drainage, Oregon. Information for Washington was obtained through surveys and contacts with <br />state and federal biologists. <br /> <br />In most cases the information contained within this assessment represents the best professional <br />judgement of state and federal biologists in each state. There is a tremendous amount of information <br />that is unknown about westslope cutthroat trout populations, but Mure surveys should help to <br />overcome some of these deficiencies. The information presented here is a general synopsis to assess <br />the current distribution and status of westslope cutthroat across its range. The reader is encouraged <br />to obtain additional information from each state. <br /> <br />RESULTS AND DISCUSSION <br /> <br />Idaho <br /> <br />In Idaho, the historic range is believed to have been the Kootenai River drainage above its barrier falls, <br />and the Pend Oreille, Spokane, Clearwater, and Salmon river drainages. Behnke (1992) speculates <br />that Clearwater and Salmon river populations originated from heaclwater transfers from the Clark Fork <br />River after redband trout displaced Yellowstone cutthroat which was likely the original ancestor in <br />these drainages. <br /> <br />Historic abundance was thought to be high throughout this subspecies range (Rieman and Apperson <br />1989). Gilbert and Everman (1894) during their early explorations of the Columbia River reported that <br />the Pend Oreille River was "abundant with trout and salmon trout" They were referring to cutthroat <br />and bull trout. Region 1 Idaho Fish and Game Files contain reports from the St. Maries Courier <br />reporting from 1901 to 1905 that anglers caught 50-100 "speckled trout" averaging 3 to 5 Ibs. <br /> <br />More recently, estimates by Rieman and Apperson (1989) indicate that strong populations (> 50% <br />of historic potential) persist in 11 % of the historic range, while viable (strong and depressed) popula- <br />tions remain in 36% of their historic range (Table 1). Depressed populations were defined as <50% <br />of their historic potential but were considered viable and common in samples. The potential to restore <br />westslope cutthroat to historic levels was subjectively rated poor in 46% of this range due to their <br />limited importance as a fishery while 20% of the populations could be restored with special regula- <br />tions. Potential was classified as the fishery manager's ability to use restoration techniques, i.e. <br />species removal, barrier construction, hatchery supplementation, special regulations, and habitat <br />recovery (Rieman and Apperson 1989). <br /> <br />Genetic inventories in Idaho are limited; only the upper Priest Lake population has been genetically <br />tested (Personal Communication, Dave Cross, Idaho Panhandle National Forest). Suspected pure <br />(the drainage had no history of stocking of other trout) populations exist in 13% of their range with <br />only 4% of the historic range considered strong and pure (Rieman and Apperson 1989). <br /> <br />Decline in westslope cutthroat trout abundance was attributed to habitat loss in 87% of the streams, <br />while overfishing contributed to 47% of the decline. Competition was thought to affect 12% of the <br />population decline and genetic introgression 15% (Rieman and Apperson 1989). Habitat degradation <br />has negatively affected populations. Forest management, including but not limited to timber harvest, <br /> <br />3 <br />