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' APPENDIX G <br />' Annual report Colorado River Fish and Wildlife Council <br />Colorado River Cutthroat Trout Conservation <br />Aoril 21, 1998 <br />pure populations within the tri-state area, and to identify populations in each GMU <br />which could be used for translocation or broodstock development activities. <br />On March 2, 1998, the Biology Committee met to begin these tasks. During that <br />meeting, it became clear that the viability definitions developed as part of the <br />overall Conservation Strategy (and described above in #2) were not workable for <br />establishing the tri-state baseline population. It was apparent that the <br />discrepancies among participants between the goals (what is wanted in the future) <br />and the baseline (what is here today) required another level of decision-making. As <br />a result, representatives from each of the three states were assigned to develop a <br />' listing of populations in their states with descriptors of important variables relating <br />to each population. <br />' Following this meeting, a joint, two-day meeting of the Colorado-Wyoming and <br />Bonneville (Utah) Chapters of the American Fisheries Society was conducted and <br />featured special sessions on research and conservation for Colorado River cutthroat <br />' trout. This met a Coordination Committee objective for initiating an annual <br />conference for information transfer among CRN experts and stakeholders. <br />Draft baseline lists of existing CRN populations with purity, adult population size, <br />habitat area, stocking and barrier data have been prepared in tabular form for <br />Colorado (Bruce Rosenlund) and Wyoming (Ron Remmick). These lists are to be <br />used to develop the summary of pure populations by consensus rather than a <br />definitional process. Rationale behind the inclusion of each population will be <br />included. Implied in this process is a consistent application of available results <br />' from five standardized information sources: morphometrics-meristics, mitochondrial <br />DNA, nuclear DNA, stocking history, presence of barriers; but application of a <br />single set of criteria is unlikely. What has emerged from group discussions are the <br />concepts of "restoration" and "conservation" designations for pure populations of <br />CRN, and these designations have been applied to the Colorado and Wyoming <br />1 population lists. Utah has yet to provide a similar baseline list or participate in any <br />of the discussion surrounding development of these tables. At this time we must <br />assume Utah wants the CRN populations listed in their existing conservation <br />strategy to serve as their proposed baseline list for group review. A major effort <br />will be necessary to resolve questions of how the various kinds of information <br />related to purity should be used in developing the baseline and for the listing of <br />potential source populations for restoration. The Fish and Wildlife Service has <br />offered some definitions of "conservation" and "restoration" populations, and how <br />both serve to preserve the remaining CRN genetic diversity. <br /> <br />3 <br />