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changed in 1996 to fry (34%), fingerling (13%), subcatchable (2%), catchable (5%). From these <br />data it is evident that, at this time, changing to total wild trout management in streams would not <br />provide substantial opportunities to forego or redistribute hatchery-reared fish. The greatest <br />"savings" would be realized from the 2.3 million trout fry (34% of statewide fry production). <br />However, because of their small size, production of trout fiy has limited requirements for hatchery <br />space and costs (food, feeding, and transportation). <br />It should be noted that this situation could change if the DOW increased its capability to <br />produce more WD- trout, some of which might be scheduled for additional stream stocking. This <br />situation might again encourage stocking plans that would more closely reflect 1992 stocking <br />numbers, where a much greater proportion of the state's fish production was used in streams. <br />Use of stocked trout to meet fishing pressure in certain high-use stream segments in populated <br />corridors would make wild trout management a more viable option in surrounding stream habitat <br />areas. Conversion of all suitable coldwater stream habitat to wild trout management may be a <br />desirable and appropriate objective in and of itself, and would contribute toward less dependency <br />on fish stocking and the risk of exposure to WD. If maintaining fishing recreation at or near the <br />1992 level (6+ million recreation days) is also a management objective (as suggested in the LRP), <br />then an alternate strategy that exploits the recreation potential of WD+ fish in low-risk waters <br />until they can be replaced by WD- fish during a transition period would be warranted. If not, then <br />fish recreation goals in the LRP should be reevaluated with respect to increased participation in <br />fishing, increased angler satisfaction, and stocking to maintain angler satisfaction. <br />Management of the native cutthroat species encompasses both conservation and recreation <br />elements. Given the declining status of these species, the conservation objectives must take <br />precedence over recreation opportunities or demand. Restoration and long-term management of <br />the native cutthroats have the best prospects for success if they are managed as the exclusive <br />salmonid species in the headwaters of their respective drainages. This is consistent with existing <br />restoration management plans for each species, which emphasizes the need to isolate their habitat <br />from other salmonids to minimize hybridization and other negative interactions. The <br />implementation of this management alternative for Colorado River and greenback cutthroat will <br />require at least a 10-year time frame. <br />Recreational benefits provided by self-sustaining native cutthroat populations are similar to <br />other wild trout. Catch-and-release and limited-harvest regulations will be required to protect <br />them from overfishing, to which they are very susceptible. As unique native gamefish, the <br />attractiveness and desirability of these limited cutthroat fisheries to the public may enhance their <br />recreation potential. However, management for native species (within the Special Use category) <br />provided only 9,800 recreation days in 1992, or about 0.2% of the statewide recreation days. <br />Even a doubling of waters managed for native species would do little to increase recreation days <br />due to greater difficulty of reaching the remote waters targeted for restoration actions. Expansion <br />of native species management that may take place over the next decade is unlikely to decrease the <br />need for fish production or to increase recreation days, given that those potential waters now <br />receive little management or fishery pressure. <br />27