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Mortality was not immediate but delayed following release for razorback <br />sucker stocked both in the Upper Colorado and Gunnison rivers. The low number <br />of radio contacts in 1995 suggests either radiotag failure or missing fish had <br />moved outside the tracking search routes. Three habitat types used most <br />frequently were main channel (47X), backwaters (23X), and eddy/pools (16X). Six <br />control fish held for observation in ponds at Horsethief State Wildlife area all <br />retained their radiotags. Four of these six control fish were later stocked in <br />the Gunnison River; two of the control fish in the ponds died four months <br />following handling and radiotag implantation which was attributed to a bacterial <br />infection not associated to the surgical incision. <br />Stocking different sizes of razorback sucker and determining the optimum <br />size to release should enhance post-stocking survival. Post-stocking survival <br />might be enhanced if captive-reared fish are physically conditioned to flow prior <br />to release. Conditioning captive-reared fish prior to stocking may <br />physiologically and behaviorally prepare them to adapt faster and survive in <br />riverine environments. <br />Recommendations include, 1) stocking fish as far upstream as possible due <br />to the predominantly downstream dispersal of fish immediately following release. <br />In the Gunnison River, fish should be stocked immediately downstream of Hartland <br />Diversion Dam; the most feasible stocking location being Confluence Park boat <br />launch. In the Upper Colorado River, fish could be stocked at Rifle (RM 240.7); <br />2) determining the optimum size of razorback sucker to stock to increase post- <br />stocking survival by evaluating the survival and performance of different sizes <br />of hatchery- and pond-reared razorback sucker to be stocked over the next 4 years <br />in the Gunnison River; 3) stocking captive-reared razorback sucker in the spring, <br />if the target fish have attained adequate size; 4) collecting food availability <br />and density data (zooplankton densities) from potential reintroduction sites <br />prior to stocking to determine if the habitat selected has suitable food <br />resources for released fish; 5) determining if post-stocking survival might be <br />enhanced if captive-reared fish are physically conditioned to flow prior- to <br />stocking; 6) determining if post-stocking behavioral stress can be reduced and <br />survival increased if fish are allowed to slowly acclimate in a backwater before <br />migrating to other riverine habitat; 7) stocking large numbers of various-sized <br />razorback suckers, each marked with a unique, identification code or number, <br />followed by intensive monitoring; and 8) recapturing stocked fish at 4 to 6-week <br />intervals to assess body condition and health, growth, and assessing if any <br />complications related to handling and tagging procedures occurred. Planned in <br />situ river acclimation and conditioning studies with captive-reared, sub-adult <br />razorback sucker might also prepare released fish to adapt better physiologically <br />and behaviorally and provide insight into increasing post-stocking survival. <br />viii