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<br />. ... <br /> <br /> <br />....h--tJ[;ir(1 <br /> <br /> <br />368 <br /> <br />The Southwestern NaluTalist <br /> <br />vol. 38, no. 4 <br /> <br />wild fish moved out of the reservoir into the river <br />and seemed to survive the experience more suc- <br />cessfully (2 out of 3 survived, compared to only <br />1 out of 4 hatchery fish surviving until the end <br />of the study). There was no discernable difference <br />in behavior between the surviving fish attribut- <br />able to their origin. Implanting dual tags may <br />have contributed to the unusually high (43%) <br />mortality of the tagged fish, confounding the re- <br />sults. <br />Low recapture may also be attributable to the <br />difficulty of sampling Colorado squaw fish in the <br />size range 100 mm to 250 mm. Wild specimens <br />are seldom collected in this size range, although <br />recruitment into the adult size-classes occurs. The <br />stocked fish may reappear at a larger size. In <br />support of this is the recent recapture of adult <br />squawfish in the Colorado River that were marked <br />with coded wire tags and stocked as fingerlings <br />in 1982, 1983 or 1984. Three out of 21 adult <br />Colorado squaw fish collected during spring sam- <br />pling in 1990 had coded wire tags, although their <br />stocking year could not be determined without <br />surgery (B. Burdick, pers. comm.). <br />Not only did catch rate decline following stock- <br />ing, but, also, total capture success in the reservoir <br />was quite low. One percent of the total fish stocked <br />were eventually recaptured. Only 14 fish were <br />collected in their second year. Only four of these <br />fish were caught in Kenney Reservoir. Five of <br />these were collected in 1991, one in the reservoi r, <br />three above, and one below. No squaw fish were <br />collected in the third year after stocking. <br />Unless the Colorado squaw fish subsequently <br />reappear at a larger size when they are more <br />susceptible to capture, little additional informa- <br />tion can be gained from this stocking effort. In- <br />cidental catch by anglers may also contribute in- <br />formation on the fate of any surviving Colorado <br />squawfish. Due to the small number and sizes <br />(112 to 184 mm) of stocked fish collected in 1991, <br />the Colorado Division of Wildlife recommended <br />that further intensive evaluation of stocked Col- <br />orado squaw fish be postponed until evidence is <br />obtained, either through sampling or creel survey, <br />that any of the stocked fish remaining in the res- <br />ervoir are vulnerable to angling capture. The suc- <br />cess of subsequent stockings of squaw fish might <br />be improved by stocking larger-sized fish after <br />runoff. Some fish loss could be prevented by mod- <br />ification of the spillway and release procedures. <br />Techniques employed to minimize fish escape- <br />ment over the spillway should be explored if fu- <br /> <br />; <br />I <br /> <br />l <br /> <br />ture stocking is planned. This strategy should <br />include efforts to minimize the magnitude and <br />duration of surface releases at the time of stock- <br />ing. <br />The concept of establishing a sport fishery for <br />Colorado squawfish has been previously pro- <br />posed and discussed as a recovery strategy (Wy- <br />doski, 1982). Colorado squaw fish are attractive, <br />silvery fish that reach trophy sizes, take lures <br />readily, are strong fighters, and are reputed to be <br />delectable. In short, they have air the prerequi- <br />sites of a fine sportfish except for the regard of <br />the anglers, and wide ranging movements that <br />may exceed the confines of small-sized mainstem <br />impoundments. The low return of stocked fish, <br />regardless of the cause, does not generate much <br />promise for establishing a sportfishery. Nor does <br />stocking Colorado squawfish in mainstem res- <br />ervoirs appear to be an effective mitigation pro- <br />cedure for habitat loss due to impoundment. <br /> <br />This research was supported by grants from the <br />Colorado Division of Wildlife and the Sigma Delta <br />Epsilon Graduate Women in Science. The U.S. Fish <br />and Wildlife Service office, Grand Junction, Colorado, <br />provided radio equipment and field assistance and ar- <br />ranged for stocking the fish. We wish to thank Water <br />Users Association #1 in Rangely, Colorado for their <br />cooperation and support during this study. We wish <br />to thank W. Wiltzius for offering helpful comments <br />and suggestions on the manuscript. Cooperators in the <br />Colorado Cooperative Fish and Wildlife Research Unit <br />include the United States Fish and Wildlife Service, <br />Colorado Division of Wildlife, and Colorado State <br />University. <br /> <br />LITERATURE CITED <br /> <br />CARLSON, C, A., ET AL. 1979. Fishes and macroin- <br />vertebrates of the White and Yampa rivers, Colo- <br />rado. U.S. Bur. Land Mgmt. BioI. Sci. Ser., 1:1- <br />276 <br />CHART, T. E., AND E. P. BERGERSEN. 1992. Impact <br />of mainstream impoundment on the distribution <br />and movements of the resident flannelmouth sucker <br />(Catostomidae: Catostomus latipinnis) population in <br />the White River, Colorado. Southwestern Nat., 37: <br />9-15. <br />_. 1988. Methods for long-term identification <br />of salmon ids: a review. U.S. Fish and Wildlife Ser- <br />vice, Biological Report, 88:1-18. <br />CLARK, C. F. 1942. A study of the loss of fish from <br />an artiliciallake over a wasteweir, Lake Loramie, <br />Ohio. North American ConL Transactions, 7:250- <br />256. <br />COLORADO RIVER FISHES RECOVERY TEAM. 1988. <br /> <br />, <br />",;"- <br /> <br /> <br />'~" :.:~~, "~~:-' ~~~(~'~9~:-~B~1~~~f~~~~~~:~~~~W~~~T~~~~~~~~~gf~~~~~~~S~~S~:-~~~~~~~~~~~~}~~, '.'" ',~. <br />. . ,"' -" ',". <br /> <br />. " ::.-~..:. ~...: <br />