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<br />I <br />I <br /> <br />floodplain ecosystem of the Upper Colorado River Basin must be restored <br />if recovery of the endangered fishes is to be achieved. <br /> <br />Re-introduction stocking of razorback suckers in the upper Colorado and <br />Gunnison rivers and augmentation stocking in the middle Green River <br />should be continued following approved stocking plans and genetics <br />conservation measures (Williamson and Wydoski 1994) to increase numbers <br />of razorback suckers in those rivers. Although augmentation stocking is <br />not recovery, it provides a mechanism to maintain adult razorback suckers <br />in the upper Colorado River Basin to prevent extinction until a solution <br />is found to achieve self-sustaining populations (i.e., recovery). <br /> <br />I <br />I <br /> <br />I <br /> <br />I <br />I <br />I <br /> <br />Evaluate factors identified in a stocking plan that may affect survival <br />of captive-reared fish including (1) use of floodplain ponds as a "half- <br />way" habitat where captive-reared razorback suckers can become <br />conditioned to eating natural food organisms, (2) importance of physical <br />conditioning to various water velocities prior to release, (3) size of <br />fish at release, (4) time of release, etc. Experimental stocking in the <br />Green and Gunnison rivers with captive-reared fish of 100 mm TL (- 4 in) <br />has not been successful. Few of the fish were recovered shortly after <br />stocking and recaptures have not been made. However, seven razorback <br />suckers were recaptured in 1997 from 1,068 that were stocked as larger <br />fish (209-308 mm TL; - 8-12 in) into the middle Green River in 1996 (T. <br />Pruitt, 1998, personal communication) . <br /> <br />I <br />t <br /> <br />Recaptures of razorback suckers stocked into the San Juan River (F. <br />Pfeifer, 1997, personal communication) suggested that larger fish may <br />survive better than small fish. Although survival of juvenile razorback <br />suckers that were stocked at 113 mm TL (- 4 in) into the Gila River, <br />Arizona increased because of less predation by ictalurids, Marsh and <br />Brooks (1989) recommended stocking fish that are 300 mm TL (12 in) or <br />larger in the Lower Colorado River Basin. Recaptures of fish stocked at <br />300 mm TL has been considered successful in Lake Mohave (G. Mueller, <br />1996, personal communication). The former Recovery Program Propagation <br />Coordinator (RSW) recommended that fish 300 mm TL ( - 12 in) or larger <br />should be stocked in the Upper Colorado River Basin. Razorback suckers <br />in floodplain ponds along Upper Basin rivers will grow to 300 mm TL (- 12 <br />in) by the end of the second growing season (Figure 3). Fish that are <br />reared in floodplain ponds would reach 400 mm TL (16 in) or larger by the <br />end of the third growing season. Fish stocked after three seasons of <br />growth in the fall should mature and produce larvae in Upper Basin rivers <br />the following spring. <br /> <br />I <br />I <br /> <br />I <br />I <br /> <br />In conclusion, the Recovery Program elements of (1) streamflow, (2) <br />habitat enhancement/restoration, (3) control of nonnative fishes and (4) <br />captive propagation/ stocking of razorback suckers must be integrated <br />conscientiously and concurrently because these four Recovery Program <br />elements are closely interconnected and are expected to affect the <br />responses of native (including endangered) and nonnative fishes. <br /> <br />I <br />, <br />I <br />j <br />I <br /> <br />37 <br />