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<br />12 <br /> <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br /> <br />downstream of the three major irrigation canals of the Grand Valley, and habitat structure. Fish <br />surveys were difficult to complete at several sites due to increased agricultural return flows. <br />Native fish exceeding 170 mm total length were floy tagged. Overall, 1,895 fish were collected. <br />Thirty-two percent of these fish consisted of the four native fish species collected; the bluehead <br />sucker (Catostomus discobolus), flannelmouth sucker, roundtail chub (Gila robusta), and <br />speckled dace. Flannelmouth and bluehead suckers were collected at all seven sites sampled, while <br />roundtail chub and speckled dace were each collected at five sites. Size distributions of the native <br />fishes collected suggested that the bluehead and flannelmouth suckers, along with the roundtail <br />chub may be reproducing and maintaining self-sustaining populations within several of these <br />intermittent, irrigation-influenced tributaries. Eight nonnative, nonsalmonid fish species <br />constituted 68% of the total fish captured. The fathead minnow (Pimephales promelas), red <br />shiner (Cyprinus lutrensis), and green sunfish (Lepomis cyanellus) accounted for 94% of the total <br />nonnative fish species collected. Species composition fluctuated from site to site, and may be <br />influenced by habitat structure and flow. Water chemistry results indicated that during the <br />irrigation season, these tributaries were highly conductive alkaline systems, with elevated total <br />phosphorus (maximum of620 ugIL) and suspended solids concentrations. Instream metal <br />concentrations did not exceed state water quality standards for aquatic life. Dissolved selenium <br />concentrations ranged from 3.1 to 13.1 ugIL. The CDOW will increase monitoring efforts in <br />2002, assessing variability of fish community structure, habitat, and water chemistry in relation to <br />changes across irrigation seasons. Such studies may help determine what role, ifany, these <br />irrigation-influenced waters play in the life cycles of native and nonnative fishes of the Grand <br />Valley. <br /> <br />Trammell, M.t, and R. A. Valder <br /> <br />ISWCA Inc., Environmental Consultants; 2R, A. Valdez and Associates <br /> <br />Non-native Fish Control in Backwater Habitats in the Colorado River, 1999-2001. <br />Predation and competition between small, non-native cyprinid species and young endangered <br />fishes has been demonstrated in laboratory experiments (Ruppert et al. 1995; Muth and Beyers, <br />~uWished data), and is perceived to be influential in limiting survival and recruitment ofthe <br />endangered razorback sucker {Xyrauchen texanus) and Colorado pikeminnow (Ptychocheilus <br />lucius) in the wild. The objectives ofthis study were to significantly reduce the abundance of <br />small, non-native cyprinid and centrarchid fish species present in backwaters in the Colorado <br />River, significantly increase the survival and abundance of native and endangered fish species <br />using backwater habitats, and evaluate backwater seining as an effective field method for <br />controlling the abundance of small, non-native cyprinid and centrarchid fish species and for <br />inducing a positive biological response within the native fish communities. Response to depletion <br />was evaluated using Interagency Standardized Monitoring Program (ISMP) catch data Depletion <br />sampling was conducted on the Colorado River in the 15- and 18-mile reaches in June-July, 1999, <br />March-April, 2000, and June 2001. Four to five depletion passes were made in each year. In <br />1999,8,863 non-native fish were removed from 65 backwaters. In 2000, 7,054 non-native fish <br />were removed from 58 backwaters. In 2001, 180,379 non-native fish were removed from 82 <br />backwaters. Catch and catch rate of all fish initially declined after the first pass in all reaches and <br />years, but increased by the fourth pass in most cases. The effects of depletion by seining were thus <br />temporary at best. Comparison ofISMP fall catch rates prior to, and after, depletion efforts were <br />