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<br />Recovery Program participants are we77 aware that total control of <br />nonnative fish species in the large rivers of the Upper Colorado River <br />Basin is not possible. A large volume of fishery literature exists to <br />demonstrate that total control of fish in such waters is unrealistic <br />(Wiley and Wydoski 1993). However, it is believed that even partial <br />contro I of the nonnative fishes wi 77 reduce predation on and competition <br />with the endangered Colorado River fishes. All ponds where nonnative <br />fi shes are removed and the adjacent river envi ronments wi 77 be monitored <br />to evaluate the response of both endangered, native, and nonnative <br />fishes. <br /> <br />During the development of a strategic plan for control of nonnative fish <br />species (Tyus and Saunders 1996), the Recovery Program participants <br />reviewed potential control methods and examined the life histories of <br />the nonnative fishes to determine whether certain life stages were most <br />vulnerable .to control (Lentsch et a1. 1995). During their discussions, <br />the Recovery Program participants decided that preventive measures to <br />manage/control the distribution and population expansion of nonnative <br />fishes was a top priority (Wydoski 1995). Several preventive measures <br />that were identified included (1) completion of the IIProcedures for <br />Stocking Nonnative Fish Species in the Upper Colorado River Basin", (2) <br />preventing/minimizing nonnative fish escapement from riverside ponds, <br />(3) chemical reclamation of riverside ponds, and (4) preventing/ <br />minimizing nonnative fish escapement from large reservoirs. The <br />"Procedures" were completed and adopted by the Colorado Division of <br />Wildlife, Utah Division of Wildlife Resources, Wyoming Game and Fish <br />Department, and U.S. Fish and Wildlife Service (Colorado Division of <br />Wildlife et al. 1996). Floodplain ponds were inventoried by Mitchell <br />(1995) to determine the number and identify those with outlets to the <br />rivers that could be screened to prevent chronic escapement of nonnative <br />fishes. Screens (Burns 1966; Schnick et al. 1982) will be installed on <br />ponds in the future where appropriate. The berms of some ponds may be <br />increased in height so that they would not connect with the river unless <br />a 50-year or larger flood occurred. Ponds that are above the 50-year <br />floodplain can be stocked with nonnative, warnwater fish species under <br />the "Procedures for Stocking Nonnative Fish Species in the Upper <br />Colorado River Basinll (Colorado Division of Wildlife et a1. 1996). A <br />scope-of-work was developed by the Colorado Division of Wildlife and <br />approved through the Recovery Program to begin the chemical reclamation <br />of floodplain ponds (Martinez and Nesler 1996). A feasibility study was' <br />completed for insta77ation of fish control structures on reservoirs with <br />warnwater fish species and with outlets to Upper Basin rivers (Miller <br />and Laiho 1997). The focus of the feasibility study was on Elkhead <br />Reservoir (Yampa River) and Highline Reservoir (Colorado River). <br />Therefore, a number of Recovery Program efforts are underway to control <br />or manage nonnative fish species in the Upper Colorado River Basin to <br />reduce predation and competition by nonnative fishes on the endangered <br />fishes. <br /> <br />3. Some anglers would like to have warmwater angling opportunities from the <br />floodplain ponds. <br /> <br />29 <br />