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increase survival in the critical early life stages of the endangered <br />fishes. Zooplankton densities must be adequate to realize survival of <br />larval endangered fishes based on studies of razorback suckers by Papoulias <br />and Minckley (1990). At the same time, nonnative fishes would not be given <br />the opportunity to multiply in the floodplain ponds since they would enter <br />the river as the high spring streamflows subside. Earlier in this <br />Environmental Assessment, it was stated that the target nonnative fish <br />species for control in floodplain ponds are centrachids, primarily <br />largemouth bass and green sunfish (Martinez and Nesler 1996). Centrarchid <br />species do not fare well in the riverine environment based on monitoring of <br />fish populations by the Recovery Program (McAda et al. 1994 a,b; 1995). <br />This alternative would be applicable to either natural floodplain <br />depressions or gravel-pit ponds in the floodplains of the Colorado and -- <br />Gunnison rivers that connect with the river on a frequent basis. Mitchell <br />(1995) stated that about 60% of the floodplain ponds, included in his -__ <br />inventory, connected with the rivers either annually or one out of ten <br />years. Reconnection of these ponds with the rivers would allow the <br />productive off-channel habitats to connect with the rivers annually, <br />producing zooplankton that are needed by the early life stages of the <br />endangered fishes. <br />Burdick (1994} developed a conceptual management plan to experimentally test <br />the assumptions that were described in the above paragraphs. In the Fall <br />of 1996, a gravel-pit pond (29 5/8 Road pond) along the Colorado-River near <br />Grand Junction was re-connected with the river. The fish populations using <br />this manmade "embayment" are currently being monitored by the Colorado River <br />Fishery Project of the U.S. Fish and Wildlife Service in Grand Junction, <br />Colorado. This experimental study will provide insight into the use by <br />native fishes, including endangered fishes, and nonnative fishes. The <br />results of this experimental field study will be used for decisions on re- <br />connecting other floodplain ponds with the river and how to best manage such <br />manmade "embayments" in the future. <br />Obviously, this alternative has potential for endangered fish recovery in <br />some of the floodplain ponds but not all. Therefore, it would be premature <br />to re-connect a large number of ponds with the rivers until the response of <br />both native and nonnative fishes is better understood. <br />Because of the limited floodplain area along the Colorado and Gunnison <br />rivers, gravel-pit ponds will be reconnected with the rivers under the <br />Recovery Program element involving habitat rehabilitation and restoration. <br />The number of ponds that will be involved under the habitat element depends <br />upon success in gaining access through willing landowners. Ponds under <br />private ownership on the Colorado River constitute about 73% of the total <br />number and about 44% on the Gunnison River (Mitchell 1995). Therefore, this <br />alternative by itself cannot achieve the level required by the Recovery <br />Program to control chronic escapement of nonnative fishes. <br />No impacts are expected on land use, Indian trust assets, or environmental <br />justice under this alternative. <br />24 <br />