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<br />6 <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 />barriers to historic bottomlands, and by providing sufficient flow to inundate bottomlands in a manner that <br />approximates the natural hydrograph. Because the peaks and duration of high flows have decreased in the <br />post-water development era, it will be necessary to regain connectivity of wetlands at the lower flows and <br />maintain water in these sites as long as possible. Management (Le. draining, water elevation control, etc.) <br />of flooded bottomlands may be needed during the early phases of the recovery process to reduce the <br />abundance of exotic predators and allow for the marking of razorback sucker produced in these nursery <br />sites. The marking of fish produced in rehabilitated bottomlands is necessary to monitor the importance of <br /> <br /> <br />these sites to recovery. Specific bottomland management strategies have yet to be developed which would <br /> <br /> <br />maximize recruitment. In isolated coves in Lake Mohave, Mueller et a!. (1993) have been successful in <br /> <br /> <br />rearing razorback sucker to nearly adult size in a single growing season. In the Upper Colorado River Basin, <br /> <br /> <br />two growing seasons may be required before razorback sucker would be impervious to piscivorous <br /> <br />predation. <br /> <br />PROPOSED DEVELOPMENT <br /> <br />Old Charley Wash is encircled by both natural and man-made dikes and has been developed and <br /> <br /> <br />managed as a waterfowl production site by the U.S. Fish and Wildlife Service since 1961. As such, the <br /> <br /> <br />wetland has inlet and outlet structures that control water entry and release. Options available for <br /> <br /> <br />management of the wetland include passive management which allows periodic flooding, but, does not <br /> <br />reconnect the wetland to the river at the end of the growing season. This strategy has been in effect for <br /> <br /> <br />over thirty years with little perceived benefit to endangered fishes. The second option is to actively manage <br /> <br /> <br />the bottomland to maintain water levels, restrict. potential fish predators and allowing the capture of fish <br /> <br /> <br />produced at the end of the growing season. <br /> <br /> <br />Inflow into Old Charley Wash can be controlled until river elevations approach 14,000 cfs, at which <br /> <br /> <br />time water flows over the downstream dike and into the wetland. During October 1993, a fish access control <br /> <br /> <br />structure was constructed at the outlet to Old Charley Wash at a cost of $87K (Appendix 2, Figures 1 and <br />