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n <br />' experimentation. The evaluation of these five sites will provide information to <br />help in the selection of future bottomland sites that will be most suitable for <br />' habitat enhancement and restoration, and to improve designs to reconnect <br />bottomlands to the river. Therefore, adaptive management will be employed to <br />make necessary refinements in design and operation. <br />' Most researchers believe that connecting isolated ponds to the river is <br />seasonally beneficial to endangered fishes. In this experiment, ponds that are <br />gently graded and connected to the river will be evaluated for their possible <br />' benefit for endangered fishes by providing off-channel habitats while reducing <br />or minimizing proliferation of non-native fishes that either compete with or <br />predate upon endangered fishes. Two ponds will be evaluated in the same general <br />' stream reach to compare seasonal use by native and non-native fish and food <br />production. It is critical to determine if graded ponds are more beneficial to <br />endangered fishes than ungraded ponds (Valdez and Wick 1983). If isolated ponds <br />' are to be connected to the river as habitat restoration for endangered fishes, <br />evaluations are crucial for decisions on this type of habitat restoration. For <br />example, this might allow managers to make recommendations and provide assisting <br />federal agencies conditions for permits and design of ponds following gravel- <br />mining activities and followup reclamation. <br />Evaluations will commence prior to connection of the larger pond to the <br />' river. Temporal and spatial data on fish species composition and abundance and <br />food production will be collected. Following connection, the ponds will be <br />monitored at least four times annually (more if time permits). Monitoring will <br />continue for a minimum of three years and conducted prior to, during, and <br />' following spring runoff annually. Fall sampling will be conducted if time <br />permits. Seines and entanglement nets will be used to inventory fish. Fishes <br />captured in each of the two ponds will be tagged or marked to determine possible <br />' seasonal movements between ponds and fidelity to the ponds. Tagging and marking <br />of endangered fishes will follow Recovery Program protocol. All other native and <br />non-native fishes will be marked either by fin-clipping, fin punches, or a <br />' combination of the two techniques. <br />Plankton nets will be used to obtain zooplankton densities from pelagic <br />(mid water) and littoral (shoreline) areas. Sampling of benthic invertebrates <br />' and zooplankton species and densities will be conducted to determine seasonal <br />changes in the two ponds and compared with the river. Specific scopes of work <br />for initial inventories, biological monitoring, and evaluation of this proposed <br />' habitat restoration project will be developed and reviewed through the Recovery <br />Program. <br />' Because there are too few riverine razorback sucker in the Grand Valley, <br />adult razorback sucker will be stocked in the immediate stream reach to evaluate <br />their potential use of these "pond habitats". The Recovery Program approved a <br />plan (Burdick 1992) for experimental stocking of about 20 adult razorback sucker <br />' in the Grand Valley. Stocking adult razorback sucker, implanted with <br />radiotransmitters, will allow researchers to obtain habitat use and ecological <br />requirements of this species. Forty-one, pond-reared adult razorback sucker were <br />' obtained from Etter Pond (an isolated pond immediately adjacent to the Colorado <br />River near Debeque) and implanted with long-term (theoretical life expectancy, <br />4-years +) radiotransmitters. Twenty of these fish were stocked into the upper <br />' 17 <br />