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separating it from the river with heavy machinery (back hoe). This work would <br />be accomplished during low-flow periods prior to or after runoff. <br /> <br />Potential Impacts from Operations on Native Flora and Fauna <br />No razorback sucker have been reported recently in the immediate area of <br />these two proposed sites at the Escalante SWA. However, a small remnant <br />population of Colorado squawfish resides in the Gunnison River downstream of the <br />proposed area. One radiotagged Colorado squawfish was located at river mile 48.4 <br />in the Gunnison River in 1993 (Unpublished data, USFWS). This same fish was <br />located at river mile 59.1 in May 1994, indicating that it had passed by the <br />Escalante SWA sometime between October 1993 and May 1994. <br />At the present time, it is anticipated that the operations at the sites <br />will benefit native endangered fishes. If necessary, operations will be modified <br />to benefit native endangered fishes. <br />PROPOSED EVALUATION <br />11 <br /> <br /> <br />Factors to be Evaluated <br />Evaluations are essential to determine if the action was beneficial, <br />detrimental, or had no affect on the intended target species. Each of the five <br />selected sites were intended to be "pilot" or "test" sites for experimentation. <br />The evaluation of these five sites will provide information to help in the <br />selection of future bottomland sites that will be most suitable for habitat <br />enhancement and restoration, and to improve designs to reconnect bottomlands to <br />the river. Therefore, adaptive management will be employed to make necessary <br />refinements in design and operation. <br />The specific factors to be evaluated differ greatly at the two sites at <br />Escalante SWA because of the nature of the proposed development. <br />Site 1. The proposed development at Site 1 was designed to take advantage <br />of a former natural riverine feature now isolated from the river. Although this <br />extensive development is not economical or practical at all potential sites, it <br />provides a variety of habitats and separate experimental units that are needed <br />to determine ecological requirements of early life stages. Few floodplain areas <br />provide this opportunity. Several questions still need to be answered regarding <br />factors that are limiting some of the endangered fishes. Except for the bonytail <br />which is functionally extirpated in the upper Colorado River basin, immediate <br />concern is for the recovery of the razorback sucker. <br />Waterborne selenium levels in the Gunnison River near the Escal ante SWA are <br />' elevated (range at study sites: 3-7 ug L-1; Cooper and Severn 1994c). Selenium <br />and other trace elements are thought to impair reproductive success of razorback <br />sucker and larval fish (Appendix B). To date, only laboratory tests using <br />reconstituted water from sites known to have levels of trace elements that impair <br />early life stages of endangered fishes in the Colorado River basin have been <br />conducted. Laboratory tests of seven trace elements (vanadium, zinc, selenite, <br />20 <br />