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<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 />13 <br /> <br />River contains the most viable remaining population of the Colorado <br />squawfish and that any further development of the Grp.en River basin <br />could severely affect the continued reproductive success of squawfish. <br />He judged that the major threats to the squawfish are loss of habitat <br />through dewatering, altered streamflow patterns, and competition with <br />exotic fish species. <br />Joseph et al. (1977) noted that on the basis of the available <br />data, the Green River from its confluence with the Yampa to its ter- <br />minus at the Colorado River is important habitat for all four rare and <br />endangered species in the Colorado System, i.e., the Colorado squawfish, <br />razorback sucker, humpback chub, and bony tail chub. <br />BIO/WEST, Inc., has been sampling a station at Jensen for the <br />past two years as part of a study to determine the effects of Flaming <br />Gorge Dam penstock modifications upon fishes in the Green River. Young <br />and adult squawfish and adult razorback suckers have been captured <br />there with some frequency (Holden and Crist 1978) (Table 1). <br />Benthic Macroinvertebrates - Information on the benthic inverte- <br />brates of the Moon Lake study reach of the Green River is found in only <br />two reports. Pearson (1967) studied the distribution of macroinverte- <br />brates in the river. While most of his emphasis was on the reach im- <br />mediately below Flaming Gorge Dam, he did establish supplementary sites <br />at Split Mountain and at Ouray. At Split Mountain, mayflies (Ephemeroptera) <br />and chironomids comprised a major portion of the invertebrate fauna in <br />1964 and 1965. Pearson stated that the Split Mountain data was generally <br />similar to data he collected in Island Park 12 miles upriver. The Ouray <br />