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<br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />r <br />I <br />I <br />I <br />, <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br /> <br />35 <br /> <br />habitat does not change from a backwater to a run on a daily basis, <br />thus reducing the need for daily movement to new areas or the increased <br />exertion of remaining in one area. This data should be compared to in- <br />formation from areas without daily fluctuations, as this habitat prefer- <br />ence may have considerable survival value in the natural situation. <br />The permanency or longevity of these small backwaters is generally <br />no more than a month during mid-late summer as the river is receding <br />fairly rapidly. We suspect they are more permanent in fall and winter, <br />although we have never conducted studies during those months. <br />The failure to capture any bony tail chubs was normal as this spe- <br />cies is very rare and may be well on the road to extinction. The last <br />known adult bony tail in the upper Colorado Basin was taken from the <br />study area in 1977 (Holden 1977). Failure to capture humpback chubs <br />was also expected as they prefer canyon areas with swifter current and <br />have rarely been taken in this section of the river. <br /> <br />Benthic Macroinvertebrates <br />The general trend noted in the invertebrate data is typical for <br />rivers with large spring floods. During the high water period, samples <br />are taken in areas that are generally dry and therefore numbers of or- <br />ganisms are usually low compared to lower flow periods. This was <br />obvious in the Moon Lake data as well as that collected by Holden and <br />Crist (1978) in the Green River about 40 km upstream. The large num- <br />ber of organisms found in the May lower station sample exemplifies this <br />phenomenon very well. The river rose over 60 cm between May 15 when <br />