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<br />habitat use studies in the UCR should be interpreted carefully because habitat <br />alteration has been extensive and because so few fish were available for study. <br />Therefore, it would be prudent to compare habitat preferences in this part of the basin <br />~ with those of other populations, especially in the Green and Yampa rivers where there <br />are fewer barriers to fish movement. As indicated previously, habitat use in the <br />unregulated portion of the basin is somewhat variable, and appears to differ from that <br />reported for the 15-Mile Reach. <br />~ In general, the larger (subadult and adult) Colorado pikeminnow will move into upper <br />river reaches when there is opportunity. For example, adult pikeminnow in the Yampa <br />River frequently travel as far upstream as Craig, and have been reported as far <br />upstream as Steamboat Springs. In the White River, before Taylor Draw Dam was <br />closed, pikeminnow traveled up river as far as Meeker: Historical records from the <br />~ Gunnison River basin place Colorado pikeminnow in the lower Uncompahgre River, and <br />data from the recently-completed Redlands fish passage structure show that subadults <br />from the lower UCR are now moving into the lower Gunnison River (F. Pfeifer, personal <br />communication). In all three instances adult Colorado pikeminnow were occupying, or <br />seeking, habitat that is comparable to~the Colorado mainstem above Palisade; such <br />adult habitat may be higher quality, in terms of physical and biological features, than <br />that found further downstream. The shortage of high-quality nonspawning habitat may <br />hinder expansion of the number of adult Colorado pikeminnow in the UCR. <br />The conclusion that high quality adult habitat is limited in the 15-Mile Reach in low-flow <br />years also has been reached by the USFWS (Osmundson et al. 1995). Their proposed <br />~ remedy involves optimizing adult habitat by providing higher minimum flows. <br />Underlying the USFWS proposal are the following assumptions that are standard for <br />instream flow methodologies: (1) the observed pattern of physical habitat use is <br />indicative of requirements, and (2) satisfying the apparent physical habitat requirements <br />will increase the carrying capacity of the riverine environment leading to an increase in <br />~ the number of adult Colorado pikeminnow, unless the population is really held in check <br />by another limiting factor. Both assumptions merit review. <br />Physical habitat conditions are obviously important, but may not be the primary factor <br />constraining the abundance of adult pikeminnow. The historic prey of adult pikeminnow <br />~ were native suckers and chubs. These prey species are more abundant in the upper <br />river reaches (e.g., the Yampa above Maybell, the White River above Rangely, and the <br />Colorado River above Palisade; (VV.H. Miller et al. 1982bc, Tyus et al. 1982a, Valdez et <br />al. 1982). Where adult pikeminnow have access to upper river reaches, they tend to be <br />more abundant where the prey are more abundant. Flannelmouth suckers and adult <br />~ Colorado pikeminnow congregated below Taylor Draw dam after it was closed, <br />presumably because they sought access to °preferered° habitat upstream (Chart and <br />18ergersen 1992, Trammell et al. 1993). The tendency of the adult Colorado <br />pikeminnow to be distributed in river reaches that contain their preferred prey is well <br />supported by the data, and argues that, for most of the year, physical habitat may be of <br />less direct importance to the Colorado pikeminnow than the distribution of the prey. As <br />29 <br /> <br />