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<br />2. Compare habitat measurements from above with Colorado pikeminnow habitat use <br /> <br /> <br />found in previous studies (Miller et al. 1982, Chart 1987, Tyus 1991, and Irving and <br /> <br /> <br />Modde 1994) and habitat suitability curves given in Valdez et al. 1987. <br /> <br /> <br />3. Incorporate data from above to develop an interim year-round flow recommendation <br /> <br /> <br />for Colorado pikeminnow and guidelines for discharge fluctuations a Taylor Draw Dam. <br /> <br /> <br />As a basis for formulating flow recommendations, we took two approaches, protection of <br /> <br /> <br />Colorado pikeminnow habitat and protection of riftle habitat to maintain biological productivity. <br /> <br />We measured meso- (pool, run, eddy, and riftle) and microhabitat (depth, velocity, substrate, and <br /> <br /> <br />cover) changes at three experimental flows. However, we were unable to obtain the low flow we <br /> <br />needed to determine the habitat-discharge relations; as a result, we used physical habitat <br /> <br />simulations to assist in determining these relations. <br /> <br />METHODS <br /> <br />Study Site <br /> <br /> <br />The study area (Figure 1) included the White River from its confluence with the Green <br /> <br />River near Ouray, Utah (i.e., Green River at RM 245), to Taylor Draw Dam, near Rangely, <br /> <br />Colorado (RM 0.0-105). <br /> <br /> <br />Sampling Design <br /> <br /> <br />A stratified cluster sampling scheme (Scheaffer et al. 1979, Bovee 1982, Armour et al. <br /> <br />1983) was used to collect mesohabitat data on the White River. The river was divided into four <br /> <br />strata (see Figure 2 for descriptions, lengths, and locations). The first three strata corresponded <br /> <br />3 <br />