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Backwater availability in July and August was positively correlated with both flow at the time of <br />sampling (RZ = .87) and annual peak flow at the State Line gage (RZ = .86). This relationship held true <br />for sample flows nearing 9000 cfs, but appeared to break down at higher flows when many of the side <br />channels became reconnected to the main channel. Backwater habitats were virtually non existent when <br />this stretch was sampled 07 July 93 and the river was flowing at 13,800 cfs. At extremely high flows, <br />(22 June 95; approx. 40,000 cfs), the only true low velocity habitat was the flooded mouth of Westwater <br />Wash. <br />Westwater Canyon fRK 199.2 - 190.4) <br />In this 8.8 km sub-reach, backwaters were not abundant. Only three or four backwaters formed <br />each year following the high spring flows in this canyon stretch. As was the case in the Above Canyon <br />sub-reach, the backwaters that did form varied minimally from year to year at a given flow. Due to the <br />paucity of low velocity habitats in the canyon proper, shorelines were the most commonly (39.3%) <br />sampled habitat followed by backwaters (29.7%), embayments (20.0%) and others (see Table 6 above). <br />The backwater and embayment sampling effort was representative of actual availability. Conversely, <br />shoreline habitats were less discrete and were even more abundant than the relative abundance values <br />would suggest. The less frequently sampled habitat types (side channel, pools, isolated pool, and flooded <br />tributary mouth) were accurately represented in terms of availability. <br />The multinomial analysis of YOY chub presence /absence by habitat type indicates there was no <br />selection at this level of resolution (p=0.94) (Table 9). YOY chubs were distributed among all habitat <br />types as was expected based on the distribution of sampling effort. <br />Table 9. Multinomial analysis for use of habitats by YOY Gila spp. in the Westwater Canyon sub- <br />reach (Colorado RK 199.2 - 190.4), Utah. Data collected in July and August, 1992, 1994, <br />and 1996 and July -Sept., 1993 and 1995. <br /> <br />HABITAT <br />TYPE <br /> <br />N= <br />Obs. % of <br />Hab. Type Obs. # of <br />Nabs w/YOY <br />chubs Exp. # of <br />Nabs w/YOY <br />chubs <br />Chi-square <br />factor. <br />BW 28 30.1 16 17.16 0.08 <br />SH 37 39.8 21 22.69 O.13 <br />EMB 18 19.3 13 ] l .00 0.36 <br />PO 1 1.1 0 0.63 0.63 <br />IP 3 3.2 2 1.82 0.02 <br />F1' 4 4.3 3 2.45 0.12 <br />SC 2 2.2 2 1.25 0.44 <br />Overall Chi-square =1.78; p=0.94; df=6 <br />A similar analysis accounting for the densities of YOY chub occupying each habitat type <br />indicates YOY chubs were not uniformly distributed throughout the habitat types (Table 10; Figure 9). <br />YOY chubs were collected in shoreline habitats as was expected, based on the distribution of sampling <br />effort and the total number of YOY chubs collected in Westwater Canyon. There was an apparent <br />selection for embayment habitats. However, young of year chubs did not select for backwaters in <br />Westwater Canyon. <br />11 <br />