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1 <br /> <br /> - At Oura backwaters used b Colorado ike ' <br />y, y p minnow had mean length 1.8 times that of <br /> unused backwaters. Likewise, mean width was 1.7 times greater and mean volume 2.2 <br />times greater. <br /> <br /> - Secondary (scour) channel backwaters had mean surface azea, mean depth, cover, and <br />aspect values closest to those of the "avera <br />e" backwater <br />d b <br />l <br />C <br />d <br /> g <br />use <br />y <br />o <br />ora <br />o <br /> pikeminnow. <br /> - Secondary (scour) channel habitats made up the majority of available habitat and were <br /> chazacterized by lazge size, depth, and stability. These tend to be perennial habitats <br /> that change primarily as a result of river levels, but aze available every yeaz. Because of <br /> their wide mouths and positioning in the river system, they accumulate more fine <br /> substrate and may also more readily capture drifting larvae and food items. They <br />'~, generally do not have the extreme temperature fluctuation seen in smaller backwaters. <br />- Temperature appeazed to play a role in habitat selection by Colorado pikeminnow in <br />this study during spring and summer. In summer samples, backwaters containing <br />Colorado pikeminnow were significantly warmer than others, but the difference was <br />only 1.0°C. Similar results were seen in spring backwater samples, but significance <br />was atp<0.10. Backwaters used in the spring were actually closer (+2°C) to main <br />channel temperature than unused backwaters (+3.1 °C). <br />- Turbidity has also been noted as a distinguishing characteristic for Colorado <br />pikeminnow use. Backwaters with Colorado pikeminnow were more likely to have <br />higher turbidity ratings than unused backwaters. Colorado pikeminnow were found <br />more often in backwaters opening in a downstream direction. <br />- The inability to develop an easily applicable model for discriminating between suitable <br />and unsuitable backwaters is problematic, but not entirely unexpected. Extreme <br />variability in backwater formation and availability, river conditions, and Colorado <br />pikeminnow cohort strength between years precluded developing this simple model. <br />However, the models produced are promising for eliminating backwaters from <br />consideration. <br />- <br />At Mineral Bottom, nonnative cypruuds selected for secondary (scour) channel habitats. <br />Although they were present in almost all habitats, catch rates were higher in scour <br />channel habitats. <br />- At Ouray, fall catch rates of nonnative cyprinids were positively associated with high <br />spring flows. At Mineral Bottom, they were negatively associated. <br />- This study found a high degree of variability in the correlation of CPLTE for the various <br />fish species. Both native and nonnative fish had examples where positive and negative <br />xvi <br />