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INTRODUCTION <br />The Green River forms the major northwest section of the Colorado <br />River basin (Fig 1), which occupies approximately eight percent of the <br />continental land mass of the United States. Because the river basin was <br />isolated from other river basins for millions of years, 74% of its fish fauna are <br />C,:I <br />y endemic species (Behnke and Benson 1983). Extreme variability in flow, <br />t turbidity and temperature created a harsh aquatic ecosystem. In the upper <br />portions of the Colorado River basin, above Lees Ferry, Arizona, only 13 <br />species coevolved. <br />The Colorado River is one of the most highly developed river systems <br />in the world (Carlson and Muth 1989). Although fed by mountain snowmelt, <br />most of the Colorado River drainage passes through and land. Increasing <br />regional population has placed great demands on its water resources and stress <br />on native biota and natural river function (Davies et al. 1994). <br />Dams and diversion structures blocked migratory routes, altered flows <br />and water temperatures, and diverted young and adult fishes from the main <br />river into canal and irrigation systems. When high flows passed through levied <br />areas on the Colorado River, channel beds degraded, or rivers broke through <br />levees. Spawning and nursery habitats utilized by native fish were severely <br />disrupted, causing fish displacement. emigration and recruitment failure. <br />Native fishes evolved unique adaptations to the historic river flows and <br />geomorphic structure. However. these adaptations became disadvantages for <br />native fish as a result of altered flows. temperature, sediment discharge, <br />blocked access to floodplain habitat, and introduction of nonnative species. <br />