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<br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br /> <br />1.0 INTRODUCTION <br /> <br />This document is the Annual Summary Repon for 1993 submitted to the National Park Service and Utah <br />Division of Wildlife Resources in partial fulfillment of UDWR Contract No. 90-2558 entitled Lake Powell <br />Inflow Study: Transport of Age-O Colorado Squawfish During Spring Runoff. This report presents data from <br />the first year of this two year study. <br /> <br />1.1 PURPOSE AND OBJECTIVES <br /> <br />The purpose of this investigation is to monitor the Lake Powell inflow of the Colorado River before and after <br />spring runoff to determine if significant numbers of age-O Colorado squawfish (Ptvchocheilus lucius) and larval <br />razorback suckers (Xvrauchen texanus) are being transported into the area. The objectives of this study are <br />to: <br /> <br />1. Determine the number of age-O Colorado squawfish and larval razorback suckers transponed <br />llllJlually into Lake Powell. <br /> <br />2. Assess the relationship between spring runoff level and numbers of fish transponed. <br /> <br />3. Assess the level of predation on age-O Colorado squawfish by lake-dwelling species. <br /> <br />4. Recommend management strategies to increase survival of age-O Colorado squawfish. <br /> <br />1.2 BACKGROUND <br /> <br />Mortality factors affecting age-O Colorado squawfish in the upper Colorado River basin are not well <br />understood. Although successful reproduction occurs annually, the densities of age-O at the end of their first <br />three months of life are substantially reduced by the time the fish are one year of age (Valdez 1990, Valdez <br />and Masslich 1991, Valdez and CowdeIl1992,1993). One possible explanation for this decrease in density is <br />that age-O squawfish emigrate or are transported to other regions of the river. Recent findings indicate that <br />age-O Colorado squawfish from nursery areas in the lower Green River (RM 50 - 0) may be transponed <br />downstream by periodic high flow events during summer months (Valdez 1990). <br /> <br />Since Colorado squawflsh once ranged throughout the Colorado River Basin, it is reasonable to suspect that <br />age-O Colorado squawflSh actively or passively disperse downstream during spring runoff. Thompson (1989) <br />reponed that growth rates and survival of age-O squawfish are adversely affected by cold water temperatures. <br />Kaeding and Osmundson (1988) hypothesized that temperature regimes in the Upper Colorado River Basin <br />are sub-optimal for growth of age-O Colorado squawfish, resulting in increased early-life mortality and <br />subsequent decline in numbers in the upper basin. The apparent rigors of low temperatures on young <br />Colorado squawfish, in addition to the possibility of sub-optimum temperatures in the Upper Basin, suggest <br />adaptive advantages for downstream dispersal of younger fish to warmer reaches with temperatures more <br />suitable for growth and other physiologic processes. However, this downstream dispersal or transpon today <br />may be blocked by Lake Powell with its limited nursery habitat and large number of predators. <br /> <br />The Colorado River inflow at Lake Powell has been a very dynamic aquatic environment since the completion <br />of Glen Canyon Dam in 1963. Fishery investigation of the inflow were conducted in 1979-82 (Valdez et at. <br />1982), 1983-84 (B. Williams, personal communication), and 1985-92 (Valdez 1990, Valdez and Masslich 1991, <br />Valdez and Cowdell1992,1993). These investigations have revealed variable numbers of endangered Colorado <br />River fishes, including Colorado squawfish, razorback suckers and humpback chub (Gila mlW. <br /> <br />1 <br />