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include predation, competition, and starvation, which often interact with environmental <br />conditions that influence growth to regulate recruitment of larvae (May 1974, Hunter <br />1981, Houde 1987, Bailey and Houde 1989). <br />Most populations of endangered Colorado squawfish Ptychocheilus lucius of the <br />Colorado River basin may be recruitment-limited (Tyus 1991). In Green River, which is <br />the largest remaining population, annual densities of juveniles in fall (recruits) vary from <br />near zero up to 75 fish/100 m2 of backwater habitat (Tyus and Haines 1991). However, <br />the relative effects of discharge regime, habitat alterations, and introduced fishes on <br />recruitment among and within years is poorly understood. I designed laboratory <br />experiments (chapters 1-3) and a field study (chapter 4) to evaluate the relative <br />importance of physical and biological factors on recruitment of age-0 Colorado <br />squawfish. <br />Experiments described in chapter one (Bestgen and Williams 1994) were used to <br />evaluate effects of different water temperatures, and constant and fluctuating temperature <br />regimes, on hatching success of Colorado squawfish embryos and survival of larvae to 7 <br />d. In chapter two (Bestgen 1996), growth and survival of larvae was measured at four <br />different water temperatures levels, constant and fluctuating temperature regimes, and at <br />five different levels of food abundance. In addition, an experiment to determine <br />starvation resistance of squawfish larvae was also conducted. Chapter three (Bestgen <br />and Bundy; submitted to Transactions of the American Fisheries Society) details <br />experiments to validate the use of otoliths in determining age and growth rate of <br />Colorado squawfish larvae and juveniles reared at different water temperatures with <br />constant and fluctuating regimes, and different food conditions. <br />2 <br />