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swim bladder inflation and exogenous feeding. Despite statistically significant <br />differences in lengths of larvae in some treatments, it is improbable that the small <br />differences observed for either newly hatched (difference among mean lengths in <br />treatments < 15%) or 7 d post-hatch larvae (difference < 5%) are of ecological <br />significance. Different endogenous feeding rates between treatments may be the reason <br />for differences in fish lengths. <br />Times to developmental events and length measurements were recorded <br />irregularly in the 30°C treatment due to low hatching success and poor condition of larvae <br />and may be less accurate than those reported for the other treatments. Time of first hatch <br />and swim bladder inflation may not represent the norm due to rare events (e.g., very early <br />hatch or air bladder inflation in a single fish). The times to first feeding that I report are <br />more reliable because most fish in a treatment chamber began to feed almost <br />simultaneously, thus reducing the potential influence of rare events. <br />Management implications.--Colorado squawfish apparently have complex <br />adaptive strategies for reproduction in historically fluctuating riverine habitats of the <br />Colorado River basin and tnay use discharge level and variation, and water temperature, <br />as primary environmental cues to initiate reproduction (Nesler et al. 1988; Tyus 1990). In <br />its unregulated state, flow and temperature regimes in the Colorado River basin varied <br />dramatically across seasons and years. Given such variability, eurythermicity of embryos <br />and early larvae is not surprising. <br />Reduced summer water temperature is thought to be partially responsible for <br />extirpation of Colorado squawfish in river reaches immediately downstream from dams <br />(Holden 1979; Behnke and Benson 1983; Marsh 1985). Reestablishment of self- <br />18 <br />