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<br />300 C. Differences in optimum food abundance for <br />growth (342 nauplii fish-1 day-I) and survival (235 <br />fish-l day-I) suggests that growth continued to in- <br />crease with increasing food abundance, but that sur- <br />vival reached a high plateau at a lower food abun- <br />dance. <br /> <br /># <br /> <br />Starvation resistance <br /> <br />, <br /> <br />Starvation has often been hypothesized as a factor <br />important in regulating recruitment in fish popula- <br />tions (Miller et al. 1988). Starvation resistance in <br />fish larvae is generally a function of body size at <br />hatching; larger fish are more resistant than smaller <br />ones (Miller et al. 1988). Colorado squawfish larvae <br />denied food for up to 17.5 d after feeding was first <br />possible (23.5 d after hatching) were resistant to <br />starvation, but survival was low for fish denied for <br />20 d (26 d after hatching). Time to 50% mortality <br />was estimated to be between 17.5 and 20 dafter <br />feeding could begin, or 23.5 to 26 d after hatching. <br /> <br />Ecological applications <br /> <br />, <br /> <br />Results of this study indicate that maximizing tem- <br />perature and food abundance in backwater habitat <br />should benefit growth and survival of Colorado <br />squawfish in early life. Because relatively small <br />changes in growth and survival rates may cause sub- <br />stantial changes in annual recruitment levels of fish- <br />es (Houde 1987, Crowder et al. 1992, Rice et al. <br />1993), enhancing temperature and food abundance <br />should also benefit recruitment of Colorado squaw- <br />fish. Number and area of backwaters, and growth <br />and abundance of age-O Colorado squawfish are all <br />negatively correlated with discharge levels in upper <br />Green River (Tyus & Haines 1991), so lower sum- <br />mer flows in regulated streams should benefit <br />growth and survival oflarvae. It is important to note <br />that these backwaters are ones within the bankfull <br />channel that are formed as high spring flows recede <br />and should not be confused with inundated flood- <br />plain lowlands that result from overbank flooding. <br />Backwaters that have relatively low exchange rates <br />with cooler main channels have greatest potential <br /> <br />207 <br /> <br />to provide warm, food-rich environments, but are <br />also the most susceptible to drying under fluctuat- <br />ing flow regimes. Blinn et al. (1995) found that a sin- <br />gle 12 h desiccation event, which was caused by arti- <br />ficial flow fluctuations of the Colorado River down- <br />stream of Glen Canyon Dam, Arizona, reduced <br />benthic macroinvertebrate mass by ;;:: 85%. Thus, <br />non-natural river fluctuations such as those caused <br />by power-production water releases from dams <br />should be minimized in order to maximize backwa- <br />ter temperature and productivity. <br />Diel temperature fluctuations in backwaters may <br />motivate movements of early life stages of Colora- <br />do squawfish from warm backwaters during the day <br />to relatively warm main channels at night when <br />backwaters are cool (Tyus 1991b). Such movement <br />patterns may maximize diel degree day accumula- <br />tion and growth potential of Colorado squawfish. <br />Growth of Colorado squawfish larvae may be limit- <br />ed in river reaches where main channel temper- <br />ature regimes are < 220 C. <br />Starvation resistance times for Colorado squaw- <br />fish larvae are probably shorter in the wild than in <br />the laboratory because of increased energetic costs <br />of negotiating large and swift rivers, avoiding pred- <br />ators, and securing suitable nursery habitat. High <br />and extended spring runoff, floods, and river fluctu- <br />ations caused by dams are among the factors that <br />may affect ability of larvae to find and maintain po- <br />sitions in productive backwater habitat and avoid <br />starvation. Nevertheless, relatively high resistance <br />of Colorado squawfish larvae suggests that direct <br />starvation mortality may be unimportant in wild <br />populations except during rare events. However, <br />reduced growth may result in increased mortality <br />by increasing the amount of time larvae are suscep- <br />tible to predators. <br />Further research is needed to link results of <br />growth, survival, and starvation resistance studies <br />to annual, seasonal, or daily discharge and temper- <br />ature regimes in main channels of the Colorado <br />River Basin. Interactions between feeding and <br />growth rates of early life stages of Colorado squaw- <br />fish under various environmental conditions, and <br />competition and predation are largely unstudied <br />but may playa significant role in structuring recruit- <br />