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10 <br />Sucker larvae used in this study ranged in age from 40-52 days (about 26-32 days <br />after swimup) and were in the late mesolarval to mid metalarval developmental stages <br />[terminology after Snyder (1981)]. Wild suckers are generally <40 days old when they <br />reach the lower Williamson River and Upper Klamath Lake as protolatvae or early . <br />mesolarvae (Dunsmoor, unpublished data). Miller et al. (1988) demonstrated an inverse <br />relation between larval developmental stage or size and susceptibility to predation, <br />primarily resulting from ontogenetic increases in predator detection (vision and lateral <br />line development) and avoidance (fin and muscle development) capabilities. Therefore, <br />due to age-related developmental differences, wild sucker larvae just entering.their <br />rearing habitats in Upper Klamath Lake may be even more susceptible to predation by <br />fathead minnows than the larvae used in these experiments. <br />Availability of sucker larvae as prey for fathead minnows in the wild is most likely <br />determined by factors which influence their encounter frequency and/or ability to evade <br />fathead minnows. If sucker larvae change habitat use patterns through ontogeny, <br />encounter rates with specific predators may also change. When prey and predators <br />coexist in the same habitat, complex habitats provided by macrophytes generally reduce <br />foraging efficiency of fish predators (Boyle 1979; Cooper and Crowder 1979; Savino and <br />Stein 1982; Heck and Crowder 1991). Consequently, the typical result of water <br />drawdowns in reservoirs is an increase in predation as forage fish are forced to abandon <br />refugia in littoral areas, becoming concentrated and more available to predators (Ploskey <br />1986). <br />Results of trial six follow this general pattern, in which efficiency of fathead <br />minnow predation on larval suckers was reduced in the presence of cover. The statistical <br />analysis was complicated somewhat by an outlier, but the nonparametric statistical <br />analysis showed significantly lower predation rates in the low water treatment when <br />cover was present. Parametric ANOVA with the outlier excluded showed a significantly <br />lower mean predation rate in the presence of cover regardless of water depth (P<0.06). <br />Specifically, excluding the outlier, mean predation rates were 96.6% (11.3% SD) with <br />cover absent, and 63.3% (18.4% SD) with cover present. The observed 33% decrease in <br />mean predation rate resulting from the addition of cover to tanks is biologically <br />significant because an influence of this magnitude on survival of the larval life stage <br />could be influential in year class formation for the endangered suckers in Upper Klamath <br />Lake. <br />Another factor that can influence prey selection by a predator is the presence of <br />alternative prey items (Hodgson and Kitchell 1987). In trial five of this study fathead <br />minnows had access to sucker larvae, Daphnia, and dry food. Presence of alternate prey