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Larval. Larvae have little chance for survival if water currents are <br />insufficient to keep them from settling to the bottom (Barkuloo 1970). Newly <br />hatched larvae tend to settle to the bottom of an aquarium filled with un- <br />agitated water despite swimming efforts to remain near the. surface (Pearson <br />1938; Mansueti 1958). Larvae likely require currents or turbulence for up to <br />15 hours post-hatch (Meinz and Heubach 1978). Tests conducted by Morgan <br />et al. (1976) indicated that eggs and larvae have about equal specific gravity. <br />It is assumed that a minimum current velocity of 30.5 cm/s (1 ft/s), which is <br />the velocity required to float eggs (Albrecht 1964), is necessary to buoy <br />larvae until suspension can be maintained by swimming. <br />Current velocities higher than the minimum required to buoy eggs or <br />larvae could be detrimental by moving eggs downstream into the slack water of <br />a reservoir prior to hatching or by carrying larvae into slack water before <br />they can maintain suspension by swimming. High velocity also may result in <br />shear levels that damage eggs and/or larvae. Exposure of striped bass eggs to <br />a shear level of 350 dynes/cm2 killed 36% of the eggs in 1 minute, 69% in <br />2 minutes, and 88% in 4 minutes; exposure of larvae to 350 dynes/cm2 killed <br />9.3% in 1 minute, 30.0% in 2 minutes, and 68.1% in 4 minutes (Morgan et al. <br />1976). Marcy (1971, 1973) and Morgan et al. (1976) presented information <br />which indicated that a water velocity of about 240 cm/s (7.9 ft/s) created <br />shears approaching the damaging range for striped bass eggs and larvae. <br />Lacustrine Habitat Requirements <br />Water temperature and dissolved oxygen concentration are the principal <br />variables that determine suitability of lacustrine habitat for striped bass. <br />Water temperature (U1~Vp, and USA. Temperature preferences of striped <br />bass likely vary by locale, apparently change with age and an increase in size <br />(Schaich 1979; Coutant 1980, 1983, 1985), and influence lacustrine habitat <br />selection by juveniles and adults (Waddle 1979; Coutant and Carroll 1980; <br />Cheek 1982). <br />Adult (temperature, VSO. The lower avoidance temperature by adults in <br />Cherokee Reservoir, Tennessee, was about 18.5° C (65.0° F) (Schaich 1979). <br />This was near the lower avoidance boundary for adults in coastal waters <br />(Radovich 1963) but higher than temperatures of 13.9 to 17.2° C (57.0 to <br />63.0° F) in areas in the San Francisco Bay where many adults spend the summer <br />(Crance 1985). <br />Adults in Cherokee Reservoir avoided water above 25° C (77° F) (Waddle <br />1979; Schaich 1979); adults apparently avoided water temperatures of 24 to <br />25° C (75.2 to -77.0° F) in Watts Bar Reservoir, Tennessee (Cheek 1982). <br />Merriman (1941) reported that adults avoided coastal waters above 25 to 27° C <br />(77 to 80.6° F). Dudley et al. (1977) observed that adults in the Savannah <br />River, Georgia, avoided temperatures over 26° C (78.8° F). Concentrations of <br />adults were found in areas of Lake Whitney, Texas, in temperatures ranging <br />from 27.5 to 29.0° C (81.5 to 84.2° F) when cooler water was available in the <br />lake (Crance 1985). <br />16 <br />