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<br />Cessation of spawning causes a renewed interest in food as <br />striped bass become more vulnerable to anglers. Increasing <br />surface temperatures gradually force adult fish deeper toward the <br />preferred temperature zone of 64-68 F. Cooling temperatures in <br />fall allow all sizes of striped bass and shad populations to <br />commingle once again and results in some of the best fishing of <br />the year. The catch rate of striped bass is often highest in the <br />late summer and fall (Figure 7). <br /> <br />MANAGEMENT STRATEGIES <br /> <br />Forage Introduction <br />With the discovery of natural reproduction in 1979, plans <br />were made to circumvent potential striped bass over-population. <br />stocking was immediately curtailed. Creel limits were increased. <br />Unfortunately, striped bass responded more quickly to lack of <br />food than rules could be changed to deal with the problem. <br />Elimination of shad from the open water in the 1980's and <br />subsequent decline in striped bass condition led to a proposal to <br />increase forage by adding another schooling pelagic forage <br />species (Gustaveson et ale 1990). It was proposed that <br />introducing rainbow smelt (Osmerus mordax) would provide a deep <br />water forage fish. The smelt introduction was never made due to <br />objections from other state and federal agencies against any new <br />fish introduction into the Colorado River system. The imperiled <br />nature of remnant populations of endangered Colorado River fishes <br />precluded the smelt introduction because the unknown risk of new <br />species interactions on the remnant fish populations was <br />unacceptable. <br /> <br />38 <br />