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RECOMMENDATIONS One difficulty in monitoring the striped bass spawning run is the unpredictable effect of fluctuating spring water temperature on timing of the run. A longer time period is needed in the field to cover not only the movement upstream but also the postspawning return to the reservoir. Any predation on native fishes would be more likely to occur after spawning when appetite of the fish returns. Coverage of the run at Gypsum Canyon should commence the first week of May and extend at least through the month of June. In addition, sampling above Cataract Canyon should commence before or at the latest when females enter the catch at Gypsum and continue until the run returns to the lake. Sampling crews are needed both above and below Cataract Canyon because if the lower crew shifted to above the canyon when females entered the catch and the run did not reach above the canyon, data for the year would be lost. Current gillnet mesh size is 6.4 cm (2.5 in) bar measure. If information on larger or smaller native fishes is desired, then additional mesh sizes such as 3.8 cm (1.5 in) and 8.9 cm (3.5 in) should be fished. If other mesh sizes are used, they should be fished in addition to the present size so that catch of striped bass is not diminished. The large amount of floating debris reduces the efficiency of the ichthyoplankton nets fished for bass eggs and larvae. As noted in the results section, the nets could only be fished for 2-3 minutes before filling with debris. The current mesh size of 0.565 mm is needed to catch bass larvae, but could be increased in size if only eggs were being sought with the plankton nets. The increase in mesh size would not reduce the amount of debris signi- ficantly but would lengthen the fishing time somewhat. Additional types of gear such as plexiglas larvae traps should be considered for capturing larvae after they complete the pelagic stage of life.