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able to obtain reliable information on the response of the fish community to flow and - temperature effects, but only at the lower end of the flow spectrum and the high end of the temperature spectrum. Flow and temperature conditions observed in 2002 to 2006 fell within the bounds for recommendations that would be implemented in years with low or moderately low water availability, which happen in only 30% of flow years. Average, moderately high, and high flow years, which occur the other 70% of the time, were not evaluated because those conditions were not realized during this study period. Additional years of sampling when those flow conditions are available are needed to fully assess the combined effects ofnon-native fish removals as well as flow and temperature recommendations for Flaming Gorge Dam on the lish community of the Green River. We recommend additional monitoring of water temperatures, flows, and the fish community of the Green River in Browns Park, Lodore and Whirlpool canyons, and Island- Rainbow Park. Comparisons of fish community response to different levels offish removal in the study area (Green River up and downstream of the Yampa River) and flow and temperature regimes from Flaming Gorge Dam may enhance understanding of factors that may limit invasive species, particularly predators, and enhance native fishes. Care needs to be taken when iinpleinenting these studies so that effects of fish removal and concurrent effects of flow and temperature regimes from Flaming Gorge Dam on native fishes are not inextricably confounded We offer some suggestions for that, perhaps including additional sampling in the lower Yampa River. We also recommend PIT-tagging and scanning all chubs captured, including roundtail chubs, and continued removal of predaceous and other non-native fishes from the study area. viii