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abundance or remained rare over the three study periods; speckled dace and roundtail chub <br />showed particularly large declines. Ten introduced taxa increased in abundance, rainbow trout <br />declined in abundance, and five others remained similar in abundance between the two earliest <br />periods. Largest increases were by fathead minnow, sand shiner, white sucker, and hybrid <br />suckers. Between the 1994 to 1996 and 2002 to 2004 periods, fathead minnow, redside shiner <br />and all salmonids declined, and sand shiner and red shiner increased dramatically. <br />Species composition shifts at both sites suggested a progressive shift from a cold water <br />fish community to one dominated by cool-water or warm-water taxa, with non-native warm water <br />fish progressively invading and establishing upstream. The number of fish in samples in each of <br />the upper and lower Lodore Canyon sites in the two earlier periods was similar, but more fish <br />were sampled in the later 2002 to 2004 period. Although the likely reason for the increase is due <br />to a larger number of seine samples in the last period, we feel as though the overall trends are <br />reflective of the entire fish community and not due just to increased sampling in backwaters. <br />This limited data set of electrofishing and seine captured fish at these two Lodore Canyon <br />sites showed an opposite trend of declining incidence of hybrid suckers compared to canyon-wide <br />data collected in the same period. We believe this is an artifact of combining data using different <br />gear types, because increased abundance of seine-collected small-bodied fish in the recent sample <br />reduced the percent composition of hybrids, which are most commonly detected among the fewer <br />relatively large-bodied fish. <br />SUMMARY <br />A main tenet of dam re-regulation to create more natural flow and temperature regimes is <br />that native fishes will benefit (Stanford et al. 1996, Poff et al. 1997, Muth et al. 2000). The data <br />sets presented here were used to evaluate that hypothesis. <br />Flow and temperature effects on the Green River fish community between 1994 to 1996 <br />and 2002 to 2004.-Evaluating biotic response to flow and temperature recommendations is a <br />considerable challenge given the multitude of factors that can affect the distribution and <br />65