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fish were measured (total [TL] and standard [SL] lengths) and sex and reproductive condition of <br />specimens was noted. Large samples of small-bodied fish captured by electrofishing were <br />simply counted. In addition, rare fishes were individually weighed and scanned for the presence <br />of a PIT tag. If none was detected, a PIT tag was implanted into the body cavity via a heavy bore <br />syringe, and the fish was released. Special care was taken to identify potential catostomid <br />hybrids. We identified these based on morphological characteristics of the mouth and body that <br />were intermediate between putative parental types and on intermediacy of scalation patterns and <br />scale counts in the lateral series (Hubbs and Miller 1953). Vouchers of some specimens, <br />including catostomid hybrids, were preserved in 10 % formalin, and are housed at the Larval <br />Fish Laboratory, Colorado State University. <br />Temporal and spatial changes in fish community composition.-Changes in fish <br />community composition over time were assessed at several levels of resolution and spatial scale. <br />We compared composition and reproductive status of fishes in the regulated reach for time <br />periods corresponding to just prior to closure of Flaming Gorge Dam (historical), just after <br />reservoir filling and commencement of normal operations that began in 1967, after penstock <br />modifications in 1978, and after discharge re-regulation in 1992 (this study). Data were gathered <br />from historical sources (Gaufin et al. 1960, Banks 1964, Smith 1966, Vanicek et al. 1970, <br />Holden and Crist 1981); assessments of reproductive status were made using presence of young <br />fish or by assumptions about the probability of such given water temperature regimes in the <br />reach. Reproductive status of fishes from 1967-1978 was inferred from data gathered in 1964 <br />and 1966 by Vanicek et al. (1970) and data collected in 1978 (Holden and Crist 1981) prior to <br />temperature modifications. Data describing the reproductive status of fishes in 1965 were not <br />used because flows from Flaming Gorge Dam were low and warm in those years and not typical <br />of conditions from 1967-1978 (Vanicek et al. 1970). <br />Changes in species composition and relative abundance of fishes in Lodore Canyon were <br />assessed by comparing fish species composition information collected in the period 1978-1980 <br />(Holden and Crist 1981) to that collected during -1994-1996. Holden and Crist (1981) sampled <br />