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Sand shiner was found in all study reaches and increased in abundance downstream (Fig. <br />27). Similar to red shiner, sand shiner distribution and abundance in Lodore Canyon increased <br />in 2002 to 2004 compared to 1994 to 1996. Relative abundance of sand shiner in seine samples <br />increased most in LD3 and LD4 in 2002 to 2004 and it was more common in the IRP reach in <br />2002 to 2004 than the earlier period. Sand shiner was also abundant in Whirlpool Canyon. Four <br />sand shiner were found in lower Browns Park in 2002, but were not captured there in 2003 or <br />2004. <br />Redside shiner was found in all study area reaches and showed a pattern of decreasing <br />abundance downstream (Fig. 28). Redside shiner abundance showed a particularly large <br />increase in Browns Park and reaches LD1 and LD2 in Lodore Canyon in the 2002 to 2004 <br />period. <br />Fathead minnow was distributed throughout all study reaches and its abundance <br />generally declined in a downstream direction in the 2002 to 2004 period (Fig. 29). Fathead <br />minnow relative abundance in Browns Park was high and similar among the two study periods, <br />increased in 2002 to 2004 in reaches LD1 to LD3, and declined in LD4 compared to 1994 to <br />1996. Fathead minnow abundance was relatively low in the Island-Rainbow Park reach in 2002 <br />to 2004 compared to the 1994 to 1996 period. <br />White sucker was found throughout the study area and its abundance in both <br />electrofishing and seine samples declined downstream (Fig. 30). White sucker abundance in <br />electrofishing samples was highest in upper Lodore Canyon; CPUE data showed a significant <br />increase in white sucker abundance in the 2002 to 2004 period (Table 8). Small-bodied white <br />suckers captured in seine samples comprised a substantial portion of the fish community in <br />Browns Park and upper Lodore Canyon samples, but declined in abundance in reach LD3 and <br />downstream. White sucker abundance showed a small increase in the Island-Rainbow Park <br />reach in the recent period compared to 1994 to 1996 samples. Identity of white suckers and <br />possible occurrence of Utah sucker is ongoing using comparisons of known-identity specimens. <br />Size structure of white sucker in electrofishing samples showed a preponderance of <br />relatively small fish that were 250 mm TL or less in upper Lodore Canyon, and were more <br />33