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nonnative species composition of this enclosure when compared to that observed in the <br />other enclosures. Enclosures with significant differences in nonnative species <br />composition included one in which larvae were introduced at a density of 4,000 <br />larvae/acre. This enclosure had a significantly higher (Student's t, P < 0.01) composition <br />of adult black bullhead and adult carp and the abundance estimate represents over 19% <br />survival of larval razorback sucker while the replicate enclosure indicated survival at <br />14%. Survival of larval razorback sucker ranged from 6 to 23% in the four enclosures, <br />including the two control enclosures, where larvae were introduced at a density of 400 <br />larvae/acre. These enclosures also had a significantly lower (Student's t, P < 0.01) <br />composition of fathead minnows than the other enclosures (Table 7). <br />Estimated final densities of nonnative species in each enclosure ranged from <br />48,705 fish acre to 209,819 fish acre in 2004. Estimated razorback sucker survival in <br />each enclosure indicates that higher nonnative fish densities did not negatively affect <br />survival in 2004 (Table 6 and Figure 2). The highest razorback sucker survival was <br />detected in the enclosure with the fourth highest density of nonnative fish. <br />16 <br />