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<br />56 HAMILTON ET AL <br /> <br />smaller by day 14. At day 28, fish in the 8X treatment <br />had lighter coloration, and by day 63 showed little <br />feeding. <br />Fish activity determined from video recordings was <br />increased in razorback sucker in the 8X treatment at <br />30 days of exposure, whereas for bonytail it was re- <br />duced in the IX and 2X treatments (Table VII). There <br />was no effect on feeding behavior recorded by video <br />taping. Critical swimming speed in razorback sucker <br />was reduced in the 8X treatment at 60 and 90 days of <br />exposure, and for bony tail was reduced in the 8X and <br />16X treatments (Table VII). <br />Whole-body residues of copper, selenium, and zinc <br />at each period increased generally in a concentration- <br />response manner (Table VIII). For razorback sucker, <br />residues of copper, selenium, and zinc were lower in <br />fish in the IX, 2X, and 4X treatments at day 90 <br />compared to day 30, which suggests that the inorganics <br />were being regulated. In the 8X and 16X treatments, <br />residues of the three inorganics were higher at day 90 <br />than at day 30, which suggests that the fish had lost <br />their ability to regulate these elements. For bony tail, <br />the three inorganics were lower in the IX, 2X, 4X, and <br />8X treatments at day 90, and in the 16X treatment for <br />copper, compared to day 30, which suggests that they <br />were being regulated. In the 16X treatment residues of <br /> <br />selenium and zinc stayed the same, which suggests that <br />fish were not able to regulate the inorganics in a <br />manner similar to those in the lower exposure treat- <br />ments. <br /> <br />DISCUSSION <br /> <br />For razorback sucker and bony tail, adverse effects con- <br />sistently occurred in the 8X and 16X treatments at day <br />90. These results suggest that razorback sucker and <br />bony tail generally have similar sensitivities to the inor- <br />ganic mixture. <br />The toxic effects observed in the present study were <br />suggested in acute toxicity tests with the same species <br />and mixture of inorganics. Buhl and Hamilton (1996) <br />tested the same nine-inorganic mixture with young <br />Colorado squawfish, razorback sucker, and bony tail. <br />They found no difference in sensitivity of the three <br />species to the Ashley Creek mixture. They also com- <br />pared the 96 h LCsos for the Ashley Creek mixture <br />with the measured environmental concentrations to <br />derive margins of uncertainty, i.e., ratio of biological <br />effects concentration (96 h LCso) to environmental <br />concentration, of 12-32 for the three species. The low <br />margins of uncertainty, i.e., < 100, indicated to them <br /> <br />TABLE VI. Behavioral observations of razorback sucker and bonytail exposed to a <br />mixture of nine elements simulating Ashley Creek, Utah, in a reconstituted water <br />representing the Green River <br /> <br />Species <br /> <br />Day <br /> <br />Behavior <br /> <br />Razorback sucker <br /> <br />14 <br />21 <br /> <br />42 <br />49 <br /> <br />Bonytail <br /> <br />56 <br />63 <br />7 <br /> <br />90% of 8X and 16X fish hyperactive. <br />90% of 16X fish darker coloration than other <br />treatments. <br />8X and 16X fish smaller than controls. <br />16X fish evenly distributed in aquaria; 3/4 of fish in <br />other treatments somewhat grouped, i.e., schooling <br />behavior. <br />10% of 16X fish lethargic. <br />20% of 16X fish show loss of equilibrium. 100% <br />of 16X fish not feeding and very light coloration. <br />8X fish not feeding. <br />8X fish less active than other lower treatments. <br />10% of l6X fish inactive, resting vertically on <br />screen material. <br />16X fish lighter coloration and nOticeably smaller <br />than controls. <br />16X fish feeding less intensely than other treatments. <br />8X and 16X fish have lighter coloration than other <br />treatments. <br />16X fish show little feeding. <br />16X fish unresponsive to disturbance. <br />8X fish show little feeding. <br /> <br />3 <br />7 <br /> <br />14 <br /> <br />28 <br /> <br />35 <br />56 <br />63 <br />