Page 818 - The Toxicology of Fishes
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798                                                        The Toxicology of Fishes


                                 Clark Fork River


                                                              Blackfork River
                                              30          Turah
                                              km
                                30                                Deer Lodge
                                                    Rock Cr. Flint Creek       Tissue Type
                                25                                Butte        Reference sites ( )
                                                           Silverbow           Turah Bridge
                               Copper in Tissue (µg/g, dry wt.)  15
                                                            Creek
                                                                               Warm Springs Ponds
                                20





                                10


                                 5


                                 0
                                     aa  b  a  bc  aa  b  a  ab b  a  bc  a  b  b  a a  b  a  b c
                                      Gill   Liver  Kidney  Pyloric  Stomach  Large  Stomach  Whole
                                                           caeca         intestine  contents  fish
                       FIGURE 19.12 Bioaccumulation of copper in different tissues of brown trout (Salmo trutta) from below Warm Springs
                       ponds and from Turah, on the Clark Fork River, compared to fish from uncontaminated reference sites. (Adapted from
                       Farag, A.M. et al., Can. J. Fish. Aquat. Sci., 52, 2038–2050, 1995.)



                        The lipid peroxidation observed experimentally was also observed in the liver, pyloric ceca, and large
                       intestine of brown trout resident in the Clark Fork (Farag et al., 1999). Metals that exist in more than
                       one valence state (e.g., copper) can initiate lipid peroxidation (Wills, 1985) by interacting with sulfhydryl
                       groups and oxygen or by inhibiting important antioxidant enzymes. This may ultimately result in tissue
                       damage or cell death (Sokol et al., 1990), when fatty-acid side chains in cell membranes are the targets
                       (Halliwell and Gutteridge, 1985). Brown trout from the upper Clark Fork River also contained copper
                       inclusions in  hepatocytes and vacuolation of  hepatocyte nuclei.  When energy is diverted from cell
                       metabolism to detoxify metals, cell disruption is noted by both vacuolation of nuclei and the elevated
                       lipid peroxidation.
                        The experiments reported above were somewhat controversial because nutritional content and species
                       composition of the diet were not controlled. Mount et al. (1994) repeated the dietary exposure exper-
                       iments with rainbow trout (Oncorhynchus  mykiss), but they used brine shrimp (Artemia) as a food
                       source. After 60 days, they could attribute no effects on growth or survival to the diet. Woodward et
                       al. (1995) and Mount et al. (1994) both, however, documented effects on the intestinal tract of fish fed
                       diets contaminated with metals. Gut impaction was observed in 3 to 9% brown trout, and constipation
                       was observed in nearly 50% of the trout fed diets from the uppermost Clark Fork River. Mount et al.
                       (1994) found that 7 of 18 mortalities observed were associated with actual rupture of the body cavity.
                       Hansen et al. (2004) controlled the nutritional content of the diet by feeding rainbow trout worms
                       (Lumbricus variegatus) grown in Clark Fork sediments. They found histopathologic abnormalities in
                       treated animals, along with unambiguous inhibition of growth. The growth reduction was associated
                       with reductions in conversion of food energy to biomass (rather than reduced food intake) and correlated
                       with arsenic bioaccumulation.
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