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Mining Impacts on Fish in the Clark Fork River, Montana: A Field Ecotoxicology Case Study 801


                       the fish diet is not very contaminated immediately below upstream waste containment ponds.  This
                       unexpected feature in the distribution of contamination is accompanied by the greatest numbers of fish
                       in the system. A rapid increase in invertebrate contamination downstream 5 to 10 km from the Warm
                       Springs Ponds is attributable to inputs from contaminated banks and the floodplain (probably with
                       contributions from the hyporheic zone).  This is accompanied by a rapid decline in fish abundance.
                       Invertebrate communities are also disturbed in this region. Metal-sensitive species are missing through
                       much of the Upper Clark Fork, and those species missing are the strongest bioaccumulators of copper
                       or cadmium or are the animals with the least capabilities for detoxification. Suborganismal indications
                       of stress similar to those generated by dietary exposure of trout to metal contamination are found in
                       surviving fish populations in the Clark Fork. Surviving fish appear to be stressed in some of the same
                       ways that metal-contaminated diets stress fish in the laboratory, further supporting the importance of
                       metals as a stressor in the system.
                        Important mechanistic details, however, have not been fully resolved. What is the most important risk
                       to fish: acute toxicity episodes, chronic stress and mortality to adults (e.g., from a contaminated diet),
                       toxicity to juveniles, failure of early life stages to survive, effects on reproduction? More needs to be
                       understood about why some fish species are absent and others are not. Specifically, the vulnerability of
                       native cutthroat and bull trout should be studied. The intriguing possibility that the simplified benthic
                       community that accompanies metal contamination is nutritionally inadequate for some fish species
                       remains to be fully studied. In short, mine wastes manifest their effects in both intuitively obvious and
                       very complicated ways in a contaminated river. Contentious debate is reduced as knowledge grows, but
                       full consensus on metal effects awaits better mechanistic understanding. There is value in integrating
                       long-term, multidiscipline, persistent field and laboratory investigations to unravel the mechanisms
                       behind the complex responses that mine wastes create.





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