Abstract

Rainbow trout fry were exposed in soft water to sublethal concentrations of copper for 60 days under controlled laboratory conditions. At 20-day intervals, fish were sampled for weight, length, and whole-body copper and metallothionein concentrations. Exposures to waterborne copper concentrations as low as 4.6 μg 1 −1 resulted in significantly reduced growth and significantly elevated whole-body copper concentrations after 20 days. Whole-body metallothionein concentrations did not differ significantly from controls. Fish did not recover or return to control growth rates throughout the entire exposure period; a 45% reduction in mean weight relative to controls observed on day 40 in the 9.0 μg 1 −1 Cu exposure was sustained through day 60. Whole-body accumulation rates of copper in fish exposed to 4.6 μg 1 −1 and higher levels of Cu increased significantly between 0 and 40 days and appeared to reach steady-state after 40 days. Copper accumulation was found to depend on dose and time. Trout exposed to higher copper concentrations accumulated more whole-body copper, with longer times to reach steady-state. Our data suggest that both accumulation capacity and copper depuration rates from a slowly exchangeable pool are concentraion-dependent. A linear model was developed for the relationship between exposure duration, copper accumulation, and fish weight: In (wet wt., μg) = 4.8 + 0.03 (exposure duration, days)—0.04 (whole-body copper, mg g −1 dry wt.) ( P < 0.01, R 2 = 0.94). Thus, growth reductions are predictable from tissue residues if exposure durations are known. Although exposure times may not be known for field-collected fish, residues may have utility in evaluating adverse effects on fish sampled in the wild because residues integrate exposure over time, space, and exposure route.

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