Abstract

In the present study, we used fresh preparations of mixed-cell populations to evaluate accumulation and toxicity of dissolved copper (1-100 microM) in isolated cells from posterior gills and hepatopancreas of the blue crab (Callinectes sapidus). For both gill and hepatopancreatic cells, significant increases in copper accumulation were observed after exposure to 50 or 100 microM copper. In gill cells, a linear increase in copper accumulation was observed over time. In hepatopancreatic cells, a maximum level of copper accumulation was achieved after 1 h of exposure, remaining unchanged up to 6 h. After 6 h of exposure, copper content in gill cells was 6.6-fold higher than that in hepatopancreatic cells. In both cell types, copper accumulation always followed a linear relationship with copper concentration in the incubation medium. Significant decreases in cell viability were observed after exposure to either 10 microM copper (gill cells) or 100 microM copper (gill and hepatopancreatic cells). Furthermore, an exponential rise to maximum-type relationship was observed between copper accumulation and toxicity in gill cells. Altogether, these findings indicate that the premise behind the biotic ligand model (BLM) approach is verified in isolated cells from posterior gills of the blue crab (i.e., toxicity is driven by copper accumulation in the biotic ligand, the gill cell). Therefore, these cells can be used as a model for the development of an in vitro BLM version for marine conditions. Isolated cells from the hepatopancreas, however, could be used as a model to better understand the mechanism of copper tolerance at a cellular level in crustaceans.

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