Apparent induction of a cytochrome P450 with immunochemical similarities to CYP1A in digestive gland of the common mussel (Mytilus galloprovincialis L.) with exposure to 2,2′,3,4,4′,5′-hexachlorobiphenyl and Arochlor 1254

• Published in: Aquatic toxicology 1997-06, Vol.38 (4), p.205-224
• Main Authors: Livingstone, David R, Nasci, Cristina, Solé, Montserrat, Da Ros, Luisa, O'Hara, Sean C.M, Peters, Laurence D, Fossato, Valentino, Wootton, A.Nicola, Goldfarb, Peter S
• Format: Article
• Language: English
• Subjects: 2,2′,3,4,4′,5′-Hexachlorobiphenyl; Benzo[a]pyrene metabolism; Cytochrome P4501A; Induction; Marine; Mussel digestive gland; Mytilus galloprovincialis; Polychlorobiphenyls
• ISSN: 0166-445X; 1879-1514
• DOI: 10.1016/S0166-445X(96)00847-8

The induction of a cytochrome P450 with immunochemical similarities to CYP1A, and accompanying changes in microsomal NADPH-dependent benzo[a]pyrene (BaP) metabolism, were examined in digestive gland of the common mussel (Mytilus galloprovincialis L.) with exposure to 20 ppb water-borne polychlorobiphenyl (PCB) mixture (Arochlor 1254) for 4 or 10 days, or 4 days after a single injection into the mantle cavity of the mixed-type inducer PCB congener 2,2′,3,4,4′,5′-hexachlorobiphenyl (CB-138; 2.5 μg g−1 wet weight). Whole animal tissue levels of PCB following water-column exposure or injection were similar to those for mussel species from polluted field sites, viz. 0.8 to 1.9 μg g−1 wet weight. Levels of microsomal CYP1A-immunopositive protein increased 59% (CB-138) and 72% (Arochlor 1254; 10 days exposure) as determined by Western blot analysis using polyclonal antibodies to hepatic CYP1A of perch (Perca fluviatilis). No changes were seen in levels of digestive gland CYP1A-like mRNA 4 days after injection of CB-138 as determined by Northern analysis using cDNA to hepatic CYP1A1 of rainbow trout (Oncorhynchus mykiss). The increases in levels of CYP1A-immunopositive protein were accompanied by a shift in microsomal NADPH-dependent BaP metabolism towards phenol and diol and away from dione production, the former increasing from 32 to 85% of total free metabolites. The marked decrease in dione production (which is the major BaP metabolite formed in control microsomes) resulted in no increase in total microsomal BaP metabolism with exposure to PCBs. The Type I ligand α-naphthoflavone markedly inhibited microsomal phenol but had no affect on dione production, whereas the Type II ligand clotrimazole markedly inhibited dione, but had much less effect on phenol production. The overall results are interpreted in terms of the existence of an inducible CYP1A-like enzyme catalysing predominantly 2-electron monooxygenation leading to epoxide (and hence phenol and diol) formation, and a constitutive non-inducible cytochrome P450 catalysing predominantly 1-electron oxidation leading to dione formation. Both Arochlor 1254 or CB-138 produced cellular damage in the digestive gland in the form of decreased epithelial digestive cell height and decreased lysosomal membrane stability.