INDUCTION OF CYTOCHROME-P450 1A IN FISH TREATED WITH 2,3,7,8-TETRACHLORODIBENZO-P-DIOXIN OR CHEMICALLY CONTAMINATED SEDIMENT

Citation
Mej. Vanderweiden et al., INDUCTION OF CYTOCHROME-P450 1A IN FISH TREATED WITH 2,3,7,8-TETRACHLORODIBENZO-P-DIOXIN OR CHEMICALLY CONTAMINATED SEDIMENT, Environmental toxicology and chemistry, 12(6), 1993, pp. 989-999
Citations number
45
Categorie Soggetti
Toxicology,"Environmental Sciences",Chemistry
ISSN journal
07307268
Volume
12
Issue
6
Year of publication
1993
Pages
989 - 999
Database
ISI
SICI code
0730-7268(1993)12:6<989:IOC1IF>2.0.ZU;2-L
Abstract
Mirror carp were exposed to Rotterdam Harbor sediment, highly contamin ated with polychlorodibenzo-p-dioxins (PCDDs), polychlorodibenzofurans (PCDFs), and polychlorobiphenyls (PCBs) (0.5 mug 2,3,7,8-tetrachlorod ibenzo-p-dioxin [TCDD] equivalents per kilogram dry weight). In two ad ditional separate experiments rainbow trout (Oncorhynchus mykiss) and mirror carp (Cyprinus carpio) received a single intraperitoneal inject ion of approximately 0.01, 0.03, 0.06, 0.3, 0.6, or 3.0 mug TCDD per k ilogram body weight. In all three experiments induction of hepatic P45 0 IA was measured with immunochemical and enzymatic methods. The polyc lonal antibodies anti-cod (Gadus morhua), anti-perch (Perca fluviatili s), and anti-rainbow trout P450 1A all cross-reacted with the P450 1A orthologue of the carp and rainbow trout. In most cases high correlati ons were found between 7-ethoxyresorufin O-deethylation (EROD) activit y and cytochrome P450 1A protein contents, the latter measured by the enzyme-linked immunosorbent assay (ELISA) and protein blot methods. Ho wever, the correlations between EROD activity and P450 1A protein leve ls were higher within the separate sampling periods (i.e., 3, 6, and 1 2 weeks after dosage) than with the total data set, especially in the dose-effect study with the rainbow trout. This was probably caused by a difference in time-dependent relationships between P450 1A protein c ontent and EROD enzyme activity: 12 weeks after dosage the P450 1A pro tein was still increased, although EROD activity had returned to backg round level. In addition, there were higher correlations of the EROD a ctivity and P450 1A protein content with total P450 content in rainbow trout and carp treated with a single dose of TCDD, than with total P4 50 content in carp exposed to contaminated sediment. In our study, the ELISA method appeared to be more useful than the protein blot techniq ue, because the ELISA is faster and has higher reproducibility. In add ition, in all our experiments EROD activity showed a higher induction than the P450 IA protein, indicating a higher sensitivity of the EROD assay. Our results strongly indicated that determination of the P450 1 A protein content and EROD activity provides complementary information . Thus we recommended the use of both the ELISA and the EROD activity assay in order to understand the nature of P450 1A induction,