Induction effects of polychlorinated biphenyls, polycyclic aromatic hydrocarbons and other widespread aromatic environmental pollutants on microsomal monooxygenase activities in chick embryo liver
Jazyk angličtina Země Německo Médium print
Typ dokumentu časopisecké články, práce podpořená grantem
PubMed
8975635
DOI
10.1007/s002040050286
Knihovny.cz E-zdroje
- MeSH
- 7-alkoxykumarin-O-dealkylasa biosyntéza MeSH
- cytochrom P-450 CYP1A1 biosyntéza MeSH
- cytochrom P-450 CYP2B1 biosyntéza MeSH
- enzymová indukce účinky léků MeSH
- jaterní mikrozomy účinky léků enzymologie MeSH
- kuřecí embryo MeSH
- látky znečišťující životní prostředí metabolismus toxicita MeSH
- oxidoreduktasy biosyntéza MeSH
- polychlorované bifenyly metabolismus toxicita MeSH
- polychlorované dibenzodioxiny metabolismus toxicita MeSH
- polycyklické aromatické uhlovodíky metabolismus toxicita MeSH
- zvířata MeSH
- Check Tag
- kuřecí embryo MeSH
- zvířata MeSH
- Publikační typ
- časopisecké články MeSH
- práce podpořená grantem MeSH
- Názvy látek
- 7-alkoxykumarin-O-dealkylasa MeSH
- cytochrom P-450 CYP1A1 MeSH
- cytochrom P-450 CYP2B1 MeSH
- látky znečišťující životní prostředí MeSH
- oxidoreduktasy MeSH
- polychlorované bifenyly MeSH
- polychlorované dibenzodioxiny MeSH
- polycyklické aromatické uhlovodíky MeSH
Cytochrome P450-dependent 7-ethoxyresorufin O-deethylase (EROD), 7-pentoxyresorufin O-dealkylase (PROD) and 7-ethoxycoumarin O-deethylase (ECOD) activities in 14-day-old chick embryo livers were determined 24 h after pretreatment with selected widespread aromatic environmental contaminants, including polychlorinated biphenyls (PCBs), polycyclic aromatic hydrocarbons (PAHs), hexachlorobenzene, and dialkylesters of phthalic acid, and compared with the inducing potencies of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) and the coplanar and mono-o-chlorinated PCBs. The effects of other model inducers, i.e. phenobarbital and pyrazole, were also examined. Specificity of EROD induction was estimated with regard to contaminants frequently present in environmental samples and dose-response curves for EROD induction were determined. A strong induction (comparable with that by mono-o-chlorinated biphenyl treatment) by dibenzo[a,h]anthracene, benzo[k]fluoranthene or benzo[b]fluoranthene was found, but the maximal level of EROD activity inducible by TCDD was not achieved, partly due to the high toxicity of the tested PAHs. 3-Methylcholanthrene showed moderate inducing potencies; benz[a]anthracene, benzo[a]pyrene, chrysene and 2,2',3,4,4',5'-hexachlorobiphenyl appeared to be weak inducers. Other PAHs and PCBs tested, as well as hexachlorobenzene, dialkyl phthalates, phenobarbital and pyrazole had no marked effects on the EROD level. ECOD activities were increased non-specifically by TCDD, 3-methylcholanthrene, hexachlorobenzene and phenobarbital. A significant enhancement of PROD activity by TCDD and related inducers was observed, while phenobarbital induced the PROD activity only weakly; SDS-PAGE analysis showed that the chicken phenobarbital-inducible cytochromes P4502H with apparent molecular weights 50 kDa were not markedly induced by the TCDD- or 3-methylcholanthrene treatments. Inhibition of EROD and PROD by 9-hydroxyellipticine, a specific inhibitor of rat hepatic cytochrome P4501A1, revealed that PROD induction by TCDD and other P4501A-inducers was probably a result of a broader substrate specificity of chick embryo P4501A. Measurement of EROD activities in chick embryo liver is highly sensitive, specific and suitable for the determination of TCDD-type toxicity of new drugs, agrochemicals, and industrial pollutants.
Citace poskytuje Crossref.org