INDUCTION EFFECTS OF POLYCHLORINATED-BIPHENYLS, POLYCYCLIC AROMATIC-HYDROCARBONS AND OTHER WIDESPREAD AROMATIC ENVIRONMENTAL-POLLUTANTS ON MICROSOMAL MONOOXYGENASE ACTIVITIES IN CHICK-EMBRYO LIVER
M. Machala et al., INDUCTION EFFECTS OF POLYCHLORINATED-BIPHENYLS, POLYCYCLIC AROMATIC-HYDROCARBONS AND OTHER WIDESPREAD AROMATIC ENVIRONMENTAL-POLLUTANTS ON MICROSOMAL MONOOXYGENASE ACTIVITIES IN CHICK-EMBRYO LIVER, Archives of toxicology, 70(6), 1996, pp. 362-367
Cytochrome P450-dependent 7-ethoxyresorufin O-deethylase (EROD), 7-pen
toxyresorufin O-dealkylase (PROD) and 7-ethoxycoumarin O-deethylase (E
COD) activities in 14-day-old chick embryo livers were determined 24 h
after pretreatment with selected widespread aromatic environmental co
ntaminants, including polychlorinated biphenyls (PCBs), polycyclic aro
matic hydrocarbons (PAHs), hexachlorobenzene, and dialkylesters of pht
halic acid, and compared with the inducing potencies of 2,3,7,8-tetrac
hlorodibenzo-p-dioxin (TCDD) and the coplanar and mono-o-chlorinated P
CBs. The effects of other model inducers, i.e. phenobarbital and pyraz
ole, were also examined. Specificity of EROD induction was estimated w
ith 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 treatm
ent) by dibenzo[a,h]anthracene, benzo[k]fluoranthene or benzo Cbl fluo
ranthene was found, but the maximal level of EROD activity inducible b
y 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'-hexachlorobip
henyl appeared to be weak inducers. Other PAHs and PCBs tested, as wel
l as hexachlorobenzene, dialkyl phthalates, phenobarbital and pyrazole
had no marked effects on the EROD level. ECOD activities were increas
ed non-specifically by TCDD, 3-methylcholanthrene: hexachlorobenzene a
nd phenobarbital. A significant enhancement of PROD activity by TCDD a
nd related inducers was observed, while phenobarbital induced the PROD
activity only weakly; SDS-PAGE analysis showed that the chicken pheno
barbital-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 spe
cific 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 an
d suitable for the determination of TCDD-type toxicity of new drugs, a
grochemicals, and industrial pollutants.