Rapid assessment of induced cytochrome P4501 a protein and catalytic activity in fish hepatoma cells grown in multiwell plates: Response to TCDD, TCDF, and two planar PCBS
- 1 April 1996
- journal article
- research article
- Published by Oxford University Press (OUP) in Environmental Toxicology and Chemistry
- Vol. 15 (4) , 582-591
- https://doi.org/10.1002/etc.5620150425
Abstract
Induction of cytochrome P4501A1 (CYP1A1) in cultured cells can be used to determine taxon‐specific relative potencies of Ah receptor agonists. This report describes optimized methods for growth and treatment of PLHC‐1 fish hepatoma cells in multiwell plates, in situ analysis of ethoxyresorufin O ‐deethylase (EROD) activity, and measurement of CYP1A protein by immunoblotting of cell lysates. EROD activity was undetectable (−1 mg−1) in untreated or dimethyl sulfoxide‐treated cells, but was highly induced (up to 150 pmol min−1 mg−1) in cells exposed to Ah receptor agonists such as 2,3,7,8–tetrachlorodibenzo‐p‐dioxin (TCDD), 2,3,7,8–tetrachlorodibenzofuran (TCDF), or planar chlorobiphenyls (CB). Addition of exogenous NADPH was not required for measurement of EROD activity in PLHC‐1 cells. As inducers of EROD activity, TCDD, TCDF, 3,3′,4,4′,5– pentachlorobiphenyl (CB‐126), and 3,3′,4,4′‐tetrachlorobiphenyl (CB‐77) differed both in potency and in apparent efficacy (maximal level of induced activity). In each case, EROD induction was biphasic, with stronger induction at lower concentrations and an attenuated response at higher concentrations. In contrast, the content of immunodetectable CYP1A protein increased monotonically with dose of CB, and the maximum level achieved was similar for all inducers. The discrepancy in results obtained for EROD activity versus CYP1A protein may result from inhibition or inactivation of catalytic function at high concentrations of inducer. By reducing peak EROD values, this inhibition leads to lower apparent EC50 values and thus the overestimation of relative potencies or toxic equivalency factors (TEFs) for many inducers. These studies demonstrate the necessity of measuring both EROD activity and immunodetectable CYP1A protein for the accurate assessment of CYP1A induction and relative potencies in cultured cells.Keywords
This publication has 40 references indexed in Scilit:
- Development of toxic equivalency factors for PCB congeners and the assessment of TCDD and PCB mixtures in rainbow troutEnvironmental Toxicology and Chemistry, 1995
- Induction of cytochrome P450 1A in teleosts: environmental monitoring in Swedish fresh, brackish and marine watersAquatic Toxicology, 1993
- Induction of cytochrome P450 1A in fish treated with 2,3,7,8‐tetrachlorodibenzo‐p‐dioxin or chemically contaminated sedimentEnvironmental Toxicology and Chemistry, 1993
- The cytochrome P-450 system in fish, aquatic toxicology and environmental monitoringAquatic Toxicology, 1992
- Genetic and Molecular Aspects of 2,3,7,8-Tetra-Chlorodibenzo-P-Dioxin ActionAnnual Review of Pharmacology and Toxicology, 1990
- Polychlorinated Biphenyls (PCBs), Dibenzo-p-Dioxins (PCDDs), Dibenzofurans (PCDFs), and Related Compounds: Environmental and Mechanistic Considerations Which Support the Development of Toxic Equivalency Factors (TEFs)Critical Reviews in Toxicology, 1990
- Enzyme induction in the cytochrome P-450 systemPharmacology & Therapeutics, 1990
- Uroporphyrin accumulation in cultured chick embryo hepatocytes: Comparison of 2,3,7,8-tetrachlorodibenzo-p-dioxin and 3,4,3′,4′-tetrachlorobiphenylToxicology and Applied Pharmacology, 1988
- Separation of pure polychlorinated biphenyl isomers into two types of inducers on the basis of induction of cytochrome P-450 or P-448Chemico-Biological Interactions, 1977