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Toxicology of Industrial Compounds

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208 USE OF LONG-TERM CULTURES OF HEPATOCYTES IN TOXICITY TESTING<br />

– CYP3A4 is a major catalyst in the activation <strong>of</strong> aflatoxins, pyrrolizidine<br />

alkaloids and polycyclic hydrocarbon dihydrodiols (Shimada et al.,<br />

1989a; Shimada and Guengerich, 1989).<br />

The balance between the rates <strong>of</strong> formation <strong>of</strong> reactive metabolites and<br />

detoxication will greatly determine the potential toxic response <strong>of</strong> a<br />

chemical. Variables, known to affect normal biotransformation, such as<br />

enzyme induction and inhibition can also change the bioactivation rate <strong>of</strong><br />

chemicals. A clear example is the metabolism <strong>of</strong> halogenated biphenyls<br />

after treatment with arochlor 1254 (Borlakoglu and Wilkins, 1993).<br />

Consequently, the toxicity <strong>of</strong> chemical products <strong>of</strong>ten depends upon their<br />

specific biotransformation, the presence, absence, induction and inhibition<br />

<strong>of</strong> specific phase 1 and phase 2 enzymes involved in their metabolism.<br />

Towards an in vitro approach <strong>of</strong> risk assessment<br />

Nearly all toxicological studies on chemical products, including industrial<br />

chemicals, agrochemicals, pharmaceuticals, additives, materials in contact<br />

with food and cosmetics, have been carried out in vivo using experimental<br />

animals, in particular small vertebrates (News and Views, 1993).<br />

Important scientific, technological, ethical and economic considerations,<br />

however, justify the actual search for in vitro alternatives, replacing or<br />

improving existing in vivo methods and reducing the number <strong>of</strong> animals<br />

involved (Frazier and Goldberg, 1990; Roberfroid, 1991).<br />

Since hepatocytes can be isolated from different species (Guguen-<br />

Guillouzo et al., 1982; Green et al., 1986; van’t Klooster et al., 1992)<br />

including man (Guguen-Guillouzo et al., 1982; Rogiers, 1993), they can<br />

represent a powerful tool for short-term risk assessment studies when used<br />

as suspensions <strong>of</strong> freshly isolated cells (up to 3–4 h) or as short-term<br />

cultures (up to 2 days) (Klaassen and Stacey, 1982; Guillouzo, 1986). They<br />

can be useful in biotransformation, cytotoxicity, hepatotoxicity and<br />

genotoxicity studies, in species selection and in mechanistic studies<br />

(Blaauboer, 1994). Long-term cultures <strong>of</strong> hepatocytes (up to several weeks)<br />

represent a somewhat different approach in risk assessment. Such systems<br />

are <strong>of</strong> interest for the assessment <strong>of</strong> long-term toxicity <strong>of</strong> xenobiotics<br />

including the occurrence <strong>of</strong> enzyme induction, the effects on xenobiotic<br />

biotransformation, lipid peroxidation, accumulation <strong>of</strong> triglycerides,<br />

changes in glutathione content, interaction between compounds and the<br />

hepatoprotection afforded by certain molecules. Consequently, long-term<br />

cultures have been particularly applied in the development <strong>of</strong><br />

pharmaceuticals, in pharmaco-toxicological studies (Guillouzo, 1986,<br />

1992; Rogiers and Vercruysse, 1993; Skett, 1995). As far as chemical<br />

products other than pharmaceuticals and in particular industrial chemicals<br />

and agrochemicals are concerned, the practical needs during development

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