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Toxicology of Industrial Compounds

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370 CONTROVERSIAL ISSUES IN SAFETY ASSESSMENT<br />

which can be used by industry to tailor experiments in order to refute the<br />

classification <strong>of</strong> a questionable animal carcinogen. In the long run there<br />

will be no benefit if about 50 per cent <strong>of</strong> all chemicals are classified as<br />

carcinogens, neither for the public nor for industry nor for an adequate<br />

protection <strong>of</strong> human health.<br />

Risk assessment<br />

Most scientific committees and regulatory agencies refrain from<br />

scientifically based risk assessments for carcinogens but rather propagate<br />

an exposure as low as possible. And if a risk assessment is really carried<br />

out, it usually just applies a simplistic mathematical extrapolation using the<br />

linearized multistage model and highly conservative default assumptions to<br />

bridge data gaps. These mathematical procedures arrive at a scientifically<br />

unjustified numerical precision <strong>of</strong> the risk estimate. One <strong>of</strong> the problems is<br />

to explain to the public the real meaning and the uncertainties <strong>of</strong> such a<br />

risk assessment. A possible alternative could be to substitute the<br />

mathematical extrapolation by an appropriate assessment factor which <strong>of</strong><br />

course has to take into account the severity and irreversibility <strong>of</strong> the<br />

carcinogenic effect. The simplistic mathematical modelling might be used<br />

only for selection <strong>of</strong> priority chemicals for further in-depth investigations.<br />

On the other hand, a mathematical risk assessment can be an<br />

appropriate procedure for chemicals with a broad experimental data base,<br />

when the most relevant default assumptions are substituted by real data.<br />

This would be <strong>of</strong> primary importance for:<br />

– the selection <strong>of</strong> the mathematical model: the simplistic linearized<br />

multistage model presently in use could be substituted by biologically<br />

driven models, like that proposed by Sielken (1989) or the MVK-model<br />

(Moolgavkar and Knudson, 1981; Moolgavkar et al., 1988).<br />

– dose scaling from animals to humans: presently the experimental dose in<br />

mg kg −1 body weight is <strong>of</strong>ten extrapolated to humans by transforming<br />

the dose to mg m −2 body surface. This is used both for compounds<br />

which are metabolically toxified and detoxified, the scientific basis for<br />

such an undifferentiated procedure is at best highly doubtful. In the<br />

future this default assumption could be substituted by physiologically<br />

based pharmacokinetic (PBPK) modelling.<br />

– estimation <strong>of</strong> the target dose: presently the external dose to which the<br />

animals are exposed is considered to be proportional to the dose<br />

reaching the target tissue or the target chemical entities—generally the<br />

DNA. Again in future this could be substituted by adequate PBPK<br />

modelling.

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