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Toxicology of Industrial Compounds

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A.S.WRIGHT ET AL. 191<br />

intrinsic promoter activity <strong>of</strong> the chemical arising, for example as a<br />

consequence <strong>of</strong> cell injury, would be negligible at low exposures—<br />

particularly when viewed in the context <strong>of</strong> the overall promoter pressure<br />

exerted on the populations at risk. Thus, it is unlikely that the added<br />

cancer risk would be greater than and may approximate to the increment in<br />

critical mutations caused by the specific exposure (Figure 14.1).<br />

Experimental studies indicate that all known categories <strong>of</strong> genotoxic<br />

agents ranging from methylating agents to polycyclic aromatic compounds<br />

can induce the critical mutations leading to malignancy (Figure 14.1).<br />

Furthermore, at low doses, the possibility that exposure to a particular<br />

genotoxic chemical would induce more than one <strong>of</strong> the critical mutations in<br />

any particular cell is extremely remote. Indeed it is probable that each<br />

critical mutation is induced by a different agent or mechanism, i.e.<br />

chemical, radiation or ‘spontaneous’. In this sense, each critical mutation<br />

would have equal status, i.e. no single event would be any more or any less<br />

critical than any other to the final outcome. Accordingly, the increment in<br />

cancer risk would equate with the increment in any decisive, e.g. oncogeneactivating,<br />

mutation in any critical gene. The induction <strong>of</strong> such mutations<br />

is almost certainly a direct function <strong>of</strong> overall mutagenic activity <strong>of</strong> the<br />

chemical, i.e. linked to the number <strong>of</strong> mutational events rather than the type<br />

<strong>of</strong> mutations induced by a given dose <strong>of</strong> the chemical. At low exposures,<br />

therefore, the increment in cancer incidence due to a specific genotoxic<br />

agent would approximate to the small increase in the total mutational load<br />

caused by the exposure, i.e. relative to the overall background level <strong>of</strong><br />

mutations due to all causes, multiplied by the overall cancer incidence in<br />

the population at risk. (The latter function introduces a measure <strong>of</strong> the net<br />

impact <strong>of</strong> promoter and anti-promoter pressure acting on initiated cells in<br />

the population at risk.) Of course risks may also be calculated on the basis<br />

<strong>of</strong> specific tumours and specific tissues.<br />

The determination <strong>of</strong> small increments in mutation associated with lowlevel<br />

exposures to genotoxic chemicals in human populations presents<br />

enormous technical problems not least due to the much larger and variable<br />

background <strong>of</strong> mutations due to all causes. Increasing the sensitivity <strong>of</strong><br />

mutation assays per se (vide supra) is unlikely to improve the situation.<br />

High resolving power is also needed to discriminate between effects due to<br />

different contributory factors. Nevertheless, while direct approaches to<br />

assess absolute cancer risks posed by such low-level exposures may elude<br />

us we can nevertheless begin to determine relative cancer risks and<br />

prioritise genotoxic chemicals on the basis <strong>of</strong> experimental determinations<br />

<strong>of</strong> mutagenic potency and estimates <strong>of</strong> target doses resulting from<br />

environmental or occupational exposures. Thus, according to the foregoing<br />

the relative cancer risk posed by a low exposure to a genotoxic agent<br />

would approximate to the number <strong>of</strong> mutations induced per unit target<br />

dose×estimated human target dose. Once relative cancer risks have been

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