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Toxicology of Industrial Compounds

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C.K.ATTERWILL AND S.P.AYLWARD 257<br />

or exaggerated pharmacological responses, that is Classes 1 and 2.<br />

Furthermore, it appears that endocrine toxicology can be detected reliably<br />

in pre-clinical studies. What is essential is that Class 3 toxic endocrine effects<br />

are classified appropriately. Class 3a effects would be expected to be seen<br />

across species, whereas there are numerous examples where Class 3b<br />

effects appear to be species-specific. There seems to be a paucity <strong>of</strong> clear-cut<br />

examples for Class 4 effects. There are several examples <strong>of</strong> compounds<br />

which have idiosyncratic immunotoxicological effects in susceptible humans<br />

which cannot be predicted from pre-clinical studies.<br />

Incidence <strong>of</strong> thyroid toxicity and tumours <strong>of</strong> the thyroid<br />

Most information on incidence is derived from pharmaceutical toxicity<br />

databases. Such data from Ribelin (1984) suggest that the endocrine system<br />

<strong>of</strong> the rats is particularly sensitive to toxicity from xenobiotics. This is also<br />

supported by Heywood (1984) in which he examined the target organ<br />

toxicity for 42 pharmaceutical compounds in the rat and dog. The<br />

endocrine system <strong>of</strong> the rat was only second to the liver as the most<br />

frequently affected target organ (38 per cent liver, 31 per cent endocrine).<br />

Ribelin (1984) reported that the most frequent endocrine lesion occurs in<br />

the adrenals followed by the testes but this analysis was conducted on<br />

chemicals and pharmaceuticals, and the data indicated that it was the<br />

cortical layers <strong>of</strong> the adrenal that were being predominantly effected,<br />

suggesting that the adrenal changes may be reflecting general stress<br />

responses rather than direct adrenal gland toxicity.<br />

In another analysis conducted in conjunction with the Centre <strong>of</strong><br />

Medicines Research this area was further explored. <strong>Toxicology</strong> data on<br />

124 compounds (all pharmaceuticals) were analysed. Just under 50 per<br />

cent (61/124) <strong>of</strong> these compounds have effects on one or more endocrine<br />

glands. Similar to Ribelin (1984) the adrenals were the most frequently<br />

affected, followed by the testes and the thyroid. An extensive survey <strong>of</strong> the<br />

different types <strong>of</strong> thyroid toxicity for both pharmaceutical agents and<br />

industrial chemicals was presented by Atterwill et al. (1993).<br />

Perturbation <strong>of</strong> thyroid function<br />

Thyroid function can be perturbed by agents affecting a number <strong>of</strong><br />

processes involved in the regulation <strong>of</strong> the hypothalamic-pituitary-thyroidliver<br />

(H-P-T-L) axis (Figure 19.2). These agents can affect function directly<br />

by interacting with thyroid cell receptors on their intracellular transduction<br />

mechanisms (see Figure 19.3). Alternatively thyroid function may be<br />

altered indirectly by agents affecting thyroid hormone metabolism and/or<br />

distribution—this event being followed by the release <strong>of</strong> thyrotrophic<br />

factors, or by xenobiotic-mediated alterations in the release <strong>of</strong> these factors

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