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Toxicology of Industrial Compounds

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Table 20.6 OECD 422: cyclophosphamide, tabular summary<br />

Notes:<br />

pp=post partum.<br />

Bold type indicates treatment effect. Female deaths at 3 and 4.5 mg kg −1 are<br />

attributable to treatment as, at 6.7 mg kg −1 , all females died. There was a reduction<br />

in the number <strong>of</strong> females with young, litter size, litter weight and mean pup weight.<br />

No effects on spermatogenesis were reported but, if a dosage inducing effect on the<br />

male had been selected, all the females would have died.<br />

females was slow. As far as I know this has not been mentioned in the<br />

extensive literature on EGME.<br />

These examples and others show that the OECD tests are capable <strong>of</strong><br />

detecting substances with marked effects on reproduction. With such<br />

results it would be foolhardy to consider higher level guideline tests. If the<br />

substance is not abandoned any further testing would require case by case<br />

designs to characterise the detected effects more completely.<br />

Full scale testing<br />

If pretesting prognosis suggests that a substance is unlikely to present<br />

problems <strong>of</strong> toxicity, fast track progression to level 2 testing should be<br />

considered (Table 20.2) to avoid unnecessary duplication <strong>of</strong> step by step<br />

testing. Expected tests include a two generation study in rats and an<br />

embryotoxicity study in rats and rabbits. In the harmonised guideline for<br />

medicines this same strategy is just one <strong>of</strong> several options and the same or<br />

greater flexibility should be made available for testing industrial<br />

chemicals.<br />

Tests for embryotoxicity<br />

A.K.PALMER 289<br />

An anomaly in this strategy is the specification for embryotoxicity studies<br />

in two species, when only one species is required for all other aspects <strong>of</strong>

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