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Toxicology of Industrial Compounds

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298 TESTING AND EVALUATION FOR REPRODUCTIVE TOXICITY<br />

Figure 20.10 Interpretation/extrapolation <strong>of</strong> reproductive toxicology.<br />

Conclusions<br />

In conclusion I should mention that time constraints enforce superficial<br />

mention <strong>of</strong> many important aspects. I would like to emphasise that<br />

improved testing and evaluation for toxicity to reproduction can be<br />

achieved with methodology that exists within and without regulatory<br />

guidelines. This has been illustrated by the special cases presented at this<br />

meeting.<br />

There is no necessity to be restricted to specific guidelines, there never<br />

was. We should make use <strong>of</strong> any and all test methods available as<br />

appropriate for the substance being investigated. Whatever the type <strong>of</strong><br />

substance, testing involves looking for the same hazards. Having identified<br />

a hazard, methods <strong>of</strong> assessing risk, essentially, are the same (although<br />

PBPK models for reproductive toxicity would be more complex than those<br />

used for systemic toxicity).<br />

The methodology is available, what is required is the willingness and<br />

wisdom to use it effectively and efficiently (Palmer, 1993a, b). The goal<br />

should be to investigate a specific substance to the extent necessary, no<br />

more and no less. For this there needs to be a change in attitude by<br />

industry, agencies and academia. Therein is the greatest problem since<br />

‘Change is not made without inconvenience, even from worse to better’ and<br />

people are very unwilling to change their prejudices and habits.

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