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Toxicology of Industrial Compounds

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appropriate and cost effective health protection within our industrialized<br />

world.<br />

Threshold effects<br />

Classification<br />

H.-P.GELBKE 365<br />

The classification system <strong>of</strong> the EU resides in the designation <strong>of</strong><br />

appropriate R-phrases. In most cases they are rather meant for hazard<br />

identification (e.g. irritation, sensitization, carcinogenicity) and not so<br />

much for risk characterization. Sometimes, risk aspects are also involved<br />

when specific dose levels are decisive for a specific R-phrase (e.g. acute<br />

toxicity). Thereby not only the effect per se is taken into account but also<br />

the strength <strong>of</strong> the effect.<br />

This latter principle also applies to the R 48-phrase (‘danger <strong>of</strong> serious<br />

damage to health by prolonged exposure'), if severe (irreversible) toxic<br />

effects are observed at dose levels <strong>of</strong> ≤50 mg kg −1 body weight per day in a<br />

90-day test after oral administration. For other routes and durations <strong>of</strong><br />

exposure similar provisions exist. The strategy to use dose limits is<br />

certainly appropriate for threshold effects.<br />

Although for reproductive and developmental effects thresholds are also<br />

accepted in most cases, no such dose limits are given apart from 1000 mg<br />

kg −1 body weight per day. This dose limit is not equivalent to that for the R<br />

48-phrase, because it only stems from the limit dose levels <strong>of</strong> the test<br />

guideline and is higher by more than one magnitude. Thus, for<br />

reproductive/ developmental toxicity classification, exposure and risk<br />

considerations are not influential in contrast to the R 48. Such a simplified<br />

‘yes or no’ approach for a threshold effect is not justifiable neither from a<br />

scientific point <strong>of</strong> view nor for an appropriate health protection. This is<br />

even more so, if the proposal for the ‘Restrictions on Marketing and Use<br />

Directive’ (13th Amendment to Directive 76/769/EEC) is implemented<br />

calling for a general prohibition <strong>of</strong> category 1 and 2 reproductive/<br />

developmental toxicants in consumer products in concentrations <strong>of</strong> ≥0.5%<br />

—if no specific concentration limit has been accepted according to the<br />

preparation guideline (Commission Directive 93/18/EEC; Council Directive<br />

88/379/EEC).<br />

The inconsistency <strong>of</strong> the approaches for ‘classical’ organ toxicity and<br />

developmental/reproductive toxicity can easily be demonstrated by the<br />

following theoretical example:<br />

For neurotoxicity a LOEL <strong>of</strong> 40 mg kg −1 day −1 in a 90-day oral test will<br />

result in a R 48-phrase, but a LOEL <strong>of</strong> 80 mg kg −1 day −1 would not<br />

lead to classification. On the other hand, slight foetal weight

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