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Toxicology of Industrial Compounds

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368 CONTROVERSIAL ISSUES IN SAFETY ASSESSMENT<br />

general population. Thus, AFs <strong>of</strong> >1000 should always be questioned<br />

as possibly over-conservative for threshold effects, since exposure<br />

levels thereby obtained could also be acceptable for non-threshold<br />

effects like carcinogenicity. The assumptions underlying such high AFs<br />

should be re-examined critically.<br />

In the light <strong>of</strong> these considerations AFs for a developmental toxicity <strong>of</strong><br />

1000– 5000, as they are under discussion by some groups today, should<br />

also be questioned as possibly being over-conservative. It should not only be<br />

taken into account that developmental effects most <strong>of</strong>ten will have<br />

thresholds but also that their severities span a wide range from slight foetal<br />

weight impairment up to disabling malformations.<br />

In addition an unreflected selection <strong>of</strong> default factors in ‘classical’ organ<br />

toxicity can easily lead to over-conservative AFs: starting with a factor <strong>of</strong><br />

10 each for inter- and intra-species variability yields the AF <strong>of</strong> 100 used for<br />

ADI-calculations. In addition the following default factors are sometimes<br />

proposed:<br />

– Extrapolation from subacute/subchronic exposure to chronic exposure:<br />

a default factor <strong>of</strong> 10.<br />

– Extrapolation to the NOEL, if only a LOEL was obtained: a default<br />

factor <strong>of</strong> 2–5.<br />

– Taking into account an inappropriate experimental design: a default<br />

factor <strong>of</strong> 2–5–10.<br />

Thereby, for a multiple dose study with a marginal effect at the lowest dose<br />

level and an experimental design not fully in accordance with today’s<br />

standards, these default factors would result in a final assessment factor <strong>of</strong><br />

4000– 50000. It is highly questionable whether such an AF is really<br />

appropriate for threshold effects in comparison to the example given above<br />

for carcinogenicity.<br />

Non-threshold effects<br />

Other principles and approaches for classification and risk assessment have<br />

to be applied for non-threshold effects since safe exposure levels cannot be<br />

defined at which an adverse health effect will definitely not occur. Thus,<br />

for these compounds carcinogenic and mutagenic effects cannot be<br />

excluded even at very low dose levels albeit with extremely low<br />

probability.

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