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PRINCIPLES OF TOXICOLOGY

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18.4 DOSE–RESPONSE ASSESSMENT 457<br />

Figure 18.6 Four different extrapolation models applied to the same experimental data. All fit the data equally<br />

well in the observable range, but each yields substantially different risk estimates in the low-dose region most<br />

applicable to occupational and environmental exposures. [Adapted from NRC (1983).]<br />

threshold for even those carcinogens whose mechanism is believed to involve some mutational event<br />

or other form of genetic damage. Thus, it is widely held today that thresholds exist for many<br />

carcinogens, and that cancer risk assessment for these chemicals should be conducted using threshold<br />

dose–response models similar to those used for noncancer effects.<br />

In recent years, debates involving the actual shape of the dose–response curve for carcinogens in<br />

the low-dose region, and the issue of thresholds for carcinogens, have caused scientists and regulatory<br />

agencies to reevaluate earlier cancer risk assessment methodologies. Out of this reevaluation has come<br />

a movement to adopt two major policy changes in the cancer risk assessment methodologies employed<br />

by regulatory agencies. One proposed change is to use risk extrapolation models that make fewer<br />

assumptions about the shape of the dose–response curve (e.g., the benchmark dose and margin-ofexposure<br />

method). Data within the observation range can be used to develop a “point of departure,”

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