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328                             CHAPTER 5 PHYSIOLOGICAL AND TOXICOLOGICAL CONSIDERATIONS

                  TABLE 5.23  Biomonitoring Serves Three Different Purposes of
                  Identifying and Using

                     1. Biomarkers for susceptibility of an individual within a population of
                         one species to exposure to an intoxicant—genetically determined
                         susceptibility.
                     2. Biomarkers for internal dose of the intoxicant—dose monitoring.
                     3. Biomarkers for early biological changes following exposure— effect
                         monitoring.
                      Source: Modified from Aldridge. 64


                     2. Hazard characterization and delineation of dose-effect or dose-
                        response relationships
                     3. Assessment of exposure
                     4. Risk characterization
                     Risk characterization should preferentially include qualitative and, if pos-
                  sible, also quantitative risk assessment based on steps 1-3.
                     Hazard identification, step one, means identification of new chemicals
                  or other factors that may cause harmful health effects. Previously, novel
                  hazards were usually observed in case studies or after accidents or other
                  excessive exposures, usually in occupational environments. Today, thor-
                  ough toxicity studies are required on all pesticides, food additives, and
                  drugs. New chemicals also have to be studied for their potential toxic ef-
                  fects. Thus, earlier hazards were in most cases identified after they had
                  caused harmful effects in humans. Today, most chemical products have
                  been evaluated for their toxicity with experimental animals. Therefore,
                  hazard identification has become a preventive procedure based on safety
                  studies conducted before a chemical compound or product reaches the
                  market, and before individuals are exposed to it. 49
                     Hazard characterization, step two, usually utilizes data from toxicity
                  studies with experimental animals. In step one, compounds that have to be
                  studied for their toxicity were briefly described. Health authorities in different
                 countries have issued strict guidelines and regulations on the studies that have
                 to be carried out to evaluate the toxicity of pesticides, food additives, and
                  drugs. Furthermore, the European Union and the OECD have issued regula-
                  tions that are followed in these countries. For example, in the United States,
                  the U.S. Environmental Protection Agency and Food and Drug Administration
                 carefully control the safety of drugs, food additives, pesticides, and other
                 chemicals. The technical quality of the studies has been regulated in detail by
                 good laboratory practice (GLP) guidelines. In Table 5.24, the toxicity/safety
                  studies utilizing experimental animals or other test systems required for the
                 registration of drugs, pesticides, and food additives have been listed. 49
                     Exposure assessment, step three, allows a risk assessor to estimate the sig-
                 nificance of the effects induced by high doses of a chemical in experimental
                 animals in a human situation. Exposure assessment is, in fact, a prerequisite
                 for quantitative risk assessment because it allows a comparison between ef-
                 fects induced by high dose with those induced by low doses, and also allows
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