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Science and Judgment in Risk Assessment (1994)
Board on Environmental Studies and Toxicology (BEST)

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. "Appendix I: Aggregation." Science and Judgment in Risk Assessment. Washington, DC: The National Academies Press, 1994.

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Appendix
I-1
Aggregate Risk of Nonthreshold, Quantal, Toxic End Points Caused by
Exposure to Multiple Agents (Assuming Independent Actions)

The aggregate increased probability P of occurrence of any of n (presumed) nonthreshold end points caused by exposure to an environmental mixture of m toxic agents may be conveniently expressed under a few general assumptions. First, assume that the m agents are present in an environmental mixture at corresponding concentrations Ci, where i = 1,2,…,m, each of which produce, in exposed people, corresponding lifetime, time-weighted average biologically effective dose rates Dij, each causing one or more of n quantal (all or none) toxic end points Tj, where j = 1,2,…,n (see Figure I-1). Let Oij denote the occurrence of a particular jth end point Tj induced by effective dose rate Dij, and assume that Tj has a background occurrence probability of pj = Prob(Oij ¦ D=0) for total effective dose D due to all relevant agents and that Oij may arise only by events independent of those giving rise to either the background incidence rate of Tj or to events Ogh for any g and h such that g≠i, 1≤g≤m, h≠j, and 1≤h≤n. Finally, for very small values of Dij, assume that the corresponding increased probability of occurrence of the Tj is defined by an independent ''one-hit" (nonthreshold, low-dose linear) function of Dij. In the following, ∩, ∪, and the overbar denote the logical union, intersection, and negation operations, respectively.

It follows from the stated assumptions and definitions that a Dij-induced increased probability Pij of Tj occurrence, conditional on its independent background rate pj, is:

(1)

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Page
516
Front Matter (R1-R16)
Executive Summary (1-15)
1 Introduction (16-22)
Part I Current Approaches to Risk Assessment: 2 Risk Assessment and its Social and Regulatory Contexts (23-42)
3 Exposure Assessment (43-55)
4 Assessment of Toxicity (56-67)
5 Risk Characterization (68-78)
Part II Strategies for Improving Risk Assessment: 6 Default Options (79-105)
7 Models, Methods, and Data (106-143)
8 Data Needs (144-159)
9 Uncertainty (160-187)
10 Variability (188-223)
11 Aggregation (224-242)
Part III Implementation of Findings: 12 Implementation (243-268)
References (269-286)
Appendix A: Risk Assessment Methodologies: EPA (287-350)
Appendix B: EPA Memorandum from Henry Habicht (351-374)
Appendix C: Calculation and Modeling of Exposure (375-382)
Appendix D: Working Paper for Considering Draft Revisions to the U.S. EPA Guidelines for Cancer Risk Assessment (383-448)
Appendix E: Use of Pharmacokinetics to Extrapolate from Animal Data to Humans (449-452)
Appendix F: Uncertainty Analysis of Health Risk Estimates (453-478)
Appendix G: Improvement in Human Health Risk Assessment Utilizing Site- and Chemical-Specific Information: A Case Study (479-502)
Appendix H-1: Some Definitional Concerns About Variability (503-504)
Appendix H-2: Individual Susceptibility Factors (505-514)
Appendix I: Aggregation (515-536)
Appendix J: A Tiered Modeling Approach for Assessing the Risks Due to Sources of Hazardous Air Pollutants (537-582)
Appendix K: Science Advisory Board Memorandum on the Integrated Risk Information System and EPA Response (583-590)
Appendix L: Development of Data Used in Risk Assessment (591-598)
Appendix M: Charge to the Committee (599-600)
Appendix N-1: The Case for (601-628)
Appendix N-2: Making Full Use of Scientific Information in Risk Assessment (629-640)
Index (641-652)