National Academy of Sciences | 150 Year Anniversary

Questions? Call 800-624-6242

| Items in cart [0]

The National Academies Press

PAPERBACK
price:$162.25
add to cart

Rights & Permissions

topleft topright

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

Citation Manager

. "3 Exposure Assessment." Science and Judgment in Risk Assessment. Washington, DC: The National Academies Press, 1994.

Please select a format:

BibTeX EndNote RefMan


Page
44
bottomleft bottomright

The following HTML text is provided to enhance online readability. Many aspects of typography translate only awkwardly to HTML. Please use the page image as the authoritative form to ensure accuracy.


Page 44

until it makes contact with humans in its original form or after conversion to other substances. For most airborne substances, inhalation is assumed to be the primary route of entry into the body. There has recently been an extensive review of advances in assessing human exposure to airborne constituents (NRC, 1991a). That review attempted to define exposure carefully as a part of the overall continuum that leads to illness brought about by environmental contaminants. The definition of exposure as a part of this continuum has been incorporated into the 1992 revised guidelines for exposure assessment developed by EPA (1992a).

Human exposure to a contaminant is an event consisting of contact with a specific contaminant concentration at a boundary between a human and the environment (e.g., skin or lung) for a specified interval; total exposure is determined by the integrated product of concentration and time. The amount of a substance that is absorbed or deposited in the body of an exposed person in a given period is the administered dose. Calculating the dose from the exposure depends on a number of factors, including the mode of entry into the body. For substances that move into the body through an opening—such as the mouth or nose via breathing, eating, or drinking—the dose depends on the amount of the carrier medium that enters the body. For airborne substances, the potential dose is the product of breathing rate (volume of air inhaled per unit of time), exposure concentration, and fractional deposition of the substance throughout the respiratory tract. However, an inhalation exposure will not lead to a dose if none of the substance is absorbed through the lung or deposited on the surface of the lung or other sections of the respiratory tract.

A pollutant can also enter the body through the skin or other exposed tissues, such as the eyes. The substance is then directly absorbed from the carrier medium into the tissue, often at a rate that is different from the rate of absorption of the carrier. The pollutant uptake rate is the amount of the pollutant absorbed per unit of time, and the dose is the product of exposure concentration and uptake rate at that concentration. The NRC report on exposure assessment (NRC, 1991a) provides a scientific framework to identify routes of entry and degree of contact and indicates how exposure assessment integrates data on emitted pollutants with biological effects.

Exposure assessment involves numerous techniques to identify a pollutant, pollutant sources, environmental media of exposure, transport through each medium, chemical and physical transformations, routes of entry to the body, intensity and frequency of contact, and spatial and temporal concentration patterns of the pollutant. Mathematical models that can be used to describe the relationships among emissions, exposures, and doses are shown in Appendix C.

Exposure to a contaminant can be estimated in three ways. It can be evaluated directly by having a person wear a device that measures the concentration of a pollutant when it comes into contact with the body. Environmental monitoring is an indirect method of determining exposure, in which a chemical's concentration is measured in an environmental medium at a particular site, and the extent

Page
44
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)