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Exposure assessment is a critical component of epidemiologic research, and unfortunately for many studies, it is this component that introduces many limitations. Exposure assessment has been defined by Last (2001) as the ‘process of estimating concentration or intensity, duration, and frequency of exposure to an agent that can affect health’ (p. 66). It involves preferably quantitative, but often qualitative, procedures to estimate and assign an individual's past or current exposures. Various types of exposures are studied in epidemiology. Some common examples are summarized in Table 1.

A person's behavior, dietary patterns, smoking history, family history, personal characteristics, and exercise are frequently studied in epidemiologic research as potential exposures, risk factors for exposure, and potential confounders. However, generally the area of exposure assessment in epidemiologic research refers to its application in occupational and environmental epidemiology.

Exposure assessment is also used for purposes beyond epidemiologic research such as risk assessment and regulatory compliance. As an element in risk assessment, exposure assessment has been defined by Jayjock, Lynch, and Nelson (2000) as ‘the activity that describes the nature and size of the various populations exposed to a chemical agent and the magnitude and duration of their exposures’ (p. 26). In regulatory compliance, exposure assessment serves as a quantitative method by which measures of exposure can be compared with established exposure limits. This entry discusses exposure assessment in the context of occupational and environmental epidemiologic studies, although these principles can be applied to all types of epidemiologic research.

Table 1 Types of Environmental Agents or General Factors to Which One Can Be Exposed
Agent TypeExamples
ChemicalSolvents, pesticides, acrylamides, drugs
MetalArsenic, nickel, chromium, lead, cadmium
PhysicalRadiation, temperature, noise, ergonomic, physical force
ParticulateDusts, fibers, molds, silica, fumes
BiologicalViruses, fungi, parasites, bacteria, prions
PsychosocialViolence, stress, social networks
NutritionalFiber in diet, meat consumption, vegetable consumption
BehaviorsSmoking, alcohol consumption, exercise
Family historyFamily history of specific disease
Personal characteristicsHeight, weight, race, sex, body mass index (BMI)
Source: Adapted in part from Rom (1992) and Plog (2002).

Epidemiologic Approaches to Exposure Assessment

Exposure assessment in epidemiology can be broken into various phases that include (1) identification and characterization of the exposed population; (2) evaluation of potential exposure pathways; (3) assessment of the frequency, intensity, and duration of exposure; and (4) exposure classification.

The first issue to consider in exposure assessment is choosing the group that represents the most appropriate and feasible population to study, given the specific research questions. Often, worker populations are selected because of the availability of exposure information and the fact that higher exposures typically occur in workplace settings; however, it may be more appropriate to study specific community members, consumers, or the general population depending on the research question. Most environmental or occupational epidemiologic studies estimate exposure for groups of individuals who are expected to share similar exposure characteristics (e.g., levels, variation).

The second issue to consider is the potential route of exposure, which can include dermal uptake, oral intake via ingestion or mouthing (for children), inhalation, or a combination of pathways. In the case of physical agents (e.g., electric or magnetic fields), simply being present in a field or experiencing a physical force constitutes the route of exposure. For exposure to occur, a ‘complete’ exposure pathway must exist. Examples of incomplete pathways, which prevent exposure to contaminants, include a concrete cap in a foundation that could prevent intrusion of a soil contaminant into a home, or vegetative cover that could reduce release of metal-laden dusts. The amount of agent taken into the body depends on various characteristics such as particle size (for inhalation), bioavailability, human behavior, whether natural barriers or personal protective equipment prevent actual exposure, and whether the substance is transformed within the body.

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