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Environmental Health Criteria 214

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HUMAN EXPOSURE ASSESSMENT<br />

The modelling approaches described above are mathematical<br />

abstractions of physical reality that may or may not provide adequate<br />

estimates of exposure. The preferred way to be sure that a model is<br />

capable of providing useful and accurate information is by validation,<br />

i.e., comparing model predictions with measurements independent of<br />

these used to develop the model. Models can be validated in terms of<br />

prediction accuracy and precision by comparing predicted values to<br />

those measured in the field. Although measurements are preferable as<br />

the "gold standard" in validation of models, comparison of results<br />

from different assessment methods or modelling approaches can also be<br />

used to evaluate validity, or at least agreement. This may be the only<br />

option when measurements are not feasible; for example, in<br />

retrospective assessment of exposure. Model validation is a necessary<br />

precondition for the generalization of model results to a different or<br />

larger population (Ott et al., 1988).<br />

In the statistical modelling approach, data collection is an<br />

integral part of model construction. If the data are known to be from<br />

a statistically representative sample of the population, then there is<br />

no need for further validation. However, validation is necessary if<br />

the results are to be extrapolated beyond the range for which the<br />

existing database provides a statistical description. The physical and<br />

physical-stochastic modelling approaches must be validated with actual<br />

data from separately conducted field studies. Care must be taken that<br />

the data used to validate a model are not biased with respect to<br />

crucial model parameters. The validation step is useful only to the<br />

degree that the sample population is representative of the group to<br />

which results will be extrapolated.<br />

Finally, when modelling environmental-response-health processes,<br />

and when validating such models, it is important to realize that in<br />

principle perfect modelling is possible only for closed systems, and<br />

the systems described in this report are very open-ended. The<br />

practical implication of this fact is that even the best models need<br />

to be validated for each new population and environmental setting<br />

before application.<br />

6.10 Summary<br />

An exposure model is a logical or empirical construct which<br />

allows estimation of individual or population exposure parameters from<br />

available input data. Exposure models, if supported by adequate<br />

observations, can be used to estimate group exposures (e.g., a<br />

population mean) or individual exposures (e.g., the distribution of<br />

exposures among members of a population). Models may be used to<br />

estimate exposure via single or multiple media. The latter is<br />

particularly useful for comparing the magnitude of exposures likely to<br />

occur from different media and thus for priority-setting. Exposure<br />

models may be statistical or deterministic in nature or a combination<br />

of both. Probabilistic methods may be applied to all three types as a<br />

means to estimate population distributions of exposure, i.e.,<br />

variability of exposure among individuals. In addition, probabilistic<br />

methods may be used to characterize uncertainty in model input<br />

parameters and propagate that uncertainty through to the prediction<br />

end-point. Evaluation of the accuracy of model results is critical<br />

before relying on model output for decision-making.<br />

7. MEASURING HUMAN EXPOSURES TO CHEMICALS IN AIR, WATER AND FOOD<br />

http://www.inchem.org/documents/ehc/ehc/ehc<strong>214</strong>.htm<br />

Page 110 of 284<br />

6/1/2007

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