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Impact of - IDL-BNC @ IDRC - International Development Research ...

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from the general population, <strong>of</strong>ten referred to as community controls, or from<br />

hospitals where cases were identified. Three criteria have been proposed for<br />

the selection <strong>of</strong> controls:<br />

Controls should come from the same registry (e.g., hospital, mortality<br />

records) as the index cases.<br />

Control illness should be unrelated to the risk factors under study (i.e.,<br />

a given risk factor under study should not predispose one to getting the<br />

control illness).<br />

Control illness should be similar to the illness under study, bearing in<br />

mind the factors influencing its appearance (or referral) in the registry<br />

One might want to add a second control if these criteria are not met.<br />

If farmers are under study, then ideally, the control group should also be<br />

farmers. Farming is a unique way <strong>of</strong> life, not only in terms <strong>of</strong> chemical<br />

exposure, but also with respect to diet, physical activity, exposure to viruses,<br />

habits, and life-style. Opportunity for exposure to viruses, for example, may<br />

be affected by the presence <strong>of</strong> intermediate hosts, including livestock or even<br />

particular crops.<br />

In carrying out epidemiological studies, accurate measurement <strong>of</strong> exposure is<br />

important because errors may reduce estimates <strong>of</strong> relative risk and dampen<br />

dose-response gradients. Misclassification <strong>of</strong> toxic substance increases the<br />

chance <strong>of</strong> attributing elevated cancer risk among exposed people to the wrong<br />

agent. Employment records are commonly used to assess exposure in cohort<br />

studies and interviews are used to determine exposure in case-control studies.<br />

However, these techniques are <strong>of</strong> use in both types <strong>of</strong> study and should be<br />

used, when possible, to test and improve the reliability <strong>of</strong> exposure evaluations.<br />

Information can be obtained from different sources to increase confidence in<br />

exposure estimates. Sources include suppliers who sell pesticides to the subjects<br />

under study, records <strong>of</strong> applicator companies, interviews about the type<br />

<strong>of</strong> equipment used for application, and duration and frequency <strong>of</strong> application<br />

coupled with biochemical monitoring data. For populations, estimates <strong>of</strong><br />

exposure may be developed by a panel <strong>of</strong> experts, including agricultural<br />

scientists, entomologists, and industrial hygienists familiar with patterns <strong>of</strong><br />

pesticide use. Biochemical factors can provide better measures <strong>of</strong> delivered<br />

dose than estimates based on concentration <strong>of</strong> substances in patches and<br />

ambient air or those derived from job descriptions or interviews. However,<br />

biochemical measures are typically only available for a sample <strong>of</strong> study<br />

subjects, for only a few pesticides, and at only specific times.<br />

Ideally, to allow epidemiological surveillance <strong>of</strong> a farming population using<br />

pesticides, it would be necessary to implement a system <strong>of</strong> registration that<br />

would identify the exposed subjects and specify and quantify exposure. This<br />

156

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