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toxicological profile for malathion - Agency for Toxic Substances and ...

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MALATHION 30<br />

3. HEALTH EFFECTS<br />

Respiratory Effects. In a controlled-exposure study, 16 male volunteers (4/exposure level) were<br />

exposed to aerosol bombs that contained 0 (control), 5, or 20% <strong>malathion</strong> <strong>for</strong> 1 hour 2 times/day <strong>for</strong><br />

42 days (Golz 1959). The actual exposure concentrations were 0, 5.3, 21, or 85 mg/m 3 . By adjusting the<br />

application rate of the 20% <strong>for</strong>mation, the highest exposure groups were <strong>for</strong>med.The <strong>malathion</strong> in the<br />

<strong>for</strong>mulation was 95% pure. There were no signs of toxicity during the study, with the exception of<br />

complaints of nasal irritation in men exposed to the highest concentration during the first 5–10 minutes of<br />

each exposure. One study of 85 subjects who worked in the production of six organophosphate pesticides<br />

(<strong>malathion</strong> was one of them) <strong>for</strong> periods ranging from 0.1 to 29 years found a higher frequency of upper<br />

respiratory tract infections in workers than in 67 controls (Hermanowicz <strong>and</strong> Kossman 1984) (see also<br />

in<strong>for</strong>mation under Immunological Effects). Also, those exposed <strong>for</strong> 11–29 years had more respiratory<br />

infections than individuals exposed <strong>for</strong> 0.1–2 years. Be<strong>for</strong>e <strong>and</strong> during the study, total air concentrations<br />

of organophosphates remained below admissible limits. Exposure to chlorinated solvents also occurred<br />

during pesticide production <strong>and</strong> may have contributed to the effects observed. The role of <strong>malathion</strong>, if<br />

any, cannot be ascertained. Additional in<strong>for</strong>mation was found in a study of self-reported symptoms in<br />

22 seamen who may have been exposed to a single cloud of <strong>malathion</strong> that escaped from a nearby<br />

overheated tank (Markowitz et al. 1986). Compared with a group of controls, the seamen reported<br />

significantly more problems with sore throat, stuffy nose, <strong>and</strong> laryngitis when contacted 12 days<br />

following the incident. It should be noted, however, that there was no evidence of actual exposure to the<br />

chemical.<br />

Following aerial application of <strong>malathion</strong> in Santa Clara County, Cali<strong>for</strong>nia, in 1981, a survey was<br />

conducted to assess the acute health effects of the application (Kahn et al. 1992). The study included<br />

three indirect assessments that focused on the utilization of acute care services <strong>and</strong> two surveys to assess<br />

self-reported symptoms. The results showed no significant increase in the number of visits <strong>for</strong> the broad<br />

category, respiratory, to hospital emergency departments during the application period compared with the<br />

prespray period or the corresponding period the previous year. Furthermore, there was no significant<br />

increase in the number of asthma-related visits to a university medical school in the area, although the<br />

numbers in the study may have been too small to provide definite conclusions. The results of the surveys<br />

to assess self-reported symptoms revealed no detectable increase in acute morbidity or in<br />

organophosphate-compatible symptomatology, but again, the sample size may have been too small <strong>for</strong><br />

marginal increases in the prevalence of various symptoms to be detected.

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