Crop activities lead to dermal exposure of workers to pesticides. The efficacy of hand washing as a control measure is unknown. The efficacy of water and soap was studied for some pesticides and exposure situations. Pre-washing contamination levels in field studies were calculated from foliar residues by models using transfer factors. Between 24.5% and 50.7% of the calculated prewashing contamination was removed in two field studies with three pesticides, with coefficients of variation between 43% and 72%. In a human volunteer study, on average 45.8% and 85.7% was removed for two pesticides (coefficients of variation 6% and 7%). No influence of 'washing vigour' was found and efficacy did not depend on pre-washing contamination levels. The combination of field studies and laboratory experiments was successful, partly compensating for weaknesses in both approaches.
Respiratory exposure and dermal exposure of the hands and forearms to the pesticides chlorothalonil, thiophanate-methyl, thiram, and zineb during application and during crop activities have been measured on 18 farms for carnation culture in glass-covered greenhouses in the Netherlands. Farms were selected according to a "worst case" strategy with regard to dermal exposure during cutting of flowers. For 94 workers, the geometric mean dermal exposure rate during cutting (measured on long-sleeved cotton glove monitors) was 10.1 mg/hr (active ingredient per unit of actual working time) and during sorting/bundling of these flowers by 35 workers the dermal exposure rate was 7.3 mg/hr. The average concentration in air as measured by personal air sampling during cutting after a pesticide had been dusted was 0.07 mg/m3. For the same area, spraying a pesticide exposed the applicator to a dermal exposure seven times higher than dusting. However, during dusting respiratory exposure was higher. Generally, overall exposure is higher during re-entry activities than during application. From the observed levels of dermal exposure during harvesting (re-entry) and from toxicity data, health risk occurs after application of pesticides that are relatively toxic and show relatively good skin-penetrating properties at relatively high application rates. The respiratory exposure to dusted pesticides after re-entry is about as high as during application of these pesticides and may in some situations also result in health risks. Training and education of greenhouse workers on (personal) hygiene and use of protective gloves are advocated in order to reduce exposure.
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