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

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Cholinesterase levels in red blood cells were determined before and after<br />

monocrotophos exposure using the Michel method. Twenty-four hour urine<br />

was collected before spraying, during the 3 days <strong>of</strong> application, and 1 day after<br />

completion <strong>of</strong> the spraying. The urinary metabolite, dimethyiphosphate, was<br />

determined by gasliquid chromatography.<br />

For all three studies, operational details (crop height, row spacing, area<br />

covered, and rate <strong>of</strong> application) and meteorological data (wind speed, wind<br />

direction, air temperature, and relative humidity) were recorded as recommended<br />

by the WHO protocol.<br />

Results and discussion<br />

Postexposure levels <strong>of</strong> p-nitrophenol in urine were not significantly different<br />

from baseline levels. Two factors explain this: over the previous 9 years,<br />

subjects have been exposed to a number <strong>of</strong> different pesticides, thus the<br />

relatively short exposure to methyl parathion during this study may not have<br />

been sufficient to have an additional effect; the method used to measure<br />

p-nitrophenol may not have been sensitive enough to detect changes.<br />

In keeping with the WHO protocol, contamination <strong>of</strong> the cotton overalls and<br />

potential dermal contamination represented by the gauze patches were<br />

assessed. Mixing and loading activities, which were carried out three to five<br />

times during the 1-h study periods, accounted for 55% <strong>of</strong> the contamination<br />

<strong>of</strong> clothing; that <strong>of</strong> the "all activities" group represented 28% <strong>of</strong> total contamination.<br />

Spraying at any <strong>of</strong> the three stages did not account for a large<br />

proportion <strong>of</strong> the contamination <strong>of</strong> clothing. The risks were equal for the RI<br />

and R2 stages (spraying at the vegetative and maximum tillering stages,<br />

respectively) and accounted for 8% each. The R3 group (spraying at the<br />

booting stage) represented only 1% <strong>of</strong> all contamination <strong>of</strong> clothing.<br />

Potential dermal contamination, i.e., penetration <strong>of</strong> clothing, was assessed by<br />

measuring the amount <strong>of</strong> pesticide in the gauze patches. Of total contamination,<br />

47% was found in the "all activities" groups. Farmers in these groups<br />

performed all activities in I h. They were exposed for a longer period and at<br />

greater pesticide concentrations than those undertaking specific activities.<br />

Mixing and loading accounted for 12.0%; RI for 16.0%; R2 for 21.0%; R3 for<br />

3.0%; and cleaning and disposal 1.0%. There was no dermal contamination<br />

during the reentry periods on days I and 7.<br />

The distribution <strong>of</strong> methyl parathion contamination over different regions <strong>of</strong><br />

the body was assessed by comparing the various cloth sections and patches<br />

for the "all activities" group and the R2 group (Fig. 2). Hands had the highest<br />

potential for dermal contamination and penetration. The high degree <strong>of</strong><br />

contamination <strong>of</strong> the left hand <strong>of</strong> those in the "all activities" group was due<br />

to the farmers' practice <strong>of</strong> applying the pesticide with their right hand, while<br />

the left held the cover <strong>of</strong> the tank sprayers used for measuring the pesticide.<br />

66

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