Annals of Occupational Hygiene Advance Access originally published online on March 1, 2006
Annals of Occupational Hygiene 2006 50(5):505-515; doi:10.1093/annhyg/mel005
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Biological Monitoring of Exposure to Organophosphorus Insecticides in a Group of Horticultural Greenhouse Workers
1 Chaire en analyse des risques toxicologiques pour la santé humaine and Département de santé environnementale et santé au travail, Faculté de Médecine Université de Montréal, C.P. 6128, Succursale Centre-ville, Montréal, Québec, Canada H3C 3J7
2 Institut national de santé publique du Québec, 4835 Christophe-Colomb Bureau 200, Montréal, Québec, Canada H2J 3G8
3 Département de Mathématiques et de Statistique and Centre de Recherches Mathématiques, Université de Montréal C.P. 6128, Succursale Centre-ville, Montréal, Québec, Canada H3C 3J7
4 Institut national de santé publique du Québec, 945 Wolfe Sainte-Foy, Québec, Canada G1V 5B3
*Author to whom correspondence should be addressed. Tel: +1-514-343-6111 (ext 1640); fax: +1-514-343-2200; e-mail: michele.bouchard{at}umontreal.ca
Exposure to selected organophosphorus insecticides (OPs), malathion, diazinon and acephate, was evaluated in a group of horticultural greenhouse workers. This was achieved through measurements of the cumulative urinary excretion time courses of specific and non-specific biomarkers over a 24 h period following the onset of work exposure. For malathion, the absorbed daily doses were estimated from the 24 h cumulative urinary amounts of the specific mono- and di-carboxylic acid metabolites (the sum of MCA and DCA) through the use of a kinetic model. The observed 24 h urinary levels were also compared with a biological reference value (BRV) of 57 nmol kg–1 of body weight established in a previous work on the basis of a human no-observed-effect level exposure dose. Excretion values were found to be 2.5% or less of the BRV, suggesting a negligible health risk. Both median and 95th percentile concentrations of DCA (n = 57 samples) were, however, slightly higher than the baseline values determined by the Centers for Disease Control and Prevention (CDC) in the US civilian population (MCA was not analyzed by the CDC). The cumulative urinary excretion time course of the methyl phosphoric (MP) derivatives, which are metabolites of malathion but also of several other OPs, was also determined. Though relatively low, the MP levels were from 3 to 31 times higher than would be expected on the basis of the malathion specific MCA and DCA excretions, indicating that MP excretions stem from sources other than malathion exposure. Accordingly, only the time courses of MCA and DCA excretion rate (nmol h–1) were compatible with the time of work exposure. Urinary biomarkers of exposure to diazinon and acephate were also measured. Urinary concentrations were essentially below or equal to the analytical limit of detection of 1 µg l–1 for 2-isopropyl-4-methyl-6-hydroxypyrimidine (n = 54) and of 0.8 µg l–1 for acephate and methamidophos (n = 59): values within the baseline range of the US civilian population, like the observed phosphoric metabolite concentrations. The workers under study thus appeared to be only slightly more exposed to malathion than the general population. However, their overall exposure to OPs, as measured by non-specific phosphoric metabolites, was similar to that of the general population, whose exposure occurs mainly through the ingestion of contaminated food. These results question the relevance of measuring non-specific phosphoric metabolites when attempting to assess low-dose occupational exposure to a specific OP.
Keywords: acephate • biomonitoring • diazinon • malathion • occupational exposure • organophosphorus insecticides