Title: Current internal exposure to pesticides in children and adolescents in Germany: urinary levels of metabolites of pyrethroid and organophosphorus insecticides Heudorf U, Angerer J, Drexler H Ref: Int Arch Occup Environ Health, 77:67, 2004 : PubMed
AIM: Pesticides are widely used throughout the world, in agriculture to protect crops and in public health to control diseases transmitted by vectors or intermediate hosts. After the prohibition of organochlorines such as DDT, today, mainly pyrethroids and organophosphorus insecticides are used. Whereas many studies have been published on background exposure of the population to organochlorines, data on internal exposure of the population to pyrethroids and organophosphorus insecticides are scarce. Here, we report on internal exposure of children and young people, in an urban area in Germany, to pyrethroids and organophosphorus acids, assessed by the analysis of urinary levels of their corresponding specific metabolites. METHODS: Approximately 673 children and adolescents took part in this voluntary investigation, including 331 children <6 years of age. Their parents stated that they and their children had never used pyrethroids or organophosphorus acids in their homes or for medical reasons. We analysed their spot urine samples for six metabolites of organophosphorus insecticides [dimethyl-phosphate (DMP), diethyl-phosphate (DEP), dimethyl-thiophosphate (DMTP), diethyl-thiophosphate (DETP), dimethyl-dithiophosphate (DMDTP) and diethyl-dithiophosphate (DEDTP)] and for four metabolites of pyrethroids [cis-3-(2,2-dibromo-vinyl)-2,2-dimethyl-cyclopropane carboxylic acid (Br2CA), cis-3-(2,2-dichloro-vinyl)-2,2-dimethyl-cyclopropane carboxylic acid (cis-Cl2-CA ), trans-3-(2,2-dichloro-vinyl)-2,2-dimethyl-cyclopropane carboxylic acid (trans-Cl2-CA) and 4-fluoro-3-phenoxy-benzoic acid (F-PBA)] using gas chromatographic methods with mass-selective detection. The limit of detection was 0.1-0.2 microg/l for pyrethroid metabolites and 1 microg/l for metabolites of organophosphorus acids; in DMP it was 5 microg/l. RESULTS: The 95th percentiles of the urinary metabolite concentrations were, in microgrammes per litre, DMP 158, DMTP 180, DMDTP 12, DEP 17, DETP 8, DEDTP <1; Br2CA 0.30, cis-Cl2-CA 0.44, trans-Cl2-CA 1.22, F-PBA 0.30. There were no correlations between urinary metabolite levels and the age of the children. CONCLUSION: Current background levels of internal exposure to pyrethroids and organophosphorus insecticides in children and adolescents in Germany are shown. Exposure to these substances in the general population is thought to occur mainly via residues in the diet. The level of background internal pyrethroid exposure in the children is orders of magnitude lower than the corresponding acceptable daily intake (ADI) values published, but the level of internal organophosphate exposure may reach and even exceed ADI values. This observation demands further investigation.
Title: Metabolites of organophosphorous insecticides in urine specimens from inhabitants of a residential area Heudorf U, Angerer J Ref: Environ Research, 86:80, 2001 : PubMed
The most frequently used pesticide in U.S. homes, as well as in schools and day care centers, is chlorpyrifos. In 1998, this insecticide was detected in household dust from the former U.S. Forces housing estates in Frankfurt am Main, Germany, resulting from its earlier use up to 1993, i.e., at least 4 years ago. This led to great concern in the new inhabitants. To investigate their internal exposure to the substance, they were offered the opportunity of taking part in biomonitoring examinations. Children playing on the floor were assumed to be especially at risk due to increased exposure to chlorpyrifos via oral or dermal intake. A total of 1146 inhabitants took part in this voluntary investigation. All of them stated that they had never used chlorpyrifos in their homes. Spot urine samples of the study participants were analyzed for six metabolites of organophosphorous insecticides [dimethylphosphate (DMP), diethylphosphate (DEP), dimethylthiophosphate (DMTP), diethylthiophosphate (DETP), dimethyldithiophosphate (DMDTP), and diethyldithiophosphate (DEDTP)] using a very sensitive gas chromatographic method with mass-selective detection and a limit of detection of 1 microg/L. No evidence was found of increased internal exposure due to former chlorpyrifos application in these homes (>4 years ago), either in children or in adults. The median values and 95th percentiles of the urinary metabolite concentrations in 484 adults were (microg/g creatinine): DMP, 15.5 and 102.5; DMTP, 13.5 and 125.8; DMDTP, <1 and 13.1; DEP, 2.1 and 11.6; DETP, <1 and 6.4; DEDTP, both <1. The urinary metabolite concentrations in children <6 years of age were higher; this was caused mainly by lower creatinine concentrations. To conclude, no increase in internal exposure due to former indoor application of chlorpyrifos could be found, and the reference values published for internal organophosphate exposure in adults in Germany were confirmed. However, as shown in other environmental studies, the urinary excretion of organophosphorous metabolites exceeds dietary intake several fold; this has been estimated from the data in various duplicate dietary studies. This observation calls for further investigation.
Title: Biological monitoring of phenmedipham: determination of m-toluidine in urine Schettgen T, Weiss T, Angerer J Ref: Archives of Toxicology, 75:145, 2001 : PubMed
Phenmedipham [methyl-3-(3-methylphenylcarbamoyloxy)carbamate] is used as a herbicide, especially in the growing of sugar beet and strawberries. During metabolism of the substance in rats, the two carbamate moieties of phenmedipham are cleaved and the metabolites methyl-N-(3-hydroxyphenyl)-carbamate, m-aminophenol and hydroxyacetanilide are formed. These compounds and their conjugates are excreted in urine. Additionally, it has been suggested that m-toluidine is formed during metabolism. For the first time it has been possible to detect this metabolite in the urine of workers after agricultural use of phenmedipham. The concentrations of m-toluidine in urine were significantly higher in persons occupationally exposed than in controls. The median values for each group were 0.36 microg/l and 0.16 microg/l, respectively. This means that persons not exposed to phenmedipham also excrete m-toluidine, possibly as a result of the uptake of pesticides like phenmedipham from the diet.
