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Child exposure to organophosphate and pyrethroid insecticides measured in urine, wristbands, and household dust and its implications for child health in South Africa: A panel study

AF. Veludo, M. Röösli, MA. Dalvie, P. Stuchlík Fišerová, R. Prokeš, P. Přibylová, P. Šenk, J. Kohoutek, M. Mugari, J. Klánová, A. Huss, DM. Figueiredo, H. Mol, J. Dias, C. Degrendele, S. Fuhrimann

. 2024 ; 8 (1) : e282. [pub] 20231229

Status not-indexed Language English Country United States

Document type Journal Article

BACKGROUND: Children in agricultural areas are exposed to organophosphate (OP) and pyrethroid (PYR) insecticides. This explorative study investigated child exposure to OPs and PYRs, comparing temporal and spatial exposure variability within and among urine, wristbands, and dust samples. METHODS: During spraying season 2018, 38 South African children in two agricultural areas (Grabouw/Hex River Valley) and settings (farm/village) participated in a seven-day study. Child urine and household dust samples were collected on days 1 and 7. Children and their guardians were wearing silicone wristbands for seven days. Intraclass correlation coefficients (ICCs) evaluated temporal agreements between repeated urine and dust samples, Spearman rank correlations (Rs) evaluated the correlations among matrices, and linear mixed-effect models investigated spatial exposure predictors. A risk assessment was performed using reverse dosimetry. RESULTS: Eighteen OPs/PYRs were targeted in urine, wristbands, and dust. Levels of chlorpyrifos in dust (ICC = 0.92) and diethylphosphate biomarker in urine (ICC = 0.42) showed strong and moderate temporal agreement between day 1 and day 7, respectively. Weak agreements were observed for all others. There was mostly a weak correlation among the three matrices (Rs = -0.12 to 0.35), except for chlorpyrifos in dust and its biomarker 3,5,6-trichloro-2-pyridinol in urine (Rs = 0.44). No differences in exposure levels between living locations were observed. However, 21% of the urine biomarker levels exceeded the health-risk threshold for OP exposure. CONCLUSIONS: Observed high short-term variability in exposure levels during spraying season highlights the need for repeated sampling. The weak correlation between the exposure matrices points to different environmental and behavioral exposure pathways. Exceeding risk thresholds for OP should be further investigated.

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$a BACKGROUND: Children in agricultural areas are exposed to organophosphate (OP) and pyrethroid (PYR) insecticides. This explorative study investigated child exposure to OPs and PYRs, comparing temporal and spatial exposure variability within and among urine, wristbands, and dust samples. METHODS: During spraying season 2018, 38 South African children in two agricultural areas (Grabouw/Hex River Valley) and settings (farm/village) participated in a seven-day study. Child urine and household dust samples were collected on days 1 and 7. Children and their guardians were wearing silicone wristbands for seven days. Intraclass correlation coefficients (ICCs) evaluated temporal agreements between repeated urine and dust samples, Spearman rank correlations (Rs) evaluated the correlations among matrices, and linear mixed-effect models investigated spatial exposure predictors. A risk assessment was performed using reverse dosimetry. RESULTS: Eighteen OPs/PYRs were targeted in urine, wristbands, and dust. Levels of chlorpyrifos in dust (ICC = 0.92) and diethylphosphate biomarker in urine (ICC = 0.42) showed strong and moderate temporal agreement between day 1 and day 7, respectively. Weak agreements were observed for all others. There was mostly a weak correlation among the three matrices (Rs = -0.12 to 0.35), except for chlorpyrifos in dust and its biomarker 3,5,6-trichloro-2-pyridinol in urine (Rs = 0.44). No differences in exposure levels between living locations were observed. However, 21% of the urine biomarker levels exceeded the health-risk threshold for OP exposure. CONCLUSIONS: Observed high short-term variability in exposure levels during spraying season highlights the need for repeated sampling. The weak correlation between the exposure matrices points to different environmental and behavioral exposure pathways. Exceeding risk thresholds for OP should be further investigated.
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$a Stuchlík Fišerová, Petra $u Masaryk University, Faculty of Science, RECETOX, Brno, Czech Republic $1 https://orcid.org/0000000155754975
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$a Prokeš, Roman $u Masaryk University, Faculty of Science, RECETOX, Brno, Czech Republic $u Global Change Research Institute of the Czech Academy of Sciences, Brno, Czech Republic
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$a Přibylová, Petra $u Masaryk University, Faculty of Science, RECETOX, Brno, Czech Republic
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$a Kohoutek, Jiří $u Masaryk University, Faculty of Science, RECETOX, Brno, Czech Republic $1 https://orcid.org/0000000221288512
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$a Mugari, Mufaro $u Centre for Environmental and Occupational Health Research, School of Public Health, University of Cape Town, Cape Town, South Africa $1 https://orcid.org/0000000227229142
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$a Klánová, Jana $u Masaryk University, Faculty of Science, RECETOX, Brno, Czech Republic
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$a Huss, Anke $u Institute for Risk Assessment Sciences, Utrecht University, Utrecht, the Netherlands $1 https://orcid.org/0000000192681867
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$a Figueiredo, Daniel Martins $u Institute for Risk Assessment Sciences, Utrecht University, Utrecht, the Netherlands $1 https://orcid.org/0000000160800956
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$a Dias, Jonatan $u Wageningen Food Safety Research, part of Wageningen University & Research, Wageningen, The Netherlands
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$a Fuhrimann, Samuel $u Swiss Tropical and Public Health Institute (Swiss TPH), Allschwil, Switzerland $u University of Basel, Basel, Switzerland $1 https://orcid.org/0000000218611737
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