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Exposure to permethrin used as a home insecticide: A case study comparing model predictions and excretion of metabolites

Authors
Park, Seon-KyungLee, Heon-JunSong, EugeneKim, YoonsubKim, Du YungLee, Jong-HyeonYoo, Hyun JungOh, Jeong-EunKwon, Jung-Hwan
Issue Date
Oct-2021
Publisher
PERGAMON-ELSEVIER SCIENCE LTD
Keywords
Consumer exposure; Insecticides; Intervention study; Permethrin; Pyrethroids
Citation
ENVIRONMENT INTERNATIONAL, v.155
Indexed
SCIE
SCOPUS
Journal Title
ENVIRONMENT INTERNATIONAL
Volume
155
URI
https://scholar.korea.ac.kr/handle/2021.sw.korea/136110
DOI
10.1016/j.envint.2021.106581
ISSN
0160-4120
Abstract
Pyrethroids have been widely used as an active ingredient in home insecticide products since the 1960 s. Although their occurrence in indoor environments has been studied, the contribution of home insecticide application to the aggregate exposure to pyrethroids is not well known. The objective of this study was to estimate the consumer exposure to permethrin, a representative pyrethroid, via the use of home insecticide spray during the summer season using biomonitoring and personal exposure modeling. Exposure to permethrin was assessed by analyzing its urinary metabolites, 3-phenoxybenzoic acid (3-PBA) and cis/trans-3-(2,2-dichlorovinyl)-2,2-dimethylcyclopropan carboxylic acid (cis/trans-DCCA), for a group of consumers (n = 27). The levels of metabolites were also compared with those predicted by a screening exposure model considering personal exposure parameters. The levels of metabolites in 15 participants increased significantly (p < 0.05) with the application of home insecticide products, thereby suggesting that the heavy use of home insecticides during summer could be an important exposure route of permethrin in addition to other sources, such as food consumption. The total amount of excreted 3-PBA and cis/trans-DCCA was lower than the amount estimated by the exposure model for most participants by a factor of 0.9-861.0. These differences could be attributed to the rapid loss of permethrin after application, including sorption to indoor surfaces, reaction with indoor substances, individual biological variations, and ventilation during application. However, the screening exposure model used for the initial safety assessment of biocidal products generally performed well because it did not underestimate the personal exposure to permethrin during the application of home insecticide spray.
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