Division of Environmental Science and Ecological Engineering, Korea University, 145 Anam-ro, Seongbuk-gu, Seoul 02841, Republic of Korea.
Department of Environmental Engineering, Pusan National University, 63 Busandaehak-ro, Geumjeong-gu, Busan 46241, Republic of Korea.
Environ Int. 2021 Oct;155:106581. doi: 10.1016/j.envint.2021.106581. Epub 2021 Apr 25.
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.
拟除虫菊酯自 20 世纪 60 年代以来就被广泛用作家用杀虫剂产品的有效成分。尽管已经对其在室内环境中的存在情况进行了研究,但家用杀虫剂的使用对拟除虫菊酯的综合暴露的贡献尚不清楚。本研究的目的是通过使用生物监测和个人暴露模型来估计消费者在夏季使用家用杀虫剂喷雾时对代表拟除虫菊酯的氯菊酯的接触情况。通过分析一组消费者(n=27)尿液中的代谢物 3-苯氧基苯甲酸(3-PBA)和顺/反-3-(2,2-二氯乙烯基)-2,2-二甲基环丙烷羧酸(顺/反-DCCA)来评估对氯菊酯的接触情况。还将代谢物水平与考虑个人暴露参数的筛选暴露模型预测的水平进行了比较。在 15 名参与者中,代谢物的水平随着家用杀虫剂产品的使用而显著增加(p<0.05),这表明夏季大量使用家用杀虫剂除了食物摄入等其他来源外,可能是氯菊酯的一个重要暴露途径。对于大多数参与者,通过排泄的 3-PBA 和顺/反-DCCA 的总量低于暴露模型估计的量,相差 0.9-861.0 倍。这些差异可能归因于施用后氯菊酯的快速损失,包括对室内表面的吸附、与室内物质的反应、个体生物学差异和施用期间的通风。然而,用于生物杀灭剂产品初始安全性评估的筛选暴露模型通常表现良好,因为它没有低估在使用家用杀虫剂喷雾时个人对氯菊酯的接触情况。