Department of Marine Sciences and Convergent Technology, College of Science and Technology, Hanyang University, Ansan, 426-791, Republic of Korea.
Wadsworth Center, New York State Department of Health and Department of Environmental Health Sciences, State University of New York, Albany, NY, 12201-0509, USA.
Water Res. 2016 Oct 15;103:182-188. doi: 10.1016/j.watres.2016.07.034. Epub 2016 Jul 18.
Organophosphate flame retardants (OPFRs) have been widely used as flame retardants and plasticizers in commercial products. Limited data are available on the occurrence and exposure of OPFRs via drinking water consumption. In this study, 127 drinking water samples were collected from tap water, purified water (tap water that is passed through in-house filters) and bottled water from major cities in Korea in 2014. The total concentrations of OPFRs (ΣOPFR) in all of the samples ranged from below the method detection limit (MDL) to 1660 (median: 48.7) ng/L. The predominant OPFR compounds in drinking water were tris(2-chloroethyl) phosphate (TCEP), tris(2-chloroethyl) phosphate (TCPP), and tris(2-butoxyethyl) phosphate (TBEP). Significant differences were observed in the levels of TCPP, TBEP and ΣOPFR among various types of drinking water. TCPP is introduced in the drinking water during the water purification process. Regional differences existed in the levels and patterns of OPFRs in water samples, which indicated the existence of diverse sources of these contaminants. Purified water was a significant contributor to the total OPFR intake by humans. The estimated daily intake of OPFRs was lower than the tentative oral reference dose (RfD) values. In comparison with exposure of OPFRs via dust ingestion, water consumption was a significant source of chlorinated PFRs (99% for TCEP and 34% for TCPP to the total intakes) for Koreans.
有机磷阻燃剂 (OPFRs) 已被广泛用作商业产品中的阻燃剂和增塑剂。目前关于通过饮用水摄入 OPFRs 的发生和暴露的相关数据有限。在这项研究中,2014 年从韩国主要城市的自来水、纯净水(通过内部过滤器过滤的自来水)和瓶装水中采集了 127 个饮用水样本。所有样本中 OPFRs 的总浓度(ΣOPFR)从低于方法检测限 (MDL) 到 1660(中位数:48.7)ng/L 不等。饮用水中主要的 OPFR 化合物为三(2-氯乙基)磷酸酯 (TCEP)、三(2-氯乙基)磷酸酯 (TCPP) 和三(2-丁氧基乙基)磷酸酯 (TBEP)。不同类型饮用水中 TCPP、TBEP 和 ΣOPFR 的水平存在显著差异。TCPP 是在饮用水净化过程中引入的。水样中 OPFRs 的水平和模式存在区域性差异,这表明存在多种此类污染物的来源。纯净水是人类总 OPFR 摄入量的重要贡献者。OPFRs 的估计每日摄入量低于暂定口服参考剂量 (RfD) 值。与通过灰尘摄入接触 OPFRs 相比,水的消耗是韩国人摄入氯化 PFRs 的重要来源(TCEP 占总摄入量的 99%,TCPP 占 34%)。