School of Freshwater Sciences, University of Wisconsin-Milwaukee, 600 E. Greenfield Ave., Milwaukee, WI 53204, USA; Water Technology Accelerator (WaTA), University of Wisconsin-Milwaukee, 247 W. Freshwater Way, Milwaukee, WI 53204, USA.
Water Technology Accelerator (WaTA), University of Wisconsin-Milwaukee, 247 W. Freshwater Way, Milwaukee, WI 53204, USA.
Sci Total Environ. 2020 Sep 1;733:139186. doi: 10.1016/j.scitotenv.2020.139186. Epub 2020 May 4.
Perfluorinated alkyl substances (PFAS) have come to attention recently due to their widespread presence in the environment, recalcitrance, and potential negative health associations. Because of the long-term production of PFAS using ECF, which created branched isomers as byproducts in addition to the intended linear product, branched isomers of PFAS account for a significant portion of PFAS load in the environment. The distribution of isomers is not consistent in the environment, however. Geographic location appears to be a major factor in determining the isomer makeup of PFAS in surface and groundwater as well as in humans and animals. This is largely to differences in production methods; a region that produced PFAS via ECF for many years would have a higher ratio of branched isomers than one that produces PFAS using telomerization. In addition, the different structures of branched PFAS isomers as compared to linear PFAS appear to affect transport in the environment. Research suggests that linear PFAS sorb preferentially to soil and sediments, whereas branched isomers are more likely to remain in water. The higher polarity of the branched structure explains this difference. Studies in humans and animals show that most animals preferentially accumulate the linear PFOS isomer, but humans appear to preferentially accumulate the branched isomers as they are often found in human serum at percentages higher than that of ECF product. In addition, some studies have indicated that linear and branched PFAS isomers have some unique negative health associations. Very few studies, however, account for linear and branched PFAS separately.
全氟烷基物质(PFAS)因其在环境中的广泛存在、难降解性以及潜在的负面健康关联而受到关注。由于 ECF 的长期生产,除了预期的线性产物外,还会产生支链异构体作为副产物,因此 PFAS 中的支链异构体占有相当大的比例。然而,环境中的异构体分布并不一致。地理位置似乎是决定地表水和地下水以及人类和动物体内 PFAS 异构体组成的主要因素。这主要是由于生产方法的差异;一个多年来通过 ECF 生产 PFAS 的地区,其支链异构体的比例会高于使用端基转化生产 PFAS 的地区。此外,与线性 PFAS 相比,支链 PFAS 异构体的不同结构似乎会影响环境中的迁移。研究表明,线性 PFAS 优先吸附到土壤和沉积物中,而支链异构体则更有可能留在水中。支链结构的较高极性解释了这种差异。在人类和动物中的研究表明,大多数动物优先积累线性 PFOS 异构体,但人类似乎更倾向于积累支链异构体,因为它们在人类血清中的百分比通常高于 ECF 产物。此外,一些研究表明,线性和支链 PFAS 异构体具有一些独特的负面健康关联。然而,很少有研究分别考虑线性和支链 PFAS。