Department of Civil and Environmental Engineering, The University of Auckland, Auckland, New Zealand.
School of Environment, The University of Auckland, Auckland, New Zealand.
Water Res. 2021 Jul 1;199:117187. doi: 10.1016/j.watres.2021.117187. Epub 2021 Apr 25.
Poly- and perfluoroalkyl substances (PFAS) comprise more than 4,000 anthropogenically manufactured compounds with widescale consumer and industrial applications. This critical review compiles the latest information on the worldwide distribution of PFAS and evaluates their fate in wastewater treatment plants (WWTPs). A large proportion (>30%) of monitoring studies in WWTPs were conducted in China, followed by Europe (30%) and North America (16%), whereas information is generally lacking for other parts of the world, including most of the developing countries. Short and long-chain perfluoroalkyl acids (PFAAs) were widely detected in both the influents (up to 1,000 ng/L) and effluents (15 to >1,500 ng/L) of WWTPs. To date, limited data is available regarding levels of PFAS precursors and ultra-short chain PFAS in WWTPs. Most WWTPs exhibited low removal efficiencies for PFAS, and many studies reported an increase in the levels of PFAAs after wastewater treatment. The analysis of the fate of various classes of PFAS at different wastewater treatment stages (aerobic and/aerobic biodegradation, photodegradation, and chemical degradation) revealed biodegradation as the primary mechanism responsible for the transformation of PFAS precursors to PFAAs in WWTPs. Remediation studies at full scale and laboratory scale suggest advanced processes such as adsorption using ion exchange resins, electrochemical degradation, and nanofiltration are more effective in removing PFAS (~95-100%) than conventional processes. However, the applicability of such treatments for real-world WWTPs faces significant challenges due to the scaling-up requirements, mass-transfer limitations, and management of treatment by-products and wastes. Combining more than one technique for effective removal of PFAS, while addressing limitations of the individual treatments, could be beneficial. Considering environmental concentrations of PFAS, cost-effectiveness, and ease of operation, nanofiltration followed by adsorption using wood-derived biochar and/or activated carbons could be a viable option if introduced to conventional treatment systems. However, the large-scale applicability of the same needs to be further verified.
多氟和全氟烷基物质 (PFAS) 由超过 4000 种人为制造的化合物组成,广泛应用于消费和工业领域。本综述性文章汇集了有关 PFAS 在全球范围内分布的最新信息,并评估了它们在废水处理厂 (WWTP) 中的命运。有很大比例(>30%)的 WWTP 监测研究是在中国进行的,其次是欧洲(30%)和北美(16%),而其他地区(包括大多数发展中国家)的信息通常较为缺乏。短链和长链全氟烷基酸 (PFAAs) 广泛存在于 WWTP 的进水(高达 1000ng/L)和出水(15 到 >1500ng/L)中。迄今为止,有关 WWTP 中 PFAS 前体和超短链 PFAS 的水平数据有限。大多数 WWTP 对 PFAS 的去除效率较低,许多研究报告称废水处理后 PFAAs 的水平增加。分析不同废水处理阶段(好氧和/或好氧生物降解、光降解和化学降解)各种 PFAS 类别的命运表明,生物降解是 WWTP 中将 PFAS 前体转化为 PFAAs 的主要机制。全规模和实验室规模的修复研究表明,吸附剂如离子交换树脂、电化学降解和纳滤等高级处理工艺比传统工艺更有效地去除 PFAS(~95-100%)。然而,由于放大要求、传质限制以及处理副产物和废物的管理,这些处理方法在实际 WWTP 中的应用面临重大挑战。结合多种技术以有效去除 PFAS,同时解决单个处理方法的局限性,可能是有益的。考虑到 PFAS 的环境浓度、成本效益和操作便利性,如果将其引入传统处理系统,纳滤后使用木质衍生生物炭和/或活性炭进行吸附可能是一种可行的选择。然而,同样的大规模适用性还需要进一步验证。