Chen Zhenhuan, Wei Zhangting, Yang Zilin, Chen Yinjuan, Zhang Yanyan
College of Environmental and Resource Sciences, Zhejiang University, Hangzhou 310058, China.
Key Laboratory of Coastal Environment and Resources of Zhejiang Province, School of Engineering, Westlake University, Hangzhou 310030, China.
Environ Sci Technol. 2025 Sep 9;59(35):18990-19001. doi: 10.1021/acs.est.5c03819. Epub 2025 Aug 28.
Chlorinated polyfluoroalkyl substances (Cl-PFAS) are increasingly detected in contaminated environments, and the relative ease of C-Cl cleavage offers opportunities for defluorination. Herein, we demonstrated, for the first time, the dechlorination of Cl-PFAS by nanoscale zerovalent iron (nZVI), and we revealed that such dechlorination can induce indirect defluorination when Cl is substituted at the middle of the perfluorocarbon chain. The carbanion (-CF-CF-), generated via two successive single-electron transfer steps, is the key intermediate enabling defluorination through β-elimination of F to form alkenyl products (-CF═CF-). The extent of defluorination was governed by the competitive reactivity with proton abstraction of carbanion to form hydrogenolysis products (-HCF-CF-). Through this novel pathway, an indirect defluorination of up to 25.3% was achieved for the investigated polychlorofluorocarboxylic acids within 120 h using nZVI. The reactivity for dechlorination at varying positions and subsequent β-elimination of F can be theoretically described using dissociative electron transfer and transition state theories, respectively. The lack of defluorination in ωCl-PFAS was attributed to the much higher activation energy required for β-elimination from the carbanion (CF-CF-) compared with proton abstraction. The alignment of theoretical calculations with experimental results provides a theoretical framework to predict dechlorination and defluorination reactivity of Cl-PFAS, facilitating the design of rapidly degradable alternatives.
在受污染的环境中,越来越多地检测到氯化多氟烷基物质(Cl-PFAS),而C-Cl键相对容易断裂为脱氟提供了机会。在此,我们首次证明了纳米零价铁(nZVI)对Cl-PFAS的脱氯作用,并且我们发现当Cl取代在全氟碳链的中间位置时,这种脱氯作用可诱导间接脱氟。通过两个连续的单电子转移步骤生成的碳负离子(-CF-CF-)是通过β消除F形成烯基产物(-CF═CF-)从而实现脱氟的关键中间体。脱氟程度受碳负离子与质子夺取反应形成氢解产物(-HCF-CF-)的竞争反应性控制。通过这条新途径,使用nZVI在120小时内对所研究的多氯氟羧酸实现了高达25.3%的间接脱氟。不同位置的脱氯反应性以及随后的F的β消除反应性,理论上可分别用离解电子转移理论和过渡态理论来描述。ω-Cl-PFAS中缺乏脱氟作用归因于与质子夺取相比,从碳负离子(CF-CF-)进行β消除所需的活化能要高得多。理论计算与实验结果的吻合提供了一个预测Cl-PFAS脱氯和脱氟反应性的理论框架,有助于设计快速降解的替代物。