Department of Civil and Environmental Engineering, University of California, Los Angeles, California 90095-153, United States.
Department of Civil and Environmental Engineering, University of Iowa, Iowa City, Iowa 52242, United States.
Environ Sci Technol. 2020 Sep 1;54(17):10668-10677. doi: 10.1021/acs.est.0c02773. Epub 2020 Aug 18.
Per and polyfluoroalkyl substances (PFAS), legacy chemicals used in firefighting and the manufacturing of many industrial and consumer goods, are widely found in groundwater resources, along with other regulated compounds, such as chlorinated solvents. Due to their strong C-F bonds, these molecules are extremely recalcitrant, requiring advanced treatment methods for effective remediation, with hydrated electrons shown to be able to defluorinated these compounds. A combined photo/electrochemical method has been demonstrated to dramatically increase defluorination rates, where PFAS molecules sorbed onto appropriately functionalized cathodes charged to low cell potentials (-0.58 V vs Ag/AgCl) undergo a transient electron transfer event from the electrode, which "primes" the molecule by reducing the C-F bond strength and enables the bond's dissociation upon the absorption of a hydrated electron. In this work, we explore the impact of headgroup and chain length on the performance of this two-electron process and extend this technique to chlorinated solvents. We use isotopically labeled PFAS molecules to take advantage of the kinetic isotope effect and demonstrate that indeed PFAS defluorination is likely driven by a two-electron process. We also present density functional theory calculations to illustrate that the externally applied potential resulted in an increased rate of electron transfer, which ultimately increased the measured defluorination rate.
全氟和多氟烷基物质(PFAS)是一种在消防和许多工业及消费品制造中使用的传统化学物质,广泛存在于地下水资源中,还有其他受管制的化合物,如氯化溶剂。由于它们的强 C-F 键,这些分子极难降解,需要先进的处理方法才能有效修复,而水合电子被证明能够对这些化合物进行脱氟。已经证明,光电化学联合方法可以显著提高脱氟速率,其中吸附在适当功能化阴极上的 PFAS 分子在低电池电势(-0.58 V 对 Ag/AgCl)下充电,会从电极发生瞬时电子转移事件,通过还原 C-F 键强度来“引发”分子,并在吸收水合电子后使键解离。在这项工作中,我们探讨了官能团和链长对这两个电子过程性能的影响,并将该技术扩展到氯化溶剂。我们使用同位素标记的 PFAS 分子利用动力学同位素效应,并证明 PFAS 的脱氟确实可能由两个电子过程驱动。我们还提出了密度泛函理论计算,说明外加电势导致了电子转移速率的增加,最终提高了测量的脱氟速率。