全氟辛酸
化学
电化学
矿化(土壤科学)
环境化学
降级(电信)
分解
反应机理
无机化学
催化作用
电极
有机化学
物理化学
电信
计算机科学
氮气
作者
Meng Li,Peitong Cen,Lei Huang,Yan Jia,Shaoqi Zhou,King Lun Yeung,Ce-Hui Mo,Hongguo Zhang
标识
DOI:10.1016/j.jhazmat.2024.134155
摘要
Iron complex regulated electrochemical reaction was triggered for revealing the reaction mechanism, degradation pathway, and applied potential of perfluorooctanoic acid (PFOA). The increased PMS concentrations, electrode spacing, and current density significantly enhanced PFOA elimination, with current density exhibiting a relatively strong interdependency to PFOA complete mineralization. The synergy between PMS and electrochemical reactions greatly accelerated PFOA decomposition by promoting the generation of key reaction sites, such as those for PMS activation and electrochemical processes, under various conditions. Furthermore, density functional theory calculations confirmed that the reciprocal transformation of Fe2+ and Fe3+ complexes was feasible under the electrochemical effect, further promoting the generation of active sites. The developed electrochemical oxidation with PMS reaction (EO/PMS) system can rapidly decompose and mineralize PFOA while maintaining strong tolerance to changing water matrices and organic and inorganic ions. Overall, it holds promise for use in treating and purifying wastewater containing PFOA. Perfluorooctanoic acid (PFOA) as a persistent organic pollutant, has been widely detected globally in surface water, groundwater or waste leachate from ng L−1 to μg L−1. Its persistence and stability in waterbody can cause severe toxicity for humans, including mutagenicity, immunotoxicity, carcinogenicity, and hepatotoxicity. The developed electrochemical oxidation with PMS reaction system in our study can rapidly decompose and mineralize PFOA while maintaining strong tolerance to changing water matrices and organic and inorganic ions. The corresponding removal performance, reaction mechanism, degradation pathway, and toxicity assessment of PFOA were comprehensively conducted in our study.
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