Key Laboratory of Industrial Ecology and Environmental Engineering (Ministry of Education, China), School of Environmental Science and Technology, Dalian University of Technology , Dalian 116024, China.
Environ Sci Technol. 2015 Nov 17;49(22):13528-33. doi: 10.1021/acs.est.5b03147. Epub 2015 Oct 27.
Perfluorochemicals are environmentally persistent, bioaccumulative, and globally distributed contaminants, which present potential toxicity to both humans and ecosystems. However, rapid mineralization of perfluorochemicals with cost-effective method remains great challenges. Here, an electro-Fenton system was reported for efficient mineralization of perfluorooctanoate (PFOA), where H2O2 was electro-generated in situ from O2 reduction on hierarchically porous carbon (HPC). Benefited from the high H2O2 production rate (41.2-14.0 mM/h) of HPC, PFOA (50 mg/L) was rapidly degraded by electro-Fenton with first-order kinetic constants of 1.15-0.69 h(-1) at low potential (-0.4 V) in a wide range of pH (2-6). Meanwhile, PFOA was effectively mineralized, as revealed by a total organic carbon removal efficiency of 90.7-70.4% (-0.4 V, pH 2-6, 4 h). Moreover, the current efficiency of this electro-Fenton system for PFOA degradation was 1 order of magnitude higher than those of electrochemical oxidation. On the basis of the intermediate analysis, we proposed a possible mechanism for PFOA degradation: PFOA lost one electron to the anode and got decarboxylated. The formed perfluoroalkyl radical was mainly oxidized by hydroxyl radical, resulting in the formation of shorter chain perfluorocarboxylic acid, which followed the same reaction cycle as PFOA until it was mineralized.
全氟化学品是一种在环境中持久存在、具有生物累积性且分布广泛的污染物,它们对人类和生态系统都存在潜在的毒性。然而,用具有成本效益的方法实现全氟化学品的快速矿化仍然是一个巨大的挑战。本研究中,构建了一种电芬顿体系,用于高效矿化全氟辛烷酸(PFOA),其中 H2O2 是通过在分级多孔碳(HPC)上氧气还原原位生成的。得益于 HPC 较高的 H2O2 生成速率(41.2-14.0 mM/h),在很宽的 pH 值范围(2-6)下,在低电位(-0.4 V)下,PFOA(50 mg/L)能够快速降解,一级动力学常数为 1.15-0.69 h(-1)。同时,PFOA 被有效矿化,总有机碳去除效率为 90.7-70.4%(-0.4 V,pH 2-6,4 h)。此外,该电芬顿体系用于 PFOA 降解的电流效率比电化学氧化高 1 个数量级。基于中间产物分析,提出了一种可能的 PFOA 降解机制:PFOA 向阳极失去一个电子并发生脱羧。形成的全氟烷基自由基主要被羟基自由基氧化,生成较短链的全氟羧酸,遵循与 PFOA 相同的反应循环,直到其被矿化。