Miao Zhouwei, Gu Xiaogang, Lu Shuguang, Brusseau Mark L, Zhang Xiang, Fu Xiaori, Danish Muhammad, Qiu Zhaofu, Sui Qian
State Environmental Protection Key Laboratory of Environmental Risk Assessment and Control on Chemical Process, East China University of Science and Technology, Shanghai 200237, China ; Soil, Water and Environmental Science Department, School of Earth and Environmental Sciences, The University of Arizona, 429 Shantz Bldg., Tucson, AZ 85721.
State Environmental Protection Key Laboratory of Environmental Risk Assessment and Control on Chemical Process, East China University of Science and Technology, Shanghai 200237, China.
Chem Eng J. 2015 Dec 1;281:286-294. doi: 10.1016/j.cej.2015.06.076. Epub 2015 Jun 23.
The performance of Fe(III)-based catalyzed sodium percarbonate (SPC) for stimulating the oxidation of tetrachloroethene (PCE) for groundwater remediation applications was investigated. The chelating agents citric acid monohydrate (CIT), oxalic acid (OA), and Glutamic acid (Glu) significantly enhanced the degradation of PCE. Conversely, ethylenediaminetetraacetic acid (EDTA) had a negative impact on PCE degradation, which may due to its strong Fe chelation and HO scavenging abilities. However, excessive SPC or chelating agent will retard PCE degradation. In addition, investigations using free radical probe compounds and radical scavengers revealed that PCE was primarily degraded by HO radical oxidation in both the chelated and non-chelated systems, while O also participated in the non-chelated system and the OA and Glu modified systems. According to the electron paramagnetic resonance (EPR) studies, the presence of HO in the Fe(III)/SPC system was maintained much longer than that in the Fe(II)/SPC system. The results indicated that the addition of CIT, OA or Glu indeed enhanced the generation of HO in the first 10 min and promoted degradation efficiency by increasing the amount of Fe(III) and maintaining the concentration of HO radicals in solution. In conclusion, chelated Fe(III)-based catalyzed SPC oxidation is a promising method for the remediation of PCE-contaminated groundwater.
研究了基于铁(III)催化的过碳酸钠(SPC)在地下水修复应用中刺激四氯乙烯(PCE)氧化的性能。螯合剂一水柠檬酸(CIT)、草酸(OA)和谷氨酸(Glu)显著增强了PCE的降解。相反,乙二胺四乙酸(EDTA)对PCE降解有负面影响,这可能是由于其强大的铁螯合能力和羟基自由基清除能力。然而,过量的SPC或螯合剂会阻碍PCE的降解。此外,使用自由基探针化合物和自由基清除剂的研究表明,在螯合和非螯合体系中,PCE主要通过羟基自由基氧化降解,而超氧阴离子也参与了非螯合体系以及OA和Glu改性体系。根据电子顺磁共振(EPR)研究,铁(III)/SPC体系中羟基自由基的存在时间比铁(II)/SPC体系中长得多。结果表明,添加CIT、OA或Glu确实在最初10分钟内增强了羟基自由基的生成,并通过增加铁(III)的量和维持溶液中羟基自由基的浓度提高了降解效率。总之,基于螯合铁(III)催化的SPC氧化是修复受PCE污染地下水的一种有前景的方法。