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Electrooxidation of short and long chain perfluorocarboxylic acids using boron doped diamond electrodes

机译:使用硼掺杂金刚石电极的短链和长链全氟羧酸的电氧化

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This study investigates electrooxidation of short (C3-C6) and long (C7-C-18) chain perfluorocarboxylic acids (PFCAs) including perfluorooctane sulfonate (PFOA) using Si/BDD electrode. The effect of operational parameters (supporting electrolyte type, applied current density, and initial pH) were explored for PFOA removal. At the optimized conditions, 74% TOC removal and 37% defluorination ratio were gained for 10 mg L-1 of PFOA solution which evidences that the shorter chain PFCA5 were formed. The PFOA degradation pathway followed one direct electron transfer from PFOA molecule to anode surface. Then two different degradation pathways were proposed. The first proposed degradation mechanism involved the reaction of perfluoroheptyl radical and hydroxyl radical, the release of HF and hydrolysis. The second mechanism involved the reaction between perfluoroheptyl radical and O-2, formation of C7F15O center dot and perfluorohexyl radical with releasing COF2. The removal of short- (C3-C6) and long-chain PFCAs (C7-C18) was also characterized. More than 95% of removal efficiency was gained for all long-chain PFCA5, excluding C7. The removal ratios of short-chain PFCAs (C3-C6) were 39%, 41%, 66% and 70% for C3, C4, C5 and C6, respectively. Contrary to long-chain PFCA5, chain-length dependence for short-chain PFCAs were observed. Defluorination ratio of short-chain PFCAs was only 45% signifying that defluorination partially occurred. Water matrix did not significantly affect the degradation of short-chain PFCA5 in deionized water (Dl), river water and secondary effluent of a wastewater treatment plant (WWTP). In contrast, defluorination ratio of long-chain PFCA5 was noticeably affected by water matrix with the order of DI water INWTP effluent river water. Published by Elsevier Ltd.
机译:本研究研究了使用Si / Bdd电极的全氟辛丁烷(PFOA)的短(C3-C6)和长(C7-C-18)链全氟羧酸(PFCAs)的电氧化。探索了操作参数(支撑电解质型,施加电流密度和初始pH)的效果用于PFOA去除。在优化的条件下,获得了74%的TOC去除和37%的渗透率,得到10mg L-1的PFOA溶液,证明形成较短的链PFCA5。 PFOA降解途径遵循从PFOA分子到阳极表面的一个直接电子转移。然后提出了两种不同的降解途径。第一个提出的降解机制涉及全氟肺肝自由基和羟基的反应,HF和水解的释放。第二种机制涉及全氟哌肺岩自由基和O-2之间的反应,形成C7F15O中心点和全氟己基的释放COF2。还表征了去除短(C3-C6)和长链PFCA(C7-C18)。所有长链PFCA5都获得了超过95%的去除效率,不包括C7。短链PFCAs(C3-C6)的去除比分别为C3,C4,C5和C6的39%,41%,66%和70%。与长链PFCA5相反,观察到短链PFCA的链长依赖性。短链PFCA的偏氟量仅为45%,表示偏氟部分部分发生。水基质没有显着影响去离子水(DL),河水和废水处理厂(WWTP)的河水和二级流出物中的短链PFCA5的降解。相反,长链PFCA5的偏氟比与水基质的偏滤比具有DI水分> INWTP流出物>河水。 elsevier有限公司出版

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