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Peroxymonosulfate activation by iron(Ⅲ)-tetraamidomacrocyclic ligand for degradation of organic pollutants via high-valent iron-oxo complex

机译:铁(Ⅲ)-四酰胺基大环配体活化过硫酸单硫酸盐通过高价铁-氧配合物降解有机污染物

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Herein, we proposed a new catalytic oxidation system, i.e., iron(III)-tetraamidomacrocyclic ligand (Fem(III)-TAML) mediated activation of peroxymonosulfate (PMS), for highly efficient organic degradation using pchlorophenol (4-CP) as a model one. PMS/Fem(III)-TAML is capable of degrading 4-CP completely in 9 min at the initial 4-CP of 50 mu M and pH = 7, whereas the recently explored system, H2O2/Fem(III)-TAML, could only result in similar to 22% 4-CP removal in 20 min under otherwise identical conditions. More attractively, inorganic anions (i.e.,cl(-), SO42- , NO3-, and HCO3-) exhibited insignificant effect on 4-CP degradation, and the negative effect of natural organic matters (NOM) on the degradation of 4-CP in PMS/Fe-III-TAML is much weaker than the sulfate radical-based oxidation process (PMS/Co2+). Combined with in-situ XANES spectra, UV-visible spectra, electron paramagnetic resonance (EPR) spectra, and radical quenching experiments, high-valent iron-oxo complex (Fe-Iv(O)TAML) instead of singlet oxygen (O-1(2)), superoxide radical (O-2(center dot-)), sulfate radicals (SO4 center dot-) and hydroxyl radicals (HO center dot-) was the key active species responsible for 4-CP degradation. The formation rate (k(I)) and consumption rate (k(II)) of the Fe-Iv(O)TAML in PMS/Fem(III)-TAML were pH-dependent in the range of 6.0-11.5. As expected, increasing the Fem(III)-TAML and PMS dosage resulted in a higher steady-state concentration of Fe-Iv(O)TAML and enhanced the 4-CP degradation accordingly. In addition, the oxidation capacity of PMS was almost totally utilized in PMS/Fem(III)-TAML for 4-CP oxidation due to the two-electron abstraction from 4-CP by one PMS. We believe this study will shed new light on effective PMS activation by Fe-ligand complexes to efficiently degrade organic contaminants via nonradical pathway. (C) 2018 Elsevier Ltd. All rights reserved.
机译:在这里,我们提出了一种新的催化氧化系统,即铁(III)-四酰胺基大环配体(Fem(III)-TAML)介导的过氧单硫酸盐(PMS)的活化,以使用对氯苯酚(4-CP)为模型进行高效有机降解一。 PMS / Fem(III)-TAML能够在最初的4-CP 50μM和pH = 7的情况下,在9分钟内完全降解4-CP,而最近开发的H2O2 / Fem(III)-TAML体系可以在其他条件相同的情况下,仅在20分钟内可导致22%的4-CP去除率相似。更具吸引力的是,无机阴离子(例如,cl(-),SO42-,NO3-和HCO3-)对4-CP的降解作用不明显,而天然有机物(NOM)对4-CP的降解则有负面影响在PMS / Fe-III-TAML中,它比基于硫酸根的氧化过程(PMS / Co2 +)弱得多。结合原位XANES光谱,UV-可见光谱,电子顺磁共振(EPR)光谱和自由基猝灭实验,用高价铁-氧配合物(Fe-Iv(O)TAML)代替单重态氧(O-1 (2)),超氧自由基(O-2(中心点)),硫酸根(SO4中心点)和羟基(HO中心点)是导致4-CP降解的关键活性物质。 PMS / Fem(III)-TAML中Fe-Iv(O)TAML的形成率(k(I))和消耗率(k(II))在6.0-11.5范围内与pH有关。如预期的那样,增加Fem(III)-TAML和PMS剂量会导致更高的Fe-Iv(O)TAML稳态浓度并相应地增强4-CP降解。此外,由于一个PMS从4-CP提取出两个电子,PMS / Fem(III)-TAML中的PMS氧化能力几乎全部用于4-CP氧化。我们相信这项研究将为铁配体络合物有效激活PMS从而通过非自由基途径有效降解有机污染物提供新的思路。 (C)2018 Elsevier Ltd.保留所有权利。

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