State Key Laboratory of Urban Water Resource and Environment, School of Environment , Harbin Institute of Technology , Harbin 150090 , China.
School of Municipal and Environmental Engineering , Jilin Jianzhu University , Changchun 130118 , China.
Environ Sci Technol. 2018 Oct 2;52(19):11276-11284. doi: 10.1021/acs.est.8b02266. Epub 2018 Sep 12.
It is well documented that the traditional Fenton reagent (i.e., the combination of Fe(II) and HO) produces hydroxyl radical (OH) under acidic conditions, while at near-neutral pH the reactive intermediate converts to ferryl ion (Fe(IV)) that can oxidize sulfoxides to produce corresponding sulfones, markedly differing from their OH-induced products. However, it remains unclear whether Fe(IV) is generated in the Fe(II) activated peroxydisulfate (PDS) process, where sulfate radical (SO) is long recognized as the dominant intermediate in literature. Here we demonstrated that SO oxidized methyl phenyl sulfoxide (PMSO, a model sulfoxide) to produce biphenyl compounds rather than methyl phenyl sulfone (PMSO). Interestingly, the formation of PMSO was observed when PMSO was treated by the Fe(II)/PDS system over a wide pH range, and the yields of PMSO were quantified to be ∼100% at acidic pH 3-5. The identification of Fe(IV) in the Fe(II)/PDS system could also reasonably explain the literature results on alcohol scavenging effect and ESR spectra analysis. Further, a Fe(IV)-based kinetic model was shown to accurately simulate the experimental data. This work urges re-evaluation of the Fe(II)/PDS system for environmental decontamination, given that Fe(IV) would have different reactivity toward environmental contaminants compared with SO and/or OH.
有大量文献记载,传统的芬顿试剂(即 Fe(II) 和 HO 的组合)在酸性条件下产生羟基自由基 (OH),而在近中性 pH 下,反应中间体转化为高氧离子 (Fe(IV)),可将亚砜氧化为相应的砜,与它们的 OH 诱导产物明显不同。然而,目前尚不清楚在 Fe(II) 激活过二硫酸盐 (PDS) 过程中是否会生成 Fe(IV),文献中一直认为硫酸根自由基 (SO) 是该过程中的主要中间体。在这里,我们证明了 SO 会将甲基苯基亚砜 (PMSO,一种亚砜模型) 氧化为联苯化合物,而不是甲基苯砜 (PMSO)。有趣的是,当 PMSO 被 Fe(II)/PDS 体系处理时,在很宽的 pH 范围内都观察到了 PMSO 的形成,并且在酸性 pH 3-5 时 PMSO 的产率约为 100%。在 Fe(II)/PDS 体系中鉴定出的 Fe(IV) 也可以合理地解释关于醇清除效应和 ESR 谱分析的文献结果。此外,基于 Fe(IV)的动力学模型被证明可以准确模拟实验数据。鉴于 Fe(IV)与 SO 和/或 OH 相比对环境污染物具有不同的反应性,因此需要重新评估 Fe(II)/PDS 体系在环境去污方面的应用。