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纳米零价铁负载氧化铜/过硫酸盐体系快速降解莠去津:活性物种的再评估与定量、生成途径及应用可行性。

Fast degradation of atrazine by nZVI-Cu/PMS: Re-evaluation and quantification of reactive species, generation pathways, and application feasibility.

机构信息

School of Water Conservancy and Civil Engineering, Northeast Agricultural University, Harbin 150030, China.

School of Water Conservancy and Civil Engineering, Northeast Agricultural University, Harbin 150030, China.

出版信息

Water Res. 2023 Sep 1;243:120311. doi: 10.1016/j.watres.2023.120311. Epub 2023 Jul 4.

Abstract

Additive metal to zero-valent iron (ZVI) could enhance the reduction ability and the additive Cu was incorporated to ZVI to accelerate PMS activation with atrazine (ATZ) as target compound. The efficiencies of ATZ degradation and PMS decomposition climbed up firstly and then declined as Cu loading increased from 0.01 to 1.00 wt% with the maximums at 0.10 wt%. SO, HO, Fe(IV), O and O were generated by nZVI-Cu/PMS based on the results of electron paramagnetic resonance (EPR) and simultaneous degradation of nitrobenzene, ATZ, and methyl phenyl sulfoxide (PMSO). The rate constant of Fe(IV) and ATZ was estimated as 7 × 10 M∙s via the variation of methyl phenyl sulfone (PMSO)formation at different ATZ concentrations. However, Fe(IV) contributed negligibly to ATZ degradation due to the strong scavenging of Fe(IV) by PMS. SO and HO were the reactive species responsible for ATZ degradation and the yield ratio of SO and HO was about 8.70 at initial stage. Preliminary thermodynamic calculation on the possible activation ways revealed that the dominant production of SO might originate from the atomic H reduction of PMS in the surface layer of nZVI-Cu. Ten products of ATZ degradation were identified by HPLC/ESI/QTOF and the possible degradation pathways were analyzed combined with theoretical calculation on ATZ structure. The decrease of temperature or increase of solution pH led to the decline of ATZ degradation, as well as the individual addition of common ions (HCO, Cl, SO, NH, NO and F) and natural organic matters (NOM). In real water, ATZ was still efficiently degraded with the decontamination efficiency decreasing in the sequence of tap water > surface water > simulated wastewater > groundwater. For the treatment of ATZ-polluted continuous flow, nZVI-Cu in double-layer layout had a higher capacity than the single-layer mode. Meanwhile, the leaching TFe and TCu were limited. The results indicate nZVI-Cu/PMS is applicable and the multiple-layer layout of nZVI-Cu is suggested for ATZ-polluted ground water and soil remediation.

摘要

添加金属零价铁(ZVI)可以增强还原能力,并且添加铜以加速过一硫酸盐(PMS)与莠去津(ATZ)作为目标化合物的激活。随着铜负载量从 0.01 增加到 1.00wt%,ATZ 的降解效率和 PMS 的分解效率先增加后减少,最大值在 0.10wt%。因此,基于电子顺磁共振(EPR)的结果,nZVI-Cu/PMS 生成了·SO、·HO、Fe(IV)、O 和 O。硝基苯、ATZ 和甲基苯基亚砜(PMSO)的同时降解表明。通过不同 ATZ 浓度下 PMSO 形成的变化,估计 Fe(IV)和 ATZ 的速率常数为 7×10 M·s。然而,由于 PMS 对 Fe(IV)的强烈清除,Fe(IV)对 ATZ 降解的贡献可以忽略不计。SO 和 HO 是负责 ATZ 降解的活性物质,在初始阶段,SO 和 HO 的产率比约为 8.70。对可能的活化方式进行初步热力学计算表明,表面层原子 H 还原 PMS 可能是 SO 主要产生的原因。通过 HPLC/ESI/QTOF 鉴定了 ATZ 降解的 10 种产物,并结合 ATZ 结构的理论计算分析了可能的降解途径。温度降低或溶液 pH 值升高都会导致 ATZ 降解下降,以及常见离子(HCO、Cl、SO、NH、NO 和 F)和天然有机物(NOM)的单独添加。在实际水中,ATZ 仍能有效降解,去除效率依次为自来水>地表水>模拟废水>地下水。对于 ATZ 污染的连续流处理,双层布局的 nZVI-Cu 比单层模式具有更高的容量。同时,浸出的 TFe 和 TCu 受到限制。结果表明,nZVI-Cu/PMS 是适用的,建议对 ATZ 污染的地下水和土壤修复采用多层布局的 nZVI-Cu。

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