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同步还原-氧化法高效去除三氯乙酸:H*引发脱氯反应,·OH 负责去除效率。

Synchronous Reduction-Oxidation Process for Efficient Removal of Trichloroacetic Acid: H* Initiates Dechlorination and ·OH Is Responsible for Removal Efficiency.

机构信息

Center for Water and Ecology, State Key Joint Laboratory of Environment Simulation and Pollution Control, School of Environment , Tsinghua University , Beijing 100084 , China.

Key Laboratory of Drinking Water Science and Technology , Research Center for Eco-Environmental Sciences, Chinese Academy of Sciences , Beijing 100085 , China.

出版信息

Environ Sci Technol. 2019 Dec 17;53(24):14586-14594. doi: 10.1021/acs.est.9b05389. Epub 2019 Dec 6.

Abstract

Degradation of chlorinated disinfection by-products using the electroreduction process has been considered as a promising approach for advanced water treatment, while the removal efficiency is restricted by a high barrier for dechlorination of intermediates only by reductive atomic hydrogen (H*) and excessive cost required for reducing atmosphere. In this paper, we predict that the dechlorination efficiency for trichloroacetic acid (TCA), a typical chlorinated disinfection by-product, can be accelerated via a synchronous reduction-oxidation process, where the dechlorination barrier can be lowered by the oxidation reactions toward the critical intermediates using hydroxyl radicals (·OH). Based on scientific findings, we constructed a synchronous reduction-oxidation platform using a Pd-loaded Cu/CuO/CuO array as the core component. According to the combined results of theoretical and experimental analyses, we found that the high dispersion of nano-sized Pd on a photocathode was beneficial for the production of a high concentration of H* at low overpotential, a perquisite for initiating the dechlorination reaction. Simultaneously, excess H* has the potential to convert O to HO in ambient conditions (air condition), and HO can be further activated by a Cu-containing substrate to ·OH for attacking the critical intermediates. In this system, ∼89.1% of TCA was completely dechlorinated and ∼26.8% mineralization was achieved in 60 min, which was in contrast to the value of ∼65.7% and mineralization efficiency of only ∼1.7% achieved through the reduction process (Ar condition).

摘要

使用电化学还原法降解氯化消毒副产物已被认为是一种很有前途的高级水处理方法,但由于还原原子氢(H*)只能使中间产物脱氯的势垒较高,以及还原气氛所需的成本过高,其去除效率受到限制。在本文中,我们预测三氯乙酸(TCA),一种典型的氯化消毒副产物,其脱氯效率可以通过同步还原-氧化过程来加速,其中通过·OH 对关键中间产物的氧化反应可以降低脱氯势垒。基于科学发现,我们构建了一个同步还原-氧化平台,该平台以负载 Pd 的 Cu/CuO/CuO 阵列为核心组件。根据理论和实验分析的综合结果,我们发现,纳米级 Pd 在光阴极上的高分散度有利于在低过电势下产生高浓度的 H*,这是引发脱氯反应的前提条件。同时,过量的 H*有潜力将 O 转化为 HO 在环境条件(空气条件)下,并且 HO 可以被含 Cu 的基底进一步激活为·OH 来攻击关键中间产物。在这个系统中,TCA 被完全脱氯,60 分钟内的矿化率约为 26.8%,而在还原过程(Ar 条件)下,TCA 的脱氯率约为 65.7%,矿化效率仅约为 1.7%。

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