4.2 Article

Nonradical Activation of Peroxydisulfate with In Situ Generated Amorphous MnO2 in an Electro-Permanganate Process: Involvement of Singlet Oxygen, Electron Transfer, and Mn(III)aq

期刊

ACS ES&T ENGINEERING
卷 2, 期 7, 页码 1316-1325

出版社

AMER CHEMICAL SOC
DOI: 10.1021/acsestengg.1c00464

关键词

peroxydisulfate; manganese dioxide; nonradical activation; reactive manganese; electrochemical water treatment

资金

  1. National Natural Science Foundation of China [22076015]
  2. Chongqing Natural Science Foundation Project [cstc2019jcyj-msxmX0463]
  3. Central University Basic Research Fund [2019CDXYCH0027]
  4. 111 Project [B13041]

向作者/读者索取更多资源

A novel water treatment process based on the combination of electrolysis with permanganate and peroxydisulfate was investigated, and the combination showed significant synergistic effects in degrading refractory organics. The process could efficiently mineralize diclofenac with low energy consumption. The mechanism study revealed the role of electricity in activating peroxydisulfate and generating reactive species for organic degradation.
ABSTRACT: A novel water treatment process based on a combination of electrolysis (E) with permanganate (PM) and peroxydisulfate (PDS) was systematically investigated. The combination exhibited significant synergy in degrading refractory organics such as diclofenac (DCF), carbamazepine, and nitrobenzene. In comparison to E-PDS (20.45%, 12.448 kWh m-3) and E-PM (36.36%, 5.200 kWh m-3) processes, the E-PM-PDS process could mineralize 70.45% DCF within 180 min with the lowest specific energy consumption (1.007 kWh m-3). The mechanism study revealed that electricity could significantly promote the activation of PDS with the in situ generated amorphous MnO2 via nonradical pathways (1O2 oxidation and electron transfer), and the activated PDS, in turn, facilitated Mn(II)aq to generate reactive Mn(III)aq. In the E-PM-PDS process, DCF degradation was enhanced upon increasing PM dosage, PDS dosage, and current density, and also by decreasing the pH. Cations facilitated the DCF degradation with the order of positive effects as Fe3+ > Zn2+ > Ca2+ > Mg2+. The presence of humic acid (HA) significantly enhanced the DCF degradation, while the addition of HCO3- or HPO42- caused adverse effects. This work may provide a high-efficiency and low-cost technology for water treatment.

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