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

被引:24
|
作者
Zhu, Ying [1 ,2 ]
Ding, Haojie [4 ]
Fan, Jiahui [1 ,2 ]
Liu, Shuan [5 ]
Song, Yunqian [1 ,2 ]
Deng, Huiping [5 ]
Zhao, Chun [1 ,2 ]
Dionysiou, Dionysios D. [3 ]
机构
[1] Chongqing Univ, Key Lab Three Gorges Reservoir Reg Ecoenvironm, Minist Educ, Chongqing 400045, Peoples R China
[2] Chongqing Univ, Joint Lab Int Cooperat Low Carbon & Green Bldg, Minist Educ, Chongqing 400045, Peoples R China
[3] Univ Cincinnati, Dept Chem & Environm Engn, Cincinnati, OH 45221 USA
[4] Tsinghua Univ, Sch Environm, State Key Joint Lab Envirornment Simulat & Pollut, PeopleRepubl China, Beijing 100084, Peoples R China
[5] Tongji Univ, Coll Environm Sci & Engn, Shanghai 200092, Peoples R China
来源
ACS ES&T ENGINEERING | 2022年 / 2卷 / 07期
基金
中国国家自然科学基金;
关键词
peroxydisulfate; manganese dioxide; nonradical activation; reactive manganese; electrochemical water treatment; INDUSTRIAL WASTE-WATER; BISPHENOL-A; PERSULFATE ACTIVATION; ORGANIC CONTAMINANTS; RADICAL GENERATION; OXIDATION; DEGRADATION; PEROXYMONOSULFATE; MECHANISM; EFFICIENCY;
D O I
10.1021/acsestengg.1c00464
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
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.
引用
收藏
页码:1316 / 1325
页数:10
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