Sulfite activation of Fe-Mn bimetallic oxides for rapid oxidative removal of As(III) in water: Involvement of active Mn(III)

被引:13
作者
Cai, Guiyuan [1 ,2 ]
Tian, Yu [1 ]
Li, Lipin [1 ]
Zhang, Wenxuan [3 ,4 ]
Huang, Rui [3 ,4 ]
Zhang, Jun [1 ]
Wang, Qinyu [1 ]
Xu, Hua [1 ]
Zhang, Yifeng [2 ]
机构
[1] Harbin Inst Technol, Sch Environm SKLUWRE, State Key Lab Urban Water Resource & Environm, Harbin 150090, Peoples R China
[2] Tech Univ Denmark, Dept Environm & Resource Engn, DK-2800 Kongens Lyngby, Denmark
[3] Harbin Inst Technol, Natl Engn Res Ctr Urban Water Resources Co Ltd, Harbin 150090, Peoples R China
[4] Guangdong Yuehai Water Investment Co Ltd, Shenzhen 518021, Peoples R China
基金
中国国家自然科学基金;
关键词
As(III); Fe -Mn bimetallic oxides; Sulfite; active Mn(III); Oxidation; ORGANIC CONTAMINANTS; CATALYZED OXIDATION; ENHANCED OXIDATION; EFFICIENT REMOVAL; HYDROGEN-PEROXIDE; ARSENIC(III); DEGRADATION; ADSORPTION; MECHANISM; BEHAVIOR;
D O I
10.1016/j.cej.2023.147539
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
The activation of sulfite [S(IV)] by transition metals, a new generation of advanced oxidation processes, has been widely studied for water purification. However, the application of this process to oxidize and remove arsenite [As (III)] from water through Fe-based S(IV) activation and the associated mechanisms are not fully understood. In particular, rapid removal of As(III) and secondary metal contamination have presented challenges. Herein, we develop a novel sea urchin-like magnetic Fe-Mn bimetallic oxides (FeMnO)-activated S(IV) process to address these issues. Under neutral pH, the FeMnO/S(IV) system achieved a 99.2 % removal of As(III) within only 10 min with residual arsenic concentration below 10 mu g/L, and the removed As(III) was fully oxidized to arsenate [As (V)]. Additionally, FeMnO was recyclable and capable of treating actual arsenic-contaminated water. Further-more, the oxidation mechanism of non-radical active trivalent manganese [Mn(III)] was discovered during the reaction between the FeMnO/S(IV) system and As(III). The FeMnO catalyst activated S(IV) to generate oxysulfur radicals (i.e., SO5 center dot-, SO4 center dot- and SO3 center dot-), but they were not the primary oxidizing species for As(III). Instead, As(III) oxidation was mainly attributed to the active Mn(III) generated by the electron transfer between the FeMnO catalyst and SO5 center dot- radicals. The discovery of active Mn(III) species in this work may provide a new avenue for developing novel Fe-Mn-type adsorbents to purify arsenic-contaminated water.
引用
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页数:10
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