Rapid abiotic As removal from As-rich acid mine drainage: Effect of pH, Fe/As molar ratio, oxygen, temperature, initial As concentration and neutralization reagent

被引:24
作者
Yuan, Zidan [1 ]
Zhang, Guoqing [1 ]
Ma, Xu [1 ]
Yu, Le [2 ]
Wang, Xin [1 ]
Wang, Shaofeng [1 ]
Jia, Yongfeng [1 ]
机构
[1] Chinese Acad Sci, Inst Appl Ecol, Key Lab Pollut Ecol & Environm Engn, Shenyang 110016, Liaoning, Peoples R China
[2] Northern Heavy Ind Grp Co Ltd, Shenyang 110141, Liaoning, Peoples R China
关键词
As-rich AMD; Oxidation; Fenton-like reaction; Speciation; Fe-As (co)-precipitate; Removal efficiency; HYDROGEN-PEROXIDE; CATALYZED OXIDATION; ADSORBED ARSENATE; FERRIC ARSENATE; IRON; TOOELEITE; FENTON; AS(III); ARSENIC(III); FERRIHYDRITE;
D O I
10.1016/j.cej.2019.122156
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Oxygen-induced abio-oxidation of Fe(II) and As(III) for Fe-As co-precipitation is proposed in this work as a cost-saving and time-saving method to remove As from As-rich acid mine drainage (AMD). The effect of pH, Fe/As molar ratio, oxygen flow rate, temperature, initial As concentration and neutralization reagent on As removal was investigated. The results showed that As removal efficiency was strongly controlled by pH, which increased from 33.0% to 96.2% as increasing pH from 2 to 7 after 12 h-reactions. pH was also very important to As(III) oxidation. The oxidation degree of As(III) (12.4-35.4%) generally increased with the increase of pH, but the optimal As(III) oxidation (45%) occurred at pH 5. Arsenic removal is much less affected by other five factors than pH. Insufficient and excessive Fe(II) supply caused the decrease of oxidation degree of As(III). Fenton-like reaction between Fe(II) and O-2 with reactive oxygen species (ROS) as oxidizers was the probable mechanism for Fe (II) and As(III) oxidation. Tooeleite/ferric arsenite hydroxysulfate, ferric arsenate and As(III+V)-bearing ferrihydrite were major responsible for As immobilization.
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页数:11
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