Arsenic removal in aqueous solutions using FeS2

被引:84
作者
Fu, Dun [1 ,2 ]
Kurniawan, Tonni Agustiono [2 ]
Lin, Lan [3 ]
Li, Yaqiong [4 ]
Avtar, Ram [5 ]
Othman, Mohd Hafiz Dzarfan [6 ]
Li, Feng [1 ]
机构
[1] Suzhou Univ, Sch Resources & Civil Engn, Natl Engn Res Ctr Coal Mine Water Hazard Controll, Suzhou 234000, Anhui, Peoples R China
[2] Xiamen Univ, Coll Environm & Ecol, Xiamen 361102, Fujian, Peoples R China
[3] Tohoku Univ, Grad Sch Engn, Dept Civil & Environm Engn, Aoba Ku, 6-6-06 Aoba, Sendai, Miyagi 9808579, Japan
[4] Harbin Inst Technol, Sch Environm, Harbin 150090, Heilongjiang, Peoples R China
[5] Hokkaido Univ, Fac Environm Earth Sci, Sapporo, Hokkaido 0600810, Japan
[6] Univ Teknol Malaysia, Sch Chem & Energy Engn, Adv Membrane Technol Res Ctr AMTEC, Skudai 81310, Johor, Malaysia
关键词
Arsenic contamination; Low-cost adsorbents; Natural minerals; Persulfate; Pyrite; LOW-COST ADSORBENTS; CONTAMINATED WATER; PERSULFATE ACTIVATION; DRINKING-WATER; DEGRADATION; OXIDATION; PYRITE; ADSORPTION; LADEN; 4-CHLOROPHENOL;
D O I
10.1016/j.jenvman.2021.112246
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
This study tested the technical feasibility of pyrite and/or persulfate oxidation system for arsenic (As) removal from aqueous solutions. The effects of persulfate on As removal by the pyrite in the integrated treatment were also investigated. Prior to the persulfate addition into the reaction system, the physico-chemical interactions between As and the pyrite alone in aqueous solutions were explored in batch studies. The adsorption mechanisms of As by the adsorbent were also presented. At the same As concentration of 5 mg/L, it was found that As(III) attained a longer equilibrium time (8 h) than As(V) (2 h), while the pyrite worked effectively at pH ranging from 6 to 11. At optimum conditions (0.25 g/L of pyrite, pH 8.0 and 5 mg/L of As(III) concentration), the addition of persulfate (0.5 mM) into the reaction promoted a complete removal of arsenic from the solutions. Consequently, this enabled the treated effluents to meet the arsenic maximum contaminant limit (MCL) of <10 ?g/L according to the World Health Organization (WHO)?s requirements. The redox mechanisms, which involved electron transfer from the S22- of the pyrite to Fe3+, supply Fe2+ for persulfate decomposition, oxidizing As(III) to As(V). The sulfur species played roles in the redox cycle of the Fe3+/Fe2+ of the pyrite by giving its electrons, while the As(III) oxidation to As(V) was attributed to the pyrite. Overall, this work reveals the applicability of the pyrite as an adsorbent for water treatment and the importance of persulfate addition to promote a complete As removal from aqueous solutions.
引用
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页数:10
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