Enhanced remediation of Cr(VI)-contaminated soil by modified zero-valent iron with oxalic acid on biochar

被引:9
|
作者
Xie, Lihong [1 ]
Chen, Qingjun [2 ]
Liu, Yiyang [1 ]
Ma, Qiyan [1 ]
Zhang, Jinlan [1 ]
Tang, Chenliu [1 ]
Duan, Guilan [3 ]
Lin, Aijun [1 ]
Zhang, Tingting [1 ]
Li, Shangyi [1 ]
机构
[1] Beijing Univ Chem Technol, Coll Chem Engn, Dept Environm Sci & Engn, Beijing 100029, Peoples R China
[2] China Natl Petr & Chem Planning Inst, Beijing 100013, Peoples R China
[3] Chinese Acad Sci, Res Ctr Ecoenvironm Sci, State Key Lab Urban & Reg Ecol, Beijing 100085, Peoples R China
关键词
Cr(VI)-contaminated soil; Zero valent iron; Electron transfer; Oxalic acid modification; Wet ball milling; REMOVAL; CR(VI); REDUCTION; PARTICLES; CHROMIUM; WATER; PERFORMANCE;
D O I
10.1016/j.scitotenv.2023.167399
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Hexavalent chromium (Cr(VI)) is carcinogenic and widely presented in soil. In this study, modified zero-valent iron (ZVI) with oxalic acid on biochar (OA-ZVI/BC) was prepared using wet ball milling method for the remediation of Cr(VI)-contaminated soil. Microscopic characterizations showed that ZVI were distributed on the biochar uniformly and confirmed the enhanced interface interaction between biochar and ZVI by wet ball milling. Electrochemical analysis indicated the strong electron transfer ability and enhanced corrosion behavior of OA-ZVI/BC. Moreover, inhibitory efficiencies of Cr(VI) removal with the addition of 1,10-phenanthroline suggested abundant Fe2+ generation in OA-ZVI/BC, which might facilitate the reduction of Cr(VI) to Cr(III). Theory calculation further demonstrated the ZVI modified by oxalic acid was more susceptible to solid-solid interfacial reactions with Cr(VI), and more electrons were transferred to Cr(VI). When applied to Cr(VI)contaminated soil, OA-ZVI/BC could passivate 96.7 % total Cr(VI) and maintained for 90 days. The toxicity characteristic leaching procedure (TCLP) and simple based extraction test (SBET) were used to evaluate the leaching toxicity and bioaccessibility of Cr(VI), respectively. The TCLP-Cr(VI) decreased to 0.11 mg & sdot;L- 1 after OAZVI/BC treatment, much lower than that of soils with ZVI/BC and OA-ZVI remediation (1.5 mg & sdot;L- 1 and 4.1 mg & sdot;L- 1). The bioaccessibility of Cr(VI) reduced by 93.5 % after 3-month remediation. Sequential extraction showed that Cr fractions in the soil after OA-ZVI/BC remediation was converted from acetic acid-extractable (HOAc-extractable) to more stable forms (e.g., residual and oxidizable forms). Benefiting from the synergies of oxalic acid, biochar and wet ball milling, OA-ZVI/BC exhibited an excellent performance on the remediation of Cr(VI)-contaminated soil, whose mechanisms involved adsorption, reduction (Fe0/Fe2+, Fe2+/Fe3+) and coprecipitation. This study herein develops a promising ZVI technology in the remediation of heavy metalcontaminated soil.
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页数:12
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