Immobilization of arsenate in a sandy loam soil using starch-stabilized magnetite nanoparticles

被引:49
作者
Liang, Qiqi [1 ]
Zhao, Dongye [1 ,2 ]
机构
[1] Auburn Univ, Dept Civil Engn, Environm Engn Program, Auburn, AL 36849 USA
[2] Taiyuan Univ Sci & Technol, Inst Environm Sci, Taiyuan, Shanxi, Peoples R China
基金
中国国家自然科学基金;
关键词
Metal immobilization; Magnetite; Arsenic; Nanoparticle; Groundwater remediation; Starch stabilization; Soil remediation; ZEROVALENT IRON; DRINKING-WATER; ADSORPTION; REMOVAL; ARSENIC(III); ARSENITE; GROUNDWATER; SORPTION; FERRIHYDRITE; REMEDIATION;
D O I
10.1016/j.jhazmat.2014.01.055
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 investigated effectiveness of starch-stabilized magnetite nanoparticles for in situ enhanced sorption and immobilization of arsenate, As(V), in a model sandy loam soil. Batch tests showed that the nanoparticles offered an As(V) distribution coefficient of 10,000 L/g, which is >3 orders of magnitude greater than that for the soil. Batch and column experimental results revealed that the nanoparticle treatment greatly reduced water-leachable As(V) and the leachability of As(V) remaining in the soil per TCLP (Toxicity Characteristic Leaching Procedure) analysis. Column tests showed that water-leachable As(V) from the As(V)-laden soil containing 31.45 mg/kg was reduced by similar to 93% and the TCLP leachability by >83% when the soil was treated with 34 pore volumes of a 0.1 g-Fe/L of the nanoparticle suspension. While the nanoparticles are deliverable in the soil, the effective travel distance of the nanoparticles can be manipulated by controlling the injection flow rate. Under natural groundwater flow conditions (velocity <= 2.4 x 10(-4) cm/s), the delivered nanoparticles are confined within a limited distance (<6.1 cm). (C) 2014 Elsevier B.V. All rights reserved.
引用
收藏
页码:16 / 23
页数:8
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