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采用三元改性剂现场固定土壤中的砷和铅的田间试验。

Field demonstration of on-site immobilization of arsenic and lead in soil using a ternary amending agent.

机构信息

School of Environment and Energy, South China University of Technology, Guangzhou 510006, China.

Environmental Engineering Program, Department of Civil & Environmental Engineering, Auburn University, Auburn AL 36849, USA.

出版信息

J Hazard Mater. 2022 Mar 15;426:127791. doi: 10.1016/j.jhazmat.2021.127791. Epub 2021 Nov 14.

Abstract

Soil contamination by heavy metals and metalloids has been a major environmental challenge. While various remediation technologies have been reported, field data on the remediation effectiveness have been limited. We tested a new remediation technology for on-site immobilization of As(III) and Pb(II) in a contaminated soil at an abandoned chemical plant site. A novel ternary amending agent consisting of FeO, MnO, and Mg(OH) (molar ratio = 1.0:5.5:5.5) was used to amend the soil on-site. Field monitoring data indicated that the amendment severed as a pH buffer and a long-term sequester for both As and Pb in the soil. At a dosage of 3 wt%, the acid-leachable As and Pb were lowered from 0.042-0.077 mg/L and 0.013-0.022 mg/L to 0.0062-0.0093 mg/L and 0.0030-0.0080 mg/L, respectively, after one day of the amendment, and to 0.0020-0.0050 mg/L and 0.0020-0.0054 mg/L after 240 days of aging. As(III) was oxidized to As(V) and subsequently immobilized via complexation and precipitation, whereas Pb(II) was sequestered via electrostatic attraction and chemical precipitation. The treatment cost was estimated at $31.5/m. The results indicate that complex contaminants in soil can be effectively immobilized using combined amending agents that can interact with the target chemicals and induce synergistic immobilization reactions.

摘要

土壤中重金属和类金属的污染是一个主要的环境挑战。虽然已经报道了各种修复技术,但关于修复效果的现场数据有限。我们在一个废弃化工厂现场测试了一种新的修复技术,用于原位固定污染土壤中的 As(III)和 Pb(II)。一种由 FeO、MnO 和 Mg(OH)组成的新型三元改良剂(摩尔比=1.0:5.5:5.5)用于现场改良土壤。现场监测数据表明,该改良剂在土壤中充当了 pH 缓冲剂和 As 和 Pb 的长期固定剂。在 3wt%的剂量下,酸可提取的 As 和 Pb 分别从 0.042-0.077mg/L 和 0.013-0.022mg/L 降低至 0.0062-0.0093mg/L 和 0.0030-0.0080mg/L,在改良后 1 天内,在老化 240 天后降低至 0.0020-0.0050mg/L 和 0.0020-0.0054mg/L。As(III)被氧化为 As(V),随后通过络合和沉淀固定,而 Pb(II)则通过静电吸引和化学沉淀固定。处理成本估计为 31.5 美元/m。结果表明,使用可以与目标化学物质相互作用并诱导协同固定反应的组合改良剂,可以有效地固定土壤中的复杂污染物。

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