Agronomy Department, Center for Soil and Environmental Science, Biotechnical Faculty, University of Ljubljana, Jamnikarjeva 101, 1000 Ljubljana, Slovenia.
Chemosphere. 2008 Nov;73(9):1484-91. doi: 10.1016/j.chemosphere.2008.07.043. Epub 2008 Aug 31.
The feasibility of a novel two-phase method for remediation of Pb (1374 mg kg(-1)), Zn (1007 mg kg(-1)), and Cd (9.1 mg kg(-1)) contaminated soil was evaluated. In the first phase we used EDTA for leaching heavy metals from the soil. In the second phase we used an electrochemical advanced oxidation process (EAOP) for the treatment and reuse of washing solution for soil rinsing (removal of the soil-retained, chelant-mobilized metallic species). In EAOP, a boron-doped diamond anode was used for the generation of hydroxyl radicals and oxidative decomposition of EDTA-metal complexes at a constant current density (15 mA cm(-2)). The released metals were removed from the solution by filtration as insoluble participate and by electro-deposition on the cathode. Four consecutive additions of 5.0 mm ol kg(-1) EDTA (total 20 mmol kg(-1)) removed 44% Pb, 14% Zn and 35% Cd from the soil. The mobility of the Pb, Zn and Cd (Toxicity Characteristic Leaching Procedure) left in the soil after remediation was reduced by 1.6, 3.4 and 1.5 times, respectively. The Pb oral availability (Physiologically Based Extraction Test) in the simulated stomach phase was reduced by 2.4 and in the intestinal phase by 1.7 times. The discharge solution was clear, almost colorless, with pH 7.73 and 0.47 mg L(-1) Pb, 1.03 mg L(-1) Zn, bellow the limits of quantification of Cd and 0.023 mM EDTA. The novel method enables soil leaching with small water requirements and no wastewater generation or other emissions into the environment.
我们评估了一种新型两相法修复 Pb(1374mgkg(-1))、Zn(1007mgkg(-1))和 Cd(9.1mgkg(-1))污染土壤的可行性。在第一阶段,我们使用 EDTA 从土壤中浸出重金属。在第二阶段,我们使用电化学高级氧化工艺(EAOP)处理和再利用土壤冲洗的洗涤溶液(去除土壤保留的、螯合剂迁移的金属物种)。在 EAOP 中,使用掺硼金刚石阳极在恒定电流密度(15mAcm(-2))下生成羟基自由基和 EDTA-金属配合物的氧化分解。通过过滤作为不溶性物质和在阴极上电沉积,从溶液中去除释放的金属。连续添加 4 次 5.0mmolkg(-1)EDTA(总计 20mmolkg(-1)),从土壤中去除了 44%的 Pb、14%的 Zn 和 35%的 Cd。修复后土壤中残留的 Pb、Zn 和 Cd 的迁移性(毒性特征浸出程序)分别降低了 1.6、3.4 和 1.5 倍。模拟胃相中 Pb 的口服可利用性(基于生理的提取测试)降低了 2.4 倍,肠相中降低了 1.7 倍。排放溶液清澈,几乎无色,pH 值为 7.73,Pb 为 0.47mgL(-1),Zn 为 1.03mgL(-1),低于 Cd 的定量限和 0.023mMEDTA。该新方法可实现土壤浸提,用水量少,无废水产生或其他排放到环境中。