污染土壤中的重金属镉在电场力作用下的迁移模拟OA
Simulation of the migration of heavy metal cadmium in polluted soil under electric field force
重金属污染土壤电动力修复是在人工电场作用下迫使重金属离子向阴极附近迁移并集聚,进而去除土壤重金属离子的一种修复方法.在实验室条件下电动力修复实验时间一般较短,土壤中的Cd2+离子含量难以达到国家规定的低风险标准(≤0.4 mg/kg).为研究重金属污染土壤电动力修复效果及其影响因素,依据溶质运移方程,使用COMSOL多物理场模拟软件建立重金属镉污染土壤电动修复三维数值模型,开展重金属镉污染土壤电动力修复数值模拟实验,研究Cd2+离子在电场作用下的迁移特征.数值模拟的镉离子迁移分布结果与相近实验条件的实验结果比较吻合,模拟值与实测值平均相对偏差为 3.66%,初步验证了该模型用于重金属污染土壤电动修复的适用性.在此基础上设置电场强度为 2 V/cm,修复过程中不控制阴极室Cd2+离子浓度,修复60天后土壤Cd2+离子含量部分高于 0.4 mg/kg;修复过程中,控制阴极室Cd2+离子浓度,修复 45天后,污染土壤Cd2+离子含量均低于0.4 mg/kg.研究表明修复过程中阴极室不断聚集的高浓度Cd2+离子会阻碍土壤中的重金属镉离子继续向阴极室迁移,控制阴极室Cd2+离子浓度可以有效减弱镉离子反向扩散,以及其产生的附加电场的阻碍作用,减少修复时间,提高修复效率.
Electrodynamic remediation of heavy metal-contaminated soil is a remediation method that forces heavy metal ions to migrate and accumulate near the cathode under the action of artificial electric fields,thereby removing soil heavy metal ions.Under laboratory conditions,electrokinetic remediation experiments are generally short,and the Cd2+content in soil often makes it difficult to meet the national low-risk standard(≤0.4 mg/kg).To study the effects and influencing factors of electric dynamic remediation of heavy metal-contaminated soil,a three-dimensional numerical model of electric dynamic remediation of heavy metal cadmium-contaminated soil was established using COMSOL Multiphysics field simulation software based on the solute transport equation.Numerical simulation experiments on the electric dynamic remediation of heavy-metal-contaminated soil were carried out to investigate the migration characteristics of Cd2+ions under the action of an electric field.The numerical simulation of cadmium ion migration distribution results is consistent with the experimental results under similar conditions,with an average relative deviation of 3.66%between the simulated and measured values,preliminarily verifying the applicability of the model for electric remediation of heavy-metal-contaminated soil.On this basis,the electric field strength was set to 2 V/cm,and the Cd2+ion concentration in the cathode chamber was not controlled during the remediation process.After 60 days of remediation,the Cd2+ion content in the soil was partially higher than 0.4 mg/kg.During the remediation process,the concentration of Cd2+ions in the cathode chamber was controlled.After 45 days of remediation,the Cd2+ion content in the contaminated soil remained below 0.4 mg/kg.Research has shown that the continuous accumulation of high concentrations of Cd2+ions in the cathode chamber during the remediation process can hinder the continued migration of heavy metal cadmium ions from the soil to the cathode chamber.Controlling the concentration of Cd2+ions in the cathode chamber can effectively reduce the reverse diffusion of cadmium ions and the hindering effect of the additional electric field they generate,thereby reducing remediation time and improving remediation efficiency.
YANG Chao;CHEN Jinchao;CHEN Quanzhou
College of Geophysics,Chengdu University of Technology,Chengdu 610059,ChinaCollege of Geophysics,Chengdu University of Technology,Chengdu 610059,ChinaCollege of Geophysics,Chengdu University of Technology,Chengdu 610059,China
天文与地球科学
土壤污染重金属电动修复迁移模拟
soil pollutionheavy metalselectrokinetic remediationmigration simulation
《物探化探计算技术》 2026 (1)
87-98,12
四川省重点研发项目(2023YFG0253)
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