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In situ chemical treatments for reducing heavy metal solubility and transport in smelter contaminated soils.

机译:原位化学处理,用于降低重金属在冶炼厂污染土壤中的溶解度和运输。

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摘要

Scope and method of study. The study investigated and developed chemical immobilization techniques for reducing heavy metal solubility and transport. Solute transport experiments were conducted with metal contaminated soil collected from a defunct smelter. Treatment materials included agricultural limestone, rock phosphate, and diammonium phosphate. Numerical integration of Cd, Pb, and Zn eluted from soil columns allowed for treatment comparisons. Metal elution curves were fit with a transport model to determine retardation (R) and distribution coefficients (Kd). Eluted fractions were speciated with a chemical equilibrium model to investigate heavy metal species controlling transport and potential solids controlling solubility.; Findings and conclusions. In the first study, the 10 g DAP kg--1 application was the most effective for immobilizing heavy metals eluted from the contaminated soil with only 5.4% of Cd, 1.1% of Pb, and 4.2 % of the Zn eluted when compared with untreated soil. Application of DAP released As from the contaminated soil via ligand exchange. Total phosphorus eluted from the DAP treatments was 1 % of the total added for the 10 mg DAP kg--1 treatment and 10.5% of the total added for the 90 mg DAP kg--1 treatment. Layered RP at 180 g kg--1 was the most effective treatment for reducing Pb transport (99.9% reduction). Limestone was moderately effective for reducing Cd (45%) and Pb (54.8%), but was less effective for Zn. In the second study, DAP treatments of 460, 920, and 2300 mg P kg--1 were investigated. Model-fitted metal elution curves showed increased retardation (R) and distribution coefficients (Kd) with increased P application. Chemical speciation revealed decreased total mass of high mobility metal species with DAP treatment. Activity-ratio diagrams showed DAP application shifted the mineral controlled solubility of Cd from CdCO3 and Pb from PbSO4 to metal-phosphate compounds. Phosphate minerals controlled Zn in solution for untreated and DAP amended soils. Chemical immobilization using DAP may serve as a long-term remediation treatment for Cd, Pb, and Zn in smelter contaminated soils. Application schemes with DAP must be planned to reduce As and P elution, and co-application of timing materials may be necessary to offset soil acidification.
机译:研究范围和方法。该研究调查并开发了用于降低重金属溶解度和运输的化学固定技术。溶质运移实验是用从废弃的冶炼厂收集的金属污染土壤进行的。处理材料包括农业石灰石,磷酸盐岩和磷酸氢二铵。从土壤柱中洗脱出来的Cd,Pb和Zn的数值积分可以进行处理比较。金属洗脱曲线与运输模型拟合以确定延迟(R)和分布系数(Kd)。用化学平衡模型确定洗脱级分,以研究控制迁移的重金属物质和控制溶解度的潜在固体。结论和结论。在第一个研究中,与未经处理的相比,10 g DAP kg--1的应用最有效地固定了从污染的土壤中洗脱的重金属,其中仅5.4%的Cd,1.1%的Pb和4.2%的Zn被洗脱泥。 DAP的应用通过配体交换从受污染的土壤中释放了砷。从DAP处理中洗脱的总磷小于10 mg DAP kg--1处理的总磷的1%,而90 mg DAP kg--1处理的总磷的10.5%。 180 g kg--1的分层RP是减少Pb转运的最有效方法(减少99.9%)。石灰石对降低Cd(45%)和Pb(54.8%)的效果中等,但对Zn的效果较差。在第二项研究中,研究了460、920和2300 mg P kg--1的DAP处理。拟合模型的金属洗脱曲线显示,随着施磷量的增加,延迟(R)和分布系数(Kd)均增加。化学形态显示,经DAP处理后,高迁移率金属物种的总质量降低。活性比图表明,DAP的施用将矿物质控制的Cd的溶解度从CdCO3和Pb从PbSO4转变成金属磷酸盐。磷酸盐矿物控制未处理和DAP改良土壤中溶液中的Zn。使用DAP进行化学固定可作为冶炼厂污染土壤中Cd,Pb和Zn的长期修复方法。必须计划使用DAP的施用方案以减少As和P的洗脱,并且可能需要共同施用定时材料以抵消土壤酸化。

著录项

  • 作者

    McGowen, Steven Lynn.;

  • 作者单位

    Oklahoma State University.;

  • 授予单位 Oklahoma State University.;
  • 学科 Agriculture Soil Science.; Environmental Sciences.; Geochemistry.
  • 学位 Ph.D.
  • 年度 2000
  • 页码 75 p.
  • 总页数 75
  • 原文格式 PDF
  • 正文语种 eng
  • 中图分类 土壤学;环境科学基础理论;地质学;
  • 关键词

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