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Leaching of heavy metals from fly ash stabilized soils.

机译:从飞灰稳定的土壤中浸出重金属。

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摘要

A combined experimental and computer modeling approach was used to evaluate leaching of metals from fly ash stabilized soils used in highways. Four different tasks were undertaken: (1) water leach testing, (2) laboratory column testing, (3) field testing, and (4) numerical modeling.; The pH and aqueous concentration of metals in leachate from water leach tests, and the pH and initial effluent concentration from column leaching tests on soil-fly ash mixtures increase non-linearly with increasing fly ash content. The metal concentration in leachate cannot be estimated from simple dilution calculations. The initial effluent concentration depends primarily on the type of fly ash, and the partition coefficient depends primarily on the type of soil used in the soil-fly ash mixture. The pH of the effluent is persistent for at least 30 pore volumes of flow (30-yrs of flow in the field).; Lysimeters were installed at two field sites in a conventional pavement and two fly ash stabilized pavements. The liquid flux through the pavement was approximately 4–6% of the average annual precipitation for both types of pavements. The concentration of metals in leachate was higher for the pavements constructed with stabilized soil than the conventional pavement.; A numerical model was developed to simulate leaching that occurs in pavements incorporating stabilized soils. Result of simulations with the model showed that the maximum metal concentration decreases rapidly within the first meter below a fly ash stabilized layer, and then decreases more gradually. The maximum concentration at a given depth is independent of the retardation factor, and decreases with increasing dispersion coefficient and decreasing thickness of the stabilized layer. For advection-dominated transport, the maximum concentration is independent of the Darcy flux. The time to reach the maximum concentration at a particular depth is inversely proportional to Darcy flux, and increases as the dispersion coefficient decreases and as the retardation factor increases.; Design charts were prepared from parametric simulations conducted with the model. These charts can be used for a quick and realistic prediction of the maximum concentration and the time required to achieve the maximum concentration for a wide range of field conditions.
机译:实验和计算机建模相结合的方法用于评估高速公路使用的粉煤灰稳定化土壤中金属的浸出。进行了四个不同的任务:(1)浸水测试,(2)实验室色谱柱测试,(3)现场测试,(4)数值建模;水浸试验中浸出液中金属的pH值和水的浓度,以及土-粉煤灰混合物的柱浸试验中pH和初始流出物的浓度随粉煤灰含量的增加而呈非线性增加。无法通过简单的稀释计算来估算渗滤液中的金属浓度。初始废水浓度主要取决于粉煤灰的类型,分配系数主要取决于土壤-粉煤灰混合物中使用的土壤的类型。废水的pH值在至少30个孔体积的流量(现场30年流量)中保持不变。测渗仪安装在常规路面和两个粉煤灰稳定路面的两个现场位置。通过这两种路面的液体通量约为年平均降水量的4–6%。用稳定土壤建造的人行道中渗滤液中金属的浓度要高于传统人行道。开发了一个数值模型来模拟在掺入稳定土壤的路面中发生的浸出。该模型的模拟结果表明,最大金属浓度在粉煤灰稳定层以下的第一米内迅速降低,然后逐渐降低。给定深度的最大浓度与延迟因子无关,并且随着分散系数的增加和稳定层厚度的减小而减小。对于以平流为主的输运,最大浓度与达西通量无关。在特定深度达到最大浓度的时间与达西通量成反比,并且随着色散系数的减小和延迟因子的增大而增加。根据对该模型进行的参数模拟准备了设计图。这些图表可用于在广泛的现场条件下快速,实际地预测最大浓度以及达到最大浓度所需的时间。

著录项

  • 作者

    Bin-Shafique, Md Sazzad.;

  • 作者单位

    The University of Wisconsin - Madison.;

  • 授予单位 The University of Wisconsin - Madison.;
  • 学科 Geotechnology.; Engineering Environmental.
  • 学位 Ph.D.
  • 年度 2002
  • 页码 306 p.
  • 总页数 306
  • 原文格式 PDF
  • 正文语种 eng
  • 中图分类 地质学;环境污染及其防治;
  • 关键词

  • 入库时间 2022-08-17 11:46:12

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