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测定港湾沉积物中铜、铅和锌的实验浸出率及建模。

Determining the experimental leachability of copper, lead, and zinc in a harbor sediment and modeling.

机构信息

INSA-Lyon, Laboratoire de Génie Civil et d'Ingénierie Environnementale LGCIE, Université de Lyon, 20 avenue Albert Einstein, 69621 Villeurbanne, France.

出版信息

Environ Sci Pollut Res Int. 2013 Jan;20(1):66-74. doi: 10.1007/s11356-012-1233-1. Epub 2012 Oct 21.

Abstract

The potential leaching of pollutants present in harbor sediments has to be evaluated in order to choose the best practices for managing them. Little is known about the speciation and mobility of heavy metals in these specific solid materials. The objective of this paper is to determine and model the leachability of copper, lead, and zinc present in harbor sediments in order to obtain essential new data. The mobility of inorganic contaminants in a polluted harbor sediment collected in France was investigated as a function of physicochemical conditions. The investigation relied mainly on the use of leaching tests performed in combination with mineralogical analysis and thermodynamic modeling using PHREEQC. The modeling phase was dedicated to both confirm the hypothesis formulated to explain the experimental results and improve the determination of the main physico-chemical parameters governing mobility. The experimental results and modeling showed that the release of copper, lead, and zinc is very low with deionized water which is due to the stability of the associated solid phases (organic matter, carbonate minerals, and/or iron sulfides) at natural slightly basic conditions. However, increased mobilization is observed under pH values below 6.0 and above 10.0. This methodology helped to consistently obtain the geochemical parameters governing the mobility of the contaminants studied.

摘要

为了选择管理港湾沉积物的最佳实践,必须评估污染物的潜在浸出。对于这些特殊固体材料中重金属的形态和迁移性知之甚少。本文的目的是确定和模拟港湾沉积物中铜、铅和锌的浸出率,以获得必要的新数据。法国采集的受污染港湾沉积物中无机污染物的迁移性是根据物理化学条件进行调查的。该研究主要依赖于使用浸出试验与矿物学分析相结合,并使用 PHREEQC 进行热力学模拟。模型阶段旨在证实用于解释实验结果的假设,并改进控制迁移率的主要物理化学参数的确定。实验结果和模型表明,在天然弱碱性条件下,由于相关固相(有机物、碳酸盐矿物和/或硫化铁)的稳定性,铜、铅和锌的释放非常低。然而,在 pH 值低于 6.0 和高于 10.0 时,观察到迁移性增加。该方法有助于一致地获得控制所研究污染物迁移性的地球化学参数。

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