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多瑙河口镉的释放:通过实验方法确定的物理和化学过程的贡献

Release of cadmium in the Danube estuary: contribution of physical and chemical processes as determined by an experimental approach.

作者信息

Garnier Jean-Marie, Guieu Cécile

机构信息

CEREGE, Université Aix-Marseille III/CNRS, BP 80, F 13545, Aix-en-Provence, France.

出版信息

Mar Environ Res. 2003 Feb;55(1):5-25. doi: 10.1016/s0141-1136(02)00107-1.

DOI:10.1016/s0141-1136(02)00107-1
PMID:12469773
Abstract

The behavior of dissolved cadmium (Cd) in the Danube estuary was investigated through field sampling and mixing experiments using Danube River water and Black Sea water. The experiments were performed by mixing these two end-member waters in various proportions, with the addition of stable or radioactive Cd to the freshwater Danube end-member prior to the mixing. The release of Cd that resulted in maximum concentrations under field conditions was well simulated by mixing experiments. The experimental results were modeled assuming that the release of Cd was the sum of the contribution of physical effects resulting from dilution effects and the contribution of chemical effects resulting from dissolved Cd-complex formation (and isotopic exchange when concerned). In the absence of dissolved Cd-complexing ligands, the release of Cd due to the dilution of the particulate phase during mixing could explain part of the maximum concentrations observed in field conditions. Kinetic effects were established by comparing the theoretical and measured contribution of chemical effects resulting from dissolved Cd-complex formation. The non-equilibrium state observed during the mixing experiment suggested the presence of particulate labile Cd that was not easily mobilized. All these features supported the hypothesis that Cd released in estuaries is controlled both by the dilution of the particulate phase and by kinetic competitive complexation between particulate ligands (covering a large spectrum of nature and strength) and dissolved ligands.

摘要

通过现场采样以及使用多瑙河水和黑海水进行混合实验,对多瑙河河口溶解镉(Cd)的行为进行了研究。实验通过将这两种端元水按不同比例混合来进行,在混合之前向淡水多瑙河端元中添加稳定的或放射性的Cd。混合实验很好地模拟了在现场条件下导致最大浓度的Cd释放情况。假设Cd的释放是稀释效应产生的物理效应贡献与溶解Cd - 络合物形成(以及相关时的同位素交换)产生的化学效应贡献之和,对实验结果进行了建模。在没有溶解的Cd - 络合配体的情况下,混合过程中颗粒相稀释导致的Cd释放可以解释现场条件下观察到的部分最大浓度。通过比较溶解Cd - 络合物形成产生的化学效应的理论贡献和实测贡献,确定了动力学效应。混合实验中观察到的非平衡状态表明存在不易迁移的颗粒态不稳定Cd。所有这些特征都支持了这样一种假设,即河口释放的Cd既受颗粒相稀释的控制,也受颗粒配体(涵盖多种性质和强度)与溶解配体之间的动力学竞争络合作用的控制。

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