Association of individual soil mineral constituents and heavy metals as studied by sorption experiments and analytical electron microscopy analyses
Introduction
The ability of soils to adsorb metal ions from aqueous solution is of special interest and has consequences both for agricultural issues and environmental questions. As adsorption is a major process for accumulation of potentially toxic metals in soils, its study is of utmost importance for the understanding of how metals are transferred from a liquid mobile phase to the surface of a solid phase [1]. The exact retention mechanism of metal ions at soil surfaces is often unknown, so the term sorption is preferred, which in general involves the loss of a metal ion from an aqueous to a contiguous solid phase and consist of three important processes: adsorption, surface precipitation and fixation [2]. These processes are dependent on soil properties which are strongly influenced by the soil constituents. The organic matter, clay minerals, as well as Fe and Mn oxides are the most important components determining the sorption of metals in soils [3]. The organic components form stable metal–organic complexes with a variety of metals, while clay minerals and oxides concentrate heavy metal ions through surface ion exchange and metal-complex surface adsorption.
Batch equilibrium techniques are widely used to study the retention of metals in soils and the sorption data are described by using isotherms. The analysis of isotherms may provide information about the retention capacity and the sorption strength by which the sorbate is held onto the soil. However, the information gained through adsorption isotherms is limited because the interaction of metals with solid phases cannot be determined and the actual partitioning of metals in various chemical phases cannot be identified [4]. Additionally, when extending the number of the studied soils, including soils of contrasting characteristics, it is difficult to draw clear conclusions on the soil phases responsible for the sorption of the target metals, since sorption is a process that depends on variety of factors [5]. Additionally, despite the intense study of metal sorption capacity of separated soil constituents, little is known about the metal retention capacity of discrete mineral constituents within the soil.
To overcome the limitations of sorption studies mentioned above, it is worth combining sorption isotherm analyses with direct instrumental analytical techniques to study the characteristics of metal sorption onto soil components. Besides the application of X-ray absorption spectroscopy methods [6], [7], this kind of approach was successfully used also by Sipos et al. [8] who studied the sorption properties of lead onto soil mineral constituents by analytical electron microscopy. However, metal sorption in soils is a competitive process among different ions [9], so the direct analysis of sorption of a given metal in the presence of others is of primary importance. In this study, the integrated use of analytical electron microscopy analyses and competitive sorption experiments were performed on soil samples with different composition. Samples for Cu, Zn and Pb sorption experiments were selected according to their significant organic matter, carbonate mineral and iron oxide content, as well as to their different clay mineralogy as these phases play an important role in metal immobilization in soils. The aim of this study was to investigate the metal sorption capacity of discrete soil mineral constituents (mainly clay minerals, iron oxides and carbonates). Special attention was directed to study the effect of presence of organic matter as well as carbonate and iron oxide phases on the sorption capacity of discrete soil clay mineral phases.
Section snippets
Studied soil samples
Four natural soil samples were used in the laboratory experiments. The samples were collected from a Calcic (P9) and a Haplic Luvisol (P13) profiles, with silt loam and clay loam textures, respectively [10]. The air-dried samples were passed through a 2 mm sieve. Some physico-chemical properties of the studied samples are presented in Table 1. The sample from the A horizon of the profile P9 (P9A) is characterized by relatively high total organic carbon content (67.4 g kg−1) and intermediate cation
Sorption studies
Copper, Zn and Pb sorption experiments were carried out to study the immobilization of metals by the soil samples with different composition. As the affinity of metals to soil may be strongly influenced by the initial metal concentrations in solutions used (which is six times higher for Zn than for Cu in our case), therefore, the sorption intensity values will be used to compare the sorption capacity of the studied samples. According to Xiong et al. [15] sorption intensity is a useful measure
Conclusions
Higher sorption intensity for Cu and lower for Zn was observed by both the results of sorption experiments and analytical electron microscopy analyses. Despite its highest sorption intensity among the studied metals, the generally lowest Pb sorption capacity of discrete mineral particles was found suggesting indirectly the significant role of soil organic matter in Pb immobilization which was also supported by the sorption experiments. Additionally, the competitive situation resulted in
Acknowledgements
This study was financially supported by the Hungarian Scientific Research Fund (OTKA no. F 62760 and PF 63973).
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