The importance of organic matter distribution and extract soil:solution ratio on the desorption of heavy metals from soils

The lability (mobility and bioavailability) of metals varies significantly with soil properties for similar total soil metal concentrations. We studied desorption of Cu, Ni and Zn, from 15 diverse, unamended soils. These studies included evaluation of the effects of soil:solution extraction ratio an...

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Published inThe Science of the total environment Vol. 287; no. 1; pp. 107 - 119
Main Authors Yin, Yujun, Impellitteri, Christopher A., You, Sun-Jae, Allen, Herbert E.
Format Journal Article
LanguageEnglish
Published Shannon Elsevier B.V 15.03.2002
Elsevier Science
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Summary:The lability (mobility and bioavailability) of metals varies significantly with soil properties for similar total soil metal concentrations. We studied desorption of Cu, Ni and Zn, from 15 diverse, unamended soils. These studies included evaluation of the effects of soil:solution extraction ratio and the roles of soil properties on metal desorption. Desorption was examined for each metal by computing distribution coefficients ( K d) for each metal in each soil where K d=[ M] soil/[ M] solution. Results from soil:solution ratio studies demonstrated that K d values for the metals tended to increase with increasing soil:solution ratio. This result also held true for distribution of soil organic matter (SOM). Because the soil:solution ratio has a significant effect on measured metal distributions, we selected a high soil:solution ratio to more closely approach natural soil conditions. Copper showed strong affinity to operationally defined dissolved organic matter (DOM). In this study, DOM was operationally defined based on the total organic carbon (TOC) content in 0.45-μm or 0.22-μm filtrates of the extracts. The K d of Cu correlated linearly ( r 2=0.91) with the K d of organic matter ( K d-om) where the K d-om is equal to SOM as measured by Walkley–Black wet combustion and converted to total carbon (TC) by a factor of 0.59. These values representing solid phase TC were then divided by soluble organic carbon as measured by TOC analysis (DOM). The conversion factor of 0.59 was employed in order to construct K d-om values based on solid phase carbon and solution phase carbon. SOM plays a significant role in the fate of Cu in soil systems. Soil–solution distribution of Ni and Zn, as well as the activity of free Cu 2+, were closely related to SOM, but not to DOM. K d values for Ni, Zn and free Cu 2+ in a particular soil were divided by the SOM content in the same soil. This normalization of the K d values for Ni, Zn, and free Cu 2+ to the SOM content resulted in significant improvements in the linear relationships between non-normalized K d values and soil pH. The semi-empirical normalized regression equations can be used to predict the solubility of Ni and Zn and the activity of free Cu 2+ as a function of pH.
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ISSN:0048-9697
1879-1026
DOI:10.1016/S0048-9697(01)01000-2