Abstract

Changes in the site density and surface acidity constants (i.e. pKa1 and pKa2) of kaolinite and montmorillonite were determined after acid or alkali spills, and pH buffering capacity was evaluated as a parameter of soil function change. Surface complexation modeling with potentiometric titrations and Fourier-transform infrared spectroscopy showed that acid or alkali spills did not significantly change the surface properties of kaolinite. In montmorillonite, however, acid spills decreased the basal site density from 832 to 737 mmol kg−1 by dissolving substituted octahedral cations and decreased pKa2 from 7.32 to 5.42 by dissolving SiOH. In response to alkali spills, the basal site density increased to 925 mmol kg−1, and the edge site density increased from 84.8 to 253 mmol kg−1 due to AlOH and SiOH formation; thus, pKa2 decreased to 6.78. The pH buffering capacity of acid- or alkali-spilled kaolinite at pH 6 did not significantly change, while that of acid- or alkali-spilled montmorillonite increased from 30.3 to 35.9 and 56.0 mmol kg−1, respectively. Our results indicate that these spills greatly altered the surface properties of montmorillonite, but unexpectedly, increased the pH buffering capacity of montmorillonite.

Highlights

  • Fourier-transform infrared spectroscopy showed that acid or alkali spills did not significantly change the surface properties of kaolinite

  • The results indicated that the extent of change in the surface properties resulting from an acid or alkali spill varied with the type of clay mineral, and especially, an expandability should be carefully considered

  • We investigated the change in surface properties of clay minerals due to acid or alkali spills and its effect on the pH buffering capacity as an indicator of soil functions

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Summary

Introduction

Fourier-transform infrared spectroscopy showed that acid or alkali spills did not significantly change the surface properties of kaolinite. Neutralizers have been poured onto acid- or alkali-spilled soils for pH recovery[10,11], neutralization cannot recover nonreversible dissolution of organic matter or clay minerals and the change in cation exchange capacity (CEC) caused by the structural deterioration[12]. Changes in these properties will alter soil functions, pH buffering capacity. There have been several studies on soil acidification phenomenon, and they revealed that the long-term acidification led to chemical weathering of clay minerals and decreased the base saturation[20,21,22] These reaction conditions are unrealistic in natural environment after acid or alkali spills. Clay minerals play a significant role in the pH buffering capacity of soils with low organic matter content resulting from acid or alkali spills; knowledge of the changes in clay minerals’ properties after these spills is essential to interpret the pH buffering capacity of the soils

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