Abstract

The tailings dam breach at the Ajka alumina plant, western Hungary in 2010 introduced ∼1millionm3 of red mud suspension into the surrounding area. Red mud (fine fraction bauxite residue) has a characteristically alkaline pH and contains several potentially toxic elements, including arsenic. Aerobic and anaerobic batch experiments were prepared using soils from near Ajka in order to investigate the effects of red mud addition on soil biogeochemistry and arsenic mobility in soil–water experiments representative of land affected by the red mud spill. XAS analysis showed that As was present in the red mud as As(V) in the form of arsenate. The remobilisation of red mud associated arsenate was highly pH dependent and the addition of phosphate to red mud suspensions greatly enhanced As release to solution. In aerobic batch experiments, where red mud was mixed with soils, As release to solution was highly dependent on pH. Carbonation of these alkaline solutions by dissolution of atmospheric CO2 reduced pH, which resulted in a decrease of aqueous As concentrations over time. However, this did not result in complete removal of aqueous As in any of the experiments. Carbonation did not occur in anaerobic experiments and pH remained high. Aqueous As concentrations initially increased in all the anaerobic red mud amended experiments, and then remained relatively constant as the systems became more reducing, both XANES and HPLC–ICP-MS showed that no As reduction processes occurred and that only As(V) species were present. These experiments show that there is the potential for increased As mobility in soil–water systems affected by red mud addition under both aerobic and anaerobic conditions.

Highlights

  • Bauxite residue is the fine fraction waste remaining after Al extraction from bauxite using the Bayer Process

  • (2) To use a combination of X-ray absorption spectroscopy and high performance liquid chromatography–ion coupled plasma–mass spectroscopy to determine changes in solid or aqueous phase As speciation induced by long term anaerobic incubation

  • X-ray absorption spectroscopy (XAS) analysis has determined that As in the red mud sampled is present primarily as an inorganic arsenate phase (Fig. 2), in this case EXAFS analysis could not resolve the exact nature of the phases present due to a lack of evidence for second shell backscatters in the spectra

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Summary

Introduction

Bauxite residue (red mud) is the fine fraction waste remaining after Al extraction from bauxite using the Bayer Process. Under these conditions there is potential for enhanced mobility of oxyanion forming trace elements (e.g. Al, As, Cr, Mo and V) (Cornelis et al, 2008; Langmuir, 1997; Smedley and Kinniburgh, 2002) due to their reduced adsorption to surfaces at high pH These issues aside, the abundance of red mud as a waste product (up to 120 million tonnes are produced annually (Power et al, 2011)) has led to much research into possible uses. These include: recovery of Al, Fe, trace and rare earth metals (Hammond et al, 2013; Hind et al, 1999); a low cost sorbent for water decontamination (Altundogan et al, 2002; Bhatnagar et al, 2011; Liu et al, 2011); in CO2 sequestration (Yadav et al, 2010); as an additive to ceramics and building materials (Liu and Zhang, 2011; Somlai et al, 2008) or as a soil amendment (Feigl et al, 2012; Friesl et al, 2004; Gray et al, 2006; Lombi et al, 2002)

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