Abstract

Pyrite and calcite are mineral phases that play a major role in acid and neutral mine drainage processes. However, the prediction of acid mine drainage (AMD) or contaminated neutral drainage (CND) requires knowledge of the mineral composition of mining waste and the related potential for element release. This paper studies the combination of acid–base neutralizing capacity (ANC–BNC) with geochemical modeling for the characterization of mining waste and prediction of AMD and CND. The proposed approach is validated with three synthetic mineral assemblages: (1) siliceous sand with pyrite only, representing mining waste responsible for AMD, (2) siliceous sand with calcite and pyrite, representing calcareous waste responsible for CND, and (3) siliceous sand with calcite only, simulating calcareous matrices without any pyrite. The geochemical modeling approach using PHREEQC software was used to model pH evolution and main element release as a function of the added amount of acid or base over the entire pH range: 1 < pH < 13. For calcareous matrices (sand with calcite), the results are typical of a carbonated environment, the geochemistry of which is well known. For matrices containing pyrite, the results identify different pH values favoring the dissolution of pyrite: pH = 2 in a pyrite-only environment and pH = 6 where pyrite coexists with calcite. The neutral conditions can be explained by the buffering capacity of calcite, which allows iron oxyhydroxide precipitation. Major element release is then related to the dissolution and precipitation of the mineral assemblages. The geochemical modeling allows the prediction of element speciation in the solid and liquid phases. Our findings clearly prove the potential of combined ANC–BNC experiments along with geochemical modeling for the characterization of mining waste and the assessment of risk of AMD and CND.

Highlights

  • Mining and mineral processing activities produce large volumes of byproducts known as mining waste

  • The experimental protocol was divided into four steps: (1) prestudy, with simple titration to estimate the amount of acid and base to be introduced to cover the whole range of pH, (2) batch preparation using a solid/liquid ratio of around

  • Calcite and pyrite solid phases were chosen for the ANC–BNC titrations

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Summary

Introduction

Mining and mineral processing activities produce large volumes of byproducts known as mining waste. In most investigations of closed mines, high concentrations of trace metals and sulfates were mobilized by leaching from tailings [15,16]. Under these conditions, effluents are generated and some toxic metals and metalloids, such as Ni, Zn, Co, As, and Sb, may be solubilized [1,10]. Effluents are generated and some toxic metals and metalloids, such as Ni, Zn, Co, As, and Sb, may be solubilized [1,10] In both drainage situations (AMD or CND), pyrite and other mineral phase dissolutions pose a crucial environmental problem [17].

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