Abstract

Waste rock can contain high concentrations of deleterious trace elements, which upon oxidation can be released, having a significant impact on water quality. Therefore, knowledge about their occurrence and overall mobility is crucial to ensure suitable environmental protection measures. Sulfide-rich waste rock was characterized and quantified using automated mineralogy (QEMSCAN). Selected pyrite grains were analyzed for trace element occurrence using LA-ICP-MS before, during, and after leaching the waste rock in 10 L small-scale test cells for two years to assess trace element occurrence and mobility. Sequential extraction was used to estimate elemental sequestration during the experiment. The high abundance of pyrite (66%) and scarcity of buffering minerals resulted in low pH (<1.3) leachate with high concentrations of trace elements such as As (21 mg/L), Cu (20 mg/L), Hg (13 µg/L, Pb (856 µg/L), Sb (967 µg/L), Tl (317 µg/L ), and Zn (23 mg/L) in solution with limited retention in secondary minerals, primarily due to these elements’ association with pyrite either as inclusions or impurities showing an average abundance of 193 ppm As, 15 ppm Cu, 13 ppm Hg, 20 ppm Pb, 24 ppm Sb, 26 ppm Tl, and 74 ppm Zn in the waste rock. The occurrence of Cu and Zn as inclusions associated with the pyrite led to their extensive mobilization of 79% and 72%, respectively, despite their low abundance in the waste rock. Provided the overall leachability of S (11%) and limited formation of secondary minerals, the average oxidation rate suggests depletion of the pyrite within approximately 18 years. In conclusion, this study shows the importance of detailed mineralogical investigations and early preventive measures of waste rock to ensure sustainable mine waste and water management.

Highlights

  • The oxidation of sulfide minerals with the subsequent generation of acid rock drainage (ARD), characterized by a low pH and high concentrations of metal(loids), is considered one of the most challenging environmental consequences of mining [1,2,3]

  • Mining is focused on ore mineral extraction, it is common minerals such as pyrite, ending up as mine waste, which are mainly responsible for ARD generation

  • Revealed that the waste rock was dominated by pyrite (66%) with smaller amounts of quartz

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Summary

Introduction

The oxidation of sulfide minerals with the subsequent generation of acid rock drainage (ARD), characterized by a low pH and high concentrations of metal(loids), is considered one of the most challenging environmental consequences of mining [1,2,3]. ARD develops in sulfide-bearing mine waste where the neutralization capacity (mainly in the form of carbonate minerals) is absent, depleted due to ongoing sulfide oxidation, or when carbonate dissolution is inefficient due to limited contact between the neutralizing and acid-producing minerals. Mining is focused on ore mineral extraction, it is common minerals such as pyrite, ending up as mine waste, which are mainly responsible for ARD generation. Despite promising results, these methods are still only under the development stage and studies are dominated by batch-type laboratory tests focusing on single mineral systems such as pure pyrite. A single mineral system does not consider interactions between minerals in more complex mineral systems, such as waste rock

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