Abstract

Regular features of ground and surface waters affected by drainage from mine waste include their acidity and elevated concentrations of dissolved metals, with their attendant negative effects on drinking water quality and aquatic life. One parameter that aids in buffering these waters against acidity and sustains aquatic life is dissolved inorganic carbon (DIC). In this study, the chemical and isotopic (δ13C) composition of primary calcite and DIC (δ13CDIC) in groundwater and surface waters within and downstream, respectively, of abandoned Cu–W–F skarn tailings at Yxsjöberg, Sweden, were used to trace the biogeochemical processes controlling their respective δ13CDIC signatures. In addition, the δ13C signatures of the inorganic (carbonate) fractions of the tailings were used to verify the formation of secondary carbonates within the tailings. Lower average δ13C values of the carbonate fractions (δ13Ccarb = −2.7‰) relative to those of the primary calcite (δ13C = +0.1‰) from the orebodies from which the tailings originated pointed to the precipitation of secondary carbonates. These lower δ13Ccarb signatures were assumed to represent mixed-source C signals involving isotopically light CO2 from the atmosphere, the degradation of organic matter in the upper part of the tailings and HCO3− from calcite dissolution. The groundwater δ13CDIC values (−12.6‰ to −4.4‰) were far lower than the hypothetical range of values (−4.6‰ to +0.7‰) for primary calcite and secondary carbonate dissolution. These signatures were attributed to carbonate (calcite and secondary carbonate) dissolution and the degradation of dissolved organic carbon (DOC) from various organic sources such as peat underneath the tailings and the surrounding forests. Downstream surface water samples collected in May had low δ13CDIC values (−16‰) and high DOC (14 mg C/L) compared to the groundwater samples. These signatures represented the oxidation of the DOC from the wash out of the mires and forests during the snowmelt and spring flood. The DOC and δ13CDIC values of the surface waters from June to September ranged from 6–15 mg·C/L and −25‰ to −8.6‰, respectively. These signatures were interpreted to reflect mixed C sources, including carbonate dehydration by acidity from Fe3+ hydrolysis due to the mixing of groundwater with surface waters and the subsequent diffusive loss of CO2 (g), aquatic photosynthesis, photooxidation, DOC degradation, as well as microbial respiration. Although the 13CDIC signatures of the downstream surface waters seemed to be seasonally controlled and influenced by variable groundwater contributions, the lack of data with respect to DIC concentrations, coupled with multiple potential biogeochemical processes that could influence the DIC pool and 13CDIC values, made it difficult to identify the major regulating process of the 13CDIC signatures. Therefore, other complimentary isotopes and elemental concentrations are recommended in order to decipher the dominant biogeochemical process.

Highlights

  • The complex biological, chemical and thermal processes of sulphide mineral oxidation, mainly due to their exposure to water and oxygen and the subsequent dissolution of acid-neutralising minerals in mine waste, result in the production of sulphate (SO4 2− ), dissolved metal-(loids) and variable pH drainage, commonly referred to as acid mine drainage (AMD) or neutral mine drainage (NMD) [1].These drainages usually contain toxic and potentially hazardous metal-(loids) such as Co, Cu, Ni, Zn, As, Mo, Sb, Tl and W [2,3]

  • −4.4%) were far lower than the hypothetical range of values (−4.6% to +0.7%) for primary calcite and secondary carbonate dissolution. These signatures were attributed to carbonate dissolution and the degradation of dissolved organic carbon (DOC) from various organic sources such as peat underneath the tailings and the surrounding forests

  • Dissolved inorganic carbon (DIC), which consists of carbon dioxide (CO2 ), carbonic acid (H2 CO3 ), bicarbonate (HCO3 − ) and carbonate (CO3 2− ), plays a very critical biogeochemical role in such mine-impacted surface waters due to its capacity to buffer the pH in these waters

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Summary

Introduction

The complex biological, chemical and thermal processes of sulphide mineral oxidation, mainly due to their exposure to water and oxygen and the subsequent dissolution of acid-neutralising minerals in mine waste, result in the production of sulphate (SO4 2− ), dissolved metal-(loids) and variable pH drainage, commonly referred to as acid mine drainage (AMD) or neutral mine drainage (NMD) [1].These drainages usually contain toxic and potentially hazardous metal-(loids) such as Co, Cu, Ni, Zn, As, Mo, Sb, Tl and W [2,3]. Dissolved inorganic carbon (DIC), which consists of carbon dioxide (CO2 (aq) ), carbonic acid (H2 CO3 ), bicarbonate (HCO3 − ) and carbonate (CO3 2− ), plays a very critical biogeochemical role in such mine-impacted surface waters due to its capacity to buffer the pH in these waters. It provides ecological importance by sustaining organic productivity such as photosynthesis [5] in such waters. The stable carbon isotope composition of DIC (δ13 CDIC ) is non-conservative and the pH-dependent transformation of the various DIC species causes shifts in the DIC pool and the δ13 CDIC

Objectives
Methods
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