蒙古额尔登涅特矿区溶解硫酸盐硫氧同位素系统及硫化物氧化剂的相对贡献。

IF 4.3 3区 环境科学与生态学 Q3 ENGINEERING, ENVIRONMENTAL
Duk-Min Kim, Bayartungalag Batsaikhan, Dae-Gyu Im, Jae-Hoon Choi, Hyeon-Soo Seo, Bayartogtokh Buyankhishig, Seong-Taek Yun
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引用次数: 0

摘要

溶解的硫酸盐是矿区的主要污染物,通常是由分子氧或铁(III)氧化硫化物产生的。由于Fe(III)氧化硫化物的速度要快得多,因此它更有效地提高了SO42-浓度。本文对蒙古额尔德涅特矿区地下水和地表水中的δ34SSO4、δ18OSO4、δ18OH2O和δ2HH2O进行了分析。根据δ18OSO4和δ18OH2O,推测了铁(III)作为黄铁矿氧化剂的电位分数。理论和先前报道的最小分数似乎限制了Fe(III)贡献的较低范围,而硫酸盐还原和石膏溶解可能降低某些样品中的表观分数。此外,石膏的沉淀似乎限制了SO42-浓度的上限,而荧光盐的溶解可能会增加SO42-浓度。在排除可能受这些过程影响的样品后,作为氧化剂的Fe(III)的电位分数与SO42-浓度之间的正相关关系仍然很明显。这些结果表明,铁(III)介导的氧化在控制采矿环境中硫酸盐浓度方面具有潜在的重要性。此外,当适当考虑其他地球化学过程时,δ18OSO4和δ18OH2O的组合使用为阐明此类环境中硫化物氧化机制提供了一个系统的框架。此外,整个采矿环境中作为氧化剂的Fe(III)电位分数与SO42-浓度之间关系的变化可能为特定地点的地球化学过程(如石膏溶解和硫酸盐还原)提供证据。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Sulfur and oxygen isotopic systematics of dissolved sulfate and relative contributions of sulfide oxidants in the Erdenet mining region, Mongolia.

Dissolved sulfate, a major contaminant in mining areas, is generally produced by the oxidation of sulfides by either molecular oxygen or Fe(III). Because Fe(III) oxidizes sulfides much more rapidly, it contributes more effectively to elevated SO42- concentrations. This study analyzed δ34SSO4, δ18OSO4, δ18OH2O, and δ2HH2O in groundwater and surface water from the Erdenet mining region, Mongolia. The potential fraction of Fe(III) as the oxidant of pyrite was inferred based on δ18OSO4 and δ18OH2O. Theoretical and previously reported minimum fractions appear to constrain the lower range of Fe(III) contributions, whereas sulfate reduction and gypsum dissolution may reduce the apparent fractions in some samples. In addition, gypsum precipitation appears to limit the upper range of SO42- concentrations, while the dissolution of efflorescent salts may increase SO42- concentrations. After excluding samples potentially influenced by these processes, a positive relationship between the potential fraction of Fe(III) as the oxidant and SO42- concentration remains evident. These results suggest the potential importance of Fe(III)-mediated oxidation in controlling sulfate concentrations in mining environments. Furthermore, when additional geochemical processes are appropriately accounted for, the combined use of δ18OSO4 and δ18OH2O provides a systematic framework for elucidating the mechanisms of sulfide oxidation in such environments. Additionally, variations in the relationship between the potential fraction of Fe(III) as the oxidant and SO42- concentration across mining environments may provide evidence for site-specific geochemical processes, such as gypsum dissolution and sulfate reduction.

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来源期刊
Environmental Geochemistry and Health
Environmental Geochemistry and Health 环境科学-工程:环境
CiteScore
8.00
自引率
4.80%
发文量
279
审稿时长
4.2 months
期刊介绍: Environmental Geochemistry and Health publishes original research papers and review papers across the broad field of environmental geochemistry. Environmental geochemistry and health establishes and explains links between the natural or disturbed chemical composition of the earth’s surface and the health of plants, animals and people. Beneficial elements regulate or promote enzymatic and hormonal activity whereas other elements may be toxic. Bedrock geochemistry controls the composition of soil and hence that of water and vegetation. Environmental issues, such as pollution, arising from the extraction and use of mineral resources, are discussed. The effects of contaminants introduced into the earth’s geochemical systems are examined. Geochemical surveys of soil, water and plants show how major and trace elements are distributed geographically. Associated epidemiological studies reveal the possibility of causal links between the natural or disturbed geochemical environment and disease. Experimental research illuminates the nature or consequences of natural or disturbed geochemical processes. The journal particularly welcomes novel research linking environmental geochemistry and health issues on such topics as: heavy metals (including mercury), persistent organic pollutants (POPs), and mixed chemicals emitted through human activities, such as uncontrolled recycling of electronic-waste; waste recycling; surface-atmospheric interaction processes (natural and anthropogenic emissions, vertical transport, deposition, and physical-chemical interaction) of gases and aerosols; phytoremediation/restoration of contaminated sites; food contamination and safety; environmental effects of medicines; effects and toxicity of mixed pollutants; speciation of heavy metals/metalloids; effects of mining; disturbed geochemistry from human behavior, natural or man-made hazards; particle and nanoparticle toxicology; risk and the vulnerability of populations, etc.
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