中性pH砂岩含水层沉积物中含微量元素黄铁矿的微生物介导好氧氧化作用

IF 3.5 Q3 ENGINEERING, ENVIRONMENTAL
Lisa Haas, Matthew Ginder-Vogel, James J. Zambito, David Hart and Eric E. Roden
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引用次数: 0

摘要

黄铁矿(FeS2)是地球上最丰富的硫化物矿物,是现代和远古沉积物中重要的铁和硫储层。黄铁矿在陆地地下的氧化通常与地下水 pH 值降低和向溶液释放微量元素有关。虽然微生物活动在黄铁矿氧化过程中的核心作用在酸性矿山/岩石排水和其他低 pH 值(如 pH 值为 2)环境中已得到很好的理解,但在中性 pH 值条件下,微生物介导黄铁矿氧化的潜力还没有得到很好的理解。在这里,我们展示了有氧微生物新陈代谢促进美国威斯康星州 Trempealeau 县寒武纪砂岩中含微量元素黄铁矿环中性 pH 氧化的潜力。微生物活动使含黄铁矿的还原沉积物中硫酸盐释放(黄铁矿氧化的直接测量指标)的速度和程度加快了约 5 倍。在含有有限碳酸盐(白云石)缓冲能力的微生态系统中,pH 值降至 3。黄铁矿氧化产生的酸溶解碳酸盐和/或钙铝硅酸盐后,钙和镁与硫酸盐一起按比例释放到溶液中。当黄铁矿氧化产生的酸量超过系统缓冲能力时,地质材料中的金属就会有选择性地释放出来。在非生物反应器中,痕量金属没有明显释放,黄铁矿氧化的速率要低得多。这些发现表明,与含黄铁矿地质构造接触的地下水中含有能够加速这些地质构造中原生黄铁矿氧化的微生物。一项反应迁移建模工作表明,微生物活动导致黄铁矿氧化率增加几倍,会对含氧地下水流入先前还原地质层的短期反应产生重大影响。我们的研究结果对控制含黄铁矿地质层内饮用水井的低 PH 值条件和相关地下水质量变化具有重要意义。
本文章由计算机程序翻译,如有差异,请以英文原文为准。

Microbially-mediated aerobic oxidation of trace element-bearing pyrite in neutral-pH sandstone aquifer sediments†

Microbially-mediated aerobic oxidation of trace element-bearing pyrite in neutral-pH sandstone aquifer sediments†

Pyrite (FeS2) is the most abundant sulfide mineral on Earth and represents a significant reservoir of iron and sulfur in modern and ancient sediments. Oxidation of pyrite in the terrestrial subsurface is commonly associated with lowering of groundwater pH and release of constituent trace elements to solution. Although the central role of microbial activity in pyrite oxidation is well understood in acid mine/rock drainage and other low-pH (e.g. pH < 2) environments, the role of microorganisms in mediating pyrite oxidation under circumneutral pH conditions is not well understood. Here we demonstrate the potential for aerobic microbial metabolism to promote circumneutral pH oxidation of trace element-bearing pyrite in Cambrian-age sandstones from Trempealeau County, WI (USA). Microbial activity accelerated ca. 2–5 fold the rate and extent of sulfate release (a direct measure of pyrite oxidation) from reduced pyrite-bearing sediments. pH values dropped to 3 in biotic microcosms which contained limited carbonate (dolomite) buffering capacity. The overall surface area-specific rate constant for pyrite oxidation inferred from batch reaction modeling of these microcosms (10−7.8 mol m−2 s−1) was ca. 25-fold higher than for the corresponding abiotic reactors (10−9.2 mol m−2 s−1). Calcium and magnesium were proportionally released to solution with sulfate as a result of carbonate and/or Ca-aluminosilicate dissolution by acid generated from pyrite oxidation. When the amount of acid from pyrite oxidation exceeded the system buffering capacity, metals were selectively released from the geological material. No significant release of trace metals took place in abiotic reactors, which showed much lower rates of pyrite oxidation. These findings suggest that groundwaters in contact with pyrite-containing geological formations contain microorganisms capable of accelerating the oxidation of native pyrite in those formations. Analysis of microbial community composition in the microcosms by 16S rRNA gene amplicon sequencing showed enrichment in organisms related to taxa associated with chemolithotrophic metabolism (Candidatus Tenderia electrophaga, Thioprofundum lithophicum, and Thiobacillus thioparus) from background levels (<2%) to up to 40% of total sequence reads. A reactive transport modeling exercise demonstrated how microbial acceleration of pyrite oxidation could have a crucial, near-term (<10 years) impact on pH decline and trace element release in response to influx of oxygenated groundwater into previously reduced geological strata. Our results have key implications for controls on the onset of low-pH conditions and associated changes in groundwater quality in drinking water wells located within pyrite-bearing geological formations.

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