首页> 外文期刊>Journal of Geophysical Research. Biogeosciences >Experimental inflow of groundwater induces a “biogeochemical regime shift” in iron-rich and acidic sediments
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Experimental inflow of groundwater induces a “biogeochemical regime shift” in iron-rich and acidic sediments

机译:实验性地下水流入在富含铁和酸性的沉积物中引起“生物地球化学态转变”

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In acid mine drainage (AMD) polluted lakes, sediments may show a stable iron- or sulphate-reducing regime. We tested the hypothesis that increased inflow of groundwater can trigger a shift between these regimes. Schwertmannite-bearing sediment, rich in iron (40–43%), sulphur (2.5%), and carbon (4.5%), was sampled from an acidic mine lake, and percolated (0, 5, and 20 L m~-2 d~-1) with two solutions (1/1 mmol L~-1 versus 10/15 mmol L~-1 sulphate/ferrous iron, pH 5) in sediment columns. A dissolved organic carbon (DOC) source was added after 46 days (~2.5 mmol C L~-1) to ease the carbon limitation of reductive processes. The sediment remained in an iron-reducing and acidic regime during percolation without DOC. Percolation at a high rate and addition of DOC raised pH values in schwertmannite-rich layers from 2.8 to 4.5–5. Schwertmannite transformation to goethite partly accelerated by a factor of >2 but effectively buffered proton consumption only at the low percolation rate. Input of dissolved ferrous iron and sulphate reduced the mobilization of ferrous iron from the sediment. With pH increase, iron reduction slowed relative to CO2 production, sulphate was reduced, and iron sulphides were formed. Input of alkalinity and electron donors by percolation thus shifted the biogeochemical regime from iron to sulphate reduction. Similar regime shifts can be expected for other sediments containing immobile proton or redox buffers when exposed to the advective input of alkalinity and acidity, or electron acceptors and donors.
机译:在酸性矿山排水(AMD)污染的湖泊中,沉积物可能显示出稳定的铁或硫酸盐还原态。我们检验了一个假设,即地下水流入量增加会触发这些制度之间的转换。从酸性矿山湖中取样并富含铁(40-43%),硫(2.5%)和碳(4.5%)的含Schwertmannite的沉积物,并进行了渗滤(0、5和20 L m〜-2 d〜-1)在沉淀柱中使用两种溶液(1/1 mmol L〜-1与10/15 mmol L〜-1硫酸盐/亚铁,pH 5)。 46天后(〜2.5 mmol C L〜-1)添加了溶解的有机碳(DOC)源,以缓解还原过程的碳限制。在没有DOC的渗滤过程中,沉积物保持在还原铁和酸性状态。高渗透速率和DOC的添加使富含schwertmannite的层的pH值从2.8提高到4.5-5。 Schwertmannite向针铁矿的转变部分以> 2的速度加速,但仅在低渗滤速率下有效地缓冲了质子的消耗。溶解的亚铁和硫酸盐的输入减少了沉积物中亚铁的迁移。随着pH值的增加,铁的还原相对于CO2的产生减慢,硫酸盐被还原,形成硫化铁。通过渗滤作用输入的碱度和电子给体将生物地球化学过程从铁还原为硫酸盐还原。当暴露于碱度和酸度的对流输入或电子受体和施主时,对于含有固定质子或氧化还原缓冲液的其他沉积物,也可能会发生类似的变化。

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