铁(III)和锰(IV)对地下水碳氢化合物生物转化的影响

N. Fisher, Н К Фишер
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引用次数: 1

摘要

根据热力学阶梯,地下水中的微生物一致地使用电子受体——将污染从污染羽流边缘转移到其核心。然而,一些研究人员得出结论,在污染羽流中只能发生污染的产甲烷生物转化或从固相中还原Fe(III)和Mn(IV),并且由于动力学因素,微生物只在污染羽流的边缘使用来自水相的电子受体(O2, NO3-和SO42-)。本研究的目的是确定微生物是否利用Fe(III)和Mn(IV)作为电子受体在黑龙江中河-阿穆尔河流域含水层北部地下水中进行碳氢化合物转化。在研究区域,注意到地下水表面(高达2.5米)的石油碳氢化合物(非水相液体)透镜和高浓度的溶解碳氢化合物(高达1000毫克/升)。采用地球化学指标法对微生物过程进行了原位评价。春夏地下水位上升期间生物地球化学过程最为活跃。季节性升高导致Fe(III)和Mn(IV)进入污染羽流,并激活其还原的微生物过程。微生物大多使用固相的电子受体——Fe(III)和Mn(IV),而不使用水相的NO3、SO42。地下水中HCO3-的形成与Fe(II)、Mn(II)的形成密切相关(r2达0.93),证实了这一点。这说明对地下水自净化起决定性作用的是动力学因素而不是热力学因素;微生物使用目前可用的电子受体。由于微生物污染破坏,地下水中Fe(II)含量最高达100 mg/l, Mn (II) -最高达16 mg/l,分别超过自然本底的4倍和8倍。这也与研究区(阿穆尔河流域)的区域地球化学背景形成Fe和Mn有关。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
The influence of Fe(III) and Mn(IV) on the biotransformation of hydrocarbons in groundwater
According to the thermodynamic ladder, microorganisms in groundwater use electron acceptors consistently – for transformation of pollution from the pollution plume edge to its core. However, some researchers come to the conclusion that only methanogenic biotransformation of pollution or reduction of Fe(III) and Mn(IV) from the solid phase can occur in the plume, and due to the kinetic factor microorganisms use electron acceptors from the aqueous phase (O2, NO3- и SO42-) only on the edge of the pollution plume. The purpose of the research was to determine whether microorganisms use Fe(III) and Mn(IV) as acceptors of electrons for hydrocarbons transformation in groundwater in the northern part of the Middle Heilongjiang-Amur River basin aquifer. In the study area, both lenses of petroleum-hydrocarbons (non-aqueous phase liquids) on the surface of groundwater (up to 2.5 m) and high concentrations of dissolved hydrocarbons (up to 1000 mg/l) are noted. Microbiological processes were assessed in situ by the method of geochemical indicators. The most active biogeochemical processes occurred during the spring-summer rise of groundwater level. The seasonal increasing of level led to the entry of Fe(III) and Mn(IV) into the pollution plume and activation of the microbiological processes of its reduction. Microorganisms mostly use electron acceptors from the solid phase – Fe(III) and Mn(IV), but not NO3, SO42 from the aqueous phase. This is confirmed by the close correlation of HCO3- formation and that of Fe(II) and Mn(II) in groundwater (r2 up to 0.93). This says that for the groundwater self-purification the kinetic factor rather than thermodynamic one is decisive; and microorganisms use electron acceptors that are currently available. As a result of microbiological pollution destruction, the content of Fe(II) in groundwater increased up to 100 mg/l, Mn (II) – up to 16 mg/l, which exceeds the natural background 4 and 8 times, respectively. This was also because the regional geochemical background of the study area (Amur River basin) forms Fe and Mn.
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