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Iron (III) bioavailability during anaerobic biodegradation of organic pollutants in groundwater

机译:铁(III)在地下水中有机污染物的厌氧生物降解期间的生物利用度

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The biodegradation of organic pollutants coupled to iron(III) reduction is an important and frequently observed process in the natural attenuation of anaerobic plumes in contaminated aquifers. However, microbial access to this oxidising capacity is limited since iron(III) mineral phases cannot be transported to or across bacterial cell walls. A brief review of current literature on iron reduction in groundwater reveals three hypotheses for electron transfer between microbe and iron(III) mineral surfaces. Iron reducing activity is 1) linked to attached growth, 2) depends on transport of dissolved iron(III) from the groundwater to the cell surface before enzymatic reduction and 3) electron transfer between the cell membrane and iron(III) sites is mediated by electron shuttles. This conceptual framework suggests that prediction and enhancement of the potential for natural attenuation by microbial iron(III) reduction will require assessment of the relative importance and interaction of cell wall physiology, the physical chemistry of cell-mineral surface interactions as well as the general geochemistry of the groundwater environment.
机译:结合铁(III)还原的有机污染物的生物降解是污染含水层中厌氧羽毛的自然衰减中的重要且经常观察的过程。然而,对于这种氧化能力的微生物进入是受限制的,因为铁(III)矿物相不能于或穿过细菌细胞壁。关于地下水的铁还原的目前文献的简要介绍了三个假设用于微生物和铁(III)矿物表面的电子转移。氧化铁还原活性为1)连接到连接的生长,2)取决于从地下水到酶促的溶解铁(III)的运输到酶促还原之前的细胞表面,并且通过介导所述细胞膜和铁(III)位点之间的电子转移电子班车。这种概念框架表明,通过微生物铁(III)减少的自然衰减潜力的预测和增强将需要评估细胞壁生理学,细胞矿物表面相互作用的物理化学和地球化学的相对重要性和相互作用。地下水环境。

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