首页> 外文期刊>Geochimica et Cosmochimica Acta: Journal of the Geochemical Society and the Meteoritical Society >Dissimilatory bacterial reduction of Al-substituted goethite in subsurface sediments
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Dissimilatory bacterial reduction of Al-substituted goethite in subsurface sediments

机译:地下沉积物中异化细菌还原铝取代针铁矿

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摘要

The microbiologic reduction of a 0.2 to 2.0 μm size fraction of an Atlantic coastal plain sediment (Eatontown) was investigated using a dissimilatory Fe(III)-reducing bacterium (Shewanella putrefaciens, strain CN32) to evaluate minralogic controls on the rate and extent of Fe(III) reduction and the resulting distribution of biogenic Fe(II). Mossbauer spectroscopy and X-ray diffraction (XRD) were used to show that the sedimentary Fe(III) oxide was Al-substituted geothite (13-17% Al) that existed as 1- to 5-μm aggregates of indistinct morphology. Bioreduction experiments were performed in two buffers [HCO_3~-; 1, 4-piperazinedi-ethansulfonic acid (PIPES)] both without and with 2,6-anthraquinone disulfonate (AQDS) as an electron shuttle. The production of biogenic Fe(II) and the distribution of Al (aqueous and sorbed) were followed over time, as was the formation of Fe(II) biominerals and Physical/chemical changes to the goethite. The extent of reduction was comparable in both buffers. The reducibility (rate and extent) was enhanced by AQDS; 9% of dithionite-citrate-bicarbonate (DCB) extractable Fe(III) was reduced without AQDS whereas 15% was reduced in the presence of AQDS. XRD and Mossbauer spectroscopy were used to monitor the disposition of biogenic Fe(II) and changes to the Al-geothite. Fe(II) biomineralization was not evident by XRD. Biomineralization was observed by Mossbauer when sorbed Fe(II) concentrations exceeded a threshold value. The biomineralization products displayed Mossbauer spectra consistent with siderite FeCO_3 (HCO_3~- buffer only) and green rust [Fe_(6-x)~(II)Fe_x~(III)(OH)_(12)]~(x+)[(A~(2-)_(x/2.y)H_2O]~(x-). Adsorption of biogenic Fe(II) to accessory mineral phases (e.g., kaolinite) and bacterial surfaces appeared to limit biomineralization. Al evolved during reduction was sorbed, and extractable Al increased with reduction. XRD analysis indicated that neither crystallite size or the Al content of the geothite was affected by bacterial reduction, i.e., Al release was congruent with Fe(II).
机译:使用异化还原性Fe(III)细菌(Shewanella putrefaciens,CN32株)研究了大西洋沿海平原沉积物(Eatontown)的0.2-2.0μm大小的微生物减少,以评估Fe的速率和程度的矿物学控制(III)还原以及生物型Fe(II)的最终分布。使用Mossbauer光谱和X射线衍射(XRD)表明,沉积的Fe(III)氧化物是Al取代的方铁矿(13-17%Al),以1至5μm的聚集体存在,形态不明显。在两种缓冲液[HCO_3〜-; 1,4-哌嗪二-戊磺酸(PIPES)]既可以作为电子穿梭,也可以作为2,6-蒽醌二磺酸盐(AQDS)使用。随着时间的推移,随着时间的推移,生物成因的Fe(II)的产生和Al的分布(水溶液和吸附态铝),Fe(II)生物矿物的形成以及针铁矿的物理/化学变化也随之变化。两种缓冲液的还原程度均相当。 AQDS增强了还原性(速率和程度);在不使用AQDS的情况下,还原了9%的连二亚硫酸氢盐-碳酸氢盐(DCB)可萃取的Fe(III),而在AQDS的存在下,还原了15%。 XRD和Mossbauer光谱被用来监测生物成因Fe(II)的分布和铝型沸石的变化。 X射线衍射未显示Fe(II)的生物矿化作用。当吸附的Fe(II)浓度超过阈值时,Mossbauer观察到了生物矿化作用。生物矿化产物的Mossbauer光谱与菱铁矿FeCO_3(仅HCO_3〜-缓冲液)和绿锈[Fe_(6-x)〜(II)Fe_x〜(III)(OH)_(12)]〜(x +)[ A〜(2-)_(x / 2.y)H_2O]〜(x-)。生物成因的Fe(II)吸附到辅助矿物相(例如高岭石)和细菌表面似乎限制了生物矿化作用。 XRD分析表明,硅藻土的晶粒尺寸和铝含量均不受细菌还原的影响,即铝的释放与Fe(II)的含量一致。

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