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Impact of natural organic matter coatings on the microbial reduction of iron oxides

机译:天然有机物质涂料对铁氧化物微生物减少的影响

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Iron (Fe) oxyhydroxides are important constituents of the soil mineral phase known to stabilize organic matter (OM) under oxic conditions. In an anoxic milieu, however, these Fe-organic associations are exposed to microbial reduction, releasing OM into soil solution. At present, only few studies have addressed the influence of adsorbed natural OM (NOM) on the reductive dissolution of Fe oxyhydroxides. This study therefore examined the impact of both the composition and concentration of adsorbed NOM on microbial Fe reduction with regard to (i) electron shuttling, (ii) complexation of Fe(II, III), (iii) surface site coverage and/or pore blockage, and (iv) aggregation. Adsorption complexes with varying carbon loadings were synthesized using different Fe oxyhydroxides (ferrihydrite, lepidocrocite, goethite, hematite, magnetite) and NOM of different origin (extracellular polymeric substances from Bacillus subtilis, OM extracted from soil Oi and Oa horizons). The adsorption complexes were characterized by X-ray diffraction (XRD), Fourier transform infrared spectroscopy (FTIR), X-ray photoelectron spectroscopy (XPS), N-2 gas adsorption, electrophoretic mobility and particle size measurements, and OM desorption. Incubation experiments under anaerobic conditions were conducted for 16 days comparing two different strains of dissimilatory Fe(III)-reducing bacteria (Shewanella putrefaciens, Geobacter metallireducens). Mineral transformation during reduction was assessed via XRD and FTIR. Microbial reduction of the pure Fe oxyhydroxides was controlled by the specific surface area (SSA) and solubility of the minerals. For Shewanella putrefaciens, the Fe reduction of adsorption complexes strongly correlated with the concentration of potentially usable electron-shuttling molecules for NOM concentrations 2 mg C L-1, whereas for Geobacter metallireducens, Fe reduction depended on the particle size and thus aggregation of the adsorption complexes. These diverging results suggest
机译:铁(Fe)羟基氧化物是已知的土壤矿物相的重要组成部分,以稳定氧体条件下有机物质(OM)。然而,在缺氧内部,这些Fe-Informaseciacations暴露于微生物还原,释放成土壤溶液。目前,只有少数研究已经解决了吸附的自然OM(NOM)对Fe羟基氧化物的还原溶解的影响。因此,该研究研究了吸附的NOM对微生物Fe减少的组成和浓度对(i)电子穿梭的影响,(ii)的Fe(II)表面位点覆盖和/或孔隙的络合物的影响堵塞和(iv)聚合。使用不同的Fe羟基氧化物(Ferrihydrite,Lepidocroce,Getethite,赤铁矿,磁铁矿)和不同源(来自枯草芽孢杆菌的细胞外聚合物物质,OM从土壤OI和OA Horizo​​ ns提取的OM提取的具有不同碳含量的吸附复合物。吸附复合物的特征在于X射线衍射(XRD),傅里叶变换红外光谱(FTIR),X射线光电子能谱(XPS),N-2气体吸附,电泳迁移率和粒度测量,以及Om解吸。对厌氧条件下的孵育实验进行16天,比较两种不同的含量含量的含量(III)菌株(III)细菌(Shewanella Putrefaciens,Geobacter金属)。通过XRD和FTIR评估还原过程中的矿物转化。纯Fe羟基氧化物的微生物还原由比表面积(SSA)和矿物质的溶解度控制。对于Shewanella putrefaciens,对吸附复合物的Fe减少与NOM浓度的潜在可用的电子穿梭分子的浓度强烈相关。 2 Mg C L-1,而对于Geobacter金属,Fe降低依赖于粒径并因此依赖于吸附复合物的聚集。这些发散结果表明

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