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以不同Fe(III)相作为末端电子受体时,嗜金属还原地杆菌厌氧氧化甲苯过程中的碳和氢同位素分馏

Carbon and hydrogen isotope fractionation during anaerobic toluene oxidation by Geobacter metallireducens with different Fe(III) phases as terminal electron acceptors.

作者信息

Tobler Nicole B, Hofstetter Thomas B, Schwarzenbach René P

机构信息

Institute of Biogeochemistry and Pollutant Dynamics, ETH Zurich, 8092 Zurich, Switzerland.

出版信息

Environ Sci Technol. 2008 Nov 1;42(21):7786-92. doi: 10.1021/es800046z.

DOI:10.1021/es800046z
PMID:19031861
Abstract

Microbial oxidation of BTEX compounds under iron-reducing conditions is an important attenuation process for fuel-contaminated sites. We evaluated the use of compound-specific isotope analysis for the identification and quantification of anaerobic toluene oxidation by Geobacter metallireducens. 13C and 2H enrichment of toluene was measured in laboratory batch systems and varied significantly for a solid vs a dissolved Fe(III) phase provided as terminal electron acceptor. 13C enrichment factors (epsilonC) in suspensions of a solid Fe(III) phase were between -1.0 and -1.3% per hundred, whereas epsilonC-values were significantly higher in solutions of Fe(lll) citrate (-2.9 to -3.6% per hundred. The same trend was observed for 2H fractionation. Solid phase reduction resulted in an epsilonH-value of -34.6 +/- 0.9% per hundred, compared to -98.4 +/- 3.0% per hundred for the reduction of dissolved Fe(lll). The linear correlation of delta(2)H vs. delta(13)C during toluene oxidation resulted in nearly identical slopes for both systems, confirming that the reaction mechanism, that is enzymatic methyl-group oxidation, was the same. We hypothesize that smaller 2H and 13C fractionation in suspensions is due to toluene transport limitations to cells of G. metallireducens at surfaces of solid Fe(III) phases. Enrichment factors determined in Fe(III) mineral suspensions should be more representative for anaerobic toluene degradation owing to the abundance of solid Fe(III) in soils and aquifers.

摘要

在铁还原条件下,微生物对BTEX化合物的氧化是燃料污染场地的一个重要衰减过程。我们评估了使用化合物特异性同位素分析来鉴定和定量嗜铁地杆菌对甲苯的厌氧氧化。在实验室批次系统中测量了甲苯的13C和2H富集情况,对于作为终端电子受体提供的固相和溶解的Fe(III)相,其变化显著。固相Fe(III)相悬浮液中的13C富集因子(εC)为每百-1.0%至-1.3%,而柠檬酸铁(III)溶液中的εC值显著更高(每百-2.9%至-3.6%)。对于2H分馏也观察到相同趋势。固相还原导致εH值为每百-34.6±0.9%,而溶解的Fe(III)还原的εH值为每百-98.4±3.0%。甲苯氧化过程中δ(2)H与δ(13)C的线性相关性导致两个系统的斜率几乎相同,证实了反应机制,即酶促甲基氧化,是相同的。我们推测悬浮液中较小的2H和13C分馏是由于在固相Fe(III)相表面,甲苯向嗜铁地杆菌细胞的运输受限。由于土壤和含水层中固相Fe(III)的丰富性,在Fe(III)矿物悬浮液中确定的富集因子对于厌氧甲苯降解应该更具代表性。

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