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首页> 外文期刊>Environmental Science & Technology >Stable Carbon Isotope Fractionation of Chloroethenes by Dehalorespiring Isolates
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Stable Carbon Isotope Fractionation of Chloroethenes by Dehalorespiring Isolates

机译:脱卤呼吸分离物对氯丁酮的稳定碳同位素分馏

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Stable carbon isotope fractionation during the reductive dechlorination of chloroethenes by two bacterial strains that dechlorinate to ethene, Dehalococcoides ethenogenes 195 and Dehalococcoides sp. strain BAV1 as well as Sulfurospirillum multivorans and Dehalobacter restrictus strain PER-K23, isolates that do not dechlorinate past DCE, are reported. Fractionation by a Dehalococcoides-containing enrichment culture is also measured for comparison to the isolates. All data adequately fit the Rayleigh model and results are presented as enrichment factors. For strain 195, the measured enrichment factors were -9.6 ± 0.4, -21.1 ± 1.8, and -5.8 ± 0.5 when degrading TCE, cDCE, and 1,1-DCE, respectively. Strain BAV1 exhibited enrichment factors of -16.9 ± 1.4, -8.4 ± 0.3, -21.4 ± 0.9, and -24.0 ± 2.0 for cDCE, 1,1-DCE, tDCE, and VC, respectively. The surprisingly large differences in enrichment factors caused by individual reductases (RDases) reducing different chloroethenes is likely the result of chemical structure differences among the chloroethenes. For TCE reduction, S, multivorans and D. restrictus strain PER-K23 exhibited enrichment factors of -16.4 ± 1.5 and -3.3 ± 0.3, respectively. While all of the organisms studied here utilize RDases that require corrinoid cofactors, the biotic TCE enrichment factors varied widely from those reported for the abiotic cobalamin-catalyzed reaction, indicating that additional factors affect the extent of fractionation in these biological systems. The enrichment factors measured for the Dehalococcoides-containing enrichment culture did not match well with those from any of the isolates, demonstrating the inherent difficulties in predicting fractionation factors of undefined communities. Although compound-specific isotope fractionation is a powerful tool for evaluating the progress of in situ bioremediation in the field, given the wide range of enrichment factors associated with functionally similar and phylogenetically diverse organisms, caution must be exercised when applying enrichment factors for the interpretation of dechlorination data.
机译:由两种脱氯为乙烯的细菌菌株对氯乙烯进行还原性脱氯过程中的稳定碳同位素分馏:Dehalococcoides ethenogenes 195和Dehalococcoides sp。据报道,菌株BAV1以及多重硫螺旋螺菌和限制性脱氢杆菌PER-K23菌株,这些菌株不会在DCE之前脱氯。还测量了含有脱卤球菌的富集培养物的分级分离,以与分离物进行比较。所有数据都完全适合瑞利模型,结果以富集因子表示。对于菌株195,降解TCE,cDCE和1,1-DCE时,测得的富集因子分别为-9.6±0.4,-21.1±1.8和-5.8±0.5。对于cDCE,1,1-DCE,tDCE和VC,菌株BAV1的富集因子分别为-16.9±1.4,-8.4±0.3,-21.4±0.9和-24.0±2.0。由还原不同氯乙烯的单个还原酶(RDase)引起的富集因子差异出乎意料的巨大差异,很可能是这些氯乙烯之间化学结构差异的结果。为了降低TCE,S,杂菌和限制链霉菌PER-K23的富集因子分别为-16.4±1.5和-3.3±0.3。尽管此处研究的所有生物均利用了需要类胡萝卜素辅助因子的RDase,但生物TCE富集因子与非生物钴胺素催化反应的报道差异很大,这表明其他因素会影响这些生物系统中的分级分离程度。对于含Dehaloccocoides的富集培养物测得的富集因子与任何分离物中的富集因子均不匹配,这说明了预测不确定社区的分离因子时存在的固有困难。尽管化合物特异性同位素分级分离是评估该领域原位生物修复进展的有力工具,但鉴于与功能相似和系统发育多样性的生物相关的多种富集因子,在应用富集因子来解释生物多样性时必须谨慎行事。脱氯数据。

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