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Responses of the Anaerobic Bacterial Community to Addition of Organic C in Chromium(VI)- and Iron(III)-Amended Microcosms

机译:厌氧细菌群落对铬(VI)和铁(III)修饰的微观世界中有机碳添加的响应

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摘要

Chromium (VI) is toxic to microorganisms and can inhibit the biodegradation of organic pollutants in contaminated soils. We used microcosms amended with either glucose or protein (to drive bacterial community change) and Fe(III) (to stimulate iron-reducing bacteria) to study the effect of various concentrations of Cr(VI) on anaerobic bacterial communities. Microcosms were destructively sampled based on microbial activity (measured as evolution of CO2) and analyzed for the following: (i) dominant bacterial community by PCR-denaturing gradient gel electrophoresis (DGGE) of the 16S rRNA gene; (ii) culturable Cr-resistant bacteria; and (iii) enrichment of iron-reducing bacteria of the Geobacteraceae family by real-time PCR. The addition of organic C stimulated the activities of anaerobic communities. Cr(VI) amendment resulted in lower rates of CO2 production in glucose microcosms and a slow mineralization phase in protein-amended microcosms. Glucose and protein amendments selected for different bacterial communities. This selection was modified by the addition of Cr(VI), since some DGGE bands were intensified and new bands appeared in Cr(VI)-amended microcosms. A second dose of Cr(VI), added after the onset of activity, had a strong inhibitory effect when higher levels of Cr were added, indicating that the developing Cr-resistant communities had a relatively low tolerance threshold. Most of the isolated Cr-resistant bacteria were closely related to previously studied Cr-resistant anaerobes, such as Pantoea, Pseudomonas, and Enterobacter species. Geobacteraceae were not enriched during the incubation. The studied Cr(VI)-contaminated soil contained a viable anaerobic bacterial community; however, Cr(VI) altered its composition, which could affect the soil biodegradation potential.
机译:铬(VI)对微生物有毒,可以抑制受污染土壤中有机污染物的生物降解。我们用葡萄糖或蛋白质(驱动细菌群落变化)和Fe(III)(刺激铁还原细菌)修饰的微观世界研究了各种浓度的Cr(VI)对厌氧细菌群落的影响。根据微生物活性(以CO2的释放量衡量)以破坏性方式取样微生物,并进行以下分析:(i)通过16S rRNA基因的PCR变性梯度凝胶电泳(DGGE)形成优势细菌群落; (ii)可培养的抗Cr细菌; (iii)通过实时PCR富集土杆菌科的还原铁细菌。有机碳的添加刺激了厌氧群落的活动。 Cr(VI)修饰剂导致葡萄糖微观世界中较低的CO2产生速率和蛋白质修饰的微观世界中缓慢的矿化阶段。针对不同细菌群落选择的葡萄糖和蛋白质修饰剂。由于增加了某些DGGE谱带,并且在Cr(VI)修正的微观世界中出现了新的谱带,因此通过添加Cr(VI)修改了此选择。在活动开始后添加第二剂量的Cr(VI),当添加更高水平的Cr时具有很强的抑制作用,表明正在发展的Cr抗性群落的耐受性阈值相对较低。大多数分离的抗Cr细菌与先前研究的抗Cr厌氧菌(如泛菌,假单胞菌和肠杆菌)密切相关。孵育过程中土杆菌科没有富集。被研究的被六价铬污染的土壤含有一个可行的厌氧细菌群落。但是,Cr(VI)改变了其组成,这可能会影响土壤的生物降解潜力。

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