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本文引用的文献

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Remediation of chromium(VI) by a methane-oxidizing bacterium.甲烷氧化菌对六价铬的修复。
Environ Sci Technol. 2010 Jan 1;44(1):400-5. doi: 10.1021/es901723c.
2
Bioaugmentation of aerobic microbial granules with Pseudomonas putida carrying TOL plasmid.用携带TOL质粒的恶臭假单胞菌对好氧微生物颗粒进行生物强化。
Chemosphere. 2008 Mar;71(1):30-5. doi: 10.1016/j.chemosphere.2007.10.062.
3
Efficient removal of hexavalent chromium by a tolerant Streptomyces sp. affected by the toxic effect of metal exposure.一株耐受的链霉菌对六价铬的高效去除受金属暴露毒性效应的影响。
J Appl Microbiol. 2007 Dec;103(6):2704-12. doi: 10.1111/j.1365-2672.2007.03510.x.
4
Multimetal resistance and tolerance in microbial biofilms.微生物生物膜中的多金属抗性与耐受性
Nat Rev Microbiol. 2007 Dec;5(12):928-38. doi: 10.1038/nrmicro1774.
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XAS and XPS studies on chromium-binding groups of biomaterial during Cr(VI) biosorption.铬(VI)生物吸附过程中生物材料铬结合基团的X射线吸收光谱(XAS)和X射线光电子能谱(XPS)研究
J Colloid Interface Sci. 2008 Jan 1;317(1):54-61. doi: 10.1016/j.jcis.2007.09.049. Epub 2007 Sep 21.
6
Mechanisms of bacterial resistance to chromium compounds.细菌对铬化合物的耐药机制。
Biometals. 2008 Jun;21(3):321-32. doi: 10.1007/s10534-007-9121-8. Epub 2007 Oct 13.
7
Chromate reduction by Burkholderia cepacia MCMB-821, isolated from the pristine habitat of alkaline crater lake.从碱性火山口湖原始栖息地分离出的洋葱伯克霍尔德菌MCMB-821对铬酸盐的还原作用
Appl Microbiol Biotechnol. 2007 Jun;75(3):627-32. doi: 10.1007/s00253-007-0862-7. Epub 2007 Mar 15.
8
Analysis of novel soluble chromate and uranyl reductases and generation of an improved enzyme by directed evolution.新型可溶性铬酸盐和铀酰还原酶的分析以及通过定向进化产生改良酶。
Appl Environ Microbiol. 2006 Nov;72(11):7074-82. doi: 10.1128/AEM.01334-06.
9
Biodegradation of nitrilotriacetic acid (NTA) and ferric-NTA complex by aerobic microbial granules.好氧微生物颗粒对次氮基三乙酸(NTA)和铁-NTA络合物的生物降解作用
Water Res. 2006 May;40(8):1539-46. doi: 10.1016/j.watres.2006.02.006. Epub 2006 Apr 4.
10
Bio-reduction of soluble chromate using a hydrogen-based membrane biofilm reactor.使用基于氢气的膜生物膜反应器对可溶性铬酸盐进行生物还原。
Water Res. 2006 May;40(8):1634-42. doi: 10.1016/j.watres.2006.01.049. Epub 2006 Mar 27.

颗粒状生物膜固定六价铬及其还原为磷酸铬。

Immobilization of Cr(VI) and its reduction to Cr(III) phosphate by granular biofilms comprising a mixture of microbes.

机构信息

Environmental Sciences Department, Brookhaven National Laboratory, Upton, New York 11973, USA.

出版信息

Appl Environ Microbiol. 2010 Apr;76(8):2433-8. doi: 10.1128/AEM.02792-09. Epub 2010 Feb 19.

DOI:10.1128/AEM.02792-09
PMID:20173073
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC2849200/
Abstract

We assessed the potential of mixed microbial consortia, in the form of granular biofilms, to reduce chromate and remove it from synthetic minimal medium. In batch experiments, acetate-fed granular biofilms incubated aerobically reduced 0.2 mM Cr(VI) from a minimal medium at 0.15 mM day(-1) g(-1), with reduction of 0.17 mM day(-1) g(-1) under anaerobic conditions. There was negligible removal of Cr(VI) (i) without granular biofilms, (ii) with lyophilized granular biofilms, and (iii) with granules in the absence of an electron donor. Analyses by X-ray absorption near edge spectroscopy (XANES) of the granular biofilms revealed the conversion of soluble Cr(VI) to Cr(III). Extended X-ray absorption fine-structure (EXAFS) analysis of the Cr-laden granular biofilms demonstrated similarity to Cr(III) phosphate, indicating that Cr(III) was immobilized with phosphate on the biomass subsequent to microbial reduction. The sustained reduction of Cr(VI) by granular biofilms was confirmed in fed-batch experiments. Our study demonstrates the promise of granular-biofilm-based systems in treating Cr(VI)-containing effluents and wastewater.

摘要

我们评估了以颗粒生物膜形式存在的混合微生物群落的潜力,以还原并从合成基本培养基中去除铬酸盐。在分批实验中,有氧条件下用乙酸喂养的颗粒生物膜以 0.15 毫米/天·克的速度从基本培养基中还原 0.2 毫米/克,而在厌氧条件下以 0.17 毫米/天·克的速度还原。在没有颗粒生物膜的情况下(i)、没有冻干颗粒生物膜的情况下(ii)、没有电子供体的情况下(iii),几乎没有去除 Cr(VI)。X 射线吸收近边光谱(XANES)对颗粒生物膜的分析表明,可溶性 Cr(VI)转化为 Cr(III)。对含铬颗粒生物膜的扩展 X 射线吸收精细结构(EXAFS)分析表明,其与 Cr(III)磷酸盐相似,表明 Cr(III)在微生物还原后与生物量上的磷酸盐固定在一起。在分批进料实验中证实了颗粒生物膜对 Cr(VI)的持续还原。我们的研究表明,基于颗粒生物膜的系统在处理含 Cr(VI)废水和废水方面具有很大的潜力。