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本文引用的文献

1
Introduction of a de novo bioremediation activity into anaerobic granular sludge using the dechlorinating bacterium DCB-2.利用脱氯细菌DCB-2将一种全新的生物修复活性引入厌氧颗粒污泥。
Antonie Van Leeuwenhoek. 1996 Jan;69(1):61-6. doi: 10.1007/BF00641612.
2
Desulfitobacterium sp. strain PCE1, an anaerobic bacterium that can grow by reductive dechlorination of tetrachloroethene or ortho-chlorinated phenols.脱氯脱硫杆菌属菌株PCE1,一种能够通过四氯乙烯或邻氯酚的还原脱氯作用生长的厌氧细菌。
Arch Microbiol. 1996 Feb;165(2):132-40. doi: 10.1007/s002030050308.
3
Tetrachloroethene metabolism of Dehalospirillum multivorans.多噬脱卤螺旋菌的四氯乙烯代谢
Arch Microbiol. 1994;162(4):295-301. doi: 10.1007/BF00301854.
4
Reductive dehalogenation as a respiratory process.还原脱卤作用作为一种呼吸过程。
Antonie Van Leeuwenhoek. 1994;66(1-3):239-46. doi: 10.1007/BF00871642.
5
Biological reductive dechlorination of tetrachloroethylene and trichloroethylene to ethylene under methanogenic conditions.在产甲烷条件下,四氯乙烯和三氯乙烯生物还原脱氯生成乙烯。
Appl Environ Microbiol. 1989 Sep;55(9):2144-51. doi: 10.1128/aem.55.9.2144-2151.1989.
6
Reductive dechlorination of high concentrations of tetrachloroethene to ethene by an anaerobic enrichment culture in the absence of methanogenesis.在不发生甲烷生成的情况下,通过厌氧富集培养将高浓度四氯乙烯还原脱氯为乙烯。
Appl Environ Microbiol. 1991 Aug;57(8):2287-92. doi: 10.1128/aem.57.8.2287-2292.1991.
7
Complete biological reductive transformation of tetrachloroethene to ethane.四氯乙烯完全生物还原转化为乙烷。
Appl Environ Microbiol. 1992 Jun;58(6):1996-2000. doi: 10.1128/aem.58.6.1996-2000.1992.
8
Introduction of a de novo bioremediation ability, aryl reductive dechlorination, into anaerobic granular sludge by inoculation of sludge with Desulfomonile tiedjei.通过用蒂氏脱硫单胞菌接种污泥,将一种全新的生物修复能力——芳基还原脱氯作用引入厌氧颗粒污泥中。
Appl Environ Microbiol. 1992 Nov;58(11):3677-82. doi: 10.1128/aem.58.11.3677-3682.1992.

通过将多氯代螺旋菌纳入颗粒污泥来提高上流式厌氧污泥床反应器的脱氯性能。

Improved Dechlorinating Performance of Upflow Anaerobic Sludge Blanket Reactors by Incorporation of Dehalospirillum multivorans into Granular Sludge.

作者信息

Hörber C, Christiansen N, Arvin E, Ahring BK

机构信息

Department of Environmental Science and Engineering, Technical University of Denmark, 2800 Lyngby, Denmark.

出版信息

Appl Environ Microbiol. 1998 May 1;64(5):1860-3. doi: 10.1128/AEM.64.5.1860-1863.1998.

DOI:10.1128/AEM.64.5.1860-1863.1998
PMID:9572963
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC106242/
Abstract

Dechlorination of tetrachloroethene, also known as perchloroethylene (PCE), was investigated in an upflow anaerobic sludge blanket (UASB) reactor after incorporation of the strictly anaerobic, reductively dechlorinating bacterium Dehalospirillum multivorans into granular sludge. This reactor was compared to the reference 1 (R1) reactor, where the granules were autoclaved to remove all dechlorinating abilities before inoculation, and to the reference 2 (R2) reactor, containing only living granular sludge. All three reactors were fed mineral medium containing 3 to 57 µM PCE, 2 mM formate, and 0.5 mM acetate and were operated under sterile conditions. In the test reactor, an average of 93% (mole/mole) of the effluent chloroethenes was dichloroethene (DCE), compared to 99% (mole/mole) in the R1 reactor. The R2 reactor, with no inoculation, produced only trichloroethene (TCE), averaging 43% (mole/mole) of the effluent chloroethenes. No dechlorination of PCE was observed in an abiotic control consisting of sterile granules without inoculum. During continuous operation with stepwise-reduced hydraulic retention times (HRTs), both the test reactor and the R1 reactor showed conversion of PCE to DCE, even at HRTs much lower than the reciprocal maximum specific growth rate of D. multivorans, indicating that this bacterium was immobilized in the living and autoclaved granular sludge. In contrast, the R2 reactor, with no inoculation of D. multivorans, only converted PCE to TCE under the same conditions. Immobilization could be confirmed by using fluorescein-labeled antibody probes raised against D. multivorans. In granules obtained from the R1 reactor, D. multivorans grew mainly in microcolonies located in the centers of the granules, while in the test reactor, the bacterium mainly covered the surfaces of granules.

摘要

在将严格厌氧的还原性脱氯细菌多食脱卤螺旋菌引入颗粒污泥后,研究了在升流式厌氧污泥床(UASB)反应器中四氯乙烯(也称为全氯乙烯,PCE)的脱氯情况。将该反应器与参考1(R1)反应器进行比较,在参考1反应器中,颗粒在接种前经过高压灭菌以去除所有脱氯能力;还与参考2(R2)反应器进行比较,参考2反应器仅含有活性颗粒污泥。所有三个反应器均加入含有3至57 μM PCE、2 mM甲酸盐和0.5 mM乙酸盐的矿物培养基,并在无菌条件下运行。在测试反应器中,流出物中氯代乙烯的平均93%(摩尔/摩尔)为二氯乙烯(DCE),而在R1反应器中为99%(摩尔/摩尔)。未接种的R2反应器仅产生三氯乙烯(TCE),平均占流出物中氯代乙烯的43%(摩尔/摩尔)。在由无菌颗粒且未接种的非生物对照中未观察到PCE的脱氯现象。在逐步降低水力停留时间(HRT)的连续运行过程中,测试反应器和R1反应器均显示PCE转化为DCE,即使在远低于多食脱卤螺旋菌最大比生长速率倒数的HRT下也是如此,这表明该细菌固定在活性和经高压灭菌的颗粒污泥中。相比之下,未接种多食脱卤螺旋菌的R2反应器在相同条件下仅将PCE转化为TCE。使用针对多食脱卤螺旋菌产生的荧光素标记抗体探针可以证实固定化。在从R1反应器获得的颗粒中,多食脱卤螺旋菌主要在位于颗粒中心的微菌落中生长,而在测试反应器中,该细菌主要覆盖颗粒表面。