نتایج جستجو برای: anaerobic denitrifying bacteria

تعداد نتایج: 204290  

2015
Zhang Bin Xue Bin Qiu Zhigang Chen Zhiqiang Li Junwen Gong Taishi Zou Wenci Wang Jingfeng

Denitrifying capability of glycogen accumulating organisms (GAOs) has received great attention in environmental science and microbial ecology. Combining this ability with granule processes would be an interesting attempt. Here, a laboratory-scale sequencing batch reactor (SBR) was operated to enrich GAOs and enable sludge granulation. The results showed that the GAO granules were cultivated suc...

2018
Blas Blázquez Manuel Carmona Eduardo Díaz

Alkylbenzenes, such as toluene and m-xylene, are an important class of contaminant hydrocarbons that are widespread and tend to accumulate in subsurface anoxic environments. The peripheral pathway for the anaerobic oxidation of toluene in bacteria consists of an initial activation catalyzed by a benzylsuccinate synthase (encoded by bss genes), and a subsequent modified β-oxidation of benzylsucc...

2003
Randhir S. Makkar Menka Mittal Karl J. Rockne

We have previously reported on anaerobic pure cultures that degrade naphthalene in the strict absence of oxygen. One of these pure cultures NAP-3 was phylogenetically most closely related to Pseudomonas stutzeri based on 16S rDNA sequences. Further studies in our laboratory have shown that the degradation of naphthalene was slow or nearly absent when volatile fatty acids (VFAs) were not present...

2015
Anna Hanke Jasmine Berg Theresa Hargesheimer Halina E. Tegetmeyer Christine E. Sharp Marc Strous

In coastal marine sediments, denitrification and fermentation are important processes in the anaerobic decomposition of organic matter. Microbial communities performing these two processes were enriched from tidal marine sediments in replicated, long term chemostat incubations at 10 and 25°C. Whereas denitrification rates at 25°C were more or less stable over time, at 10°C denitrification activ...

Journal: :Applied and environmental microbiology 1988
E P Kuhn J Zeyer P Eicher R P Schwarzenbach

Toluene and m-xylene were rapidly mineralized in an anaerobic laboratory aquifer column operated under continuous-flow conditions with nitrate as an electron acceptor. The oxidation of toluene and m-xylene was coupled with the reduction of nitrate, and mineralization was confirmed by trapping 14CO2 evolved from 14C-ring-labeled substrates. Substrate degradation also took place when nitrous oxid...

2014
Kristina Rathsack Jörg Böllmann Marion Martienssen

Bacteria capable of denitrification play a significant role in the nitrogen cycle of freshwater ecosystems. By metabolizing nitrogen compounds they e.g. counteract the eutrophication of natural waters. To get detailed insights into the in situ turnover rates of nitrogen a reliable tool of quantification for active microorganisms is essential. In the present investigation, quantification capabil...

Journal: :Journal of bacteriology 2011
Lawrence Feinberg Justine Foden Trisha Barrett Karen Walston Davenport David Bruce Chris Detter Roxanne Tapia Cliff Han Alla Lapidus Susan Lucas Jan-Fang Cheng Samuel Pitluck Tanja Woyke Natalia Ivanova Natalia Mikhailova Miriam Land Loren Hauser D Aaron Argyros Lynne Goodwin David Hogsett Nicky Caiazza

Clostridium thermocellum DSM1313 is a thermophilic, anaerobic bacterium with some of the highest rates of cellulose hydrolysis reported. The complete genome sequence reveals a suite of carbohydrate-active enzymes and demonstrates a level of diversity at the species level distinguishing it from the type strain ATCC 27405.

Journal: :Antimicrobial agents and chemotherapy 1998
P C Fuchs A L Barry S D Brown

Clinafloxacin was more active than ciprofloxacin against 4,213 aerobic and facultative anaerobic bacterial isolates from 10 medical centers, as tested by broth microdilution and disk diffusion methods. The percentage of 201 anaerobes susceptible to clinafloxacin by broth microdilution was comparable to cefoxitin. Our data support the proposed disk diffusion interpretive criteria for aerobic bac...

2009
Grzegorz Cema

.................................................................................................................................................... 1 I – INTRODUCTION .................................................................................................................................... 2 II – BACKGROUND .................................................................................

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