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本文引用的文献

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Production of NO(2) and N(2)O by Nitrifying Bacteria at Reduced Concentrations of Oxygen.在低氧浓度下硝化细菌产生的 NO(2) 和 N(2)O。
Appl Environ Microbiol. 1980 Sep;40(3):526-32. doi: 10.1128/aem.40.3.526-532.1980.
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Assay of poly-beta-hydroxybutyric acid.聚-β-羟基丁酸的测定
J Bacteriol. 1961 Jul;82(1):33-6. doi: 10.1128/jb.82.1.33-36.1961.
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The thiobacilli.硫杆菌
Bacteriol Rev. 1957 Sep;21(3):195-213. doi: 10.1128/br.21.3.195-213.1957.
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A colorimetric method for the determination of thiosulfate.一种测定硫代硫酸盐的比色法。
Biochim Biophys Acta. 1957 Feb;23(2):412-6. doi: 10.1016/0006-3002(57)90346-3.
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Heterotrophic nitrification among denitrifiers.反硝化菌中的异养硝化作用。
Appl Environ Microbiol. 1984 Apr;47(4):620-3. doi: 10.1128/aem.47.4.620-623.1984.
6
Aerobic denitrification--old wine in new bottles?好氧反硝化——旧瓶装新酒?
Antonie Van Leeuwenhoek. 1984;50(5-6):525-44. doi: 10.1007/BF02386224.
7
New facultative Thiobacillus and a reevaluation of the heterotrophic potential of Thiobacillus novellus.新型兼性硫杆菌及对诺氏硫杆菌异养潜力的重新评估。
J Bacteriol. 1969 Oct;100(1):487-97. doi: 10.1128/jb.100.1.487-497.1969.
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Heterotrophic nitrifiction by Arthrobacter sp.节杆菌属的异养硝化作用
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9
Dissimilatory nitrate and nitrite reduction under aerobic conditions by an aerobically and anaerobically grown Alcaligenes sp. and by activated sludge.好氧和厌氧培养的产碱杆菌属细菌以及活性污泥在有氧条件下的异化硝酸盐和亚硝酸盐还原作用。
J Appl Bacteriol. 1976 Jun;40(3):245-60. doi: 10.1111/j.1365-2672.1976.tb04172.x.

好氧搅拌槽培养混合硫杆菌时的同步硝化反硝化作用。

Simultaneous Nitrification and Denitrification in Aerobic Chemostat Cultures of Thiosphaera pantotropha.

机构信息

Laboratory of Microbiology and Enzymology, Delft University of Technology, Julianalaan 67A, 2628BC Delft, The Netherlands.

出版信息

Appl Environ Microbiol. 1988 Nov;54(11):2812-8. doi: 10.1128/aem.54.11.2812-2818.1988.

DOI:10.1128/aem.54.11.2812-2818.1988
PMID:16347780
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC204378/
Abstract

Thiosphaera pantotropha is capable of simultaneous heterotrophic nitrification and aerobic denitrification. Consequently, its nitrification potential could not be judged from nitrite accumulation, but was estimated from complete nitrogen balances. The maximum rate of nitrification obtained during these experiments was 93.9 nmol min mg of protein. The nitrification rate could be reduced by the provision of nitrate, nitrite, or thiosulfate to the culture medium. Both nitrification and denitrification increased as the dissolved oxygen concentration fell, until a critical level was reached at approximately 25% of air saturation. At this point, the rate of (aerobic) denitrification was equivalent to the anaerobic rate. At this dissolved oxygen concentration, the combined nitrification and denitrification was such that cultures receiving ammonium as their sole source of nitrogen appeared to become oxygen limited and the nitrification rate fell. It appeared that, under carbon-and energy-limited conditions, a high nitrification rate was correlated with a reduced biomass yield. To facilitate experimental design, a working hypothesis for the mechanism behind nitrification and denitrification by T. pantotropha was formulated. This involved the basic assumption that this species has a "bottleneck" in its cytochrome chain to oxygen and that denitrification and nitrification are used to overcome this. The nitrification potential of other heterotrophic nitrifiers has been reconsidered. Several species considered to be "poor" nitrifiers also simultaneously nitrify and denitrify, thus giving a falsely low nitrification potential.

摘要

硫杆菌属 pantotropha 能够同时进行异养硝化和好氧反硝化。因此,不能根据亚硝酸盐积累来判断其硝化能力,而要通过氮的完全平衡来估算。在这些实验中获得的最大硝化速率为 93.9 nmol min mg 的蛋白质。硝化速率可通过向培养基中提供硝酸盐、亚硝酸盐或硫代硫酸盐来降低。随着溶解氧浓度的降低,硝化和反硝化都会增加,直到达到约 25%空气饱和度的临界点。此时,(好氧)反硝化速率与厌氧速率相当。在这个溶解氧浓度下,联合硝化和反硝化的结果是,以铵盐作为唯一氮源的培养物似乎受到氧气限制,硝化速率下降。在碳和能量有限的条件下,似乎高硝化速率与生物量产量降低有关。为了便于实验设计,制定了硫杆菌属硝化和反硝化机制的工作假设。这涉及到一个基本假设,即该物种的细胞色素链对氧气有“瓶颈”,反硝化和硝化被用来克服这个瓶颈。其他异养硝化菌的硝化能力也被重新考虑。一些被认为是“较差”硝化菌的物种也同时进行硝化和反硝化,从而导致硝化能力被低估。