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本文引用的文献

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Greenhouse Effects due to Man-Mad Perturbations of Trace Gases.人为痕量气体的扰动导致的温室效应。
Science. 1976 Nov 12;194(4266):685-90. doi: 10.1126/science.194.4266.685.
2
Evolution of Nitrogen Oxide(s) during In Vivo Nitrate Reductase Assay of Soybean Leaves.大豆叶片体内硝酸还原酶测定过程中氮氧化物的演变
Plant Physiol. 1981 Dec;68(6):1488-93. doi: 10.1104/pp.68.6.1488.
3
Dissimilatory Reduction of NO(2) to NH(4) and N(2)O by a Soil Citrobacter sp.土壤柠檬酸杆菌属异化还原 NO(2) 为 NH(4) 和 N(2)O
Appl Environ Microbiol. 1982 Apr;43(4):854-60. doi: 10.1128/aem.43.4.854-860.1982.
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Production of nitrous oxide by ammonia-oxidizing chemoautotrophic microorganisms in soil.土壤中氨氧化化能自养微生物产生一氧化二氮。
Appl Environ Microbiol. 1980 Dec;40(6):1060-6. doi: 10.1128/aem.40.6.1060-1066.1980.
5
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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Microtechnique for most-probable-number analysis.最可能数分析的微技术。
Appl Environ Microbiol. 1977 Mar;33(3):675-80. doi: 10.1128/aem.33.3.675-680.1977.
7
Dissimilatory reduction of nitrate and nitrite in the bovine rumen: nitrous oxide production and effect of acetylene.牛瘤胃中硝酸盐和亚硝酸盐的异化还原:一氧化二氮的产生及乙炔的影响
Appl Environ Microbiol. 1981 Mar;41(3):705-9. doi: 10.1128/aem.41.3.705-709.1981.
8
Medium without rumen fluid for nonselective enumeration and isolation of rumen bacteria.用于瘤胃细菌非选择性计数和分离的不含瘤胃液的培养基。
Appl Microbiol. 1966 Sep;14(5):794-801. doi: 10.1128/am.14.5.794-801.1966.
9
Physiological factors affecting transformation of Azotobacter vinelandii.影响棕色固氮菌转化的生理因素。
J Bacteriol. 1976 Mar;125(3):1080-7. doi: 10.1128/jb.125.3.1080-1087.1976.

非硝化菌或反硝化菌产生的一氧化二氮。

Nitrous oxide production by organisms other than nitrifiers or denitrifiers.

机构信息

Departments of Crop and Soil Sciences and Microbiology and Public Health, Michigan State University, East Lansing, Michigan 48824.

出版信息

Appl Environ Microbiol. 1982 Dec;44(6):1342-8. doi: 10.1128/aem.44.6.1342-1348.1982.

DOI:10.1128/aem.44.6.1342-1348.1982
PMID:16346152
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC242194/
Abstract

Heterotrophic bacteria, yeasts, fungi, plants, and animal breath were investigated as possible sources of N(2)O. Microbes found to produce N(2)O from NO(3) but not consume it were: (i) all of the nitrate-respiring bacteria examined, including strains of Escherichia, Serratia, Klebsiella, Enterobacter, Erwinia, and Bacillus; (ii) one of the assimilatory nitrate-reducing bacteria examined, Azotobacter vinelandii, but not Azotobacter macrocytogenes or Acinetobacter sp.; and (iii) some but not all of the assimilatory nitrate-reducing yeasts and fungi, including strains of Hansenula, Rhodotorula, Aspergillus, Alternaria, and Fusarium. The NO(3)-reducing obligate anaerobe Clostridium KDHS2 did not produce N(2)O. Production of N(2)O occurred only in stationary phase. The nitrate-respiring bacteria produced much more N(2)O than the other organisms, with yields of N(2)O ranging from 3 to 36% of 3.5 mM NO(3). Production of N(2)O was apparently not regulated by ammonium and was not restricted to aerobic or anaerobic conditions. Plants do not appear to produce N(2)O, although N(2)O was found to arise from some damaged plant tops, probably due to microbial growth. Concentrations of N(2)O above the ambient level in the atmosphere were found in human breath and appeared to increase after a meal of high-nitrate food.

摘要

异养细菌、酵母、真菌、植物和动物的呼吸被认为是 N(2)O 的可能来源。研究发现,能够将 NO(3)转化为 N(2)O 但不能消耗它的微生物包括:(i) 所有被检测的硝酸盐呼吸细菌,包括大肠杆菌、沙雷氏菌、克雷伯氏菌、肠杆菌、欧文氏菌和芽孢杆菌;(ii) 被检测的同化硝酸盐还原细菌中的一种,即维氏固氮菌,但不是巨球形固氮菌或不动杆菌;(iii) 一些但不是所有的同化硝酸盐还原酵母和真菌,包括汉逊酵母、红酵母、曲霉属、链格孢属和镰刀菌属。专性厌氧的硝酸盐还原菌 Clostridium KDHS2 不会产生 N(2)O。N(2)O 的产生仅发生在静止期。硝酸盐呼吸细菌产生的 N(2)O 比其他生物体多得多,3.5mMNO(3)的 N(2)O 产率范围为 3%至 36%。N(2)O 的产生显然不受铵的调节,也不限于有氧或无氧条件。植物似乎不会产生 N(2)O,尽管发现一些受损的植物顶部会产生 N(2)O,可能是由于微生物的生长。在大气中,人类呼吸中发现的 N(2)O 浓度高于环境水平,并且在食用高硝酸盐食物后似乎会增加。