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佛罗里达大沼泽地泥灰岩和泥炭沉积物中的反硝化作用。

Denitrification in marl and peat sediments in the Florida everglades.

机构信息

Department of Biological Sciences, Old Dominion University, Norfolk, Virginia 23508; Drinking Water Research Center, Florida International University, Tamiami Campus, Miami, Florida 33199; and Everglades National Park, South Florida Research Center, Homestead, Florida 33030.

出版信息

Appl Environ Microbiol. 1986 Nov;52(5):987-91. doi: 10.1128/aem.52.5.987-991.1986.

DOI:10.1128/aem.52.5.987-991.1986
PMID:16347228
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC239162/
Abstract

The potential for denitrification in marl and peat sediments in the Shark River Slough in the Everglades National Park was determined by the acetylene blockage assay. The influence of nitrate concentration on denitrification rate and N(2)O yield from added nitrate was examined. The effects of added glucose and phosphate and of temperature on the denitrification potential were determined. The sediments readily denitrified added nitrate. N(2)O was released from the sediments both with and without added acetylene. The marl sediments had higher rates than the peat on every date sampled. Denitrification was nitrate limited; however, the yields of N(2)O amounted to only 10 to 34% of the added nitrate when 100 muM nitrate was added. On the basis of measured increases in ammonium concentration, it appears that the balance of added nitrate may be converted to ammonium in the marl sediment. The sediment temperature at the time of sampling greatly influenced the denitrification potential (15-fold rate change) at the marl site, indicating that either the number or the specific activity of the denitrifiers changed in response to temperature fluctuations (9 to 25 degrees C) in the sediment. It is apparent from this study that denitrification in Everglades sediments is not an effective means of removing excess nitrogen which may be introduced as nitrate into the ecosystem with supply water from the South Florida watershed and that sporadic addition of nitrate-rich water may lead to nitrous oxide release from these wetlands.

摘要

使用乙炔阻断法测定了大沼泽地国家公园 Shark 河漫滩的泥灰岩和泥炭沉积物中的反硝化潜力。研究了硝酸盐浓度对添加硝酸盐的反硝化速率和 N2O 产量的影响。还测定了添加葡萄糖和磷酸盐以及温度对反硝化潜力的影响。沉积物可以很容易地将添加的硝酸盐进行反硝化。在添加和不添加乙炔的情况下,N2O 都会从沉积物中释放出来。在每次采样时,泥灰岩沉积物的反硝化速率都高于泥炭沉积物。反硝化受硝酸盐限制;但是,当添加 100 μM 硝酸盐时,N2O 的产量仅占添加硝酸盐的 10%至 34%。根据铵盐浓度的测量增加,泥灰岩沉积物中添加的硝酸盐可能会转化为铵盐。采样时的沉积物温度极大地影响了泥灰岩沉积物中的反硝化潜力(变化了 15 倍),这表明反硝化菌的数量或特定活性可能会因沉积物中的温度波动(9 至 25°C)而发生变化。从这项研究中可以明显看出,大沼泽地沉积物中的反硝化并不是一种有效去除过量氮的方法,过量氮可能会随着南佛罗里达州集水区的供水作为硝酸盐而被引入生态系统,而且富含硝酸盐的水的间歇性添加可能会导致这些湿地释放出氧化亚氮。

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本文引用的文献

1
Denitrification in san francisco bay intertidal sediments.旧金山湾潮间带沉积物中的反硝化作用。
Appl Environ Microbiol. 1984 May;47(5):1106-12. doi: 10.1128/aem.47.5.1106-1112.1984.
2
Kinetic explanation for accumulation of nitrite, nitric oxide, and nitrous oxide during bacterial denitrification.在细菌反硝化过程中,亚硝酸盐、一氧化氮和氧化亚氮积累的动力学解释。
Appl Environ Microbiol. 1981 Dec;42(6):1074-84. doi: 10.1128/aem.42.6.1074-1084.1981.
3
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.
4
Denitrification.反硝化作用
Microbiol Rev. 1982 Mar;46(1):43-70. doi: 10.1128/mr.46.1.43-70.1982.
5
N2 fixation in the rhizosphere of Thalassia testudinum.泰来草(Thalassia testudinum)根际的固氮作用
Can J Microbiol. 1980 Aug;26(8):998-1005. doi: 10.1139/m80-169.
6
The reduction of nitrate to ammonium by a Clostridium sp. isolated from soil.从土壤中分离出的一种梭状芽孢杆菌将硝酸盐还原为铵。
J Gen Microbiol. 1980 Jul;119(1):217-23. doi: 10.1099/00221287-119-1-217.
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Reduction of nitrogenous oxides by microorganisms.微生物对氮氧化物的还原作用。
Bacteriol Rev. 1973 Dec;37(4):409-52. doi: 10.1128/br.37.4.409-452.1973.
8
Blockage by acetylene of nitrous oxide reduction in Pseudomonas perfectomarinus.乙炔对完美海假单胞菌中氧化亚氮还原的阻碍作用。
Appl Environ Microbiol. 1976 Apr;31(4):504-8. doi: 10.1128/aem.31.4.504-508.1976.
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Acetylene inhibition of nitrous oxide reduction by denitrifying bacteria.乙炔对反硝化细菌还原氧化亚氮的抑制作用。
Biochem Biophys Res Commun. 1976 Apr 5;69(3):705-10. doi: 10.1016/0006-291x(76)90932-3.