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Mechanisms of N_2O production in biological wastewater treatment under nitrifying and denitrifying conditions

机译:硝化反硝化条件下生物废水处理中N_2O产生的机理

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摘要

Nitrous oxide (N_2O) is an important greenhouse gas and a major sink for stratospheric ozone. In biological wastewater treatment, microbial processes such as autotrophic nitrification and heterotrophic denitrification have been identified as major sources; however, the underlying pathways remain unclear. In this study, the mechanisms of N_2O production were investigated in a laboratory batch-scale system with activated sludge for treating municipal wastewater. This relatively complex mixed population system is well representative for full-scale activated sludge treatment under nitrifying and denitrifying conditions. Under aerobic conditions, the addition of nitrite resulted in strongly nitrite-dependent N_2O production, mainly by nitrifier denitrification of ammonia-oxidizing bacteria (AOB). Furthermore, N_2O is produced via hydroxylamine oxidation, as has been shown by the addition of hydroxylamine. In both sets of experiments, N_2O production was highest at the beginning of the experiment, then decreased continuously and ceased when the substrate (nitrite, hydroxylamine) had been completely consumed. In ammonia oxidation experiments, N_2O peaked at the beginning of the experiment when the nitrite concentration was lowest. This indicates that N_2O production via hydroxylamine oxidation is favored at high ammonia and low nitrite concentrations, and in combination with a high metabolic activity of ammonia-oxidizing bacteria (at 2 to 3 mgO_2/l); the contribution of nitrifier denitrification by AOB increased at higher nitrite and lower ammonia concentrations towards the end of the experiment. Under anoxic conditions, nitrate reducing experiments confirmed that N_2O emission is low under optimal growth conditions for heterotrophic denitrifiers (e.g. no oxygen input and no limitation of readily biodegradable organic carbon). However, N_2O and nitric oxide (NO) production rates increased significantly in the presence of nitrite or low dissolved oxygen concentrations.
机译:一氧化二氮(N_2O)是重要的温室气体,也是平流层臭氧的主要汇。在生物废水处理中,自养硝化和异养反硝化等微生物过程已被确定为主要来源。但是,其潜在途径仍不清楚。在这项研究中,在带有活性污泥的实验室批量处理系统中研究了N_2O的产生机理,以处理市政废水。这种相对复杂的混合种群系统非常适合在硝化和反硝化条件下进行大规模活性污泥处理。在有氧条件下,亚硝酸盐的添加主要通过亚硝酸盐对氨氧化细菌(AOB)的反硝化作用而导致强烈依赖于亚硝酸盐的N_2O产生。此外,如通过添加羟胺所显示的,N_2O是通过羟胺氧化产生的。在这两组实验中,N_2O的产生在实验开始时最高,然后连续下降并在底物(亚硝酸盐,羟胺)被完全消耗时停止。在氨氧化实验中,当亚硝酸盐浓度最低时,N_2O在实验开始时达到峰值。这表明在高氨水和低亚硝酸盐浓度下,并结合氨氧化细菌的高代谢活性(2-3 mgO_2 / l),有利于通过羟胺氧化生产N_2O;在实验结束时,在较高的亚硝酸盐和较低的氨浓度下,AOB对硝化器反硝化的贡献增加。在缺氧条件下,减少硝酸盐的实验证实,对于异养反硝化剂,最佳生长条件下的N_2O排放量较低(例如,没有氧气输入且没有易于生物降解的有机碳的限制)。但是,在存在亚硝酸盐或低溶解氧浓度的情况下,N_2O和一氧化氮(NO)的生产率显着提高。

著录项

  • 来源
    《Water Research》 |2012年第4期|p.1027-1037|共11页
  • 作者单位

    Eawag, Swiss Federal Institute of Aquatic Science and Technology, Ueberlandstrasse 133, P.O. Box 611, 8600 Duebendorf, Switzerland;

    Empa, Swiss Federal Laboratories for Materials Testing and Research, Laboratory for Air Pollution and Environmental Technology,Ueberlandstrasse 129, 8600 Duebendorf, Switzerland;

    Eawag, Swiss Federal Institute of Aquatic Science and Technology, Ueberlandstrasse 133, P.O. Box 611, 8600 Duebendorf, Switzerland;

    Empa, Swiss Federal Laboratories for Materials Testing and Research, Laboratory for Air Pollution and Environmental Technology,Ueberlandstrasse 129, 8600 Duebendorf, Switzerland;

    Eawag, Swiss Federal Institute of Aquatic Science and Technology, Ueberlandstrasse 133, P.O. Box 611, 8600 Duebendorf, Switzerland;

  • 收录信息 美国《科学引文索引》(SCI);美国《工程索引》(EI);
  • 原文格式 PDF
  • 正文语种 eng
  • 中图分类
  • 关键词

    biological wastewater treatment; denitrifying condition; hydroxylamine oxidation; nitrous oxide; nitric oxide; nitrifying condition;

    机译:生物废水处理;反硝化条件羟胺氧化;笑气;一氧化氮;硝化条件;
  • 入库时间 2022-08-17 13:46:16

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