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Heterotrophic denitrification plays an important role in N_2O production from nitritation reactors treating anaerobic sludge digestion liquor

机译:异养反硝化在硝化反应器处理厌氧污泥消化液的N_2O生产中起重要作用

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摘要

Nitrous oxide (N_2O) emissions from nitritation reactors receiving real anaerobic sludge digestion liquor have been reported to be substantially higher than those from reactors receiving synthetic digestion liquor. This study aims to identify the causes for the difference, and to develop strategies to reduce N_2O emissions from reactors treating real digestion liquor. Two sequencing batch reactors (SBRs) performing nitritation, fed with real (SBR-R) and synthetic (SBR-S) digestion liquors, respectively, were employed. The N_2O emission factors for SBR-R and SBR-S were determined to be 3.12% and 0.80% of the NH_4~+-N oxidized, respectively. Heterotrophic denitrification supported by the organic carbon present in the real digestion liquor was found to be the key contributor to the higher N_2O emission from SBR-R. Heterotrophic nitrite reduction likely stopped at N_2O (rather than N_2), with a hypothesised cause being free nitrous acid inhibition. This implies that all nitrite reduced by heterotrophic bacteria was converted to and emitted as N_2O. Increasing dissolved oxygen (DO) concentration from 0.5 to 1.0 mg/L, or above, decreased aerobic N_2O production from 2.0% to 0.5% in SBR-R, whereas aerobic N_2O production in SBR-S remained almost unchanged (at approximately 0.5%). We hypothesised that DO at 1 mg/L or above suppressed heterotrophic nitrite reduction thus reduced aerobic heterotrophic N_2O production. We recommend that DO in a nitritation system receiving anaerobic sludge digestion liquor should be maintained at approximately 1 mg/L to minimise N_2O emission.
机译:据报道,使用实际厌氧污泥消化液的硝化反应器中的一氧化二氮(N_2O)排放量大大高于使用合成消化液的反应器中的排放。这项研究的目的是找出造成这种差异的原因,并制定策略来减少处理实际消化液的反应器中的N_2O排放。使用了两个进行硝化的测序间歇反应器(SBR),分别供入了真正的(SBR-R)和合成的(SBR-S)消化液。确定SBR-R和SBR-S的N_2O排放因子分别为被氧化的NH_4〜+ -N的3.12%和0.80%。实际消化液中存在的有机碳支持的异养反硝化作用是造成SBR-R较高N_2O排放的关键因素。异养亚硝酸盐的还原可能在N_2O(而不是N_2)处停止,据推测原因是游离亚硝酸抑制。这意味着所有由异养细菌还原的亚硝酸盐都转化为N_2O并以N_2O的形式排放。将溶解氧(DO)浓度从0.5增至1.0 mg / L或更高,会使SBR-R中的好氧N_2O产生从2.0%降低至0.5%,而SBR-S中的好氧N_2O产生几乎保持不变(约0.5%) 。我们假设溶解氧在1 mg / L或更高时会抑制异养亚硝酸盐的减少,从而减少好氧异养N_2O的产生。我们建议在接受厌氧污泥消化液的硝化系统中,溶解氧应保持在约1 mg / L,以最大程度地减少N_2O的排放。

著录项

  • 来源
    《Water Research》 |2014年第1期|202-210|共9页
  • 作者单位

    Advanced Water Management Centre (AWMC), The University of Queensland, QLD 4072, Australia;

    Advanced Water Management Centre (AWMC), The University of Queensland, QLD 4072, Australia;

    Advanced Water Management Centre (AWMC), The University of Queensland, QLD 4072, Australia,School of Chemical Engineering, The University of Queensland, QLD 4072, Australia;

    Advanced Water Management Centre (AWMC), The University of Queensland, QLD 4072, Australia,Catalan Institute for Water Research (ICRA), Technological Park of the University of Girona, 17003, Spain;

    Advanced Water Management Centre (AWMC), The University of Queensland, QLD 4072, Australia;

  • 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

    Nitrous oxide; Heterotrophic denitrification; Nitritation; Anaerobic digestion liquor; Free nitrous acid; Dissolved oxygen;

    机译:笑气;异养反硝化;亚硝化厌氧消化液;游离亚硝酸;溶解氧;

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