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Characterization and mitigation of nitrous oxide (N2O) emissions from partial and full-nitrification BNR processes based on post-anoxic aeration control

机译:基于缺氧曝气控制的部分和完全硝化BNR工艺中一氧化二氮(N2O)排放的表征和缓解

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It has been reported that a directional change from anoxic to aerobic conditions is a common trigger for nitrous oxide (N2O) production by ammonia oxidizing bacteria (AOB). By extension, during anoxic-aerobic cycling, post-anoxic dissolved oxygen (DO) concentrations might likely play a role in the magnitude of N2O emissions observed. The overall goal of this study was to determine the impact of three select post-anoxic DO concentrations (0.8, 2.0, and 3.0mg O-2/L) on N2O emissions from partial-nitrification (PN) and full-nitrification (FN) reactors subjected to anoxic-aerobic cycling and, ultimately, to explore the development of strategies to minimize N2O emissions from PN and FN based biological nitrogen removal (BNR) processes. Statistically similar N2O emissions were observed during anoxia for both PN (0.62 +/- 0.21% N load) and FN (0.61 +/- 0.070% N load) processes. In contrast, N2O emissions were statistically lower for PN (0.86 +/- 0.25% N load) than for FN (4.6 +/- 2.8% N load), during the post-anoxic aerobic phase, when compared together for all three post-anoxic DO concentrations. Further, for PN, the highest N2O emissions were observed at the highest post-anoxic DO concentration of 3.0mg O-2/L (1.2%N load), likely due to the highest corresponding AOB specific growth rate. In contrast, for FN, the highest N2O emissions were at the lowest post-anoxic DO concentration of 0.8mg O-2/L (8.5%N load). The higher emissions from FN process at low DO concentrations were associated with a lag in nitrite oxidizing bacteria activity upon recovery to aerobic conditions. This lag phase contributed to transient nitrite accumulation, and in turn correlated positively to the observed N2O emissions. Based on our findings, a gradual ramp up in post-anoxic DO concentrations can minimize N2O emissions during PN-based BNR, whereas a completely different strategy, entailing a rapid increase in post-anoxic DO concentrations can minimize emissions during FN-based BNR operations. Biotechnol. Bioeng. 2015;112: 2241-2247. (c) 2015 Wiley Periodicals, Inc.
机译:据报道,从缺氧状态到有氧条件的方向变化是氨氧化细菌(AOB)产生一氧化二氮(N2O)的常见诱因。通过扩展,在缺氧-好氧循环中,缺氧后的溶解氧(DO)浓度可能在观察到的N2O排放量中起一定作用。这项研究的总体目标是确定三种选择的缺氧后DO浓度(0.8、2.0和3.0mg O-2 / L)对部分硝化(PN)和完全硝化(FN)产生的N2O排放的影响进行缺氧-好氧循环的反应堆,并最终探索开发策略以最大程度地减少基于PN和FN的生物脱氮(BNR)过程中的N2O排放。在PN(0.62 +/- 0.21%N负载)和FN(0.61 +/- 0.070%N负载)过程中,在缺氧过程中观察到统计上相似的N2O排放。相比之下,在缺氧后有氧阶段,PN(0.86 +/- 0.25%N负荷)的N2O排放在统计学上低于FN(4.6 +/- 2.8%N负荷)的氮排放,与所有三个后氧阶段相比缺氧溶解氧浓度。此外,对于PN,在最高缺氧后DO浓度为3.0mg O-2 / L(1.2%N负载)时观察到最高N2O排放,这可能是由于最高的相应AOB比生长速率所致。相比之下,对于FN,最高的N2O排放在最低的缺氧后DO浓度为0.8mg O-2 / L(8.5%N负荷)下发生。在低溶解氧浓度下,FN工艺产生的较高排放与恢复至好氧条件后亚硝酸盐氧化细菌活性的滞后有关。滞后阶段促进了亚硝酸盐的瞬时积累,继而与观测到的N2O排放呈正相关。根据我们的发现,逐渐增加的缺氧后DO浓度可以使基于PN的BNR期间的N2O排放量最小化,而一种完全不同的策略,即迅速增加的缺氧后DO浓度可以使基于FN的BNR操作期间的N2O排放量最小化。生物技术。生恩2015; 112:2241-2247。 (c)2015年威利期刊有限公司

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