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Source identification of nitrous oxide on autotrophic partial nitrification in a granular sludge reactor

机译:颗粒污泥反应器自养部分硝化过程中一氧化二氮的来源识别

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摘要

Emission of nitrous oxide (N2O) during biological wastewater treatment is of growing concern since N2O is a major stratospheric ozone-depleting substance and an important greenhouse gas. The emission of N2O from a lab-scale granular sequencing batch reactor (SBR) for partial nitrification (PN) treating synthetic wastewater without organic carbon was therefore determined in this study, because PN process is known to produce more N2O than conventional nitrification processes. The average N2O emission rate from the SBR was 0.32 ± 0.17 mg-N L−1 h−1, corresponding to the average emission of N2O of 0.8 ± 0.4% of the incoming nitrogen load (1.5 ± 0.8% of the converted NH4+). Analysis of dynamic concentration profiles during one cycle of the SBR operation demonstrated that N2O concentration in off-gas was the highest just after starting aeration whereas N2O concentration in effluent was gradually increased in the initial 40 min of the aeration period and was decreased thereafter. Isotopomer analysis was conducted to identify the main N2O production pathway in the reactor during one cycle. The hydroxylamine (NH2OH) oxidation pathway accounted for 65% of the total N2O production in the initial phase during one cycle, whereas contribution of the NO2− reduction pathway to N2O production was comparable with that of the NH2OH oxidation pathway in the latter phase. In addition, spatial distributions of bacteria and their activities in single microbial granules taken from the reactor were determined with microsensors and by in situ hybridization. Partial nitrification occurred mainly in the oxic surface layer of the granules and ammonia-oxidizing bacteria were abundant in this layer. N2O production was also found mainly in the oxic surface layer. Based on these results, although N2O was produced mainly via NH2OH oxidation pathway in the autotrophic partial nitrification reactor, N2O production mechanisms were complex and could involve multiple N2O production pathways.
机译:在生物废水处理过程中,一氧化二氮(N2O)的排放日益引起人们的关注,因为N2O是一种主要的平流层臭氧消耗物质,也是一种重要的温室气体。因此,在这项研究中确定了实验室规模的颗粒测序间歇反应器(SBR)用于部分硝化(PN)处理不含有机碳的合成废水中N2O的排放,因为已知PN过程比常规硝化过程会产生更多的N2O。 SBR的平均N2O排放速率为0.32±0.17 mg-N L-1 h-1,相当于N2O的平均排放量为输入氮负荷的0.8±0.4%(转化的NH4 +的1.5±0.8%)。在SBR操作的一个周期内对动态浓度分布的分析表明,刚开始曝气后,废气中的N2O浓度最高,而在曝气期的最初40分钟内,废水中的N2O浓度逐渐增加,此后逐渐降低。进行了同位素异构体分析,以确定一个循环中反应器中主要的N2O产生途径。在一个周期的初始阶段,羟胺(NH2OH)氧化途径占N2O产生总量的65%,而NO2-还原途径对N2O产生的贡献与后期的NH2OH氧化途径相当。另外,用微传感器并通过原位杂交确定了从反应器中取出的单个微生物颗粒中细菌的空间分布及其活性。部分硝化作用主要发生在颗粒的氧化表面层,该层中有大量的氨氧化细菌。还发现主要在有氧表面层中产生N 2O。基于这些结果,尽管N2O主要通过自养部分硝化反应器中的NH2OH氧化途径产生,但N2O的产生机理复杂且可能涉及多个N2O产生途径。

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