Advanced Water Management Centre (AWMC), The University of Queensland , Brisbane, QLD 4072, Australia.
Environ Sci Technol. 2016 Jul 19;50(14):7425-33. doi: 10.1021/acs.est.6b00660. Epub 2016 Jun 23.
An increase of nitrite in the domestic-strength range is generally recognized to stimulate nitrous oxide (N2O) production by ammonia-oxidizing bacteria (AOB). It was found in this study, however, that N2O emission from a mainstream nitritation system (cyclic nitrite = 25-45 mg of N/L) that was established by free nitrous acid (FNA)-based sludge treatment was not higher but much lower than that from the initial nitrifying system with full conversion of NH4(+)-N to NO3(-)-N. Under dissolved oxygen (DO) levels of 2.5-3.0 mg/L, N2O emission from the nitritation stage was 76% lower than that from the initial stage. Even when the DO level was reduced to 0.3-0.8 mg/L, N2O emission from the nitritation stage was still 40% lower. An investigation of the mechanism showed that FNA treatment caused a shift of the stimulation threshold of nitrite on N2O emission. At the nitritation stage, the maximal N2O emission factor occurred at ∼16 mg of N/(L of nitrite). However, it increased with increasing nitrite in the range of 0-56 mg of N/L at the initial stage. FNA treatment decreased the biomass-specific N2O production rate, suggesting that the enzymes relevant to nitrifier denitrification were inhibited. Microbial analysis revealed that FNA treatment decreased the microbial community diversity but increased the abundances of AOB and denitrifiers.
国内浓度范围内亚硝酸盐的增加通常被认为会刺激氨氧化菌 (AOB) 产生氧化亚氮 (N2O)。然而,本研究发现,通过游离亚硝酸 (FNA) 基污泥处理建立的主流亚硝化系统 (循环亚硝酸盐 = 25-45mg/L 的 N) 的 N2O 排放量并没有更高,而是低得多与 NH4(+)-N 完全转化为 NO3(-)-N 的初始硝化系统相比。在溶解氧 (DO) 水平为 2.5-3.0mg/L 时,亚硝化阶段的 N2O 排放量比初始阶段低 76%。即使将 DO 水平降低至 0.3-0.8mg/L,亚硝化阶段的 N2O 排放量仍降低了 40%。对机制的研究表明,FNA 处理导致亚硝酸盐对 N2O 排放的刺激阈值发生变化。在亚硝化阶段,最大的 N2O 排放因子出现在约 16mgN/(L 亚硝酸盐)。然而,在初始阶段,当亚硝酸盐在 0-56mgN/L 的范围内增加时,它会随着亚硝酸盐的增加而增加。FNA 处理降低了生物量特异性 N2O 产生率,表明与硝化反硝化相关的酶被抑制。微生物分析表明,FNA 处理降低了微生物群落的多样性,但增加了 AOB 和反硝化菌的丰度。