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N20 EMISSION FROM A NITRITATION DOUBLE-SLUDGE SYSTEM TREATING WASTEWATER WITH A HIGH CONCENTRATION OF AMMONIUM

机译:N20亚硝化双污泥系统的排放处理具有高浓度铵的废水

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Wastewaters such as landfill leachate and anaerobically digester effluent are usually contain high concentrations of ammonium (NH4-N) and low concentrations of biodegradable organic matters. A high efficient nitrite (N02-N) based double-sludge system combining sequential denitrification and nitritation reactors has been developed to remove nitrogen from such types of wastewater. Denitrification process could fully utilize the limited low carbon source, and nitrite accumulation was achieved in the nitritation reactor. By this means, enhanced biological nitrogen removal could be realized. However, nitrous oxide (N20), a potent greenhouse gas, can be produced and emitted during biological nitrogen removal. In this study, nitrite accumulation was achieved under low dissolved oxygen (DO) concentrations, high free ammonia (FA) concentrations and high NH4-N/DO ratios in the nitritation reactor. The nitritation efficiency (the ratio of N02-N to the oxidized nitrogen, NOX-N) reached to 99.8% at the ammonium loading rate of 1.47 g/(L-d). N20 emission was measured under different aeration rates (0.24 L/min, 0.36 L/min and 0.48 L/min, respectively). With increasing the aeration rate, ammonium oxidizing rate increased, indicating that the activity of ammonia oxidizing bacteria was enhanced with increasing the aeration rate. However, N20 emission decreased with increasing the aeration rate. In addition, the effect of initial N02-N concentrations on N20 emission under different aeration rates (0.24 L/min, 0.36 L/min and 0.48 L/min, respectively) was also examined. N20 emission was high with the addition of N02-N and a high initial N02-N concentrations led to a high emission of N20. The aeration rate had a high effect on N20 emission under high initial N02-N concentrations, with the N20 emission factor ranged from 0.61% to 1.82%. While the effect of aeration rate on N20 emission was not obvious without the addition of N02-N, with the emission factor of around 0.24%.
机译:垃圾填埋渗滤液和厌氧蒸煮器流出物等废水通常含有高浓度的铵(NH 4 -N)和低浓度的可生物降解有机物质。基于一种高效的亚硝酸盐(NO 2-N)双污泥系统相结合顺序反硝化作用和亚硝化反应器已发展到从这些类型的废水中除去氮。反硝化过程可以充分利用有限的低碳源,并在氮化响反应器中实现亚硝酸盐积聚。通过这种方式,可以实现增强的生物氮去除。然而,可以在生物氮去除期间产生并排放氧化亚氮(N20),有效的温室气体。在本研究中,在低溶解的氧(DO)浓度,高自由氨(FA)浓度和亚硝基反应器中的高NH 4 -N /确实比下达到亚硝酸盐积累。在1.47g /(L-D)的铵加载速率下达到氮效率(NO 2-N至氧化氮的比率,NOX-N)达到99.8%。在不同的曝气速率下测量N20发射(0.24L / min,0.36L / min,分别为0.48L / min)。随着曝气速率的增加,氧化率增加,表明氨氧化细菌的活性随着曝气率的增加而增强。然而,N20发射随着曝气率的增加而降低。此外,还检查了初始N02-N浓度对不同曝气速率下N20发射的影响(0.24L / min,0.36L / min分别分别为0.48L / min)。 N20发射率高,加入NO 2-N和高初始N02-N浓度导致高发射N20。曝气速率对高初始N02-N浓度下的N20发射具有高效果,N20排放因子范围为0.61%至1.82%。虽然在没有添加N02-N的情况下,曝气率对N20发射的影响并不明显,但排放因子约为0.24%。

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