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实验室规模的数据和微生物群落结构表明,短程硝化反硝化是好氧消化(PAD)后氮去除的主要机制。

Lab-scale data and microbial community structure suggest shortcut nitrogen removal as the predominant nitrogen removal mechanism in post-aerobic digestion (PAD).

机构信息

Black & Veatch, Overland Park, Kansas, USA.

Department of Civil, Construction and Environmental Engineering, Marquette University, Milwaukee, Wisconsin, USA.

出版信息

Water Environ Res. 2022 Jul;94(7):e10762. doi: 10.1002/wer.10762.

Abstract

Implementing an aerobic digestion step after anaerobic digestion, referred to as "post aerobic digestion" (PAD), can remove ammonia without the need for an external carbon source and destroy volatile solids. While this process has been documented at the lab-scale and full-scale, the mechanism for N removal and the corresponding microbial community that carries out this process have not been established. This research gap is important to fill because the nitrogen removal pathway has implications on aeration requirements and carbon demand, that is, short-cut N-removal requires less oxygen and carbon than simultaneous nitrification-denitrification. The aims of this research were to (i) determine if nitrite (NO ) or nitrate (NO ) dominates following ammonia removal and (ii) characterize the microbial community from PAD reactors. Here, lab-scale PAD reactors were seeded with biomass from two different full-scale PAD reactors. The lab-scale reactors were fed with biomass from full-scale reactors and operated in batch mode to quantify nitrogen species concentrations (ammonia, NH , NO , and NO ) over time. Experimental results revealed that NO production rates were several orders of magnitude greater than NO production rates. Indeed, nitrite accumulation rate (NAR) was greater than 90% at most temperatures, confirming that shortcut nitrogen removal was the dominant NH removal mechanism in PAD. Microbial community analysis via 16S rRNA sequencing indicated that ammonia oxidizing bacteria (AOB) were much more abundant than nitrite oxidizing bacteria (NOB). Overall, this study suggests that aeration requirements for post-aerobic digestion should be based on NO shunt and not complete simultaneous nitrification denitrification. PRACTITIONER POINTS: AOB are a key feature of PAD microbial communities NOB are present, but in much lower abundance than AOB High nitrite accumulation ratio suggests shortcut nitrite as the main mechanism for nitrogen removal Nitritation in PAD reactors is sustained at temperatures as high as 40°C No ammonia oxidation occurred at 50°C implying different mechanisms of nitrogen removal including ammonia stripping.

摘要

在厌氧消化之后实施好氧消化步骤,称为“后好氧消化”(PAD),可以在不需要外部碳源的情况下去除氨并破坏挥发性固体。虽然该过程已在实验室规模和全规模下得到记录,但去除氮的机制以及执行该过程的相应微生物群落尚未建立。填补这一研究空白很重要,因为氮去除途径对曝气要求和碳需求有影响,即短程 N 去除所需的氧气和碳比同时硝化-反硝化少。本研究的目的是:(i)确定氨去除后是亚硝酸盐(NO )还是硝酸盐(NO )占主导地位,以及(ii)从 PAD 反应器中表征微生物群落。在这里,实验室规模的 PAD 反应器用来自两个不同的全规模 PAD 反应器的生物量进行接种。实验室规模的反应器以全规模反应器的生物质为食,并以分批模式运行,以随时间定量测定氮物种浓度(氨、NH 、NO 和 NO )。实验结果表明,NO 生成速率比 NO 生成速率高出几个数量级。实际上,在大多数温度下,亚硝酸盐积累率(NAR)大于 90%,这证实了短程脱氮是 PAD 中主要的氨去除机制。通过 16S rRNA 测序进行的微生物群落分析表明,氨氧化细菌(AOB)比亚硝酸盐氧化细菌(NOB)丰富得多。总的来说,这项研究表明,后好氧消化的曝气要求应基于 NO 支路,而不是完全同时硝化反硝化。

从业者要点

AOB 是 PAD 微生物群落的一个关键特征

NOB 存在,但丰度远低于 AOB

高亚硝酸盐积累比表明亚硝酸盐是氮去除的主要机制

在高达 40°C 的温度下,PAD 反应器中的硝化作用得以维持

在 50°C 时没有氨氧化发生,这意味着包括氨汽提在内的不同氮去除机制。

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