National Engineering Laboratory for Advanced Municipal Wastewater Treatment and Reuse Technology, Key Laboratory of Beijing for Water Quality Science and Water Environment Recovery Engineering, Beijing University of Technology, Beijing, 100124, China.
National Engineering Laboratory for Advanced Municipal Wastewater Treatment and Reuse Technology, Key Laboratory of Beijing for Water Quality Science and Water Environment Recovery Engineering, Beijing University of Technology, Beijing, 100124, China.
Water Res. 2021 Mar 1;191:116807. doi: 10.1016/j.watres.2021.116807. Epub 2021 Jan 4.
Rapid enrichment of anaerobic ammonia oxidation bacteria (AnAOB) is highly associated with the granulation process; however, the interactive mechanism remains unclear, especially for the initial granulation process. A single-stage partial nitritation-anammox (PN/A) bioreactor combined with granular/floc sludge was operated for 400 days. During the experimental period, the nitrogen removal rate increased from 0.60 to 1.21 kg N md, and the nitrogen removal capability improved primarily during a transition period (days 200-250), which was accompanied by a particle size increase and AnAOB proliferation (4.9 ± 1.7 days). Moreover, as observed by the biomass physio-morphology, the size distribution, and the microbial community shift, small flocs (< 200 μm) aggregated due to the addition of excess sodium acetate. The emerging floc aggregates represented an early form of granules, providing the initial biological carrier and necessary anaerobic microenvironment for the growth of attached AnAOB, resulting in a high AnAOB growth-rate. These results are the first direct evidence that floc aggregates are essential to AnAOB enrichment, and that they can be affected by operational conditions. This study provides an in-depth understanding of the link between floc aggregations and AnAOB enrichment and broadens the feasibility of optimizing PN/A applications.
厌氧氨氧化菌(AnAOB)的快速富集与颗粒化过程高度相关;然而,其相互作用机制尚不清楚,特别是在初始颗粒化过程中。采用单级部分硝化-厌氧氨氧化(PN/A)生物反应器与颗粒/絮体污泥相结合,运行了 400 天。在实验期间,氮去除率从 0.60 增加到 1.21 kg N md,氮去除能力主要在过渡阶段(第 200-250 天)得到改善,这伴随着粒径的增加和 AnAOB 的增殖(4.9±1.7 天)。此外,通过生物量生理形态学、粒径分布和微生物群落变化的观察,由于添加了过量的乙酸钠,小絮体(<200μm)聚集在一起。新出现的絮体聚集体代表了颗粒的早期形式,为附着生长的 AnAOB 提供了初始的生物载体和必要的厌氧微环境,从而实现了高的 AnAOB 增长率。这些结果是絮体聚集体对 AnAOB 富集至关重要的直接证据,并且它们可以受到操作条件的影响。本研究深入了解了絮体聚集与 AnAOB 富集之间的联系,并拓宽了优化 PN/A 应用的可行性。