Advanced Water Management Centre, The University of Queensland, St. Lucia, Brisbane, QLD 4072, Australia; Process and Systems Engineering Center (PROSYS), Department of Chemical and Biochemical Engineering, Technical University of Denmark, 2800 Kgs. Lyngby, Denmark.
Advanced Water Management Centre, The University of Queensland, St. Lucia, Brisbane, QLD 4072, Australia.
Water Res. 2018 Oct 15;143:99-108. doi: 10.1016/j.watres.2018.06.025. Epub 2018 Jun 15.
This work aims to clarify the role of potential nitrite (NO) accumulation inside sludge flocs in NO production by ammonium-oxidizing bacteria (AOB) at different dissolved oxygen (DO) levels with focus on the conditions of no significant bulk NO accumulation (<0.2 mg N/L). To this end, an augmented nitrifying sludge with much higher abundance of nitrite-oxidizing bacteria (NOB) than AOB was enriched and then used for systematically designed batch tests, which targeted a range of DO levels from 0 to 3.0 mg O/L at a fixed ammonium concentration of 10 mg N/L. A two-pathway NO model was applied to facilitate the interpretation of batch experimental data, thus shedding light on the relationships between NO production pathways and key process parameters (i.e., DO and NO accumulation inside sludge flocs). The results demonstrated (i) the biomass specific NO production rate firstly increased and then decreased with DO, with the maximum value of 3.03 ± 0.05 mg N/h/g VSS obtained at DO level of 0.75 mg O/L, (ii) the AOB denitrification pathway for NO production was dominant (98.0%) at all DO levels tested even without significant bulk NO accumulation (<0.2 mg N/L) observed in the system, but its contribution decreased with DO, (iii) DO had a positive impact on the hydroxylamine pathway for NO production which therefore increased with DO, and (iv) the nitrite accumulation existed inside the sludge flocs and induced significant NO production from the AOB denitrification pathway.
本研究旨在阐明在不存在显著硝态氮积累(<0.2mgN/L)的情况下,不同溶解氧(DO)水平下氨氧化菌(AOB)在污泥絮体内潜在亚硝酸盐(NO)积累对 NO 生成的作用。为此,富集了一种硝化污泥,其中亚硝酸盐氧化菌(NOB)的丰度远高于 AOB,然后进行了系统设计的批式试验,该试验针对 DO 水平从 0 到 3.0mgO/L,固定的氨氮浓度为 10mgN/L。采用双途径 NO 模型对批式实验数据进行了处理,从而阐明了 NO 生成途径与关键工艺参数(即 DO 和污泥絮体内的 NO 积累)之间的关系。结果表明:(i)比生物量特定的 NO 生成速率随 DO 先增加后降低,在 DO 水平为 0.75mgO/L 时,最大值为 3.03±0.05mgN/h/gVSS;(ii)即使在系统中未观察到显著的硝态氮积累(<0.2mgN/L),AOB 反硝化途径也是产生 NO 的主要途径(98.0%),但其贡献随 DO 降低;(iii)DO 对生成 NO 的羟胺途径有积极影响,因此随着 DO 的增加而增加;(iv)硝态氮积累存在于污泥絮体内,并通过 AOB 反硝化途径诱导了显著的 NO 生成。