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通过用游离亚硝态氮彻底抑制 AOB 和 NOB 后恢复 AOB 活性,在主流污水处理中恢复 PN/A 系统中的部分亚硝化。

Recovering partial nitritation in a PN/A system during mainstream wastewater treatment by reviving AOB activity after thoroughly inhibiting AOB and NOB with free nitrous acid.

机构信息

National Engineering Laboratory for Advanced Municipal Wastewater Treatment and Reuse Technology, Engineering Research Center of Beijing, Beijing University of Technology, Beijing, China.

National Engineering Laboratory for Advanced Municipal Wastewater Treatment and Reuse Technology, Engineering Research Center of Beijing, Beijing University of Technology, Beijing, China; Research Institute for Environmental Innovation (Suzhou) Tsinghua, Suzhou, China.

出版信息

Environ Int. 2020 Jun;139:105684. doi: 10.1016/j.envint.2020.105684. Epub 2020 Apr 1.

Abstract

Starting up or recovering partial nitritation is a major challenge for achieving or maintaining stable partial nitritation/anammox (PN/A) during mainstream wastewater treatment. This study presents a novel strategy for recovering the nitrite pathway by selectively reviving ammonium oxidizing bacteria (AOB) after thoroughly inhibiting AOB and nitrite oxidizing bacteria (NOB) using free nitrous acid (FNA). A sequencing batch reactor was operated for PN/A to treat real domestic wastewater for 423 days, during which twice FNA treatment was temporarily implemented. Results showed that with a single 0.45 mg/L FNA treatment on flocculent sludge, the NO-N concentration during the aerobic period showed an uptrend again and the partial nitritation performance was deteriorated. In contrast, 1.35 mg/L FNA treatment induced the inhibition of both AOB and NOB leading to regressive ammonium oxidation, but a subsequently higher DO (1.5 mg/L) and longer aeration duration recovered partial nitritation. For the relative abundances of the acquired biomass related to nitrogen conversion, Nitrosomonas, Nitrospira and Nitrolancea increased to 9.65%, 10.27% and 4.35%, respectively, at the beginning of the 1.35 mg/L FNA treatment, and Nitrospira and Nitrolancea decreased to 2.80% and 0.03% whereas Nitrosomonas declined to 8.71% after 76 days. Ca. Brocadia showed less resilience after the 1.35 mg/L FNA treatment, with the relative abundance decreasing from 13.38% to 0.62% due to insufficient nitrite. Molecular ecological network analysis indicates that among anammox taxa, Ca. Kuenenia and Ca. Brocadia formed important links with other N cycle processes. Moreover, the proposed strategy shows operational flexibility because it can be easily used to control NOB in mainstream PN/A applications offered by flocculent sludge systems.

摘要

实现或维持主流废水处理中稳定的部分亚硝化/厌氧氨氧化(PN/A)是启动或恢复部分亚硝化的主要挑战。本研究提出了一种通过在彻底抑制氨氧化菌(AOB)和亚硝酸盐氧化菌(NOB)后,使用游离亚硝酸(FNA)选择性地恢复亚硝酸途径的新策略。采用序批式反应器处理实际生活污水,进行 PN/A 处理 423 天,期间两次临时实施 FNA 处理。结果表明,在絮状污泥上进行单次 0.45mg/L 的 FNA 处理后,好氧期的 NO-N 浓度再次呈上升趋势,部分亚硝化性能恶化。相比之下,1.35mg/L 的 FNA 处理导致 AOB 和 NOB 同时受到抑制,从而导致反硝化氨氧化,但随后较高的 DO(1.5mg/L)和更长的曝气时间恢复了部分亚硝化。对于与氮转化相关的获得生物量的相对丰度,硝化单胞菌、亚硝酸菌和 Nitrolancea 分别增加到 9.65%、10.27%和 4.35%,在 1.35mg/L 的 FNA 处理开始时,亚硝酸菌和 Nitrolancea 减少到 2.80%和 0.03%,而硝化单胞菌下降到 8.71%,76 天后。Ca. Brocadia 在 1.35mg/L 的 FNA 处理后恢复能力较差,相对丰度从 13.38%下降到 0.62%,原因是亚硝酸盐不足。分子生态网络分析表明,在厌氧氨氧化菌中,Ca. Kuenenia 和 Ca. Brocadia 与其他氮循环过程形成了重要的联系。此外,该策略显示出操作灵活性,因为它可以很容易地用于控制主流 PN/A 应用中絮状污泥系统中的 NOB。

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