絮状污泥调控强化厌氧氨氧化生物膜生长效能及微生物机制

Performance and microbial mechanisms of suspended sludge biomass management for enhancing ANAMMOX biofilm formation

  • 摘要: 主流厌氧氨氧化(ANAMMOX)技术的广泛应用受限于如何快速富集高纯度厌氧氨氧化菌(AnAOB)。传统生物膜系统具备良好的微生物持留能力,且AnAOB倾向于附着生长,但由于AnAOB生长缓慢,易受到反硝化菌(DB)对亚硝酸盐的竞争抑制,导致ANAMMOX生物膜启动周期较长、丰度较低,限制了其实际应用。为此,结合生物膜系统优势,提出“絮状污泥促启动—适时淘汰促富集”的动态调控策略,在系统启动初期,利用高浓度絮状污泥提供足量种源和EPS促进生物膜构建,系统启动后,通过调控絮状污泥生物量以缩短生物膜的启动周期,促进AnAOB富集。实验采用序批式反应器(SBR),接种纯絮状污泥,反应器内设置海绵和K3生物膜载体,经70天的启动培养后,通过分阶段排放絮状污泥(第71天排放部分,第141天彻底排空),最终在210天连续运行后,成功构建了稳定的纯生物膜系统。结果表明,该策略增强了ANAMMOX在脱氮过程中的主导作用,脱氮贡献率从83.53%增至91.34%,总氮去除效率(NRE)由81.94%提高至88.55%。16S rRNA测序结果显示,生物膜中主要AnAOB属为Candidatus_Jettenia,随着絮状污泥逐步排出,AnAOB相对丰度提升了5.13%。宏基因组分析进一步表明, Candidatus_Jettenia 在生物膜中主导氮代谢关键酶基因的表达;经调控后, NarG基因丰度上升, NorB基因丰度下降,促进了NO₃⁻向NO₂⁻的转化,加速了ANAMMOX反应底物的积累,进而强化了以ANAMMOX为主导的氮循环过程。因此,基于“絮状污泥促启动—适时淘汰促富集”的动态调控策略,为AnAOB在生物膜上高效富集提供了一种简单有效的方法,以期推动主流ANAMMOX技术在实际污水处理中的规模化应用。

     

    Abstract: The widespread application of mainstream anaerobic ammonium oxidation (ANAMMOX) technology is limited by the challenge of rapidly enriching high-purity anaerobic ammonium-oxidizing bacteria (AnAOB). Traditional biofilm systems exhibit excellent microbial retention capacity, and AnAOB tend to grow in attached forms. However, due to the slow growth rate of AnAOB and competition for nitrite by denitrifying bacteria (DB), the ANAMMOX biofilm startup period is prolonged, and their abuandance is low, hindering practical implementation. To address this, we propose a strategy of “suspended sludge-assisted startup followed by phased elimination for enrichment” combining the advantages of biofilm systems. In the early stage of system startup, high-concentration suspended sludge is used to provide sufficient species flock and EPS to promote biofilm formation. After system startup, the startup period of biofilm is shortened by regulating the biomass of suspended sludge to promote AnAOB enrichment. A sequencing batch reactor (SBR) was inoculated with pure suspended sludge and equipped with sponge and K3 biofilm carriers. After 70 days of startup cultivation, a stepwise discharge of suspended sludge was implemented (partial discharge on day 71 and complete removal on day 141). By day 210 of continuous operation, a stable pure biofilm system was successfully established. Results demonstrated that this strategy strengthened the dominant role of ANAMMOX in nitrogen removal, increasing its contribution from 83.53% to 91.34%, while the total nitrogen removal efficiency (NRE) improved from 81.94% to 88.55%. 16S rRNA sequencing revealed that the dominant AnAOB genus in the biofilm was Candidatus_Jettenia, whose relative abundance increased by 5.13% as floccular sludge was gradually discharged. Metagenomic analysis further confirmed that Candidatus_Jettenia dominated the expression of key nitrogen metabolism enzymes genes in the biofilm. After management, the abundance of NarG genes increased, while the abundance of NorB genes decreased, promoting the conversion of NO₃⁻ to NO₂⁻, accelerating the accumulation of ANAMMOX reaction substrates, and thereby enhancing the nitrogen cycling process driven primarily by ANAMMOX. Thus, the dynamic regulation strategy of "suspended sludge-assisted startup followed by phased elimination for enrichment" provides a simple yet effective method for efficient AnAOB enrichment in biofilms, offering promising potential for scaling up mainstream ANAMMOX technology in real wastewater treatment applications.

     

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