Review on the formation of Anammox granular sludge

doi:10.19965/j.cnki.iwt.2023-0881

Abstract

Abstract:

As a new nitrogen removal technology, Anammox has the advantages of energy conservation, emission reduction and no additional carbon source. The Anammox technology has great application value in the treatment of wastewater with low C/N. However, Anammox can not be quickly started up due to sludge loss in the practical application. Adding mature Anammox granular sludge (AnGS) is an effective way to overcome the above-mentioned challenges. The formation process, mechanism and influencing factors of AnGS were introduced, and the technical issues related to the rapid cultivation of AnGS were summarized. The models of AnGS formation and related researches based on various models were explored. The structural characteristics and microbial community characteristics of AnGS were introduced. The relationship between anaerobic ammonia oxidizing bacteria(AnAOB) and AnGS was elucidated. The effects of inoculation sludge type, reactor type, nitrogen loading rate, organic concentration, quorum sensing, and external forces on the formation of AnGS were analyzed. The phenomenon of AnGS floating was introduced. The relationship between AnGS floating and nitrogen loading rate, bubble was analyzed and discussed. The current issues with AnGS technology were summarized and the research direction on AnGS was prospected. The purpose was to provide reference for the formation of AnGS in full-scale industrialization.

Key words: Anammox, granular sludge, formation models, influence factors

摘要：

作为新型脱氮工艺，厌氧氨氧化（Anammox）具有节能减排、无需外加碳源等优点，在处理低C/N废水领域具有极高的应用价值，但在实际应用过程中因存在污泥流失问题，该工艺难以快速启动。投加成熟的厌氧氨氧化颗粒污泥（AnGS）是攻克上述难题的有效途径。对AnGS的形成过程、机理及影响因素进行综述，归纳总结AnGS快速培养的相关技术问题。介绍了AnGS的形成假说及基于各类假说的相关研究成果；阐述了AnGS的结构特征和微生物群落特征，总结分析了厌氧氨氧化菌（AnAOB）同AnGS之间的关系；分析了接种污泥类型、反应器类型、氮负荷率、有机物浓度、群体感应、外力作用等因素对AnGS形成的影响；介绍了AnGS的上浮现象，分析讨论了AnGS上浮与氮负荷率及颗粒污泥气体通道的关系；总结了现阶段AnGS技术存在的问题，并对AnGS的研究方向进行了展望，旨在为大规模工业化形成AnGS提供参考。

关键词: 厌氧氨氧化, 颗粒污泥, 形成假说, 影响因素

CLC Number:

X703

Yafeng LI, Jianbo WU, Chi ZHANG. Review on the formation of Anammox granular sludge[J]. Industrial Water Treatment, 2024, 44(9): 23-30.

李亚峰, 伍健伯, 张驰. 厌氧氨氧化颗粒污泥形成的研究进展[J]. 工业水处理, 2024, 44(9): 23-30.

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属	种	最大比生长速率/d^-1	来源	参考文献
Brocadia	Anammoxidans	0.06	废水	〔37〕
	Fulgida	0.13	废水	〔38〕
	Sinica	0.33	废水	〔39〕
	Brasiliensis		废水	〔40〕
	Caroliniensis	0.12	废水	〔41〕
	Sapporoensis	0.21	废水	〔42〕
Kuenenia	Stuttgartiensis	0.28	废水	〔43〕
Jettenia	Asiatica		淡水	〔44〕
	Caeni	0.18	废水	〔45〕
	Moscovienalis	0.03	废水	〔46〕
Scalindua	Sorokinii		海水	〔47〕
	Japonica	0.18	海洋沉积物	〔48〕
	Brodae		废水	〔49〕
	Wagneri		废水	〔49〕
	Arabica		海水	〔50〕
	Sinooilfield		含油废水	〔51〕
	Rubra		海水	〔52〕
	Richardsii		海水	〔53〕
	Zhenghei		海洋沉积物	〔54〕
	Profunda	0.05	海水	〔55〕
	Marina		海洋沉积物	〔56〕
Anammoxoglobus	Propionicus		废水	〔57〕
Anammoxoglobus	Sulfate		废水	〔58〕
Anammoxomicrobium	Moscowii	0.02	淡水	〔59〕

属	种	最大比生长速率/d^-1	来源	参考文献
Brocadia	Anammoxidans	0.06	废水	〔37〕
	Fulgida	0.13	废水	〔38〕
	Sinica	0.33	废水	〔39〕
	Brasiliensis		废水	〔40〕
	Caroliniensis	0.12	废水	〔41〕
	Sapporoensis	0.21	废水	〔42〕
Kuenenia	Stuttgartiensis	0.28	废水	〔43〕
Jettenia	Asiatica		淡水	〔44〕
	Caeni	0.18	废水	〔45〕
	Moscovienalis	0.03	废水	〔46〕
Scalindua	Sorokinii		海水	〔47〕
	Japonica	0.18	海洋沉积物	〔48〕
	Brodae		废水	〔49〕
	Wagneri		废水	〔49〕
	Arabica		海水	〔50〕
	Sinooilfield		含油废水	〔51〕
	Rubra		海水	〔52〕
	Richardsii		海水	〔53〕
	Zhenghei		海洋沉积物	〔54〕
	Profunda	0.05	海水	〔55〕
	Marina		海洋沉积物	〔56〕
Anammoxoglobus	Propionicus		废水	〔57〕
Anammoxoglobus	Sulfate		废水	〔58〕
Anammoxomicrobium	Moscowii	0.02	淡水	〔59〕

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