基于缺氧时间调控内源性亚硝酸盐强化N-EPD-CANON工艺脱氮研究

李冬, 陈晓义, 傅思博, 张景昭, 张杰

中国环境科学 ›› 2025, Vol. 45 ›› Issue (5) : 2470-2480.

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中国环境科学 ›› 2025, Vol. 45 ›› Issue (5) : 2470-2480.
水污染与控制

基于缺氧时间调控内源性亚硝酸盐强化N-EPD-CANON工艺脱氮研究

  • 李冬1, 陈晓义1, 傅思博1, 张景昭1, 张杰1,2
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Enhanced nitrogen removal in the N-EPD-CANON process by regulating endogenous nitrite accumulation based on anoxic time

  • LI Dong1, CHEN Xiao-yi1, FU Si-bo1, ZHANG Jing-zhao1, ZHANG Jie1,2
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摘要

采用SBR反应器,以模拟市政污水为进水基质,启动硝化-内源部分反硝化-全程自养脱氮(N-EPD-CANON)工艺.实验通过调控EPD单元缺氧时间考察了单元内亚硝酸盐积累量变化对CANON工艺脱氮性能,功能菌活性以及微生物群落结构的影响.结果表明:在缺氧时间为40min时,EPD单元可以有效地捕获进水有机物,同时维持有利于CANON稳定运行的适量浓度的内源性亚硝酸盐.长期稳定运行下CANON反应器的总氮去除率达到86.43%,比厌氧氨氧化活性(SAA)达到0.82gN/(gVSS·d).此外,EPS质量分数逐渐增长到69.17mg/gVSS,再通过3D-EEM结合PARAFAC技术对污泥的EPS荧光组分进行分析表明,内源性亚硝酸盐的强化作用能够在不改变EPS组成成分的前提下,有效提升了芳香族蛋白质的含量,有助于污泥颗粒化及其稳定性的提高.微生物群落分析揭示,在EPD系统中CandidatusCompetibacter为优势菌属占24.61%,CANON系统中Nitrosomonas的相对丰度为2.67%,这保证了AnAOB菌的NO2--N供应.此外,AnAOB的主要组成部分CandidatusBrocadia菌属的相对丰度也达到了13.34%.

Abstract

Employed a SBR to simulate municipal wastewater as the influent matrix and initiated the Nitritation-Enhanced Partial Denitrification-Complete Autotrophic Nitrogen Removal Over Nitrite (N-EPD-CANON) process. The anoxic duration within the EPD system was meticulously adjusted to scrutinize the impact on endogenous nitrite accumulation and the consequent performance alterations within the CANON system. The objective was to elucidate the influence of anoxic time on endogenous nitrite concentration and its subsequent effects on nitrogen removal efficiency, the activity of functional microbial groups, and the structure of microbial communities within the CANON process. The findings revealed that an anoxic duration of 40minutes within the EPD system was optimal for capturing influent organic matter while concurrently promoting the endogenous nitrite to accumulate at a favorable concentration of approximately 4mg/L. Under sustained operational conditions, the CANON reactor achieved a total nitrogen removal rate of 86.43%. The specific anammox activity (SAA) was determined to be 0.82gN/(gVSS·d), the particular nitrate production rate (SNPR) was reduced to 0.28gN/(gVSS·d), and the specific ammonium removal rate (SAOR) was recorded at 0.70gN/(g VSS·d). Additionally, the application of 3D-EEM and PARAFAC techniques to analyze the fluorescence components of EPS in the sludge indicated that the intensification of endogenous nitrite had a beneficial effect on increasing the content of aromatic proteins within the EPS without altering its composition. Microbiota community analysis reveals that Candidatus_Competibacter is the dominant genus in the EPD system, accounting for 24.61%. In contrast, in the CANON system, the relative abundance of Nitrosomonas at 2.67% ensures the NO2--N supply for AnAOB, and Candidatus Brocadia, as the main genus of AnAOB, accounts for 13.34%.

关键词

反硝化聚糖菌 / 内源部分反硝化 / 全程自养脱氮工艺 / 市政污水

Key words

complete autotrophic nitrogen removal over nitrite(CANON) / denitrifying glycogenaccumulating organisms(DGAOs) / endogenous partial denitrification / municipal wastewater

引用本文

导出引用
李冬, 陈晓义, 傅思博, 张景昭, 张杰. 基于缺氧时间调控内源性亚硝酸盐强化N-EPD-CANON工艺脱氮研究[J]. 中国环境科学. 2025, 45(5): 2470-2480
LI Dong, CHEN Xiao-yi, FU Si-bo, ZHANG Jing-zhao, ZHANG Jie. Enhanced nitrogen removal in the N-EPD-CANON process by regulating endogenous nitrite accumulation based on anoxic time[J]. China Environmental Science. 2025, 45(5): 2470-2480
中图分类号: X703.5   

参考文献

[1] Miao Y, Zhang L, Yang Y, et al. Start-up of single-stage partial nitrification-anammox process treating low-strength swage and its restoration from nitrate accumulation [J]. Bioresource Technology, 2016,218:771-779.
[2] Yue X, Yu G, Liu Z, et al. Fast start-up of the CANON process with a SABF and the effects of pH and temperature on nitrogen removal and microbial activity [J]. Bioresource Technology, 2018,254:157-165.
[3] Nielsen M, Bollmann A, Sliekers O, et al. Kinetics, diffusional limitation and microscale distribution of chemistry and organisms in a CANON reactor [J]. FEMS Microbiology Ecology, 2005,51(2):247- 256.
[4] Gong S, Qin Y, Zheng S, et al. The rapid start-up of CANON process through adding partial nitration sludge to ANAMMOX system [J]. Journal of Environmental Management, 2023,338:117821.
[5] Cao Y, van Loosdrecht M C M, Daigger G T. Mainstream partial nitritation–anammox in municipal wastewater treatment: status, bottlenecks, and further studies [J]. Applied microbiology and biotechnology, 2017,101(4):1365-1383.
[6] Zhang X, Zhang H, Ye C, et al. Effect of COD/N ratio on nitrogen removal and microbial communities of CANON process in membrane bioreactors [J]. Bioresource Technology, 2015,189:302-308.
[7] 付昆明,仇付国,左早荣.厌氧氨氧化技术应用于市政污水处理的前景分析[J]. 中国给水排水, 2015,31(4):8-13. Fu K M, Qiu F G, Zuo Z R. Prospect analysis of applying anaerobic ammonia oxidation technology to municipal sewage treatment [J]. China Water & Wastewater, 2015,31(4):8-13.
[8] 李冬,苏庆岭,梁瑜海,等.CANON颗粒污泥高效脱氮及处理生活污水实验研究[J]. 哈尔滨工业大学学报, 2015,47(8):79-86. Li D, Su Q L, Liang Y H, et al. Efficient nitrogen removal from domestic wastewater by CANON granular sludge [J]. Journal of Harbin Institute of Technology, 2015,47(8):79-86.
[9] Ma B, Wang S, Cao S, et al. Biological nitrogen removal from sewage via anammox: recent advances [J]. Bioresource Technology, 2016,200: 981-990.
[10] Chen W, Chen S, Wu J. Biomass segregation in the granules and flocs affects the role of heterotrophic bacteria in the ANAMMOX process [J]. Chemical Engineering Journal, 2020,392:123727.
[11] 付昆明,付巢,王会芳,等.亚硝酸盐对生物膜CANON工艺脱氮性能和N2O释放的影响[J]. 环境工程学报, 2018,12(10):2776-2782. Fu K M, Fu C, Wang H F, et al. Effects of nitrite on nitrogen removal performance and N2O emission in biofilm CANON process [J]. Chinese Journal of Environmental Engineering, 2018,12(10):2776- 2782.
[12] Szatkowska B, Cema G, Plaza E, et al. A one-stage system with partial nitritation and Anammox processes in the moving-bed biofilm reactor [J]. Water Science and Technology, 2007,55(8/9):19-26.
[13] 徐柏林.污水处理厂环境管理现状与污染防治对策研究[J]. 清洗世界, 2024,40(2):150-152. Xu B L. Research on the current status of environmental management and pollution prevention measures in sewage treatment plants [J]. Cleaning World, 2024,40(2):150-152.
[14] 张超,陈银广.聚糖菌的代谢机制及生物学特性研究进展[J]. 环境污染与防治, 2008,(8):78-81. Zhang C, Chen Y G. Research advances in the metabolic mechanisms and the microbial characterization of glycogen-accumulating organisms [J]. Environmental Pollution & Control, 2008,(8):78-81.
[15] Du R, Peng Y, Cao S, et al. Mechanisms and microbial structure of partial denitrification with high nitrite accumulation [J]. Applied Microbiology and Biotechnology, 2016,100:2011-2021.
[16] Liu Y, Peng L, Chen X, et al. Mathematical modeling of nitrous oxide production during denitrifying phosphorus removal process [J]. Environmental Science & Technology, 2015,49(14):8595-8601.
[17] Pawlowski L. Standard methods for the examination of water and wastewater, 18th edition [J]. Science of the Total Environment, 1994,142(3):228-277.
[18] Li G F, Huang B C, Cheng Y F, et al. Determination of the response characteristics of anaerobic ammonium oxidation bioreactor disturbed by temperature change with the spectral fingerprint [J]. Science of the Total Environment, 2020,719:137513.
[19] Sheng G P, Yu H Q, Li X Y. Extracellular polymeric substances (EPS) of microbial aggregates in biological wastewater treatment systems: a review [J]. Biotechnology Advances, 2010,28(6):882-894.
[20] Li G F, Ma W J, Cheng Y F, et al. A spectra metrology insight into the binding characteristics of Cu2+ onto anammox extracellular polymeric substances [J]. Chemical Engineering Journal, 2020,393:124800.
[21] Guo H, Tian L, Liu S, et al. The potent effects of polyoxometalates (POMs) on controlling sulfide and methane production from sewers [J]. Chemical Engineering Journal, 2023,453:139955.
[22] Zeng R J, Van Loosdrecht M C M, Yuan Z, et al. Metabolic model for glycogen ‐ accumulating organisms in anaerobic/aerobic activated sludge systems [J]. Biotechnology and Bioengineering, 2003,81(1): 92-105.
[23] Kowalski M S, Devlin T, di Biase A, et al. Accelerated start-up of a partial nitritation-anammox moving bed biofilm reactor [J]. Biochemical Engineering Journal, 2019,145:83-89.
[24] Li D, Dang Z, Zhang J. Study on two anammox start-up and operation strategies: Low-intensity direct current electric field and negative pressure [J]. Chemical Engineering Journal, 2022,435:134791.
[25] 付昆明,周厚田,苏雪莹,等.生物膜短程硝化系统的恢复及其转化为CANON工艺的过程[J]. 环境科学, 2017,38(4):1536-1543. Fu K M, Zhou H T, Su X Y, et al. Short-cut nitrification recovery and its transformation into CANON process in a biofilm reactor [J]. Environmental Science, 2017,38(4):1536-1543.
[26] 赵杰俊,刘祖文,蔡晓媛,等.短程硝化-厌氧氨氧化工艺控制方法与机理分析[J]. 工业水处理, 2021,41(10):36-43. Zhao J J, Liu Z W, Cai X Y, et al. Control method and mechanism analysis of partial nitritation-Anammox process [J]. Industrial Water Treatment, 2021,41(10):36-43.
[27] 夏琼琼,尚巍,郑兴灿,等.曝气方式对低基质CANON工艺的影响[J]. 中国给水排水, 2022,38(17):67-73. Xia Q Q, Shang W, Zheng X G, et al. Effect of aeration mode on the CANON process treating low ammonia nitrogen wastewater [J]. China Water & Wastewater, 2022,38(17):67-73.
[28] Sheng G, Yu H, Li X. Extracellular polymeric substances (EPS) of microbial aggregates in biological wastewater treatment systems: A review [J]. Biotechnology Advances, 2010,28(6):882-894.
[29] 陈重军,曹茜斐,邹馨怡,等.厌氧氨氧化颗粒污泥EPS的作用、成分及影响因素研究进展[J]. 环境工程学报, 2022,16(2):381-389. Chen C J, Cao Q F, Zou X Y, et al. Review on function, composition and influencing factors of EPS in anammox granular sludge [J]. Chinese Journal of Environmental Engineering, 2022,16(2):381-389.
[30] 刘丽,任婷婷,徐得潜,等.高强度好氧颗粒污泥的培养及特性研究[J]. 中国环境科学, 2008,28(4):360-364. Liu L, Ren T T, Xu D Q, et al. Cultivation and characteristics of the high strength aerobic granular sludge [J]. China Environmental Science, 2008,28(4):360-364.
[31] 王冬,王少坡,周瑶,等.胞外聚合物在污水处理过程中的功能及其控制策略[J]. 工业水处理, 2019,39(10):14-19. Wang D, Wang S P, Zhou Y, et al. Functions and control strategies of extracellular polymeric substances in wastewater treatment processes [J]. Industrial Water Treatment, 2019,39(10):14-19.
[32] Chen W, Westerhoff P, Leenheer J A, et al. Fluorescence excitation- emission matrix regional integration to quantify spectra for dissolved organic matter [J]. Environmental Science & Technology, 2003,37(24): 5701-5710.
[33] Zeng R J, Yuan Z, Keller J. Enrichment of denitrifying glycogenaccumulating organisms in anaerobic/anoxic activated sludge system [J]. Biotechnology and Bioengineering, 2003,81(4):397-404.
[34] 王琪,李冬,李鹏垚,等.厌/缺氧时间对好氧颗粒污泥同步硝化内源反硝化和除磷的影响[J]. 中国环境科学, 2022,42(9):4199-4206. Wang Q, Li D, Li P Y, et al. Effects of anaerobic/anoxic time on simultaneous nitrification - endogenous denitrification and phosphorous removal from aerobic granular sludge [J]. China Environmental Science, 2022,42(9):4199-4206.
[35] Kerrn-Jespersen J P, Henze M. Biological phosphorus uptake under anoxic and aerobic conditions [J]. Water Research, 1993,27(4):617- 624.
[36] Tayà C, Garlapati V K, Guisasola A, et al. The selective role of nitrite in the PAO/GAO competition [J]. Chemosphere, 2013,93(4):612-618.
[37] 鞠洪海.不同电子受体驯化聚糖菌反硝化过程及N2O释放特性[J]. 环境工程, 2020,38(9):113-118. Ju H H. Characteristics of denitrification and N2O emission of acclimated glycogen accumulating organisms using different electron acceptor [J]. Environmental Engineering, 2020,38(9):113-118.

基金

北京高校卓越青年科学家计划项目(BJJWAZYJH01201910005019)

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