Abstract:An integrated PN/A denitrification treatment system was constructed with a mixture of anammox granular sludge and floc sludge. Efficient denitrification of sludge digestion supernatant pretreated with thermal hydrolysis was achieved through the optimization of operating parameters. By inoculating AnAOB biofilm sludge and ordinary activated sludge simultaneously and keeping a high FA (>20mg/L) and low aeration (DO£0.2mg/L), the partial nitrification and anammox reaction was rapidly initiated, and the nitrous accumulation rate got over 85% while the denitrification load reached 0.60kgN/(m3·d). The diluted digestion supernatant still had a certain inhibition on AnAOB activity, resulting in the total nitrogen load of the reactor decreased to less than 0.20kgN/(m3·d). However, the abundance of AnAOB in the system exhibited an overall increasing trend, indicating that the proliferation of AnAOB was not completely restrained. The average median diameter of the sludge mixture in the system increased slowly from 53μm to 109μm. Results of quantitative PCR and high-throughput sequencing showed that the treatment system enriched the AnAOB with a higher purity, the maximum abundance ratio could reach 8.06% with the dominant genus being Kuenenia. In addition, in the 93rd run cycle, the abundance ratio of Kuenenia in granular sludge was higher than that of AOB, which was 5.26%; while in the floc sludge, the abundance of Nitrosomonas for nitrification accounted for 1.64%, higher than that of AnAOB. This demonstrated the different spatial distribution characteristics of AOB and AnAOB abundance.
姚雪薇.两段式MBBR亚硝化-厌氧氨氧化处理污泥热水解消化液技术研究[D]. 西安:西安建筑科技大学, 2021. Yao X Y. Two-stage MBBR nitrification-anammox treatment of sludge thermal hydrolysis digestate technology[D]. Xi'an, Xi'an University of Architecture and Technology, 2021.
[2]
韩晓宇,黄京,刘新春,等.厌氧氨氧化技术处理热水解消化液的实验研究[J]. 中国环境科学, 2017,37(7):2542-2549. Han X Y, Huang J, Liu X C, et al. Experimental study on the treatment of thermally hydrolyzed digestate by anammox technology[J]. China Environmental Science, 2017,37(7):2542-2549.
[3]
Gu Z L, Li Y, et al. Inhibition of anammox by sludge thermal hydrolysis and metagenomic insights[J]. Bioresource Technology, 2018,270:46-54.
[4]
Strous M, Fuerst J A, Kramer E H, et al. Missing lithotroph identified as new planctomycete[J]. Nature, 1999,400:446-449.
[5]
Henze M, van Loosdrecht M, Ekama G, et al. Biological Wastewater Treatment:Principles, Modelling and Design[M]. London:IWA Publishing, 2008,pp:139-154.
[6]
Morales N, Val Del Río Á, Vázquez-Padín J R, et al. Integration of the anammox process to the rejection water and main stream lines of WWTPs[J]. Chemosphere, 2015,140:99-105.
[7]
Siegrist H, Salzgeber D, Eugster J, et al. Anammox brings WWTP closer to energy autarky due to increased biogas production and reduced aeration energy for N-removal[J]. Water Science & Technology, 2008,57(3):383-388.
[8]
Liang Z, Liu J. Landfill leachate treatment with a novel process:Anaerobic ammonium oxidation (ANAMMOX) combined with soil infiltration system[J]. Journal of Hazardous Materials, 2008,151(1):202-212.
[9]
Figueroa M, Vázquez-Padín J R, Mosquera-Corral A, et al. Is the CANON reactor an alternative for nitrogen removal from pre-treated swine slurry[J]. Biochemical Engineering Journal, 2012,65:23-29.
[10]
Shalini S S, Joseph K. Start-up of the SHARON and anammox process in landfill bioreactors using aerobic and anaerobic ammonium oxidising biomass[J]. Bioresource Technology, 2013,149(4):474-485.
[11]
Jenni S, Vlaeminck S, Morgenroth E, et al. Successful application of nitritation/anammox towastewater with elevated organic carbon to ammonia ratios[J]. Water Research, 2014,49:316-326.
[12]
Yao H, Li H, Xu J, et al. Inhibitive effects of chlortetracycline on performance of the nitritation-anaerobic ammonium oxidation (ANAMMOX) process and strategies for recovery[J]. Journal of Environmental Sciences, 2018,70(8):29-36.
[13]
Qian F Y, Huang Z H, Liu Y X, et al. Conversion of full nitritation to partial nitritation/anammox in a continuous granular reactor for low-strength ammonium wastewater treatment at 20℃[J]. Biodegradation, 2021,32(1):87-98.
[14]
Wang L, Zheng P, Chen T T, et al. Performance of autotrophic nitrogen removal in the granular sludge bed reactor[J]. Bioresource Technology, 2012,123:78-85.
[15]
Vlaeminck S E, Cloetens L F F, Carballa M, et al. Granular biomass capable of partial nitritation and anammox[J]. Water Science & Technology, 2008,58(5):1113-1120.
[16]
Helio Lox pez, Sebastia Puig, Ramon Ganigue, et al. Start-up and enrichment of a granular anammox SBR to treat high nitrogen load wastewaters[J]. Journal of Chemical Technology and Biotechnology, 2008,83(3):233-241.
[17]
Dapena-Mora A, Campos J L, Mosquera-Corral A, Jetten M S M, Méndez R. Stability of the ANAMMOX process in a gas-lift reactor and a SBR[J]. Journal of Biotechnology, 2004,110(2):159-170.
[18]
国家环境保护局.水和废水监测分析方法[M]. (第4版).北京:中国环境科学出版社, 2002. State Environmental Protection Administration. Water and Wastewater Monitoring and Analysis Methods[M]. (4th). Beijing:China Environmental Science Press, 2002.
[19]
王佳伟,高永青,孙丽欣,等.中试SBR内好氧颗粒污泥培养和微生物群落变化[J]. 中国给水排水, 2019,35(7):1-7,14. Wang J W, Gao Y Q, Sun L X, et al. Aerobic granular sludge culture and microbial community changes in pilot-scale SBR[J]. China Water Supply and Drainage, 2019,35(7):1-7,14.
[20]
Miao Y, Peng Y, Liang Z, et al. Partial nitrification-anammox (PNA) treating sewage with intermittent aeration mode:Effect of influent C/N ratios[J]. Chemical Engineering Journal, 2018,334:664-672.
[21]
付璐璐,李思琦,甄毓,等.用于海洋沉积物中厌氧氨氧化细菌分子生态学研究的引物比较[J]. 中国海洋大学学报:自然科学版, 2019, 49(9):80-91. Fu L L, Li S Q, Zhen Y, et al. Comparison of primers for the molecular ecology of anammox bacteria in marine sediments[J]. Journal of Ocean University of China:Natural Science Edition, 2019,49(9):80-91.
[22]
Qian F Y, Huang Z H, Liu Y X, et al. Conversion of full nitritation to partial nitritation/anammox in a continuous granular reactor for low-strength ammonium wastewater treatment at 20℃[J]. Biodegradation, 2021,32(1):87-98.
[23]
Qian F Y, Wang J F, Shen Y L, et al. Achieving high performance completely autotrophic nitrogen removal in a continuous granular sludge reactor[J]. Biochemical Engineering Journal, 2017,118:97-104.
[24]
黄子恒,张立,崔舒惠,等.冷冻PN/A颗粒污泥快速活化过程中的污泥形态与菌群演化特征分析[J]. 环境科学, 2022,43(2):920-927. Huang Z H, Zhang L, Cui S H, et al. Analysis on the characteristics of sludge morphology and flora evolution during the rapid activation of frozen PN/A granular sludge[J]. Environmental Science, 2022,43(2):920-927.
[25]
Zhang Q, Haydee DC, Su C, et al. Deammonification for digester supernatant pretreated with thermal hydrolysis:overcoming inhibition through process optimization[J]. Enviromental Biotechnology, 2016, 100:5595-5606.
[26]
Zhang Q, Siegfried E, Christine D, et al. Supernatant organics form anaerobic digestion after thermal hydrolysis cause direct and/or diffusional activity loss for nitritation and anammox[J]. Water Research, 2018,143:270-281.
[27]
Figdore B, Bowden G, Stinson B, et al. Treatment of Dewatering Sidestream from a Thermal Hydrolysis-Mesophilic Anaerobic Digestion Process with a Single-Sludge Deammonification Process[J]. Proceedings of the Water Environment Federation, 2011, 2011(18):249-264.
[28]
汪瑶琪,喻徐良,陈重军,等.有机物对厌氧氨氧化菌活性影响研究进展[J]. 化学通报, 2017,80(2):173-178. Wang Y Q, Yu X L, Chen C J, et al. Research progress on the effect of organic matter on the activity of anammox bacteria[J]. Bulletin of Chemistry, 2017,80(2):173-178.
[29]
杨延栋,黄京,韩晓宇,等.一体式厌氧氨氧化工艺处理高氨氮污泥消化液的启动[J]. 中国环境科学, 2015,35(4):1082-1087. Yang Y D, Huang J, Han X Y, Zhang L, Zhang S J, Peng Y Z. Start-up of integrated anaerobic ammonium oxidation process for treating high ammonia nitrogen sludge digestate[J]. China Environmental Science, 2015,35(4):1082-1087.
[30]
周梦雨,彭党聪,韩芸,等.间歇曝气对部分硝化-厌氧氨氧化处理氨氮废水的影响[J]. 中国环境科学, 2022,42(3):1120-1127. Zhou M Y, Peng D C, Han Y, et al. Effects of intermittent aeration on partial nitrification-anammox treatment of ammonia nitrogen wastewater[J]. Environmental Science in China, 2022,42(3):1120-1127.
[31]
Zhang D, Wang G P, Dai X H. Operation of pilot-scale nitrification-anammox reactors for the treatment of reject-water produced from the anaerobic digestion of thermal hydrolysis-treated sludge[J]. Bioresource Technology, 2020,314:123717.
[32]
Ochs P, Martin B D,Germain E, et al. Ammonia removal from thermal hydrolysis dewatering liquors via three different deammonification technologies[J]. Science of The Total Environment, 2020,755(Pt 1):142684.
[33]
Han X Y, Zhang S J, Yang S H, et al. Full-scale partial nitritation/anammox (PN/A) process for treating sludge dewatering liquor from anaerobic digestion after thermal hydrolysis[J]. Bioresource Technology, 2020,297:122380.