厌氧氨氧化颗粒污泥的快速培养与形成机理

刘晓宇, 王思慧, 薛耀琦, 郭延凯, 廉静, 郭建博. 厌氧氨氧化颗粒污泥的快速培养与形成机理[J]. 环境工程学报, 2016, 10(3): 1223-1227. doi: 10.12030/j.cjee.20160335
引用本文: 刘晓宇, 王思慧, 薛耀琦, 郭延凯, 廉静, 郭建博. 厌氧氨氧化颗粒污泥的快速培养与形成机理[J]. 环境工程学报, 2016, 10(3): 1223-1227. doi: 10.12030/j.cjee.20160335
Liu Xiaoyu, Wang Sihui, Xue Yaoqi, Guo Yankai, Lian Jing, Guo Jianbo. Rapid cultivation and formation mechanism of ANAMMOX granular sludge[J]. Chinese Journal of Environmental Engineering, 2016, 10(3): 1223-1227. doi: 10.12030/j.cjee.20160335
Citation: Liu Xiaoyu, Wang Sihui, Xue Yaoqi, Guo Yankai, Lian Jing, Guo Jianbo. Rapid cultivation and formation mechanism of ANAMMOX granular sludge[J]. Chinese Journal of Environmental Engineering, 2016, 10(3): 1223-1227. doi: 10.12030/j.cjee.20160335

厌氧氨氧化颗粒污泥的快速培养与形成机理

  • 基金项目:

    河北省杰出青年科学基金(E2012208012)

    河北省高校百名优秀创新人才支持计划(II)(BR2-211)

    河北省高校重点学科建设项目

    国家自然科学基金青年科学基金项目(51208170)

  • 中图分类号: X703.1

Rapid cultivation and formation mechanism of ANAMMOX granular sludge

  • Fund Project:
  • 摘要: 利用反硝化颗粒污泥掺杂少量厌氧氨氧化污泥启动厌氧氨氧化反应器,掺杂体积比为10:1,旨在快速启动厌氧氨氧化反应器并培养厌氧氨氧化颗粒污泥。结果表明,反应器连续运行60 d,成功培养出厌氧氨氧化颗粒污泥。反应器启动可分为细胞自溶期、活性提高期以及活性稳定期3阶段,细胞自溶期,颗粒污泥大量裂解,PN/PS由0.6升高到1.25,VSS/SS由0.45降低至0.38。活性提高期,PN/PS比值降低,VSS/SS比值回升。反应器进入活性稳定期,NH4-N、NO2-N、NO3-N 3种氮素转化比率维持在理论值1:1.32:0.26左右,PN/PS比值继续降低至0.6,VSS/SS比值回升至0.41。培养过程中污泥颜色由黑经棕逐渐变为红色,内部有大量类似于厌氧氨氧化菌的球型菌和椭球型菌。
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  • [1] Jetten M. S. M., Strous M., van de Pas-schoonen K. T., et al. The anaerobic oxidation of ammonium. FEMS Microbiology Reviews, 1999, 22(5):421-437
    [2] van der Star W. R. L., Abma W. R., Blommers D., et al. Startup of reactors for anoxic ammonium oxidation:Experiences from the first full-scale anammox reactor in Rotterdam. Water Research, 2007, 41(18):4149-4163
    [3] 郝晓地, 仇付国, van der Star W. R. L., 等. 厌氧氨氧化技术工程化的全球现状及展望. 中国给水排水, 2007, 23(28):15-19 Hao Xiaodi, Qiu Fuguo, van der Star W. R. L., et al. Global situation of developing ANAMMOX technology towards engineering application. China Water & Wastewater, 2007, 23(28):15-19(in Chinese)
    [4] 任宏洋, 张代钧, 丛丽影. EGSB反应器中实现完全自营养脱氮与运行优化. 环境科学, 2009, 30(5):1454-1460 Ren Hongyang, Zhang Daijun, Cong Liying. Implement of completely autotrophic nitrogen removal in EGSB reactor and its operation optimization. Environmental Science, 2009, 30(5):1454-1460(in Chinese)
    [5] López H., Puig S., Ganigué R., et al. Start-up and enrichment of a granular anammox SBR to treat high nitrogen load wastewaters. Journal of Chemical Technology and Biotechnology, 2008, 83(3):233-241
    [6] Dapena-Mora A., Campos J. L., Mosquera-Corral A., et al. Stability of the ANAMMOX process in a gas-lift reactor and a SBR. Journal of Biotechnology, 2004, 110(2):159-170
    [7] 丛岩, 黄晓丽, 王小龙, 等. 厌氧氨氧化颗粒污泥的快速形成. 化工学报, 2014, 65(2):664-671 Cong Yan, Huang Xiaoli, Wang Xiaolong, et al. Faster formation of anammox granular sludge. CIESC Journal, 2014, 65(2):664-671(in Chinese)
    [8] 唐崇俭, 郑平, 汪彩华, 等. 高负荷厌氧氨氧化EGSB反应器的运行及其颗粒污泥的ECP特性. 化工学报, 2010, 61(3):732-739 Tang Chongjian, Zheng Ping, Wang Caihua, et al. Granulation and characteristics of extracellular polymers of anammox sludge in high-load EGSB reactor. CIESC Journal, 2010, 61(3):732-739(in Chinese)
    [9] 国家环境保护总局. 水和废水监测分析方法(第4版). 北京:中国环境科学出版社, 2002
    [10] Wu Jing, Zhou Hongming, Li Huaizhi, et al. Impacts of hydrodynamic shear force on nucleation of flocculent sludge in anaerobic reactor. Water Research, 2009, 43(12):3029-3036
    [11] Strous M., Kuenen J. G., Jetten M. S. M. Key physiology of anaerobic ammonium oxidation. Applied and Environmental Microbiology, 1999, 65(7):3248-3250
    [12] 张蕾. 厌氧氨氧化性能的研究. 杭州:浙江大学博士学位论文, 2009 Zhang Lei. Performance of anaerobic ammonium oxidation. Hangzhou:Doctor Dissertation of Zhejiang University, 2009(in Chinese)
    [13] Liu Yongqiang, Liu Yu, Tay J. H. The effects of extracellular polymeric substances on the formation and stability of biogranules. Applied Microbiology and Biotechnology, 2004, 65(2):143-148
    [14] 朱邦辉, 万金保. 好氧颗粒污泥中胞外聚合物作用机理的探讨. 江西科学, 2009, 27(6):848-854 Zhu Banghui, Wan Jinbao. Study on mechanism of extracellular polymeric substances in aerobic granular sludge. Jiangxi Science, 2009, 27(6):848-854(in Chinese)
    [15] Wang Zhiping, Liu Lili, Yao Jie, et al. Effects of extracellular polymeric substances on aerobic granulation in sequencing batch reactors. Chemosphere, 2006, 63(10):1728-1735
    [16] Franco A., Roca E., Lema J. M. Granulation in high-load denitrifying upflow sludge bed (USB) pulsed reactors. Water Research, 2006, 40(5):871-880
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    [18] van de Graaf A. A., de Bruijn P., Robertson L. A., et al. Autotrophic growth of anaerobic ammonium-oxidizing micro-organisms in a fluidized bed reactor. Microbiology, 1996, 142(8):2187-2196
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出版历程
  • 收稿日期:  2014-12-15
  • 刊出日期:  2016-03-18
刘晓宇, 王思慧, 薛耀琦, 郭延凯, 廉静, 郭建博. 厌氧氨氧化颗粒污泥的快速培养与形成机理[J]. 环境工程学报, 2016, 10(3): 1223-1227. doi: 10.12030/j.cjee.20160335
引用本文: 刘晓宇, 王思慧, 薛耀琦, 郭延凯, 廉静, 郭建博. 厌氧氨氧化颗粒污泥的快速培养与形成机理[J]. 环境工程学报, 2016, 10(3): 1223-1227. doi: 10.12030/j.cjee.20160335
Liu Xiaoyu, Wang Sihui, Xue Yaoqi, Guo Yankai, Lian Jing, Guo Jianbo. Rapid cultivation and formation mechanism of ANAMMOX granular sludge[J]. Chinese Journal of Environmental Engineering, 2016, 10(3): 1223-1227. doi: 10.12030/j.cjee.20160335
Citation: Liu Xiaoyu, Wang Sihui, Xue Yaoqi, Guo Yankai, Lian Jing, Guo Jianbo. Rapid cultivation and formation mechanism of ANAMMOX granular sludge[J]. Chinese Journal of Environmental Engineering, 2016, 10(3): 1223-1227. doi: 10.12030/j.cjee.20160335

厌氧氨氧化颗粒污泥的快速培养与形成机理

  • 1. 河北科技大学环境科学与工程学院,河北省污染防治生物技术实验室, 石家庄 050018
基金项目:

河北省杰出青年科学基金(E2012208012)

河北省高校百名优秀创新人才支持计划(II)(BR2-211)

河北省高校重点学科建设项目

国家自然科学基金青年科学基金项目(51208170)

摘要: 利用反硝化颗粒污泥掺杂少量厌氧氨氧化污泥启动厌氧氨氧化反应器,掺杂体积比为10:1,旨在快速启动厌氧氨氧化反应器并培养厌氧氨氧化颗粒污泥。结果表明,反应器连续运行60 d,成功培养出厌氧氨氧化颗粒污泥。反应器启动可分为细胞自溶期、活性提高期以及活性稳定期3阶段,细胞自溶期,颗粒污泥大量裂解,PN/PS由0.6升高到1.25,VSS/SS由0.45降低至0.38。活性提高期,PN/PS比值降低,VSS/SS比值回升。反应器进入活性稳定期,NH4-N、NO2-N、NO3-N 3种氮素转化比率维持在理论值1:1.32:0.26左右,PN/PS比值继续降低至0.6,VSS/SS比值回升至0.41。培养过程中污泥颜色由黑经棕逐渐变为红色,内部有大量类似于厌氧氨氧化菌的球型菌和椭球型菌。

English Abstract

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