CANON工艺的典型抑制及其恢复性策略

黄鹏飞, 张锦耀, 秦玉洁, 李伙生, 周少奇. CANON工艺的典型抑制及其恢复性策略[J]. 环境工程学报, 2016, 10(5): 2387-2393. doi: 10.12030/j.cjee.201412110
引用本文: 黄鹏飞, 张锦耀, 秦玉洁, 李伙生, 周少奇. CANON工艺的典型抑制及其恢复性策略[J]. 环境工程学报, 2016, 10(5): 2387-2393. doi: 10.12030/j.cjee.201412110
Huang Pengfei, Zhang Jinyao, Qin Yujie, Li Huosheng, Zhou Shaoqi. Typical inhibition of CANON process and its restorative strategy[J]. Chinese Journal of Environmental Engineering, 2016, 10(5): 2387-2393. doi: 10.12030/j.cjee.201412110
Citation: Huang Pengfei, Zhang Jinyao, Qin Yujie, Li Huosheng, Zhou Shaoqi. Typical inhibition of CANON process and its restorative strategy[J]. Chinese Journal of Environmental Engineering, 2016, 10(5): 2387-2393. doi: 10.12030/j.cjee.201412110

CANON工艺的典型抑制及其恢复性策略

  • 基金项目:

    国家自然科学基金资助项目(21277052,51578244)

    广东省省级科技计划项目(2014A050503025)

  • 中图分类号: X703

Typical inhibition of CANON process and its restorative strategy

  • Fund Project:
  • 摘要: 全程自养脱氮(CANON)工艺在110 d时,总氮去除负荷(NRR)达到了1.8 kg N/(m3·d)。在高溶解氧(DO)的条件下,CANON工艺脱稳失活,脱氮性能急剧下降,ANAMMOX菌受到抑制。采取减少曝气量,降低反应器中的DO,可以有效恢复CANON工艺的脱氮性能。在第327天时,进水氨氮浓度高达1 245.5 mg/L,氨氮和总氮去除效率分别达到98.4%和80.3%,而NRR高达了1 kg N/(m3·d)。此后,CANON工艺脱氮效果较为稳定,表明CANON工艺恢复效果明显。SEM分析表明,颗粒污泥表面附着大量的短杆状细菌,细菌之间联系紧密,部分颗粒污泥表面呈现网状结构,细菌之间通过丝状物联系形成颗粒污泥。能谱分析表明,颗粒污泥表面含有O、Na、P、Fe、Ca、C和Si等元素。
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  • [1] Sliekers A. O., Derwort N., Campos Gomez J. L., et al. Completely autotrophic nitrogen removal over nitrite in one single reactor. Water Research, 2002, 36(10): 2475-2482
    [2] 付昆明, 张杰, 曹相生, 等. CANON反应器运行稳定性及温度冲击的影响. 环境科学, 2012, 33(10): 3507-3512 Fu Kunming, Zhang Jie, Cao Xiangsheng, et al. Performance stability of CANON reactor and temperature impact. Environmental Science, 2012, 33(10): 3507-3512(in Chinese)
    [3] Chang Xiaoyan, Li Dong, Liang Yuhai, et al. Performance of a completely autotrophic nitrogen removal over nitrite process for treating wastewater with different substrates at ambient temperature. Journal of Environmental Sciences, 2013, 25(4): 688-697
    [4] Vázquez-Padín J. R., Pozo M. J., Jarpa M., et al. Treatment of anaerobic sludge digester effluents by the CANON process in an air pulsing SBR. Journal of Hazardous Materials, 2009, 166(1): 336-341
    [5] Cho S., Fujii N., Lee T., et al. Development of a simultaneous partial nitrification and anaerobic ammonia oxidation process in a single reactor. Bioresource Technology, 2011, 102(2): 652-659
    [6] 李伙生. 部分亚硝化耦合厌氧氨氧化的工艺控制及其垃圾渗滤液脱氮特性. 广州: 华南理工大学博士学位论文, 2013 Li Huosheng. Process control on partial nitritation coupled with anaerobic ammonium oxidation and its application to nitrogen removal from landfill leachate. Guangzhou: Doctor Dissertation of South China University of Technology, 2013(in Chinese)
    [7] 孟了, 陈永, 陈石. CANON工艺处理垃圾渗滤液中的高浓度氨氮. 给水排水, 2004, 30(8): 24-29 Meng Liao, Chen Yong, Chen Shi. CANON process in treating high concentrated ammonium of leachate. Water & Wastewater Engineering, 2004, 30(8): 24-29(in Chinese)
    [8] Liu Tao, Li Dong, Zeng Huiping, et al. Biodiversity and quantification of functional bacteria in completely autotrophic nitrogen-removal over nitrite (CANON) process. Bioresource Technology, 2012, 118: 399-406
    [9] Third K. A., Sliekers A. O., Kuenen J. G., et al. The CANON system (completely autotrophic nitrogen-removal over nitrite) under ammonium limitation: Interaction and competition between three groups of bacteria. Systematic and Applied Microbiology, 2001, 24(4): 588-596
    [10] 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
    [11] Daverey A., Su S. H., Huang Y. T., et al. Partial nitrification and anammox process: A method for high strength optoelectronic industrial wastewater treatment. Water Research, 2013, 47(9): 2929-2937
    [12] 付昆明, 张杰, 曹相生, 等. 好氧条件下CANON工艺的启动研究. 环境科学, 2009, 30(6): 1689-1694 Fu Kunming, Zhang Jie, Cao Xiangsheng, et al. Study of CANON process start-up under aerobic conditions. Environmental Science, 2009, 30(6): 1689-1694(in Chinese)
    [13] Scaglione D., Tornotti G., Teli A., et al. Nitrification denitrification via nitrite in a pilot-scale SBR treating the liquid fraction of co-digested piggery/poultry manure and agro-wastes. Chemical Engineering Journal, 2013, 228: 935-943
    [14] Helmer C., Tromm C., Hippen A., et al. Single stage biological nitrogen removal by nitritation and anaerobic ammonium oxidation in biofilm systems. Water Science and Technology, 2000, 43(1): 311-320
    [15] 陈婷婷. 厌氧氨氧化工艺运行性能及微生物特性研究. 杭州: 浙江大学博士学位论文, 2013 Chen Tingting. Process performance and microbiology characteristics of anaerobic ammonium oxidation. Hangzhou: Doctor Dissertation of Zhejiang University, 2013(in Chinese)
    [16] Wang Lan, Zheng Ping, Chen Tingting, et al. Performance of autotrophic nitrogen removal in the granular sludge bed reactor. Bioresource Technology, 2012, 123: 78-85
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    [18] Liu Tao, Li Dong, Zeng Huiping, et al. Distribution and genetic diversity of functional microorganisms in different CANON reactors. Bioresource Technology, 2012, 123: 574-580
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出版历程
  • 收稿日期:  2015-03-22
  • 刊出日期:  2016-06-03

CANON工艺的典型抑制及其恢复性策略

  • 1.  华南理工大学环境与能源学院, 广州 510006
  • 2.  华南理工大学亚热带建筑科学国家重点实验室, 广州 510640
  • 3.  广东省教育厅环境保护与生态修复重点实验室, 广州 510006
  • 4.  贵州科学院, 贵阳 550001
基金项目:

国家自然科学基金资助项目(21277052,51578244)

广东省省级科技计划项目(2014A050503025)

摘要: 全程自养脱氮(CANON)工艺在110 d时,总氮去除负荷(NRR)达到了1.8 kg N/(m3·d)。在高溶解氧(DO)的条件下,CANON工艺脱稳失活,脱氮性能急剧下降,ANAMMOX菌受到抑制。采取减少曝气量,降低反应器中的DO,可以有效恢复CANON工艺的脱氮性能。在第327天时,进水氨氮浓度高达1 245.5 mg/L,氨氮和总氮去除效率分别达到98.4%和80.3%,而NRR高达了1 kg N/(m3·d)。此后,CANON工艺脱氮效果较为稳定,表明CANON工艺恢复效果明显。SEM分析表明,颗粒污泥表面附着大量的短杆状细菌,细菌之间联系紧密,部分颗粒污泥表面呈现网状结构,细菌之间通过丝状物联系形成颗粒污泥。能谱分析表明,颗粒污泥表面含有O、Na、P、Fe、Ca、C和Si等元素。

English Abstract

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