厌氧氨氧化反应快速启动方法的研究进展
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摘要
当今水体污染中氮素污染问题日益突出。厌氧氨氧化作为一种新型的生物脱氮技术,和传统脱氮工艺相比,在处理高氨氮废水方面有着较高的应用价值。对近年来在厌氧氨氧化反应启动方面所做的研究进行总结,探讨了不同污泥源、反应器对厌氧氨氧化启动的影响,并分析了影响厌氧氨氧化反应器启动的可控因素,以期为快速启动厌氧氨氧化反应提供帮助。
Nowadays,water contamination by nitrogen is increasingly conspicuous. Compared with the conventional biological denitrification technique,the emerging anaerobic ammonia oxidation( ANAMMOX) showed great application value for the treatment of wastewater with high ammonia nitrogen concentration. In this study,based on the recent researches about the activation of ANAMMOX,the influences of sludge source and reactors on ANAMMOX activation were investigated,and the related controllable factors were also analyzed. This would provide theoretical and experimental guidance for the quick activation of ANAMMOX process.
Nowadays,water contamination by nitrogen is increasingly conspicuous. Compared with the conventional biological denitrification technique,the emerging anaerobic ammonia oxidation( ANAMMOX) showed great application value for the treatment of wastewater with high ammonia nitrogen concentration. In this study,based on the recent researches about the activation of ANAMMOX,the influences of sludge source and reactors on ANAMMOX activation were investigated,and the related controllable factors were also analyzed. This would provide theoretical and experimental guidance for the quick activation of ANAMMOX process.
引文
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[2]郑平,胡宝兰,徐向阳.新型生物脱氮理论与技术[M].北京:科学出版社,2004.
[3]Li Z,Xu X,Shao B,et al.Anammox granules formation and performance in a submerged anaerobic membrane bioreactor[J].Chemical Engineering Journal,2014,254(7):9-16.
[4]Tsushima I,Ogasawara Y,Kindaichi T,et al.Development of high-rate anaerobic ammonium-oxidizing(anammox)biofilm reactors[J].Water Research,2007,41(8):1623.
[5]于德爽,赵丹,李津,等.接种不同污泥源条件下厌氧氨氧化菌的特性[J].环境工程学报,2013,7(11):4339-4345.
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[7]李祥,黄勇,袁怡,等.不同泥源对厌氧氨氧化反应器启动的影响[J].环境工程学报,2012,6(7):2143-2148.
[8]宋振辉,胡筱敏,王宇佳.反应器类型及接种污泥对厌氧氨氧化工艺启动阶段的影响[J].环境工程,2017,35(5):58-63.
[9]徐相龙,刘国华,范强,等.SBR反应器厌氧氨氧化系统启动过程中细菌群落结构的变化[J].环境科学学报,2017,37(5):1695-1703.
[10]胡勇有,梁辉强,雒怀庆.厌氧序批式反应器培养厌氧氨氧化污泥[J].华南理工大学学报(自然科学版),2005,33(10):93-97.
[11]周凌,操家顺,蔡娟,等.低浓度氨氮条件下厌氧氨氧化反应器的启动研究[J].给水排水,2006,32(11):34-37.
[12]Chamchoi N,Nitisoravut S.Anammox enrichment from different conventional sludges[J].Chemosphere,2007,66(11):2225-2232.
[13]唐晓雪,彭永臻,徐竹兵,等.低基质浓度厌氧氨氧化颗粒污泥反应器的快速启动[J].中南大学学报(自然科学版),2014(12).
[14]彭绪亚,李治阳,王璐,等.UASB反应器培养厌氧氨氧化菌的试验研究[J].中国给水排水,2011,27(11):20-24
[15]黄晓丽,高大文,丛岩,等.利用EGSB反应器富集高纯度厌氧氨氧化菌[J].生物工程学报,2014,30(12):1845-1853.
[16]丁爽,郑平,唐崇俭,等.不同接种物启动Anammox-EGSB反应器的污泥性能[J].化工学报,2011,62(5):1395-1401.
[17]Trigo C,Campos J L,Garrido J M,et al.Start-up of the anammox process in a membrane bioreactor[J].Journal of Biotechnology,2006,126(4):475-487.
[18]路青,华兆哲,李秀芬,等.MBR中厌氧氨氧化运行特性及微生态结构[J].食品与生物技术学报,2010,29(4):581-588.
[19]朱清江,张大超,熊昌狮,等.厌氧氨氧化反应器的启动及其脱氮性能研究[J].工业水处理,2016,36(6):83-86.
[20]曾国驱,贾晓珊.制革废水的厌氧氨氧化ABR脱氮工艺研究[J].环境科学,2014,35(12):4618-4626.
[21]张海芹,王翻翻,李月寒,等.不同接种污泥ABR厌氧氨氧化的启动特征[J].环境科学,2015,36(6):2216-2221.
[22]陈宗妲,黄勇,李祥.p H对亚硝化、厌氧氨氧化反应及联合工艺氮素转化的影响[J].环境工程,2016,34(1):55-60.
[23]周同,于德爽,李津,等.温度对海洋厌氧氨氧化菌脱氮效能的影响[J].环境科学,2017,38(5):2044-2051.
[24]任玉辉,王科,李相昆,等.常温低基质下碱度和溶解氧对厌氧氨氧化的影响[J].环境科学,2014,35(11):4218-4223.
[25]Egli K,Fanger U,Alvarez P,et al.Enrichment and characterization of an anammox bacterium from a rotating biological contactor treating ammonium-rich leachate[J].Archives of Microbilogy,2001,175(3):198-207.
[26]朱莉,李祥,黄勇,等.铜离子对厌氧氨氧化脱氮效能的影响[J].环境工程学报,2013,7(11):4361-4366.
[27]张正哲.重金属离子对厌氧氨氧化颗粒污泥的影响及其修复策略研究[D].杭州:杭州师范大学,2016.
[2]郑平,胡宝兰,徐向阳.新型生物脱氮理论与技术[M].北京:科学出版社,2004.
[3]Li Z,Xu X,Shao B,et al.Anammox granules formation and performance in a submerged anaerobic membrane bioreactor[J].Chemical Engineering Journal,2014,254(7):9-16.
[4]Tsushima I,Ogasawara Y,Kindaichi T,et al.Development of high-rate anaerobic ammonium-oxidizing(anammox)biofilm reactors[J].Water Research,2007,41(8):1623.
[5]于德爽,赵丹,李津,等.接种不同污泥源条件下厌氧氨氧化菌的特性[J].环境工程学报,2013,7(11):4339-4345.
[6]路青,李秀芬,华兆哲,等.接种污泥源对厌氧氨氧化启动效能的影响[J].生态与农村环境学报,2009,25(4):60-65.
[7]李祥,黄勇,袁怡,等.不同泥源对厌氧氨氧化反应器启动的影响[J].环境工程学报,2012,6(7):2143-2148.
[8]宋振辉,胡筱敏,王宇佳.反应器类型及接种污泥对厌氧氨氧化工艺启动阶段的影响[J].环境工程,2017,35(5):58-63.
[9]徐相龙,刘国华,范强,等.SBR反应器厌氧氨氧化系统启动过程中细菌群落结构的变化[J].环境科学学报,2017,37(5):1695-1703.
[10]胡勇有,梁辉强,雒怀庆.厌氧序批式反应器培养厌氧氨氧化污泥[J].华南理工大学学报(自然科学版),2005,33(10):93-97.
[11]周凌,操家顺,蔡娟,等.低浓度氨氮条件下厌氧氨氧化反应器的启动研究[J].给水排水,2006,32(11):34-37.
[12]Chamchoi N,Nitisoravut S.Anammox enrichment from different conventional sludges[J].Chemosphere,2007,66(11):2225-2232.
[13]唐晓雪,彭永臻,徐竹兵,等.低基质浓度厌氧氨氧化颗粒污泥反应器的快速启动[J].中南大学学报(自然科学版),2014(12).
[14]彭绪亚,李治阳,王璐,等.UASB反应器培养厌氧氨氧化菌的试验研究[J].中国给水排水,2011,27(11):20-24
[15]黄晓丽,高大文,丛岩,等.利用EGSB反应器富集高纯度厌氧氨氧化菌[J].生物工程学报,2014,30(12):1845-1853.
[16]丁爽,郑平,唐崇俭,等.不同接种物启动Anammox-EGSB反应器的污泥性能[J].化工学报,2011,62(5):1395-1401.
[17]Trigo C,Campos J L,Garrido J M,et al.Start-up of the anammox process in a membrane bioreactor[J].Journal of Biotechnology,2006,126(4):475-487.
[18]路青,华兆哲,李秀芬,等.MBR中厌氧氨氧化运行特性及微生态结构[J].食品与生物技术学报,2010,29(4):581-588.
[19]朱清江,张大超,熊昌狮,等.厌氧氨氧化反应器的启动及其脱氮性能研究[J].工业水处理,2016,36(6):83-86.
[20]曾国驱,贾晓珊.制革废水的厌氧氨氧化ABR脱氮工艺研究[J].环境科学,2014,35(12):4618-4626.
[21]张海芹,王翻翻,李月寒,等.不同接种污泥ABR厌氧氨氧化的启动特征[J].环境科学,2015,36(6):2216-2221.
[22]陈宗妲,黄勇,李祥.p H对亚硝化、厌氧氨氧化反应及联合工艺氮素转化的影响[J].环境工程,2016,34(1):55-60.
[23]周同,于德爽,李津,等.温度对海洋厌氧氨氧化菌脱氮效能的影响[J].环境科学,2017,38(5):2044-2051.
[24]任玉辉,王科,李相昆,等.常温低基质下碱度和溶解氧对厌氧氨氧化的影响[J].环境科学,2014,35(11):4218-4223.
[25]Egli K,Fanger U,Alvarez P,et al.Enrichment and characterization of an anammox bacterium from a rotating biological contactor treating ammonium-rich leachate[J].Archives of Microbilogy,2001,175(3):198-207.
[26]朱莉,李祥,黄勇,等.铜离子对厌氧氨氧化脱氮效能的影响[J].环境工程学报,2013,7(11):4361-4366.
[27]张正哲.重金属离子对厌氧氨氧化颗粒污泥的影响及其修复策略研究[D].杭州:杭州师范大学,2016.