期刊文献+

厌氧水解酸化-好氧氧化A_1/A_2/O工艺剩余污泥减量影响因素 被引量:4

Factors Affecting Residual Sludge Reducing by Anaerobic Hydrolysisacidification and Aerobic Oxidation Process of A_1/A_2/O Bio-Treatment System
下载PDF
导出
摘要 厌氧水解酸化-好氧氧化工艺实现剩余污泥减量,不需要高温、高压、强氧化剂或强碱性等破坏微生物细胞结构的强化措施,可操作性和经济性良好.污泥减量系统的主要目的是实现对污染物的降解,系统污泥减量效果与系统的有机负荷、水力停留时间、温度等因素有关,并受这些因素影响.在碱减量印染废水A1/A2/O生物处理系统,把剩余污泥回流到A1段、利用水解酸化和好氧氧化工艺实现对剩余污泥减量的试验表明:A1段容积负荷(COD)在2.54kg·(m^3·d)^-3、水力停留时间为7.56h、温度在2512~4012,系统在长期运行可以实现对系统污泥的有效减量和对废水处理达标排放要求(GB8978—96一级标准).污泥回流到A,段进行减量,细胞中N、P的释放可以有效克服碱减量印染废水中N、P不足的缺点,大大降低向系统添加N、P营养物的费用. Hydrolysis-acidification and aerobic oxidation process could realize sludge reducing without those strengthening conditions such as high temperature, high pressure, strong oxidant or alkali which may destroy the cell structure of microorganisms, so it has good maneuverability and is economical. The purpose of sludge reducing system is mainly to degrade the pollutants in it ant its reducing effect is related to organic loading, HRT and temperature, etc. In the A1/A2/O bio-treatment system dealing with alkali minimization and dyeing-printing wastewater, residual sludge can be reduced effectively by recycling sludge to A1 segment. It proved that sludge could be reduced effectively and treated water could reach the grade I standard of GB8978-96 for long time operation of the system, when the volume loading of A1 (COD) was 2.54 kg· (m^3·d) - l, the HRT of A1 was 7.56h and the temperature of the system was 2512 -4012. The sludge reducing could be realized through recycling to A1 segment, and the N, P released from the broken bacteria cell could compensate the shortage of N and P of alkali minimization and dyeing-printing wastewater, and then the cost of adding the nutrition of N and P to the system could be reduced greatly.
出处 《环境科学》 EI CAS CSCD 北大核心 2006年第4期675-680,共6页 Environmental Science
基金 上海市科委基金项目(02DZ12096)
关键词 厌氧水解酸化 好氧氧化 污泥减量 A1/A2/O生物处理系统 碱减量 印染废水 anaerobic hydrolysis-acidification aerobic oxidation sludge reducing A1/A2/O bio-treatment system alkali minimization dyeing printing wastewater
  • 相关文献

参考文献12

  • 1Yasui H,Shibata M.An innovative approach to reduce excess sludge production in the activated sludge process[J].Wat.Sci.Tech.,1994,30(9):11~20.
  • 2Sakai Y,Fukase,Yasui H,et al.An activated sludge process without excess sludge production[J].Wat.Sci.Tech.,1997,36(11):163~ 170.
  • 3Ghyoot W,Verstraete W.Reduced sludge production in a twostage membrane-assisted bioreactor[J].Water Research,2000,34(1):205~215.
  • 4Rocher M,Roux G,Goma G,et al.Excess sludge reduction in activated sludge processes by integrating biomass alkaline heat treatment[J].Wat.Sci.Tech.,2001,44(2,3):437~444.
  • 5Djafer M,Luck F,Rose J,et al.Transforming sludge into a recyclable and valuable carbon source by wet air oxidation[J].Wat.Sci.Tech.,2002,41(8):77~83.
  • 6Shiota N,Akashi A,Hasegawa S.A strategy in wastewater treatment process for significant reduction of excess sludge production[J].Wat.Sci.Tech.,2002,45(12):127~134.
  • 7杨波,陈季华,奚旦立,沈佳璐.厌氧水解酸化-好氧氧化A_1/A_2/O工艺剩余污泥减量[J].环境科学,2006,27(3):478-482. 被引量:14
  • 8国家环保局.水和废水监测分析方法[M].(第四版).北京:中国环境科学出版社,2002 88~223.
  • 9佟宏,白毓谦.对苯二甲酸的微生物降解[J].环境科学学报,1990,10(4):464-470. 被引量:15
  • 10阮文权,邹华,陈坚.乙酸钠为碳源时进水COD和总磷对生物除磷的影响[J].环境科学,2002,23(3):49-52. 被引量:22

二级参考文献26

  • 1许晓路,申秀英.活性污泥生物除磷机制及其影响因素[J].农业环境与发展,1994,11(3):25-28. 被引量:4
  • 2姚毅.活性污泥的表面特性与其沉降脱水性能的关系[J].中国给水排水,1996,12(1):22-26. 被引量:34
  • 3王凯军.活性污泥膨胀机理与控制[M].北京:中国环境出版社,1993..
  • 4王凯军.厌氧(水解)处理低浓度污水[M].北京:中国环境出版社,1992..
  • 5国家环保局.水和废水监测分析方法,第三版[M].中国环境出入出版社,1989.234-246.
  • 6团体著者,伯杰氏细菌鉴定手册(第8版),1984年
  • 7邹惠仙,中国环境科学,1982年,5卷,29页
  • 8林万明,微生物学通报,1981年,8卷,5期,245页
  • 9团体著者,一般细菌常用鉴定方法,1978年
  • 10王宝贞.水污染控制工程[M].北京:高等教育出版社,1994.36-37.

共引文献115

同被引文献22

引证文献4

二级引证文献27

相关作者

内容加载中请稍等...

相关机构

内容加载中请稍等...

相关主题

内容加载中请稍等...

浏览历史

内容加载中请稍等...
;
使用帮助 返回顶部