新型活性污泥的培养及其处理高盐有机废水

谭淞文, 李维国, 公天齐, 刘伟, 杨慧茹, 徐爱琴, 刘君虎, 徐海滨. 新型活性污泥的培养及其处理高盐有机废水[J]. 环境工程学报, 2012, 6(11): 4059-4064.
引用本文: 谭淞文, 李维国, 公天齐, 刘伟, 杨慧茹, 徐爱琴, 刘君虎, 徐海滨. 新型活性污泥的培养及其处理高盐有机废水[J]. 环境工程学报, 2012, 6(11): 4059-4064.
Tan Songwen, Li Weiguo, Gong Tianqi, Liu Wei, Yang Huiru, Xu Aiqin, Liu Junhu, Xu Haibin. Cultivation of novel activated sludge and saline wastewater treatment[J]. Chinese Journal of Environmental Engineering, 2012, 6(11): 4059-4064.
Citation: Tan Songwen, Li Weiguo, Gong Tianqi, Liu Wei, Yang Huiru, Xu Aiqin, Liu Junhu, Xu Haibin. Cultivation of novel activated sludge and saline wastewater treatment[J]. Chinese Journal of Environmental Engineering, 2012, 6(11): 4059-4064.

新型活性污泥的培养及其处理高盐有机废水

  • 基金项目:

    城市水资源和环境国家重点实验室开放研究基金(QA201016)

  • 中图分类号: X703.1

Cultivation of novel activated sludge and saline wastewater treatment

  • Fund Project:
  • 摘要: 在好氧反应器中,将海泥通过海水和营养物质培养成新型的活性污泥,在处理含盐废水时有较好的活性和沉降性能,对这种新型的活性污泥我们称其为海洋活性污泥。通过10周的培养,海泥的污泥体积指数(SVI)从最初的19 mL/g升高到70 mL/g,对有机废水处理12 h后高锰酸盐指数(CODMn)降解率达到90%,氨氮降解率达到45%。在污泥培养时,营养物质投加频率为一日一次最有利于污泥的培养,又葡萄糖比淀粉更有利于污泥的培养。对于含盐有机废水的处理,海洋活性污泥也比传统活性污泥有优势,甚至对于含盐量6%的高盐有机废水,处理12 h后能达到CODMn降解率达为70%,氨氮降解率达到30%。当NaCl浓度高于6%,海洋活性污泥仍具有一定的活性,但仍能观察到明显的抑制作用。此外,海洋活性污泥具有比传统活性污泥更强的盐度变化抗性,甚至在低盐度下盐浓度变化时,海洋活性污泥的氨氮降解稳定性也优于传统活性污泥。
  • [1] 李维国,马放,苏俊峰,等. 一株中度嗜盐菌的分离鉴定及其强化高盐有机废水处理的研究. 湖南大学学报(自然科学版), 2008, 35(2): 84-88 Li Weiguo, Ma Fang, Su Junfeng, et al. Isolation and identification of a moderately halophilic bacterium and its bioaugmention in intensifying high-salty organic wastewater treatment. Journal of Hunan University (Natural Sciences), 2008, 35(2): 84-88(in Chinese)
    [2] 程宏伟,林里,刘德明. 香港应用海水冲厕工程综述. 福建建筑, 2010, (8): 1-3 Cheng Hongwei, Lin Li, Liu Deming. The use of sea water for toilet flushing in Hong Kong. Fujian Architecture & Construction, 2010, (8): 1-3 (in Chinese)
    [3] Wen C.G. Effect of salinity on removal confficient of receiving waters. Water Science and Technology, 1984, 16(1): 139-154
    [4] Belkin S., Brenner A., Abeliovich A. Biological treatment of a high salinity chemical industry wastewater. Water Science and Technology, 1993, 27(9): 61-72
    [5] Lefebvre O., Moletta R. Treatment of organic pollution in industrial saline wastewater (a literature review). Water Research, 2006, 40(20): 3671-3682
    [6] Keller J., Yuan Z., Blackall L.L. Integrating process engineering and microbiology tools to advance activated sludge wastewater treatment research and development. Reviews in Environmental Science and Biotechnology, 2002, 1(1): 83-97
    [7] An L., Gu G.W. Treatment of saline wastewater using a two-stage contact oxidation method. Water Science and Technology, 1993, 28(7): 31-37
    [8] Kargi F., Dincer A.R. Effect of salt concentration on biological treatment of saline wastewater by fed-batch operation. Enzyme and Microbial Technology, 1996, 19(7): 529-537
    [9] Panswad T., Chadarut A. Impact of high chloride wastewater on an anaerobic/anoxic/aerobic process with and without inoculation of chloride acclimated seeds. Water Research, 1999, 33(5): 1165-1172
    [10] Wagner M., Loy A., Nogueira R., et al. Microbial community composition and function in wastewater treatment plants. Antonie Van Leeuwenhoek, 2002, 81(1-4): 665-680
    [11] Lee T.H., Kurata S., Nakatsu C.H., et al. Molecular analysis of bacterial community based on 16S rDNA and functional genes in activated sludge enriched with 2,4-dichlorophenoxyacetic acid (2,4-D) under different cultural conditions. Microbial Ecology, 2005, 49(1): 151-62
    [12] Yoshie S., Makino H., Hirosawa H., et al. Molecular analysis of halophilic bacterial community for high-rate denitrification of saline industrial wastewater. Applied Microbiology and Biotechnology, 2006, 72(1): 182-189
    [13] 刘铁汉, 周培瑾. 嗜盐微生物. 微生物学通报, 1999, 26(3): 232 Liu Tiehan, Zhou Peijing. Halophilic microorganisms. Microbiology, 1999, 26(3): 232 (in Chinese)
    [14] Oren A. Halophilic Microorganisms and Their Environments. Dordrecht, Dutch: Kluwer Academic Publishers, 2002. 368-369
    [15] Diaz M.P., Boyd K.G., Grigon S.J., et al. Biodegradation of crude oil across a wide range of salinities by an extremely halotolerant bacterial consortium MPD-M, immobilized onto polypropylene fibers. Biotechnology & Bioengineering, 2002. 79(2):145-153
    [16] Margesin R., Schinner F. Potential of halotolerant and halophilic microorganisms for biotechnology. Extremophiles, 2001, 5(2): 73-83
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出版历程
  • 收稿日期:  2011-12-14
  • 刊出日期:  2012-11-09
谭淞文, 李维国, 公天齐, 刘伟, 杨慧茹, 徐爱琴, 刘君虎, 徐海滨. 新型活性污泥的培养及其处理高盐有机废水[J]. 环境工程学报, 2012, 6(11): 4059-4064.
引用本文: 谭淞文, 李维国, 公天齐, 刘伟, 杨慧茹, 徐爱琴, 刘君虎, 徐海滨. 新型活性污泥的培养及其处理高盐有机废水[J]. 环境工程学报, 2012, 6(11): 4059-4064.
Tan Songwen, Li Weiguo, Gong Tianqi, Liu Wei, Yang Huiru, Xu Aiqin, Liu Junhu, Xu Haibin. Cultivation of novel activated sludge and saline wastewater treatment[J]. Chinese Journal of Environmental Engineering, 2012, 6(11): 4059-4064.
Citation: Tan Songwen, Li Weiguo, Gong Tianqi, Liu Wei, Yang Huiru, Xu Aiqin, Liu Junhu, Xu Haibin. Cultivation of novel activated sludge and saline wastewater treatment[J]. Chinese Journal of Environmental Engineering, 2012, 6(11): 4059-4064.

新型活性污泥的培养及其处理高盐有机废水

  • 1. 哈尔滨工业大学(威海)海洋学院,威海 264209
  • 2. 中联重科环境产业分公司,长沙 410000
基金项目:

城市水资源和环境国家重点实验室开放研究基金(QA201016)

摘要: 在好氧反应器中,将海泥通过海水和营养物质培养成新型的活性污泥,在处理含盐废水时有较好的活性和沉降性能,对这种新型的活性污泥我们称其为海洋活性污泥。通过10周的培养,海泥的污泥体积指数(SVI)从最初的19 mL/g升高到70 mL/g,对有机废水处理12 h后高锰酸盐指数(CODMn)降解率达到90%,氨氮降解率达到45%。在污泥培养时,营养物质投加频率为一日一次最有利于污泥的培养,又葡萄糖比淀粉更有利于污泥的培养。对于含盐有机废水的处理,海洋活性污泥也比传统活性污泥有优势,甚至对于含盐量6%的高盐有机废水,处理12 h后能达到CODMn降解率达为70%,氨氮降解率达到30%。当NaCl浓度高于6%,海洋活性污泥仍具有一定的活性,但仍能观察到明显的抑制作用。此外,海洋活性污泥具有比传统活性污泥更强的盐度变化抗性,甚至在低盐度下盐浓度变化时,海洋活性污泥的氨氮降解稳定性也优于传统活性污泥。

English Abstract

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