高级搜索

新型立体浮床处理河道微污染源水的挂膜特性

,  ,  ,  ,  , 

downloadPDF

上一篇

下一篇

陈亚男, 郭宗楼, 郑水生, 汪开英, 武海涛, 刘露. 新型立体浮床处理河道微污染源水的挂膜特性[J]. 环境工程学报, 2013, 7(2): 477-482.
引用本文: 陈亚男, 郭宗楼, 郑水生, 汪开英, 武海涛, 刘露. 新型立体浮床处理河道微污染源水的挂膜特性[J]. 环境工程学报, 2013, 7(2): 477-482.
shu
Chen Yanan, Guo Zonglou, Zheng Shuisheng, Wang Kaiying, Wu Haitao, Liu Lu. Biofilm colonization characteristics of tridimensional floating bed in treating micro-polluted river source water[J]. Chinese Journal of Environmental Engineering, 2013, 7(2): 477-482.
Citation: Chen Yanan, Guo Zonglou, Zheng Shuisheng, Wang Kaiying, Wu Haitao, Liu Lu. Biofilm colonization characteristics of tridimensional floating bed in treating micro-polluted river source water[J]. Chinese Journal of Environmental Engineering, 2013, 7(2): 477-482.
shu

新型立体浮床处理河道微污染源水的挂膜特性

  • 1.

    浙江大学生物系统工程与食品学院,杭州 310029

  • 2.

    广东工业大学环境科学与工程学院,广州 510006

  • 基金项目:

    国家水体污染控制与治理科技重大专项课题(2008ZX07421-001)

    中央高校基本科研业务费专项资金

  • 中图分类号: X522

Biofilm colonization characteristics of tridimensional floating bed in treating micro-polluted river source water

  • 1.

    School of Biosystems Engineering and Food Science, Zhejiang University, Hangzhou 310029, China

  • 2.

    School of Environmental Science and Engineering, Guangdong University of Technology, Guangzhou 510006,China

  • Fund Project:

  • 摘要: 立体浮床是一种新型的生物预处理方法。采用了"曝气充氧+新型立体浮床"强化处理方法治理微污染河水,对立体浮床挂膜期间底部填料上的生物膜特性及微污染河水处理效果进行了实验研究。结果表明,在河道水温为15.2~23.6℃,pH在7.0~7.8,溶解氧浓度为4.0~5.9 mg/L时,经40 d左右时填料挂膜成熟。通过对水质和微生物指标分析,填料挂膜分为4阶段:物理吸附阶段—物理吸附-生物繁殖阶段—生物强化吸附降解阶段—挂膜成熟阶段。填料挂膜成熟后,污染物去除效果良好,浊度、COD和NH3-N的去除率分别达到了20.1%、17.5%和18.3%。
    Abstract: Tridimensional floating bed is an innovative type of biological pretreatment. This test used an enhanced treatment composed of aeration system and new tridimensional floating bed for micro-polluted river water purification. The biofilm characteristics on the packing and purification of the water during biofilm colonization were studied. The results showed that when temperature was 15.2~23.6℃,pH was 7.0~7.8, dissolved oxygen was 4.0~5.9 mg/L, it took approximately 40 days for the biofilm maturation. Based on the analysis of water quality and microbial indicator, the process of biofilm colonization could be divided into four stages including physical adsorption, physical adsorption with rapid proliferation of microbes, enhanced adsorption and degradation by microbes, as well as the biofilm maturation. After maturation of biofilm, the removal efficiency of turbidity, COD and NH3-N could reach 20.1%,17.5% and 18.3%, respectively, showing a high purification efficiency.
  • 加载中
  • [1] 李先宁,宋海亮,朱光灿,等.组合型浮床生态系统的构建及其改善湖泊水源地水质的效果.湖泊科学, 2007,19(4):367-372 Li X. N., Song H. L., Zhu G. C., et al. Effect of combined floating bed ecosystem on water quality improvement in lake water source area. Journal of Lake Sciences, 2007,19(4):367-372(in Chinese)
    [2] Stephen R., Carpenter, David L., et al. Biological control of entrophication in lakes. Environ. Sci. Technol.,1995,29(3):784-786
    [3] 李海英,冯慕华,李玲,等.微曝气生态浮床净化入湖河口污染河水原位模型实验.湖泊科学,2009,21(6):782-788 Li H. Y., Feng M. H., Li L., et al. In-situ model experiment on purification of polluted river water into lake based on micro-aerated ecological floating bed. Journal of Lake Sciences,2009,21(6):782-788(in Chinese)
    [4] Sun L., Liu Y., Jin H. Nitrogen removal from polluted river by enhanced floating bed grown canna. Ecological Engineering,2009,35(1):135-140
    [5] 周小平,王建国,薛利红,等.浮床植物系统对富营养化水体中氮、磷净化特征的初步研究.应用生态学报,2005,16(11):2199-2203 Zhou X. P., Wang J. G., Xue L. H., et al. N and P removal characters of eutrophic water body under planted float. Chinese Journal of Applied Ecology,2005,16(11):2199-2203(in Chinese)
    [6] 司友斌,包军杰,曹德菊,等.香根草对富营养化水体净化效果研究.应用生态学报,2003,14(2):277-279 Si Y. B., Bao J. J., Cao D. J., et al. Purification of eutrophicated water body by Vetiveria zizanioids. Chinese Journal of Applied Ecology, 2003,14(2):277-279(in Chinese)
    [7] Li W., Friendrich R. In situ removal of dissolved phosphorus in irrigation drainage water by planted floats:Preliminary results from growth chamber trial. Agric. Ecosyst. Environ.,2001,90(1):9-15
    [8] Aoi T., Hayashi T. Natrient removal by water lettuce (pistia stratiotes). Water Sci. Technol.,1996,34(7-8):407-412
    [9] 李英杰,年跃刚,胡社荣,等.生态浮床对河口水质的净化效果研究.中国给水排水, 2008,24(11):60-63,67 Li Y. J., Nian Y. G., Hu S. R., et al. Purification effect of ecological floating bed on water quality of an estuary. China Water & Wastewater, 2008,24(11):60-63,67(in Chinese)
    [10] 方云英,杨肖娥,常会庆,等.利用水生植物原位修复污染水体.应用生态学报, 2008,19(2):407-412 Fang Y. Y., Yang X. E., Chang H. Q., et al. In-situ remediation of polluted water body by planting hydrophytes. Chinese Journal of Applied Ecology, 2008,19(2):407-412(in Chinese)
    [11] 黎华寿,聂呈荣,方文杰,等.浮床栽培植物生长特性的研究.华南农业大学学报(自然科学版), 2003,24(2):12-15 Li H. S., Nie C. R., Fang W. J., et al. Studies on the growing characteristics of plants grown in floating soilless culture system.Journal of South China Agricultural University (Natural Science Edition), 2003,24(2):12-15(in Chinese)
    [12] Peterson S. B., Teal J. M. The role of plants in ecologically engineered wastewater treatment systems. Ecological Engineering, 1996,6(1-3):137-148
    [13] 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
    [14] 刘雨,赵庆良,郑兴灿.生物膜法污水处理技术.北京:中国建筑工业出版社, 2000
    [15] 范洁群,邹国燕,宋祥甫,等.浮床黑麦草对城市生活污水氮循环细菌繁衍和脱氮效果的影响.生态学报,2010,30(1):265-271 Fan J. Q., Zou G. Y., Song X. F., et al. Effect of ryegrass floating-bed on the nitrogen cycling bacteria and nitrogen removal in the synthetic municipal wastewater. Acta Ecologica Sinica, 2010,30(1):265-271(in Chinese)
    [16] 张东,徐建华.受污染原水的弹性填料生物接触氧化处理挂膜试验研究.重庆环境科学,2001,23(1):59-61,75 Zhang D., Xu J. H. Experimental research on biofilm culturing of elastic packing biological contact oxidation pond treating polluted water. Journal of Chongqing Eviromental Sicence, 2001,23(1):59-61,75(in Chinese)
    [17] 陈汉辉,孙国胜.东深源水生物预处理工程挂膜启动过程水质净化效果变化的分析.环境污染治理技术与设备,2002,3(2):59-61,90 Chen H H, Sun G S. Analysis on water quality purifying effect in biofilm formation and start process of Dongshen source water biological pretreatment project. Techniques and Equipment for Environmental Pollution Control, 2002,3(2):59-61,90(in Chinese)
    [18] 陈洪斌,梅翔,高廷耀,等.受污染源水生物预处理挂膜过程研究.水处理技术,2001,27(4):196-199 Chen Hongbin, Mei Xiang, Gao Tingyao, et al. Study on biofilm colonization of polluted raw water bio-pretreatment.Technology of Water Treatment, 2001,27(4):196-199(in Chinese)
    [19] 曹蓉,邢海,金文标.生物膜处理城市河道污染水体的挂膜试验研究.环境工程学报,2008,2(3):374-377 Cao R., Xing H., Jin W. B.Study on biofilm colonization in treatment of urban polluted river water.Chinese Journal of Environmental Engineering, 2008,2(3):374-377(in Chinese)
    [20] 吴春笃,张波,李海燕.生物接触氧化工艺用填料的生物膜特性.江苏大学学报(自然科学版),2008,29(1):74-77 Wu Chundu, Zhang Bo, Li Haiyan.Biofilm characteristics in biological contact oxidation packing. Journal of Jiangshu University(Natural Science Editon),2008,29(1):74-77(in Chinese)
  • 加载中
WeChat 点击查看大图
计量
  • 文章访问数:  2175
  • HTML全文浏览数:  1007
  • PDF下载数:  1128
  • 施引文献:  0
出版历程
  • 收稿日期:  2011-12-14
  • 刊出日期:  2013-02-02
陈亚男, 郭宗楼, 郑水生, 汪开英, 武海涛, 刘露. 新型立体浮床处理河道微污染源水的挂膜特性[J]. 环境工程学报, 2013, 7(2): 477-482.
引用本文: 陈亚男, 郭宗楼, 郑水生, 汪开英, 武海涛, 刘露. 新型立体浮床处理河道微污染源水的挂膜特性[J]. 环境工程学报, 2013, 7(2): 477-482.
shu
Chen Yanan, Guo Zonglou, Zheng Shuisheng, Wang Kaiying, Wu Haitao, Liu Lu. Biofilm colonization characteristics of tridimensional floating bed in treating micro-polluted river source water[J]. Chinese Journal of Environmental Engineering, 2013, 7(2): 477-482.
Citation: Chen Yanan, Guo Zonglou, Zheng Shuisheng, Wang Kaiying, Wu Haitao, Liu Lu. Biofilm colonization characteristics of tridimensional floating bed in treating micro-polluted river source water[J]. Chinese Journal of Environmental Engineering, 2013, 7(2): 477-482.
shu

新型立体浮床处理河道微污染源水的挂膜特性

  • 1. 浙江大学生物系统工程与食品学院,杭州 310029
  • 2. 广东工业大学环境科学与工程学院,广州 510006
  • 收稿日期:  2011-12-14
基金项目:

国家水体污染控制与治理科技重大专项课题(2008ZX07421-001)

中央高校基本科研业务费专项资金

摘要: 立体浮床是一种新型的生物预处理方法。采用了"曝气充氧+新型立体浮床"强化处理方法治理微污染河水,对立体浮床挂膜期间底部填料上的生物膜特性及微污染河水处理效果进行了实验研究。结果表明,在河道水温为15.2~23.6℃,pH在7.0~7.8,溶解氧浓度为4.0~5.9 mg/L时,经40 d左右时填料挂膜成熟。通过对水质和微生物指标分析,填料挂膜分为4阶段:物理吸附阶段—物理吸附-生物繁殖阶段—生物强化吸附降解阶段—挂膜成熟阶段。填料挂膜成熟后,污染物去除效果良好,浊度、COD和NH3-N的去除率分别达到了20.1%、17.5%和18.3%。

English Abstract

    全文HTML

参考文献 (20)

返回顶部

目录

/

返回文章
返回

Copyright © 2019 中国科学院生态环境研究中心