期刊文献+

1株2,4-D降解菌的gfp标记及其在废水生物处理系统中的检测方法 被引量:1

Study on gfp Labeling of a 2,4-D Degrading Strain and Its Detection in a Wastewater Biotreatment System
原文传递
导出
摘要 通过mini-Tn7转座子系统将绿色荧光蛋白基因(gfp)插入到2,4-二氯苯氧乙酸(2,4-dichlorophenoxyacetic acid,2,4-D)降解菌Achromobacter sp.的染色体上,考察了标记前后该菌株的生长、发光及降解污染物特性,并探讨了将其投加到不同废水生物处理系统(活性污泥和颗粒污泥系统)后的定量检测方法.结果表明,Achromobacter sp.标记前后生长和降解2,4-D特性基本不变,在103~112 h内可将初始浓度约为100 mg/L的2,4-D完全降解.标记后菌株在生长和降解2,4-D过程中都能够稳定表达绿色荧光,降解过程荧光强度/D600稳定在4 500左右.向活性污泥系统投加该标记菌,可通过直接测定混合液荧光强度对该标记菌进行定量检测,在标记菌质量分数为0~75%的范围内,绿色荧光蛋白的表达水平与该标记菌的质量分数线性相关(R2=0.995 2).向颗粒污泥系统投加该标记菌,需要对混合液破碎均质化处理后测定荧光强度,在标记菌质量分数为0~42%的范围内,绿色荧光蛋白的表达水平与该标记菌的质量分数线性相关(R2=0.980 1).基于Tn7插入gfp的标记方法可以用来跟踪检测生物处理系统中的特异微生物. A 2,4-dichlorophenoxyacetic acid(2,4-D) degrading special bacteria Achromobacter sp.was chromosomally labeled with a green fluorescent protein gene(gfp) using a mini-Tn7 transposon delivery system.The growth status,fluorescence expression and degradation ability of the strain before and after labeling were compared.Methods to quantify the strain in different biotreatment systems(activated sludge or granular sludge system) after inoculation were also investigated.Results showed that the labeled Achromobacter sp.and its control strain demonstrated a similar growth pattern and 2,4-D degradation ability: both of them could completely remove 2,4-D of about 100 mg/L within 103-112 h.The labeled strain could express fluorescence stably during the course of growth and degradation with fluorescence intensity/D600 stabilized at about 4 500.For an activated sludge system bioaugmented with this labeled strain,its abundance could determined through direct measuring fluorescence emitted by the sludge mixture,for it was linearly associated to the percentage of the strain in the range of 0-75%(R2 = 0.995 2).For a granular sludge system bioaugmented with this strain,fluorescence of the sludge mixture could be measured after homogenous pretreatment,and the percentage of the strain in the range of 0-42% was also linearly related to the fluorescence intensity emitted by the sludge mixture(R2 = 0.980 1).Overall,this gfp labeling method based on Tn7 delivery system can be used to monitor specific bacteria in a biotreatment system.
出处 《环境科学》 EI CAS CSCD 北大核心 2010年第8期1864-1870,共7页 Environmental Science
基金 国家自然科学基金项目(50878024,50508006)
关键词 绿色荧光蛋白 2 4-D 活性污泥 颗粒污泥 降解 green fluorescent protein(gfp) 2 4-dichlorophenoxyacetic acid(2 4-D) activated sludge granular sludge degradation
  • 相关文献

参考文献30

  • 1Jin Y O, Mattes T E. Adaptation of aerobic, ethene-assimilating Mycobacterium strains to vinyl chloride as a growth substrate[ J]. Environ Sci Technol, 2008, 42 (13 ) : 4784-4789.
  • 2Wang M, Yang G, Min H, et al. Bioaugmentation with the nicotine-degrading bacterium Pseudomonas sp. HF-1 in a sequencing batch reactor treating tobacco wastewater: Degradation study and analysis of its mechanisms[ J]. Water Res, 2009, 43 (17) : 4187-4196.
  • 3Nam I H, Hong H B, Kim Y M, et al. Biological removal of polychlorinated dibenzo-p-dioxins from incinerator fly ash by Sphingomonas wittichii RW1 [ J]. Water Res, 2005, 39 (19) : 4651-4660.
  • 4Kasai Y, Kodama Y, Takahata Y, et al. Degradative capacities and bioaugmentation potential of an anaerobic benzene-degrading bacterium strain DN11 [ J ]. Environ Sci Technol, 2007, 41 ( 17 ) : 6222-6227.
  • 5全向春,施汉昌,吕萍萍,王建龙,钱易.采用高效菌提高普通活性污泥系统抗2,4-DCP负荷冲击能力[J].环境科学,2004,25(4):59-64. 被引量:8
  • 6全向春,汤华,呼丽娟,王然,张宁.质粒pJP4水平转移介导生物膜系统强化降解2,4-D效应[J].环境科学,2009,30(9):2728-2734. 被引量:4
  • 7Amos B K, Suchomel E J, Pennell K D, et al. Microbial activity and distribution during enhanced contaminant dissolution from a NAPL source zone [ J ]. Water Res, 2008, 42 (12) : 2963-2974.
  • 8Maes A, Van Raemdonck H, Smith K, et al. Transport and activity of Desulfitobacterium dichloroeliminans strain DCA1 during bioaugmentation of 1,2-DCA-contaminated groundwater [ J ]. Environ Sci Technol, 2006, 40 ( 17 ) : 5544-5552.
  • 9Yang C, Zhao macromolecule autofluorescent 2008, 42(16) Q, Liu z, et al. Cell surface display of functional fusions on Escherichia coli for development of an whole-cell biocatalyst [ J]. Environ Sci Technol, : 6105-6110.
  • 10Li J, Mclellan S, Ogawa S. Accumulation and fate of green fluorescent labeled Escherichia coli in laboratory-scale drinking water biofilters[ J ]. Water Res, 2006, 40 (16) : 3023-3028.

二级参考文献83

共引文献34

同被引文献25

  • 1刘春,黄霞,王慧.绿色荧光蛋白标记阿特拉津降解基因工程菌的特性[J].环境科学,2006,27(7):1439-1443. 被引量:9
  • 2Zhao LJ, Guo JB, Yang JX, et al. Bioaugmentation as a tool toaccelerate the start - up of anoxic - oxic process in a full - scale municipal wastewater treatment plant at low temperature [ J]. International Journal of Environment and Pollution, 2009,37(2 -3) :205 -215.
  • 3Yu FB, Ali SW, Guan LB, et al. Bioaugmentation of a sequencing batch reactor with Pseudomonas putida ONBA - 17, and its impact on reactor bacterial communities [ J ]. Journal of Hazardous Materials,2010,176 ( 1 - 3 ) :20 - 26.
  • 4Cirja M, Hommes G, Ivashechkin P, et al. Impact of bio- augmentation with Sphingomonas sp. strain TFNP3 in membrane bioreactors degrading nonylphenol [ J ]. Applied Micro- biology and Biotechnology,2009,84( 1 ) : 183 - 189.
  • 5Ma F, Guo JB, Zhao LJ. Application of bioaugmenta- tion to improve the activated sludge system into the contact oxi- dation system treating petrochemical wastewater[ J ]. Bioresource technology,2009,100 (2) : 597 - 602.
  • 6Park D, Lee DS, Kim YM, et al. Bioaugmentation of cyanide - degrading microorganisms in a full - scale cokes wastewater treatment facility [ J ]. Bioresource Technology, 2008, 99 (6) :2092 - 2096.
  • 7Kubota K, Imachi H, Kawakami S, et al. Evaluation of enzymatic cell treatments for application of CARD - FISH to methanogens [ J ]. Journal of Microbiological Methods, 2008,72 (1) :54 -59.
  • 8Domde P, Kapley A, Purohit HJ. Impact of bioaug- mentation with a consortium of bacteria on the remediation of wastewater- containing hydrocarbons [ J]. Environmental Science and Pollution Research International,2007,14( 1 ) :7 -11.
  • 9Campelo AB, Rodriguez A, Martinez B. Use of Green fluorescent protein to monitor cell envelope stress in Lactococcus lactis [ J ]. Applied and Environmental Microbiology, 2010, 76 (3) :978 -981.
  • 10Morales BI, Gerin PA. Factors affecting the fate ofactive proteins introduced in wastewater sludges:investigation with green fluorescent protein [ J ]. Water Research, 2007,41 (8) :1723 - 1733.

引证文献1

二级引证文献2

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