微囊藻毒素对典型微生物生长及生理生化特性的影响

杨翠云, 李敦海, 刘永定

杨翠云, 李敦海, 刘永定. 微囊藻毒素对典型微生物生长及生理生化特性的影响[J]. 水生生物学报, 2008, 32(6): 818-823.
引用本文: 杨翠云, 李敦海, 刘永定. 微囊藻毒素对典型微生物生长及生理生化特性的影响[J]. 水生生物学报, 2008, 32(6): 818-823.
YANG Cui-Yun, LI Dun-Hai, LIU Yong-Ding. THE EFFECT OFMICROCYSTIN ON THE GROWTH AND SOME PHYSIO-BIOCHEMICAL CHARACTERISTICS OF REPRESENTATIVEM ICROBIAL SPECIES[J]. ACTA HYDROBIOLOGICA SINICA, 2008, 32(6): 818-823.
Citation: YANG Cui-Yun, LI Dun-Hai, LIU Yong-Ding. THE EFFECT OFMICROCYSTIN ON THE GROWTH AND SOME PHYSIO-BIOCHEMICAL CHARACTERISTICS OF REPRESENTATIVEM ICROBIAL SPECIES[J]. ACTA HYDROBIOLOGICA SINICA, 2008, 32(6): 818-823.

微囊藻毒素对典型微生物生长及生理生化特性的影响

基金项目: 

国家重点基础研究发展规划项目(2003CB716801)

863项目(2005AA601010)资助

THE EFFECT OFMICROCYSTIN ON THE GROWTH AND SOME PHYSIO-BIOCHEMICAL CHARACTERISTICS OF REPRESENTATIVEM ICROBIAL SPECIES

  • 摘要: 研究了不同浓度微囊藻毒素对典型微生物大肠杆菌和枯草芽孢杆菌生长及生理生化特性的影响。微囊藻毒素对大肠杆菌和枯草芽孢杆菌的生长和细胞活性具有一定的剂量效应,较高浓度微囊藻毒素对其生长和活性有短时间的抑制作用,随着处理时间的延长,细胞的生长和活性逐渐恢复。细胞内可溶性糖和可溶性蛋白的含量,处理组和对照组相比均有先上升后下降的趋势。结果表明,微囊藻毒素的处理对大肠杆菌和枯草芽孢杆菌具有一定的胁迫作用,细胞通过调节细胞内可溶性蛋白和可溶性糖的含量来抵抗外界胁迫,但随着处理时间的延长,细菌逐渐适应了这种胁迫,恢复正常的生长。
    Abstract: Blooms of cyanobacteria have occurred in many regions all over the world and produced a number of toxins,including dermatotoxins,neurotoxins and hepatotoxins.Among hepatotoxins,microcystins are the most widespread and found to have more than 75 kinds of structural analogues.The toxic effects of microcystins on animals have been carried out widely.Microcystins could result in the death of invertebrate,fish,birds and other wild and domestic animals.Moreover,the bioaccumulation of microcystins by aquatic organisms including fish,shellfish and zooplankton determines the risk of health problems among animals and people that eat food contaminated by cyanotoxins.It was reported that mcirocystins could inhibit the growth and induce the antioxidant system reaction of plant.However,few studies have been tried to elucidate the possible effect of microcystins on microbes,which are equally important in aquatic ecosystem.Escherichia coli(E.coli) and Bacillus subtilis(B.subtilis) are procaryotic microorganisms and often used to be representative of Gram-negative and Gram-positive bacteria respectively.Moreover,Microcystin-LR,RR and YR are the most common isomers of microcystin.We investigated the effects of microcystin-RR(MC-RR) on the growth and some physio-biochemical characteristics of representative microbial species E.coli and B.subtilis.The results in the present study showed that the growth of E.coli and B.subtilis were significantly prolonged when exposed to microcystin-RR of 10mg/L compared with that of the control group.But the OD600 only showed a slight decrease when E.coli and B.subtilis exposed to microcystin-RR of 5mg/L or below for 1h.The OD600 of the high concentration(10mg/L) toxin-treated group was lower than that of the control group during the experiment.Since toxin-treated E.coli and B.subtilis cells had to consume a lot of endogenous compounds to conjugate or transform this xenobiotic,the growth and reproduction of E.coli and B.subtilis were unavoidable to be prolonged.But the dose of microcystin-RR did not have a lethal effect.E.coli and B.subtilis only showed growth inhibition at the initial growth phase when cells were treated with microcystin-RR.Indeed,the normal rate of growth was gradually re-established and the growth curves of the toxin-treated and untreated bacteria became parallel.The cell viability of E.coli and B.subtilis were also inhibited for a short period compared with that of the control group,which was similar to the growth of bacteria.The contents of protein and soluble sugar in cells increased compared with that of the control group at the beginning of MC-RR exposure,and then gradually decreased.The results showed the stress of MC-RR on E.coli and B.subtlis.The change of protein and soluble sugar made cells suit for the stress of MC-RR gradually.
  • [1]

    Hallegreff GM1A review of harmful algal bloom and their appar2ent global increase [J]1Phycologia, 1993, 2: 79-84

    [2]

    Svrcek C, Smith D W1Cyanobacteria toxins and the current stateof knowledge on water treatment op tions: a review [J]. Envi2ron1Eng1Sci1, 2004, 3: 155-185

    [3]

    Lankoff A, CarmichaelW W, Grasman K A, et al1The up take ki2netics and immunotoxic effects of microcystin2LR in human andchicken peripheral blood lymphocytes in vitro [J] 1Toxicology,2004, 204: 23-40

    [4]

    Zhang J Y, Zhang H J, Chen Y X1Sensitive apop tosis induced bymicrocystins in the crucian carp (Carassius auratus) lymphocytesin vitro [J]1Toxicology in V itro, 2006, 20: 560-566

    [5]

    Li X Y,Liu Y D, Song L R, et al1Responses of antioxidant sys2tems in the hepatocytes of common carp (Cyprinus carpio L1) tothe toxicity of microcystin2LR [J] 1Acta Hydrobiologica S inica,2003, 5: 472-475 [李效宇,刘永定,宋立荣,等. 鲤肝细胞抗氧化系统对微囊藻毒素毒性的反应. 水生生物学报, 2003, 5:472-475]

    [6]

    Hu Z Q, Liu Y D1The effect of microcystin on some physio2bio2chemical characteristic of synechococcus elongates [J] 1ActaHydrobiologica S inica, 2004, 2: 155-158 [胡智泉,刘永定. 微囊藻毒素对细长聚球藻生长及生理生化特性的影响. 水生生物学报, 2004, 2: 155-158]

    [7]

    Pflugmacher S1Promotion of oxidative stress in the aquatic macro2phyte Ceratophyllum dem ersum during biotransformation of the cy2anobacterial toxin microcystin2LR [J]1Aquatic Toxicology, 2004,70: 169-178

    [8]

    Yin L Y, Huang J Q, HuangW M, et al1Responses of antioxidantsystem in Arabidop sis thaliana suspension cells to the toxicity ofmicrocystin2RR [J]1Toxicon, 2005, 46: 859-864

    [9]

    Foxall T L, Sasner J J1Effects of a hepatic toxin from the cyano2phyteMicrocystis aeruginosa1 In: CarmichaelW W ( Eds1), Thewater environment1Algal Toxins and Health [M]1New York: Ple2num Press11998

    [10]

    Valdor R,AboalM1Effects of living cyanobacteria, cyanobacterialextracts and pure microcystins on growth and ultrastructure ofmi2croalgae and bacteria [J]1Toxicon, 2007, 49: 769-779

    [11]

    Dixon R A, Al2NazawiM, Alderson G1Permeabilising effects ofsub2inhibitory concentrations ofmicrocystin on the growth of Esch2erichia coli [J]1FEMS M icrobiol Lett1, 2004, 230: 167-170

    [12]

    Harada K I, SuzukiM, Dahlem A M, et al1 Imp roved method forpurification of toxic pep tides p roduced by cyanobacteria [J]. Tox2icon, 1988, 26: 433-439

    [13]

    Velapzquez E, Ruiz2Albusac JM,Bla′zquez E1Glucagon2like pep2tide22 stimulates the p roliferation of cultured rat astrocytes [J].European Journal of B iochem istry, 2003, 270: 3001-3009

    [14]

    Li H S, Sun Q, Zhao S J, et al1The physiological and biochemicalexperiments p rincip le and technology of p lant [M] 1Beijing:Higher Education Press11999 [李合生,孙群,赵世杰,等. 植物生理生化实验原理和技术. 北京:高教出版社. 1999]

    [15]

    Singh D P, TyagiM B, KumarA, et al1Antialgal activity of a hepatox2in2producing cyanobacterium, Microcystis aeruginosa [J]. WorldJournal ofM icrobiology and B iotechnology, 2001, 17: 15-22

    [16]

    Duan X J,Min H1Physiological toxicology of Cd2 + to rep resenta2tive microbial species in submerged paddy soil [J]1Ecology andEnvironm ent, 2005, 14 (6) : 865-869 [段学军,闵航. 镉对稻田土壤典型微生物种的胁迫生理毒性. 生态环境, 2005, 14 (6) :865-869]

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出版历程
  • 收稿日期:  2006-12-05
  • 修回日期:  2007-10-11
  • 发布日期:  2008-11-24

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