九龙江河口红树林湿地石油降解菌群落结构研究
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摘要
在21世纪,环保工作者们对红树林湿地以及红树林中具有海洋污染生物修复功能的微生物资源的研究已经成为一个热点。本研究的目的是探索红树林区微生物在石油污染压力下的细菌数量、代谢活性以及群落结构的变化,并从中分离筛选石油降解菌。样品采集于中国福建省九龙江口红树林湿地的3个站位,以原油和柴油为选择压力富集驯化样品中的微生物。在富集驯化过程中,测定了可培养细菌的数量、微生物的代谢活性,并用PCR-DGGE的方法分析了驯化过程中细菌群落结构的变化。结果如下:
     1.经过富集驯化,从红树林沉积物中获得了大量的可培养细菌。非转接组在驯化过程的第一周到第五周,细菌的数量恒定,从第六周开始到第八周,所有实验组的细菌数量都呈缓慢的减少趋势。在转接组,15号站位可培养细菌数量最高,其次是14号站位,12号站,丰度最低的是海水的驯化样品。结果还显示,以柴油为富集压力下的样品中的平均细菌数高于原油样品,此外,所有站位样品以2216E作为富集培养基得到的细菌数均高于经R_2A培养的。
     2.测定了不同站位以及富集富集驯化的微生物的电子传递系统的活性(ETSA)。在非转接组中,ETSA值从第一周到第五周基本不变,第六周到第八周开始下降。在转接组中的结果表明,15号站位的样品表现有最高的活性,其次是海水富集物),14号站位和12号站位。另外,以柴油为富集压力下的样品的ETSA平均值高于原油的。同时发现所有站位的样品在以2216E作为富集培养基得到的ETSA平均值高于R_2A。
     3.利用PCR-DGGE方法分析了研究了红树林沉积物在原油和柴油污染压力下微生物群落结构的变化。DGGE的条带表明,第一周到第八周,细菌的群落结构没有明显的变化。并且,对获得的8条优势条带进行了测序,结果表明它们的分别属于Vibrio natriegens,Vibronaceae bacterium,Vibrio campbellii,Uncultured marine bactyerium,Vibrioparahaemolyticus,Pseudomonas sp,Vibrio sp和Vibrio alginolyticus。
     4.从原油和柴油富集培养基中分离得到了11株菌,16S rDNA文库分析表明,绝大多数分离到得细菌其序列相对应的细菌为此前已确定的潜在的多环芳烃(PAHs)降解菌,在Gene bank比对结果表明这11株菌分别归属于Pseudomonas sp.,Flexibacteraceaebacterium,Rhodobacteraceae bacterium,Marinobacter sp.,Alteromonas sp.,MarineCFB-group bacterium,Marinobacter aquaeolei,Thalassospira sp.,Alteromonas sp.,Muricauda sp.,and Uncultured4lteromonas.其中2株的相似性低于97%,可能是潜在的新种、属。
Research about mangrove areas as well as their microbial resources for the bioremediation of oil pollution in marine environment has become a hot spot in the twenty-first century by environmentalists.This study was set out to determine the ability of oil-degrading bacteria in mangrove ecosystem to utilize diesel oil and crude oil as a carbon source in an in-situ condition in both non-transfer and transfer enrichment samples and determine their community structure.Sediment samples were collected from three stations in Fugong mangrove swamp of the Jiulong River Estuary,Fujian,China and the microorganism were enriched in MSM supplemented with crude oil and diesel oil.The metabolic activities of microorganism were analyzed and the changes in microbial community structure were evaluated using PCR- DGGE analysis of amplified 16S rDNA gene fragment during batch culture enrichment.The results obtained are as follows:
     1.The mangrove sediments harbored abundant cultivatable bacteria.In the non-transfer sample,there was a constant bacteria number between the first 1st to the 5th week of enrichment and the number start declining in the 6~(th) to the 8~(th) weeks of enrichment in all the stations with little variation.In the transfer sample there was a decrease in the cultivatable bacteria number from the first week of enrichment in all the stations.
     2.The Electron Transport System Activity(ETSA) of sediment samples and enrichment cultures were tested in both non-transfer and the transfer enrichment sample.In the non-transfer sample.there was a constant ETSA number between the first 1-5 weeks as shown by their OD value and the number started to decline in the 6~(th) to the 8~(th) weeks of enrichment in all the stations.In the transfer sample,the result showed a decrease in the ETSA value and station 15 exhibited high activity rate followed by the sea water enrichment,station 14 and the least was recorded at station 12.
     3.The DGGE profile demonstrated that there was no remarkably shift in bacteria community from first subculture to the eighth subculture.DGGE bands were successfully sequenced and eight dominant species were identified.They were closely related to Vibrio natriegens,Vibronaceae bacterium,Vibrio campbellii, Uncultured marine bactyerium,Vibrio parahaemolyticus,Pseudomonas sp., Vibrio sp.and Vibrio alginolyticus respectively.
     4.Eleven strains were isolated from the cultivatable culture dependent bacteria from both the crude oil and diesel oil enrichment culture and 16S rDNA library analysis showed that the vast majority of the corresponding sequences of cultured bacteria are microorganisms that have been previously identified as potential polycyclic aromatic hydrocarbons(PAHs) degraders,Furthermore, when the corresponding sequences were compared with the GeneBank database revealed the following populations of bacteria capable of utilizing petroleum product as a carbon source as follows;Pseudomonas sp.,Flexibacteraceae bacterium,Rhodobacteraceae bacterium,Marinobacter sp.,Alteromonas sp., Marine CFB-group bacterium,Marinobacter aquaeolei,Thalassospira sp., Alteromonas sp.,Muricauda sp.,and Uncultured Alteromonas sp.respectively.
引文
1.Maciel-Souza,M.D.,et al.,Chemical and microbiological characterization of mangrove sediments after a large oil-spill in Guanabara Bay,RJ,Brazil.Brazilian Journal of Microbiology,2006.37(3):p.262-266.
    2.Day,R.H.,et al.,Effects of the Exxon Valdez oil spill on habitat use by birds in Prince William Sound,Alaska.Ecological Applications,1997.7(2):p.593-613.
    3.Speight,J.G.,Petroleum asphaltenes-Part 2-The effect of asphaltenes and resin constituents on recovery and refining processes.Oil & Gas Science and Technology-Revue De L Institut Francais Du Petrole,2004.59(5):p.479-488.
    4.Nam,J.J.,A.J.Sweetman,and K.C.Jones,Polynuclear aromatic hydrocarbons(PAHs)in global background soils.Journal of Environmental Monitoring,2009.11(1):p.45-48.
    5.Rogers,K.M.and M.M.Savard,Detection of petroleum contamination in river sediments from Quebec City region using GC-IRMS.Organic Geochemistry,1999.30(12):p.1559-1569.
    6.Barakat,A.O.,et al.,Application of a multimolecular marker approach to fingerprint petroleum pollution in the marine environment.Marine Pollution Bulletin,1999.38(7):p.535-544.
    7.Fingas,M.and B.Fieldhouse,Studies on crude oil and petroleum product emulsions:Water resolution and theology.Colloids and Surfaces a-Physicochemical and Engineering Aspects,2009.333(1-3):p.67-81.
    8.Aldrett,S.,et al.,Microbial degradation of crude oil in marine environments tested in a flask experiment.Water Research,1997.31(11):p.2840-2848.
    9.Boehm,P.D.and D.S.Page,Exposure elements in oil spill risk and natural resource damage assessments:A review.Human and Ecological Risk Assessment,2007.13(2):p.418-448.
    10.Boniewicz-Szmyt,K.and S.J.Pogorzelski,Crude oil derivatives on sea water:Signatures of spreading dynamics.Journal of Marine Systems,2008.74:p.S41-S51.
    11.DeMello,J.A.,et al.,Biodegradation and environmental behavior of biodiesel mixtures in the sea:An initial study.Marine Pollution Bulletin,2007.54(7):p.894-904.
    12.Vinson,M.R.,et al.,Effects of oil pollution on aquatic macroinvertebrate assemblages in Gabon wetlands.African Journal of Aquatic Science,2008.33(3):p.261-268.
    13.Topouzelis,K.N.,Oil Spill Detection by SAR Images:Dark Formation Detection,Feature Extraction and Classification Algorithms.Sensors,2008.8(10):p.6642-6659.
    14.Zytner,R.G.,A.C.Salb,and W.H.Stiver,Bioremediation of diesel fuel contaminated soil:Comparison of individual compounds to complex mixtures.Soil & Sediment Contamination,2006.15(3):p.277-297.
    15.Ramachandran,S.D.,et al.,Oil dispersant increases PAH uptake by fish exposed to crude oil.Ecotoxicology and Environmental Safety,2004.59(3):p.300-308.
    16.Diez,S.,et al.,The Prestige oil spill.I.Biodegradation of a heavy fuel oil under simulated conditions.Environmental Toxicology and Chemistry,2005.24(9):p.2203-2217.
    17.Siddiqi,H.A.,F.A.Ansari,and A.B.Munshi,Assessment of hydrocarbons concentration in marine fauna due to Tasman Spirit oil spill along the Clifton beach at Karachi coast.Environmental Monitoring and Assessment,2009.148(1-4):p.139-148.
    18.Wang,Z.Y.,et al.,Petroleum Hydrocarbon Degradation Potential of Soil Bacteria Native to the Yellow River Delta.Pedosphere,2008.18(6):p.707-716.
    19.Peterson,C.H.,The “Exxon Valdez” oil spill in Alaska:Acute,indirect and chronic effects on the ecosystem.Advances in Marine Biology,Vol 39,2001.39:p.1-103.
    20.Anisuddin,S.,N.Al Hashar,and S.Tahseen,Prevention of oil spill pollution in seawater using locally available materials.Arabian Journal for Science and Engineering,2005.30(2B):p.143-152.
    21.Roling,W.F.M.,et al.,Bacterial community dynamics and hydrocarbon degradation during a field-scale evaluation of bioremediation on a mudflat beach contaminated with buried oil.Applied and Environmental Microbiology,2004.70(5):p.2603-2613.
    22.Dorigo,U.,L.Volatier,and J.F.Humbert,Molecular approaches to the assessment of biodiversity in aquatic microbial communities.Water Research,2005.39(11):p.2207-2218.
    23.Chilingar,G.V.,et al.,Electrobioremediation of soils contaminated with hydrocarbons and metals:Progress report.Energy Sources,1997.19(2):p.129-146.
    24.Sarkar,D.,et al.,Bioremediation of petroleum hydrocarbons in contaminated soils:Comparison of biosolids addition,carbon supplementation,and monitored natural attenuation.Environmental Pollution,2005.136(1):p.187-195.
    25.Wiens,J.A.,et al.,Changing habitat and habitat use by birds after the Exxon Valdez oil spill,1989-2001.Ecological Applications,2004.14(6):p.1806-1825.
    26.Bowyer,R.T.,et al.,Effects of the Exxon Valdez oil spill on river otters:Injury and recovery of a sentinel species.Wildlife Monographs,2003(153):p.1-53.
    27.Kuyukina,M.S.,et al.,Bioremediation of crude oil-contaminated soil using slurry-phase biological treatment and land farming techniques.Soil & Sediment Contamination,2003.12(1):p.85-99.
    28.Rike,A.G,et al.,In situ biodegradation of petroleum hydrocarbons in frozen arctic soils.Cold Regions Science and Technology,2003.37(2):p.97-120.
    29.Janikowski,T.B.,et al.,Use of a two-phase partitioning bioreactor for degrading polycyclic aromatic hydrocarbons by a Sphingomonas sp.Applied Microbiology and Biotechnology,2002.59(2-3):p.368-376.
    30.Medina,L.C.,et al.,Nitrogen release patterns of a mixed control led-release fertilizer and its components.Horttechnology,2008.18(3):p.475-480.
    31.Richnow,H.H.,et al.,Microbial in situ degradation of aromatic hydrocarbons in a contaminated aquifer monitored by carbon isotope fractionation.Journal of Contaminant Hydrology,2003.65(1-2):p.101-120.
    32.Margesin,R.and F.Schinner,Bioremediation of diesel-oil-contaminated alpine soils at low temperatures.Applied Microbiology and Biotechnology,1997.47(4):p.462-468.
    33.Perianez,R.,Chemical and oil spill rapid response modelling in the Strait of Gibraltar-Alboran Sea.Ecological Modelling,2007.207(2-4):p.210-222.
    34.Singh,C.and J.Lin,Isolation and characterization of diesel oil degrading indigenous microrganisms in Kwazulu-Natal,South Africa.African Journal of Biotechnology,2008.7(12):p.1927-1932.
    35.Mandri,T.and J.Lin,Isolation and characterization of engine oil degrading indigenous microrganisms in Kwazulu-Natal,South Africa.African Journal of Biotechnology,2007.6(1):p.23-27.
    36.Lee,K.and S.de Mora,In situ bioremediation strategies for oiled shoreline environments.Environmental Technology,1999.20(8):p.783-794.
    37.Onwurah,I.N.and C.Nwuke,Enhanced bioremediation of crude oil-contaminated soil by a Pseudomonas species and mutually associated adapted Azotobacter vinelandii.Journal of Chemical Technology and Biotechnology,2004.79(5):p.491-498.
    38.Maciel-Souzal,M.d.C.,et al.,CHEMICAL AND MICROBIOLOGICAL CHARACTERIZATION OF MANGROVE SEDIMENTS AFTER A LARGE OIL-SPILL IN GUANABARA BAY Brazilian Journal of Microbiology,2006.37:p.262-266.
    39.Tian,Y.,et al.,PAHs contamination and bacterial communities in mangrove surface sediments of the Jiulong River Estuary,China.Marine Pollution Bulletin,2008.57(6-12):p.707-715.
    40.Grundmann,G.L.,Spatial scales of soil bacterial diversity-the size of a clone.Fems Microbiology Ecology,2004.48(2):p.119-127.
    41.Andreoni,V.,et al.,Detection of genes for alkane and naphthalene catabolism in Rhodococcus sp strain 1BN.Environmental Microbiology,2000.2(5):p.572-577.
    42.van Beilen,J.B.,et al.,Rubredoxins involved in alkane oxidation.Journal of Bacteriology,2002.184(6):p.1722-1732.
    43.Guo,C.L.,et al.,Isolation of PAH-degrading bacteria from mangrove sediments and their biodegradation potential.Marine Pollution Bulletin,2005.51(8-12):p.1054-1061.
    44.Neumann,B.,A.Pospiech,and H.U.Schairer,Rapid isolation of genomic DNA from gram-negative bacteria.Trends Genet,1992.8(10):p.332-3.
    45.Ikenaga,M.,et al.,Community structure of the microbiota associated with nodal roots of rice plants along with the growth stages:estimation by PCR-RFLP analysis.Biology and Fertility of Soils,2002.36(6):p.397-404.
    46.Muyzer,G.,E.C.de Waal,and A.G.Uitterlinden,Profiling of complex microbial populations by denaturing gradient gel electrophoresis analysis of polymerase chain reaction-amplified genes coding for 16S rRNA.Appl Environ Microbiol,1993.59(3):p.695-700.
    47.Jay,D.A.,et al.,A review of recent developments in estuarine scalar flux estimation.Estuaries,1997.20(2):p.262-280.
    48.Sergy,G.A.,et al.,In-situ treatment of oiled sediment shorelines.Spill Science & Technology Bulletin,2003.8(3):p.237-244.
    49.Barathi,S.and N.Vasudevan,Bioremediation of crude oil contaminated soil by bioaugmentation of Pseudomonas fluorescens NSI.Journal of Environmental Science and Health Part a-Toxic/Hazardous Substances & Environmental Engineering,2003.38(9):p.1857-1866.
    50.Leahy,J.G.,et al.,The concentrations of hexadecane and inorganic nutrients modulate the production of extracelhdar membrane-bound vesicles,soluble protein,and bioemulsifier by Acinetobacter venetianus RAG-1 and Acinetobacter sp strain HO1-N.Canadian Journal of Microbiology,2003.49(9):p.569-575.
    51.Breedveld,G.D.and M.Sparrevik,Nutrient-limited biodegradation of PAH in various soil strata at a creosote contaminated site.Biodegradation,2000.11(6):p.391-399.
    52.Mueller,S.A.,et al.,Comparison of Plate Counts,Petrifilm,Dipslides,and Adenosine Triphosphate Bioluminescence for Monitoring Bacteria in Cooling-Tower Waters.Water Environment Research,2009.81(4):p.401-406.
    53.Luan,T.G.,et al.,Study of metabolites from the degradation of polycyclic aromatic hydrocarbons(PAHs)by bacterial consortium enriched from mangrove sediments.Chemosphere,2006.65(11):p.2289-2296.
    54.Krivobok,S.,et al.,Identification of pyrene-induced proteins in Mycobacterium sp strain 6PY1:Evidence for two ring-hydroxylating dioxygenases.Journal of Bacteriology,2003.185(13):p.3828-3841.
    55.Pagnout,C.,et al.,Isolation and characterization of a gene cluster involved in PAH degradation in Mycobacterium sp strain SNP11:Expression in Mycobacterium smegmatis mc(2)155.Research in Microbiology,2007.158(2):p.175-186.