低温下活性污泥膨胀的微生物群落结构研究端正花1

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37320163ENVIRONMENTALSCIENCEVol.37No.3Mar.20161231232311.3003842.3000513.300051.SVI1~412..SaprospiraceaeFlavobacterium..X172X171.5A0250-3301201603-1070-05DOI10.13227/j.hjkx.2016.03.0362015-09-082015-10-2051103161981~E-mailduanzhenghua@mail.nankai.edu.cnChangesofMicrobialCommunityStructureinActivatedSludgeBulkingatLowTemperatureDUANZheng-hua1PANLiu-ming23CHENXiao-ou1WANGXiu-duo23ZHAOLe-jun23TIANLe-qi11.SchoolofEnvironmentalScienceandSafetyEngineeringTianjinUniversityofTechnologyTianjin300384China2.TianjinMunicipalEngineeringDesignandResearchInstituteTianjin300051China3.TianjinEnterpriseKeyLaboratoryofInfrastructureDurabilityTianjin300051ChinaAbstractThemechanismofactivatedsludgebulkinginZhengzhouwastewatertreatmentplantwasstudiedbymeasurementofwaterqualityparametersandhigh-throughputsequencingtechnology.ThechangeofSVIvaluewassignificantlynegativelycorrelatedwiththeseasonaltemperaturevariationandsludgebulkingwaseasytooccurduringDecembertothenextAprilbutthewaterqualitywasnotaffected.Theresultverifiedbyhigh-throughputsequencingtechnologyanalysisshowedthatthemicrobialcommunitystructureofbulkingsludgewassignificantlydifferentfromthatofthenon-bulkingone.ThedominantfilamentousbacteriainthebulkingsludgeinthisplantwereSaprospiraceaeandFlavobacterium.Thereforetheactivatedsludgebulkinginthiswastewatertreatmentplantwascausedbythepropagationoffilamentousbacteriaatlowtemperature.Keywordslowtemperatureactivatedsludgebulkinghigh-throughputsequencingmicrobialcommunitystructurefilamentousbacteria、.60%1~34~6.50%795%89.10~12.、1314...2014.11.1A2/O30m3·d-11.30.BOD520mg·L-1COD80mg·L-1.14dBOD50.08kg·kg·d-13.80g·L-10.97kg·kg-112℃.3.COD.A2/O.-20℃.1.2OMEGADNAE.Z.N.A.TMSoilDNAKitOMEGAD5625-01USADNA.DNA.DNA50μLTEbuffer-20℃.1CODFig.1CODchangesofeffluentandinfluent30μLDNA16SrDNAV4Roche454GSFLXsequencer.silva119aligned16S/18SSSUOTU.mothurhttp//.mothur.org/chao1ACEShannon.22.12.1.1COD2014112COD1COD339mg·L-1.22.40mg·L-150mg·L-1COD90%.1~414~20℃COD90%COD..158~20℃SUFRSUFRCOD86%.16310.40~17.10℃A/OCOD82.10%.17.2.1.2SVI20142SVI.1SVI1502502250.34.512SVI100.81、2、3、4、12.1819.Knoop2012℃..2.22.2.161、2、3、1701372SVIFig.2ChangeofSVIvaluethroughouttheyear4、81268194、53100、61602、68481、3353265724.400~500bp.rarefactioncurve.PC-ORDPCA.38.3PCAFig.3Principlecomponentanalysis438...2.2.297%OTU4Fig.4Wholesamplesimilarityanalysisoperationaltaxonomicunits.30.5.81、2、3、4、12..Proteobacteria1、2、3、4、81250.18%、43.77%、43.24%、43.58%、36.15%44.39%.Bacteroidetes815.66%.Chloroflexi.Actinobacteria270135Fig.5Relativeabundancesofdifferentphyla1%88.50%.、、.SVI.2.2.3OTU.68.Saprospiraceae1、2、3、4、1250%825%SVIFlavobacteriales.SaprospiraceaeFlavobacteriales.AnaerolineaeCandidatusMicrothrix21228.2324...、2526..6Fig.6Relativeabundancesoffilamentousbacteria31.2SaprospiraceaeFlavobacteriales.1.J.20051520172-173.2.4J.37013720123351646-1651.3.CANONJ.20153682939-2946.4.、J.200829123342-3347.5.J.2010361143-45.6.A/OJ.20153672610-2616.7.A2OJ.20088121074-1078.8.SBRJ.2000202129-133.9.J.2006751-9.10.J.2008356939-943.11.J.201329383-86.12.J.20143583031-3037.13.J.2015311535-39.14.J.2001215569-572.15.SUFRJ.2005254512-518.16.D.2014.22-23.17.J.20113771085-1089.18.J.20031995-7.19.MBRJ.2009301155-159.20KnoopSKunstS.InfluenceoftemperatureandsludgeloadingonactivatedsludgesettlingespeciallyonMicrothrixparvicellaJ.WaterScienceandTechnology1998374-527-35.21.J.20123181151-1156.22.A2OJ.20133472912-2917.23KragelundCLevantesiCBorgerAetal.IdentityabundanceandecophysiologyoffilamentousbacteriabelongingtotheBacteroidetespresentinactivatedsludgeplantsJ.Microbiology2008154Pt3886-894.24.FISHJ.2012184705-712.25.J.200724229-33.26.SBRJ.201127791-94.4701

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