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33820128ENVIRONMENTALSCIENCEVol.33No.8Aug.2012IC*21412235℃IC.ICCOD20kg·m3·d-1COD85%VSS210mL·g·d-1DGGEDGGEDGGEF420DGGEF420Methanosaetasp.MethanosarcinamazeiMethanosaetasp.F42020kg·m3·d-1F420VSS0.16μmol·g-1Methanosaetasp.UPGAMAShannon.ICShannonPCR-DGGEF420X797A0250-3301201208-2715-082011-10-202011-12-068632009AA0330041986~E-mailtxzhuwenxiu@126.com*E-mailwqruan@jiangnan.edu.cnPerformanceandMicrobialCommunityDynamicCharacteristicsofanInternalCirculationReactorTreatingBreweryWastewaterZHUWen-xiuHUANGZhen-xingRENHong-yanRUANWen-quanSchoolofEnvironmentandCivilEngineeringJiangnanUniversityWuxi214122ChinaAbstractAlab-scaleinternalcirculationreactorICfedbyartificialbrewerywastewaterwasoperatedwithincreasingvolumetricloadingrateunder35℃continuously.Thereactorperformanceandtherelationshipbetweenmicrobialcommunitystructureandbioactivityintheanaerobicsludgewereinvestigatedduringtheoperation.TheCODremovalefficiencywasabove85%furthermorethemaximumvolumetricloadingrateVLRandthemaximumspecificmethanogenicactivitySMAofthereactorcouldbeupto20kg·m3·d-1and210mL·g·d-1respectively.TheresultsfromthedehydrogenaseandthebacteriaDGGEexperimentsdemonstratedthatthedehydrogenasevariationtendencywaspositivelycorrelatedtototallightintensityofthewholebacteriaDGGEbandsforeachsample.ThetotallightintensityofthewholebacteriaDGGEbandscanuseasareferentialindexforbiomassliveweightinanaerobicsystem.MoreoverthecoenzymeF420contentrelatedtotherelativeabundanceofMethanosaetabasedoncoenzymeF420andarchaebacteriaDGGEanalysis.AsthevolumetricloadingrateincreasedMethanosaetabecamesignificantlydominantwhichwasaccompaniedbythecoenzymeF420contentincreasing.Thecontentcouldbeupto0.16μmol·g-1meanwhilethesuperiorityofMethanosaetabecamesignificantlyobviousUPGAMAanalysisandShannonindexalsoconfirmedthedynamicchangesofmicrobialcommunitystructureduringtheoperation.KeywordsinternalcirculationreactorICShannonindexPCR-DGGEdehydrogenasecoenzymeF4202080..1t10~20m31.ASBR2、UASB3、AFB4、、.IC、、.DOI:10.13227/j.hjkx.2012.08.02033.、.PCR-DGGE、、5、、、6.IC.PCR-DGGEF420.11.1.2000mg·L-1FeCl3·4H2O80μg·L-1NiCl2·7H2O2μg·L-1CuCl2·2H2O1.2μg·L-1ZnCl22μg·L-1MnCl2·4H2O20μg·L-1CoCl2·2H2O80μg·L-1NH46Mo7O2·2H2O3.6μg·L-1.pHNaHCO3pH7.0.1.286%mVSS/mTSS0.760.9~2mm10L1/2.1.31IC180mm10mm20L...35±1℃.1ICFig.1DiagramofICreactor1.41.4.1COD、SS、VSSpH7F42089TTC10.1.4.2PCR-DGGEMO-BIOPowerSoilDNAIsolationKitDNAPCRPCR16SrDNAV3.Muzyer11F341R534PARC109FPRUN518R12~14.DGGEF341PARC109F5'GC20.PCR25μLFermentasPCRMasterMix2×PCR.PCR94℃4min94℃1min65℃1min0.5℃72℃1min2094℃1min55℃1min72℃1min1072℃6minPCR94℃4min94℃45s58.5℃45s0.5℃72℃45s2194℃45s48.5℃45s72℃45s1072℃6min.PCR1%.DGGEDcode61728ICBio-Rad8%35%~55%30%~60%.1×TAE80V60℃12hSYBRGreenIDGGEQuantityOne.1.4.3DGGEGCPCR.5.GenBankBlast.1.4.4DGGEShannonH'H'DGGE.Shannon15H'=-Σni/Nlgni/NniN.22.12.1.1COD106d..、COD2000mg·L-1COD3kg·m3·d-116h..3kg·m3·d-18、10、15、18、20kg·m3·d-1COD2000mg·L-1COD20kg·m3·d-12.4h.COD、COD2CODCODCOD85%.15kg·m3·d-120kg·m3·d-1COD.22kg·m3·d-1COD20kg·m3·d-110dCOD80%15dCOD85%.2CODCODFig.2Influent/effluentCODconcentrationandchangesofremovalrate2.1.23Fig.3Specificmethanogenicactivityatdifferentvolumetricloadingrates25mL100mLSMA.3VSS56mL·g·d-1210mL·g·d-12.75.7172333kg·m3·d-1.COD.2.2DGGE16..、QuantityOneDGGE.43kg·m3·d-1TF/SS5.3mg·g·h-14.1mg·g·h-112.7mg·g·h-1.DGGE.DGGE16SrDNAV3DGGE.4DGGEFig.4RelationbetweendehydrogenaseandintensityofDGGEbandforbacteriaatdifferentvolumetricloadingrates2.3F420F4208Delafontaine17F420.5F420F420.2、3、41F420.20kg·m3·d-1F420VSS0.16μmol·g-11.F420.5F420Fig.5RelationbetweenF420andarchaealcommunitystructureatdifferentvolumetricloadingrates2.42.4.1PCR-DGGE、DGGEDGGEQuantity81728ICOneUPGAMA6DGGE.R1122R322121、2、3、4、5、6、7、8、9、13.R2.141461561514.20kg·m3·d-1.UPGAMA6.81、2、3、45、6、87.20kg·m3·d-1.R1R2~R73、8、10、15、18、20kg·m3·d-1R822kg·m3·d-16DGGEFig.6DGGEfingerprintofbacteriaunderdifferentvolumetricloadingrates2.4.2PCR-DGGE、DGGEDGGEQuantityOneUPGAMA7.52、3、42215.14、Roest18.7DGGEFig.7DGGEfingerprintofarchaeaunderdifferentvolumetricloadingratesQantityOneDGGE1R2~R871.4%、69.1%、80.5%、47.7%、44.6%、25.9%、22.9%.R3R180.5%R822.9%3、8kg·m3·d-170%22.9%IC.9172331Table1DicecoefficientcomparingthesimilaritiesofPCR-DGGEfingerprints123456781100.071.469.180.547.744.625.922.9271.4100.075.685.659.846.934.136.5369.175.6100.079.653.449.027.231.4480.585.679.6100.055.151.226.432.1547.759.853.455.1100.050.935.354.1644.646.949.051.250.9100.052.547.1725.934.127.226.435.352.5100.052.6822.936.531.432.154.147.152.6100.0ShannonH'8.19、20.3kg·m3·d-1Shannon15kg·m3·d-1Shannon.2.56723.8ShannonFig.8Shannonindexofgranularsludgethroughoutoperationalprocess2Table2PhylogeneticrelationshipofdifferentclonesequencesofbacteriaGenBank%Streptomycesclavuligerus98%、Vibriosp.90%、Flavobacteriumpsychrophilum98%、Serratiasp.98%、Clostridiumbeijerinckii98%、UnculturedVeillonellaceaebacterium98%、Unculturedbacterium98%、Unculturedbacterium98%、UnculturedLactococcussp.100%、UnculturedClostridialesbacterium98%1、2、3、4、5、6、7、8、9、13UnculturedLactococcussp.100%14UnculturedVeillonellaceaebacterium98%、Lactococcuslactissubsp.98%6、153Table3Phylog
本文标题:IC反应器处理啤酒废水的效能及其微生物群落动态分析朱文秀
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