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37520175ActaScientiaeCircumstantiaeVol.37No.5May2017No.15XNLD04SupportedbytheFundamentalResearchFundsfortheCentralUniversitiesandtheResearchFundsofRenminUniversityofChinaNo.15XNLD041989—E-mail1227790602@qq.com*E-maillgh@ruc.edu.cnwhc@ruc.edu.cnBiographyXUXianglong1989—maleE-mail1227790602@qq.com*CorrespondingauthorE-maillgh@ruc.edu.cnwhc@ruc.edu.cnDOI10.13671/j.hjkxxb.2016.0347.2017.SBRJ.3751695-1703XuXLLiuGHFanQetal.2017.Theshiftofbacterialcommunitystructureduringstart-upofanaerobicammoniaoxidationANAMMOXinasequencingbatchreactorJ.ActaScientiaeCircumstantiae3751695-1703SBR**1008722016-07-192016-08-242016-08-24SBR.PCR-DGGE、PCRANAMMOX.26.6%~50.5%ANAMMOXANAMMOXBrocadia.SBRANAMMOX1.73×109copies·g-182%.SBR0253-2468201705-1695-09X703ATheshiftofbacterialcommunitystructureduringstart-upofanaerobicammoniaoxidationANAMMOXinasequencingbatchreactorXUXianglongLIUGuohua*FANQiangWANGYuanyuanWANGHaoSONGXinxinQILuWANGHongchen*SchoolofEnvironment&NaturalResourceRenminUniversityofChinaBeijing100872Received19July2016receivedinrevisedform24August2016accepted24August2016AbstractThestart-upofanaerobicammoniaoxidationANAMMOXsysteminasequencingbatchreactorSBRwhereBaiyangdianLakeshoresedimentswereinoculated.ThemicrobialcommunitystructureoftotalbacteriaandANAMMOXbacteriainthesystemalongwiththeenrichmenttimewasinvestigatedbyusingmolecularbiologymethodse.g.PCR-DGGEqPCRandDNAsequencing.Meanwhilethewaterqualityoftheinfluentandeffluentwascontinuouslymonitoredduringthewholestart-upstage.Theresultsshowedthatthedynamicchangeoftotalbacterialcommunityalongwiththeenrichmenttimeincreasedfrom26.6%to50.5%andtheirdiversitydecreasedfirstandthenincreasedafterwards.TheANAMMOXbacterialcommunitydiversityintheSBRbecamesingleattheendofenrichmentandwaspredominantlyCandidutusBrocadia.ThemaximumbiomassofANAMMOXbacteriaachieved1.73×109copies·g-1drysludgeduringtheenrichmentwiththehighestremovalrateofTNaround82%.KeywordsBaiyangdiansedimentsANAMMOXSBRreactorbacterialdiversitycommunitystructure1Introduction..、.ANAMMOX371977BrodaBroda1997NH+4N2.1994MulderDelftANAMMOXVandeGraafetal.1995.199715NANAMMOXANAMMOXNH+4NO-2VandeGraafetal.1997StrousANAMMOXNH+4NO-21NO-3Strousetal.1998.NH+4+1.32NO-2+0.066HCO3-+0.13H+→1.02N2+0.26NO-3+0.066CH2O0.5N0.15+2.03H2O1/ANAMMOX2012、20132015Thirdetal.2005Rysgaardetal.2004.ANAMMOXN250%~70%Kuypersetal.2003ANAMMOX.16SrRNAANAMMOX.ANAMMOX5Schmidetal.20052007Kartaletal.2007CandidutusBrocadia、CandidatusKuenenia、CandidatusScalindua、CandidatusAnammoxoglobusCandidatusJettenia.、.、ANAMMOX.ANAMMOXANAMMOXANAMMOX、、SBRUASBANAMMOXANAMMOX.ANAMMOXANAMMOXPentonetal.2006Schmidetal.2007Kartaletal.2007..ANAMMOX15NANAMMOXN103g·Nm-2·a-1Zhuetal.2013.ANAMMOX9ANAMMOXSBRANAMMOX.2Materialsandmethods2.131m-80℃DNASBR.2.28LSBRANAMMOX.6L1.525min、15min、20h、3h、15min.1Fig.1Diagramofexperimentalsystem35℃80r·min-1pH7.5~8.2.69615SBR.5500mg·L-1.NH4ClNaNO2NH4ClNaNO2ANAMMOXNH4Cl15mg·L-160mg·L-1NaNO215mg·L-178mg·L-1.NaHCO31.85g、KH2PO40.00625g、CaCl2·2H2O0.3g、MgSO4·7H2O0.2g、FeSO4·7H2O0.018g、EDTA·2H2O0.0125g1mL.VandeGraaf1996.2.3pHMettlerToledoDelta320pHNH+4-N、NO-2-N、NO-3-N《》520002mol·L-12h.NH+4-NNO-2-NN-1--NO-3-N.2.42.4.1DNAPCR0.5gFASTDNADNAQbiogeneCarlsbadCA.27FAGAGTTTGATCMTGGCTCAG518RATTACCGCGGCTGCTGGPCR40bpGC357FCCTACGGGAGGCAGCAG518RPCR2015.ANAMMOXPCR1PLA46f/630rNeefetal.1998Purkholdetal.200012ANAMMOXAmx368f/Amx820rAmanoetal.2007.2.4.2PCR-DGGEPCR-DGGE.1.5μLLoadingbuffer4μLPCRDNAD-codeBio-Rad8%35%~65%.110V60℃400min.SYBRGREENIBio-RadGel-DocTMXR+DGGE.BIO-RADQuantityOne.NTSTSUPGMA.Shannon-wienerH2014Ht=-ΣPilgPi2Pi=ni/NniiN.2.4.3PCR、、PromegaAgaroseGelDNASolarbioPCRpGEM-TeasyPromegaMadisonWITrans1-T137℃.96.HhaⅠMboⅠ.DNAstarMothur3%OTU.NCBIBLASTANAMMOX16SrRNAMEGA5.0Neighbor-JoiningGarbevaetal.2001.2.4.4PCRqPCRAOB、NOBANAMMOXqPCRNOB.qPCRSYBYGreen①DNA3、、、、.TE7SYBYGreen.20μLSYBYGreenmix10μL5μmol·L-10.4μLDNA1μLddH2O20μL.12016..10CT-3.5~-4.295%.②qPCRSYBYGreen、.7961371Table1PCRprimersintheamplificationAOBAmoA-1fAmoA-2r-TCGGGGTTTCTACTGGTGGTCCCCTCTGCAAAGCCTTCTTC95℃5min95℃30s55℃45s72℃45s40NitrobacterF1370F1nxrAF2843R2nxrACAGACCGACGTGTGCGAAAGTCCACAAGGAACGGAAGGTC95℃5min95℃30s55℃45s72℃45s40NitrospiraNSR1113fNSR1264rCCTGCTTTCAGTTGCTACCGGTTTGCAGCGCTTTGTACCG95℃5min95℃30s56℃30s72℃30s40AnammoxAMX809fAMX1066rGCCGTAAACGATGGGCACTAACGTCTCACGACACGAGCTG95℃5min95℃15s55℃45s72℃30s403Resultsanddiscussion3.12.2Table2CharacteristicsofthesedimentssamplesinBaiyangdianLakeT/℃DO/mg·L-1pHNH+4/mg·kg-1NO-2/mg·kg-1NO-3/mg·kg-1143.28.18214.62.214.13.2SBRANAMMOX.321~52dHRT4dNH+4NO-21∶115mg·L-130mg·L-1.TN55%TN.53~187dANAMMOXHRT4d2dNH+4NO-21∶1.32NH+4-NNO-2-N50mg·L-166mg·L-1.N2.TN20%.188~265dANAMMOXHRT2dNH+4NO-260mg·L-178mg·L-1NH+4NO-295%TN82%.NH+4NO-21.3ANAMMOX.2Fig.2Thenitrogentransformationinthereactor3.3DGGEDGGE3.1~51、30、90、165、250d.3.1~30d30d1d73.4%.31~250d3a2、3、6、11、12、1889615SBR6、8、9、10、14、15161、4、71717.3b250d1d49.5%250d26.6%~50.5%Osbornetal.2000.3DGGEabFig.3DGGEprofileoftotalbacteriaunderdifferentperiodaandthebandsandstrengthschematicofDGGEprofilebNTSYSDGGEUPGMA4.1~51、30、90、165250d.1、2、3231、3090d3085d45165250d.4UPGMAFig.
本文标题:SBR反应器厌氧氨氧化系统启动过程中细菌群落结构的变化徐相龙
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