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50220182JOURNALOFHARBININSTITUTEOFTECHNOLOGYVol.50No.2Feb.2018DOI10.11918/j.issn.0367-6234.201705098123211331.2002342.1500903.200439COD.pH=6.5~8.5CODAiba.pHCODpH=7.5.CODpHpH7.5~8.0.COD5.6~11.312.4~16.8.3AOBNitrosomonaseuropaeaATCC19178、NitrosomonasstercorisNitrosospirasp.PM266%.X703.1A0367-6234201802-0065-06DegradationkineticsofpollutantsandmicrobialcommunitiesinshortcutnitrificationXIAJunfang123WANGShutao2ZHANGYongming1HUJunjie13FANGXiaoqin31.CollegeofLifeandEnvironmentalSciencesShanghaiNormalUniversityShanghai200234China2.SchoolofEnvironmentHarbinInstituteofTechnologyHarbin150090China3.ShanghaiJingYuEnvironmentEngineeringCo.Ltd.Shanghai200439ChinaAbstractThedegradationkineticsofammonianitrogenandCODandthemicrobialcommunitiesinanintermittent-flowshortcutnitrificationreactorwereinvestigatedtoremoveammoniaandorganicmattersfromlandfillleachate.TheresultsshowthatwhenpH=6.5-8.5thedegradationofammoniaconformstotheMichaelis-MentenmodelwhiletheCODdegradationissuitableforAibakineticmodel.WiththeincreaseofpHthemaximumdegradationrateandsaturationconstantsofammoniaandCODincreasefirstandthendecreasereachingthemaximumvalueswhenpH=7.5.TheresultsindicatethatthedegradationsofammoniaandCODareinfluencedbypHandtheoptimumpHshouldbecontrolledbetween7.5and8.0.InadditionthedegradationrateandthemaximumdegradationrateofCODare5.6-11.3and12.4-16.8timeshigherthanthoseofammoniaintheshortcutnitrificationprocessrespectively.Thismaybebecausethatthehighconcentrationoforganicmattersininfluentleadstotheheterotrophicbacteriatogrowfasterthanautotrophicbacteriainthebiologicalsystem.FinallythedomainspeciesofammoniaoxidizingbacteriaAOBinthereactorareNitrosomonaseuropaeaATCC19178NitrosomonasstercorisandNitrosospirasp.PM2accountedfor66%togetherindicatingthattheAOBwasthepredominantspeciesforammoniaremovalinthisintermittent-flowshortcutnitrificationreactor.Keywordslandfillleachateshortcutnitrificationkineticsdegradationbacterialcommunities2017-05-15SK2012321977—1958—zhym@shnu.edu.cn1-2.3-4.5-625%40%7-8.9.CODammoniaoxidizingbacteriaAOB10-11.pHpHCOD12-14.COD、.11.1MLSS4.2g/LVSS2.7g/LVSSMLSS0.64.1.21.1.3500mL11Tab.1Waterqualityoflandfillleachateanditsdiluentmg·L-1pHCODρNH4+-NρNO2--NρNO3--NρTN7.894001540<0.51.615506.5~8.5200~190020~100<0.50~125~10530℃1#、2#、3#、4#5#.5150mL5100mL.2min0、COD、.DO0.8~1.2mg/L1h、COD、5.pH6.5、7.0、7.5、8.08.530℃pHCOD.1—2—3—4—5—1Fig.1Schematicofexperimentalsetup1.4CODN-1--.DNAzolDNAPCRpolymerasechainreaction15.50μL2×Hotstart-PCRmix25μL0.8μLDNA1μL22.4μL16SrDNAF5'-AGAGTTTGATCC-TGGCTCAG-3'R5'-CAKAAAGGAGGTGAT-CC-3'16.PCR94℃4min94℃30s50℃30s72℃1min3572℃10minPCR1%DNApMD-18T-vectorE.coliDH5α16SrDNAbasiclocalalignmentsearctoolBLASTGenBank15.1.51r=-dρdt.11ρ0-ρt=rt.2ρ0mg/Lρttmg/Lrmg/L·hth.ρ0-ρt-t.2Michaelis-Menten17r=rmaxρKS+ρ.331r=KSrmax·1ρ+1rmax.4r=rmaxρ-1000KS+ρ-1000.5·66·5051r=KSrmax·1ρ-1000+1rmax.6rmg/L·hrmaxmg/L·hKSmg/Lρmg/L.KSrmax.3Aiba18r=rmaxρ-200KS+ρ-200exp-ρ-200KSI().7rmg/L·drmaxmg/L·dρmg/LKSmg/LKSImg/L.22.1pHρ1~ρ520.1、37.9、57.2、74.4100mg/L30℃pH2.20~100mg/LpH.ρ1~ρ5pH6.58.5.19pH5.0~8.0pHpH8.0~10.0pHpH8.06.6mg/L·h.ρ1=20.1mg·L-1ρ2=37.9mg/Lρ3=57.2mg/Lρ4=74.4mg/Lρ5=100mg/L2Fig.2DegradationofNH4+-Nunderdifferentinitialconcentrations4pH32.2pH6.58.5rmaxKS.pH7.542.7mg/L·h177.3mg/LpH6.543.6%42.9%.pHpH7.5pH.20pH6.0~8.0pH.21pH7.5pH7.08.0·76·2.2Tab.2KineticparametersofNH4+-NdegradationpHrmax/mg·L1·h1KS/mg·L1R26.524.1101.10.97347.032.2138.30.99127.542.7177.30.97018.035.1170.60.99598.530.9155.10.9958pHpHpHpH———NH3freeammoniaFApHNH3pH.pHNH3pHNH3.22ρNH4+-N=65mg/L、t=28℃pH6.5FA0.17mg/LpH8.0FA5.18mg/LpH6.58.FA30.5.pH6.524.1mg/L·hpH8.035.1mg/L·h.pH6.5~8.0.3pHFig.3FittingcurvesofNH4+-NdegradationunderdifferentpH2.2pHCODCODρ1~ρ5238、550、1298、14161900mg/L30℃pHCOD4.4CODFig.4DegradationofCODunderdifferentinitialconcentrations·86·504ρ200~1416mg/LCODCODρ1416mg/LCOD.Aiba718r~ρ-200pH53.pH6.58.5rmax、KSKSIpH7.5719.2mg/L·h、920.41404.2mg/LpHCODpHCODpH7.0~8.0.5CODFig.5FittingcurvesofCODdegradationunderdifferentpH3CODTab.3KineticparametersofCODdegradationpHrmax/mg·L-1·h-1KS/mg·L-1KSI/mg·L-1R26.5301.1632.6935.40.98897.0653.9907.91187.40.99237.5719.2920.41404.20.99178.0467.2821.71329.60.99588.5392.6623.01256.90.9772COD4.COD5.6~11.312.4~16.8.23128.2mg/g·h7.2mg/g·h.COD.4CODTab.4ComparisonofthedegradationparametersofCODandammoniar/mg·L-1·h-1rmax/mg·L-1KS/mg·L-13.6~17.724.2~42.7101.1~77.3COD20.2~201.6301.1~719.2623.0~920.42.30.8~1.2mg/L50%~90%.PCR100GenBankBLAST5.5Tab.5ProportionsofAOBandNOBinanintermittentflowreactor/%1NitrosomonaseuropaeaATCC19178NR_040879.1342NitrosomonasstercorisAB_900133.1253NirospinamoscoviensisX82558NR_117368.1134Nitrosospirasp.PM2FN_394323.175MicrococcusmobilisKU_860096.146AlkaliphilusmetalliredigensQYMFNC_009633.127AnaerolineathermophilaUNI-1NC_014960.128ParacoccusdenitrificansPD1222NC_008687.129AromatoleumaromaticumEbN1NC_006513.1110Thauerasp.MZ1TNC_011662.2111AnoxybacillusflavithermusWK1NC_011567.1112BurkholderiaxenovoransLB400NC_007952.1113Dehalococcoidessp.BAV1NC_009455.1114DelftiaacidovoransSPH-1NC_010002.1115DesulfitobacteriumhafnienseDCB-2NC_011
本文标题:短程硝化反应中污染物降解动力学及微生物群落研究夏俊方
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