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37920099()JOURNALOFTONGJIUNIVERSITY(NATURALSCIENCE)Vol.37No.9 Sep.2009:0253-374X(2009)09-1207-05DOI:10.3969/j.issn.0253-374x.2009.09.013:2008-05-28:(EREH0712): (1978—),,,,.E-mail:whutcj@gmail.com程 静1,2,蔡伊秋1,张超杰1,周 琪1(1.,200092;2.,430070):pH、,.:--;pH7~9;;;.:;;;:X703 :AInfluenceFactorsofNitrogenousHeterocyclicCompound-QuinolineDegradationUnderAnoxicConditionsCHENGJing1,2,CAIYiqiu1,ZHANGChaojie1,ZHOU,Qi1(1.StateKeyLaboratoryofPollutionControlandResourceReuse,TongjiUniversity,Shanghai200092,China;2.SchoolofCivilEngineeringandArchitecture;WuhanUniversityofTechnology,Wuhan430070,China)Abstract:Astudywasmadeoftheanoxicdegradationandremovalofnitrogenousheterocycliccompound-quinoline,denitrificationofacclimatedsludgeaswellastheeffectofpH,C/Nratio,bio-ferricondegradationofquinolineunderanoxicconditionsbyflask-shakingtests.Themicrobialdegradationproductsweremeasuredandthedegradationpathwayofquinolineinanoxicconditionwasanalyzed.Theresultsindicatethatquinolineisremovedbythreesteps:biosorption,desorptionandbiodegradation.TheoptimalrangeofpHisbetween7and9.TheC/Nratiodoesnotaffectthereductionofquinolineobviously.Bio-ferricprocesscannotimprovethedegradationofquinoline,quinolinecanbeusedasthesolecarbonandnitrogensourcesforbiodegradation.Keywords:nitrogenousheterocycliccompound;quinoline;anoxic;influencefactors ,,C9H7N.—CH,..、、,、.,、,、.,..,[1-4].CuiComamonassp,[5];Fetzner,[6].//(AAO),[7];,[8].、,,.,,pH、,. ()37 1 1.1 ,.25cm、20cm、5L.25℃~30℃,,..1.2 ,,,,,、NaNO3,,K2HPO4·3H2O,CaCl2MgSO4、,,C∶N∶P∶Ca∶Mg=100∶20∶1∶0.18∶0.18.,.,2,.3000~3500mg·L-1.1.3 ,,,3%~5%.,,,;100ml;,,,,0.1mg·L-1,.,25℃,160r·min-1..,,-.VARIANProstar(HPLC),UV-VIS,20μL,0.20μm,WatersXTerraRP18(250*4.6mm,5μm),256nmVACN∶Vwater=40∶60,1ml·min-1,3.81min,.NO3—N,NO2—N,pH,(SS)、(VSS)[9].ThermoElectronCorporationGC/MS,,.HP,:60℃,2min,15℃·min-1,250℃3min.EI,70ev,250℃.SigmaBSTFA(GC/MS).2 2.1 ,.,.150mg·L-1,8[10].12NO-3—NNO-2—N.1 NO-3—NFig.1 NO-3—Nvariationindenitrificationprocessofacclimatedsludge2 NO-2—NFig.2 NO-2—Nvariationindenitrificationprocessofacclimatedsludge1208 9 ,: 1,8,0.5h,0.5~3hNO-3—N,.,NO-3—N.NO-3—N.12,,NO-3—NNO-2—N,NO-2—N,,NO-3—N,NO-2—N,NO-2—N,NO-2—N.,,.2.2 ,.,.150mg·L-1,8,,6h.3.3 Fig.3 Anoxicdegradationofquinolineindifferentmedia 3,.1h,.,,,,,;31h,,,,,,.(1)(2),,NO-3—N,1h,1~3h,NO-3—N,NO-3—N,,NO-3—N.2.3 pH,1g3.57g,pH,,pH,pH.100mg·L-1pH(6h),,4.4 (100mg·L-1)Fig.4 Quinoline(100mg·L-1)variationindifferentpH 4,pH6~9,.pH7~9,,pH7,,.pH6~9,,7pH6.5~7.5,:pH;,(TKN),.pH7,,pH.,pH6.5~7.5,pH7,.pH,,1209 ()37 pH.pH.,pH7~9.pH,.2.4 ,,,.,6h,NO3—N,NO2—N,1.1 Tab.1 Relationshipbetweenoutletquinolineandm(C)/m(N)ρ()/(mg·L-1)ρ(NO-x—N)/(mg·L-1)ρ()/(mg·L-1)ρ(NO-3—N)/(mg·L-1)ρ(NO-3—N)/(mg·L-1)/%1500.2514.310.350.8290.46150223.50216.2844.812.2689.15150111.75414.1622.462.4990.5615074.50614.2415.832.3290.5115055.88813.5811.332.6790.9515044.701014.389.422.4890.4215022.352014.404.282.5590.40 :ρ(NO-x—N)ρ(NO-3—N)ρ(NO-3—N);ρ(COD)/ρ(NO-3—N),ρ(COD)ρ(COD)(100mg·L-1ρ(COD)298mg·L-1). 1,,,90%.,0.25mg·L-1,0.35mg·L-1,.,,7,.,,.(=20),,.:,,,;,TKN,,.,[11].,NO-2—N.2.5 ,.,、,、.FeCl3Na2CO3,Fe3+,5.5 Fig.5 Quinolinevariationindifferentconcentrationsofbio-ferric 5,.,,,.2.6 ,GC/MS1h,3h15h,,,1210 9 ,: 2,8-,8-,.3h67.6 3hGC/MSFig.6 GC/MSspectraofsupernatantafterquinolinedenitrificationfor3h7 Fig.7 Degradationpathwayofquinolineinanoxiccondition ,,,pH,pH7~9.,,,,.3 (1),NaNO3,--,,.(2)pH,pH7~9.(3),,.(4).(5),.:[1] ,,.[J].,2003,22(1):52.CUIMingchao,LILi,CHENFanzhong.Studyprogressonbiodegradationofquinolineanditsderivatives[J].ShanghaiEnvironmentalSciences,2003,22(1):52.[2] ,.[J].,2005,25(2):32.HONGXin,YANGXianghua.Isolationcharacterizationanddieseloildenitrogenofquinoline-degradingbacterium[J].JournalofLiaoningUniversityofPetroleum&ChemicalTechnology,2005,25(2):32.[3] ,,,.[J].,2006,26(5):1390.LIUBinbin,ZHANGFeng,FENGXiaoxi,etal.Identificationoffunctionallyimportantmicroorganismsinalab-scaleanaerobicbiofilmreactorforquinoline-degradation[J].ActaEcologicaSinica,2006,26(5):1390.[4] WANGJianlong,WUWeizhong,ZHAXuan.Microbialdegradationofquinoline:kineticsstudywithburkholderiapickttii[J].BionedicalandEnvironmentalSciences,2004,17(1):21.[5] CUIMingchao,CHENFanzhong,FuJiamo,etal.MicrobialmetabolismofquinolinebyComamonassp[J].WorldJournalofMicrobiology&Biotechnology,2004,20(6):539.[6] FetznerS.Bacterialdegradationofpyridine,indole,quinoline,andtheirderivativesunderdifferentredoxconditions[J].AppliedMicrobiologyandbiotechnology,1998,49(3):237.[7] ,,.A1—A2—O[J].,2002,22(1):34.LIYongmei,GUGuowei,ZHAOJianfu.StudyonbiodegradationcharacteristicsofseveralnitrogenheterocycliccompoundsincokeplantwastewaterinA1—A2—Obiofilmsystem[J].ActaScientiaeCircumstantiae,2002,22(1):34.[8] ,,.[J].:,1999,8(3):34.HEMiao,YAOJun,ZHOUGuoqiang.StudyprogressonbiodegradationofPAHsandheterocycliccompounds[J].JournalofTianJinProfessionalCollege,1999,8(3):34.[9] .[M].4.:,2002.MinistryofEnvironmentalProtectionofthePeople'sRepublicofChina.WaterandExhaustedWaterMonitoringAnalysisMethod[M].4thed.Beijing:ChinaEnvironmentSciencePress,2002.[10] ,,.[J].,2003,22(11):734.MANa
本文标题:氮杂环化合物喹啉在缺氧条件下降解的影响因素程静
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