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当前位置:首页 > 商业/管理/HR > 质量控制/管理 > 多级厌氧法处理螺旋霉素工业发酵菌渣效果的研究朱培
82Vol.8No.220142ChineseJournalofEnvironmentalEngineeringFeb.20141222213*1.2002372.2000403.200040。44L411L。121d31.27、1.822.73kgCOD/m3·d。。2。2.73kgCOD/m3·d45%1。。80d2.73kgCOD/m3·d97%COD90%。X787A1673-9108201402-0703-06PerformanceoffourstagesanaerobicreactorsystemintreatmentofspiramycinmanufacturingbiowasteZhuPei12ZhangJianbin2LiJian2ShaoLei2ChuJu1ChenDaijie31.StateKeyLaboratoryofBioreactorEngineeringEastChinaUniversityofScience&TechnologyShanghai200237China2.StateKeyLaboratoryofNewDrug&PharmaceuticalProcessShanghaiInstituteofPharmaceuticalIndustryShanghai200040China3.ChinaStateInstituteofPharmaceuticalIndustryShanghai200040ChinaAbstractSpiramycinmanufacturingbiowastewastreatedbyafourstagesanaerobicreactorsystem.Thevolumeofthesystemwas44Lbeingdividedintofour11Lstageseachofthestagewasconnectedbyseries.ThesystemwasoperatedwiththreestepsintheorganicloadingrateOLRof1.271.82and2.73kgCOD/m3·d.Theprocessperformanceofthesystemwascharacterisedintermsofitsbiogasvolumeandspiramycinreduction.Thesystemcouldreachitsstablestateinbiogasproductionaftertwomonthoperation.About45per-centofallbiogaswasproducedfromthestage1attheOLRof2.78kgCOD/m3·d.Thoughspiramycinwasnoteliminatedrapidlyatthebeginningafter80daysanaverageof97%spiramycinand90%CODreductionwereachievedattheOLRof2.78kgCOD/m3·dindicatingthatthisantibioticcouldbedegradedefficientlyintheanaerobicreactorsystem.KeywordsfourstagesanaerobicreactorsystemspiramycinCODmanufacturingbiowastedegradation“”2012ZX092011012013-01-292013-02-261987~。E-mailpeipeiecust@163.com*E-mailhccb001@163.comspiramycinSPMStreptomycesspiramycetic-us1。2090pharmaceuticalsandpersonalcareproductsPPCPs2、3-5。。8。61%199210%1998。20027。2008《》8。。70%~80%2000/t。。、。、9-11。。anaero-bicbaffledreactor12。。。1314。COD。11.11。1#、2#、3#4#。80cm14cm20cm。10cm。6cm。。。。1Fig.1Fourstagesanaerobicreactorsystem1.2pHSartoriusPB-10。COD12000r/min10minHACHDR890。Waters1525。NikonE100。1.32UASB。。1.41.4.130L2.0%3∶724L37℃80r/min、5min2。3L。4d2.0%2L411L。1.4.2。1#40724#。2。121d31。112.0%COD14000mg/LCOD6500mg/L4LOLR1.27kgCOD/m3·d。232。22.0%4LCOD20000mg/LCOD10000mg/L。34.0%COD40000mg/LCOD18000mg/L3L。pH10dCOD。1Table1SummaryofreactoroperatingconditionsofthefourstagesanaerobicreactorsystemdOLRkgCOD/m3·dCODmg/L11~581.2714000259~921.8220000393~1212.73400001.4.32h。Welchrom-C185μm4.6×250mm232nm35℃A50mmol/LBA∶B=63∶371mL/min。。BacillussubtilisLB37℃。22.1pHpH。1#pH7.5~8.04#pH7.72pH。113~14L/d“”1#2#3#。1#2#。。3449。21#>2#>3#>4#。2、pHFig.2BiogasproductionofeachstagetotalbiogasproductionandpHoftheeffluentatstage4atdifferentOLR22。212120L/d50%2143%。3250%1.82kgCOD/m3·d2.73kgCOD/m3·d。3225%25L/d。3L4.0%。232。225078。1.82kgCOD/m3·d2.73kgCOD/m3·d1#11L/d。231#55%45%。1Chelliapan15UASR。2.2COD122%2。25、35、45278、88。32COD6500mg/L10000mg/LCOD1600mg/L1200mg/L。COD75%88%。2COD11。COD。325、35、45、7888CODFig.3SolubleCODof25th35th45th78thand88thdayinfluentsandeffluents3102112COD。64COD18671±1479、10303±772、7693±973、3884±12721868±402mg/LCOD90%。50%2.73kgCOD/m3·dCOD90%。1#50%1#45%。2.32.3.1。242%4。。4abFig.4Microscopicalmorphologicalcharactersofinfluentandeffluentofthefourstagesanaerobicreactorsystem2.3.21。2SPMⅠ、Ⅱ、Ⅲ30.30、2.702.17mg/g5.2mg/g。68d5SPMⅠSPMⅡ0.10mg/gSPMⅢ1.426072mg/g。10d78d30.2mg/g。10d88d0.2mg/g。2SPM95%Castiglioni166SPM0%~11%SPM。568、7888SPMFig.5ResidualSPMof68th78thand88thdayeffluents6102112SPMCODFig.6ResidualSPMandsolubleCODof102thand112thdayforeachstage3102112。6SPM2.99±0.05mg/g1#2#3#4#0.91±0.250.39±0.120.19±0.020.08±0.01mg/g97.3%。1#70%。7。321SPM97%。7102112Fig.7Bioactivityof102thand112thdaysamplesforeachstage312、COD。2。1.82kgCOD/m3·d20L/d12.73kgCOD/m3·d25L/d25%COD。3COD。1COD75%。23COD90%。4。88d2.73kgCOD/m3·d97%。5。。1..7078198222113-16YuQiwei.Anewkindofstreptomycetewhichcanproducespiramycin.ActaMicrobiologicaSinica198222113-16inChinese2DaughtonC.G.TernesT.A.Pharmaceuticalsandper-sonalcareproductsintheenvironmentAgentsofsubtlechangeEnviron.HealthPerspect.19991076907-9383MartaC.FranciscoO.JuanM.L.etal.Behaviorofpharmaceuticalscosmeticsandhormonesinasewagetreatmentplant.WaterRes.200438122918-29264SnyderS.A.WesterhoffP.YoonY.etal.Pharma-ceuticalspersonalcareproductsandendocrinedisruptorsinwaterImplicationsforthewaterindustry.Environ.Eng.Sci.2003205449-4695TernesT.A.MeisenheimerM.MsdowellD.Removalofpharmaceuticalsduringdrinkingwatertreatment.Environ.Sci.&Technol.200236173855-38636AndersonA.D.NelsonJ.M.RossiterS.PublichealthconsequencesofuseofantimicrobialagentsinfoodanimalsintheUnitedStates.Microb.Drug.Resist.200394373-3797176.200281.20089AlvarezJ.A.OteroLLemaJ.M.etal.Theeffectandfateofantibioticsduringtheanaerobicdigestionofpigmanure.BioresourceTechnol.2010101228581-858610OsmanA.A.Degradationandmetabolizationofchlortet-racyclineduringtheanaerobicdigestionofmanurefrommedicatedcalves.J.Hazard.Mater.20081582-3485-49011FerndezanJ.PerezM.RomeroL.I.Effectofsub-strateconcentrationondrymesophilicanaerobicdigestionoforganicfractionofmunicipalsolidwasteOFMSW.BioresourceTechnol.200899146075-608012BarberW.P.StuckeyD.C.TheuseoftheanaerobicbaffledreactorABRforwastewatertreatmentAre-view.WaterRes.19993371559-157813AlvesM.PereiraA.MotaM.
本文标题:多级厌氧法处理螺旋霉素工业发酵菌渣效果的研究朱培
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