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当前位置:首页 > 商业/管理/HR > 质量控制/管理 > 不同工艺污水处理厂的细菌气溶胶特点刘婷
2018-04-142013FY1127002013CFC0992014BHE003013xtz07。。doi10.3969/j.issn.2095-4565.2018.04.0041212312121212121435003243500334300732AB。CASSA132~228CFU/m3A2/OB63~416CFU/m32。CASS。2B。。X513A2095-4565201804-0015-06CharacteristicofAirborneBacteriainWaste-waterTreatmentPlantsUtilizingDifferentProcessingTechnologyLiuTing12ZhaoHao12ZhaoMengdi3XuHongfei12WangXin12ZhangJiaquan12ZhangLili12LiuXianli121SchoolofEnvironmentalScienceandEngineeringHubeiPolytechnicUniversityHuangshiHubei4350032HubeiKeyLaboratoryofMineEnvironmentalPollutionControlandRemediationHubeiPolytechnicUniversityHuangshiHubei4350033SchoolofInformationandSafetyEngineeringZhongnanUniversityofEconomicsandLawWuhanHubei430073AbstractTwosewagetreatmentplantsAandBwithdifferenttreatmenttechnologieswerestudiedastheob-jectsandthecharacteristicsofbacterialaerosolintheprocessofsewagetreatmentwerediscussedandana-lyzed.ResultsshowedthatbacterialaerosolconcentrationofplantAwhichusingcyclicactivatedsludgesys-temCASSwere132~228CFU/m3andbacterialaerosolconcentrationofplantBwhichmodifiedA2/Oox-idationditchprocesswere63~416CFU/m3.Thehighestconcentrationsofbacterialaerosolwerefoundintwounitsofthesludge-dewateringhouseandthegridwhereasthelowestconcentrationbacterialaerosolwasfoundinthebiologicaltreatmentunit.AndtheconcentrationsofbacterialaerosolinCASSpoolwerehigherthanthatofA2/Ooxidationditch.Thebacterialaerosolconcentrationsinbothplantswereoncleanlevelhow-evertheparticlesizeanalysisshowedthattheproportionofrespirablebacterialaerosolwashighinsewagetreatmentplantB.Theresearchresultisareferenceforevaluatingairqualityinsewagetreatmentplantswith34420188JOURNALOFHUBEIPOLYTECHNICUNIVERSITYVol.34No.4Aug.2018differenttechnologies.Keywordssewagetreatmentplantoxidationditchcyclicactivatedsludgesystembacterialaerosol、、、、、10.5~100μm2。、、3-5。6-910-13。、6-13。14814、1411-13。Malakootian15、、、。。2———CyclicActivatedSludgeSystemCASS。11.12ACASSBA2/O。A704×104t/d、、CASS。CASS、、。CASS、、。。B752.5×104t/dA2/O。、3。A2/O。、、、。。21。。12AB123CASS4CASS51.22015122。。ETW-6。。Ⅰ>7.0μmII4.7~7.0μmⅢ3.3~4.7μmⅣ2.1~3.3μmⅤ1.1~2.1μmⅥ0.65~1.1μm16。1620187min28.3L/min。75%。3。9cm20mL。37℃2d。。PositiveHoleMethod17。1.31.3.11c=T·1000t·F。11cCFU/m3TtminFL/min。1.3.22P=nT·100%。22PnT。1.4SPSS21.0tP<0.05。17。2。2CFU/m3>45000>15000>6000020000~450006000~1500030000~6000010000~200002500~600015000~300005000~100001000~250010000~150002500~5000750~10005000~100001000~2500500~7503000~5000<1000<500<300022.11。11A132~228CFU/m3B63~416CFU/m32P>0.05。Li18483CFU/m3Niazi19600~1016CFU/m3Malakootiana153780CFU/m3。2。ACASSB。24172。Li13A2/O。9。19。。ACASS142CFU/m3B77CFU/m3。CASSP>0.05。CASS。14。CASS、、、CASS。。CASS。2.21720ⅠⅡⅢ~Ⅵ。2。2ABAⅠⅡⅢ36.4%19.4%20.0%BⅢⅣⅤⅥ13.8%14.4%17.6%37.9%。2BIII23%Ⅳ26%21ⅣⅥ22IⅣ255%23。<4.7μm、24。AB44.24%83.78%。222564.6%。18201891.08%2677.2%27。2.3。A132~228CFU/m3B63~416CFU/m3182。B83.78%。31A132~228CFU/m3B63~416CFU/m322。AB。2AⅠⅡⅢ36.4%19.4%20.0%BⅢⅣⅤⅥ13.8%14.4%17.6%37.9%。32。B83.78%。1.J.2006114546-552.2NevalainenAPastuszkaJLiebhaberFetal.PerformanceofbioaerosolsamplerscollectioncharacteristicsandsamplerdesignconsiderationsJ.AtmosphericEnvironment.PartA.GeneralTopics1992264531-540.3RossMACurtisLScheffPAetal.Associationofasthmasymptomsandseveritywithindoorbio-aerosolsJ.Allergy2000558705-711.4LamWKZhongNSTanWC.OverviewonSARSinAsiaandtheworldJ.Respirology20038Suppls1S2-S5.5MeklinTReponenTToivolaMetal.Sizedis-tributionsofairbornemicrobesinmoisture-dam-agedandreferenceschoolbuildingsoftwocon-structiontypesJ.AtmosphericEnvironment200236406031-6039.6BrandiGSistiMAmaglianiG.Evaluationoftheenvironmentalimpactofmicrobialaerosolsgener-atedbywastewatertreatmentplantsutilizingdif-ferentaerationsystemsJ.JournalofAppliedMicrobiology2000885845-852.7PascualLPérez-LuzSYáezMAetal.Bio-aerosolemissionfromwastewatertreatmentplantsJ.Aerobiologia2003193-4261-270.8KarraSKatsivelaE.Microorganismsinbioaero-solemissionsfromwastewatertreatmentplantsduringsummerataMediterraneansiteJ.WaterResearch20074161355-1365.9Gotkowska-PachtaAFilipkowskaZKorzeniews-kaEetal.AirbornemicroorganismsemittedfromwastewatertreatmentplanttreatingdomesticwastewaterandmeatprocessingIndustrywastesJ.Clean-SoilAirWater2013415429-436.10OrsiniMLaurentiPBonintiF.Amoleculartyp-ingapproachforevaluatingbioaerosolexposureinwastewatertreatmentplantworkersJ.WaterResearch20023651375-1378.11FracchiaLPietronaveSRinaldiMetal.Site-relatedairbornebiologicalhazardandseasonalvariationsintwowastewatertreatmentplantsJ.WaterResearch200640101985-1994.12TabriziRDBernardAThommenAMetal.Sur-factantprotein-DandexposuretobioaerosolsinwastewaterandgarbageworkersJ.InternationalArchivesofOccupationalandEnvironmentalHealth2010838879-886.13LiJZhouLZhangXetal.BioaerosolemissionsanddetectionofairborneantibioticresistancegenesfromawastewatertreatmentplantJ.At-mosphericEnvironment2016124404-412.14Sánchez-MonederoMAAguilarMIFenollRetal.Effectoftheaerationsystemonthelevelsofair-419bornemicroorganismsgeneratedatwastewatertreat-mentplantsJ.WaterResearch200842143739-3744.15MalakootianaMRadhakrishnaNMazandaranyaMPetal.Bacterial-aerosolemissionfromwastewatertreatmentplantJ.Des
本文标题:不同工艺污水处理厂的细菌气溶胶特点刘婷
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