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109Vol.10No.920169ChineseJournalofEnvironmentalEngineeringSep.20162CMC*2016202BAFCMC0.071m3·m2·h-1、24hCOD、CMC、。COD、CMC。4∶12CODCMC72%65%、67%62%。COD、CMC、1.5、1.31.1m。。CMCCMC34.7%26.1%。CMCX703A1673-9108201609-4987-07DOI10.12030/j.cjee.201503249TwokindsofBAFsadvancedtreatingofstimulatedesizingwastewaterincludingCMCYANGBo*WANGSuifengLIFangTIANQingMAChunyanCollegeofEnvironmentalScienceandEngineeringDonghuaUniversityShanghai201620ChinaAbstractTwobiologicalaeratedfiltersBAFwithceramicfillerandactivatedcarbonfillerrespective-lywereappliedtostimulatethetreatmentofdesizingwastewaterincludingCMC.Underahydraulicloadingof0.071m3·m2·h-1andhydraulicretentiontimeHRTof24htheremovaleffectsofCODCMCandturbidityandtheaerationintensityonBAFoperationwereinvestigated.Inthispapertherelationshipbetweenpollutantremovalmicrobialbiomassandmicrobialactivityalongtheheightofthefiltercolumnarediscussed.TheresultsshowedthattheremovalefficiencyofCODandCMCincreasedwithincreasesingas-waterratioandintenseaerationcausedincreasesineffluentturbidity.Whenthegas-waterratiowas4∶1theaverageremovalratesofCODandCMCinthetwofillerswereabout72%and65%and67%and62%respectively.ThemainregionsofCODCMCandturbidityremovalintheBAFwerelocatedinthefiltercolumnbelowheightsof1.51.3and1.1m.Microbialbiomassintheceramicfilterwasslightlyhigherthanthatintheactivatedcarbonfilter.Thechangetrendsofmicrobialbiomassandmicrobialdehydrogenaseactivityalongtheheightoftheceramicfilterwassimilartothatintheactivatedcarbonfilter.TheremovalofCMCinthesetwofiltersmainlyreliedonbio-logicaladsorptionandbiodegradationaccountedforonly34.7%and26.1%ofthetotalremovalrateofCMC.KeywordsdesizingwastewaterCMCBAFceramicactivatedcarbongas-waterratiomicrobialbiomassdehydrogenaseactivity2015-03-302015-05-121973—。E-mailyangbo@dhu.edu.cn*、、1。、2。carboxymeth-ylcelluloseCMC10、、、3-4。CMC5%~10%。CMCCMC5-6CMC。BAFCMCBAFCMCCMC、2。、。11.11。1BAFFig.1SchematicdiagramofBAF2150mm3100mm54.8L47.4L。、、、、0.15m8~30mm。21.75m3~5mm1#3~5mm2#。0.3、0.5、0.7、0.9、1.1、1.3、1.5、1.7、1.9、2.12.4m0.3、0.5、0.7、0.9、1.1、1.3、1.51.7m。1.2UV-7504PCYIS550PHS-25pHLeicaLDZX-30KBOhausCP214WGZ-1A。、、CMC、CTMAB、Triton-X100、。1.3CMC25~30mg·L-1200~250mg·L-1COD200~300mg·L-1KH2PO48mg·L-1MgCl260mg·L-1NaHCO312mg·L-1NH4Cl48mg·L-1Na2SO415mg·L-1pH7.0~8.0。1.41.4.11#2#、。0.071m3·m2·h-124hCOD、CMC20~30℃。CMC7pHPHS-25pHCOD8YIS550WGZ-1A。CMC、CMC9-11。、CMCCTMAB88949CMCCTMABCMCTriton-X100240nmCMC7。1.4.2TTC-12TFμg·g-11hTF。13nmol·g-1nmol·cm-31nmolE.coli108。22.10.071m3·m2·h-124h1∶1、2∶1、3∶1、4∶12COD、CMC。7d2~4。2CODFig.2Effectofair-waterratioonCODremoval3CMCFig.3Effectofair-waterratioonCMCremoval4Fig.4Effectofair-waterratioonturbidityremoval9894102、31#2#COD、CMC4∶11#2#COD72%65%CMC67%62%。。41#2#3∶184%86%4∶1。14-17。2COD、CMC1#COD、CMC2#。1#、2#。2.24∶11#2#。110.3、0.5、0.7、0.9、1.1、1.3、1.5、1.7、1.9、2.12.4m11112211COD、CMC1#2#21。1Table1Changesofpollutionalongthefiltercolumn1234567891011COD/mg·m-11#207146.5118.789.5107130.581.5374.54.01.52#156107132123.5106119.58628.55.53.53.0CMC/mg·m-11#9.21212.814.312.310.85.53.51.40.80.32#7.88.813.812.813.310.84.63.41.50.60.3/NTU·m-11#7.311.26.75.53.31.40.30.10.10.10.12#10.812.27.66.32.31.30.80.40.20.10.11COD1.5mCMC1.3m1.1m。COD21、1#2~42#2、1#5~6、7~112#5~112#3、4~5、6、7~11CMC1~63~51~61~2。、COD、CMC。CODCMC、、。、21。CMCCMC09949CMCCMCCMC12。819~11。1#、2#CODCMC。2.318-19。。0.3、0.5、0.7、0.9、1.1、1.3、1.51.7m1~85、6。5Fig.5Resultofphospholipidmethodalongtheway51#2#20.3m1.7m1#132nmol·g-122nmol·g-12#126nmol·g-120nmol·g-11.5m1#2#6TTC-Fig.6MicrobialactivityexpressedastheratioofTFTTC-dehydrogenasetomediamass1.5m。20-22。61#2#。22。2.4CMCCMC4∶11#2#CMC2。21.50m1000mLCMCCMC。72.21~70.5m、0.5~0.7m、0.7~0.9m、0.9~1.1m、1.1~1.3m、1.3~1.5m、1.5m。22CMC。1994102CMCTable2CMCadsorptioncapacityofdifferentheightfiltercolumnmg·m-112345671#13.798.559.548.206.963.252.192#12.2610.329.649.937.823.292.372CMC1.3mCMC。CMC3、。CMC=CMC-CMC-CMC/CMCCMCCMCCMCCMC2CMCCMCCMCCMC。1#CMC66.8%43.6%23.2%33.3%2#CMC62.4%46.1%16.3%37.6%CMC34.7%26.1%。1#2#CMC。CMCCMCCMC。PVA、CMC。311#2#COD、CMC4∶12COD72%65%CMC67%62%。2COD、CMC。3COD1.5mCMC1.3m1.1m。42、1.5m。5CMC1#2#CMCCMC34.7%26.1%。1..2000261033-37DAIRichengZHANGTongGUOQianetal.Summaryofprinting-dyeingwastewatertreatmenttechnology.Water&WastewaterEngineering2000261033-37inChinese2..2010LIURongrong.Studyontreatmentofhighstrengthdesizingwastewaterwithhybridanaerobicbaffledreactor.ShanghaiDoctorDissertationofDonghuaUniversity2010inChinese3..200634153574-3575NIUShengyangHAOFengge.Applicationprogressinthecarboxymethylcellulosesodium.JournalofAnhuiAgricul-turalSciences200634153574-3575inChinese4.CMC.200311430-3329949CMCXUZhenggang.ShallowofsodiumcarboxymethylcelluloseCMCapplicationsinthetextileindustryAgreenvitalityenvironmentalpaste.CelluloseEthersIndustry200311430-33inChinese5..2008319121-122PANLutingWULeiLUOHuafei.CharacteristicsofCMCproductionwastewaterandstudyontreatmenttechnol-ogy.EnvironmentalScience&Technology2008319121-122inChinese6.CMC.2014PEIYeqing.ThestudyofaerobicbiologicaltreatmentoflowconcentrationCMCwastewater.ShanghaiDoctorDis-sertationofDonghuaUniversity2014inChinese7.CTMAB.200928528-30WANGYanhuaYAN
本文标题:2种曝气生物滤池深度处理含CMC模拟退浆废水杨波
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