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35520119JournalofNanjingForestryUniversityNaturalScienceEditionVol.35No.5Sept.2011http//.nldxb.comdoi10.3969/j.issn.1000-2006.2011.05.0192010-08-212011-06-09PAPD1982—。E-mailm2910@139.com。.J.201135587-90.121221.2100372.210008BAF。33.88%3.141.7m3/m2·h、90min、1∶1~1.2∶1、21.6~32.7℃20d3.14。CODMn、NH3-N14.66%、85.81%53.00%。TU991.2A1000-2006201105-0087-04StudyontreatmentofslightlypollutedrawwaterwithbiologicalaeratedfilterfilledwithattapulgiteLINZizeng1WANGFeng2WANGZheng1XIATing2SHENWei21.CollegeofCivilEngineeringNanjingForestryUniversityNanjing210037China2.NanjingMunicipalDesignandResearchInstituteCo.Ltd.Nanjing210008ChinaAbstractThemicro-pollutedrawwaterwastreatedbybidoyicaloeratedfilterBAFusingmediawithrepresentativefractalcharacteristicsinordertoinvestigatetheattapulgitemediastartupperformanceandthetreatmenteffectoffilter.Duringfilterstartupphasethebiofilmculturingprocessfinishedinabout20daysundertheconditionthathydraulicloadingwascontrolledat1.7m3/m2·hhydraulicretentiontime90mingas-waterratio1∶1—1.2∶1andwatertem-pertature21.6—32.7℃.Theresultsshowedthattheroughsurfaceofattapulgitemediawhosefractaldimensionwas3.14anditimprovedthemicrobialbiofilmgrowth.DuringfilteroperationphasetheremovalrateofCODMnNH3-Nturbiditycouldreach14.66%85.81%and53.00%respectivelywhichprovedasatisfieddegradationeffect.Keywordsbiologicalaeratedfiltermicro-pollutedrawwaterfractaltheoryattapulgitemediaBiologicalAeratedFilterBAFBiologicalContactOxidationBCO1-7。BAF、8。9-10。35。11.14.5m0.25m2Q1m3/h1。2~5mm。BAF。、。1Fig.1Processflowofmicro-pollutedrawwatertreatment1.216.2~47.9mg/L30.35mg/LNH3-N0.23~4.03mg/L1.54mg/LCOD5.22~9.26mg/L7.05mg/L。CODNH3-N《》GB3838—2002ⅡⅣ。NH3-NN-1--CODMn。1.31.7m3/m2·h90min1∶1~1.2∶121.6~32.7℃。-4~5L/m2·s2~3L/m2·s。22.1micromeriticsAutoPoreⅣ95102。233.88%40~553nm120nm。11-130.5~25μm9lnNr-lnr3。33.140.9889。2Fig.2Distributionofporesizeofattapulgitefiltermaterial8853Fig.3Fractaldimensioncalculationofattapulgitefiltermaterial2.2NH3-N14BAFNH3-N4a。4aNH3-N90%。50%1140%NH3-N。、NH3-N。2085%~95%NH3-N75%NH3-N。4NH3-N、CODMnFig.4RemovalefficiencyofNH3-NCODMnandturbidityofthemicropollutedrawwater。3.1420d3.14。2.3CODMnCODMn5.0~7.0mg/L4.1~6.1mg/LCODMn9.23%~22.37%14.66%4c。4cBAF。BAFCO2。CODMn15。2.4NH3-NNH3-N9835。NH3-N0.83~4.03mg/L2.69mg/L0.38mg/L。NH3-N85.81%100%NH3-N4b。NH3-N。5.0~7.0mg/LNH3-N。2.5。、、、、。4d。4d23~43NTU31NTU9.7~24.6NTU14NTU53.00%。12。Zetaζ。BAF。3120d3.14。21.7m3/m2·h、90min、1∶1~1.2∶1、21.6~32.7℃BAFCODMn、NH3-N14.66%、85.81%53.00%。3NH3-N、。1.J.200931119-12.2.J.2007231139-41.3.J.200432663-66.4.J.2006265785-790.5.J.2009251865-70.6.J.2003318977-981.7.BiostyrJ.200629184-86.8HarendranathCSAnujaKSinghAetal.ImmobilizationinfixedfilmreactorsanultrastructuralapproachJ.WaterScienceandTechnology19963387-15.9.J.1999151210-13.10.D.2002.11.M.1990.12.、M.1995.13.M.1995.14.J.201134259-61.15.J.200926165-68.09
本文标题:凹凸棒滤料曝气生物滤池对微污染原水的处理研究林子增
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