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712Vol.7No.12201312ChineseJournalofEnvironmentalEngineeringDec.2013ASBBR12111*111.4000452.453007、ASBBR。30℃7%NaCl1kgCOD/m3·d67d、、26、6、2418d79COD375mg/LCOD92.86%15kgCOD/m3·dCOD27000±2000mg/LCOD2200mg/L92.03%30、25、20、1510℃COD92.63%、84.07%、67.13%、54.61%44.19%。ASBBRX703A1673-9108201312-4697-06TreatmentofhypersalinemustardtuberwastewaterbyanaerobicsequencingbatchbiofilmreactorLiXiaopin12WeiShanshan1HanYi1ZhouJian1ChenLi1YangZhi11.KeyLaboratoryofThreeGorgesReservoirRegion’sEco-EnvironmentMinistryofEducationChongqingUniversityChongqing400045China2.HenanNormalUniversityXinxiang453007ChinaAbstractAnaerobicsequencingbatchbiofilmreactorwasusedtotreathypersalinemustardtuberwastewaterinfluencesoffillerkindsorganicloadingandtemperatureonthesystembuiltandthetreatmenteffi-ciencyofreactorwereinvestigated.Theresultsshowedthatundertheoperatingconditionsoftemperature30℃theconditionofsalinity7%calculatedasNaClorganicloading1kgCOD/m3·dthereactoraddedpoly-urethanefillerthrough67dayssuccessfullyconstructedthehypersalinemustardtuberwastewateranaerobictreat-mentsystemwhichshortened26days6days24daysand18daysthantheASBBRwithoutaddinganyfilleroraddingsemi-softcombinedfillersphericalcombinedfillerandpolystyrenefillerrespectively.Whenthestart-uptimeofreactoroperatedtothe79thdaytheeffluentCODwas375mg/Ltheremovalratewas92.86%.Whenthereactorincreasedorganicloadingto15kgCOD/m3·dtheinfluentCODwas27000±2000mg/LtheeffluentCODwas2200mg/Ltheremovalratewas92.03%.Temperaturehasremarkableeffectontheefficiencywhentemperatureswere30252015and10℃theremovalratesofCODwere92.63%84.07%67.13%54.61%and44.19%respectively.KeywordsanaerobichypersalineASBBRfillerorganicloadingtemperature2008ZX07315-0042012-08-222012-09-261984~。E-mailxiaopin0929@sina.com*E-mailzhoujiantt@126.com。1-6IlgiKarapinar782%NaClCOD1880mg/L9579mg/LCOD87%43%3%NaClCOD94%3%10%COD10%Riffat93.5%NaCl30℃3.0kgCOD/m3·dCOD80%6.0kgCOD/m3·d710ASBBRanoxicsequen-cingbatchbiofilmreactor1%NaCl30℃4kgCOD/m3·dCOD62%11UASB5%NaCl55℃78dCOD44%1238℃pH6.8~7.24.6%NaCl15.0kgCOD/m3·dCOD40%~43%。2%~5%NaCl。ASBBR、。11.11。ASBBR6L。1Fig.1Experimentalequipment1.27.0±0.2%NaClCOD5000~36000mg/LBOD2500~7500mg/LpH4.0±0.5。1.31.3.15。130g/L30±2℃7%NaCl1.0kgCOD/m3·d0.25h—11.5h—0.25hCOD。1Table1Typesoffillerinthereactor1—20.630.640.650.61.3.23。30±2℃、7%NaCl0.60.25h—11.5h—0.25h1.0、2.0、4.0、6.0、8.0、10.0、12.0、15.0、18.020.0kgCOD/m3·dCOD、pH、PCR-DGGE。1.3.3。7%NaCl0.60.25h—11.5h—0.25h15kgCOD/m3·d30、25、20、1510℃COD、pH、、VFA。22.12~8。2~8COD7.0%NaCl896412ASBBRCOD3~5dCOD1~593、73、91、6785dCOD63.82%、74.39%、73.07%、86.12%67.91%1~5103、81、97、7991dCOD1775、1163、1288、3751550mg/LCOD65.87%、77.86%、74.12%、92.86%69.08%。99647924SEM×5000Fig.9SEMphotographsofmicroorganismsinNo.2andNo.4reactor×5000COD。467dCOD92.86%《》GB8978-1996273dCOD77.86%193dCOD65%。、、1。92。2.210~12。10111.0、2.04.0kgCOD/m3·dCOD5000±200mg/LCOD375、538725mg/LCOD92.86%、89.61%86.39%1.0kgCOD/m3·d4.0kgCOD/m3·dCODpHCOD10000±1000mg/L、15000±1500mg/L、27000±2000mg/L、36000±100mg/L4.0kgCOD/m3·d6.0、8.0、15.020.0kgCOD/m3·dCOD963、2200、22003700mg/L2662.2、2085.9、1591.21565.7mg/LCOD91.21%、86.21%、92.03%89.52%10116.0kgCOD/m3·dCOD、、pH4.0kgCOD/m3·d6.0kgCOD/m3·d007412ASBBR。4.0kgCOD/m3·d20.0kgCOD/m3·d15.0kgCOD/m3·dCOD。7%NaCl12。15.0kgCOD/m3·d1591.2mg/L20.0kgCOD/m3·d1565.7mg/LCOD13。7%NaCl30±2℃ASBBR15kgCOD/m3·dCOD27000±2000mg/LCOD2200mg/LCOD92.03%。2.3132。13ASBBRCODFig.13EffectoftemperatureonCODremovalefficiencyinASBBR137%NaCl15kgCOD/m3·d30、25、20、1510℃COD92.63%、84.07%、67.13%、54.61%44.19%COD597.92、535.50、418.25、345.33275.33mg/L·hCODCOD。1410~15℃1~22、pHVFATable2EffectsoftemperatureonALKpHandVFA℃mg/LpHVFAmg/L3015258.02952514057.932732011857.226321510456.97774109756.51103810~15℃1.5~1.9。2pHVFA95mg/L1038mg/LVFA15VFApH。31。30℃7%NaCl1kgCOD/m3·d67d、、26、6、2418d79dCOD375mg/L92.86%《》GB8978-1996。2ASBBR0.630±2℃7%NaCl15kgCOD/m3·dCOD27000±2000mg/LCOD2200mg/LCOD92.03%。3ASBBR。7%NaCl15kgCOD/m3·d30、25、20、1510℃COD92.63%、84.07%、67.13%、54.61%44.19%。107471./.2011271316-18WangHuirongWeiYanfeiMeiRongwu.Studyontreat-mentofhypersalinedyewastewaterwithcombinedprocessofphotosyntheticbacteriaandactivatedsludge.ChinaWa-ter&Wastewater2011271316-18inChinese2..201124145-46ZhaoYongHanBingquanYuMin.Studyonpharmaceuti-calhypersalinewastewatertreatmentbytheactivecarrierofenzyme.PollutionControlTechnology201124145-46inChinese3.ASBBR.2010261510-13ChaiHongxiangHuXuebinHeQiangetal.Influenceofbetaineontreatmentofhigh-saltmustardtuberwastewaterbyASBBR.ChinaWater&Wastewater2010261510-13inChinese4..201111341-45ZhouJianDuGuojunZhangYongshengetal.Onthestart-upofhybridanaerobicreactorformustardtubersew-agetreatment.JournalofSafetyandEnvironment201111341-45inChinese5..2007204102-105GaoHuanJiangJinyuanHuXiangetal.Studyonther-mophilicanaerobicbiodegradationofreactivedye.Re-searchofEnvironmentalSciences2007204102-1056..201137690-93ChenYaoZhouJianGanChunjuanetal.Rapidstart-upandpollutionremovalcharacteristicofhypersalineanaero-bicsystem.TechnologyofWaterTreatment201137690-93inChinese7IlgiKarapinarKapdanBurcuErten.AnaerobictreatmentofsalinewastewaterbyHalanaerobiumlacusrosei.ProcessBi-ochemistry2
本文标题:ASBBR处理超高盐榨菜腌制废水李晓品
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