MBR/PAC朱 亮1, 朱凤春1, 许旭昌2, 徐伟欣1, 王占生3, 顾军农4(1.河海大学环境科学与工程学院,江苏南京210024;2.南通规划设计有限公司,江苏南通226000;3.清华大学环境科学与工程系,北京100084;4.北京自来水集团,北京100038) : 在MBR中试的基础上,向MBR反应器中投加40g/L粉末活性炭(PAC)构成MBR/PAC组合工艺并处理污水厂尾水。试验结果表明:MBR/PAC系统的出水BOD5≤4mg/L、COD≤18mg/L、氨氮≤0.3mg/L、浊度≤0.2NTU,处理效果优于MBR系统。PAC能吸附并降解易引起膜污染的有机物,有效降低了膜污染,减缓了过膜压力的增长趋势,保护了膜组件,并且运行效果良好。通过气洗和反冲洗能很好地维持膜的透过性能,离线清洗可基本恢复膜的透过性能。 : 膜生物反应器(MBR); 粉末活性炭(PAC); 污水厂尾水:X703 :C :1000-4602(2009)05-0059-04CombinedProcessofMBRandPACforTreatmentofTailwaterfromWWTPZHULiang1, ZHUFeng-chun1, XUXu-chang2, XUWei-xin1, WANGZhan-sheng3, GUJun-nong4(1.CollegeofEnvironmentalScienceandEngineering,HohaiUniversity,Nanjing210024,China;2.NantongUrbanPlanningandDesignCo.Ltd.,Nantong226000,China;3.DepartmentofEnvironmentalScienceandEngineering,TsinghuaUniversity,Beijing100084,China;4.BeijingWaterworksGroup,Beijing100038,China) Abstract: OnthebasisofMBRpilottest,acombinedprocessofMBRandPAC(40g/L)wascomposedtotreattailwaterfromWWTP.TheresultsshowthattheBOD5,COD,NH+4-Nandturbidityintheeffluentofthecombinedprocessareequaltoorlessthan4mg/L,18mg/L,0.3mg/Land0.2NTUrespectively.ItstreatmentefficiencyisbetterthanthatinMBRalone.PACcandegradeorganiccompoundswhicheasilyresultinmembranefouling,thusreducingmembranefouling,alleviatingthein-creasingtrendoftransmembranepressureandprotectingmembranemodule.Thepracticaloperationshowsagoodeffect.Airwashandbackwashcanmaintainhighpermeabilityofmembrane.Itspermeabilitycanberecoveredmainlybyoff-linewash. Keywords: membranebioreactor(MBR); powderedactivatedcarbon(PAC); tailwaterfromWWTP (MBR)、,、、、、、[1~5]。,、,。、[6~10]。·59·第25卷 第5期2009年3月 中国给水排水CHINAWATERWASTEWATER Vol.25No.5Mar.2009,MBR,MBR(PAC),MBR/PAC,MBR、MBR/PAC,MBR/PAC。1 试验材料及方法1.1 1。1 Fig.1 Flowchartoftreatmentprocess,80cm×120cm×160cm,1.2m3。,、,。,,,。FP-A1(PVDF),520mm×1010mm,0.22μm,12.5m2,0.125m3/(h·),7。1.2 ,SBR,,。1。1 Tab.1 QualityofinfluentCOD/(mg·L-1)BOD5/(mg·L-1)/(mg·L-1)TN/(mg·L-1)TP/(mg·L-1)/℃/NTU30~34228~1004.3~9248.6~1464.7~1113~21.66.5~315924619.682.37.0718.6341.3 300L/h;,10min、2min;HRT4h;30∶1。MBR、MBR/PAC。,MBRMLSS4500mg/L,DO1.8mg/L。MBR/PACPAC40g/L,MLSS7800mg/L、9000~13000mg/L;pH6.7~8.0,DO1~2.5mg/L。1.4 40g/LPAC,,。,,,。,,,,。1.5 COD:;:;:;:—;MLSS:;:HACH;pH:;DO:HACH。2 结果与讨论2.1 2.1.1 BOD5、CODMBR、MBR/PACBOD5、COD2、3。2 MBRMBR/PACBOD5Fig.2 BOD5removaleffectbyMBRandMBR/PAC·60·第25卷 第5期 中国给水排水 MBRMBR/PACCODFig.3 CODremovaleffectbyMBRandMBR/PAC2,MBRBOD57mg/L、MBR/PACBOD54mg/L。,MBR/PACBOD5PAC,;,,,BOD5。3,MBRCOD≤30mg/L、MBR/PACCOD≤18mg/L。,MBR/PACCODPAC;,,PAC,,,[11],(COD80%)。2.1.2 、MBR、MBR/PAC4。4 MBRMBR/PACFig.4 NH3-NremovaleffectofMBRandMBR/PAC4,MBR3mg/L、MBR/PAC0.3mg/L。,,PAC,;,PAC,MBR/PACMBR,NH+4-N、。,MBR/PAC30%,MBR(15%)。MBR/PAC,,PAC,,,,,;PAC,,。MBR/PAC、,,。30,NO-3-N。2.1.3 ,MBR0.4NTU、MBR/PAC0.2NTU。,;,PACMBR/PAC。2.2 2.2.1 MBR、MBR/PAC5。5 MBRMBR/PACFig.5 VariationoftransmembranepressureofMBRandMBR/PAC5,,MBR/PAC·61·朱 亮,等:MBR/PAC组合工艺处理污水厂尾水的中试研究第25卷 第5期MBR,,MBR/PAC,17d,MBR/PACMBR。,PAC,PACMLSS,,,MBR/PACMBR;,PAC,、,,。2.2.2 MBR/PACMBR/PAC、,。,2min,8h。(0.06MPa),,,。。,,,,。,,0.5%NaClO1%NaOH,。,,,;,,,;,,,。3 结论① MBR,MBR/PAC:BOD5≤4mg/L、COD≤18mg/L、≤0.3mg/L、≤0.2NTU。② PAC(BAC),,,,。,。:[1] ChaizeS,HuyardA.Membranebioreactorondomesticwastewatertreatmentsludgeproductionandmodelingap-proach[J].WaterSciTechnol,1991,23(7-9):1591-1600.[2] GǜenderB,KrauthK.Replacementofsecondaryclarifi-cationbymembraneseparation-resultswithtubular,plateandhollowfibermodules[J].WaterSciTechnol,1999,40(4-5):311-320.[3] ,,,.MBRUF[J].,2006,22(15):80-82.[4] ,,,.MBRMBR[J].,2006,22(3):28-31.[5] ,,.MBR[J].,2003,19(2):43-45.[6] ,,,.—[J].,2005,27(7):481-484.[7] ,,,.—[J].,2004,20(7):54-55.[8] ,,,.[J].,2006,26(3):271-274.[9] ,.[J].,2001,17(2):1-4.[10] ,.[J].,2001,17(3):12-15.[11] ,,,.[J].,2005,31(10):76-78.:15952008606E-mail:zhufengchun0314@hhu.edu.cn:2008-10-11·62·第25卷 第5期 中国给水排水