邓福生1,杨友强2,廖 利3(1.深圳市市政环卫综合处理厂,深圳518001;2.深圳市朗刊环境技术有限公司,深圳518001;3.华中科技大学,武汉430074) :,,—UASB-AF—SBR。,,GB8978-1996。:;UASB-AF;SBR:X703.1 :A :1671-1556(2005)03-0035-04 ①BriefIntroductiononUltra-highConcentrationOrganicWastewaterTreatmentProjectofShenzhenSanitaryTreatmentPlantDENGFu-sheng1,YANGYou-qiang2,LIAOLi3(1.ShenzhenEnvironmentalSanitationandMunicipalManagementFactory,Shenzhen518001China;2.ShenzhenLeokingEnvironmentalTechnologyCo.Ltd,Shenzhen518001China;3.HuazhongUniversityofScienceandTechnology,Wuhan430074,China))Abstract:Accordingtoresultsofpilotscalestudiesandpracticalsituationsofindustrialwastewater,ultra-highconcentrationorganicwastewaterofShenzhenSanitaryTreatmentPlantwastreatedwithdegrease-de-posit—UASB-AF—SBRprocess.ItwasdemonstratedthatalltheindexesofoutflowdischargecouldmeetthenationaldischargeregulationsetforClass3(BG8978-1996).Keywords:ultra-highconcentrationorganicwastewater;UASB-AFcompoundanaerobicreactor;SBR0 /。,。,1.0MPa,145~150°C,16~24h,、。,,、、。1 1.1 :(1);(2)、、,—,,1/5;(3)。1.2 1。12 32005 9 安全与环境工程SafetyandEnvironmentalEngineering Vol.12 No.3Sep. 2005①:2005-03-11 :(1980—),,,。1 Table1 CharacteristicsofwastewaterCODCrBOD5NH3-NSS/(mgL-1)80000~11000054000~770005000~7000440~9104000~60001.3 ,,《》(BG8978-1996)。2 2.1 ,,—;,AF、UASB、EGSB,;UASB;UASB,AF;,SBR。1。1 Fig.1 Flowchartofpilottest2.2 [1]。3 ,、、、,,:(1),200m2,,;,,,,,,,。(2),,。(3),,,,,,、、,。(4),,,16000mg/L5000mg/L。,:(1),;,。(2),,AF、UASB、EGSB,;,16000mg/L5000mg/L,3000mg/L,。。(3),,UASBAFUASB-AF,UASB-AFUASBAF,,。36 安全与环境工程 第12卷(4),UASB-AF,,()。2。2 Fig.2 Flowchartofwastewatertreatmentsystem4 UASB-AFUASB-AFUASB,,10kgVSS/m3。4.1 UASB-AFUASB-AF4,:(1);(2)UASB-AF;(3)UASB-AF,UASB-AF0.65~1m/h[2,3],UASB-AF,。(4),UASB-AF,。(5)UASB-AFpH、COD、,,UASB-AF[4,5]。(6)UASB-AF,SBR。(7),SBR:UASB-AF,SBR,UASB-AF,SBR,,UASB-AFSBR,,1h,SBR。4.2 UASB-AFUASB-AF,UASB-AFpH、COD、,[6,7]。UASB-AF,,UASB-AF15~25∶1,,UASB-AF15∶1,0.65m/h;,25∶1,1m/h;UASB-AF37第3期 邓福生等:超高浓度有机废水处理工程简介 ,,,,,,20~25∶1[8]。5 ,2。,2 (mg/L) Table2 Characteristicsofwastewaterinandoutateachstage(mg/L) CODCrBOD5SSUASB-AFSBR95240641205190907806216027409078062160274031301685360313016853604502633 ,CODCr99%,98%。200310。1,、。:[1] .[J].,2003,(9):35-38.[2] .(UASB)[J].,1986,12(3):177-182.[3] .、[J].,1990,2:37-43.[4] ,.UASB[J].,1988:9(5):11-15.[5] ,,..[J],1993,13(5):334.[6] VanderMeer,etal.Anaerobicdigestionprocessinindustrialwastewatertreatment[J].BiotechnologyandBioengineering,1983,25(1):2531.[7] Pretorius,W.A.Anaerobicdigestionprocess[J].WaterRe-search.1969,3:345-358.[8] ,,.[J]。,1995:15(2):170.(34)2 Table2 TreatmentstatusofodorsinHangzhouBinjiangSewagePlant/(mgm-3)/%0.2060.038681.36.7050.84288.10.0320.00584.4()38002099.5 :。,81.3%,88.1%,84.4%,99.5%。GB14554-1993。4 ,,、、、80%。,,,,,。、、,。:[1].[J].,1999,21(2):27-29.[2],,,.[J].,2002,18(2):41-42.[3].[M].:,1992.[4]Wang,R.,B.Zhang,S.Bing,etal.ApparentenergyyieldofahighefficiencypulsegeneratorwithrespecttoSO,andNOxre-moval[J].Electrostatics,1995,34:335-336.[5],,,.[J].,1999,19(3):277-280.[6]Masuda,S.Pulsecoronainducedplasmachemical-process:ahorizonofnewplasmachemicaltechnologies[J].Pure&Appl.Chem.,1988,60(5):727-731.38 安全与环境工程 第12卷