SBR陈 永 王长平 张宗农 介绍了间歇式活性污泥法(SBR法)处理固态发酵白酒废水的工程设计、调试及运行情况,总结了该工程的设计经验、存在的问题与建议。认为采用SBR法处理固态发酵白酒类废水具有工艺合理、运行稳定可靠、处理效率高、投资少、占地面积小等优点。 SBR法 固态发酵 白酒废水 工程设计 工程调试0 SBR(SequencingBatchReactor),,SBR。、、,。SBR,、,。SBR,SBR:、、、、、。、、、、、、、SBR。、,,,2t。、、、、、。SBR。,SBR、、,SBR,。。1 1.1 ,,。1。1,,(COD60000mg/L)COD,。,1。《》(GB8978-96)。,1000m3/d。1 COD/mg/LBOD/mg/LSS/mg/LpH141~551841~149994~16194.4~7.8750~1200400~650200~4506.0~8.512006504507.0150601501.2 1,2。,,。1 1.3 (1)。、。36 Vol.28 No.10 2002DOI:10.13789/j.cnki.wwe1964.2002.10.0382 3mm,ABS。(2)。。18.6m3,0.45h。,,。(3)。。157.5m3,3.78h。SBR。SBR。(4)SBR。2,500m3,0.5。0.15kgBOD/(kgMLSS·d),MLSS4000mg/L,SVI100~120mL/g。12h,,6h,8h(2h),1h,1h。,。(5)。SBR1,2.5m,,,,;SBR,。(6)。,PAM。1.4 2。2 20015,40d,。,SBRSBR,。2 /m3/d1000/100//m31000/4//m30.6/kW59/kW/m30.035/kW·h/m30.85/kW35.4/m2502/m2/m30.5,,。SBR300kg。4,10d,3。、SBR4。,,,SS,SS。3 /h/h2451/41841/31231/21021/2 ,560~730m3/d,COD,SS,SBR。,SBR18h,9h,,4h,10h,2h,1h,1h。,,5。3 3.1 Vol.28 No.10 200237 4 /℃19.720.119.820.3pH7.487.077.037.138.127.987.917.83COD/mg/L1954162314591767/mg/L138170328669/%29.356.780.496.1SS/mg/L63792812471023/mg/L40438523679/%36.658.581.192.3MLSS/g/L0.7641.3221.9853.241SV/%8141829,,,,,,,,5 COD/mg/LBOD/mg/LSS/mg/L/mg/LpH418~23611717338~796609895~195111861.4~15.85.14.8~7.76.346.6~54.149.110.1~11.110.6155~86690.63~0.730.667.6~8.27.9/%97.198.394.187.13.1.1 ,SBR。,SBR。,、,SBR。,,,,,。3.1.2 ,。,,58%,,。,,SBR。,,6.4,1.5,4.9。,,。,19kW·h,10.5/d(0.55/(kW·h))。,、、,。3.1.3 SBRSBR。,,。,4,13℃,。,SBR。3.2 3.2.1 ,3mm。,3mm、,,,。,SBR,SBR。,0.3mm,SBR。3.2.2 ,SBR,,,。,SBR1m。,,。,。3.2.3 38 Vol.28 No.10 2002 ,。,SBR1h,、。,0.38mm/s,2h。,2h,。,,1h。,。0.5~1h,1.5~2h,。,。4 (1)SBR,,,,;(2)SBR,、;(3),0.3mm、;(4)SBR,。:100044 E-mail:yong_chbj@sohu.com5180214002100084 :2002-3-8 AF-SBR张 敏 包 南 刘和义 介绍了应用AF-SBR工艺处理植物油废水的工程实例。工艺以隔油+气浮为预处理部分,有效地去除了油和悬浮物,为后续厌氧处理创造了一个良好的运行环境;AF-SBR生化处理部分能稳定高效地去除COD,BOD。一年多的运行情况表明,经处理后各项主要水质指标均低于国家二级排放标准。 植物油废水 厌氧滤池(AF) SBR 1100t/d,500~600m3/d。、、、,,[1]。,--AF-SBR,COD97%99%,。1 、。,,,,;、、,,、,()、、、、,[2]。,1;。,,。、1。1,,、pH。 Vol.28 No.10 200239 WATER&WASTEWATERENGINEERINGVol.28No.10October2002ABSTRACTSBiowinProcessAppliedinGrossWTP,NorwayHuFengpingetal(1………………………………………………………)Abstract:Biowin,aCanadadevelopedprocessforwastewatertreatment,hasbeenappliedbyGrossWTPinGrim-stad,Norwayforyears.Theoperatingdataof1996to1997areshowntodeliberatetheperformanceofthisfacility.Atthetowtempreture,BiouinprocesscanremoveN,PeffectivelyincaseoflongSRTandhighMLSS.WaterResourcesUtilizationinSydneyOlympicsWangKaijunetal(4………………………………………………………)Abstract:ThecomprehensivewaterresourcesutilizationandtheecologicalplanninginSydneyOlympicsarepre-sentedbrieflyinthispaper.ForthesetheOlympicvillageWTPandcomprehensiverainwatergathering,treatmentsys-temsandutilizationfacilitiesareincluded.Alsothebiologicallandscapeplanisdiscussedwiththerainwatertreatment.OzoneConcentrationMeasurementandMonitoringinWaterworksZhouYunetal(9………………………………………)Abstract:Themethodsofozoneconcentrationmeasurementandmonitoringinwaterworksarepresentedgenerally.Thesamplingpointsofozonedetectionshallbesetupattheoutletofozonegenerator,theinletandoutletoftailgasandthewateroutletofcontacttank.Therearealotofwaystomeasuretheozoneconcentration,foronlinemeasurementtheUV-spectrometerandmembranegalvano-probearepreferableforozonegasandozonedissolvedinwaterrespectively.Furthermoreaportableindigoticinstrumentwillbenecessaryforperiodiccalibrationofonlinemeters.RemovalandDistributionofNandPataSimulatedArtificialWetlandSystemTreatingStormyRunoffXuLihuaetal(12…………………………………………………………………………………………………………)Abstract:TheNandPremovalsfromwastewateranddistributionsinfourwetlandsystemswithdifferentpackagesandwithorwithoutplantation,includingtheaccumulationinartificialpackagemedia,thetimevariedmicrobialfixingandtheadsorptionineachsectionofplantsofNandPwereinvestigated.Theresultsshowthatthemicroorganism,plantationandmediaarecompetitivefornutrients;theplantsshallusethemedia-adsorbedNandmicrobialdegradedPpreferentially.AlsoitisobservedthatchangingofenvironmentalconditionsshallinfluencetheNandPdistributionintheplantbody.PracticeofWaterPollutionControlPrograminZhouzhuangSongLepingetal(19…………………………………………)Abstract:Thelandscapeandarchitectureprotectionsaretakenintoconsiderationinformulationofriverbodycon-servationandwaterenvironmentcontrolplaninanoldtownshipareaZhouzhuanginJiangsuProvince.Wastewatercol-lectedfromfivetopographicalsubzonesbygravitationalpipelinecasuallywithlocalpumpinghouseswillbeconductedintoaconcentratedwastewatertreatmentplantconstructedattheendofthepipeline.Thesewagemainsshallbelaidundertheriverbedsandthecheckingwellsshallbeinstalledalongthebothbanksoftheriveralternately.Thewastewatertreatmentplantshallbelocatedattheendofthepipelinenetwork.ComparisononBio-ContactOxidationTankandCeramicBio-FilterProcessesforMicro-PollutedRawWaterPre-TreatmentJiMinetal(26……………………………………………………………………………………………)Abstract:Bothbio-contactoxidationtankandceramicbio-filterarealwaysadoptedforbio-pretreatmentofmicro-pollutedrawwater.Theoperatingperformancesofthesetwokindsofreactorswerere