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42120142JournalofFuzhouUniversityNaturalScienceEditionVol.42No.1Feb.2014.fzu.edu.cnDOI10.7631/issn.1000-2243.2014.01.01611000-2243201401-0161-0611211.3501162.350013SBR35±0.1℃、pH8.0~8.4、FA19~35mg·L-124、36、48、60L·h-1.pH“”DO“”95%100%36L·h-136L·h-1.X703.1AEffectofaerationflowontheperformanceofpartialnitrificationinasequencingbatchreactorWUHuang-zhou1QIULing-feng1CHENYi-ming2SUMei-ping11.CollegeofEnvironmentandResourcesFuzhouUniversityFuzhouFujian350116China2.FujianProvincialAcademyofEnvironmentalScienceFuzhouFujian350013ChinaAbstractThepartialnitrificationreactorwassuccessfullystartedupwithintwoweeksatahightemper-ature35±0.1℃initialpH8.0~8.4andfreeammonia19~35mg·L-1.Theeffectofaera-tionflow24364860L·h-1ontheperformanceofpartialnitrificationwasinvestigated.Resultsshowedthereal-timecontrolstrategybasedonpHDOdissolvedoxygenandORPoxidation-re-ductionpotentialwasaneffectivemethodformonitoringtheendpointofpartialnitrificationtoterminatetheaeration.Nitriteaccumulationshowedtobestableunderdifferentaerationflowswiththeeffluentni-triteaccumulationratioallupto95%and100%ofammoniaremoval.Theammonium-oxidizingreac-tioninSBRaccordedwithzero-orderreactionkineticsequationandthereactionrateconstantin-creasedwiththeincreaseofaerationflowindicatingthattheaerationflowwasacriticalfactorinachie-vingpartialnitrification.Besideswithincreasingaerationflowthespecificrateconstantofnitrite-producingperaerationamountshowedanearlierraisedandlaterdecreasedstate.Theresultsindicatedthattheaerationflowof36L·h-1representedanimportantreductioninoperationalcosts.Keywordspartialnitrificationaerationfloweconomicevaluationreal-timemonitoring01.2①25%②63%30%~40%③33%~35%④3.nitrite-oxidizingbacteriaNOBammonia-oxidizingbacteriaAOB2013-08-131971-E-mailfzuniqlf@sina.comZZLX120242.fzu.edu.cnNOB.pH、dissolvedoxygenDO、、freeammoniaFA4.DO.Laanbroek5AOB0.2~0.4mg·L-1NOB1.2~1.5mg·L-1DO.628L·h-1DO0.3mg·L-180%5mg·L-1·h-1.715.7L·h-17.96mg·L-1·h-1...DO、oxidation-reductionpotentialORP、pH.11.11SBRFig.1SchematicdiagramoftheSBRreactorsequencingbatchreactorSBR1400mm150mm4L.35±0.1℃.3.MLVSS1300mg·L-1.1.21∶2.NH42SO4NaHCO3300mg·L-1NaHCO31800mg·L-1AOBpHHCO-3NH+42∶1.0.3h、、0.5h、0.5h.1.38.N-1--MLVSSDOWTWoxi330pHORPWTWpH3310.22.1AOBNOBAOBNOBNOB.9-1020℃AOBNOB20℃AOBNOBNOB.1128℃.pHAOB7.0~8.511NOB6.0~7.5.FAAOBNOB·261·1.fzu.edu.cn2ESEMFig.2TheESEMimageofthestablepartialnitrificationsludgeNOBAOB.FANOB0.1~10mg·L-1AOB10~150mg·L-1FANOB12-13.35±0.1℃pH8.0~8.4FA19~35mg·L-1AOBNOB.36L·h-1nitriteaccumulationrateNARNAR=ρNO-2-NρNO-x-N95%.2.2214.ESEM2.2.324、36、48、60L·h-13.3SBRFig.3TheoperationofSBRunderdifferentconditions2.3.14.100%NAR95%.AOBNOB..2.3.241.411524L·h-136L·h-10.5136L·h-148L·h-10.1248L··361·42.fzu.edu.cnh-160L·h-10.15.a60L·h-1b48L·h-1c36L·h-1d24L·h-14SBRFig.4CyclicstudyshowingnitrogentransformationprocessinSBRunderdifferentaerationflows1Tab.1RegressionequationofnitriteproductionL·h-1k/mg·L-1·h-1/g·g-1·d-1/g·g-1·L-124y=25.21x+75.20.990C=C0+25.21t25.210.4651.05036y=38.11x+83.50.986C=C0+38.11t38.110.7041.05948y=42.55x+80.70.987C=C0+42.55t42.550.7860.886460y=48.75x+83.80.994C=C0+48.75t48.750.0380.8132.3.31617..pH、DO、ORP6.45pHCO2pHDOORP.pHCO2pH“”DODO“”ORPDO18.pH“”DO“”.·461·1.fzu.edu.cna60L·h-1b48L·h-1c36L·h-1d24L·h-15SBRDO、ORPpHFig.5CyclicstudyshowingvariationofDOORPandpHinSBRunderdifferentaerationflows2.3.4136L·h-11.059g·g-1·L-124L·h-11.050g·g-1·L-136L·h-1.4860L·h-10.8860.813g·g-1·L-1.36L·h-1.3135±0.1℃pH8.0~8.4FA19~35mg·L-1NAR95%.2.3pH、DOORPpH“”DO“”.4.36L/h.1DostaJGaliATBMaceSetal.Operationandmodeldescriptionofasequencingbatchreactortreatingrejectwaterforbio-logicalnitrogenremovalvianitriteJ.BioresourTechnol200798112065-2075.2VerstraeteWPhilipsS.Nitrification-denitrificationprocessesandtechnologiesinnewcontextsJ.EnvironmentalPollution19981028717-726.·561·42.fzu.edu.cn3StrousMHeijnenJJKuenenJGetal.Thesequencingbatchreactorasapowerfultoolforthestudyofslowlygrowinganae-robicammonium-oxidizingmicroorganismsJ.AppliedMicrobiologyandBiotechnology1998505589-596.4.J.20115763-67.5LaanbroekHJGerardsS.CompetitionforlimitingamountsofoxygenbetweenNitrosomanaseuropaeaandNitrobacteriawino-gradskyigrowninmixedcontinuousculturesJ.ArchMicrobiology199315945.6.J.200622930-33.7.SBBRJ.20123292112-2118.8.M.4.2002.9.SBR-J.2003461-4.10.J.200531438-42.11.J.200526163-67.12AnthonisenACLoehrRCParkasamTBS.InhibitionofnitrificationbyammoniaandnitrousacidJ.JWatPollutControlFed1976485835-852.13FuxCBoehlerMHuberPetal.Biologicaltreatmentofammonium-richwastewaterbypartialnitritationandsubsequentanaerobicammoniumoxidationanammoxinapilotplantJ.JournalofBiotechnology2002993295-306.14.SBRJ.2009253526-530.15.J.2009301218-221.16.SBRJ.2004483-88.17.SBR-J.2003461-4.18.J.2011311153-56.(责任编辑:杨青)·661·
本文标题:不同曝气量对短程硝化特性的影响吴煌州
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