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96Vol．9No．620156ChineseJournalofEnvironmentalEngineeringJun．20151211111．1101682．110016SBＲ1SBＲ2。6h96%3．8mg/L。、。5%7%15mg/L0%3%15mg/L。。SBＲX703A1673-9108201506-2699-07EfficiencyofsalinewastewaterdenitrificationbybioaugmentationwithcompositemicrobialinoculumTangJing12QuShanshan1FuJinxiang1ZhaoKai1BaoJie11．SchoolofMunicipalandEnvironmentalEngineeringShenyangJianzhuUniversityShenyang110168China2．InstituteofAppliedEcologyChineseAcademyofScienceShenyang110016ChinaAbstractSalt-tolerantdenitrificationcompositemicrobialinoculumwereaddedintosequencingbatchre-actortodevelopabioaugmentationsystemSBＲ1takingasystemwithoutcompositemicrobialinoculumSBＲ2ascontrol．Thisstudycomparedandanalyzedtheirtransformationofnitrogenandchangesofdissolvedoxygenintypicaloperationcycleandtheperformanceundersalinityshock．Theresultsdemonstratedthatwhentheaerationtimewas6hoursthedenitrificationratemaintainedabove96%inthebioaugmentationsystemandthetotalnitrogenofeffluentwasaround3．8mg/L．Meanwhilenitrateandnitritealwayshadnoaccumulationthebioaugmentationsystemhadthecapacityofsimultaneousnitrificationandaerobicdenitrification．Whenfacingsa-linityshockof5%and7%thebioaugmentationsystemhadremarkableperformance．Afterquickrecoveryitsef-fluenttotalnitrogenwasbelow15mg/L．Whenshockedby0%salinitythecontrolsystemwasfailedandunabletorestore．Whilethebioaugmentationsystemrecoveredquicklybyinoculating3%ofsalt-tolerantdenitrificationcompositemicrobialinoculumandtotalnitrogenofeffluentdroppedtobelow15mg/Lagain．Thisresearchcouldprovidetechnicalsupportforconstructionandoperationofbioaugmentationsalinewastewaterdenitrificationsystem．KeywordsbioaugmentationsalinewastewatercompositemicrobialinoculumSBＲsalinityshock513083542014-K7-0172015－01－162015－02－051980—。E-mailfairy_ben@163．com．。2500m31。。20201000m3/2。NaCl1%～3%。3、4、5、6NaCl3%78100mg/L91000mg/L。。9。1011。12CASTCOD30mg/L90%20%95%65%30%～75%。Lefebvre13SBＲ12%CODTKN83%72%3020mg/L。Choi14A9PichiaguilliermondiiNaCl10%BOD590%A9。、。。15DO2SBＲ。11．1Halomonassp．F3F5、Ba-cillussp．X23Halomonassp．N391∶1∶10∶6015。1．2NaCl30g/LMgSO43．248g/LMgCl22．26g/LCaCl21．153g/LNaHCO30．198g/LKCl0．721g/LK2HPO4·3H2O1g/LNH4Cl0．357g/LNaNO30．607g/LCH3COONa5．13g/LFeSO4·7H2O0．05g/L2mL2mL16。1．34SBＲ1150mm120mm0．8L。30℃pHDOpHDO、。1Fig．1BiologicaldenitrificationtestequipmentSBＲ2、、、、、。SBＲ1h、1hSBＲ5、5．5、66．5h6h。1．4CODN-1--MLSSDOHQ40dpHOＲPS20pH。22．1SBＲSBＲ121．51mg/L、mC∶mN14．95、5．4%17120mg/L、C/N150%007263%2SBＲ5．4%MLSS2500mg/LOD6001．6SBＲ1SBＲ2。MLSS2512．25mg/L2507．88mg/L。SBＲDO18。DO。5、5．5、66．5h。2SBＲ1SBＲ2。5h5．5hSBＲ190%SBＲ220mg/L。6h9．50mg/L18．00mg/L92%85%。6．5hSBＲ1SBＲ295．50%～96．87%90．50%～91．20%3．80～5．50mg/L10．00～11．00mg/LA。56h96．8%91%2SBＲ1SBＲ2Fig．2DenitrificationcharacteristicsofSBＲ1andSBＲ2underdifferentaerationtimes3．80mg/L10．00mg/L。5．5h15mg/L。6h25～3515～20。6h6．5h15mg/L6h。2．2SBＲ1SBＲ2SBＲ1SBＲ2DO。2．12SBＲ1SBＲ2MLSS2502．15mg/L2497．78mg/L。3SBＲ1SBＲ24．62mg/L10．27mg/L96．22%91．58%SBＲ15mg/L。SBＲ1SBＲ2SBＲ1-DO16SBＲ1SBＲ2。SBＲ10．004mg/LSBＲ1323SBＲ1SBＲ2Fig．3VariationtrendofNH+4-NconcentrationandNO2-NconcentrationofSBＲ1andSBＲ210729SBＲ1。19-X315%、24h398．29%、99．07%96．48%。4SBＲ11mg/L3SBＲ1。SBＲ24．32mg/L1h6SBＲ21hSBＲ2。SBＲ1SBＲ2SBＲ1。4SBＲ1SBＲ2DOFig．4VariationtrendofNO3-NconcentrationandDOofSBＲ1andSBＲ2、DO。1hDO3．9mg/L3．6mg/L4CODDO。SBＲ1SBＲ245DO。CODDO。SBＲ11hDO。。2．3SBＲ1SBＲ2。42505．78mg/L2498．15mg/L5～1415～22SBＲ1SBＲ25%、7%0%3%。2．3．15%、7%SBＲ1SBＲ2120mg/L、C/N155．4%SBＲ。5、64SBＲ1SBＲ290%。SBＲ1SBＲ25%7%。Cl－68SBＲ1SBＲ260%～65%50%6Cl－80%。3%SBＲ1SBＲ2SBＲ1210mg/LSBＲ2TN17mg/LSBＲ1SBＲ2。2．3．20%SBＲ1SBＲ24SBＲ1SBＲ295．8%91．62%5．16mg/L10．27mg/L。5～140%3%2072655%SBＲ1SBＲ2Fig．5DenitrificationcharacteristicsofSBＲ1andSBＲ2under5%salinityshock67%SBＲ1SBＲ2Fig．6DenitrificationcharacteristicsofSBＲ1andSBＲ2under7%salinityshock7SBＲ1SBＲ2721．65%18．89%。43．09%35．95%69．92mg/L78．51mg/L。5%7%0%5%7%。MLSS15%7%MLSSSBＲ1MLSSSBＲ2。0%MLSS0%5%7%。。70%SBＲ1SBＲ2Fig．7DenitrificationcharacteristicsofSBＲ1andSBＲ2under0%salinityshock1Table1Changesofbiomassaftersalinityshockintwosystemsmg/L5%7%0%SBＲ1MLSS2380．492355．202129．91SBＲ2MLSS2248．342223．432000．523%SBＲ1SBＲ2745．59%38．66%。0%。22SBＲ13%394．9%6．24mg/LSBＲ22639．24%。3%。。316h96%307293．8mg/L。、。2。5%7%15mg/L0%3%。。3DNA。1．．201315139WangLi．Waterresourcesprotectionandutilizationintheconstructionofeconomysociety．ScienceandTechnologyandEnterprise201315139inChinese2．、．20122130-33ZhuQingpingShiXiaomingZhanHonglietal．Seawa-terutilizationinChinacurrentsituationissueanddevel-opmentstrategy．ChinaWaterＲesources20122130-33inChinese3．．2013731029-1034LinYulianZhangZhaoZhuangＲuixinetal．Treatmentofphenolinsalinesolutionsbyanoveltwo-phasepartitio-ningbioreactor．ChineseJournalofEnvironmentalEngi-neering2013731029-1034inChinese4．ASBBＲ．201329118-21ZhangYongshengZhouJianHanYietal．Efficiencyofanaerobicsequencingbatchbiofilmreactorfortreatmentofhypersalinemustardtuberwastewater．ChinaWater＆Wastewater201329118-21inChinese5．．201364184-94ＲenNanqiZhouXianjiaoGuoWanqianetal．Areviewontreatmentmethodsofdyewastewater．CIESCJournal201364184-94inChinese6PendashtehA．Ｒ．AbdullahL．C．Fakhru’l-ＲaziA．etal．Evaluationofmembranebioreactorforhypersalineoilywastewatertreatment．ProcessSafetyandEnviro