A2NSBR工艺短程反硝化除磷脱氮研究李微

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A2/N-SBR*111211.1101682.110000-A2/N-SBR。A2/N-SBRNO-2-NTP0.53mg/L1.14mg/LTP88.8%COD107.21mg/L76.81mg/LPHB150.88mg/LTPTP2.6TPNO-2-N94%96%。A2/N-SBRPHB。DOI10.13205/j.hjgc.201608014SHORTCUTDENITRIFYINGPHOSPHORUSREMOVALINA2/N-SBRPROCESSLIWei1LIUJing1MENGHai-ting1ZHULei2FUJin-xiang11.MunicipalandEnvironmentalEngineeringShenyangJianzhuUniversityShenyang110168China2.ShenyangInstituteofEnvironmentalScienceShenyang110000ChinaAbstractAlab-scaleA2/N-SBRprocesswasoperatedtoinvestigatetheperformanceofbiologicalnutrientsremovalanddenitrifyingphosphorusremovaltheoperationeffectoftypicalcycleandmetabolicmechanismofdenitrifyingphosphorusremovalbacteriafromthedomesticsewage.TheresultsindicatedthatsimultaneousanoxicphosphateuptakeandbiologicaldenitrificationwithgoodperformancecouldbeobtainedintheA2/N-SBRprocessoperatedinlong-termstableoperation.EffluentconcentrationofNO-2-NandTPwere0.53mg/Land1.14mg/LinthetypicalcycleandtheTPremovalefficiencywas88%.TheconcentrationCODandglycogendecreasedby107.21mg/Land76.81mg/LPHBasinternalcarbonsourceincreasedby150.88mg/LtheTPanaerobicconcentrationwas2.6timesoftheinitialconcentration.TheremovalefficiencyofTPandNO-2-Nwere94%and96%.TheeffectofdenitrifyingphosphorusremovalofA2/N-SBRprocesswassignificantandstable.TheelectrondonorPHBinshortcutdenitrifyingphosphorusremovalprocesswassynthesizedbyexternalcarbonsourceandglycogen.Keywordsdenitrifyingphosphorusremovalshortcutnitrificationmetabolicmechanismremovalefficiency*2014ZX07202-0112015010692015K7007XKHY-89。2015-12-130“”、、。1-2。A2/N-SBRSBRA2/N-SBR3-6SBR、。Kuba7-8/NO-3-NO2PAOsDPB。26EnvironmentalEngineeringNO-2-N、NO-3-NO29SDPB。“”PAOs9-10。-A2/N-SBRA2N-SBR。11.1-A2/N-SBR1N-SBR1A2-SBR1、2。N-SBR5L—3h—0.5h—0.5h—2A2-SBR30L—2h—2.5h—0.5h—0.5h—。SBRNO-2-NN-SBRA2-SBR。1N-SBRA2-SBRN-SBRNO-2A2-SBRNO-22N-SBRNO-2A2-SBRN-SBRA2-SBR。3200mg/L。1.2NH4ClKH2PO4CaCl2、MgSO4·7H2O、H2O、NaHCO31。CODTN-TP-MLSS1A2/N-SBRFig.1FlowchartofA2N-SBRsystem1—A2-SBR2—N-SBR3—4—5—6—7—8—9—10—A2-SBR11—A2-SBR12—13—A-SBR14—N-SBR。2A2/N-SBRFig.2SchematicdiagramofA2/N-SBRsystem1Table1WastewaterqualityofA2N-SBRmg/LN-SBRA2-SBRCOD30.2~50.540.2COD141.0~158.7150.2NH+4-N30~8055.0NH+4-N1.0~3.02.0TN32~8156.5TN1.6~4.02.4TP2.5~5.13.8TP7.8~13.010.0pH7.0~7.57.25pH7.5~8.07.8DOWTWDOpHORPWTWlevel2PHBPHB11-。2N-SBR25~30℃ρDO0.5~1.2mg/LpH7.2~7.5SRT8dA2-SBR36WaterPollutionControl24℃pH7.8SRT24d。2.1A2/N-SBRCODN-SBRρCOD30.2~50.5mg/L40.2mg/LN-SBRA2-SBRρCOD141.7~158.7mg/L150.2mg/L3。CODA2-SBRA2-SBRPHB。N-SBRA2-SBRSDPBPHBNO-2-N。CODA2-SBR。A2/N-SBRρCOD22.72mg/LCOD80.49%~86.39%84.08%A2/N-SBRCOD。—×—。3A2/N-SBRCODFig.3ConcentrationvariationofCODintheA2N-SBRsystem2.2A2/N-SBRTN4A2/N-SBRρTN9.20~23.25mg/L16.23mg/LN-SBRρTN77.5~80.3mg/LA2-SBRρTN1.76~2.07mg/L。N-SBRTNA2-SBRPHB。TN3.64mg/LTN78.26%~87.91%83.87%。—■—。4A2/N-SBRTNFig.4ConcentrationvariationofTNintheA2N-SBRsystem2.3A2/N-SBRTP5TPA2/N-SBRρTP6.5~7.2mg/L6.7mg/LN-SBRρTP2.3~3.2mg/LA2-SBR7.6~8.4mg/L。N-SBRA2-SBRA2-SBRρTP0.82~1.54mg/L1.1mg/L76.31%~89.58%83.55%CODTNTP。TPN-SBRCODA2-SBRCODTP。—■—TP。5A2/N-SBRTPFig.5ConcentrationvariationofTPintheA2/N-SBRsystem2.4A2/N-SBR6A2/N-SBR46EnvironmentalEngineeringCOD。N-SBRTPρTP2.59mg/L。60minCOD42.64mg/LCOD93.7%。60minCODρNH+4-N4.85mg/L95.8%ρNO-2-N74.4mg/LρNO-3-N4.05mg/L94.8%。a—N-SBRb—A2-SBR。—■—NH+4-N—●—NO-3-N—▲—NO-2-N—△—TP—○—COD。6Fig.6VarationofCODnitrogenandphosphorusinatypicalcycleA2-SBR120minCODTP19.38mg/LN-SBR。A2-SBRCOD117.3mg/LCOD83.5%CODDPAOPHBCOD。TP18.13mg/L10.53mg/LDPAO。A2-SBRTPρTP1.14mg/L88.8%。0.53mg/L。1.61mg/L0.78mg/L12-14。2.5COD、TP、NO-2-NPHBρMLSS2800mg/L。7。COD137.5mg/L30.29mg/L23.15mg/gPHBTPTPTP2.6PHB32.19mg/g。PHBATP。CODPHB、TPNO-2-NNO-2-N94%96%。NO-2-NPHB15-16。2PHB150.88mg/LCOD107.21mg/LPHBCODMinoPHB76.81mg/L74.07mg/LPHB69%PHB31%56WaterPollutionControl—□—COD—○——■—TP—●—NO-2-N—▲—PHB。7/Fig.7Substratetransformationinanaerobic/anoxicreaction、。19.55mg/LNO-2-N162.13mg/LPHB16.45mg/L。2/Table2Variablequantityofsubstrateinanaerobic/anoxicreactionCOD/mg·L-1-107.21-11.22PHB/mg·g-132.19-34.59COD/mg·L-1150.88-162.13/mg·g-1-23.1524.65COD/mg·L-1-76.8181.79NH+4/mg·L-1-0.68-1.04NO-2/mg·L-1-19.55TP/mg·L-1-11.0316.45/mg·g-15.488.39COD/mg·L-17.811.94C5H7O2N12.4%。。ρMLVSS/ρMLSS85%ρMLVSS/ρMLSS63%~70%。PHB89。PHBPHBPHB。31N-SBR8PHBFig.8ThedyeingpictureofPHB9Fig.9Thedyeingpictureofpoly-phosphateNO-2-NA2-SBRSDPBNO-2-NA2/N-SBR32dCOD、TNTP84.08%、83.87%83.55%。2N-SBR60min42.64mg/LCOD300min94.8%。A2-SBR10.4mg/LTP88.8%0.53mg/L。3NADH2ATP66EnvironmentalEngineering。469%PHB32.19mg/gPHBPHBNO-2-N17.05mg/L。1.J.2012356209-213.2Kerrn-JespersenJPHenzeM.BiologicalphosphorusuptakeunderanoxicandaerobicconditionsJ.WaterRes1993274617-624.3.SBRJ.20082961526-1532.4WangYYPengYZLiTWetal.Phosphorusremovalunderanoxicconditionsinacontinuous-flowA2NtwosludgeprocessJ.WatSciTechnol200450637-44.5.A/AJ.201535755-59.6.pHJ..20134452144-2149.7KubaTSmoldersGvanLoosdrechtMCM.Biologicalphosphorusremovalfromwastewaterbyanaerobic-anoxicsequencingbatchreactorJ.WaterSciTechnol1993275241-252.8BarkerPSDoldPL.DenitrificationbehaviourinbiologicalexcessphosphorusremovalactivatedsludgesystemsJ.WaterRes1996304769-780.9HuJYOngSLNgWJe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