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27720147ResearchofEnvironmentalSciencesVol.27No.7July2014.UASB-A/OJ.2014277733-741.LIChaoYINErqinTANGSiyuanetal.PilotstudyontreatmentofprintinganddyeingwastewaterbyUASB-A/OprocessJ.ResearchofEnvironmentalSciences2014277733-741.2013-10-152014-03-122012ZX07101-0031984-lichao0609@163.com.*1964-caojiashun@163.comUASB-A/O1222212*1.2100982.210098UASB-A/O.UASB0.065m3/hUASB0.260m3/hA/O200%ρCODCr<200mg/LρNH3-N<10mg/LρTN<15mg/LUASBρNH3-NρTN80%85%UASBVFAsPVAUASBPVA10%~40%A/OPVA60%.UASBVFAsPVAX1711001-6929201407-0733-09ADOI10.13198/j.issn.1001-6929.2014.07.08PilotStudyonTreatmentofPrintingandDyeingWastewaterbyUASB-A/OProcessLIChao12YINEr-qin2TANGSi-yuan2ZHOUBin-yu2CAOJia-shun121.KeyLaboratoryofIntegratedRegulationandResourceDevelopmentonShallowLakesMinistryofEducationHohaiUniversityNanjing210098China2.SchoolofEnvironmentHohaiUniversityNanjing210098ChinaAbstractInapilotexperimentthetreatmentofprintinganddyeingwastewaterbytheUASBup-flowanaerobicsludgebed-A/Ocouplingprocesswasstudied.Optimalpollutantremovalperformancewasobtainedundertheconditionsofinflowrates0.065m3/hand0.260m3/hforpretreatmentanddyeingwastewaterrespectivelyandrefluxratiofixedat200%fortheA/Oprocess.IntheeffluentCODCrwas<200mg/Lammonianitrogenwas<10mg/Landtotalnitrogenwas<20mg/L.IntheUASBprocesssectionthedyeingandpretreatmentwastewatershowedhighefficiencyanaerobicammoniation.Ammonianitrogenoccupiedmorethan80%and85%ofthetotalnitrogenintheanaerobiceffluentofthedyeingandpretreatmentwastewaterrespectively.Evenatnormaltemperatureanaerobicdigestioncouldalsoachievegoodammoniation.InordertoenhancethedenitrificationVFAsvolatilefattyacidcouldbecontrolledbyadjustingtheoperationparametersoftheUASBsectionwhichproducedasufficientandhigh-qualitycarbonsourceforanoxicdenitrification.ThecouplingprocesshadagoodremovalefficiencyofPVApolyvinyalcoholinprintinganddyeingwastewater.TheremovalrateofPVAwas10%-40%intheUASBsectionwhileintheA/Osectiontheremovalratewasmorethan60%.KeywordsprintinganddyeingwastewaterUASBVFAshighefficientammoniationPVAρTN50mg/L1.ρCODCr、ρ、2-4.275-6、7-8、9.、、..Somarsiri10UASB90%CODCr92%.LIANG11HRT6h1296.5%.-.Kulla12-.ρTN.①13.TN14-15.②16-17.VFAsVFAs18-19VFAs.ρCODCr、ρ、UASBA/O.①UASB②UASBVFAs-.11.1UASB-A/OUASB-A/O1.6UASBΦ1232mm×4000mm4.0m3.2A/O4000mm×1100mm×2700mm2.3m36.7m31.6m3.1—2—UASB3—4—5—6—7—8—.1UASB-A/OFig.1SchematicdiagramofUASB-A/Oprocess1.2.、、4377UASB-A/OPVA.、.2UASBA/O1.2.1.1Table1InfluentqualitypHρCODCr/mg/LρNH3-N/mg/LρTN/mg/L7.5~8.53500~500025~4550~851024~20487.5~8.51000~150010~3025~452048~40961.3UASB..2.2UASB-A/OTable2OperatingparametersofUASB-A/OprocessUASB/m3/h0.0651、0.26020.20.2HRT/h601、15211.533.5ρMLSS/g/L30~403~43~4ρDO/mg/L0<0.32.0~3.0pH7.5~8.07.2~7.57.2~7.5/%—200—12.1.4ρCODCrGB/T7486—1987《》pHpHHACHρNH3-NρTNρVFAsVFAs7890.820129VFAs.22.1UASB-A/OCODCr.UASB.22012101—18CODCr.2CODCr20%~40%.VFAs12.CODCr50%.CODCr.2A/OA/OCODCr80%ρCODCr200mg/L.2UASB-A/OCODCrFig.2CODCrremovalefficiencyofUASB-A/Oprocess537273VFAs.3HRTCODCrVFAs.ρVFAsVFAs———.ρρVFAs94.3%89.7%.20-21.CODCrHRT6015h.20.ρCODCrPVAHRTCODCr2A/OHRT10CODCr..3VFAsTable3AnalysisofVFAsineachsectionρ/mg/LVFAs253.926.901.900282.7562.537.95.903.80610.1UASB414.916.94.04.000439.8UASB207.281.919.616.530.03.4358.642.313.03.600058.92.2UASB-A/ONH3-NTN2.2.122.30023.TN.TN、ρTN24.、2、ρNH3-N/ρTN3、4.3、43UASB、ρNH3-N/ρTNFig.3EfficiencyofdyeingwastewateranaerobicammoniationρNH3-N30%~45%ρNH3-N/ρTN97%98%.ρNH3-N/ρTN.6377UASB-A/O4UASB、ρNH3-N/ρTNFig.4Efficiencyofpretreatmentwastewateranaerobicammoniation.2..ρNH3-N/ρTN95%、.A/OTN.2.2.2.30~33℃20~23℃.510℃ρNH3-N/ρTN5、6.CODCrCODCr50%30%6.52ρNH3-N/ρTN80%...①、、、、pH.②8.UASB./℃1—30~332—20~23.5UASBρNH3-N/ρTNFig.5ImpactoftemperatureondyeingwastewateranaerobicammoniationbyUASB/℃1—30~332—20~23.6UASBρNH3-N/ρTNFig.6ImpactoftemperatureonpretreatmentwastewateranaerobicammoniationbyUASB2.2.3A/ONH3-NTN12.7A/O10TN75%11.1023~25℃1117~18℃2573727TN10.A/ONH3-N85%10—11TN.ρNH3-N10mg/LρTN15mg/L.TNUASBVFAs.7A/ONH3-NTNFig.7RemovalefficiencyofNH3-NandTNbyA/O2.3ρVFAsA/OTN-.-、.26.NH3-NA/OA/O.CODCr.UASBA/O———VFAs..VFAsA/O27-2829.ρVFAsρVFAsA/O4.4UASB4VFAsA/OTNTable4VFAsonimpactoftotalnitrogenremovalinA/OprocessρVFAs/mg/LρCODCr/mg/LρTN/mg/LρVFAs/ρTNρTN/mg/LTN/%194.9121560.93.220.266.8201.3123261.03.319.867.5362.7178555.86.514.274.6498.1234758.68.513.177.6646.0254452.112.411.378.3771.1277664.811.911.182.9772.2228859.413.011.680.5849.3228861.113.913.178.6837889.8209666.913.311.083.67UASB-A/OVFAsρVFAs/ρTNTN.ρVFAsVFAs、.ρVFAs/ρTN6.5TN75%.VFAs.VFAs-.VFAs、.2.4UASB-A/OPVAPVA、PVAρBOD5/ρCODCr0.0643031.UASBA/OPVA8、9.8UASBPVAFig.8PVAdegradationinpretreatmentwastewaterbyUASBprocess9A/OPVAFig.9PVAdegradationinpretreatmentwastewaterbyA/OprocessρPVA100~300mg/L.8UASBPVA10%~40%ρPVA230mg/L.32PVA6.3%.9A/OPVA60%79%.3aUASB-A/O、.CODCr、NH3-NTNρCODCr<200mg/LρNH3-N<10mg/LρTN<15mg/L.bUASBρNH3-N/ρTN80%85%.cUASBVFAsVFAs.ρVFAs.ρVFAs/ρTNTN6.5TN75%.VFAs-.dUASB-A/O.UASBVFAsρVFAs/ρTNPVA.References1.BAFJ.2007328119-123.LANShanhongZHANGChihuiLIANGMouhuietal.StudiesonremovalofnitrogenfromdyeingandfinishingwastewaterbybaffilledbyanewtypemediamaterialJ.E
本文标题:UASBAO耦合工艺处理高含氮印染废水中试李超
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