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当前位置:首页 > 商业/管理/HR > 管理学资料 > 城市污水处理过程中不同形态氮类营养物的转化特性
99环境工程学报Vol.9No.920159ChineseJournalofEnvironmentalEngineeringSep.2015710055A/A/O。39.28mg/L41.24mg/L93.2%36.61mg/L2.67mg/L。96.58%39.83mg/L。45%。。/。X703A1673-9108201509-4193-06TransformationcharacteristicsofdifferentformsofnitrogennutrientsinprocessofwastewatertreatmentJinPengkangSongLiRenWuangSchoolofEnvironmental&MunicipalEngineeringXi’anUniversityofArchitecture&TechnologyXi’an710055ChinaAbstractTheaimofthisstudywastoinvestigatethetransformationprocessofdifferentformsofnitrogennutrientsbyfiledmeasurementandsimulatetestinthewholecitysewagetreatmentA/A/Osystem.Thestudyshowedthatinfluentdissolvednitrogenandparticulatenitrogenproportionwerealmostthesameconcentrationsof39.28mg/Land41.24mg/Lrespectively.Dissolvednitrogenwasmainlycomposedofdissolvedinorganicnitrogenwhichportionconstituted93.2%36.61mg/Lbutdissolvedorganicnitrogenconcentrationwasverylow2.67mg/L.Theparticulateorganicnitrogenportionconstituted96.26%oftheparticulatenitrogen.Dis-solvednitrogenchangeswasverysmallintheprocessofthewholeprimarytreatmentbutparticulateorganicni-trogendecreased45%.Particulateorganicnitrogenwasremovedduetoprecipitationwhichresultedinlowerto-talnitrogen.Filedmeasurementandsimulatetestshowedthatdissolvedorganicnitrogenwassignificantlyre-ducedbyanaerobicmicrobialdegradationintheanaerobicandanoxiccompartmentsofthesecondarytreatmentwhereasaslightlyincreaseofdissolvedorganicnitrogenconcentrationswasobservedintheaerobiccompartment.Secondaryeffluentnitrogenmainlycomposedofinorganicnitrogenthroughthefurtheroptimizationofprocesspa-rameterswecanenhancesystemnitrification/denitrificationtoremovetheresidueofinorganicnitrogeninthewastewater.Keywordsnitrogennutrientsurbansewagetreatmentsystemtransformationprocess511783762011ZX07302-001CX121602014-09-292014-11-281974—。E-mailpkjin@hotmail.comPONDON2NH3-N、NO3-NNO2-N。AAO、、SBR/9N21。234-6。、。A/A/OTN。11.1A/A/O20t8.0m16.5h2h5.5h9h。1。。1Fig.1Sewagetreatmentplantprocessesandsamplingpoints2particulatenitrogenPNdissolvednitrogenDN0.45μm。dissolve-dorganicnitrogenDONdissolvedinorganicnitrogenDINparticulateorganicnitrogenPONadsorptionofni-trogenAN。500mLTN1SS100mL0.45μm。TN2TINNH+4-N、NO-3-NNO-2-N。100mL25℃、200r/min2h5000r/min5min7100mL0.45μmTN3、NH+4-N、NO-3-NNO-2-NAN。2Fig.2DifferenttypesofnitrogencomponentdiagramPN=TN1-TN2DN=TN2AN=TN3PON=PN-ANDON=TN2-TINTN、NH+4-N、NO-3-NNO-2-NTU-1901《》449149。PONAN。50℃0.2g2。150mL100mL25℃、200r/min2h5000r/min5min100mL0.45μmTN、NH+4-N、NO-3-NNO-2-N。ANDON=TN-NH+4-N-NO-3-N-NO-2-N。250mLKN。PON=KN-NH+4-N-DON。1.23。MLSS4000~5000mg/L。3Fig.3Reactorreactiontimeandsamplingtime32h5.5h9h。2h10mg/LKNO32mg/LA/A/O。30.45μmTN、NH+4-N、NO-3-NNO-2-N。22.12.1.1污水中氮组分分布180.52±1.4mg/LPNDN41.24mg/L39.28mg/L51.24%48.78%。1DINDN93.2%36.61mg/L。DNDON2.67mg/L。PNPON96.58%3.42%AN。ANDONAN53.19%27.66%AN。73.43mg/LPNDN35.04mg/L38.39mg/L47.72%52.28%。2DNPN6.2mg/LAN。60.46mg/LPNDNPONDIN90%。PON+DON24.3mg/L40.19%PONTON90.16%3。Czer-wionka88BNRTON15.5~35mg/L24%~45%PON50%78%。2.1.2沉淀泥中氮组分分布PONANANDON、、。TN12.66mg/g39.1mg/g。1Table1Differenttypesofnitrogennutrientdistributioninrawsewagemg/L%2.676.835.640.940.0390.732.390.0839.8396.580.390.240.750.030.940.581.820.08591492Table2Differenttypesofnitrogennutrientdistributioninaeratedgritchambermg/L%2.456.3834.871.050.0290.832.730.0633.7496.290.540.190.560.011.540.541.60.033Table3Differenttypesofnitrogennutrientdistributioninprimarysettlingtankmg/L%2.396.3833.81.270.0290.183.380.0621.9195.34—0.530.530.01—2.302.300.06PONPON94.31%11.94mg/g70.69%31.16mg/g。ANDON20%4。1、23AN。4Table4Differenttypesofnitrogennutrientdistributioninprecipitationmudmg/g%11.9494.310.22—0.5—1.74—3.95—31.1670.693.611.412.890.039.233.617.390.082.2TN4。7.09mg/L12.96mg/LPN6.2mg/L12.06mg/LDON。4Fig.4Nitrogenfractionsinprimarytreatment5TN12.66mgN/g6.51mgN/L△TN×△SS/100012.51mgN/L。47.09mg/L12.96mg/LTNPON。Sattayatewa.9Mulholland10PON、、PON50%DON。5Table5NitrogenbalanceanalysisintheprimarytreatmentSSmg/L1186672514TNmgN/L80.5273.437.09TNmgN/L——6.51SSmg/L672352320TNmgN/L73.4360.4612.96TNmgN/L——12.51TN。2.352.46mg/LDON69149DON1.02mg/L1.25mg/LDON1.88mg/L。Makinia112BNR。、SRTpH12。5DONFig.5DONconcentrationschangesinthesecondarytreatmentDONDON6。DON1314DON。DON1231516。DON。65%DON1.94±0.26mg/L15%~20%、6//3Fig.6Changesofnitrogencompoundsinanaerobic/anoxic/aerobiccompartments。31DNPNPNDN41.24mg/L39.28mg/L。DINDNDON2.67mg/LPNPON96.58%39.83mg/L。2DNPON17.92mg/L45%。3DON。4DONDONSMP、。5TNNH3-N+NO3-N。、。1..201432728-3179149WangJuantingYuYanzhen.Researchprogressofnitrogenandphosphorusremovalinmunicipalsewage.ChinaRe-sourcesComprehensiveUtilization201432728-31inChinese2..2007275712-716MengWei.Thestrategyofcomprehensivepollutionpreven-tionandcureofwaterenvironmentinChinesewatershed.ChinaEnvironmentalScience2007275712-716inChinese3..2013329-30YuLinkang.TNindicatorsexploretheimportanceofwastewatertreatment.StraitsScience2013329-30inChinese4..201412310-12ZhouYongliZuoJiaolanLiYijunetal.Researchad-vancesofnitrogenremovalbybiotechnologyinwastewatertreatment.ExperimentScienceandTechnology201412310-12inChinese5..2011369108-112WangZebinMaYunMaQiang.Advanceandtrendofbiologicaln
本文标题:城市污水处理过程中不同形态氮类营养物的转化特性
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