您好,欢迎访问三七文档
当前位置:首页 > 商业/管理/HR > 质量控制/管理 > SBR反应器同步硝化反硝化影响因素及其特性马放
43820118JOURNALOFHARBININSTITUTEOFTECHNOLOGYVol.43No.8Aug.2011SBR150090mafang@hit.edu.cn、SBR.25~30℃、pH7~91∶1~8∶1COD、、TN0.12~0.80L·min-199.8%TN0.2L·min-195.52%COD91%COD.25~30℃、1.5∶1、0.2L·min-1、pH7~9.pHX522A0367-6234201108-0055-06Theinfluencingfactorsandthecharacteristicsofsimultaneousnitrification-denitrificationinSBRMAFangLIPingZHANGXiao-qiSUNJing-wenWANGHong-yuZHANGJiaStateKeyLaboratoryofUrbanWaterResourceandEnvironmentHarbinInstituteofTechnology150090HarbinChinamafang@hit.edu.cnAbstractToinvestigatethemechanismofsimultaneousnitrificationanddenitrificationSNDandpromotetheefficiencyofSNDsystembyusingthedomesticatedefficientSNDsludgetheeffectsoforganismDOandtemperatureontheSBRreactorwerestudied.Theexperimentresultsshowedthatwhenthetemperaturewas25-30andpHwas7-9thenitrate-nitrogenremovalwaspreferablywhenC/Nratevariedbetween1∶1-8∶1CODconcentrationammonianitrogenremovalrateandTNremovalratedecreasewiththeincreasingofC/Nrate.Dosingorganiccompoundsintwicecanenhancetheaerobicdenitrificationeffect.Whenaerationvolumevariedfrom0.12to0.80L·min-1ammonianitrogenremovalrateincreasedfirstandthenkeptap-proximateconstantwiththeincreaseofaerationvolumefinallybecamestableat99.8%.TNremovalratein-creasedfirsttothehighestat95.52%thendecreasedwhenaerationvolumewas0.2L·min-1andCODwasstableabove91%.TheinfluenceofaerationrateontheCODremovalisnotdistinct.Thebesteffectwillbeachievedifthesystemtemperatureis25-30℃C/Nrateis1.5∶1aerationvolumeis0.2L·min-1pHis7-9andthedosingoforganiccompoundsisintwice.Keywordssimultaneousnitrification-denitrificationSNDorganiccompoundsaerationratetemperaturepH2010-03-18.507780522008ZX07202-005.1963—.SimultaneousnitrificationanddenitrificationSND、、、、、1-5.Ying-Chih6、7.8SBRpH.pH8.5COD90.0%99.4%.9TN58%.10TN80~110mg·L-10.8~4.0mg·L-1NH3-N100%TN54%~77%NH3-N.11DO1.0mg·L-1MLSS8~9g·L-124℃pH7.2COD、NH3-N52317.24~24.00mg·L-195%92%.12.、COD、DO..、SBR.11.1SBR3L..12h、10min0.5h.1.2NO3--N、KH2PO4、MgSO4·7H2O、CaCl2、NaAc、NaHCO3.NaHCO3pH.1.1NH4+-N100~130mg·L-1NO3--N-COD100~250mg·L-1NaHCO33~6gMgSO450mg·L-1KH2PO422mg·L-1CaCl210mg·L-11.313COD、NO3--N、NO2--N、NH4+-NTNpHS-25pHYSI5000DO.22.12.1.1、SBR.27℃0.2L·min-1DO2.4~4.5mg·L-197.13~160.2mg·L-11∶1、1.5∶1、3∶1、4∶1、6∶1、8∶1.2.21∶1~8∶1CODTN1.5∶1..“”14.COD35~·65·43300mg·L-11.5∶1、TNCOD99.86%93.53%99.7%.2mg·L-1mg·L-1%TNmg·L-1mg·L-1%CODmg·L-1mg·L-1%1∶197.136.1793.64126.3821.4183.20155.4201001.5∶1152.80.19999.86178.8211.5593.59243.700.74699.73∶1111.13.7896.59138.0134.3275.34500.417.7898.44∶1160.210.2393.67200.8762.7263.30663.627.7898.86∶1110.415.1286.21157.8657.0055.52978.9372.7392.68∶1106.417.1983.84141.0964.8254.451316.5122.690.72.1.231.COD290.3mg·L-1、、TN111.0、12.4、11.2、155.7mg·L-1.DO0.5~3.0mg·L-128℃.24h.、、TN121.0、12.4、8.7、167.3mg·L-1、4h295.1mg·L-1.3.COD175.3mg·L-1、、TN117.0、10.3、10.8、148.7mg·L-1.4COD205.1mg·L-1..13.140120100806040200246810120h4h0h+4ht/h籽(氨氮)/(mg·L-1)0h:进水时一次性投加有机物;4h:进水时不添加,4h后添加有机物;0h+4h:0h和4h分两次投加有机物.13ta=0.05excelt1-2=2.91>t=1.78P<a=0.05t1-3=3.90>t=1.78、P<a=0.05.1423...3.23.1310254.224.30.3ta=0.05excelt1-2=0.3<t=1.78、P1-2>a=0.05t1-3=1.15<t=1.78、P1-3>a=0.05·75·8SBR.0h4h0h+4h252015105024681012t/h籽(硝氮)/(mg·L-1)233.籽(亚硝氮)/(mg·L-1)0h4h0h+4h252015105024681012t/h3ta=0.05excelt1-2=3.86>t=1.78P<a=0.05t1-3=1.95>t=1.78、P<a=0.05..231.43TN.3TN92.3%89.2%94.2%3TNta=0.05ex-celt1-2=1.26<t=1.78、P1-2>a=0.05TN.12TN.t1-3=3.63>t=1.78、P1-3<a=0.05133TN.TN/(mg·L-1)0h4h0h+4h20015010050024681012t/h4TNCOD.51COD290.3mg·L-14hCOD75.1mg·L-175%.3COD175.3mg·L-13hCOD50mg·L-1.3CODta=0.05excelt1-2=0.66<t=1.78、P1-2>a=0.05t1-3=0.36<t=1.78、P1-3>a=0.05COD396.9%96.1%97.2%.COD/(mg·L-1)0h4h0h+4h35030025020015010050024681012t/h5COD2.2.DO15.DOSND16.·85·4317.DO.0.12~0.80L·min-1DO2.0~8.0mg·L-1.0.12~0.20L·min-1.0.12L·min-120.9mg·L-1.18DODOSND.Bemet19DO.≥0.4L·min-10.8L·min-1102.65mg·L-1.60.12L·min-178.84%99.8%TN0.2L·min-195.52%COD91%COD.1201008060402000.120.200.400.600.80曝气量/(L·min-1)氨氮TNCOD去除率/%6DO、TN、COD2.320~30℃15℃5℃.20、2530℃3.0.2L·min-112h.10℃1~2..20~30℃TN.Arrhenius.20.25~30℃..730℃99.8%95.67%CODCOD20~30℃96.6%~98.25%.20℃25℃30℃120100806040200氨氮TNCOD去除率/%7、TN、COD2.4pHpHpH.12DO1mg·L-1pH6.8~9.7CODNH4+-NTNpH7.2pH5.0.2L·min-11.2∶1100mg·L-1pHCOD8.pH.pH≥70TN82%pH=6TN85.47%36.91%·95·8SBRpH7.pH6~9COD85%.pH7~9.pH=9pH=8pH=7pH=6120100806040200氨氮TNCOD去除率/%8pH、TN、COD31.1∶1~8∶1CODTN.1.5∶1、TNCOD99.86%93.53%99.7%.TNCOD.2.0.12~0.80L·min-1DO2.0~8.0mg·L-10.4L·min-199.8%TN0.2L·min-195.52%.COD91%COD.325~30℃pH7~9SBR-SND.1DINGAZFUMSHENGGY.EvidenceofaerobicdenitrificationJ.ChinScieBull20004532779-2785.2.J.200520280-83.3PATUREAUD.Combinedphosphateandnitrogenre-movalinasequencingbatchreactorusingtheaerobicdenitrifierJ.WatRes2000351189-197.4LUKOWTDIEKMANNH.AerobicdenitrificationbyanewlyisolatedheterotrophicbacteriumstrainTL1J.BiotechnologyLetters199711191157-1159.5CHIUAYCLEELLCHANGCNetal.ControlofcarbonandammoniumratioforsimultaneousnitrificationanddenitrificationinasequencingbatchbioreactorJ.InternationalBiodeterioration&Biodegradation2007591-7.6HOLMANJBWAREHAMDG.CODammoniaanddissolvedoxygentimeprofilesinthesimultaneousnitrifi-cation/denitrificationpr
本文标题:SBR反应器同步硝化反硝化影响因素及其特性马放
链接地址:https://www.777doc.com/doc-6540800 .html