您好,欢迎访问三七文档
当前位置:首页 > 行业资料 > 其它行业文档 > 好氧除磷颗粒对亚硝化颗粒污泥启动的影响李冬
39220182ENVIRONMENTALSCIENCEVol.39No.2Feb.2018/11112121.1001242.150090R1、R2、R3SBR、.S10~22dR1、R2、R319d.S223~56dR1R2、R320%20%R1、R2R376、42d56d412、468、400μm.S357~108dCOD0.4kg·m3·d-10.5kg·m3·d-10.2kg·m3·d-10.5kg·m3·d-1R1、R2R3.108dR1R2689μm893μm.C/N.CODX703.1A0250-3301201802-0872-08DOI10.13227/j.hjkx.2017070992017-07-102017-07-292014000026833TD021976~E-maillidong2006@bjut.edu.cnEffectofAerobic/PhosphorusGranulesonStart-upofPartialNitrificationGranularSludgeLIDong1GUOYue-zhou1CAOMei-zhong1ZHANGZe-wen1LIShuai2ZHANGJie121.KeyLaboratoryofBeijingforWaterQualityScienceandWaterEnvironmentRecoveryEngineeringBeijingUniversityofTechnologyBeijing100124China2.StateKeyLaboratoryofUrbanWaterResourceandEnvironmentHarbinInstituteofTechnologyHarbin150090ChinaAbstractThedifferenteffectsofadditionalaerobicgranulesAGsandphosphorusremovalgranulesPRGsonthestart-upandstableoperationofpartialnitrificationgranularsludgePNGSwerecomparedatroomtemperature22-28℃.Theresultsshowedthatinthefirststagedays0-22partialnitrificationwasaccomplishedonday19forthethreereactorsR1R2andR3.Inthesecondstagedays23-5620%AGsand20%PRGswereaddedtoR2andR3toinducePNGS.Thestart-upofthegranulesofthethreereactorswassuccessfullyachieved.ThemeanparticlesizesofR1R2andR3reached412μmatday76468μmatday42and400μmatday56.Inthethirdstagedays57-108becausetheinfluentammonialoadincreasedfrom0.4kg·m3·d-1to0.5kg·m3·d-1andtheCODloadincreasedfrom0.2kg·m3·d-1to0.5kg·m3·d-1themeanparticlesizesofR1andR2increasedsignificantly.TheaverageparticlesizesofR1andR2reached689μmand893μmbytheendoftheoperationday108butsludgeexpansionoccurredinR3.TheinoculationofeitherAGsorPRGscouldquicklyachievegranulationbutthePNGSinoculatedwiththeAGscouldadapttohigherC/Nandbemoretolerabletoshockloadsandlong-termstableoperation.KeywordsaerobicgranulesphosphorusremovalgranulespartialnitrificationgranularsludgeammonianitrogenloadCODload、12.1.NH+4+1.32NO-2+0.066HCO-3+0.13H→+1.02N2+0.26NO-3+0.066CH2O0.5N0.15+2.03H2O11.-.34.AOB、NOB、、5.67.630%12d82/18d92min19d..21011..Wu12、13..R1R2、R320%、20%.3、MLSS、SVI、EPS.11.1SBR3SBR70cm15cm10.5L2/3.3SBR22~28℃.SBR38h12min、202~218min、4h、20~4min3min3min.1.1Table1Reactoroperatingparametersatdifferentstages/d/h/mg·L-1/mg·L-1NH+4-N/kg·m3·d-1COD/kg·m3·d-1S10~2240.02±0.010.5±0.20.40.2S223~5640.02±0.010.5±0.20.40.2S357~10840.02±0.010.8±0.20.50.51.23SBR.MLSS2700±200mg·L-1、SVI140mL·g-1.100~250mg·L-1NH+4-N10∶10.136gKH2PO4、0.02gMgSO4·7H2O、0.136gCaCl214.S1、S2、S33S1S2R2、R320%、20%S3COD.1.3NH+4-N、NO-2-N、NO3-N、SS、VSS、SVI152min.pH、DOWTWPh/Oxi340i.OlympusBX51.MalvernMastersizer2000.、FAFNA2~5=ρNO-2-NρNO-2-N+ρNO-3-N2=ρNH+4-NρNH+4-Nin3FA=17×ρNH+4-Ninner14(×e6344237+T+10)pH4FNA=47×ρNO-2-Ninner(14×e-2300273+T×10)pH+15ρNO-2-N、ρNO-3-NNO-2-N、NO-3-Nmg·L-1ρNH+4-Nin37839NH+4-Nmg·L-1ρNH+4-Ninner、ρNO-2-NinnerNH+4-N、NO-2-Nmg·L-1.22.11S1Fig.1VariationofammonianitrogenintheinfluentandeffluentandthenitriteaccumulationrateduringtheS1stageR1、R2、R31.NOB0.AOB“”AOBNOB1617/FAFNA.73d50mg·L-1100mg·L-15..196d100mg·L-1200mg·L-1.1aR15719d92%96%790%17.1b1cR2R35719d93%92%790%.2.22.2.1R1、R2、R35719d.R130d.2R176d412μm1819.S357~108dR1S2CODEPS20~22.108dR1689μm71.54%500μm.23dR2、R320%20%R1.SBRCOD300mg·L-1、NH+4-N30mg·L-1、KH2PO4-P5mg·L-1C、N、P95%、83%、90%MLSS4200mg·L-1SVI34mL·g-1SBRKH2PO4-P10mg·L-1P95%MLSS4280mg·L-1SVI32mL·g-1.226dR2182μm150μm①C/N②23.27dR3196μm160μm.R2800μm18%5%/R3800μm20%12%.242d24R2468μm4782/R134d.S357~108dR2108dR2893μm72%600μm.56dR3400μmR120dR2.S357~108dR32.2.2108d200μm.COD0.5kg·m3·d-10.5kg·m3·d-1.2Fig.2Variationofthemeanparticlesizeduringoperation2.2.2MLSSSVI3S10~22dR1、R2、R3MLSS2770、2541、2760mg·L-12493、2732、2469mg·L-1.3MLSS.①C/N②25③NO-2-N26.33SVI.S223~56d20min4min8918.23dR2、R320%20%R1.3aR1MLSS.56dR1MLSS647mg·L-1.3b3c27R2、R3MLSS.56dR2、R3MLSS2591mg·L-1、2562mg·L-1.3MLSS、MLVSSSVIFig.3VariationsofMLSSMLVSSandSVIduringoperationS357~108d3a3b0.4kg·m3·d-10.5kg·m3·d-1COD0.2kg·m3·d-10.5kg·m3·d-1R1、R2C/NMLSS.108dR1MLSS2415mg·L-1R2MLSS3012mg·L-1.R1、R2SVI.108dR1、R2SVI62mL·g-1、42mL·g-1.3c108dR3MLSS2000mg·L-1SVI134mL·g-1.COD0.5kg·m3·d-10.5kg·m3·d-157839.R3①COD28②29~31.32.2.2.3EPS4EPSPN/PSFig.4VariationsofEPSandPN/PSduringoperation4S10~22d50mg·L-1200mg·L-1PN33R1、R2、R3EPSPN/PS.S223~56dEPS34R1、R2、R3EPS78.1、81.4、81.4mg·g-1142.8、176.4、164mg·g-1.4a23dR1PN/PS1.2PNPN/PS3556dPN/PS2.4.4b4cR2、R3R1PN/PS23d、56d1.21.19、3.22.7.R2R3.S357~108dCODEPS36.4a4bS3R1R2EPS.EPS34.R1、R2EPS159mg·g-1、164.6mg·g-1.4cR3EPSPN/PS31.2.2.45、Fig.5Variationsofammonianitrogenintheinfluentandeffluentofnitratenitrogenintheeffluentandofnitriteaccumulationrate5aS223~56dR1AOB.R1AOB.108d0mg·L-1.R1108d0mg·L-1R1NOB.FA6~9mg·L-1NOB37FNA0.023mg·L-1NOB0.4mg·L-1AOB3839.FA0.48~21.09mg·L-16782/FNA0.0007~0.023mg·L-1FAFNANOBR190%.5bR1R2AOB108d0mg·L-10mg·L-190%./40、FAFNANOBR1R2.5cR3S2.S3R3MLSSAOB.91%108d46%S2NOB.2.2.5COD、、R1、R2COD、、6aR1154mg·L-1146mg·L-10.42kg·m3·d-1173∶30.4kg·m3·d-16bR2156mg·L-1150mg·L-10.426kg·m3·d-1..6aR124.94%R1R2COD2.R1COD29mg·L-1COD21mg·L-1.6bR233.55%.R2R1100~200μm4041R2.R2COD29mg·L-1R2COD10mg·L-1R1.R2R1COD.abR1、R290dCOD6COD、、Fig.6VariationsofCODammonianitrogennitritenitr
本文标题:好氧除磷颗粒对亚硝化颗粒污泥启动的影响李冬
链接地址:https://www.777doc.com/doc-6568991 .html