不同pH值下初沉污泥与二沉污泥厌氧发酵对比李晓玲

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pH12111.7100642.100124pH。pH5~1214d。SCOD、VFAs、、、。SCODVFAsSCODpH=9、=9.5dpH=10、=7.5dVFAspH=10SCOD671.9mgSCOD/gVSS501.6mgSCOD/gVSS、52.8mgNH+4-N/gVSS、13.2mgPO3-4-P/gVSS21.8mgNH+4-N/gVSS、3.6mgPO3-4-P/gVSS。、pH=10、=8d。pHX703A1000-4602201603-0015-07310829151074ComparativeStudyonPrimarySludgeandSecondarySludgeinAnaerobicFermentationatDifferentpHValuesLIXiao-ling1PENGYong-zhen2HANBo-tao1ZHAOJian-qiang11.KeyLaboratoryofWaterSupplyandDrainage<MinistryofHousingandUrban-RuralDevelopment>Chang’anUniversityXi’an710064China2.KeyLaboratoryofBeijingforWaterQualityScienceandWaterEnvironmentRecoveryEngineeringEngineeringResearchCenterofBeijingforNitrogenandPhosphorusRemovalandProcessControlBeijingUniversityofTechnologyBeijing100124ChinaAbstractpHvalueandfermentationtimearetwoimportantfactorsinthefermentationprocessofsludge.SequencingbatchmethodwasusedtoexaminethefermentationprocessesofprimarysludgeandsecondarysludgeatpHvalueof5to12andthefermentationtimeof14days.ThedissolutionprocessesandthedissolutionratesoffermentationproductsofthetwodifferentkindsofsludgewerecomparedintermsofSCODVFAsproteincarbohydratenitrogenandphosphorus.Theresultsshowedthatalkaline·1·32320162CHINAWATER&WASTEWATERVol.32No.3Feb.2016conditionswereobviouslybeneficialtothedissolutionofSCODandVFAsSCODdissolvedrapidlyintheinitialstageandtheoptimumfermentationconditionsofprimarysludgewerepHof9andfermentationtimeof9.5dayswhilethoseofsecondarysludgewerepHvalueof10andthefermentationtimeof7.5days.PrimarysludgecouldproducealargenumberofVFAsinarelativelyshorttimethereforefermen-tationofsoleprimarysludgewasconsideredtobethemosteffectiveandrapidmethodtoobtaintheinter-nalcarbonsource.ThoughtheamountofSCODdissolvedbysecondarysludge671.9mgSCOD/gVSSwasmuchhigherthanthatbyprimarysludge501.6mgSCOD/gVSSatpHvalueof10afterstabiliza-tionthereleaseratesofnitrogenandphosphorusfromsecondarysludge52.8mgNH+4-N/gVSSand13.2mgPO3-4-P/gVSSwerealsohigherthanthosefromprimarysludge21.8mgNH+4-N/gVSSand3.6mgPO3-4-P/gVSS.Besidesalargeamountofnitrogenandphosphorusreleasedbysecondarysludgeseriouslyaggravatedthetreatmentloadofthefollow-upsystemthereforeinordertoeasethisim-pactandcombinedwiththerespectivefermentationcharacteristicsofthetwokindsofsludgeitwassug-gestedthatfermentationofmixedsludgewasusedtoobtaintheinternalcarbonsourcesundertheoptimumconditionsofpHvalueof10andfermentationtimeof8days.KeywordsalkalinesludgefermentationmixedsludgefermentationtimepHvaluedissolutionratefromfermentationC/N。①、、、②、“”③BNR。。1、2、3~5、6YuanWu34pHSCODVFAs、。pH。11.11。1Tab.1SludgepropertiespH5.876.75TSS/mg·L-1542035050VSS/mg·L-1346903550VSS/TSS0.640.70SCOD/mg·L-1116549/mg·L-145.064.38/mg·L-1416.0518.49NH+4-N/mg·L-197.597.16PO3-4-P/mg·L-122.033.41、、NH+4-N、PO3-4-P。1.2pH51#、62#、73#、84#、95#、106#、117#、128#pH9500mL100r/min25℃。100mL0.9mol/LH2SO4·2·323.watergasheat.com1。1Fig.1SchematicdiagramofexperimentsetuppH2mol/LNaOHHCl12hpH±0.324h6000r/minSCOD、、、、8000r/minVFAs。1.3COD、NH+4-N、PO3-4-P、MLSS、MLVSSLowrypH。VFAs7890H2250℃1∶170℃0min25℃/min170℃2minFID300℃45mL/min450mL/min。22.1pHSCOD7。、、95%~97%99%。2pHSCOD。SCODYuan4。pHpHpHSCOD。Chen8SCODSCOD。2pHSCODFig.2SCODyieldsinfermentationofprimarysludgeandsecondarysludgeatdifferentpHs2d4dEPS。pHSCODSCOD·3·.watergasheat.compH323SCODCai。3SCOD。pHpHSCODSCOD。SCODSCODpH=10、11、12、5pH=6、7、8、9SCODSCOD。3SCODFig.3ComparisonofSCODdissolutionratebetweenprimaryandsecondarysludge2.2、、EPS4。EPS。pH4。Tanaka41%、25%、14%20%。4pHFig.4DissolutionratesofcarbohydrateandproteininfermentationofprimarysludgeandsecondarysludgeatdifferentpHs2.3pHVFAs。、、、VFAsNH3、CO2、H2SVFAs、CO2H2。VFAs。Tong9VFAsPantelis10VFAs、、、。5pHVFAsCOD1.071.51·4·323.watergasheat.com1.822.04。5pHVFAsFig.5VFAsyieldsinfermentationofprimarysludgeandsecondarysludgeatdifferentpHvalues5apH89VFAs9.5d。5bpH910VFAs7.5dVFAs。VFAsVFAsSCODSCODVFAs。VFAsVFAs。Miron25℃8d。VFAs。VFAs。SRTHRTVFAs。2.4pHSCODSCOD、、VFAspH9、107.5、9.5dSCOD。VFAs40%~50%20%~25%3%~5%VFAs25%~30%5%~10%。6SCODFig.6SCODcomponentsinfermentationofprimarysludgeandsecondarysludge2.5、BNR、·5·.watergasheat.compH323。pH、SCOD2。A2O、。2、Tab.2AmmoniaandphosphorusreleaseinfermentationprimarysludgeandsecondarysludgepH=5pH=6pH=7pH=8pH=9pH=10pH=11pH=12NH+4/VSS16.217.019.521.923.924.522.014.88.3PO3-4/VSS2.32.52.33.02.43.03.64.33.2SCOD/N13.89.29.47.313.719.828.852.3124.3SCOD/P166.6108.3137.991.2231.3281.5302.4310.8548.3NH+4/VSS23.157.041.09.337.747.749.346.79.3PO3-4/VSS10.113.011.48.37.511.310.911.87.4SCOD/N2.53.22.67.62.88.214.524.3147.8SCOD/P9.824.115.914.624.559.1112.8164.3319.2pH、pH、NH+4-NNH+4+H2O→NH3+H+NH+4NH3pH10、11、12Mg2+、Ca2+pH12。COD/NCOD/PBNRCOD/N4COD/P8~15。2pHSCOD/NBNR。2.6①pH12>11>10>9>8>pH。②SCOD2d4d6、、、4dVFAs7.5~9.5d7.5dSRTVFAs。。SCODVFAs、11SCOD。Su12。pH=10、SRT=8d、。3①SCODVFAsSCODSRT=2dSRT=4dSRTVFAsSRT=7.5~9.5dVFAsSRT=7.5dSCODVFAspH=9、SRT=9.5dpH=10、SRT=7.5d。②·6·323.watergasheat.comSCODVFAs、。③SCOD25.4%、58.7%73.1%pH=10、SRT=8d。1LiuYLLiXKangXRetal.Shortchainfattyacidsaccumulationandmicrobialcommunitysuccessionduringultrasonic-pretreatedsludgeanaerobicfermentationprocessEffectofalkalineadjustmentJ.IntBiodeteri-orBiodeg

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