36220152ENVIRONMENTALSCIENCEVol.36No.2Feb.2015OA/O11231*1.1000842.1000833.410082A/O.A、BO2~3mg·L-15~6mg·L-1.HRT20hACOD72.5mg·L-1±14.8mg·L-1B68.7mg·L-1±14.6mg·L-1COD67.0%68.8%0.8mg·L-195%.BOD55mg·L-1.A/O.O454、A、B58.7%59.2%、14.7%12.7%10.8%12.4%.BNitrosomonas、NitrospiraPlanctomyces.AzospiraAcidovoraA.Novosphingobium、Comamonas、SphingobiumAltererythrobacter、、.A/O454X172X703A0250-3301201502-0604-08DOI10.13227/j.hjkx.2015.02.0312014-06-302014-09-202012ZX07201-005-06-011985~E-mailricky1115@163.com*E-mailwangjl@tsinghua.edu.cnEffectsofDissolvedOxygenintheOxicPartsofA/OReactoronDegradationofOrganicPollutantsandAnalysisofMicrobialCommunityforTreatingPetrochemicalWastewaterDINGPeng-yuan1CHULi-bing1ZHANGNan2WANGXing3WANGJian-long1*1.InstituteofNuclearandNewEnergyTechnologyTsinghuaUniversityBeijing100084China2.SchoolofWaterResourcesandEnvironmentChinaUniversityofGeosciencesBeijing100083China3.CollegeofEnvironmentalScienceandEngineeringHunanUniversityChangsha410082ChinaAbstractEffectsofdissolvedoxygenDOonthebiodegradationoforganicpollutantswereinvestigatedusingA/Oreactorsforthetreatmentofactualpetrochemicalwastewater.TwoA/OreactorsDOwerecontrolledat2-3mg·L-1intheoxicpartsofreactorAand5-6mg·L-1ofreactorBwereoperatedinparallelforcomparison.ThenearlyahalfofyearoperationresultsshowedthattheeffluentCODinreactorA72.5±14.8mg·L-1wasslightlyhigherthanthatinreactorB68.7±14.6mg·L-1ataHRTof20h.TheaverageCODremovalefficiencieswere67.0%and68.8%respectively.Theeffluentammoniumconcentrationwasmaintainedat0.8mg·L-1andapproximately95%ofammoniumremovalwasachieved.TheeffluentBOD5concentrationwaslowerthan5mg·L-1.ThisindicatedthattheorganicpollutantscouldbedegradedthoroughlybytheA/OprocesseswhichwereaffectedslightlybyDO.Resultsof454pyrosequencinganalysisofthesludgeinoxicpartsshowedthatatthephylumlevelssequencesbelongedtoProteobacteriaPlanctomycetesandBacteroideteswereabundantwith58.7%and59.2%14.7%and12.7%10.8%and12.4%oftotalbacterialsequencesinreactorAandBrespectively.AmmoniumoxidationbacteriaNitrosomonasnitriteoxidizingbacteriaNitrospiraandobligateaerobicbacteriawerehighlyenrichedinreactorBwithhighDOlevelswhiletheanaerobicdenitrifiersAzospiraandAcidovorawerehighlyenrichedinreactorAwithlowDOlevels.TheidentifiedbacteriabelongedtogeneraNovosphingobiumComamonasSphingobiumandAltererythrobacterwerereportedtodegradePAHschloronitrobenzenepesticidesandpetroleumwhichcontributedtothedegradationofpetrochemicalwastewater.KeywordsdissolvedoxygenpetrochemicalwastewaterA/Oreactor454high-throughputpyrosequencingmicrobialcommunity2OA/O.、、.、1./23.、/A/O、4.A/O.O.60%~80%5.6.7A2/OODO4.0mg·L-11.0mg·L-1COD.Guo8DO1.5~2.4mg·L-1A/O.DODO..Rocher4549、、、.10.DOA/ODOA/O.11.11.A/OA.A、B.AO1、O245LA、O1O21∶2∶228L.AO.AODO2~3mg·L-1B5~6mg·L-123~26℃.1Fig.1Schematicdiagramoftheexperimentalset-up1.2、.3∶1.、、、.1.CODTNTP.11Table1CharacteristicsoftheinfluentCODTOCBOD5UV254237.3±67.654.8±5.676.6±23.520.0±3.90.68±0.628.6±5.01.7±0.61.5±0.21UV254mg·L-1.201342448h.HRT30h100%.COD70%.2013520201394HRT30h2013952013116HRT20h.SRT50d.506362~3d、COD.、BOD5、TN、TPCOD.0.45μm.O.、SMP、、3D-EEM.1.3BOD5、COD、、、11.TOCTNTOC-VCPH/CPN..MLSS.DOYSI-550A.3D-EEMHitachiF-700012Ex200~400nmEm240~500nm5nm1200nm·min-1PMT700V.454.1.3.1DNADNAE.Z.N.A.DNAOMEGA.1.3.2PCRDNA16SrRNA27F533RV1~V3.5'-GCCTTGCCAGCCCGCTCAGAGAGTTTGATCCTGGCTCAG-3'454B27F.5'-GCCTCCCTCGCGCCATCAGNNNNNNNNNNTTACCGCGGCTGCTGGCAC-3'454A10PCR533R.PCR20μL0.4μmol·L-11μLDNA200nmol·L-1dNTP1×FastPfuBuffer.DNAPCR.PCR94℃2min95℃30s55℃30s72℃30s2572℃5min.2%.AxyPrepTMAXYGEN.1.3.3、DNAQuant-iTPicoGreendsDNAInvitrogenDNA30μLTE2XPicoGreen60μL.465~485nm515~575nmTurnerBiosystemsTBS-380.DNA.454GSFLXTitanium.0.03OTU.MOTHURUsearch4.0.38.Silva106.22.1DOA/OA/O.A、BAOMLSS3~4g·L-15~6g·L-1MLVSS/MLSS71%~75%.23、COD.HRTA、B2.CODCODA/O.BOD55mg·L-1A/O.HRT20hCOD30h.HRT20hACOD72.5mg·L-1±14.8mg·L-1B68.7mg·L-1±14.6mg·L-1COD2A、BTable2AnalysisoftheeffluentfromreactorAandBHRT/hCOD/mg·L-1BOD5/mg·L-1/mg·L-1/mg·L-1/mg·L-1/mg·L-1UV254A3077.2±14.52.7±1.11.2±1.49.2±2.111.7±2.10.8±0.30.61±0.022072.5±14.84.9±0.30.8±0.314.4±3.022.0±1.01.2±0.20.67±0.07B3078.9±17.03.4±2.41.0±0.610.1±2.312.5±2.91.0±0.30.63±0.022068.7±14.62.8±0.60.8±0.515.5±3.423.4±1.61.1±0.20.70±0.076062OA/O2、CODFig.2TimecourseofCODconcentrationsintheinfluentandeffluentandCODremovalefficiency3、Fig.3TimecourseofNH+4-NconcentrationsintheinfluentandeffluentandNH4-Nremovalefficiency67.0%68.8%TOC64.4%69.1%.DO.DOA.37063690%.2.2A、BCOD、NH+4-N、TNTP4.A、B.100%ACODA.CODO.OCOD.OTNAB4A、BCOD、NH4-N、TNTPFig.4ChangesinCODNH+4-NTNandTPconcentrationsatdifferentpartsofreactorsATNA.OO.ATN31%B26%BOATN.TN0.07mg·L-1..A/O、.BTPA39%34%.1.0mg·L-1《》.2.3A/O、SMP13.SMPCOD5、SMPFig.5ChangesinSMPcompositionintheinfluentandeffluent30%SMPCOD70%~75%.A、BSMP5.8062OA/O.61.3%48.9%16.5%.A、BDOAB20%.3D-EEM3、SMP14.A/OSMP.AB.2.4DOO3A、BO454.AceChao1OUT.ShannonSimpsonOUT.ShannonSimpson.3DOBDO.31Table3CharacteristicsofbacterialcommunitydiversitybasedondiversityindicesReadsOTUsAceChao1ShannonSimpsonA174232331496441926.310.007B152002408563743926.500.005197%OTUsO6.Proteobacteria、Planctomycetes、Bacteroidet