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3511201411ENVIRONMENTALSCIENCEVol.35No.11Nov.2014Fe2+Fe3+1212*1212121.2150092.215009Fe.05mg·L-15mg·L-1..71Fe2+R10.28kg·m3·d-10.65kg·m3·d-1Fe3+R21.28.Fe2+.Fe3+R21.17Fe2+R11.24.X703.1A0250-3301201411-4224-06DOI10.13227/j.hjkx.2014.11.0262014-04-042014-05-2951408387201104XKY2011031984~E-maillixiang@mail.usts.edu.cn*E-mailyhuang@mail.usts.edu.cnEffectofFe2+andFe3+ontheActivityofANAMMOXLIXiang12HUANGYong12WUChuan12WANGMeng-ke12YUANYi121.SchoolofEnvironmentalScienceandEngineering.SuzhouUniversityofScienceandTechnologySuzhou215009China2.InstituteofEnvironmentalBiotechnologySuzhouUniversityofScienceandTechnologySuzhou215009ChinaAbstractTheeffectofthechangeinconcentrationandvalenceofironionontheANAMMOXsludgeactivitywasstudiedbyinoculatingANAMMOXsludge.TheconcentrationexperimentalresultsshowedthattheANAMMOXsludgeactivitywasstimulatedandgraduallyincreasedwhentheinfluentironionconcentrationincreasedfrom0to5mg·L-1.IronhydroxideprecipitatewasformedwiththepHvalueincreasedduetothealkalinityoftheANAMMOXproductwhentheinfluentironionconcentrationwashigherthan5mg·L-1whilethebiologicalactivitywasnotinhibited.TherewasnosignificantdifferenceintheeffectsoftheconcentrationchangeofironionswithdifferentvalenceeffectsontheANAMMOXsludgeactivity.Thelong-termexperimentalresultsshowedthatthenitrogenremovalrateasNofanammoxreactorR1wasincreasedfrom0.28kg·m3·d-1to0.65kg·m3·d-1withFe2+ininfluentwhichwas1.28timesashighasthatintheANAMMOXreactorR2containingFe3+ininfluentafter71cyclesofcultivation.ThereforeFe2+couldbettermeetthegrowthneedsofANAMMOXbacteria.TheresultsalsoshowedthatFe3+easilyledtotheexcessiveconversionofammoniaintheANAMMOXreactor.Theconversionratiobetweennitrateandammoniawas1.17inreactorR2whichwassignificantlylowerthanthatinthereactorR1withaconversionratiobetweennitrateandammoniaof1.24.KeywordsANAMMOXironionvalencereactionprocesseffectNH+4-NNO-2-N..1.2~4.、pH、、5~8.、9.daGraaff10Ca2+..vanNiftrik11Fe.12Strous13Fe.FeFe11Fe2+Fe3+.Fe.Fe2+Fe3+FeFe3+.Fe.Fe.11.1100mL500mL.5cm.32℃pH6.5~6.60.1mol·L-1pHFe.1.2200814.NH+4-N、NO-2-N98%20kg·m3·d-1.0.5~2mmMLVSS/MLSS0.7~0.8.1.3.NH4Cl、NaNO2、NaHCO31000mg·L-1、KHCO31000mg·L-1、KH2PO427mg·L-1、CaCl2·2H2O136mg·L-1、MgSO4·7H2O200mg·L-1、Ⅰ1mL·L-1Ⅱ1.25mL·L-1.ⅠEDTA5000mg·L-1ZnSO4·7H2O430mg·L-1CoCl2·6H2O240mg·L-1MnCl2·4H2O990mg·L-1CuSO4·5H2O250mg·L-1NaMoO4·2H2O220mg·L-1NiCl2·6H2O190mg·L-1NaSeO4·10H2O210mg·L-1H3BO414mg·L-1ⅡEDTA5000mg·L-1FeSO4FeCl3Fe2+Fe.30min.1.4《》15.NH+4-NNO-2-NN-1-NO-3-NpHpH21119Fe2+、Fe3+.1.5Fe2+、Fe3+Fe242g.100mL8h5%1.251.331.21.2812Fe.Fe2.Fe2+Fe3+94.2mg·L-1、128mg·L-110hFe2+、Fe3+.Fe2500mL10gR1、R2.R1Fe2+R2Fe3+.10g10h.Fe.22.1Fe2+Fe3+Fe2+Fe3+1.1aFe2+.Fe2+0mg·L-15mg·L-150.47mg·L-166.37mg·L-117.57mg·L-129.51mg·L-1..16FeSO40.1mol·L-1Fe2+5.6mg·L-1.12Fe5224350.075mmol·L-14.2mg·L-1Fe0.03mmol·L-11.68mg·L-1Fe.Fe2+5mg·L-165mg·L-117.99mg·L-130.86mg·L-1Fe.1Fe2+Fe3+Fig.1EffectofthechangeinFe2+andFe3+concentrationonnitrogenremovalefficiencyofANAMMOXsludgeFe3+Fe2+1b.Fe3+05mg·L-150.4mg·L-166.6mg·L-116.66mg·L-129.56mg·L-1Fe3+.Fe3+5mg·L-165mg·L-116.46mg·L-133.88mg·L-1Fe.3、9.Fe.FeFeFe.Fe5mg·L-1Fe5~6mg·L-1.FeFeOH3FeOH2FeOH32.64×10-39.OH-pH.Fe.Fe2+Fe3+.2.2Fe2+Fe2+Fe2+5mg·L-1Fe2+Fe2+5.05~5.08mg·L-1.2R1100.2mg·L-1128mg·L-146.1mg·L-154.4mg·L-10.28kg·m3·d-1.622411Fe2+Fe3+R1.R13598%0.47kg·m3·d-1.R136120mg·L-1150mg·L-12.6mg·L-17mg·L-10.56kg·m3·d-1.R160140mg·L-1175mg·L-10.76kg·m3·d-1.126.58mg·L-17.5mg·L-129.55mg·L-10.65kg·m3·d-1.2Fe2+Fig.2Long-timeeffectofFe2+onnitrogenremovalefficiencyofANAMMOX2.3Fe3+Fe3+Fe3+5mg·L-1.3100.2mg·L-1128mg·L-146.75mg·L-166.6mg·L-10.29kg·m3·d-1.57R295.2mg·L-1122mg·L-17.2mg·L-116.5mg·L-10.43kg·m3·d-1.R258120mg·L-1150mg·L-10.65kg·m3·d-1.R27112.9mg·L-123.5mg·L-10.51kg·m3·d-1R10.78.Fe3+Fe2+.3Fe3+Fig.3Long-termeffectofFe3+onnitrogenremovalefficiencyofANAMMOX33.1FeStours131.320.2617.Fe2+Fe3+4.Fe2+R11.240.22Strous18.1920.Fe3+R21.170.19.Fe3+R2Fe2+R1.12Fe2+1.02~1.15..Fe2+.Fe2+Fe3+Fe3+.Shrestha21722435NH+4Fe3+N2.R2.R2Fe3+.4Fe2+Fe3+Fig.4EffectofFe2+andFe3+onnitrogenconversionratioofANAMMOX3.2FeFe..Zhu22Rhodobactersphaeroides3.2mg·L-1.Wei23Fe3+Fe3+Fe3+1.6~3.3C...2682425.Fe.Zhang26Fe2+.Fe2+.Fe2+Fe3+.5mg·L-1.Strous181.8mg·L-1.pHFe.Fe.Fe2+Fe3+FeFe3+.FeFe3+.Fe2+Fe3+.Fe3+Fe2+.41Fe2+Fe3+Fe.Fe05mg·L-1.Fe5mg·L-1OH-FeFe.2Fe71Fe2+0.28kg·m3·d-10.65kg·m3·d-1、1.240.22Fe3+0.29kg·m3·d-10.51kg·m3·d-11.170.19.Fe2+.1.J.20133392359-2368.2.J.20132761078-1083.822411Fe2+Fe3+3LiHSZhouSQMaWHetal.Faststart-upofANAMMOXreactorOperationalstrategyandsomecharacteristicsasindicatorsofreactorperformanceJ.Desalination2011286436-441.4LvYTWangLWangXDetal.MacroscaleandmicroscaleanalysisofANAMMOXinanaerobicrotatingbiologicalcontactorJ.JournalofEnvironmentalSciences201123101679-1683.5LottiTvanderStarWRLKleerebezemRetal.TheeffectofnitriteinhibitionontheANAMMOXprocessJ.WaterResearch20124682559-2569.6ChenJWZhengPTangCJetal.EffectoflowpHontheperformanceofhigh-loadedANAMMOXreactorJ.JournalofChemicalEngineeringofChineseUniversities2010242320-324.7JungJYKangSHChungYCetal.Factorsaffectingtheactivityofanammoxbacteriaduringstartupinthecontinuousculturereactor
本文标题:Fe2和Fe3对厌氧氨氧化污泥活性的影响李祥
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