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当前位置:首页 > 建筑/环境 > 工程监理 > 化学沉淀法去除稀土湿法冶炼废水中钙与高浓度氨氮研究王浩
34720137ENVIRONMENTALSCIENCEVol.34No.7Jul.20131212*11212121.5410042.541004Ca2+Ca2+.Na2CO3CaCO3Ca2+MAP..SEMXXRD.nCa2+∶nCO2-3=1∶1.051500r·min-130minCa2+100%pH=9.03nMg∶nN=1.20nP∶nN=1.130min1000r·min-195.40%5.65mg·L-1CaCO3MgNH4PO4·6H2O.XX703.1A0250-3301201307-2718-112012-10-252013-01-061201Z0281987~E-mailjasson1124@163.com*E-mail1986017@glut.edu.cnRemovalofCalciumandHigh-strengthAmmoniaNitrogenfromtheWastewaterofRare-earthElementsHydrometallurgicalProcessbyChemicalPrecipitationWANGHao12CHENGGuan-wen12SONGXiao-wei1XUZi-han12MENGJin-jie12DONGChuan-qiang121.CollegeofEnvironmentalScienceandEngineeringGuilinUniversityofTechnologyGuilin541004China2.GuangxiKeyLaboratoryofEnvironmentalPollutionControlTheoryandTechnologyGuilinUniversityofTechnologyGuilin541004ChinaAbstractAlotofhigh-strengthammonianitrogenwastewaterisgeneratedintheion-typerare-earthelementshydrometallurgicalprocess.MagnesiumammoniumphosphateMAPprecipitationwaschosentoremovetheammonianitrogenfromthewastewaterafterCa2+waseliminatedusingNa2CO3togenerateCaCO3precipitatebecausethewastewatercontainedalotofCa2+andCa2+wasanimportantimpactfactorforMAPprecipitation.CentralcompositedesignCCDisaprincipalresponsesurfacemethodologyRSMusedinexperimentaldesign.ResponsesurfacemethodologyRSMwasusedtooptimizethefactorsinMAPprecipitationachievingtheoptimalconditionsandtheprecipitatesundersuchconditions.TwokindsofprecipitateswereanalyzedbyscanningelectronmicroscopeSEMandX-raydiffractionXRD.TheresultsshowedthatwhennCa2+∶nCO2-3=1∶1.05mixrateandreactiontimewere1500r·min-1and30minrespectivelytheremovalratioofCa2+reached100%theoptimalconditionofMAPprecipitationwaspH=9.03nMg∶nN=1.20nP∶nN=1.1withareactiontimeof30minandamixrateof1000r·min-1theremovalratioofammonianitrogenreached95.40%andtheresidualtotalphosphorusconcentrationwas5.65mg·L-1.SEMandXRDanalysisshowedthatthetwokindsofprecipitateswerepureCaCO3andMgNH4PO4·6H2Orespectively.KeywordsmagnesiumammoniumphosphateMAPresponsesurfacemethodologyRSMCa2+removalrare-earthwastewaterSEMXRD1MAP2、3、4.MAP.5.267、8、9、10.MAPCa2+MAP11Ca2+.RSMDOI:10.13227/j.hjkx.2013.07.045712~14.CaCO3MAPRSM、、.11.11、、COD、.1.2CaCO3.Na2CO3CaCO3.300mLnCa2+∶nCO2-3Na2CO330min0.45μmCa2+.1Table1Maincompositionsoftheinvestigatedrare-earthwastewaterpHNH+4-N/mg·L-1CODOH-KI/mg·L-1TP/mg·L-1Cl-/mg·L-1Ca2+/mg·L-1Mg2+/mg·L-1Cu/mg·L-1Zn/mg·L-1Fe/mg·L-1Mn/mg·L-1NO-3/mg·L-1CH3COO-/mg·L-1/μS·m-1/NTU2.3844209820314337573529394.865.728.593.23201299534.32×10547.31.3MAPpH、nMg∶nN、nP∶nN、54Na2HPO4·12H2OMgCl2·6H2ONH+4-NTP..1.4RSMcentralcompositedesignCCDRSM.CCD2k2kn0.pHA、nMg∶nNB、nP∶nNCD4.k=4N=2k+2k+n024+2×4+6=301516NH+4-NY1TPY2.Y=b0+b1A+b2B+b3C+b4D+b12AB+b13AC+b14AD+b23BC+b24BD+b34CD+b11A2+b22B2+b33C2+b44D21Yb0bibiibijA、B、C、D4.Design-Expert8.0.6.1.5.NH+4-NTPCOD.DDSJ-308WGZ-800.DIONEXICS-1000Perkin-ELmerAAnalyst700.MAPJSM-6380LVX'PertPROX.22.1Ca2+MAP、、、ρNH+4-N4420mg·L-1、ρCH3COO-9953mg·L-1ρCa2+0、5000、10000、20000、4000080000mg·L-1NH+4-N4.32×105μS·m-1HClpH2.4300mLnMg∶nN∶nP=1∶1∶1MgCl2·6H2ONa2HPO4·12H2O30min30minNH+4-N.1Ca2+NH+4-NCa2+93.52%50%Ca2+MAP.Na2HPO4·12H2OCa2+PO3-4Mg2+NH+4PO3-4NH+4-N.2.2Ca2+MAPNH+4-NMAP9172341Ca2+MAPFig.1EffectofCa2+ontheammonianitrogenremovalbyMAPprecipitationCa2+MAP..2.2.1Ca2+nCa2+∶nCO2-31∶1、1∶1.01、1∶1.02、1∶1.03、1∶1.04、1∶1.05、1∶1.06、1∶1.07、1∶1.1Na2CO32000r·min-130minCa2+nCa2+∶nCO2-32.Na2CO3Ca2+nCa2+∶nCO2-3=1∶197.47%nCa2+∶nCO2-3=1∶1.0599.9%.CO2-3Ca2+.2nCa2+∶nCO2-3Ca2+Fig.2EffectofnCa2+∶nCO2-3ontheremovalratioofCa2+2.2.2nCa2+∶nCO2-3=1∶1.05、30min3.Ca2+1500r·min-1Ca2+99.9%.CO2-330minCa2+Ca2+.1500r·min-1.2.2.34.20minCa2+99.5%30minCa2+100%.CO2-330minCa2+30min.2.2.4Ca2+nCa2+∶nCO2-3=1∶1.051500r·min-130min.Ca2+99.99%.350℃48hSEMXRD.55000CaCO36XCaCO3.Na2CO3Ca2+MAP.3Ca2+Fig.3EffectofmixrateontheremovalefficiencyofCa2+2.3MAPMAP.Na2CO3pH027274Ca2+Fig.4EffectofreactiontimeontheremovalefficiencyofCa2+5Fig.5SEMpictureoftheprecipitateformedundertheoptimalconditionsofCa2+removal6XFig.6XRDpictureoftheprecipitateformedundertheoptimalconditionsofCa2+removalNH+4-NNH+4-N3189.30mg·L-1.2.3.1pH7.pHNH+4-NpH=10NH+4-N89.53%TP36.42mg·L-1Ohlinger17pH=10.3.pHNH+4-NNH+4-N18pH>10Na2HPO4·12H2OPO3-4Mg3PO42Ksp=1.0×10-24MgNH4PO4Ksp=2.5×10-131920Mg3PO42MgNH4PO421MgNH4PO4.MAPpH9~10.7pHFig.7EffectofpHontheremovalofammonianitrogenandphosphorus2.3.2nMg∶nN8nMg∶nNFig.8EffectofnMg∶nNontheremovalofammonianitrogenandphosphorus8.nP∶nN=1∶1nMg∶nNNH+4-NnMg∶nN=1∶188.98%TPnMg∶nN=1∶140.42mg·L-1nMg∶nN>1.2∶1TP4mg·L-1.nMg∶nN1∶1Mg2+MAPnMg∶nN>1∶1Mg2+127234NH+4-NMg2+Mg2+NH+4、PO3-4PO3-4.NH+4-NMg2+nMg∶nN1∶1~1.2∶1.2.3.3nP∶nNnMg∶nN=1∶1nP∶nNNH+4-NTP9.nP∶nN<1∶1NH+4-NnP∶nNnP∶nNPO3-4NH+4-NNH+4-NPO3-4TPnP∶nN>1∶1NH+4-N91%TP.PO3-4.nP∶nN0.9∶1~1∶1.9nP∶nNFig.9EffectofnP∶nNontheremovalofammonianitrogenandphosphorus2.3.410.NH+4-N30minTP.20minMAP30min.2.3.511.NH+4-NTPNH+4-N90%~92%TP41~44mg·L-11000~1500r·min-1.MAP.1000~1500r·min-1.10Fig.10Effectofreactiontimeontheremovalofammonianitrogenandphosphorus11Fig.11Effectofmixrateontheremovalofammonianitrogenandphosphorus2.4Design-Expert8.0.6NH+4-NTPNH+4-N3DNH+4-NTP.NH+4-NTPNH+4-NTPNH+4-NTP22.2.4.123.NH+4-
本文标题:化学沉淀法去除稀土湿法冶炼废水中钙与高浓度氨氮研究王浩
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