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当前位置:首页 > 商业/管理/HR > 质量控制/管理 > 采用强酸型阳离子交换树脂分离铝离子和磷酸盐贺子良
115Vol.11No.520175ChineseJournalofEnvironmentalEngineeringMay201751422813ZDRW-ZS-2015-5-42016-08-042016-09-191989—。E-mail1028337894@qq.com*E-mailliuruiping@rcees.ac.cn12122*1.3004002.100085Al3+Al3+。001×7Al3+。Al3+Al3+“S”ThomasAl3+。Al3+Al3+01000mg·L-14、610BV·h-1Al3+10mg·L-114.08、12.1611.09mg·g-1Al3+4300mg·L-116.50%、9.61%6.37%。4%HCl98.3%。Al3+。001×7X786A1673-9108201705-2640-06DOI10.12030/j.cjee.201608041SeparationofaluminumionsandphosphatebycationexchangeresinHEZiliang12WANGLijuan1ZHULijun2LIURuiping2*1.CollegeofCivilandTransportationEngineeringHebeiUniversityofTechnologyTianjin300400China2.KeyLaboratoryofDrinkingWaterScienceandTechnologyResearchCenterforEco-EnvironmentalSciencesChineseAcademyofSciencesBeijing100085ChinaAbstractTheproductiveprocessofthiophosphorylchloridewhichwasanimportantpesticideintermediatemayproducestrongacidwastewaterwithhighconcentrationofAl3+andphosphate.It’sofgreatsignificancetoa-chieveeffectiveseparationofAl3+andphosphateforrecoveryandutilization.Thisstudyfocusedontheaboveproblems.ThedynamicadsorptionexchangebehaviorofAl3+andphosphateinsingleandcoexistencesystemonthe001×7strongacidicstyrenecationexchangeresinwasresearched.Itwasfoundthattheresinhadgoodad-sorptionperformanceforAl3+.TheAl3+breakthroughcurveshowedatypical“S”typeandtheThomasmodelcouldbeusedtosimulatetheadsorptionprocessofAl3+effectively.WiththeinitialconcentrationofAl3+1000mg·L-1andtheflowratesof46and10BV·h-1thebreakthroughexchangecapacitywas14.0812.16and11.09mg·g-1respectively.ThepresenceofphosphatepromotedtheexchangeofAl3+.ThebreakthroughexchangecapacityofAl3+wasincreasedby16.50%9.61%and6.37%attheconcentrationofphosphate4300mg·L-1.The4%HClsolutioncouldbeusedasregeneratorachievinga98.3%ofregenerationrate.ItwasfeasibletoseparateandrecoverofAl3+andphosphatefromstrongacidwastewaterbyusingcationexchangeresinasscavenger.Keywordsstrongacidwastewaterphosphateradicalaluminumion001×7cationexchangeresinadsorption2014374.40t180%、。5。、2。Al3+、PO3-4。、10004300mg·L-1。。3Al3+Al3+27mg·L-1。4Al3+。5-6。。。、。、、7-9。、。、。001×7Al3+PO3-4PO3-4Al3+Al3+PO3-4。11.1。AlCl3·6H2OAl3+1000mg·L-1NaH2PO4·2H2OPO3-44300mg·L-1pH=2.385mol·L-1pH2.3。1001×7Fig.1Chemicalformulaofstronglyacidicstyrenetypecationexchangeresin001×711。1001×7Table1Mainparametersof001×7cationexchangeresinpH/mm/%/g·mL-11~140.3~1.245~550.75~0.8550%~100%、101mol·L-18h1mol·L-1NaOH8h48%。1.21.2.125.00g32.00mL20mm×H100mm、4、6、10BV·h-1Al3+PO3-4。q=C0-Ce·Vm1146211C0、Cemg·L-1VLmg。1.2.211ThomasAl3+2。。lnC0-C()C=lnexpk1QeM()F-[]1-k1C0t2C0mg·L-1Ctmg·L-1Qemg·g-1k1L·mg·h-1MgFL·h-1th。expk1QeM/F123lnCC0()-C=k1C0t-k1QeMF=k1C0t-QeMC0()F3lnC/C0-Ct4lnCC0()-C=kt-τ4τ=QeM/C0Fk=k1C0τC=C0/2h。1.2.32%、3%、4%、5%6BV·h-1。3BV1BV·h-15BVAl3+。1.3BT100-2JYZ1515X-AQUINTIX124-1CNpHOrionStarA211S-3000N。PO3-4/U3010Al3+ICP-OESAgilent710。22.12Al3+001×7Fig.2DynamicbreakthroughcurvesofAl3+onto001×7strongacidtypecationexchangeresinbedatdifferentflowrates24、610BV·h-1。pH=2.3Al3+0=1000mg·L-10=0mg·L-1。Al3+“S”。4BV·h-10~165minAl3+Al3+212minAl3+181.02mg·L-1285minAl3+。Al3+610BV·h-19552min4BV·h-116.71%35.02%。、Al3+。24625Al3+10mg·L-11。4BV·h-110BV·h-114.08mg·g-111.09mg·g-1。Al3+12Al3+13。Al3+。2ThomasAl3+4、610BV·h-1R20.994、0.9880.991。2ττThomasAl3+。2Al3+Table2DominantparametersinvolvedinremovalofAl3+bycationexchangebed/BV·h-1τ/minτ/min/min/min/mg·L-1/mg·L-1425325016528514.0819.2561591639519512.1619.2110102995213011.0919.182.23PO3-4001×7Fig.3DynamicbreakthroughcurvesofPO3-4onto001×7strongacidtypecationexchangeresinbedatdifferentflowrates3。pH=2.3Al3+0=0mg·L-10=4300mg·L-1。。4、610BV·h-11min3083.70、3612.79、3809.37mg·L-13min3973.67、4073.604203.75mg·L-1。4BV·h-150~110min4200.00mg·L-1300min100.00mg·L-1pH=2.3H3PO4142~4nmH3PO4-15。610BV·h-1。2.3Al3+Al3+4、610BV·h-14。Al3+10004300mg·L-1。Al3+Al3+“S”。。4、610BV·h-1Al3+5、32min42、3112min。Al3+16.50%、9.61%6.37%。3462114Al3+PO3-4001×7Fig.4DynamicbreakthroughcurvesofAl3+andPO3-4onto001×7strongacidtypecationexchangeresinbedatdifferentflowrates。1min1594.59、1771.472047.15mg·L-11489.11、1841.321762.22mg·L-1。Al3+15.92%、12.17%、5.81%。5001×7SEMFig.5SEMimagesfor001×7resin2.4Al3+pH=2.3H+H+13Al3+Al3+4。2pH2.3H3PO4—SO3H16。5a001×71。5b6bC、O、SAl31%5c6cC、O、SPP9%5d6dC、O、S、AlPAlP35%12%。2.572%、3%、4%5%。2%3%4%63.01%84.68%98.30%5%99.10%。4%Al3+2330.85mg·L-1Al3+2.3。17。446256001×7EDSFig.6EDSanalysisfor001×7resin7Fig.7SorptionefficiencyofsolutionofHCl3Al3+Al3+。Al3+Al3+。、Al3+、4%。Al3+Al3+。1.2014M.201514-222.J.198928483.J.201036638-414.J.2007294244-2465.J.201482735-7396CABIROLNBARRAGANEJDURANAetal.EffectofaluminiumandsulphateonanaerobicdigestionofsludgefromwastewaterenhancedprimarytreatmentJ.WaterScienceandTechnology2003486235-2407DABROWSKIAHUBICKIZPODKOSCIELNYPetal.Selectiveremovaloftheheavymetalionsfromwatersandindustrialwastewatersbyion-exchangemethodJ.Chemosphere200456291-1068PEHLIVANEALTUNT.ThestudyofvariousparametersaffectingtheionexchangeofCu2+Zn2+Ni2+Cd2+andPb2+fromaqueoussolutiononDowex50WsyntheticresinJ.JournalofHazardousMaterials20061341/2/3149-1569STEFANDSMEGHEAI.MechanismofsimultaneousremovalofCa2+Ni2+Pb2+andAl3+ionsfromaqueoussolutionsu-singPuroliteRS930
本文标题:采用强酸型阳离子交换树脂分离铝离子和磷酸盐贺子良
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