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31420188EnvironmentalScienceandTechnologyVol.31No.4Aug.2018:2018-04-13:(1988-),,,,,.,,,(,201507):,。、、、、、、3.5%,。,。:;;;;:X5:A:1674-4829(2018)04-0074-05TheLatestProgressofTreatmentTechnologyforHighSalinityWastewaterLIJun-hu,ZHOUMin,WANGQiao,CHENChun-yue(ShanghaiChemicalIndustryParkSinoFrenchWaterDevelopment,Shanghai201507,China)Abstract:Thesource,compositionandcharacteristicsofhighsalinitywastewaterwhichcontainsTDSmorethan3.5%arebrieflyintroducedinthispaper.Thelatesttreatmentprogressofvarioushighsalinitywastewatersuchasbiologicaltreatment,adsorption,extraction,incineration,electrochemicaloxidation,Fentonoxidation,wetcatalyticoxidationisreviewed.Thefuturedevelopmentdirectionofthehighsalinitywastewatertreatmentprocesshasbeenpointedout.Keywords:Salinitywastewater;Halophilicbacteria;Advancedoxidation;Adsorption;Extraction0,,。,(NaCl)1%[1-2];3.5%()[3-4]。2:①、、、、,,,、、、,[5-6];②,,,,,,,[7]。,,,[8]。,。,33.5%。1,,,,[9],。,3.5%,1%,314,,,,,[10]。,[11]。TAN[12],3。,3.7%5.7%,220mg/L1100mg/L。,90%。,。[13]33∶2∶1,48hCODCr81.85%,。FERRER-POLONIO[14]SBRNaCl80g/L,SBR,P.persalinus,20.9±3.1℃,22.5±7.5d,MLVSS3292±532mg/L,CODCr425.6±66.2mg/L,12.2±1.6mg/L,CODCr79.9%±2.9%。2,,,,,,,。、,,[15]。2.1,,,,,,[16]。[17]3.6%,P507/,pH8~9,1∶10,60min,95%,CODCr76%,。GUO[18]。12h,87.9%,,68.1%,。2.2,,。、,,[19]。[20]HYA-10618.9~38.9g/LTNT。pH3.0,1.0BV/h,0.5%NaOH+(V/V=4∶1),2.0BV/h,CODCr272.5mg/g,,。CHEN[21]NAD-150NaCl146.1g/LNa2CO31.5mol/L,NAD-150400mg/g。,。,,,,,,,。2.3,,7520188,,,,,[22]。JORFI[23],4%,pH5,0.5A,(,××12×3×0.3cm)2cm,CODCr94%,TDS,CODCr。,,,,。[24](NaCl15%),Ti/SnO2,Ti/β-PbO2,Ti/RuO2,Ti/RuO2,,。,,,。71mA/cm2,7h,98%,134mA/cm2,4h,98%,,。2.4,Fe2+H2O2。2.80V,,,[25]。,。SHI[26]NaCl20%,pH3,Fe2+25mmol/L,H2O2500mmol/L,m(Fe2+)∶m(H2O2)=1∶20,120min,TOC62.50%,Fenton,TOC89.27%,。PENG[27],0.1mol/L,,。(NaCl292.2g/L),40%。(HA)(BQ),60%,。2.5,[28]。[29]NaCl18.5%,200℃,5g/L,2h,TOC94.7%。。[30]166g/L,280℃、60min、Fe2+100mg/LTOC97.9%。t470.2。,,,,。,。2.6,,,[31]。[32]6%31,0.7MPa、1.2V,15A,pH6,/Sb-N-TiO2/Sb-SnO2/A/Al2O399%,,,,。[33],,,CODCr,CODCr。NaCl5%,,0.05mol/L,CODCr95%。5%76314,,0.05mol/L,CODCr90%。,,,。,,。。2.7800~1000℃,,,。,,,ρ(CODCr)≥100000mg/L,≥2500×4.1868kJ/kg10%[34]。[35]20%,,600℃,1100℃,4s,550kg/h,6900Pa,1.23%,。,,,,,。,,,。、1。1、(),,,。,,,,,。,,,,。,,,,。,,,,。,,,。,,,。,,,,。,,,,。,,。,。,,。,SS,。,,,,,,。,,,,。,,,,。3。,,,。,,,。,。,,,,,,。[][1],,.[J].,2002,22(11):1-4.[2],,,.SBBR[J].,2010,29(4):281-284.[3]WOOLARDCR,IRVINERL.Treatmentofhypersalinewast-ewaterinthesequencingbatchreactor[J].Waterresearch,1995,29(4):1159-1168.[4]LPEZDE,TREMBLYJP.Desalinationofhypersalinebrineswithjoule-heatingandchemicalpre-treatment:Conceptualdesignandeconomics[J].Desalination,2017,415:49-57.[5]SOLTANIRDC,JORFIS,RAMEZANIH,etal.UltrasonicallyinducedZnO-biosilicananocompositefordegradationofatextiledyeinaqueousphase[J].Ultrasonicssonochemistry,2016,28:69-78.[6]OGDENDD,TREMBLYJP.Dsesalinationofhypersalinebri-nesviaJouleheating:Experimentalinvestigationsandcompar-isonofresultstoexistingmodels[J].Esalination,2017,(424):149-158.[7]ZHOUW,LIY,GAOY,etal.NutrientsremovalandrecoveryfromsalinewastewaterbySpirulinaplatensis[J].Bioresourcetechnology,2017,245(PtA):10-17.7720188[8]GAGLIANOMC,LSMAILSB,AJMS,etal.Biofilmformationandgranulepropertiesinanaerobicdigestionathighsalinity[J].Waterresearch,2017,121:61-67.[9]MIRBOLOOKIH,AMIRNEZHADR,PENDASHTEHAR.Treatmentofhighsalinetextilewastewaterbyactivatedsludgemicroorganisms[J].Journalofappliedresearch&technology,2017,15(2):167-172.[10]PRADHANS,FANL,RODDICKFA,etal.ImpactofsalinityonorganicmatterandnitrogenremovalfromamunicipalwastewaterROconcentrateusingbiologicallyactivatedcarboncoupledwithUV/H2O2[J].Waterresearch,2016,94:103-110.[11],.[J].,2002,24(5):293-296.[12]TANS,CUIC,HOUY,etal.Cultivationofactivatedsludgeusingseamudasseedtotreatindustrialphenolicwastewaterwithhighsalinity[J].Marinepollutionbulletin,2016,114(2):867-870.[13],,,.[J].,2015,44(11):33-39.[14]FERRER-POLONIOE,PEREZ-UZB,MENDOZA-ROCAJA,etal.Biologicaltreatmentofhypersalinewastewaterfromtableoliveprocessing:processperformanceandprotistpopulationunderdifferentoperatingconditions[J].Journalofindustrial&engineeringchemistry,2017,56:364-374.[15]LABIADHL,FERNANDESA,CIRIACOL,etal.Electroch-emicaltreatmentofconcentratefromreverseosmosisofsanitarylandfillleachate[J].Journalofenvironmentalmanagement,2016,181:515-521.[16].[D].:,2016.[17],,.[J].,2016,24(2):14-17.[18]GUOP,HUAL,HONG-RUIMA,etal.Effectsofmonocarb-oxylicacidsstructureparametersonperstractionbytwokindsofsiliconerubbermembrane[J].Finechemicals,2016,33(8):915-920.[19]JORFIS,DARVISHICSR,AHMADIM,etal.Sono-assistedadsorptionofatextiledyeonmilkvetch-derivedcharcoalsupportedbysilicananopowder[J].Journalofenvi-ronmentalmanagement,2017,187:111-121.[20].———TNT[D].:,2016.[21]CHENJD,XIONGWL,TANGJQ,etal.Adsorptionbehaviorofbenzylalcoholonhyper-crosslinkedNAD-150Resin[J].Journalofwuhaninstituteoftechnology,2017,39(1):19-24.[22]JAAFARZADEHN,GHANBARIF,AHMADIM,etal.Efficientintegratedprocessesforpulpandpaperwastewatertreatmentandphytotoxicityreduction:Permanganate,Electro-FentonandCo3O4/UV/peroxymonosulfate[J].Chemicalengineeringj
本文标题:高盐废水处理工艺最新研究进展李俊虎
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