化工工程项目 制药 生物工程.docx
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化工工程项目制药生物工程
Microflowphoto-radicalreactionusingacompactlightsource:
applicationtotheBartonreactionleadingtoakeyintermediateformyricericacidA?
?
Tetrahedron
Graphicalabstract
OptimizationofphotocatalytictreatmentofdyesolutiononsupportedTiO2nanoparticlesbycentralcompositedesign:
Intermediatesidentification?
HazardousMaterials
OptimizationofphotocatalyticdegradationofC.I.BasicBlue3(BB3)underUVlightirradiationusingTiO2nanoparticlesinarectangularphotoreactorwasstudied.TheinvestigatedTiO2wasMillenniumPC-500(crystallitesmeansize5¨C10?
nm)immobilizedonnon-wovenpaper.CentralcompositedesignwasusedforoptimizationofUV/TiO2process.Predictedvaluesofdecolorizationefficiencywerefoundtobeingoodagreementwithexperimentalvalues(R2?
=?
0.9686andAdj-R2?
=?
0.9411).Optimizationresultsshowedthatmaximumdecolorizationefficiencywasachievedattheoptimumconditions:
initialdyeconcentration10?
mg/L,UVlightintensity47.2?
W/m2,flowrate100?
mL/minandreactiontime120?
min.PhotocatalyticmineralizationofBB3wasmonitoredbytotalorganiccarbon(TOC)decrease,andchangesinUV¨CvisandFT-IRspectra.ThephotodegradationcompoundswereanalyzedbyUV¨Cvis,FT-IRandGC¨Cmasstechniques.ThedegradationpathwayofBB3wasproposedbasedontheidentifiedcompounds.
ArticleOutline
1.Introduction
2.Experimental
2.1.Materials
2.2.Photocatalysisexperiments
2.3.Analyticalprocedures
2.4.Experimentaldesign
3.Resultsanddiscussion
3.1.CCDmodelandresidualsanalysis
3.2.Effectofvariablesasresponsesurfaceandcounterplots
3.3.DeterminationofoptimalconditionsfordecolorizationofBB3
3.4.PhotocatalyticmineralizationofBB3andanalysisofdegradationcompounds
4.Conclusions
Acknowledgements
Treatmentofphenolicwastewaterinananaerobicfixedbedreactor(AFBR)¡ªRecoveryaftershockloading?
?
Ananaerobicfixedbedreactor(AFBR)wasrunfor550dayswithamixedmicrobialfloratostabilizesyntheticwastewaterthatcontainedglucoseandphenolasmaincarbonsources.Theinfluentphenolconcentrationwasgraduallyincreasedfrom2to40?
mmol/lwithin221days.Themicrobialflorawasabletoadapttothishighphenolconcentrationwithanaverageof94%phenolremoval.Microbialadaptationatsuchahighphenolconcentrationisnotreportedelsewhere.Themaximumphenolremovalobservedbeforethephenolshockloadwas39.47?
mmol/lor3.7?
g?
phenol/latahydraulicretentiontime(HRT)of2.5daysandanorganicloadingrate(OLR)of5.3?
g/l.dwhichamountstoaphenolremovalrateofca.15.8?
mmolphenol/l.d.Thechemicaloxygendemand(COD)removalbeforeexposingthereactortoashockloadcorrespondedwithphenolremoval.Ashockloadwasinducedinthereactorbyincreasingthephenolconcentrationfrom40to50?
mmol/lintheinfluent.Themaximumphenolremovalrateobservedaftershockloadwas18?
mmol/l.dat5.7?
gCOD/l.d.ButthiswasnotastablerateandaconsistentdropinCODandphenolremovalwasobservedfor1week,followedbyasharpdeclineandproductionoffattyacids.Recoveryofthereactorwaspossibleonlywhennofeedwasprovidedtothereactorfor1monthandthephenolconcentrationwasincreasedgradually.Whenglucosewasomittedfromtheinfluent,unknownintermediatesofanaerobicphenolmetabolismwereobservedforsometime.
ArticleOutline
Nomenclature
1.Introduction
2.Materialandmethods
2.1.Reactordesignandinoculum
2.2.Analyticalmethods
3.Results
3.1.Microbialacclimatizationtohighphenolconcentrationinthereactor
3.2.Phenolshockloadingandrecoverypossibilities
3.3.ReactorperformanceintermsofCODremovalbeforeandafterphenolshockloading
3.4.Fattyacidandbiogasproduction
4.Discussion
5.Conclusions
Acknowledgements
Synthesisandhydrogenationof(E)-¦Ã-aryl-¦Ã-morpholino-¦Á-trifluoromethylatedallylalcoholsthroughthereactionoftrifluoroacetaldehydeethylhemiacetalwithenamines?
Treatmentoftrifluoroacetaldehydeethylhemiacetalwithenamines,derivedfromacetophenonederivatives,atroomtemperaturegave(E)-1,1,1-trifluoro-4-morpholino-4-aryl-but-3-en-2-ols,whichareintermediatesforpreparationofthe¦Â-trifluoromethylatedaldolproducts,4,4,4-trifluoro-3-hydroxy-1-aryl-butan-1-ones.Thestructureoftheintermediate(E)-1,1,1-trifluoro-4-morpholino-4-(4-nitrophenyl)-but-3-en-2-olscouldbeassignedby1H,13CNMR,IR,andX-raycrystallography.Furthermore,hydrogenationandreductivedeaminationoftheintermediate(E)-1,1,1-trifluoro-4-morpholino-4-aryl-but-3-en-2-olswithhydrogeninthepresenceofacatalyticamount(10?
mol?
%)ofpalladiumoncarbonintrifluoroethanolproceededsmoothlyatroomtemperaturetogive1,1,1-trifluoro-4-aryl-2-butanolsingoodtoexcellentyields.
Graphicalabstract
1.Introduction
2.Resultsanddiscussion
2.1.AssignmentofthestructureandreactivityoftheintermediateproductbyreactingCF3CHOethylhemiacetal1awithenamine2derivedfromacetophenones
2.2.Synthesisandhydrogenationof(E)-¦Ã-aryl-¦Ã-morpholino-¦Á-trifluoromethylatedallylalcoholsthroughthereactionofCF3CHOethylhemiacetalandenaminetogive4-aryl-1,1,1-trifluoro-2-butanols(5)
3.Conclusion
4.Experimentalsection
4.1.General
4.2.Preparationof(E)-1,1,1-trifluoro-4-morpholino-4-(4-nitrophenyl)but-3-en-2-ol(9j)
4.2.1.(E)-1,1,1-trifluoro-4-morpholino-4-(4-nitrophenyl)but-3-en-2-ol(3ac)
4.3.Atypicalprocedure
4.3.1.1,1,1-Trifluoro-4-phenylbutan-2-ol(5aa)17
4.3.2.1,1,1-Trifluoro-4-morpholino-4-phenylbutan-2-ol(6aa)
4.3.3.1,1,1-Trifluoro-4-p-tolylbutan-2-ol(5ad)
4.3.4.1,1,1-Trifluoro-4-(4-methoxyphenyl)butan-2-ol(5ae)
4.3.5.1,1,1-Trifluoro-4-(4-(trifluoromethyl)phenyl)butan-2-ol(5ag)
4.3.6.1,1,1-Trifluoro-4-m-tolylbutan-2-ol(5ah)
4.3.7.1,1,1-Trifluoro-4-o-tolylbutan-2-ol(5ai)
4.3.8.1,1,1-Trifluoro-4-(naphthalen-1-yl)butan-2-ol(5aj)
4.3.9.1,1,1-Trifluoro-4-(4-fluorophenyl)butan-2-ol(5ak)
4.3.10.1,1,1-Trifluoro-4-(4-fluorophenyl)-4-morpholinobutan-2-ol(6ak)
4.3.11.1,1-Difluoro-4-(naphthalen-1-yl)butan-2-ol(5bj)
4.3.12.1-(4,4-Difluorobutyl)naphthalene(7)
4.3.13.1-Butylnaphthalene(8)18
4.3.14.2,2,2-Trifluoro-1-(2-morpholinocyclohexyl)ethanol(6al)
Acknowledgements
Supplementarydata
ProgressinunderstandinganddevelopmentofBa0.5Sr0.5Co0.8Fe0.2O3?
¦Ä-basedcathodesforintermediate-temperaturesolid-oxidefuelcells:
Areview?
PowerSources
¹ÌÌåÑõ»¯ÎïȼÁϵç³Ø¿ª·¢»Ø¹ËÖÆÔ칤ÒÕ¹ý³ÌÖмäÌåÓëζȿØÖƼ¼Êõ²¬îÜÌúïÈ»¯ºÏÎï
Solid-oxidefuelcells(SOFCs)convertchemicalenergydirectlyintoelectricpowerinahighlyefficientway.LoweringtheoperatingtemperatureofSOFCstoaround500¨C800?
¡ãCisoneofthemaingoalsincurrentSOFCresearch.Theassociatedbenefitsincludereducingthedifficultiesassociatedwithsealingandthermaldegradation,allowingtheuseoflow-costmetallicinterconnectorsandsuppressingreactionsbetweenthecellcomponents.However,theelectrochemicalactivityofthecathodedeterioratesdramaticallywithdecreasingtemperatureforthetypicalLa0.8Sr0.2MnO3-basedelectrodes.Thecathodebecomesthelimitingfactorindeterminingtheoverallcellperformance.Therefore,thedevelopmentofnewelectrodeswithhighelectrocatalyticactivityforoxygenreductionbecomesacriticalissueforintermediate-temperature(IT)-SOFCs.Ba0.5Sr0.5Co0.8Fe0.2O3?
¦Ä(BSCF)perovskiteoxidewasfirstreportedasapotentialIT-SOFCcathodematerialin2004byShaoandHaile.Afterthat,theBSCFcathodehasattractedconsiderableattention.ThispaperreviewsthecurrentresearchactivitiesonBSCF-basedcathodesforIT-SOFCs.EmphasiswillbeplacedontheunderstandingandoptimizationofBSCF-basedmaterials.TheissuesraisedbytheBSCFcathodearealsopresentedandanalyzedtoprovidesomeguidelinesinthesearchforthenewgenerationofcathodematerialsforIT-SOFCs.
ArticleOutline
1.Ageneralintroduction
2.Perovskiteoxides
3.OriginationofBSCF
4.ApplicationsofBSCFasthecathodeofIT-SOFCs
4.1.BSCFcathodesonvariouselectrolytes
4.2.SynthesisofBSCFpowder
4.3.Morphologyofthecathode
4.4.Intheapplicationofsingle-chamberSOFCs
5.FundamentalunderstandingofBSCF
5.1.Massandchargetransportinmixedconductingoxides
5.2.Electrochemicalprocessesatsolid-oxidefuelcell(SOFC)cathodes
5.3.OxygensurfaceexchangeandbulkdiffusioninBSCF
5.4.Rate-determiningstepinORRonBSCFcathodeoperatedbelow600?
¡ãC
6.OptimizationoftheBSCFcathode
6.1.EnhancementofORRontheBSCF
6.1.1.BSCF-electrolytecompositecathode
6.1.2.Surfacemodification
6.2.Thermalexpansionbehavior
6.3.A-orB-sitedopingofBSCF
7.NewissuesraisedbyBSCF
8.Summaryandoutlook
Acknowledgements
Highlyefficientandsafeprocedureforthesynthesisofaryl1,2,3-triazolesfromaromaticamineinacontinuousflowreactor?
?
TetrahedronLetters
Graphicalabstract
TheLetterreportsasafeandreliablesynthesisofaryl1,2,3-triazolesfromthecorrespondinganilinesviaintermediatearylazides,usingacontinuousprocess.Themethodwasappliedtoavarietyofsubstrateswithgoodtoexcellentyields,withouttheneedtoisolatethereactiveandpossiblyunstableintermediateswhichwereconstantlykeptatlowconcentrationinthematrixenvironment.
΢·´Ó¦Æ÷£¬Á¬ÐøÁ÷¶¯Ç⻯·´Ó¦£¬Ç⻯¹Ì¶¨´²µÄÓ¦Ó÷½°¸
Determinationoffastozoneoxidationratefortextiledyesbyusingacontinuousquench-flowsystem?
HazardousMaterials
Tostudythefastkineticdecolourisationoftextiledyesbyozoneacontinuousquench-flowsystemwasused.Thissystemhasnotbeenusedbeforeforthesepurposes.Reactiontimesintherangeof7¨C3000?
mswereexplored.Thereactionwasquenchedwithpotassiumiodide,whichproved