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Applied Surface Science
j o ur na l ho me pa g e :w w w . e l s e v i e r . c o m / l o c a t e / a p s u s c
Cyclodextrin-grafted electrospun cellulose acetate nanofibers via
“Click” reaction for removal of phenanthrene
Asli Celebioglu
a,b, Serkan Demirci
a,c, Tamer Uyar
a,b,∗aUNAM-NationalNanotechnologyResearchCenter,BilkentUniversity,Ankara06800,Turkey
bInstituteofMaterialsScienceandNanotechnology,BilkentUniversity,Ankara06800,Turkey
cDepartmentofChemistry,FacultyofArtsandSciences,AmasyaUniversity,Amasya05100,Turkey
a r t i c l e i n f o
Articlehistory:
Received23January2014
Receivedinrevisedform17March2014 Accepted21March2014
Availableonline29March2014
Keywords:
Electrospinning Nanofibers Cyclodextrin
“Click”reaction Phenanthrene Filtration
a b s t r a c t
Beta-cyclodextrin(-CD)functionalizedcelluloseacetate(CA)nanofibershavebeensuccessfullypre- paredbycombiningelectrospinningand“click”reaction.Initially,-CDandelectrospunCAnanofibers weremodifiedsoastobeazide--CDandpropargyl-terminatedCAnanofibers,respectively.Then,“click”
reactionwasperformedbetweenmodifiedCDmoleculesandCAnanofiberstoobtainpermanentgraft- ingofCDsontonanofiberssurface.ItwasobservedfromtheSEMimagethat,whileCAnanofibershave smoothsurface,thereweresomeirregularitiesandroughnessatnanofibersmorphologyafterthemodi- fication.Yet,thefibrousstructurewasstillprotected.ATR-FTIRandXPSrevealedthat,CDmoleculeswere successfullygraftedontosurfaceofCAnanofibers.Theadsorptioncapacityof-CD-functionalizedCA (CA-CD)nanofiberswasalsodeterminedbyremovingphenanthrene(polycyclicaromatichydrocarbons, PAH)fromitsaqueoussolution.OurresultsindicatethatCA-CDnanofibershavepotentialtobeusedas molecularfiltersforthepurposeofwaterpurificationandwastewatertreatmentbyintegratingthehigh surfaceareaofnanofiberswithinclusioncomplexationpropertyofCDmolecules.
©2014ElsevierB.V.Allrightsreserved.
Introduction
Electrospunnanofibers/nanowebspossessseveraluniqueprop- ertiesthatmakethemgoodcandidateforthefiltration,separation andcleaningapplications,suchas;largespecificsurfacearea,highly porousstructure withnanosizerange,highdegreeofintercon- nectionandmodifiablenature[1–5].Thepotentialofnanofibrous structureforfiltrationpurposeshasbeenreportedinliteratureby showingseparationoftinyparticles,filtrationofliquidmedium [4–6]andwastevaportreatment[3,7,8].Even,productionvariabil- ity,low-costandhighout-putofthistechniquemakepossiblethe filtrationperformancetoenterintocompetitionwithconventional filtrationsystems.Moreover,electrospunnanofibersfacilitatefor chemical/physicalfunctionalizationsthatcanleadstobetteruptake performanceduringthefiltrationprocess[9–13].
Cyclodextrins(CDs)arenaturalcyclicoligosaccharideswhich areregeneratedbytheenzymaticdegradationofstarch.Thereare threenativetypesofCDmolecules;␣-CD,-CDand␥-CDwhichare consistedofsix,sevenandeightglucopyranosesubunits,respec- tively[14,15].CDshavetoroid-shapedmolecularstructurewitha
∗ Correspondingauthor.Tel.:+903122903571;fax:+903122664365.
E-mailaddresses:tamer@unam.bilkent.edu.tr,tameruyar@gmail.com(T.Uyar).
relativelyhydrophobicinteriorcavity.Duetotheintriguingmolec- ularstructure,CDsareabletoforminclusioncomplexes(CD-IC) withavarietyofmoleculesalongwithnon-covalentinteractions [14,15].TheinclusioncomplexationwithCD moleculesenhance solubility,stabilityandbioavailabilityofguestmolecules.So,these CD-ICsupramolecularstructuresarequiteapplicableinpharma- ceuticals,foods,cosmetics,home/personalcareandtextilesareas [14–16].Additionally,filtrationandseparationsystemsareanother applicationfieldsforCDmoleculesowingtotheircapturingcapa- bilityofhazardousorganicmoleculesbyinclusioncomplexation [17–20].
CD moleculesare commonly utilizedin theform ofpowder orcrosslinkedpolymericgranules[14–16,20].Unfortunately,this statecancauselimitationduringtheirusage.So,tobenefitfrom CDsuniquepropertiesmoreefficientlyandrenderthemintomore applicableform,theycanbecombinedwithpolymericmatrix.In ourpreviousstudies,wehavephysicallyblendedCDmoleculesinto polymericnanofibersbyelectrospinning[7,21,22].Itwasobserved that,whilemostoftheCDmoleculeswereembeddedinsidethe nanofibers,someofthemwerelocatedonthefibersurfaceand theseaccessibleCDenabletheremovaloforganicwastemolecules frombothvaporphase[7]andwater-basedenvironment[21,22].
However,watersolubilityofCDsrestrictstheiruseforwaterpurifi- cation purposes,becauseofa probableleachingfromnanofiber http://dx.doi.org/10.1016/j.apsusc.2014.03.138
0169-4332/©2014ElsevierB.V.Allrightsreserved.
582 A.Celebiogluetal./AppliedSurfaceScience305(2014)581–588
surfacethatcanbeoccurredduringfiltration.Therefore,another approachshouldbeadoptedforthemodificationofnanofibersthat includesthelastingattachmentsofCDmoleculesonthefibersur- face.Thus,complexformationpropertyofCDmoleculeswouldbe integratedwiththehighsurfaceareaofpolymericnanofibersina morepermanentwaythatwouldleadtoproductionofpromising filteringmembranes.Actually,thechemicalsurfacemodification withCDmoleculeswasfirstlyperformedonthefiberandfabric surfacesbyusingappropriatecrosslinkingagents[23–30].These functionalizationswereperformedbygraftingCDsontosubstance [23–26]orthesubstanceswerecoveredbycrosslinkedCDpoly- mers[27–30]forthefiltrationofwastemoleculesordeliveryof drugs,antibacterialsetc.Ontheotherhand,wehavefirstlyreported thesurfacemodificationofelectrospunnanofiberswithCDpoly- merin ourpreviousstudy[31]. Here,citric acidwasusedas a crosslinkingagentfortheformationofCD(␣-CD,-CDand␥-CD) polymer(CDP)andafterthesurfacemodificationofpolyethylene terephthalate (PET) nanofibers, the molecularfiltration perfor- manceofPET/CDPwasinvestigatedaswell[31].
Surfacemodifiedelectrospunnanofibersareofgreat interest duetotheirhigherpotentialfortheapplicationofaforementioned fields.Nanofibersfunctionalizedinthiswaycouldbeexpectedto increasetheirperformanceforthedesiredapplications,sincethe availabilityof more activesidesontheirsurface.“Click” chem- istrycanbeanalternativewaytomodifysurfaceofnanofibers, because“click”reactionsshowhighyields andexceptional tol- erancetowardsa wide rangeof functional groupsand reaction conditions in thematerial science [32,33]. Very recent studies have also been reported in the literature about the modifica- tionofelectrospunnanofibersvia“click”reaction.For instance, Fu et al. formed thermal-sensitive poly-N-isopropylacrylamide (PNIPAM)brushesonthesurfaceofpoly(4-vinylbenzylchloride)- block-poly(glycidylmethacrylate)(PVBC-b-PGMA)nanofibersby using“click”reaction[34].InanotherstudyofChangetal.,“click”
wasused for thefunctionalization of polyimide nanofibers via alkyne-terminatedpoly(methylmethacrylate)chains[35].Inthe studyofYangetal.nanofibershavingthermallysensitivesurface wereproducedbythegraftingofPNIPAMbrushesonthepoly((3- mercaptopropyl)methylsiloxane)(PMMS)nanofiberswiththeaid of“click”chemistry[36].Inanotherrelatedstudy,Lancuskietal.
developedcarbohydrate-decoratedPCLnanofibersforthespecific proteinadhesionbyapplying“click”reaction[37].In oneofthe associatedstudies,Qianetal.reportedtheintroductionofsaccha- rideresiduestothesurfaceofthepolyphosphazenenanofibrous membraneusing“click”chemistry[38].Mostofthestudiesmen- tionedabovefocusonthebiomedicalapplicationsofnanofibers.
Ontheotherhand,inourstudywehaveapplied“click”reaction forsurfacemodificationofnanofiberstoimprovetheirfiltration performance.
Polycyclicaromatichydrocarbons(PAHs)areoneofthemost widespreadpollutants whicharehighlytoxic,carcinogenic, and theirtoxicity increases withincreasing molecularweight [39].
Moreover,severalstudiesshowthatPAHspollutionscauseseri- oushealthproblemsforhumanandlivingorganisms[39,40].For thesereasons,varietiesofadsorbentssuchasnanofibers,silicagel, porousnanoparticlesetc.,havebeendevelopedfortheremovalof PAHs[31,41,42].
In this study, -CD-functionalized CA nanofibers were suc- cessfullyproducedbycombinationofelectrospinningand“click”
chemistry(Fig.1).Thatis,-CDwasgraftedontoelectrospunCA nanofibersvia“click”reaction.Themorphologicalcharacterization ofnanofiberswerecarriedoutbyusingscanningelectronmicro- scope(SEM).The surfacecharacteristicsof thenanofiberswere investigated by attenuated total reflectance-Fourier transform infraredspectroscopy(ATR-FTIR)and x-rayphotoelectronspec- troscopy(XPS).Furthermore,thecomparativemolecularfiltration
performance of -CD-functionalized CAnanofibersand pristine CAnanofiberswereinvestigatedbyremovingphenanthrene(asa modelPAH)fromtheaqueoussolutions.Ourpreliminaryfindings suggestedthat-CD-functionalizedCAnanofibershavepotentials tobeusedasmolecularfiltersforthepurposeofwaterpurifica- tionand/orwastewatertreatmentbyintegratingthehighsurface areaoftheelectrospunnanofiberswithinclusion complexation propertyofCDmolecules.
Materialsandmethods Materials
Celluloseacetate (CA, Mw: 30000,39.8wt. %acetyl, Sigma–
Aldrich) dichloromethane (DCM, ≥99% (GC), Sigma–Aldrich), methanol (≥99.7% (GC), Sigma–Aldrich), beta-cyclodextrin (-CD) (Wacker Chemie AG), sodium hydroxide (NaOH, Fluka, ≥98%, small beads), acetonitrile (99.9%, Sigma–Aldrich), p-toluenesulfonyl chloride (puriss., ≥99.0%, Sigma–Aldrich) dimethyformamide (≥99% (GC), Sigma–Aldrich), sodium azide (ReagentPlus,≥99.5%,Sigma–Aldrich),sodiumhydride(60%dis- persioninmineraloil,Aldrich),propargylbromidesolution(80%in toluene,Fluka),acetone(≥99%(GC),Sigma–Aldrich),2-propanol (≥99.5%(GC),Sigma–Aldrich),coppersulfate(anhydrous,≥99.0%, Sigma–Aldrich), l-ascorbic acid (reagent grade, Sigma–Aldrich) phenanthrene(98%,Sigma–Aldrich) were purchased.The water usedwasfromaMilliporeMilli-QUltrapureWaterSystem.Allthe materialswereusedwithoutanypurification.
ElectrospinningofCAnanofibers
Theelectrospinning solutionofCAwaspreparedbydissolv- ingpolymerinaDCM/methanol(4/1(v/v))binarysolventmixture ata12%(w/v)polymerconcentration.TheclearCAsolutionwas then placed in a 5mL syringe fitted with a metallic needle of a0.4mminnerdiameter.Thesyringewasfixedhorizontallyon thesyringepump(modelKDS-101,KDScientific,USA).Theelec- trodeofthehigh-voltagepowersupply(Spellman,SL30,USA)was clampedtothemetalneedletip,andtheplate-shapedaluminum collectorwasgrounded.Electrospinningparameterswereadjusted asfollows:feedrateofsolutions=1mL/h,appliedvoltage=15kV, tip-to-collectordistance=10cm.Theelectrospinningprocesswas performedat25◦Cat20%relativehumidityinPlexiglasbox.After theelectrospunnanofibersweredepositedonthegroundedmetal collectorcoveredwithaluminumfoil,theywerekeptinvacuum oven(40◦C)foralmost12htoremovethesolventresidualinthe nanofibers.
Synthesisoftheazide-ˇ-cyclodextrin
-CD(63g,35.2mmol)wasdispersedin500mLofwaterand bytheadditionofNaOHsolution(5.6gin20mlwater),CDswere completelydissolved.Afterstirring1h,thep-toluenesulfonylchlo- ride solution(9.5g in 30ml acetonitrile) was dropped into CD solution slowly. The suspension was stirred vigorously for 6h and kept in refrigerator overnight. The precipitate white pow- der was filtered and dried under vacuum (12g TsO--CD). In the second step, the TsO--CD (6g) powder was dissolved in DMF (50ml) and sodium azide (NaN3, 2.75g) was added into solution.Thissystem wasstirredat 80◦C forabout 24hunder nitrogenatmosphereandthen, itwascooledtoroomtempera- ture.Finally,thesolutionwasdroppedintocoldacetone(600ml) andthewhiteprecipitateoftheproductwasobtainedafterthe filtration.
Fig.1.(a)SchematicrepresentationofelectrospinningofCAnanofibers.(b)Schematicviewandchemicalstructureof-CD,schematicviewofazide--CDsynthesisand CA-propargylnanofibersformation.(c)TheschematicrepresentationofthemodificationofCA-propargylnanofiberswithazide--CDby“click”reaction.
Graftingofazide-ˇ-CDontoCAnanofibersby“click”chemistry
Underanitrogenatmosphere,CAnanofibers(1.0equiv.)and 2-propanolsolutionof NaH(1.2equiv.)were addedtoa round bottomedflaskat0◦Candstirredforfewminutes.Thereaction mixturewasgraduallywarmedtoroomtemperaturefor2h,and propargylbromide(1.8equiv.)wassubsequentlyaddeddropwise.
Theresulting mixturewasstirred atroomtemperature for 6h.
TheCAnanofiberswererecoveredfromthereactionmixtureand washedwith2-propanolandwatertoremovetheunreactedchem- icals,anddriedundervacuumat30◦C.Theazide--CDobtained intheformerstep(0.6mmol,0.7g)wasfirstlydissolvedin20ml water and CA nanofiberhaving propargylmoiety wasputinto thisCDsolution.Meanwhile,thefreshsolutionsofl-ascorbicacid (0.12mmol,21mg)in1.5mlwaterandcopper(II)sulfateanhy- drous(0.052mmol,8.8mg)in1.5mlwaterwerepreparedandboth ofthemaddedintothesolutionwhichincludeazide--CDandCA- propargylnanofibers.Thissystemwasstirredabout24hatroom temperature.Finally, obtainedCA-CD nanofiberswereremoved fromthesolution,washedwithwateranddriedatvacuumoven at40◦C.
Characterizationsandmeasurements
Themorphologicalcharacterizationandthediametercalcula- tionoftheCA,CA-propargylandCA-CDnanofiberswereperformed byusingscanningelectronmicroscope(FE-SEM)(FEI,Quanta200 FEG).Samplesweresputteredwith5nmAu/Pd (PECS-682)and around100fiberdiametersweremeasuredfromtheSEMimages tocalculatetheaveragefiberdiameterofeachsample.Theinfrared spectraof theCDswere obtainedbyusing a Fouriertransform infrared spectrometer (FTIR) (Bruker-VERTEX 70). The samples weremixedwithpotassiumbromide(KBr)andpressedaspellets.
Thescans(64scans)wererecordedbetween4000and400cm−1 ataresolutionof4cm−1.TheAttenuatedtotalreflectance-Fourier transforminfrared(ATR-FTIR)wasusedforthesurfacestructural analysisof nanofibers.ATR-FTIRspectraofthenanofibers were obtainedusingaThermoNicolet6700spectrometerwithaSmart Orbit attenuated total reflection attachment. The spectra were takenataresolution4cm−1 after128scanaccumulationforan acceptablesignal/noiseratio.Thex-rayphotoelectronspectraof nanofiberswererecordedbyusingx-rayphotoelectronspectrom- eter(XPS)(ThermoScientific).XPSwasusedbymeansofaflood
584 A.Celebiogluetal./AppliedSurfaceScience305(2014)581–588
gunchargeneutralizersystemequippedwithamonochromated AlK-␣ x-ray source(h=1486.6eV). Thehighresolution spec- traofCandNwerealsorecordedfortherelatedsamplestoget moredetailedinformation.Highperformanceliquidchromatogra- phy(HPLC)system(Agilent1200Series)wasusedtoinvestigate thephenanthreneremovingperformanceofbothCAandCA-CD nanofibers.Theseparationofphenanthrenewasperformedwith ZorbaxEclipseXDB-C18column(150mm×4.6mm,5mparticle size)anditwasdetectedat254nmwavelength.Acetonitrile(100%) wasusedasmobilephaseataflowrateof0.3ml/min.andtheinjec- tionvolumewaskeptat10l.Thephenanthrenewassolvedin acetonitrileandthendilutedinwatertocarryoutthemeasure- ments.The0.1gweightednanofiberswereimmersedin1.8ppm phenanthreneincludedwatersolutions(30ml)and0.5mlaliquots weretakenfromthesystematdefinitetimeintervals.Thecalibra- tioncurveofphenanthrenewaspreparedbyusingstocksolutions in4differentconcentrations;1.8g/ml,0.9g/ml0.45g/ml,and 0.23g/ml.It showedlinearity andacceptabilitywithR2≥0.99.
Themeasurementresultswereadaptedtothiscalibrationcurve intermsof peakareaundercurves.Theexperimentswerecar- riedoutintriplicateandtheresultsweregivenwiththeirstandard deviations.
Resultsanddiscussion Formationofazide-ˇ-CD
The modification of the -CD molecules was confirmed by usingFTIRspectraasillustratedin Fig.2a.Asseen, thecharac- teristicabsorption bands of -CD for the given three samples, appeared at around 1030,1080, and 1155cm−1 corresponding to the coupled C–C/C–O stretching vibrations and asymmet- ric stretching vibration of the C–O–C glycosidic bridge. After p-toluenesulfonyl chloride treatment, beside the -CD signals, toluenesulfonylgroupcharacteristicbandswerealsoobservedas aromaticC Cstretchingat1599cm−1,S Ostretchingat1366cm−1 andS–O–Arstretchingat838cm−1 [43].Asa resultofthenext step,toluenesulfonylgroupsignalswasdisappearedinFTIRspec- trumandstretchingfrequencyofN3becameobviousat2040cm−1 demonstrating asymmetrical azide (–N3) functionality of -CD [44].
Morphologicalcharacterizationofnanofibers
ThemorphologicalbehaviorofCAnanofibersbeforeandafter thesurfacemodificationhavebeencomparedbySEMasdepicted inFig.3.AsitisshownintheSEMimages, somechangeswere occurredatthemorphologyofCAnanofibersaftereachprocess.The uniformandsmoothmorphologywasobservedforun-modifiedCA nanofibers,whereasslightswellingwasobservedbythepropar- gyltreatment(Fig.3aandb).Theroughandirregularappearance wasrecordedafterthe“click”reactionwhichprovedthesuccessful surfacemodificationofCAnanofibers.Thesimilarmorphological changewasalsoobservedinastudyofourresearchgroupinwhich theCDpolymerwasgraftedonthePETnanofibers[31].Theover- allresultssuggestedthat,adoptedproceduredidnotcausetoany deformationandfibrousstructureofnanofiberswaspreserveddur- ingthechemicaltreatments.Theaveragefiberdiameters(AFD) weredeterminedas675±160,960±190and1520±370forCA, CA-propargylandCA-CDnanofibers,respectively.Theincreaseof AFDcouldbeoriginatedfromtheswellingofnanofibersthrough themodificationand/orirregularpartsyieldedasaresultofCD grafting.
Fig.2. (a)FTIRspectraof-CD,TsO--CDandazide--CDpowder,(b)ATR-FTIR spectraofCA,CA-propargylandCA-CDnanofibers.
Structuralsurfacecharacterizationofnanofibers
TheATR-FTIRcharacterizationwasperformedtoprovetheCD modificationonthenanofibersurface(Fig.2b).Thecharacteristic bandofCAwasobservedat1739and1221cm−1duetotheC Oand C–Ostretching,respectively.Thebroadbandat3700–3100cm−1 indicatesthepresenceofOHgroupintheCAstructure.FTIRspec- trumofCAalsoshowedabsorbancebandat2924and2855cm−1 fortheC–Hstretching.Initially,CAnanofibersweremodifiedwith propargylbromide.Thismodificationwasobviousfromtheappear- anceofC Cbandat2019cm−1intheATR-FTIRspectrum(Fig.2b).
Then, azide--CD was attached to the CA-propargyl nanofiber surface by a “click” reaction and accordingly, the C C bandat 2019cm−1andN3at2040cm−1disappeared[45,46].Furthermore, allcharacteristicbandsofCAandCDwereobservedfortheCA-CD nanofibers(Fig.2b).
ThesurfaceoftheCA,CA-propargylandCA-CDnanofiberswere alsocharacterized byusing XPSwide scan and highresolution scanstoverifythefunctionalizationofthesesamples.Table1sum- marizesthecompositionalpercentagesofnanofiberswhichwere obtainedasaresultofwideenergysurveyscan.Itwasobserved that,C1sandO1saretwointensiveelementsasthemaincompo- sitionsofnanofibers.Forun-modifiedCAnanofibers,theratioofC 1s:O1sis62.77:37.23(%),whereasforCA-propargyl,theintensity ofC1sincrease(C1s:O1sis71.21:28.79(%))duetocontribution
Fig.3.RepresentativeSEMimagesof(a)CA,(b)CA-propargyland(c)CA-CDnanofibers.Theinsetsshowhighermagnificationimages.
Fig.4.HighresolutionC1sXPSspectraof(a)CA,(b)CA-propargyland(c)CA-CDnanofibers.(d)HighresolutionN1sXPSspectrumofCA-CDnanofibers.
586 A.Celebiogluetal./AppliedSurfaceScience305(2014)581–588
Table1
AtomicconcentrationsofnanofiberswhichwereobtainedfromXPSwideenergy surveyscans.
Samples C(%) O(%) N(%)
CAnanofibers 62.77 37.23 –
CA-propargylnanofibers 72.21 28.79 –
CA-CDnanofibers 72.75 25.58 1.67
of CH2C CH group in the first step of modification [47]. After
“click”reaction,N1swasalsorecordedasoneofthecomponent whichindicatesthesuccessfulformationoftrizoleringbetween CAnanofibersurfaceandCDmolecules[48].HighresolutionC1s scanwasperformedtogetmoredetailedinformationaboutthe chemicalstateofnanofibers’surface.Fig.4a–cshowsC1sspectra ofun-modifiedCA,CA-propargylandCA-CDnanofiberswiththeir subpeaksobtainedbyfitting.Inaddition,thehighresolutionscanof N1sisgiveninFig.4dthatbelongstoCA-CDnanofibers.Thecorre- spondingpositionsofpeakbindingenergiesandtheirvalues(%area ratio)werealsolistedinTable2.Forun-modifiedCAnanofibers,C 1sspectrumisdeconvolutedintofoursubpeaksassignedtoC–(C, H)at284.62eV,C–Oat286.28eV,O–C–Oat287.62eVandO C–O at289.22eV[49].Afterthefirststepofmodification,theC1sspec- trum(Fig.4b)clearlyshowsincreaseofC–(C–H)peakratiofrom 30.45%to43.21%anddecreaseofotherpeaks(Table2)duetothe graftingofCH2C CHmoiety[47].Thisevidencemadeitpossible togotonextstepofCAnanofibersfunctionalization.Inthecaseof azide--CDgrafting,thepeakratiosofC–OandO–C–Osituatedat 286.66and287.91,respectivelyincreased,ontheotherhand,the chemicalstateofO C-Oat289.13eVdecreasedsignificantlyowing tothelocationof-CDonthenanofibersurface(Fig.4c,Table2).
InadditiontoC1speak,theN1speakwasalsodetectedatabout 400eVforCA-CDnanofibersoriginatedfromthetriazolegroupas aresultof“click”reaction[48].Fortriazolering,theN1score-level peak can be curve-fitted into two components having binding energyat398.4and399.7eVattributedtoC–NandN N,respec- tively [48,50]. From XPS measurements, it was also confirmed thatthesurfacemodificationofCAnanofiberswithCDmolecules wasachievedbyusing“click”chemistry.Inaddition,thegrafting densityofCDmoleculesontoCAnanofiberswerecalculatedfrom highresolutionXPSspectraofC1s.Forthis,O–C–Opeakoriginated frombothCAand CD,and O C-Opeak onlyexisting intheCA structurewerechosenandused.Thepeakratio(O–C–O/O C-O) belongstoCAnanofiberwascalculatedas0.72anditisrelatively close to the theoretical values (0.80) calculated from atomic compositionofCAnanofibers.Ontheotherhand,O–C–O/O C–O ratiowasdeterminedas4.55forCA-CDnanofibers.Asitisknown, each -CD molecules have 7 glucopyranose subunits and after theclickreaction,O–C–Opeakarearatioincreasedby6.32times, whichmeansthateach-CDmoleculewasapproximatelybound toonerepeatunitsoftheCApositionedatnanofibersurface.
Fig.5.Thetimedependentdecreaseofphenanthreneconcentrationinaqueous solutionwhichcontainsCAandCA-CDnanofiberswebs.
MolecularfiltrationcapabilityofCAandCA-CDnanofibers
PAHs are important organic pollutants because of their mutagenicand carcinogenicpotentials.However,thelow-water solubilityofthesecomponentslimitstheremediationprocessof contaminatedwaterandsoil[39,40].Asitisknown,CDsarecapable ofencapsulatingorganiccompoundsduetotheirhydrophobiccav- ityandtherearemanystudiesreportedcomplexationbetweenCDs andPAHsmolecules[51–55].Phenanthreneisthemostcommonly knownexamplethroughotherhydrocarbons,sointhisstudy,it waschosenasamodelPAHtoexaminethemolecularfiltration potentialofCAandCA-CDnanofibers.Fig.5depictsthecumulative decreaseofphenanthreneconcentration(%)againstprogressing time intervalswhileCAand CA-CDnanofiberswere beingkept intothis organiccompoundaqueoussolution.Asit isseen,the adsorptionofphenanthrenewasachievedbybothCAandCA-CD nanofibers.Even,inthefirst30min,whileCAnanofibersremoved 50%ofphenanthrenefromthesolution,thisratioreachedto64%
for CD-CA nanofibers.Towards theend of experiment, the dif- ferencesofadsorbedamountbetweenCAandCA-CDnanofibers increase,therefore phenanthreneconcentrationdecreased more significantlyfor CA-CDnanofiberscompared toun-modifiedCA nanofibers.ThehigherremovingefficiencyofCD-CAnanofibersis probablyoriginatedfromtheinclusioncomplexationpropertyof CDmoleculeswhichwerelocatedonthesurfaceofnanofibersand leadedtohigheradsorptionoforganiccompoundfromaqueous medium.Itisknownthat,hydrophobicinteractionsaretherelation typebetweenCDscavityandphenanthrenemoleculeduringthe inclusion complexation.Besides,repulsive interactions between
Table2
FittingparametersoftheC1sXPSspectraofCA,CA-propargylandCA-CDnanofibers.
Samples Fittingpeaks Bonds Peakbindingenergy(eV) Arearatio(%)
CAnanofibers C1s#1 C–(C–H) 284.62 30.45
C1s#2 C–O 286.28 20.32
C1s#3 O–C–O 287.62 20.61
C1s#4 O C–O 289.22 28.62
CA-propargylnanofibers C1s#1 C–(C–H) 284.73 43.21
C1s#2 C–O 286.66 20.29
C1s#3 O–C–O 287.91 5.37
C1s#4 O C-O 289.13 13.74
CA-CDnanofibers C1s#1 C–(C–H) 284.80 43.13
C1s#2 C–O 286.41 45.09
C1s#3 O–C–O 287.99 9.66
C1s#4 O C–O 289.30 2.12
Fig.6. RepresentativeSEMimagesof(a)CAand(b)CA-CDnanofibersafterthefiltrationtest.
thehydrophobicguestandtheaqueousenvironment,andmore favorableinteractionsbetweenhydrophobicguestandapolarCD cavity arethedriving forcesfor theremoving ofphenanthrene moleculesfromtheaqueousenvironment[16–53].Inthecaseof CDgraftingonto nanofiberssurface, onlyCDmoleculesbecome moreapplicablecomparedtotheirpowderformbythelocation onastablecarriermatrix.However,itdoesnotcauseanychange at the entrapment and removing mechanism of phenanthrene moleculesbyCDs.Here,itwasalsoobservedthat,bothCAand CA-CDnanofibersstill kepttheirfiberstructureafterthefiltra- tiontest(Fig.6).CAisalready goodcandidatefor thefiltration oforganicpollutantsandtherearealsoreportsintheliterature abouttheuptakingofPAHsfromtheconcernedenvironmentby usingCAbasedmembranes[56–59].Ontheotherhand,tothebest knowledge,thisisfirststudyabouttheinvestigationofmolecular filtrationcapabilityofCAnanofibersanditsCDmodifiedtypeby
“click”chemistry.Fromourresults,itcanbeconcludedthat,thesur- facemodificationofelectrospunCAnanofiberswithCDmolecules improvedthemolecularfiltrationpotentialbyutilizingfromthe inclusioncomplexationpropertyofCDs.The“click”chemistryisa quitenewandpromisingmethodforthefunctionalizationofelec- trospunnanofibers.Inourstudy,betteradsorptionefficiencywas obtainedforCDmodifiedCAnanofiberscomparedtountreatedone duringtheremovingtest.However,theadsorbedamountofPAH orotherorganiccompoundscanbeenhancedbygraftinghigher amountofCDonthenanofibersurfaceusing“click”chemistry.
Conclusion
Inthisstudy,thepermanentgraftingofCDmoleculesonthe electrospunCAnanofiberswasachievedbyusing“click” chem- istry.First,-CDwasmodifiedsoastobeazide--CD.Atthesame time,CAnanofiberswereproducedviaelectrospinningandthey weretreatedchemicallytobepropargyl-terminatedCAnanofibers.
Then,“click”reactionwasperformedtograftthe-CDmoleculeson thesurfaceofCAnanofibers.Themorphologicalcharacterizations ofnanofiberswerecarriedoutbySEMtechnique.Itwasrevealed that,theCDmodifiedCAnanofibershave rougherandirregular surfacewhenitwascomparedwithpristineCAnanofibers.The existenceoftheCDmoleculesonthenanofibersurfacewasproved byusingATR-FTIRandXPSanalyses.ThefiltrationcapabilityofCD graftedCAnanofiberswasinvestigatedbytheremovalofphenan- threnefromitsaqueoussolution.Forcomparison,filtrationtestof pristineCAnanofiberswasalsoperformed.Itwasobservedthat, CA-CDnanofibersadsorbedhigheramountofphenanthrenecom- paredtoCAnanofibersduetotheinclusioncomplexationcapability ofCDmolecules.Wehavealsocheckedthat,thefibrousstructure ofnanofiberswasprotectedafterthefiltrationtest.Inbrief,our
resultsindicatethatCDfunctionalizedCAnanofiberswouldhave potentialtobeusedasmolecularfiltersforthepurposeofwater purificationandwastewatertreatmentbyintegratingthehighsur- faceareaof nanofiberswithinclusioncomplexationpropertyof CDmolecules.Moreover,“click”chemistrywouldbeapromising candidateforthemodificationofnanofiberssurfacewithvarious functionalgroupsandmoietiestobenefitfromthepotentialsof nanofibersmoreefficientlyintheirapplications.
Acknowledgements
Dr.T.UyaracknowledgesTUBITAK-TheScientificandTechno- logicalResearchCouncilofTurkey(project#110M612)forfunding theresearch.Dr.T.UyaralsoacknowledgesEUFP7-PEOPLE-2009- RG Marie Curie-IRG(NANOWEB, PIRG06-GA-2009-256428) and TheTurkishAcademyofSciences–OutstandingYoungScientists AwardProgram (TUBA-GEBIP)for partialfunding. A.Celebioglu acknowledgesTUBITAK-BIDEBforthenationalPh.D.scholarship.
References
[1]S.Ramakrishna,K.Fujihara,W.Teo,T.Lim,Z.Ma,AnIntroductiontoElectro- spinningandNanofibers,WorldScientificPublishingCompany,2005.
[2]J.H.Wendorff,S.Agarwal,A.Greiner,Electrospinning:Materials,Processing, andApplications,Wiley-VCH,Germany,2012.
[3]V.Thavasi,G.Singh,S.Ramakrishna,Electrospunnanofibersinenergyand environmentalapplications,Energ.Environ.Sci.1(2008)205–221.
[4]C.Srisitthiratkul,W.Yaipimai,V.Intasant,Environmentalremediationand superhydrophilicityofultrafineantibacterialtungstenoxide-basednanofibers undervisiblelightsource,Appl.Surf.Sci.259(2012)349–355.
[5]K.Yoon,B.S.Hsiao,B.Chu,Functionalnanofibersforenvironmentalapplica- tions,J.Mater.Chem.18(2008)5326–5334.
[6]R.S.Barhate,S.Ramakrishna,Nanofibrousfilteringmedia:filtrationproblems andsolutionsfromtinymaterials,J.Membr.Sci.296(2007)1–8.
[7]T.Uyar,R.Havelund,Y.Nur,A.Balan,J.Hacaloglu,L.Toppare,F.Besenbacher, P.Kingshott,Cyclodextrinfunctionalizedpoly(methylmethacrylate)(PMMA) electrospunnanofibersfororganicvaporswastetreatment,J.Membr.Sci.365 (2010)409–417.
[8]E.Scholten,L.Bromberg,G.C.Rutledge,T.A.Hatton,Electrospunpolyurethane fibersforabsorptionofvolatileorganiccompoundsfromair,ACSAppl.Mater.
Interface.3(2011)3902–3909.
[9]Z.Ma,M.Kotaki,S.Ramakrishna,Surfacemodifiednonwovenpolysulphone (PSU)fibermeshbyelectrospinning:anovelaffinitymembrane,J.Membr.Sci.
272(2006)179–187.
[10]Y.Mei,C.Yao,K.Fan,X.Li,Surfacemodificationofpolyacrylonitrilenanofibrous membraneswithsuperiorantibacterialandeasy-cleaningpropertiesthrough hydrophilicflexiblespacers,J.Membr.Sci.417–418(417)(2012)20–30.
[11]P.K. Neghlani, M. Rafizadeh, F.A. Taromi, Preparation of aminated- polyacrylonitrilenanofiber membranes for theadsorptionof metal ions:
comparisonwithmicrofibers,J.Hazard.Mater.186(2011)182–189.
[12]M. Stephen, N. Catherine, M. Brenda, K. Andrew, P. Leslie, G. Corrine, Oxolane-2,5-dionemodifiedelectrospuncellulosenanofibersforheavymetals adsorption,J.Hazard.Mater.192(2011)922–927.
[13]J.Niu,J.Xu,Y.Dai,J.Xu,H.Guo,K.Sun,R.Liu,Immobilizationofhorseradish peroxidasebyelectrospunfibrousmembranesforadsorptionanddegradation ofpentachlorophenolinwater,J.Hazard.Mater.246/247(2013)119–125.
588 A.Celebiogluetal./AppliedSurfaceScience305(2014)581–588
[14]J.Szejtli,Introductionandgeneraloverviewofcyclodextrinchemistry,Chem.
Rev.98(1998)1743–1754.
[15]A.Hedges, Industrialapplicationsofcyclodextrins,Chem.Rev. 98(1998) 2035–2044.
[16]E.M.DelValle,Cyclodextrinsandtheiruses:areview,ProcessBiochem.39 (2004)1033–1046.
[17]D.Landy,I.Mallard,A.Ponchel,E.Monflier,S.Fourmentin,Remediationtech- nologiesusingcyclodextrins:anoverview,Environ.Chem.Lett.10 (2012) 225–237.
[18]W.C.E.Schofield,C.D.Bain,J.P.S.Badyal,Cyclodextrin-functionalizedhierarchi- calporousarchitecturesforhigh-throughputcaptureandreleaseoforganic pollutantsfromwastewater,Chem.Mater.24(2012)1645–1653.
[19]G.Crini,M.Morcellet,Synthesisandapplicationsofadsorbentscontaining cyclodextrins,J.Sep.Sci.25(2002)789–813.
[20]N. Morin-Crini, G. Crini, Environmental applications of water-insoluble- cyclodextrin–epichlorohydrinpolymers,Prog.Polym.Sci.38(2013)344–368.
[21]T.Uyar,R.Havelund,J.Hacaloglu,F.Besenbacher,P.Kingshott,Functional electrospunpolystyrenenanofibersincorporating␣-,-,and␥-cyclodextrins:
comparisonofmolecularfilterperformance,ACSNano4(2010)5121–5130.
[22]T.Uyar,R.Havelund,Y.Nur,J.Hacaloglu,F.Besenbacher,P.Kingshott,Molecular filtersbasedoncyclodextrinfunctionalizedelectrospunfibers,J.Membr.Sci.
332(2009)129–137.
[23]E.S.Abdel-Halim,M.M.G.Fouda,I.Hamdy,F.A.Abdel-Mohdy,S.M.El-Sawy, Incorporationofchlorohexidindiacetateintocottonfabricsgraftedwithgly- cidylmethacrylateandcyclodextrin,Carbohyd.Polym.79(2010)47–55.
[24]B.Martel,P.LeThuaut,S.Bertini,G.Crini,M.Bacquet,G.Torri,M.Morcellet, Graftingofcyclodextrinsontopolypropylenenonwovenfabricsfortheman- ufactureofreactivefilters.III.Studyofthesorptionproperties,J.Appl.Polym.
Sci.85(2002)1771–1778.
[25]P.L.Nostro,L.Fratoni,F.Ridi,P.Baglioni,SurfacetreatmentsonTencelfabric:
graftingwithcyclodextrin,J.Appl.Polym.Sci.88(2003)706–715.
[26]R.Romi,P.L.Nostro,E.Bocci,F.Ridi,P.Baglioni,Bioengineeringofacellulosic fabricforinsecticidedeliveryviagraftedcyclodextrin,Biotechnol.Progr.21 (2008)1724–1730.
[27]N.Blanchemain,S.Haulon,E.Marcon-Bachari,M.Traisnel,C.Neut,J.Kirk- Patrick, M.Morcellet,H. Hildebrand,B.Martel, Vascularprostheses with controlledreleaseofantibioticsPart1.Surfacemodificationwithcyclodextrins ofPETprostheses,Biomol.Eng.24(2007)149–153.
[28]L.Ducoroy,B.Martel,B.Bacquet,M.Morcellet,Ionexchangetextilesfromthe finishingofPETfabricswithcyclodextrinsandcitricacidforthesorptionof metalliccationsinwater,J.Incl.Phenom.Macro.57(2007)271–277.
[29]N.Blanchemain,T.Laurent,S.Haulon,M.Traisnel,C.Neut,J.Kirkpatrick,M.
Morcellet,H.F.Hildebrand,B.Martel,InvitrostudyofaHPgamma-cyclodextrin graftedPETvascularprosthesisforapplicationasanti-infectiousdrugdelivery system,J.Incl.Phenom.Macro.57(2007)675–681.
[30]B.Martel,M.Morcellet,D.Ruffin,L.Ducoroy,M.Weltrowski,Finishingof polyesterfabricswithcyclodextrinsandpolycarboxylicacidsascrosslinking agents,J.Incl.Phenom.Macro.44(2002)443–446.
[31]F. Kayaci,Z.Aytac,T.Uyar, Surfacemodificationofelectrospunpolyester nanofiberswithcyclodextrinpolymerfortheremovalofphenanthrenefrom aqueoussolution,J.Hazard.Mater.261(2013)286–294.
[32]W.H.Binder,R.Sachsenhofer,Clickchemistryinpolymerandmaterialsscience, Macromol.RapidCommun.28(2007)15–54.
[33]J.E.Moses,A.D.Moorhouse,Thegrowingapplicationsofclickchemistry,Chem.
Soc.Rev.36(2007)1249–1262.
[34]G.D.Fu,L.Q.Xu,F.Yao,SmartNanofibersfromCombinedLivingRadicalPoly- merization,clickChemistryandElectrospinning,ACSAppl.Mater.Interface.1 (2009)239–243.
[35]Z.Chang,Y.Xu,X.Zhao,Q.Zhang,D.Chen,Graftingpoly(methylmethacry- late)ontopolyimidenanofibersviaclickreaction,ACSAppl.Mater.Interface.
1(2009)2804–2811.
[36]H.Yang,Q.Zhang,B.Lin,G.Fu,X.Zhang,L.Guo,Thermo-sensitiveelectrospun fiberspreparedbyasequentialthioleneclickchemistryapproach,J.Polym.Sci.
APolym.Chem.50(2012)4182–4190.
[37]A.Lancuˇski,F.Bossard,S.Fort,Carbohydrate-decoratedPCLfibersforspecific proteinadhesion,Biomacromolecules14(2013)1877–1884.
[38]Y.-C.Qian,N.Ren,X.-J.Huang,C.Chen,A.-G.Yu,Z.-K.Xu,Glycosylationof polyphosphazenenanofibrousmembranebyclickchemistryforproteinrecog- nition,Macromol.Chem.Phys.214(2013)1852–1858.
[39]A.K.Haritash, C.P.Kaushik,Biodegradationaspectsof polycyclicaromatic hydrocarbons(PAHs):areview,J.Hazard.Mater.169(2009)1–15.
[40]S.K.Samanta,O.V.Singh,R.K.Jain,Polycyclicaromatichydrocarbons:environ- mentalpollutionandbioremediation,TrendsBiotechnol.20(2002)243–248.
[41]K.Yang,L.Zhu,B.Xing,Adsorptionofpolycyclicaromatichydrocarbonsby carbonnanomaterials,Environ.Sci.Technol.40(2006)1855–1861.
[42]A.Walcarius,L.Mercier,Mesoporousorganosilicaadsorbents:nanoengineered materialsforremovaloforganicandinorganicpollutants,J.Mater.Chem.20 (2010)4478–4511.
[43]K.Tungala,P.Adhikary,S.Krishnamoorth,Trimerizationof-cyclodextrin throughtheclickreaction,Carbohyd.Polym.95(2013)295–298.
[44]V.I.Bhoi,C.N.Murthy,Aqueoussolubilizationof[60]fullerenebyselectively modified-cyclodextrin,fullerenes,nanotubes,CarbonNanostruct.19(2011) 668–676.
[45]R.Ranjan,W.J.Brittain,Combinationoflivingradicalpolymerizationandclick chemistryforsurfacemodification,Macromolecules40(2007)6217–6223.
[46]H.Toiserkani,G.Yilmaz,Y.Yagci,L.Torun,Functionalizationofpolysulfonesby clickchemistry,Macromol.Chem.Phys.211(2010)2389–2395.
[47]A.Uliniuca,M.Popa,E.Drockenmullera,F.Boisson,D.Leonard,T.Hamaide, Toward tunable amphiphilic copolymers via CuAAC click chemistry of oligocaprolactones onto starch backbone, Carbohyd. Polym. 96 (2013) 259–269.
[48]T.Cai, W.J.Yang,Z.Zhang,X.Zhu,K.-G.Neoh,E.-T.Kang,Preparationof stimuli-responsive hydrogelnetworks with threaded b-cyclodextrin end- cappedchainsviacombinationofcontrolledradicalpolymerizationandclick chemistry,SoftMatter8(2012)5612–5620.
[49]R. Barbar,A.Durand,J.J.Ehrhardt,J. Fanni,M.Parmentier,Physicochem- ical characterization of a modified cellulose acetate membrane for the designofoil-in-wateremulsiondisruptiondevices,J.Membr.Sci.310(2008) 446–454.
[50]A.A.Qaiser,M.M.Hyland,D.A.Patterson,Surfaceandchargetransportchar- acterizationofpolyaniline-celluloseacetatecompositemembranes,J.Phys.
Chem.B115(2011)1652–1661.
[51]C.Raveler,E.Peyrin,A.Villet,C.Grosset,A.Ravel,J.Alary,Chromatographic studyofPAH--CDinclusioncomplexesusingabinarymixtureandcyano- stationaryphase,Chromatographia53(2001)624–628.
[52]J.Rima,E.Aoun,K.Hanna,Effectofn-alkylchainlengthonthecomplexation ofphenanthreneand9-alkyl-phenanthrenewith-cyclodextrin,Spectrochim.
ActaA60(2004)1515–1521.
[53]T.Badr,K.Hanna,C.deBrauer,Enhancedsolubilizationandremovalofnaph- thaleneandphenanthrenebycyclodextrinsfromtwocontaminatedsoils,J.
Hazard.Mater.112(2004)215–223.
[54]G. Chalumot,C. Yao,V. Pino,J.L.Anderson, Determiningthestoichiome- tryandbindingconstantsofinclusioncomplexesformedbetweenaromatic compoundsand-cyclodextrinbysolid-phasemicroextractioncoupledto high-performance liquid chromatography, J. Chromatogr. A 1216 (2009) 5242–5248.
[55]R.Orprecio,C.H.Evans,Polymer-immobilizedcyclodextrintrappingofmodel organicpollutantsinflowingwaterstreams,J.Appl.Polym.Sci.90(2003) 2103–2110.
[56]X.Li,Y.Zhu,T.Wu,S.Zhang,P.Christie,Usinganovelpetroselinicacidembed- dedcelluloseacetatemembranetomimicplantpartitioningandinvivouptake ofpolycyclicaromatichydrocarbons,Environ.Sci.Technol.44(2010)297–301.
[57]Y.Tao,B.Xue,S.Yao,J.Deng,Z.Gui,Trioleinembeddedcelluloseacetatemem- braneasatooltoevaluatesequestrationofPAHsinlakesedimentcoreatlarge temporalscale,Environ.Sci.Technol.46(2012)3851–3858.
[58]R.Ke,Y.Xu,Z.Wang,S.U.Khan,Estimationoftheuptakerateconstantsfor polycyclicaromatichydrocarbonsaccumulatedbysemipermeablemembrane devicesandtriolein-embeddedcelluloseacetatemembrane,Environ.Sci.Tech- nol.40(2006)3906–3911.
[59]Y.Tao,S.Zhang,Z.Wang,R.Ke,X.-Q.Shan,P.Christie,Biomimeticaccumu- lationofPAHsfromsoilsbytriolein-embeddedcelluloseacetatemembranes (TECAMs)toestimatetheirbioavailability,WaterRes.42(2008)754–762.