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Synthesis and Exchange Properties of Sulfonated Poly(phenylene sulfide) with Alkali Metal Ions in Organic Solvents

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Synthesis and Exchange Properties of Sulfonated Poly(phenylene sulfide) with Alkali Metal Ions in Organic Solvents

Won-KeunSon,* Sang Hern Kim,f andSoo-Gil Park*

Dept. of Poly. Sci. and Eng., ChungnamNational Univ., Taejon305-764, Korea

* Dept of Chemical Technology, Taejon National Univ. of Technology, Taejon 305-719, Korea

*Dept. ofInd. Chem. Eng., ChungbukNationalUniv., Cheongju360-763, Korea ReceivedFebruary 9, 2000

Sulfonated poly(phenylene sulfide) (SPPS) polymers were prepared by sulfonation of poly[methyl[4-(phe- nylthio)phenyl]sulfonium trifluoromethanesulfonat(PPST) with fumic sulfonic acid(10% SO3-H2SO4)and demethylation with aqueousNaOHsolution.The equilibrium constants of ion exchangereactions between al­ kali metal cations (Li+, Na+,and K+) andSPPS ion exchangerin organic solventssuchastetrahydrofuran(THF) anddioxaneweremeasured.The equilibrium constantsofionexchangereactionsincreasedasthe polarity of the solventincreased,andthereactiontemperaturedecreased. Theequilibriumconstants of theionexchange reaction(Keq)alsoincreased in theorder of Li+, Na+, and K+. To elucidatethe spontaneity of theexchangere­ action in organic solvents, theenthalpy,entropy,andGibbs freeenergywerecalculated. The enthalpy of reac­ tionrangedfrom -0.88 to -1.33 kcal/mol, entropy ranged from 1.42 to 4.41 cal/Kmol, and Gibbs freeenergy rangedfrom -1.03 to-2.55 kcal/mol. Therefore, the exchange reactionswere spontaneous becausethe Gibbs freeenergieswerenegative. The SPPS ion exchanger and alkali metal ion bounding each otherproduced good ion exchange capability inorganic solvents.

Keywords: Sulfonated poly(phenylene sulfide),Thermostable ionexchanger, Equilibrium constants ofion ex­ changein organic solvents.

Introduction

Recentrapid developments in industryhave brought atten­ tion to the removaloftoxic heavy metalionfrom sewage, industrial, and mining wastewater.Theremoval of toxic heavy metal ions requires materials for the treatment of waste­

water, suchasion exchanger.

In earlier experiments, the polymers for thecation exchange were prepared by the condensationofphenol-formaldehyde followedby the introduction ofacidic groups such as sul­ fonic and carboxylic acid.1 Thesepolymerswerelessstable chemically and physically and relatively less moldable into shape of regular spheres.

At present, most strong acid cation exchange resins are based on sulfonated crosslinked polystyrene. The well- definedgeometric shape ofbead polymers can be obtained bythetechnique known as “suspension” or "bead” polymer­

ization of styrene in the presence ofa small amount of a crosslinking agent such as divinylbenzene.2-6 Theresulting polymers are chemically stable, but they have limiteduse at temperaturesbelow 150 oC.

Manyhomopolymers, randomcopolymers, and block and graftcopolymerscontainingaromaticrings ordoublebonds can be sulfonated. Toqualify as appropriatematerials for ion exchangeresins, polymer materialsmustpossess anumber of properties such asexcellent chemical and environmental resistance and especiallyhigh thermaland dimensionalsta­ bility. Several attemptshavebeenmade in order to synthe-

^Corresponding Author: e-mail : wkson@cuvic.cnu. ac .kr

size a morethermally stable cationexchange polymer con­

taininga phenylene unit in themainchain.Theroutewidely employed in the synthesis ofsulfonatedaromaticpolymers is represented by the polymer reaction with fumic sulfonic acid, chlorosulfonic acid or sulfur trioxide-triethylphosphate complex.7-10 Sulfonated poly(2,6-dimethylphenylene oxide) was categorized as available for use as an ion exchange resin.11-15 Noshay and Robensonprepared sulfonated poly­

sulfone and investigated its structure, thermal behavior, and mechanicalproperties in detail.16 Alsosulfonatedpoly(aryl- eneether sulfone)membraneshave been useful in desalina­ tion application.7-10Nolte and co-workersreported the evalu­

ation of poly(arylene etherether sulfone)-based solid poly­ mer electrolytes prepared by sulfonation of commercially availablepoly(aryleneether ether sulfone).17 Sulfonatedpoly­

carbonates,polyesters, and polyimidesarealsomentioned in theliterature.18-20

Poly(arylsulfone)resins are importantengineering thermo­ plastics that exhibit the concurrent properties ofexcellent resistanceto hydrolysis and oxidation,excellentmechanical properties, goodthermalstability, andtoughness. Poly(pheny- lene sulfide) (PPS) hasbeen known tohave excellent ther­

mal and chemical properties.21-24 Therefore, PPS could be used as the polymermaterial ofan ion exchanger.

In our laboratory, we prepared and studiedmany kinds of strong acid cation exchange resins containing the sulfonic acid group. Wereported the ion exchange resins based on aromatic polymers such as poly(p-phenylene sulfide)25 and poly(ether ether sulfone).26 The sulfonated poly(phenylene sulfide) (SPPS) used in the presentstudy was prepared by

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oxidativepolymerizationviapoly(sulfoniumcation) obtain­

ed from phenylsulfoxide. We determinedthe spontaneity of the ion exchange reaction of sulfonatedPPS from theequi­ librium constants of ion exchange reaction for the alkali metal cations (Li, Na, and K)in THF and dioxane by using an UV-spectrophotometer.

Experiment지 Section

Materi지s. Thioanisole, bromine, trifluoromethanesulfonic acid, and methanesulfonic acidwerepurchasedfromAldrich Co. and used without furtherpurification. Potassium hydro­

gen carbonate (Kanto Co.) and methylene chloride (Junsei ChemicalCo.)were used as received. Reagent-gradeLizCOs, NazCO* and K2CO3 were purchased from Jusnei Chemical Co. and were used as received. Picric acid was purchased from BDH Ltd. Tetrachloroethane, THF, dioxane, ethanol, andotherchemicalswerereagentgradeand used without fur­

ther purification.

Synthesis of Py(phenylene sulfide) and Sulfonated Py(phenylenesulfide).Thesolublepoly[methyl[4-(phenyl- thio)phenyl] sulfoniumtrifluoromethanesulfonate] (PPST) in organic solvents was synthesized by self-condensation polymerization of methyl(phenylthio) phenyl sulfoxide (MPPSO).27,28Poly(phenylenesulfide) (PPS) and sulfonated poly(phenylene sulfide) (SPPS) were prepared from PPST as showninScheme 1.

1) Poly(phenylene sulfide): A three-neck flask (250mL) equipped with a Teflon-coveredmagneticstirringbar, reflux condenser,thermometer, and N2 gas inletwas chargedwith PPST (3 g, 7.8 mmol) and pyridine (30mL). The reaction mixture was stirred atroom temperature,becomingslightly pale yellow. After afewminutes, the color of the mixture turned into white. The reaction was continued for 1 h at room temperature, and the temperature of the mixture in­ creasedslowly toreflux. Afterrefluxing for 20 h, the reac­

tion was stopped by cooling the solution to room tempera­

ture. The solutionwas thenpoured into 10% HClmethanol solution(600mL). The precipitatewas washed with metha­ nol and chloroform. Theprecipitatewaspurified by continu­ ous extractionusing a Soxhletapparatus with ethanol for 24 h and driedin a vacuum oven at 50 oC for 48h.

2) Sulfonated Poly(phenylene sulfide): A three-neck flask (100 mL) equipped with a Teflon-covered magnetic stirring bar, reflux condenser, thermometer andN2 gasinlet was charged with PPST (3 g,7.8mmol) and fumic sulfonic acid (30mL 10% SO3-H2SO4). The reaction proceeded for 12 h at 80 oC, thenitwasstoppedby coolingthesolutionto room temperature, and the solutionwas poured into ethanol (300 mL). After the precipitate was washedwith distilled water, itwasredissolved in anaqueous NaCl/NaOH (0.5 M/

0.1 M) solution(500mL), which wasrefluxed for 10 h. The solution was poured into ethanol,and the obtained precipi­

tate was washed with distilledwater and ethanol. The poly­

mer was purified by continuous extraction in a Soxhlet apparatus with ethanol for 24 h and dried in a vacuumoven at40 oC for 24 h.

Ion Exchange Capacity in Non-Aqueous Solution.

SPPS(1g)was placed in an Erlenmeyer flask (250 mL) con­

tainingexactly 200 mLof 0.1 N Na-picratesolution in water and organic solvents (dioxane and THF), and it wasallowed to stand for 24 h. Thequantitativeanalysis of eachmetal ele­

mentinthe solutionwasconducted using Smith Hiefje for atom adsorption analyzer(Thermo Jarrau Ash Co., U.S.A).

The ion exchange capacity was obtained by the following equation.

Capacity (meq/g)= (Cst -Ceq)X Koln

--- 22.989xMp

where Cst and Ceqaretheconcentration of metal ionsinstan­ dardsolution and equilibrium,respectively. Mp is the weight of the ion exchange resin, and Vsoln is the volume of the whole solution.

Scheme 1. Synthesis of sulfonated poly(phenylene sulfide).

Sective Adsorption Ability. Todeterminethe selective adsorptionability of metal ions, 0.1 g of SPPSwasaddedto 100 mL of amixed metal aqueous solution and allowed to stand for 24 h. Then the SPPS was filtered, washed three times with distilled water, and driedinavacuumovenat 60 oC.

The analyses oftherelative adsorptionamountsofmetal ions were carried out in an ED AX (Energy Dispersive AnalyticalX-Ray).

Preparation of Alkali Picrate. The ethanol solutions of alkalimetal salts (Li2CO3, Na2CO3, and K2CO3) werepoured into the ethanol solution of picric acid. The crude picrate salts werefiltered, recrystallized,filtered, and driedinava­ cuumoven for 24 h and placed in a refrigeratorat 4 oC.

EquilibriumConstantof Ion ExchangeReaction. A 10 mg sample ofSPPSwas placed in20mL stocksolutions of Li, Na, andK picrates, respectively, and the solutions were agitated for 48 h. The concentrations of picrate salts were measuredwith anUV-spectrophotometer. The

max’sof Li, Na, and K picrates were 333 nm, 351 nm, and357 nm in

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Figure 1. FT-IR spectra of (a) PPST, (b) PPS and (c) SPPS.

THF, and 335 nm, 347nm, and 349 nmin dioxane, respec­ tively. For 30, 40, 50, 60, 70,80, and 90mLstocksolutions, the sameprocedurewasfollowed by dilution.

ResultsandDiscussion

The Fourier transform infrared spectraofPPST, PPS and SPPS are shown in Figure 1. Thespectrumof PPSTdisplays thecharacteristicabsorption bandsofPPS at1565, 1471 and

1379 cm-1,whichareattributedtothe ring stretchingvibra­ tions. The typicalabsorption band attributedto a C-Hout-of­ planevibrationofthe 1,4-phenylene structureis observedat 810 cm-1. The appearance ofthe C-F absorption bands at 1254, 1027 and 637cm-1 andS=O absorption bandsat1155 and 1067 cm-1indicate that the resulting polymer contained CF3SO3-. These spectroscopic data reveal the formation of poly [methyl[4-(phenylthio)phenyl]sulfonium trifluoro­ methanesulfonate] (PPST) (Figure 1a).27

Toconvert from PPST to PPS,thedemethylation was car­

ried outusing pyridine asa nucleophile.The IR spectrum of the resulting polymer is shown in Figure 1b. Theabsorption bands attributedto the CF3SO3- disappeared in PPST. The resultingpolymeralsoshows a band attributed to a C-Hout- of-planevibrationof the 1,4-phenylenestructure at 810 cm-1. This indicates thelinearpolymer with para substituted phe­

nylring.28

SPPSwaspreparedbydemethylationof sulfonated PPST.

The IR spectrumof SPPS is showninFigure 1c. The absorp­

tionbands attributedto the CF3SO3- disappeared in SPPS.

Thesulfonic acid groupswere confirmed by thepresence of the high absorption band of the SO3H group at 1200 cm-1 and the S-O bond at 650 cm-1. From theseresultswe con­

cludedthatthesulfonation in poly(ethylenesulfide)wassuc-

Table 1. Na+ Ion Exchange Capacity of SPPS in aqueous and organic solvent at room temperature

Solutions Dioxane THF Water

Capacity (meq/g) 3.60 3.72 4.07

Table 2. Relative Adsorption of Metal Ions for SPPS ion exchanger in aqueous at room temperature

Elements Total Na(I) K(I) Mg(II) Ba(II)

meq/g 4.01 0.47 0.54 1.27 1.74

cessfully performed.28 It was found that the ion exchange capacityofSPPSwas 4.11meq/g, and thedegreeofsulfona­ tion per repeating unitwas 0.78 by a base line method ofIR absorbance.25

Ion Exchange Capacity in a Non-Aqueous System.

Generally,ion exchangeabilityofanionexchangercanalso be observedinanon-aqueous system, but the exchange rate is much slower than that in an aqueous solution, and the exchange capacities are dependentonthe solvent. The ion exchangecapacitiesof SPPS in organic solvents are listed in Table 1. As shown in Table1, the ion exchangecapacitiesin an organicsolventsystem are lower than thosein an aqueous system, and they are related to dielectric constant of the organic solvent. The dielectric constants of dioxane, THF, and water are 2.2, 7.4, and77.4, respectively, and the ion exchangecapacityvalues in eachorganic solventsystem are 3.60, 3.72, and 4.07 meq/g. As shown in Table 1, ion exchange capacityincreases with increasing solvent polarity.

Selectivity of Metallic Ions. The ion exchange capacity increased with increasingthecharge and atomicnumber of the ion in the same charge because ofthe electricattraction between exchangegroups and ions. They followed the gen­

eral orderofexchange for dilute metal solutions but changed slightly at higher concentrations and higher temperatures of metal solution and by the pH of metal solution. Table 2 showstherelative amount ofadsorbed metal ions in mixed metal solutionanalyzed by EDAX. The amount ofadsorp­ tion ions increased with increasing atomic number. From these results,itwasfound that ions withtwo positivecharges wereadsorbed much more rapidlythan ions with oneposi­ tive charge, and the ions with the same valence ions were adsorbedeasily as theatomicnumber increased.

EquilibriumConstantof Ion ExchangeReaction (Keq). The equilibrium constants ofion exchange reaction (Keq) between metal ions and the SPPS ion exchanger were obtained with thefollowingprocedure. It was supposed that the SPPS ion exchanger and metal picrate reacted asin the following equation.29

P- SO3H +Mn+nPi- M(P- SO3-)nMn+ + n• Picric Acid, (1) whereP - SO3H and (P - SO3-)nMn+,respectively,represent the free SPPS ion exchanger and SPPS ion exchanger bonded withmetalpicrate. Mn+nPi- is unbindingpicrate in the solution, the concentration of which was measuredby

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UV spectrophotometer.Theconcentrationsof all theseSPPS ionexchangers in Eq. (1) wereequalto [P- SO3H]total, and the numberof SPPS ionexchangers attachedtometal ions wasproportional to n. Substituting these conditionsinto eqn (1) producedEq. (2). The concentration of theresin bound by metal ions can becalculatedfromEq.(3).

[P - SO3H]

=[P- SO3H]free + [(P -,。3課"+] -n (2) [(P- SO3-)nMn+] = [M+nPi-]total - [M+nPi-]free (3) Theequilibriumconstantsof the ion exchange reaction for picrate saltofSPPS ion exchanger were calculated by fol­ lowing the Klotz equationobtained from Eqs. (1), (2), and (3), where [(P - SO-)nMn+] represents the concentration of SPPS ion exchanger bonded withmetal picrate.

1 [ P-SO3H]t°tal [ P-SO3H] +n

[(

P-SO-)nMn+ ] -=---=--- r [(P-SO-)nMn+ ] [(P-SO-)nMn+ ]

[P-SO3H]free +

=---+ n (4)

[(P-SO-)nMn ]

_ [(P-SO-)nMn+]

[ Picric Acid]n eq [P-SQHke •[M^nPi-]

1 [P - SO3H]fee • [PicricAcid]n

-- = --- + n (6) r Keq •[ P-SO3H]free •[ M「nPi-]free

If n wasequal to unity,theconcentration of picric acid was equal tothe concentration of bindingalkali metal ion from Eq. (1).

1 = [(P-SO-)nMn+] + 1 r Keq • [M+Pi-]free ' where 1/r was [P - SO3H]total/[(P - SO-)nMn+].

From the plot of 1/r versus [(P -SO-)nMn+] /[M+Pi-]free, Keq was obtainedfromthe slopeand the bonding number of binding SPPS ion exchanger (1/n = 1/1) was determined from the intercept, where [M Pi-]free represented unbind­ ingpicrate. Figures 2, 3, and 4 showthe plotsof1/rversus [(P-SO-)nMn+] /[M+Pi-]free of alkali metal ions for SPPS ion exchanger within therangefrom 10 oCto 40 oCin THF and dioxane.

As the dielectric constant (

£

) and the polarityof a solvent increased, the reaction constant of ion exchange increased.

As shown in Figures 2, 3, and 4, the equilibriumconstant of ionexchange reaction (Keq) inTHF (e= 7.4) waslarger than thatindioxane (e=2.2). With decreasingreactiontempera­ ture,the Keq value for alkali metalionsincreased. Thecalcu­ lated Keq valueswere presentedin Table 3. The equilibrium constants of ion exchange reaction (Keq) were calculated fromthe slopes ofthelines in Figures 2,3,and 4. The equi­ librium constantsofionexchangereaction(Keq) increasedin theorder ofLi+, Na+, and K+.

TheKeq valueswere plotted inFigure 5by means of Vn’t

Figure 2. Binding of Li-picrate to SPPS in (a) THF and (b) dioxane.

0 2 4 § 3 10 12 14

|P』마히■니司 f 卩业门기丄더

0 2 4 5 B 10 12 H P-SOita|f卩니 ・r거]Fl-

Figure 3. Binding of Na-picrate to SPPS in (a) THF and (b) dioxane.

Hoffmethod. Gibbs freeenergy (

4

G) was equaltothe-RT lnKeq in reactive solution.

A

G wasdependenton the temper­

ature.

d

(N

---=—---G/RT) _ AH

dT RT2

dlnKe A H

— -=—----

dT RT2

(8)

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AH (10) lnKeq =- -R--T-- + C

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Figure 4. Binding of K-picrate to SPPS in (a) THF and (b)

dioxane. Figure 5. In Keq vs. T-1 plots for reaction of SPPS with alkali metal

picrate in (a) THF and (b) dioxane.

Table 3. Keq of Alkali Metal Picrates for SPPS Ion Exchanger in THF and Dioxane

Temp.

(oC).

Keq

THF Li

Dioxane THF Na

Dioxane THF K

Dioxane

10 7.05 2.78 12.53 5.45 15.44 7.01

20 5.03 2.35 8.36 4.02 9.37 5.35

30 3.76 1.76 6.09 3.27 8.02 3.87

40 3.03 1.59 5.19 2.66 6.50 3.42

Enthalpy (

H)wascalculatedfromtheslopes oftheplots inFigure5,wheretheenthalpyof exchange reaction showed a negativevalue. Entropywas obtainedfrom

S=

A

HfT +R lnKeq, which showed a positive value (Table 4).

H value wasinthe range from-0.88 to -1.33 kcal/mol,whichimplied thatthe exchangereactionbetweenthe SPPSion exchanger and alkali picrate was exothermic. Similarly, it was found thatthe

S value was in the range from 1.42 to 4.41 cal/

Kmol. From

H and

S, Gibbs free energy

0

G) values wereobtained, rangingfrom -1.03 to -2.55 kcal/mol. Itwas found that theionexchangereactionof SPPS for alkalimet­ als in organic solventwas spontaneous reaction due to the negative value ofGibbs free energy. From these results, it

was concluded that the stability ofsystem increased when SPPSionexchanger and alkali metal ionsbound each other.

Therefore, the newly manufactured SPPS ion exchanger showedgoodionexchangecapability for alkalimetalionsin organic solvents.

Conclusion

Sulfonated poly(phenylene sulfide) (SPPS) wasprepared frompoly[methyl[4-(phenylthio)phenyl]sulfoniumtrifluoro­ methanesulfonate] (PPST). The reaction constants of ion exchange between SPPSasanionexchangeresin and alkali metalcation (Li, Na, K) dissolvedinTHF and dioxanewere determined. The sulfonation ofPPS was confirmed by the presence ofthe high absorption band of the SO3H groupat 1200cm-1 and the S-O bond at 650 cm-1. As thepolarityof the solvent increased and the reaction temperature decreas­ ed, the equilibrium constant of ion exchange reaction be­ came larger. The equilibrium constants of ion exchange reaction increasedin theorderof Li+, Na+, and K+.

4

H values ranged from -0.88 to -1.33 kcal/mol, and valuesrangedfrom 1.42 to 4.41 cal/Kmol. From the

4

Hand

S,Gibbs free energies(

4

G) were obtainedand rangedfrom -1.03 to-2.55 kcal/mol. It wasfoundthatthe ion exchange

Table 4. In Keq, Enthalpy, Entropy, and Gibbs Free Energy Changes on the binding of SPPS Ion Exchanger with Alkali Metals in THF and Dioxane

Alkali _ Metals

In Keq (at 25 oC) -4H (kcal/mol) 4S (cal/K - mol at 25 oC) -4G (kca血iol at 25 oC)

THF Dioxane THF Dioxane THF Dioxane THF Dioxane

Li 1.49 0.78 1.26 0.88 2.95 1.42 2.14 1.30

Na 2.01 1.30 1.33 1.06 4.00 2.58 2.52 1.83

K 2.22 1.54 1.23 1.11 4.41 3.06 2.55 2.02

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reactions of SPPS for alkali metal ions in organic solvent were spontaneous reactions, as indicatedby negative Gibbs free energies. When SPPS ion exchanger and alkali metal ionsbound eachother,ithad good ion exchange capability inorganicsolvent.

Acknowledgment. Thiswork wassupported by theKorea Scienceand EngineeringFoundationthroughtheAdvanced Materials ResearchCenter for Better Environmentat Taejon NationalUniversityofTechnology.

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186180.

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