Preparation and characterization of biodegradable condensation polyimide
Rong-Hsien Lin
a,*, Wei-Ming Wang
a, Yi-Hung Chen
b, Tzung-Han Ho
aaDepartment of Chemical and Material Engineering, National Kaohsiung University of Applied Sciences, Kaohsiung, Taiwan bDepartment of Chemical Engineering and Biotechnology, National Taipei University of Technology, Taipei, Taiwan
a r t i c l e i n f o
Article history:
Received 17 February 2012 Received in revised form 17 April 2012
Accepted 23 April 2012 Available online 12 May 2012
Keywords: Polyimide Biodegradable Condensation Poly(propylene fumarate)
a b s t r a c t
Various biodegradable polyimides (bio-PI) were successfully synthesized and investigated in this study. First, biodegradable oligomer, amine terminated poly (propylene fumarate) (PPF-NH2), was preliminarily
synthesized from poly (propylene fumarate) oligomer (PPF) and 3-chloropropylamine hydrochloride. The resulting PPF-NH2was subsequently used to react with equal mole ratio of 3,30,4,40-biphenyl
tetra-carboxylic dianhydride (s-BPDA) in the solvent to generate biodegradable poly (amic acid) (bio-PAA) through condensation reaction. Afinal product of biodegradable polyimide (bio-PI) was successfully obtained by immidization of bio-PAA at a low-temperature (120C) under the vacuum condition. A 3-component system of biodegradable polyimide (3C-bio-PI) was also synthesized by replacing different level of PPF-NH2by 4,40-oxydianiline (4,40-ODA) in previously mentioned bio-PI.
The biodegradation characterizations of the various bio-PIs (including 3C-bio-PI) were performed with phosphate buffer solution. Morphological changes for the biodegraded surface of the various bio-PIfilms were apparent after buffer solution test. Mechanism of morphological changes for the biodegraded surface is also proposed in this work. The bio-PIfilm synthesized from equal mole ratio of PPF-NH2and
s-BPDA was biodegraded more quickly than the 3-component system of biodegradable PIfilm incorporated with 4,40-ODA.
The thermal properties of various bio-PIs are slightly inferior to those of regular PI; however, it is comparable to those of regular PI. The mechanical property of various bio-PIs is a little worse than that of regular PI, but it’s still in the same order of magnitude.
Ó 2012 Elsevier Ltd. All rights reserved.
1. Introduction
Polyimides were widely used in electron devices, anti-soldiering
ink, and flexible printed circuit boards because of its excellent
thermal stability, low dielectric constant, and excellent mechanical properties. The recovery and treatment of waste polyimide is a considerable environmental problem because of the increase in the consumption of polyimide. We attempted to introduce a biodegradable polymer segment into polyimide chain to circumvent this problem. Poly (propylene fumarate) (PPF) is a
well-known biodegradable polymer [1e6]. It is a linear unsaturated
polyester, and may undergo a self-polymerization through its
unsaturated carbonecarbon double bond. In addition, it may
undergo crosslinking reaction to be a biodegradable network through the introduction of curing agent, such as N-vinyl pyrroli-dinone or PPF-diacrylate (PPF-DA). The cross-linked biodegradable network exhibited excellent mechanical properties and low water
uptake; its mechanical intensity and biodegradation ability can be
controlled by tuning the ratio of PPF/PPF-DA[7,8].
Elmalak et al.[5]produced a biomedical material in application
of bone-bonding, based on PPF and MMA as a matrix, and calcium
phosphate and calcium carbonate as fillers by controlling its
crosslinking density and molecular weight. This literature also
reported that PPF can be biodegraded to non-poisonous
compounds of propylene glycol and fumaric acid. This literature suggested that the di-ol functional groups on PPF molecule can react with other compounds to yield a PPF derivative with amine
groups on both ends (PPF-NH2). Consequently, we attempted to
synthesize PPF-NH2using the suggested method, as described in
this literature, and performed a condensational polymerization of
PPF-NH2with di-anhydrides to yield biodegradable polyimide.
Mikos et al.[6]presented a number of synthesis methods for PPF
in his patent, and subsequently presented a series of methods for
modifying PPF tofit the application in biomedical category. This
patent illustrated that PPF may undergo crosslinking reaction with curing agents to yield a biodegradable network. We referred to the synthesis methods, as stated in the patent, to synthesize PPF oligomer.
* Corresponding author. Tel.: þ886 7 3814526x5118; fax: þ886 7 3830674. E-mail address:[email protected](R.-H. Lin).
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Polymer Degradation and Stability
j o u r n a l h o m e p a g e : w w w . e l s e v i e r . c o m / l o c a t e / p o l y d e g s t a b
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Several researchers focused on modification and crosslinking of
PPF [9e13]. Among them, Gangula et al. [13] attempted to
synthesize amine terminated PPF (PPF-NH2).
In addition, most studies related to biodegradable polyimide focused on bio-absorbable materials, such as poly (anhydride-co-imides). Among these materials, polyanhydride has a hydrophobic main chain and an easily hydrolyzed anhydride linkage, resulting in a number of characteristics with favorable biocompatibility and
obvious biodegradability. However, its relatively inferior
mechanical strength limits its applications. Consequently, Langer
et al. [14e16] developed a biodegradable polymer comprising
polyanhydrides and polyimides. Because most polyimides have the advantages of excellent mechanical properties and thermal stability, a biodegradable copolymer with high performance may be obtained by incorporating biodegradable polyanhydride with polyimide (referred to as poly (anhydride-co-imides)). They per-formed the degradation test for various constitutes of poly (anhydride-co-imides) at varying pH values to investigate the
effect of pH value on the degradation. Langer et al.[17]also found
that degradation of polyanhydride was attributed to surface-eroding.
Laurencin et al.[18e20]conducted a series of studies on poly
(anhydride-co-imides), such as performing in vitro biolysis test for the decomposed products of poly (anhydride-co-imides). Situa-tions of decomposed products of those copolymer were in situ observed by an environmental scanning electron microscopy (ESEM) during the period of degradation of poly (anhydride-co-imides); the cell growth situation was also observed when the cells
were exposed to the decomposed products of those copolymer[18].
In addition, in vivo biolysis test for poly (anhydride-co-imides) was
also presented[19]. The biocompatibility between poly
(anhydride-co-imides) and bone cells was further investigated. Subsequently, they presented the effect of decomposed products of previously stated copolymer on the bone cells, such as growth rate and
geomorphology of the bone cells[20].
To obtain various mechanical properties, Gopferich et al.[21]
copolymerized PEG with PLA to obtain a biodegradable copol-ymer, followed by tethering various imide moieties on the ends of copolymer chains. Based on a series of biolysis tests, these copolymers were applicable to tissue engineering.
Biodegradable polymers consisting of polyimide were subjected
to application in biomedical category[14e21]; few investigations of
biodegradable polyimide containing PPF with high mechanical performance were reported. Consequently, we attempted to incorporate biodegradable segment of poly (propylene fumarate) (PPF) into polyimide main chain. First, PPF oligomer was
synthe-sized. Subsequently, PPF-NH2 was synthesized by converting
di-functional group ofeOH on PPF oligomer to another di-functional
group ofeNH2. Finally, biodegradable polyimide was synthesized
using the synthesized PPF-NH2 to undergo condensational
poly-merization with di-anhydrides. Furthermore, the mechanical properties, thermal stability, and degradation phenomena of these biogradable polyimides (bio-PI) were investigated.
In addition, it is well-known that an aromatic polyimide can be produced by successively conducting an operation for poly-condensing an aromatic tetracarboxylic acid with an aromatic diamine, and another operation for converting the resulting poly-condensation product, that is, a polyamic acid (PAA), into the cor-responding polyimide resin. The converting process, that is, an imidization reaction, was performed by a dehydration procedure at
an elevated temperature of approximately 250e310 C [22,23].
However, polyimide containing PPF segments (bio-PI) cannot be prepared under such elevated temperatures; otherwise, PPF segment in PI chain will undergo thermal decomposition. This problem was also addressed in this work.
2. Experimental 2.1. Materials
The main chemical compounds used are fumaryl chloride
(Acros, U.S.A.), propylene glycol (Aldrich, Germany),
3-chloropropylamine hydrochloride (Aldrich, U.S.A.), 3,30,4,40
-biphe-nyltetracarboxylic dianhydride (s-BPDA; Chriskev, U.S.A.), and 4,40
-oxydianiline (4,40-ODA; Aldrich, U.S.A.). These chemical
compounds were used as purchased without further purification;
and were used to synthesize PPF, PPF-NH2 and biodegradable
condensation PI (bio-PI). In addition, phosphate buffered saline
(SigmaeAldrich, U.S.A.) was used for the degradation test.
2.2. Instrumentation
The instruments and their operation conditions are as follows:
(1) Fourier Transform Infrared Spectrometer (FTIR; PerkineElmer
Spectrum ONE): FTIR spectrum was obtained on FTIR
spectrom-eter in an optical range of 400e4000 cm1by averaging 32 scans at
a resolution of 8 cm1, the sample of which was mixed with dried
KBr powder, and pressed into a pellet; (2) 1H NMR (Nuclear
Magnetic Resonance) spectra were obtained using an
Inova-500 MHz highfield FT NMR spectrometer. Samples were dissolved
in DMSO-d6. Chemical shifts (
d
) in ppm are reported relative toTMS; (3) the storage modulus (E0) was measured in DMA (Dynamic
Mechanical Analysis; PerkineElmer, Pyris Diamond) over the
temperature range of 25e460C at a heating rate of 10C/min, and
film size 40 20 mm with a thickness of approximately 30
m
m wereused for measurement. The frequency and amplitude were set to 1 Hz and 0.2 mm, respectively; (4) thermal stability and the weight loss were measured by TGA (Thermal Gravimetric Analysis;
PerkineElmer, Diamond TG/DTA). Samples of approximately
5e10 mg in weight were placed in platinum pans and scanned in
a TGA at a heating rate of 20C/min. A stream of nitrogen at aflow
rate of 100 ml/min1was used to purge the TGA chamber; (5) the
morphology changes of samples before and after degradation were observed in SEM (Scanning Electron Microscopy; JEOL-5610); (6)
the reaction results were justified by thin layer chromatography
(TLC) with acetate/hexane (1/3 v/v%) as an eluent, and (7) the number average molecular weights were measured by GPC (Gel Permeation Chromatography; Waters 717 plus) with 3 columns of
7.8 300 mm Styragel HR 2-4 THF in series and waters 2414
Refractive index detector. The sample of polymer was dissolved at
0.05e0.1 wt.% in THF. After sonication, the completely dissolved
solution wasfiltered with a 0.45
m
m pore-sizedfilter and injectedinto GPC, performed at aflow rate of 1 ml/min.
2.3. Synthesis and structure identification of Poly(propylene
fumarate) (PPF)[6]
A three-neck reactor was charged with 8.88 g potassium
carbonate (K2CO3), 27 mL of ethyl acetate (EA), and 9.12 g propylene
glycol (PG) in a completely dissolved situation, and controlled at
0C under a nitrogen atmosphere. Another completely dissolved
solution of 6.12 g fumaryl chloride in 8 mL of EA solvent (mole ratio
of fumaryl chloride/propylene glycol/K2CO3¼ 1/3/1.5) was slowly
added into the reactor over a period of 2 h by means of a dropping
funnel. Subsequently, the resultant mixture was raised to 25C and
stirred further for another 5 h to a complete reaction situation at this temperature. The reacted mixture was slowly poured into a separation funnel, and washed sequentially with a large amount of cold de-ionic water and saline several times to remove the
un-reacted reagents (PG, K2CO3). An appropriate amount of
(organic layer) to remove residual water, followed byfiltration of magnesium sulfate from organic layer. Furthermore, EA was evap-orated by a rotary vacuum operation, and a pale-yellow liquid product, that is, di-(2-hydroxypropyl) fumarate (DHPF), was
obtained. Finally, DHPF was subjected to inter-esterification for 1 h
at 160C under a reduced atmosphere of 2 cm Hg. A pale-yellow
viscous liquid of oligomer was subsequently obtained, that is, poly (propylene fumarate) (PPF). The overall reaction paths are
illustrated inScheme 1.
The synthesized PPF was characterized by its FTIR spectrum and
1H NMR spectrum. Shown inFig. 1are some corresponding FTIR
spectra of (a) propylene glycol, (b) fumaryl chloride, and (c) PPF
oligomer. Fig. 1 (c) indicates the characteristic absorptions at
3340 cm1 (OH), 1730 cm1(C]O in ester linkage), 1640 cm1
(C]C), and 1260 cm1(O in ester linkage). These characteristic
absorptions, nearly the same as those in patent[6], demonstrate
the structure of PPF. In addition, these stated characteristic absorptions result from cure (a) and cure (b), respectively, indi-cating that PPF oligomer was successfully synthesized from propylene glycol and fumaryl chloride.
The PPF oligomer was further verified by the1H NMR spectrum.
An analysis of the1H NMR spectrum was conducted to identify the
structure of the PPF oligomer, as shown inFig. 2. Each chemical shift
was individually assigned and associated with the identified
hydrogen atoms in the PPF oligomer, the structure of which was inserted above the spectrum. It should be mentioned that
1.207e1.244 ppm are attributed to the hydrogen atoms of the
methyl groups (indicated as a) within repeat unit (inner site);
however, 1.063e1.075 ppm are attributed to the hydrogen atoms of
the methyl groups (indicated as h) on both ends of oligomer (outer
side). Chemical shifts of 4.285e4.298 ppm and 3.990e3.997 ppm
are attributed to the hydrogen atoms of the methylene groups (indicated as f and g) on both ends of oligomer. Because PPF is an oligomer with various degrees of polymerization, hydrogen atoms on methyl group or on methylene group have various positions in PPF main chain, resulting in a small shift of a number of hydrogen peaks for the same group. Those chemical shifts demonstrate that PPF oligomer was successfully synthesized from propylene glycol and fumaryl chloride.
In addition, molecular weight of the synthesized PPF oligomer
was measured by GPC, as shown inFig. 3. A number of separated
peaks were observed, resulting from various degrees of polymeri-zation in the same pot of PPF oligomer. Each peak was individually
assigned and associated with the identified degree of
polymeriza-tion in the PPF oligomer. Degree of polymerizapolymeriza-tion was 1e4. The
average number molecular weight was calculated from the GPC spectrum as 347 g/mol, that is, average degree of polymerization was 1.7.
2.4. Synthesis and structure identification of amine terminated PPF
(PPF-NH2)
A three-neck reactor was charged with 3.25 g of 3-chloropropylamine hydrochlorid (CPH), 1.518 g of triethyl amine (TEA), and 25 mL of DMSO in a completely dissolved situation, and controlled at ambient temperature under a nitrogen atmosphere. Another completely dissolved solution of 2.34 g of previously synthesized PPF in 15 mL of DMSO solvent (mole ratio of PPF/CPH/
TEA¼ 1/2.5/1.5) was slowly added into the reactor over a period of
2 h using a dropping funnel. Subsequently, the resultant mixture was further stirred for another 24 h to a complete reaction situation at ambient temperature.
The reacted mixture was slowly poured into a separation funnel, and washed with a homogenously mixed solution of
Scheme 1. Synthesis paths of poly (propylene fumarate) (PPF).
dichloromethane and de-ionic water (with 1:1 v/v%) several times. The upper layer containing DMSO, water, and un-reacted reagents (CPH, PPF, TEA) was discarded. An appropriate amount of magne-sium sulfate anhydrous was added in the collected lower layer
containing PPF-NH2 and dichloromethane to remove residual
water, followed by filtration of magnesium sulfate from the
mixture. Furthermore, dichloromethane was evaporated by a rotary vacuum operation, and a yellow liquid product, that is, amine
terminated PPF (PPF-NH2) oligomer, was obtained. Structure of
PPF-NH2oligomer is shown asFig. 4.
The synthesized PPF-NH2was characterized by its FTIR
spec-trum and 1H NMR spectrum. Fig. 5 shows corresponding FTIR
spectra of (a) PPF, (b) 3-chloropropylamine hydrochloride, and (c)
PPF-NH2oligomer.Fig. 5(c) shows the characteristic absorptions at
3424 cm1(NH), 1730 cm1(C]O in ester linkage), 1642 cm1
(C]C), 1260 cm1 (O in ester linkage), and 1024 cm1 for
primary amine group, preliminarily demonstrating the structure of
PPF-NH2 oligomer. These stated characteristic absorptions result
from cure (a) and cure (b). In addition, a comparison ofFig. 5(b) and
Fig. 5(c) revealed that disappearing absorption bands ofeNH3þCl
at 3014 cm1were accompanied by the emerging absorptions of
primary amine group at 1024 cm1. This suggests that PPF-NH2
oligomer was successfully synthesized from PPF and
3-chloropropylamine hydrochloride. However, chemical structures
of PPF and PPF-NH2 are not easily discerned from FIIR spectra
because of their similar characteristic absorptions. Therefore, thin layer chromatography (TLC) was used to discern these structures. Results of TLC comparison revealed that the disappearing site of
PPF was accompanied by the emerging site for PPF-NH2, further
demonstrating that PPF-NH2 oligomer was successfully
synthe-sized from PPF and 3-chloropropylamine hydrochloride.
The synthesized PPF-NH2 was finally characterized by its 1H
NMR spectrum (not shown here). Chemical shifts of this
Fig. 2.1H NMR spectrum of poly (propylene fumarate) (PPF) oligomer.
Fig. 3. GPC spectrum of synthesized poly (propylene fumarate) (PPF) oligomer.
Fig. 4. Structure of amine terminated PPF (PPF-NH2) oligomer.
Fig. 5. FTIR spectra of (a) PPF oligomer, (b) 3-chloropropylamine hydrochloride, and (c) PPF-NH2oligomer.
[12] Jo S, Engel PS, Mikos AG. Synthesis of poly (ethylene glycol)-tethered poly (propylene fumarate) and its modification with GRGD peptide. Polymer 2000; 41:7595e604.
[13] Elati CR, Kolla N, Vankawala PJ, Gangula S, Chalamala S, Sundaram V, et al. Substrate modification approach to achieve efficient resolution: didesme-thylcitalopram: a key intermediate for escitalopram. Org Process Res Dev 2007;11:289e92.
[14] Uhrich KE, Thomas TT, Laurencin CT, Langer R. In Vitro degradation charac-teristics of poly (anhydrideimides) containing trimellitylimidoglycine. Jnl Appl Polym Sci 1997;63:1401e11.
[15] Uhrich KE, Larrier DR, Laurencin CT, Langer R. In Vitro Degradation Charac-teristics poly (anhydrideimides) containing Pyromellitylimidoalanine. J Polym Sci Part A Polym Chem 1996;34:1261e9.
[16] Attawia MA, Uhrich KE, Botchwey E, Langer R, Laurencin C. In vitro bone biocompatibility of poly (anhydride-co-imides) containing pyromellitylimi-doalanine. Jnl Orthop Res 1996;14:445e54.
[17] Seidel JO, Uhrich KE, Laurencin CT, Langer R. Erosion of poly (anhydride-co-imides): a preliminary mechanistic study. Jnl Appl Polym Sci 1996;62: 1277e83.
[18] Attawia MA, Uhrich KE, Botchwey E, Fan M, Langer R, Laurencin CT. Cyto-toxicity testing of poly (anhydride-co-imides) for orthopedic applications. Jnl Biomed Mater Res 1995;29:1233e40.
[19] Ibim SEM, Uhrich KE, Attawia M, Shastri VR, El-Amin SF, Bronson R, et al. Preliminary in vivo report on the osteocompatibility of poly (anhydride-co-imides) evaluated in a tibial model. Jnl Biomed Mater Res 1998;43: 374e9.
[20] Attawia MA, Herbert KM, Uhrich KE, Langer R, Laurencin CT. Proliferation, morphology, and protein expression by osteoblasts cultured on Poly (anhy-dride-co-imides). Jnl Biomed Mater Res 1999;48:322e7.
[21] Tessmar JK, Mikos AG, Gopferich A. Amine-reactive biodegradable diblock copolymers. Biomacromolecules 2002;3:194e200.
[22] Yu KH, Yoo YH, Rhee JM, Lee MH, Yu SC. Synthesis of poly ((amic acid)-co-(amic ester)) precursors and studies of their imidization using IR and FT-Raman spectroscopy. Mat Res Innovat 2003;7:51e6.
[23] Shantalii TA, Karpova IL, Dragan KS, Privalko EG, Privalko VP. Synthesis and thermomechanical characterization of polyimides reinforced with the sol-gel derived nanoparticles. Sci Technol Adv Mater 2003;4:115e9.
[24] Lin RH, Chinese patent 2011; CN 200810091403.6.
[25] Yue CL, Gross RA, McCarthy SP. Composting studies of poly (b -hydrox-ybutyrate-co-b-hydroxyvalerate). Polym Degrad Stab 1996;51:205e10. [26] Jang JC, Shin PK, Lee IM, Lee HS, Kim MN. Glucose effect on the biodegradation
of plastics by compost from food garbage. Polym Degrad Stab 2002;76:155e9. [27] Kuzyakov Y, Friedel JK, Stahr K. Review of mechanisms and quantification of
priming effects. Soil Biol Biochem 2000;32:1485e98.
[28] Rychter P, Biczak R, Herman B, Smylla A, Kurcok P, Adamus G, et al. Envi-ronmental degradation of polyester blends containing atactic poly (3-hydroxybutyrate). biodegradation in soil and ecotoxicological impact. Bio-macromolecules 2006;7:3125e31.
[29] Choi JS, Park WH. Effect of biodegradable plasticizers on thermal and mechanical properties of poly (3-hydroxybutyrate). Polym Test 2004;23: 455e60.
[30] Pena J, Corrales T, Barba II , Doadrio AL, Regi MV. Long term degradation of poly (ε-caprolactone) films in biologically related fluids. Polym Degrad Stab 2006;91:1424e32.
[31] Mugnozza GS, Schettini E, Vox G, Malinconico M, Immirzi B, Pagliara S. Mechanical properties decay and morphological behaviour of biodegradable films for agricultural mulching in real scale experiment. Polym Degrad Stab 2006;91:2801e8.