Nantinee Mantaranona,
Masaya Kotakicd,
Chwee Teck Lime and
Suwabun Chirachanchai*ab
aThe Petroleum and Petrochemical College, Chulalongkorn University, Bangkok, Thailand. E-mail: csuwabun@chula.ac.th
bCenter for Petroleum, Petrochemical, and Advanced Materials, Chulalongkorn University, Bangkok, Thailand
cKaneka US Material Research, Kaneka Americas Holding, Inc., 800 Raymond Stotzer Pkwy, College Station, Texas 77843, USA
dCenter for Fiber and Textile Science, Kyoto Institute of Technology, Sakyoku, Kyoto 606-8585, Japan
eDivision of Bioengineering and Department of Mechanical Engineering, National University of Singapore, 7 Engineering Drive 1, 117574, Singapore
First published on 9th September 2016
Polyoxymethylene (POM) is an engineering plastic which tends to release formaldehyde under a melt-mixing process. The present work proposes a simple way to control the formaldehyde generation by a reactive blending with bisphenol-A and amine to form in situ benzoxazines via the Mannich reaction. Further thermal treatment leads to partial conversion of benzoxazines (BA-a) to polybenzoxazines (poly(BA-a)) and the POM–poly(BA-a) obtained is under a semi-interpenetrating network. At that time, the BA-a and poly(BA-a) reached the amorphous phase to induce an increase in elongation at break. When POM blends were electrospun, the molecular orientation of POM was induced and this synergistically functions with the poly(BA-a) network, resulting in an increase in tensile strength which never occurs in the bulk material. The present work shows, for the first time, not only reactive blending as a way to control the formaldehyde generation of POM but also an in situ semi-interpenetrating network as an approach to fine tune the properties of POM.
This comes to our idea about the formation of other polymers which require formaldehyde, such as phenolic resins in POM, as the way to control the formaldehyde generation of POM. In this viewpoint, bisphenol-A based benzoxazines (BA-a), which can be prepared from bisphenol-A, amine and formaldehyde via the Mannich reaction, are good candidates. In other words, by simply mixing bisphenol-A and amine with POM, the thermal processing of POM which leads to the formaldehyde generation might allow an in situ BA-a formation. In fact, after BA-a was formed, thermal treatment (150 °C) led to thermoset polybenzoxazines (poly(BA-a))11,12 (Scheme 1). In this way, the two steps of oxazine ring formation and oxazine ring opening polymerization allow us to prepare a reactive blending with POM after the blending with bisphenol-A and amine. When the benzoxazine ring is formed by consuming the formaldehyde generated from POM, the thermal stability of POM can be expected.
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Scheme 1 Reactive blend of bisphenol-A and aniline via melt-mixing process to form in situ BA-a and poly(BA-a) after POM deformaldehyde. |
The present work, therefore, aims to demonstrate a reactive blending to form BA-a and poly(BA-a) in POM matrices as an approach to retard the formaldehyde generation. The work extends to studies on the packing structure of the blend to clarify an in situ semi-interpenetrating network of poly(BA-a) where poly(BA-a) might play a role in the amorphous phases and tune the mechanical properties of POM, especially the elongation at break. The work also covers comparative studies between bulk sheets and electrospunfibers of the POM blends to clarify how the POM molecular orientation in nano-confinement synergistically functions with poly(BA-a) networks to further fine tune the mechanical properties.
FEA (ppm) = [(V2 − V1) × CHCl × 30.03 × 1000]/M | (1) |
In order to identify the existence of BA-a in the blend, the following procedures were carried out. Each blend was carefully dissolved in 1,1,1,3,3,3-hexafluoro-2-propanol (HFIP) to obtain a clear yellowish solution. The HFIP was evaporated to obtain a porous product. The porous product was washed thoroughly with CHCl3 to dissolve BA-a. At this point, the CHCl3 phase was evaporated and the precipitates obtained were characterized by FTIR.
The precipitates showed the characteristic peaks of benzoxazines, i.e. 920–950 cm−1 and 1500–1510 cm−1 (trisubstituted benzene ring), 1327 cm−1 (CH2 wagging of oxazine), 1233 cm−1 and 1031 cm−1 (ether linkage in benzoxazine ring) (Fig. S2†). This confirmed the formation of BA-a as a consequence of the in situ reactive blending in POM.
An attempt to confirm BA-a in the bulk POM blend sample by using CP-MAS NMR was also carried out. In the case of the pristine POM, the CH2 resonance of POM at 88.5 ppm is observed (Fig. 1A). For POM–BA-a such as POM–BA05a10 (Fig. 1B), the spectrum was curve-fitted to identify each peak clearly. Here, the peaks at 31 ppm and 41 ppm assigned to methyl group (carbon k) and quaternary carbon (carbon j), respectively, are observed. The peak at 151 ppm assigned to the aromatic carbon bonded to the oxygen atom of the oxazine ring (carbon e) and the peak at 95 ppm assigned to the aromatic carbon between the oxygen atom and nitrogen atom (carbon b) are also identified. It is important to note that the peaks at 126 ppm and 158 ppm which belong to carbon i′ and e′ of poly(BA-a) are also identified. This reveals that not only BA-a but also poly(BA-a) are formed in the POM matrix. The confirmation of BA-a and poly(BA-a) in POM after reactive blending confirms the reaction between bisphenol-A, aniline, and formaldehyde which was generated from POM during the melt-mixing process, as in Scheme 1.
Since BA-a was further polymerized to give poly(BA-a), the question here is which factors relate to the control the polymerization in POM.
As the disappearance of the oxazine ring, i.e. the C–O–C peak at 1233 cm−1, reflects the polymerization of poly(BA-a), the integral ratio between the C–O–C peak at 1233 cm−1 and the CH stretching of the CH3 group (2965 cm−1) determined the conversion of BA-a to poly(BA-a) as in the following equation:
![]() | (2) |
As shown in Fig. S3,† the conversion of BA-a to poly(BA-a) increased from 19% to 76% with an increase in bisphenol-A content from 0.023 mol to 0.23 mol. This confirmed that the bisphenol-A content was one of the main factors in the polymerization. This can be explained from the mechanism of the ring opening for which the hydrogen bond between phenol and oxazine ring is required in the initial step.14
The formaldehyde generation and consumption were traced by the formaldehyde emission amount (FEA) (Table S2†). The sample (10–20 g) was added to a test tube and heated at 200 °C for 2 h under nitrogen atmosphere. The pristine POM showed the FEA for 105.3 ppm. When the pristine POM was melted in a Brabender at 200 °C for 2 h, for so-called thermally treated POM, the FEA became as much as 8 times as high. In this work, it should be noted that the preparation of the in situ reactive blends was similar to that of the thermally treated POM but with addition of bisphenol-A and aniline. Bisphenol-A and aniline were added to the test tube containing POM and heated at 200 °C for 2 h under nitrogen atmosphere. It is clear that the FEA was still identified until the content of bisphenol-A was as high as 0.01 mole content (Table S2†). This indicated that above this bisphenol-A mole content, the formaldehyde generated from thermal decomposition of POM was completely consumed. In fact, when POM, bisphenol-A and aniline were reactively blended in a Brabender at 200 °C for 2 h, e.g. POM–BA05a10, the sample obtained did not show any FEA. This implied that the formaldehyde generated was completely consumed once the reactive blending was accomplished.
This comes to the question of how much formaldehyde was consumed in the in situ reactive blends. To answer this, the weight loss and char yield of POM–BA-a blends, which represented BA-a and poly(BA-a), were considered from TGA. The amount of both in moles also reflected the formaldehyde consumed. In fact, the pristine POM and the thermally treated POM are completely degraded at 420 °C without char yield (Fig. S4†) since there is no thermoset poly(BA-a) in the system. In the case of POM–BA-a blends, the weight loss, starting at 450 °C and rising to 600 °C, is observed in the range of 5–17 wt%, referred to the degradation of BA-a (Fig. 2A and S4†). The char yield, which reflected the cross-linked poly(BA-a), is observed from 6 wt% to 18 wt% at 600 °C (Fig. 2A and S4†). From the weight loss and the char yield, one can evaluate the amount of formaldehyde generated in the system. For example, POM–BA01a02 showed the weight loss of BA-a determined from 450 °C to 600 °C to be 5 wt% (0.008 mol). The char yield of poly(BA-a) at 600 °C is 6 wt% (0.008 mol). The result implied that the formaldehyde consumed in POM–BA01a02 was 0.064 mol (Table S1†). When the bisphenol-A content was increased to 7% mol and 10% mol (i.e. POM–BA07a14 and POM–BA10a20), the formaldehyde consumed was found to be around 0.20 mol (Table S1†). As the stoichiometry ratio of formaldehyde: bisphenol-A: aniline to form BA-a is 4:
1
:
2, the amount of formaldehyde can be calculated. For POM–BA10a20, the formaldehyde consumed is 0.20 mol, which is 85
714 ppm. This number is much higher than the amount identified in the FEA test. The reason behind this might be related to the conditions of the FEA test, in which only a small amount of sample under nitrogen atmosphere was used. Moreover, from the weight loss and the char yield, it can be concluded that the content of poly(BA-a) increased with an increase in bisphenol-A content and this supports the mechanism of benzoxazine ring opening, which requires the phenol.14
In order to trace the degradation temperature and the degradation component at each stage, TG-FTIR was applied. In the case of pristine POM (Fig. 3A), the degradation with HCHO peaks at 1745 cm−1 and 2800 cm−1 can be observed from 289 °C. From the HCHO peaks, the initial degradation temperature of pristine POM is identified at 289 °C. For the thermally treated POM, the HCHO peak starts at 251 °C (Fig. 3B), which is much lower than the pristine POM. This implies the ease of releasing formaldehyde if the pristine POM is once thermally treated. However, in the cases of POM–BA-a blends, for example POM–BA05a10, the release of formaldehyde can be observed at a temperature as high as 338 °C (Fig. 2B and 3C) which is 87 °C higher than those of POM and the thermally treated POM. It is also important to mention that the degradation temperature (Td) of POM–BA05a10 is 431 °C, which is higher than that of pristine POM (378 °C). This suggests that the formaldehyde released during the in situ reactive blending was reacted with bisphenol-A and aniline to form BA-a. As a consequence, the free formaldehyde to form formic acid was drastically reduced.
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Fig. 3 TG-FTIR spectra of gases generated during thermal degradation of (A) pristine POM, (B) thermally treated POM, and (C) POM–BA05a10 as a function of temperature. |
Moreover, in the case of POM–BA05a10, an additional Td at 475 °C was observed, indicating the formation of BA-a (Fig. S4†).
This comes to our question: what if the bisphenol-A and aniline were in excess? For example, in the case of POM–BA01a02, the TGA thermogram and derivative weight loss indicated that unreacted bisphenol-A and aniline were identified at 280 °C, and 167 °C, respectively (Fig. S4†). Therefore, this comes to our idea of extending the in situ BA-a formation by adding more formaldehyde. Table S1† indicates that 0.064 mol of formaldehyde generated was used to react with bisphenol-A and aniline. Thus, an additional 0.028 mol of formaldehyde was added so that the reaction with 0.023 mol of bisphenol-A and 0.046 mol of aniline is stoichiometric, i.e. formaldehyde: bisphenol-A: aniline for 4:
1
:
2, and the blend was termed POM–F04BA01a02. However, the blend obtained did not show a greater amount of poly(BA-a), as seen from the weight loss (3 wt%) at 450 °C to 600 °C and char yield (6.8 wt%). In fact, the result was no different from the case of POM–BA01a02 (6 wt%) (Table S1†). Surprisingly, POM–F04BA01a02 started to release formaldehyde at a much lower temperature, i.e. 232 °C as compared to the thermally treated POM which shows the release at 251 °C. The results suggest that the additional formaldehyde did not effectively react with bisphenol-A and aniline but rather initiated the degradation of POM. This might be due to the fact that the additional formaldehyde can be further oxidized to formic acid, leading to acidolytic degradation of the POM chain.4
In fact, the shift in glass transition temperature (Tg) also reflects the molecular chain penetration of two or more polymer chains.15 Although DSC is a good way to determine the Tg, for POM, the Tgs could not be clearly recognized since the heat capacity change (ΔCp) of crystalline polymer is very difficult to detect.16
DMA was, thus, applied to trace the ratio of loss modulus (E′′) to storage modulus (E′) (tanδ) as a function of temperature for pristine POM, thermally treated POM, and POM–BA-a blends (Fig. 4A). In the present work, the DMA was applied to measurements from −100 °C to 100 °C. In fact, a temperature above 130 °C may lead to the breaking of the samples. From the DMA analysis, the tan
δ of the pristine POM and the thermally treated POM are at about −68 °C (Fig. 4A(a and b)), which can be referred to the Tg of POM. For the POM–BA-a blends, two tan
δ are observed (Fig. 4A(c–h)) at around −68 °C and 20 °C, which referred to the Tgs of POM and poly(BA-a), respectively. In fact, both tend to shift to the lower temperature when bisphenol-A content is increased (Fig. 4B). For example, in the case of POM–BA10a20, the Tg of POM is identified at −80 °C while that of poly(BA-a) is at 17 °C (Fig. 4A(h)). For Tg of poly(BA-a), it was in the range from 17 °C to 26 °C. This might be due to the low molecular weight of poly(BA-a) that existed in the POM matrices (Table S3†). However, the decrease in Tg of POM for POM–BA-a blends implies the in situ formation of BA-a, the polymerization of BA-a, and the semi-interpenetrating network of poly(BA-a) in POM. As shown in Fig. 4A, the baseline at 50 °C to 100 °C is shifting up. This might be because the POM was in the α-relaxation state. This state is associated with the motions of the crystalline phase.17,18
It is important to confirm the semi-interpenetrating network of poly(BA-a) in POM matrices. In order to clarify this, the morphologies of the fracture surfaces of pristine POM and POM–BA-a blends were observed by SEM (Fig. S5†). The micrograph of POM–BA03a06 exhibited a rougher surface than that of pristine POM. This might be due to an incomplete semi-interpenetration of poly(BA-a) in POM matrices. In the case of POM–BA07a14 and POM–BA10a20, their micrographs exhibited smooth surfaces, suggesting the semi-interpenetrating poly(BA-a) in POM matrices.
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Fig. 5 WAXD patterns of (A) before extraction and (B) after extraction: (a) pristine POM, (b) POM–BA01a02, (c) POM–BA03a06, (d) POM–BA10a20 and (e) poly(BA-a). |
Moreover, the residues obtained from the CHCl3 phase show the halo position at 2θ = 19° (Fig. 5B(e)). This confirms that BA-a and poly(BA-a) form a semi-interpenetration network in POM matrices. The micro-structure was further investigated by 2D-SAXS. The circular patterns (Fig. S6†) indicated the random orientation of the lamella in the pristine POM, the thermally treated POM and POM–BA-a blends. The SAXS profile showed a scattering maximum at the relative qm position, suggesting a lamella stacking structure of the samples (Fig. S6†). The POM–BA-a blends showed slight changes in scattering maxima at the relative qm position as compared to those of the pristine POM and the thermally treated POM. The qm values slightly decreased until they could not be observed when the bisphenol-A content was increased. From qm values, the long period (L) can be calculated from the magnitude of the qm vector as L = 2π/qm. It was found that the L increased from 12.57 nm to 22.44 nm with an increase in bisphenol-A content from 0.023 mol to 0.11 mol (Fig. 7A). In the cases of POM–BA07a14 and POM–BA10a20, which contained 0.16 mol and 0.23 mol of bisphenol-A content, respectively, their L values could not be calculated because no circular pattern was observed. This implied the poly(BA-a) disturbed the packing of POM.
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Fig. 6 Mechanism of semi-interpenetrating network of poly(BA-a) in POM matrices. Blue: POM chain, pink: formaldehyde, purple: bisphenol-A, and brown: aniline. |
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Fig. 7 Reactive blends of POM under various bisphenol-A contents for; (A) long period, (B) elongation at break, and (C) tensile modulus (●) and storage modulus (○). |
It was found that in the case of POM–BA-a in sheet form, the E values decreased from 729 MPa to 219 MPa with an increase in bisphenol-A content from 0.023 mol to 0.23 mol. In other words, the tensile modulus decreases with an increase in poly(BA-a). For the POM–BA-a nanofibers, the E increases with an increase in bisphenol-A content (Fig. 8). For example, the E of the POM–BA10a20 nanofiber (26.7 GPa), to which 0.23 mol of bisphenol-A was added, increases almost 7-fold compared to that of the pristine POM nanofiber (3.8 GPa). This characteristic is attributed to the alignment of fibers which was promoted during the fiber formation process, as reported earlier.24
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Fig. 8 Reactive blends of POM under various contents of bisphenol-A for; poly(BA-a) content (●), tensile moduli of sheet (○) and single nanofiber (△). |
Footnote |
† Electronic Supplementary Information (ESI) available: Table of conditions to prepare in situ reactive blend of BA-a in POM together with weight loss, char yield and utilized formaldehyde, TGA, FTIR, SEM, and 2D-SAXS patterns. See DOI: 10.1039/c6ra18841a |
This journal is © The Royal Society of Chemistry 2016 |