Open Access Article
Yong
Chen
*a,
Yang
Zhao
b,
Min
Xiao
c and
Yue-Zhong
Meng
c
aSchool of Light Industry & Engineering, Guangdong Polytechnic, Foshan 528041, P. R. China. E-mail: cheny78@gdpt.edu.cn
bGuangdong Biomaterials Engineering Technology Research Center, Institute of Biological and Medical Engineering, Guangdong Academy of Sciences, Guangzhou 510316, P. R. China. E-mail: drzhaoy88@163.com
cThe Key Laboratory of Low-Carbon Chemistry & Energy Conservation of Guangdong Province, School of Materials Science and Engineering, Sun Yat-sen University, Guangzhou 510275, P. R. China. E-mail: mengyzh@mail.sysu.edu.cn
First published on 9th January 2026
This study aimed to develop fully biodegradable ternary composite films based on poly(vinyl alcohol) (PVA), poly(propylene carbonate)-based polyurethane (PPC-PU), and poly(propylene carbonate) (PPC-X) for sustainable packaging applications. The films were prepared by melt blending pre-plasticized PVA1788 with PPC-PU and PPC-X at varying mass ratios, followed by hot-pressing. A comprehensive set of analyses-including mechanical tests, FTIR, SEM, DSC, TGA, gas permeability, water contact angle, and water absorption measurements-was conducted to evaluate the structure-property relationships. The results demonstrate that PPC-PU serves as both a compatibilizer and a toughener via hydrogen bonding and polar interactions with PPC-X and PVA. The optimal formulation, PVA/PPC-PU/PPC-X (30/30/40 wt%), exhibited a balanced performance: a tensile strength of 14.32 MPa, an elongation at break of 30.29%, a glass transition temperature of 44.6 °C, and a thermal degradation onset at 191 °C. The films showed moderate hydrophilicity, suitable for humidity regulation in fresh produce packaging. Notably, the composites displayed superior CO2 and oxygen barrier properties, with the 30/40/30 blend achieving a CO2 permeability of 5360 cm3 µm (m2 day)−1 and an O2 permeability of 1002 cm3 µm (m2 day)−1. However, water vapor permeability increased due to PVA's hydrophilicity. Overall, these ternary composites exhibit promising mechanical, thermal, and barrier properties, positioning them as viable and sustainable alternatives to conventional non-biodegradable plastics such as LDPE, PET, and PP, with significant potential to reduce petroleum dependence and promote carbon dioxide valorization.
Biodegradable polymers including cellulose, thermoplastic starch, polylactic acid (PLA), polyhydroxyalkanoates (PHAs), polycaprolactone (PCL), poly(1,4-butanediol Succinate) (PBS) and poly(butylene adipate-co-terephthalate) (PBAT) are recognized for their favorable environmental profile. A primary limitation for their use in high-barrier packaging, however, is their generally insufficient resistance to oxygen and water vapor transmission. This has spurred significant research into modification and surface coating technologies as a promising avenue for enhancing the performance of biodegradable films.3,4 Blending modification techniques involving the incorporation of metal oxides (e.g., zinc oxide, mesoporous silica, calcium carbonate, hydrotalcite, copper oxide),5–9 metal–organic frameworks (MOFs),10 natural minerals (e.g., graphene oxide, montmorillonite),11,12 or renewable natural resources (e.g., cellulose and its derivatives, lignin derivatives, bamboo flour, nanocellulose, zein, polydopamine, polycitric acid, polyaspartamide, rice husk)13–17 into polymer matrices such as PLA, PBAT, or PLA/PBAT blends have been shown to enhance the mechanical and barrier properties (against oxygen and water vapor) of the resulting composites. For instance, Mahsa Ansari et al. prepared a novel biodegradable nanocomposite film using a poly(lactic acid) (PLA)/poly(butylene adipate-co-terephthalate) (PBAT) matrix incorporated with zinc–aluminum layered double hydroxide (Zn–Al LDH) nanoparticles via melt compounding. They found that the nanocomposite containing 1 phr of nanoparticles exhibited the lowest water vapor transmission rate (WVTR) of 0.00244 g h−1 m−2, representing a 70% reduction compared to the unfilled material.5 Jissy Jacob et al. produced PLA composites with functionalized mesoporous silica (PLA/0.6SPA-MPS-ACN) using a solution casting method. Their results indicated that incorporating 5 wt% of the filler reduced the oxygen transmission rate (OTR) by 52%.8 Similarly, Zheng Cheng et al. developed a bamboo-plastic composite by mixing bamboo powder lignocellulose with PBAT resin granules (10 wt% bamboo content), followed by hot-pressing to form films. The resulting bamboo/PBAT bioplastic composite demonstrated a superior oxygen permeability of 1.48 × 10−2 cm3 m (m2 24 h 0.1 MPa)−1, while its water vapor permeability remained close to that of neat PBAT.13 Furthermore, Li Wu et al. fabricated PLA/poly(propylene carbonate) (PPC)/acetylated lignin (ACEL) films via melt blending and biaxial drawing, using PPC and ACEL as functional toughening components. The biaxially oriented films exhibited an exceptional oxygen permeability of 0.13 × 10−13 cm3 cm (cm2 s Pa)−1, surpassing the barrier performance of neat PLA.17 However, these improvements still remain at the experimental stage and fall significantly short of the performance requirements for high-barrier packaging materials. Moreover, advanced coating strategies deployed via wet deposition are pivotal for improving the barrier properties of polymers in sustainable packaging.18 Key approaches include organic/inorganic hybrid coatings, which provide tunable oxygen barriers but are often limited by mechanical fragility, and nanocomposite coatings, which offer excellent gas barrier performance yet raise questions regarding food-contact safety. While multilayer thin-film structures represent a viable approach, their economic feasibility depends on successful optimization. Critically, these innovations must align with circular economy principles, comply with evolving regulations such as the EU Packaging and Waste Regulation, and incorporate bio-based or biodegradable matrices to develop next-generation packaging that balances functionality with end-of-life sustainability.19,20 In summary, although these commercially applied polymer materials have achieved certain research progress, they still face several limiting factors for development. For instance, PBAT production relies entirely on non-renewable petroleum resources, and the material typically exhibits poor mechanical strength. Conversely, PLA is produced via microbial fermentation from agricultural feedstocks, which may compete with food resources, and it often suffers from high mechanical brittleness and high production costs.21
Consequently, ongoing research is dedicated to overcoming these drawbacks through the development of novel materials and modification strategies. An environmentally promising alternative, poly(propylene carbonate) (PPC), produced through the copolymerization of carbon dioxide and propylene oxide, was first commercialized by Empower Materials in 2010.22 However, unmodified PPC suffers from: low glass transition temperature (∼35 °C), limiting thermal stability, inadequate mechanical strength (tensile strength <10 MPa).23,24 Recent breakthroughs in PPC-P terpolymer synthesis (phthalate-modified) and PPC-X quadripolymers synthesis (cyclohexene carbonate phthalate-modified) by Sun Yat-sen University's research group, demonstrated enhanced thermal stability (Tg up to 54 °C for PPC-P/116 °C for PPC-X) and high mechanical strength (43 MPa for PPC-P/53.9 MPa for PPC-X), but retained suboptimal toughness (elongation at break below 5% for PPC-P/10% for PPC-X),25–27 which restricts its widespread use. Consequently, developing effective toughening strategies for PPC-P/PPC-X represents a critical research challenge. To date, only a limited number of studies have explored this area, primarily employing two approaches: (1) physical blending modification and (2) chemical chain extension or cross-linking. For instance, Zhang T. W. et al. from Meng's group prepared PPC-P/PBAT blends with 30–50 wt% PBAT and found that PBAT incorporation improved thermal stability and elongation at break but compromised barrier properties.28 Similarly, Deng J. T. et al. achieved an optimal property balance using reactive compatibilization with a dual-component system of methylene diphenyl diisocyanate (MDI) and glycerol (3
:
1 molar ratio) at 2 wt% content in a PPC-P/PBAT (75 wt%
:
25 wt%) matrix. The chain extender significantly enhanced thermal stability and tensile elongation, though barrier performance deteriorated with increasing PBAT content. Notably, samples containing the chain extender exhibited superior barrier properties compared to unmodified blends at the same composition.29 Although both above-mentioned modification approaches improved the overall mechanical properties of PPC-P, the high PBAT incorporation ratio significantly compromised its gas barrier performance and negative carbon characteristics. Concurrently, no studies have yet reported the modification of PPC-X (tetrapolymer with analogous backbone structure to PPC-P, Scheme 1) in prior literature. Therefore, the goal was to identify a modifier capable of substantially improving the mechanical properties of PPC-X while maintaining its acceptable gas barrier characteristics, thereby obtaining a composite composed of biodegradable constituents with confirmed degradation potential.30
Poly(vinyl alcohol) (PVA), a semicrystalline polymer, is widely recognized for its superior oxygen barrier properties (OP < 0.1 cm3 mm [m2 day atm]−1) and complete biodegradability in food packaging applications. It is polymerized through vinyl acetate followed by hydrolysis with controlled saponification degrees ranging from 70% to 99%. The molecular structure of PVA features densely packed hydroxyl groups that establish robust hydrogen bonding networks, resulting in exceptional gas barrier performance.31 For instance, recent studies on EVOH/PVA blend systems (LDPE/EVOH-PVA/LDPE multilayers) have demonstrated that incorporating PVA (15vol%) via melt-blending significantly enhances oxygen barrier properties while preserving thermal-mechanical performance, attributed to improved morphological compatibility from structural similarity between PVA segments and EVOH matrices.32 Wu et al. studied bio-based PA610/PVA blends and found that the oxygen barrier properties of the composite blown films depended on composition. The optimal performance was achieved at critical PVA contents inversely related to the degree of polymerization (10 wt% for DP1400, 15 wt% for DP800, 20 wt% for DP500), where DSC/DMA/WAXD analyses confirmed molecular-level miscibility below these thresholds due to enhanced intermolecular interactions between PA610 and PVA. The results showed performance comparable to EVOH copolymer while maintaining single-phase thermal characteristics.33 Zeng et al. investigated the impact of film-forming methods including solution casting, blown film extrusion and extrusion casting on the structural and physical properties of PVA films. The results showed that both blown film and solution-cast films exhibited high tensile strength, excellent puncture resistance, and superior oxygen barrier properties.34 It is evident that PVA exhibits excellent oxygen barrier properties, and its incorporation into composite films significantly enhances oxygen barrier performance while preserving biodegradability. Thus, introducing PVA into PPC-X matrices is expected to further improve oxygen barrier characteristics. However, the poor miscibility between highly hydrogen-bonded PVA and weakly polar PPC-X necessitates a compatibilizer to enhance interfacial adhesion. Polycarbonate-based polyurethane (PPC-PU), synthesized from biodegradable low-molecular-weight polycarbonate polyols (PPCDL) via epoxide/CO2 copolymerization, serves as a promising candidate.35–37 This FDA-approved biodegradable elastomer for food-contact applications contains carbamate groups capable of strong hydrogen-bonding interactions, exhibiting superior mechanical elasticity, hydrolysis resistance, abrasion resistance, chemical stability, and biodegradability compared to conventional polyurethanes.30
In this study, interfacial engineering plays a critical role in balancing barrier properties and processability, aligning with polymer composite design principles. Polyvinyl alcohol (PVA) is incorporated to enhance oxygen barrier performance, while polycarbonate-based polyurethane (PPC-PU) serves as an interfacial compatibilizer and toughener, enabling controlled dispersion of PVA while preserving CO2 and O2 barrier properties. Further investigation is needed to determine the optimal component concentrations required to achieve these synergistic effects. In contrast to conventional packaging material preparation technologies, the proposed design strategy offers several key advantages: it achieves high CO2 utilization efficiency, thereby reducing dependence on petroleum-based resources; the resulting materials are free of metallic compounds, mitigating safety concerns associated with metal ion migration in food contact applications; and the approach demonstrates strong potential to significantly enhance gas barrier performance, contributing to the development of sustainable packaging solutions.
:
0.15
:
0.05 wt%) were precisely weighed and fed into a premixing apparatus. The mixture was premixed at room temperature (25 ± 2 °C) for 5 min at 2000 rpm. The premixed blend was then transferred to a ceramic tray and placed in a constant-temperature oven at 80 °C for 10 h to enable thorough diffusion of glycerol and PEG-4K into the PVA1788 matrix, achieving effective preplasticization. This procedure ensures uniform plasticizer distribution within the polymer structure prior to further processing.
| Entry | PVAa (wt%) | PPC-PU (wt%) | PPC-X (wt%) | (xPVA/yPPC-PU/zPPC-X, wt%) |
|---|---|---|---|---|
| a Pre-plasticized according to the procedure described in Section 2.2.1. | ||||
| 1 | 20 | 10 | 70 | 20/10/70 |
| 2 | 20 | 20 | 60 | 20/20/60 |
| 3 | 20 | 30 | 50 | 20/30/50 |
| 4 | 20 | 40 | 40 | 20/40/40 |
| 5 | 30 | 10 | 60 | 30/10/60 |
| 6 | 30 | 20 | 50 | 30/20/50 |
| 7 | 30 | 30 | 40 | 30/30/40 |
| 8 | 30 | 40 | 30 | 30/40/30 |
| 9 | 40 | 10 | 50 | 40/10/50 |
| 10 | 40 | 20 | 40 | 40/20/40 |
| 11 | 40 | 30 | 30 | 40/30/30 |
| 12 | 40 | 40 | 20 | 40/40/20 |
| 13 | 100 | 0 | 0 | 100/0/0 |
| 14 | 0 | 100 | 0 | 0/100/0 |
| 15 | 0 | 0 | 100 | 0/0/100 |
| 16 | 0 | 30 | 70 | 0/30/70 |
Thermogravimetric analysis (TGA) was performed on a NETZSCH TG 209F3 instrument (NETZSCH-Gerätebau GmbH, Germany) in a nitrogen atmosphere with a flow rate of 50 mL min−1. Samples were heated dynamically from 35 °C to 600 °C at a heating rate of 10 °C min−1. The isothermal thermogravimetric analysis (ITG) was performed under a nitrogen flow rate of 20 mL min−1, with heating from 50 °C to 200 °C at a rate of 10 °C min−1, followed by an isothermal hold at 200 °C for 35 minutes.
Thermal transitions of the samples were evaluated using differential scanning calorimetry (DSC Q2000, TA Instruments, New Castle, DE) via the following procedure: an initial heating from 25 °C to 160 °C at 10 °C min−1 under N2 at 50 mL min−1, followed by a 2-minute isothermal hold; rapid cooling to −70 °C at 10 °C min−1 using liquid nitrogen cooling; and a second heating to 160 °C at the same rate to remove thermal history. Glass transition temperatures (Tg) were determined from the second heating scan.
Fourier transform infrared (FTIR) spectroscopy was conducted on a Bruker Invenio S FTIR spectrometer (Bruker Optics China, Beijing) equipped with a diamond ATR accessory. The samples were prepared by compression molding at 150 °C in a hydraulic hot press to form uniform thin films with thicknesses between 5 and 8 μm. Spectra were acquired by averaging 32–64 scans at a resolution of 4 cm−1 across the mid-infrared region from 400 to 4000 cm−1. Background spectra were collected under ambient conditions and automatically subtracted from all sample measurements to minimize atmospheric contributions.
Morphological analysis of fracture surfaces was performed using cryogenic preparation methods. Specimens with a thickness of 1 mm were submerged in liquid nitrogen for 120 seconds to induce brittle fracture and subsequently dried at ambient conditions. A 30 nm gold layer was deposited using a high-performance ion sputtering system (108, Cressington Scientific Instruments, Watford, UK) with a deposition current of 25 mA for 30 seconds. High-resolution images were acquired using a Phenom Pro X desktop SEM (FUNA Scientific Instruments, Shanghai, China) operated at 15 kV under high vacuum conditions of 5 × 10−5 Torr and a working distance of 10 mm.
Gas barrier performance was quantitatively evaluated through standardized permeability measurements. Prior to testing, all samples underwent 48-hour conditioning at 23 ± 2 °C and 50 ± 5% RH. The thickness of all samples was measured in accordance with the standard procedure by a digital thickness gauge, which involved taking five measurements at the four corners and the geometric center, with the average value being used for the gas permeability test. The oxygen permeability coefficient (OP) were determined with an OX-TRAN 2/12R system (AMETEK MOCON, USA) following ISO 15105-1:2007 at 23 ± 0.5 °C. Similarly, the carbon dioxide permeability coefficient (CO2P) was measured using a PERMATRAN-C 4/30 analyzer (same manufacturer) under identical thermodynamic conditions. Water vapor permeability coefficient (WVP) was characterized with a MOCON 3/61 instrument (AMETEK MOCON) in accordance with ASTM F-1249 at 23 °C and 50% RH.
Water absorption was characterized in accordance with ASTM D570-22. Square specimens measuring 60 × 60 × 1 mm3 were prepared by compression molding with a flat vulcanizing press and then dried in a vacuum oven at 50 °C for 24 h to remove residual moisture. The initial dry mass (m1) of each sample was measured using a precision analytical balance with 0.1 mg resolution. All samples were fully immersed in deionized water maintained at 25.0 ± 0.5 °C for 24 h. After immersion, surface moisture was promptly blotted with lint-free filter paper and the saturated mass (m2) was determined within 30 seconds to minimize evaporation loss. The water absorption percentage was calculated as:
| Water absorption (wt%) = [(m2 − m1)/m1] × 100% |
Surface wettability was evaluated by static contact angle measurements following ASTM D7334-08. Square specimens (20 × 20 × 1 mm3) were ultrasonically cleaned at 40 kHz in analytical-grade isopropanol for 10 minutes and dried using a high-purity nitrogen jet (N2 ≥ 99.999%). Measurements were carried out on a commercial contact angle goniometer featuring a high-resolution CCD camera (5 μm per pixel) and a temperature-controlled stage set to 25.0 ± 0.5 °C. Ultrapure water droplets (5.0 μL, 18.2 MΩ cm) were dispensed using a precision syringe with a 0.5 mm flat-tipped needle under static conditions. Images were captured at 5 seconds after deposition to minimize evaporation effects. Contact angles were determined via Young–Laplace fitting using Attension Theta software with the Drop Analysis module, with five replicates performed at randomized locations (≥5 mm apart) to account for surface heterogeneity. All procedures were conducted under controlled ambient conditions (23 ± 2 °C, 50 ± 5% RH) to ensure reproducibility.
| Sample | Tensile strength (mean ± SD) (MPa) | Elongation at break (mean ± SD) (%) | Yong's modulus (mean ± SD) (MPa) |
|---|---|---|---|
| PVA | 42.37 ± 0.50 | 585.00 ± 2.83 | 332.22 ± 14.14 |
| PPC-PU | 10.88 ± 0.22 | 931.89 ± 7.28 | 50.07 ± 2.82 |
| PPC-X | 37.52 ± 0.28 | 3.76 ± 0.28 | 1798.17 ± 28.28 |
| 20/10/70 | 25.56 ± 0.22 | 3.04 ± 0.06 | 1287.35 ± 15.21 |
| 20/20/60 | 19.74 ± 0.23 | 7.51 ± 0.28 | 1051.57 ± 16.32 |
| 20/30/50 | 16.08 ± 0.25 | 20.13 ± 0.71 | 737.10 ± 21.21 |
| 20/40/40 | 12.56 ± 0.24 | 51.42 ± 1.41 | 475.13 ± 14.14 |
| 30/10/60 | 25.04 ± 0.26 | 3.53 ± 0.28 | 1381.73 ± 22.57 |
| 30/20/50 | 18.39 ± 0.23 | 11.30 ± 0.71 | 856.26 ± 20.25 |
| 30/30/40 | 14.32 ± 0.22 | 30.29 ± 1.47 | 584.59 ± 19.80 |
| 30/40/30 | 11.20 ± 0.21 | 78.86 ± 2.83 | 283.63 ± 13.57 |
| 40/10/50 | 14.45 ± 0.25 | 4.93 ± 0.29 | 787.80 ± 22.26 |
| 40/20/40 | 13.61 ± 0.22 | 12.32 ± 0.57 | 659.86 ± 14.21 |
| 40/30/30 | 12.09 ± 0.20 | 24.03 ± 1.06 | 574.77 ± 21.23 |
| 40/40/20 | 8.56 ± 0.21 | 94.95 ± 1.44 | 79.77 ± 2.83 |
The incorporation of PVA and PPC-PU significantly improved the toughness of PPC-X, as reflected by a systematic increase in elongation at break. At a fixed PVA content of 20 wt%, the elongation at break increased from 3.04% to 51.42% as the PPC-PU content increased from 10 wt% to 40 wt%, while the tensile strength decreased from 25.25 MPa to 12.56 MPa. A similar linear enhancement in elongation was observed when the PVA content was held constant at 30 wt% or 40 wt% with increasing PPC-PU loadings. Furthermore, increasing the PVA content enhanced the toughening effect at any given PPC-PU content. For example, with 40 wt% PPC-PU, the elongation at break increased from 51.42% to 94.95% as the PVA content increased from 20 wt% to 40 wt%.
These results indicate that PPC-PU acts as an effective compatibilizer and toughening agent for PVA/PPC-X blends. This behavior is attributed to two primary factors: the presence of shared poly(propylene carbonate) segments in PPC-PU and PPC-X, which improves miscibility, and the hydrogen bonding and polar–polar interactions between the urethane and carbonate groups in PPC-PU and the hydroxyl groups in PVA. Additionally, carbonate groups in PPC-X contribute to polar interactions with PVA, further enhancing the interfacial adhesion between the phases (Fig. 2). The Young's modulus values of pure PPC-X, PPC-PU, and preplasticized PVA were 1789.17 MPa, 332.22 MPa, and 50.07 MPa, respectively. Upon forming composites, the Young's modulus of the composite films showed a decreasing trend. The PPC-PU elastomer contributed most significantly to this reduction. When the PVA content was held constant at 30 wt% and the PPC-PU content increased from 10 wt% to 40 wt%, the modulus of the ternary composite films dropped from 1381.73 MPa to 283.63 MPa. Similarly, with PPC-PU fixed at 30 wt% and PVA content rising from 20 wt% to 40 wt%, the modulus decreased from 737.10 MPa to 574.77 MPa. This decline in modulus is mainly due to the substantially lower modulus of PPC-PU and pre-plasticized PVA compared to PPC-X, resulting in an overall reduction in the modulus of the composite system after blending. The synergistic effect of these interactions results in significant toughening of the PPC-X matrix. However, a conventional trade-off between mechanical strength and toughness was observed, consistent with typical behavior in polymer blends.
O stretching of carbonyl groups, and (iii) a distinct peak at 1530 cm−1 resulting from N–H bending vibrations, collectively indicative of intermolecular hydrogen bonding within the composites. The signals at 2986 cm−1 are assigned to aromatic C–H stretching vibrations present in both PPC-X and PPC-PU, while adjacent peaks at 2934 cm−1 and 2881 cm−1 correspond to asymmetric and symmetric –CH2– stretching modes, respectively, common to all components. The spectral region between 1400 and 1600 cm−1 reveals fingerprint vibrations associated with aromatic ring skeletons, and absorptions between 1061 and 1230 cm−1 are characteristic of asymmetric C–O–C stretching from ester/ether linkages and terminal hydroxyl groups. These spectral features confirm the molecular structures and intermolecular interactions within the PVA/PPC-PU/PPC-X composite system, consistent with the mechanism proposed in Fig. 2.
![]() | ||
| Fig. 3 FTIR spectra of PVA/PPC-PU/PPC-X composites (1: PPC-X; 2. PPC-PU; 3: preplasicized PVA. 4–9: xPVA/yPPC-PU/zPPC-X (wt%) = 20/30/50, 30/10/60, 30/20/50, 30/30/40, 30/40/30, 40/30/30). | ||
| Entry |
T
d,5%
/°C |
T
d,max1
/°C |
T
d,max2
/°C |
|---|---|---|---|
| a 5 wt% weight loss temperature. b The first maximum degradation rate temperature. c The second maximum degradation rate temperature. d Not detected. | |||
| PPC-X | 227.5 | 245.5 | 353.3 |
| PPC-PU | 236.3 | 289.6 | NDd |
| Peplasticized PVA | 107.5 | 224.2 | 366.4 |
| 0/30/70 | 233.6 | 282.2 | 341.1 |
| 20/30/50 | 192.5 | 206.8 | 301.1 |
| 30/10/60 | 169.3 | 205.4 | 305.6 |
| 30/20/50 | 192.0 | 208.3 | 301.4 |
| 30/30/40 | 191.5 | 209.2 | 302.6 |
| 30/40/30 | 176.2 | 210.7 | 290.7 |
| 40/30/30 | 166.5 | 210.2 | 292.5 |
![]() | ||
| Fig. 6 SEM images of cryogenically fractured PVA/PPC-PU/PPC-X blends with varying compositions (xPVA/yPPC-PU/zPPC-X, wt%): (a1–h1) 2000×; (a2–h2) 5000×. | ||
![]() | ||
| Fig. 7 Water contact angle (a) and absorption behavior (b) of the PVA/PPC-PU/PPC-X composites (xPVA/yPPC-PU/zPPC-X, wt%). | ||
P) of neat PPC-X was measured as 5180 cm3 µm (m2 day)−1. The introduction of PVA into the PPC-PU/PPC-X system markedly increased the CO2 permeability coefficient of the ternary composite films, with values rising consistently as the PVA content increased. Specifically, the highest permeability coefficient value of 6906 cm3 µm (m2 day)−1 was observed for the film containing 30 wt% PVA and 10 wt% PPC-PU. In contrast, when the PVA content was fixed at either 20 wt% or 30 wt% and the PPC-PU loading was raised from 10 wt% to 40 wt%, the CO2 permeability coefficient decreased linearly. For instance, at 40 wt% PPC-PU, the permeability coefficient values reached 5417 and 5360 cm3 µm (m2 day)−1 for the 20/40/40 and 30/40/30 (wt%) of PVA/PPC-PU/PPC-X blends, respectively. Furthermore, increasing the PVA content from 30 wt% to 40 wt% at a constant PPC-PU content of 30 wt% had only a minimal effect on CO2 permeability coefficient.
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| Fig. 8 Carbon dioxide permeability coefficient of PVA/PPC-PU/PPC-X composite films (xPVA/yPPC-PU/zPPC-X, wt%). | ||
| Entry | xPVA/yPPC-PU/zPPC-X (wt%) | Thickness (µm) (mean ± SD) | Entry | xPVA/yPPC-PU/zPPC-X (wt%) | Thickness (µm) (mean ± SD) |
|---|---|---|---|---|---|
| 1 | 0/0/100 | 260 ± 4.24 | 7 | 30/10/60 | 233 ± 2.37 |
| 2 | 0/100/0 | 216 ± 2.38 | 8 | 30/20/50 | 241 ± 2.82 |
| 3 | 20/10/70 | 237 ± 1.41 | 9 | 30/30/40 | 213 ± 2.13 |
| 4 | 20/20/60 | 212 ± 1.51 | 10 | 30/40/30 | 210 ± 2.19 |
| 5 | 20/30/50 | 231 ± 2.82 | 11 | 40/30/30 | 231 ± 2.42 |
| 6 | 20/40/40 | 227 ± 2.53 |
These variations are primarily governed by the compatibility of PVA within the composite. As indicated in Fig. 6, low PPC-PU content resulted in poor compatibility between PVA and PPC-X, yielding weak interfacial adhesion and ample interfacial free volume, which enhanced CO2 diffusion coefficient. Conversely, when the PPC-PU content reached 30 wt% or higher, the enhanced interfacial adhesion constrained gas transport along the interfaces, necessitating diffusion through the bulk matrix and thereby decreasing diffusion coefficient while reducing permeability. Moreover, with PPC-PU fixed at 30 wt%, only a marginal reduction in permeability coefficient was observed as the PVA content increased from 20 wt% to 40 wt%, further underscoring the critical role of interfacial compatibility in governing gas transport behavior. Even at 40 wt% PPC-PU, the permeability coefficient of the composite remained slightly higher than that of neat PPC-X. The result may be attributed to an overall increase in diffusion and solubility resulting from the incorporation of both preplasticized PVA and PPC-PU, combined with moisture-induced plasticization caused by the hydrophilic PVA, thereby collectively compromising the barrier resistance to CO2.
740 cm3 µm (m2 day)−1 for neat PPC-PU, respectively. The oxygen permeability coefficient of the ternary blend films exhibited a decreasing trend with increasing content of both PVA and PPC-PU. When the PVA content was held constant, the oxygen permeability coefficient decreased linearly with higher PPC-PU loadings. Similarly, with PPC-PU fixed at 30 wt%, increasing the PVA content from 20 wt% to 40 wt% also resulted in a linear reduction in permeability coefficient. These findings clearly demonstrate that both components contribute to improved oxygen barrier performance. Notably, when PVA content was maintained at 30 wt% and PPC-PU exceeded 30 wt%, the oxygen permeability coefficient of certain composite films fell slightly below that of neat PPC-X. Specifically, compositions of 30/30/40 and 30/40/30 (PVA/PPC-PU/PPC-X, wt%) exhibited oxygen permeability coefficient values of 1015 cm3 µm (m2 day)−1 and 1002 cm3 µm (m2 day)−1, respectively. Moreover, with PPC-PU content fixed at 30 wt%, increasing PVA to 40 wt% further reduced the oxygen permeability coefficient to 982 cm3 µm (m2 day)−1. This systematic variation indicates that PVA content plays a primary and more sensitive role in controlling the oxygen barrier properties, primarily by significantly reducing the oxygen diffusion coefficient (D). This reduction is largely attributed to the increased crystallinity and strong hydrogen bonding within the PVA phase, which decreases the polymer's free volume and restricts chain mobility, thereby hindering the passage of gas molecules. To achieve high barrier performance, the PPC-PU content should be no less than 30 wt%, which aligns with its compatibilizing function within the blend to assure a dense interface and minimize defects. Above this threshold, the strengthened interfacial adhesion eliminates easy diffusion pathways along the interfaces, forcing oxygen molecules to traverse the bulk material, which correspondingly lowers the effective diffusion coefficient (D). Furthermore, when the PVA content exceeds 30 wt%, its inherent superior barrier properties, driven by its low intrinsic oxygen solubility (S) due to high polarity and strong interchain interactions, significantly enhance the overall oxygen resistance of the composite films.
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| Fig. 9 Oxygen permeability coefficient of PVA/PPC-PU/PPC-X composite films (xPVA/yPPC-PU/zPPC-X, wt%). | ||
| Entry | xPVA/yPPC-PU/zPPC-X (wt%) | Thickness (µm) (mean ± SD) | Entry | xPVA/yPPC-PU/zPPC-X (wt%) | Thickness (µm) (mean ± SD) |
|---|---|---|---|---|---|
| 1 | 0/0/100 | 253 ± 2.52 | 7 | 30/10/60 | 226 ± 1.28 |
| 2 | 0/100/0 | 220 ± 1.23 | 8 | 30/20/50 | 235 ± 2.24 |
| 3 | 20/10/70 | 230 ± 2.01 | 9 | 30/30/40 | 221 ± 1.52 |
| 4 | 20/20/60 | 217 ± 1.21 | 10 | 30/40/30 | 220 ± 1.34 |
| 5 | 20/30/50 | 235 ± 1.67 | 11 | 40/30/30 | 235 ± 2.15 |
| 6 | 20/40/40 | 222 ± 1.23 |
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| Fig. 10 Water vapor permeability coefficient of PVA/PPC-PU/PPC-X composite films (xPVA/yPPC-PU/zPPC-X, wt%). | ||
| Entry | xPVA/yPPC-PU/zPPC-X (wt%) | Thickness (µm) (mean ± SD) | Entry | xPVA/yPPC-PU/zPPC-X (wt%) | Thickness (µm) (mean ± SD) |
|---|---|---|---|---|---|
| 1 | 0/0/100 | 240 ± 2.52 | 7 | 30/10/60 | 235 ± 1.97 |
| 2 | 0/100/0 | 231 ± 2.13 | 8 | 30/20/50 | 226 ± 1.42 |
| 3 | 20/10/70 | 235 ± 2.32 | 9 | 30/30/40 | 232 ± 1.63 |
| 4 | 20/20/60 | 225 ± 1.67 | 10 | 30/40/30 | 218 ± 1.22 |
| 5 | 20/30/50 | 227 ± 1.44 | 11 | 40/30/30 | 233 ± 2.25 |
| 6 | 20/40/40 | 230 ± 2.05 |
Overall, the PVA/PPC-PU/PPC-X ternary composite films exhibits superior barrier performance against CO2, O2 and water vapor. Nevertheless, compared to commercially established biodegradable composites such as PBAT, PLA, and other reported analogous biodegradable film systems (Table 7),29,43–50 the PVA/PPC-PU/PPC-X ternary composite films maintains superior comprehensive barrier efficacy.
| Entry | Carbon dioxidea | Oxygena | Water vapora |
|---|---|---|---|
CO2 P/cm3 µm [m2 day]−1 |
OP/cm3 µm [m2 day]−1 | WVP/mg µm (m2 day)−1 | |
a The permeability coefficient of carbon dioxide (CO2 P), oxygen (OP) and water vapor (WVP) were detected under the identical condition, respectively.
b The units are converted from other units in the references.
c ND denotes ‘not determined’.
|
|||
| 30 wt%PVA/30 wt%PPC-PU/PPC-X | 5.68 × 103 | 1.02 × 103 | 5.00 × 103 |
| 75 wt%PPC-P/25 wt%PBAT/2%MDI@Gly29 | NDc | 1.79 × 103 | 4.75 × 104 |
| 30%PPC-P/70%PBAT/1.0 wt%ADR50 | ND | 1.31 × 104 | 1.63 × 107 |
PBAT/30 wt%PLLA43 b |
2.32 × 106 | 5.13 × 104 | ND |
| PBSb | ND | 5.28 × 103,7,44 | 4.39 × 104,24,46 |
| PPC47 | ND | 2.25 × 103 | 1.25 × 106 |
PLA24,48 b |
ND | 3.35 × 103 | 8.57 × 104 |
PET49 b |
ND | 1.54 × 103 | 9.80 × 104 |
PBAT50 b |
ND | 4.97 × 104 | 2.73 × 107 |
P) of 5.68 × 103 cm3 µm (m2 day)−1, close to that of neat PPC-X, and an O2 permeability (OP) of 1.02 × 103 cm3 µm (m2 day)−1, almost equivalent to that of pure PPC-X. However, the hydrophilic characteristic of PVA led to an increase in water vapor permeability, reaching 5.00 × 103 cm3 µm (m2 day)−1. Although the water vapor permeability (WVP) is significantly higher than that of pure PPC-X, the findings of this study still demonstrate certain advantages and reference value when compared to commercially available packaging films and reports in the literature. Overall, the ternary composite films exhibit promising gas barrier properties, significantly enhanced mechanical performance compared to neat PPC-X, and viable processability, making them attractive sustainable alternatives to conventional non-biodegradable packaging materials such as LDPE, PVC, PET, and PP. These materials demonstrate considerable potential for reducing petroleum dependence, promoting CO2 valorization, and supporting the transition toward more sustainable packaging technologies.
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