1. Introduction
Packaging is one of the main strategies for preserving food and maintaining its quality and safety. The objective of food packaging is to satisfy both industrial requirements, i.e. transport and preservation, and customer satisfaction, that is, safety and marketing and information. The most commonly used materials in food packaging are metals, glass, and paper. However, plastics, since their massive use from the 1950s onwards, have been replacing these other materials thanks to their extraordinary characteristics, such as durability, low cost, and ease of production as well as their excellent physical and barrier properties [
1]. There is a wide variety of polymers in use today including polyethylene (PE), polyethylene terephthalate (PET), polypropylene (PP), polystyrene (PS) and polyvinyl chloride (PVC), which can be used in a large range of applications including food packaging, both in flexible and rigid designs, in the form of trays, bottles or films [
2]. However, these plastics are petroleum-based and non-biodegradable, and their huge use leads to a depletion of natural resources, as well as to an accumulation of waste that causes serious environmental damage [
3].
Bioplastics have been claimed to be suitable substitutes for these synthetic plastics. They are of fully or partially renewable origin, and can be obtained directly from biomass products, including animals and plants, from conventional synthesis such as poly(lactic acid) (PLA) and from natural/genetically modified organisms including polyhydroxyalkanoates (PHA) [
4]. They have attracted attention because of their similarity to conventional plastics, their biocompatibility, biodegradability, and non-toxicity, among other characteristics [
5]. In this context, PHAs have gained a prominent position due to their biodegradability in different scenarios, i.e. compost, soil or aquatic media [
6]. Moreover, their physical properties can be modified by changing their monomeric components, which broadens their field of application. Poly(3-hydroxybutyrate) (PHB), for instance, is one of the most studied and widely used PHAs, because it has some properties that are very similar to conventional plastics such as PP and PE [
7]. However, it also has some drawbacks including brittleness, rigidity and high crystallinity, which make its industrial processing difficult. Thus, the addition of monomers such as 3-hydroxyvalerate (3HV) or 3-hydroxyhexanoate (HHx) leads to a reduction in crystallinity and an increase in flexibility [
8]. Nevertheless, although the use of copolymers can improve some properties, PHAs still have a narrow processing window and are susceptible to thermal degradation during manufacturing processes such as extrusion. For this reason, blending PHAs with other polymers has been used as an alternative to improve some of their mechanical and thermal properties. Thus, when PHAs have been blended with other bio-based biodegradable polymers such as PLA or chitosan, the materials showed an improvement in ductility, toughness and thermal stability as reported by previous authors [
9,
10]. However, this does not solve the problem of high production costs. Therefore, PHAs have also been blended with biodegradable polymers of petroleum origin, which maintain the biodegradability of the mixture but reduces the costs. Between them, poly(butylene adipate-co-terephthalate) (PBAT) stands out for its degradability in a few weeks by natural enzymes, as well as for its excellent mechanical properties, improving the processability of the blends [
11]. For instance, an increase of up to 500 % in strain at break and about two orders of magnitude in toughness was reported for a PHBV/PBAT blend compared to pure PHBV [
12].
In addition to polymer blending, the use of nanoparticles (NPs) has been studied as an alternative or additional method to improve certain characteristics such as transparency, mechanical and barrier properties [
13]. Cellulose nanocrystals (CNC), obtained by acid hydrolysis of cellulosic sources, are one of the most widely used NPs due to their unique properties such as high transparency, reinforcing capacity, and high oxygen barrier [
14]. Moreover, they are biodegradable and renewable materials. They have a low aspect ratio with lengths ranging from 50–500 nm and widths between 5–70 nm and their potential properties are associated with the percolation threshold, where the formation of a specific network with the polymeric matrices occurs [
15]. All this makes CNC perfect candidates for their use in combination with biopolymers such as PHAs. Thus, when PHB was blended with the CNC, the nanocomposite showed a 50 % and 35 % increase in Young´s modulus and tensile strength, respectively [
16]. In addition, the nanocomposite exhibited a reduction in water vapor permeability (WVP) because the CNC resulted in a larger tortuous pathway for water vapor. Similarly, in another study, the addition of CNC to a PHB matrix resulted in a 52.9 % and 46.6 % decrease in WVP and oxygen permeability (OP), respectively [
17]. However, one of the main drawbacks of these nanocelluloses is that their high gas barrier in the dry state is lost at high relative humidity (RH). Many attempts have been made to make the surface of CNC hydrophobic, using physical and chemical modification methods [
18]. Nevertheless, these modifications sometimes change not only the surface properties, but also the original morphology and integrity of the crystal [
19]. For this reason, the strategy of using multilayer systems in order to protect the layer of CNC between hydrophobic polymers could solve this challenge. In these structures, the outer layers are made of polymers that have proven mechanical and moisture resistance while the interlayers provide the gas barrier and other properties such as antimicrobial or antioxidant effects [
20]. In the field of food packaging, these multilayer systems consist of three to seven layers that meet all requirements and functionalities but in a lighter and more compact form [
21]. Different techniques have been developed to form these multilayer systems such as layer by layer, lamination, co-extrusion, coating, among others [
22]. In recent years, electrospinning has emerged as an impressive technique for the development of thin biopolymers layers.
Electrospinning technology focuses on the development of polymeric fibers through the application of electrical and hydrodynamic forces to polymeric solutions. The high voltage causes the appearance of charges on the surface of the solution, which after a certain threshold results in the so-called Taylor cone, which is emitted to the collector in the form of fibres (electrospinning) or particles (electrospraying) [
23]. The characteristics of the resulting polymeric material can be modified by adjusting both the parameters of the equipment and the properties of the polymeric solution. Environmental conditions could also affect the final result [
24]. In addition to the production of polymeric nanostructures, electrospinning has been used for the encapsulation of active substances, due to its high specific surface area, its high encapsulation efficiency and the preservation of oxidation- and heat- sensitive ingredients by processing at room temperature [
25]. This provides the material with antimicrobial and/or antioxidant properties for a longer period of time [
26]. Mechanical and barrier properties can also be improved by the addition of some nanoparticles to the fibers, such as CNC [
27]. Moreover, electrospun fibers can act not only as a film, after a thermal post-treatment, but also as a coating layer that can be used as interlayers in multilayer systems [
28]. As interlayers, in addition to providing barrier and antimicrobial properties, they can act as adhesive layers, the so-called hot-tack (HT), eliminating the use of synthetic glues [
29]. Previous studies, developed barrier [
30] and barrier and antimicrobial [
29] multilayers based on different blown film substrates based on commercial PHA, containing a CNC layer and an electrospun hot-tack adhesive layer made of PHBV derived from residues. The latter studies focused, among other PHA-based materials, on blends of commercial PHA with PBAT, in which the content of PHA in the blend was of ca. 50 wt.%. This relatively high content of PHA in the blends made the films more difficult to stabilize during film blowing of thin films. Moreover, the latter two studies focused their characterization on morphology, barrier and antimicrobial properties.
In this context, the objective of this study was to develop a similar compostable multilayer system based on fully compostable materials and characterize additional properties, but in which the PHA content of the substrate was reduced to 30% to increase blowing processability. For this purpose, two outer layers made of a PHB/PBAT blown film (30/70) were used as a mechanical support and water vapor barrier. Moreover, one of these layers was coated with a layer of CNC to provide the system with a high oxygen barrier. Finally, the system was laminated using a hot-tack made from electrospun fibers of a PHA derived from fermented cheese whey biowaste. The final multilayer structure was characterized in terms of surface roughness, surface tension, migration, mechanical, adhesion and barrier properties, as well as disintegration performance during composting in order to assess the necessary requirements for its use in food packaging.
Figure 1.
Lamination process of the PBAT Blend with a layer of cellulose nanocrystals (CNC) and a layer of electrospun poly(3-hydroxybutyrate-co-3-hydroxyvalerate) (PHBV) fibers.
Figure 1.
Lamination process of the PBAT Blend with a layer of cellulose nanocrystals (CNC) and a layer of electrospun poly(3-hydroxybutyrate-co-3-hydroxyvalerate) (PHBV) fibers.
Figure 2.
Scanning map (a), intensity (b) and colour (c) mode images for the selected area, and 3D surface (d) for the PBAT Blend film taken by confocal laser scanning microscopy (CLSM).
Figure 2.
Scanning map (a), intensity (b) and colour (c) mode images for the selected area, and 3D surface (d) for the PBAT Blend film taken by confocal laser scanning microscopy (CLSM).
Figure 3.
Atomic Force Microscope (AFM) 3D topographic images for 10 µm x 10 µm scanning areas of PBAT Blend film. Profile parameters: arithmetic mean value of the single roughness depths of consecutive sampling lengths (Rz), mean profile roughness (Ra), root mean square height (Rq), and maximum height (Rmax).
Figure 3.
Atomic Force Microscope (AFM) 3D topographic images for 10 µm x 10 µm scanning areas of PBAT Blend film. Profile parameters: arithmetic mean value of the single roughness depths of consecutive sampling lengths (Rz), mean profile roughness (Ra), root mean square height (Rq), and maximum height (Rmax).
Figure 4.
Visual progress of disintegration over time of PBAT Blend film monolayer.
Figure 4.
Visual progress of disintegration over time of PBAT Blend film monolayer.
Figure 5.
Figure 5. Visual progress of disintegration over time of the multilayer.
Figure 5.
Figure 5. Visual progress of disintegration over time of the multilayer.
Table 1.
Surface roughness parameters for the substrate PBAT Blend film.
Table 1.
Surface roughness parameters for the substrate PBAT Blend film.
Sample |
L-filter (µm) |
Sq (µm) |
Sa (µm) |
Sz (µm) |
Ssk |
Sku |
Sdr (%) |
Film |
10 |
0.14 ± 0.01 |
0.079 ± 0.002 |
12.4 ± 2.3 |
-4.9 ± 3.6 |
193.9 ± 96.5 |
4.1 ± 0.6 |
Table 2.
Solvent contact angle and surface tension measurements for the PBAT Blend film with and without corona treatment.
Table 2.
Solvent contact angle and surface tension measurements for the PBAT Blend film with and without corona treatment.
|
|
Samples |
|
|
Film without surface treatment |
Film with surface treatment |
Contact angle |
Θ (o) Water |
73.9 ± 0.7a
|
53.2 ± 1.0b
|
Θ (o) Ethylene Glycol |
53.2 ± 0.8a
|
24.5 ± 1.1b
|
Θ (o) Diiodomethane |
31.6 ± 1.6a
|
46.0 ± 1.2b
|
Surface tension |
Surface Energy (mN/m) |
52.8 ± 0.2a
|
55.5 ± 0.3b
|
Dispersive (mN/m) |
31.7 ± 0.6a
|
27.8 ± 0.5b
|
Polar (mN/m) |
18.2 ± 0.4a
|
12.0 ± 0.3b
|
H-H (mN/m) |
3.0 ± 0.1a
|
15.6 ± 0.3b
|
Table 3.
Overall mean migration of the multilayer film.
Table 3.
Overall mean migration of the multilayer film.
Sample |
Test (40 °C, 10 days) |
Result (mg/dm2) |
Multilayer |
Migration in ethanol 10 % (A) |
1.7 ± 0.6 |
Migration in acetic acid 3 % (B) |
1.7 ± 0.6 |
Migration in olive oil (D2) |
2.5 ± 0.7 |
Table 4.
Methyl methacrylate (MMA) expressed as methacrylic acid (MA) migrated from the monolayer and multilayer films into different food simulants after contact condition of 10 days at 40 °C.
Table 4.
Methyl methacrylate (MMA) expressed as methacrylic acid (MA) migrated from the monolayer and multilayer films into different food simulants after contact condition of 10 days at 40 °C.
Sample |
Food simulants |
10 % (v/v) Ethanol/Water |
3 % (v/v) Acetic acid/Water |
95 % (v/v) Ethanol / Water * |
[mg/Kg] |
[mg/g film] |
[mg/Kg] |
[mg/g film] |
[mg/Kg] |
[mg/g film] |
PBAT Film |
10.70 ± 2.17 |
3.74 ± 1.12 |
7.49 ± 6.34 |
3.24 ± 1.53 |
0.63 ± 1.00 |
0.49 ± 0.25 |
Multilayer Film |
ND |
ND |
ND |
ND |
ND |
ND |
Table 5.
Mechanical properties in terms of elastic modulus (E), tensile strength at yield (σy), elongation at break (εb) of PBAT Blend monolayer and multilayer with cellulose nanocrystals (CNC) in machine direction (MD) and transverse direction (TD).
Table 5.
Mechanical properties in terms of elastic modulus (E), tensile strength at yield (σy), elongation at break (εb) of PBAT Blend monolayer and multilayer with cellulose nanocrystals (CNC) in machine direction (MD) and transverse direction (TD).
Sample |
MD |
TD |
Thickness (mm) |
E (MPa) |
σy (MPa) |
εb (%) |
E (MPa) |
σy (MPa) |
εb (%) |
Monolayer |
0.05 |
1270 ± 64a
|
20.3 ± 1.3a
|
330 ± 22a
|
1030 ± 87a
|
17.8 ± 0.3a
|
243 ± 19a
|
Multilayer |
0.105 |
950 ± 64b
|
20.6 ± 1.7a
|
27 ± 20b
|
1030 ± 64a
|
14.3 ± 0.5b
|
7.6 ± 2.3b
|
Table 6.
Peeling properties of the multilayer with cellulose nanocrystals (CNC) in machine direction (MD) and transverse direction (TD).
Table 6.
Peeling properties of the multilayer with cellulose nanocrystals (CNC) in machine direction (MD) and transverse direction (TD).
Machine direction |
Peeling load (N) |
T-peel strength (N/mm) |
MD |
0.083 ± 0.024a
|
0.006 ± 0.002a
|
TD |
0.081 ± 0.009a
|
0.005 ± 0.001a
|
Table 7.
Thickness and permeance values in terms of water vapor permeance (WVP) and oxygen permeance (OP) of polyhydroxybutyrate (PHB) Blend film monolayer and multilayer with and without cellulose nanocrystals (CNC).
Table 7.
Thickness and permeance values in terms of water vapor permeance (WVP) and oxygen permeance (OP) of polyhydroxybutyrate (PHB) Blend film monolayer and multilayer with and without cellulose nanocrystals (CNC).
|
|
Permeance |
Sample |
Thickness (mm) |
WVP x 1012 (kg·m-2·Pa-1·s-1) |
OP x 1015 (m3·m-2·Pa-1·s-1) |
Monolayer PBAT Blend |
0.045 |
3.6 ± 0.3a
|
9.3 ± 0.1a
|
Multilayer PBAT Blend with hot-tack |
0.107 |
2.0 ± 0.6b
|
5.9 ± 0.4b
|
Multilayer PBAT Blend with hot-tack and CNC |
0.105 |
2.4 ± 0.1b
|
0.5 ± 0.3c
|
Table 8.
Percentage disintegration of the multilayer from start to 60 days.
Table 8.
Percentage disintegration of the multilayer from start to 60 days.
Time (days) |
Disintegration (%) |
0 |
0.0 ± 0.0 |
10 |
-1.8 ± 0.2 |
15 |
2.8 ± 3.7 |
21 |
18.3 ± 7.5 |
23 |
24.6 ± 7.5 |
25 |
30.5 ± 0.7 |
28 |
47.9 ± 7.4 |
30 |
49.8 ± 5.7 |
32 |
53.4 ± 14.1 |
35 |
56.8 ± 10.6 |
37 |
58.7 ± 11.2 |
46 |
84.5 ± 5.2 |
50 |
82.7 ± 6.8 |
60 |
99.9 ± 0.2 |