1. Introduction
Over the last years, the field of classical petro–based polymers was enriched by the so called biopolymers and bioplastics, with the purpose of exploiting and marketing new kinds of materials more sustainable and friendly for the environment, simpler to be recycled or re–used, in the context of the circular economy, whose aim is the valorization of waste products as new raw sources and the consequent reduction of pollution [
1,
2]. Biopolymers are interesting for their biodegradability and ease of recyclability, which nowadays can be pivotal in packaging applications. Moreover, they are interesting for nontoxicity and biocompatibility, which make them suitable to be employed in the personal care and biomedical fields [
3,
4]. A particular class of biopolymers is represented by biocomposites, consisting of natural fibers reinforced biopolymeric matrix that represent an alternative to conventional materials that may be non–renewable, recalcitrant, or manufactured by polluting processes [
3,
5,
6].
When matrix and fibers are both biodegradable, the corresponding final waste results to be fully green, following an entirely sustainable pathway of life cycle and reducing carbon footprint. In fact, carbon dioxide, which is released at the end of life of the material, during composting, is absorbed again by plants to perform the photosynthesis process [
7,
8]. Most natural additives improve the biodegradability of bio–based polymers such as poly(lactic acid) (PLA). Under controlled composting conditions, the biodegradation rate is increased by hydrophilic fillers, for example starch, bran, high amounts of chitosan or kenaf fibers [
9,
10,
11].
One of the most available agricultural waste is represented by bran, obtained by the cereal agricultural stream. In particular, wheat bran is currently the most abundant bran waste. In fact, bran content of wheat is approximately 15% of the whole grain. Assuming that all wheat for human food consumption is milled, the wheat bran by–product stream would account for about 150 million tons per year [
12]. Hence its valorization in composites can be particularly interesting. Nevertheless, bran is a very complex filler on a compositional point of view. The chemical composition of wheat bran predominantly includes non–starch polysaccharides (approximately 38%), starch (approximately 19%), protein (approximately 18%), and lignin (approximately 6%), with the non–starch polysaccharides being approximately 70% arabinoxylans, approximately 19% cellulose and approximately 6% β–(1,3)/β–(1,4)–glucan [
13,
14,
15,
16]. Despite of wheat bran was found as a promising reinforcing filler in natural rubber [
17], in PLA biocomposites, rice bran was reported to induce polymer chain scission [
18] because of the increased water uptake of composites. The interaction between matrix and bran can be improved by surface modification of the bran, for instance using biobased waxes [
19].
In the case of biocomposites, the modification of the polymeric matrix is necessary to improve the interactions with fillers whose role is playing a reinforcing action. An example of compatibilizer is represented by polymeric coupling agents which improve the adhesion of inorganic fillers to the polymer matrix by physical interactions or chemical bonds [
20,
21,
22]. Another possibility is the employment of a chain extender, which allows to obtain by reactive extrusion an extended polymeric network rich of crosslinking points where fillers and fibers, chemically linked to the matrix, could better hang to it. This pathway results very efficient for PLA–based blend [
21,
23,
24].
However, biobased and biodegradable polymers require time for the degradation process in industrial composting plants under specific conditions, and their production is also linked to territorial availability [
8,
9,
25]. The mechanical recycling of bioplastics would be thus important in the end of life phase. In fact, the recyclable items could be turned into raw materials that can then be used to make new products without needing to synthesize completely new resources. These products, obtained from secondary raw materials, in their end of life could then be treated by composting or anaerobic digestion, thus increasing the lifetime of the material before transforming it in basic chemicals [
26]. For PLA–based bioplastics, incineration, composting, and anaerobic digestion processes seem to be clearly underperforming if compared with mechanical recycling methods, from an environmental point of view [
10,
27].
In studies regarding recyclability by mechanical recycling, widely applied in the packaging field, recovered products are collected, washed, and reprocessed, undergoing multiple extrusions, to assess the durability of the material by accelerated thermal aging: the major problem derived from this kind of recycling is the poor hydrolytic and thermal stability of PLA, subjected thus to chain scission, associated to decrease in terms of average molecular weight and mechanical properties [
28]. Reprocessing through multiple successive injection or compression cycles in the presence of humidity, even in low concentration, causes chain scission, crystallization, and onset of cracks in the polymer. Thus, the embrittlement makes it not suitable for being used again for its initial scope [
29]. The use of chain extenders enables the modulation melt viscosity and thermal stability, avoiding earlier degradation. Chain extension is a type of reaction to increase molecular weight during polymer processing of condensation polymers, promoting in the case of use of multifunctional reagents also chain branching, by means of a sort of post polymerization during melt compounding [
21,
30]. The substances which are employed are called chain extenders, having two (case of amines, anhydrides, epoxies and carboxylic acids, which provide linear polymers) or more functionalities [
31,
32]. Chain extension usually works by reacting end–groups with bi– or multifunctional reactive components. In the latter case, linear structures change their topology to long chain branched structures [
21].
The higher the percentage of chain extender, the higher the value of molecular weight and broader will be the processing window of the bioplastic, which it is known to be very narrow. In fact, especially during processing at very high temperatures, biopolymers tend to degrade, and their molecular weight decreases fast, thereby the employment of a chain extender can overcome this problem [
33,
34].
In the case of biopolymer blends, chain extender action can be explained also in terms of in situ reactive compatibilization because they improve the compatibility of components of polymeric blends which, as already described [
35], are often not miscible between each other. Both polymer species have reactive end groups, so that, through chain extender action, a graft copolymer between the two polymer chains is formed [
35]. At the same time, the compatibilization effect enhances mechanical properties [
22].
One of the most used fossil–based chain extender agents in polymers reactive blending is known with the trade name of Joncryl ADR (styrene–acrylate–glycidyl methacrylate copolymer, thus with multifunctional epoxy functionality), produced by BASF Company. In the case of biodegradable polyesters blends, its presence maximizes melt strength of polymer, acting also as a potential compatibilizer, increasing the adhesion between the filler and the predominant phase [
36,
37]. It can be used to compatibilize PLA/poly(butylene succinate–co–adipate) (PBSA) and PLA/poly(butylene adipate–co–terephthalate) (PBAT) blends, during various extrusion processes, like injection molding. Joncryl reacts with hydroxyl and/or carboxyl terminal groups of PLA and PBSA, working as a bridging element between the two polymers, improving interface properties [
26,
37].
In particular, in PLA/PBSA blends, Joncryl revealed to be very useful to control the fluidity and the processability of the melt. In fact, with the increase of PBSA content, the melt fluidity of blends increased, but the addition of the chain extender helped to re–establish the original situation, because of the increase in molecular weight consequent to the branching reactions [
38]. Considering that Joncryl is not biobased or biodegradable, it might be important to design, define, and exploit as largely as possible chain extenders of biobased origin to grant a full circularity of the material [
33,
39,
40], also avoiding the potential formation of microplastics after composting [
41]. In fact, during composting tests on PLA blends containing fossil and not compostable polycarbonate (PC) [
42] it was noticed that the final percentage of degradation was similar to the percentage of PLA in the blend. This means that PC remains persistently in the compost. In general, non–degradable additives represent a persistent fraction in compost [
43].
Possible biobased alternatives could be epoxidized cardanol–based prepolymers, modified vegetable oils (like hydroxylated soybean oil), oil–based diisocyanates, green diols and acids (like furan oligomer (FO)), and by isosorbide, an ester of organic alcohols and nitric acid, often used in medical field as excipient in the treatment of cardiovascular diseases. For example, cardanol is an eco–friendly agro by–product of the cashew industry and can be used as a plasticizer for PVC and PLA or as co–reagent of epichlorohydrin to obtain biobased epoxy networks through curing reaction [
34,
44]. Thus, epoxidized vegetable oils constitute a good alternative because of their wide availability. However, their effectiveness is limited, because they consist of molecules having a few epoxide groups for each molecule, less efficient than commercial fossil alternatives in increasing the molecular weight of polyesters. In fact, they are mainly added in PLA as plasticizers [
39].
In researches regarding innovative biobased thermosets, biobased diisocyanates and acids, such as tannic acid [
45], were used to induce the crosslinking of the epoxidized vegetable oil (EVO) [
46]. Alternatively, due to their hydrophobic nature, EVOs might be grafted on fibers surface (usually hydrophilic) to increase the interfacial adhesion with the polymeric matrix [
47].
The combination of epoxidized oils and renewable acids was never considered in biopolyester blends and composites, with the exception of Liu et al. [
48]. This paper reported the use of polyphenolic tannic acid crosslinked epoxidized soybean oil oligomers for strengthening and toughening bamboo fibers reinforced PLA biocomposites.
The objective of the present work is selecting an alternative chain–extension reaction occurring in the melt that can replace the use of fossil–based epoxy oligomers with natural and biobased counterparts, to formulate a fully sustainable polymeric material.
The selected reaction, never studied before for biopolyester chain extension, is the one between epoxidized soybean oil (ESO) and biobased dicarboxylic acids (DCA), in particular malic acid (MA) and succinic acid (SA).
This reaction will be studied in two different contests. The first system consists of blends of biopolyesters and, as reference, a PLA/PBSA 60/40 blend was selected since it showed properties similar to polyolefins and thus promising to replace them in many applications [
38]; the second system consists of biocomposites of PLA–based blends, containing short fibers coming from agricultural waste. In this case, wheat bran was considered a representative example of short fibrous and complex polysaccharidic–based waste.
The reaction will be studied to be applied as a reactive extrusion process to provide an efficient polymeric network and to control the melt fluidity, the compatibility and stability of final blends and composites. The effect onto thermomechanical properties will be also investigated comparing chain extended biocomposites with those obtained by using Joncryl.
2. Materials and Methods
2.1. Materials
In this work the following polymeric granules and additives were used:
Poly(lactic acid), trade name Luminy LX175, produced by Total Corbion. It is a highly viscous, amorphous, and transparent PLA that appears as white pellets and contains about 4% of D–lactic acid and a molecular weight of 163,000. This PLA, according to the producer’s data sheet has a density of 1.24 g/cm3 and a melt flow index (MFI) of 6 g/10 min (210 °C, 2.16 kg).
Poly(butylene succinate–co–adipate) (PBSA), trade name BioPBS FD92PM, purchased from Mitsubishi Chemical Corporation (Tokyo, Japan). It is a copolymer of succinic acid, adipic acid and 1,4–butandiol with a melt flow index (MFI) of 4 g/10 min (190 °C, 2.16 kg) and a density of 1.24 g/cm3.
Wheat bran available from WEAREBIO is a light brown powder with a content of protein (crude) of 13.84% (p/p), dietary fiber soluble of 0.93% (p/p), and dietary fiber insoluble of 19.70% (p/p) (CAS number: 130498–22–5; density: 0.51 g/cm3).
Joncryl ADR 4468, indicated as JONCRYL, produced by BASF, is an epoxy oligomer. It is an oligomeric chain extender of fossil origin, carrying 20 average epoxy groups per macromolecule which react with chain ends of polycondensates (epoxy equivalent weight: 310 g/mol). Its molecular weight is 7250 g/mol, the density is 1.08 g/cm3, and it appears as solid flakes.
Epoxidized soybean oil ESO, commercialized by Alcoplast (AP), is a light–yellow viscous liquid soluble in alcohols with an epoxide number of 4, a density 0.994 g/cm3 and a molar mass 950 g/mol.
L–malic acid (MA), from renewable sources, provided by OENO S.r.l. group, was used. It is a dicarboxylic acid that appears as a solid white powder, odorless, with a molecular weight of 134.1 g/mol, a melting point of 131 °C, a decomposition point >225 °C and a solubility in ethanol of 45.5 g/100 g at 20 °C.
Succinic acid (SA), purchased by Carlo Erba Reagents S.A.S. (Dast Group), is an organic compound belonging to the family of (di)carboxylic acids. It appears as a white and odorless powder having a density of 1.56 g/cm3, a melting point of 185 °C, a decomposition point of 235 °C and a molecular weight of 118.1 g/mol.
In this research work, the reference blend was a binary blend 60 wt %. PLA Luminy LX175 and 40 wt %. PBSA BioPBS–FD92PM used in previous works [
38].
2.2. Methods
The blends were prepared by adding the modified bran to the 60/40 PLA/PBSA by using a micro–compounder Haake Minilab II (Thermo Scientific Haake GmbH, Karlsruhe, Germany), that provided also torque data. After the introduction of the material, the melt, pushed by the screws, runs through a closed circuit (with the valve closed) for 1 min, during which the torque is measured as a function of time. In the tests, the rotating speed was 110 rpm and the processing temperature was 190 °C. The final torque value represents the most significant value for the sample as the melt stabilizes. With the opening of the valve, the material was recovered and used in a Haake MiniJet Mini–Injection Molding System to prepare the specimens needed for the tensile tests. The cylinder temperature was 190 °C and the mold temperature was 45 °C. In the test, a pressure ranged from 350 bar to 600 bar (according to the kind of material) was used for 15 s and a post pressure of 200 bar for 5 s was needed to obtain the necessary filling of the mold.
The blends compositions are listed in
Table 1. On the basis of a previous work [
38] a PLA–PBSA matrix containing 60 wt % of PLA and 40 wt % of PBSA was chosen due to the good starting mechanical properties. The samples are named in a synthetic way using the letter
b to indicate the blend PLA/PBSA 60/40, whereas the letter
c indicates the composites with bran at 20% by weight. Then the additive ESO, MA, SA, and Joncryl are indicated in samples names. The last number the total percentage by weight of the modifier (0.5, 1, 2, or 5). > (or <) indicates an excess (or defect) of epoxydic groups of ESO with respect to carboxylic groups of MA.
Wheat bran fibers were added to decrease polymer final cost and ESO alone or in combination with malic acid or succinic acid in different ratio were used to prepare modified bran maintaining the same starting weight percentage of PLA/PBSA blend (80 wt %) in final extrusion. Bran weight percentage varied thus every time according to the quantity of modifier.
Plasticizer and/or acid–based modifier systems were obtained firstly by dissolution in beaker with 150 mL of ethanol as solvent, progressively adding bran powder. The sample were then left upon mechanical agitation by magnetic stirring for an entire night, until total evaporation of the solvent. Then it was placed for 24 h in oven (60 °C), to eliminate any residue of ethanol or humidity in the final samples. The solid product obtained was grinded to obtain a fine powder and then put again in oven (60 °C) for 24 h, to get ready for Minilab extrusion.
The investigation of flow behavior was carried out with a CEAST Melt Flow Tester M20 (Instron, Canton, MA, USA) equipped with an encoder. The ISO1133D custom TTT was followed. The sample was preheated without weight for 40 s at 190 °C, then a weight of 2.160 kg is released on the piston and after 5 s a blade cuts the strand starting the real test. Through the encoder, every 3 s, an MVR measurement is recorded and the MFR was determined weighing the material.
Tensile tests, performed on Haake Type III specimens (25 mm × 5 mm × 1.5 mm) obtained with the Haake MiniJet, were carried out by an MTS Criterion model 43universal tensile testing machine (MTS System Corporation, Eden Praire, MN, USA). The machine was equipped with a 10 kN load cell and interfaced with a MTS elite software. The initial grip separation was 25 mm, and the deformation rate was set at 10 mm/min.
Thermal properties were investigated by differential scanning calorimetric analysis (DSC) using a Q200 TA–DSC (TA Instruments, New Castle, UK). The samples were quickly cooled very fast from room temperature to −70 °C (equilibrate to −70 °C) and kept at this temperature for 1 min. Then the samples were heated at 10 °C/min to 190 °C and held for 5 min to remove the thermal history. Subsequently, the samples were cooled again at 10 °C/min to −50 °C and held at this temperature for 1 min. A second cooling scan from −70 °C to 190 °C, at 10 °C/min, was carried out to record the crystallization and melting behaviors. Melting temperature (
Tm) and the cold crystallization temperature (
Tcc) of the blends were recorded at the maximum of the melting peak and at the minimum of the cold crystallization peak respectively. As a consequence, the enthalpies of melting and of the cold crystallization were determined from the corresponding peak areas in the thermograms. DSC analysis was performed considering only the second heating scan to disregard the thermal history of the material. The percentage of crystallinity of PLA
Xcc,PLA can be obtained through the relation
where Δ
Hm,PLA and Δ
Hcc,PLA are the melting enthalpy and the enthalpy of cold crystallization of PLA obtained in J/g,
X is the weight fraction of PLA that crystallizes and
is the melting enthalpy of the 100% crystalline PLA, equal to 93 J/g [
20].
SEM analyses were carried out on samples previously cryo–fractured along the cross–section with liquid nitrogen, to cause fragile fracture, ensuring a smoother surface available for the study. The instrument was FEI Quanta 450 ESEM FEG scanning electron microscope (SEM) (Thermo Fisher Scientific, Waltham, MA, USA), which has a resolution power of 3.5 nm and possibility of magnification until 300,000×. Samples were not conductive and were coated with a thin metallic layer prior to microscopy to avoid charge build up.
Infrared spectra were recorded in the 550–4000 cm−1 range with a Nicolet 380 Thermo Corporation Fourier Transform Infrared (FTIR) Spectrometer (Thermo Fisher Scientific, Waltham, MA, USA) equipped with smart Itx ATR (Attenuated Total Reflection) accessory with a diamond plate, collecting 128 scans at 4 cm−1 resolutions. ONMIC software was used to modify the intensity of spectra and to compare different spectra profiles. To perform the reactivity study the starting DCA and ESO ratio corresponding to the stochiometric ratio between epoxide and carboxylic groups was selected. The reagents were deposited on a Petri plate made in Teflon. Then they were treated at 60 °C in oven (to simulate the treatment drying) or at 190 °C in a compression molding press (to simulate melt processing conditions).
Thermogravimetric analysis (TGA) was performed in nitrogen gas atmosphere by using a TA Q–500 (TA Instruments, Waters LLC, New Castle, DE, USA). The samples, in form of pellets or powder of about 10 mg, were heated at 10 °C/min from 30 °C to 800 °C in order to investigate degradation features.
4. Discussion
As already said, epoxidized vegetable oils, like ESO, can be cured with biobased dicarboxylic acids, to favor the formation of high molecular weight branched networks, completely biobased and biodegradable [
40,
46]. If the presence of ESO alone formulations performed mainly plasticization effects, the curing of this oil with diacids was performed according to the ratio between epoxy and –COOH groups, whose interaction led to the formation of bridges. In the reaction the epoxy ring opened hanging the carboxyl group to form an ester bond, following the pattern of a nucleophilic addition (
Figure 12).
In practice, considering the polar malic acid, it performs physical interactions (for instance by hydrogen bonding) or grafting on bran, and its terminal carboxyl groups on the other side are ready to react with epoxy rings of ESO, which open out. On the other hand, ESO rings react in the same way with terminal carboxyl groups of PLA/PBSA blend. Rings opening leads to the formation of ester bonds and increases the number of ramifications, represented by skeletons of malic acid, ESO, and bran. The overall curing reaction can be thus considered an efficient chain extension, including reactive compatibilization. ESO and MA work as a unique compatibilizer system between fibers and the polymeric blend. This mechanism is confirmed by the higher effectiveness in melt fluidity decrease in bran composites than in blends (
Figure 7 and
Figure 8). The results showed that bran plays an important role in the branching mechanism. This mechanism is acceptable because reminds to an analogue process already defined in the case of PLA/maleic anhydride–grafted–starch blends, compatibilized by ESO. Starch is again a polysaccharide, rich of –OH groups (like bran filler), and maleic anhydride has a structure similar to malic acid one, but with a double bond [
60]. A schematic pattern of the reaction is summarized in
Figure 13.
An analogue reaction pattern was successively hypothesized when succinic acid was exploited as dicarboxylic acid in place of malic acid. The most significant difference is related to degradation effects caused by two acids. In fact, this kind of phenomena, which develop in competition with the desired chain extension reaction, is hindered in succinic acid–based formulations. In fact, being lack of the hydroxyl group, it does not favor early hydrolysis of polyester matrix as much as malic acid did. Hence, succinic acid better embodies requirements which had been described by Zeng and coworkers [
46], improving properties of prepared blends and biocomposites. Looking at the comparison with MA and Joncryl, it can be considered a very promising alternative in chain extenders field, since it is fully biobased and cheap and it is able to ensure ideal values for melt flow parameters, similar to ones showed by pure matrix of PLA/PBSA (b formulation).
Interestingly in ESO +MA system the stoichiometric ratio is the most advantageous for having a good chain extension. On the other hand, in both ESO + MA and ESO + SA systems the best results in terms of melt fluidity reduction are achieved by adding 0.72–0.73% of reagents in stoichiometric ratio. This represents a limitation in this bran composites and makes the melt fluidity not fully modulable. The reason why this minimum exists is difficult to explain, but it is reasonably linked at hydrolysis kinesis, heavily influenced by the DCA content in the system. On the other hand, bran represents a filler that tends to easily promote biopolyesters chain scission because of its complex composition, including proteins and starch. Thus, the further addition of acids, yet indicated as reagents inducing hydrolysis in PLA [
61,
62] is particularly disadvantageous.
As observed from TGA thermograms, it is possible to conclude that the degradation of biocomposites depends on the thermal stability of the secondary additives (dicarboxylic acids), which showed onset temperatures even lower than extrusion temperature and catalyzed polyester matrices decomposition already during processing. Since values of Ton were higher than 240 °C for all blends, it would be logical to set at about 230–240 °C the limit temperature of practical use. This is in agreement with the literature, from which it is known that processes and applications of natural fibers composites should be restricted at a maximum of 250 °C [
63]. Moreover, it is clear to observe that the incorporation of hydrophilic bran fibers (even modified) led to a decrease (even if slight) in the thermal stability of the original matrix, but for this reason it could be advantageous for improving thermal decomposition properties of composites as well [
64].
From DSC studies, not significant changes of pure PLA/PBSA matrix thermal characteristics were observed when bran was added and chain extender systems were employed. The crystallization was, on the whole, slightly promoted using ESO + SA but the chain extended final materials resulted mainly amorphous.
5. Conclusions
Biobased chain extenders were formulated by combining epoxidized soybean oil (ESO) and dicarboxylic acids (DCA), in particular malic acid (MA) and succinic acid (SA).
Thanks to thermogravimetric and spectroscopic studies it was possible to verify the reactivity between ESO and the acids at the temperature typical of polyester composites processing. Then, thanks to miniextruder torque and melt fluidity analysis, it was possible to verify the occurrence of the reaction in the melt during the processing of both PLA/PBSA 60/40 blend and its composite including 20 wt % of wheat bran.
As bran much affects the processability of biopolyester blends, because of induced chain scissions, the biobased chain extenders were validated in a severe system. The obtained results indicated that linking the new chain extension systems on fillers, following the stoichiometric ratio between epoxide and carboxylic groups in ESO and DCA, allowed to achieve better results. At this purpose, a minimum point for melt fluidity at 0.7–0.8% by weight (hence close to 1%) of chain extension system was found for both ESO + MA and ESO + SA in these bran composites. Despite this represents a limit in the tailoring of melt fluidity, by using ESO and SA values allowing biopolyesters processing and an improved melt stability were achieved.
The mechanical properties are not much significantly affected by the different chain extension systems, despite good elongation at break values were reached adding ESO + SA. Regarding thermal properties, the slight nucleating effect of bran is reduced by ESO + MA and slightly improved by ESO + SA, suggesting a parallelism with the occurrence of more extensive disordering by branching using MA, due to its –OH group.
The commercial Joncryl resulted more efficient in terms of melt fluidity reduction, but it is necessary to consider that Joncryl oligomers contain about 20 epoxydic groups for each molecule, whereas the ESO has 4 epoxide groups for each molecule on average. The capacity of Joncryl of chain extending and branching polymers is thus necessarily higher. Despite this difference, thanks to the cross–linking action on ESO played by the SA, the ESO/SA system assumes a behavior similar to the one of Joncryl considering the difference in epoxydic groups number. The average number of reactive groups per chain extender molecule is increased thanks to the reaction between epoxidized oils and dicarboxylic acids.
These biobased chain extenders are promising for the processing of biobased composites and they could be also considered in the future to allow their recycling. In fact, using not bio–based chain extenders can be detrimental for the biodegradability of the material. Thanks to this approach composites could be processed and then, in their final stage of life, they can be fully composted overcoming the issue of possible micro–plastic residues.