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1. Introduction
Biocomposites are sustainable, ecologically acceptable, and recyclable bio-based materials made from renewable resources [1]. The polymeric base of such materials is biopolymers [2], such as thermoplastic starch, polyhydoxyalkanoates (PHA), polylactides (PLA), lignin-based epoxy, soy-based resins, and epoxidised linseed oil [3]. Biocomposites can also be made using wood as raw material, which is, like all other materials of biological origin, characterized by a high degree of diversity and variability of properties, and which is additionally distinguished from the above-mentioned materials due to its complex chemical composition. Considering its chemical composition, wood can be described as a three-dimensional biopolymer composite, comprising an interconnected network of cellulose, hemicellulose, and lignin, with a small share of inorganics and extractives [4, 5]. The share of cellulose in wood, varying between 38% and 51%, dependent on wood species and the method of its isolation [4, 6–9], alongside the possibility of chemical modification of cellulose by acetylation, emphasizes its use as a polymeric base in biocomposite materials. Therefore, the acetyl group bonding to the anhydroglucose units of cellulose directly affects the properties of cellulose acetate (CA) in terms of its biodegradability [10–12] and solubility in various solvents [13]. Exactly those properties are of key importance for the potential use of CA as the polymeric base for biocomposite materials. However, the degradation of cellulose and other chemical constituents of wood, alongside the difficulties related to the isolation of completely pure cellulose, limits the development of CA-based biocomposite materials. Regardless of that, CA is commercially used for the preparation of various membranes for reverse osmosis, gas separation, and micro-, nano-, and ultrafiltration [14–20]. Such applications of CA are almost exclusively based on the chemical modification of cellulose by acetylation and membrane preparation by the polymer spinning method or phase inversion and do not involve the interactions between cellulose matrices and fillers, as in the case of wood-based biocomposites. With the introduction of fillers into the structure of materials, the properties of the latter substantially change, since they no longer depend solely on the properties of the cellulose matrix but also on those of the fillers and their mutual interaction. In addition, the origin of the fillers is very important, as the situation is very different in the case of fillers of inorganic and organic origins. Fillers of inorganic origin, such as talc, kaolin, or zinc-borate, are easier to work with due to the isotropic properties of such materials. The properties of fillers of organic origin are highly dependent on the process of their isolation, which somewhat defines the limits of their usability because of their pronounced anisotropy [21]. Natural fillers in the form of cellulose nanofibrils and microfibrilated cellulose are suitable substitutions for inorganic fillers, whereby the size of the added particles is an essential factor affecting the strength, durability, and stability of lignocellulose-based biocomposite materials [22–24].
Lignocellulosic filler particle size and addition, alongside their chemical composition, have strong influence on various properties of composite materials (e.g., mechanical and thermal properties). Zaini et al. reported on the effect of filler content and size on the mechanical properties of polypropylene/oil palm wood flour composites with the conclusion that the composites filled with larger sized filler showed a higher modulus and tensile strength, especially at higher filler content [25]. Similar results for lignin-based date palm wood powder and rice husk-filled epoxy matrix were obtained by Rout and Satapathy [26] and AlMaadeed et al. [27], who reported high increase in mechanical and thermal properties (stability) of thus prepared composites, thus assigning cellulose as the chemical composition constituent responsible for mechanical property increase and lignin as responsible for the increase in thermal stability. Le Digabel and Avérous [28] obtained similar results for aromatic copolyester matrix filled with wheat straw particles and report that the addition of lignocellulosic fillers did not change the matrix crystallinity but influenced the nucleation process. David et al. [29] examined the influence of cellulosic filler particle addition on properties of biopolyester-based composites and revealed that intrinsic properties of polymeric matrix do not change significantly with the addition of cellulosic filler. Ni’mah et al. [30] examined the effect of the particle size and crystallinity of the cellulose filler on mechanical and thermal properties of poly(L-lactic acid) acid-based biocomposites. They report that the tensile strength decreases with the increase of the filler content, which is most probably due to filler particle agglomeration and that the composite strength and thermal stability rise with the rise in fillers’ crystallinity. Treimanis et al. [31] examined the mechanical properties of hybrid composites with polyethylene and lignin matrix filled with microcrystalline cellulose and emphasized the importance that cellulose crystallinity and filler aspect ratios have on mechanical properties of such composites. Various authors report also on the influence that cellulose polymorphism (crystal structure) has on mechanical and thermal properties of polymer matrices filled with lignocellulosic fillers, where the cellulose II polymorph is described as one that significantly contributes the mentioned properties [32–36].
In order to determine the influence of filler type and chemical composition on the thermal and mechanical properties, as well as the surface morphology of composites, in this study, CA-based biocomposite materials were prepared with different fillers, i.e., microsized particles of extracted wood, holocellulose, and alpha cellulose, and examined. Both the CA and the filler used in the formulation originated from the same wood species.
2. Materials and Methods
2.1. Materials
In this study, the white willow (Salix alba L.) and the black alder (Alnus glutinosa [L.] Gaertn.) wood were used as the basic raw material. Both wood species were sampled during mid-June and July 2013, in accordance with the TAPPI T 257 cm-12 standard [37]. After sampling, the obtained wood samples were transported to the laboratory and allowed to dry naturally to 6-10% moisture content, before being debarked and milled using a Retsch SM 300 cutting mill. The obtained wood flour was screened, and particles sized between 0.5 and 1 mm were used for cellulose isolation and filler preparation.
Ethanol, benzene, nitric acid, acetic acid, sodium hydroxide, toluene, acetic anhydride, monopotassium salt of phthalic acid, and dichloromethane were all purchased from Kemika Ltd., Croatia. Sodium chlorite, perchloric acid, and pyridine were purchased from Sigma-Aldrich, Germany. All the chemicals and reagents were of analytical grade and were used without purification. Deionized water was used in all the experiments; it was prepared according to the ASTM type II specifications, using a TKA MicroMed system.
2.2. Methods
2.2.1. Cellulose Isolation and Filler Preparation
Prior to cellulose isolation, the wood flour of both wood species was extracted in a Soxhlet apparatus, according to the TAPPI T 204 cm-97 standard [38], using a benzene/ethanol mixture (1 : 1%
Table 1
L/D ratios of fillers.
Type of filler | L/D ratio | |
---|---|---|
White willow | Black alder | |
Extracted wood | 5.03 | 5.20 |
Holocellulose | 6.30 | 6.41 |
Alpha cellulose | 3.65 | 3.52 |
2.2.2. Cellulose Acetylation and CA Characterization
Cellulose was acetylated as described in our earlier work [41]. Briefly, 100 g of cellulose (per wood species) was treated for 1 minute with a reaction mixture consisting of 500 ml of acetic acid, 1000 ml of toluene, and 5 ml of perchloric acid as the catalyst. After 1 min, 500 ml of acetic acid was added to the reaction mixture. Acetylation was conducted at ambient temperature, and the process took 45 minutes, after which 1000 ml of deionized water was added to the reaction mixture in order to precipitate the CA. The obtained CA was then vacuum filtered and washed repeatedly with 1000 ml of ethanol and 1000 ml of deionized water until the strong acetic acid scent faded. The thus-prepared CA was dried for 8 h at 40°C and afterwards used for biocomposite preparation. After acetylation and drying, CA was analysed according to ASTM D 817-96 [42] in order to determine the acetyl content (% acetyl) and the degree of substitution (DS). Monopotassium salt of phthalic acid was used for the blanks and pyridine as the appropriate solvent. The CA obtained from white willow had 38.5% acetyl and 2.32 DS, while that from black alder had 42.5% acetyl and 2.73 DS.
2.2.3. Preparation of Biocomposites
Neat CA films and biocomposites were prepared by the solvent cast method using dichloromethane as the appropriate solvent. The CA was dissolved in a glass laboratory beaker, to which a known amount of solvent was added (
2.3. Characterization
2.3.1. Thermogravimetric Analysis
The thermal behaviour of the fillers was evaluated by thermogravimetric analysis (TGA), which was carried out on a PerkinElmer Pyris 1 TGA analyser, at temperatures ranging from 50°C to 700°C, with a heating rate of 10°C/min, under a synthetic airflow of 30 ml/min. The derivation of the TG curves, in order to obtain DTG curves, was done using Pyris Ver. 11 software.
2.3.2. Differential Scanning Calorimetry
The thermal properties of the neat CA films and biocomposites were determined by differential scanning calorimetry (DSC), which was carried out on a PerkinElmer DSC 6000 by heating and cooling the samples (~5 mg) from 30°C to 315°C, using a scanning rate of 10°C/min, under a nitrogen flow of 20 ml/min. The melting (
2.3.3. FT-IR Analysis
Fourier transform infrared (FT-IR) spectra were recorded on a Shimadzu FTIR-8400S spectrometer by the KBr pellet method, in the range of 4000-400 cm-1, with the resolution of 4 cm-1. Subsequent processing of the obtained results was performed using IRSolution Ver.1.30 software.
2.3.4. XRD Analysis
Diffraction patterns of fillers were taken by a Philips diffractometer PW1820 having a proportional counter and a graphite monochromator with CuKα radiation in Bragg-Brentano geometry. Patterns were recorded in the 2Θ range 5-70°, with the step size of 0.02°/step with the recording time of 1 s/step.
The crystallinity index (
2.3.5. Mechanical Properties
Tensile tests were performed in accordance with the ASTM D882-02 [45] standard on a Zwick/Roell Z005 universal testing machine. Thin strips (
2.3.6. Surface Morphology
The images of surface morphology were collected on a TESCAN MIRA/LMU scanning electron microscope (SEM). In order to increase the conductivity of the mounted specimens, they were coated with gold/palladium on a Quorum Technologies sputter coater, model SC7620-CF Mini.
2.3.7. UV-VIS Spectroscopy and Porosity Test
UV-VIS spectroscopy was performed in order to determine the percentage transmittance (%T) of the neat CA films. Thin strips were cut using a surgical blade and mounted on the film holder, and their %T was determined according to the ASTM D 1003-07 standard [46], on a Shimadzu UVmini-1240 spectrophotometer.
The porosity test was performed according to Wang et al. [47] by immersion of thin strips of neat CA films into deionized water (20°C) for 1 h and subsequent film drying in a vacuum oven at reduced pressure for 4 h.
3. Results and Discussion
3.1. Thermal Characterization of Fillers and Biocomposites
Biocomposites were prepared using white willow (Salix alba L.) and black alder (Alnus glutinosa [L.] Gaertn.) wood flour as the starting material for both CA synthesis and filler preparation. Their thermal properties were determined using differential scanning calorimetry (DSC). Supplementary data were obtained from the thermogravimetric analysis (TGA), Fourier transform infrared (FT-IR) spectroscopy, and X-ray diffraction (XRD) of the fillers.
3.1.1. Thermal Properties of Fillers
TGA was conducted on the fillers in a stream of synthetic air in order to obtain data relevant to the functional environment that they would be used in. The TGA results of the fillers are given in Table 2 and in Figure 1, while representative TG-DTG curves of extracted wood flour are presented in Figure 2.
Table 2
Summary of TGA data on wood and different types of fillers used.
Material | |||||
---|---|---|---|---|---|
White willow | |||||
Nonextracted wood | 314.9 | 276.2 | 335.5 | 436.0 | 335.9 |
Extracted wood | 316.9 | 273.8 | 335.5 | 436.0 | 337.9 |
Holocellulose | 304.9 | 263.3 | 331.2 | 408.8 | 330.0 |
Alpha cellulose | 318.8 | 301.3 | 346.7 | 473.8 | 341.8 |
Black alder | |||||
Nonextracted wood | 315.4 | 267.0 | 335.0 | 436.7 | 336.8 |
Extracted wood | 314.1 | 272.9 | 334.6 | 434.6 | 336.4 |
Holocellulose | 310.4 | 273.3 | 331.8 | 394.7 | 334.2 |
Alpha cellulose | 317.7 | 289.5 | 340.4 | 472.6 | 337.9 |
As expected, due to oxidative atmosphere, sample degradation occurred in two stages, as indicated by the formation of two distinctive peaks on the DTG curves of all of the examined fillers. The first step (peak) represents primary sample degradation, and the second one could be related to oxidative degradation of the residues or completion of lignin degradation as its thermal stability is very high, and thus, it degrades over a wide temperature range [48, 49]. The formation of peak shoulders (marked in Figure 2) in the case of unextracted wood flour, extracted wood flour, and holocellulose from both wood species indicates two-step degradation of cellulose and hemicelluloses with partial overlapping with lignin [50]. The peak shoulders of unextracted wood flour and extracted wood flour, in the case of white willow, appear at 296.4°C and 295.7°C, respectively. In the case of black alder, the peak shoulders appear at 295.3°C and 298.3°C, respectively. Such narrow distribution and small differences of the peak values indicate the presence of other components, different in each species, which affect the thermal stability of cellulose and hemicelluloses [50]. As in the case of both wood species, extraction was performed using a benzene/ethanol mixture and part of the organic extractives had been removed, leading to small differences in thermal stability between unextracted wood flour and extracted wood flour (Table 2), which is in correspondence with the results reported in previous studies [51, 52]. The peak shoulder of holocellulose prepared from white willow appears at 297.4°C and of that from black alder at 296.0°C. As holocellulose is composed of cellulose and hemicelluloses, the formation of shoulders at lower temperature could be attributed to the degradation of hemicelluloses, while higher temperature peaks can be attributed to cellulose degradation [50, 53–56].
Although the TGA results are comparable and are within measurement error, data presented in Figure 1, alongside the
Table 3
Crystallinity indices of fillers.
Type of filler | Crystallinity index (%) | |
---|---|---|
White willow | Black alder | |
Extracted wood | 56 | 41 |
Holocellulose | 58 | 50 |
Alpha cellulose | 62 | 67 |
Note: deconvoluted diffraction peaks for holocellulose prepared from black alder and alpha cellulose prepared from white willow are shown in the Supplementary information.
In order to obtain additional information on the chemical composition of the prepared holocellulose, FT-IR analysis has been performed. As can be seen from Figure 3, in the fingerprint region of the FT-IR spectra of holocellulose, peaks related exclusively to carbohydrates are present.
[figure omitted; refer to PDF]The presence of a well-marked peak at 1738 cm-1 related to unconjugated C=O in xylans (hemicelluloses), whose shape and intensity are almost the same in the case of both extracted wood flour and holocellulose from both wood species, suggests that the chemical treatments have not induced the degradation of hemicelluloses. The peak at 1640 cm-1, related to absorbed water, is more pronounced in the FT-IR spectra of holocellulose, which is explained by its preparation method. The absence of the low intensity peak formed at 1596 cm-1 and the intensity drop of the peak at 1508 cm-1 related to the C=C stretching of the aromatic ring (lignin) in the FT-IR spectra of holocellulose indicate complete delignification. This is additionally confirmed by the absence of the peak at 1462 cm-1 and the intensity drop of the peak at 1426 cm-1 related to C-H deformations in lignin [59, 60]. The formation and small intensity changes of the peaks at 1375 cm-1 (C-H deformations in cellulose and hemicellulose), 1324 cm-1 (C-H vibration in cellulose), 1253 cm-1 (C-O stretch in hemicellulose), 1158 cm-1 (C-O-C vibrations in cellulose and hemicellulose), 1112 cm-1 and 1053 cm-1 (C-O stretch in cellulose and hemicellulose), and 895 cm-1 (C-H deformation in cellulose) [59, 61, 62] clearly indicate that high-purity, lignin-free holocellulose was prepared.
Kürschner-Hoffer’s cellulose treatment with sodium hydroxide solution caused cellulose II polymorphic form creation that was confirmed by XRD analysis (Figure 4). Samples S1, S2, S4, and S5 show a typical diffraction pattern for cellulose I, with the diffraction peaks at 2Θ around 14.5°, 16.5°, and 22.5° corresponding to (11 ̅0), (110), and (200) maxima, respectively. This fully corresponds to the characteristic diffraction maxima of cellulose I [63]. XRD patterns of the samples S3 and S6 belong to cellulose II, with the Bragg intensities located at 2Θ around 12.0°, 20.0° and 22.0° corresponding to (11 ̅0), (110), and (020) maxima, respectively [63]. Clear difference between the diffraction patterns of cellulose I and II samples can be seen from figures of deconvoluted diffraction peaks of samples S5 and S3 given in the Supplementary Material (available here).
[figures omitted; refer to PDF]
As cellulose II is a more thermodynamically stable polymorphic form than cellulose I [64], it is easy to conclude why the
3.1.2. Thermal Properties of Biocomposite Materials
The results of DSC analysis (Table 4, Figures 5 and 6) indicate that prolonged chemical treatment during the preparation of the fillers caused the decline of
Table 4
DSC analysis of biocomposite materials.
Type of filler | ||||||
---|---|---|---|---|---|---|
White willow | ||||||
Neat CA | 177.8 | 303.6 | 254.4 | 25.5 | 18.7 | 11.6 |
Extracted wood | 178.0 | 304.6 | 257.8 | 26.9 | 16.0 | 20.5 |
Holocellulose | 177.5 | 304.5 | 252.1 | 18.7 | 13.0 | 10.8 |
Alpha cellulose | 176.6 | 303.9 | 247.6 | 19.7 | 16.0 | 7.0 |
Black alder | ||||||
Neat CA | 173.1 | 305.7 | 263.2 | 25.0 | 18.5 | 11.1 |
Extracted wood | 178.3 | 307.3 | 267.7 | 21.3 | 14.6 | 12.8 |
Holocellulose | 177.3 | 306.7 | 265.2 | 20.5 | 15.1 | 10.3 |
Alpha cellulose | 176.6 | 306.3 | 262.6 | 18.2 | 13.5 | 8.9 |
[figures omitted; refer to PDF]
[figures omitted; refer to PDF]
As can be seen from Table 4, the
If the distributions of
The presence of fillers undoubtedly influenced the evolution of Gibbs energy (G) and melting enthalpy (
3.2. Analysis of Mechanical Properties and Surface Morphology of Biocomposite Materials
3.2.1. Mechanical Properties
The mechanical properties of the biocomposite materials prepared from white willow and black alder are presented in Tables 5 and 6, respectively. The addition of fillers to the CA matrix resulted in a decrease of density in the case of both wood species. However, statistical analysis showed that there are no significant differences in the density of the composites as a function of the type of filler used. Therefore, the density decrease could be related to the presence of highly porous (hollow) fillers, which are not completely filled with polymer matrix.
Table 5
Density and mechanical properties of biocomposites prepared from white willow.
Type of filler | Median | Min | Max | ||
---|---|---|---|---|---|
Density (g/cm3) | |||||
Neat CA | 10 | 1.23 | 1.10 | 1.27 | |
Extracted wood | 10 | 0.83 | 0.78 | 0.93 | |
Holocellulose | 10 | 0.86 | 0.81 | 0.95 | |
Alpha cellulose | 10 | 0.85 | 0.82 | 0.91 | |
Tensile strength (MPa) | |||||
Neat CA | 10 | 66.67 | 49.02 | 75.50 | |
Extracted wood | 10 | 27.30 | 24.00 | 31.14 | |
Holocellulose | 10 | 31.55 | 27.72 | 35.90 | |
Alpha cellulose | 10 | 29.88 | 25.29 | 34.52 | |
Tensile modulus (GPa) | |||||
Neat CA | 10 | 2.23 | 2.19 | 2.51 | |
Extracted wood | 10 | 1.21 | 1.15 | 1.36 | |
Holocellulose | 10 | 1.37 | 1.22 | 1.60 | |
Alpha cellulose | 10 | 1.29 | 1.24 | 1.39 | |
Elongation at break (%) | |||||
Neat CA | 10 | 7.04 | 4.37 | 9.83 | |
Extracted wood | 10 | 5.25 | 4.35 | 7.23 | |
Holocellulose | 10 | 5.20 | 4.31 | 6.01 | |
Alpha cellulose | 10 | 5.11 | 4.18 | 6.07 |
Note: means sharing the same superscript are not significantly different from each other (Tukey’s HSD,
Table 6
Density and mechanical properties of biocomposites prepared from black alder.
Type of filler | Median | Min | Max | ||
---|---|---|---|---|---|
Density (g/cm3) | |||||
Neat CA | 10 | 1.22 | 1.32 | 1.27 | |
Extracted wood | 10 | 0.86 | 0.79 | 0.94 | |
Holocellulose | 10 | 0.87 | 0.83 | 0.99 | |
Alpha cellulose | 10 | 0.91 | 0.77 | 0.97 | |
Tensile strength (MPa) | |||||
Neat CA | 10 | 58.71 | 40.77 | 74.05 | |
Extracted wood | 10 | 29.65 | 27.66 | 33.11 | |
Holocellulose | 10 | 30.33 | 23.49 | 38.98 | |
Alpha cellulose | 10 | 26.35 | 18.78 | 30.04 | |
Tensile modulus (GPa) | |||||
Neat CA | 10 | 2.07 | 1.60 | 3.27 | |
Extracted wood | 10 | 1.27 | 1.06 | 1.41 | |
Holocellulose | 10 | 1.33 | 1.29 | 1.45 | |
Alpha cellulose | 10 | 1.27 | 0.82 | 1.47 | |
Elongation at break (%) | |||||
Neat CA | 10 | 5.87 | 3.82 | 8.52 | |
Extracted wood | 10 | 5.13 | 4.40 | 6.50 | |
Holocellulose | 10 | 4.61 | 3.67 | 6.33 | |
Alpha cellulose | 10 | 4.53 | 4.03 | 5.34 |
Note: means sharing the same superscript are not significantly different from each other (Tukey’s HSD,
The tensile strength and tensile modulus values of neat CA, regardless of the examined wood species, are in the range of values of generic commercial CA (41 to 87 MPa and 1.9 to 3.8 GPa, respectively), as stated by Paunonen [74]. However, there is a difference between the tensile strength values as a function of the wood species from which the CA was prepared (Tables 5 and 6). Those differences could be assigned to the bound acetyl group (% acetyl) values that are different for the examined CA [75]. More precisely, the tensile strength value is lower in the case of the CA prepared from black alder, which had a lower % acetyl value. Although it is common for the tensile modulus to increase with the addition of filler, data in Tables 5 and 6 show significant declines in both the tensile strength and modulus, regardless of the wood species. This can be explained with the low L/D ratio of filler particles (Table 1) and their agglomeration due to high van der Waals attraction forces [76] resulting with insufficient particle wetting. Additionally, it can be related with the polarity differences between the polymer matrix and the fillers [33, 77]. The presence of agglomerated particles limit the load transfer from the matrix (additionally emphasized with the low L/D ratio) to filler particles, and as a consequence, cracks in the structure of biocomposites form at much lower loads and propagate easily. L/D ratios given in Table 1 and the results of mechanical testing (Tables 5 and 6) reveal that the slight rise in tensile strength and modulus in the case of holocellulose-filled composites is most probably due to a slightly higher L/D ratio of such fillers.
The influence of filler rigidity on the values of elongation at break can also be observed in Tables 4 and 5. The decline in the composites’ elongation upon filler addition is caused by the low elongation of the fillers, which restricts the polymer molecules from flowing past one another [74].
If the results obtained in the present study are compared to the findings reported by other authors, it can be noted that the neat CA mechanical properties are somewhat similar. The small differences between our data and those provided in the literature can be attributed to the CA degree of substitution [78, 79], film thickness [80, 81], and plasticizer addition [81]. As for the biocomposites, it is rather difficult to compare the obtained results with the ones from the available literature. This is because the results obtained in different laboratories on natural filler-reinforced composites are often contradictory, as their properties depend on many factors, such as filler size and content, interface adhesion, fibre aspect ratio and orientation, fibre dispersion in the matrix, and stress transfer efficiency through the interface [82]. However, it is obvious that the addition of natural fillers affected the stiffness and decreased the elongation of the matrix. In order to improve the wetting and fibre-matrix adhesion, a compatibilizer should be added [83]. Still, the addition of the plasticizer would probably only partially solve the severe decline of mechanical properties, as the filler size should also be taken into consideration. This is because, in thin composites, nanoscaled fillers can act as reinforcement, while microscaled ones (as those used in this experiment) can decrease the mechanical properties of biocomposite materials [84]. Therefore, future experimental work should be done in order to investigate the effect of the addition of a compatibilizer and filler size reduction on the mechanical (thermal/morphological) properties of CA-based biocomposites.
3.2.2. Surface Morphology
The SEM micrographs in Figures 7(a) and 7(b) show the surfaces of neat CA films prepared from white willow and black alder. It can be seen that the CA film prepared from black alder (Figure 7(b)) has a smooth and even surface, while the one prepared from white willow (Figure 7(a)) exhibits a slightly rougher surface structure. As the unevenness on the surface of the white willow-based CA film resembles a fibre-like structure, its appearance could be associated with the presence of foreign matter and/or cellulose fibres, which have not been successfully acetylated. However, the transparency of the CA film prepared from white willow (
[figures omitted; refer to PDF]
Neat CA films exhibit almost identical morphological structures on both sides (i.e., the one facing the Petri dish bottom and the opposite one facing the Petri dish cover), while the surface morphologies on the two sides of the biocomposites are different for both wood species and all the types of fillers used. In Figure 8, the surface morphology of the white willow-based biocomposite prepared using extracted wood filler is shown. Figure 8(a) exhibits the side facing the Petri dish bottom and Figure 8(b) the upper side of the composite material.
[figures omitted; refer to PDF]
The morphological difference between the two sides can be associated with the evaporation behaviour of the solvent and the fact that prolonged solvent evaporation caused the formation of thin (on average 240 μm thick) films filled with partially overlapping filler particles. Quite slow evaporation of the solvent probably resulted in higher solvent pressure, thus forming smooth surfaces affected only by substrate roughness on the side facing the Petri dish bottom. As mentioned above, insufficient wetting caused the agglomeration of filler particles, thus leading to the formation of a rougher surface on the side facing the Petri dish cover. In Figure 9, the surface morphologies of the biocomposites prepared from white willow using holocellulose (Figure 9(a)) and alpha cellulose (Figure 9(b)) fillers are shown. Figures 9(c) and 9(d) represent the morphologies of the biocomposites prepared from black alder filled with the same types of fillers. In all 4 cases, only the upper sides facing the Petri dish cover are shown, as the bottom-side morphologies are almost identical to the ones showed in Figure 8(a).
[figures omitted; refer to PDF]
As can be remarked from Figure 9(a)–9(d), filler particle agglomeration and overlaying occurred. Also, it is noticeable that some areas of the prepared biocomposites present lack filler, indicating that neat mechanical stirring resulted in the preparation of nonhomogeneous polymer/filler mixtures. In the case of the black alder-based biocomposite filled with alpha cellulose (Figure 9(d)), microcracks surrounding the filler particles are noticeable. The microcracks, particle agglomeration and particle-free spots in the thin films also had a significant influence on the mechanical properties of the biocomposites. Therefore, in further studies, alternative methods (e.g., using a high-speed homogenizer) of homogenization should be examined, alongside the previously mentioned considerations regarding the influence of filler size and plasticizer addition.
4. Conclusions
Biocomposites were prepared, using wood as the starting material for both the matrix and the filler preparation. Such composites were produced based on principles of well-defined (semi-) industrial processes (i.e., acetylation; solvent casting). Therefore, they represent an alternative rational use of somewhat industrially underutilized wood species, with the aim of producing high end-value products. However, the obtained results emphasize the importance of properly selecting the raw material synthesis processes, as well as those for the production of biocomposites. The results also suggest the importance of filler particle chemical composition, size, L/D ratio, and their dispersion in a CA matrix on the properties of the achieved biocomposites. The seclusion of lignin due to prolonged chemical treatments, the formation of cellulose II polymorphic variety, and the more or less pronounced presence of certain crystalline allomorph (i.e., celluloses Iα and Iβ) caused changes in thermal properties of fillers and composites, respectively. As the filler particle size was larger than the polymer matrix radius of gyration, the particle-rich phase segregated and fillers agglomerated during solvent casting of composites, thus causing changes in their thermal properties, surface morphology, and mechanical properties. Additionally, problems associated with the matrix-filler relationship, caused by polarity differences and insufficient wetting due to the filler’s low L/D ratio, have been pointed out, leading to the conclusion that carbohydrate-based fillers used in CA-based matrices acted as nonfunctional fillers, impairing the overall properties of the developed biocomposites.
Although this work undoubtedly demonstrated the possibility to produce biocomposites based on a single wood species for both the matrix and the filler, the results pointed out the need for conducting further experiments in order to fine-tune the structure and properties of CA-based biocomposites. Using higher purity CA and nanosized carbohydrate-based fillers can be one of the possible research directions.
Conflicts of Interest
The authors declare that there is no conflict of interest regarding the publication of this paper.
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Abstract
In the present study, the influence of adding natural fillers to a cellulose acetate (CA) matrix, in order to develop biocomposites, on the properties of the achieved materials has been investigated. Extracted wood flour, holocellulose, and alpha cellulose were used as appropriate fillers. The results of the thermogravimetric analysis (TGA) and differential scanning calorimetry (DSC) of the fillers and biocomposites suggested the importance of the degree of degradation of filler properties, induced by the chemical treatment necessary for the preparation of the fillers, with emphasis on the content of lignin and the degradation of cellulose. Scanning electron microscopy (SEM) and mechanical analysis revealed that the matrix-filler ratio had a major effect on the prepared CA-based biocomposites, since polarity differences between the two major components caused the reduction of attractive forces in the matrix-filler relation, subsequently altering the properties of the developed materials.
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1 Department of Material Technologies, Faculty of Forestry, University of Zagreb, 10 002 Zagreb, Croatia
2 Department of Wood Science and Technology, Biotechnical Faculty, University of Ljubljana, 1 000 Ljubljana, Slovenia