Research article Topical Sections

Exploration of cassava clones for the development of biocomposite films

  • Due to the growing interest in developing bioplastic films from renewable sources, the performance of biocomposite films produced of native starch from cassava clones reinforced with cassava bagasse was explored. The biocomposites were prepared from the starch of cassava clones MMEXV5, MMEXV40, and MMEXCH23, reinforced with bagasse at 1%, 5%, and 15%. Their structural, mechanical, and thermal properties were subsequently assessed. When analyzing the starch, differences in the intensities of the Raman spectra exhibit a possible variation in the amylose-amylopectin ratio. In the biocomposites, the bagasse was efficiently incorporated into polymeric matrixes and their thermogravimetric analysis revealed the compatibility of the matrix-reinforcement. The starch films from the MMEXV40 clone showed better tension (2.53 MPa) and elastic modulus (60.49 MPa). The assessed mechanical properties were also affected by bagasse concentration. Because of the above, the MMEXV40 cassava clone showed potential to develop polymeric materials, given its tuberous roots high yield, starch extraction, and good performance in its mechanical properties. At the same time, the starch source (clone) and the bagasse concentration interfere with the final properties of the biocomposites.

    Citation: José Luis Del Rosario-Arellano, Gloria Ivette Bolio-López, Alex Valadez-González, Luis Zamora-Peredo, Noé Aguilar-Rivera, Isaac Meneses-Márquez, Pablo Andrés-Meza, Otto Raúl Leyva-Ovalle. Exploration of cassava clones for the development of biocomposite films[J]. AIMS Materials Science, 2022, 9(1): 85-104. doi: 10.3934/matersci.2022006

    Related Papers:

    [1] Mahdi Rafiee, Roozbeh Abidnejad, Anton Ranta, Krishna Ojha, Alp Karakoç, Jouni Paltakari . Exploring the possibilities of FDM filaments comprising natural fiber-reinforced biocomposites for additive manufacturing. AIMS Materials Science, 2021, 8(4): 524-537. doi: 10.3934/matersci.2021032
    [2] Rakesh Kumar . Aluminium/iron reinforced polyfurfuryl alcohol resin as advanced biocomposites. AIMS Materials Science, 2016, 3(3): 908-915. doi: 10.3934/matersci.2016.3.908
    [3] Dmitriy V. Likhachev, Natalia Malkova, Leonid Poslavsky . Quantitative characterization and modeling of sub-bandgap absorption features in thin oxide films from spectroscopic ellipsometry data. AIMS Materials Science, 2015, 2(4): 356-368. doi: 10.3934/matersci.2015.4.356
    [4] Alejandro Sandá, Rocío Ruiz, Miguel Ángel Mafé, Jon Ander Sarasua, Antonio González-Jiménez . Scrapping of PEKK-based thermoplastic composites retaining long fibers and their use for compression molded recycled parts. AIMS Materials Science, 2023, 10(5): 819-834. doi: 10.3934/matersci.2023044
    [5] Thomas J. Lee, Andrew H. Morgenstern, Thomas A. Höft, Brittany B. Nelson-Cheeseman . Dispersion of particulate in solvent cast magnetic thermoplastic polyurethane elastomer composites. AIMS Materials Science, 2019, 6(3): 354-362. doi: 10.3934/matersci.2019.3.354
    [6] Larysa Khomenkova, Mykola Baran, Jedrzej Jedrzejewski, Caroline Bonafos, Vincent Paillard, Yevgen Venger, Isaac Balberg, Nadiia Korsunska . Silicon nanocrystals embedded in oxide films grown by magnetron sputtering. AIMS Materials Science, 2016, 3(2): 538-561. doi: 10.3934/matersci.2016.2.538
    [7] Prashant Tripathi, Vivek Kumar Gupta, Anurag Dixit, Raghvendra Kumar Mishra, Satpal Sharma . Development and characterization of low cost jute, bagasse and glass fiber reinforced advanced hybrid epoxy composites. AIMS Materials Science, 2018, 5(2): 320-337. doi: 10.3934/matersci.2018.2.320
    [8] Iryna Markevich, Tetyana Stara, Larysa Khomenkova, Volodymyr Kushnirenko, Lyudmyla Borkovska . Photoluminescence engineering in polycrystalline ZnO and ZnO-based compounds. AIMS Materials Science, 2016, 3(2): 508-524. doi: 10.3934/matersci.2016.2.508
    [9] Wisawat Keaswejjareansuk, Xiang Wang, Richard D. Sisson, Jianyu Liang . Electrospinning process control for fiber-structured poly(Bisphenol A-co-Epichlorohydrin) membrane. AIMS Materials Science, 2020, 7(2): 130-143. doi: 10.3934/matersci.2020.2.130
    [10] João Otávio Donizette Malafatti, Thamara Machado de Oliveira Ruellas, Camila Rodrigues Sciena, Elaine Cristina Paris . PLA/starch biodegradable fibers obtained by the electrospinning method for micronutrient mineral release. AIMS Materials Science, 2023, 10(2): 200-212. doi: 10.3934/matersci.2023011
  • Due to the growing interest in developing bioplastic films from renewable sources, the performance of biocomposite films produced of native starch from cassava clones reinforced with cassava bagasse was explored. The biocomposites were prepared from the starch of cassava clones MMEXV5, MMEXV40, and MMEXCH23, reinforced with bagasse at 1%, 5%, and 15%. Their structural, mechanical, and thermal properties were subsequently assessed. When analyzing the starch, differences in the intensities of the Raman spectra exhibit a possible variation in the amylose-amylopectin ratio. In the biocomposites, the bagasse was efficiently incorporated into polymeric matrixes and their thermogravimetric analysis revealed the compatibility of the matrix-reinforcement. The starch films from the MMEXV40 clone showed better tension (2.53 MPa) and elastic modulus (60.49 MPa). The assessed mechanical properties were also affected by bagasse concentration. Because of the above, the MMEXV40 cassava clone showed potential to develop polymeric materials, given its tuberous roots high yield, starch extraction, and good performance in its mechanical properties. At the same time, the starch source (clone) and the bagasse concentration interfere with the final properties of the biocomposites.



    Plastics from fossil origin are indispensable materials for various human activities [1]; however, they relate to waste accumulation in the environment, damage to aquatic and terrestrial fauna, and effects on human health [2,3,4,5]. Nowadays, 8.3 billion tons of plastic have been manufactured globally; however, if production and consumption trends continue in the next three decades, up to 12 billion tons could end up in open-air dumps or the environment [6], especially by industrial packaging products [7]. Therefore, an appropriate waste management plan, certain government regulations, and using innovative solutions are necessary to decrease the inconveniences of conventional plastics [8].

    Bioplastics are materials proposed as an eco-friendly alternative, where starch is considered one of the most widely used biopolymers [7], due to its abundance, and renewable and economic nature [9,10]. In this regard, corn is a raw material to extract polysaccharides for bioplastics manufacture [11]. It is one of the most important cereals in the world, cultivated on 192 million hectares, with an average yield of 5.6 t ha−1 [12]. Nevertheless, for bioplastics production, it is necessary to explore other resources not competing with food production, given the continuous increase in the demand for food products because of population growth [13]. It should be noted that cassava (Manihot esculenta Crantz) is a tropical tuber with a world average yield of 11.26 t ha−1 [12], which stands out from other starchy crops for its ability to produce in infertile soils, under water stress, and for its drought adaptability [14,15,16]. Moreover, it can produce ~74% to 90% starch (dry base [17,18]) which is easy to extract [19]. This, together with the clarity of its paste and gel stability, including the low gelatinization temperature of its starch, makes it an ideal raw material for the sustainable development of biodegradable materials [20].

    It is worth mentioning that starch-based bioplastic films have low mechanical and barrier properties [21,22], due to the hydrophilic nature of their polymer [23], which is why thermoplastic starch conversion (TPS) or using mixtures with other polymers is frequent [24]. Nevertheless, the origin, morphological and structural properties, and chemical composition of native starch are factors that can induce a wide range of properties in their films [21,22,23,24,25,26]. Also, incorporating natural fibers into polymeric matrixes improves the functional properties of bioplastic films [27], which have attracted attention because of their bioavailability, renewability, high resistance, rigidity, low density, and cost [28,29].

    To this regard, the cassava industry produces a large amount of lignocellulosic solid waste [30], which could be used as reinforcing agents in biocomposites. It should be noted that up to 2.5 tons of bagasse are generated for each extracted starch ton [31], and from 100 to 200 kg of peels per ton of processed roots [32]. Although both byproducts can be used as reinforcement materials in biocomposites, bagasse has greater efficiency, partly due to its high residual starch content [33]. Thus, its incorporation into polymeric matrixes can contribute to sustainable waste management and offer added value to their byproducts [34].

    In Mexico, cassava crop is done following traditional agricultural systems for self-consumption [35,36]. Despite this, a 12.58 t ha−1 yield is reached, which is 11.72% higher than the world average [12]. At the same time, there is great native germplasm diversity with contrasting morpho-agronomic and industrial characteristics [37,38,39,40], not yet extensively explored for biodegradable films development. Furthermore, the importance in Mexico of cassava to produce bioplastics is that it is an alternative to the usage of starch from food sources such as corn, a staple food cereal, which requires to import up to 17 million tons per year to meet its demand [41,42]. Therefore, the objective of this research was to explore the structural, mechanical, and thermal properties of biocomposite films made with starches from three native cassava clones, MMEXV5, MMEXV40, and MMEXCH23, reinforced with three bagasse concentrations (1%, 5%, and 15%) as reinforcement.

    The cassava clones, MMEXV5, MMEXV40, and MMEXCH23, were sown and harvested 10 months after sowing (February–December 2018 agricultural cycle) at the Cotaxtla Experimental Field (18°56'11.28" NL and 96°11'49.53" WL) of the National Institute of Forestry, Agricultural, and Livestock Research (NIFALR), Veracruz, Mexico. Later, in the General Uses Laboratory of the Faculty of Biological and Agricultural Sciences, from the University of Veracruz, the native starch was extracted from the tuberous roots, following the methodology by López et al. [43], and Vargas et al. [44], with slight modifications. To do this, the roots were immersed in a NaClO solution (250 ppm L−1) for 10 min, then peeled. After this, the pulp was removed and cut into small pieces, then grounded in a juice extractor (Haus, model: 74.20304, China) until a whitish suspension was obtained and the bagasse byproduct separated. The suspension was filtered through a mesh plastic (0.5 mm); 500 mL distilled water was added to the filtrate, and then stirred, the starch was let to settle for three hours. Afterward, it was decanted until a starch paste (settled starch) was obtained. This procedure was repeated three times. The fresh bagasse was squeezed in a plastic mesh until a starch suspension was obtained. The resulting settled starch was then placed in an oven (Ecoshel 9023A, United States) at a 50 ℃ temperature for 24 h, while the fresh bagasse was dried at 50 ℃ for 72 h [34].

    The diameter of the native starch granules was determined with optical microscope images (Leica DMLM, Germany), for which 120 granules were measured with the Image Pro-Plus software. Also, the amylose-amylopectin ratio was qualitatively calculated by comparing the average of three Raman spectra per starch (DXR Raman Microscope, Thermo Scientific, United States). For this, a small starch sample was placed in an aluminum sample holder. Samples were subjected to a 100 mW power laser for excitation and scattered radiation was collected at 180°. For each spectrum, an average of 1024 scans were taken at a 4 cm−1 resolution. It should be noted that Raman spectroscopy has been proposed to evaluate various organic compounds content in samples [45,46,47].

    Meanwhile, the distribution of the dry bagasse particles of the three cassava clones was assessed by a set of sieves with mesh sizes of 250 and 75 µm (Mont-Inox, MON200A060 and MON200A200, Mexico). The sieving procedure was carried out manually for 5 min. The retained fractions on each mesh were separated and weighed on an analytical balance (Denver Instrument A-200DS, United States). Due to a higher proportion of bagasse in the roots of the MMEXCH23 clone reported from previous research [48], and the reinforcement efficiency of < 300 µm particle sizes [49,50], the cassava bagasse of the MMEXCH23 clone with a 250–75 µm particle size was used as a reinforcing agent for the polymeric matrixes. The microscopic morphologies of the samples were observed by scanning electron microscope (JSM 7600F, JEOL, Japan) using 1 kV acceleration voltage and a thin graphite layer as a conductive adhesive to fix the sample and to avoid images variation.

    Biocomposite films were prepared using a casting method. The film-forming solution included 5 g of cassava starch dispersed with 100 mL distilled water, glycerol as a plasticizer (0.39 g dry starch), and the addition of 1%, 5%, and 15% of dry bagasse by weight of starch. The bagasse was pre-mixed with the starch to achieve good particle dispersion [51]. The suspensions were gelatinized at 90 ℃ for 20 min under vigorous mechanical shaking (Thermo Scientific Cimarec, United States). The film-forming solution was poured into a 12 × 13 cm cellulose acetate container. To facilitate the films' removal, the container was previously impregnated with a light vegetable oil layer (Pam Spray®). Subsequently, the films were dried in an oven (Ecoshel 9023A, United States) at 40 ℃ for 48 hours; then, gently removed and stored in polyethylene bags at room temperature. A control film without bagasse was used for comparison (Table 1).

    Table 1.  Biocomposite films from native starch of the MMEXV5, MMEXV40, and MMEXCH23 cassava clones, reinforced with three bagasse concentrations.
    Biocomposite films Starch (g) Bagasse (g)
    MMEXV5–B0 5 0
    MMEXV5–B1 5 0.05
    MMEXV5–B5 5 0.25
    MMEXV5–B15 5 0.75
    MMEXV40–B0 5 0
    MMEXV40–B1 5 0.05
    MMEXV40–B5 5 0.25
    MMEXV40–B15 5 0.75
    MMEXCH23–B0 5 0
    MMEXCH23–B1 5 0.05
    MMEXCH23–B5 5 0.25
    MMEXCH23–B15 5 0.75
    Cassava bagasse concentration with particle size between 250–75 µm: B0 = 0% (control), B1 = 1%, B5 = 5% and B15 = 15% by weight of dry starch.

     | Show Table
    DownLoad: CSV

    The films were conditioned in a desiccator at 25 ℃ with 55% relative humidity under a saturated solution of magnesium nitrate hexahydrate ((Mg (NO3)2·6H2O)) for 96 h before each test, following the ASTM E 104, 2002 standard. The films were then removed and placed in dry plastic bags and sealed for 24 hours.

    The mechanical analysis was determined following the ASTM D882-02 norm. A universal testing machine, equipped with a 10 N load cell, was used at a 2 mm min−1 speed (Shimadzu AGS-X, Japan). The tensile strength values (σ), elastic modulus (E), and elongation percentage at break (e) of five specimens were recorded. Additionally, the film thickness was recorded on ten measurements of different segments of each sample with a digital micrometer (Mitutoyo, Model 500-196-30, Japan).

    The thermal degradation and stability of the biocomposites were assessed by thermogravimetric analysis (Perkin Elmer TGA7, United States). For this, ~10 mg film samples were heated from 50 to 600 ℃ at a heating rate of 10 ℃ min−1 in a nitrogen atmosphere with a 20 mL min−1 flow rate. Weight loss as a function of temperature was plotted as a thermogravimetric analysis curve.

    The traits of the native starch (diameter of the granule) and bagasse (distribution of the bagasse particles) were analyzed by descriptive statistics. The biocomposite films´ properties were evaluated with an ANOVA and Tukey (P < 0.05) means comparison test for a completely randomized design with a factorial arrangement. However, the research's traits were verified for statistical assumptions, analyzing their normal distribution of errors using the Shapiro–Wilk test and homogeneity of the variance using Leven test using the SPSS statistical software [52].

    Regard the native starch properties, the granules of the MMEXV40 and MMEXCH23 clones were larger, 14.26 ± 2.16 and 14.15 ± 2.01 µm respectively, than those of the MMEXV5 clone, with 12.80 ± 1.92 µm. The diameters were like those reported by Oyeyinka et al. [53]. However, these are considered small [54,55] due to the wide variation of starch in the species (4–40 µm) [56,57,58].

    In Figure 1, the typical Raman spectra of starch are shown, which are associated with the amylose and amylopectin bands, although there is a similarity in the bands' position between the starches of the three cassava clones, they differ in their intensity. It has been mentioned that, in the spectra of the two α-D-glucose polymers, band changes occur, such as the vibrating band of the pyranose ring skeleton around 475–485 cm−1, attributed to the C–O–C ring mode and C–C–O, likewise, the bands around 320, 410, 769 and 1382 cm−1 [59,60]. For amylose, a band has been assigned at 480 cm−1 [61], while for amylopectin, there are additional bands at 614, 844, 865, 910, and 1396 cm−1 [59,62]. Thus, although amylose and amylopectin almost completely share their spectral characteristics, their different molecular assemblages, and the intensity of their peak are useful for their identification [61,62,63]. Based on the aforementioned, in the 473 cm−1 signals, a greater intensity (height) of the peak was observed for MMEXV40 and MMEXCH23 samples, which shows that these clones have a similarly amylose–amylopectin ratio than the starch of the MMEXV5 clone, an aspect that can cause differences in their size, shape, and granules properties, both, between species and within them [64], and consequently, affect the bioplastics' final properties.

    Figure 1.  Raman spectra of starch from MMEXV5, MMEXV40, and MMEXCH23 cassava clones.

    Based on the size of the bagasse particle distribution (Figure 2), a greater quantity of >250 µm particles (89.9% and 91.79%) was reported. This differs from that stated by Versino and García [34], who reported 56% of <53 µm particles, probably due to these authors subjecting the fibrous residue to mechanical treatment, a procedure that could cause the fibers to break and thus affect their size and concentration. A similar proportion of particles sizes between each clone's bagasse suggests that the byproduct separation was efficient. Likewise, the results show that, like cassava flour, bagasse is the product of a mixture of various particle sizes [65]. Also, carbohydrates are the largest component in bagasse, mainly starch granules [66], as evidenced in the SEM micrographs (Figure 3), where native starch have very varied forms, including spherical, oval, and truncated, which are characteristic shapes of the species [57,67,68].

    Figure 2.  Size of the particle distribution in bagasse of three cassava clones.
    Figure 3.  SEM micrographs of the cassava clones bagasse: (a) MMEXV5, (b) MMEXV40, and (c) MMEXCH23 (×1000).

    Significant differences were found for film thickness in the function of the bagasse concentration (P < 0.01) and Clone* Bagasse interaction (P < 0.05). In this regard, the thickness of the film increased up to 20.51% in the 15% reinforced films compared to the control (Figure 4b, c). The found 0.29, and 0.40 thicknesses are lower than those obtained by de Azêvedo et al. [69], who reported thicknesses of 0.55 to 0.61 mm and 0.44 to 0.76 mm when using twice corn and potato starch ratios as matrixes respectively, plasticized with 5% glycerol and reinforced with 0.5% to 1.5% silicon particles, while by increasing the amount of plasticizer (7.5%), the thickness increased from 0.71 to 0.77 mm and from 0.54 to 0.75 mm. Therefore, the quantity of the solids presents in the bioplastic films, their botanical origin, and the addition of plasticizers and particles as reinforcement affect their thickness. Also, although no differences were shown for this variable in function of the starch, it was observed that the biocomposites from MMEXV40 and MMEXCH23 were less thick, compared to those from MMEXV5 (Figure 4a), a clone with lower amylose content (Figure 2). This result concurs with those by Ploypetchara and Gohtani [70], who report greater thickness when using waxy starch from corn and rice, compared to films formulated with normal starch from both species.

    Figure 4.  Thickness performance in biocomposite films as a function of: (a) starch source; (b) concentrations of cassava bagasse as reinforcement at B0 = 0%, B1 = 1%, B5 = 5%, B15 = 15%; and (c) Clone*Bagasse interaction. Means with the same letter are not significantly different (P > 0.05).

    The bagasse presence increased both, the superficial and transverse roughness of the biocomposites, which resulted in heterogeneous surfaces [71], especially at the 15% concentration, compared to lower concentrations and the control. The finding agrees with those by Edhirej et al. [49], who report smooth and homogeneous textures in films with 3% and 6% cassava bagasse with particle sizes of ˂300 and 300–600 µm. When a high reinforcement proportion is used, the particles density increases, which directly affects the structural integrity of the biocomposites as well as the chemical composition of the lignocellulosic residues. The presence of greater quantity fibers, even at low concentrations, can significantly affect the surface of biocomposites [72]. Likewise, it concurs with the low reinforcement concentrations found by Fazeli et al. [73], who reported smooth films when adding 1% of henequen cellulose nanofibers from Agave fourcroydes, to starch polymeric matrixes. On other hand, visually, there were no cracks, pores, or agglomerations (Figure 5). This indicates a good particle dispersion in the polymeric matrix [74] and their structural incorporation due to their biocompatibility [71,75]. This is important, given that dispersion effects matrix properties [2,76]. In this regard, good load incorporation promotes strong interactions between the reinforcement and the matrix, which results in better ductility, resistance, optical properties, among others [51]. However, there are some overtones of unbroken granules; an aspect indicating the possibility of improving the processing conditions.

    Figure 5.  SEM micrographs and stereoscopic images of biocomposites based on thermoplastic starch reinforced with cassava bagasse. MMEXV5, (a) 0%, (b) 1%, (c) 5%, (d) 15%; MMEXV40, (e) 0%, (f) 1%, (g) 5%, (h) 15% and MMEXCH23, (i) 0%, (j) 1%, (k) 5%, (l) 15%.

    The statistical analysis showed significant differences (P < 0.05) in the mechanical properties: σ, E, and e for the different assessed biocomposites due the source of the starch of their polymeric matrix (Figure 6) and the Clone*Bagasse interaction (Figure 7). Still, the bagasse reinforcement only affected E (P < 0.05) (Figure 6).

    Figure 6.  Main effects on the mechanical properties of biocomposite films: (a–c) starch source (MMEXV5, MMEXV40, and MMEXCH23); and (d–f), bagasse concentration as a reinforcing agent of the polymeric matrix. Means with the same letter are not significantly different (P > 0.05). Bagasse concentration at B0 = 0%, B1 = 1%, B5 = 5%, and B15 = 15%.
    Figure 7.  Effect of the Clone*Bagasse interaction on the mechanical properties: (a) stress at break, (b) Young's modulus, and (c) percent elongation at break. Means in the column with the same letter are not significantly different (P > 0.05). Bagasse concentration at B0 = 0%, B1 = 1%, B5 = 5%, and B15 = 15%.

    From the abovementioned, the starch of the MMEXV40 clone had better tensile stress and elastic modulus performance, of 2.53 and 60.49 MPa respectively (Figure 6a, b). This performance is probably due to a high content of amylose in the starch granules since the linear chains of this molecule have a high tendency to hydrogen bonds interaction, which forms a rigid rod-shaped filaments network (10 to 30 nm in diameter). Consequently, this provides more rigid, strong, cohesive, and dense films and solutions [77,78,79]. In contrast, biocomposites made with MMEXV5, which, as expected, achieved a higher elongation at break percentage (37.72%) due to a high amylopectin content (Figure 6c). Lourdin et al. [80], detected a more than 80% increase in tensile strength in bioplastic films made with a high amylose content; compared with greater flexibility in those made from starch with a high amylopectin content [80,81].

    At the same time, in the biocomposites with 15% bagasse, a modulus increase of up to 68.90% was recorded, compared to films without reinforcement (Figure 6e). This is because of the rigid nature of the components of the fibrous material [82], such as hemicellulose, cellulose, and lignin, which after starch, are found in greater quantities [83,84]. Furthermore, increasing the concentration of the reinforcing agent reduces the free volume of the polymeric matrix chains and increases the intermolecular forces. However, mobility is reduced [34,85], which in turn reduces the elongation percentage. Also, due to the fiber's hydrophilic nature, good compatibility between the reinforcement and the matrix is obtained [27]. Overall, the biocomposites reached mechanical values already reported in the literature [71,86]; however, these are considered as low, if they are contrasted with commercial PVC and LDPE films [26].

    Furthermore, the best combined mechanical performance for tensile stress (Figure 7a) and elastic modulus (Figure 7b) resulted from MMEXV40 and MMEXCH23, mechanical properties that showed a correlation coefficient of 0.83 (P < 0.01); however, at a higher concentration (15%), the MMEXV40 biocomposite decreased these properties, contrary to MMEXV5 and MMEXCH23. In this regard, has been reported that the best compatibility between the matrix and the reinforcement (starch, cassava bagasse) was reached at a 6% concentration, independently of the fiber's size, while above this proportion, the films tend to be brittle, with a rough surface with pores and cracks appearance, which are factors that lead to mechanical failures. Nevertheless, given the obtained results, biocomposites could withstand reinforcements of up to 15%, depending on the starch source. Finally, the elongation at break (Figure 7c) performed significantly inverse to tensile stress, by showing a correlation coefficient of −0.48 (P < 0.01).

    From the above, although a low mechanical performance of the biocomposites was achieved, based on tensile strength and elastic modulus, compared with other materials reinforced with cellulose nanofibers [87], and nanocellulose [88,89,90,91], and even with other biodegradable polymers, such as polylactic acid [92], the materials obtained can withstand large loads of cassava bagasse as a reinforcing agent (5% to 15%), which leads to savings in the raw material used as matrix, and with it, the possibility of offering added value to the co-product. On the other hand, the biocomposites produced lead to green chemistry [93], by not using chemical agents for the pre-treatment or treatment of bagasse. Meanwhile, elongation at break > 300% higher than that reported by Edhirej et al. [49], suggests that biocomposites can be used for the production of single-use plastics, where high percentages of elongation are required, such as packaging for the food industry.

    The mass loss curve as a function of TGA temperature shows the thermal degradation of the components of the biocomposite film. The TGA curves revealed a similar performance independently of the starch source (Figure 8). A first mass loss was detected from 50 ℃ to approximately 145 ℃, which relates to the dehydration of the materials [85]. The greatest mass loss occurred between 200–350 ℃ [76,94], an event that relates to the component's starch (amylose, amylopectin) and glycerol decomposition, from hydrogen groups loss, decomposition and depolymerization of carbon chains, as well as structural carbohydrates of the bagasse, such as cellulose and hemicellulose [95,96,97]. The maximum decomposition temperature occurred at ~306 ℃ for all the biocomposites; these results are similar to those by Edhirej et al. [49], even for unreinforced films [86]. In general, the presence of a high proportion of cassava bagasse (5% and 15%) led to a lower mass loss (Figure 8), thus improving the thermal stability of the biocomposites.

    Figure 8.  Thermal performance of biocomposite films from: (a) MMEXV5, (b) MMEXV40, and (c) MMEXCH23, reinforced with cassava bagasse at B0 = 0%, B1 = 1%, B5 = 5%, and B15 = 15%.

    Based on the obtained results and considering the agro-industrial behavior of the cassava clones in previous research [45], where the MMEXV5 and MMEXV40 clones reached high tuberous roots yield, pulp, peel, fresh and dry bagasse, and starch yield; It is concluded that good agro-industrial performance increases the productive potential of cassava clones to produce bioplastic films, which, together with cassava bagasse as a reinforcing agent of the polymeric matrix, are a sustainable alternative to boost the biorefinery in cassava cultivation [98].

    In native starch, there are variations in the amylose–amylopectin ratio at the intravarietal level, which contributes to differences in the mechanical properties of biodegradable films. On other hand, cassava bagasse, an underutilized byproduct, can be used as a reinforcing agent for the polymeric matrixes, thereby helping to decrease industrial waste, offering an added value. From the aforementioned, a 5% bagasse concentration in biocomposites manufacture reported better mechanical performance and thermal stability, which is related to the surface homogeneity of the films. Also, the MMEXV40 cassava clone has the potential to be distributed among farmers due to its high agricultural productivity, which together with its high starch extraction yield and outstanding properties for biocomposite films, make it a promising material for bioplastics production. Finally, it is important to conserve and value the native plant species' germplasm, since they have the potential for unknown uses.

    The authors thank the National Council for Science and Technology (CONACYT) for the scholarship granted for the development of postgraduate studies, the technicians of Scientific Research Center of Yucatan (CICY). To the M.Sc. María Veronica Moreno Chulim for her support for the thermogravimetric analysis. M.Sc. Silvia Andrade Canto for her help on scanning electron microscopy, and M.Sc. Javier Cauich Cupul for his help in determining the mechanical properties. We would also like to thank the Popular University of the Chontalpa (UPCH), for the attention provided during the doctoral period. Finally, we wish to thank the technical team of the Micro and Nanotechnology Research Center (MICRONA) of the University of Veracruz for the microscopy of and Raman analyses.

    All authors declare no conflicts of interest in this paper.



    [1] Ciardelli F, Bertoldo M, Bronco S, et al. (2019) Environmental impact, In: Ciardelli F, Bertoldo M, Bronco S, et al., Polymers from Fossil and Renewable Resources, 1 Ed., Cham: Springer, 161-187. https://doi.org/10.1007/978-3-319-94434-0
    [2] Aigbodion VS, Okonkwo EG, Akinlabi ET (2019) Eco-friendly polymer composite: State-of-arts, opportunities and challenge, In: Inamuddin TS, Kumar MR, Asiri A, Sustainable Polymer Composites and Nanocomposites, 1 Ed., Cham: Springer, 1233-1265. https://doi.org/10.1007/978-3-030-05399-4_42
    [3] Shankar S, Singh S, Mishra A, et al. (2019) Microbial degradation of polyethylene: Recent progress and challenges, In: Arora P, Microbial Metabolism of Xenobiotic Compounds. Microorganisms for Sustainability, 1 Ed., Singapore: Springer, 245-262. https://doi.org/10.1007/978-981-13-7462-3_12
    [4] Singh N, Duan H, Tang Y (2020) Toxicity evaluation of e-waste plastics and potential repercussions for human health. Environ Int 137: 105559. https://doi.org/10.1016/j.envint.2020.105559 doi: 10.1016/j.envint.2020.105559
    [5] Saturno J, Liboiron M, Ammendolia J, et al. (2020) Occurrence of plastics ingested by Atlantic cod (Gadus morhua) destined for human consumption (Fogo Island, Newfoundland and Labrador). Mar Pollut Bull 153: 110993. https://doi.org/10.1016/j.marpolbul.2020.110993 doi: 10.1016/j.marpolbul.2020.110993
    [6] Geyer R, Jambeck RJ, Lavender LK (2017) Production, use, and fate of all plastics ever made. Sci Adv 3: 25-29. https://doi.org/10.1126/sciadv.1700782 doi: 10.1126/sciadv.1700782
    [7] New Market Data 2019: Bioplastics Industry Continues Dynamic Grow Over the Next Five Years. European Bioplastics, 2019. Available from: https://www.european-bioplastics.org/new-market-data-2019-bioplastics-industry-continues-dynamic-grow-over-the-next-five-years/.
    [8] Babayemi JO, Nnorom IC, Osibanjo O, et al. (2019) Ensuring sustainability in plastics use in Africa: consumption, waste generation, and projections. Environ Sci Eur 31: 20. https://doi.org/10.1186/s12302-019-0254-5 doi: 10.1186/s12302-019-0254-5
    [9] Andrade JC, Acosta DL, Bucheli MA, et al. (2014) Development of an edible coating compound for the conservation of tree tomato (Cyphomandra betacea S.). Inf Tecnol 25: 57-66 (In Spanish). http://dx.doi.org/10.4067/S0718-07642014000600008 doi: 10.4067/S0718-07642014000600008
    [10] Edhirej A, Sapuan SM, Jawaid M, et al. (2015) Cassava: Its polymer, fiber, composite, and application. Polym Composite 38: 555-570. https://doi.org/10.1002/pc.23614 doi: 10.1002/pc.23614
    [11] IfBB, Biopolymers—Facts and Statistics: Production Capacities, Processing Routes, Feedstock, Land and Water Use. Institute for Bioplastics and Biocomposites, 2019. Available from: https://www.ifbb-hannover.de/en/facts-and-statistics.html.
    [12] Crops and Livestock Products. FAOSTAT, 2020. Available from: https://www.fao.org/faostat/en/#data/QCL.
    [13] World Population Prospects. United Nations, Department of Economic and Social Affairs, Population Division, 2019. Available from: https://population.un.org/wpp/.
    [14] Sharma HK, Kaushal P (2016) Introduction to tropical roots and tubers, In: Sharma HK, Njintang NY, Singhal RS, et al., Tropical Roots and Tubers: Production, Processing and Technology, 1 Ed., Hoboken: John Wiley & Sons, 1-33. https://doi.org/10.1002/9781118992739.ch1
    [15] Shigaki T (2016) Cassava: Nature and uses. In: Caballero B, Finglas P, Toldra F, Encyclopedia of Food and Health, 1 Ed., Oxford: Elsevier, 687-693. https://doi.org/10.1016/B978-0-12-384947-2.00124-0
    [16] Cock JH (2019) Cassava: New Potential for a Neglected Crop, Boca Raton: CRC Press. https://doi.org/10.1201/9780429049064
    [17] Mtunguja MK, Laswai HS, Muzanila YC, et al. (2014) Farmer's knowledge on selection and conservation of cassava (Manihot esculenta) genetic resources in Tanzania. J Biol Agric Healthc 4: 120-129.
    [18] Parmar A, Sturm B, Hensel O (2017) Crops that feed the world: Production and improvement of cassava for food, feed, and industrial uses. Food Secur 9: 907-927. https://doi.org/10.1007/s12571-017-0717-8 doi: 10.1007/s12571-017-0717-8
    [19] Alarcon F, Dufour D (1998) Sour Starch from Cassava in Colombia. Production and Recommendations, Cali: CIAT, 9-24 (In Spanish). Available from: https://www.clayuca.org/sitio/images/publicaciones/almidon_agrio_tomo_1.pdf.
    [20] Chisenga SM, Workneh TS, Bultosa G, et al. (2019) Progress in research and applications of cassava flour and starch: a review. J Food Sci Tech 56: 2799-28131. https://doi.org/10.1007/s13197-019-03814-6 doi: 10.1007/s13197-019-03814-6
    [21] Arifin B, Sugita P, Masyudi DE (2016) Chitosan and lauric acid addition to corn starch-film based effect: Physical properties and antimicrobial activity study. Int J Chem Sci 14: 529-544.
    [22] Dharmalingam K, Anandalakshmi R (2019) Polysaccharide-based films for food packaging ppplications, In: Katiyar V, Gupta R, Ghosh T, Advances in Sustainable Polymers. Materials Horizons: From Nature to Nanomaterials, 1 Ed., Singapore: Springer, 183-207. https://doi.org/10.1007/978-981-32-9804-0_9
    [23] Teodoro AP, Mali S, Romero N, et al. (2015) Cassava starch films containing acetylated starch nanoparticles as reinforcement: Physical and mechanical characterization. Carbohyd Polym 126: 9-16. https://doi.org/10.1016/j.carbpol.2015.03.021 doi: 10.1016/j.carbpol.2015.03.021
    [24] Krishnamurthy A, Amritkumar P (2019) Synthesis and characterization of eco-friendly bioplastic from low-cost plant resources. SN Appl Sci 1: 1432. https://doi.org/10.1007/s42452-019-1460-x doi: 10.1007/s42452-019-1460-x
    [25] Sagnelli D, Hebelstrup KH, Leroy E, et al. (2016) Plant-crafted starches for bioplastics production. Carbohyd Polym 152: 398-408. https://doi.org/10.1016/j.carbpol.2016.07.039 doi: 10.1016/j.carbpol.2016.07.039
    [26] Luchese CL, Spada JC, Tessaro IC (2017) Starch content affects physicochemical properties of corn and cassava starch-based films. Ind Crop Prod 109: 619-626. https://doi.org/10.1016/j.indcrop.2017.09.020 doi: 10.1016/j.indcrop.2017.09.020
    [27] Berthet AM, Angellier-Coussy H, Guillard V, et al. (2016) Vegetal fiber-based biocomposites: Which stakes for food packaging applications? J Appl Polym Sci 133: 1-18. https://doi.org/10.1002/app.42528 doi: 10.1002/app.42528
    [28] Noorjahan SE, Sekar S, Sastry TP (2008) Preparation and characterization of cellulose triacetate from Musa paradisiaca and cellulose triacetate-polyvinyl chloride blends. Curr Sci 95: 958-962.
    [29] Jonoobi M, Oladi R, Davoudpour Y, et al. (2015) Different preparation methods and properties of nanostructured cellulose from various natural resources and residues: a review. Cellulose 2: 935-969. https://doi.org/10.1007/s10570-015-0551-0 doi: 10.1007/s10570-015-0551-0
    [30] Li S, Cui Y, Zhou Y, et al. (2017) The industrial applications of cassava: Current status, opportunities and prospects. J Sci Food Agric 97: 2282-2290. https://doi.org/10.1002/jsfa.8287 doi: 10.1002/jsfa.8287
    [31] Trakulvichean S, Chaiprasert P, Otmakhova J, et al. (2017) Integrated economic and environmental assessment of biogas and bioethanol production from cassava cellulosic waste. Waste Biomass Valorization 10: 691-700. https://doi.org/10.1007/s12649-017-0076-x doi: 10.1007/s12649-017-0076-x
    [32] Anyanwu CN, Ibeto CN, Ezeoha SL, et al. (2015) Sustainability of cassava (Manihot esculenta Crantz) as industrial feedstock, energy and food crop in Nigeria. Renew Energ 81: 745-752. https://doi.org/10.1016/j.renene.2015.03.075 doi: 10.1016/j.renene.2015.03.075
    [33] Versino F (2017) Biodegradable composite materials with agronomic uses from tuberous roots [PhD's thesis]. National University of the Plata, Argentina (In Spanish). Available from: http://sedici.unlp.edu.ar/handle/10915/66038.
    [34] Versino F, García MA (2014) Cassava (Manihot esculenta) starch films reinforced with natural fibrous filler. Ind Crop Prod 58: 305-314. https://doi.org/10.1016/j.indcrop.2014.04.040 doi: 10.1016/j.indcrop.2014.04.040
    [35] Mateos-Maces L, Castillo-González F, Chávez SJL, et al. (2016) Managing and use of the agrobiodiversity in the milpa system from southeast of Mexico. Acta Agron 65: 413-421 (In Spanish). https://doi.org/10.15446/acag.v65n4.50984 doi: 10.15446/acag.v65n4.50984
    [36] Centurión-Hidalgo D, Espinosa-Moreno J, Cruz-Lázaro E, et al. (2019) Seasonality of vegetables commercialized in Tabasco's public markets. Rev Aliment Contemp Desarro Reg 29: 16 (In Spanish). https://doi.org/10.24836/es.v29i53.629 doi: 10.24836/es.v29i53.629
    [37] Meneses MI, Vázquez HA, Rosas GX, et al. (2014) Dry matter and starch content in cassava clones (Manihot esculenta Crantz). Rev Biol Agropecu Tuxpan 26: 271-274 (In Spanish). https://doi.org/10.47808/revistabioagro.v2i1.268 doi: 10.47808/revistabioagro.v2i1.268
    [38] Meneses MI, Vázquez HA, Rosas GX, et al. (2014) Collection and ex situ conservation of cassava germplasm in the state of Veracruz. XXVI Forest and Agricultural Scientific-Technological Meeting Tabasco 2014 and III International Symposium on Tropical Food Production, México: Tabasco 426-431 (In Spanish). Available from: https://www.researchgate.net/profile/Jorge-Herrera-19/publication/310828417_XXVI_Reunion_Cientifica_Tecnologica_Forestal_y_Agropecuaria_Tabasco_2014_La_Innovacion_tecnologica_para_la_seguridad_alimentaria_ISBN_978-607-606-212-8/links/583890aa08ae3d91723ddda5/XXVI-Reunion-Cientifica-Tecnologica-Forestal-y-Agropecuaria-Tabasco-2014-La-Innovacion-tecnologica-para-la-seguridad-alimentaria-ISBN-978-607-606-212-8.pdf.
    [39] García-Sánchez AS, González-Valdivia NA, Arcocha-Gómez E, et al. (2018) Accessions and varieties of cassava (Manihot esculenta Crantz.) in the Yucatan peninsula, Mexico. Rev Cent Grad Investig 33: 30-33 (In Spanish). Available from: http://www.revistadelcentrodegraduados.com/2019/05/accesiones-y-variedades-de-yuca-manihot.html.
    [40] Support for the Selective Collection of Plant Genetic Resources for Food and Agriculture. Cassava. SNICS (National Seed Inspection and Certification Service), 2020 (In Spanish). Available from: https://www.gob.mx/snics/acciones-y-programas/linea-5-apoyo-a-la-recoleccion-selectiva-de-recursos-fitogeneticos-para-la-alimentacion-y-la-agricultura.
    [41] Flores-Cruz LA, García-Salazar JA (2016) Benefits of the adoption of improved corn seed in the central region of Puebla. Rev Fitotec Mex 39: 277-283 (In Spanish). https://doi.org/10.35196/rfm.2016.3.277-283 doi: 10.35196/rfm.2016.3.277-283
    [42] OCDE/FAO, OCDE-FAO Agricultural Outlook 2019-2028. Paris/Food and Agriculture Organization of the United Nations (FAO), 2019 (In Spanish). Available from: https://www.oecd-ilibrary.org/agriculture-and-food/ocde-fao-perspectivas-agricolas-2019-2028_7b2e8ba3-es.
    [43] López OV, Viña SZ, Pachas ANA, et al. (2010) Composition and food properties of Pachyrhizus ahipa roots and starch. Int J Food Sci Technol 45: 223-233 (In Spanish). https://doi.org/10.1111/j.1365-2621.2009.02125.x doi: 10.1111/j.1365-2621.2009.02125.x
    [44] Vargas ENA, Veleva L, Rodríguez CM, et al. (2017) Cassava (Manihot esculenta), alternative for the production of bioplastics, In: Martínez SR, González HRI, Environmental and Chemical Engineering Faced with Environmental Problems in the Mexican Southeast, 1 Ed., Chiapas: University of Sciences and Arts of Chiapas, 159-174 (In Spanish). Available from: https://catalogo.altexto.mx/la-ingenieria-ambiental-y-quimica-ante-los-problemas-ambientales-en-el-sureste-mexicano-ii-7nxlt.html.
    [45] Yang D, Ying Y (2011) Applications of Raman spectroscopy in agricultural products and food analysis: A review. Appl Spectrosc Rev 46: 539-560. https://doi.org/10.1080/05704928.2011.593216 doi: 10.1080/05704928.2011.593216
    [46] Velázquez JR, Zamora-Peredo L (2018) Does a mango ripen from the bone to the skin? Mat Cienc Nanotecnol 1: 38-47 (In Spanish). Available from: https://www.researchgate.net/profile/Luis-Zamora-Peredo/publication/325732721_un_mango_se_madura_desde_el_hueso_hacia_la_cascara/links/5b20683c0f7e9b0e373ef19c/un-mango-se-madura-desde-el-hueso-hacia-la-cascara.pdf.
    [47] Zamora-Peredo L, Rodríguez-Jimenez R, García GL, et al. (2018) Study of the pericarp of habanero chili (Capsicum chínense Jacq.) by Raman spectroscopy. Chil J Agric Anim Sci 34: 68-74 (In Spanish). https://doi.org/10.4067/S0719-38902018005000103 doi: 10.4067/S0719-38902018005000103
    [48] Del Rosario-Arellano JL, Meneses-Márquez I, Leyva-Ovalle OR, et al. (2020) Morphoagronomic and industrial performance of cassava (Manihot esculenta Crantz) germplasm for the production of starch and solid byproducts. AIMS Agr Food 5: 617-634. https://doi.org/10.3934/agrfood.2020.4.617 doi: 10.3934/agrfood.2020.4.617
    [49] Edhirej A, Sapuan SM, Jawaid M, et al. (2017) Preparation and characterization of cassava bagasse reinforced thermoplastic cassava starch. Fibers Polym 18: 162-171. https://doi.org/10.1007/s12221-017-6251-7 doi: 10.1007/s12221-017-6251-7
    [50] Versino F, García MA (2018) Cassava starch-based reinforced eco-compatible materials with agronomic applications. Matéria 23: 11. https://doi.org/10.1590/s1517-707620180002.0545 doi: 10.1590/s1517-707620180002.0545
    [51] Castillo L, López O, López C, et al. (2013) Thermoplastic starch films reinforced with talc nanoparticles. Carbohyd Polym 95: 664-674. https://doi.org/10.1016/j.carbpol.2013.03.026 doi: 10.1016/j.carbpol.2013.03.026
    [52] IBM Corp. Released. IBM SPSS Statistics for Windows, Version 25.0. IBM Corp, 2017. Available from: https://www.ibm.com/docs/en/spss-statistics/25.0.0.
    [53] Oyeyinka SA, Adeloye AA, Olaomo OO, et al. (2020) Effect of fermentation time on physicochemical properties of starch extracted from cassava root. Food Biosci 33: 100485. https://doi.org/10.1016/j.fbio.2019.100485 doi: 10.1016/j.fbio.2019.100485
    [54] Tetchi FA, Rolland-Sabaté A, Guessan AGN, et al. (2007) Molecular and physicochemical characterisation of starches from yam, cocoyam, cassava, sweet potato and ginger produced in the Ivory Coast. J Sci Food Agric 87: 2527-2533. https://doi.org/10.1002/jsfa.2928 doi: 10.1002/jsfa.2928
    [55] Lebot V (2019). Tropical Root and Tuber Crops: Cassava, Sweet Potato, Yams and Aroids, Wallingford: CABI. https://doi.org/10.1079/9781789243369.0000
    [56] Hernández-Medina M, Torruco-Uco JG, Chel-Guerrero L, et al. (2008) Physicochemical characterization of starches from tubers grown in Yucatan, Mexico. Ciênc Tecnol Aliment 28: 718-726 (In Spanish). https://doi.org/10.1590/S0101-20612008000300031 doi: 10.1590/S0101-20612008000300031
    [57] Gu B, Yao Q, Li K, et al. (2013) Change in physicochemical traits of cassava roots and starches associated with genotypes and environmental factors. Starch-Starke 65: 253-263. https://doi.org/10.1002/star.201200028 doi: 10.1002/star.201200028
    [58] de Oliveira PHGA, Barbosa ACO, Diniz RP, et al. (2018) Morphological variation of starch granules in S1 cassava progenies. Euphytica 214: 14. https://doi.org/10.1007/s10681-018-2175-6 doi: 10.1007/s10681-018-2175-6
    [59] Gussem KD, Vandenabeele P, Verbeken A, et al. (2005) Raman spectroscopic study of Lactarius spores (Russulales, Fungi). Spectrochim Acta A 61: 2898-2908. https://doi.org/10.1016/j.saa.2004.10.038 doi: 10.1016/j.saa.2004.10.038
    [60] Bernardino-Nicanor A, Acosta-García G, Güemes-Vera N, et al. (2016) Fourier transform infrared and Raman spectroscopic study of the effect of the thermal treatment and extraction methods on the characteristics of ayocote bean starches. J Food Sci Tech 54: 933-943. https://doi.org/10.1007/s13197-016-2370-1 doi: 10.1007/s13197-016-2370-1
    [61] Almeida RM, Alves SR, Nascimbem LRLB, et al. (2010) Determination of amylose content in starch using Raman spectroscopy and multivariate calibration analysis. Anal Bioanal Chem 397: 2693-2701. https://doi.org/10.1007/s00216-010-3566-2 doi: 10.1007/s00216-010-3566-2
    [62] Pezzotti G, Zhu W, Chikaguchi H, et al. (2021) Raman spectroscopic analysis of polysaccharides in popular Japanese rice cultivars. Food Chem 354: 129434. https://doi.org/10.1016/j.foodchem.2021.129434 doi: 10.1016/j.foodchem.2021.129434
    [63] Liu Y, Xu Y, Yan Y, et al. (2015) Application of Raman spectroscopy in structure analysis and crystallinity calculation of corn starch. Starch-Starke 67: 612-619. https://doi.org/10.1002/star.201400246 doi: 10.1002/star.201400246
    [64] Chen J, Chen L, Xie F, et al. (2019) Starch, In: Drug Delivery Applications of Starch Biopolymer Derivatives, 1 Ed., Singapore: Springer, 29-40. https://doi.org/10.1007/978-981-13-3657-7_3
    [65] Chisenga SM, Workneh TS, Bultosa G, et al. (2019) Proximate composition, cyanide contents, and particle size distribution of cassava flour from cassava varieties in Zambia. AIMS Agr Food 4: 869. https://doi.org/10.3934/agrfood.2019.4.869 doi: 10.3934/agrfood.2019.4.869
    [66] Patle S, Lal B (2008) Investigation of the potential of agro-industrial material as low cost substrate for ethanol production by using Candida tropicalis and Zymomonas mobilis. Biomass Bioenergy 32: 596-602. https://doi.org/10.1016/j.biombioe.2007.12.008 doi: 10.1016/j.biombioe.2007.12.008
    [67] Zhu F (2015) Composition, structure, physicochemical properties, and modifications of cassava starch. Carbohyd Polym 122: 456-480. https://doi.org/10.1016/j.carbpol.2014.10.063 doi: 10.1016/j.carbpol.2014.10.063
    [68] Ayetigbo O, Latif S, Abass A, et al. (2018) Comparing characteristics of root, flour and starch of biofortified yellow-flesh and white-flesh cassava variants, and sustainability considerations: A review. Sustainability 10: 3089. https://doi.org/10.3390/su10093089 doi: 10.3390/su10093089
    [69] de Azêvedo LC, Rovani S, Santos JJ, et al. (2020) Study of renewable silica powder influence in the preparation of bioplastics from corn and potato starch. J Polym Environ 29: 1-14. https://doi.org/10.1007/s10924-020-01911-8 doi: 10.1007/s10924-020-01911-8
    [70] Ploypetchara T, Gohtani S (2018) Effect of sugar on starch edible film properties: plasticized effect. J Food Sci Technol 55: 3757-3766. https://doi.org/10.1007/s13197-018-3307-7 doi: 10.1007/s13197-018-3307-7
    [71] de Carvalho GR, Marques GS, de Matos Jorge LM, et al. (2018) Cassava bagasse as a reinforcement agent in the polymeric blend of biodegradable film. J Appl Polym Sci 136: 1-7. https://doi.org/10.1002/app.47224 doi: 10.1002/app.47224
    [72] Versino F, López OV, García MA (2015) Sustainable use of cassava (Manihot esculenta) roots as raw material for biocomposites development. Ind Crop Prod 65: 79-89. https://doi.org/10.1016/j.indcrop.2014.11.054 doi: 10.1016/j.indcrop.2014.11.054
    [73] Fazeli M, Keley M, Biazar E (2018). Preparation and characterization of starch-based composite films reinforced by cellulose nanofibers. Int J Biol Macromol 116: 272-280. https://doi.org/10.1016/j.ijbiomac.2018.04.186 doi: 10.1016/j.ijbiomac.2018.04.186
    [74] Perotti GF, Auras R, Constantino VRL (2013) Bionanocomposites of cassava starch and synthetic clay. J Carbohyd Chem 32: 483-501. https://doi.org/10.1080/07328303.2013.858726 doi: 10.1080/07328303.2013.858726
    [75] Yang J, Ching YC, Chuah CH (2019) Applications of lignocellulosic fibers and lignin in bioplastics: A review. Polymers 11: 751. https://doi.org/10.3390/polym11050751 doi: 10.3390/polym11050751
    [76] Rodríguez-Castellanos W, Flores-Ruiz FJ, Martínez-Bustos F, et al. (2015) Nanomechanical properties and thermal stability of recycled cellulose reinforced starch-gelatin polymer composite. J Appl Polym Sci 132: 7. https://doi.org/10.1002/app.41787 doi: 10.1002/app.41787
    [77] Rindlav-Westling A, Standing M, Hermansson AM, et al. (1998) Structure, mechanical and barrier properties of amylose and amylopectin films. Carbohyd Polym 36: 217-224. https://doi.org/10.1016/S0144-8617(98)00025-3 doi: 10.1016/S0144-8617(98)00025-3
    [78] López OV, García MA, Zaritzky NE (2008) Film forming capacity of chemically modified corn starches. Carbohyd Polym 73: 573-581. https://doi.org/10.1016/j.carbpol.2007.12.023 doi: 10.1016/j.carbpol.2007.12.023
    [79] Mukurumbira AR, Mellem JJ, Amonsou EO (2017) Effects of amadumbe starch nanocrystals on the physicochemical properties of starch biocomposite films. Carbohyd Polym 165: 142-148. https://doi.org/10.1016/j.carbpol.2017.02.041 doi: 10.1016/j.carbpol.2017.02.041
    [80] Lourdin D, Della VG, Colonna P (1995) Influence of amylose content on starch films and foams. Carbohyd Polym 27: 261-270. https://doi.org/10.1016/0144-8617(95)00071-2 doi: 10.1016/0144-8617(95)00071-2
    [81] Mali S, Karam LB, Ramos LP, et al. (2004) Relationships among the composition and physicochemical properties of starches with the characteristics of their films. J Agr Food Chem 52: 7720-7725. https://doi.org/10.1021/jf049225 doi: 10.1021/jf049225
    [82] Pereda M, Dufresne A, Aranguren MI, et al. (2014) Polyelectrolyte films based on chitosan/olive oil and reinforced with cellulose nanocrystals. Carbohyd Polym 101: 1018-1026. https://doi.org/10.1016/j.carbpol.2013.10.046 doi: 10.1016/j.carbpol.2013.10.046
    [83] Jimenez RM, Amaral-Fonseca M, Fernandez-Lafuente R, et al. (2019) Recovery of starch from cassava bagasse for cyclodextrin production by sequential treatment with α-amylase and cyclodextrin glycosyltransferase. Biocatal Agric Biotechnol 22: 101411. https://doi.org/10.1016/j.bcab.2019.101411 doi: 10.1016/j.bcab.2019.101411
    [84] Pason P, Tachaapaikoon C, Panichnumsin P, et al. (2020) One-step biohydrogen production from cassava pulp using novel enrichment of anaerobic thermophilic bacteria community. Biocatal Agric Biotechnol 27: 101658. https://doi.org/10.1016/j.bcab.2020.101658 doi: 10.1016/j.bcab.2020.101658
    [85] Cruz G, Rodrigues ALP, da Silva DF, et al. et al. (2020) Physical-chemical characterization and thermal behavior of cassava harvest waste for application in thermochemical processes. J Therm Anal Calorim 143: 3611-3622. https://doi.org/10.1007/s10973-020-09330-6 doi: 10.1007/s10973-020-09330-6
    [86] Luchese CL, Benelli P, Spada JC, et al. (2018) Impact of the starch source on the physicochemical properties and biodegradability of different starch-based films. J Appl Polym Sci 135: 1-11. https://doi.org/10.1002/app.46564 doi: 10.1002/app.46564
    [87] Fazeli M, Keley M, Biazar E (2018) Preparation and characterization of starch-based composite films reinforced by cellulose nanofibers. Int J Biol Macromol 116: 272-280. https://doi.org/10.1016/j.ijbiomac.2018.04.186 doi: 10.1016/j.ijbiomac.2018.04.186
    [88] Teixeira EM, Pasquini D, Curvelo AAS, et al. (2009) Cassava bagasse cellulose nanofibrils reinforced thermoplastic cassava starch. Carbohyd Polym 78: 422-431. https://doi.org/10.1016/j.carbpol.2009.04.034 doi: 10.1016/j.carbpol.2009.04.034
    [89] Savadekar NR, Mhaske S T (2012) Synthesis of nano cellulose fibers and effect on thermoplastics starch based films. Carbohyd Polym 89: 146-151. https://doi.org/10.1016/j.carbpol.2012.02.063 doi: 10.1016/j.carbpol.2012.02.063
    [90] de Campos A, de Sena NAR, Rodrigues VB, et al. (2017) Bionanocomposites produced from cassava starch and oil palm mesocarp cellulose nanowhiskers. Carbohyd Polym 175: 330-336. https://doi.org/10.1016/j.carbpol.2017.07.080 doi: 10.1016/j.carbpol.2017.07.080
    [91] Dufresne A (2018) Cellulose nanomaterials as green nanoreinforcements for polymer nanocomposites. Philos T Roy Soc A 376: 20170040. https://doi.org/10.1098/rsta.2017.0040 doi: 10.1098/rsta.2017.0040
    [92] Laaziz SA, Raji M, Hilali E, et al. (2017) Bio-composites based on polylactic acid and argan nut shell: Production and properties. Int J Biol Macromol 104: 30-42. https://doi.org/10.1016/j.ijbiomac.2017.05.184 doi: 10.1016/j.ijbiomac.2017.05.184
    [93] Thakur S, Chaudhary J, Sharma B, et al. (2018) Sustainability of bioplastics: Opportunities and challenges. Curr Opin Green Sustain Chem 13: 68-75. https://doi.org/10.1016/j.cogsc.2018.04.013 doi: 10.1016/j.cogsc.2018.04.013
    [94] Versino F, López OV, García MA (2019) Exploitation of by-products from cassava and ahipa starch extraction as filler of thermoplastic corn starch. Compos Part B-Eng 182: 8. https://doi.org/10.1016/j.compositesb.2019.107653 doi: 10.1016/j.compositesb.2019.107653
    [95] López GJ, Cuarán CJC, Arenas GLV, et al. (2014) Potential uses of banana peel: elaboration of a bioplastic. Rev Colomb Investig Agroind 1: 7-21 (In Spanish). https://doi.org/10.23850/24220582.109 doi: 10.23850/24220582.109
    [96] Sanyang ML, Sapuan SM, Jawaid M, et al. (2015) Effect of plasticizer type and concentration on tensile, thermal and barrier properties of biodegradable film based on sugar palm (Arenga pinnata) starch. Polymers 7: 1106-1124. https://doi.org/10.3390/polym7061106 doi: 10.3390/polym7061106
    [97] Zanatta ER, Reinehr TO, Awadallak JA, et al. (2016) Kinetic studies of thermal decomposition of sugarcane bagasse and cassava bagasse. J Therm Anal Calorim 125: 437-445 https://doi.org/10.1007/s10973-016-5378-x doi: 10.1007/s10973-016-5378-x
    [98] Budzianowski WM (2017) High-value low-volume bioproducts coupled to bioenergies with potential to enhance business development of sustainable biorefineries. Renew Sust Energ Rev 70: 793-804. https://doi.org/10.1016/j.rser.2016.11.260 doi: 10.1016/j.rser.2016.11.260
  • This article has been cited by:

    1. Pablo Andrés–Meza, Noé Aguilar–Rivera, Isaac Meneses–Márquez, José Luis Del Rosario–Arellano, Gloria Ivette Bolio–López, Otto Raúl Leyva–Ovalle, Cassava cultivation; current and potential use of agroindustrial co–products, 2024, 11, 2372-0352, 248, 10.3934/environsci.2024012
  • Reader Comments
  • © 2022 the Author(s), licensee AIMS Press. This is an open access article distributed under the terms of the Creative Commons Attribution License (http://creativecommons.org/licenses/by/4.0)
通讯作者: 陈斌, bchen63@163.com
  • 1. 

    沈阳化工大学材料科学与工程学院 沈阳 110142

  1. 本站搜索
  2. 百度学术搜索
  3. 万方数据库搜索
  4. CNKI搜索

Metrics

Article views(3694) PDF downloads(153) Cited by(1)

Figures and Tables

Figures(8)  /  Tables(1)

/

DownLoad:  Full-Size Img  PowerPoint
Return
Return

Catalog