This study focuses on the extraction of nanocrystalline cellulose (NCC) from the dried stalk of Corchorus olitorius,commonly known as jute,using a combination of a microwave-assisted alkaline peroxide pulping process (AHP) and ultrasonication. Dried jute stalk powder was pretreated using sodium hydroxide under microwave irradiation for the removal of lignin. The partially delignified sample was bleached using 30% hydrogen peroxide solution. The resulting crude cellulose was hydrolyzed using ultrasonication in the presence of ionic liquid and sulfuric acid. The effect of hydrolyzing medium on the physicochemical characteristics of the extracted nanocellulose was investigated. The nanocrystalline cellulose (NCC) obtained after combined treatments was rod-like, with diameters of 10 to 15 nm and lengths of 92 to 105 nm. Fourier transform infrared spectroscopy (FTIR) and X-ray diffraction analysis (XRD) showed that some breakages of intramolecular hydrogen bonds and glycosidic bonds occurred during the hydrolysis reaction of pretreated biomass. Ultrasonication in the presence of an acid hydrolyzing medium most effectively accelerated these breakages in the long chain cellulose biopolymer, leading to the formation of nanocrystalline cellulose (NCC) with higher crystallinity.
Preparation and Characterization of Nanocrystalline Cellulose using Ultrasonication Combined with a Microwave-assisted Pretreatment Process
Zaira Z. Chowdhury* and Sharifah Bee Abd Hamid
This study focuses on the extraction of nanocrystalline cellulose (NCC) from the dried stalk of Corchorus olitorius,commonly known as jute, using a combination of a microwave-assisted alkaline peroxide pulping process (AHP) and ultrasonication. Dried jute stalk powder was pretreated using sodium hydroxide under microwave irradiation for the removal of lignin. The partially delignified sample was bleached using 30% hydrogen peroxide solution. The resulting crude cellulose was hydrolyzed using ultrasonication in the presence of ionic liquid and sulfuric acid. The effect of hydrolyzing medium on the physicochemical characteristics of the extracted nanocellulose was investigated. The nanocrystalline cellulose (NCC) obtained after combined treatments was rod-like, with diameters of 10 to 15 nm and lengths of 92 to 105 nm. Fourier transform infrared spectroscopy (FTIR) and X-ray diffraction analysis (XRD) showed that some breakages of intramolecular hydrogen bonds and glycosidic bonds occurred during the hydrolysis reaction of pretreated biomass. Ultrasonication in the presence of an acid hydrolyzing medium most effectively accelerated these breakages in the long chain cellulose biopolymer, leading to the formation of nanocrystalline cellulose (NCC) with higher crystallinity.
Keywords: Biomass; Nanocrystalline Cellulose (NCC); Ultrasonication; Hydrolysis; Alkaline peroxide pulping process (AHP)
Contact information: Nanotechnology and Catalysis Research Center (NANOCAT), University Malaya, Kuala Lumpur 50603, Malaysia;
* Corresponding author: email@example.com, firstname.lastname@example.org
The delignification of renewable biomass for the extraction of advanced materials such as micro- and nanodimensional cellulose has become an attractive arena of research (Kalia et al. 2014). Biomass substrate can provide cellulosic materials with distinctive physico-chemical properties with little impact on the environment (Wicklein and Salazar-Alvarez 2013; Xu et al. 2013; Hossain et al. 2014; Kengkhetkit and Amornsakchai 2014). Cellulose is the most abundantly available biopolymer and is primarily found in plant biomass, but it can also be obtained from some animals (e.g., tunicates), algae, and a few bacteria (Henriksson and Berglund 2007; Iwamoto et al. 2007). It is a kind of semi-crystalline polysaccharide consisting of β-D-glucopyranose units connected by β-1,4 glycosidic linkages (Chowdhury et al. 2014). Micro- (MCC) and nanocrystalline cellulose (NCC) usually exhibit unique properties, such as large surface area, high elastic modulus, high aspect ratio, and non-abrasive, non-toxic features with less thermal expansion. They are widely used as reinforcing agents in polymer nanocomposites (Klemm et al. 2011; Moon et al. 2011; Jiang et al. 2013a,b; Abdul Khalil et al. 2014). NCC is used to fabricate optically transparent films with excellent visible light transmittance (Fukuzumi et al. 2013). The versatile properties of nanofibrillated cellulose allow it to be used in medicine, tissue engineering scaffolds, catalysis, textiles, surface coatings, drug delivery, and food packaging (Deng et al. 2010; Das et al. 2011; Klemm et al. 2011; Sacui et al.2014).
The existence of hemicellulose and lignin in biomass substrate is intended to impart strength to the cell walls of plant residues and shield cellulose from chemical disintegration. Thus, the efficient pretreatment of lignocellulosic biomass must be addressed for delignification as well as the release of cellulosic content for ultimate transformation into nanocrystalline cellulose (NCC). The supra-molecular chain of cellulose contains a disordered amorphous domain, which is preferentially hydrolyzed by chemical treatment. However, the crystalline region of cellulose is rather more difficult to attack, as it is bonded by strong and complicated intra- and intermolecular hydrogen bonding. The extraction of cellulose from the lignocellulosic matrix and its digestion into nano-fibrillated cellulose is encumbered by numerous physiochemical, structural, and compositional aspects. Nanocellulose can be isolated by mechanical treatments, such as high-pressure homogenization (Nakagaito and Yano 2004; Stenstad et al. 2008), ultrasonication (Chen et al. 2011), cryocrushing (Chakraborty et al. 2005), microfluidization (Ferrer et al. 2012), and by chemical treatments such as TEMPO-mediated oxidation and acid and enzymatic hydrolysis (Sacui et al. 2014). Until recently, nano-structured cellulose has been synthesized from various types of biomass residue, such as rice straw (Jiang and Hsieh 2013b), mulberry barks (Li et al. 2009), sugarcane bagasse (Li et al. 2012), agricultural residues (Uma Maheswari et al. 2012), corncob (Silvério et al. 2013), cotton linters (Morais et al. 2013), mengkuang leaves (Sheltami et al. 2012), bamboo (Nguyen et al. 2013), and hemp and flax fiber (Mondragon et al. 2014).
Currently, pretreatment methods using microwave heating have gained attention. Basically, microwave irradiation can generate volumetric heating within a short timespan by initiating efficient internal heating through a combination of microwave energy with reactant molecules present in the reaction mixture (Kappe 2009). This provides rapid energy-efficient heating of the biomass substrate and can yield NCC within a short period of reaction time. Microwave-assisted acid hydrolysis was used to extract NCC from microcrystalline cellulose (MCC) (Kos et al.2014).The extraction process was very fast. Within 10 min, 38% NCC was extracted using 60% sulfuric acid at 70 oC temperature (Kos et al. 2013). Compared with microwave heating, conventional heating is relatively slow and inefficient (Yin 2012). It has been previously reported that microwave irradiation can increase organic reaction efficiency, have a severe impact on the ultrastructure of cellulose, and degrade the lignin and hemicellulose of biomass (Zhang and Zhao 2010; Binod et al. 2012). However, to improve NCC yield and dispersion, acid hydrolysis has been widely used (Lai and Idris 2013). Acid hydrolysis aids in the breaking of the disordered and amorphous region of cellulose, which eventually releases single and well-defined nano-fibrillated cellulose. The acid hydrolysis process has been extensively used to prepare nanocellulose from wood (Revol et al. 1992), sisal (Moran et al. 2008), bacterial cellulose (Araki and Kuga 2001; Roman and Winter 2004), wheat straw (Helbert et al. 1996), and tunicate cellulose (Favier et al. 1995). Ultrasonication improves the accessibility and reactivity of the cellulose with acid (Tang et al. 2005). Previously, nanocellulose has been extracted from wood using high-intensity ultrasonication combined with chemical pretreatments (Chen et al. 2011). Many researchers have applied ultrasonication after the acid hydrolysis of cellulose for better dispersion of the NCC product (Dujardin et al. 2003; Beck-Candanedo et al.2005). However, to the best of our knowledge, less attention has been paid to the delignification of dried stalk of Corchorus olitorius, usually known as jute stick powder by a microwave-assisted alkaline peroxide pulping process (AHP), thereby extracting nanocrystalline cellulose (NCC) through the ultrasound-assisted hydrolysis process.
The extraction of nano-fibrillated cellulose using an alkali pretreatment process and acid hydrolysis has been investigated extensively. Nevertheless, the industrial-scale application of concentrated acidic medium has several limitations, such as corrosion of the reaction unit, lower yield of cellulosic substrate, char formation without careful optimization of process parameters, and the recovery and recycling of acidic effluents with the successive handling of hazardous waste. Harsh conditions or an inappropriate hydrolyzing medium will result in further dissolution of the extracted cellulose to yield different types of organic compounds as a liquid fraction, rather than solid cellulosic substances (Hamid et al. 2014; Karim et al. 2014). Recently, a new type of solvent – ionic liquids (ILs) – has become extensively used for pretreatment and extraction of nanocellulose from biomass and microcrystalline cellulose due to its versatile properties (Man et al. 2011; Han et al. 2013). Ionic liquids are organic salts having an organic cation and an inorganic anion. ILs are often considered as “green solvents” as these do not form any toxic or explosive gases (Anderson et al. 2002). Compared to traditional solvents, they have high thermal stabilities, low melting points, and low flammability with non-volatility (Holm and Lassi 2011; Han et al. 2013). However, there is little information available on the effects of a combination of alkali pretreatment with chlorite-free peroxide pulping process using hydrogen peroxide (H2O2) for the delignification of jute stalk biomass. The crude cellulose thus obtained was hydrolyzed using acid (H2SO4) as well as ionic liquid ([EMIM]+Cl−) to extract nanocrystalline cellulose (NCC). The physicochemical characteristics of nanocellulose obtained after ultrasonication using different hydrolyzing mediums were studied. Field emission scanning electron microscope (FESEM) images, transmission electron microscopy (TEM), Fourier transform infrared (FT-IR) spectra, X-ray diffraction (XRD) patterns, and thermogravimetric analysis (TGA) of untreated, pretreated, bleached, and extracted nanocellulose were examined and analyzed to reveal the influence of microwave irradiation as well as ultrasonication on the structure and chemical composition of the starting biomass substrate.
The starting biomass sample of dried jute stalk (S-1) was commercially available from the Bangladesh Jute Research Institute. The jute stalks (S-1) were ground and sieved. The material was passed through a 100-mesh screen to remove large particles. The average particle size of the biomass sample was kept at approximately 0.8 to 1.0 mm. The ground jute stalk powder (S-1) was dried at 110 °C for 24 h and stored in a sealed container before initial characterization. Concentrated sulfuric acid (H2SO4-99% purity), the ionic liquid 1-ethyl 3-methyleimidazolium chloride ([EMIM]+Cl−), sodium hydroxide (NaOH), and hydrogen peroxide (H2O2) were purchased from Sigma Aldrich, Malaysia. The chemicals purchased were of analytical grade.
Pretreatment of biomass
The dried biomass sample was pretreated with 2.5 M NaOH under microwave irradiation, where the biomass to solvent ratio was kept at 1:30, i.e. 1 g of biomass was pretreated with 30 mL of 2.5 M NaOH solution. During microwave pretreatment, the power was kept at approximately 350 W. The sample was heated for 45 min at a temperature of approximately 90 °C. The slurry thus obtained was cooled to room temperature and filtered through Whatman filter paper No. 3. The pulp thus obtained as filter cake was washed with hot deionized water several times until the filtrate reached a neutral pH. The sample was oven-dried at 60 °C and sent for characterization. The starting raw biomass (S-1) and microwave-assisted alkali pretreated sample (S-2) was characterized using scanning electron microscope (SEM) and transmission electron microscope (TEM) analyses, FTIR spectroscopy, XRD, and thermogravimetric analysis (TGA). To ensure complete delignification, the alkali-pretreated sample (S-2) was bleached using 30% H2O2 for 4 h at a temperature of 55 °C. The bleaching process was performed by adding 1 g of pretreated sample (S-1) with 30 mL of 30% H2O2 solution. The resulting sample was repeatedly washed with hot deionized water, oven-dried at 60 °C, stored in an airtight container for further characterization, and labeled as S-3.
Hydrolysis of pulp
The bleached sample (S-3) was subjected to hydrolysis using 1 M 1-ethyl 3-methyleimidazolium chloride, [EMIM]+Cl− (S-4) and 1 M sulfuric acid, H2SO4 (S-5) using ultrasonication for 35 min, where the power was kept constant at 90 W at temperature 90 oC. At this stage, 1 g of bleached sample was (S-3) was mixed with 20 mL of hydrolyzing medium. Prepared NCC samples were freeze-dried and stored for further characterization.
Chemical composition analysis
The percentage of α-cellulose was determined by ASTM D1103-55T. The percentage of lignin and holocellulose was determined using ASTM D-1106-56 and ASTM D 1104-56. The difference between holocellulose and α-cellulose gives hemicellulose content of the sample. The moisture content was estimated using ASTM D4442-92.Triplicate tests were carried out and the average values are reported.
The changes in morphological features of acid-hydrolyzed nanocellulose (S-5) and ionic liquid-treated nanocellulose (S-4) were observed using a scanning electron microscope (SEM, Model Leo Supra 50VP Field Emission, UK). The sample after consecutive treatment of pulping and hydrolyzing along with the raw sample was placed on black carbon tape before capturing the image. The morphology of the ultrasonicated sample in the presence of different catalytic solvents was observed using an HR-TEM model JEOL JEM-2100F (Japan) field emission electron microscope with a voltage of 200 kV. The NCC samples were deposited from an aqueous dilute dispersion onto the surface of copper grids and allowed to dry in vacuum desiccator before analysis.
The changes in the chemical functional groups were verified using the infrared spectroscopy technique. FTIR spectra for the raw biomass and cellulosic samples were recorded using Bruker spectrometer model IFS 66V/S (USA). The test samples were prepared by mixing the sample with KBr at a fixed ratio to fabricate a translucent disc. The FT-IR spectra were recorded in the range of 400 to 4000 cm−1.
The crystalline structure of the samples was analyzed using X-ray diffraction (XRD, Burker AXSD8 Avance, Germany) at 40 kV and 40 mA using Cu-Kα radiation sources. A continuous 2 scan mode from 5 – 60 was applied for high degree scanning at step size of 0.02 and step time of 2s.
The percentage of crystallinity was calculated according to Eq. 1 (Terinte et al. 2011; Segal et al. 1959):
Here, C is the percentage of crystallinity, I002 is the maximum intensity of the 002 peak at 2θ = 22.5°, and Iam is the intensity at 2θ = 18.7°.
Thermogravimetric analysis coupled with a differential thermal analyzer (DTA) (Mettler Toledo Star SW901, Japan) was carried out to determine the thermal stability of the samples under a 10 mL/min nitrogen flow. In the TGA analysis, 5 mg of each sample was heated under a N2 flow at 1000 °C with a heating rate of 10 °C/min.
RESULTS AND DISCUSSION
Chemical Composition analysis
The chemical composition of the sample at different stages was determined, and results are listed in Table 1. The untreated sample showed the highest proportion of hemicellulose and lignin with the lowest percentages of α-cellulose. After the microwave assisted alkali pretreatment and bleaching, the proportion of α-cellulose increased whereas hemicellulose and lignin percentages were decreased. Ultrasonication in presence of ionic liquid and acid hydrolyzing medium effectively dissolved lignin and hemicellulose from the sample. During alkali treatment α-ether linkages between lignin and hemicellulose were disrupted (Xiao et al. 2001). After bleaching, only a trace amount of lignin was present inside the sample.
Table 1. Chemical Composition Analysis of Untreated jute stalk (S-1), Microwave-assisted alkaline-treated jute stalk (S-2), Bleached jute stalk (S-3), [EMIM]+Cl− treated jute stalk (S-4), and H2SO4 treated jute stalk (S-5)
The moisture content increased slightly after the successive pretreatment process. As the cellulosic content increased after the pretreatment process, the rate of moisture adsorption also increased. There are three free –OH groups in cellulose, and these enhance the rate of moisture adsorption (Cherian et al. 2010). During alkali pretreatment, swelling of fiber caused development of hydrophilic ionic groups over the surface, which promoted water absorption by the bleached sample (Deepa et al. 2011).
The yield percentages were decreasing with successive pretreatment steps (Table 1). This phenomenon was expected, as alkaline per oxide pulping process was reducing lignin and hemicellulose content of the fiber and making the fiber more susceptible to be disrupted by hydrolyzing medium. Ultrasonication in the presence of acid and ionic liquid medium hydrolyzed the amorphous region of cellulose up to a certain extent as well as some portion of cellulosic fragments were completely broken to yield soluble oligo- and mono-saccharides.
Cellulose fibers extracted after successive chemical treatments, along with untreated samples, were analyzed using FTIR spectroscopy to observe changes in the chemical structure of the biomass. The broad absorption peak at approximately 3394 to 3390 cm−1 appeared as a result of stretching of H-bonded -OH groups of the cellulose chain, whereas the band at 2900 to 2800 cm−1 can be ascribed to C-H stretching (Wang et al. 2007a; Chirayil et al. 2014). The most significant absorption bands observed in the FTIR spectra of all the samples near 1055 cm−1 can be assigned to the C–O–C stretching vibration of the pyranose ring and glycosidic ether linkages between the glucose units in cellulose, respectively (Alemdar and Sain 2008). The peak observed at 1500 to 1510 cm−1 for untreated biomass, alkali-treated samples, and bleached samples represents the aromatic ring vibration of lignin (Sun et al. 2005; Chen et al. 2011). However, the peak intensity decreased after alkali pretreatment and the peroxide bleaching process, reflecting the partial delignification of the sample. The peak in this region almost disappeared after the ultrasonication process using sulfuric acid and ionic liquid. The peaks observed near 1620 to 1650 cm−1 for all the samples can be attributed to -O-H bending vibration of adsorbed water (Mandal and Chakrabarti 2011). The band around 1069 to 1080 cm-1 represents C=C band vibration of aromatic ring, which was reduced after the treatment (Sun et al. 2005). The sharp bands ranging between 899 and 893 cm−1 have been attributed to the β-glycosidic linkage between the sugar units in cellulose (Sekkal et al. 1995).
The minor peaks appearing at around 1448, 1385, 1349, 1267, 1177, 1035, and 899 cm-1 are associated with the typical cellulosic bands inside the sample (Sun et al. 2005). During the microwave-assisted pretreatment process, the NaOH penetrates the lignocellulosic structure more efficiently. This initiates the disruption of some bands associated with lignin and hemicellulose. Basically, the alkali sodium hydroxide acts as a microwave absorber. Thus a uniform microwave heating process takes place, leading to changes in the biomass structure and composition to a greater extent. Similar observations were previously reported for the microwave-assisted alkaline pretreatment of oil palm trunk and empty fruit bunch (Lai and Idris 2013). Table 2 provides the list of major vibrational frequencies (cm-1) in the FTIR spectra of the sample prepared at different stages.
Table 2. Vibrational Frequencies in FTIR Spectra of Sample at Different Stages
SEM and TEM Analysis
The surface textural features of S-1, S-2, S-3, and S-4 samples were observed by SEM analysis and are illustrated in Fig. 1. The surface of the untreated sample was comparatively smooth because of the presence of an outer non-cellulosic layer composed of pectin, wax, lignin, and hemicellulose, which acted as cementing materials to hold the fibers in bundles (Fig. 1(a)). After microwave-assisted alkaline pretreatment of S-1, partial delignification occurred, and the surface became rough and uneven, with some folds (Fig. 1(b)).
After bleaching with H2O2, the fiber bundles were further separated into micro-fibrillated cellulose. Occasional pores were visible over the surface (Fig. 1(c)). During bleaching, further removal of amorphous materials (lignin, hemicellulose) from the inner matrix of the biomass substrate took place via depolymerization and defibrillation. The microfibrils were separated from each other (Abraham et al. 2011). Similar morphological change was previously reported for bleaching of steam exploded banana fiber (Deepa et al. 2015). The structure clearly reveals that successive treatment with microwave-assisted alkaline peroxide pulping process aids in hemicellulose and extractive removal with delignification of the sample. This observation was previously supported by our FTIR analysis.
Figures 1(d) and 1(e) show the surface of ultrasound-assisted [EMIM]+Cl− and H2SO4 hydrolyzed samples. After hydrolysis and drying, the sample tended to be self-assembled into micro-fibrillated fiber. This is attributed to the increase of strong inter-fibrillar attraction via the hydrogen bonding of –OH groups of cellulose during the drying process (Jiang and Hsieh 2013 a, b). The sample surface was further eroded by hydrolysis. The dimension of the fiber was reduced because of the removal of the amorphous region of cellulose. The erosion of hydrolyzed samples (S-4 and S-5) may be caused by the emission of heat and excited species during ultrasonication. The cavitation effect of ultrasonication forms microbubbles. The high-velocity movement of these microbubbles reduces cohesion between the microfibrils (Li et al. 2011).
Fig. 1. SEM images of (a) untreated jute stalk (S-1); (b) microwave-assisted alkaline-treated jute stalk (S-2); (c) bleached jute stalk (S-3); (d) ionic liquid ([EMIM]+Cl−) treated jute stalk (S-4); and (e) sulfuric acid (H2SO4) treated jute stalk (S-5)
Transmission electron microscopy images (TEM) were acquired after ultrasonication to observe the structures of the extracted cellulose samples in the presence of different hydrolyzing media. The fibers were overlapping each other due to evaporation of water and were forming large aggregates consisting of wire like cellulosic fibers. A number of partially individualized nano-fibers were attached with the large aggregates as well (Fig. 2(a)). The crude cellulose obtained after alkaline per oxide pulping process contains highly crystalline and amorphous domain. The inter- and intra-molecular hydrogen bonds need to be broken to obtain nanocellulose. Previous literature stated that interactions between –OH groups of cellulose and anion of ionic liquids played a crucial role in this process (Han et al. 2013). When delignified sample (S-3) was added with [EMIM]+Cl−, the ion pairs were dissociated to give [EMIM]+ cation and Cl− anion. The hydrogen and oxygen atom of –OH groups of cellulose would form electron donor-electron acceptor complexes with the cation and anion of the ionic liquid (Pinkert et al. 2009). The dissociated [EMIM]+Cl−could enter the space inside the polymeric chain of cellulose where the free Cl− could associate with hydroxyl proton of H-O—H bonds while positive [EMIM]+ could attack the oxygen of H-O–H bonds. This interaction would cause swelling of the fiber with separation of -OH groups of the different cellulose chain (Han et al. 2013; Holm and Lassi 2011). Inside the single cellulose chain, Cl− ion would interact with the carbon of β-1,4 glycosidic bonds and [EMIM]+ with its electron rich ᴫ system would attack oxygen atom of β-1,4 glycosidic bonds. This would disintegrate the hydrogen bonding between two cellulosic chains with disruption of β-1,4 glycosidic bonds within single cellulosic chain (Han et al. 2013). Thus depolymerization of crude cellulose took place to yield nanocrystalline cellulose. The cellulose fiber isolated after ultrasonication in the presence of [EMIM]+Cl− was comparatively long and fibrillated (Fig. 2(a)). The average length was 105 nm, and the average width was 12 to 15 nm. After ultrasonication in the presence of an acid, the sample became rod-like (Fig. 2(b)). The average length of the sample was 92 nm, and the average width was 10 to 12 nm. The number of individualized cellulose nano-crystals increased after acid hydrolysis. This reveals that the ultrasound-assisted acid hydrolysis process was efficient for the scission of long chain cellulose biopolymers.
Fig. 2. TEM images of (a) Ionic liquid ([EMIM]+Cl−) treated jute stalk (S-4); and (b) sulfuric acid (H2SO4) treated jute stalk (S-5)
It has been reported that bonding inside the cellulose polymer can be broken by ultrasonic cavitation. This process causes solvo-dynamic shear, which involves the nucleation, growth, and collapse of micro-bubbles inside the solution (Caruso et al. 2009). Some bubbles in a certain size range may suddenly collapse during ultrasonication. This would create shock waves, which can generate large amounts of mechanical and thermal energy inside the solution. Thus, the hydrolyzing solution comes in contact with the cellulose surface at a velocity of several hundred meters per second. This ensures morphological changes in cellulose by enhancing its hygroscopicity. This further facilitates easy penetration of the solvent (Cintas and Luche 1999; Tang et al. 2005; Li and Renneckar 2009; Moon et al. 2011). The violent collapse induces microjets over the surface of the cellulose resulting erosion of the surface to split the fiber along the axial direction. The impact of sonication can easily break the hydrogen bond inside the fiber matrix and gradually disintegrate the micron sized cellulose fibers into nanofibers (Tischer et al. 2010).
XRD studies of untreated jute stalk (S-1) along with cellulosic samples after treatment (S-2, S-3, S-4, and S-5) were conducted to investigate the crystalline behavior of these fibers, and results are illustrated in Fig. 3. All the diffractograms showed two peaks at approximately 2θ = 14.0° to 16.0° and 22.0° to 24.0°, which are thought to represent the typical cellulose I structure (Nishiyama et al. 2003). This indicated that the crystalline structure of cellulose was not completely changed during the alkaline per oxide pulping and ultrasonication treatment (Chen et al. 2011; Li et al. 2014). The peak at approximately 2θ = 14.0° to 16.0° is classified as a secondary peak for the amorphous region of cellulose, whereas the primary peak near 22.0° to 24.0° represents the crystalline region of cellulose (Liu et al. 2012).
The crystallinity of the sample was increased significantly when untreated jute stalk (S-1) was converted to nanocellulose (Table 3). After microwave-assisted alkali pretreatment and the bleaching process, the crystallinity index increased. The increase in the crystallinity index might be attributed to the delignification of the sample (Binod et al. 2012). Dissolution of the amorphous phase took place along with hemicellulose removal. Thus, the resulting nanocellulose after ultrasonication in the presence of ionic liquid and sulfuric acid (S-4 and S-5) further showed a higher crystallinity index. The untreated jute stalk had a crystallinity index of 55.36%, which after alkali pretreatment and bleaching became 63.89% and 72.44%, respectively. However, ultrasonication using H2SO4treatment provided NCC samples with a higher crystallinity index (88.32%) than [EMIM]+Cl− treated samples (83.42%) (Table 3).
Fig. 3. XRD Diffraction of (a) untreated jute stalk (S-1); (b) microwave-assisted alkali-pretreated jute stalk (S-2); (c) bleached jute stalk (S-3); (d) ionic liquid ([EMIM]+Cl−)-hydrolyzed jute stalk (S-4); and (e) sulfuric acid (H2SO4) hydrolyzed jute stalk (S-5)
The extent of increase of crystallinity in chemically treated sample compared to the untreated one can be attributed to the effective elimination of lignin and hemicellulose from the amorphous region of cellulose (Li et al. 2014).The intensity of the secondary peak after successive pretreatment displayed a certain proportion of reduction, indicating a disruption in the amorphous region.
NaOH solution under microwave irradiation effectively acts as an intra-crystalline swelling agent, which selectively penetrates and swells the amorphous domain of cellulose (Wang et al. 2007b). As a result, the sample was partially delignified. After bleaching, the microfibrils were separated further. Thus, the surface area and porosity of cellulose increased, which eventually facilitated the accessibility of hydrolyzing solvent during ultrasonication. This results in disintegration of long chain polymer of cellulose to yield nano dimensional cellulose with higher crystallinity. The increase in crystallinity can increase the tensile strength and stiffness of the cellulosic fiber owing to the highly ordered, compact molecular structure among the cellulose molecules. This can further enhance Young’s modulus along the longitudinal directions (Li et al. 2014). Thus it can be concluded that the combined application of microwave assisted alkaline per oxide pulping process with hydrolysis could be efficient to obtain nanocrystalline cellulose (NCC) which can be used as a better reinforcing agent in composite preparation.
The thermal stability of the cellulose biopolymer is a crucial aspect of its impending application as a reinforcing agent for the preparation of bionanocomposites. The thermal stability of a polymeric material is known to depend on physicochemical characteristics as well as on intermolecular interactions between the various monomer units (Maiti et al. 2013). The thermal stability of untreated jute stalk and extracted cellulose after two consecutive treatments was investigated using the thermogravimetric method. The thermal degradation curve for untreated samples shows several stages, indicating the presence of bio-macromolecules of lignin, hemicellulose, and cellulose that decompose at different temperatures.
Fig. 4(a). TGA spectra for untreated jute stalk (S-1); microwave-assisted alkali-treated jute stalk (S-2); bleached jute stalk (S-3); ionic liquid ([EMIM]+Cl−) treated jute stalk (S-4); and sulfuric acid (H2SO4) treated jute stalk (S-5)
Fig. 4(b). DTG spectra for untreated jute stalk (S-1); microwave-assisted alkali-treated jute stalk (S-2); bleached jute stalk (S-3); ionic liquid ([EMIM]+Cl−) treated jute stalk (S-4); and sulfuric acid (H2SO4) treated jute stalk (S-5)
The first degradation step at approximately 70 to 100 °C corresponds to the evaporation of chemisorbed water (weight loss 3.2% for S-1, 2.8% for S-2, 2.6% for S-3, 1.8% for S-4, and 1.4% for S-5). The second degradation step proceeds in the temperature range of 220 to 365 °C for all the samples. This is mostly from the thermal decomposition of hemicelluloses and some portion of lignin. The major decomposition step was observed at high temperatures of approximately 300 to 400 °C, which accounts for the pyrolysis of cellulose. The cellulosic component decomposes at this temperature. However, the decomposition of lignin is far more difficult because of the presence of phenyl groups. Thus lignin decomposition takes place throughout the whole temperature range, starting below 200 °C and up to 800 °C.
In the case of untreated jute stalk (S-1), alkali-treated jute stalk (S-2), bleached jute stalk (S-3), [EMIM]+Cl− treated samples (S-4), and H2SO4 treated samples (S-5), the peak temperatures corresponding to the degradation of cellulose were found to be 365, 363, 360, 358, and 353 °C, respectively. Thermal decomposition for both ionic liquid and acid-treated samples shifted to a lower temperature. This demonstrated the lower thermal stability of the extracted NCC samples resulting from the nano size of the sample and larger number of free ends of chains in the NCC sample (Li et al. 2011). Table 3 showed major decomposition temperature with crystallinity index and char residues for all the samples.
The char residues obtained for untreated sample was highest (16.78%). After successive treatment of alkalization and bleaching it was reduced. This is due to partial removal of lignin and hemicellulose from the biomass matrix. The amount of residues were further reduced for ionic liquid (S-4) and acid hydrolyzed sample (S-5), reflecting complete removal of lignin and hemicellulose from the starting biomass sample (S-1). Similar phenomenon was previously reported for preparation of nano cellulose from de-pectinated sugar beet pulp (Li et al. 2014) and sisal fiber (Deepa et al. 2015).
Table 3. Degradation Characteristics and Char Residues at Different Stages of Treatment
1. Nanocrystalline cellulose (NCC) with a high crystallinity index was successfully synthesized from dried jute stalk (S-1) using a novel method that combined a microwave-assisted pretreatment method with ultrasonication in the presence of various hydrolyzing mediums. The crystallinity index reached up to 88.32% and 83.42%, respectively for H2SO4 and [EMIM]+ Cl− hydrolysis process.
2. Microwave-assisted alkali pretreatment caused the partial delignification of jute stalk samples. A chlorite-free bleaching process using H2O2 further removed a substantial amount of lignin and the surface of the sample was eroded, leading to defibrillation. This provided more active sites for the penetration of the hydrolyzing medium during ultrasonication.
3. Thermogravimetric analysis of the NCC sample showed lower thermal stability compared with untreated jute stalk, alkali-treated samples, and bleached samples. This was caused by the smaller size and higher number of free ends of macromolecular chains of the cellulosic sample.
4. Alone, a microwave-assisted alkali pretreatment process and bleaching using H2O2 was not sufficient enough for the complete removal of lignin. Further ultrasonication in the presence of acid and ionic liquid was required to extract NCC samples with a higher crystallinity index.
5. In this research, a green and sustainable approach of using [EMIM]+ Cl− with traditional H2SO4 acid hydrolysis was compared to extract NCC sample from jute stalk. The yield percentage obtained using [EMIM]+ Cl− hydrolysis (48.33%) process was higher than the H2SO4 hydrolysis (42.98%) process.
The authors would like to thank BKP (BK054-2015) and High Impact Research (HIR F-000032) of University Malaya, Malaysia for their cordial support in completing this work.
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Article submitted: June 4, 2015; Peer review completed: July 30, 2015; Revised version received and accepted; November 21, 2015; Published: February 18, 2016.