Mridula Prakash Menon
a,
R. Selvakumar
*a,
Palaniswamy Suresh kumar
*b and
Seeram Ramakrishna
*c
aNanobiotechnology Laboratory, PSG Institute of Advanced Studies, Coimbatore, India-641004. E-mail: selvabiotech@gmail.com
bEnvironmental & Water Technology Centre of Innovation (EWTCOI), Ngee Ann Polytechnic, Singapore-599489. E-mail: sureshinphy@yahoo.com
cCenter for Nanofibers and Nanotechnology, Department of Mechanical Engineering, National University of Singapore, Singapore 117576. E-mail: seeram@nus.edu.sg
First published on 4th September 2017
Cellulose is a natural biopolymer that is abundantly available in plant cell walls and is secreted in its pure forms by many bacteria. Due to their unique features cellulose materials are considered as efficient replacements for conventional polymers. Cellulose nanofibers (CNF) have attracted wide interest due to their nano size, ease of preparation, low cost, tuneable surface properties and enhanced mechanical properties. However, the efficiency of CNF depends on the extraction method employed from its source and their features vary from source to source. Hence, there is a need to understand the specificity of CNF extraction from its source in order to obtain highly efficient CNF with maximum potential. CNF has been extracted from plant sources using physical, chemical and enzymatic methods. Although plant derived CNF possess excellent features, the involvement of chemicals and complexity in extraction process limits their usage. Bacterial CNF overcome this limitation through its extracellular secretion which makes extraction easy. CNF is also extracted from various marine filamentous algae. The percentage of CNF obtained from algal sources is less compared to plants and bacterial sources. CNF finds wide variety of applications such as drug carriers, tissue regenerating scaffolds, water purifying membranes, electrodes, supercapacitors, fluorescent probes and flexible electronics. In this review, various extraction techniques of CNF from different plant and bacterial sources are discussed critically with special emphasis on CNF based composites.
The properties of CNF such as purity, biocompatibility, crystallinity, wettability and surface tuneable structure have intense effect on various environmental applications. Biocompatibility of CNF is an important property that makes them highly suitable for various biomedical applications especially in scaffold development for tissue engineering. This is also an important property for its environmental applications.18 As filtration system or membranes for water purification, the CNF should not degrade and release toxic materials that make the treated water unfit for human consumption. Highly pure CNFs are important in environmental aspect. This is due to the fact that, increase in CNF purity enhances the thermal stability of the fibers. This is especially important in applications such as sensor fabrication and catalytic decomposition of various pollutants in waste water remediation where thermal stability of CNFs is highly demanded. In catalytic decomposition, the CNF acts as catalyst and prevent the aggregation of nanoparticles such as TiO2, Au and CuO that are introduced along with CNF for decomposing the pollutants. High purity of CNFs also improves the crystallinity of the nanofibers. This enhances the compactness of the CNF structure thereby maintaining their integrity. Highly crystalline nature increases the stability of the CNF structure. When combined with other materials having low crystallinity such as PVA, PLA etc., CNF imparts stiffness and high strength to the nanocomposite in addition to the native properties of the added materials.19,20 The high crystallinity observed in CNF also enhances their sorption property towards various volatile compounds from water and air. Thus, CNF based adsorbents can be used in the remediation of air and water pollution. Besides this, the sorption ability of CNF can also be utilised in sensors, catalysis and molecular level compound separation applications. CNF can accommodate a wide variety of guest nanoparticles such as Au, Ag, Pb, Ni, TiO2, CuO, SiO2 etc. in its structure. This is due to their high mechanical stability, intact crystalline structure, surface area and porosity. An important feature of CNFs is the high concentration of reactive –OH groups present on their surface that helps in CNF modification. These OH groups present on the cellulose surface crosslinks with quaternary ammonium compounds forming quaternary amines. This process is called quaternization. Through this process, cationic groups are introduced on the CNF surface to improve the adsorption of anions from polluted water sources.21 Apart from being used as ion exchange resins for water purification, the tuneable surface property of CNFs is also exploited in the fabrication of anti-bacterial water filters, energy devices and sensor applications. For example, CNF–AgNp based water filters prevents biofouling of the membrane and improves the life of the filter used.22 The high wettability of CNFs is used in various environmental applications such as water purification, development of absorbents for oil–water separation from oil-spills, anti-fouling coatings etc. The wettability of CNF plays an important role in water and oil separation. While conventional methods have drawbacks of ineffectiveness, high demand of chemicals and energy, CNF based adsorbents (sponges and filters) are effective and efficient alternatives. The CNF adsorbents allow selective permeation of either oil/water and omit the other compound. CNF based environmental friendly anti-fouling coatings has been developed to protect the surfaces of marine vessels, environmental sensors, water treatment plants etc. The CNF coatings due to high wettability prevent the attachment and growth of the microbial flora on the surfaces.
The CNF's can be prepared using physical, chemical, biological and oxidation methods.23 In chemical methods, cellulosic nanofibers are prepared through acid digestion, where amorphous area of fibers is destroyed to yield nanocrystalline nanofibers.24 During physical methods, the wood pulps are ground at high rpm, subjected to high intensity ultrasonic treatment, mechanical nanofibrillation25 to obtain nanofibers of nanometer diameter.26 In case of biological treatments, cellulosic materials are treated with cellulolytic enzymes like cellulase that cleave the fiber structures to simpler ones.15,26 Since biological treatment takes more time, they are often coupled with mechanical/chemical methods to reduce the process time and get better CNF.23 Better yield of CNF has been obtained through oxidation of CNFs mediated through 2,2,6,6-tetrame-thylpiperidine-1-oxyl radical.27 The exposure of such oxidised fibers to mechanical treatment results in easier defibrillation due to the generation of negative charges that repels the microfibrils against each other inside the cell wall.27 The main purpose of the oxidation process is to make the secondary cell wall accessible to mechanical treatment by loosening the primary cell wall. Besides, the water retention value (WRV) of the CNF enhances during the oxidation process and this hydration results in swelling of the fibers thereby making the process of defibrillation easier during mechanical treatment.
Recently cellulose isolated and purified from various agriculture sources have been electrospun to get CNF of various diameters.28 However the challenges like solubility of cellulosic biopolymer in conventional solvent system and its properties to aggregate and form gel always leaves processing problems.29 Hence researchers have looked into extracellular/intracellular bacterial cellulose as alternative for easing the processing steps. Unlike plant cellulose, bacterial cellulose extraction does not need physical/chemical intervention. Eichhorn et al. reviewed various methods used for the preparation of CNF based nanocomposites.30 The authors briefly detailed different methods employed for the extraction of CNF from plants and bacterial sources. In their work, more emphasis was given on CNF based nanocomposites preparation and their applications.30 In another study, Chirayil et al. described the preparation of nanocellulose from various fibers of lignocellulosic origin. The review explains in detail various chemical and mechanical treatments employed for the extraction of nanocellulose from plant sources.31 Similarly, Wei et al. in 2014 critically reviewed the environmental applications of plants and bacteria derived nanocellulose based nanocomposites. The authors focused mainly on different forms of nanocellulose such as nanofibrillated cellulose, nanocrystalline cellulose etc.32 Although there are several reviews available on the CNF extraction from plants and bacterial sources, a consolidated and detailed CNF extraction procedures customised for individual plant and microbial sources, their modification and applications are not available till date. In this study, we have tried to critically review and present consolidated information on CNF extraction from individual plant (cotton, wood pulp, banana, corn and wheat straw, soy hulls and sea grasses) and microbial (bacteria and algae) sources. The review also sheds light on the development of various CNF based composites. The authors also discussed in detail about CNF functionalization using various polymers, nanoparticles and carbon for numerous applications with special emphasis on water purification, biomedical and food packaging. Since the principle behind the methods involved in production of various CNF and its advances has been reviewed already by Nechyporchuk et al.33 and the information given in the review has not been included to avoid repeatability.
Johnson et al. reported that midseason exhibits algal cell wall with maximum strength cellulose fibers. CNF with high tensile strength (9 Mpa) has been obtained from Cladophora harvested during the mid of the season.43 The CNF extracted from filamentous marine green algae are highly crystalline in nature due to the presence of thick microfibrils of 10–30 nm width with high degree of orientation.44,45 Algal CNFs were reported to have high density (1.64 g cm−3) and less moisture absorption due to its high crystallinity. The high crystallinity in algal CNFs provides inertness that is responsible for its resistance to different chemical treatments.46 In a study, Hayashi et al. reported that the algal cellulose fibers are rich in Iα allomorph that are highly susceptible to enzymatic attack.47
CNFs derived from algae have several industrial and environmental significance. They are used as reinforcing agents in polyurethane foams. Such cellulose fiber reinforced materials exhibits tremendous improvement in strength, elastic modulus, biodegradability and thermal resistance. Cladophora extracted CNFs also find immense application as filter membrane materials in water purification. They are used in drug delivery purposes due to their inert nature and high surface area. The high drug loading capacity makes them suitable carriers for liquid and solid drug materials. The pores present in the algal CNFs protect the loaded drug molecules from unfavourable environment.
Albert et al. reported that Cladophora CNFs form highly stable and transparent gels by means of high speed sonication.48 Their strong rheological properties and robustness makes them suitable materials for food packaging, wound dressings and pharmaceutical applications. Cladophora CNF composites are reported as suitable materials for ion exchange resins and paper based battery fabrication. The insulating property of algal CNF is converted into conductive nature by coating the fibers with polymers such as polypyrrole (PPy) and polyaniline. Such composite algal CNFs are used for the fabrication of conductive paper based energy storage devices.49 Such a battery cell consisting of two electrodes, PPy/Cladophora CNF was reported by Nyström et al. The algal CNF based paper batter systems are cost effective and environmental friendly.49
Despite all the advantages, the CNF extraction from algal sources is less compared to plants and bacterial sources. Hence, this review focusses in depth on CNFs derived from plants and bacterial sources in the following sections.
Source | Cellulose content (%) | Reference |
---|---|---|
Rice husk | ||
Ahu variety | 94.2 | 87 |
Boro variety | 89.6 | 66 |
Banana | 16.62 | 60 |
Eucalyptus | 76 | 93 |
Wheat straw | 43 | 89 |
Rice straw | 71 | 130 |
Flax fibers | 72 | 153 |
Cotton fibers | 85–90 | 154 |
Corn silage | 32 | 155 |
Hemp fibers | 68 | 155 |
Sisal fibers | 65.5 | 156 |
Cassava bran | 16.71 | 27 |
Achirafibers | 19.1 | 50 |
Source of CNF | Method of preparation | Properties of the material developed | Ref. |
---|---|---|---|
Natural cellulose | |||
Pineapple peel juice, Gluconacetobacter swingsii sp. | Spray coating | Anti-microbial activity, enhanced spread factor (ξmax = +0.040C2 and −0.075C2) | 136 |
Rice husk from Oryza sativa | Hydrothermal approach, acid-alkali treatment, mechanical disruption | Size; 30–40 nm, innate fluorescence property, purity, crystallinity, thermostability | 87 |
Fibrous residues of Achira rhizomes | Acid hydrolysis, high pressure homogenisation | Size; 13.8–37.2 nm, high crystallinity (Icr = 57.5% and 69.8%), biodegradability, mechanical stability | 50 |
Banana peel | Chemical and enzymatic treatment using xylanase | Size; 10.9 nm and 7.6 nm, biodegradability, high crystallinity (Icr = 49.2%) | 64 |
Powder from poplar wood | Chemical pretreatment, high intensity ultrasonication | Size; 5–20 nm, high thermostability (335 °C), high crystallinity (69.34%) | 61 |
Poplar wood, culms of moso bamboo, rice straw, corn straw | Chemical treatment, ultrasonication, high pressure homogenisation | Size; 2–5 nm, high stability, ribbon like structure, high flexibility | 25 |
Tomato peels | Acidified sodium chlorite, chlorine free alkaline peroxide | Size; 260 ± 79 nm, high crystallinity (Icr = 69%) | 146 |
Posidonia oceanica balls and leaves | Chemical treatment, fibrillation | Size; 5–21 nm and 2–15 nm | 53 |
Cotton stalks | Chemical treatment, ultrasonication, mechanical treatment | Size; 3–15 nm, cost effective, biodegradable | 17 |
Waste pulp residues from paper industry | Etherification of pulp, mechanical disintegration | Size; 10–100 nm, high fibrillation, high thermostability (320 °C), high nitrate adsorption capacity (0.7 mmol g−1) | 92 |
Culinary banana peel | Chemical treatment, high intensity ultrasonication | High crystallinity (Icr = 63.64%), high thermal stability (295.33 °C) | 60 |
Eucalyptus pulp | TEMPO mediated oxidation | High water retention value (WRV = 8.3 g g−1), high modulus of rupture and modulus of elasticity (MOR = 35 MPa, MOE = 5160 MPa), high strength | 93 |
Canola straw | Nanowelding | Size; 53 ± 16 nm, high tensile strength (208 MPa), Young's modulus (20 GPa), superior transparency (76%), biodegradability | 147 |
Oil palm trunk, oil palm frond, okara | Alkaline treatment, electrospinning | Size; <500 nm, high fiber content (107.9%, 67.2%, 25.1%), high anti-oxidant activity (377.2%, 367.8%), superior mineral (Fe, Zn, Cu, Ca) binding activity, high emulsion activity (66.3 ± 0.6%, 6.6 ± 0.1%, 4.0 ± 0.1%) | 85 |
Bacterial cellulose (native) | |||
Acetobacter xylinum (ATCC10245) | Static culture | High cytochrome c adsorption efficiency (36.4 mg g−1), high protein binding efficiency, high selectivity | 148 |
Acetobacter xylinum X-2 | Static culture | Size; 68 ± 15 nm and 117 ± 15 nm, enhanced cell proliferation, high crystallinity (Icr = 88.3%), excellent hydrophilicity with contact angle 50 ± 2.4°, favourable thermal stability (290–370 °C), biocompatibility | 131 |
Gluconoacetobacter hansenii (strain NCIM 2529) | Static culture | BSA protein adsorption (>90%), high bioadsorption of Pb2+, enhances porosity and water holding capacity of soil | 115 |
Acetobacter xylinum FF-88 | Static culture obtained from (Fujicco Co., Ltd.) | High flexibility, high transparency (90%), low coefficient of thermal expansion (4 ppm K−1), low thermal expansion (0.05%), high mechanical properties | 115 |
Acetobacter xylinum ATCC-700178 | Static culture | Cost effective, biocompatibility, promotes migration of fibroblast cells, enhanced deposition of collagen, assist wound closure | 149 |
Acetobacter xylinum (subspecies-sucrofermentas BPR2001, Trade number 700178™) | Static culture | Enhanced porosity, high Young's modulus (8.25(1.14) MPa), biodegradable, enhanced migration of smooth muscle cells | 101 |
Synthetic cellulose (cellulose acetate) | |||
Commercially obtained | Electrospinning | Size; 10 μm, biocompatibility | 144 |
Commercially obtained | Electrospinning | Size; 0.59 ± 0.24 μm, cost effective, exhibited reverse phase behaviour | 145 |
Commercially obtained | Electrospinning | Size; 300 nm to 1.5 μm, high specific surface area (4.39 m 23 g−1) | 150 |
Commercially obtained | Electrospinning | Size; 450 nm, enhanced blending capacity with polymers, enhanced thermostability | 151 |
Commercially obtained | Electrospinning | Size; 4.6 ± 1.8 μm and 8.1 ± 2.2 μm, high fluid permeability (8.9 × 10−12 m2) | 152 |
The preparation method, source and the surface type of CNF has considerable impact on its thermal degradation properties.17,52 CNF prepared from white and coloured cotton by acid hydrolysis had a length of 85–225 nm and diameter of 6–18 nm. The CNF obtained from white and coloured cotton were 17 to 24 nm in size and retained its original colour in water even after acid extraction process. They also reported that the coloured CNF were thermally more stable at 180 °C than white under isothermal oxidizing conditions.52
The efficiency of TEMPO mediated oxidation for isolating uniform CNFs from cotton were reported by Soni et al.17 They demonstrated the production of four varieties of CNF from cotton stalks using various chemical approaches. Their method of extraction comprised of fine grinding and sieving of the cotton stalks obtained using 30–80 mesh sieves. The cotton was subjected to 16 h ethanol treatment for dewaxing followed by drying at 105 °C for 18 h. The obtained purified cotton stalks were then exposed to acid/alkaline treatment for extracting the cellulose in pure form. First, the cotton stalks were treated with 15% NaOH solution for 2 h at 23 °C. After collecting the resulting fibers, they were washed well using distilled water and subjected to acid hydrolysis by treating with 1 M HCl solution for 2 h at 80 °C. After filtering and washing the acid hydrolysed fibers, they were exposed to alkaline treatment again under the conditions mentioned above. Further, the fibers were bleached with sodium chlorite solution at 75 °C followed by filtration. Soni et al.17 demonstrated the extraction of CNFs from the prepared pulp using TEMPO mediated oxidation and acid hydrolysis using H2SO4. The advantages of including ultra-sonication at the end of chemical treatments in the extraction of CNFs were also shown in their study. In acid hydrolysis, the bleached cellulose pulp was treated with 64% H2SO4 for 50 min at 45 °C. To this aqueous solution of Na2CO3 was added and subjected to centrifugation for 20 min at 9000 rpm. The centrifugation was repeated thrice and the final CNFs obtained were redispersed in water. The TEMPO mediated oxidation method used for isolating cellulose fibers were similar to the protocol described by Bettaieb et al.53 Finally, the acid hydrolysed and TEMPO oxidised cellulose fibers were subjected to ultrasonication in ice water bath for 20 min.17 The CNF obtained were of 3 to 50 nm in size after subjecting to H2SO4 treatment and TEMPO oxidation process. The thermal degradation temperature was greater with untreated bleached pulp and H2SO4 neutralised CNF when compared to H2SO4 dialysed and TEMPO oxidized CNFs. The authors suggested that the CNFs containing free sulfate group in the frame was more thermally stable in the high temperature region than that containing sodium carboxylate group, especially in oxidative conditions. He et al.54 synthesized uniaxially aligned CNF (212–221 nm average dia) from cotton based cellulose nano crystals (CNC) using electrospinning process and tested it as scaffold for tissue engineering. For this purpose, a non cellulose degrading solvent system, lithium chloride/dimethyl acetamide (LiCl/DMAc) was used to electrospun non derivative cellulose onto a rotating steel drum collector. 20% loading of CNC into the cellulose solution increased the tensile strength and elastic modulus of electrospun cellulose/CNCs nanocomposite nanofibers by 101.7 and 171.6%, respectively in the fiber alignment direction. These nanocomposite nanofibers were found to be compatible for hDFCs (human dental follicle cells) attachment and proliferation. Li et al.55 prepared electrospun CNF from natural cotton cellulose having degree of polymerization above 10000. These cotton nanofibers were functionalized and made into composites by coating CeO2 nanoparticles on surface using hydrothermal reaction. This composite nanofiber was reported to possess excellent UV-shielding properties as compared to the natural cotton CNFs that can be used for medical, military, biological, and optoelectronic applications. Similarly, Liu et al.56 synthesized CdS nanoparticle-functionalized natural cotton cellulose electrospun nanofibers for photocatalytic applications.
The CNF surfaces were homogeneously dispersed with CdS nanoparticles having cubic zinc-blend structure. These heteromatrices CNF/CdS nanocomposite had excellent ability to photo degrade 99% of Rhodamine B (RhB) under visible light irradiation. The scanning electron microscopic images of various CNF synthesized by above mentioned authors are given in Fig. 1.
Fig. 1 SEM images of various types of CNF synthesized from cotton (a) natural electrospun CNF56 (b) aligned CNF (scale bar 1 μm)54 (c): CdS functionalized CNF33 (d): CeO2 functionalized CNF56 (e): CNF prepared by acid hydrolysis52 (adopted with permission). |
Fig. 2 TEM images of various types of CNF synthesized from banana (a): CNF after high intensity ultra-sonication;60 (b) CNF after chemical60 and (c) enzymatic treatment64 (scale bar: 2 μm) (adopted with permission). |
Chen et al.25 demonstrated efficient CNF extraction from different sources such as newspaper, corn straw, bamboo, wood and rice straw using three different mechanical nanofibrillation techniques namely, blender, ultrasonicator and high pressure homogenizer. All raw materials were collected, sieved and air-dried. The materials were dewaxed for 6 h in mixture of benzene:ethanol solution (2:1). Later, the samples were acidified multiple times for 1 h at 75 °C using sodium chlorite solution and subsequently treated with 3% KOH for 1 h at 90 °C. Another cycle of acidification and alkaline treatment using KOH was carried out under the same conditions as mentioned above to produce highly purified cellulose pulp. For nanofibrillation of cellulose pulp using a blender, the pulp was made into suspension using distilled water and agitated for 20 min using a domestic blender. In case of ultra-sonication, the cellulose suspension was subjected to high intensity ultra-sonication for 20 min at 1200 W. Similarly, during high pressure homogenisation, the purified cellulose suspension was first fibrillated using high intensity ultrasonicator for 5 min at 1000 W. These samples were then exposed to high pressure homogeniser for 20 min.25 The benefits of adopting a combination of chemical and mechanical treatment for the extraction of CNFs were reported by Sehaqui et al.92 In their study, cationic CNFs were isolated from pulp residues. The pulp material was beaten mechanically and allowed to react with aqueous NaOH to result in suspension. Under constant stirring, glycidyltrimethyl ammonium chloride was introduced to the suspension at 65 °C and the reaction was allowed to proceed for 8 h. It was then treated with HCl followed by filtration and washing. Finally, the resulting material was dispersed in water and agitated well for 10 min. This was later taken for high shear homogenisation for the disintegration of cellulose fibers at 1200 bar pressure.92 Similarly, Theng et al.93 demonstrated the production of CNFs from Eucalyptus pulp and corn biomass using TEMPO mediated oxidation. The corn pulp production comprised of chopping the corn biomass and sieving those using 10 mm mesh sieve. They were then boiled in a digester for 15 min at 160 °C using distilled water in ratio of 6:1. The obtained pulp was washed well and filtered using a Sprout-Waldron refiner. The resulting pulp material was vaccum dried and stored at RT. The TEMPO oxidation carried out were similar to the protocol followed by Soni et al.17 After TEMPO mediated oxidation, the resulting fibers were exposed to mechanical disintegration using high pressure homogeniser operating at 600 bar pressure for 5 min at 60–70 °C. This resulted in the formation of CNF gels.93
Mohite et al.95 reported the synthesis of bacterial cellulose from Gluconacetobacter hansenii NCIM 2529 using shaking culture method for various environmental applications. The organism was maintained in a medium containing yeast extract, mannitol, peptone and agar at a pH 5.5. For the production of cellulose, the organism was cultured in Hestrin and Schramn (HS) medium which was composed of citric acid monohydrate, glucose, peptone, yeast extract and Na2HPO4·12H2O at pH 5.0. Their production protocol involved inoculation of the organism in the HS medium and culturing them for 120 h at 30 °C at a speed of 120 rpm. After incubation, bacterial cellulose containing broth was obtained and filtered, resulting in bacterial cellulose beads which were further purified using 0.1 N NaOH for 30 min at 90 °C. This is followed by filtration and thorough washing using distilled water. The resulting cellulose was finally dried in the oven for 8 h at 50 °C. The obtained CNF was reported to be white, translucent and oval shaped spheres containing micro and nano sized fine fibers. The resulting fibers exhibited high elasticity, surface area, wettability and strength.95 Similar method was adopted by Fang et al.96 for the production of CNFs using G. xylinus that were genetically modified using Agrobacterium sp. ATCC31749. The genetically transformed organism was cultured in HS medium at 30 °C for 2.5 days with 0.1% additional cellulose. The bacterial cells obtained by high speed centrifugation was washed thoroughly using concentrated glycerol and was further maintained at 80 °C. This method produced CNFs that were highly crystalline in nature.96 Gonçalves et al.97 reported the production of bacterial CNF using static culture technique. In this work, bacterial CNF were produced from G. xylinus ATCC 53582. The organism was cultured for 30 days in HS medium. The bacterial cellulose sheets produced were purified using 0.1 N NaOH. After thorough washing using distilled water, the cellulose sheets were cut in to appropriate sizes and dried at 50 °C for 8 h. Biocompatible, highly porous, ultrafine CNFs were produced using this technique.98 Similarly, Quero et al.98 reported the production of bacterial CNF gel using static culture. In their study, G. xylinum 13693 was cultured in the HS medium for 14 days at 27 °C during which highly fibrous cellulose gel was formed. The gel was then squeezed in sterile environment to produce suspension of cells. To the main culture medium, the prepared cell suspension was inoculated and maintained for 14 days. The formed bacterial cellulose fibrous structure was then purified using NaOH and distilled water. In order to remove the water content completely from the produced cellulose network, their group adopted the method of hot pressing at 120 °C for 4 min.98 Apart from cellulose gels, mats of bacterial CNFs were also produced using static culturing technique. For instance, Olsson et al.99 developed a protocol for the synthesis of bacterial cellulose mats containing microfibers and nanofibers using G. xylinus (ATCC 23767). The procedure comprised of initial inoculation of the bacteria in 2 mL culture medium to produce initial suspension containing cellulose. After 3 days, the cellulose suspension obtained was used as the inoculum for second cycle of culturing in higher volume of growth medium. This cycle was repeated with higher volumes of culture medium until final inoculation in 20 L of medium. Pure cellulose mat generation was observed after 2 days of final inoculation in the medium while a fully grown cellulose mat was harvested by the 7th day. The obtained mats were further purified by boiling in NaOH solution and washing with distilled water. The water content was completely removed by compressing the mats into thin sheets after which it was stirred continuously at 60 °C for 72 h in aqueous H2SO4. This step completely dissolved the cellulose in the solution. To obtain CNF suspension, the acid dissolved cellulose suspension was subjected to 3 cycles of centrifugation under isothermal conditions at 24000 rpm. The final cellulose pellet obtained was redispersed in distilled water or appropriate solvent using high shear mixer for 5 min.99
In another study, Lee et al.100 reported the extraction of bacterial CNFs from coconut gel using Acetobacter sp. The synthesis protocol comprised thorough blending of the gel contents using a high speed blender after they were washed carefully using deionised water. The contents were then subjected to high speed homogenisation at 20000 rpm followed by centrifugation at 14000g. The purification of bacterial CNFs were then carried out by boiling the water dispersed cellulose content in NaOH for 20 min. A final centrifugation step was carried out to obtain highly homogenous bacterial CNFs. This procedure resulted in the formation of nanofibers of 50 nm size.100 Acetobacter xylinum derived bacterial CNF hydrogel was produced by Bäckdahl et al.101 for the synthesis of highly porous tissue engineering scaffold. In his work, sub species of A. xylinum sucrofermentas BPR2001 was used as the source of CNF. Corn steep liquid media was used as both culture and production medium.
Composite composition | Source of CNF | Method of preparation | Properties of the material developed | Ref. |
---|---|---|---|---|
Modified cellulose composites | ||||
Anthocyanins from B. oleracea L, cellulose acetate | Commercially obtained | Electrospinning | Size; 228 ± 118 nm, high stability at −50 °C, 100 °C and RT, pH responsiveness (visual colour differences) at pH 7–8 | 157 |
Cellulose acetate, polyamides b, poly vinyl acetate, poly acrylonitrile | Commercially obtained | Electrospinning | Moderate filtration efficiency | 158 |
Cellulose acetate, poly hydroxyl butyrate | Commercially obtained | Electrospinning | Size; 80–680 nm, high porosity (81 ± 2.1% to 85 ± 2.6%), high tensile strength (5.05 ± 0.52 MPa), high yield strength (4.6 ± 0.82 MPa), biodegradability, high osteoblast compatibility | 159 |
Cellulose acetate, poly vinyl alcohol | Commercially obtained | Electrospinning | Size; 251–368 nm, high tensile strength (9.8 ± 1 MPa), high entrapment efficiency (64.96 ± 3.14%), high permeation of capsaicin through skin model (shed snake skin), moderate human foreskin fibroblast (NHF) compatibility | 135 |
Cellulose acetate, polyacrylonitrile | Commercially obtained | Electrospinning | Excellent flexibility, enhanced mechanical strength | 160 |
Cellulose acetate, chitosan, oxolane-2,5-dione, furan-2,5-dione, furan-2,5-dione | Commercially obtained | Electrospinning | High metal adsorption capacity (221 μg L−1-lead) | 161 |
Cellulose acetate, carbon | Commercially obtained | Electrospinning | Size; 0.5–1.5 μm, hydrophilicity, highly amorphous nature, high specific surface area (25 m2 g−1), moderate electrical conductivity (6.3 S cm−1), high specific capacitance (20.9 F g−1) | 162 |
Cellulose acetate, (AgNP), (RuNP) | Commercially obtained | Electrospinning, wet reduction method | Size; 325 ± 2.0 nm, high catalytic activity, high selectivity in oxidation of benzyl alcohol (100%), high stability and reusability | 108 |
Carboxy-methyl cellulose, cellulose acetate, silver (AgNP) | Commercially obtained | Electrospinning | Size; 370 ± 174 nm and 410 ± 195 nm, high stability, selectivity, biocompatibility, high electrical conductivity, lower detection limit (1.64 μm) | 106 |
1,4-Dihydroxyanthraquinone (1,4-DHAQ), cellulose acetate | Commercially obtained | Electrospinning | High selectivity and sensitivity in detecting Cu2+, high reusability, favourable detection range of Cu2+ (2.5 × 10−9 to 3.75 × 10−8 M), lower detection range of Cr3+ (2.5 × 10−9 to 2.5 × 10−8 M) | 163 |
Oxolane-2,5-dione, cellulose acetate | Commercially obtained | Electrospinning | Size; 384.86 nm, high surface area (13.68 m2 g−1), reusability, high adsorption capacities (1.0–2.91 mmol g−1), cost effective | 127 |
Hydroxyapatite (HAp), cellulose triacetate | Commercially obtained | Electrospinning | Size; 346 to 815 nm, high protein (BSA) adsorption capacity (18.39 mg g−1) | 109 |
Poly caprolactone, cellulose acetate | Commercially obtained | Co-electrospinning | Size; 700–850 nm and 300–550 nm, high mechanical strength, enhanced wicking rate | 164 |
Hydroxypropyl cellulose, PCL, sulfisoxazole–cyclodextrin complex | Commercially obtained | Electrospinning | Size; 90 ± 40 nm and 60 ± 25 nm, high conductivity, high viscosity | 134 |
Modified cellulose, poly vinyl alcohol | Commercially obtained | Electrospinning | Size; 117–500 nm, enhanced glass transition temperature (Tg = 15.6 °C), low crystallinity (52.10%), high mechanical properties | 132 |
Nanofibrillated cellulose, hydroxyl ethyl cellulose | Never-dried softwood sulphite pulp fibers | Enymatic treatment, mechanical disintegration | Size; 15 nm, enhanced ductility, moderate stress yield of 8 MPa, enhanced strength of 80–93 MPa, increased stiffness, low Young's modulus (0.8–1.3 GPa), low storage modulus (<60 MPa) | 65 |
Bacterial cellulose composites | ||||
Bacterial cellulose, polyethyleneimine | Commercially obtained | Flush coating and cross linking | Large surface area, high porosity, high regeneration capacity, high adsorption of Cu2+ (90.1 mg g−1) and Pb2+ (130 mg g−1) | 105 |
Bacterial cellulose, poly vinyl alcohol | Commercially obtained | — | Enhanced pore structure, enhanced heat resistance (209 °C), high Young's modulus (1.0 MPa), high tensile strength (4.73 MPa), enhanced compression modulus (0.87 MPa) | 133 |
Bacterial cellulose membranes, acrylate polymers | Gluconacetobacter sacchari | Conventional static culture technique, in situ atom transfer radical polymerization | High hydrophobicity (contact angle 134°), enhanced thermal stability (241–275 °C), high flexibility | 165 |
Carbon nanofiber, bacterial cellulose | Bacterial cellulose polypyrrole | Mechanical treatment, carbonization reaction | Excellent electrochemical performance, high reversible specific capacity (240 mA h g−1), enhanced rate performance (146.5 mA h g−1), high cycling stability (148.8 mA h g−1 over 400 cycles) | 104 |
Bacterial cellulose, silver (AgNP) | Acetobacter xylinum NUST5.2 | Conventional static culture | Size; 30 nm, high anti-bacterial (E. coli and S. aureus) activity (inhibition zone 32 mm), favourable crystallinity, high thermal stability (250–290 °C) | 107 |
Natural cellulose composites | ||||
Natural cellulose, high density poly ethylene | Needle leaf bleached kraft pulp (NBKP) | Mechanical disintegration, injection molding | High tensile strength (43.4 MPa), high Young's modulus (1.97 GPa), excellent mechanical strength | 11 |
Natural cellulose, poly lactic acid | Wheat straw | Chemi–mechanical treatment, high speed homogenisation | High crystallinity at high pressure condition, high viscosity | 166 |
Cellulose, starch | Rice straw | Chemo-mechanical method, film casting, salt leaching, freeze drying | Size; 40–90 nm, high chondrocyte compatibility, biodegradability | 88 |
Polyurethane, cellulose | Rachis of date palm tree (Phoenix dactylifera) | Mechanical treatment, high intensity homogenising, solvent exchange method | Size; 29 ± 9 nm, high degree of crystallinity (40.0%), moderate thermal stability (51 °C), high tensile strength | 167 |
Cellulose, hemicellulose | Spruce sulfite pulp (commercially obtained) | Enzyme treatment, mechanical disintegration, filtration, drying | Size; 190 nm, enhanced storage modulus (>20 GPa), high thermal stability (300 °C), favourable Young's modulus (33 MPa), moderate tensile strength (3 MPa), high work of fracture (560 kJ m−3) | 168 |
Cellulose, starch | Kenafbast fibers (Hibiscus cannabinus) | Solution casting | High tensile strength (38.0 ± 3 MPa), high Young's modulus (141.0 ± 35 MPa), moderate elongation at break (27 ± 4%), biodegradability | 169 |
Cellulose, polyester resin | Softwood (Pinus sp.) and hardwood (Eucalyptus sp.) | Mechanical treatment | Size; 70–90 nm, high thermal stability (374 °C), moderate crystallinity index (72.8%) | 170 |
Unsaturated polyester, cellulose | Never-dried wood pulp (Nordic Paper, Sweden) | Mechanical treatment, template-based processing approach | Size; 100–200 μm, enhanced storage modulus, thermal stability up to 60 °C, high glass transition temperature (Tg = 78 °C), high moisture sensitivity | 80 |
Cellulose, amylopectin | Spruce sulphite pulp (Nordic pulp and Paper, Sweden) | Enzyme degradation, mechanical treatment, disintegration using microfluidizer | Size; 68 nm, 361 nm, 186 nm, moderate Young's modulus (13.6 GPa), high yield strength (117 MPa), enhanced strength (221 MPa) | 171 |
Cellulose, polyacrylamide | Fibrous cellulose powder-CF11 (commercially obtained) | Acid hydrolysis | High compressive stress (4.43 ± 0.06 kPa), hydrophilicity, high mechanical strength, favourable thermal stability (286–289 °C) | 160 |
Cellulose, polyaniline, carbon nanotubes | Bamboo powders from moso bamboo | Chemical treatment, in situ chemical polymerization | Size; 10 to 30 nm, flexible, foldable, high specific capacitance (249.7 F g−1) | 172 |
Cellulose, multi-walled carbon nanotubes, polyaniline | Bamboo powder from moso bamboo | Chemical treatment, solvent extraction, in situ polymerization | Size; 10–30 nm, high specific capacitance of 791.13 F g−1, high porosity, superior cycling stability, high redox reversibility | 143 |
Cellulose, carbon nanotubes, TiO2 nanotubes | Bamboo cellulose tissues | Mechanical treatment | Size; 10–30 nm, high porosity, high mechanical strength, superior discharge capacity (62.5 mF cm−2) | 103 |
Cellulose, cadmium sulphate (CdS) | Natural cotton | Electrospinning, chemical bath deposition | Size; 100 nm, amorphous nature, high photocatalytic activity | 56 |
Titanium dioxide (TiO2), cellulose, gold (Au), silver (Ag) | Eucalyptus pulp (USDA Forest Service-Forest products Laboratory (Madison, WI) | TEMPO mediated oxidation, mechanical treatment | Size; 4–20 nm, superior mechanical properties, reusability, high Young's modulus (17.7 ± 6.6 MPa), high tensile strength (70.7 ± 12.1 MPa), enhanced photocatalytic activity | 126 |
Cellulose, quaternary ammonium | Softwood kraft pulp | Mechanical treatment | Size; 10–40 nm, high porosity, high reusability (84.9% after 4 cycles of adsorption) | 128 |
Others | ||||
Polyethylene-b-poly(ethylene glycol), cellulose | Commercially obtained | Spray drying, surface adsorption, extrusion | High tensile modulus | 173 |
Cellulose, poly vinyl alcohol | Micro crystalline cellulose (commercially obtained) | Acid hydrolysis | High water resistance, enhanced thermal stability (100 °C), size; 10–65 nm | 174 |
Cellulose, poly lactic acid | Commercially obtained | Solvent casting | Size; 28 ± 10 nm, high thermal stability (156.3 °C), high tensile strength (33.1 MPa), high elastic modulus (188.9%) | 175 |
Cellulose, poly(lactic acid) | Nano Novin polymer co. (Iran) | Solution casting method | Size; 21 nm, high crystallinity (72%), high thermal stability (260.5 °C), high maximum degradation temperature (290.8 °C) | 176 |
Cellulose, starch, poly vinyl alcohol | Microcrystalline cellulose (commercially obtained) | Acid treatment, solution casting | Size; 20–35 nm, excellent mechanical properties, high strength (19.5 MPa), high stiffness (1199 MPa) | 141 |
Polyethylene oxide, cellulose nanocrystal | Microcrystalline cellulose (commercially obtained) | Acid hydrolysis, high pressure homogenisation, electrospinning | Size; 149 ± 49 nm, high Young's modulus (37.9 ± 0.6 MPa), high glass transition temperature, enhanced elongation at break (200 ± 17%) | 177 |
Cellulose, copper (Cu2+) | Cellulose sludge (commercially obtained) | Mechanical treatment, TEMPO mediated oxidation | Size; 15–40 nm, enhanced wettability, hydrophilicity, high Cu2+ adsorption capacity (75 mg g−1) | 124 |
Fig. 4 SEM images of various nanocomposites made of bacterial cellulose (a) commercial BC/polyethylenimine nanofibers adsorbed with cu2+ (ref. 105) (b) cross sectional image of PMMA grafted on BC nanofibers obtained from Gluconacetobacter sacchari106 (c) Acetobacter xylinum produced CNF coated with calcium phosphate107 (d) cytochrome C coated CNF processed from A. xylinum (ATCC 10245)108 (e) commercially obtained bacterial cellulose template synthesized carbon nanofiber104 (f) lecithin immobilized BC produced by A. xylinum X-2 (ref. 109) (all images were reproduced with permission). |
Fig. 5 SEM images of various nanocomposites delivered using plant CNF (a) softwood derived CNF and PLA blend110 (b) core shell nanofiber obtained by blending spruce sulphite pulp derived CNF and amylopectin (c) soft wood sulphite pulp derived nanofibrillated cellulose–HEC composite119 (d) palm tree ranchis processed CNF and polyurethane blend172 (e) Core–shell image of hemicellulose and spruce sulphite pulp extracted CNF blend171 (f) Pinus sp. and Eucalyptus sp. extracted cellulose nanofiber–polyester blend173 (g) composite obtained from 1-butyl-3-methylimidazolium chloride (BMIMCl) and canola straw derived CNF174 (all images were reproduced with permission). |
The CNF composites has been prepared using in situ chemical polymerization technique, oxidative polymerization, freeze drying with in situ polymerization102 and hydrothermal technique. Combination of plant derived CNF/carbon nanotubes/PANI and CNF/carbon nanotubes/TiO2 resulted in fibers with diameters of 10–30 nm while bacterial cellulose/carbon nanotubes resulted in fibers with 30–60 nm diameter. Association of CNF with fluorophores has been reported by Wang et al.105 where CNF/1,4-dihydroxyanthraquinone (1,4-DHAQ) composite has been employed for effectively detecting Cu2+ and Cr3+ in contaminated water.105
Fig. 6 Nanocomposites obtained using modified CNF (a) SEM image of cellulose acetate/1,4-DHAQ/CA nanofiber film (insert-high magnification image of cellulose acetate/1,4-DHAQ/CA nanofiber)175 (b) cellulose actetate–poly hydroxybutyrate blended nanofibers180 (c) hydroxyapatite decorated cellulose triacetate nanofibers179 (d) cellulose acetate nanofibers decorated with AgNP178 (e) cellulose actetate–PCL blended nanofibers after deacetylation181 (f) polyamide layer coated on PAN/cellulose acetate nanofibers (inset (10000×) image of polyamide surface)182 (all images were obtained with permission). |
In another study, Snyder et al.126 showed the potential of Eucalyptus pulp derived CNF doped with TiO2, Au and Ag particles in effective removal of organic compound, methylene blue from contaminated water source. They demonstrated that the photocatalytic activity of TiO2–CNF enhanced with the surface functionalization of Au and Ag particles in the presence of simulated sunlight.117 Cellulose acetate nanofibers modified using oxolane-2,5-dione has also been reported as excellent adsorbents of heavy metal ions such as lead and cadmium from contaminated water sources by Stephen et al.127 The developed CNF composite exhibited high reusable capacity without compromising its adsorption efficiency.127 CNF based aerogels has also been successfully employed in decontamination of water. Xu He et al.128 demonstrated the efficiency of chemically crosslinked, highly porous CNF aerogels functionalised with ammonium in remediating Cr(IV) ions from waste water. They reported that 99% of Cr(IV) ions from 1 L of contaminated water was successfully remediated using 1 g of CNF aerogel.128 In another study, Sehaqui et al.92 used waste pulp derived CNF for efficient removal of PO43−, SO42−, F− and NO3− from polluted water source. They demonstrated the transformation of CNFs to cationic CNFs by the surface functionalization of quaternary ammonium. The developed CNF paper showed high potential towards nitrate removal (380 mg m−2) when compared to other anions present in the contaminated water.92 Similar to the plant derived and modified CNF, bacterial originated CNFs also acted as potential bioadsorbant agents in water purification. Bhavna, Mohite and Patil95 reported that cellulose obtained from Gluconacetobacter hansenii successfully removed heavy metal ions such as Pb2+, Cd2+ and Ni2+. They also showed the potential of bacterial CNF in removal of azo dyes resulting in clean environment.95 Similarly, Wang et al.105 reported the fabrication of Cu2+ and Pb2+ adsorbing biomembranes made of bacterial CNFs coated with polyethylenimine using flush coating technique for purification of waste water. The fabricated membrane exhibited superior adsorption and desorption capacity after acid treatment using ethylene diamine tetra acetic acid and better recycling ability. A unique feature of this biomembrane is reported to be their ability to adsorb Cu2+ ions, their subsequent reduction into copper nanoparticles which further catalyses the reduction of methylene blue dye from aqueous solutions.110 CNFs were also used to separate oil and organic contaminants from water. One such study was reported by Huazheng Sai et al.129 where CNFs derived from bacteria was used as oil adsorbents from water sources. They used a method in which the nanofiber was surface modified using trimethylchlorosilane to obtain CNFs with hydrophobicity. The resulting nanofibers exhibited well defined porous structure with high surface area and oil absorption ability of 185 g g−1.129
Modified CNFs also acted as suitable drug carriers. Hydrophobic drugs such as sulfisoxazole encapsulated hydroxy propyl-β-cyclodextrin incorporated hydroxy propyl CNFs were fabricated to develop sustainable drug delivery system.134 The release of sulfisoxazole from the developed nanofiber material was prolonged up to 720 min. High surface area, enhanced solubility of the drug, controlled drug delivery and biocompatibility makes them a potential choice as wound dressing material. Similarly, Opanasopit et al.135 reported the fabrication of transdermal patches containing cellulose acetate and PVA nanofibers incorporated with capsicum extract. The developed material showed high skin permeation while tested on shed snake skin as the model and superior cytocompatibility while studied on normal human foreskin fibroblast cells (NHF).135
CNF are also used as reinforcing agents in food packaging material. The applications of food packaging materials available commercially are limited due to its poor mechanical properties. Incorporation of CNF enhances the efficiency of the fabricated edible materials for packing the foods. The potential of CNFs as reinforcing agents in developing edible coatings for fruits and vegetables are reported by Azeredo et al.142 They tried to develop edible films of mango puree incorporated with CNFs. The presence of cellulose fibers are reported to enhance the mechanical properties such as tensile strength and elastic modulus of the fabricated film. The cellulose fibers also reduced the permeability of water vapour thereby ensuring high stability of the composite edible film produced.142
CNF | Cellulose nanofiber |
CNC | Cellulose nanocrystal |
hDFC | Human dental follicle cells |
RhB | Rhodamine B |
TFNC | Thin film nanofibrous composite |
DTPA | Diethylene triamine penta acetic acid |
TEMPO | 2,2,6,6-Tetramethylpiperidin-1-yl)oxy radical oxidation |
NaOH | Sodium hydroxide |
KOH | Potassium hydroxide |
FDP | Flat panel display |
DHAQ | Dihydroxy anthraquinone |
HAp | Hydroxyapatite |
AOBC | Amidoxime surface functionalised CNF |
MWCNT | Multi wall carbon nanotube |
This journal is © The Royal Society of Chemistry 2017 |