Bacterial nanocellulose (BNC) has been drawing enormous attention because of its versatile properties. Herein, we shed light on the BNC production by a novel bacterial isolate (MD1) utilizing various agro-industrial wastes. Using 16S rRNA nucleotide sequences, the isolate was identified as Komagataeibacter saccharivorans MD1. For the first time, BNC synthesis by K. saccharivorans MD1 was investigated utilizing wastes of palm date, fig, and sugarcane molasses along with glucose on the Hestrin-Schramm (HS) medium as a control. After incubation for 168 h, the highest BNC yield was perceived on the molasses medium recording 3.9 g/L with an initial concentration of (v/v) 10%. The physicochemical characteristics of the BNC sheets were inspected adopting field-emission scanning electron microscope (FESEM), atomic force microscopy (AFM), X-ray diffraction (XRD), and Fourier transform infrared (FTIR) analysis. The FESEM characterization revealed no impact of the wastes on either fiber diameter or the branching scheme, whereas the AFM depicted a BNC film with minimal roughness was generated using date wastes. Furthermore, a high crystallinity index was estimated by XRD up to 94% for the date wastes-derived BNC, while the FTIR analyses exhibited very similar profiles for all BNC films. Additionally, mechanical characteristics and water holding capacity of the produced BNCs were studied. Our findings substantiated that expensive substrates could be exchanged by agro-industrial wastes for BNC production conserving its remarkable physical and microstructural properties.
In the last decades, bacterial nanocellulose (BNC) has earned increasing global interest because of its remarkable physical and chemical properties, including green processing, low production costs, elevated mechanical properties, hydrophilicity, excellent biocompatibility, and biodegradability1,2.
Certain gram-negative non-pathogenic bacterial genera like Rhizobium, Xanthococcus, Pseudomonas, Azotobacter, Aerobacter, and Alcaligenes were reported to produce nanocellulose extracellularly, but the most common BNC-producing strains belong to the genus Komagataeibacter (formerly Acetobacter or commonly acetic acid bacteria)1.
Bacteria produce the BNC through a process of dual coupled steps: polymerization and crystallization. In the bacterial cytoplasm, glucose residues polymerize to β-1,4 glucan linear chains where they are extracellularly secreted. The developed chains are crystallized to microfibrils, then certain numbers of microfibrils consolidate to materialize highly pure 3D porous network of entangled nanoribbons of 20–60 nm in width3.
Compared to plant cellulose, BNC is produced in a pure form; free of lignin, pectin, and hemicelluloses. BNC ultra-fine structure possesses much higher merits of crystallinity, higher liquid absorption capacity, higher degree of polymerization, higher specific surface area, and higher mechanical properties making it a superior choice to the plant cellulose in many applications3,4. Moreover, the readiness of BNC for modification renders it highly superior compared to cellulose of plant origin. BNC could be shaped during the fermentation period to devise tubes, spheres, or membranes according to the application demands2.
Another aspect is the abundance of hydroxyl groups in the BNC, which facilitates its functionalization or compositing with other reinforcing compounds that confer BNC with new physical properties1, such as antimicrobial activity5, electro-conductivity6, or even multifunctional BNC composites7. Thus, the application sectors of BNC are continuously broadening, including bioprocessing, biomedical and pharmaceutical applications, wastewater treatment8, electro-conductive materials, packaging9, and food industry10.
On the other hand, the overall production process of BNC still requires major improvement to be more competitive, primarily due to the low BNC productivity of the known strains and the use of fine and expensive culture medium constituents. It is worth pointing out that the culture medium comprises approximately 30% of the total BNC production cost11. Therefore, one of the main reported confrontations was to totally or partially replace the pricy medium components with new low-cost ones that could promote the BNC yield within short time periods12,13. Towards this aim, intensive studies have been conducted utilizing waste stream and agricultural wastes for obtaining high yields of BNC, demonstrating how the properties of the produced BNC might be altered according to the medium constituents, culture conditions and/or the BNC producer12,14.
Hence, we report on the exploration of a novel and high potent BNC-producing bacterial isolate, Komagataeibacter saccharivorans, which are able to utilize the hydrolysates of three cheap agro-industrial wastes (palm date fruits, fig fruits, and sugarcane molasses) for cost-effective BNC production. The impact of these treated wastes on the physical and structural properties of the produced BNC is investigated employing a series of characterization instruments. Gopu and Govindan15 isolated the strain Komagataeibacter saccharivorans BC1 and ascertained mannitol as the best carbon source for BNC production. To the best of our knowledge, the present study is the first report probing the BNC productivity using Komagataeibacter saccharivorans utilizing these wastes.
Results and Discussion
The global demands to upcycling wastes for producing value-added products become an imperative not only for the economic viewpoint, but also from the waste reduction perspective and the implementation of higher green standards to the agriculture and food processing industries.
Many agricultural and industrial wastes have been already investigated for the BNC production, including cashew tree residues16, dry olive mill residues17, konjac powder18, rice bark19, waste beer yeast20, oat hulls21, and coffee cherry husk22. However, there is still substantial interest to find out and utilize economical substrates that could promote the yield of BNC.
Egypt is the largest producer of palm date fruits over the world, and second largest fig producing country as well23. The processes of harvesting, packing, transporting, storing, and marketing of these fruits generate considerable amounts of unsold low-quality fruits, which are usually discarded as wastes. Being considered debris does not rule out their richness of nutritional contents, which can be exploited as substrates for synthesizing several unique and worthy microbial products; for instance, BNC14. On the other hand, molasses is a common by-product of the sugar industry, which was extensively studied as cheap carbon sources for BNC production as well24,25,26.
Isolation and identification of BNC-producing strain
In the current study, our isolation plan unraveled two BNC positive cultures; one was isolated from fermented beverages and designated as (MD1), while the other was purified from table vinegar remnant and denominated as (VB3). Further evaluations nominated the dominant isolate (MD1) to undergo advanced inspections as the highest BNC-producing isolate reached to 2.6 g/L. The isolate (MD1) underwent a set of morphological and physiological examinations to determine its phenotypical features as presented in Table S1. Furthermore, the FESEM analysis at a magnification of 30000 x illustrated the rod cells of isolate MD1 harboring the network structure of the synthesized BNC as shown in Fig. 1A. Moreover, the genotypic characterization of the isolate MD1 was performed by amplifying the 16S rRNA and the size of the obtained fragment was about 1500 bp. The 16S rRNA nucleotide sequences of 1294 bp were obtained using the 16S rRNA forward and reverse primers. The homologous sequences were retrieved via the Nucleotide Basic Local Alignment Search Tool (BLASTn)27 and the results exhibited 100% similarity to various Komagataeibacter saccharivorans strains such as Komagataeibacter saccharivorans LMG 1582 (NR_118189), and Komagataeibacter saccharivorans JCM 25121 (NR_113398). Accordingly, the isolate MD1 was identified as Komagataeibacter saccharivorans MD1, and deposited in The National Center for Biotechnology Information (NCBI) GenBank under the accession number KY584252 (https://www.ncbi.nlm.nih.gov/nuccore/KY584252). Figure 1B demonstrates the phylogenetic tree of the 16S rRNA including the position of Komagataeibacter saccharivorans MD1 compared to the available sequences on NCBI GenBank database.
Production of BNC on wastes
We could statically produce BNC by K. saccharivorans MD1 on (HS) media as a control along with the three media formulated by replacing the glucose in the (HS) with the extract of date fruit wastes (E-DFW), extract of fig fruit wastes (E-FFW), and the treated sugarcane molasses (T-SCM) as indicated in Fig. 2. This blueprint pinpoints the implemented methods in the current research to produce the BNC indicating the assimilation of sugars within the bacterial cells and the formulation of β-1,4 glucan chains to finally construct the microstructure of cellulose. Indeed, the BNCs generated on the three wastes primarily showed comparable morphological features to the control BNC, particularly after washing (Fig. 3).
Figure 4A depicts that after 168 h of bacterial cultures incubation, the treated molasses medium (M-HS) exhibited the highest BNC productivity yielding 3.9 g/L, followed by the medium complemented with the date extract (D-HS) recording 3.2 g/L. Both media enhanced the BNC production compared to the (HS) medium that yielded 2.6 g/L dry weight of BNC. Moreover, out of the four media, the (M-HS) exhibited the highest conversion ratio (α = 91%), which was higher with two points than the ratio shown by the (HS) media (α = 89%) that contains the more pricy fine D-glucose as a carbon source (Table 1).
The thermal-acidic pre-treatment was proposed to improve the properties of the molasses, raise its (glucose-fructose) contents per volume, and eliminate most of chemicals that might hinder the microbial growth or affect the product yield28,29. Bae and Shoda24 elucidated the role of thermal acidic pre-treatment of molasses in almost full degradation of the included sucrose to its initial precursors: glucose and fructose. They reported that cultivation of the strain Acetobacter xylinum BPR2001 on the pre-treated molasses augmented the BNC yield by 76%, comparing to the yield on crude molasses. Meanwhile, the strain Komagataeibacter rhaeticus yielded 4.01 g/L as a consequence of growing on a blend of glucose and crude sugarcane molasses as an ideal carbon source at concentrations of 30 and 20 g/L, in respective order26.
Rodrigues et al.30 reported the greatest BNC production, about 7.5 g/L, by the strain Komagataeibacter xylinus BPR 2001 after cultivation for 9 days on a mixture of sugarcane molasses (5.38%, m/v) and ethanol (1.38%, v/v).
Date fruit and date syrup revealed high contents of glucose and fructose, in addition to naturally existing minerals (Se, Cu, Ca, K, Mg, Mn, Zn)31,32. Besides being one of the main energy sources for the metabolic machinery, glucose is the building block of the cellulose polymer; therefore, D-glucose is the main constituent of most synthetic reported media for BNC production33,34,35. Additionally, a previous study pointed out that fructose represents an ideal carbon source for BNC production as glucose36. Accordingly, introducing both of them with high amounts might explain the higher BNC harvested from date wastes compared to the BNC production on (HS) medium that contains 20 g/L of initial glucose concentration. Furthermore, Keshk36 corroborated that the yield of BNC increased in the presence of mixed sugars comparing to the glucose as a sole carbon source.
The medium amended by fig extract (F-HS) presented the lowest initial sugar concentration (14 g/L), and BNC production in turn. However, in terms of sugar to BNC conversion yield Y (%), the (F-HS) medium exhibited the second highest BNC yield (Y = 7.8%), after the (HS) medium yield.
As can be observed in Fig. 4B, K. saccharivorans MD1 showed augmentation in BNC production until 120 h before the rate slows down at the last 48 h. Hence, we might presume that BNC generation rate reduces with the plummeting of nutrients, the accumulation of the organic acids, and other by-products in the culture. The produced floating nanocellulose pellicle itself might obstruct the medium aeriation that compensate the O2 consumed since the culture had been launched, and the nanocellulose mat secure oxygen demands exclusively for the cells entrapped in its matrix37. Accordingly, the cells beneath the nanocellulose mat turn out dormant, and they were quashed from participation in the BNC fabrication13. Throughout 168 h of incubation, the four cultures media demonstrated declining in pH rate profiles, and the pH values of the cultures (M-HS) and (D-HS) were dramatically decreased at the time end point pinpointing 3.8 and 4.1, respectively (Fig. 4C).
The pH profiles of the four cultures emphasized the significance of investigating the optimum initial carbon source concentration for the maximum BNC yield. Figure 4D elucidates how the elevated initial wastes concentrations influence BNC production.
The decrease in the initial concentrations of the date fruit extract and the treated molasses to (v/v) 5% was effective to elevate the BNC productivity to 3.5 and 5.5 g/L, respectively. On the other hand, the same proportion of the fig extract was not supportive for the BNC production, and the improved BNC productivity on fig extract showed with an initial concentration of (v/v) 20% recording 2.5 g/L, before the BNC productivity declined again at (v/v) 30% proportion.
Considering the sugar-content richness of the utilized date extract and the treated molasses comparing to the fig extract (Table 1), it is clearly recognized that BNC production depends linearly with the initial sugar concentration up to certain level, 5% for the date extract and molasses, and 20% for the fig extract, where an excess of sugar contents impairs the BNC production.
We suppose that the best BNC production is a compromise between the best sugar concentration and the resulted medium pH. For instance, acetic acid bacteria assimilate glucose monomers as building blocks to construct nanocellulose fibers, in addition to burn glucose units through various metabolic pathways to derive energy and keep proliferation. As a result of all these biochemical processes, gluconic acid is generated as the most abundant by-product. Therefore, the higher initial glucose concentration, the higher gluconic acid production, and its excess resulted in significant reduction of BNC productivity as the medium pH becomes extremely acidic38.
Microstructure by (FESEM) investigation
Many reports explained the influence of the culturing parameters such as the acting bacterial strain, temperature, incubation state, incubation time, or medium constituents on the properties of the produced BNC39,40,41,42,43. Recently, when studying non-conventional media in BNC production, it was found out that the chemical composition of the produced BNC was not much affected; however, the physical properties like water holding capacity, tensile, polymerization degree, and crystallinity index might be influenced by the utilized carbon source44. Thus, the relationship between BNC properties and medium carbon source has been drawled great attentions to get careful inspections as long as the produced BNC might be implemented in diverse applications16,45,46. In the current case, FESEM investigations for the four BNC fabrics were carried out. Figure 5 shows the typical tridimensional nanofibrous network distinguishing the BNC. Furthermore, FESEM analyses indicated no major variations could be observed in the dimensions of the nanofibers of the four produced BNCs, or the branching scheme of the fibrous network. The diameter of the nanofibers of the four produced BNCs scales in the range of 10–90 nm, almost in a similar manner.
We suppose that the inconsiderable impact of the utilized wastes on the microstructural and morphological features of the produced BNC nanofibers could be attributed to the efficient elaboration of the utilized extracts that made them effective substitution for D-glucose. Through growing of K. saccharivorans MD1 on the three media, (D-HS), (F-HS), and (M-HS), glucose and fructose are the predominant carbon sources, where they were assimilated by the cells of K. saccharivorans MD1 for cells propagation and to generate BNC simultaneously. The other constituents of the utilized extracts such as phytocompounds, antioxidants, and minerals may affect the physical properties of the produced BNC, but they seem to have mild or no impact on the diameter of the nanofibers or their branching scheme.
Water holding capacity and water release rate
Water holding capacity (WHC) and water release rate (WRR) are substantial physical respects for BNC pellicles, particularly when the BNC is intended for biomedical applications such as wound dressing and tissue engineering. BNC, which is a hydrogel, retains large amounts of water mainly because of its elevated porosity and surface area per mass unit47.
The WHC of the BNC films produced on (HS), (D-HS), (F-HS), and (M-HS) media were ascertained as depicted in Fig. 6A, where the BNC fabricated on the M-HS exerts the highest WHC, recording 104 g/g. The lowest water load was found by the F-HS product, recording 97.3 g/g. Both the BNCs of the HS and D-HS exhibited comparable water capacity, with 98.6 and 99.6 g/g, respectively. This behavior implies that the WHC profiles are in accordance with the FE-SEM inspection, and corroborate our assumption of the low impact of the utilized agro-industrial wastes on the size of fibers and pores or the fibrous branching scheme.
On the other hand, the WRRs of the four BNC products throughout 48 h configure the speed, by which, the water evaporates from the films. Figure 6B demonstrates that the BNCs produced on M-HS and D-HS has the lowest WRR, where they needed 44 h to completely evaporate the water content. Meanwhile, the BNC product of HS medium could retain water until 40 h, while no further water evaporation from the BNC of the F-HS after only 36 h was observed.
The ability of BNC to load water regarded mainly to the hydrogen bonds of the forming glucan chains. Rebelo et al.48 deduced a mathematical model to elucidate the BNC water evaporation process. They proposed that the “BNC drying reaction” takes place on two steps: evaporation of the surface water as a physical process depending on the temperature, humidity, and air velocity; then heat transfer and unbinding of internal water molecules because of the breakage of hydrogen bonds per time unit.
Surface topography by (AFM) analysis
Surface roughness is a crucial feature for validating BNC in many electronic devices49,50 and biomedical implementations51. The (AFM) in tapping mode was employed to study the topography of the surface area of 30 ×30 µm for the four BNC products (Fig. 7). Out of the four BNC fabrics, the highest (Rq) value was for the BNC produced on the control (HS) medium recording 0.67 µm. The BNC produced on (D-HS) formulation exhibited the smoothest surface morphology with Rq = 0.19 µm approximately less than one third of that of the control BNC product. Both BNC products of the (F-HS) and (M-HS) media showed approximate (Rq) values of 0.44 and 0.48 µm, respectively. Thus, the roughness of the four BNC products could be ordered as follows (higher roughness first): HS > M-HS > F-HS > D-HS. Fig. S1 and Table S1 correspondingly exhibit the results for the BNCs surface roughness.
Crystalline structure by XRD analysis
BNC is a semi-crystalline biopolymer mainly composed of cellulose I, that comprises Iα and Iβ polymorphs in certain proportions, which differ in correspondence to the production status43. In all cases, the Iα/Iβ ratio found to be non-correlated with the crystallinity index of any cellulose sample52.
The X-ray diffractograms of the BNCs produced on the four media indicated the emergence of three main peaks; d1, d2, and d3 as given in Fig. 8A. The peak d1 appeared at 2Ɵ = 14.66° ± 0.2° as an average of the peaks of the four BNC products, and assigned to (100) plane of Iα or to the plane (1–10) of Iβ. The peak d2 is detected at 2Ɵ = 16.7° ± 0.2°, and attributed to (010) plane of Iα or (110) plane of Iβ. The d3 at 2Ɵ = 22.4° ± 0.1°, and could be a contribution of (110) plane of Iα, the (200) plane of cellulose Iβ43.
The BNC produced on the (D-HS) medium revealed the highest CrI (94%), which was higher than that of the control (HS) medium (87%). The crystallinity index of the BNC produced on (F-HS) and (M-HS) were 81% and 84%, respectively. The estimated crystallite sizes (CrS) and inter-planar distances or d-spacing (d) for each peaking crystallite are illustrated in Table 2.
Interestingly, we observed some variations in the crystallite sizes of each BNC product proposing a direct impact of the media on the BNC crystals. The crystallite size of the BNC produced on the (D-HS) medium was the greatest (5.5 nm), while that produced on (F-HS) medium showed the smallest size among the four products, recording (2 nm), postulating that some chemical substances included within the fig waste extract could interfere the assembly of chains in the corresponding BNC crystallite.
FTIR profiles of the produced BNCs by K. saccharivorans MD1 on the media supplemented with the three wastes revealed identical chemical composition to the BNC control (Fig. 8B). As demonstrated in the four FTIR spectra, the wide peak around 3352 cm−1 is assigned to the O-H stretching, while the peak around 2900 cm−1 is related to C-H stretching53. The water bending vibrations peaked at 1639 cm−1, while the peaks around 1357 cm−1 indicate the C-H bending. Many peaks appeared between 1055-1049 cm−1 are corresponding to C-O stretching at C3; C-C stretching; and C-O stretching at C6. A band at 896 cm−1 is attributed to as C-O-C stretching at β (1,4) glycosidic linkage. Single peak of out of plan bending C-O-H appeared at 667 cm−1 54,55. The entire band assignments are detailed in Table 3. As a consequence of these measurements, it could be inferred that the production of BNC utilizing the selected three wastes showed no impact on their chemical features, which might play an important role over the application phase. The FTIR spectra of the four BNC products demonstrated no clues for existence of cellulose II, and the whole peaks came in complete accordance with the cellulose I profile as reported by Oh et al.56 suggesting that the hydrothermal alkaline washing protocol is mild enough not to convert cellulose I to cellulose II.
The BNC films produced on the media HS, D-HS, F-HS, and M-HS were characterized for their stress-strain performances. Table 4 summarizes the values of tensile (MPa), elongation at break (%), and Young’s modulus for the four BNC products. The BNC films generated on (D-HS) medium showed both the highest tensile and Young’s modulus with 57 ± 6 and 17 ± 4 MPa, respectively. Meanwhile, the BNC purified from the (HS) media came in the second order with tensile value of 42 ± 6 MPa, and Young’s modulus of 14 ± 3 MPa. Eventually, the BNC of the M-HS and F-HS showed comparable values for the both determinations.
In terms of ductility, the BNC film of the HS medium exhibited the highest ductility measured by elongation at break (4.3 ± 2.7%), followed by the film derived from M-HS (3.6 ± 1.8%); whereas, the elongation at break of films from D-HS and F-HS recorded 2.4 ± 1.1% and 1.7 ± 0.9%, respectively. The results presented a significant correspondence between the crystallinity of the BNC fibers from one side, and the tensile and Young’s modulus in the other side. This is in accordance with a previous investigation57, which compared the mechanical properties of the wet BNC, lyophilized BNC, and oven-dried BNC films produced by the strain Gluconacetobacter hansenii CGMCC 3917.
Utilizing various wastes as substrates for cultivating the BNC-producing strains will impact the physical properties of the produced BNC, where the mechanical properties for instance are substantial for exploiting BNC in food packaging and biomedical applications.
Our findings are encouraging and are consequently recommended to optimize the significant parameters for boosting BNC production by K. saccharivorans MD1. Moreover, some composites based on BNC could be developed, characterized, and nominated for adequate application.
We isolated and identified the strain Komagataeibacter saccharivorans MD1 as a novel BNC producer. Furthermore, we explored the potentiality of the pretreated date fruit wastes, fig fruit wastes, and sugarcane molasses as carbon sources for BNC biosynthesis. After 168 h of static incubation, the molasses medium (M-HS) achieved the highest BNC yield and the best substrate conversion ratio. Increasing the proportions of the carbon sources reduced the BNC production, whereas utilizing low concentrations of date wastes or molasses considerably increased the BNC yield. The four BNC products showed almost the same size of nanofibers and porosity degree under FESEM analyses, while their surface roughness varied greatly; where the (HS) product record the roughest surface, while the smoothest was the (D-HS) one. XRD diffraction revealed slight variations in crystallinity indices and crystallite sizes. However, the FTIR spectra of the four sheets show identical chemical profile assigned to cellulose I. Mechanical properties and water holding capacity revealed the great versatility of the produced BNCs, which confer them the feasibility to implement in diverse applications and manifold.
Screening and isolation of BNC producers
Eleven samples of garden flowers, rotten fruits, fermented foods, fermented beverage, and vinegar remnants were collected to isolate BNC producing strains. The production was carried out on Hestrin-Schramm33 (HS) medium consists of (g/L): D-glucose (20), peptone (5), yeast extract (5), sodium di-basic hydrogen phosphate (2.7), and citric acid (1.15). D-Glucose and citric acid were purchased from Fisher chemical; peptone, yeast extract and agar were purchased from Conda Lab; and the sodium di-basic hydrogen phosphate was provided from Sigma Aldrich and used as received. The 11 Erlenmeyer flasks were incubated at 28 °C for 10 days. The positive cultures that showed floating gel-like pellicles underwent purification procedures to isolate pure BNC-producing bacterial isolates for selecting the potent BNC producer.
Identification of the most potent bacterial isolate
A dominant bacterial isolate that showed highest BNC yield was identified based on the morphological and physiological characters58. Furthermore, the bacterial cells were examined within the entangled BNC via scanning the unprocessed BNC employing FESEM. Moreover, the identification was supported with the help of a molecular tool by sequencing the 16S rRNA gene nucleotides. The PCR reaction was carried out using the universal 16S rRNA primers: 27 F Mod (5′-AGR(AG)GTTTGATCM(AC)TGGCTCAG-3′) and 1492 R Mod (5′-GGY(CT)TACCTTGTTAYGACTT-3′). The thermal cycler was set out as follows: initial denaturation at 94 °C for 5 min followed by 30 cycles of 1 min at 94 °C for further denaturation, 1 min at 55 °C for annealing, and 2 min at 72 °C for extension, and the final extension step at 72 °C for 10 min59. The amplified 16S rRNA gene was purified and sequenced by GenoScreen Innovative Genomics Company (Lille, France) following the protocol of Sanger approach60. The obtained nucleotide sequences were compared with available sequences on the National Center for Biotechnology Information GenBank (NCBI GenBank) database employing BLASTn through Basic Local Alignment Search Tool (BLAST). The comparable sequences were retrieved and multiple sequence alignment was performed by ClastalW using MEGA software (V. 6.0). Then, the phylogenetic tree was constructed adopting the Neighbor-Joining tree method, which assessed by bootstrap analysis with a value of 50061,62.
Preparation of the wastes
Semi-dry date fruit (tamer) wastes (DFWs) and fig fruit wastes (FFWs) were collected from local markets at Alexandria governorate, while we obtained sugarcane molasses (SCM) from Al-Hawamdia Sugar Fabric., Giza, Egypt (https://www.siicegypt.com/). The seeds were excluded from date fruit wastes (DFW), while the fig fruit wastes (FFW) were first dried in a hot air oven at 70 °C for 36 h before advanced treatment.
Preparation of date and fig extracts was executed following the method described by El-Nagga & Abd El Tawab32 with minor amendments. Weights of 100 g of both the (DFWs) and (FFWs) were separately immersed in an equal volume of d-H2O for 2 h before transferring into another volume of d-H2O with waste: water ratio of 1:2. The soaked wastes were then homogenized using the handheld homogenizer for 10 min and transferred to a water bath at 70 °C for 1 h before double filtration by Whatman filter paper no 41. The final two syrups were collected, adjusted at an overall volume of 100 ml for each. Afterward, they were autoclaved at 121 °C for 20 min and stored in the fridge at 4 °C, labeled as extracts of date fruit wastes (E-DFW) and fig fruit wastes (E-FFW) stock solutions.
The sugarcane molasses (SCM) solution was treated following Bae & Shoda63 protocol of acid-heat pre-treatment. About 100 g of sugarcane molasses (SCM) was diluted by 2 folds (w/v) of d-H2O before centrifugation at 6000 rpm for 20 min to eliminate solid matters. The supernatant was then collected and its pH was altered to 3.0 with 4 N H2SO4, heated at 120 °C for 20 min, retained overnight at room temperature. Subsequently, the supernatant was centrifuged at 6000 rpm for 20 min and adapted to a volume of 100 ml, before storing at 4 °C as a treated sugarcane molasses (T-SCM) stock solution.
Preparation of bacterial inocula
Inocula of isolate MD1 were prepared on (HS) medium for the whole study. Aliquots of 10 ml volume of sterile (HS) medium were prepared and inoculated by a loopful of 10 days old culture. The inoculated aliquots were incubated at 28 °C for 7 days in the dark. Upon using, all tube contents were gently mixed and the liquid phase was exploited as the inocula for all accomplished BNC biosynthesis beakers.
Media and BNC production
In the present study, (HS) medium was the principal BNC production medium. Another three sets of (HS) media were formulated, but the supplemented glucose was substituted by (v/v) 10% of the 3 stock solutions (E-DFW, E-FFW, and T-SCM), and the prepared blends labelled as (D-HS), (F-HS), and (M-HS), respectively. The initial pH was adjusted at 6 by using 0.1 N H2SO4. The production volumes for all media were 50 ml in 250 ml beakers, which were inoculated and statically incubated in the dark at 28 °C for 7 days.
Harvesting and purification of the produced BNC
Positive outcome of the nanocellulose pellicles could be perceived by the formation of a gel-like mat floating on the medium surface. The BNC films produced by the bacterial isolate were washed twice with boiling d-H2O and 0.1 N NaOH (2 times for each and 20 min for each step), and then thoroughly rinsed with d-H2O till reaching the neutral pH. The wet films were kept in water at 4 °C or dried at room temperature for 24 h.
The total sugar content was determined by the sulfuric acid/anthrone colorimetric method described by Dubios et al.64. The total sugar contents of the prepared waste extracts were estimated, as well as the final sugar contents after the cultivation.
Kinetics of BNC production
Efficiency of the BNC production was calculated using the following equations reported by Gomes and his co-workers17:
where (Si) is the initial substrate concentration (g/L), (Sf) is the final substrate concentration (g/L), (M) is the amount of the produced BNC (g), (V) is the production volume (L), and (t) is the cultivation time period (h).
Time course of the BNC production on the utilized four media
The production of BNCs on the four formulations was conducted for an incubation period of 168 h to explore the production behavior, time point of maximal BNC production, and the pH fluctuation for the utilized BNC-producing strain on each medium. The obtained films were washed and dried as mentioned above. The pH values were measured for the whole harvested liquid cultures; subsequently, means and standard deviations (SD) were plotted versus time (h).
Influence of carbon source concentration on BNC productivity
The impact of the different carbon source concentrations on the BNC productivity was examined. The same media formulations; (D-HS), (F-HS), and (M-HS) were prepared in the ordinary proportion (v/v) 10%, in addition to the proportions of 5, 20, and 30% for each waste. The inocula proportion fixed at (v/v) 10% for all replicates, and they were statically incubated in the dark at 28 °C for 7 days.
Physical characterization of the BNC produced on HS and the three wastes media field-emission scanning electron microscope (FESEM) analysis
We investigated the produced BNC films using field emission scanning electron microscope (FESEM) by mounting a piece of about 3 × 3 mm on a SEM metal holder and sputter the sample surface by gold nanoparticles for 2 min. The sputtered samples were then scanned by QuantaTM Field emission gun (FEG 250) high resolution scanning electron microscope (SEM) at a voltage of 5 kV using the Everhart-Thornley Detector (ETD) at high vacuum.
Water holding capacity (WHC) and water release rate (WRR)
To evaluate water holding capacity (WHC) of the four BNC products, never dried samples were extracted from storing and the excess water was blotted by a paper towel. The samples were weighed (Wwet), and then left to dry in room temperature for 48 h. Afterwards, the samples were dried at 50 °C for 12 h to evaporate any humidity remnants, before determining the final weight of samples (Wdry). The water holding capacity for the BNC sample can be estimated using Eq. 4 as follow:
With regard to water release rate (WRR), never dried BNC samples were weighed (Wwet), and then left in room temperature with frequent weighing of the samples every 4 h. The weights were plotted as percentages of the Wwet versus time (h).
Analysis by atomic force microscopy (AFM)
The BNCs generated on the four media were analyzed using atomic force microscopy AFM (Keysight 5500LS) to characterize surface topography. The tapping mode was employed for imaging an area of 30 ×30 µm for each sample. The root mean square roughness RMS (Rq) was applied to compare surface roughness of the four BNC products. (Rq) is defined as the mean squared absolute values of surface roughness profile (µm) representing more sensitive parameter to surface peaks and valleys due to the squaring of amplitudes in its calculation65.
X-ray diffraction (XRD) analysis
Structural properties of the obtained BNCs from the four media were examined employing X-ray Diffractometer (labX XRD-6100, Shimadzu, Japan). The patterns were recorded at the CuKα radiation wavelength (λ = 1.54 Å), generated at a voltage of 40 kV and a filament emission of 30 mA. BNC samples were scanned at 2Ɵ range of 5–80 degrees at a scan speed of 0.5° min−1. Crystallinity was calculated through the following equation:
where I(200) is the intensity of the peak at 2Ɵ = 22°, I(am) is the background height between the peaks 2Ɵ = 22° and 2Ɵ = 16°.
The crystallite size was estimated using Scherrer’s equation:
where (k) is the dimensionless Scherrer constant = 0.9, (λ) is the X-ray wavelength, (β) is the peak full width at half maximum in radians, and (Ɵ) is the diffraction angle in radians.
Bragg’s equation was used to determine the atomic inter-planar spacing (d) as following:
where (n) is the order of the peak plane43.
Analysis by Fourier transform infrared (FTIR) spectrophotometry
The FTIR (FTIR-8400 S, Shimadzu, Japan) was applied to compare the functional groups of the processed BNC films from the utilized four media at spectra range 4000-400 cm−1 at 4 cm−1 resolution for 32 scans prior to the Fourier transformation.
Mechanical properties determination
The mechanical properties of the four BNC films were characterized by a universal testing machine (AG-1S, SHIMADZU, Japan). Each film was cut into rectangle with dimension of 20 ×50 mm, and the thickness was then gauged by (Sealey AK9635D) digital micrometer. The cell preload was 5 N and testing speed of 10 mm/min was applied to reach a constant strain rate. Young’s modulus, tensile strength and elongation at break (%) were calculated from the stress-strain data through exponent software.
All investigations were performed in six replicates, and the results were statistically analyzed using GraphPad Prism software (Version 7). The data were analyzed employing one-way and two-way analysis of variance (ANOVA) with the Tukey’s test for multiple comparisons66. The multiple comparisons were carried out based on the values, which were expressed by means ± SD of each group. The significant values were determined at P-value < 0.05, whereas the high significant values were considered at P-value < 0.01, and P-value < 0.001 using n = 6.
Gao, M. et al. A natural in situ fabrication method of functional bacterial cellulose using a microorganism. Nature communications 10, 437, https://doi.org/10.1038/s41467-018-07879-3 (2019).
Ullah, H., Wahid, F., Santos, H. A. & Khan, T. Advances in biomedical and pharmaceutical applications of functional bacterial cellulose-based nanocomposites. Carbohydrate Polymers 150, 330–352, https://doi.org/10.1016/j.carbpol.2016.05.029 (2016).
Torres, F. G., Arroyo, J. J. & Troncoso, O. P. Bacterial cellulose nanocomposites: An all-nano type of material. Materials Science and Engineering: C 98, 1277–1293, https://doi.org/10.1016/j.msec.2019.01.064 (2019).
Chen, X. et al. Recent approaches and future prospects of bacterial cellulose-based electroconductive materials. Journal of Materials Science 51, 5573–5588, https://doi.org/10.1007/s10853-016-9899-2 (2016).
Junka, A. et al. Potential of Biocellulose Carrier Impregnated with Essential Oils to Fight Against Biofilms Formed on Hydroxyapatite. Scientific reports 9, 1256, https://doi.org/10.1038/s41598-018-37628-x (2019).
Abol-Fotouh, D. et al. Farming thermoelectric paper. Energy & Environmental Science 12, 716–726, https://doi.org/10.1039/C8EE03112F (2019).
Roig-Sanchez, S. et al. Nanocellulose films with multiple functional nanoparticles in confined spatial distribution. Nanoscale Horizons 4, 634–641, https://doi.org/10.1039/C8NH00310F (2019).
Li, D. et al. Multifunctional adsorbent based on metal-organic framework modified bacterial cellulose/chitosan composite aerogel for high efficient removal of heavy metal ion and organic pollutant. Chemical Engineering Journal 383, 123127, https://doi.org/10.1016/j.cej.2019.123127 (2020).
Wang, W. et al. Properties and antimicrobial activity of polyvinyl alcohol-modified bacterial nanocellulose packaging films incorporated with silver nanoparticles. Food Hydrocolloids 100, 105411, https://doi.org/10.1016/j.foodhyd.2019.105411 (2020).
Cacicedo, M. L. et al. Progress in bacterial cellulose matrices for biotechnological applications. Bioresource Technology 213, 172–180, https://doi.org/10.1016/j.biortech.2016.02.071 (2016).
Revin, V., Liyaskina, E., Nazarkina, M., Bogatyreva, A. & Shchankin, M. Cost-effective production of bacterial cellulose using acidic food industry by-products. Brazilian Journal of Microbiology 49, 151–159, https://doi.org/10.1016/j.bjm.2017.12.012 (2018).
Hussain, Z., Sajjad, W., Khan, T. & Wahid, F. Production of bacterial cellulose from industrial wastes: a review. Cellulose 26, 2895–2911, https://doi.org/10.1007/s10570-019-02307-1 (2019).
Keshk, S. M. A. S. & El-Kott, A. F. In Science and Principles of Biodegradable and Bioresorbable Medical Polymers (ed. Xiang Zhang) 295–319 (Woodhead Publishing, 2017).
Islam, M. U., Ullah, M. W., Khan, S., Shah, N. & Park, J. K. Strategies for cost-effective and enhanced production of bacterial cellulose. International Journal of Biological Macromolecules 102, 1166–1173, https://doi.org/10.1016/j.ijbiomac.2017.04.110 (2017).
Gopu, G. & Govindan, S. Production of bacterial cellulose from Komagataeibacter saccharivorans strain BC1 isolated from rotten green grapes. Preparative biochemistry & biotechnology 48, 842–852, https://doi.org/10.1080/10826068.2018.1513032 (2018).
Pacheco, G. et al. Development and characterization of bacterial cellulose produced by cashew tree residues as alternative carbon source. Industrial Crops and Products 107, 13–19, https://doi.org/10.1016/j.indcrop.2017.05.026 (2017).
Gomes, F. P. et al. Production of bacterial cellulose by Gluconacetobacter sacchari using dry olive mill residue. Biomass and Bioenergy 55, 205–211, https://doi.org/10.1016/j.biombioe.2013.02.004 (2013).
Hong, F. & Qiu, K. An alternative carbon source from konjac powder for enhancing production of bacterial cellulose in static cultures by a model strain Acetobacter aceti subsp. xylinus ATCC 23770. Carbohydrate Polymers 72, 545–549, https://doi.org/10.1016/j.carbpol.2007.09.015 (2008).
Goelzer, F. D. E., Faria-Tischer, P. C. S., Vitorino, J. C., Sierakowski, M. R. & Tischer, C. A. Production and characterization of nanospheres of bacterial cellulose from Acetobacter xylinum from processed rice bark. Materials Science and Engineering: C 29, 546–551, https://doi.org/10.1016/j.msec.2008.10.013 (2009).
Lin, D., Lopez-Sanchez, P., Li, R. & Li, Z. Production of bacterial cellulose by Gluconacetobacter hansenii CGMCC 3917 using only waste beer yeast as nutrient source. Bioresource Technology 151, 113–119, https://doi.org/10.1016/j.biortech.2013.10.052 (2014).
Skiba, E. A. et al. A technology for pilot production of bacterial cellulose from oat hulls. Chemical Engineering Journal 383, 123128, https://doi.org/10.1016/j.cej.2019.123128 (2020).
Rani, M. U., Rastogi, N. K. & Appaiah, K. A. Statistical optimization of medium composition for bacterial cellulose production by Gluconacetobacter hansenii UAC09 using coffee cherry husk extract–an agro-industry waste. Journal of microbiology and biotechnology 21, 739–745 (2011).
FAO. FAOSTAT, 2016).
Bae, S. O. & Shoda, M. Production of bacterial cellulose by Acetobacter xylinum BPR2001 using molasses medium in a jar fermentor. Applied microbiology and biotechnology 67, 45–51, https://doi.org/10.1007/s00253-004-1723-2 (2005).
Jung, H. I. et al. Production and characterization of cellulose by Acetobacter sp. V6 using a cost-effective molasses-corn steep liquor medium. Applied biochemistry and biotechnology 162, 486–497, https://doi.org/10.1007/s12010-009-8759-9 (2010).
Machado, R. T. A. et al. Komagataeibacter rhaeticus grown in sugarcane molasses-supplemented culture medium as a strategy for enhancing bacterial cellulose production. Industrial Crops and Products 122, 637–646, https://doi.org/10.1016/j.indcrop.2018.06.048 (2018).
Abol Fotouh, D. M., Bayoumi, R. A. & Hassan, M. A. Production of Thermoalkaliphilic Lipase from Geobacillus thermoleovorans DA2 and Application in Leather Industry. Enzyme Research 2016, 9, https://doi.org/10.1155/2016/9034364 (2016).
Bae, S. O., Sugano, Y., Ohi, K. & Shoda, M. Features of bacterial cellulose synthesis in a mutant generated by disruption of the diguanylate cyclase 1 gene of Acetobacter xylinum BPR 2001. Applied microbiology and biotechnology 65, 315–322, https://doi.org/10.1007/s00253-004-1593-7 (2004).
Çakar, F., Özer, I., Aytekin, A. Ö. & Şahin, F. Improvement production of bacterial cellulose by semi-continuous process in molasses medium. Carbohydrate Polymers 106, 7–13, https://doi.org/10.1016/j.carbpol.2014.01.103 (2014).
Rodrigues, A. C. et al. Response surface statistical optimization of bacterial nanocellulose fermentation in static culture using a low-cost medium. New Biotechnology 49, 19–27, https://doi.org/10.1016/j.nbt.2018.12.002 (2019).
Al-Farsi, M. A. & Lee, C. Y. Nutritional and functional properties of dates: a review. Critical reviews in food science and nutrition 48, 877–887, https://doi.org/10.1080/10408390701724264 (2008).
El-Nagga, E. & El–Tawab, Y. A. Compositional characteristics of date syrup extracted by different methods in some fermented dairy products. Annals of Agricultural Sciences 57, 29–36 (2012).
Hestrin, S. & Schramm, M. Synthesis of cellulose by Acetobacter xylinum. II. Preparation of freeze-dried cells capable of polymerizing glucose to cellulose. The Biochemical journal 58, 345–352, https://doi.org/10.1042/bj0580345 (1954).
Yamanaka, S. et al. The structure and mechanical properties of sheets prepared from bacterial cellulose. Journal of Materials Science 24, 3141–3145, https://doi.org/10.1007/bf01139032 (1989).
Zhou, L. L., Sun, D. P., Hu, L. Y., Li, Y. W. & Yang, J. Z. Effect of addition of sodium alginate on bacterial cellulose production by Acetobacter xylinum. Journal of Industrial Microbiology & Biotechnology 34, 483, https://doi.org/10.1007/s10295-007-0218-4 (2007).
Keshk, S. M. Bacterial cellulose production and its industrial applications. Journal of Bioprocessing & Biotechniques 04, 1–10 (2014).
Shirai, A. et al. Biosynthesis of a novel polysaccharide by Acetobacter xylinum. International Journal of Biological Macromolecules 16, 297–300, https://doi.org/10.1016/0141-8130(94)90059-0 (1994).
Gullo, M., La China, S., Petroni, G., Di Gregorio, S. & Giudici, P. Exploring K2G30 Genome: A High Bacterial Cellulose Producing Strain in Glucose and Mannitol Based Media. Frontiers in microbiology 10, 58, https://doi.org/10.3389/fmicb.2019.00058 (2019).
Aytekin, A. Ö., Demirbağ, D. D. & Bayrakdar, T. The statistical optimization of bacterial cellulose production via semi-continuous operation mode. Journal of Industrial and Engineering Chemistry 37, 243–250, https://doi.org/10.1016/j.jiec.2016.03.030 (2016).
Bilgi, E., Bayir, E., Sendemir-Urkmez, A. & Hames, E. E. Optimization of bacterial cellulose production by Gluconacetobacter xylinus using carob and haricot bean. International Journal of Biological Macromolecules 90, 2–10, https://doi.org/10.1016/j.ijbiomac.2016.02.052 (2016).
Costa, A. F. S., Almeida, F. C. G., Vinhas, G. M. & Sarubbo, L. A. Production of Bacterial Cellulose by Gluconacetobacter hansenii Using Corn Steep Liquor As Nutrient Sources. Frontiers in microbiology 8, 2027, https://doi.org/10.3389/fmicb.2017.02027 (2017).
Czaja, W., Romanovicz, D. & Brown, R. M. Structural investigations of microbial cellulose produced in stationary and agitated culture. Cellulose 11, 403–411, https://doi.org/10.1023/b:cell.0000046412.11983.61 (2004).
Zeng, M., Laromaine, A. & Roig, A. Bacterial cellulose films: influence of bacterial strain and drying route on film properties. Cellulose 21, 4455–4469, https://doi.org/10.1007/s10570-014-0408-y (2014).
Foresti, M. L., Vázquez, A. & Boury, B. Applications of bacterial cellulose as precursor of carbon and composites with metal oxide, metal sulfide and metal nanoparticles: A review of recent advances. Carbohydrate Polymers 157, 447–467, https://doi.org/10.1016/j.carbpol.2016.09.008 (2017).
Basu, A., Vadanan, S. V. & Lim, S. Rational design of a scalable bioprocess platform for bacterial cellulose production. Carbohydrate Polymers 207, 684–693, https://doi.org/10.1016/j.carbpol.2018.10.085 (2019).
Marín, P. et al. Bacterial nanocellulose production from naphthalene. Microbial Biotechnology 12, 662–676, https://doi.org/10.1111/1751-7915.13399 (2019).
Ul-Islam, M., Khan, T. & Park, J. K. Water holding and release properties of bacterial cellulose obtained by in situ and ex situ modification. Carbohydrate Polymers 88, 596–603, https://doi.org/10.1016/j.carbpol.2012.01.006 (2012).
A, R. R. et al. Dehydration of bacterial cellulose and the water content effects on its viscoelastic and electrochemical properties. Science and technology of advanced materials 19, 203–211, https://doi.org/10.1080/14686996.2018.1430981 (2018).
Choi, M.-C., Kim, Y. & Ha, C.-S. Polymers for flexible displays: From material selection to device applications. Progress in Polymer Science 33, 581–630, https://doi.org/10.1016/j.progpolymsci.2007.11.004 (2008).
Ummartyotin, S., Juntaro, J., Sain, M. & Manuspiya, H. The role of ferrofluid on surface smoothness of bacterial cellulose nanocomposite flexible display. Chemical Engineering Journal 193–194, 16–20, https://doi.org/10.1016/j.cej.2012.03.074 (2012).
Gutiérrez-Hernández, J. M. et al. In vitro evaluation of osteoblastic cells on bacterial cellulose modified with multi-walled carbon nanotubes as scaffold for bone regeneration. Materials Science and Engineering: C 75, 445–453, https://doi.org/10.1016/j.msec.2017.02.074 (2017).
Klechkovskaya, V. V. et al. Structure of cellulose Acetobacter xylinum. Crystallography Reports 48, 755–762, https://doi.org/10.1134/1.1612596 (2003).
Sriplai, N. et al. Enhancing piezoelectric properties of bacterial cellulose films by incorporation of MnFe2O4 nanoparticles. Carbohydrate Polymers 231, 115730, https://doi.org/10.1016/j.carbpol.2019.115730 (2020).
Kondo, T., Rytczak, P. & Bielecki, S. In Bacterial Nanocellulose (eds Miguel Gama, Fernando Dourado, & Stanislaw Bielecki) 59–71 (Elsevier, 2016).
Moharram, M. A. & Mahmoud, O. M. FTIR spectroscopic study of the effect of microwave heating on the transformation of cellulose I into cellulose II during mercerization. Journal of Applied Polymer Science 107, 30–36, https://doi.org/10.1002/app.26748 (2008).
Oh, S. Y. et al. Crystalline structure analysis of cellulose treated with sodium hydroxide and carbon dioxide by means of X-ray diffraction and FTIR spectroscopy. Carbohydrate Research 340, 2376–2391, https://doi.org/10.1016/j.carres.2005.08.007 (2005).
Feng, X. et al. Characterization of Bacterial Cellulose by Gluconacetobacter hansenii CGMCC 3917. Journal of food science 80, E2217–2227, https://doi.org/10.1111/1750-3841.13010 (2015).
Hassan, M. A., Bakhiet, E. K., Ali, S. G. & Hussien, H. R. Production and characterization of polyhydroxybutyrate (PHB) produced by Bacillus sp. isolated from Egypt. J. App. Pharm. Sci. 6, 46–51 (2016).
Hassan, M. A., Bakhiet, E. K., Hussein, H. R. & Ali, S. G. Statistical optimization studies for polyhydroxybutyrate (PHB) production by novel Bacillus subtilis using agricultural and industrial wastes. International Journal of Environmental Science and Technology 16, 3497–3512, https://doi.org/10.1007/s13762-018-1900-y (2019).
Sanger, F., Nicklen, S. & Coulson, A. R. DNA sequencing with chain-terminating inhibitors. Proceedings of the National Academy of Sciences of the United States of America 74, 5463–5467, https://doi.org/10.1073/pnas.74.12.5463 (1977).
Tamura, K., Stecher, G., Peterson, D., Filipski, A. & Kumar, S. MEGA6: Molecular Evolutionary Genetics Analysis version 6.0. Molecular biology and evolution 30, 2725–2729, https://doi.org/10.1093/molbev/mst197 (2013).
Hassan, M. A. et al. Insight into multidrug-resistant microorganisms from microbial infected diabetic foot ulcers. Diabetes & Metabolic Syndrome: Clinical Research & Reviews 13, 1261–1270, https://doi.org/10.1016/j.dsx.2019.01.044 (2019).
Bae, S. & Shoda, M. Bacterial cellulose production by fed-batch fermentation in molasses medium. Biotechnology progress 20, 1366–1371, https://doi.org/10.1021/bp0498490 (2004).
Dubois, M., Gilles, K. A., Hamilton, J. K., Rebers, P. T. & Smith, F. Colorimetric method for determination of sugars and related substances. Analytical chemistry 28, 350–356 (1956).
De Oliveira, R., Albuquerque, D., Cruz, T., Yamaji, F. & Leite, F. Measurement of the nanoscale roughness by atomic force microscopy: basic principles and applications. (Rijeka: IntechOpen, 2012).
Hassan, M. A., Omer, A. M., Abbas, E., Baset, W. M. A. & Tamer, T. M. Preparation, physicochemical characterization and antimicrobial activities of novel two phenolic chitosan Schiff base derivatives. Scientific reports 8, 11416, https://doi.org/10.1038/s41598-018-29650-w (2018).
The authors would like to express their grateful thanks to the City of Scientific Research and Technological Applications (SRTA-City), New Borg El-Arab City, Alexandria, Egypt for its support in implementing this study.
The authors declare no competing interests.
Publisher’s note Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.
About this article
Cite this article
Abol-Fotouh, D., Hassan, M.A., Shokry, H. et al. Bacterial nanocellulose from agro-industrial wastes: low-cost and enhanced production by Komagataeibacter saccharivorans MD1. Sci Rep 10, 3491 (2020). https://doi.org/10.1038/s41598-020-60315-9
Hemostatic and antibacterial PVA/Kaolin composite sponges loaded with penicillin–streptomycin for wound dressing applications
Scientific Reports (2021)
Enhanced polyhydroxybutyrate (PHB) production by newly isolated rare actinomycetes Rhodococcus sp. strain BSRT1-1 using response surface methodology
Scientific Reports (2021)
Polyhydroxybutyrate (PHB) Production via Bioconversion Using Bacillus pumilus in Liquid Phase Cultivation of the Biomass of Arthrospira platensis Hydrolysate as a Carbon Source
Waste and Biomass Valorization (2021)
Statistical Optimization of Poly-β-Hydroxybutyrate Biosynthesis Using the Spent Mushroom Substrate by Bacillus tequilensis PSR-2
Waste and Biomass Valorization (2021)
A review of culture media for bacterial cellulose production: complex, chemically defined and minimal media modulations