- Open Access
Cellulase activity of a novel bacterial strain Arthrobacter woluwensis TDS9: its application on bioconversion of paper mill sludge
Journal of Genetic Engineering and Biotechnology volume 20, Article number: 87 (2022)
Lignocellulosic biomasses produced from agriculture and forest-based industries are the cheapest or negative-cost biomass with a great potential for biotransformation to value-added bioproducts. Paper mill sludge, an important lignocellulosic biomass creates an environmental threat, which requires financial input for disposal. Thus, this study was aimed to isolate a novel bacterial strain capable of degrading cellulosic biomass including paper mill sludge to produce reducing sugar and other value-added bioproducts.
A novel bacterial strain Arthrobacter woluwensis TDS9 isolated from the soil was screened for its cellulolytic activity using carboxymethyl cellulose (CMC) as the sole carbon source. The incubation period, temperature, pH, carbon, and nitrogen sources are the most important factors ruling the CMCase and sugar productions of the strain A. woluwensis TDS9, and an alkaline pH (pH 8.0) led to enhanced sugar production up to 1100.09 μg/mL after 72 h of incubation at 25°C in a medium containing 1.5% CMC and 1.25% beef extract. The optimal conditions for maximum CMCase activity were defined, and the potassium ion boosted the CMCase activity up to 1.06 U/mL when the enzymatic reaction was performed for 30 min at 50°C and pH 8 using CMC as a substrate. Moreover, the strain A. woluwensis TDS9 produced 433.33 μg/mL reducing sugar from 1% pretreated paper mill sludge. Significant alterations in the structural arrangement of cellulosic fiber of paper mill sludge observed under microscope after each step of chemical treatment process helped for loosening the cellulose fibers and increased the saccharification for enzymatic hydrolysis. Endoglucanase IV (33 KDa) and beta-glucosidase II (53 KDa) were identified in crude enzyme based on the zymogram analysis and substrate specificity.
The research has for the first time proved that this A. woluwensis TDS9 strain can efficiently convert cellulose. Therefore, the strain TDS9 could be a potential candidate for cellulase production in an industrial biotransformation process of paper mill sludge to produce reducing sugar. This sugar stream can be further used as a substrate to produce biofuels and other organic acids using another microorganism, which represents a greener alternative to add value to the paper production helping paper mill industries.
Cellulose, being one of the mostly found biomaterials, is present in plant biomass interlinked with lignin and hemicellulose. The cellulose is a polymeric polysaccharide of 𝛃-1,4-linked 𝛃-glucose molecules, and the degree of polymerization ranges from 10000 to 15000 . In cellulose, each anhydroglucose ring is linked covalently through an oxygen and bonded to the C1 of one glucose to the C4 of the next ring (1→4 linkage) .
The enzyme family responsible for the hydrolysis of cellulose is known as cellulase [3,4,5,6,7]. Cellulases are a group of enzymes produced by a wide range of microorganisms including fungi, bacteria, and actinomycetes that catalyze the hydrolysis of cellulose to produce monosaccharides and shorter polysaccharides or oligosaccharides [7,8,9,10,11]. Based on the information found in Carbohydrate-Active Enzymes database (CAZy) , cellulase belongs to glycoside hydrolase EC 3.2.1 group of enzymes. Cellulase comprises catalytic and non-catalytic modules. The catalytic modules have been classified into numerous families based on their amino acid sequences and crystal structures. The non-catalytic carbohydrate-binding modules and/or other domains located at N- or C-terminus of a catalytic module.
Cellulolysis is a complex process involving a group of enzymes belonging to cellulase family and multiple steps of enzymatic hydrolysis in the presence of water [13,14,15,16]. The complete hydrolysis of cellulose polymer into glucose residues involves at least three types of enzymes in synergy . The endoglucanase attacks amorphous region of cellulose at random site and cleave the internal bonds of the glycan chains providing reducing and/or nonreducing ends of cellooligosaccharides for cellobiohydrolases; therefore, cellobiohydrolases hydrolyse those short chains and yielding cellobiose as a major product. The glucosidase finally hydrolyses cellobiose to produce glucose.
The booming of papermill industries all over the world has led to generate a large amount of primary and secondary sludges, created an environment friendly disposal issue. It is estimated that paper mills produce 300–350 million tons sludges per year, which ensures its availability as the substrate for biofuel production . These paper sludges, unless properly treated pose major threat to the environment as well as to aquatic and agricultural fields [19,20,21]. So, we need to take eco-symbiotic and economically efficient initiative to relieve the environment from this burden and to achieve a greener environment. Paper mill sludge is the final solid waste recovered from the wastewater treatment process in pulp and paper mills. Sludge discharged from paper mills is divided into four categories: (1) primary sludge (PS) that is the by-product of virgin wood fiber coming from primary screening of wastewater, (2) de-inking paper sludge (DPS) that is the by-product of ink and other dye removal from recycled or waste papers, (3) secondary sludge (SS) that comes from the secondary screening of wastewater treatment system during pulping process, and finally (4) combined primary and secondary sludge that contain a mixture of both primary and secondary sludge characterized with longer fiber length . The primary sludge of paper mill contains a massive amount of lignocellulosic (cellulose, hemicellulose, and lignin) biomass.
Sludge disposal is nowadays a contemporary issue as current disposal methods (landfilling, incineration, and land spreading, etc.) are not economically and environmentally attractive. Over 50% of the total paper mills sludge produced are currently being landfilled or incinerated, which cause both environmental and financial problem . On average, 60% of the total wastewater treatment costs of pulp and paper mills account for sludge disposal . Therefore, paper mill sludge is now considered as a negative-cost biomass. The primary sludge of paper mill contains a significant amount of cellulose, which can be utilized by carboxymethylcellulase (CMCase) producing microorganisms to produce reducing sugar . While conventional waste management methods require significant financial input, bioremediation can play a more efficient role both from economic point of view as well as environmental safety. Consequently, this study was aimed for isolating a potential cellulolytic bacterial candidate which can degrade cellulosic biomass in a cost-effective and eco-friendly way.
Bioconversion process of lignocellulosic biomass consists of various types of processes including physical, chemical, and biological processes . However, each of these processes have their own drawbacks when implemented on a large scale [27, 28]. One of the major hurdles of biomass conversion into biofuel is the high cost of catalytic enzymes and the lack of their reusability and stability. The nanotechnology comes as a boon with its ability to stabilize the biocatalysts and immobilize the enzymes on nanostructures for better catalytic efficiency [29,30,31]. Nanotechnology has achieved these qualities in two main methods: covalent bonding of different enzymes on nanomaterials and employing functionalized nanoparticles [32, 33]. Nanoparticles are also well known for their bioremedial potential as well as photocatalytic activity to degrade environmental pollutants [34,35,36]. However, the high cost of processing hinders the effectiveness of the current nanotechnology technique employed on the conversion of lignocellulosic biomasses. Therefore, our study creates an opportunity to valorize the lignocellulosic biomasses including paper mill sludge through a cost-effective biological recycling process that can increase the efficiency of enzymatic hydrolysis.
Even though there are a number of cellulase producing microbial strains commercially available, most of them are not efficient enough to utilize paper mill sludge. Paper sludge contains fair amount of harmful chemicals including acids, alkali, and bleaches that inhibit the growth of microorganisms. Furthermore, the structural arrangement of paper mill sludge is not favorable for microbial degradation due to a complex association of hemicellulose and xylan with cellulosic fibres. Hence, the chemical treatment is required prior to bioconversion of such complex biopolymers. The aim of this research work is the enzymatic degradation of paper mill sludge using efficient cellulase producing bacterial strain to produce sugar; therefore, this bioconversion process was designed to removal of harmful chemical residues from the paper mill sludge by chemical treatment to make cellulose fibres available for enzymatic hydrolysis of cellulase producing microorganism. The uniqueness of our research from other existing study on the conversion of paper mill sludge is that it comprises both chemical treatment and biological agent for successful conversion of paper mill sludge; as no other study attempted the same as far as we know. This sugar residue can be further converted to value-added chemicals. In this research work, a novel bacterial strain Arthrobacter woluwensis TDS9 was isolated and characterized, which can efficiently produce CMCase for utilizing cellulosic substrate from lignocellulosic biomass paper mill sludge to produce sugar streams. Therefore, this research might have a significant contribution to the development of biorefinery and paper mill industries.
Isolation of bacterial strain
The soil sample for isolation of paper mill waste degrading and cellulase producing bacteria was collected from degraded paper mill waste of Karnaphuli Paper Mill located at Chandraghona (Latitude: 22.4796389, Longitude: 92.133864), Chattogram, Bangladesh.
About 5.0 g of the collected sample was inoculated into 100 mL of minimal salt (MS) medium (0.5 g/L NaNO3, 1.0 g/L K2HPO4, 0.5 g/L KCl, and 0.5 g/L MgSO4) supplemented with 3% primary sludge of paper mill as a sole carbon source cellulose in a 250-mL Erlenmeyer flask, incubated at 35°C with shaking (150 rpm) for 5 days. Following incubation, cellulolytic bacterial isolates were isolated from enriched culture broth using spread plate method. Briefly, 100 μL of enriched broth or diluted enriched broth culture was spread on Luria-Bertani (LB) agar (10.0 g/L peptone, 5.0 g/L yeast extract, 5.0 g/L NaCl, and 15 g/L agar) plate using sterilized glass spreader. Plates were incubated at 35°C for 24h. Bacterial colonies were selected from these plates based on their morphological features such as colony morphology, colony color, and colony size. Single colonies with distinctive visual characteristics were picked and streaked on LB agar plates. Following isolation, pure bacterial isolates were screened for their cellulase activities.
Screening for carboxymethyl cellulase (CMCase) activity
Bacterial isolates were grown in tubes containing 5.0 mL LB broth (10.0 g/L peptone, 5.0 g/L yeast extract, and 5.0 g/L NaCl) for 24h at 35±2oC with shaking at 200 rpm. A subsequent incubation of 5.0 μL of culture broth was dropped on the center of CZAPEK’s agar (10.0 g/L CMC, 1.0 g/L K2HPO4, 0.5 g/L MgSO4. 7H2O, 0.5 g/L KCl, 2.0 g/L NaNO3, 0.01 g/L FeSO4, 15.0 g/L agar) plate, incubated at 35°C for 48h. Following incubation, the plates were flooded with 1% Congo red followed by washing with 1M NaCl to see the cellulolytic activity of bacterial isolates. This primary screening was further confirmed by a semi-quantitative method using Gram’s iodine solution (2.0 g potassium iodide, 1.0 g iodine crystal, and 300 mL distilled water). The formation of a clear zone of hydrolysis (clear zone) indicated the cellulose degradation by bacterial CMCase. The diameter of the clear zone was measured in millimeter. Therefore, the largest zone of hydrolysis producing bacterial isolate TDS9 was selected as a potential candidate for utilizing paper mill sludge to produce CMCase as well as reducing sugar.
Identification of bacterial isolate
The most promising bacterial isolate TDS9 was identified using 16s rRNA gene sequencing. The isolate TDS9 was cultured in LB broth (10.0 g/L peptone, 5.0 g/L yeast extract, and 5.0 g/L NaCl) for 24h at 35°C. Following incubation, the cells from 1000 μL of broth culture were collected by centrifugation at 12,000 rpm. The genomic DNA was isolated from these bacterial cells using DNA extraction kit (Presto™ mini genomic DNA Bacteria kit, Geneaid, USA) following manufacturer protocols. The extracted DNA was amplified by PCR (polymerase chain reaction) using universal 16S primers 27F (5′-AGAGTTTGATCNTGGCTCAG-3′) and 1492R (5′-GCTTACCTTGTTACGACTT-3′). The resulting PCR product was purified using QIAquick PCR Purification Kit (QIAGEN, Germany) according to manufacturer’s protocol. The purified PCR product was sequenced using the Applied Biosystems BigDyeTM Terminators v3.1 (Thermo Fisher Scientific, USA). The sequence similarity analysis was carried out by comparing the 16S rRNA sequences of the selected strains from sequence data in the GenBank database of the National Center for Biotechnology Information (NCBI) using the “blastn” suite optimized for “Highly similar sequences (Megablast)” [37, 38].
Finally, the sequences of 16S rRNA were aligned using the multiple sequence alignment program CLUSTAL. Phylogenetic and molecular evolutionary analyses were processed through the molecular evolutionary genetics analysis software MEGA X using the neighbor-joining method [39,40,41]. The identification of selected isolate TDS9 was confirmed using morphological, cultural, and biochemical characteristics .
Fermentation medium and culture condition
Bacterial isolate TDS9 was grown in LB broth medium, and 1.0 mL of overnight culture was transferred into 200 mL conical flask containing 50 mL of minimal salt (MS) medium supplemented with CMC and/paper mill sludge as the sole carbon source. When indicated, the MS medium was supplemented with a specified concentration of different nitrogen and carbon sources. The flasks were incubated in a shaker incubator at 200 rpm. Following incubation, the cell-free supernatant was collected from the culture broth by centrifugating at 4°C and 10,000 rpm for 10 min, which was used for estimation of sugar concentration. The release of reducing sugar from CMC or paper mill sludge was determined using the dinitrosalicylic acid (DNS) method [43,44,45]. Bacterial growth was observed at 24h intervals. Biomass or cell growth was measured as absorbance at 600 nm (OD600) using microplate spectrophotometer. The extracellular protein was estimated using the standard method [46, 47].
Quantitative assay of reducing sugar and CMCase
The released reducing sugar from CMC or paper mill sludge by CMCase enzyme was analyzed using dinitrosalicylic acid (DNS) method. A modified microplate-based assay method was used for measuring reducing sugars. Briefly, 20 μL of cell-free supernatant (crude enzyme) was mixed with 80 μL of 0.5% CMC and 50 mM citrate buffer at pH 6.0, incubated for 30 min at 50°C [48,49,50]. The reaction was terminated by adding 200 μL DNS solution (3.15 g/L DNS, 10.48 g/L NaOH, 91.0 g/L Na-K tartrate, 2.5 g/L phenol, and 2.5 g/L sodium metabisulfite). The mixture was boiled for 5 min. The absorbance was determined at OD540nm using microplate reader spectrophotometer. All experiments were repeated at least three. The CMCase production was determined by estimating the amount of reducing sugar by DNS method.
Optimization of culture condition for CMCase production
Microbial growth and metabolite production are significantly influenced by different environmental as well as chemical factors leading to highest enzyme production when they are cultured in their optimum environment. Thus, the effect of incubation period, temperature, pH, carbon, and nitrogen sources on the production of reducing sugar and CMCase were determined.
Cells from slant culture was inoculated into a LB broth medium to prepare the seed culture. After 24 h of incubation at 35°C under aerobic condition, the seed culture was inoculated into fermentation medium for optimization of fermentation parameters. In case of sugar production, batch fermentations were carried out in conical flasks containing a 50-mL fermentation medium (MS broth medium supplemented with CMC) with 100 μl of 24h seed culture. Aerobic condition was maintained by incubating the culture flasks in a shaker incubator at 200 rpm. For optimizing the incubation time for maximum sugar production, the culture flasks were incubated at 35±2°C for different incubation times (24, 48, 72, 96, 120, and 144 h). After optimizing the incubation time for maximum sugar production, the strain TDS9 was cultured at different temperatures (20, 25, 35, 45, and 55°C) for determining the optimum incubation temperature. Likewise, each parameter was optimized by keeping the values constant that were optimized in the preceding stages. Initial pH of the culture medium was also optimized using a range of medium pH from 3 to 9. In addition, 1% of several carbon (glucose, xylose, lactose, cellobiose, starch, fructose, sucrose, salicin, glycerol, CMC, filter paper, cotton, rice straw, and paper sludge) and nitrogen (ammonium sulfate, sodium nitrate, potassium nitrate, ammonium chloride, urea, soya bean meal, yeast extract, tryptone, beef extract, and peptone) sources were tested to optimize the culture media composition for maximum sugar productions. When indicated, the medium was supplemented with a specified concentration of different nitrogen and carbon sources. The pH of the medium was adjusted with 1 M NaOH or 1 M HCl depending on the experiment. The cell-free supernatant was collected by centrifuging the culture broth at 4°C and10,000 rpm for 10 min, used for the estimation sugar concentration. All experiments were performed in triplicate, and the results are expressed as mean values of three replicates. The standard deviation of the results obtained from triplicate experiments were shown as error bars.
Characterization of CMCase (cellulase) enzyme
For partial purification of the enzyme, 70% ammonium sulfate was used in cell-free culture broth and kept it overnight at 4°C to allow precipitation. The precipitate was collected by centrifuging the solution at 10,000 rpm for 10 min at 4°C. The precipitate was dissolved in 50-mM sodium citrate buffer (pH 6) and used for determining the molecular weight of enzyme by SDS-PAGE analysis and enzyme activity. SDS-PAGE was performed using 12% (w/v) polyacrylamide gel according to the protocol described by Laemmli  and Brunelle and Green . The separated enzyme and molecular markers containing gel was stained overnight in Coomassie Brilliant Blue R-250 followed by destaining with the destaining solution for 1–3 h. The approximate molecular weight of the enzyme was determined from the bands developed in the gel using standard protein marker (Puregene genetix brand, pre-stained protein ladder, lot no: 3 color protein ladder pg-pmt 2922, lot: 00139874).
Factors affecting CMCase activity
The effects of various physico-chemical parameters along with different carbon and nitrogen sources, metal ions, and surfactants on CMCase activity were determined in cell-free supernatant of bacterial culture broth, which was used as crude enzyme solution. The CMCase activity was assayed using the International Union of Pure and Applied Chemistry (IUPAC) guideline [53, 54] which was designed to measure cellulase activity in terms of CMCase units per milliliter of original enzyme solution. One unit (U) of enzyme activity is defined as the amount of enzyme that releases 1.0 μmol of reducing sugars per minute [54, 55]. For the effect of reaction time, temperature and pH on enzyme activity enzyme-substrate reactions were carried out at a wide range reaction time, temperature, and pH.
Pre-treatment of paper mill sludge
Primary sludge of paper mill was collected from Domtar’s Windsor Mill (Windsor, Canada). The Paper mill sludge contained 66.7% cellulose, 14.4% lignin, 13.8% hemicellulose, and 5.1% ash. The primarily sludge is inaccessible to the microbial attack due to the structural complexity and residual toxic chemical substituent used during pulping process. However, the sludge was washed with distilled water under continuous stirring for 3 h, filtered to remove other impurities, dried overnight in an oven at 55°C, and shredded into smaller pieces. Moreover, the shredded sludge was subjected to chemical treatment process for removing hemicellulose and lignin contents present in association with the cellulosic fiber to make available for microbial degradation. Therefore, the shredded sludge was submerged in 7% NaOH at a ratio of 1:10 (w/v). The process was carried out thrice under continuous mechanical stirring at 80°C for 3 h. Each time, the sludge was washed with distilled water until pH becomes neutral. Subsequently, the sludge was treated with H2O2 (11% v/v) under continuous mechanical stirring, where the pH was adjusted to 11 using 7% NaOH and this treatment process was performed thrice (3 h at 45°C in each step). Finally, the sludge was washed with distilled water for several times until the pH became neutral, dried again, and shredded into small pieces.
Microbial degradation of sludge in the presence of inducers
Several complex carbohydrates (cellobiose, lactose, sucrose, CMC, glucose, and fructose) were used in the culture medium at a concentration of 0.15% (w/v) as the inducers . Each of these inducers was incorporated in separate culture flasks with 1% of chemically treated paper mill sludge in previously optimized culture media to assess their activity to induce cellulase production. Overnight grown seed culture was used as an inoculum and incubated in the previously optimized culture condition. After incubation, sugar was estimated from the culture filtrate to determine the cellulase activity.
Isolation and screening for CMCase activity
A total of 83 bacterial isolates were isolated based on their colony color, appearance, and characteristics from LB agar plate. Furthermore, the isolates were screened for their CMCase activity. Among the 83 isolates, the isolate TDS9 showed the largest hydrolyzing zones 12.75 and 8.47 mm in diameters on CZAPEK’s agar plates using 1% CMC and 1% pre-treated paper mill sludge, respectively (Table 1). Also, the isolate TDS9 produced 683.33 and 350.00 μg/mL reducing sugar from 1% CMC and 1% pre-treated paper mill sludge, respectively (Table 1).
Identification and evolutionary relationship of the isolates
The selected bacterial isolate TDS9 was identified based on 16s rRNA gene sequencing. The sequencing result was submitted into the nucleotide BLAST of the National Center for Biotechnology Information (NCBI) database for possible identification based on sequence similarity. The NCBI BLAST result showed 99.90% similarity of the isolate TDS9 with a previously reported strain Arthrobacter woluwensis 1551, and the phylogenetic analysis confirmed its relatedness to the genus Arthrobacter (Fig. 1). Furthermore, the 16s rRNA gene sequence of TDS9 has been submitted to the NCBI GenBank for an accession number, and the very strain reported in this paper has been assigned as a new strain Arthrobacter woluwensis TDS9 with an accession number MT071300. Moreover, the identification of Arthrobacter woluwensis TDS9 strain was confirmed using morphological, cultural, and biochemical properties (Table 2).
Optimization of culture conditions
For maximum production of reducing sugar from MS medium supplemented with CMC (biomass) using the novel strain A. woluwensis TDS9, the culture conditions (incubation period, time, temperature, pH, carbon, and nitrogen sources) were optimized, and the results are presented in Figs. 2, 3, and 4. As shown in Fig. 2A, the maximum sugar production 683.00 μg/mL was obtained after 72 h of incubation. The CMCase activity of the strain TDS9 has been significantly influenced by the incubation temperature of growth culture; thus, the optimum incubation temperature for maximum reducing sugar production (803.49 μg/mL) was 25°C (Fig. 2B). Also, the yields of reducing sugar were decreased gradually with the increase of incubation temperature.
However, the initial pH of the culture medium had played a significant role on reducing sugar production by A. woluwensis TDS9, and the results are shown in Fig. 2C. Consequently, when A. woluwensis TDS9 was cultured in the medium with different initial pH, the maximum amount of reducing sugar (850.24 μg/mL) was attained at pH 8 (Fig. 2C). The concentrations of sugar in culture medium were raised with the increase of medium pH up to 8 and then decreased at pH 9.
The impact of fourteen different carbon sources including CMC on the production of reducing sugar by A. woluwensis TDS9 was investigated under optimized temperature (25°C), pH (8), and incubation time (72 h) of the culture, and the results are presented in Fig. 3. As shown in Fig. 3, the results showed that the maximum sugar concentration obtained after 72 h of incubation using A. woluwensis TDS9 strain was 947.94 μg/mL when 1.5% CMC was used as a sole carbon source.
Moreover, the effects of different nitrogen sources on the production of reducing sugar by the strain A. woluwensis TDS9 are presented in Fig. 4. The strain TDS produced the highest amount (1100.09 μg/mL) of reducing sugar when grown with 1.25% (w/v) beef extract as a nitrogen supplement (Fig. 4).
SDS-PAGE and zymogram analysis
Gel picture of SDS-PAGE after staining with Coomassie blue stain revealed that there were two enzyme bands with molecular weight of 33 KDa and 53 KDa, respectively (Fig. 5). According to the “Worthington Enzyme Manual,” the two types of cellulases from A. woluwensis were identified as endoglucanase IV (33 KDa) and beta-glucosidase II (53 KDa) based on their molecular weight and substrate (CMC) specificity .
The CMCase activity of the newly isolated bacterial strain A. woluwensis TDS9 was studied under a wide range of reaction period, temperature, and pH. The optimum enzyme activity (0.46 U/mL) was achieved after 60 min of reaction time (Fig. 6A) at 50°C, indicating the thermal stability of the cellulase for a long period of reaction (Fig. 6B). While assaying the effect of different pH on the CMCase activity of the cellulase from A. woluwensis TDS9, the highest enzyme activity (0.93 U/mL) was observed at pH 8 (Fig. 6C). The CMCase activity was decreased at pH 9.
Crude enzyme from A. woluwensis TDS9 showed the highest CMCase activity (0.96 U/mL) against carboxymethyl cellulose (CMC) followed by chemically treated paper sludge (0.56 U/mL), which was also our target biomass in this study (Fig. 6D). While studying the effect of different nitrogen sources on the CMCase activity of the cellulase from A. woluwensis TDS9, tryptone induced the highest CMCase activity of 1.01 U/mL (Fig. 6E).
The studies on the effect of several metal ions on CMCase activity revealed that the treatment with a 10mM concentration of K+, Mg2+, and Zn2+ enhanced the CMCase activity slightly, while Fe2+ inhibited the enzyme activity a bit with the highest being 1.06 U/mL and lowest 0.76 U/mL (Fig. 6F). On the other hand, surfactants and reductants had significant effect on the enzymatic activity of cellulases from A. woluwensis. EDTA was found to induce the enzyme activity while SDS significantly inhibited the CMCase activity (Fig. 6G).
Utilization of paper mill sludge
The chemical treatment process loosened the cellulose fiber from residual lignin and hemicellulose components as observed under microscope at 10⨯ magnification (Fig. 7). A small amount of simple and synthetic carbon source aided microbial growth and metabolism which further triggered the degradation process of sludge. Therefore, biotransformation of pretreated paper mill sludge by TDS9 was evaluated under optimized culture condition. The optimal conditions for the batch culture of strain TDS9 were determined using CMC as the sole carbon source where 1.25% beef extract was an inducer (nitrogen source) for maximum sugar production. In addition to 1.25% beef extract, 35oC and pH 8 are the optimal incubation temperature and initial pH of the culture, respectively.
After chemical treatment, the paper sludge was subjected to microbial degradation in the presence of different carbon sources as the co-substrate for cellulase enzyme production. Therefore, in case of paper mill sludge degradation, the MS medium was supplemented with 1% pre-treated paper mill sludge, 1.25% beef extract, and different inducers at 0.15% concentration. Concentration of reducing sugar in broth culture was determined at 24h interval up to 120 h. The effect of inducers on paper mill sludge degradation is presented in Fig. 8. The highest paper mill sludge degradation was observed in the presence of 0.15% CMC, yielding 433.33 μg/mL reducing sugar using the strain TDS9 under optimized culture condition (Fig. 8). Consequently, the amount 433.33 μg/mL reducing sugar obtained from bioconversion of paper mill sludge is the highest amount until today (Fig. 8).
Cellulolytic microorganisms have long been a topic of interest to the scientists for their feasibility to be exploited and numerous industrial applications [58, 59]. The current enzyme repertoire is still inadequate to meet the industrial requirement, and the quest is being continued to isolate cellulolytic strains from unexplored environments [60, 61]. Several cellulase-producing bacterial isolates were isolated from different soil samples and paper mill waste. After screening for qualitative and quantitative cellulase activities, a potential cellulase-producing bacterial isolate TDS9 was finally selected for this study. The 16S rRNA gene sequencing and phylogenetic analysis of the gene sequences confirmed the identity of the isolate TDS9 as Arthrobacter woluwensis TDS9 strain. Moreover, morphological and biochemical study of the isolate also aided to characterize the isolate. Although the saccharification of cellulose production results in different simpler sugar forms is a key step of the bioconversion, priority was given to assay the reducing sugar production for each parameter.
Being an inducible enzyme, cellulase is prone to be exploited by its culture condition, and carbon and nitrogen sources [58, 62]. In the present study, different culture conditions were optimized for maximum saccharification of lignocellulosic biomasses. The newly isolated strain Arthrobacter woluwensis TDS9 produced the highest amount of reducing sugar from CMC after 72h of incubation which is decreased afterwards. It might be due to the depletion of nutrients in the batch culture medium which may have stressed the bacterial physiology to utilize complex carbon source. Similar incubation period was also reported on the production of cellulase by Bacillus subtilis Q3 and Enhydrobacter sp. ACCA2 strains [63, 64]. Thus, the production of maximum cellulase at early stage (72h incubation) of fermentation indicated that the strain TDS9 can be useful for large-scale cellulase production.
Therefore, it was observed that the optimum temperature for maximum cellulase production by A. woluwensis TDS9 was 25°C which also coincides with the mesophilic nature of the bacterial candidate. Moreover, the production of reducing sugar gradually depleted with the increase of incubation temperature which might be due to the alteration of cell membrane composition and stimulation of protein catabolism at higher temperature. Similar optimum temperature was found for the production of cellulase and xylanase using Micrococcus luteus SAMRC-UFH3 KU171371 , Pleurotus sapidas , Trichoderma viride VKF3 , and for Bacillus sp. .
Also, the highest cellulase activity at pH 8 indicates slightly alkaliphilic nature of the strain TDS9. Similar optimum initial medium pH was also found for Thermomonospora curvata  and for Paenibacillus terrae . However, the strain Bacillus subtilis Q3 also produced maximum cellulase at pH 7 . Premalatha et al.  observed the pH 6.5 as optimum medium pH for maximum enzyme production using Enhydrobacter sp ACCA2 strain.
Thereafter, among different types of carbon sources, A. woluwensis TDS9 was able to produce maximum reducing sugar when CMC was provided as sole carbon source. However, it was found that A. woluwensis TDS9 produced maximum sugar when medium was supplemented with simpler form of cellulose rather than those of natural origin with complex structures. Similar findings were observed using CMC as the ideal source of carbon for cellulase production by Bacillus cereus LAZ 518  and Enhydrobacter sp. ACCA2 .
The strain A. woluwensis TDS9 yielded the highest amount of reducing sugar from CMC when cultured with beef extract as a nitrogen supplement. Moreover, our results revealed that the inorganic sources of nitrogen were found less capable to induce cellulase activity compared to that of organic and complex form of nitrogen sources. Similar results were also reported by other researchers using Streptomyces viridobrunneus SCPE-09 , Pseudomonas sp. , Bacillus pumilus B20 , and Psychrobacter aquimaris LBH-10  strains. In our research work, the optimum conditions of the batch culture for A. woluwensis TDS9 strain were optimized for the maximum production of reducing sugar. Therefore, under optimized conditions, a significant product yield (1100.09 μg/mL) of reducing sugar was attained by a novel strain A. woluwensis TDS9 at an alkaline pH (pH 8). There is no any report on the production of considerable amount of reducing sugar using this strain TDS9.
Concentration variation of media components exerts a significant effect on cellulase activity [76, 77]. Therefore, optimization of individual components of a medium has been considered as a measure to reduce production cost as well as obtain higher enzyme activity. Subsequently, the highest cellulase activity was observed at 50 °C and 60 min of reaction period, indicating the enzyme is thermo-tolerant which signifies its application for industrial use. Optimum enzyme activity at pH 8 gives us insight about formulating the bioconversion process at which it can function best and the alkaline pH 8 indicates the optimum cellulase activity for hydrolyzing cellulosic substrate by this strain TDS9 in this growth condition, which can be supported by a previous study conducted by McDermid et al. . Similar optimum condition for cellulase activity was also reported by Patagundi et al. , Giese et al. , and Liang et al.  for temperature, reaction time, and pH in Bacillus cereus, Trichosporon mycotoxinivorans UFMG-CLM68, and Paenibacillus terrae ME27-1, respectively.
Endoglucanase IV identified from the zymogram analysis of the newly isolated strain A. woluwensis TDS9 was characterized to exhibit enzymatic activity on substrates containing beta-1,4- glycosidic bond, such as carboxymethylcellulose (CMC), hydroxyethylcellulose (HEC), and beta-glucan . Thus, it could be involved in the degradation of complex natural cellulosic substrates. A. woluwensis TDS9 showed the highest cellulase activity against CMC indicating its substrate specificity according to the nature of the enzyme itself. CMC induced maximum cellulase activity in TDS9, which is comparable to other studies on cellulolytic bacteria. A comparison of cellulase activity among various other bacteria is presented in Table 3, where CMC was used as a substrate.
The effect of several nitrogen sources and metal ions on the cellulase activity of the selected isolate was not significant. Moreover, tryptone and potassium chloride slightly increased the cellulase activity compared to that of other nitrogen sources and metal ions tested in this study. This nitrogen sources were unresponsiveness to the extracted enzyme as the external nitrogen content. Nitrogenous compounds do not affect the availability of substrate or catalyze reaction of cellulase with relevant substrate in any ways. Among four different surfactants and reductants SDS inhibited the cellulase activity. This might be due to the fact that surfactants tend to decrease the surface tension of aqueous systems, which may alter the properties of liquids such as detergency, emulsification, greasing, and solubilization. Surfactant properties can decrease the nonproductive adsorption of cellulases on lignin, acting as “activators agents” of these enzymes .
Lignocellulosic biomasses pose certain challenges against microbial degradation due to its rigid crystalline structure of cellulose as well as hemicellulose and lignin contents. All these structural complexities restrict the availability of cellulose components for microbial degradation. Thus, the chemical treatment of the lignocellulosic biomasses is a prerequisite for microbial degradation. Alkali treatment of the paper mill sludge successfully loosened the cellulose fibers from lignin and hemicellulose as observed under microscope. While other toxic substances present in paper mill sludge were removed via hydrogen peroxide treatment. Finally, the culture of Arthrobacter woluwensis TDS9 was used as an inoculum for the bioconversion of chemically pre-treated paper mill sludges. The significant production of reducing sugar from pre-treated paper mill sludge was observed in the presence of small amount of CMC as an inducer. A similar prevalence of crystalline cellulose or CMC-induced higher rate of endoglucanase activity was reported in several other studies [88,89,90,91]. The inducers may have significant role on the induction of cellulase gene activation which then further accomplished the degradation of cellulosic content from paper mill sludge. This result depicted that the strain TDS9 has complex enzyme activity with lignocellulolytic effect and saccharification potential. Therefore, our newly isolated strain A. woluwensis TDS9 could utilize cellulose from paper mill sludge as a carbon and energy source for their growth and produce significant amount of bioproducts reducing sugar under aerobic condition. Our report indicated that the batch fermentation with initial paper mill sludge 10 g/L (1%) was the optimal concentration for maximum sugar production, which is the highest concentration in batch culture till now (Fig. 8). Still now, there is no any significant report for the bioconversion of paper mill sludge by bacterial candidate. However, a high product yield (433.33 μg/mL) of reducing sugar obtained from batch culture process was the highest amount using paper mill sludge as a cellulosic feed stock until now. We have proved, however, that a newly isolated bacterial strain A. woluwensis TDS9 could utilize paper mill sludge to produce a significant amount of reducing sugar. The primary objective of this study was to obtain simpler carbohydrate form from complex negative cost biomass paper mill sludge. This simpler sugar forms can further be converted into other biofuels or related compounds which have economic significance.
Nevertheless, cellulases have a potential application for hydrolyzing cellulosic biomass in biorefining industries which are based on agro-industrial wastes. The bacterial strain Arthrobacter woluwensis TDS9 reported in this study was capable of utilizing lignocellulose substrates including paper mill sludge. This work acts as a step towards for further study on bio-refinery feedstocks that are composed of low or negative cost biomass.
A potential cellulase-producing bacterial strain isolated from the soil was characterized and identified as Arthrobacter woluwensis TDS9. This efficient cellulase producing bacterial strain TDS9 showed a potential activity on the biotransformation of cellulosic biomass as well as primary sludge of paper mill to produce value-added product (reducing sugar). Moreover, finding an eco-friendly method for negative-cost biomass conversion remains an important goal in bioremediation, and implementing microorganisms as biocatalyst is an expressively promising greener method. Therefore, an increased (433.33 μg/mL) sugar production was attained from negative-cost biomass (paper mill sludge) using the newly isolated strain A. woluwensis TDS9. It is demonstrated that the strain A. woluwensis TDS9 able to utilize paper mill waste (primary sludge) derived from pulp production process has a high cellulose utilization rate and high product yield of reducing sugar. Therefore, further studies with our newly isolated strain TDS9 are granted to boost the utilization rate of cellulosic biomass and the production of reducing sugar. Our result also showed that it is possible to discover novel microbial strains to produce value-added bioproducts using negative cost biomass paper mill sludge. The present study also introduces the novel strain A. woluwensis TDS9 as a potential biocatalyst for the saccharification of cellulolytic biomass, which represent the economic significance for biomass bioconversion industries. Thus, the bacterial strain TDS9 could be a potential candidate for cellulase enzyme production.
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Carboxy methyl cellulose
Carboxy methyl cellulase
Rotation per minute
International Union of Pure and Applied Chemistry
Sodium dodecyl sulfate
Ethylenediamine tetraacetic acid
Moon RJ, Martini A, Nairn J, Simonsen J, Youngblood J (2011) Cellulose nanomaterials review: Structure, properties and nanocomposites. Chem Soc Rev 40:3941–3994. https://doi.org/10.1039/c0cs00108b
Klemm D, Heublein B, Fink HP, Bohn A (2005) Cellulose: Fascinating biopolymer and sustainable raw material. Angew Chem Int Ed 44:3358–3393. https://doi.org/10.1002/anie.200460587
Lee SB, Kim IH, Ryu DDY, Taguchi H (1983) Structural properties of cellulose and cellulase reaction mechanism. Biotechnol Bioeng 25:33–51. https://doi.org/10.1002/bit.260250105
Rabinovich ML, Melnick MS, Bolobova AV (2002) The structure and mechanism of action of cellulolytic enzymes. Biochem 67:850–871. https://doi.org/10.1023/A:1019958419032
Kim IJ, Lee HJ, Choi IG, Kim KH (2014) Synergistic proteins for the enhanced enzymatic hydrolysis of cellulose by cellulase. Appl Microbiol Biotechnol 98:8469–8480. https://doi.org/10.1007/s00253-014-6001-3
Parsiegla G, Belaïch A, Belaïch JP, Haser R (2002) Crystal structure of the cellulase Ce19M enlightens structure/function relationships of the variable catalytic modules in glycoside hydrolases. Biochemistry 41:11134–11142. https://doi.org/10.1021/bi025816m
Jayasekara S, Ratnayake R (2019) Microbial Cellulases: An Overview and Applications. In: Cellulose. IntechOpen, London
McCarthy AJ (1987) Lignocellulose-degrading actinomycetes. FEMS Microbiol Rev 3:145–163. https://doi.org/10.1111/j.1574-6968.1987.tb02456.x
Enari TM, Markkanen P (2005) Production of cellulolytic enzymes by fungi. Adv Biochem Eng 5:1–24. https://doi.org/10.1007/bfb0008739
Ariffin H, Abdullah N, Umi Kalsom MS, Shirai Y, Hassan M (2006) Production and characterization of cellulase by Bacillus pumilus EB3. Int J Eng Technol 3:47–53
Rabinovich ML, Melnik MS, Bolobova AV (2002) Microbial cellulases (review). Appl Biochem Microbiol 38:305–321. https://doi.org/10.1023/A:1016264219885
Cantarel BI, Coutinho PM, Rancurel C, Bernard T, Lombard V, Henrissat B (2009) The carbohydrate-active enzymes database (CAZy): an expert resource for glycogenomics. Nucleic Acids Res 37:233–238. https://doi.org/10.1093/nar/gkn663
Enari TM, Niku-Paavola ML (1987) Enzymatic hydrolysis of cellulose: is the current theory of the mechanisms of hydrolysis valid? Crit Rev Biotechnol 5:67–87. https://doi.org/10.3109/07388558709044153
Reese ET (1956) Enzymatic hydrolysis of cellulose. Appl Microbiol 4:39–45. https://doi.org/10.1128/am.4.1.39-45.1956
Wang M, Li Z, Fang X, Wang L, Qu Y (2012) Cellulolytic enzyme production and enzymatic hydrolysis for second-generation bioethanol production. Adv Biochem Eng Biotechnol 128:1–24. https://doi.org/10.1007/10_2011_131
Liu L, Huang WC, Liu Y, Li M (2021) Diversity of cellulolytic microorganisms and microbial cellulases. Int Biodeter Biodegr 163:105277. https://doi.org/10.1016/j.ibiod.2021.105277
Xie G, Bruce DC, Challacombe JF, Chertkov O, Detter JC, Gilna P, Han CS, Lucas S, Misra M, Myers GL, Richardson P, Tapia R, Thayer N, Thompson LS, Brettin TS, Henrissat B, Wilson DB, McBride MJ (2007) Genome sequence of the cellulolytic gliding bacterium Cytophaga hutchinsonii. Appl Environ Microbiol 73:3536–3546. https://doi.org/10.1128/AEM.00225-07
Ioelovich M (2014) Waste paper as promising feedstock for production of biofuel. J Sci Res Rep 3:905–916. https://doi.org/10.9734/jsrr/2014/8025
Hawrelak M, Bennett E, Metcalfe C (1999) The environmental fate of the primary degradation products of alkylphenol ethoxylate surfactants in recycled paper sludge. Chemosphere 39:745–752. https://doi.org/10.1016/S0045-6535(99)00010-7
Sharma P, Singh SP (2021) Pollutants characterization and toxicity assessment of pulp and paper industry sludge for safe environmental disposal. In: Emerging Treatment Technologies for Waste Management. Springer Singapore, Singapore, pp 207–223
Kuokkanen T, Nurmesniemi H, Pöykiö R, Kujala K, Kaakinen J, Kuokkanen M (2008) Chemical and leaching properties of paper mill sludge. Chem Spec Bioavailab 20:111–122. https://doi.org/10.3184/095422908X324480
Geng X, Zhang SY, Deng J (2007) Characteristics of paper mill sludge and its utilization for the manufacture of medium density fiberboard. Wood Fiber Sci 39:345–351
Chen H, Han Q, Daniel K, Venditti R, Jameel H (2014) Conversion of industrial paper sludge to ethanol: fractionation of sludge and its impact. Appl Biochem Biotechnol 174:2096–2113. https://doi.org/10.1007/s12010-014-1083-z
Mahmood T, Elliott A (2006) A review of secondary sludge reduction technologies for the pulp and paper industry. Water Res 40:2093–2112. https://doi.org/10.1016/j.watres.2006.04.001
Cao Y, Tan H (2002) Effects of cellulase on the modification of cellulose. Carbohydr Res 337:1291–1296. https://doi.org/10.1016/S0008-6215(02)00134-9
Arora A, Nandal P, Singh J, Verma ML (2020) Nanobiotechnological advancements in lignocellulosic biomass pretreatment. Mater Sci Energy Technol 3:308–318. https://doi.org/10.1016/j.mset.2019.12.003
Raud M, Kikas T, Sippula O, Shurpali NJ (2019) Potentials and challenges in lignocellulosic biofuel production technology. Renew Sustain Energy Rev 111:44–56. https://doi.org/10.1016/j.rser.2019.05.020
Cheng JJ, Timilsina GR (2011) Status and barriers of advanced biofuel technologies: a review. Renew Energy 36:3541–3549. https://doi.org/10.1016/j.renene.2011.04.031
Kim J, Grate JW, Wang P (2006) Nanostructures for enzyme stabilization. Chem Eng Sci 61:1017–1026. https://doi.org/10.1016/j.ces.2005.05.067
Singh K, Mishra A, Sharma D, Singh K (2018) Nanotechnology in enzyme immobilization: an overview on enzyme immobilization with nanoparticle matrix. Curr Nanosci 15:234–241. https://doi.org/10.2174/1573413714666181008144144
Cipolatti EP, Valério A, Henriques RO, Moritz DE, Ninow JL, Freire DMG, Manoel EA, Fernandez-Lafuente R, De Oliveira D (2016) Nanomaterials for biocatalyst immobilization-state of the art and future trends. RSC Adv 6:104675–104692. https://doi.org/10.1039/c6ra22047a
Garlapati VK, Chandel AK, Kumar SPJ, Sharma S, Sevda S, Ingle AP, Pant D (2020) Circular economy aspects of lignin: towards a lignocellulose biorefinery. Renew Sustain Energy Rev 130:109977. https://doi.org/10.1016/j.rser.2020.109977
Elumalai S, Agarwal B, Runge TM, Sangwan RS (2018) Advances in transformation of lignocellulosic biomass to carbohydrate-derived fuel precursors, pp 87–116
Ebrahimzadeh MA, Naghizadeh A, Mohammadi-Aghdam S, Khojasteh H, Ghoreishi SM, Mortazavi-Derazkola S (2020) Enhanced catalytic and antibacterial efficiency of biosynthesized Convolvulus fruticosus extract capped gold nanoparticles (CFE@AuNPs). J Photochem Photobiol B Biol 209:111949. https://doi.org/10.1016/j.jphotobiol.2020.111949
Shirzadi-Ahodashti M, Ebrahimzadeh MA, Ghoreishi SM, Naghizadeh A, Mortazavi-Derazkola S (2020) Facile and eco-benign synthesis of a novel MnFe2O4@SiO2@Au magnetic nanocomposite with antibacterial properties and enhanced photocatalytic activity under UV and visible-light irradiations. Appl Organomet Chem 34:e5614. https://doi.org/10.1002/aoc.5614
Naghizadeh A, Mizwari ZM, Ghoreishi SM, Lashgari S, Mortazavi-Derazkola S, Rezaie B (2021) Biogenic and eco-benign synthesis of silver nanoparticles using jujube core extract and its performance in catalytic and pharmaceutical applications: removal of industrial contaminants and in-vitro antibacterial and anticancer activities. Environ Technol Innov 23:101560. https://doi.org/10.1016/j.eti.2021.101560
McGinnis S, Madden TL (2004) BLAST: at the core of a powerful and diverse set of sequence analysis tools. Nucleic Acids Res 32:W20–W25. https://doi.org/10.1093/nar/gkh435
Morgulis A, Coulouris G, Raytselis Y, Madden TL, Agarwala R, Schäffer AA (2008) Database indexing for production MegaBLAST searches. Bioinformatics 24:1757–1764. https://doi.org/10.1093/bioinformatics/btn322
Kumar S, Stecher G, Li M, Knyaz C, Tamura K (2018) MEGA X: molecular evolutionary genetics analysis across computing platforms. Mol Biol Evol 35:1547–1549
Saitou N, Nei M (1987) The neighbor-joining method: a new method for reconstructing phylogenetic trees. Mol Biol Evol 4:406–425. https://doi.org/10.1093/oxfordjournals.molbev.a040454
Simonsen M, Mailund T, Pedersen CNS (2011) Inference of large phylogenies using neighbour-joining. In: Communications in Computer and Information Science, pp 334–344
Sneath P, Mai N, Sharpe MA, Holts J (1986) Bergey’s manual systematic bacteriology. The Williams and Wilkins Company, Baltimore
Gonalves C, Rodriguez-Jasso RM, Gomes N, Teixeira JA, Belo I (2010) Adaptation of dinitrosalicylic acid method to microtiter plates. Anal Methods 2:2046–2048. https://doi.org/10.1039/c0ay00525h
Yin JX, Hong LU, Xie Q, Ding JL, Ni-Hang LI (2007) A study on rapid colorimetric determination of water soluble total sugar, reducing sugar and starch in tobacco with 3,5-dinitrosalicylic acid. J. Yunnan Agric. Univ https://en.cnki.com.cn/Article_en/CJFDTotal-YNDX200706012.htm. Accessed 14 Dec 2021
Miller GL (1959) Use of dinitrosalicylic acid reagent for determination of reducing sugar. Anal Chem 31:426–428. https://doi.org/10.1021/ac60147a030
Lowry OH, Rosebrough NJ, Farr AL, Randall RJ (1951) Protein measurement with the Folin phenol reagent. J Biol Chem 193:265–275. https://doi.org/10.1016/s0021-9258(19)52451-6
Waterborg JH (2009) The lowry method for protein quantitation. In: Walker JM (ed) The Protein Protocols Handbook. Springer Protocols Handbooks. Humana Press, Totowa. https://doi.org/10.1007/978-1-59745-198-7_2
Colombatto D, Beauchemin KA (2003) A proposed methodology to standardize the determination of enzymic activities present in enzyme additives used in ruminant diets. Can J Anim Sci 83:559–568. https://doi.org/10.4141/a03-016
Zainudin MHM, Mustapha NA, Hassan MA, Bahrin EK, Tokura M, Yasueda H, Shirai Y (2019) A highly thermostable crude endoglucanase produced by a newly isolated Thermobifida fusca strain UPMC 901. Sci Rep 9:1–8. https://doi.org/10.1038/s41598-019-50126-y
Sohag MMH, Hasan MM, Ahmed J, Daud SNA, Alam MK, Amin MR, Hoq MM, Azad AK (2016) Production and partial characterization of cellulase from pseudomonas isolates obtained from cow dung and municipal solid wastes. Bangladesh J Microbiol 30:11–16. https://doi.org/10.3329/bjm.v30i1-2.28447
Laemmli U (1970) Cleavage of structural proteins during the assembly of the head of bacteriophage T4. Nature 227:680–685
Brunelle JL, Green R (2014) One-dimensional SDS-polyacrylamide gel electrophoresis (1D SDS-PAGE). In: Methods in Enzymology, pp 151–159
Ghose TK (1987) Measurement of cellulase activities. Pure Appl Chem 59:257–268. https://doi.org/10.1351/pac198759020257
Dashtban M, Maki M, Leung KT, Mao C, Qin W (2010) Cellulase activities in biomass conversion: measurement methods and comparison. Crit Rev Biotechnol 30:302–309
Wood TM, Bhat KM (1988) Methods for measuring cellulase activities. Methods Enzymol 160:87–112. https://doi.org/10.1016/0076-6879(88)60109-1
Sternberg D, Mandels GR (1979) Induction of cellulolytic enzymes in Trichoderma reesei by sophorose. J Bacteriol 139:761–769. https://doi.org/10.1128/jb.139.3.761-769.1979
Worthington K (2011) Worthington enzyme manual. Worthington Biochemical Corporation, Lakewood
Singh A, Bajar S, Devi A, Pant D (2021) An overview on the recent developments in fungal cellulase production and their industrial applications. Bioresour Technol Rep 14. https://doi.org/10.1016/j.biteb.2021.100652
Bhati N, Shreya SAK (2021) Cost-effective cellulase production, improvement strategies, and future challenges. J Food Process Eng 44. https://doi.org/10.1111/jfpe.13623
Singhania RR, Ruiz HA, Awasthi MK, Di DC, Chen CW, Patel AK (2021) Challenges in cellulase bioprocess for biofuel applications. Renew Sustain Energy Rev 151. https://doi.org/10.1016/j.rser.2021.111622
Barbosa FC, Silvello MA, Goldbeck R (2020) Cellulase and oxidative enzymes: new approaches, challenges and perspectives on cellulose degradation for bioethanol production. Biotechnol Lett 42:875–884. https://doi.org/10.1007/s10529-020-02875-4
Sadhu S (2013) Cellulase production by bacteria: a review. Br Microbiol Res J 3:235–258. https://doi.org/10.9734/bmrj/2013/2367
Yan S, Sun X, Zhang W, Zhu L (2019) Isolation, identification and cellulase-producing condition optimization of Bacillus subtilis Q3 strain. AIP Conf Proc 2110. https://doi.org/10.1063/1.5110798
Premalatha N, Gopal NO, Jose PA, Anandham R, Kwon SW (2015) Optimization of cellulase production by Enhydrobacter sp. ACCA2 and its application in biomass saccharification. Front Microbiol 6:1046. https://doi.org/10.3389/fmicb.2015.01046
Mmango-Kaseke Z, Okaiyeto K, Nwodo UU, Mabinya LV, Okoh AI (2016) Optimization of cellulase and xylanase production by Micrococcus species under submerged fermentation. Sustain 8:1–15. https://doi.org/10.3390/su8111168
Vinet L, Zhedanov A (2011) A “missing” family of classical orthogonal polynomials. J Phys A Math Theor 44:50–59. https://doi.org/10.1088/1751-8113/44/8/085201
Nathan VK, Rani ME, Rathinasamy G, Dhiraviam KN, Jayavel S (2014) Process optimization and production kinetics for cellulase production by Trichoderma viride VKF3. Springerplus 3:92. https://doi.org/10.1186/2193-1801-3-92
Nkohla A, Okaiyeto K, Olaniran A, Nwodo U, Mabinya L, Okoh A (2017) Optimization of growth parameters for cellulase and xylanase production by Bacillus species isolated from decaying biomass. J Biotech Res 8:33–47
Stutzenberger FJ (1971) Cellulase production by Thermomonospora curvata isolated from municipal solid waste compost. Appl Microbiol 22:147–152
Liang YL, Zhang Z, Wu M, Wu Y, Feng JX (2014) Isolation, screening, and identification of cellulolytic bacteria from natural reserves in the subtropical region of China and optimization of cellulase production by Paenibacillus terrae ME27-1. Biomed Res Int 2014:512497. https://doi.org/10.1155/2014/512497
Abu-Gharbia MA, El-Sawy NM, Nasr AM, Zedan LA (2018) Isolation, optimization and characterization of cellulases and hemicellulases from bacillus cereus LAZ 518 isolated from cow dung using corn cobs as lignocellulosic waste. J Pharm Appl Chem 4:67–79. https://doi.org/10.18576/jpac/040201
Da Vinha FNM, Gravina-Oliveira MP, Franco MN, MacRae A, Da Silva Bon EP, Nascimento RP, Coelho RRR (2011) Cellulase production by streptomyces viridobrunneus SCPE-09 using lignocellulosic biomass as inducer substrate. Appl Biochem Biotechnol 164:256–267. https://doi.org/10.1007/s12010-010-9132-8
Sheng P, Huang S, Wang Q, Wang A, Zhang H (2012) Isolation, screening, and optimization of the fermentation conditions of highly cellulolytic bacteria from the hindgut of Holotrichia parallela larvae (Coleoptera: Scarabaeidae). Appl Biochem Biotechnol 167:270–284. https://doi.org/10.1007/s12010-012-9670-3
Geetha K, Gunasekaran P (2010) Optimization of nutrient medium containing agricultural waste for xylanase production by Bacillus pumilus B20. Biotechnol Bioprocess Eng 15:882–889. https://doi.org/10.1007/s12257-009-3094-0
Kim HJ, Lee YJ, Gao W, Chung CH, Son CW, Lee JW (2011) Statistical optimization of fermentation conditions and comparison of their influences on production of cellulases by a psychrophilic marine bacterium, psychrobacter aquimaris LBH-10 using orthogonal array method. Biotechnol Bioprocess Eng 16:542–548. https://doi.org/10.1007/s12257-010-0457-5
Wang H, Zhai L, Geng A (2020) Enhanced cellulase and reducing sugar production by a new mutant strain Trichoderma harzianum EUA20. J Biosci Bioeng 129:242–249. https://doi.org/10.1016/j.jbiosc.2019.08.016
da Silva DP, Lima DJ, Robl D, Rabelo SC, Farinas CS, da Cruz Pradella JG (2016) Enhanced cellulase production by Trichoderma harzianum by cultivation on glycerol followed by induction on cellulosic substrates. J Ind Microbiol Biotechnol 43:617–626. https://doi.org/10.1007/s10295-016-1744-8
McDermid AS, McKee AS, Marsh PD (1988) Effect of environmental pH on enzyme activity and growth of Bacteroides gingivalis W50. Infect Immun 56:1096–1100. https://doi.org/10.1128/iai.56.5.1096-1100.1988
Patagundi BI, Shivasharan CT, Kaliwal BB (2002) Isolation and characterization of pretense producing bacteria from soil. J Korean Soc Food Sci Nutr 31:754–759. https://doi.org/10.3746/jkfn.2002.31.5.754
Giese EC, Dussán KJ, Pierozzi M, Chandel AK, Pagnocca FC, Da Silva SS (2017) Cellulase production by Trichosporon laibachii. Orbital Electron J Chem 9. https://doi.org/10.17807/orbital.v9i4.1024
Karlsson J, Saloheimo M, Siika-Aho M, Tenkanen M, Penttilä M, Tjerneld F (2001) Homologous expression and characterization of Cel61A (EG IV) of Trichoderma reesei. Eur J Biochem 268:6498–6507. https://doi.org/10.1046/j.0014-2956.2001.02605.x
Huang S, Deng G, Yang Y, Wu Z, Wu L (2015) Optimization of endoglucanase production from a novel bacterial isolate, Arthrobacter sp. HPG166 and characterization of its properties. Braz Arch Biol Technol 58:692–701. https://doi.org/10.1590/S1516-89132015050256
Deka D, Bhargavi P, Sharma A, Goyal D, Jawed M, Goyal A (2011) Enhancement of cellulase activity from a new strain of bacillus subtilis by medium optimization and analysis with various cellulosic substrates. Enzyme Res 2011:1–8. https://doi.org/10.4061/2011/151656
Lokapirnasari WP, Nazar DS, Nurhajati T, Supranianondo K, Yulianto AB (2015) Production and assay of cellulolytic enzyme activity of Enterobacter cloacae WPL 214 isolated from bovine rumen fluid waste of Surabaya abbatoir, Indonesia. Vet World 8:367–371. https://doi.org/10.14202/vetworld.2015.367-371
Guruk M, Karaaslan M (2020) Production and biochemical characterization of cellulase enzyme by trichoderma strains from harran plain. Int J Life Sci Biotechnol. https://doi.org/10.38001/ijlsb.756818
Shivanand P, Mugeraya G, Kumar A (2013) Utilization of renewable agricultural residues for the production of extracellular halostable cellulase from newly isolated halomonas sp. strain PS47. Ann Microbiol 63:1257–1263. https://doi.org/10.1007/s13213-012-0583-8
Hsieh CC, Cannella D, Jørgensen H, Felby C, Thygesen LG (2015) Cellobiohydrolase and endoglucanase respond differently to surfactants during the hydrolysis of cellulose. Biotechnol Biofuels 8:52. https://doi.org/10.1186/s13068-015-0242-y
Abdel-Fatah OM, Hassan MM, Elshafei AM, Haroun BM, Atta HM, Othman AM (2012) Physiological studies on carboxymethyl cellulase formation by Aspergillus terreUS DSM 826. Braz J Microbiol 43:1–11. https://doi.org/10.1590/s1517-83822012000100001
Rao M, Gaikwad S, Mishra C, Deshpande V (1988) Induction and catabolite repression of cellulase in Penicillium funiculosum. Appl Biochem Biotechnol 19:129–137. https://doi.org/10.1007/BF02921478
Magnelli P, Forchiassin F (1999) Regulation of the cellulase complex production by Saccobolus saccoboloides: induction and repression by carbohydrates. Mycologia 91:359–364. https://doi.org/10.1080/00275514.1999.12061027
Maki ML, Broere M, Leung KT, Qin W (2011) Characterization of some efficient cellulase producing bacteria isolated from paper mill sludges and organic fertilizers. Int J Biochem Mol Biol 2:146–154
We thank Dr. Nur Alam, Biorefining Research Institute, Lakehead University, Canada, for providing the sample paper mill sludge.
This research study was funded by the University of Chittagong, Bangladesh.
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Das, T., Ali, F. & Rahman, M.S. Cellulase activity of a novel bacterial strain Arthrobacter woluwensis TDS9: its application on bioconversion of paper mill sludge. J Genet Eng Biotechnol 20, 87 (2022). https://doi.org/10.1186/s43141-022-00373-w
- Negative-cost biomass
- Paper mill sludge
- Biological treatment