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Screening of cellulolytic bacteria from rotten wood of Qinling (China) for biomass degradation and cloning of cellulases from Bacillus methylotrophicus

Abstract

Background

Cellulosic biomass degradation still needs to be paid more attentions as bioenergy is the most likely to replace fossil energy in the future, and more evaluable cellulolytic bacteria isolation will lay a foundation for this filed. Qinling Mountains have unique biodiversity, acting as promising source of cellulose-degrading bacteria exhibiting noteworthy properties. Therefore, the aim of this work was to find potential cellulolytic bacteria and verify the possibility of the cloning of cellulases from the selected powerful bacteria.

Results

In present study, 55 potential cellulolytic bacteria were screened and identified from the rotten wood of Qinling Mountains. Based on the investigation of cellulase activities and degradation effect on different cellulose substrates, Bacillus methylotrophicus 1EJ7, Bacillus subtilis 1AJ3 and Bacillus subtilis 3BJ4 were further applied to hydrolyze wheat straw, corn stover and switchgrass, and the results suggested that B. methylotrophicus 1EJ7 was the most preponderant bacterium, and which also indicated that Bacillus was the main cellulolytic bacteria in rotten wood. Furthermore, scanning electron microscopy (SEM) and X-ray diffraction analysis of micromorphology and crystallinity of wheat straw also verified the significant hydrolyzation. With ascertaining the target sequence of cellulase β-glucosidase (243 aa) and endoglucanase (499 aa) were successfully heterogeneously cloned and expressed from B. methylotrophicus 1EJ7, and which performed a good effect on cellulose degradation with enzyme activity of 1670.15 ± 18.94 U/mL and 0.130 ± 0.002 U/mL, respectively. In addition, based on analysis of amino acid sequence, it found that β-glucosidase were belonged to GH16 family, and endoglucanase was composed of GH5 family catalytic domain and a carbohydrate-binding module of CBM3 family.

Conclusions

Based on the screening, identification and cellulose degradation effect evaluation of cellulolytic bacteria from rotten wood of Qinling Mountains, it found that Bacillus were the predominant species among the isolated strains, and B. methylotrophicus 1EJ7 performed best on cellulose degradation. Meanwhile, the β-glucosidase and endoglucanase were successfully cloned and expressed from B. methylotrophicus for the first time, which provided new materials of both strain and the recombinant enzymes for the study of cellulose degradation and its application in industry.

Background

Cellulosic biomass (composed of cellulose, lignin and hemicellulose) is one of the most abundant renewable resources, which is also considered as a potential and promising raw material for future energy production [1]. Cellulose has been reported as the critical component that can be converted into various value-added products: e.g. ethanol, 5-hydroxymethylfurfural (HMF), levulinic acid, butanol, alkanes, hexane, succinic acid, ethyl lactate, and other chemicals [2,3,4], and no matter which procedure conducted, cellulose should be firstly hydrolyzed to glucose, and then various bio- or chemical processes can be really carried out. Therefore, the degradation of cellulosic material has attracted huge attentions for the improvement of the efficiency and cleaning process.

There were various methods proposed to hydrolyze cellulose, including acid-activated montmorillonite catalysts, steam explosion, acid, alkaline, enzymatic hydrolysis and microbiological methods [5,6,7]. In view of protecting of environment and saving energy, the enzymatic and microbiological methods were prioritized to be practically applied, and what’s more, both of which were associated with microorganisms, such as fungi and bacteria [5]. Indeed, fungi exhibit a strong ability to secret considerable extracellular enzymes including multi-cellulases, which was the main reason why numerous studies had been conducted on fungi producing cellulases, such as Trichoderma reesei RUT-C30 [8], Trichoderma koningiopsis FCD3–1 [9], and Melanoporia sp. CCT 7736 [10]. However, it has also been found that the culture and genetically modification of fungi were relatively more difficult to achieve than bacteria, which seriously hindered the practical application of fungi and fungi-producing cellulases to celluloses hydrolyzation [11, 12]. In general, bacteria were commonly considered as a powerful tool for functional modification or genomic operation, for instance, the heterogeneous cloning and expressing of single cellulase or recombinant cellulases. Unfortunately, the library of bacteria that possessed powerful activity to hydrolyze cellulose was not sufficient, which partly limited the study and application of the cellulolytic bacteria. Therefore, lots of researches about screening of cellulolytic bacteria had been conducted and reported, such as Bacillus sp. BS-5 [13], Bacillus licheniformis 2D55 [14], Bacillus subtilis BY-4 [15], Paenibacillus chitinolyticus CKS1 [16], Ochrobactrum sp K38 [17], and Clostridium thermocellum [18], which also suggested that various species of bacteria from different origins should be screened and highlighted.

The Qinling Mountains (32°30′N-34°45′N and 104°30′E-112°45′E) are located in the center of China and has 1500 km in length, which act as a crucial geographic demarcation line separating semi-arid area and humid regions in China [19]. It is well known that Qinling Mountains possess the unique climate, plants, and microorganism resource. Hence, rotten woods originating from Qinling Mountains contains various of biomass degrading microorganisms, which provides good materials for the screening of valuable bacteria for lignocellulose degradation. Consequently, in the present study, bacteria with the capability of cellulose degradation were screened and identified from rotten woods of Qinling Mountains. Subsequently, cellulase activities were assayed and the strains were inoculated with the wheat straw, corn stover and switchgrass to investigate the degradation effect on lignocellulosic biomass. Furthermore, for the purpose to verify the possibility of the heterologous expression for the cellulase from B. methylotrophicus 1EJ7, the cloning and expression of the proposed enzymes were conducted. Based on the target sequence exploring in National Center for Biotechnology Information (NCBI) database, β-glucosidase and endoglucanase with food cellulase activity were successfully cloned and expressed on the pET-28a(+) plasmid in E.coli BL21 (DE3), which provide valuable materials for the further study about cellulase in engineering modifications and application to industry.

Results

Isolation and identification of cellulolytic bacteria

A total of 81 strains were isolated from five rotten wood samples, in which 8, 17, 19, 15 and 22 isolates were obtained from weed tree, red birch, poplar, alpine rhododendron and willow, respectively. Meanwhile, based on “diameters ratio between clear zone and strain” during the investigation by Congo red method (Additional file 1: Figure S1) and the growth of strains in the process of subculture, 55 cellulolytic strains were finally selected for the further study. In addition, it needed to be mentioned that strains named as B. subtilis 1CJ1 and Bacillus sp. 1CJ4 had the largest diameters of clear zone more than 25 mm, and the largest value of “diameters ratio between clear zone and strain” was 3.71 belonged to Bacillus sp. 3AJ7 (Additional file 2: Table S2).

The isolated strains were identified according to their 16S rRNA gene, after which phylogenetic tree was established as shown in Fig. 1. Results indicated that the strains could be classified into Bacillus subtilis, Bacillus sp., Pseudomonas aeruginosa, Bacillus licheniformis, Bacillus methylotrophicus and Bacillus megaterium, which suggested that the Bacillus might be the predominant strains possessing the cellulose degradation activity in the rotten wood.

Fig. 1
figure1

Phylogenetic tree and strains distribution of cellulosic bacteria. a Circular maximum likelihood phylogenetic tree of bacterial of 16S rDNA sequence. The tree was constructed in iTOL. b Strains distribution. a and b with the same color band of different species

Cellulase activities and hydrolysis capability

The isolated strains were inoculated into sole carbon source medium for 48 h at 37 °C under 120 rpm. Reducing sugar concentration and cellulase activities were investigated and shown in Fig. 2 as a heat map which obviously indicated the relationship between bacteria and the cellulase activity as well as the production of cellulose degradation (reducing sugar content). In addition, the detail results were supplied in the Additional file 3: Table S3.

Fig. 2
figure2

Heat map of reducing sugar production and enzyme activities

The crude enzyme extracts were collected to determine reducing sugar content and cellulase activities. The maximum reducing sugar concentration was observed in CMC-Na medium by B. subtilis 1AJ3 of 4.83 mg/100 mL, followed by B. subtilis 1BJ4 of 4.54 mg/100 mL and B. subtilis 1BJ6 of 4.47 mg/100 mL. Compared with CMC-Na medium, a maximum production of reducing sugar content (1.61 mg/100 mL) was obtained by B. subtilis 3BJ7 in Avicel medium. The results showed that strains selected from CMC-Na medium had a higher enzyme activity than that selected from Avicel. In addition, B. subtilis 1BJ4 had both the highest FPase activity (0.0133 U/mL) and CMCase activity (0.0368 U/mL), while B. licheniformis 3EJ7 had the highest Avicelase activity of 0.010 U/mL. For the majority of strains, the results were coincided with the general sense that strains selected from CMC-Na always had a high CMCase activity, while that from Avicel had a high Avicelase activity. It was also interesting to find that strains processing both CMCase activities and Avicelase activities did not appear in present study. For example, B. subtilis 1BJ4 had the highest CMCase activity, but it didn’t exhibit Avicelase activity, which was possibly explained by the fact that different strains might produce different cellulases under the same or different carbon source [20]. Interestingly, although B. subtilis 3CJ6 had the highest Avicelase activity, and both other two enzyme activities were tested, no reducing sugar was detected.

From the heat map, it found that the difference of intergeneric impacted the cultivation process and which led to the differences in reducing sugar production and cellulase activities. As the results shown, B. subtilis strains possessed the advantages in secreting of cellulases, which led to the high reducing sugar content, FPase and CMCase activity. Meanwhile, B. methylotrophicus and B. licheniformis performed relatively well just in the reducing sugar content. In addition, bacteria isolated from CMC-Na as solo carbon source medium had the higher FPase and CMCase activities than that from Avicel medium.

According to the reducing sugar content and cellulase activities, eight strains were further selected as B. subtilis 1AJ2, B. subtilis 1AJ3, B. subtilis 1BJ4, B. methylotrophicus 1EJ7, B. subtilis 3BJ4, B. subtilis 3CJ6, B. subtilis 3CJ8 and B. methylotrophicus 3EJ7, which would be applied to carbon sources to evaluate the cellulose degradation activity.

Reducing sugar production and cellulase activities in different carbon sources

The selected eight strains were cultured with different carbon sources: wheat straw, corn stover, switchgrass, Avicel and CMC-Na (Fig. 3).

Fig. 3
figure3

Reducing sugar and cellulase activities of eight strains in different carbon source medium. a Reducing sugar content; b FPase; c CMCase; d Avicelase

Each strain was separately inoculated into the medium with five different carbon sources (wheat straw, corn stover, switchgrass, Avicel, and CMC-Na) for 48 h with 6% seed inoculation. Figure 3a shows the reducing sugar concentration obtained from different carbon sources by the treatment with each strain. B. subtilis 1AJ3 and B. methylotrophicus 1EJ7 showed strong potential in the producing of reducing sugar, even in the lignocellulosic biomass without any other pretreatments (wheat straw, corn stover, and switchgrass), which then followed by B. subtilis 3BJ4 and B. subtilis 1AJ2. It also found that the strains showed similar FPase and CMCase activities (Fig. 3b and Fig. 3c) in different carbon sources. Specifically, only B. subtilis 1AJ3 and B. subtilis 3BJ4 produced Avicelase in all medium, and B. subtilis 1AJ2 only produced Avicelase in CMC-Na medium. Meanwhile, other strains produced Avicelase in three or more carbon sources. Accordingly, based on the reducing sugar content, cellulase activities and carbon source type, three strains (B. subtilis 1AJ3, B. methylotrophicus 1EJ7, and B. subtilis 3BJ4) were selected for the further study.

Pretreatment of lignocellulosic biomass

Three strains of B. subtilis 1AJ3, B. methylotrophicus 1EJ7 and B. subtilis 3BJ4 were used to pretreat wheat straw, switchgrass and corn stover separately or mixed-up. After sterilization at 121 °C for 20 min, the initial reducing sugars concentration were 136.34 mg/100 mL, 109.46 mg/100 mL, and 39.16 mg/100 mL in the medium of corn stover, switchgrass and wheat straw, respectively.

The reducing sugar content in all samples tended to be stable (Fig. 4) after culturing 36 h, and the highest sugar content of 95 mg/100 mL was obtained by B. methylotrophicus 1EJ7 in switchgrass. Meanwhile, 73 mg/100 mL in wheat straw and 72 mg/mL in corn stover were also obtained by B. methylotrophicus 1EJ7, which also indicated that no synergistic effect was observed in the pretreatment of the mixture.

Fig. 4
figure4

Reducing sugar production by different strains in 7% wheat straw, corn stover and switchgrass for 72 h. SEM of wheat straw before (a) and after (b) 72 h fermentation by B. methylotrophicus 1EJ7. X-ray of untreated wheat straw and fermented by B. methylotrophicus 1EJ7 was showed in c

SEM test was benefit for understanding the process of the straw degradation caused by the proposed strains. As one of the major agricultural waste in China, wheat straw has a relatively denser lignocellulosic structure, and which was selected as the sample to be investigated after the hydrolyzation by B. methylotrophicus 1EJ7. It was found that the surface (Fig. 4a) of the wheat straw particles was dramatically changed (Fig. 4b) after bacteria pretreatment. Specifically, it was obviously found that the smooth surface of wheat straw particles was destroyed to form numerous holes and lots of bacteria were observed as adhering on the surface. Therefore, the sunken tiny holes suggested that the bacteria processed the cellulase activity and which initially destroyed the surface structure of wheat straw. In addition, the similar phenomenon was also observed in corn stover hydrolysis [21].

As the cellulose content affected the degree of crystallinity in various of plant biomass, the decrease of crystallinity is also an index of the decrease of cellulose content or the destruction of the cellulose structure, therefore, which was also used to evaluate the efficiency of the pretreatment [22]. Hence, X-ray diffraction was used to analyze crystallinity of wheat straw samples in the present study. The results indicated that the Cr I of wheat straw decreased from 41.57 to 40.52 (Fig. 4c) after the pretreatment, which also verified the degradation of wheat straw caused by the pretreatment of B. methylotrophicus 1EJ7.

Cellulases clone and expression

The target genes of β-glucosidase and endoglucanase were 732 bp and 1500 bp, respectively, and which were successfully cloned. In addition, universal primer T7/T7er was utilized to amplify the two recombinant plasmids (pET-28a-Bgl and pET-28a-Egl), and then PCR products were tested for the complete sequences. Thereafter, heterologous expressions of the proposed two genes in E. coli BL21 (DE3) were carried out to obtain the enzymes. As shown in SDS-PAGE, two cellulases were both successfully expressed in E.coli BL21 (DE3), and the Mws were tested as 28.5 kDa and 56.3 kDa (Fig. 5), respectively. Bgl and Egl crude cellulase activities were 1670.15 ± 18.94 U/mL and 0.130 ± 0.002 U/mL, respectively (Additional file 4: Table S4).

Fig. 5
figure5

Agarose gel electrophoresis and SDS-PAGE of Bgl and Egl. a 1% Agarose gel electrophoresis use universal primer of T7/T7er by the recombined plasmid. b 15% SDS-PAGE for expression of Bgl and Egl

The results of domains analysis showed that Bgl belonged to GH16 family (Additional file 5: Figure S5), and Egl contained two domains as catalytic domain (CD) and carbohydrate-binding module (CBM), which belonged to GH5 family and CBM3 family, respectively (Additional file 6: Figure S6).

Meanwhile, by blast on PDB (protein database) website, the highest identification of Bgl was endo-beta-1,3–1,4 glucanase (PDB id 3O5S_A) from Bacillus subtilis 168 with a similarity of 93.55%, and Egl was 94.92% similarity with endo-1,4-beta-glucanase (PDB id 3PZT_A) and 90.41% with CBM3 lacking the calcium-binding site (PDB id 2L8A_A) from B. subtilis 168. In addition, compared with Bgl sequence of Bacillus velezensis JTYP2, it was found that only four amino acids (70 M → V, 96 V → A, 156A → K, 204 N → T) were different with the Bgl in present study, and the predicted secondary structure didn’t obviously affect by these differences. It also indicated the Bgl of B. subtilis 168 showed more differences with the proposed Bgl as 22 amino acids were different (Additional file 7: Figure S7). For the Egl, the sequence analysis showed that it had a 96.6% similarity with the Egl of Bacillus velezensis JTYP2, and there are 51 different bases between the two sequences led to 17 different amino acids (27A → T, 31G → E, 52Q → R, 199P → I, 238S → F, 285 K → N, 316S → T, 331S → G, 332 N → T, 334S → L, 339A → G, 364S → R, 382 T → A, 404F → V, 411I → M, 414S → G, 440 K → T), in which most changes appeared on the carbohydrate-binding module (CBM) and the linked peptide [23], and all the changes of the amino acids didn’t significantly influent the secondary structure (Additional file 8: Figure S8).

Bioinformatics analysis and homology modeling

The recombined Bgl contains 251 amino acids included a His-tag with a molecular weight of 28.47 kDa. The computed pI was 6.79, and the negative GRAVY score (− 0.491) suggested that the protein might be hydrophilic. Bgl showed instability index and aliphatic index of 16.14 and 60.24, respectively. Correspondingly, the recombined Egl contained 507 amino acids including his-tag with a predicted molecular weight of 56.32 kDa, and the computed pI was 7.26 and the negative GRAVY score (− 0.616) suggested the Egl was a hydrophilic protein. In addition, Egl showed instability index and aliphatic index of 29.60 and 73.69, respectively, and instability index less than 40 also indicated that both the Bgl and Egl from B. methylotrophicus 1EJ7 was stable.

Bgl (Fig. 6a) and Egl (Fig. 6b) homology structural models were obtained by the I-TASSER. The information about the active site was obtained through superimposing 3D model structure of the Bgl with the template structure of cellulase from Paenibacillus macerans hybrid endo-1,3-1,4-beta-D-glucan 4-glucanohydrolase (PDB id 2AYH) [24], which provided accuracy of homology between two structures and also contributed to find the conserved active site residues. Active sites of Bgl were represented by 6 amino acid residues as Leu103, Phe105, Thr175, Asp179, Tyr188 and Asp236. The 35th to 242th amino acid domain of Bgl included a classical sandwich-like beta-jelly roll fold, and formed by two main, closely packed and curved antiparallel beta sheets, which led to a deep channel harboring the catalytic machinery. Bgl was found to be a catalytic sequence motif similar with GH16 family [23, 25], E-[ILV]-D-[IVAF]-[VILMF] (0, 1)-E, which was formed by amino acid 134th to 138th (EIDIE). The structural analysis of Egl showed that domains of CD and CBM, in which the catalytic domain had the critical TIM-barrel fold structure of GH5 family, consisting of 8 β-strands surrounded by 8 α-helices with the active site located at the cleft.

Fig. 6
figure6

3D structure prediction of Bgl (a) and Egl (b)

Discussions

The unique cellulolytic bacteria in rotten woods from the Qinling Mountains

Microbial biodegradation has been applied as an environmental-friendly method in cellulosic materials to produce various valuable compounds. Over the past decades, numerous cellulolytic microorganisms have been screened and characterized. In this study, it was found that the strains isolated from Qinling rotten wood distributed in a widely taxonomic coverage (e.g. Bacillus subtilis, Pseudomonas aeruginosa, Bacillus licheniformis, Bacillus methylotrophicus and Bacillus megaterium), in which Bacillus subtilis was found as the most abundant species.

Similar with the related studies, Bacillus strains were the dominant bacteria in rotten wood during the process of screening by LB as enrich medium, which might attribute to the robust enzymes secretory system of the B. subtilis strains [26, 27]. Meanwhile, this results also suggested that B. subtilis was a promising resource of potential cellulase enzymes. Besides, B. subtilis was also detected in forest system, such as forest soil [28], freshwater swamp forest [29]. In addition, B. licheniformis was another vital species found in rooden trees, exhibiting the ability to degrade cellulose or other natural cellulosic biomass, and which has been extensively found in hot spring, soil, gut of animals, paddy field and agricultural environment, with a high production of cellulase [30, 31]. It is noteworthy that B. megaterium, B. methylotrophicus and Pseudomonas aeruginosa in this study were scarcely reported to exhibit the ability to produce cellulase or degradation activity of cellulosic materials. To the best of our knowledge, only B. megaterium BM05 has been reported for wheat straw fermentation [32], and B. methylotrophicus Y37 [33] were reported to have cellulolytic enzyme. Accordingly, it suggested that the strains screened in present study possessed the special bacteria composition for novel cellulases development. Meanwhile, various species of cellulolytic bacteria were also identified, such as B. subtilis, P. aeruginosa, B. licheniformis, B. methylotrophicus and B. megaterium, which have been rarely reported. Consequently, the results revealed that the special areas (e.g. Qinling mountains) were good sources for the development of cellulolytic bacterium, and the B. subtilis might need to be paid more attentions during the potential bacterial screening.

Hydrolysis capability of the strains and its cellulolytic enzymes

On the whole, wild bacteria exhibit low enzyme production capacity and generally low enzyme activity. In this study, CMC-Na medium with different stains had the maximum reducing sugar content of 4.83 mg/100 mL, while Avicel medium only had 1.61 mg/100 mL reducing content (Fig. 2), revealing that the hydrolysis capability of stains can be affected by the types of cellulose substrates. Moreover, the sugar consumption for the strain’s growth was also a cause of the low content of reduced sugar in cultivation broth. It was also reported in some studies that no reducing sugars were detected in the finial CMC medium when cultured with the isolated bacteria [34].

The strains of B. subtilis 1AJ3, B. methylotrophicus 1EJ7 and B. subtilis 3BJ4 all belonged to Bacillus, which were selected and applied to the pretreatment of switchgrass for their relatively higher cellulase activity and better cellulose degradation efficiency. Although the three strains all processed the cellulose hydrolyzation activity in various types of substrates, B. methylotrophicus 1EJ7 performed best for the highest reducing sugar content in the final broth compared with other two strains. It was interesting to find that Avicelase activity was only not detected in B. methylotrophicus 1EJ7 in the medium with switchgrass as only carbon source, which was mainly attributed to the different enzyme system of the strains. In detail, although the B. subtilis has the powerful ability for the enzyme secretion, Avicelase needed special carbon sources to induce in the B. methylotrophicus 1EJ7, and as the switchgrass was not the suitable carbon sources for the B. methylotrophicus 1EJ7, which led to the lacking of Avicelase activity. In addition, as an herbaceous plant resource, switchgrass was easily to be degraded compared to wheat straw and corn stover, therefore, it was used for the effect investigation of the biomass degradation caused by the proposed strains. What’s more, when the pretreatment with the strains in a high concentration of substrates, the reducing sugar content in the final broth was the most important index to evaluate the pretreatment efficiency, since the high reducing sugar content was the preconditions for the conversion of ethanol and other valuable chemical products. In this view, compared with other two strains, B. methylotrophicus 1EJ7 possessed the obvious advantages for the highest reducing sugar content after pretreatment of switchgrass. Meanwhile, as there was no report on the cellulase from B. methylotrophicus 1EJ7, it was promising to found some novel cellulases and apply both the strain and cellulase to the degradation of the biomass in the industry.

It was noteworthy that different carbon substrates would induce different cellulases and further lead to different capabilities of reducing sugar production. When 8 strains were applied to hydrolyze different carbon source substrates, the strains exhibited a better performance in reducing sugar production in CMC-Na medium than that in Avicel, which was mainly attributed to two parts: 1. the different structure of cellulose substrates: Avicel was more difficult to hydrolyze than CMC-Na by cellulase for the unique microcrystalline structure [35]; 2. the different action modes of exocellulase and endocellulase: as the type of cellulolytic enzyme was critical to the hydrolysis of different cellulose substrates, the efficiency in hydrolyzing CMC or Avicel was also significantly affected by the enzyme types [36, 37].

Moreover, it was also found that the strains performing well in Avicel and CMC-Na degradation did not show a same good performance in hydrolyzing biomass, which was probably due to the complex network of lignin-hemicellulos-cellulose in biomass materials. It also needed to note that FPase and CMCase of different strains (Fig. 4b and c) exhibited similar cellulase activity in different mediums. Furthermore, except for B. subtilis 1AJ3 and the B. subtilis 3BJ4, Avicelase activity was detected in all mediums. Other strains could synthesize enzyme in limited carbon source medium pretreated by all other strains. An interesting phenomenon was also found that B. subtilis 1AJ2 could produce Avicelase enzyme only in CMC-Na medium, which indicated that the selected strains processed the function to synthesize enzyme in a limited carbon source medium. However, not all strains could be induced to produce Avicelase, which might be the reason why crystalline cellulose or more complex structure were hard to hydrolyze reported by the related study [38], on the other hand, the results further proved the special applicability of the selected stains.

Among the three biomass materials in present study, the pretreatment of switchgrass, considered as major non-food biomass resources originated from US [39], led to the highest production of reducing sugar. Compared with wheat straw and corn stover, switchgrass was a herbaceous plant with a less tight and crystalline structure and primarily composed of glucose than xylose or other monomeric sugars, which might be the main reason for the easily hydrolyzation by the strains, and a similar study also has been reported by Sharma R [40]. Compared with acid pretreatment or hot compress water pretreatment [41], bacteria cultivation was always considered as a gentle pretreatment method without any chemicals (such as salt ion, acid and alkali) or dramatic physical conditions (such as high temperature, high pressure and radiation). In this study, B. methylotrophicus 1EJ7 was used to pretreat switchgrass, and 0.95 mg/mL reducing sugar was finally obtained, which also needed to be improved before the application. Existing studies showed that the competitiveness of the strains was always improved by optimizing cultivation condition or cooperating with other enzymes, meanwhile, novel technologies were also feasible, including gene editing and cellulase cloning expression, which was preliminarily conducted as shown follows.

Cellulase of B. methylotrophicus

When talking about B. methylotrophicus, the majority of studies mainly focused on the following parts: 1. Screening [42]; 2. Utilized as biosurfactant-producer and agricultural agent [43], bioflocculant [44], as well as biofertilizer or biocontrol agent [45]; 3. Cyclic lipopeptides [46] and lipopeptides [47]; 4. Production of enzymes, such as levansucrase [48], α-amylase [49], lactosylfructoside [50], and xylanase [51]. However, there were rare reports about cellulases from B. methylotrophicus, and just only two types of cellulase, 1,3-1,4-beta-glucanase [52] and carboxymethyl cellulase [33] had been reported, which were both obtained by the purification from strain cultivation broth. But so far, the heterogeneously cloning and expression of polypeptides or enzymes of B. methylotrophicus were not found.

Accordingly, in this study, the molecular biology methods were applied to clone and express cellulase from bacteria B. methylotrophicus 1EJ7. Fortunately, two cellulases were successfully cloned and expressed, and the cellulolytic enzyme activities of cloning peptide were also verified, which can be considered as the first study about the heterogeneously cloning and expression of the cellulases (β-glucosidase and endoglucanase) from B. methylotrophicus strain. Enzyme activities of recombined crude enzyme Bgl and Egl reached 1670.15 ± 18.94 U/mL and 0.130 ± 0.002 U/mL, respectively. According to the results of SDS-PAGE, the light color band of Egl can be speculated to exhibit a low expression level, which might lead to relative low enzyme activity (U/mL) of cellulase, however, the expression level was still higher than the CMCase in strain growth broth in this study or other Bacillus [53]. A high expression level of Bgl was also detected under the proposed expression conditions and a high crude enzyme activity was obtained. Based on the sequence alignment results, several enzymes of high similarity with Bgl were found. For examples, β-1,3–1,4-glucanase from B. subtilis 168 with a crude enzyme activity of 1366.48 U/mL had highest sequence similarity of 94% with Bgl [54], and a beta-glucosidase with a similar Mw (27.35 kDa) from B. licheniformis showed enzyme activity of 67.34 U/mL [55]. Importantly, all the reported similar Bgls did not possesses a better enzyme activity than the recombinant Bgl in the present study, even the industrial optimized beta-glucosidase (560.4 U/mL) [56] and other heterogeneous expressed β-1,4-glucosidase from bacteria (Paenibacillus sp. 5.8 U/mL [57]) and fungi (Daldinia eschscholzii, 3.21 U/mg [58]; Trichoderma reesei, 25.13 U/mL [59]). What’s more, the enzyme activity of the recombinant Bgl was tens of thousands of times than that from wild microorganism, such as Penicillium pinophilum KMJ601 (3.2 U/mL) [60] and Bacillus sp. AS3 (0.04 U/mL) [53]. It was an interesting scientific issue that what the reason for the differences in the enzyme activity of Bgl with a similarity amino acid sequence. It was deduced that although it was highly similarity in the amino acid sequence (for instance, 94% similarity of Bgl with β-glucanases from B. subtilis 168 in amino acid sequence), the different amino acids might be the important part for the enzyme protein structure or the active sites, such as the binding sites of enzyme with substrates, catalytic sites, etc. If the different amino acid located in the important part and significantly influenced the active sites structure of the protein, the activity of the enzyme also might be significantly influenced, although just several amino acids were different. Eventhough this was just a deduction about this phenomenon obtained by the comparation with other reported similar enzymes, it provided a valuable study direction to make sure the function of the different amino acid on the enzyme activity. In this view, directed mutagenesis or knocking down of the proposed sites in peptides can be conducted to study the influence of proposed amino acid on the enzyme structure and activity. Moreover, the relationship between the enzyme structure and the activity, and the mechanism of the catalytic process should be also deeply studied in the further study.

In addition, as the β-glucosidase and endoglucanase had been expressed successfully, the characterization and optimization of the proposed recombinant enzymes should be studied in the further study. Correspondingly, the present study provided new materials of both strain and the recombinant enzymes for the cellulose degradation related studies and promoted the bio-pretreatment of the cellulose applied to industry.

Conclusions

Various of cellulose-degrading bacteria in rotten wood of Qinling Mountains were isolated and identified as well as the characterization of cellulose degradation. Among the isolated strains, Bacillus were the dominant species, in which B. methylotrophicus 1EJ7 processed the best ability for cellulose degradation. Meanwhile, the β-glucosidase and endoglucanase were successfully heterogeneously cloned and expressed from B. methylotrophicus for the first time, which were also verified having well activity for cellulose degradation. In addition, the characterization, enzyme activity improvement and the mechanism of the cellulose degradation about the recombinant cellulases would be further studied.

Materials and methods

Materials

Five rotten wood samples (weed tree, red birch, poplar, alpine rhododendron and willow) were collected from Qinling Mountain in Shaanxi Province, China. Samples were transported to the laboratory and stored at 4 °C. Wheat straw, corn stover, switchgrass was washed by water and dried at 60 °C, and then crushed by high-peed pulverizer to 40 mesh. The chemicals used in this study were purchased from Kelong Chemical Reagent Chengdu Co., Aladdin or Sigma.

Cellulolytic bacteria isolation and identification

Each sample was broken into pieces, and took 1 g added into LB medium (10 g/L NaCl, 10 g/L tryptone and 5 g/L yeast extract), then incubated at 37 °C for 24 h with a constant shaking speed of 120 rpm. The bacteria suspension was respectively transferred to two selective media. The two selective media, CM and AM, were used CMC-Na and Avicel as single carbon source separately, contained of 2.0 g/L sodium carboxymethyl cellulose (CMC-Na) or Avicel (PH-101), and others of 2.0 g/L (NH4)2SO4, 0.5 g/L MgSO4•7H2O, 1.0 g/L K2HPO4 at natural pH of 7.20 were the same. The strains were cultured for 48 h at 37 °C with 120 rpm before being spread on the selective media agar plates with 0.4 g/L Congo red. Plates were incubated at 37 °C for 72 h, and then different colonies on the plates were picked.

The strains which probably could produce cellulolytic enzymes had a hydrolyzed circle around the colony. 10 μL broth of each isolated strains was dripped on the Congo red agar plates and the hydrolysis circle diameters of were measured to primarily evaluate the cellulolytic capability. The selected strains were shown in Additional file 1: Figure S1.

The strains were cultured in broth for 48 h, then the cells were harvested and subjected to genome DNA extraction by a DNA extraction kit (Sangon Biotech, Shanghai, China). The universal primers of 27F and 1492R were utilized to amplify the 16S rRNA gene fragments. Polymerase chain reaction (PCR) was performed in a 25 μL reaction system containing 1 μL DNA template, 1 μL upstream primer (10 μM), 1 μL downstream primer (10 μM), 12 μL mixture, and 10 μL double-distilled water. The PCR amplification was performed as follows: initial denaturation at 95 °C for 5 min; 35 cycles of 94 °C for 1 min, 58 °C for 30 s, and 72 °C for 1 min; and final extension at 72 °C for 10 min.

Agarose gel electrophoresis was used to confirm target products and the PCR products were sequenced. The sequences were applied to BLAST on the NCBI database (http://blast.ncbi.nlm.nih.gov/). The 16S rRNA gene sequences have been submitted to GenBank (Accession Numbers showed in Additional file 9). Phylogenetic tree was constructed in iTOL (http://itol.embl.de).

Reducing sugar determination and enzymatic activity assay

Fifty mL of the two selective media were individually transferred into 100 mL flasks and autoclaved under 121 °C for 20 min. The flasks were inoculated with 6% (v/v) seed bacteria (dilute broth OD600 to 1.0) and grow at 37 °C for 48 h under 120 rpm. The cell-free supernatant was obtained by centrifugation (11,000 rpm, 4 °C, and 10 min) to examine reducing sugar content and the activities of crude cellulase. The FPase (filter paper activity), CMCase activity, and Avicelase activity were analyzed according to the methods described [61]. All cellulase activities were determined at 50 °C. Reducing sugar of each cultivated liquid was analyzed by DNS method [62]. One unit (U) of FPase/CMCase/Avicelase were defined as the amount of enzyme that produce 1 μmol of glucose per minute under standard conditions. The activities of recombinant β-glucosidase was determined by p-NPG (p-4-nitrophenyl β-D-glucopyranoside) as substrate at 50 °C, 10 min with p-NP as standard [63]. One unit (U) of β-glucosidase enzyme was defined as the amount of enzyme required to release 1 μmol of p-NP per minute.

Cultivation in different carbon sources

Different carbon source of wheat straw (4.0 g/L), corn stover (4.0 g/L), switchgrass (4.0 g/L), Avicel (2.0 g /L) or CMC-Na (2.0 g/L) was used as sole carbon source. Reducing sugar and cellulase activity were measured.

Single and mixed strain cultivation of cellulosic materials without pretreatment

Three bacteria strains (B. methylotrophicus 1EJ7, B. subtilis 1AJ3 and B. subtilis 3BJ4) were selected to degrade wheat straw, corn stover or switchgrass by single and mixture owing to their higher cellulolytic activity. Mixture of the three strains (1:1:1) had the same inoculum size as the single strain. The inoculum size of the single strain or mixed strains was 6%. The concentrations of wheat straw, corn stover, and switchgrass were 7% (w/v), after which they were grown at 37 °C, 120 rpm for 72 h. Reducing sugar was determined at intervals of 12 h.

Scanning electron microscopy (SEM) and X-ray diffraction

B. methylotrophicus 1EJ7 was utilized to hydrolyze wheat straw without pretreatment as an example to show morphology changes before and after hydrolysis by SEM method [64].

X-ray diffraction (Xian Asn Tech) was used to show wheat straw physical structures with diffraction angles spanned from 2θ = 5–50°. The radiation was generated at a voltage of 40 kV with a current of 35 mA, and by a scan step size of 0.033° [22]. Crystallinity Index CrI (%) = [(I002 - Iam)/I002] × 100 (I002 is the intensity of crystalline portion of cellulose at 2θ = 22°, and Iam is the peak intensity of the amorphous portion at 2θ = 18°).

Cloning and expression of cellulase gene from B. methylotrophicus 1EJ7 in E. coli

B. methylotrophicus 1EJ7 was cultured in LB medium at 37 °C for 24 h under 150 rpm. The cells were collected by centrifugation (10,000 rpm, 4 °C, and 10 min) and the genomic DNA was extracted using an Ezup column bacteria genomic DNA purification kit (Shanghai Sangon Biotech Co., Ltd.). The extracted DNA was used as a template for PCR amplification. The genes encoding β-glucosidase and endoglucanase were amplified by using primers based on the gene sequences of the β-glucosidase of Bacillus velezensis AS43.3 (CP003838.1) and endoglucanase of Bacillus velezensis strain JTYP2 (CP020375.1). The gene encoding the β-glucosidase was amplified by PCR (94 °C for 5 min, and then 35 cycles of 94 °C for 1 min, 65 °C for 1 min (− 0.5 °C/c), 72 °C 3 min, and 72 °C for 10 min) with a forward primer of 5′- CATGCCATGGGCATGTTTTATCGTATGAAACGAGTG (NcoI site was underlined) and a reverse primer 5′-CCGCTCGAGTTTTTTTGTATAGCGCACCCA (XhoI site was underlined) using a Takara ExTaqHS (Takara Bio, Shiga, Japan). The gene encoding the endoglucanase was amplified under the same PCR condition described above with a forward primer of 5′-CATGCCATGGGCATGAAACGGTCAATTTCTATTTTT (NcoI site was underlined) and a reverse primer of 5′-CCGCTCGAGATTGGGTTCTGTTCCCCAAA (XhoI site was underlined). The amplified genes were double digested with NcoI and XhoI, and inserted into the corresponding site of the pET-28a(+) vector (Novagen) by T4 ligase.

Then, the constructed plasmid was transformed into E.coli BL21 (DE3) by hot hit under 42 °C for 90s and correct transformants were identified by PCR amplification and sequencing. The transformant was cultured in 1 L LB medium containing 1 mg/mL kanamycin at 37 °C until the absorbance at 600 nm reached 0.6. After that, expression was induced by adding a final density of 0.2 mM IPTG, and the transformant was further cultured at 25 °C for 16 h. The cells were collected by centrifuging (8000×g, 4 °C, 10 min), and then suspended in PBS buffer (pH 7.2). Cells were disrupted by ultrasonication under 300 W output power, a repeating cycle of 1 s ultrasonic treatment and 5 s shutdown, for 60 min on a SCIENTZ-IID ultrasonic homogenizer (Ningbo Scientz Biotechnology Polytron Technologies Inc. Zhejiang province, China). The resulting cell lysates were centrifuged (8000×g, 4 °C, 30 min). A 15% SDS-PAGE was performed to analyze the supernatant and the insoluble fraction of the sonicated whole cell lysate.

Bioinformatic analysis and homology modeling

The plasmids of pET-28a-Bgl and pET-28a-Egl were sequenced. The primary sequences of Bgl and Egl protein were obtained by amino acid translation software, and the homology templates were obtained through retrieving in the protein database PDB. Physiochemical characteristics were predicted on ExPASy (http://web.expasy.org/protparam/). Conserved domain was analyzed by CDD of NCBI (https://www.ncbi.nlm.nih.gov/cdd). Clustal Omega (https://www.ebi.ac.uk/Tools/msa/clustalo/) was used for sequence alignments. Secondary structure and 3D structure were predicted by PSIPRED (http://bioinf.cs.ucl.ac.uk/psipred/) and I-TASSER (https://zhanglab.ccmb.med.umich.edu/I-TASSER/).

Availability of data and materials

All data generated or analyzed during this study are included in this published article and its supplementary information files.

Abbreviations

CMC-Na:

Sodium carboxymethyl cellulose

FPase:

Filter paper activity

NCBI:

National center for biotechnology information

PCR:

Polymerase chain reaction

p-NPG:

p-4-nitrophenyl β-D-glucopyranoside

SEM:

Scanning electron microscopy

References

  1. 1.

    Limayem A, Ricke SC. Lignocellulosic biomass for bioethanol production: current perspectives, potential issues and future prospects. Prog Energy Combust Sci. 2012;38(4):449–67.

    CAS  Article  Google Scholar 

  2. 2.

    Ching TW, Haritos V, Tanksale A. Microwave assisted conversion of microcrystalline cellulose into value added chemicals using dilute acid catalyst. Carbohydr Polym. 2017;157:1794–800.

    CAS  PubMed  Article  PubMed Central  Google Scholar 

  3. 3.

    Xia Q, Chen Z, Shao Y, Gong X, Wang H, Liu X, Parker SF, Han X, Yang S, Wang Y. Direct hydrodeoxygenation of raw woody biomass into liquid alkanes. Nat Commun. 2016;7:11162.

    PubMed  PubMed Central  Article  CAS  Google Scholar 

  4. 4.

    McIntosh S, Zhang Z, Palmer J, Wong HH, Doherty WO, Vancov T. Pilot-scale cellulosic ethanol production using eucalyptus biomass pre-treated by dilute acid and steam explosion. Biofuels Bioprod Biorefin. 2016;10(4):346–58.

    CAS  Article  Google Scholar 

  5. 5.

    Sun S, Sun S, Cao X, Sun R. The role of pretreatment in improving the enzymatic hydrolysis of lignocellulosic materials. Bioresour Technol. 2016;199:49–58.

    CAS  PubMed  Article  PubMed Central  Google Scholar 

  6. 6.

    Singh J, Suhag M, Dhaka A. Augmented digestion of lignocellulose by steam explosion, acid and alkaline pretreatment methods: a review. Carbohydr Polym. 2015;117:624–31.

    CAS  PubMed  Article  PubMed Central  Google Scholar 

  7. 7.

    Wan C, Li Y. Microbial pretreatment of corn Stover with Ceriporiopsis subvermispora for enzymatic hydrolysis and ethanol production. Bioresour Technol. 2010;101(16):6398–403.

    CAS  PubMed  Article  PubMed Central  Google Scholar 

  8. 8.

    Peterson R, Nevalainen H. Trichoderma reesei RUT-C30--thirty years of strain improvement. Microbiol. 2012;158(Pt 1):58–68.

    CAS  Article  Google Scholar 

  9. 9.

    Zhang Z, Liu J-L, Lan J-Y, Duan C-J, Ma Q-S, Feng J-X. Predominance of Trichoderma and Penicillium in cellulolytic aerobic filamentous fungi from subtropical and tropical forests in China, and their use in finding highly efficient β-glucosidase. Biotechnol Biofuels. 2014;7(1):107.

    Article  CAS  Google Scholar 

  10. 10.

    do Rêgo de Oliveira SL, Maciel TC, de Oliveira Sancho S, Rodrigues S. Solid-state production of cellulase by Melanoporia sp. CCT 7736: a new strain isolated from coconut shell (Cocos nucifera L.). Bioresources Bioprocessing. 2016;3(1):9.

    Article  Google Scholar 

  11. 11.

    Ang SK, Shaza EM, Adibah Y, Suraini AA, Madihah MS. Production of cellulases and xylanase by Aspergillus fumigatus SK1 using untreated oil palm trunk through solid state fermentation. Process Biochem. 2013;48(9):1293–302.

    CAS  Article  Google Scholar 

  12. 12.

    Wang Y, Liu Q, Yan L, Gao Y, Wang Y, Wang W. A novel lignin degradation bacterial consortium for efficient pulping. Bioresour Technol. 2013;139:113–9.

    CAS  PubMed  Article  Google Scholar 

  13. 13.

    Xu JX, Gao Z, Wu B, He BF. Lactose-inducted production of a complete lignocellulolytic enzyme system by a novel bacterium Bacillus sp BS-5 and its application for saccharification of alkali-pretreated corn cob. Cellulose. 2017;24(5):2059–70.

    CAS  Article  Google Scholar 

  14. 14.

    Kazeem MO, Shah UKM, Baharuddin AS, AbdulRahman NA. Prospecting agro-waste cocktail: supplementation for Cellulase production by a newly isolated Thermophilic B. licheniformis 2D55. Appl Biochem Biotechnol. 2017;182(4):1318–40.

    CAS  PubMed  PubMed Central  Article  Google Scholar 

  15. 15.

    Ma L, Yang WP, Meng FX, Ji SY, Xin HY, Cao BY. Characterization of an acidic cellulase produced by Bacillus subtilis BY-4 isolated from gastrointestinal tract of Tibetan pig. J Taiwan Inst Chem E. 2015;56:67–72.

    CAS  Article  Google Scholar 

  16. 16.

    Mihajlovski KR, Carevic MB, Devic ML, Siler-Marinkovic S, Rajilic-Stojanovic MD, Dimitrijevic-Brankovic S. Lignocellulosic waste material as substrate for Avicelase production by a new strain of Paenibacillus chitinolyticus CKS1. Int Biodeterior Biodegrad. 2015;104:426–34.

    CAS  Article  Google Scholar 

  17. 17.

    Ma J, Zhang K, Liao H, Hector SB, Shi X, Li J, Liu B, Xu T, Tong C, Liu X, et al. Genomic and secretomic insight into lignocellulolytic system of an endophytic bacterium Pantoea ananatis Sd-1. Biotechnol Biofuels. 2016;9:25.

    PubMed  PubMed Central  Article  CAS  Google Scholar 

  18. 18.

    Joliff G, Béguin P, Juy M, Millet J, Ryter A, Poljak R, Aubert J-P. Isolation, crystallization and properties of a new Cellulase of Clostridium thermocellum overproduced in Escherichia coli. Nat Biotechnol. 1986;4(10):896–900.

    CAS  Article  Google Scholar 

  19. 19.

    Liu Y, Linderholm HW, Song HM, Cai QF, Tian QH, Sun JY, Chen DL, Simelton E, Seftigen K, Tian H, et al. Temperature variations recorded in Pinus tabulaeformis tree rings from the southern and northern slopes of the central Qinling Mountains, Central China. Boreas. 2009;38(2):285–91.

    Article  Google Scholar 

  20. 20.

    Liming X, Xueliang S. High-yield cellulase production by Trichoderma reesei ZU-02 on corn cob residue. Bioresour Technol. 2004;91(3):259–62.

    PubMed  Article  CAS  Google Scholar 

  21. 21.

    Peng X, Qiao W, Mi S, Jia X, Su H, Han Y. Characterization of hemicellulase and cellulase from the extremely thermophilic bacterium Caldicellulosiruptor owensensis and their potential application for bioconversion of lignocellulosic biomass without pretreatment. Biotechnol Biofuels. 2015;8:131.

    PubMed  PubMed Central  Article  CAS  Google Scholar 

  22. 22.

    Ravindran R, Jaiswal S, Abu-Ghannam N, Jaiswal AK. A comparative analysis of pretreatment strategies on the properties and hydrolysis of brewers' spent grain. Bioresour Technol. 2018;248(Pt A):272–9.

    CAS  PubMed  Article  Google Scholar 

  23. 23.

    Badino SF, Bathke JK, Sorensen TH, Windahl MS, Jensen K, Peters GHJ, Borch K, Westh P. The influence of different linker modifications on the catalytic activity and cellulose affinity of cellobiohydrolase Cel7A from Hypocrea jecorina. Protein Eng Des Sel. 2017;30(7):495–501.

    CAS  PubMed  Article  Google Scholar 

  24. 24.

    Hahn M, Keitel T, Heinemann U. Crystal and molecular structure at 0.16-nm resolution of the hybrid Bacillus Endo-1,3-1,4-beta-D-Glucan 4-Glucanohydrolase H(A16-M). Eur J Biochem. 1995;232(3):849–58.

    CAS  PubMed  Article  Google Scholar 

  25. 25.

    Takagi E, Hatada Y, Akita M, Ohta Y, Yokoi G, Miyazaki T, Nishikawa A, Tonozuka T. Crystal structure of the catalytic domain of a GH16 beta-agarase from a deep-sea bacterium, Microbulbifer thermotolerans JAMB-A94. Biosci Biotechnol Biochem. 2015;79(4):625–32.

    CAS  PubMed  Article  Google Scholar 

  26. 26.

    Tasaki S, Nakayama M, Shoji W. Morphologies of Bacillus subtilis communities responding to environmental variation. Develop Growth Differ. 2017;59(5):369–78.

    Article  Google Scholar 

  27. 27.

    Zhang XZ, Zhang Y. Simple, fast and high-efficiency transformation system for directed evolution of cellulase in Bacillus subtilis. Microb Biotechnol. 2011;4(1):98–105.

    PubMed  Article  Google Scholar 

  28. 28.

    Lee CK, Jang MY, Park HR, Choo GC, Cho HS, Park SB, Oh KC, An JB, Kim BG. Cloning and characterization of xylanase in cellulolytic Bacillus sp strain JMY1 isolated from forest soil. Appl Biol Chem. 2016;59(3):415–23.

    CAS  Article  Google Scholar 

  29. 29.

    Kanchanadumkerng P, Sakka M, Sakka K, Wiwat C. Characterization and secretive expression in Bacillus subtilis of endoglucanase from Bacillus safensis isolated from freshwater swamp forest. Walailak J Sci Technol (WJST). 2017;14(3):199–213.

    Google Scholar 

  30. 30.

    Abdel-Rahman MA, El-Din MN, Refaat BM, Abdel-Shakour EH, Ewais EE-D, Alrefaey HM: Biotechnological Application of Thermotolerant Cellulose-Decomposing Bacteria in Composting of Rice Straw. Annals of Agricultural Sciences 2016.

  31. 31.

    Abdel-Rahman MA, Abdel-Shakour E, El-din MN, Refaat M, Ewais E, Alrefaey H. A novel promising Thermotolerant Cellulase-producing Bacillus licheniformis 1-1v strain suitable for composting of Rice straw. Int J Adv Res. 2015;3(12):413–23.

    CAS  Google Scholar 

  32. 32.

    Shahid ZH, Irfan M, Nadeem M, Syed Q, Qazi JI. Production, purification, and characterization of Carboxymethyl Cellulase from novel strain Bacillus megaterium. Environ Prog Sustain. 2016;35(6):1741–9.

    CAS  Article  Google Scholar 

  33. 33.

    Duman Y, Yuzugullu Karakus Y, Sertel A, Polat F. Production, purification, and characterization of a thermo-alkali stable and metal-tolerant carboxymethylcellulase from newly isolated Bacillus methylotrophicus Y37. Turk J Chem. 2016;40(5):802–15.

    CAS  Article  Google Scholar 

  34. 34.

    Jonnadula R, Verma P, Shouche YS, Ghadi SC. Characterization of Microbulbifer strain CMC-5, a new biochemical variant of Microbulbifer elongatus type strain DSM6810T isolated from decomposing seaweeds. Curr Microbiol. 2009;59(6):600–7.

    CAS  PubMed  Article  PubMed Central  Google Scholar 

  35. 35.

    Percival Zhang YH, Himmel ME, Mielenz JR. Outlook for cellulase improvement: screening and selection strategies. Biotechnol Adv. 2006;24(5):452–81.

    CAS  PubMed  Article  PubMed Central  Google Scholar 

  36. 36.

    Hamid SBA, Islam MM, Das R. Cellulase biocatalysis: key influencing factors and mode of action. Cellulose. 2015;22(4):2157–82.

    Article  CAS  Google Scholar 

  37. 37.

    Kanda T, Wakabayashi K, Nisizawa K. Modes of action of exo- and endo-cellulases in the degradation of celluloses I and II. J Biochem. 1980;87(6):1635–9.

    CAS  PubMed  Article  PubMed Central  Google Scholar 

  38. 38.

    Saratale GD, Saratale RG, Lo YC, Chang JS. Multicomponent cellulase production by Cellulomonas biazotea NCIM-2550 and its applications for cellulosic biohydrogen production. Biotechnol Prog. 2010;26(2):406–16.

    CAS  PubMed  PubMed Central  Google Scholar 

  39. 39.

    Wright L, Turhollow A. Switchgrass selection as a “model” bioenergy crop: a history of the process. Biomass Bioenergy. 2010;34(6):851–68.

    Article  Google Scholar 

  40. 40.

    Sharma R, Lamsal BP, Mba-Wright M. Performance of Bacillus subtilis on fibrous biomass sugar hydrolysates in producing biosurfactants and techno-economic comparison. Bioprocess Biosyst Eng. 2018;41(12):1817–26.

    CAS  PubMed  Article  PubMed Central  Google Scholar 

  41. 41.

    Amarasekara AS, Shanbhag P. Degradation of untreated Switchgrass biomass into reducing sugars in 1-(Alkylsulfonic)-3-Methylimidazolium Bronsted acidic ionic liquid medium under mild conditions. Bioenerg Res. 2013;6(2):719–24.

    CAS  Article  Google Scholar 

  42. 42.

    Chandankere R, Yao J, Choi MMF, Masakorala K, Chan Y. An efficient biosurfactant-producing and crude-oil emulsifying bacterium Bacillus methylotrophicus USTBa isolated from petroleum reservoir. Biochem Eng J. 2013;74(9):46–53.

    CAS  Article  Google Scholar 

  43. 43.

    Chandankere R, Yao J, Cai MM, Masakorala K, Jain AK, Choi MMF. Properties and characterization of biosurfactant in crude oil biodegradation by bacterium Bacillus methylotrophicus USTBa. Fuel. 2014;122(8):140–8.

    CAS  Article  Google Scholar 

  44. 44.

    Li T, Wang J, Wei XL, Zhao HY, Zhao ZX, Liu HB. Identification and characterization of a Bacillus methylotrophicus strain with high flocculating activity. RSC Adv. 2015;5(111):91766–75.

    CAS  Article  Google Scholar 

  45. 45.

    Ge B, Liu B, Nwet TT, Zhao W, Shi L, Zhang K. Bacillus methylotrophicus strain NKG-1, isolated from Changbai Mountain, China, has potential applications as a biofertilizer or biocontrol agent. PLoS One. 2016;11(11):e0166079.

    PubMed  PubMed Central  Article  CAS  Google Scholar 

  46. 46.

    Jemil N, Manresa A, Rabanal F, Ben Ayed H, Hmidet N, Nasri M. Structural characterization and identification of cyclic lipopeptides produced by Bacillus methylotrophicus DCS1 strain. J Chromatogr B Analyt Technol Biomed Life Sci. 2017;1060(15):374–86.

    CAS  PubMed  Article  PubMed Central  Google Scholar 

  47. 47.

    Jemil N, Ben Ayed H, Manresa A, Nasri M, Hmidet N. Antioxidant properties, antimicrobial and anti-adhesive activities of DCS1 lipopeptides from Bacillus methylotrophicus DCS1. BMC Microbiol. 2017;17(1):144.

    PubMed  PubMed Central  Article  CAS  Google Scholar 

  48. 48.

    Li R, Zhang T, Jiang B, Mu W, Miao M. Purification and characterization of an intracellular levansucrase derived from Bacillus methylotrophicus SK 21.002. Biotechnol Appl Biochem. 2015;62(6):815–22.

    CAS  PubMed  Article  PubMed Central  Google Scholar 

  49. 49.

    Hmidet N, Jemil N, Nasri M. Simultaneous production of alkaline amylase and biosurfactant by Bacillus methylotrophicus DCS1: application as detergent additive. Biodegradation. 2019;30(4):247–58.

    CAS  PubMed  Article  PubMed Central  Google Scholar 

  50. 50.

    Wu C, Zhang T, Mu W, Miao M, Jiang B. Biosynthesis of lactosylfructoside by an intracellular levansucrase from Bacillus methylotrophicus SK 21.002. Carbohydr Res. 2015;401:122–6.

    CAS  PubMed  Article  Google Scholar 

  51. 51.

    Panthi S, Choi YS, Choi YH, Kim M, Yoo JC. Biochemical and thermodynamic characterization of a novel, low molecular weight Xylanase from Bacillus Methylotrophicus CSB40 isolated from traditional Korean food. Appl Biochem Biotechnol. 2016;179(1):126–42.

    CAS  PubMed  Article  Google Scholar 

  52. 52.

    Niu Q, Zhang G, Zhang L, Ma Y, Shi Q, Fu W. Purification and characterization of a thermophilic 1,3-1,4-beta-glucanase from Bacillus methylotrophicus S2 isolated from booklice. J Biosci Bioeng. 2016;121(5):503–8.

    CAS  PubMed  Article  Google Scholar 

  53. 53.

    Toledano A, Erdocia X, Serrano L, Labidi J. Influence of extraction treatment on olive tree (Olea europaea) pruning lignin structure. Environ Prog Sustain. 2013;32(4):1187–94.

    CAS  Article  Google Scholar 

  54. 54.

    Furtado GP, Ribeiro LF, Santos CR, Tonoli CC, de Souza AR, Oliveira RR, Murakami MT, Ward RJ. Biochemical and structural characterization of a β-1,3–1,4-glucanase from Bacillus subtilis 168. Process Biochem. 2011;46(5):1202–6.

    CAS  Article  Google Scholar 

  55. 55.

    Wen-Ping LU, Zi-Rong XU, Sun JY, Wei-Fen LI, Wen-Li DU. Cloning and expression of β-1,3-1,4-glucanase gene from Bacillus licheniformis. J Zhejiang Univ. 2004;12.

  56. 56.

    Shi X, Xie J, Liao S, Wu T, Zhao LG, Ding G, Wang Z, Xiao W. High-level expression of recombinant thermostable beta-glucosidase in Escherichia coli by regulating acetic acid. Bioresour Technol. 2017;241:795–801.

    CAS  PubMed  Article  Google Scholar 

  57. 57.

    Gupta S, Adlakha N, Yazdani SS. Efficient extracellular secretion of an endoglucanase and a beta-glucosidase in E. coli. Protein Expr Purif. 2013;88(1):20–5.

    CAS  PubMed  Article  Google Scholar 

  58. 58.

    Karnchanatat A, Petsom A, Sangvanich P, Piapukiew J, Whalley AJS, Reynolds CD, Gadd GM, Sihanonth P. A novel thermostable endoglucanase from the wood-decaying fungus Daldinia eschscholzii (Ehrenb.:Fr.) Rehm. Enzym Microb Technol. 2008;42(5):404–13.

    CAS  Article  Google Scholar 

  59. 59.

    Xia Y, Yang L, Xia L. Combined strategy of transcription factor manipulation and beta-glucosidase gene overexpression in Trichoderma reesei and its application in lignocellulose bioconversion. J Ind Microbiol Biotechnol. 2018;45(9):803–11.

    CAS  PubMed  Article  Google Scholar 

  60. 60.

    Joo A-R, Jeya M, Lee K-M, Lee K-M, Moon H-J, Kim Y-S, Lee J-K. Production and characterization of β-1,4-glucosidase from a strain of Penicillium pinophilum. Process Biochem. 2010;45(6):851–8.

    CAS  Article  Google Scholar 

  61. 61.

    Yang JK, Zhang JJ, Yu HY, Cheng JW, Miao LH. Community composition and cellulase activity of cellulolytic bacteria from forest soils planted with broad-leaved deciduous and evergreen trees. Appl Microbiol Biotechnol. 2014;98(3):1449–58.

    CAS  PubMed  Article  Google Scholar 

  62. 62.

    Miller GL. Use of Dinitrosalicylic acid reagent for determination of reducing sugar. Anal Chem. 1959;31(3):426–8.

    CAS  Article  Google Scholar 

  63. 63.

    Odoux E, Escoute J, Verdeil JL, Brillouet JM. Localization of beta-D-glucosidase activity and glucovanillin in vanilla bean (Vanilla planifolia Andrews). Ann Bot. 2003;92(3):437–44.

    CAS  PubMed  PubMed Central  Article  Google Scholar 

  64. 64.

    Yang CX, Wang T, Gao LN, Yin HJ, Lu X. Isolation, identification and characterization of lignin-degrading bacteria from Qinling. China J Appl Microbiol. 2017;123(6):1447–60.

    CAS  PubMed  Article  Google Scholar 

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Acknowledgements

The authors complete this work together, thank everyone’s contribution to the experiments design, experimentation, and thesis writing. We thank Dr. Chenxian Yang, Dr. Xing Guo and Dr. Zhu Qiao for their kindly help in experiments and spiritual encouragement.

Funding

This work was supported by Special Fund for Agro-scientific Research in the Public Interest (Grant No. 201503135). The funding body had no role in the design of the study, the collection, analysis, and interpretations of data and in writing the manuscript.

Author information

Affiliations

Authors

Contributions

LM, XW, and XL conceived and designed the experiments. LM, YL, HY, and YY performed the experiments. YS, BL, and YZ analyzed the data. LM and XL wrote the manuscript. All authors read and approved the final manuscript.

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Correspondence to Xin Lü.

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Additional file 1: Figure S1. Hydrolyzed circle of isolates on the Congo red agar plate. (a) Plates with CMC-Na as the sole carbon source. (b) Plates with Avicel as the sole carbon source

Additional file 2: Table S2. Isolated strains growth situation and clear zone size on Congo red plates

Additional file 3: Figure S3. Reducing sugar production and enzyme activities in CMC-Na (a) and Avicel (b) as sole carbon source medium

Additional file 4: Table S4-1. p-NP standard curve. Table S4-2. Bgl enzyme activity. Table S4-3. Glucose standard curve. Table S4-4. Egl enzyme activity.

Additional file 5: Figure S5. Domain analysis of Bgl

Additional file 6: Figure S6. Domain analysis of Egl

Additional file 7: Figure S7. Amino acid sequence alignments for Bgl and comparison with same gene in different strains. In which Bgl stand for β-glucosidase in this study; AS43.3 for β-glucosidase gene of Bacillus velezensis AS43.3 (CP003838.1) (complete gene); JTYP2 for Bacillus velezensis JTYP2 (CP020375.1), and 168 for Bacillus subtlis 168 (AL009126.3)

Additional file 8: Figure S8. Amino acid sequence alignments for Egl and comparison with same gene in different strains. In which Egl stand for endoglucanase in this study; JTYP2 for endoglucanase gene of Bacillus velezensis JTYP2 (CP020375.1) (complete gene); AS43.3 for Bacillus velezensis AS43.3 (CP003838.1), and 168 for Bacillus subtlis 168 (AL009126.3)

Additional file 9. Accession Numbers

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Ma, L., Lu, Y., Yan, H. et al. Screening of cellulolytic bacteria from rotten wood of Qinling (China) for biomass degradation and cloning of cellulases from Bacillus methylotrophicus. BMC Biotechnol 20, 2 (2020). https://doi.org/10.1186/s12896-019-0593-8

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Keywords

  • Rotten wood
  • Bacillus methylotrophicus
  • Cellulase
  • Biomass
  • Cloning and expression