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Cellulose-degrading enzymes from Aspergillus terreus D34 and enzymatic saccharification of mild-alkali and dilute-acid pretreated lignocellulosic biomass residues
Bioresources and Bioprocessing volume 2, Article number: 7 (2015)
Production of cellulose-degrading enzymes from Aspergillus terreus D34 using different growth substrates was studied under solid-state cultivation. We have tested two lignocellulosic biomass residues viz., rice straw (RS) and sugarcane bagasse (BG), both separately and in combinations, and crystalline cellulose as a sole source of carbon for cellulase production. We also demonstrated different cellulase cocktail formulations and enzymatic saccharification studies on mild-alkali and dilute-acid pretreated RS- and BG-biomass residues.
Substrate-specific non-denaturing native gels showed two exoglucanases, four endoglucanases, three β-glucosidases, and four xylanases in the microbial culture extract of RS-grown cells. While in the BG-culture extract, two exoglucanases, five endoglucanases, three β-glucosidases, and four xylanases were detected. Similarly, in crystalline cellulose-grown culture extract, three exoglucanases, four endoglucanases, one β-glucosidase, and two xylanases were detected. However, the cellulase compositions were highly varied with the culture extracts obtained from the mixed biomass (RSBG) growth substrate. We found that few enzymes were specifically induced while others were repressed in RSBG-grown cultures. Enzymatic saccharification resulted in the production of maximum reducing sugars of 0.733 and 0.498 g g−1 with mild-alkali treated RS- and BG-biomass residues with saccharification yields reaching up to 82.8% ± 1.0% and 59.3% ± 1.7%, respectively.
The cellulase activities, namely FPase, CMCase, avicelase, β-glucosidase, and endoxylanase, were significantly higher in the BG-grown culture extract. Optimization of microbial growth carbon sources produced an efficient cellulase enzyme cocktail mixture with an approximately twofold higher total cellulase (FPase) activity that drastically reduced the required amount of enzyme (in terms of unit volumes) for enzymatic hydrolysis studies.
Lignocellulosic plant biomass is the most abundant renewable bioenergy resource available on Earth. It will play a major role in the near future as an alternative bioresource to the currently existing non-renewable and exhaustive petroleum products for bioenergy applications. Globally, large quantities of agro-industrial wastes and crop residues are available in plenty and efficient utilization and microbial biodegradation of these biomaterials will lead to several processes of great economic value . Particularly in Asian countries, surplus amounts of lignocellulosic residues are available annually without much usage, namely rice straw (667.6 million tons) and sugarcane bagasse (74.8 million tons). These could be used as a potential bioresource material for cellulosic ethanol production [2,3]. However, large amounts of these agricultural residues are still frequently burnt in the fields causing severe environmental pollution problems and may foresee in utilizing these biomass residues for various potential industrial applications, for example, production of microbial enzymes and liquid biofuels, etc.
The major components of lignocellulosic biomass residues are celluloses, hemicelluloses, and lignin. The cellulosic fractions could be broken down into simple reducing sugars either by enzymatic or chemical processes for fuel ethanol production [4,5]. A broad range of cellulolytic and hemicellulolytic enzymes belonging to the glycoside hydrolase (GH) super family are produced by a variety of bacteria and fungi and are primarily involved in the breakdown of complex biomass residues into simple reducing sugars . The major cellulase enzymes involved in lignocellulosic bioconversion processes are the following: (i) exoglucanases (1,4-β-cellobiohydrolase; avicelase; E.C: 220.127.116.11) which act in a processive manner on the reducing and non-reducing ends of cellulose polysaccharide chains, liberating either cellobiose or glucose as major end products; (ii) endoglucanases (carboxymethyl cellulase; CMCase; E.C: 18.104.22.168) which randomly cut β-1,4 bonds of cellulose chains generating new ends; and (iii) β-glucosidases (E.C: 22.214.171.124) which specifically cut the cellobiose dimer units producing glucose monomers. Along with these enzymes, other key enzymes belonging to hemicellulases, mainly endoxylanases (E.C: 126.96.36.199), are known to act on the xylan portion of the biomass residue into pentoses, where xylan constitutes nearly 30% to 35% of total dry weight of the biomass.
Among several hypercellulolytic fungal strains, filamentous fungi such as Trichoderma and Aspergillus sps are considered as the major microbial sources for production of cellulose-degrading enzymes [7,8]. The genome sequencing of T. reesei revealed two cellobiohydrolases (CBHI and CBHII) and eight endoglucanases (EG) , among which only two major proteins (EGI and EGII) are usually secreted in notable quantities . Trichoderma sps is a well-known commercial cellulase producer but lacks sufficient β-glucosidase activity in the enzyme mixture. Although up to 12 β-glucosidases have been identified in T. reesei genome, most of them are found to be intracellular with low expression levels . In contrary, Aspergillus sps produces high amounts of β-glucosidase in the extracellular medium and is commonly used for commercial production of this enzyme. A. terreus NIH 2624 genome is known, and it contains genes encoding 5 exoglucanases, 22 endoglucanases, 18 β-glucosidases, and 7 xylanases and other genes with conserved domains that encode several putative cellulose-degrading enzymes and strongly establishes that multiple cellulase genes are present in A. terreus. Since expression of endoglucanases and cellobiohydrolases is very poor from Aspergillus sps, much research is focused towards β-glucosidase and xylanase production .
The process of lignocellulosic biomass bioconversion to ethanol involves three major steps, namely pretreatment, saccharification, and fermentation. Keeping in view of voluminous research reports on mild-alkali and dilute-acid pretreatments of lignocellulosic biomass residues and microbial fermentation processes [12-14], the detailed description on the two steps is not described in detail in this report and further researchers are suggested to refer recent reviews [15,16]. Saccharification of the pretreated lignocellulosic biomass depends mainly on the hydrolytic efficiency of each individual cellulase enzyme component present in the multi-cellulase complex and their synergistic action towards the breakdown of insoluble celluloses and hemicelluloses into simple reducing sugars . In continuation to our earlier published work on the production of cellulases from A. terreus D34 and enzymatic hydrolysis on mild-alkali pretreated RS biomass [12,13], here we report the detailed zymographic identification studies of multiple cellulase hemicellulase enzymes and microbial growth substrate optimization for low-cost production of cellulases using cheap lignocellulosic biomass residues. In addition, enzymatic saccharification studies on mild-alkali and dilute-acid pretreated RS- and BG-biomass residues with different cellulase cocktails are also reported.
Chemicals and raw materials
Precut, washed, and dried RS- and BG-biomass residues and microcrystalline cellulose (Sigma-Aldrich, St. Louis, MO, USA) were used as substrates for microbial growth and cellulase production. Celluclast 1.5 L and Novozyme 188, Avicel, carboxymethyl cellulose (CMC), p-nitrophenyl-β-D-glucopyranoside (PNPG), 4-methylumbelliferyl-β-D-cellobioside (MUC), 4-methylumbelliferyl-β-D-glucopyranoside (MUG), birchwood xylan, glucose, xylose, and cellobiose were purchased from Sigma-Aldrich (St. Louis, MO, USA) and were used for activity staining and enzyme assay measurements. The reagents for polyacrylamide gel electrophoresis (PAGE) analysis were purchased from Bio-Rad, Gurgaon, Haryana, India. All other chemicals and reagents were of analytical grade quality and were obtained from commercial sources.
Lignocellulosic biomass preparation
RS- and BG-biomass residues were procured from local agricultural fields and sugarcane refineries near Anand district, Gujarat. Initially, the biomass residues were extensively washed with water and then dried in sunlight for 3 to 4 days until the moisture content was reduced <5% (w/w). The dried biomass residues were then cut into small size (5 to 10 mm) using hammer mill. The precut biomasses were directly used without any further processing for microbial growth and enzyme production.
Microbial culture and growth conditions
We have recently reported the isolation of lignocellulose-degrading filamentous fungus A. terreus D34; microbial growth conditions and identification and complete details were given previously [12,13]. In brief, the filamentous fungus was grown for 7 days at 45°C on sterile agar slants comprising 2% (w/v) potato dextrose agar (PDA) and sub-cultured on fresh agar slants every 15 days. For long-term storage, spore suspensions were made in 0.1% (w/v) Triton X-100 and then glycerol stock cultures were prepared and stored at −80°C until further use.
Enzyme production in solid-state cultivation
Solid-state cultivation was carried out separately in 250 mL Erlenmeyer flasks containing RS- and BG-biomass residues and in combinations as a sole source of carbon for microbial growth. Crystalline cellulose was used as a synthetic growth substrate, and comparative analysis were performed with the naturally available lignocellulosic biomass residues. The RS to BG combinations tested were the following: 100:0, 25:75, 50:50, 75:25, and 0:100, where 100 correlate to 5 g dry weight of the respective biomass. All other growth parameters were maintained similar to our recent published report on cellulase production [12,13]. The incubated flasks were removed periodically every 24 h for 7 days, and enzyme activities and protein concentrations were measured.
Crude cellulase extraction and ammonium sulfate precipitation
The culture extract was separated from the microbial cells by the addition of 40 mL of 50 mM sodium citrate buffer (pH 4.8) to the solid-state grown cells and incubated at 45°C for 1 h under mild stirring conditions (100 rpm) to remove loosely bound enzymes from the biomass residue. The solid residual slurry was separated by vacuum filtration, and then the filtrate was subjected to centrifugation at 10,000 xg for 10 min for separation of the suspended particles. The so-obtained supernatant was further filtered through 0.45 μm glass fiber filters under vacuum pressure (Millipore system, Millipore India Ltd, Bengaluru, Karnataka, India) to obtain a clear enzyme solution. Finally, the proteins in the clarified culture extract were subjected to ammonium sulfate precipitation (85% to 90% (w/v)), respectively. The precipitated proteins were resolubilized in 50 mM sodium citrate buffer (pH 4.8) and then desalted in the above buffer by membrane dialysis (10 kDa cutoff) for 3 to 4 h with frequent buffer exchange. The desalted crude cellulases were used for enzymatic saccharification and zymographic experiments.
Determination of cellulase activities
Total cellulase activity (FPase) was measured by standard filter paper assay method following the NREL protocol . In brief, 50 mg of Whatman filter paper (grade I) incubated with 1 mL of diluted enzyme at pH 5.0 for 60 min at 50°C. The concentration of reducing sugars formed was determined by dinitrosalicylic acid (DNSA) method . Avicelase (exoglucanase) activity was measured by incubating 0.5 ml of crude enzyme dilute with 2.5% (w/v) Avicel in 50 mM citrate buffer (pH 5.0) for 60 min at 50°C. One unit of FPase activity and avicelase activity is measured as the amount of enzyme required to release 1 μg of glucose per min. Endoglucanase (CMCase) activity was measured by incubating 0.5 mL of diluted enzyme with 0.5 mL of 2% (w/v) CMC in 50 mM citrate buffer (pH 5.0) for 30 min at 50°C. Finally, xylanase activity was measured by incubating 0.5 mL of diluted enzyme with 0.5 mL of 1% (w/v) birchwood xylan in 50 mM citrate buffer (pH 5.0) for 30 min at 50°C. The concentration of reducing sugars formed in the above assay experiments were determined as described above. The amount of enzyme required for liberating either 1 μg of glucose or 1 μg of xylose per minute under the above assay conditions was considered as one unit of CMCase or xylanase activity. β-Glucosidase assay was performed by incubating 0.2 mL of enzyme dilute and 0.2 mL of 0.01 M PNPG and 1.6 mL of 50 mM citrate buffer (pH 5.0) for 30 min at 50°C. Then, the reaction was stopped by the addition of 4 mL of 0.2 M NaOH-glycine buffer (pH 10.6) . The amount of enzyme required for liberating 1 μg p-nitrophenol per minute was considered as one unit of β-glucosidase activity. All the assay experiments were carried out either voiding enzyme or substrate and were used as control. Enzyme activities were also determined for commercial enzymes (Celluclast 1.5 L and Novozyme 188) following the similar method described above. FPase and endoglucanase activities were measured for Celluclast 1.5 L, and β-glucosidase activity was measured for Novozyme 188. The mean values from triplicate experiments were calculated and presented here.
Native PAGE for zymographic analysis
Native PAGE using concentrated enzyme solution from RS-, BG-, and cellulose-grown culture extracts was performed. Zymogram analysis for the identification of avicelase, CMCase, xylanase, and β-glucosidase isoforms was done. CMCase and xylanase active protein bands were detected separately on a 10% (w/v) separating gel with 2% (w/v) CMC and 2% (w/v) birchwood xylan substrates, respectively. Congo red dye staining method was used for the detection of zone of clearance by the enzymatic action of CMCase and xylanase proteins. Briefly, gel was loading with 30 μg of crude enzyme sample obtained from RS-, BG-, RSBG-, and cellulose-grown cells. After running electrophoresis, the gel was incubated in 50 mM sodium citrate buffer (pH 5.0) for 60 min at 50°C and then stained with 0.1% (w/v) Congo red solution for 20 min. The gels are washed with 1 M NaCl to visualize the clear bands corresponding to the cellulase and hemicellulase active proteins. The developed gels were visualized and digitally imaged using gel documentation system (G-BOX, Syngene, Bengaluru, Karnataka, India). Whereas, avicelase and β-glucosidase enzyme proteins were identified separately with post-incubation of the gel either with 10 mM MUC or 10 mM MUG for 15 to 60 min at 37°C and was then viewed directly under UV light using gel documentation system. It is to be noted that the highly active proteins were initially detected as a clear band as soon as the dye reagent was added and were turned into dark color immediately after addition of developing agent. Whereas, at this staining period the less active protein bands were detected as clear white bands against dark background. Based on the mobility of the protein bands on the gel, the different enzyme active bands were labeled separately on each gel from top to bottom.
Pretreatment of lignocellulosic biomass residues
Mild-alkali and dilute-acid pretreatments were performed separately with 0.2 kg of the respective dried biomass. Alkali pretreatments were done at room temperature with 0.5% NaOH at a solid-to-liquid ratio of 1:20 for 24 h following the optimized conditions that was reported recently by us [12,13], while acid pretreatments were conducted at 121°C for 10, 30, and 60 min by incubating the biomass residues with 1.5% H2SO4 at a solid to liquid ratio of 1:10. After both pretreatments, the biomass residues were neutralized to pH 7.0 and washed thoroughly with distilled water until the residual glucose concentrations were <0.1 g L−1. The pretreated biomass residues were stored in air-tight containers and kept at 4°C until use.
All the enzymatic hydrolysis experiments were performed at 10% (w/v) solid loading at 45°C for 48 h in 50 mL screw-capped bottles. Based on our recently reported enzyme optimization studies, an enzyme loading of 9 FPU g−1 was selected in the current investigation [12,13]. All other experimental parameters were similar as detailed previously, unless specified. Control experiments were performed voiding both substrate and enzyme in the reaction mixtures. Enzymatic saccharification was also performed using commercial enzymes at an enzyme loading of 9 FPU of Celluclast 1.5 L and 100 U of Novozyme 188 per gram of pretreated biomass. After enzymatic saccharification, the liquefied fraction was separated and clarified from the residual biomass by filtration method using glass fiber membrane filters. Reducing sugars were analyzed by both HPLC and DNSA methods. Saccharification yields were calculated as described by Taniguchi .
Enzyme formulation and cellulase cocktail preparation
Before the experimental setup, the crude cellulases obtained from RS- and BG-grown cells were physically premixed to a final 9 FPU g−1 in a ratio of RS25:BG75, RS50:BG50, and RS75:BG25, respectively. Saccharification experiments were also performed with three different formulated cellulase enzyme cocktails. All other parameters of saccharification process were not altered and maintained similar as described in the above section.
Protein concentration was determined using BSA as standard following the method described by Bradford . The contents of cellulose, hemicellulose, and lignin in the untreated and pretreated biomass residues were determined following the method described by Goering and Van Soest . All the assay experiments were carried out in triplicates, and the mean values are given. Statistical analysis of the enzyme activities and saccharification yields was performed using ANOVA software, and the significance of difference in each data was denoted in superscripts by special characters. All the data presented in this study were the mean of three or more experiments with a variation within 10%.
Results and discussion
Aspergillus sps were reported to utilize a broad range of lignocellulosic biomass residues for microbial growth and production of cellulose-degrading enzymes . Also, the cellulase enzymes produced from A. terreus were highly active at low pH conditions and thermotolerant; thus it is a potential microbial source for hyperproduction of a broad range of cellulases for cellulose breakdown, especially towards enzymatic saccharification processes and bioethanol production. These cellulase active proteins form a synergetic network of complex biochemical mechanisms.
Microbial cellulase production
The cellulase and hemicellulase enzyme activities in the tested growth carbon substrates were found to gradually increase with the incubation time and reached maximum on the 7th day. Similarly, secretion of extracellular soluble proteins was also linearly increased with the growth incubation time irrespective of growth carbon substrate, and maximum concentration of proteins were found in the BG- (32.8 ± 2.2 g L−1), followed by RS- (22.9 ± 1.8 g L−1) and cellulose- (20.2 ± 1.3 g L−1) grown cultures, respectively.
Filter paper activity
Total cellulase (FPase) activity (FPU g−1) in the crude extract was found to be maximum in BG-grown culture (5.74 ± 0.3), followed by RS- (4.62 ± 0.4) and cellulose- (1.96 ± 0.3) grown cultures, respectively (Figure 1). Nearly a threefold increase in FPase activity in BG-grown culture extract and approximately fivefold with the mixed (RS-BG) growth substrates were obtained when compared to cellulose-grown extract (Table 1). The FPase activities in the culture extracts of the RS75:BG25-, RS50:BG50-, and RS25:BG75-mixed growth substrates were 6.3 ± 1.1, 11.34 ± 0.7, and 10.22 ± 0.7, respectively (Figure 1). Although the FPase activities were comparatively higher in the RS75:BG25 growth culture extract, higher BG content in the mixed growth substrate produced effective cellulase components in the enzyme cocktail that enhanced the total cellulase activity. Recently, it is reported that FPase activity of 1.02 and 3.2 U ml−1 was obtained with A. fumigates NIYDGPKA3  and A. heteromorphus  using rice straw and wheat straw biomass residues as growth residues. The FPase activities presented in our study were significantly higher than other reports. A brief comparison was made with other reported cellulases and xylanases and their activities from Aspergillus strains and is given in Table 2.
In similar to FPase, the exoglucanase (Ex) activities (U g−1) were also found to be maximum in the BG-grown culture (10.5 ± 0.3) with a twofold increase in enzyme activity followed by RS- (6.86 ± 0.3) and cellulose-(5.32 ± 0.3) grown cultures, respectively (Figure 2). However, with the mixed RS-BG growth substrates, the exoglucanase activities were comparable with the BG-grown culture. Whereas, in contrary to the findings on enzyme activities in different growth substrates, zymogram studies showed that cellulose substrate induced more number of exoglucanase proteins compared to BG- and RS-biomass substrates (Figure 3). In cellulose-grown culture, two high molecular proteins (Ex1 and Ex2) and one low molecular protein (Ex3) with exoglucanase activity were detected (Figure 3C). Whereas, Ex2 protein band in RS-grown culture and Ex3 protein band in BG-grown culture were not detected. Similar to RS-grown culture, both Ex1 and Ex3 protein bands were observed in RSBG-grown culture (Figure 3D). Among these protein bands, Ex1 protein showed high intensity in RS- and BG-grown culture extracts, while Ex3 in cellulose-grown culture was highly intense. Correlating both zymogram and enzyme activity analysis, it is clearly evident that majority of the exoglucanase activity might be associated with these high intense bands of their respective growth substrate. Detailed molecular and biochemical investigation on characterization of these individual exoglucanase active protein bands will provide further insight into the functional properties of the enzyme isoforms.
The endoglucanase activity (U g−1) in BG-grown culture extract was significantly higher (145.32 ± 2.5) than the RS- (96.6 ± 1.1) and cellulose- (62.44 ± 1.3) grown cultures, respectively (Figure 4). The enzyme activities were approximately 1.5- to 2-fold higher in BG compared to other growth carbon substrates. Similar to FPase, the endoglucanase activities were also increased in the all the RSBG-mixed growth cultures. The enzyme activities were 159.32 ± 1.7, 213.22 ± 0.3, and 203.42 ± 2.2 in RS75:BG25-, RS50:BG50-, and RS25:BG75-grown culture extracts, respectively (Figure 4). Jecu  also used mixed substrates (wheat straw and wheat bran) for cellulase production by A. niger; however, the endoglucanase activity was only 11.25 U ml−1, which is very low compared to our mixed growth substrates. Five endoglucanase proteins in BG- (Eg1, Eg2, Eg3, Eg5, and Eg6) and four each in cellulose- (Eg2, Eg3, Eg4, and Eg5) and RS- (Eg1, Eg2, Eg3 and Eg5) grown cultures, respectively, were detected by zymogram analyses (Figure 5). However, protein bands corresponding to Eg1 and Eg6 in cellulose-grown culture, Eg4 in BG- and RS-grown cultures and Eg4 and Eg5 in RSBG-grown cells, were not detected. These results indicate that BG induced production of additional endoglucanase proteins compared to RS-and cellulose-grown substrates. Sequential expression of multiple endoglucanase and β-glucosidase isoforms in different culture conditions and carbon sources was also recently reported in A. terreus; where, addition of fructose and cellobiose upregulated the endoglucanase activity while addition of mannitol, ethanol, and glycerol selectively repressed three endoglucanase isoforms . Similarly, in Hypocrea jecorina, sophorose was reported to induce selective expression of endoglucanses and one xylanase isoform where xylobiose specifically induced xylanase I and xylanase II proteins .
In contrary to the other cellulase activities, high β-glucosidase activity (U g−1) was obtained in both RS- and BG-grown culture extracts (75.18 ± 1.4) (Figure 6). Whereas, in cellulose-grown culture extract, negligible amount of β-glucosidase activity (1.01 ± 0.02) was observed, indicating that cellulose repressed production of β-glucosidase. Unlike other cellulase activities, β-glucosidase activities were not affected with the type of growth substrate. In RSBG-grown culture extracts, the enzyme activity was nearly similar (69.14 ± 1.5) in all the tested substrate ratios (Figure 6). Our results were in close comparison to A. fumigatus, where 80.1 U ml−1 β-glucosidase was obtained . Very recently, a newly isolated A. terreus strain EMOO 6-4 showed a maximum β-glucosidase activity of 4457.162 U g−1 using rice straw under statistically optimized growth conditions . The enzyme activity results were also supported by the zymogram studies. A single broad protein band (Bg1) was detected in cellulose-grown cells, whereas, two additional proteins (Bg2 and Bg3) were detected in BG- and only Bg3 in RS-grown culture extracts (Figure 7). Similar to RS-grown culture, RSBG-grown extracts produced only Bg1 and Bg3 proteins. Apparently, the slightly higher β-glucosidase activity in BG-grown extract could be correlated with the additional Bg2 protein. In contrary to the induction of endoglucanase expression in A. terreus; glucose, fructose, sucrose, cellobiose, mannitol, and glycerol addition also resulted in the repression of few β-glucosidase isoforms .
Xylanase activities (U g−1) in BG-grown culture extract (8,472 ± 490) was approximately twofold higher than the RS-grown extracts (3,921 ± 406) and approximately fivefold higher than cellulose-grown extracts (1,763 ± 251) (Figure 8). Interestingly, the xylanase activities were increased linearly with the amount of BG content. The enzyme activities in RSBG-grown culture extracts were 6,050 ± 294, 6,959 ± 252, and 7,280 ± 462 from RS75:BG25-, RS50:BG50-, and RS25:BG75-grown culture extracts, respectively (Figure 8). It is recently reported that a newly isolated A. terreus RWY produced xylanase activity of 872 U g−1 when sorghum bagasse was tested under solid-state conditions . Significantly lower xylanase activity obtained from cellulose growth culture in correlation with the zymogram studies found that it could be due to the poor expression of xylanase active proteins. Only two xylanase proteins (Xy2 and Xy3) were detected in cellulose growth culture extract while additional proteins viz. Xy1, Xy4, and Xy5 in RS- and Xy1 and Xy5 in BG-grown culture extracts were detected (Figure 9). Although four xylanase proteins were detected in RS- and BG-grown extracts, however, a high molecular weight protein (Xy3) in RS-grown extract and a low molecular weight protein (Xy4) in BG-grown extract were not detected. In contrary to cellulase enzyme variants, all the xylanase enzymes were detected when RSBG-mixed growth culture extract was used in the growth medium (Figure 9D). From zymogram analysis and xylanase assay activity measurements, we could infer that the low intense protein (Xy3) might be crucial for enhancing the overall xylanase activity in the BG-grown culture extract. Our results on the identification of various xylanases from RS-, BG-, cellulose-, and RSBG-grown culture extracts also correlate with the earlier reports on the expression of distinct enzyme isoforms with the culturing conditions, where production of different multiple xylanases in Myceliopthora sps  and exoglucanases in A. niger  is detected.
From our results, it is clearly evident that the expression and repression of cellulase and hemicellulase genes in A. terreus D34 varied with the type of growth carbon source. This may be mostly due to the structural difference and architecture of the carbon source that play a crucial role in differential expression of the cellulolytic enzymes . In addition to the culture conditions, small molecules and metabolites were also found to affect the production of cellulase enzymes in microbes like Aspergillus sps [25,32]. However, it is not clearly understood how the expression of these multiple proteins is regulated at gene level and further detailed molecular and proteomic analysis will provide the mechanism on the metabolic role of cell-bound regulatory proteins and the cell-substrate interactions. But to some extent, it was reported that the regulation of cellulases was mediated by induction and repression of the genes that control the expression of cellulose-degrading enzymes [33,34]. Such studies on multiple and differential expression of cellulase and hemicellulase enzymes and the corresponding enzyme activities in the culture extracts from different growth carbon substrates will produce an effective cellulase enzyme cocktail with all the cellulase enzyme components in a single mixture. The mechanism of expression and repression of each enzyme variant is under the control of a complex metabolic process, and this could be mostly due to the production and accumulation of various extracellular metabolites in the culture medium and their continuous interactions with the membrane transporter proteins . Thus, it triggers the secretion of cellulose-degrading proteins into the extracellular medium during microbial growth on a specific lignocellulosic biomass residue . For example, our experimental results showed nearly twofold higher xylanase activity in BG- than RS-biomass residues and may be correlated with high hemicellulose content present in the BG biomass that may induce the secretion of additional xylanase active proteins. From zymogram and enzyme activity studies, the induction and repression of each enzyme variant and their probable correlation with the enzyme activities as discussed in this report strongly suggest the significant effect of biomass on the corresponding enzyme activities and was clearly demonstrated in Table 1. As shown in the case of exoglucanase, although Ex3 was not produced in BG-grown culture extract, the exoglucanase activity was significantly higher than the RS- and cellulose-grown extracts, indicating that the total exoglucanase activity was primarily from the Ex1 protein with no major contribution from Ex3 protein and was also clearly evident from the detection of a high intense sharp exoglucanase active protein band in zymographic analysis. Similarly, the role of Eg4 protein in endoglucanase activity could also support this inference. Moreover, the presence of Bg3 protein is crucial for increased β-glucosidase activity. This conclusion was made on the observations with cellulose growth extract where Bg3 protein was not detected and a fourfold decrease in β-glucosidase activity was obtained. Also, the correlation data between xylanase activity and two low molecular xylanase isoforms (Xy4 and Xy5) strongly supports our results.
Pretreatment of lignocellulosic biomass residues
Delignification of RS biomass by mild-alkali pretreatment method increased the cellulose content from 40.0% ± 1.8% to 60.1% ± 1.2% with a marginal loss of hemicellulose content (28.0% ± 2.0% to 19.2% ± 1.6%). The cellulose availability was slightly higher after mild-alkali treatment. Interestingly, more than 70% of lignin was removed after mild-alkali pretreatment (Table 3). While after acid treatment, the holocellulose (mainly cellulose content) in the pretreated RS-biomass residue was increased to 76.8% ± 1.1% with nearly complete removal of hemicellulose (1.3% ± 0.23%). Moreover, similar results were also obtained with BG biomass after both pretreatment methods. The cellulose content of BG after mild-alkali treatment was increased from 35.1% ± 2.1% to 49.9% ± 1.2% with hemicellulose content of 25.2% ± 1.6%. Although the holocellulose content was comparatively lower after acid pretreatment (55.2% ± 1.4%), similar to RS, the hemicelluloses (1.6% ± 0.9%) in BG were completely removed. Comparative amount of lignin was removed by mild-alkali treatment in the biomass residues while majority of the lignin content was retained after dilute-acid pretreatment (Table 3).
Enzymatic hydrolysis of pretreated biomass
Saccharification efficiency (%) from mild-alkali pretreated RS-biomass residue was found to be 82.8 ± 1.0, 79.3 ± 1.2, and 73.0 ± 2.0 using crude concentrated cellulase mixture obtained from the RS-, BG-, and RSBG-grown culture extracts, respectively. With mild-alkali pretreated BG-biomass residue, the saccharification yields were comparatively lower (37.1 ± 2.1, 52.4 ± 1.9, and 59.3 ± 1.7), where approximately 59% higher saccharification yields were obtained with enzyme obtained from RSBG culture extract. Similarly, with acid treated RS biomass, maximum reducing sugars were obtained with RSBG-grown culture extracts followed by RS-grown extract and vice versa when acid treated BG biomass was used for saccharification. However, with Celluclast 1.5 L, the saccharification yields reached up to 93.3 ± 0.7 and 82.1 ± 0.4 with mild-alkali treated RS- and BG-biomass residues and 52.9 ± 0.5 and 49.0 ± 1.7 were obtained with acid treated RS- and BG-biomass residues, respectively. While with mixed Celluclast 1.5 L and Novozyme 188, the saccharification yields reached maximum and were 96.5 ± 0.3 and 88.3 ± 0.4 with mild-alkali treated RS- and BG-biomass residues and 74.5 ± 0.9 and 54.2 ± 1.0 with acid treated RS- and BG-biomass residues, respectively. The synergetic affect of β-glucosidase in enhancing reducing sugar production from the pretreated biomass residues is clearly evident from these results. Moreover, the RS-grown culture extract enzyme produced reducing sugars which are nearly comparable with the commercial enzyme, Celluclast 1.5 L. Detailed reducing sugar concentrations and corresponding saccharification efficiencies of the respective pretreated biomasses and their enzyme sources were given in Table 4. Interestingly, saccharification studies with the formulated enzyme cocktails showed slightly lower efficiencies for both alkali and acid treated biomass residues when compared with the crude cellulase enzymes from individual growth carbon sources (Additional file 1 Supplementary Table S1). With alkali treated RS- and BG-biomass residues, the maximum saccharification yields obtained with the formulated enzymes were 57.0 ± 1.8 and 42.5 ± 1.7, respectively. Whereas, with acid treated RS- and BG-biomass residues, the maximum saccharification yields were 44.2 ± 1.4 and 21.5 ± 1.9, respectively. A comparison data of enzymatic hydrolysis of alkali and acid treated rice straw along with alkali and acid treated sugarcane bagasse was detailed in supplementary Table 2.
Beside zymogram studies of enzyme variants, interesting observations were made during this investigation and showed that nearly 1.25- and 2.5-fold increase in FPase, exoglucanase, endoglucanase, and xylanase activities were obtained with BG- and RS50:BG50-grown culture extracts when compared to RS-grown culture. Since these enzymes are known to be used in a wide variety of industrial applications, this may be an important factor to consider for large-scale production of enzymes and may significantly reduce the capital expenditures towards handling large capacity of biomass residues, reactor vessel volumes, and downstream processing costs, etc. . However, for bioethanol production, the saccharification efficiencies with the isolated enzymes from RS-grown culture extracts were marginally higher compared to the RSBG-mixed growth culture extracts but at a fixed enzyme loading of 9 FPU/g biomass; the volume of protein required was significantly low (on the basis of respective enzyme activities shown in Table 1), where, in order to obtain the same enzyme loading, nearly twofold of the enzyme was required for RS-grown culture extract.
Similarly, most of the commercially available cellulase enzymes are formulated cocktails and there is a continuous thrust towards the development of efficient cellulase enzyme mixtures prepared by physical mixing of subtle amounts of other cellulose-degrading enzyme components for synergistic action and high product yields at low enzyme loadings. Formulation of cellulase enzyme activities for saccharification process will not only reduce the total enzyme loadings and but also decrease the capital expenditure costs (as described above) in a cellulosic biofuel production. Moreover, adding requisite amounts of enzyme components that were deficient in the cocktail mixture may further improve the overall process efficiency. It was clearly evident from the high saccharification yields of pretreated biomasses that using commercial enzymes were mainly attributed due to the external supplementation of β-glucosidase. All together, optimization of each enzyme component is attractive for lowering enzyme loadings; preparing such type of complex mixtures is quite challenging. Because it generally requires the separation of a particular enzyme component from the broth and re-addition into the cocktail which is considered to be one of the costly process , attempts were made to overcome such challenges in the preparation of formulated cellulase cocktails by physical mixing of crude enzymes and optimizing the growth carbon substrates, separately resulted in the production of an efficient enzyme mixture with at least twofold higher cellulase activities. Thus, it was concluded that crude cellulose-degrading enzymes produced by the A. terreus D34 with mixed growth substrates produced efficient crude enzyme mixture with the required enzyme components in appropriate proportions to yield high reducing sugars. These studies provide a clear evidence of the production of multiple cellulase proteins and their correlation with the corresponding enzyme activities with a complex synergetic mechanism for combined action between the enzyme components for effective lignocellulosic breakdown.
In the present study, we have demonstrated that during microbial growth, addition of BG-biomass residue to the RS-biomass residue enhanced the production of multiple cellulases and hemicellulases. Whereas, in RS-biomass residue and cellulose substrates, A. terreus was deficient in producing some cellulose-degrading enzymes that were found to be critical in increasing the overall enzyme activity. We further suggest that RSBG-mixed growth substrate could be a potential growth carbon source for cost-effective production of cellulases at a larger scale. Moreover, using RS-grown culture extract enzymes, saccharification yields of up to 82.8% ± 1.0% were obtained from mild-alkali treated RS biomass and with mild-alkali treated BG biomass, up to 59.3% ± 1.7% were obtained using RS50:BG50-grown culture extract enzymes.
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The authors are thankful to the Director, Sardar Patel Renewable Energy Research Institute, Gujarat, India, for the support of this research. The research work is financially supported by DBT, Govt. of India, through grant BT/PR10103/PBD/26/131/2007 and ICAR, Govt. of India. The authors acknowledge helpful discussions with Dr. S.P. Singh, SPRERI, and Prof. Datta Madambar, BRD School of Biosciences, Sardar Patel University, Gujarat, India.
The authors declare that they have no competing interests.
BSP performed the research experiments; AKK designed the research and wrote the paper. Both authors read and approved the final manuscript.
AKK, is a Senior Scientist and BSP is a Technical Assistant at the Sardar Patel Renewable Energy Research Institute, Bioconversion Technology Division, near BVM Engineering College, Vallabh Vidyanagar, Gujarat, India.
Enzymatic saccharification of mild-alkali and dilute-acid pretreated lignocellulosic biomass residues at 10% solid loading and enzyme loadings# of 9 FPU/g substrate using crude cellulase enzymes and formulated enzyme cocktails.
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Kumar, A.K., Parikh, B.S. Cellulose-degrading enzymes from Aspergillus terreus D34 and enzymatic saccharification of mild-alkali and dilute-acid pretreated lignocellulosic biomass residues. Bioresour. Bioprocess. 2, 7 (2015). https://doi.org/10.1186/s40643-015-0038-8
- A. terreus
- Multiple expression
- Lignocellulosic biomass