- Research article
- Open Access
Characterization of hemicellulase and cellulase from the extremely thermophilic bacterium Caldicellulosiruptor owensensis and their potential application for bioconversion of lignocellulosic biomass without pretreatment
Biotechnology for Biofuels volume 8, Article number: 131 (2015)
Pretreatment is currently the common approach for improving the efficiency of enzymatic hydrolysis on lignocellulose. However, the pretreatment process is expensive and will produce inhibitors such as furan derivatives and phenol derivatives. If the lignocellulosic biomass can efficiently be saccharified by enzymolysis without pretreatment, the bioconversion process would be simplified. The genus Caldicellulosiruptor, an obligatory anaerobic and extreme thermophile can produce a diverse set of glycoside hydrolases (GHs) for deconstruction of lignocellulosic biomass. It gives potential opportunities for improving the efficiency of converting native lignocellulosic biomass to fermentable sugars.
Both of the extracellular (extra-) and intracellular (intra-) enzymes of C. owensensis cultivated on corncob xylan or xylose had cellulase (including endoglucanase, cellobiohydrolase and β-glucosidase) and hemicellulase (including xylanase, xylosidase, arabinofuranosidase and acetyl xylan esterase) activities. The enzymes of C. owensensis had high ability for degrading hemicellulose of native corn stover and corncob with the conversion rates of xylan 16.7 % and araban 60.0 %. Moreover, they had remarkable synergetic function with the commercial enzyme cocktail Cellic CTec2 (Novoyzmes). When the native corn stover and corncob were respectively, sequentially hydrolyzed by the extra-enzymes of C. owensensis and CTec2, the glucan conversion rates were 31.2 and 37.9 %,which were 1.7- and 1.9-fold of each control (hydrolyzed by CTec2 alone), whereas the glucan conversion rates of the steam-exploded corn stover and corncob hydrolyzed by CTec2 alone on the same loading rate were 38.2 and 39.6 %, respectively. These results show that hydrolysis by the extra-enzyme of C. owensensis made almost the same contribution as steam-exploded pretreatment on degradation of native lignocellulosic biomass. A new process for saccharification of lignocellulosic biomass by sequential hydrolysis is demonstrated in the present research, namely hyperthermal enzymolysis (70–80 °C) by enzymes of C. owensensis followed with mesothermal enzymolysis (50–55 °C) by commercial cellulase. This process has the advantages of no sugar loss, few inhibitors generation and consolidated with sterilization.
The enzymes of C. owensensis demonstrated an enhanced ability to degrade the hemicellulose of native lignocellulose. The pretreatment and detoxification steps may be removed from the bioconversion process of the lignocellulosic biomass by using the enzymes from C. owensensis.
Production of biofuels from the renewable lignocellulosic biomass is gradually considered as a promising way to replacement of fossil fuels. However, its bioconversion has been limited by its hydrolysis because the main components of the lignocellulosic biomass (cellulose, hemicellulose and lignin) are tightly held together and form lignin-carbohydrate complexes (LCC). The lignin-carbohydrate complexes create a barrier for microbial conversion . Conversion of lignocellulosic biomass to fermentable sugars represents a major challenge in global efforts to utilize renewable resources in place of fossil fuels to meet the rising energy demands . Enzymatic hydrolysis is the most common process to degrade the cellulose and hemicellulose into fermentable sugars such as glucose and xylose.
Currently, the high cost of enzymolysis is a major obstacle for production of biofuels at an industrial scale . Exploring the highly efficient cellulase and hemicellulase is attached much attention for reducing the cost of biofuels production. Before enzymatic hydrolysis, pretreatment process is required to break down the rigid association of lignocelluloses, so that the enzymes can easily access the cellulose to hydrolyze into monomers . Pretreatment, such as steam-explosion pretreatment, hydrothermal pretreatment, and acid or alkali pretreatment, allows to change the structure of the lignocellulose, such as increasing the surface area and porosity of biomass, partially removing the hemicelluloses and lignin, and reducing the crystallinity of cellulose . Although pretreatment is efficient for improving the enzymatic hydrolysis of lignocelluloses, it has been viewed as one of the most expensive processing steps in biomass-to-biofuel conversion . Moreover, during pretreatment process some sugars are damaged and converted into furan derivatives (furfural and HMF) and carboxylic acids, which, together with phenol derivatives (from lignin), will inhibit the fermentation process .
Therefore, after pretreatment the detoxification step is essential for improving the fermentation efficiency. The methods of detoxification can be divided into three main groups: biological, physical and chemical , such as using microorganisms or enzymes to change the inhibitors’ chemical structures [9, 10], adsorbing the inhibitors by using activated charcoal  and ion exchange resins , and adding reductive substances  or pH modification [14, 15]. The detoxification process is also costly and many of the detoxification methods result in sugar losses . Can the pretreatment and detoxification be removed from the bioconversion process of lignocellulosic biomass?
Many extreme thermophiles are able to utilize a variety of carbohydrates pertinent to the conversion of lignocellulosic biomass to biofuels. Characterization of the enzymes from these extremely thermophilic bacteria is likely to generate new opportunities for the use of renewable resources as biofuels [16, 17]. Among them, the genus Caldicellulosiruptor, an obligatory anaerobic and extreme thermophile has recently attracted high interest for it can produce a diverse set of glycoside hydrolases (GHs) for deconstruction of lignocellulosic biomass [18–20]. It was reported  that the open Caldicellulosiruptor pangenome encoded 106 glycoside hydrolases (GHs) from 43 GH families. The gene clusters that encode multidomain cellulases or hemicellulases were found in the genome of Caldicellulosiruptor. Many novel heat-stable extracellular enzymes for biomass degradation had been heterogeneously expressed [21–26]. Especially, some enzymes are not only multimodular, but possess catalytic domains with different activities (multifunctional) [19, 27]. They differ from the two general cellulolytic enzymes systems: one with free cellulases and hemicellulases produced by fungi and most bacteria , and the other in which glycosidases self-assemble onto a common protein scaffold to form large macromolecular assemblies called cellulosomes [29, 30]. For example, the cellulase CelA produced from C. bescii, comprises a GH 9 and a GH 48 catalytic domain, could hydrolyze the microcrystalline cellulose not only from the surface as common cellulases done but also by excavating extensive cavities into the surface of the substrate . The major commercial cellulolytic enzymes are currently produced by fungi with free noncomplexed cellulases and hemicellulases . The cellulolytic enzymes from genus Caldicellulosiruptor with different characteristics may be complementary with fungal cellulolytic enzymes on hydrolysis of lignocellulosic biomass, therefore showing potential commercial application value. C. owensensis grows on a wide variety of carbon sources including pentose, hexose, oligosaccharide, and polysaccharide . Comparing of the growth of the seven species of Caldicellulosiruptor (C. bescii, C. hydrothermalis, C. kristjanssonii, C. kronotskyensis, C. lactoaceticus, C. saccharolyticus, C. owensensis) on xylose, the cell density of C. owensensis was only slightly lower than C. saccharolyticus and higher than the other five species . Moreover, the results of analyzing of the diversity of biomass deconstruction-related glycoside hydrolases in Caldicellulosiruptor showed that C. owensensis owned abundant xylan deconstruction-related glycoside hydrolases including the 5, 10, 11, 39, 43, 51 and 67 GH families, which were the total xylan deconstruction-related glycoside hydrolase families in Caldicellulosiruptor . The diversity of the xylan deconstruction-related glycoside hydrolases and the physiological characteristics of C. owensensis showed that it is a promising candidate for hemicelluloses deconstruction.
The hemicellulose is much easier to be enzymatically hydrolyzed than cellulose in the native lignocellulose because the hemicellulose is amorphous. Removing hemicellulose can increase the surface area and porosity of lignocellulose hence improving the access for cellulase to touch with cellulose. The two-step hydrolysis by first using lignocellulolytic enzymes focusing on hemicelluloses deconstruction then hydrolysis by cellulase may be an efficient strategy for avoiding the current pretreatment process for biofuels production. Here we hope that the enzymes of C. owensensis which has the high ability of deconstructing native hemicellulose would be competent to support the two-step hydrolysis strategy.
In this work, the characteristics of hemicellulase and cellulase of C. owensensis cultivated on different carbon sources were assayed. The extra-enzymes and intra-enzymes of C. owensensis were applied to deconstruct lignocellulosic biomasses by themselves or synergetic hydrolysis with the commercial enzyme cocktail Cellic CTec2 (Novoyzmes). The aims are to comprehensively understand the lignocellulolytic enzymes of C. owensensis and develop new enzyme cocktails and enzymatic hydrolysis processes for bioconversion of lignocellulosic biomass.
Results and discussion
Growth and xylanase secretion lines
Selecting a suitable incubation time for C. owensensis is important for assaying its enzymes. The growth and xylanase secretion lines were therefore analyzed at the beginning of this work. Figure 1 shows that regardless of xylose or corncob xylan as carbon source the cell quantity reached the highest after 24 h cultivation. The xylanase activities in the culture supernatant also increased to the peak after 24 h cultivation. The cell quantity by xylose was higher than that by xylan while the xylanase activity was reverse. It seems that xylose is more benefit for biomass accumulation while xylan can induce a higher xylanase secretion. The enzymes produced after 24 h cultivation were used in the following experiments.
Characteristic of cellulase and hemicellulase from C. owensensis
The culture supernatants and cells were separated by centrifugation after 24 h cultivation. The extra-enzyme and intra-enzyme C. owensensis were respectively obtained after precipitation of the protein in supernatant by ammonia sulfate and breaking the cell wall by sonication. The hemicellulase (xylanase/Xyan, beta-xylosidase/pNPX, arabinofuranosidase/pNPAF, xylan esterase/pNPAC) and cellulase (endoglucanase/CMC, cellobiohydrolase/pNPC, beta-glucosidase/pNPG, filter paper activity/FPA) activities were measured.
Table 1 shows that no matter cultivated on xylose or corncob xylan both the extra-enzyme and intra-enzyme of C. owensensis had hemicellulase and cellulase activities. Hemicellulase and cellulase are not essential for cell growth and usually considered as the induced enzymes. However, the result of this experiment indicates that substrate inducing is not necessary for C. owensensis on hemicellulase and cellulase secretion. Maybe some genes for such enzymes share the promoters of the constitutive enzyme and are expressed during cell growth. On the whole, the hemicellulase activities cultivated on corncob xylan were higher than those on xylose. For example, the xylanase activities of extra-enzyme and intra-enzyme on corncob xylan were, respectively, 4.72 and 1.57 U/mg, while those on xylose were, respectively, 1.93 and 0.19 U/mg. However, the cellulase activities of the enzymes on corncob xylan and on xylose were varied slightly. This is possibly because both xylose and xylan are not the inducing substrates for cellulase secretion.
Table 1 also shows that the activities of extra-enzyme and intra-enzyme were different. The extra-enzyme had higher xylanase and endoglucanase activities, while the intra-enzyme had higher β-d-xylosidase, β-d-glucosidase and arabinofuranosidase activities. Especially, the β-d-glucosidase activity of intra-enzyme on corncob xylan was about 125-fold higher than that of the extra-enzyme (532.4 mU/mg VS 4.2 mU/mg). This indicates that for degrading the lignocellulosic biomass by C. owensensis the main function of the extra-enzyme is to cleave the polysaccharides to oligosaccharides, while further hydrolysis of xylobiose and cellobiose takes place mainly in cell by intra-enzyme.
Comparing with the thermophilic fungi Thermoascus aurantiacus and Thielavia terrestris which were recently reported to be high cellulase producers , the hemicellulase activities of C. owensensis were higher than those of fungi (Table 1, the highest activities of each enzyme were used as the results for discussing). With regard to the cellulase, it showed that although the endoglucanase activity of C. owensensis was much lower than those of fungi, the cellobiohydrolase activity was almost the same as those of the fungi and the β-d-glucosidase activity was much higher than those of fungi. Three enzymes, endoglucanases, exoglucanases and β-d-glucosidases, compose the cellulase system functions in a coordinated manner for degradation of cellulose into glucose units . Since most glucanases are inhibited by cellobiose and short cellooligosaccharides, β-d-glucosidases catalyze the rate limiting step of the cellulose hydrolysis process as a whole . Filamentous fungi are the major source of commercial cellulases. Commercial cellulase preparations are mainly based on mutant strains of T. reesei which have usually been characterized by a low secretion of β-glucosidase . Thus, T. reesei cellulase preparations had to be supplemented with added β-glucosidase to provide the more efficient saccharification of cellulosic substrates [32, 37]. The enzyme system of C. owensensis with high hemicellulases and β-d-glucosidase activities may complement with the fungi cellulase for deconstruction of native lignocellulose.
To identify the protein components in extra- and intra-enzymes of C. owensensis cultivated on corncob xylan, the proteins were analyzed with HPLC/MS. More than 100 and 150 kinds of proteins were identified in the extra- and intra-enzymes respectively. Enzymes related to polysaccharide degradation were shown in Table 2. The extra-enzymes include β-xylanase (Calow_0121, Calow_1924), β-galactosidase (Calow_2098), α-N-arabinofuranosidase (Calow_0926), polysaccharide deacetylase (Calow_2141), pectate disaccharide-lyase (Calow_2109), esterase (Calow_1899), α-l-fucosidase (Calow_1765), α-amylase (Calow_0101 and Calow_0294), pullulanase, type I (Calow_0483) and a glycoside hydrolase belong to family 28 (Calow_2114). The intra-enzymes include the glycoside hydrolases belong to family 18 (Calow _2166), family 31 (Calow_1739), family 43 (Calow_2016, Calow_0925), family 4 (Calow_1700) and family 20 (Calow_0048), pullulanase, type I (Calow_0282, Calow_0483), arabinogalactan endo-β-1,4-galactanase (Calow_0481) and α-l-fucosidase (Calow_1754). Although the cellulase were not identified, the enzymes belong to different GH families might have multi-activity, including cellulolytic activity. Besides these enzymes related to polysaccharide degradation, the extra-enzymes related to carbohydrate metabolism were also identified and shown in Additional file 1, including glycosyltransferase, extracellular solute-binding protein, ATP-binding cassette (ABC) transporter-related protein, and S-layer domain-containing protein. They gave useful information for further research on carbohydrate hydrolysis and metabolism of C. owensensis.
Hydrolysis of lignocellulosic biomass by enzymes of C. owensensis
The enzymes of C. owensensis were used to hydrolyze native corn stover, native corncob and steam-exploded corn stover with the loading rate of 15 mg enzyme per gram dry substrate at 70 °C for 48 h. The experiment was performed in three groups respectively using extra-enzyme, intra-enzyme and extra-enzyme mixed with intra-enzyme at the ratio of 1:1. The data in Table 3 show that the enzyme of C. owensensis had high ability of degrading hemicellulose. The highest conversion rates of xylan on native corn stover, native corncob and steam-exploded corn stover were respectively 14.7, 16.8 and 59.1 %. Moreover, the conversion rates of araban on native corn stover and native corncob reached 53.5 and 60.0 %, respectively. However, the enzyme of C. owensensis was not such perfect at degrading cellulose. As Table 3 shows the glucose can not be detected after hydrolysis of both native corncob and steam-exploded corn stover for 48 h. This may because the endoglucanase in the enzyme of C. owensensis was weak (shown in Table 1). Blumer–Schuette et al.  analyzed the core genomes, pangenomes, and individual genomes and predicted that the ancestral Caldicellulosiruptor was likely cellulolytic and evolved, in some cases, into species that lost the ability to degrade crystalline cellulose while maintaining the capacity to hydrolyze amorphous cellulose and hemicelluloses. The results in this experiment were in accord with the prediction.
As described in the section of characteristic of cellulase and hemicellulase, the xylanase was mainly existed in the extra-enzyme of C. owensensis while the β-d-xylosidase and arabinofuranosidase were mainly existed in the intra-enzyme of C. owensensis. The extra-enzyme and the intra-enzyme may have synergetic function for hemicellulose hydrolysis. For each substrate, extra-enzyme mixed with intra-enzyme contributed higher levels of xylose releasing than those by extra-enzyme and intra-enzyme respective hydrolysis. However, the extra-enzyme led to the highest reducing sugar releasing, indicating that the xylanase, with the function of cleaving the xylan to xylo-oligosaccharides and xylose, is the most important enzyme for xylan degradation.
The morphology changes induced by hydrolysis with the extra-enzyme of C. owensensis were examined by SEM to provide direct insight into the structure modification in the native corn stover. Before hydrolysis, the vascular bundle and the epidermis (with stoma and epidermal hair, Fig. 2a, b) of the samples were intact. After hydrolysis, the residual corn stover was changed dramatically (Fig. 2c, d); the initial structure was destroyed and replaced by a collapsed and distorted cell wall structure. The cuticle waxy layer appeared to be almost desquamated, and the microfibrils were exposed to the surface. Clearly, the structure of the native corn stover was greatly changed in appearance after hydrolysis. Figure 2e, f shows the images of the corn stover after incubation in the acetate buffer at 70 °C for 48 h as control. When comparing with the initial corn stover (Fig. 2a, b), the acetate-buffer-incubated corn stover was slightly changed with some fissures in the sample. The acetate-buffer incubation cannot make much change for the biomass structure was proved by the hydrolysis experiment: The acetate-buffer-incubated corn stover and corncob and the samples without incubation were hydrolyzed by CTec2 (Novoyzmes) at 50 °C for 72 h. As a result, the sugar yields of the buffer-incubated samples and the corresponding samples without incubation were almost the same. The glucan conversion rates (%) were as follows: incubated corn stover 18.1 ± 1.7, corn stover without incubation 17.9 ± 1.5, incubated corncob 20.1 ± 1.6, corncob without incubation 20.4 ± 1.9.
Synergetic hydrolysis by the enzymes of C. owensensis and CTec2
Two trials were performed for synergetic hydrolysis by the enzymes of C. owensensis cultivated on corncob xylan and the commercial enzyme cocktail Cellic CTec2 (Novoyzmes). One was that the native corn stover and corncob were sequentially hydrolyzed (SH) by the enzymes of C. owensensis at 70 °C for 48 h then added CTec2 and incubated at 50 °C for 72 h. The other was that these lignocellulosic biomasses were co-hydrolyzed (CH) by the enzyme of C. owensensis and CTec2 at 50 °C for 72 h. The loading rates of CTec2 (http://www.bioenergy.novozymes.com/) for synergetic hydrolysis were 30 mg/g glucan (High loading). These lignocellulosic biomasses were hydrolyzed by CTec2 only at 50 °C for 72 h as controls.
Figure 3 shows that after sequential hydrolysis (SH) on native corn stover and native corncob by extra-enzyme and CTec2, the conversion rates of glucan were 31.2 and 37.9 %, which respectively were 1.7- and 1.9-fold of each control (hydrolyzed by CTec2 only). Using the same loading (high loading, 30 mg enzyme/g glucan) of CTec2 for hydrolysis of the steam-exploded (SE) corn stover and SE corncob the glucan conversion rates were 38.2 and 39.6 %, respectively (Fig. 4a), which were not much higher than glucan conversion rates of the native corn stover and corncob sequentially hydrolyzed (SH) by the enzyme of C. owensensis and CTec2. The glucan conversion rates of native corn stover and corncob by SH were respectively 81.7 % and 95.7 % of those of the SE corn stover and SE corncob hydrolyzed by CTec2 (Fig. 4b). It seems that in this experiment, the hydrolysis by the extra-enzyme of C. owensensis made almost the same contribution as steam-exploded pretreatment for glucan degradation from native lignocellulosic biomass. Sequential hydrolysis by the extra-enzyme of C. owensensis and CTec2 could greatly increase the hydrolysis rate for native lignocellulosic biomass possibly due to the hemicelluloses degraded by the hemicellulase in extra-enzyme of C. owensensis hence increasing the accessibility of cellulose to CTec2. The cellulases, especially the endoglucanase in the extra-enzyme (shown in Tables 1, 2) would also contribute to improve the cellulose hydrolysis. This is made sure by what Brunecky et al.  have recently reported that pre-digestion of biomass with the cellulases (CelA and endocellulase E1) from extremely thermophilic bacterium C. becsii, and Acidothermus cellulolyticus at elevated temperatures prior to addition of the commercial cellulase formulation increased conversion rates and yields when compared to commercial cellulase formulation alone.
Co-hydrolyzed (CH) by the extra-enzyme of C. owensensis and CTec2 the conversion rates of glucan from native corn stover and corncob were 21.4 and 23.1 % which were respectively 1.19 and 1.13 times of each control (Fig. 3). The increased extents of glucan conversion were not high as those of SH. This is because the optimum temperature for the enzymes of C. owensensis was 70–80 °C . When co-hydrolyzed with CTec2 at 50 °C the enzyme activity was decreased.
Figure 3 also shows the xylan conversion rates from native corn stover and corncob synergetically hydrolyzed by the extra-enzyme of C. owensensis and CTec2. Totally, the xylan conversion rates of native corncob were higher than those of native corn stover. Especially, the xylan conversion rate of native corncob by sequential hydrolysis (SH) reached 34.8 %. The possible reason is that the enzyme of C. owensensis used in this experiment was produced using corncob as inducing substrate; hence, the ratio of the compositions in this enzyme was more fitted for corncob hydrolysis. It is believed that deconstructing of hemicellulose in lignocellulose will benefit cellulose degradation. This was proved by the results in Fig. 3. Namely, the higher xylose releasing (34.8 % from native corncob vs 11.8 % from native corn stover) led to a higher glucose releasing (37.9 % from native corncob vs 31.2 % from native corn stover).
Figure 5 shows the sugar conversion rates from native corn stover and corncob by synergetic hydrolysis using intra-enzyme of C. owensensis and CTec2. It can be see that the conversion rates of glucan and xylan were lower than those counterparts of synergetic hydrolysis with extra-enzyme of C. owensensis and CTec2 (Fig. 3). This is possibly due to the higher xylanase and endoglucanase activities in the extra-enzyme.
Inhibitors in the hydrolysate
The furfural and 5-hydroxymethyl furfural (HMF) were not detected in the hydrolysates from the native corn stover and corncob by sequential hydrolysis (SH). It is not surprising since at the temperature of 70 and 50 °C in the hydrolysis buffer the sugars are stable.
Kataeva et al.  found that C. bescii could solubilize all components of switchgrass, including lignin. Therefore, the phenolics may be released from lignin during hydrolysis by the extra-enzyme of C. owensensis. Really, the phenolics concentrations of the hydrolysates form native corn stover and corncob by SH were respectively 35.8 ± 3.2 and 34.3 ± 2.7 mg/l, which were slightly higher than these of the hydrolysates form native corn stover and corncob by CTec2 with 24.4 ± 1.8 and 25.1 ± 2.3 mg/l respectively. The phenolics concentrations of the hydrolysis buffer soaked (at 70 °C for 48 h) with native corn stover and corncob were, respectively, 4.2 ± 0.3 and 3.7 ± 0.3 mg/l. While the phenolics concentrations of the hydrolysates form the stream exploded corn stover and corncob by CTec2 were much high as 232 ± 17.6 and 219 ± 20.5 mg/l, respectively. These results show that only few phenolics from lignin can be released by the extra-enzyme of C. owensensis and CTec2. Among the biofuel-production microorganisms, Clostridium is very sensitive to phenolics which are lethal to Clostridium even at low concentrations [40, 41]. Even so, the research by Lee et al.  showed that the cell growth and metabolite production of Clostridium tyrobutyricum and Clostridium beijerinckii were not or slight inhibited when the phenolics concentrations were less than 100 mg/l. Wang and Chen  used the detoxified hydrolysate from steam-exploded rice straw to produce butanol by Clostridium acetobutylicum ATCC 824, and found that fermentation was improved when the phenolics concentration of the hydrolysate was less than 890 mg/l. The phenolics concentration of the hydrolysate by SH in this work was below 40 mg/l. This suggests that the hydrolysate by SH may be used for biofuels production without detoxification.
Pretreatment is currently an essential step for bioconversion of the lignocellulosic biomass. The common biomass pretreatment methods, such as steam-explosion pretreatment, hydrothermal pretreatment, and acid or alkali pretreatment, are costly and would inevitably lead to sugar loss and inhibitor generation . The followed detoxification process is also laborious and costly. Fortunately, the extreme thermophiles Caldicellulosiruptor can produce a diverse set of GHs, which are different from the current commercial cellulase, for deconstruction of native lignocellulosic biomass [16–18]. Synergetic hydrolysis by these thermophilic enzymes and the commercial cellulase may efficiently deconstruct the native lignocellulosic biomass without pretreatment.
The results in this work show that the extra-enzyme of C. owensensis had high ability for degrading the hemicellulose of native lignocellulosic biomass. High temperature pre-hydrolysis on native lignocellulosic biomass by the extra-enzyme of C. owensensis could greatly improve the glucan conversion rate, making almost the same contribution as steam-exploded pretreatment which is nowadays a most widely employed method for treating the lignocellulosic biomass [7, 45, 46]. Application of the enzyme of C. owensensis will make it possible for avoiding the traditional pretreatment process. Based on this work, the sequential hydrolysis process by extra-enzyme of C. owensensis and commercial cellulase is presented for replacing the traditional pretreatment process for bioconversion of native lignocellulosic biomass.
The profiles of the traditional and sequential hydrolysis bioconversion processes are shown in Fig. 6. In the traditional bioconversion process, pretreatment and detoxification steps are used to improve the efficiencies of hydrolysis and fermentation. The sequential hydrolysis bioconversion process contains three sequential steps: hyperthermal enzymolysis (70–80 °C) by the extra-enzyme of C. owensensis, mesothermal enzymolysis (50–55 °C) by commercial cellulase and fermentation. The hyperthermal enzymolysis step, replacing the pretreatment step of traditional bioconversion process, undertakes three functions: degradation of hemicellulose, partly changing the cellulose structure and sterilization, which benefit for both mesothermal enzymolysis and fermentation. After mesothermal enzymolysis the hydrolysate may directly be used for fermentation without detoxification and sterilization. These advantages of the sequential hydrolysis bioconversion process make it a promising way for lignocellulose bioconversion.
In this work, the loading rate of the crude enzyme from C. owensensis was 15 mg/g dry substrate, which may not be economically feasible now. However, it could be improved by developing more efficient thermophilic hydrolase cocktails through heterogeneously expressing the relative enzymes of C. owensensis (shown in Table 2) and combining these enzymes in suitable composition.
The extremely thermophilic bacterium C. owensensis has comprehensive hemicellulase and cellulase system. The enzymes of C. owensensis had high ability for degrading the hemicellulose of native lignocellulosic biomass. High temperature pre-hydrolysis on native lignocellulosic biomass by the extra-enzyme of C. owensensis could greatly improve the glucan conversion rate, making almost the same contribution as steam-exploded pretreatment. These results suggest that the costly and laborious pretreatment and detoxification steps may be removed from the bioconversion process of lignocellulosic biomass by using the enzymes from C. owensensis. A new process for saccharification of lignocellulosic biomass by sequential hydrolysis: hyperthermal enzymolysis (70–80 °C) by enzymes of C. owensensis followed with mesothermal enzymolysis (50–55 °C) by commercial cellulase is introduced in the present research. This process has the advantages of no sugar loss, few inhibitors generation and consolidated with sterilization. This research demonstrated a potential approach for bioconversion of lignocellulosic biomass without pretreatment.
Strain and cultivation
The extremely thermophilic cellulolytic anaerobic bacteria Caldicellulosiruptor owensensis DSM 13100 was purchased from the DSMZ (German Collection of Microorganisms and Cell Cultures, Braunschweig, Germany). The medium 640 (DSMZ) was used for cell cultivation and contained per liter 0.9 g NH4Cl, 0.9 g NaCl, 0.75 g KH2PO4, 1.5 g K2HPO4, 0.4 g MgCl2·6H2O, 2.5 mg FeCl3·6H2O, 1 ml Trace elements (medium 320, DSMZ, http://www.dsmz.de), 1 mg Resazurin, 2 g Trypticase, 1 g Yeast extract, 0.75 g Cysteine-HCl·H2O and 1 g xylose (or corncob xylan) as carbon source. Lyophilized cells were reactivated for 24 h at 75 °C and inoculated in new medium 640 to prepare stock cultures of 1 ml containing 30 % (w/v) glycerol which were then stored at −80 °C. The stock culture was inoculated in 10 ml of 640 medium for 16–24 h at 75 °C to be used as inoculum for growth and enzyme production tests.
Anaerobic culture media was boiled and flushed with oxygen-free N2 gas, distributed in Hungate tubes or serum vials and autoclaved at 121 °C for 20 min. The carbon source (corncob xylan or xylose) was added in the medium in different ways: corncob xylan was added together with other materials and autoclaved in the serum bottles with the medium, the anoxic xylose solution was filter sterilized and added with a sterile syringe to the medium after autoclave.
The corn stover and corncob were obtained as generous gifts from a farm in Beijing suburb. The pretreatment condition [47–49] for the steam-exploded corn stover and corncob was 1.4 MPa retained for 4 min. Composition (glucan/xylan/araban/lignin content as percentage) of each lignocellulosic substrate was as follows: native corn stover (35.6/17.7/4.3/21.3), steam-exploded corn stover (45.3/2.2/0/29.6), native corncob (33.5/27.3/3.5/17.8) and steam-exploded corncob (43.7/5.5/0/23.4). The chemicals and other substrates were purchased from Sinopharm Chemical Reagent Beijing Co., Ltd or Sigma.
Growth line assay
Bacterial cell growth was determined by measurement of the optical density (OD) at 600 nm with a spectrophotometer (Biochrom, UK). Vials containing autoclaved medium were incubated without inoculum as a control.
Extra- and intra-enzymes extraction
After cultivation for 24 h, the culture was centrifuged at 6000×g for 15 min to separate the cells from the fermented broth. The cells were resuspended in a 10–15 ml binding buffer (50 mM Tris–HCl, pH 7.4, 150 mM NaCl) and broken by sonication. Then the mixture was centrifuged at 13,000×g for 15 min. The supernatant was collected as intra-enzymes stored in 4 °C fridge for further experiment. The protein in the cell-free fermented broth was precipitated by adding ammonia sulfate to 80 % ammonium sulfate saturation (w/v) and centrifuged at 13,000×g for 15 min and then resuspended in a 10–15 ml binding buffer. The binding buffer containing protein was moved into a semipermeable membrane bag and dialyzed in new binding buffer for 12 h. After this treatment the extra-enzymes were obtained.
Protein and glycoside hydrolase assays
The protein concentrations of intra- and extra-enzymes were determined by the Coomassie Brilliant Blue G250 binding method using bovine serum albumin solution to make standard curve .
Endoglucanase, FPA and xylanase activities were assessed using the PHBAH (p-Hydroxy benzoic acid hydrazide) method using carboxymethylcellulose (CMC), filter paper (FP, Waterman) and beechwood xylan as substrate, respectively, with either glucose or xylose as the standard [51, 52]. One unit of enzyme activity was defined as the amount of protein capable of releasing 1 mmol of reducing sugar from substrate per minute. Cellobiohydrolase (pNPC, p-nitrophenyl-β-d-cellobioside), β-d-glucosidase (pNPG, p-nitrophenyl-β-d-glucopyranoside), and β-d-xylosidase (pNPX, p-nitrophenyl-β-d-xylopyranoside) arabinofuranosidase (pNPAF, p-nitrophenyl-α-l- arabinofuranoside), xylan esterase (pNPAC, p-nitrophenyl-acetate) activities were determined using their respective p-nitrophenyl sugar or ester substrates. 90 μl of sugar substrate was incubated with 10 μl of diluted enzyme, incubated for 10 min and quenched with 200 μl of 2 M sodium carbonate. The absorbance of released p-nitrophenol was measured at 400 nm. One unit of activities using p-nitrophenyl substrates was defined as the amount of protein capable of releasing 1 mmol pNP from the substrates per minute. To analyze all the enzyme activities citrate buffer (50 mM sodium citrate, pH 6.0, 150 mM NaCl) was used with the incubation temperature at 70 °C.
HPLC/MS analysis of extra- and intra-enzymes
The enzymes were digested by trypsin. The peptides in the digest mixture were analyzed by HPLC/MS. The on-line chromatographic separation was performed by reversed-phased chromatography on an Agilent Zorbax SB C18 column (2.1 × 150 mm, 5 mm) using the Agilent 1100 system. Solvent A was water (containing 0.1 % trifluoroacetic acid), and solvent B was 60 % acetonitrile in water (v/v, containing 0.1 % trifluoroacetic acid). The gradient was that, solvent B increased from 5 to 40 % in 0–35 min, then, the solvent B increased from 40 to 50 % in 35–65 min. The flow rate was 0.2 ml/min. The outlet of the column was introduced into the ion source of an electrospray ionization mass spectrometer (LCQ DecaXP, Thermo Electron, San Jose, CA, USA). The spray voltage was set to 4.5 kV, and the heat capillary was kept at 300 °C. The data acquisition consists of three scan events, an MS scan followed by one zoomscan to determine the charge state of the ion, and MS/MS scan to provide an MS/MS spectrum. The MS scan range was set from m/z 300–2000. The zoomscan and tandem mass spectrometry (MS/MS) functions were performed in data-dependent mode. Dynamic exclusion was enabled with one count and a 0.5 min exclusion duration unit. The collision energy value was set as 35 %.
Sequence information from MS/MS data was processed using Turbo SEQUEST algorithm in Bioworks 3.2 software (ThermoElectron, San Jose, CA, USA). The protein file was created by extracting C. owensensis protein entries from the UniProtKB/Swiss-Prot database (http://www.uniprot.org). The peptide sequences (as shown in Table 2) were further verified based on the following criteria: (1) continuity of the b and y ion series, (2) the quality of the MS/MS spectrum, and (3) the number of ions in the MS/MS spectrum .
Biomass hydrolysis and analysis
For hydrolysis by the enzyme of C. owensensis alone, each reaction system was prepared in 50 mM sodium acetate, pH 6.0 with the dry substrate of 2 % (w/v) and the enzyme loading of 15 mg protein per gram dry substrate. The reaction volume was 500 μl in a 2 ml Eppendorf tube, which was sealed by winding parafilm after closing the lip, and put in a water bath at 70 °C for 48 h.
For synergetic hydrolysis by the enzyme of C. owensensis and the commercial enzyme cocktail Cellic CTec2 (Novoyzmes), two trials were performed. One was that the lignocellulosic biomass (native corn stover or native corncob) was sequentially hydrolyzed (SH) by the enzyme of C. owensensis (the first step) and CTec2 (the second step). The first step was the same as described above (for hydrolysis by the enzyme of C. owensensis only). After 48 h hydrolysis by the enzyme of C. owensensis (the first step) the CTec2 and 500 μl of sodium acetate buffer, pH 5.0 were added, forming a reaction system of pH 5.0 with the dry substrate of 1 %, and then incubated in water bath at 50 °C for 72 h (the second step). The other was that the lignocellulosic biomass was co-hydrolyzed (CH) by the enzyme of C. owensensis and CTec2 in the sodium acetate buffer of pH 5.0 with the dry substrate of 1 % at 50 °C for 72 h. The loading rates of CTec2 (http://www.bioenergy.novozymes.com/) for synergetic hydrolysis were 30 mg/g glucan (high loading). These lignocellulosic biomasses were hydrolyzed by CTec2 alone in the sodium acetate buffer of pH 5.0 with the dry substrate of 1 % at 50 °C for 72 h as controls.
Reducing sugar assay was carried out by PHBAH method with xylose as the standard [51, 52]. Glucose and xylose concentrations were measured on a HPLC system equipped with a Hi-Plex Ca column (7.7 × 300 mm, Agilent Technology, USA), LC-20AT pump (Shimadzu, Japan) and RID-10A refractive index detector (Shimadzu, Japan), using water at a flow rate of 0.6 ml/min as mobile phase. The amounts of released glucose and xylose were used for calculating glucan and xylan conversions, respectively. The furfural and 5-hydroxymethyl furfural (HMF) were analyzed by HPLC as described above. The phenolics in the hydrolysate were analyzed by ultraviolet spectra at 280 nm using p-hydroxy benzaldehyde as the standard.
The native corn stover morphologies before and after hydrolysis and after incubated in the acetate buffer (pH 6.0) at 70 °C for 48 h were examined by scanning electron microscopy (SEM). The specimens were mounted on stubs and sputter-coated with gold prior to imaging with a JEOL JSM-6700F scanning electron microscope using 5-kV accelerating voltage and 10-mm distance.
filter paper activity
p-hydroxy benzoic acid hydrazide
high performance liquid chromatography/mass spectrometry
scanning electron microscopy
Ghosh A, Bhattacharyya B (1999) Biomethanation of white rotted and brown rotted rice straw. Bioproc Eng 20:297–302
Lynd LR, Laser MS, Bransby D et al (2008) How biotech can transform biofuels. Nat Biotechnol 26:169–172
Liu G, Qin Y, Li Z, Qu Y (2013) Development of highly efficient, low-cost lignocellulolytic enzyme systems in the post-genomic era. Biotechnol Adv 31:962–975
Brodeur G, Yau E, Badal K et al (2011) Chemical and physicochemical pretreatment of lignocellulosic biomass: a review. Enzyme Res. doi:10.4061/2011/787532
Zhang YHP, Berson E, Sarkanen S, Dale BE (2009) Sessions 3 and 8: pretreatment and biomass recalcitrance: fundamentals and progress. Appl Biochem Biotechnol 153:80–83
Mosier N, Wyman C, Dale B et al (2005) Features of promising technologies for pretreatment of lignocellulosic biomass. Bioresour Technol 96:673–686
Behera S, Arora R, Nandhagopal N, Kumar S (2014) Importance of chemical pretreatment for bioconversion of lignocellulosic biomass. Renew Sust Energ Rev 36:91–106
Silva JPA, Carneiro LM, Roberto IC (2013) Treatment of rice straw hemicellulosic hydrolysates with advanced oxidative processes: a new and promising detoxification method to improve the bioconversion process. Biotechnol Biofuels 6:23
Chandel AK, Kapoor RK, Singh A, Kuhad RC (2007) Detoxification of sugarcane bagasse hydrolysate improves ethanol production by Candida shehatae NCIM 3501. Bioresour Technol 98:1947–1950
López M, Nichols N, Dien B et al (2004) Isolation of microorganisms for biological detoxification of lignocellulosic hydrolysates. Appl Microbiol Biotechnol 64:125–131
Lee JM, Venditti RA, Jameel H, Kenealy WR (2011) Detoxification of woody hydrolyzates with activated carbon for bioconversion to ethanol by the thermophilic anaerobic bacterium Thermoanaerobacterium saccharolyticum. Biomass Bioenerg 35:626–636
Zhuang J, Liu Y, Wu Z et al (2009) Hydrolysis of wheat straw hemicellulose and detoxification of the hydrolysate for xylitol production. BioResource 4:674–686
Alriksson B, Cavka A, Jönsson LJ (2011) Improving the fermentability of enzymatic hydrolysates of lignocellulose through chemical in situ detoxification with reducing agents. Bioresour Technol 102:1254–1263
Martinez A, Rodriguez ME, Wells ML et al (2001) Detoxification of dilute acid hydrolysates of lignocellulose with lime. Biotechnol Progr 17:287–293
Palmqvist E, Hahn-Hägerdal B (2000) Fermentation of lignocellulosic hydrolysates. I: inhibition and detoxification. Bioresour Technol 74:17–24
Yeoman CJ, Han Y, Dodd D et al (2010) Thermostable enzymes as biocatalysts in the biofuel industry. Adv Appl Microbiol 70:1–55
Blumer-Schuette SE, Kataeva I, Westpheling J et al (2008) Extremely thermophilic microorganisms for biomass conversion: status and prospects. Curr Opin Biotechnol 19:210–217
Blumer-Schuette SE, Lewis DL, Kelly RM (2010) Phylogenetic, microbiological, and glycoside hydrolase diversities within the extremely thermophilic, plant biomass-degrading genus Caldicellulosiruptor. Appl Environ Microbiol 76:8084–8092
Blumer-Schuette SE, Giannone RJ, Zurawski JV et al (2012) Caldicellulosiruptor core and pangenomes reveal determinants for noncellulosomal thermophilic deconstruction of plant biomass. J Bacteriol 194:4015–4028
Blumer-Schuette SE, Ozdemir I, Mistry D et al (2011) Complete genome sequences for the anaerobic, extremely thermophilic plant biomass-degrading bacteria Caldicellulosiruptor hydrothermalis, Caldicellulosiruptor kristjanssonii, Caldicellulosiruptor kronotskyensis, Caldicellulosiruptor owensenis, and Caldicellulosiruptor lactoaceticus. J Bacteriol 193:1483–1484
Park JI, Kent MS, Datta S et al (2011) Enzymatic hydrolysis of cellulose by the cellobiohydrolase domain of CelB from the hyperthermophilic bacterium Caldicellulosiruptor saccharolyticus. Bioresour Technol 102:5988–5994
Su X, Mackie RI, Cann IK (2012) Biochemical and mutational analyses of a multidomain cellulase/mannanase from Caldicellulosiruptor bescii. Appl Environ Microbiol 78:2230–2240
Bai A, Zhao X, Jin Y et al (2013) A novel thermophilic β-glucosidase from Caldicellulosiruptor bescii: characterization and its synergistic catalysis with other cellulases. J Mol Catal B-Enzym 85:248–256
Qiao W, Tang S, Mi S et al (2014) Biochemical characterization of a novel thermostable GH11 xylanase with CBM6 domain from Caldicellulosiruptor kronotskyensis. J Mol Catal B-Enzym 107:8–16
Jia X, Mi S, Wang J et al (2014) Insight into glycoside hydrolases for debranched xylan degradation from extremely thermophilic bacterium Caldicellulosiruptor lactoaceticus. PLoS One 9:e106482
Mi S, Jia X, Wang J et al (2014) Biochemical characterization of two thermostable xylanolytic enzymes encoded by a gene cluster of Caldicellulosiruptor owensensis. PLoS One 9:e105264
Lochner A, Giannone RJ, Rodriguez M et al (2011) Use of label-free quantitative proteomics to distinguish the secreted cellulolytic systems of Caldicellulosiruptor bescii and Caldicellulosiruptor obsidiansis. Appl Environ Microbiol 77:4042–4054
Martinez D, Berka RM, Henrissat B et al (2008) Genome sequencing and analysis of the biomass-degrading fungus Trichoderma reesei (syn. Hypocrea jecorina). Nat Biotechnol 26:553–560
Bayer EA, Belaich J-P, Shoham Y, Lamed R (2004) The cellulosomes: multienzyme machines for degradation of plant cell wall polysaccharides. Annu Rev Microbiol 58:521–554
Doi RH, Kosugi A (2004) Cellulosomes: plant-cell-wall-degrading enzyme complexes. Nat Rev Microbiol 2:541–551
Brunecky R, Alahuhta M, Xu Q et al (2013) Revealing nature’s cellulase diversity: the digestion mechanism of Caldicellulosiruptor bescii CelA. Science 342:1513–1516
Gusakov AV (2011) Alternatives to Trichoderma reesei in biofuel production. Trends Biotechnol 29:419–425
Huang C-Y, Patel BK, Mah RA, Baresi L (1998) Caldicellulosiruptor owensensis sp. nov., an anaerobic, extremely thermophilic, xylanolytic bacterium. Int J Syst Bacteriol 48:91–97
McClendon SD, Batth T, Petzold CJ et al (2012) Thermoascus aurantiacus is a promising source of enzymes for biomass deconstruction under thermophilic conditions. Biotechnol Biofuels 5:1–10
Juturu V, Wu JC (2014) Microbial cellulases: engineering, production and applications. Renew Sust Energ Rev 33:188–203
Lynd LR, Weimer PJ, Van Zyl WH, Pretorius IS (2002) Microbial cellulose utilization: fundamentals and biotechnology. Microbiol Mol Biol Rev 66:506–577
Merino ST, Cherry J (2007) Progress and challenges in enzyme development for biomass utilization. In: Biofuels. Springer, pp 95–120
Brunecky R, Hobdey SE, Taylor LE II et al (2014) High temperature pre-digestion of corn stover biomass for improved product yields. Biotechnol Biofuels 7:1–7
Kataeva I, Foston MB, Yang SJ et al (2013) Carbohydrate and lignin are simultaneously solubilized from unpretreated switchgrass by microbial action at high temperature. Energ Environ Sci 6:2186–2195
Ezeji T, Qureshi N, Blaschek HP (2007) Butanol production from agricultural residues: impact of degradation products on Clostridium beijerinckii growth and butanol fermentation. Biotechnol Bioeng 97:1460–1469
Ezeji TC, Qureshi N, Blaschek HP (2007) Bioproduction of butanol from biomass: from genes to bioreactors. Curr Opin Biotechnol 18:220–227
Lee KM, Min K, Choi O et al (2015) Electrochemical detoxification of phenolic compounds in lignocellulosic hydrolysate for Clostridium fermentation. Bioresour Technol 187:228–234
Wang L, Chen H (2011) Increased fermentability of enzymatically hydrolyzed steam-exploded corn stover for butanol production by removal of fermentation inhibitors. Process Biochem 46:604–607
Agbor VB, Cicek N, Sparling R et al (2011) Biomass pretreatment: fundamentals toward application. Biotechnol Adv 29:675–685
Chen H, Qiu W (2010) Key technologies for bioethanol production from lignocellulose. Biotechnol Adv 28:556–562
Sassner P, Mårtensson CG, Galbe M, Zacchi G (2008) Steam pretreatment of H2SO4-impregnated Salix for the production of bioethanol. Bioresour Technol 99:137–145
Chen HZ, Liu LY (2007) Unpolluted fractionation of wheat straw by steam explosion and ethanol extraction. Bioresour Technol 98:666–676
Peng XW, Chen HZ (2012) Hemicellulose sugar recovery from steam-exploded wheat straw for microbial oil production. Process Biochem 47:209–215
Chen HZ, Liu ZH (2014) Multilevel composition fractionation process for high-value utilization of wheat straw cellulose. Biotechnol Biofuels 7:137
Bradford MM (1976) A rapid and sensitive method for the quantitation of microgram quantities of protein utilizing the principle of protein-dye binding. Anal Biochem 72:248–254
Blakeney AB, Mutton LL (1980) A simple colorimetric method for the determination of sugars in fruit and vegetables. J Sci Food Agr 31:889–897
Han Y, Agarwal V, Dodd D et al (2012) Biochemical and structural insights into xylan utilization by the thermophilic bacterium Caldanaerobius polysaccharolyticus. J Biolog Chem 287:34946–34960
Zhang G, Liu T, Wang Q et al (2009) Mass spectrometric detection of marker peptides in tryptic digests of gelatin: a new method to differentiate between bovine and porcine gelatin. Food Hydrocolloid 23:2001–2007
XP and YH designed the study, analyzed the results, and drafted the manuscript. WQ participated in the enzymatic characterization analysis. XJ, SM, and HS participated in the experiment of enzymatic hydrolysis and polishing the writing of the manuscript. All authors read and approved the final manuscript.
We would like to thank the financial support from the National High Technology Research and Development Program of China (863 Project no. 2014AA021905), and 100 Talents Program of institute of process engineering, Chinese Academy of Sciences.
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Competing interests The authors declare that they have no competing interests.
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Peng, X., Qiao, W., Mi, S. et al. 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 8, 131 (2015). https://doi.org/10.1186/s13068-015-0313-0
- Thermophilic enzyme
- Synergetic hydrolysis