Identification of novel glycosyl hydrolases with cellulolytic activity against crystalline cellulose from metagenomic libraries constructed from bacterial enrichment cultures
© Mori et al.; licensee Springer. 2014
Received: 3 June 2014
Accepted: 8 July 2014
Published: 16 July 2014
To obtain cellulases that are capable of degrading crystalline cellulose and cedar wood, metagenomic libraries were constructed from raw soil sample which was covered to pile of cedar wood sawdust or from its enrichment cultures. The efficiency of screening of metagenomic library was improved more than 3 times by repeating enrichment cultivation using crystalline cellulose as a carbon source, compared with the library constructed from raw soil. Four cellulase genes were obtained from the metagenomic libraries that were constructed from the total genome extracted from an enrichment culture that used crystalline cellulose as a carbon source. A cellulase gene and a xylanase gene were obtained from the enrichment culture that used unbleached kraft pulp as a carbon source. The culture supernatants of Escherichia coli expressing three clones that were derived from the enrichment culture that used crystalline cellulose showed activity against crystalline cellulose. In addition, these three enzyme solutions generated a reducing sugar from cedar wood powder. From these results, the construction of a metagenomic library from cultures that were repetition enriched using crystalline cellulose demonstrated that this technique is a powerful tool for obtaining cellulases that have activity toward crystalline cellulose.
KeywordsMetagenome Glycosyl hydrolase Cellulase Xylanase
Lignocellulosic pools are a renewable source of feedstock for biofuel production. Cellulose, hemicellulose, and lignin are closely associated, and covalent cross-linkages have been suggested to occur between lignin and polysaccharides. Cellulose is the most abundant biomass in nature. Cellulose has great potential for a number of applications, including biofuel production. The cost of ethanol production from lignocellulosic materials is high, and the main challenge is high cost of the hydrolysis process. Numerous studies have been performed to improve the hydrolysis of lignocelluloses by pretreatment (Sun and Cheng 2002).
Lignocellulosic biomass can be converted to ethanol by hydrolysis and downstream fermentation processing. This process is much more complicated than the fermentation of a C6 sugar, and is more expensive than the production of bioethanol from starch or sugar crops. Structural features of native biomass limit accessibility to enzymes or microorganisms. Lignocellulose is difficult to hydrolyze because it is associated with hemicellulose, it is surrounded by a lignin seal that has a limited covalent association with hemicellulose, and much of cellulose has a crystalline structure (Weil et al. 1994). Especially, depolymerization step is the rate-limiting step for the whole cellulose hydrolysis process.
Cellulolytic fungi and bacteria play an important role in carbon cycle in nature. Especially, filamentous fungi are main microbe performing cellulose degradation in aerobic environment. Several strains of Trichoderma produce an extracellular cellulase complex that degrades native cellulose (Wojtczak et al. 1987). Fungal cellulases act synergistically with endoglucanases (EC 188.8.131.52, hydrolyze internal β-1,4-glucosidic linkages randomly in the cellulose chain), exoglucanases (also known as cellobiohydorolases, breakdown celllose into cellobiose from the ends), and β-glucosidases (EC 184.108.40.206, hydrolyze cellobiose and cellooligosaccharides to glucose) for cellulosic hydrolysis. Many other fungi produce cellulases and degrade soluble cellulose derivatives such as carboxymethylcellulose (CMC). However, they are not so effective on crystalline cellulosic substrates. Although mesophilic fungal strains produce cellulase, these fungal cellulases have limited efficiency in cellulose hydrolysis (Kumar et al. 2008). Some bacterial strains that produce cellulases are also able to degrade cellulose in aerobic or facultative anaerobic conditions (e.g. Kato et al. 2005).
Bacterial cellulases have the advantages over fungus for the genetic improvement and for the economic production because there are technical difficulties of construction of enzyme expression system from fungal species. Although many of cellulases are already characterized, a further screenings of new cellulases that have better characteristics (strong activity, resistance to various stresses, easily producing in large scale, and so on) are necessary for cost reduction of biorefinery process. Metagenomics is the study of genetic material recovered directly from environmental samples and it is a powerful tool to identify novel biocatalysts, natural products, and new molecular structures (Iqbal et al. 2012). However, many efforts are required for selecting the target genes because environmental genome has extremely broad diversity. Therefore, enrichment of an environmental genome may make it possible to select the purpose gene efficiently.
In present study, metagenomic libraries were prepared using DNA from raw environmental samples or short enrichment cultures, and screening was based on enzyme activity. The Japanese cedar, Cryptomeria japonica, is a widely distributed coniferous tree that is an important plantation tree in Japan. Therefore, cellulase genes that were able to degrade the cellulose of raw cedar wood were main target in this study. In addition, for construction of the effective screening method, the metagenomic libraries were constructed from enrichment bacterial cultures using a different cellulosic carbon source, and the enrichment effect was evaluated.
Total DNA from the original soil sample (collected from under the pile of cedar wood sawdust) and its enrichment cultures (1st and 2nd enrichment culture with Avicel or unbleached kraft pulp as the carbon source) was extracted, and the 16S rRNA genes were amplified. The purified rRNA gene fragments were cloned into the pGEM-T easy vector. Recombinants were randomly selected, and clonal plasmids were extracted. The sequences of a few bacterial 16S rRNA gene clones (500–600 bp) were determined. A total of 16 clones (4 clones from the original soil [GenBank/EMBL/DDBJ under accession numbers (AN): AB921992 ~ AB921995], 8 clones from 1st enrichment culture with Avicel [AN: AB21996 ~ AB22003], and 4 clones from 2nd enrichment culture with Avicel [AN: AB22004 ~ AB22007]) were analyzed to estimate the bacterial diversity in the original soil and Avicel enrichment cultures. The genes from the original soil bacteria were from several bacterial groups. However, 5 of 8 sequences from the 1st Avicel enrichment culture and all 4 clones from the 2nd Avicel enrichment culture were within the gamma-proteobacteria group. It was expected that the diversity of bacteria has lowered considerably by 2nd enrichment cultivation. Thus, Enrichment cultivation was stopped at 2nd time enrichment.
Clones containing glycosyl hydrolase genes from metagenomic libraries constructed from different environmental samples
Screening number (Library size)
Sequence name (accession no.)
30,000 (130 Mb)
Avicel 1st enrichment culture
25,000 (108 Mb)
p1a2, p1a3, p1a4
Avicel 2nd enrichment culture
32,000 (138 Mb)
Pulp 1st enrichment culture
23,000 (100 Mb)
Pulp 2nd enrichment culture
40,000 (172 Mb)
p2p3, p2p4, p2p4
Sequence analysis and annotation of the genes isolated from the environmental genomic libraries
Most homologous microorganism (%)
1A1 (3107 bp)
Cellvibrio mixtus (63%)
Azotobacter vinelandii DJ (82%)
1A2 (13375 bp)
Uncultured organism (79%)
Uncultured organism (92%)
YceI family protein
Uncultured organism (73%)
bacterium enrichment culture clone CelA10 (85%)
Uncultured organism (91%)
Cellvibrio japonicus Ueda107 (60%)
Cellvibrio japonicus Ueda107 (76%0
2A1 (4136 bp)
Sinorhizobium meliloti (56%)
Rhizobium etli CFN 42 (59%)
2A3 (2539 bp)
Cellvibrio mixtus (61%)
2P3 (7273 bp)
Glutathione S-transferase-like protein
Polaromonas sp. JS666 (72%)
Bacillus cereus SJ1 (35%)
Pseudoxanthomonas suwonensis 11-1 (70%)
2P1 (3551 bp)
Paenibacillus dendritiformis C454 (39%)
Paenibacillus sp. aloe-11 (77%)
Paenibacillus sp. aloe-11 (80%)
Cellulase activity for crystalline cellulose (Avicel) and cedar wood powder
Production of reducing sugar (μg/ml)
Relative activity (%) (sugi/avicel)
Ceder wood powder
It was reviewed that a number of cellulase genes had been isolated from metagenomic libraries (Duan and Feng 2010; Li et al. 2009), the hit rate was too low, at least 100 Mb metagenomic per one cellulase gene is required by functional screening of the library from soil or sediment sample. On the other hand, one cellulase gene was provided per 10-50 Mb in the metagenomic library made from rumen of cow, buffalo etc. In the report of the screening from library made from enrichment culture, one cellulase per 40 Mb was provided in the case of highest hit rate (Voget et al. 2003). In present study, the size of the metagenomic library that was constructed from soil was around 130 Mb; however, no positive cellulase/xylanase clones were obtained (Table 1). On the other hand, the hit rate was about 1 cellulase gene per 54 and 46 Mb metagenomic DNA from 1st and 2nd enrichment cultures with Avicel, respectively. The cause that the number of isolated cellulase genes after 2nd avicel enrichment only slightly increased was predicted that the bacterial diversity in enrichment culture has considerably reduced already by 1st Avicel enrichment, and that the diversity of cellulase-producing bacteria did not change so much between 1st and 2nd Avicel enrichment. Because that an identical cellulase gene (C1A2) has been obtained from metagenomic libraries of 1st and 2nd enrichment culture. When unbleached pulp was used as a carbon source for enrichment, glycoside hydrolase genes (cellulase and xylanase) were provided with hit rate of 0/100 Mb (1st enrichment) and 2/172 Mb (2nd enrichment). Although the screening efficiency improved by repeating enrichment, the efficiency was greatly different between enrichment cultures using Avicel and unbleached pulp. It was presumed that non-cellulolytic bacteria have grown vigorously in enrichment culture with unbleached pulp than enrichment culture with Avicel, because unbleached pulp has more various components that are easy to utilize such as amorphous cellulose and hemicellulose than avicel as crystaline cellulose. The efficiency of screening was improved by repeating enrichment and was also possible to improve more than three times by enrichment cultivation with strong selective pressure. Because the 16S rRNA gene diversity suggested that bacterial diversity decreased by the enrichment and the positive cellulase clones contained the same cellulase gene were identified from 1st and 2nd enrichment culture with Avicel, repeating the enrichment cultivation reduced the cellulase gene diversity (Table 1). However, it seems that the cellulase genes identified in this study had been shown enough diversity (Figure 2).
Previously, most purified cellulases from metagenomic library showed no/weak activity toward crystalline cellulose (Duan and Feng 2010). In this study, the cellulases containing a CBM hydrolyzed Avicel and had cellulase activity against cedar wood powder (Table 3), because the soil used in this study was collected from cedar sawdust sediment. Generally, cellulases do not show sufficient activity against lignocellulosic material, because hemicelluloses and lignin work as physical barriers and prevent the access of enzymes to cellulose surface. In addition, soluble hemicelluloses may strongly inhibit the cellulase activity and lignin adsorbed enzymes non-specificity. (Rahikainen et al. 2013a; Zhang et al. 2012). Because Cellulosin T3 has the xylanase activity, there is a possibility that soluble xylan was produced and has inhibited cellulase activity during process. Research group of Rahikainen et al has studied about detail of inhibition of cellulases by lignin. They reported that the lignin-rich residue provided by enzymatic hydrolysis of Spruce was found to have a strong inhibitory effect on enzymatic hydrolysis of microcrystalline cellulose (MCC). Inhibition of cellulase activity by lignin became strong depending on temperature, and endoglucanase activity of lignin-bound commercial T. reesei cellulase mixture was lost ~ 40% at 45°C for 1.5 hours (Rahikainen et al. 2011). And it was mentioned that the lignin-binding properties were different depending on CBM type and the surface properties of catalytic domain. (Rahikainen et al. 2013b). In this study, however, crude cellulases showed comparable activity against crystalline cellulose and cedar wood flour. It is possible that the structures of these enzymes do not adsorb to the lignin surface or that other crude proteins are adsorbed to lignin, protecting the cellulase activity.
Although cellulases C1A1 and C2A3, which have tandem CBM6 domains (Figure 1), has similar domain construction of endoglucanase of Celivibrio mixtus (endoglucanase 5A) has been investigated (Henshaw et al. 2004; Pires et al. 2004). The family 6 CBM from endoglucanase 5A also has two binding sites. The binding site in ‘cleft A’ can accommodate the chain ends of β-1,4-glucans, β-1,3-glucans and xylans. ‘Cleft B’ binds to internal regions of β-1,4-glucans and mixed β-(1,4) (1,3)-glucans. In addition, Kimura and Kamei investigated β-1,3(4)-glucanase A (GluA) of marine bacterium Pseudomonas sp. PE2 also has tandem CMB6 domains, suggesting that the tandem CBM of GluA may play a key role in the binding of Avicel and xylan and is very important for binding insoluble polysaccharides (Kitamura and Kamei 2006). These observations suggest that tandem-repeated CBM of cellulases C1A1 and C2A3 may play key role in binding and hydrolyzing crystalline cellulose and other insoluble polysaccharides in lignocellulosic materials. Cellulase C1A2 had a putative MAM domain (Figure 1). The MAM domain is an extracellular domain that mediates protein-protein interactions and is found in a diverse set of proteins that function in cell adhesion (Beckmann and Bork 1993). However, it is still unknown how the MAM-like domain works in hydrolysis of lignocellulose material. Although these cellulases isolated in present study are analog domain structure of known cellulases, the understanding of details of the function of each domain for hydrolysis of lignocellulose is not enough. Therefore, it is necessary to clarify the characteristics of these cellulases in future studies.
In this study, metagenomic libraries were constructed from enrichment cultures that were seeded with the soil that was covered to cedar sawdust to obtain cellulases that degrade crystalline cellulose. The cellulase genes were identified effectively by using enrichment cultivation, and three of cellulase active clones showed activity against crystalline cellulose and cedar wood powder. These results demonstrated that this technique is a powerful tool for obtaining cellulases that have activity toward crystalline cellulose.
Bacterial strains, sample sites, and enrichment cultures
E. coli DH5α was the host and the plasmid pUC119 (TaKaRa Bio.) was the vector for cloning experiments.
To construct metagenomic libraries, a soil sample under C. japonica sawdust sediment was collected from a backyard, in Kyushu University, Fukuoka, Japan. Enrichment was performed in modified M9 minimal medium with microcrystalline cellulose (Avicel®) or unbleached hardwood kraft pulp as a carbon source. Enrichment cultures from the soil sample were prepared by adding 1.0 g soil to 40 mL sterile minimal medium containing 20 g/L carbon source, 6.0 g/L Na2HPO4, 3.0 g/L KH2PO4, 0.5 g/L NaCl, 1.0 g/L Yeast Extract (Difco), 1 mM MgSO4, 0.1 mM CaCl2, and 0.04 mM FeSO4. Cultures were grown at 37°C for 7 days at 120 rpm (1st enrichment culture). Then, 0.5 mL culture medium was transferred to new minimal medium and incubated for an additional 7 days (2nd enrichment culture). Bacteria were recovered from each enrichment culture by centrifugation (3,000 × g for 20 min), and the obtained pellets were washed with 50 mM Tris-HCl (pH 8.0). The resulting precipitates were used for DNA extraction.
Total DNA extraction
DNA was extracted using a protocol based on the direct lysis method of Zhou et al. (1996) with minor modifications. Briefly, collected samples (5 g) were extracted by adding 13.5 mL DNA extraction buffer (100 mM Tris-HCl pH 8.0, 100 mM EDTA, 100 mM sodium phosphate, 1.5 M NaCl, and 1% cetyltrimethylammonium bromide) and 0.1 mL proteinase K (100 mg/mL) with horizontal shaking for 30 min at 37°C. Next, 1.5 mL 20% (w/v) sodium dodecyl sulfate was added, and the suspensions were incubated at 65°C for 2 h with gentle shaking every 15–20 min before the supernatant was collected by centrifugation at 3000 × g for 10 min. The pellet was re-extracted, and the combined supernatants were extracted with an equal volume of phenol-chloroform (1:1, v/v). The aqueous phase was recovered by centrifugation, and the DNA was precipitated with 0.6 volume of isopropanol at room temperature for 20 min. A pellet of crude nucleic acids was obtained by centrifugation at 12,000 × g for 10 min. After washing with 70% (v/v) ethanol, the DNA was re-suspended in 1 mL 10 mM Tris-HCl (pH 8.5) and purified by electrophoresis in a 1.0% low melting point agarose gel (agarose L, Wako). Then, DNA fragments over 22 kb were collected and extracted. Recovered DNA was precipitated with an equal volume of isopropanol, washed with 70% ethanol, and air-dried. Dried DNA was dissolved with 50 μL TE buffer (10 mM Tris-HCl, 1 mM EDTA, pH 8.0).
Purified DNA samples were used to construct genomic DNA libraries following partial digest with Sau3A1. Digested DNA was roughly fractionated by polyethylene glycol precipitation with 15 mM MgCl2 and 7.5% polyethylene glycol 6000. The DNA fragments were ligated into the pUC19 vector, which had been digested with BamHI and phosphatase treated with the TaKaRa Ligation Kit v2.1. E. coli DH5α was transformed with ligated pUC19, and transformants were selected on Luria-Bertani medium (LB) agar plates containing ampicillin (100 μg/mL) and 0.2% (w/v) rimazol brilliant blue dyed CMC or xylan (Kok and van der Velde 1991). By velvet replication (Lederberg and Lederberg 1952), the library was provided for both active screening. The active cellulolytic clones were visible by a clear halo against a blue background. Plasmid DNA was isolated from positive cellulolytic clones, and DNA was sequenced at Macrogen Japan, Tokyo University of Agriculture, using ABI BigDye Terminator v3.1 Cycle Sequencing Kits and an ABI 3730xl Analyzer. Complete coverage of the sequence was obtained by primer walking from the 5′ and 3′ ends or the shotgun-based approach described by Emonet et al. (2007). Sequences were compared to those in databases. The open reading frame (ORF) finder from NCBI was used to identify possible ORFs.
Cloning and DNA sequencing of the 16S rRNA gene
PCR amplification of the 16S rRNA genes was performed using purified metagenomic DNA as a template and bacterial universal primers (Lane 1991). The PCR conditions were as follows: initial denaturation at 95°C for 9 min and 18 cycles of 95°C for 1 min, 50°C for 1 min, and 72°C for 2 min. PCR products were ligated into the pGEM-T easy vector (Promega) and transformed into competent E. coli DH5α cells. Clones were randomly selected and sequenced. Sequencing was performed with primer 907R (5′-CCGYCAATTCMTTTRAGTTT-3′). All sequences (500–600 nucleotides) were compared with those in the GenBank database (http://www.ncbi.nlm.nih.gov/BLAST) using BLAST. Multiple sequence alignment was carried out using ClustalX software, and a phylogenic tree was generated by the neighbor-joining method (Saitou and Nei 1987).
Cellulase activity assays
Cellular extracts were prepared by dissolving positive cellulolytic E. coli clones with bugbuster® (Merck). The supernatants were concentrated 7.5 times by ultrafiltration. To measure the cellulase activity, crude concentrates were incubated with 1.0% (w/v) Avicel or cedar wood powder (extract free) in 100 mM Tris-HCl (pH 6.8) for 2 h at 50°C. The released reducing sugars were measured as D-glucose equivalents (Miller 1959). Cellulosin T3 (HBI Enzyme Inc., Hyogo, Japan) was used as a positive control.
This work was supported in part by a Grant- in-Aid for Scientific Research (A) from the Ministry of Education, Culture, Sports, Science and Technology of Japan (no. 21248023 and 24248030).
- Beckmann G, Bork P: An adhesive domain detected in functionally diverse receptors. Trends Biochem Sci 1993, 18: 40-41. 10.1016/0968-0004(93)90049-SView ArticleGoogle Scholar
- Duan CJ, Feng JX: Mining metagenomes for novel cellulase genes. Biotechnol Lett 2010, 32: 1765-1775. 10.1007/s10529-010-0356-zView ArticleGoogle Scholar
- Emonet SF, Grand G, Brisbarre NM, Moureau GN, Temmam S, Charrel RN, de Lamballerie X: Long PCR product Sequencing (LoPPS): a shotgun-based approach to sequence long PCR products. Nat Protoc 2007, 2: 340-346. 10.1038/nprot.2006.453View ArticleGoogle Scholar
- Henshaw JL, Bolam DN, Pires VM, Czjzek M, Henrissat B, Ferreira LM, Fontes CM, Gilbert HJ: The family 6 carbohydrate binding module CmCBM6-2 contains two ligand-binding sites with distinct specificities. J Biol Chem 2004, 279: 21552-21559. 10.1074/jbc.M401620200View ArticleGoogle Scholar
- Iqbal HA, Feng Z, Brady SF: Biocatalyst and their small molecule products from metagenomic studies. Curr Opin Chem Biol 2012, 16: 109-116. 10.1016/j.cbpa.2012.02.015View ArticleGoogle Scholar
- Kato S, Haruta S, Cui ZJ, Ishii M, Igarashi Y: Stable coexistence of five bacterial strains as a cellulose-degrading community. Appl Environ Microbiol 2005, 71: 7099-7106. 10.1128/AEM.71.11.7099-7106.2005View ArticleGoogle Scholar
- Kitamura E, Kamei Y: Molecular cloning of the gene encoding beta-1,3(4)-glucanase A from a marine bacterium, Pseudomonas sp. PE2, an essential enzyme for the degradation of Pythium porphyrae cell walls. Appl Microbiol Biotechnol 2006, 71: 630-637. 10.1007/s00253-005-0200-xView ArticleGoogle Scholar
- Kok CJ, van der Velde G: The influence of selected water quality parameters on the decay rated and exoenzymatic activity of detritus of Nymphaea alba L. floating leaf blades in laboratory experiments. Oecologia 1991, 88: 311-316. 10.1007/BF00317572View ArticleGoogle Scholar
- Kumar R, Singh S, Singh OV: Bioconversion of lignocellulosic biomass: biochemical and molecular perspectives. J Ind Microbiol Biotechnol 2008, 35: 377-391. 10.1007/s10295-008-0327-8View ArticleGoogle Scholar
- Lane DJ: Nucleic Acid Techniques in Bacterial Systematics. John Wiley & Sons, New York; 1991.Google Scholar
- Lederberg J, Lederberg EM: Replica plating and indirect selection of bacterial mutants. J Bacteriol 1952, 63: 399-406.Google Scholar
- Li LL, McCorkle SR, Monchy S, Taghavi S, van der Lelie D: Bioprospecting metagenomes: glycosyl hydrolases for converting biomass. Biotechnol Biofuel 2009, 2: 10. 10.1186/1754-6834-2-10View ArticleGoogle Scholar
- Miller LG: Use of dinitrosalicylic acid reagent for determination of reducing sugar. Biotechnol Bioeng 1959, 5: 193-219.Google Scholar
- Pires VM, Henshaw JL, Prates JA, Bolam DN, Ferreira LM, Fontes CM, Henrissat B, Planas A, Gilbert HJ, Czjzek M: The crystal structure of the family 6 carbohydrate binding module from Cellvibrio mixtus endoglucanase 5A in complex with oligosaccharaides reveals two distinct binding site with different ligand specificities. J Biol Chem 2004, 279: 21560-21568. 10.1074/jbc.M401599200View ArticleGoogle Scholar
- Rahikainen JL, Mikander S, Marjamaa K, Tamminen T, Lappas A, Viikari L, Kruus K: Inhibition of enzymatic hydrolysis by residual lignins from softwood – study of enzyme binding and inactivation on liginin-rich surface. Biotechnol Bioeng 2011, 108: 2823-2834. 10.1002/bit.23242View ArticleGoogle Scholar
- Rahikainen JL, Martin-Sampedro R, Heikkinen H, Rovio S, Marjamaa K, Tamminen T, Rojas OJ, Kruus K: Inhibitory effect of lignin during cellulose bioconversion: the effect of lignin chemistry on non-productive enzyme adsorption. Bioresour Technol 2013, 133: 270-278.View ArticleGoogle Scholar
- Rahikainen JL, Moilanen U, Nurmi-Rantala S, Lappas A, Koivula A, Viikari L, Kruus K: Effect of temperature on lignin-derived inhibition studied with three structurally different cellobiohydrolases. Bioresour Technol 2013, 146: 118-125.View ArticleGoogle Scholar
- Saitou N, Nei M: The neighbor-joining method: a new method for reconstructing phylogenetic trees. Mol Biol Evol 1987, 4: 406-425.Google Scholar
- Sun Y, Cheng J: Hydrolysis of lignocellulosic materials for ethanol production: a review. Biores Technol 2002, 83: 1-11. 10.1016/S0960-8524(01)00212-7View ArticleGoogle Scholar
- Voget S, Leggewie C, Uesbeck A, Raasch C, Jaeger KE, Streit WR: Prospecting for novel biocatalysts in a soil metagenome. Appl Environ Microbiol 2003, 69: 6235-6242. 10.1128/AEM.69.10.6235-6242.2003View ArticleGoogle Scholar
- Weil J, Westgate P, Kohlmann K, Ladisch MR: Cellulose pretreatments of lignocellulosic substrates. Enzyme Microb Technol 1994, 16: 1002-1004. 10.1016/0141-0229(94)90012-4View ArticleGoogle Scholar
- Wojtczak G, Breuil C, Yamuda J, Saddler JN: A comparision of the thermostability of cellulose from various thermophilic fungi. Appl Miocrobiol Biotechnol 1987, 27: 82-87.Google Scholar
- Zhang J, Tang M, Viikari L: Xylans inhibit enzymatic hydrolysis of lignocellulosic materials by cellulases. Bioresour Technol 2012, 121: 8-12.View ArticleGoogle Scholar
- Zhou JZ, Bruns MA, Tiedje JM: DNA recovery from soils of diverse compositions. Appl Environ Microbiol 1996, 71: 2347-2354.Google Scholar
This article is published under license to BioMed Central Ltd. This is an Open Access article distributed under the terms of the Creative Commons Attribution License (http://creativecommons.org/licenses/by/4.0), which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly credited.