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Utilization of Agro-industrial Wastes for the Simultaneous Production of Amylase and Xylanase by Thermophilic Actinomycetes

Abstract

Agro-industrial wastes such as sugarcane bagasse, wheat bran, rice bran, corn cob and wheat straw are cheapest and abundantly available natural carbon sources. The present study was aimed to production of amylase and xylanase simultaneously using agro-industrial waste as the sole carbon source. Seven thermophilic strains of actinomycete were isolated from the mushroom compost. Among of these, strain designated MSC702 having high potential to utilize agro-industrial wastes for the production of amylase and xylanase. Strain MSC702 was identified as novel species of Streptomyces through morphological characterization and 16S rRNA gene sequence. Enzyme production was determined using 1% (w/v) of various agro-industrial waste in production medium containing (g/100mL): K2HPO4(0.1), (NH4)2SO4(0.1), NaCl (0.1), MgSO4(0.1) at pH 7.0 after incubation of 48 h at 50°C. The amylase activity (373.89 IU/mL) and xylanase activity (30.15 IU/mL) was maximum in rice bran. The decreasing order of amylase and xylanase activity in different type of agro-industrial wastes were found rice bran (RB) > corn cob (CC) > wheat bran (WB) > wheat straw (WS) > sugarcane bagasse (SB) and rice bran (RB) > wheat bran (WB) > wheat straw (WS) > sugarcane bagasse (SB) > corn cob (CC), respectively. Mixed effect of different agro-industrial wastes was examined in different ratios. Enzyme yield of amylase and xylanase was ~1.3 and ~2.0 fold higher with RB: WB in 1:2 ratio.

Agro-industrial wastes; thermophilic actinomycetes; Streptomyces; amylase; xylanase


INDUSTRIAL MICROBIOLOGY

Utilization of Agro-industrial Wastes for the Simultaneous Production of Amylase and Xylanase by Thermophilic Actinomycetes

Renu Singh* * Corresponding Author. Mailing address: Laboratory of Microbiology, Department of Botany, Christ Church College, Kanpur, 208001, India.; Tel.: +91-9838111617.; E-mail: renu_87@sify.com ; Vishal Kapoor; Vijay Kumar

Laboratory of Microbiology, Department of Botany, Christ Church College, Kanpur, 208001, India

ABSTRACT

Agro-industrial wastes such as sugarcane bagasse, wheat bran, rice bran, corn cob and wheat straw are cheapest and abundantly available natural carbon sources. The present study was aimed to production of amylase and xylanase simultaneously using agro-industrial waste as the sole carbon source. Seven thermophilic strains of actinomycete were isolated from the mushroom compost. Among of these, strain designated MSC702 having high potential to utilize agro-industrial wastes for the production of amylase and xylanase. Strain MSC702 was identified as novel species of Streptomyces through morphological characterization and 16S rRNA gene sequence. Enzyme production was determined using 1% (w/v) of various agro-industrial waste in production medium containing (g/100mL): K2HPO4(0.1), (NH4)2SO4(0.1), NaCl (0.1), MgSO4(0.1) at pH 7.0 after incubation of 48 h at 50°C. The amylase activity (373.89 IU/mL) and xylanase activity (30.15 IU/mL) was maximum in rice bran. The decreasing order of amylase and xylanase activity in different type of agro-industrial wastes were found rice bran (RB) > corn cob (CC) > wheat bran (WB) > wheat straw (WS) > sugarcane bagasse (SB) and rice bran (RB) > wheat bran (WB) > wheat straw (WS) > sugarcane bagasse (SB) > corn cob (CC), respectively. Mixed effect of different agro-industrial wastes was examined in different ratios. Enzyme yield of amylase and xylanase was ~1.3 and ~2.0 fold higher with RB: WB in 1:2 ratio.

Key words: Agro-industrial wastes, thermophilic actinomycetes, Streptomyces, amylase, xylanase

INTRODUCTION

The continued development of biosustainable and renewable resource technology is of great importance with respect to environmental concerns. The bioconversion of lignocellulosics, natural and anthropogenic, in the production of biofuels is an extremely important part of renewable resource technology. A large amount of agro-industrial waste generated every year in all over the world contained high lignocellulosics and starch content. Lignocellulose is the major component of biomass, comprising around half of the plant matter produced by photosynthesis (also called photomass) and representing the most abundant renewable organic resource in soil (34). It consists of three types of polymers, cellulose, hemicellulose and lignin that are strongly intermeshed and chemically bonded by non-covalent forces and by covalent cross-linkages (28).

The microorganisms degrade lignocellulosic and starchy materials due to their highly efficient enzymatic system. The two types of extracellular enzymatic systems are present in microorganisms; the hydrolytic system (responsible for polysaccharide degradation) and ligninolytic system (degrades lignin and opens phenyl rings) (34). Thermophilic actinomycetes are well known components of the microbiota of composts and play an important role in habitats where decomposition of organic matter such as lignocellulose, starch and chitin, takes place at elevated temperatures and under aerobic conditions. They are aerobic, Gram-positive with high G + C in DNA (10).

Amylases and xylanases are hydrolytic enzymes those facilitate the complete hydrolysis of starch and xylan respectively. Xylan is the major structural component of plant cell walls and the most renewable hemicellulose, composed of 1, 4- linked β-D-xylopyranosyl residues. A great deal of attention has been received due to the potential application of amylases in sugar, textile, paper, brewing, distilling industries and pharmaceuticals (2, 13, 27) while of xylanases in the food, feed, pulp and paper industries (5, 7, 16, 24, 43). The advantages of using thermostable enzymes in industrial processes include the decreased risk of contamination, cost of external cooling and increased diffusion rate with resistant to denaturing agents, solvents and proteolytic enzymes (6, 20).

In order to convert biomass to ethanol, the efficient utilization of both starch-derived and hemicellulose-derived carbohydrates is essential. At present, the dominant cost element in fermentative production of fuel ethanol is starch, though some fermentable starch and sucrose are easily obtainable from agricultural by-products such as sugarcane bagasse, wheat bran, rice bran, corn cob and wheat straw (12, 19, 36). Expansion of this fermentation process towards utilization of low-value substrates such as agro-industrial wastes offers a great potential for reducing the production cost and increasing the use of ethanol as a fuel additive. The conventional method of starch and hemicellulose hydrolysis using acid has been replaced by processes using saccharifying enzymes of microbial origin (39).

The selection of a particular strain, however, remains a tedious task, particularly when commercially significant enzyme yields are required. Agro-industrial wastes are generally considered the best substrates for the solid state fermentation (SSF) processes (17) but in present study we utilized these in submerged fermentation (SmF). Since thermostability is a feature of most of the enzymes sold in bulk for industrial application, thermophilic microorganisms are of particular interest for the production of thermostable amylases and xylanases. This study was focused on the isolation and selection of particular strain having affinity to produce industrially valuable thermostable extracellular enzymes (amylase and xylanase) from the low cost carbon substrates to reduce the cost of enzyme production and make a better alternative for utilization of crop biomass (largest renewable reservoir of potentially fermentable carbohydrates) generated every year in million tones as "waste".

MATERIALS AND METHODS

All the media ingredients and chemicals were of analytical grade, procured from E-Merck, Hi-Media and Qualigen Chemicals, India, Ltd. All agro-industrial wastes (sugarcane bagasse, wheat bran, rice bran, corn cob and wheat straw) used as sole carbon source, were obtained from the local market, Kanpur, India. All the substrates prior to the use for enzyme production were oven dried at 65°C. Sugarcane bagasse, corn cob and wheat straw were powdered in a grinder to get 4-5 mm particle size while wheat bran and rice bran were used at mesh size 2-4 mm.

Sampling site and collection of samples

Our sampling site Kanpur is situated in India within Uttar Pradesh province in between 26° 28′ North latitude and 80° 21′ East longitude with an elevation of 125.6 m. Twelve mushroom compost samples were collected from Mushroom Research and Development Centre, Department of Plant Pathology,Chandra Shekhar Azad University of Agriculture and Technology, Kanpur, India. These samples were collected from four different zones (outermost, under depth 25 cm, under depth 50 cm, centre) covering whole diameter of the heap of mushroom compost, in three visits.

Samples of mushroom compost were collected by inserting a polyvinyl corer (10 cm diameter) (previously sterilized with alcohol) into the heap of mushroom compost. The central portion of the top 2 cm sediment sample has been taken out with the help of a sterile spatula. These samples have been transferred to a sterile polythene bags and kept at 4ºC until the experiments were carried out.

Isolation and maintenance of isolates

Serial dilution method (42) was applied for isolation of thermophilic actinomycetes. They were isolated on M medium agar (25) containing (g/100mL) soluble starch 1.0, dipotassium hydrogen phosphate (K2HPO4) 0.1, ammonium sulphate {(NH4)2SO4} 0.1, sodium chloride (NaCl) 0.1, magnesium sulphate (MgSO4. 7H2O) 0.1, pH 7.0 at 45°C. M medium was modified with 1% (v/v) trace metal salt solution (40). All isolated strains of thermophilic actinomycetes were maintained on modified M medium agar slants at 4ºC.

Selection of working strain

Selection of working strain was done on the basis of their enzyme (amylase and xylanase) productivity on agro-industrial waste (wheat straw). Seven isolated strains of thermophilic actinomycetes were inoculated in M broth medium (25) contained 1% (w/v) wheat straw (WS). Highest enzyme (amylase and xylanase) producing strain was selected for further study.

To enhance the production of both enzymes, different other types of agro-industrial wastes (sugarcane bagasse (SB), wheat bran (WB), rice bran (RB) and corn cob (CC)), its combinations (1:1 ratio) and ten combinations (0.5:0.5; 1:1; 1:2; 1:3; 1:4; 1:5; 2:1; 3:1; 4:1 and 5:1) of the rice bran and wheat bran were analyzed.

Inoculum preparation

The inoculum was prepared by adding 10 ml sterile distilled water into the 2-3 days old culture slant and a cell suspension was made with the help of a sterile loop. 1 ml of the cell suspension (1.9-2.2 x 108 CFU/ml) was used in 100 ml medium (250 mL Erlenmeyer) as the inoculum for subsequent fermentation. The number of viable spores in the inoculum was determined by the pour plate count technique.

Enzyme production in submerged fermentation (SmF)

Amylase and xylanase production in SmF was carried out using the basal medium containing (g/100mL) dipotassium hydrogen phosphate (K2HPO4) 0.1; ammonium sulphate {(NH4)2SO4} 0.1; sodium chloride (NaCl) 0.1; magnesium sulfate (MgSO4.7H2O) 0.1, pH 7.0. Initially all the tested agro-industrial wastes were used at 1% (w/v) in basal medium. Production medium (100 mL) was placed in Erlenmeyer flask (250 mL) and autoclaved at 121°C (15 lbs pressure) for 20 min and cooled. After sterilization, production medium was inoculated with 1% inoculum and incubated at 50°C for 48 h. The fermented biomass were filtered with Whatman filter papers 1 (qualitative circles, 125 mm diameter) and centrifuged at 5000 g for 20 min at 4°C, and the clear cell-free supernatant was used as a source of enzymes.

Analytical procedure

Amylase and xylanase activity was estimated by measuring the reducing sugar released during hydrolysis of 1.0% (w/v) starch and oat-spelt xylan, respectively in 0.1 M phosphate buffer (pH 7.0) by enzyme (cell free supernatant) incubated at 50°C for 10 minutes using 3, 5-dinitrosalicylic acid method (21). Absorbance at 550 nm and 540 nm respectively was recorded by using UV-visible spectrophotometer (UV-1700 Pharmaspec Shimadzu) and activity was calculated from a standard curve using maltose and xylose as the standard. One unit (U) of enzyme activity was defined as the amount of enzyme required for the liberation of 1 µmol of reducing sugar equivalent to maltose or xylose respectively per minute under assay condition. All experiments were carried out in triplicate and average values were given in presented data.

Sequencing of 16S rRNA and analysis of sequence data

The chromosomal DNA of strain MSC702 was isolated accordingto Rainey et al. (32). The 16S rRNA gene was amplified withprimers 8-27f (5'-AGAGTTTGATCCTGGCTCAG-3') and 1500r (5'-AGAAAGGAGGTGATCCAGCCA-3').The amplified DNA fragment was separated on 1% agarose gel,eluted from the gel and purified using a QIAquick gel extractionkit (Qiagen). The purified PCR product was sequenced with fourforward and three reverse primers, namely 8-27f, 357f (5'-CTCCTACGGGAGGCA GCAG-3'),704f (5'-TAGCGGTGAAATGCGTAGA-3'), 1114f (5'-GCAACGAGCGCAACC-3'),685r (5'-TCTACGCATTTCAC CGCTAC-3'), 1110r (5'-GGGTTGCGCTCGTTG-3')and 1500r (Escherichia coli numbering system). The 16S rRNAgene sequence was determined by the dideoxy chain-terminationmethod with the Big-Dye terminator kit using an ABI 310 GeneticAnalyzer (Applied Biosystems). The 16S rRNA gene sequence ofstrain MSC702 generated in this work (1474 bases) was alignedwith 16S rRNA gene sequences of other membersof the genus Streptomyces. A sequence similarity search was done using GenBank BLASTN (1).

RESULTS AND DISCUSSION

Thermophilic microorganisms have been proven as a potential source of bioactive compounds and richest source of secondary metabolites. They are the most economically and biotechnologically valuable microorganisms. However, the research on thermophilic actinomycetes from Indian peninsula is very scanty. In the present study we have demonstrated that our isolated strains of thermophilic actinomycetes having potential to produce extracellular enzymes (amylase and xylanase) simultaneously using agro-industrial waste as sole carbon source. The increasing expansion of agro-industrial activity has led to the accumulation of a large quantity of lignocellulosic residues all over the world.

Isolation and screening of thermophilic actinomycetes

In the course of isolation and systematic screening of thermophilic actinomycetes, we have isolated seven thermophilic strains of actinomycetes. 10-6 dilution was found to be most suitable for isolation of thermophilic actinomycetes from mushroom compost. Morphological and colony characteristics of isolates were described in Table 1. Screening of isolates for utilization of agro-industrial wastes and their simultaneous production of amylase and xylanase was done on wheat straw as sole carbon source. Out of seven isolates four isolates (MSC702, MSC703, MSC704 and MSC707) have potential to produce amylase and xylanase enzymes simultaneously on agro-industrial waste (wheat straw) (Table 1). Isolate designated MSC702 having highest potential to produce amylase (234.54 IU/ml) and xylanase (28.40 IU/ml) on wheat straw. Strain MSC702 seems to be a novel species of Streptomyces through morphological characterization and 16S rRNA gene sequence.

Characterization of the strain

An almost complete 16S rRNA gene sequence (1474 nucleotides) for strain MSC702 was determined in this study. This sequence was subjected to similarity searches against public databases to infer a possible relationship of strain MSC702. This analysis revealed that strain MSC702 was a member of the genus Streptomyces. The comparative analysis of 16S rRNA gene sequence yielded following closest fits: 98.28% (25 nucleotides differences out of 1492). S. thermocoprophilus B19T (18), 98.13% with S. mexicanus CH-M-1035T (27 nucleeotides differences out of 1450) (29), 98.08% with S. laurentii LMG 19959T (28 nucleotides differences out of 1460) (41), 97.94% with S. coeruleorubidus NBRC 12761T (30 nucleotides differences out of 1459) (31), 97.89% with S. curacoi NRRL B-2901 (31 nucleotides differences out of 1471) (Cataldi 1963; have no publication) and 97.88% with S. thermoviolaceus subsp. apingens DSM 41392T (31 nucleotides differences out of 1462) (14).

It is apparent from the genotypic data that strain MSC702 forms a distinct centre of taxonomic variation within the genus Streptomyces. Further chemotaxonomical and biochemical studies will be carried out for this microorganism be recognized as a novel species of Streptomyces.

Streptomyces sp. MSC702 was deposited in the Microbial Type Culture Collection and Gene Bank (MTCC), Chandigarh, India with accession number MTCC 10772.

Production of amylase and xylanase by Streptomyces sp. MSC702

To check the agro-industrial wastes suitability for amylase and xylanase production by Streptomyces sp. MSC702, fermentation was done with the addition of 1 % (w/v) sugarcane bagasse (SB), wheat bran (WB), rice bran (RB) and corn cob (CC) separately in the production medium by replacing wheat straw (WS). The order of substrate suitability was RB > CC > WB > WS > SB and RB > WB > WS > SB > CC for amylase and xylanase production respectively (Table 2). Table 2 also describes the starch and hemicelluloses content in agro-industrial wastes. Rice bran was found most suitable for amylase (373.89 IU/mL) and xylanase (30.15 IU/mL) production by Streptomyces sp. MSC702. Present study on utilization of agro-industrial wastes for the production of amylase and xylanase by Streptomyces sp. MSC702 showed that production of amylase is directly related to the raw starch content in agro-industrial wastes while high hemicellolose content in agro-industrial wastes have no effect on xylanase production. This may be due to the preferred utilization of starch for their metabolic activities by Streptomyces sp. MSC702 over hemicellulose. Stutzenberger (38) reported production of extracellular enzymes (amylase and xylanase) on sugarcane bagasse as sole carbon source by Thermomonospora curvata. Recently, both the enzymes were attempted separately by the workers. Kammoun et al. (15) reported amylase (148.0 U/mL) production on gruel (wheat grinding by-product) based medium by Aspergillus oryzae CBS 819.72 in SmF. Dey et al. (8) used wheat bran as media component for the production of amylase (76.4 U/ml) by Bacillus circulans GRS 313 in SmF. Shatta et al. (35) utilized many agro-industrial wastes (wheat bran, rice bran, yellow maize meal, dry yeast, brewery yeast and corn steep liquor) in basal medium as sole carbon source for the production of amylase by Streptomyces aureofaciens 77 in SmF. Dhillon et al. (9) found that agro-industrial wastes (bagasse, rice straw, oat husk, rice husk and wheat straw) were the best inducers for the xylanase production by Bacillus circulans AB 16 in SmF. They reported highest xylanase activity (20.6 IU/mL) on rice straw.

To enhance the production of amylase and xylanase by Streptomyces sp. MSC702 different combinations (1:1 w/v) of other agro-industrial wastes with rice bran were analyzed in production medium (Fig. 1). In the present study, out of the different combinations (RB:SB; RB:WB; RB:CC and RB:WS) tested, amylase and xylanase activity reached up to 398.10 IU/mL and 53.15 IU/mL respectively in rice bran and wheat bran containing medium. Ten different combinations (0.5:0.5; 1:1; 1:2; 1:3; 1:4; 1:5; 2:1; 3:1; 4:1 and 5:1) of rice bran and wheat bran were analyzed to maximize amylase and xylanase production (Fig. 2). The highest amylase (549.11 IU/mL) and xylanase (63.91 IU/mL) activity was found at the level from the cultivation of mixed substrates of rice bran: wheat bran in 1:2 ratio. Mixed agro-industrial wastes (wheat bran: rice husk; wheat bran: wheat straw) were also utilized by many workers for the production of amylases and xylanases (3, 4) by different microorganisms in SSF.



There are very few reports for the production of extracellular enzymes on mixed agro-industrial wastes in SmF. Mostly, mixed agro-industrial wastes are employed in SSF processes. Rather than applying SmF or SSF, it's important to utilize the agro-industrial wastes for production of industrially valuable products for making low cost processes and point of environmental concern. Various waste and underutilized lignocellulosic agricultural residues can serve as low-cost feed stock for production of industrially important extracellular enzymes (amylase and xylanase).

CONCLUSION

Lignocellulosic residues from wood, grass, agricultural, forestry wastes and municipal solid wastes are particularly abundant in nature and have a potential for bioconversion into many useful biological and chemical products. The results showed the potential use of cheaply available raw substrates (agro-industrial wastes) for single step production of extracellular enzymes (amylase and xylanase) by a newly isolated strain of thermophilic actinomycete, Streptomyces sp. MSC702 in SmF. The mixture of rice bran and wheat bran (1:2) was found as the best substrate and support in SmF in laboratory level fermentations. The enzyme activity was reached up to 549.11 IU/mL (~1.3-fold increase) and 63.91 IU/mL (~2.0-fold increase) for amylase and xylanase, respectively, on the mixture of rice bran and wheat bran (1:2) as sole carbon source. The use of this microorganism, Streptomyces sp. MSC702 in low cost bioremediation processes might be attractive for given their highly efficient starch and lignocellulose hydrolysis enzyme machinery.

ACKNOWLEDGEMENTS

Renu Singh thanks the University Grant Commission, Selection and Award Bureau, New Delhi, Government of India for providing 'Rajiv Gandhi National Fellowship' to carry out this work.

Submitted: April 01, 2011

Approved: June 07, 2012

  • 1. Altschul, S.F.; Madden, T.L.; Schaffer, A.A.; Zhang, J.; Zhang, Z.; Miller, W.; Lipman, D.J. (1997). Gapped BLAST and PSI-BLAST: a new generation of protein database search programs. Nucleic Acids Res 25, 3389-3402.
  • 2. Aygan, A.; Arikan, B.; Korkmaz, H.; Dincer, S.; Colak, O. (2008). Highly thermostable and alkaline -amylase from a halotolerant-alkaliphilic Bacillus sp. AB68.Braj. J. Microbiol. 39 (3), 547-553.
  • 3. Azin, M.; Moravej, R.; Zareh, D. (2007). Production of xylanase by Trichoderma longibrachiatum on a mixture of wheat bran and wheat straw:Optimization of culture condition by Taguchi method. Enzyme Microb. Tech. 40, 801-805.
  • 4. Baysal, Z.; Uyar, F.; Aytekin, C. (2003). Solid state fermentation for production of -amylase by a thermotolerant Bacillus subtilis from hot-spring water. Process Biochem. 38, 1665-1668.
  • 5. Beg, Q.A.; Kapoor, M.; Mahajan, G.; Hoondal, S. (2001). Microbial xylanases and their industrial applications: a review. Appl. Microbiol. Biotechnol. 56, 326-338.
  • 6. Bragger, J.M.; Daniel, R.M.; Coolbear, T.; Morgan, H.W. (1989). Very stable enzymes from extremely thermophilic archebacteria and eubacteria. Appl. Microbiol. Biotechnol. 31, 556-561.
  • 7. Damaso, M.C.T.; Andrade, C.M.M.C.; Jr, N.P. (2002). Production and properties of the cellulase-free xylanase from Thermomyces lanuginosus IOC-4145. Braj. J. Microbiol. 33, 333-338.
  • 8. Dey, G.; Mitra, A.; Banerjee, R.; Maiti, B.R. (2001). Enhanced production of amylase by optimization of nutritional constituents using response surface methodology. Biochem. Eng. J. 7, 227-231.
  • 9. Dhillon, A.; Gupta, J.K.; Jauhari, B.M.; Khanna, S. (2000). A cellulase-poor, thermostable, alkalitolerant xylanase produced by Bacillus circulans AB 16 grown on rice straw and its application in biobleaching of eucalyptus pulp. Bioresource Technol. 73, 273-277.
  • 10. Edwards, C. (1993). Isolation properties and potential applications of thermophilic actinomycetes. Appl. Biochem. Biotechnol. 42, 161-178.
  • 11. Fang, H.Y.; Chang, S.M.; Hsieh, M.C.; Fang, T.J. (2007). Production, optimization growth conditions and properties of the xylanase from Aspergillus carneus M34. J. Mol. Catal. B: Enzymatic. 49, 36-42.
  • 12. Goyal, M.; Kalra, K.L.;Sareen, V.K.; Soni, G. (2008). Xylanase production with xylan rich lignocellulosic wastes by a local soil isolate of Trichoderma viride Braj. J. Microbiol. 39 (3), 535-541.
  • 13. Gupta, R.; Gigras, P.; Mohapatra, H.; Goswami, V.K.; Chauhan, B. (2003). Microbial -amylases: a biotechnological perspective. Process Biochem. 38, 1599-1616.
  • 14. Henssen, A. (1957). Morphology and system of thermophilic actinomycetes. Arch. Mikrobiol. 26 (4), 373-414.
  • 15. Kammoun, R.; Naili, B.; Bejar, S. (2008). Application of a statistical design to the optimization of parameters and culture medium for - amylase production by Aspergillus oryzae CBS 819.72 grown on gruel (wheat grinding by-product). Bioresource Technol 99, 5602-5609.
  • 16. Kapoor, M.; Beg, Q.K.; Bhushan, B.; Singh, K.; Dadhich, K.S.; Hoondal, G.S. (2001). Application of an alkaline and thermostable polygalacturonase from Bacillus sp. MG-cp-2 in degumming of ramie (Boehmeria nivea and sunn hemp (Crotalaria juncea bast fibers. Process Biochem. 36, 803-807.
  • 17. Kapoor, V.; Singh, R.; Banerjee, R; Kumar, V. (2011). Application of response surface methodology (RSM) for optimization of physico-chemical parameters for the production of endoglucanase by Trichoderma ressei Rut C-30 using agro-residues. Dyn. Biochem. Process Biotech. Mol. Biol. (2), 35-40.
  • 18. Kim, B.; Al-Tai, A.M.; Kim, S.B.; Somasundaram, P.; Goodfellow, M. (2000). Streptomyces thermocoprophilus sp nov, a cellulase-free endo-xylanase-producing streptomycete. Int. J. Syst. Evol. Microbiol. 50, 505-509.
  • 19. Lee, J. (1997). Biological conversion of lignocellulosic biomass to ethanol. J. Biotechnol. 56, 1-24.
  • 20. Lin, L.L.; Chyau, C.C.; Hsu, W.H. (1998). Production and properties of a raw starch-degrading amylase from the thermophilic and alkalophilic Bacillus sp. TS-23. Biotechnol. Appl. Biochem. 28, 61-68.
  • 21. Miller, L. (1959). Use of dinitrosalicylic acid reagent for determination of reducing sugar. Anal. Chem. 31, 426-428.
  • 22. McKendry, P. (2002). Energy production from biomass: overview of biomass. Bioresource Technol. 83, 37-43.
  • 23. Mihara, S.; Inaba, Y.; Tachibana, K.; Endo, T.; Yasui, E. (1974). Process for complete separation of constituents of rice-bran and the like, United State Patent, 3852504.
  • 24. Niehaus, F.; Bertoldo, C.; Kahler, M.; Antranikian, G. (1999). Extremophiles as a source of novel enzymes for industrial applications. Appl. Microbiol. Biotechnol. 51, 711-729.
  • 25. Obi, S.K.C.; Odibo, F.J.C. (1984). Partial purification and characterization of a thermostable actinomycete -amylase. Appl. Environ. Microbiol. 47 (3), 571-575.
  • 26. Osborne, T.B.; Mendel, L.B. (1919). The nutritive value of the wheat kernel and its milling products. J. Biol. Chem. 37, 557-601.
  • 27. Pandey, A.; Nigam, P.; Soccol, C.R.; Soccol, V.T.; Singh, D.; Mohan, R. (2000). Advances in microbial amylases. Biotechnol. Appl. Biochem. 31, 135-152.
  • 28. Perez, J.; Munoz-Dorado, J.; De-la-Rubia, T.; Martinez, T. (2002). Biodegradation and biological treatments of cellulose, hemicellulose and lignin: an overview. Int. Microbiol 5, 53-63.
  • 29. Petrosyan, P.; Varela, M.G.; Madrigal, A.L.; Huitron, C.; Flores, M.E. (2003). Streptomyces mexicanus sp. nov., a xylanolytic micro-organism isolated from soil. Int. J. Syst. Evol. Microbiol. 53, 269-273.
  • 30. Prassad, S.; Singh, A.; Joshi, H.C. (2007). Ethanol as an alternative fuel from agricultural, industrial and urban residues. Resour. Conserv. Recycling. 50, 1-39.
  • 31. Pridham, T.G.; Hesseltin, C.W.; Benedict, R.G. (1958). A guide for the classification of streptomycetes according to selected groups. Placement of strains in morphological sections. Appl. Microbiol. 6, 52-79.
  • 32. Rainey, F.A.; Ward-Rainey, N.; Kroppenstedt, R.M.; Stackebrandt, E. (1996). The genus Nocardiopsis represents a phylogenetically coherent taxon and a distinct actinomycete lineage: proposal of Nocardiopsaceae fam. nov. Int. J. Syst. Bacteriol. 46, 1088-1092.
  • 33. Rowell, M.R. (1992). Opportunities for lignocellulosic materials and composites. Emerging technologies for material and chemicals from biomass: Proceedings of symposium. Washington, DC: American Chemical Society, p. 26-31.
  • 34. Sanchez, C. (2009). Lignocellulosic residues: Biodegradation and bioconversion by fungi. Biotechnol. Adv. 27, 185-194.
  • 35. Shatta, A.M.; El-hamahmy, A.F.; Ahmed, F.A.; Ibrahim, M.M.K.; Arafa, M.A.I. (1990). The influence of certain nutritional and environmental factors on the production of amylase enzyme by Streptomyces aureofaciens 77. J. Islamic Acad. Sci. (2), 134-138.
  • 36. Singh, R.; Kapoor, V.; Kumar, V. (2011). Production of thermostable, Ca+2-independent, maltose producing -amylase by Streptomyces sp.MSC702(MTCC 10772) in submerged fermentation using agro-residues as sole carbon source. Ann. Microbiol. DOI: 10.1007/s13213-011-0340-4.
  • 37. Singh, R.; Kapoor, V.; Kumar, V. (2011). Influence of carbon and nitrogen sources on the -amylase production by a newly isolated thermophilic Streptomyces sp. MSC702 (MTCC 10772). Asian J. Biothechnol. (6), 540-553.
  • 38. Stutzenberger, F. (1994). Extracellular enzyme production grown on by Thermomonospora curvata grown on bagasse. J. Ind. Microbiol. 13, 35-42.
  • 39. Sukumaran, R.K.; Singhania, R.R.; Mathew, G.M.; Pandey, A. (2009). Cellulase production using biomass feed stock and its application in lignocellulose saccharification for bio-ethanol production. Renewable Energy 34, 421-424.
  • 40. Techapun, C.; Sinsuwongwat, S.; Poosaran, N.; Watanabe, M.; Sasaki, K. (2002). Thermostable and alkaline - tolerant cellulase - free xylanase produced by thermotolerant Streptomyces sp. Ab106. J. Biosci. Bioeng. 93 (4), 431-433.
  • 41. Trejo, W.H.; Dean, L.D.; Pluscec, J.; Meyers, E.; Brown, W.E. (1977). Streptomyces laurentii, a new species producing thiostrepton. The J. Antibiot. 30 (8), 639-643.
  • 42. Waksman, S.A. (1927). Principles of Soil Microbiology, Bailliere Tindall and Cox, London.
  • 43. Wong, K.K.Y.; Saddler, J.N. (1992). Trichoderma xylanases, their properties and application. Crit. Rev. Biotechnol. 12, 413-435.
  • *
    Corresponding Author. Mailing address: Laboratory of Microbiology, Department of Botany, Christ Church College, Kanpur, 208001, India.; Tel.: +91-9838111617.; E-mail:
  • Publication Dates

    • Publication in this collection
      19 Feb 2013
    • Date of issue
      Dec 2012

    History

    • Received
      01 Apr 2011
    • Accepted
      07 June 2012
    Sociedade Brasileira de Microbiologia USP - ICB III - Dep. de Microbiologia, Sociedade Brasileira de Microbiologia, Av. Prof. Lineu Prestes, 2415, Cidade Universitária, 05508-900 São Paulo, SP - Brasil, Ramal USP 7979, Tel. / Fax: (55 11) 3813-9647 ou 3037-7095 - São Paulo - SP - Brazil
    E-mail: bjm@sbmicrobiologia.org.br