Enhancement of methane production from cassava residues by biological pretreatment using a constructed microbial consortium.

In the study, a stable thermophilic microbial consortium with high cellulose-degradation ability was successfully constructed. That several species of microbes coexisted in this consortium was proved by DGGE (denaturing gradient gel electrophoresis) and sequence analysis. The cooperation and symbiosis of these microbes in this consortium enhanced their cellulose-degradation ability. The pretreatment of cassava residues mixing with distillery wastewater prior to anaerobic digestion was investigated by using this microbial consortium as inoculums in batch bioreactors at 55 °C. The experimental results showed that the maximum methane yield (259.46 mL/g-VS) of cassava residues was obtained through 12h of pretreatment by this microbial consortium, which was 96.63% higher than the control (131.95 mL/g-VS). In addition, it was also found that the maximum methane yield is obtained when the highest filter paper cellulase (FPase), carboxymethyl cellulase (CMCase) and xylanase activity and soluble COD (sCOD) are produced.

[1]  Zhonggui Mao,et al.  A novel full recycling process through two-stage anaerobic treatment of distillery wastewater for bioethanol production from cassava. , 2010, Journal of hazardous materials.

[2]  S. Pommier,et al.  Analysis of the outcome of shredding pretreatment on the anaerobic biodegradability of paper and cardboard materials. , 2010, Bioresource technology.

[3]  A. Vivas,et al.  Assessing the impact of composting and vermicomposting on bacterial community size and structure, and microbial functional diversity of an olive-mill waste. , 2009, Bioresource technology.

[4]  P. V. Soest,et al.  Methods for dietary fiber, neutral detergent fiber, and nonstarch polysaccharides in relation to animal nutrition. , 1991, Journal of dairy science.

[5]  Qunhui Wang,et al.  Degradation of volatile fatty acids in highly efficient anaerobic digestion , 1999 .

[6]  Irini Angelidaki,et al.  Comparative study of mechanical, hydrothermal, chemical and enzymatic treatments of digested biofibers to improve biogas production. , 2010, Bioresource technology.

[7]  S. Leschine,et al.  Spirochaeta caldaria sp. nov., a thermophilic bacterium that enhances cellulose degradation by Clostridium thermocellum , 2004, Archives of Microbiology.

[8]  Bo Mattiasson,et al.  Two-stage anaerobic digestion of aerobic pre-treated sisal leaf decortications residues: hydrolases activities and biogas production profile , 2008 .

[9]  Wilson Parawira,et al.  Profile of hydrolases and biogas production during two-stage mesophilic anaerobic digestion of solid potato waste. , 2005 .

[10]  A. E. Greenberg,et al.  Standard Methods for the Examination of Water and Wastewater seventh edition , 2013 .

[11]  Analiza P. Rollon,et al.  Comparison of organic matter degradation and microbial community during thermophilic composting of two different types of anaerobic sludge. , 2009, Bioresource technology.

[12]  S. Haruta,et al.  Construction of a stable microbial community with high cellulose-degradation ability , 2002, Applied Microbiology and Biotechnology.

[13]  R. Bakke,et al.  Enhancing hydrolysis with microaeration. , 2006, Water science and technology : a journal of the International Association on Water Pollution Research.

[14]  K. A. Gilles,et al.  COLORIMETRIC METHOD FOR DETER-MINATION OF SUGAR AND RELATED SUBSTANCE , 1956 .

[15]  Seokhwan Hwang,et al.  Effect of output power, target temperature, and solid concentration on the solubilization of waste activated sludge using microwave irradiation. , 2010, Bioresource technology.

[16]  L. Zhu,et al.  Isolation of genomic DNAs from plants, fungi and bacteria using benzyl chloride. , 1993, Nucleic acids research.

[17]  Seokhwan Hwang,et al.  Co-digestion of lignocellulosics with glucose using thermophilic acidogens , 2004 .

[18]  R. Gonçalves,et al.  Alkaline and acid hydrolytic processes in aerobic and anaerobic sludges: effect on total EPS and fractions. , 2006, Water science and technology : a journal of the International Association on Water Pollution Research.

[19]  Li Jiang,et al.  Optimization of thermal-dilute sulfuric acid pretreatment for enhancement of methane production from cassava residues. , 2011, Bioresource technology.

[20]  Y. Igarashi,et al.  Analysis of a thermophilic lignocellulose degrading microbial consortium and multi-species lignocellulolytic enzyme system , 2010 .

[21]  Bo Mattiasson,et al.  Enhancement of anaerobic batch digestion of sisal pulp waste by mesophilic aerobic pre-treatment. , 2005, Water research.

[22]  F. Smith,et al.  COLORIMETRIC METHOD FOR DETER-MINATION OF SUGAR AND RELATED SUBSTANCE , 1956 .

[23]  X Flotats,et al.  Hydrolysis kinetics in anaerobic degradation of particulate organic material: an overview. , 2008, Waste management.

[24]  B. Schink Energetics of syntrophic cooperation in methanogenic degradation , 1997, Microbiology and molecular biology reviews : MMBR.

[25]  W. Boer,et al.  Phylogenetic composition and properties of bacteria coexisting with the fungus Hypholoma fasciculare in decaying wood , 2009, The ISME Journal.

[26]  Om V. Singh,et al.  Bioconversion of Lignocellulosic Biomass: Biochemical and Molecular Perspectives , 2009 .

[27]  Souichiro Kato,et al.  Effective cellulose degradation by a mixed-culture system composed of a cellulolytic Clostridium and aerobic non-cellulolytic bacteria. , 2004, FEMS Microbiology Ecology.

[28]  Souichiro Kato,et al.  Stable Coexistence of Five Bacterial Strains as a Cellulose-Degrading Community , 2005, Applied and Environmental Microbiology.

[29]  Chulhwan Park,et al.  Upgrading of anaerobic digestion by incorporating two different hydrolysis processes. , 2005, Journal of bioscience and bioengineering.

[30]  T. Chandra,et al.  Cellulose degradation by a mixed bacterial culture , 1987, Journal of Industrial Microbiology.