Development of an anaerobic, thermophilic and cellulolytic consortium to improve anaerobic digestion of lignocellulosic biomass. Kinet R., Rouneaux N.,

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Development of an anaerobic, thermophilic and cellulolytic consortium to improve anaerobic digestion of lignocellulosic biomass. Kinet R., Rouneaux N., Hissette M., Delvigne F., Destain J., Thonart Ph. Bio-industry Units, Gembloux Agro-Bio Tech (GxABT) University of Liège, Belgium Introduction Over the last years, the development of green industrial processes using products from plant biomass induces an important increase of lignocellulosic by- products. Anaerobic digestion of this organic matter can be an attractive option as a source of alternative energy. Moreover, this biological mechanism is also the only degradation pathway occurring in the landfill where organic fraction of municipal solid waste is buried. The low biodegradation rate of this biomass is an important obstacle in anaerobic microbial decomposition process. Rate-limiting step in anaerobic digestion is the lignocellulosic hydrolysis. The purpose of the project is to develop an anaerobic consortium able to degrade lignocellulosic products in thermophilic conditions to improve the methane production. Conclusions  The enrichment methodology, with high temperature compost as microbial source, permitted to obtain a consortium able to degrade efficiently different cellulosic products in anaerobic and thermophilic conditions.  Cellulosis cristalliny slows-down the anaerobic degradation but don’t stop it.  Cellulosis degradation kinetics is divided in three distinct phases comparable to classic microbial grown phases: latency, exponential growth and stationary Cellulosis degradation kinetics Figure 3 : kinetic of filter paper (1% w/v) degradation by consortium (10% v/v). Experiments under thermophilic (55°C) and anaerobic static conditions.  3 distinct phases : -0  22h : adaptation period (0%  6.4%) -22h  70h : exponential degradation phase (6.4%  69%) -70h  142h : slow-down (69%  82%)  Conditions : -Inoculum 10% (v/v) -Anaerobia, 55°C, static -Cellulose 1% (w/v)  Filter paper Isolation of the enriched microbial consortium and its cellulosis degradation ability : Figure 1 : Enrichment method to obtain a cellulolytic, anaerobic and thermophilic consortium from compost. Transfer after 5 days growth at 55°C and in anaerobic static conditions. Scale-up in the fourth transfer (50ml to 1L). Figure 2 : Consortium ability to degrade different cellulosic substrates (filter paper and microcrystalline cellulose) in thermophilic (55°C) and anaerobic static conditions. Maximum degradation ratio (%) obtained after 7 days growth. Microcrystalline cellFilter paper  Successive subcultivations : -Compost as microbial inoculum (10%) -Anaerobia, 55°C, static -Filter paper 1% (w/v) -Transfer after 5 days growth -Scale-up in the fourth transfer (50ml  1L)  Conditions of cellulosis degradation test : -Inoculum 10% (v/v) = consortium obtained after 4 transfers -Anaerobia, 55°C, static -Cellulose 1% (w/v)  Filter paper or Microcrystalline cellulose  Maximal degradation ratio : -Filter paper  99% -Microcrystalline cellulose  98%  Cellulosis cristallinity impact: -Cristallinity slows-down degradation process BUT don’t stop it This work is supported by the national found for scientific research, Brussels, Belgium The authors thank the national found for scientific research, Brussels, Belgium for travel grant