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This review discusses the problem of management of digested sludge with the use of various methods for the management, including extrusion cooking. Extrusion cooking as a method of management of digestate can be an innovative approach to this topic. Until now there have been no studies on the use of the extrusion process to convert anaerobic digestion sludge. The extrusion process plays an important role in the transformation of materials on an industrial scale. An agricultural biogas plant can produce up to several tons of digested sludge per year (depending on the size of the installation). The most common method for utilisation of this kind of material is the use thereof as a fertiliser. However, this solution requires large areas of farmland. The best methods for conversion of digested sludge are those allowing the separation of the solid part from the liquid part. One of these methods consists in obtaining pellets in the extrusion process.
Apart from the basic input, the right course of fermentation process is determined by the appropriate microorganism populations and the parameters such as: pH, particle size, ionic strength (salinity) and concentration of nutrients and toxic compounds. Three microorganism groups are involved in the process of anaerobic transformation of organic substances in fermentation gas: acid forming bacteria, acetate bacteria and methanogenic bacteria. The first two phases are dominated by the bacteria which are both obligate, facultative and absolute anaerobes (Clostridium spp., Bifidobacterium spp., Streptococcus spp., Enterobacter spp., Bacillus spp., Pseudomonas spp., Aerobacter spp., Alcaligenes spp, Escherichia spp, Lactobacillus spp, Micrococcus spp. czy Flavobacterium spp.) [Nimmrichter, Kuebler, 1999]. Their number during the mesophile fermentation is estimated for between 108-109 per 1ml [Hartman, 1999]. The rate of bacteria growth at both phases fluctuates from 5 hrs, in the presence of carbohydrates to 72 hrs during fat decomposition [Heidrich, Nieścier, 1999]. Presented research aimed at determining the quantity and quality of biogas depending on the microbiological environment in fractions originating from agriculture and agro-food industry. To achieve the objective of research, was evaluated the number and biodiversity of microorganisms that inhabit selected agricultural raw materials used in the production of biogas. A very important aspect of the study was to investigate the species composition of the bacteria and fungi population at different stages of fermentation process. Isolation of microorganisms from selected agricultural raw materials that stimulate the production of biogas could contribute in the future to optimize the process of its obtaining. The following substrates were used in the investigations: distillery’s grain, ensilaged beet pulp, rapeseed cake from biofuel manufacturing, apple pulp, fresh brewer’s grains (wet), corn silage harvested by silage harvester without grain squeezer, corn silage harvested by silage harvester combined with grain squeezer, cellulose from paper industry. Results of analysis of biogass yield in relation to dry mass revealed the highest productivity of the input from waste cellulose from paper industry at low productivity of biomass from agri-food industry. A delay in biogas volume increment visible in the course of fermentation of inputs from agri-food industry biomass is caused by the pasteurization of the mass which lacks microbiological environment, where microorganisms of methane fermentation multiply very slowly. The strongest inhibition of growth and delay in biogass formation was observed in the inputs made on the basis of distillery’s grains and fresh brewers’ grains. A normal productivity of biogass generation was obtained for the inputs prepared from cellulose and corn silage harvested by silage harvester equipped with grain squeezer.
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Recruiting and using agricultural biogas

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We are calling gas acquired of biomass, in particular from the installation alterations of animal wastes or plant, of the sewage treatment plant and landfill sites. The large potential of the biogas production has the farming. In farm households considerable quantities of waste which can be used in the fermentation are arising. Special agricultural cultivations and waste of the food production are a next source of biomass. In the article vital statistics were described about biogas, the process of the biogas production and conditions in which he should run.
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