Abstract

The results of long­term research of various ways and methods of collection and processing of blue­green algae that cause “bloom” of the Dnieper reservoirs were presented. The possibility and feasibility of the blue­green algae biomass processing to biogas by methanogenesis were substantiated. It was found experimentally that preliminary mechanical cavitation of the blue­green algae biomass increases the biogas yield by 21.5 %. It was determined that the biogas produced contains up to 72 % of methane and hydrogen, up to 21 % of carbon dioxide, up to 6.5 % of molecular nitrogen. Oxygen, carbon oxide (II), hydrogen sulfide and other impurities constitute up to 2 % of the biogas volume. Biotesting of the spent substrate to determine its toxicity for further use as a biofertilizer in agriculture and forestry was held. Modern methods of electron microscopy found that the average diameter of cells of blue­green algae Microcystis aeruginosa is 3.14 microns. The flow diagram of the blue­green algae biomass complex processing was proposed. It consists in removal of valuable components for medicine, cosmetics, pharmaceu ticals, production of technical detergents, mixtures of aliphatic alcohols as biofuels or additives to gasoline. Thus, it is possible to obtain more biogas by involving the spent activated sludge from sewage treatment facilities in methanogenesis. This will improve the treatment quality of wastewater of various productions. The similarity of the nutritional value of the blue­green algae spent substrate to the green biomass of plants in terms of the elemental composition was experimentally proved. The environmental, energy saving and agricultural efficiency of the cyanogen biomass use was proved.

Highlights

  • Financial instability of the world economy as a result of an energy crisis brings into focus the search for new nonconventional energy sources

  • Since 2007, the first and major stages of the blue-green algae (BGA) biomass deep processing have been tested in the field and laboratory conditions: a) extraction of lipids after cavitation; b) allocation of the biogas resulting from methanogenesis; c) biotesting of the output mineral-organic fertilizer (Fig. 2)

  • The results indicate that the elemental composition of the cyanogenobacteria biomass after methanogenesis is similar to the elemental composition of the green mass of plants

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Summary

Introduction

Financial instability of the world economy as a result of an energy crisis brings into focus the search for new nonconventional (alternative) energy sources. Among others, these include solar energy, accumulated in the biomass of photosynthetic (autotrophic) plants (so-called solar energy bioconservation). It should be noted that to date a certain portion of the energy potential of land-based plant biomass is already utilized by mankind. A sixth of the energy consumed is produced from agricultural and other phytomass. This is equivalent to the daily use of more than 4 million tons of oil. The biomass of aquatic microorganisms and phytoplankton (algae) is not in demand at all [1]

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