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14 декабря, 2021
In open anaerobic ecosystems where biomass is not sterilized, the degradation carried out by ubiquitous microorganisms normally follows a rather well-defined pathway as shown in Fig. 1. If no inorganic electron acceptors such as sulfate or nitrate are present, methane is the inevitable terminal biofuel product since all intermediates from the fermentative bacteria can be degraded to methane, carbon dioxide, and water. The natural end products of the fermentative bacteria in such open systems are short-chained volatile fatty acids, hydrogen, and carbon dioxide. Alcohols are only formed in small amounts. Approximately 90% of the energy of the converted biomass is conserved in the end products, and only 10% is used by the fermentative bacteria [1]. In the terminal formation of methane from the fermentation
Fig. 1 Degradation pathway and available energy to participating microorganisms and in intermediates and end products during anaerobic degradation of organic matter. The percentages refer to residual energy in substrate and fermentation products (in bold), and to the energy used by the microorganisms (in italics) |
products, the biomass carbon is sequestered completely to the most oxidized (CO2) and the most reduced (CH4) states. Only 4% of the original biomass energy is utilized by the terminal link, leaving 86% of the original energy content in the formed methane (Fig. 1), which constitutes the sound energetic rationale for the extensive exploitation of the biogas process. The obligate biology leading to methane formation has an intrinsic stability governed by thermodynamics, which ensures that methanogenesis proceeds within a wide spectrum of physical and chemical conditions. In most methanogenic fermentations the methane yield lies close to the theoretical maximum of 3 mol of methane per mol of glucose, calculated from the Buswell equation [12,13]:
CaHbOc + (a — b/4 — c/2)H2O ^
(a/2 — b/8 + c/4)CO2 + (a/2 + b/8 — c/4)CH
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