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Energy Extraction From Toxic Waste Originating From Food Processing Industries 27
Inlet For cooking Pipe
and electricity
Seal Access cover
CH + CO 2 4 Methanogenesis
4
Biogas Nutrient-rich
sludge for fertilizer
Complex proteins, O +CO 2 + H
fats, and carbohydrates CH 2
3 Acetogenesis
1 Hydrolysis Slurry
Short-chain
volatile acids
O
Amino acids, fatty acids,
and simple sugars OH
O
OH
2 Acidogenesis
Fig. 3.7 Photograph of anaerobic digester.
in January–February [31]. Thus, there is a need to improve the overall effi-
ciency of the anaerobic digestion process. Attempts have been made to ei-
ther reduce the HRT or enhance the biogas production for the same HRT
by incorporating fixed film matrices in the reactors [32]. The photograph of
anaerobic digester is shown in Fig. 3.7.
Several mechanical, thermal, chemical, and biological pretreatment
methods have been investigated to improve the performance by easy ac-
cessibility of intermolecular matters to anaerobic micro-bacteria. Farland
[33] reported that the stability of the anaerobic process and the rate of gas
production depend upon the organic feed rates. Deublein and Steinhauser
[34] documented that the optimized methane gas production is dependent
on the rate of optimized decomposition.
3.5.3.1 Biogas From Biomass, a Feasibility Issue
Weiland [35] documented that biomass is comprised of a high content
of cellulose, proteins, hemicellulose, lignin, and extractives, thus forming
a natural renewable resource for an eco-friendly inexpensive and sustain-
able material. These materials of biomass are readily available in municipal
solid waste (MSW), food waste (FW), crop residue (CR), agricultural waste
(AW), and wood residues (WR).