Biofuels in Perspective
Biofuels in Perspective
Biofuels in Perspective
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184 <strong>Biofuels</strong><br />
Figure 10.9 Schematic representation of a conventional UASB reactor for anaerobic digestion of wastes<br />
with a low suspended solids concentration.<br />
<strong>in</strong> the digestion section is captured by the separator, so that unh<strong>in</strong>dered settl<strong>in</strong>g can take<br />
place <strong>in</strong> the upper zone. To avoid block<strong>in</strong>g of the biogas outlet and allow separation of<br />
biogas bubble from sludge particles, a gas chamber is <strong>in</strong>troduced under the separator element.<br />
The settled sludge particles on the separator elements eventually slide back <strong>in</strong>to the<br />
digestion zone. Thus, the settler enables the system to ma<strong>in</strong>ta<strong>in</strong> a large sludge mass <strong>in</strong> the<br />
reactor, while an effluent essentially free from the suspended solids is discharged. Recently<br />
several variants of the UASB concept have been developed, basically to make more efficient<br />
use of the reactor volume of the digestion section of the reactor (EGSB, Expended<br />
Granular Sludge bed reactor), and/or to <strong>in</strong>crease the efficiency of the sludge retention <strong>in</strong> the<br />
settl<strong>in</strong>g section. Under favourable operational conditions, the UASB reactor can receive an<br />
organic volumetric load of 20 kgCOD/m 3 .d. UASB reactors and its variants are currently<br />
used <strong>in</strong> a variety of liquid waste from agro bus<strong>in</strong>ess (stillage, paper mill, fruit cann<strong>in</strong>g effluents,<br />
tanneries, slaughterhouses) and <strong>in</strong>dustry (breweries, pharmaceutical, petrochemical<br />
wastes)<br />
10.4.2 Different Process Configurations for Wet Digestion Fermenters<br />
If the suspended solids concentration of the material to be digested is not low, biogas can<br />
be produced by wet- or dry-fermentation processes (see Figure 10.10). Today about 90<br />
% of German agricultural biogas plants are operated by wet fermentation, which allows<br />
for a cont<strong>in</strong>uous treatment of liquid, pasty or solid substrates. The typical total solids<br />
content of the digester content is <strong>in</strong> a range of between 8 and 10 % TS which permits<br />
conventional pumps and mixers to be used. Dry-fermentation processes are operated with<br />
solid substrates with a result<strong>in</strong>g total solids content <strong>in</strong> the digester of at least 20 % TS. These<br />
processes are ma<strong>in</strong>ly operated discont<strong>in</strong>uously without any mix<strong>in</strong>g of the solid substrate<br />
(Weiland, 2004b). Dry fermentation is of <strong>in</strong>creas<strong>in</strong>g <strong>in</strong>terest because an extra technology