Biofuels in Perspective
Biofuels in Perspective
Biofuels in Perspective
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180 <strong>Biofuels</strong><br />
Table 10.3 Demand of macronutrients for cane production required to produce of 1 m 3 of alcohol and<br />
availability <strong>in</strong> the liquid and solid residues<br />
kg/m3 of alcohol % of the demand<br />
N P K N P K<br />
Demand for production 30 5 30 – – –<br />
In v<strong>in</strong>asse 4 3 20 13 60 67<br />
In bagasse 16 0.4 1.2 53 8 4<br />
Total <strong>in</strong> subproducts 20 3.4 21.2 67 68 71<br />
significantly, thus reduc<strong>in</strong>g the potential for methane and power production. In pr<strong>in</strong>ciple,<br />
the v<strong>in</strong>asse should be processed shortly after it has been produced. However the duration<br />
of the sugar cane harvest is not more than about 180 days per year, so that dur<strong>in</strong>g one<br />
semester per year there would be no v<strong>in</strong>asse digestion nor associated methane production.<br />
If year around energy is to be produced, one solution is to store part of the bagasse and use<br />
this material between harvests.<br />
A retention time of 10–12 days <strong>in</strong> the reactor is required for the conversion of 50 % of<br />
the solids <strong>in</strong>to methane. Consider a cont<strong>in</strong>uous solid anaerobic digester, for example the<br />
DRANCO type (De Baere, 2001). Assum<strong>in</strong>g that the digested bagasse has a 25 % solids,<br />
this results <strong>in</strong> a load<strong>in</strong>g rate of 250/12 ≈ 20 kg DM/m 3 .d. Because the production of 1 m 3<br />
of alcohol leads to the release of 2 t DM of biogases, the required volume is 2000/20 =<br />
100 m 3 of solids digester per m 3 /d of alcohol. If power production is spread out over the<br />
whole year, the volume can be decreased to 50 m 3 , provided bagasse is stored: by the end of<br />
the season half of the yearly bagasse production or 0,5*4*180 = 360 t per m 3 /d of alcohol<br />
(50 % humidity) must have been accumulated. It is important to note that anaerobic bagasse<br />
digestion or elutriation have not yet been implemented <strong>in</strong> cont<strong>in</strong>uous reactors at pilot or<br />
full scale. Therefore, at this stage the costs of bagasse digestion cannot yet be evaluated<br />
with a high degree of precision and reliability.<br />
In Figures 10.7 and 10.8 it can be noted that the productive use of residues not only<br />
<strong>in</strong>creases very significantly the output of useful energy, it also enables the recovery of a<br />
large fractions of the nutrients required for cane production. Table 10.3 shows the demand<br />
of macronutrients as well as the masses or percentages present <strong>in</strong> stillage and bagasse.<br />
Anaerobic bagasse digestion m<strong>in</strong>eralizes practically all the nitrogen, so that after digestion<br />
some 67 % of the required nutrients for production are <strong>in</strong> the liquid phase and can be<br />
recovered just by recycl<strong>in</strong>g the effluents on the sugar cane field. Thus only about 30 % of<br />
the nutrients <strong>in</strong> a production cycle are lost and must be replenished.<br />
Table 10.4 illustrates that the conventional alcohol production <strong>in</strong> Brazil can be <strong>in</strong>creased<br />
<strong>in</strong> terms of output of products from 2775 US $ per ha per year to 3775 US $ per ha per year<br />
(factor 1.36) by <strong>in</strong>corporat<strong>in</strong>g the anaerobic digestion of the stillage and biogases. However,<br />
direct total digestion of the sugar cane biomass and conversion to green electricity is not<br />
yet competitive to the production alcohol for motor vehicles.<br />
Nationwide the electric power production potential of v<strong>in</strong>asse digestion and bagasse<br />
combustion (1.5 MWh per m 3 of alcohol) at the current alcohol production rate of 15*10 6<br />
m 3 /ano is 22.5 TWh/year or 2.6 GW if year around production is applied. This represents