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Potenciales y Viabilidad del Uso de Bioetanol y Biodiesel para el ...

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<strong>Potenciales</strong> y <strong>Viabilidad</strong> <strong><strong>de</strong>l</strong> <strong>Uso</strong> <strong>de</strong> <strong>Bioetanol</strong> y <strong>Biodies<strong>el</strong></strong> <strong>para</strong> <strong>el</strong> Transporte en México (SENER-BID-GTZ)<br />

Task 6: Potentials in r<strong>el</strong>ation to sustainability criteria<br />

weight (in water). Cassava also uses large quantities of water. For sugar cane the average<br />

water withdrawal from the sources (rivers, lakes, un<strong>de</strong>rground water) in Brazil 1.8 m 3 / t cane,<br />

but the system can be improved (Chapter 7.2).<br />

Sugar cane (and sorghum): air pollution with bagasse boilers: bagasse boilers are conventional<br />

biomass boilers (r<strong>el</strong>ativ<strong>el</strong>y low temperatures) and the emissions associated are w<strong>el</strong>l known<br />

(PM, NOx, ozone); they can be controlled in all mo<strong>de</strong>rn boilers (Chapter 5.2).<br />

Stillage disposal / utilization: stillage treatment is required to avoid the discharge of high<br />

organic matter loads in rivers. This concept is still true, but the possibility of profiting with<br />

ferti-irrigation has been <strong>de</strong>monstrated with the evolution in the last 25 years: the nutrients<br />

(mainly the Potassium) and water in stillage can pay for all application costs with increased<br />

productivity (Chapter 9). Ferti-irrigation must be the first priority in stillage use, whenever<br />

possible; it requires a better management, but this will be nee<strong>de</strong>d for all the agricultural<br />

procedures in the near future, approaching a “precision agriculture” for the energy crops.<br />

Some lev<strong>el</strong> of concentration (or some process <strong>de</strong>v<strong>el</strong>opment to reduce stillage volume) may be<br />

economically feasible, to improve the distribution in ferti-irrigation, <strong>de</strong>pending on the<br />

topography.<br />

High concentration (~60 Brix) to allow for burning is a process intensive in capital and<br />

energy, being difficult to justify, except in very special situations.<br />

Anaerobic Digestion is an option to be reserved for situations where full ferti-irrigation is not<br />

possible. It usually is not sufficient to comply with the local requirements set by the<br />

environmental legislation; and an aerobic complementation may be mandatory.<br />

The ethanol end use<br />

Ethanol partial substitution for gasoline h<strong>el</strong>ps increasing energy security and reducing gasoline<br />

/ additives imports (economic impacts). Economic impacts are also seen in the r<strong>el</strong>ative costs of<br />

ethanol and the (expected) gasoline cost; in the economic <strong>de</strong>v<strong>el</strong>opment due to equipment and<br />

services suppliers for the new energy sector; and in the strengthening of the rural area, with<br />

job creation.<br />

Bio-ethanol (and co-generated <strong>el</strong>ectricity) show positive environmental impacts by reducing<br />

the use of natural resources (fossil fu<strong>el</strong>s) and the corresponding GHG emissions.<br />

Ethanol use in blends with gasoline (and also the use of ETBE) presents different atmospheric<br />

emissions (than those from gasoline). The possibility and consequences of leakage and<br />

contamination of groundwater must be consi<strong>de</strong>red.<br />

The main environmental impacts are summarized b<strong>el</strong>ow.<br />

The biomass and conversion processes proposed, for Mexico conditions (Chapter 2), present<br />

energy ratios (energy output / fossil energy inputs) varying from nearly one (corn: 1.3) to ten<br />

(sugar cane, with co-generation). Sweet sorghum ratio is ~4; wheat and sugar beets ratios are<br />

~2; and cassava is ~1. Impacts in fossil energy utilization are shown b<strong>el</strong>ow, for 10% blend of<br />

4

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