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APPLYING THERMOECONOMICS TO THE ANALYSIS OF ... - circe

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Proceedings of ECOS 2009 22 nd International Conference on Efficiency, Cost, Optimization<br />

Copyright © 2009 by ABCM Simulation and Environmental Impact of Energy Systems<br />

August 31 – September 3, 2009, Foz do Iguaçu, Paraná, Brazil<br />

Table 3. Production costs due to fossil fuel, recycling 10% biomass<br />

Fossil Fuels<br />

Process P c (GJ/GJ) C P (GJ)<br />

1 0 0<br />

2 0.08 5<br />

3 10.15 19.29<br />

4 4.45 13.79<br />

5 9.19 33.08<br />

Total 33.50<br />

Table 3 shows the new costs due to fossil fuels. As it can be seen, recycling 10% of crop residues reduces the fuel<br />

consumption by 2 GJ, or what is the same, the ratio between the fuel required and the energy consumption is reduced by<br />

5.25%.<br />

3.3. Process efficiency impact<br />

In this scenario we will assume that the efficiency of each single process is increased by 10% without modifying<br />

the final demand and the system structure (junction ratios). Eqn (7) is used for this purpose, with Δ κi<br />

= 0.1.<br />

The impact<br />

in resources consumption is decomposed into the part coming from biomass and from fossil fuels (see table 4).<br />

Table 4. Impact of resources consumption with a 10% increase on the process efficiency<br />

Process 0 C Δ Fossil Fuels (GJ) 0 C Δ Biomass (GJ) 0 C<br />

Δ Total (GJ)<br />

1 0.000 0.00% 6.000 7.50% 6.000 5.19%<br />

2 0.627 1.77% 7.881 9.85% 8.507 7.37%<br />

3 0.060 0.17% 0.216 0.27% 0.276 0.24%<br />

4 0.254 0.71% 0.094 0.12% 0.347 0.30%<br />

5 2.514 7.08% 5.808 7.26% 8.322 7.21%<br />

Eqn. (10) is used to compute the fuel impact of each efficiency simulation. The cost of fuel is evaluated for the<br />

simulated scenario and the production corresponds to the base case.<br />

i<br />

0<br />

Δ C0 = cF, iΔ κi<br />

Pi<br />

(10)<br />

Note that improving the efficiency of the last stage of the food chain has an important impact on the fossil fuel<br />

consumption. On the other hand improving the efficiency of the first stages of the process has an impact only on the<br />

reduction of biomass requirements. An important conclusion can be thus drawn: for improving the energy efficiency of<br />

the food chain, major efforts should be focused on the last production stages.<br />

3.4. Change in the food diet<br />

The last scenario analyzes a change in the diet. As it has been shown, the production of animal food requires much<br />

more resources than vegetable food. In the base model a person consumes 62% of vegetables and 38% of animal food.<br />

What would happen if we reduced the consumption of meat by 10% maintaining the final demand of energy per person<br />

in 3.6 GJ?<br />

To simulate this scenario we must change the junction ratios q 35 = 0,38 → 0,318 and q 45 = 0.62 → 0.682 . The rest<br />

of the parameters are kept constant. Eqn. (7) can be used to compute the resources consumption impact for this<br />

simulation as:<br />

Δ C0 = ( cP,3Δ q35 + cP, 4Δ q45) F5<br />

(11)<br />

Using Eqn. (11) with the unit production cost due to fossil fuel and biomass, the change implies a saving of 10.74<br />

GJ (13.42 %) of biomass resources, and 2.04 GJ (5.73 %) of fossil fuels.<br />

On the other hand, if we would reduce the energy demand per person by 10%, the associated saving would be equal<br />

to 3.49 GJ (9.84%) of fossil fuels and 7.33 GJ (9.16 %) of biomass, which could be computed using the expression:<br />

Δ C0 = cP, 5Δ E50<br />

(12)<br />

In these simulations we have differentiated between fossil fuel and biomass resources. The first one has an explicit<br />

cost: it has a market price, an environmental impact, externality costs, etc. The second one is a different case, since<br />

biomass energy is provided by the sun which is “free”. Nevertheless, the solar energy provided to biomass is<br />

proportional to the harvest area. Furthermore in this model we are considering the energy consumed per habitant,<br />

891

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