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trends and future of sustainable development - TransEco

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Comparing with energy uses in Campania region <strong>and</strong> Campania agriculture, bioenergy frommarginal l<strong>and</strong>s only covers a small amount <strong>of</strong> the energy dem<strong>and</strong> <strong>and</strong> these results cannot besignificantly improved by increasing the cropping intensity (machinery, fertilizers).Concerning the economic assessment, the required investment consists <strong>of</strong> both direct <strong>and</strong> indirectlabor (services) <strong>and</strong> it does not include the cost <strong>of</strong> fuels used nor other costs for indirect fossil energysaved, because a fraction <strong>of</strong> the energy delivered is assumed to feedback the production process in orderto make it independent from fossil energy input (a pre-condition for process sustainability).Table 2.Energetic evaluation for low <strong>and</strong> high input B. carinata cropping systems. Data arecalculated for biodiesel production <strong>and</strong> heat generation by combustion <strong>of</strong> straw <strong>and</strong>cake meal, considering the total selected area (44,998 ha).Energy Invested forprocess (J/yr) (a)Usable EnergyDelivered (J/yr) (b)Net Energy Delivered(J/yr) (b-a)Ratio b/aLow Input 7.87E+14 1.74E+15 9.56E+14 2.21High Input 1.30E+15 2.33E+15 1.03E+15 1.79The total NED from Table 2 corresponds to 22,800 t <strong>of</strong> oil equivalent in the case <strong>of</strong> low intensitycropping <strong>and</strong> to 24,700 t <strong>of</strong> oil equivalent in the case <strong>of</strong> high intensity cropping (1 t oil equivalent =4.186E+10 J). Considering that the average oil cost was 61.25 €/barrel (0.45 €/kg in the year 2010,www.oil-price.net), it is possible to calculate the saving rate <strong>of</strong> economic investment in terms <strong>of</strong> fossilfuel not used. As shown in Table 3, the net economic balance is negative for both low <strong>and</strong> high inputcropping systems <strong>and</strong> the economic investment required is respectively 3.83 <strong>and</strong> 4.24 times higher thanthe economic savings associated to the oil not used thanks to the NED in the form <strong>of</strong> biodiesel <strong>and</strong> heat.Table 3.Economic evaluation for low <strong>and</strong> high input B. carinata cropping systems. Data arecalculated for biodiesel production <strong>and</strong> heat generation by combustion <strong>of</strong> straw <strong>and</strong>cake meal, considering the total selected area (44,998 ha).Economic investment(€/yr) (a)Saving rate <strong>of</strong>economic investment<strong>of</strong> produced energy(€/yr) (b)Net Economic ( €/yr)(b-a)Ratio a/bLow Input 3.97E+07 1.04E+07 -2.94E+07 3.83High Input 4.75E+07 1.12E+07 -3.63E+07 4.24The poor energetic <strong>and</strong> economic performance achieved within the previous case study is the startingpoint <strong>of</strong> the biorefinery approach. The worth <strong>of</strong> biorefinery processes relies in their ability to exploit alarger fraction <strong>of</strong> available substrate <strong>and</strong> generate higher value added products than just energy. Suchproducts seem to be potentially capable <strong>of</strong> providing higher income <strong>and</strong> energy replacement value(indirect energy savings from alternative fossil-based chemistry). The enhanced economic performance<strong>of</strong> a biorefinery compared to a bioenergy system was verified previously (Fahd et al., 2011, submitted)but it is not shown here: considering the total economic income from a biorefinery chain includingseveral chemical products that can be separated <strong>and</strong> sold to the market, the economic investmentneeded results to be lower (the ratio <strong>of</strong> gross income to costs is about 1.8:1). While cropping for50

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