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LCA Food 2012 in Saint Malo, France! - Manifestations et colloques ...

LCA Food 2012 in Saint Malo, France! - Manifestations et colloques ...

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PARALLEL SESSION 6B: FISHIERIES, SOIL, AND EMERGY METHODS 8 th Int. Conference on <strong>LCA</strong> <strong>in</strong> the<br />

Agri-<strong>Food</strong> Sector, 1-4 Oct <strong>2012</strong><br />

3. Results<br />

3.1 Characterisation factors<br />

Fig. 1 shows the regionalised CFs for (a) the resource-depl<strong>et</strong>ion impact pathway and (b) the ecosystemquality<br />

impact pathway. As stated previously, for resource depl<strong>et</strong>ion, larger CFs were for th<strong>in</strong>ner soils, and<br />

for ecosystem quality, larger CFs were for soils with higher biomass productivities.<br />

a<br />

Resource depl<strong>et</strong>ion [MJse g -1 b<br />

6 soil loss] 24 0 Ecosystem quality [decimal % NPP lost] 1<br />

Figure 1. Characterisation factors for (a) resource depl<strong>et</strong>ion and (b) ecosystem quality.<br />

3.2 Case study on food and energy crops<br />

At the LCI level, soil erosion of three of the crops grown <strong>in</strong> the evaluated rotations as well as of the unseeded<br />

fallow reference system are depicted <strong>in</strong> Fig. 2. Results are shown group<strong>in</strong>g the analysed plots on the<br />

ten ma<strong>in</strong> water-bas<strong>in</strong>s <strong>in</strong> Spa<strong>in</strong> and on the country scale. It can be seen how soil loss varies as a function of<br />

location for the same crop, hence the importance of <strong>in</strong>clud<strong>in</strong>g geospatial <strong>in</strong>formation as accurately as possible<br />

<strong>in</strong> the <strong>in</strong>ventory step.<br />

Figure 2. Soil erosion (t ha -1 y -1 ) on the 120 studied plots grouped on the water-bas<strong>in</strong> and arithm<strong>et</strong>ic average<br />

±standard deviation on the country level. The reported soil losses were calculated for a whole year (crop +<br />

crop residues + rough fallow before next seed<strong>in</strong>g).<br />

Results at the LCIA stage for the five crop rotations evaluated are shown <strong>in</strong> table 1. As <strong>in</strong> the <strong>in</strong>ventory,<br />

damage to resources and to ecosystem quality varies greatly b<strong>et</strong>ween water-bas<strong>in</strong>s for one and the same crop<br />

rotation, with a coefficient of variation higher than 60% <strong>in</strong> almost all cases (except for the poplar rotation,<br />

CV is 35%). Accord<strong>in</strong>g to the presented results, the most appropriate comb<strong>in</strong>ation of rotation and location<br />

was the poplar energy-crop short rotation forestry grown <strong>in</strong> the North of the country (Duero water bas<strong>in</strong> <strong>in</strong><br />

table 1). Other water bas<strong>in</strong>s, such as the Guadiana (Central Spa<strong>in</strong>, results not shown here) scored very close<br />

to the Duero water bas<strong>in</strong>.<br />

525

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