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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 1A: WATER FOOTPRINT 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 />

Table 4. Water Footpr<strong>in</strong>t of the 330g organic Strawberry jam<br />

Water Footpr<strong>in</strong>t account<strong>in</strong>g (l/functional unit) Water Footpr<strong>in</strong>t (l/functional unit)<br />

Primary Packag<strong>in</strong>g 7.0 1.1<br />

Transport and Secondary packag<strong>in</strong>g 20.8 6.3<br />

Production 9.0 3.0<br />

Farm<strong>in</strong>g 200.5 78.0<br />

Total 237.3 88.4<br />

4. Discussion<br />

The water footpr<strong>in</strong>t account<strong>in</strong>g was conducted to d<strong>et</strong>erm<strong>in</strong>e the quantity of water used to grow organic<br />

and non-organic strawberries <strong>in</strong> a site <strong>in</strong> Bulgaria. In this study the organic farm<strong>in</strong>g m<strong>et</strong>hod resulted to be<br />

more water <strong>in</strong>tensive then the non-organic one. This result strongly depends on the different yield of the two<br />

farm<strong>in</strong>g m<strong>et</strong>hod <strong>in</strong> this specific production site (Table 2). Other studies confirm the importance of this value<br />

when d<strong>et</strong>erm<strong>in</strong><strong>in</strong>g the environmental performances of agricultural products (Erc<strong>in</strong> <strong>et</strong> al., <strong>2012</strong>; Bleng<strong>in</strong>i and<br />

Busto, 2009). The values of the blue and green water footpr<strong>in</strong>t of the two farm<strong>in</strong>g m<strong>et</strong>hods resulted to be<br />

very similar. These results depend on the quantity of water used for irrigation and the effective precipitation.<br />

Grey water of non-organic farm<strong>in</strong>g is higher because chemicals fertilisers and pesticides (+93.75%) are used.<br />

This value do not consider environmental impacts but it is d<strong>et</strong>erm<strong>in</strong>ed through a water dilution approach<br />

(Jeswani and Azapagic, 2011)<br />

The product water footpr<strong>in</strong>t of a 330g strawberry jam was then quantified. Fig.2 represents the contribution<br />

of macro-processes to the overall Water Footpr<strong>in</strong>t. The farm<strong>in</strong>g processes resulted to be responsible for<br />

the majority of the product water footpr<strong>in</strong>t (84.49%) then follows transport and secondary packag<strong>in</strong>g, production<br />

and primary packag<strong>in</strong>g. The value of the transport and secondary packag<strong>in</strong>g depends on the use of<br />

cardboard and wood to pack the f<strong>in</strong>al product. Figure 3 represent the contribution of different processes after<br />

characterisation us<strong>in</strong>g WSI (Pfister <strong>et</strong> al., 2009). Changes <strong>in</strong> contribution depend on the% of blue water of<br />

the different materials/processes considered. Even <strong>in</strong> this case farm<strong>in</strong>g is still responsible for the majority of<br />

the water used. Other processes account for over the 11% of the product overall water footpr<strong>in</strong>t.<br />

48<br />

Figure 2. Contribution of processes to the product Water Footpr<strong>in</strong>t account<strong>in</strong>g<br />

Figure 3. Contribution of processes to the product Water Footpr<strong>in</strong>t after characterisation with WSI

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