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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 />

sary directly or <strong>in</strong>directly to obta<strong>in</strong> a certa<strong>in</strong> good or service.” (Odum, 1996). In eMergy, the term Unit<br />

Emergy Value (UEV) (i.e. usually named trasformity,<strong>in</strong> seJ/J, or specific eMergy, <strong>in</strong> seJ/g), def<strong>in</strong>es the<br />

eMergy necessary to obta<strong>in</strong> one unit of product or service (Odum, 1996), represent<strong>in</strong>g the coefficient through<br />

which different types of energy are converted to solar energy. Every biotic and abiotic resource <strong>in</strong> the geobiosphere<br />

can be evaluated <strong>in</strong> eMergy terms and can be accounted for with<strong>in</strong> the system’s output. Emergy<br />

can be considered as an “energy memory”, i.e. a memory of all solar energy necessary to support a def<strong>in</strong>ed<br />

system, consider<strong>in</strong>g the environmental work required previously for the production. In eMergy every life<br />

cycle <strong>in</strong>put to the system is multiplied by the correspond<strong>in</strong>g UEV and the result<strong>in</strong>g eMergy flows are added<br />

to obta<strong>in</strong> the total eMergy flow of the output. This last value is divided by the product of the considered<br />

process (i.e. annual quantity of olive oil and w<strong>in</strong>e per hectare here) to obta<strong>in</strong> its UEV, which <strong>in</strong> the classical<br />

eMergy m<strong>et</strong>hod is considered as an environmental performance’s <strong>in</strong>dex for comparison of products: the<br />

higher the UEV, the higher is the equivalent solar energy demand per unit of product and thus lower is the<br />

life-cycle resource consumption’s efficiency to generate that product. This study refers to the 9.26E+24 sej/J<br />

basel<strong>in</strong>e (Campbell, 2000).<br />

2.3 Case studies: w<strong>in</strong>e and olive oil productions<br />

The selected farms are all located <strong>in</strong> the centre of Tuscany. The organic w<strong>in</strong>e farm (hereafter OW) had a<br />

v<strong>in</strong>eyard of 10 ha and an average production of 3500L/ha per year (Chianti Colli Senesi w<strong>in</strong>e). The conventional<br />

w<strong>in</strong>ery (hereafter CW) presented a semi-<strong>in</strong>dustrial management that covered an area of 120 ha and<br />

produced about 2200 L/ha of w<strong>in</strong>e per year (Nobile di Montepulciano CGOD w<strong>in</strong>e). CW presented a lower<br />

yield <strong>in</strong> w<strong>in</strong>e production because of a rigorous selection of grapes; <strong>in</strong> fact, <strong>in</strong> order to improve the quality of<br />

the f<strong>in</strong>al product, only half of all the grapes harvested by CW are generally suitable for w<strong>in</strong>e production. The<br />

two farms were selected because of the same price of the w<strong>in</strong>e bottle at the mark<strong>et</strong>. For both farms the production<br />

cha<strong>in</strong> can be divided <strong>in</strong> three phases: plant<strong>in</strong>g and production (Phase 1), w<strong>in</strong>e-mak<strong>in</strong>g and storage<br />

(Phase 2) and bottl<strong>in</strong>g (Phase 3). Concern<strong>in</strong>g olive oil production, the organic farm (hereafter OO) extended<br />

for 4 ha, while the annual average yield of olives was 1500 kg/ha with annual production of 250 kg of oil.<br />

With regard to the conventional farm (hereafter CO), olive cultivation extended for 20 ha, whereas the conduction<br />

was directed towards an <strong>in</strong>tensive production management, characterised by hard mechanisation and<br />

chemicals use. The annual mean production was 3820 kg/ha of olives, which are processed <strong>in</strong> 483 kg of oil<br />

per year (Protected Geographical Indication, PGI, quality). Similarly to w<strong>in</strong>e, these two farms were also selected<br />

because of the same price of one olive oil bottle at mark<strong>et</strong>. However, the olive oil production was divided<br />

<strong>in</strong>to two phases: agricultural phase (Phase 1) and oil mill phase, <strong>in</strong>clud<strong>in</strong>g bottl<strong>in</strong>g phase (Phase 2).<br />

Inventory data (the same used for <strong>LCA</strong> and EME) for both w<strong>in</strong>e and olive oil productions are showed <strong>in</strong> the<br />

third and fourth columns, respectively, of the correspond<strong>in</strong>g eMergy tables (see Tables 2 and 4).<br />

3. Results<br />

3.1. W<strong>in</strong>e <strong>LCA</strong> results<br />

The comparison of the impacts characterisation of the two w<strong>in</strong>e life cycles (Table 1) shows mean<strong>in</strong>gful<br />

differences, highlight<strong>in</strong>g that major values are connected to CW. The major departures were found for the<br />

packag<strong>in</strong>g phase for both managements (average 50% for the 4 impact categories), with the higher values<br />

recorded by the CW. Concern<strong>in</strong>g phase 1 (plant<strong>in</strong>g and production) and 2 (storage), the higher values are<br />

related to OW.<br />

Table 1. LCIA of conventional (CW) and organic (OW) w<strong>in</strong>e productions. Data reported for functional unit<br />

(1 L bottled w<strong>in</strong>e).<br />

Impact category unit conventional w<strong>in</strong>e (CW) organic w<strong>in</strong>e (OW)<br />

AP kg SO2 eq. 6,00E-03 4,00E-03<br />

EP kg PO4 eq. 9,80E-04 6,40E-04<br />

GWP100 kg CO2 eq. 7,30E-01 4,80E-01<br />

POP kg C2H4 eq. 2,40E-04 1,50E-04<br />

535

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