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

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PARALLEL SESSION 3A: LAND USE CHANGE 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 />

LC GHG balance<br />

(kg CO 2eq/kg soybean oil)<br />

1,2<br />

1,0<br />

0,8<br />

0,6<br />

0,4<br />

0,2<br />

0,0<br />

-0,2<br />

-0,4<br />

-0,6<br />

0,51<br />

0,91<br />

0,98<br />

Figure 2. LC GHG emissions of soybean oil (no LUC, no-tillage): different m<strong>et</strong>hods for handl<strong>in</strong>g coproducts.<br />

Fig. 3 presents soybean oil life-cycle GHG emissions (energy allocation) from soybean produced <strong>in</strong> 2<br />

climate regions <strong>in</strong> Brazil. The results for the alternative LUC scenarios are comparatively assessed. The contribution<br />

of each LC phase (LUC, cultivation, transport and oil extraction) is also shown. The results show a<br />

huge variation <strong>in</strong> GHG emissions: b<strong>et</strong>ween 0.9 kg CO2eq/kg (no LUC) and 12.9 kg CO2eq/kg (previous improved<br />

management savannah, tropical moist region). LUC dom<strong>in</strong>ates the results. GHG emissions due to<br />

LUC represent more than 69% <strong>in</strong> all scenarios, except for the scenarios where soybean is cultivated <strong>in</strong> previous<br />

severely degraded grassland <strong>in</strong> warm temperate region. The GHG emissions of soybean oil associated<br />

with cultivation, transport and oil extraction are also compared <strong>in</strong> Fig. 3. Concern<strong>in</strong>g the scenarios with no<br />

LUC, process contributions to the GHG balance are as follows: cultivation (3-44%), transport (3-44%) and<br />

oil extraction (1-14%).<br />

Figure 3. LC GHG emissions of soybean oil (energy allocation): LUC scenarios and phase contribution.<br />

4. Conclusions<br />

The ma<strong>in</strong> goal of this paper is to assess and discuss the implications of adopt<strong>in</strong>g different allocation<br />

m<strong>et</strong>hods (mass, energy and marked price based allocation) and different scenarios of system expansion on<br />

the LC GHG emissions of soybean oil. The sensitivity analysis conducted to illustrate the consequences of<br />

different multifunctionality approaches shows that results are very sensitive to the approach adopted. The<br />

1,12<br />

Mass Energy Economic<br />

1,05<br />

ISM: Imported soybean meal<br />

IS: Imported soybean<br />

-0,36<br />

M<strong>in</strong> Max Av ISM IS<br />

Allocation Substitution m<strong>et</strong>hod<br />

LC GHG balance<br />

(kg CO 2eq/kg soybean oil) Transport<br />

14<br />

12<br />

10<br />

8<br />

6<br />

4<br />

2<br />

0<br />

NT T NT T NT T NT T NT T NT T NT T NT T NT T NT T<br />

Managed forest Improved Moderatly degraded<br />

management savannah savannah<br />

Severely degraded<br />

savannah<br />

Managed forest Perennial crop<br />

(reduced-tillage)<br />

Improved Moderatly degraded<br />

management grassland grassland<br />

No LUC Tropical, moist (Brazil, Central-West) Warm temperate, moist (Brazil, South)<br />

0,51<br />

Oil extraction<br />

Cultivation<br />

LUC<br />

NT: No-tillage<br />

T: Tillage<br />

Severely degraded<br />

grassland<br />

265

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