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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 4A: CARBON 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 />

Greenhouse gas emissions<br />

(g CO2 eq. kg-1 crop DM)<br />

500<br />

400<br />

300<br />

200<br />

100<br />

0<br />

Mulch<strong>in</strong>g No <strong>in</strong>put Slurry Conventional<br />

Figure 3. Carbon footpr<strong>in</strong>ts per kg sales crop DM at farm gate based on the full crop rotations 2006-8. The<br />

values are the means over the three years ± S.E.<br />

The analysis of the <strong>in</strong>dividual crops provided a specific carbon footpr<strong>in</strong>t value of e.g. spr<strong>in</strong>g barley grown<br />

<strong>in</strong> the different crop rotations (Figure 4). Figure 4 shows that the carbon footpr<strong>in</strong>t values for e.g. spr<strong>in</strong>g barley<br />

grown <strong>in</strong> the ‘Mulch<strong>in</strong>g’ rotation was affected by the soil carbon sequestration and the N2O emissions<br />

caused by the green manure crop compared to the ‘Slurry’ or ‘Conventional’ rotations. These f<strong>in</strong>d<strong>in</strong>gs show<br />

that the contributions caused by the green manure crop to the carbon footpr<strong>in</strong>t of the organic crops are considerable.<br />

Mulch<strong>in</strong>g<br />

No <strong>in</strong>put<br />

Slurry<br />

Conventional<br />

-400 -200 0 200 400 600<br />

SPRING BARLEY<br />

2006-2008<br />

Manure <strong>in</strong>put<br />

N2O, ma<strong>in</strong> crop<br />

N2O, grass-clover<br />

N2O, catch crop<br />

Diesel and mach<strong>in</strong>ery, ma<strong>in</strong> crop<br />

Diesel and mach<strong>in</strong>ery, grass clover<br />

Soil C change<br />

Greenhouse gas emissions per kg spr<strong>in</strong>g barley<br />

(g CO2 eq. kg<br />

Figure 4. Carbon footpr<strong>in</strong>ts of spr<strong>in</strong>g barley at farm gate <strong>in</strong> the different crop rotations 2006-8. The values<br />

are the means over the three locations and three years (2006-8).<br />

-1 spr<strong>in</strong>g barley)<br />

4. Discussion<br />

When calculat<strong>in</strong>g the carbon footpr<strong>in</strong>t of crops from crop rotations where green manure crops or catch<br />

crops are <strong>in</strong>cluded, there is a need to <strong>in</strong>clude the environmental burdens and benefits from the green manure<br />

or catch crops and thus <strong>in</strong>clude the full crop rotation <strong>in</strong> the assessment.<br />

One solution, as suggested here, is to assess the full crop rotation as a ‘black box’ based on kg sales crop<br />

DM from the different crops. The analysis over the whole rotation can be used to judge on different rotation<br />

designs. The evaluation could be based on kg DM, as suggested here or be related to the functions of agriculture<br />

as discussed by Nemecek <strong>et</strong> al., (2011). Another option is to use a functional unit that reflects the di<strong>et</strong>ary<br />

needs by humans as discussed by Smedman <strong>et</strong> al., (2010).<br />

However, there is a need for carbon footpr<strong>in</strong>t values for the specific crops. Furthermore, the full crop rotation<br />

implies several crop specific <strong>in</strong>puts and several outputs i.e. different sales crops from the rotation,<br />

371

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