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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 />

Primary data for the recipe used, packag<strong>in</strong>g composition, process<strong>in</strong>g energy consumption and transport<br />

was primarily obta<strong>in</strong>ed from the Bilan Carbone report or, where it was miss<strong>in</strong>g, collected by Jean Hénaff and<br />

its suppliers.<br />

For GHG emission data, the Carbonostics (<strong>2012</strong>) onl<strong>in</strong>e food <strong>LCA</strong> application was used. Carbonostics is<br />

a lifecycle assessment tool designed to p<strong>in</strong>po<strong>in</strong>t the hotspots of any food product or menu along three key<br />

criteria: cost + carbon + nutrition. Carbonostics' built-<strong>in</strong> database <strong>in</strong>cludes GHG emission factors to assess all<br />

the life cycle stages, as well as nutritional <strong>in</strong>formation on <strong>in</strong>gredients. Us<strong>in</strong>g Carbonostics enabled the <strong>in</strong>tegration<br />

of GHG and six nutritional <strong>in</strong>dicators, namely calories, prote<strong>in</strong>, lipids, carbohydrates, sodium and<br />

sugar - all <strong>in</strong> the same analysis.<br />

Local data was also collected for the life cycle stages with higher <strong>in</strong>fluence <strong>in</strong> f<strong>in</strong>al results, namely the agricultural<br />

production phase. Bass<strong>et</strong>-Mens and van der Werf (2005) provide GHG emissions factors at the<br />

farm outl<strong>et</strong> for pigs reared <strong>in</strong> Brittany <strong>in</strong> three agricultural circuits: conventional (2.30 kg CO2e/kg live pig),<br />

Label Rouge (3.46 kg CO2e/kg live pig) and organic (3.97 kg CO2e/kg live pig). We then used local study<br />

(Chevillon <strong>et</strong> al., 2011) to allocate GHG emissions for rear<strong>in</strong>g pigs amongst the different parts of the carcass<br />

(liver, throat, breast, sk<strong>in</strong>, <strong>et</strong>c.). We used mass allocation, <strong>in</strong> l<strong>in</strong>e with the BPX 30-323 guidel<strong>in</strong>es (AFNOR-<br />

ADEME, 2009), the reference frame for the experimentation on the environmental display of consumer<br />

products conducted <strong>in</strong> <strong>France</strong> from mid-2011 to the end of <strong>2012</strong>.<br />

Amongst the hypotheses used, the follow<strong>in</strong>g should be noted:<br />

The emission factors for Bleu-Blanc-Cœur (BBC) pork are the same as those for conventional meat.<br />

Indeed, the specific feed<strong>in</strong>g phase is of relatively short duration (2 months) and the proportion of<br />

high-Omega 3 plants <strong>in</strong> the food ration is low, circa 2%.<br />

Emissions ascribed to secondary and tertiary packag<strong>in</strong>g are negligible when compared to those of the<br />

product. They were thus not <strong>in</strong>cluded <strong>in</strong> the study.<br />

F<strong>in</strong>ally, a sensitivity analysis (study of the impact of modulat<strong>in</strong>g different <strong>in</strong>put variables on end result<br />

variation) was conducted and the ma<strong>in</strong> results are presented <strong>in</strong> the follow<strong>in</strong>g section. As part of the sensitivity<br />

analysis we also changed the procedure for allocat<strong>in</strong>g emissions to pork parts from mass to economic.<br />

3. Results<br />

3.1. GHG emissions for each pâté l<strong>in</strong>e<br />

An <strong>in</strong>itial observation is that the carbon footpr<strong>in</strong>t of pâté products is b<strong>et</strong>ween 160 g and 260 g CO2e for<br />

78 g (Figure 2), i.e. b<strong>et</strong>ween 200 and 330 g CO2e for 100 g, which is below available <strong>in</strong>ternational benchmarks.<br />

This can be attributed to the fact that the GHG emissions for pork production <strong>in</strong> Bass<strong>et</strong>-Mens and van<br />

der Werf (2005) were lower than the equivalent emission factors for other countries <strong>in</strong> the Carbonostics<br />

(<strong>2012</strong>) database. Moreover, the organic country-style pâté has the highest carbon footpr<strong>in</strong>t, while Label<br />

Rouge and conventional/Bleu-Blanc-Cœur pâtés have a comparable footpr<strong>in</strong>t. This result is expla<strong>in</strong>ed not<br />

only because organic pork production <strong>in</strong> Br<strong>et</strong>agne has higher emissions (Bass<strong>et</strong>-Mens and van der Werf,<br />

2005), but also because the proportions of the different pork cuts <strong>in</strong> the recipe vary.<br />

An analysis of results per life-cycle phase for GHG shows that raw materials are responsible for over 80%<br />

of the total impact. Pork is the ma<strong>in</strong> hotspot amongst raw materials. The contribution of packag<strong>in</strong>g to emissions<br />

reveals that glass has the greatest impact, followed by t<strong>in</strong> plate and alum<strong>in</strong>ium. Although packag<strong>in</strong>g<br />

emissions are not comparable to pork emissions, the difference b<strong>et</strong>ween packag<strong>in</strong>g materials is sufficient to<br />

differentiate b<strong>et</strong>ween pâtés. Energy spent for process<strong>in</strong>g, the only life cycle step that Hénaff controls directly,<br />

lag far beh<strong>in</strong>d with only 10% of the total impact. The transport-related impact appears negligible.<br />

These percentages are consistent with the Bilan Carbone f<strong>in</strong>d<strong>in</strong>gs for the bundle of Hénaff products.<br />

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