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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 2A: LAND USE 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 />

average LUC <strong>in</strong> the whole country rather than a specific area (e.g. plantation) was assessed, there was no<br />

need for allocat<strong>in</strong>g it to the first 20 years of land use (as suggested <strong>in</strong> BSI, 2008; Koellner <strong>et</strong> al., <strong>2012</strong>a;<br />

Flynn <strong>et</strong> al., <strong>2012</strong>). In order to smooth out short-term fluctuations <strong>in</strong> land use, 5-year averages were used.<br />

FAOSTAT (2011) data were used to perform this analysis.<br />

Figure 1. Decision tree to d<strong>et</strong>erm<strong>in</strong>e the existence and magnitude of land use change for the studied crops <strong>in</strong><br />

the sourc<strong>in</strong>g countries (Milà i Canals <strong>et</strong> al., <strong>2012</strong>).<br />

This approach is consistent with the recommended approach <strong>in</strong> the PAS 2050 (BSI, 2011) where the<br />

country of production is known but the previous land use is not known (section 5.6.2, po<strong>in</strong>t b). BSI (2011)<br />

suggest exclud<strong>in</strong>g <strong>in</strong>direct land use changes (ILUC); however, it must be noted that this approach actually<br />

does <strong>in</strong>clude ILUC occurr<strong>in</strong>g with<strong>in</strong> the produc<strong>in</strong>g country. ILUC caused by displacement of crops to be<br />

grown <strong>in</strong> other countries, on the other hand, is not <strong>in</strong>cluded. This is a limitation of an attributional-focused<br />

approach; see e.g. Kløverpris <strong>et</strong> al., (2007) or Brandão (<strong>2012</strong>) for approaches to deal with ILUC.<br />

3. Results<br />

Figures 2a-g provide the contributions per functional unit of the different <strong>in</strong>gredients and life cycle stages<br />

of the two margar<strong>in</strong>es for the seven land use-related impact categories. For most impact categories (except<br />

FWRP, not shown here) the UK margar<strong>in</strong>e with a 38% fat content shows larger total impacts than the German<br />

margar<strong>in</strong>e with the higher 70% fat content. This is because the UK margar<strong>in</strong>e conta<strong>in</strong>s a higher proportion<br />

of oils from low-yield<strong>in</strong>g crops such as sunflower (yield: 1.5 t/ha). Sunflower grow<strong>in</strong>g dom<strong>in</strong>ates the<br />

impact results for the UK margar<strong>in</strong>e (where it represents about 25% of the <strong>in</strong>gredients) and it also has a significant<br />

contribution towards the impacts of the German margar<strong>in</strong>e <strong>in</strong> which it is only 3.5% of the <strong>in</strong>gredients.<br />

In comparison the impacts for rapeseed are generally lower even though it represents 36% of the German<br />

margar<strong>in</strong>e. This can be expla<strong>in</strong>ed by the higher yield for rapeseed (4.2 t/ha) compared to sunflower.<br />

Palm oil, which makes up ca. 26% of the German recipe, has a relatively low contribution to all the land use<br />

impact categories, even though significant LUC of 435 m 2 / ha*year of tropical ecosystems with high biodiversity<br />

and carbon values was attributed to this crop. This can be expla<strong>in</strong>ed by the lower impacts associated<br />

to permanent agricultural systems such as plantations for most impact categories relative to annual crops.<br />

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