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

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PLENARY SESSION 1: FOOD 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 />

3. Results<br />

For all <strong>in</strong>dicators the results show strong variation b<strong>et</strong>ween the genders. Even if the physiologically different<br />

consumption amounts among men and women are levelled out on the basis of 2,000 kcal person -1 day -<br />

1 , men still show a higher impact <strong>in</strong> terms of GWP (CO2e +8%), ammonia emissions (+14%), land use<br />

(+11%), P use (+10%) and CED (+2%). In contrast, women demonstrate a higher water demand (+18%;<br />

Table 4 and Fig. 1). These differences are primarily caused by a higher share of meat products and butter <strong>in</strong><br />

the usual di<strong>et</strong> of men as well as more fruit, veg<strong>et</strong>ables and nuts & seeds <strong>in</strong> the typical di<strong>et</strong> of women.<br />

112<br />

Low-fat milk products (milk,<br />

yoghurt)<br />

Vegan milk products (<strong>in</strong><br />

whole milk equivalents)<br />

Veg<strong>et</strong>al oils, margar<strong>in</strong>e<br />

High-fat milk products<br />

(cheese, cream)<br />

Potato products<br />

Modelled as<br />

Meat products<br />

Fish products<br />

Nuts & seeds<br />

Egg products<br />

Veg<strong>et</strong>ables<br />

Legumes<br />

Gra<strong>in</strong>s<br />

Butter<br />

Sugar<br />

Fruits<br />

Data concern<strong>in</strong>g food consumption from BML (1991); data concern<strong>in</strong>g food <strong>in</strong>take from Kübler<br />

<strong>et</strong> al. (1995)<br />

0.77 0.89 0.89 0.73 0.48 0.69 0.52 0.89 0.68 0.68 0.48 0.15 0.42 0.57 0.29<br />

Conversion factor<br />

1985-89 = con-<br />

sumption /<br />

<strong>in</strong>take<br />

Data concern<strong>in</strong>g food consumption from BMELV (2009); data concern<strong>in</strong>g food <strong>in</strong>take from<br />

MRI (2008)<br />

0.71 0.73 0.73 0.73 0.46 0.54 0.61 0.96 0.85 0.85 1.04 0.33 0.41 0.28 0.56<br />

Conversion factor<br />

2006<br />

Data concern<strong>in</strong>g domestic agriculture & upstream processes from Schmidt & Osterburg<br />

(2011) and Brentrup & Pallière (2008); data concern<strong>in</strong>g fish from Nielsen <strong>et</strong> al. (2003); data<br />

concer<strong>in</strong>g fruits partly from Sanjuan <strong>et</strong> al. (2005); data concern<strong>in</strong>g dLUC, LU from Leip <strong>et</strong> al.<br />

(2010); data concern<strong>in</strong>g process<strong>in</strong>g from BMELV (2009); data concern<strong>in</strong>g trade/transport from<br />

DIW (2008) and data concern<strong>in</strong>g packag<strong>in</strong>g from Institute of Applied Ecology (2010). If no<br />

data for imported products were available, domestic conditions were assumed.<br />

kg / kg 19.7 10.0 2.7 0.7 9.3 3.1 2.4 1.5 0.8 1.1 0.8 0.8 0.5 3.4 1.9<br />

CO₂ₑ-emissions<br />

Data concern<strong>in</strong>g domestic agriculture from Schmidt & Osterburg (2011); data concern<strong>in</strong>g fish<br />

from Nielsen <strong>et</strong> al. (2003); data concern<strong>in</strong>g process<strong>in</strong>g from BMELV (2009); data concern<strong>in</strong>g<br />

trade/transport from DIW (2008) and data concern<strong>in</strong>g packag<strong>in</strong>g from Institute of Applied<br />

Ecology (2010). If no data for imported products were available, domestic conditions were assumed.<br />

g / kg 82.5 39.4 9.7 0.2 39.6 19.7 0.2 1.9 0.7 0.6 0.6 0.6 0.3 3.3 1.5<br />

NH₃-emissions<br />

Data concern<strong>in</strong>g domestic agriculture from Schmidt & Osterburg (2011); data concern<strong>in</strong>g<br />

packag<strong>in</strong>g from Institute of Applied Ecology (2010). Data for imported products from FAO<br />

Stat. (<strong>2012</strong>).<br />

Land use m² / kg 20.7 9.9 2.4 0.7 11.0 3.8 0.2 1.8 0.5 2.1 0.9 2.9 0.3 4.1 1.2<br />

Data concern<strong>in</strong>g domestic agriculture from Schmidt & Osterburg (2011) and Mekonnen &<br />

Hoekstra (2010); data concern<strong>in</strong>g process<strong>in</strong>g from BLE (2007) and data concern<strong>in</strong>g packag<strong>in</strong>g<br />

from Institute of Applied Ecology (2010). Data for imported products from Mekonnen &<br />

Hoekstra (2010).<br />

l / kg 86.0 44.3 15.6 6.4 36.7 8.8 14.7 5.2 27.4 8.8 87.6 1425.3 5.7 15.7 9.5<br />

Water use (blue)<br />

Data concern<strong>in</strong>g domestic agriculture from Schmidt & Osterburg (2011). P use dur<strong>in</strong>g process<strong>in</strong>g<br />

was not exam<strong>in</strong>ed.<br />

g / kg 70.0 33.5 8.2 1.3 33.0 10.3 4.4 5.3 2.7 3.7 1.4 1.4 0.9 9.7 3.6<br />

Phosphorous<br />

use<br />

Data concern<strong>in</strong>g domestic agriculture & upstream processes from Schmidt & Osterburg<br />

(2011) and Brentrup & Pallière (2008); data concern<strong>in</strong>g fish from Nielsen <strong>et</strong> al. (2003); data<br />

concer<strong>in</strong>g fruits partly from Sanjuan <strong>et</strong> al. (2005); data concern<strong>in</strong>g process<strong>in</strong>g from BMELV<br />

(2009); data concern<strong>in</strong>g trade/transport from DIW (2008) and data concern<strong>in</strong>g packag<strong>in</strong>g from<br />

Institute of Applied Ecology (2010). If no data for imported products were available, domestic<br />

conditions were assumed.<br />

MJ / kg 52.7 33.0 12.5 7.4 44.5 20.2 13.1 11.2 10.2 7.7 11.1 11.1 5.0 19.4 18.0<br />

Cumulative<br />

energy demand<br />

(CED)

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