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

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PARALLEL SESSION 4B: DIET 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 />

4. Discussion<br />

The number of studies <strong>in</strong>cluded <strong>in</strong> our environmental analysis was limited. Besides, two of the three studies<br />

were from the same author. We found, however, that meals are not a good basis for comparison of the<br />

environmental impact of human di<strong>et</strong>s, as meals are not representative for daily consumption. Because meals<br />

conta<strong>in</strong> a limited number of food products, the amount of quantified nutrients <strong>in</strong> meals is also more sensitive<br />

to product choice compared to the quantified amount of nutrients <strong>in</strong> daily or yearly di<strong>et</strong>s.<br />

The prote<strong>in</strong> quality of a food product can be evaluated us<strong>in</strong>g the Prote<strong>in</strong> digestibility-corrected am<strong>in</strong>o acid<br />

score (PDCAAS) (Hughes <strong>et</strong> al., 2011). Because questions were raised concern<strong>in</strong>g the usability of the<br />

PDCAAS m<strong>et</strong>hod for assess<strong>in</strong>g prote<strong>in</strong> quality at a di<strong>et</strong> level (FAO/WHO, 1991; Schaafsma, 2000), we did<br />

not account for differences <strong>in</strong> prote<strong>in</strong> quality b<strong>et</strong>ween plant and animal based products.<br />

5. Conclusion<br />

Current comparisons of the global warm<strong>in</strong>g potential (GWP) of human di<strong>et</strong>s show that di<strong>et</strong>s that have<br />

higher levels of animal-source food products have higher GWP compared to di<strong>et</strong>s that have lower levels of<br />

animal-source food products. However, these comparisons do not account for differences <strong>in</strong> the nutritional<br />

quality of these di<strong>et</strong>s. The environmental impact of these di<strong>et</strong>s is expressed relative to the functional unit<br />

(FU) ‘day’. In this review, we computed the nutritional quality of di<strong>et</strong>s and evaluated the effect of account<strong>in</strong>g<br />

for nutritional quality when compar<strong>in</strong>g the environmental impacts of di<strong>et</strong>s that vary <strong>in</strong> their amount of animal-source<br />

food products.<br />

We concluded that di<strong>et</strong>s with higher levels of animal-source food products have higher (excess) contents<br />

of prote<strong>in</strong> and generally lower composite nutritional quality compared to di<strong>et</strong>s that are lower <strong>in</strong> animalsource<br />

food products.<br />

We evaluated the effect of us<strong>in</strong>g the FUs ‘prote<strong>in</strong> <strong>in</strong>take’ and ‘composite nutritional quality’. When we<br />

expressed GWP with respect to grams of prote<strong>in</strong>, we found that GWP was lower for di<strong>et</strong>s that had higher<br />

levels of animal-source food products. This lower GWP per gram of prote<strong>in</strong> <strong>in</strong> di<strong>et</strong>s with higher levels of<br />

animal-source food products was due to the higher (excess) <strong>in</strong>take levels of total prote<strong>in</strong> <strong>in</strong> these di<strong>et</strong>s. To<br />

avoid credit for overconsumption, we capped the prote<strong>in</strong> <strong>in</strong>take levels at 100% of the Daily Recommended<br />

Value and found that GWP per unit ‘prote<strong>in</strong> capped’ was <strong>in</strong> fact higher for di<strong>et</strong>s that had higher levels of<br />

animal-source food products. When we expressed GWP <strong>in</strong> terms of the composite nutritional quality, i.e.<br />

us<strong>in</strong>g ‘NRD9.3’ as FU, we found that GWP per unit NRD9.3 was higher for di<strong>et</strong>s that had higher levels of<br />

animal-source food products.<br />

Overall, the regression coefficient for the FU ‘day’ was significantly higher compared to the regression<br />

coefficient for the FU ‘prote<strong>in</strong> uncapped’, and was significantly lower compared to the regression coefficient<br />

for the FU ‘NRD9.3’. Not credit<strong>in</strong>g for overconsumption of prote<strong>in</strong> and account<strong>in</strong>g for overall nutritional<br />

quality thus gives a stronger contrast <strong>in</strong> the GWP b<strong>et</strong>ween di<strong>et</strong>s that vary <strong>in</strong> their amount of animal-source<br />

food products.<br />

6. References<br />

Carlsson-Kanyama, A., 1998. Climate change and di<strong>et</strong>ary choices - how can emissions of greenhouse gases from food consumption<br />

be reduced? <strong>Food</strong> Policy 23, 277-293.<br />

Carlsson-Kanyama, A., Ekstrom, M.P., Shanahan, H., 2003. <strong>Food</strong> and life cycle energy <strong>in</strong>puts: consequences of di<strong>et</strong> and ways to<br />

<strong>in</strong>crease efficiency. Ecological Economics 44, 293-307.<br />

Carlsson-Kanyama, A., Gonzalez, A.D., 2009. Potential contributions of food consumption patterns to climate change. American<br />

Journal of Cl<strong>in</strong>ical Nutrition 89, S1704-S1709.<br />

Coll<strong>in</strong>s, A., Fairchild, R., 2007. Susta<strong>in</strong>able food consumption at a sub-national level: An ecological footpr<strong>in</strong>t, nutritional and economic<br />

analysis. Journal of Environmental Policy and Plann<strong>in</strong>g 9, 5-30.<br />

Cordell, D., Drangert, J.O., White, S., 2009. The story of phosphorus: Global food security and food for thought. Global Environmental<br />

Change-Human and Policy Dimensions 19, 292-305.<br />

Davis, J., Sonesson, U., 2008. Life cycle assessment of <strong>in</strong>tegrated food cha<strong>in</strong>s - A Swedish case study of two chicken meals. Int J<br />

Life Cycle Assess 13, 574-584.<br />

Davis, J., Sonesson, U., Baumgartner, D.U., Nemecek, T., 2010. Environmental impact of four meals with different prote<strong>in</strong> sources:<br />

Case studies <strong>in</strong> Spa<strong>in</strong> and Sweden. <strong>Food</strong> Research International 43, 1874-1884.<br />

Drewnowski, A., 2009. Def<strong>in</strong><strong>in</strong>g Nutrient Density: Development and Validation of the Nutrient Rich <strong>Food</strong>s Index. Journal of the<br />

American College of Nutrition 28, 421S-426S.<br />

efsa, 2009. Scientific Op<strong>in</strong>ion of the Panel on Di<strong>et</strong><strong>et</strong>ic products, Nutrition and Allergies on a request from European Commission on<br />

the review of labell<strong>in</strong>g reference <strong>in</strong>take values for selected nutritional elements. The EFSA, 1-14.<br />

efsa, 2010. EFSA Panel on Di<strong>et</strong><strong>et</strong>ic Products, Nutrition, and Allergies (NDA); Scientific Op<strong>in</strong>ion on Di<strong>et</strong>ary Reference Values for<br />

carbohydrates and di<strong>et</strong>ary fibre. EFSA Journal 3, 1462 [77 pp.].<br />

efsa, <strong>2012</strong>. EFSA Panel on Di<strong>et</strong><strong>et</strong>ic Products, Nutrition and Allergies (NDA); Scientific Op<strong>in</strong>ion on Di<strong>et</strong>ary Reference Values for<br />

prote<strong>in</strong>. EFSA Journal 2, 2557 [66 pp.].<br />

399

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