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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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GROUP 3, SESSION A: LABELLING, CONSUMERS, 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 />

69. Assessment of the environmental impact of di<strong>et</strong>ary <strong>in</strong>take habits <strong>in</strong><br />

the UK<br />

Jan<strong>et</strong> Kyle 1,* , Jennie Macdiarmid 2 and Tony Craig 3<br />

1 Public Health Nutrition Research Group, Institute of Applied Health Sciences, University of Aberdeen, Foresterhill,<br />

Aberdeen, AB25 2ZD, UK, 2 Row<strong>et</strong>t Institute of Nutrition and Health, University of Aberdeen, UK,<br />

3 James Hutton Institute, Craigiebuckler, Aberdeen, AB15 8QH, UK, * Correspond<strong>in</strong>g author. E-mail:<br />

j.kyle@abdn.ac.uk<br />

The food system is estimated to account for 18-20% of total UK greenhouse gas (GHG) emissions, <strong>in</strong>creas<strong>in</strong>g<br />

to 30% factor<strong>in</strong>g land use change (Audsley <strong>et</strong> al 2009), and food consumption habits make an important<br />

contribution to these emissions. With the <strong>in</strong>troduction of legally b<strong>in</strong>d<strong>in</strong>g commitments to reduce GHGE; the<br />

UK Climate Change Act (2008) s<strong>et</strong> targ<strong>et</strong>s to reduce GHGE by at least 34% by 2020, this will require not<br />

only efficiency sav<strong>in</strong>gs <strong>in</strong> food production and process<strong>in</strong>g, but also adoption of lower impact di<strong>et</strong>s by consumers.<br />

However, <strong>in</strong> the UK, few studies have assessed the impact of actual di<strong>et</strong>ary habits and the environmental<br />

impact, measured <strong>in</strong> the form of GHG emissions. The current study aimed to <strong>in</strong>vestigate the potential<br />

of assess<strong>in</strong>g the environmental impact of di<strong>et</strong>ary <strong>in</strong>take habits us<strong>in</strong>g a novel approach to measur<strong>in</strong>g and rank<strong>in</strong>g<br />

the environmental impact of food consumption <strong>in</strong>to high, medium and low levels of emissions and compare<br />

this with the nutritional quality of the di<strong>et</strong>.<br />

A random sample to people liv<strong>in</strong>g <strong>in</strong> the South West of Scotland were asked to compl<strong>et</strong>ed an anonymised<br />

postal survey, 527 people, average age 58y (range 20-90y) r<strong>et</strong>urned the questionnaires. Habitual di<strong>et</strong> was<br />

measured us<strong>in</strong>g a food frequency questionnaire (FFQ) (www.foodfrequency.org), which asks for the frequency<br />

of consumption of 170 food and dr<strong>in</strong>k items and has been previously validated for di<strong>et</strong>ary assessment.<br />

<strong>Food</strong> and nutrient <strong>in</strong>take and environmental impact were d<strong>et</strong>erm<strong>in</strong>ed by l<strong>in</strong>k<strong>in</strong>g, the FFQ response<br />

<strong>in</strong>formation to an <strong>in</strong>-house food nutrient composition and food related GHG emissions database. Estimation<br />

of average daily GHG emissions acted as a marker of environmental impact.<br />

GHG emissions values for food items ‘as eaten’ were calculated from raw food commodities data from one<br />

of the most comprehensive lists of GHG emissions <strong>in</strong> the UK (Audsley <strong>et</strong> al 2009). These food commodity<br />

data did not represent the full ‘cradle to grave’ life cycle analysis (<strong>LCA</strong>), but rather the average GHG emissions<br />

for the production of raw food commodities up to the regional distribution centre (RDC). The RDC<br />

was described as a nom<strong>in</strong>al boundary of agricultural and food <strong>in</strong>gredient production up to the po<strong>in</strong>t of distribution<br />

<strong>in</strong> the UK and estimated to account on average for 56% of the total <strong>LCA</strong> GHG emissions. The later<br />

stages of process<strong>in</strong>g raw basic <strong>in</strong>gredients <strong>in</strong>to edible food products ready for consumption were not <strong>in</strong>cluded.<br />

These data were harmonised with the nutrient composition data to reflect food as eaten, with adjustments<br />

for edible portion, cook<strong>in</strong>g ga<strong>in</strong>s and losses, and production of composite dishes and food products,<br />

such as lasagne, crisps and cakes, employ<strong>in</strong>g a proportion of <strong>in</strong>gredients approach,. It is important to note for<br />

example that GHG emissions for cooked meat will <strong>in</strong> relative terms <strong>in</strong>crease due to weight loss whilst cook<strong>in</strong>g,<br />

while the emissions for rice will fall with cook<strong>in</strong>g due to weight ga<strong>in</strong>s through hydration. However it is<br />

important to highlight there is a lack of compl<strong>et</strong>e ‘cradle to grave’ <strong>LCA</strong> for commonly consumed foods.<br />

Prelim<strong>in</strong>ary results <strong>in</strong>dicate that though, as expected, <strong>in</strong>creas<strong>in</strong>g energy <strong>in</strong>take and levels of GHG emissions<br />

are closed l<strong>in</strong>ked, the actual quality of the di<strong>et</strong> from a health perspective does not appear to dim<strong>in</strong>ish. For<br />

example, the relative contribution of fat (34% of total energy), prote<strong>in</strong> (16% of total energy), to total energy<br />

<strong>in</strong>take rema<strong>in</strong>s unchanged with <strong>in</strong>creas<strong>in</strong>g levels of GHG emissions from the di<strong>et</strong>. This study has lead to<br />

deeper <strong>in</strong>sights <strong>in</strong>to the <strong>in</strong>teractions b<strong>et</strong>ween di<strong>et</strong>, environment and health which will contribute to development<br />

of the population based approaches to reduc<strong>in</strong>g the environmental impact of di<strong>et</strong>ary <strong>in</strong>take.<br />

References<br />

Audsley E, Brander M, Chatterton J, Murphy-Bokern D, Webster C, Williams A., 2009. How Low Can We<br />

Go? An assessment of greenhouse gas emissions from the UK food system and the scope for reduction by<br />

2050. WWF-UK.<br />

758

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