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

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PLENARY SESSION 2: METHODOLOGICAL CHALLENGES FOR ANIMAL PRODUCTION SYSTEMS 8 th Int. Conference on<br />

<strong>LCA</strong> <strong>in</strong> the<br />

Agri-<strong>Food</strong> Sector, 1-4 Oct <strong>2012</strong><br />

of labour and <strong>in</strong>put costs), while remov<strong>in</strong>g livestock production compl<strong>et</strong>ely and substitut<strong>in</strong>g with arable<br />

where possible would lead to more than a 90% reduction <strong>in</strong> the value of ecosystems services from current<br />

livestock land if labour is viewed as a benefit and about 60% when labour is viewed as a cost.<br />

The analysis clearly shows the significant trade-offs b<strong>et</strong>ween provision<strong>in</strong>g of livestock products and regulat<strong>in</strong>g<br />

services, especially regard<strong>in</strong>g impacts on air and water. These impacts, which constitute real costs<br />

borne by others without compensation, reduce the overall economic efficiency of the sector. They reflect a<br />

failure of mark<strong>et</strong>s and governance to adequately pass environmental costs to polluters. This is a generic failure,<br />

and the livestock <strong>in</strong>dustry should not be picked out a special case.<br />

It is important to note that while these scenarios demonstrate how the model can be used to optimise the<br />

n<strong>et</strong> flow of ecosystem benefit from the livestock sector, they have not <strong>in</strong>corporated the social acceptability of<br />

los<strong>in</strong>g whole sectors of the livestock <strong>in</strong>dustry. This can be built <strong>in</strong>to the scenarios as constra<strong>in</strong>ts, so that, for<br />

example, the model would optimise n<strong>et</strong> ecosystem benefits by not reduc<strong>in</strong>g production from any sector by<br />

more than a given level. Furthermore, the systems-based nature of the model means that it also provides<br />

extensive outputs on how management and physical impacts with<strong>in</strong> each of the livestock sectors change.<br />

5. Conclusion<br />

The model enabled trade-offs b<strong>et</strong>ween provision<strong>in</strong>g, cultural and regulat<strong>in</strong>g services to be analysed, confirm<strong>in</strong>g,<br />

for example, the important role of livestock systems <strong>in</strong> provid<strong>in</strong>g cultural services, particularly the<br />

contribution of less <strong>in</strong>tensive systems to landscape and biodiversity, and additionally the significant tradeoffs<br />

b<strong>et</strong>ween provision<strong>in</strong>g and regulat<strong>in</strong>g services, especially regard<strong>in</strong>g impacts on air and water. The results<br />

show the importance of the use of a systems based-<strong>LCA</strong> approach <strong>in</strong> identify<strong>in</strong>g the trade-offs b<strong>et</strong>ween the<br />

cultural benefits of extensive systems and the potential efficiencies of more <strong>in</strong>tensive systems. Tak<strong>in</strong>g an<br />

ecosystem-services viewpo<strong>in</strong>t shows the substantial <strong>in</strong>fluence that livestock systems have on wider ass<strong>et</strong>s<br />

such as cultural services that are not <strong>in</strong>corporated <strong>in</strong>to normal account<strong>in</strong>g processes. Furthermore, attempt<strong>in</strong>g<br />

to assign a landscape value to hill and upland livestock, comb<strong>in</strong>ed with a land suitability analysis, shows the<br />

proportion of land that would become abandoned under a “no livestock” scenario, comb<strong>in</strong>ed with a significant<br />

loss <strong>in</strong> cultural value of the land, and highlights the trade-offs and potential losses aris<strong>in</strong>g from radical<br />

changes to the livestock sector <strong>in</strong> the UK.<br />

6. References<br />

Defra, 2007. An <strong>in</strong>troductory guide to valu<strong>in</strong>g ecosystem services. Report published by the Department for Environment, <strong>Food</strong> and<br />

Rural Affairs. London, UK. 68pp. Available at www.defra.gov.uk<br />

Defra, 2009. Agriculture <strong>in</strong> the United K<strong>in</strong>gdom 2009. 146pp. Available at www.defra.gov.uk<br />

HM Treasury, 2011. GDP deflators. Available from: http://www.hm-treasury.gov.uk/data_gdp_fig.htm<br />

Ed<strong>in</strong>a, 2010. AgCensus data. Available from: http://ed<strong>in</strong>a.ac.uk/agcensus/<br />

Jacobs, 2008. Environmental Accounts for Agriculture. F<strong>in</strong>al report submitted to Defra. 175 pp.<br />

Magic, 2011. Available from: http://magic.defra.gov.uk/<br />

Millennium Ecosystem Assessment, 2005. Available from: http://www.milleniumassessment.org/en/<strong>in</strong>dex.asp<br />

Morgan, RPC, Morgan, DDV, F<strong>in</strong>ney, HJ, 1984. A Predictive Model for the Assessment of Soil-Erosion Risk. Journal of Agricultural<br />

Eng<strong>in</strong>eer<strong>in</strong>g Research, 30 (3), 243-253<br />

UNEP-UK NEA, 2010. UK National Ecosystem Assessment. Available from: http://uknea.unep-wcmc.org<br />

Williams, A.G., Audsley, E. and Sandars, D.L., 2006. D<strong>et</strong>erm<strong>in</strong><strong>in</strong>g the environmental burdens and resource use <strong>in</strong> the production of<br />

agricultural and horticultural commodities. Ma<strong>in</strong> Report. Defra Research Project IS0205. Bedford: Cranfield University and Defra.<br />

Available at www.agrilca.org, and www.defra.gov.uk<br />

Williams, A.G., Audsley, E., Sandars, D.L., 2007. Environmental burdens of livestock production systems derived from life cycle<br />

assessment (<strong>LCA</strong>). In: Garnsworthy, P. (Ed), 41st University of Nott<strong>in</strong>gham Feed Conference, Sutton Bon<strong>in</strong>gton, Nott<strong>in</strong>gham,<br />

Nott<strong>in</strong>gham: Nott<strong>in</strong>gham University, 171-200.<br />

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