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

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GROUP 4, SESSION B: CROP PRODUCTION SYSTEMS 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 />

822<br />

112. Modell<strong>in</strong>g Estonian field crop farm types for <strong>LCA</strong><br />

Sirli Pehme * , Eve Veromann<br />

Estonian University of Life Sciences, Estonia, * Correspond<strong>in</strong>g author. E-mail: Sirli.Pehme@emu.ee<br />

<strong>Food</strong> and beverage f<strong>in</strong>al household consumption <strong>in</strong> EU accounts for 22–34% of total life-cycle impacts <strong>in</strong> all<br />

environmental impact categories (except eutrophication that accounts 60%) (Tukker <strong>et</strong> al. 2006). Furthermore,<br />

different agricultural production practices have different impacts on environment. Thus, assessment<br />

through life cycle is needed to choose the best practises and mitigate pressure on environment.<br />

Although, field crops have significant share <strong>in</strong> Estonian agricultural production, no agricultural <strong>LCA</strong> studies<br />

have been done <strong>in</strong> Estonia so far. There are huge variability <strong>in</strong> resource use and environmental impact b<strong>et</strong>ween<br />

farms because of the variation <strong>in</strong> actual practises (Halberg 1999). Most of the <strong>LCA</strong>-s are based on data<br />

from case studies (Pfefferli and Gaillard 2000). To ensure the representativeness and to aim more general<br />

validity, assessment should be based on a larger sample of farm data. There are huge differences b<strong>et</strong>ween<br />

countries <strong>in</strong> agricultural practices, therefore country-specific <strong>in</strong>ventory data about farm practises is needed.<br />

In addition, environmental assessment through the life cycle tak<strong>in</strong>g account local conditions is necessary.<br />

The aim of this paper was to create representative farm type models of Estonian arable crop farms based on<br />

different characteristics – ma<strong>in</strong> product type, management type, animal density (<strong>in</strong> case of mixed farm<strong>in</strong>g) –<br />

for further life cycle assessments. Different data sources were used to create <strong>in</strong>ventory data of Estonian field<br />

crop farm models: systematic statistics, farm accountancy data n<strong>et</strong>works, experiments, surveys, recommendations<br />

and expert op<strong>in</strong>ion. Data of land area, energy and fertiliser use, yields and other characteristics are<br />

presented for each farm type. Challenges on creat<strong>in</strong>g farm type models are discussed.<br />

References<br />

Halberg, N., 1999. Indicators of resource use and environmental impact for use <strong>in</strong> a decision aid for Danish<br />

livestock farmers. Agriculture, Ecosystems and Environment 76 17-30.<br />

Pfefferli S., Gaillard, G., 2000. Development of a new management tool by comb<strong>in</strong><strong>in</strong>g <strong>LCA</strong> and FADN. In:<br />

Weidema, BP., Meeusen MJG., (eds.), Agricultural data for life cycle assessments, Vol 2., Agricultural<br />

Economics Research Institute, The Hague, The N<strong>et</strong>herlands, 137-144.<br />

Tukker, A., Huppes, G., Gu<strong>in</strong>ee J., Heijungs, R., de Kon<strong>in</strong>g, A., van Oers, L., Suh, S., Geerken, T., van<br />

Holderbeke, M., Jansen, B., Nielsen, B., 2006. Environmental impacts of products (EIPRO). European<br />

Science and Technology Observatory and Institute for Prospective Technological Studies, Seville, Spa<strong>in</strong>.<br />

Available from: http://ec.europa.eu/environment/ipp/pdf/eipro_report.pdf

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