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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 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 />

816<br />

108. <strong>LCA</strong>s for a large repertoire of F<strong>in</strong>nish outdoor plant products<br />

Merja Saar<strong>in</strong>en * , Yrjö Virtanen, Helena Hyvär<strong>in</strong>en<br />

MTT Agrifood Research F<strong>in</strong>land, * Correspond<strong>in</strong>g author. E-mail: merja.saar<strong>in</strong>en@mtt.fi<br />

The paper presents results of <strong>LCA</strong> for a large repertoire of outdoor crops produced <strong>in</strong> F<strong>in</strong>land <strong>in</strong> two resource<br />

use categories (land and energy) and three impact categories (climate change, eutrophication and<br />

acidification). Assessed crops were cereals, potato, rapeseed, pea, broad bean, carrot, be<strong>et</strong>root, yellow turnip,<br />

parsnip, Ch<strong>in</strong>ese cabbage, onion, strawberry and blackcurrant.<br />

The functional unit of <strong>LCA</strong>s is the kilo of a product at the farm gate (without packag<strong>in</strong>g). System boundaries<br />

<strong>in</strong>clude production of agricultural <strong>in</strong>puts and energy <strong>in</strong> the upstream phases, and use of agricultural <strong>in</strong>puts<br />

and energy, and mechanical work <strong>in</strong> the production phase on farms. However, potential packag<strong>in</strong>g and storage<br />

on farms, and transportation of agricultural <strong>in</strong>puts to the farm were excluded from the product systems.<br />

Emissions from organic soils were excluded. Data on agricultural <strong>in</strong>put manufacture were obta<strong>in</strong>ed from<br />

<strong>in</strong>dustry, which produces most agricultural <strong>in</strong>puts used <strong>in</strong> F<strong>in</strong>land. Energy consumption was based on the<br />

F<strong>in</strong>nish average grid values. Data on the use of <strong>in</strong>puts for crop production were based on the national agricultural<br />

database, compris<strong>in</strong>g data on the cultivation <strong>in</strong>stances of various crops, i.e. primary data. Data on mechanical<br />

work were based on physical models. Data represent average F<strong>in</strong>nish production. Emissions and<br />

impacts from domestic animal production (<strong>in</strong>clud<strong>in</strong>g manure-based emission from animal shelter and storage)<br />

were not allocated to the manure used as fertiliser for plant production. There were no other significant<br />

allocation issues.<br />

For the climate impact calculation, estimation of N2O, CO2 and <strong>in</strong>direct N2O emissions from the field were<br />

based on the IPCC m<strong>et</strong>hod and data (IPCC, 2006). Data on NH3 emissions from the application of fertilisers<br />

were estimated based on models from the EEA (European Environmental Agency, 2006). For the assessment<br />

of eutrophication, site-specific nitrogen and phosphorus leach<strong>in</strong>g models and site-dependent factors were<br />

applied.<br />

The climate impact and acidification of rapeseed was by far the highest, and the lowest was for root veg<strong>et</strong>ables<br />

and potato (Table 1). The eutrophication potential of broad bean was highest, followed by Ch<strong>in</strong>ese cabbage,<br />

and the lowest eutrophication potential was for carrot, followed by oat and barley. Production of rapeseed<br />

consumed most energy, and root veg<strong>et</strong>ables the least. Source of energy varied considerably among<br />

products.<br />

It is concluded that the priority order of products varies accord<strong>in</strong>g to impact category, as <strong>in</strong>dicated <strong>in</strong> Table<br />

1. CO2 and N2O are the ma<strong>in</strong> emissions that impact climate. Their share differs for different plants. Figure 1<br />

illustrates the significance of different emissions for climate impact.<br />

The study was part of the ConsEnv-project. The results have been used <strong>in</strong> the <strong>LCA</strong> for lunch portions<br />

(Saar<strong>in</strong>en <strong>et</strong> al., <strong>2012</strong>) tog<strong>et</strong>her with <strong>LCA</strong> results for animal-based products (Usva <strong>et</strong> al., <strong>2012</strong>).<br />

References<br />

European Environment Agency (EEA) 2006. EMEP/CORINAIR Emission Inventory Guidebook - 2006.<br />

Web publication. Available at: http://www.eea.europa.eu/publications/EMEPCORINAIR4<br />

IPCC, 2006. IPCC Guidel<strong>in</strong>es for National Greenhouse Gas Inventories. Volume 4. Agriculture, Forestry<br />

and Other Land Use. IPCC-NGGIP Publications<br />

Saar<strong>in</strong>en, M., Kurppa, S., Virtanen, Y., Usva, K., Mäkelä, J. and A. Niss<strong>in</strong>en, 2011. <strong>LCA</strong> approach to the<br />

impact of homemade, ready-to-eat and school lunches on climate and eutrophication. J Cleaner Production.<br />

28, 177-186.<br />

Saar<strong>in</strong>en, M., Kurppa, S., Virtanen, Y., Usva, K., Mäkelä, J. and A. Niss<strong>in</strong>en, <strong>2012</strong>b. <strong>LCA</strong> approach to the<br />

impact of homemade, ready-to-eat and school lunches on climate and eutrophication. J Cleaner Production<br />

28, 177-186.<br />

Usva, K., Nousia<strong>in</strong>en, J., Hyvär<strong>in</strong>en, H. and Y. Virtanen <strong>2012</strong>. <strong>LCA</strong>s of average animal products pork, beef,<br />

milk and eggs <strong>in</strong> F<strong>in</strong>land. Abstract for <strong>LCA</strong> <strong>Food</strong> <strong>2012</strong> Conference.

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