28.12.2012 Views

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

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

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

SHOW MORE
SHOW LESS

You also want an ePaper? Increase the reach of your titles

YUMPU automatically turns print PDFs into web optimized ePapers that Google loves.

GROUP 1, SESSION A: ANIMAL 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 />

10. Life cycle assessment of milk production <strong>in</strong> Italian <strong>in</strong>tensive dairy<br />

farms<br />

Matteo Guerci, Maddalena Zucali * , Anna Sandrucci, Alberto Tambur<strong>in</strong>i, Chiara Penati, Luciana Bava<br />

Dipartimento di Scienze Agrarie e Ambientali, Università degli Studi di Milano, Italy, Correspond<strong>in</strong>g author.<br />

E-mail: maddalena.zucali@unimi.it<br />

Environmental concerns are hav<strong>in</strong>g <strong>in</strong>creas<strong>in</strong>g priority upon political, social, and economic agendas, <strong>in</strong> particular<br />

when related to agriculture. <strong>Food</strong> production has an environmental impact, and as the global populations<br />

cont<strong>in</strong>ue to <strong>in</strong>crease, it is critical to produce sufficient high-quality food from a f<strong>in</strong>ite resource supply <strong>in</strong><br />

order to mitigate the effects upon the environment (Capper <strong>et</strong> al., 2009). In the North of Italy favorable climatic<br />

and <strong>in</strong>frastructural conditions promoted a great concentration of livestock farms with <strong>in</strong>tensive utilisation<br />

of natural resources (i.e. land, air, water). The objective of this study was to assess the environmental<br />

impact of milk production <strong>in</strong> <strong>in</strong>tensive dairy systems, <strong>in</strong> order to identify farm characteristics that guarantee<br />

at the same time low environmental impact and economic susta<strong>in</strong>ability. A cradle to farm gate Life Cycle<br />

Assessment (<strong>LCA</strong>) was performed on 41 <strong>in</strong>tensive dairy farms <strong>in</strong> Northern Italy. In addition to the evaluation<br />

of greenhouse potential, impact categories as acidification, eutrophication, land use and energy use were<br />

considered. The functional unit was 1 kg Fat and Prote<strong>in</strong> Corrected Milk (FPCM). Farm key param<strong>et</strong>ers<br />

about crop production for feed<strong>in</strong>g, livestock, manure management, purchased feed, fertilisers, pesticides,<br />

electricity and fuels, milk and meat sold were collected by personal <strong>in</strong>terview to the farmers. <strong>LCA</strong> was carried<br />

out us<strong>in</strong>g <strong>LCA</strong> software package, SimaPro 7.3.2 (Pré Consultants, 2011). Gross marg<strong>in</strong>, i.e revenues<br />

m<strong>in</strong>us the direct production costs, exclud<strong>in</strong>g labour costs (expressed <strong>in</strong> €/t FPCM), was used as economic<br />

<strong>in</strong>dicator. Database was analysed us<strong>in</strong>g the CLUSTER procedure (SAS, 2000). In order to identify different<br />

farm<strong>in</strong>g systems the follow<strong>in</strong>g variables were considered: gross marg<strong>in</strong>, feed self-sufficiency, dairy efficiency<br />

and stock<strong>in</strong>g density. Two ma<strong>in</strong> clusters of farms were identified (A and B); moreover <strong>in</strong> each of the<br />

two clusters two subgroups of farms were def<strong>in</strong>ed (Table 1). Farms from cluster B were slightly less <strong>in</strong>tensive<br />

than farms from cluster A: they had significantly larger farm land (ha), lower stock<strong>in</strong>g density (LU/ha)<br />

and higher feed self-sufficiency (%). Economic results were similar b<strong>et</strong>ween the two ma<strong>in</strong> clusters but ecological<br />

performances were b<strong>et</strong>ter for farms from cluster B: nitrogen and phosphorus balances at farm gate<br />

(kg/ha) and the off-farm components of total climate change, acidification, eutrophication, energy use and<br />

land use per kg FPCM were significantly lower <strong>in</strong> cluster B than <strong>in</strong> A. In fact farms from cluster B had<br />

higher feed self-sufficiency and purchased less feed, reduc<strong>in</strong>g off-farms fraction of all impacts but <strong>in</strong>creas<strong>in</strong>g<br />

on-farm component of eutrophication, acidification and land use. Farms from cluster B impacted more <strong>in</strong><br />

term of total eutrophication (on- and off-farm components) <strong>in</strong> comparison with farms from cluster A. Onfarm<br />

crop production weighted for the 50% on eutrophication, because of the use of fertiliser which could<br />

d<strong>et</strong>erm<strong>in</strong>e nitrate leach<strong>in</strong>g <strong>in</strong> the water and ammonia emission <strong>in</strong> the air. Consider<strong>in</strong>g the subgroups, farms<br />

from cluster 4 had b<strong>et</strong>ter economic performances than cluster 3; they were characterised by low stock<strong>in</strong>g<br />

density, high feed self-sufficiency and balanced partition of farm land among different crop production (lucerne:<br />

15.0% ; grass: 14.9%; maize for silage 21.2% of farm land). Farm <strong>in</strong>cluded <strong>in</strong> cluster 4 had lower<br />

nitrogen and phosphorus balances than cluster 3; they probably paid more attention <strong>in</strong> us<strong>in</strong>g fertilisers (134<br />

vs 178 kg of N <strong>in</strong>put from artificial fertilisers) and sold feed (446 vs 0 kg of N output from sold feed). The<br />

energy use of cluster 4 was lower than cluster 3 (P=0.10) as a consequence of reduced use of off-farm products,<br />

especially feeds. In the context of <strong>in</strong>tensive dairy farm<strong>in</strong>g of Northern Italy cluster 4 identifies a type of<br />

farm<strong>in</strong>g system that can produce good economic performances without <strong>in</strong>creas<strong>in</strong>g environmental impact.<br />

References<br />

Capper, J. L., Cady, R. A., Bauman, D. E., 2009. The environmental impact of dairy production: 1944 compared<br />

with 2007. J. Anim. Sci. 87, 2160-2167.<br />

Pré Consultants, 2011. SimaPro 7.3.2 PhD, <strong>LCA</strong> software. Pr<strong>in</strong>terweg, Amersfoort, N<strong>et</strong>herlands.<br />

SAS II, 2000. The SAS System for W<strong>in</strong>dows. In Book The SAS System for W<strong>in</strong>dows, Vol. Relase 8.01.<br />

663

Hooray! Your file is uploaded and ready to be published.

Saved successfully!

Ooh no, something went wrong!