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

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PARALLEL SESSION 3C: SHEEP AND DAIRY 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 />

Total land use impacts on biodiversity across states, when account<strong>in</strong>g for all crops, are equal to 1.37<br />

m 2 .yr.PDF/kg milk at the national level. California and Wiscons<strong>in</strong> contribute to 17% and 15% respectively.<br />

Figure 7. Milk production per state (m<strong>et</strong>ric<br />

ton/year)<br />

Figure 8. Land use impacts on biodiversity and contribution<br />

to the milk at the national level production per<br />

state (m 2 .yr.PDF/kg FPCM)<br />

4. Discussion<br />

Land use area requirements, which are ma<strong>in</strong>ly driven by the yield, for each crop to be produced <strong>in</strong> the<br />

feed ration varied up to 6 times from one crop to another. Another key-param<strong>et</strong>er is the crop production contribution<br />

per state. Results of land use impacts per kg of milk produced from state to state varied up to 15<br />

times for nationally produced crops. A comparison of the results <strong>in</strong>dicate different share of contribution to<br />

the total impacts and for which the crop provenance could be traced back to its production location.<br />

Given the distribution of feed components’ production and their share to the national level production,<br />

states such as California and Wiscons<strong>in</strong>, which are major contributors to the national milk production require<br />

significant amount of crop to feed cows. However, not be<strong>in</strong>g a sizeable <strong>in</strong>-state corn gra<strong>in</strong> production, they<br />

require a large supply of feed from other states. The latter are located <strong>in</strong> the Corn Belt region and constitute<br />

the ma<strong>in</strong> suppliers’ to many other dairy producers states (i.e. receiver states). Consequently, land use impacts<br />

on biodiversity per kg of milk produced are greater than the ones <strong>in</strong>duced by M<strong>in</strong>nesota’s milk production,<br />

as it only contributes to 4% of the national milk production. Thus, impacts from an <strong>in</strong>ducer perspective are<br />

larger than those from a receiver perspective. This reason<strong>in</strong>g applies to feed components, which their supply<br />

mix is assumed to be a national production (eg. commodity crops such as corn gra<strong>in</strong>). For local and not<br />

transportable crops, assumed to be produced with<strong>in</strong> the state where the farm is located, their contribution to<br />

land use impacts of milk production at the national level is ma<strong>in</strong>ly local. Thus, <strong>in</strong>duced and received impacts<br />

are equivalent.<br />

As part of the spatial assessment, results for land use impacts on a series of ecosystem services (groundwater<br />

recharge potential, erosion resistance potential, physico-chemical filtration and mechanical filtration<br />

potential) wer also accounted for. Impact results were ma<strong>in</strong>ly driven by the milk production fraction at national<br />

scale and thus aligned with the one observed for the biodiversity <strong>in</strong>dicator. California, Wiscons<strong>in</strong>,<br />

Pennsylvania and New York were consistently among the top contributors to total impact (results not<br />

shown). D<strong>et</strong>ailed results can be foun <strong>in</strong> the orig<strong>in</strong>al report (Jolli<strong>et</strong> <strong>et</strong> al., <strong>2012</strong>).<br />

5. Conclusion<br />

Land use impacts related to milk production across its entire life cycle are ma<strong>in</strong>ly driven by land use<br />

needed for feed production, which is required for dairy consumption. The rema<strong>in</strong><strong>in</strong>g processes beyond the<br />

farm gate contribute to 5% of the total impact to biodiversity (results not shown). These are dom<strong>in</strong>ated by<br />

forest land use necessary for pulp production used <strong>in</strong> manufactur<strong>in</strong>g paperboard cartons and other packag<strong>in</strong>g.<br />

We found that impacts of feed vary significantly depend<strong>in</strong>g on the production location. Both <strong>in</strong>ventory<br />

and impact assessment contributes to this variation. Inventory is directly <strong>in</strong>fluenced by the yield that d<strong>et</strong>erm<strong>in</strong>es<br />

the area requirements per unit of crops production. Impact assessment is directly <strong>in</strong>fluenced by several<br />

bio-geographic factors, such as climate conditions, veg<strong>et</strong>ation patterns and soil type properties. We<br />

found that spatial differentiation at the state level (the chosen regionalisation scale for this study) is as a key<br />

element when address<strong>in</strong>g land use impacts. However, future work and improvement could address a f<strong>in</strong>er<br />

and more relevant scale assessment. The latter can be addressed on U.S. ecoregions scale level <strong>in</strong>stead of<br />

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