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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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PARALLEL SESSION 6A: TOOLS AND DATABASES 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 />

GHG emissions are economic allocated b<strong>et</strong>ween milk and meat, and the allocation to nutrients (from manure)<br />

and energy (from destruction of animals) is zero.<br />

Note that the same unallocated <strong>in</strong>ventory data are used for all four switches and only the system boundaries<br />

are changed. This implies that the farm specific data can be entered <strong>in</strong> the model, and then the results can<br />

easily be presented accord<strong>in</strong>g to the desired standards mentioned above. Similarly, the results for the Danish<br />

and Swedish basel<strong>in</strong>e can be transformed to be compliant to attributional modell<strong>in</strong>g, IDF or PAS2050 guidel<strong>in</strong>es.<br />

3. Results<br />

The result for Danish basel<strong>in</strong>e milk produced <strong>in</strong> 2005 is presented <strong>in</strong> Table 1. The table is divided <strong>in</strong>to<br />

three major parts: 1) direct emissions of CH4 and N2O from the animals and their manure (from hous<strong>in</strong>g and<br />

storage). 2) upstream emissions from the production of feed, land use changes, utilisation of manure as organic<br />

fertiliser, fuels and their combustion <strong>et</strong>c. Note that services and capital goods are <strong>in</strong>cluded <strong>in</strong> these<br />

figures. 3) Avoided emissions related to the substituted beef production caused by the supply of meat from<br />

the dairy system.<br />

Table 1. GHG-emissions for 1 kg ECM, Danish basel<strong>in</strong>e 2005. Switch: Consequential (ISO14044). Unit: kg<br />

CO2-eq per kg ECM.<br />

Denmark basel<strong>in</strong>e Dairy cow Rais<strong>in</strong>g<br />

480<br />

heifer<br />

Rais<strong>in</strong>g newborn<br />

bull<br />

Rais<strong>in</strong>g<br />

bull<br />

Total Total<br />

Direct emissions<br />

CH4, enteric fermentation 0.414 0.094 0.00138 0.0380 0.548<br />

CH4, manure handl<strong>in</strong>g and storage 0.0697 0.00838 0.000347 0.00764 0.0860<br />

N2O direct 0.0312 0.00605 0.000274 0.00459 0.0422<br />

N2O <strong>in</strong>direct 0.00524 0.000731 0.0000216 0.000474 0.00647 0.682<br />

Emissions outside the animal activities (<strong>in</strong>cl. capital goods and services)<br />

Feed <strong>in</strong>puts, excl. ILUC 0.170 0.0388 0.000568 0.0156 0.225<br />

ILUC related to feed 1.47 0.336 0.00492 0.135 1.95<br />

Manure land appl. <strong>in</strong>cl. subst. m<strong>in</strong>eral fert. -0.0353 -0.00125 -0.0000160 -0.00165 -0.0382<br />

Fuels <strong>in</strong>cl. Combustion 0.00994 0.00229 0.000255 0.00175 0.0142<br />

Electricity 0.0369 0 0 0 0.0369<br />

Transport 0.0138 0.00315 0.0000461 0.00127 0.0183<br />

Destruction of fallen cattle <strong>in</strong>cl. subst. energy -0.00314 -0.000530 -0.000269 -0.000414 -0.00435<br />

Farm, capital goods 0.0113 0.0113 0.000580 0.00397 0.0271<br />

Farm, services 0.0149 0.0150 0.000767 0.00525 0.0359 2.26<br />

Substituted beef system (<strong>in</strong>cl. capital goods and services)<br />

Direct emissions (CH4 and N2O) -0.399<br />

Feed <strong>in</strong>puts, excl. ILUC -0.0324<br />

ILUC related to feed -1.20<br />

Other -0.245 -1.88<br />

Total 1.06<br />

Results with lower degree of compl<strong>et</strong>eness<br />

Total (result without ILUC) 0.316<br />

Total (result without ILUC and services) 0.254<br />

Total (result without ILUC, services and capital goods) 0.199<br />

It appears from Table 1, that the most important contributions are ILUC (sum of ILUC from several<br />

crops/grass), avoided beef (sum of contributions from several activities with<strong>in</strong> the beef system), direct emissions<br />

from the animal activities (where enteric fermentation is the most important), and the production of<br />

feedstuff (sum of all feedstuff <strong>in</strong>cl. upstream activities such as diesel for traction, farm capital goods and<br />

services, and production of fertiliser and pesticides).<br />

Transport of materials (ma<strong>in</strong>ly feed) to the dairy farms, burn<strong>in</strong>g of diesel for traction <strong>et</strong>c., and electricity<br />

do not contribute significantly to the overall result. Also the <strong>in</strong>puts of capital goods and services to the milk<br />

system are not major contributors to the overall result. It appears that the land application of manure has a<br />

negative contribution. This is because the avoided emissions from the substituted production of m<strong>in</strong>eral fertilisers<br />

are larger than the direct emissions related to the application of the manure on crops. Also the destruction<br />

of animals is associated with a negative contribution because the by-products from the activity substitutes<br />

energy that alternatively would have been produced by the burn<strong>in</strong>g of fossil fuels.<br />

In the lower part of Table 1, the results are shown with lower degrees of compl<strong>et</strong>eness. The results without<br />

ILUC are significantly lower than when <strong>in</strong>clud<strong>in</strong>g ILUC. The results without capital goods and services<br />

show, that the overall result is only affected with approximately 0.117 kg CO2-eq. by the <strong>in</strong>clusion/exclusion<br />

of capital goods and services.

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