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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 2A: LAND USE 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 />

Table 1. Input data to milk study<br />

Factor Value<br />

Milk production per cow 8000 kg ECM per year<br />

Replacement rateText 25%<br />

Meat produced per kg ECM 0.0057 kg<br />

Rapeseed oil produced per kg ECM 0.028 kg<br />

GHG emissions for substituted meat production 22 kg CO2-eq.<br />

GHG emissions for substituted rapeseed oil production 0.8 kg CO2-eq.<br />

Table 2. Feed production<br />

Product Yield a (kg/ha yr) Area (ha)<br />

Ley 4230 120<br />

Graz<strong>in</strong>g 4000 70<br />

Spr<strong>in</strong>g barley 2440 54<br />

W<strong>in</strong>ter wheat 3228 40<br />

Broad beans 2026 54<br />

Rapeseed cake 1693 40<br />

a a<br />

Yields for barley and wheat are given at 86% dry matter content (DM), rapeseed 91% and broad beans 85% DM. Ley yield is <strong>in</strong><br />

total solids (TS), with losses dur<strong>in</strong>g harvest and ensil<strong>in</strong>g subtracted<br />

The 200 ha arable farm had a 7-year crop rotation (Table 3) that <strong>in</strong>cluded ley twice, to be used as green<br />

manure (field beans, oats, ley, w<strong>in</strong>ter rapeseed, w<strong>in</strong>ter wheat, ley, rye). In the reference scenario, ley and<br />

straw were ploughed back <strong>in</strong>to the soil.<br />

Table 3. Arable crop rotation<br />

Crop Yield a (kg/ha yr)<br />

Field beans 2400<br />

Oats 3200<br />

Ley 6000<br />

W<strong>in</strong>ter rapeseed 2000<br />

W<strong>in</strong>ter wheat 3500<br />

Ley 6000<br />

Rye<br />

a<br />

Crops dried to 86% DM except ley, which is <strong>in</strong> kg DM<br />

3200<br />

2.3 System boundaries<br />

An overview of the production systems with energy self-supply is shown <strong>in</strong> Figure 1. The system boundary<br />

was s<strong>et</strong> at the farm-gate for products produced on the farm (exception: biomass which is transported to<br />

fuel production facilities and back is <strong>in</strong>cluded). Feedstock for energy carrier production is forwarded to conversion<br />

facilities (“Conversion processes”-box <strong>in</strong> Figure 1). Residual products from the conversion processes,<br />

such as ashes and digestion residues, were assumed to be r<strong>et</strong>urned to the fields as fertilisers. Byproducts<br />

from the conversion processes were accounted for (“Substituted production”-box <strong>in</strong> Figure 1). The<br />

system was compared with a reference system, <strong>in</strong> which the milk production process was supplied with energy<br />

produced with fossil fuels. M<strong>in</strong><strong>in</strong>g, extraction, ref<strong>in</strong><strong>in</strong>g, distribution and consumption of the fossil fuels<br />

were <strong>in</strong>cluded.<br />

2.4 Energy demand<br />

The annual energy demand for the milk farm was 300 GJ electricity (0.14 MJ/kg milk), 115 GJ for gra<strong>in</strong><br />

dry<strong>in</strong>g and 95 GJ for hat<strong>in</strong>g of build<strong>in</strong>gs. Annual tractor fuel demand was 460 GJ.<br />

In the arable farm, heat was supplied to the residential build<strong>in</strong>g (dimensioned capacity 7.4 kW) the hot<br />

water system (1.2 kW), the workshop (1.7 kW) and the gra<strong>in</strong> dryer (227 kW). The total annual tractor fuel<br />

demand was 414 GJ, electricity demand was 51 GJ and heat demand 290 GJ.<br />

144

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