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

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PLENARY SESSION 2: METHODOLOGICAL CHALLENGES FOR ANIMAL PRODUCTION SYSTEMS 8 th Int. Conference on<br />

<strong>LCA</strong> <strong>in</strong> the<br />

Agri-<strong>Food</strong> Sector, 1-4 Oct <strong>2012</strong><br />

such as phosphorus, pesticides, heavy m<strong>et</strong>als, and pathogenic microorganisms. This became the framework<br />

of analysis for an <strong>in</strong>tegrated livestock-ecosystems model.<br />

2. M<strong>et</strong>hods<br />

A review of factors driv<strong>in</strong>g change <strong>in</strong> the livestock sector was undertaken, <strong>in</strong>clud<strong>in</strong>g key agricultural and<br />

environmental policies. The op<strong>in</strong>ions of a range of <strong>in</strong>dustry representatives were canvassed regard<strong>in</strong>g views<br />

on the role of livestock <strong>in</strong> the rural economy and its relationship with the environment. The relationship<br />

b<strong>et</strong>ween livestock farm<strong>in</strong>g systems and soci<strong>et</strong>y was then explored us<strong>in</strong>g an ecosystems framework, namely<br />

the affect on provision<strong>in</strong>g (e.g. food production), regulat<strong>in</strong>g (e.g. GHG emissions) and cultural (e.g. landscape)<br />

services. A vari<strong>et</strong>y of scenarios were then developed to reflect actual and potential demands from the<br />

livestock sector, given current and future drivers.<br />

2.1 Scenarios for modell<strong>in</strong>g<br />

Follow<strong>in</strong>g a review of scenarios used <strong>in</strong> previous projects and the understand<strong>in</strong>g developed <strong>in</strong> a review of<br />

science and policy, a s<strong>et</strong> of plausible future scenarios was developed to explore how the UK Government<br />

Department for Environment, <strong>Food</strong> and Rural Affairs (DEFRA) objectives for the livestock sector could be<br />

m<strong>et</strong>, namely a “profitable and comp<strong>et</strong>itive domestic <strong>in</strong>dustry which enhances the biodiversity and rural landscape<br />

of England while m<strong>in</strong>imis<strong>in</strong>g its impact on climate change, soil, water, and air quality”. These were:<br />

1. Bus<strong>in</strong>ess As Usual (BAU): a basel<strong>in</strong>e bus<strong>in</strong>ess as usual scenario, exam<strong>in</strong><strong>in</strong>g the n<strong>et</strong> balance b<strong>et</strong>ween the<br />

Provision<strong>in</strong>g, Regulat<strong>in</strong>g, and Cultural impacts of the livestock sector and d<strong>et</strong>erm<strong>in</strong><strong>in</strong>g how <strong>in</strong>dividual<br />

sub-sectors contribute to this.<br />

And also a series of optimis<strong>in</strong>g scenarios to d<strong>et</strong>erm<strong>in</strong>e the effect of:<br />

2. Maximis<strong>in</strong>g employment generation associated with the livestock sector<br />

3. M<strong>in</strong>imis<strong>in</strong>g production costs from the livestock sector<br />

4. Reduc<strong>in</strong>g GHG emissions by 25%<br />

5. Shift<strong>in</strong>g from red (beef and lamb) to white meat (pork and poultry) - with red meat assumed to be provided<br />

only from dairy beef, as a by-product of milk production<br />

6. Reduc<strong>in</strong>g production of each livestock sector by 25%, balanced as far as possible by plant commodities<br />

2.2 Data <strong>in</strong>puts and model development<br />

Data for the valuation of Provision<strong>in</strong>g, Regulat<strong>in</strong>g and Cultural services were developed from a vari<strong>et</strong>y of<br />

sources and adjusted, where needed, to 2009 values with HM Treasury GDP deflators (2011). Whilst data<br />

on provision<strong>in</strong>g services were relatively easy to f<strong>in</strong>d, data on the impact of livestock systems on the value of<br />

regulat<strong>in</strong>g and cultural services were especially difficult to develop. Valuation data were developed from a<br />

vari<strong>et</strong>y of sources, <strong>in</strong>clud<strong>in</strong>g the Report on the Environmental Accounts for Agriculture (Jacobs, 2008).<br />

2.3 Development of an <strong>in</strong>tegrated livestock-ecosystems model<br />

An <strong>in</strong>tegrated livestock-ecosystems l<strong>in</strong>ear programm<strong>in</strong>g model was developed to assess the economic and<br />

environmental impacts of the livestock sector, us<strong>in</strong>g an ecosystem services framework. For this, the Cranfield<br />

Life Cycle Assessment Model (Williams <strong>et</strong> al., 2006, 2007) was comb<strong>in</strong>ed with a grassland productivity<br />

model and a soil erosion model to assess environmental consequences of the livestock sector. A model<br />

was also developed to calculate soil erosion for each 5x5km grid square <strong>in</strong> England and Wales us<strong>in</strong>g the<br />

Morgan-Morgan-F<strong>in</strong>ney model (Morgan <strong>et</strong> al., 1984). Soil erosion was calculated per unit area for each<br />

slope angle for the different land uses and slope proportions, then allocated b<strong>et</strong>ween the different systems,<br />

after remov<strong>in</strong>g non-productive land. From this, average erosion values (t ha -1 ) were derived for arable, dairy,<br />

beef and sheep, and then split among lowland (

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