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

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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 />

16. Environmental impact of the pork supply cha<strong>in</strong> depend<strong>in</strong>g on<br />

farm performances<br />

Karol<strong>in</strong>e Reckmann * , Joachim Kri<strong>et</strong>er<br />

Institute of Animal Breed<strong>in</strong>g and Husbandry, Christian-Albrechts-University Kiel, Germany, Correspond<strong>in</strong>g<br />

author. E-mail: kreckmann@tierzucht.uni-kiel.de<br />

The aim of the study is to figure the effect of changes <strong>in</strong> farm performances on the environmental impact of<br />

pork production. The environmental assessment was performed us<strong>in</strong>g data represent<strong>in</strong>g the typical Northern<br />

German pork production <strong>in</strong> 2010 on the one hand. On the other hand, data of German pig farms with 25%<br />

highest and lowest efficiency <strong>in</strong> terms of n<strong>et</strong> profit (economic success) was used. The data for the farms was<br />

gathered from an extension service for pig farms <strong>in</strong> Northern Germany (SSB, 2010). The database of the feed<br />

and slaughter<strong>in</strong>g stage was composed of own data collection from specific companies and of literature. The<br />

system boundaries of the Life Cycle Assessment cover the feed production, pig hous<strong>in</strong>g as well as the<br />

slaughter<strong>in</strong>g stage. Infrastructure, packag<strong>in</strong>g, r<strong>et</strong>ail and consumption were excluded. The manure produced at<br />

the farm had also a value as a fertiliser, thus substitut<strong>in</strong>g synth<strong>et</strong>ic fertiliser. The environmental impact of the<br />

whole production cha<strong>in</strong> was expressed per ‘1 kg pork produced’. Three impact categories were considered:<br />

Global warm<strong>in</strong>g potential (GWP), Eutrophication potential (EP) and Acidification potential (AP), expressed<br />

<strong>in</strong> equivalents (eq).<br />

Table 1 summarises the environmental performance with respect to the three impact categories. The average<br />

pork production results <strong>in</strong> a GWP of 3.62 kg CO2-eq, an EP of 42 g PO4-eq and an AP of 89 g SO2-eq per kg<br />

pork. A higher efficiency on farm level reduces the estimated environmental impacts of GWP as well as EP.<br />

The GWP is improved by 358 g CO2-eq per kg pork, whereas the reduction of EP reaches 0.37 g PO4-eq per<br />

kg pork. In contrast, the average production results <strong>in</strong> a 1% <strong>in</strong>creased AP compared to the production with a<br />

lower efficiency. However, the lowest AP arises out of the pork production with an enhanced performance<br />

on farm level. Nguyen <strong>et</strong> al. (2011) estimated a GWP of 3.1 kg CO2-eq per kg carcass weight produced <strong>in</strong><br />

Denmark. These results are <strong>in</strong> l<strong>in</strong>e with ours. In case of higher efficiency, the potential of reduc<strong>in</strong>g the GWP<br />

(2.8 kg CO2-eq per kg carcass weight) was shown more clearly than <strong>in</strong> the present study. This could arise<br />

from the different m<strong>et</strong>hod used or the fact that the higher efficiency was based on biological param<strong>et</strong>ers.<br />

For estimation of the contribution of these stages to the overall impacts, the production cha<strong>in</strong> was divided<br />

<strong>in</strong>to the stages of feed production, pig hous<strong>in</strong>g and slaughter<strong>in</strong>g. Feed production is the ma<strong>in</strong> contributor <strong>in</strong><br />

the case of GWP with a share of 80% (Fig. 1), followed by pig hous<strong>in</strong>g (15%) and slaughter<strong>in</strong>g. The largest<br />

part of Eutrophication is caused by pig hous<strong>in</strong>g (51%) and feed production (48%). In the case of AP, pig<br />

hous<strong>in</strong>g plays a key role with an amount of 72%. Feed production is responsible for 27% of the AP, whereas<br />

only 1% of the AP orig<strong>in</strong>ates from the slaughter<strong>in</strong>g process. Over all the shown impact categories, slaughter<strong>in</strong>g<br />

has only a marg<strong>in</strong>al share (1-5%) to the environmental impacts of the pork supply cha<strong>in</strong>.<br />

Further calculations will <strong>in</strong>clude different scenarios by vary<strong>in</strong>g s<strong>in</strong>gle param<strong>et</strong>ers on farm level, as e.g. number<br />

of litters per sow and year, feed <strong>in</strong>take, daily weight ga<strong>in</strong> and feed conversion rate. Results from the different<br />

<strong>LCA</strong>s will be compared to identify performance param<strong>et</strong>ers with a high effect on the overall impacts.<br />

In order to illustrate the variation of the impacts, Monte Carlo m<strong>et</strong>hods will be used for further calculations.<br />

References<br />

Nguyen TLT, Hermansen JE, Mogensen L., 2011. Environmental assessment of Danish pork. Aarhus, Denmark:<br />

Aarhus University.<br />

SSB, 2010. Schwe<strong>in</strong>ereport 2010. Schwe<strong>in</strong>espezialberatung Schleswig-Holste<strong>in</strong> e.V.<br />

Table 1. Results for the impact categories Global Warm<strong>in</strong>g Potential (GWP), Eutrophication (EP) and Acidification<br />

Potential (AP) for the three scenarios of pork production, related to 1 kg pork produced.<br />

Impact cate- + 25% farm Average produc- - 25% farm effigory<br />

efficiency tion 2010 ciency<br />

GWP<br />

CO2-eq)<br />

(kg<br />

3.46 3.62 3.67<br />

EP (g PO4-eq) 42.48 42.84 44.88<br />

AP (g SO2eq)<br />

85.41 89.56 89.10<br />

673

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