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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 2C: QUANTIFICATION AND REDUCTION OF UNCERTAINTY 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 />

198<br />

Quantify<strong>in</strong>g environmental impacts and their uncerta<strong>in</strong>ties for UK<br />

broiler and egg production systems<br />

Ilkka Le<strong>in</strong>onen 1,* , Adrian Williams 2 , Ilias Kyriazakis 1<br />

1 School of Agriculture, <strong>Food</strong> and Rural Development, Newcastle University, Newcastle upon Tyne, NE1 7RU, UK<br />

2 School of Applied Sciences, Cranfield University, Bedford, MK43 0AL, UK<br />

Correspond<strong>in</strong>g author. E-mail: ilkka.le<strong>in</strong>onen@newcastle.ac.uk<br />

ABSTRACT<br />

The environmental burdens of the ma<strong>in</strong> UK broiler and egg production systems were quantified us<strong>in</strong>g a systems modell<strong>in</strong>g approach<br />

with Monte Carlo simulations for statistical analyses. Feed was the ma<strong>in</strong> component of the global warm<strong>in</strong>g potential <strong>in</strong> all broiler and<br />

egg systems. Manure was a major source of acidification and eutrophication potentials. The length of the production cycle was lowest<br />

<strong>in</strong> the standard <strong>in</strong>door broiler system, and therefore the feed consumption and manure production were also lowest. This caused<br />

statistically significant differences <strong>in</strong> most of the impact categories b<strong>et</strong>ween the broiler systems. The number of birds required to<br />

produce equal amount of eggs, and the amount of feed consumed per bird were highest <strong>in</strong> organic and lowest <strong>in</strong> the cage system.<br />

These general differences <strong>in</strong> productivity affected the environmental impacts of the different egg systems, although <strong>in</strong> some impact<br />

categories the differences were not always significant.<br />

Keywords: broiler, egg, uncerta<strong>in</strong>ty analysis, global warm<strong>in</strong>g potential, energy use<br />

1. Introduction<br />

UK poultry production, <strong>in</strong>clud<strong>in</strong>g broilers and eggs, has been identified as be<strong>in</strong>g relatively environmentally-efficient,<br />

per unit weight, compared to the production of other animal commodities (Williams <strong>et</strong> al.,<br />

2006). However, like all agricultural systems, any current poultry system has scope to improve, and thus has<br />

the potential to reduce its environmental impacts. For example, with an annual production of 8862 million<br />

eggs (about 0.4 billion kg) produced <strong>in</strong> the UK (Defra, 2009) and 61 billion kg produced worldwide annually<br />

(FAO, 2011), the egg lay<strong>in</strong>g systems are likely to be significant contributors to both resource use and environmental<br />

burdens, and therefore have also potential for large scale reduction of impacts such as greenhouse<br />

gas emissions.<br />

The aim of the current study was to apply the <strong>LCA</strong> m<strong>et</strong>hod “from cradle to farm gate”, to quantify the environmental<br />

burdens of the ma<strong>in</strong> broiler and egg production systems <strong>in</strong> the UK, and hence to identify the<br />

ma<strong>in</strong> opportunities to reduce these impacts with<strong>in</strong> each system. The broiler systems <strong>in</strong>cluded <strong>in</strong> the study<br />

were 1) standard <strong>in</strong>door, 2) free range and 3) organic production. Accord<strong>in</strong>g to the Defra (2007) statistics,<br />

the total broiler chicken populations <strong>in</strong> these systems <strong>in</strong> the UK were 101, 4.4 and 1.8 million, respectively.<br />

The egg production systems considered <strong>in</strong> this study were 1) conventional cage, 2) barn, 3) free range and 4)<br />

organic lay<strong>in</strong>g. Although the egg production <strong>in</strong> conventional cages has been banned by the EU and is not<br />

used <strong>in</strong> the UK anymore, it is still <strong>in</strong> use <strong>in</strong> some other European countries, and therefore the results for the<br />

cage lay<strong>in</strong>g system are also presented <strong>in</strong> this study. Results for enriched cages now used <strong>in</strong> the UK are expected<br />

to be broadly similar.<br />

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

2.1. Systems approach and data<br />

The general approach taken <strong>in</strong> the current study was with systems modell<strong>in</strong>g of production. This <strong>in</strong>cluded<br />

structural models of the <strong>in</strong>dustry, process models and simulation models that were unified <strong>in</strong> the systems<br />

approach so that changes <strong>in</strong> one area caused consistent <strong>in</strong>teractions elsewhere. This approach was applied to<br />

both feed crop and animal production. The systems modelled <strong>in</strong> this study <strong>in</strong>cluded crop production, noncrop<br />

nutrient production, feed process<strong>in</strong>g, breed<strong>in</strong>g, broiler production, pull<strong>et</strong> rear<strong>in</strong>g, egg lay<strong>in</strong>g and manure<br />

and general waste management, as described by Williams <strong>et</strong> al., (2006) and Le<strong>in</strong>onen <strong>et</strong> al., (<strong>2012</strong>a;b). All<br />

modelled animal production systems <strong>in</strong>cluded farm energy, feed and water use and gaseous emissions from<br />

hous<strong>in</strong>g.<br />

The production systems <strong>in</strong> this study were considered to represent typical UK egg and broiler production<br />

(Table 1, Table 2) as described by Le<strong>in</strong>onen <strong>et</strong> al., (<strong>2012</strong>a;b). The farm energy consumption for heat<strong>in</strong>g,<br />

light<strong>in</strong>g, ventilation, feed<strong>in</strong>g and <strong>in</strong>c<strong>in</strong>eration of dead birds was based on average data from typical farms as<br />

provided by the <strong>in</strong>dustry. Information about the type and amount of bedd<strong>in</strong>g was also obta<strong>in</strong>ed from the <strong>in</strong>dustry.<br />

Additional data, such as LCI of agricultural build<strong>in</strong>gs and mach<strong>in</strong>ery, came from Williams <strong>et</strong> al.,<br />

(2006).

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