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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 6C: POULTRY AND PORK 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 />

552<br />

Effect of <strong>et</strong>hics on <strong>in</strong>tegral ecological impact of organic eggs<br />

S.E.M. Dekker 1 , I.J.M. de Boer 2 , A.J.A. Aarn<strong>in</strong>k 3 , P.W.G., Groot Koerkamp 1<br />

1 Farm Technology Group, Wagen<strong>in</strong>gen University, P.O. box 17, 6700 AA, Wagen<strong>in</strong>gen, the N<strong>et</strong>herlands<br />

2 Animal Production Systems Group, Wagen<strong>in</strong>gen University, P.O. box 338, 6700 AH, Wagen<strong>in</strong>gen, the N<strong>et</strong>herlands<br />

3 Wagen<strong>in</strong>gen UR Livestock Research, P.O. box 65, 8200 AB, Lelystad, the N<strong>et</strong>herlands<br />

Correspond<strong>in</strong>g author. E-mail: sanne.dekker@wur.nl<br />

ABSTRACT<br />

Organic agriculture has a specific perspective on susta<strong>in</strong>ability, captured <strong>in</strong> their goal, def<strong>in</strong>ition and four pr<strong>in</strong>ciples of organic agriculture<br />

and result<strong>in</strong>g certification (IFOAM, <strong>2012</strong>). We refer to this perspective as the organic-<strong>et</strong>hical framework. For organic egg<br />

production, this framework implies three ma<strong>in</strong> requirements: (1) loose hen hous<strong>in</strong>g, (2) outdoor access, and (3) limited use of external<br />

resources, i.e. artificial fertilisers, pesticides, herbicides, gen<strong>et</strong>ically modified organisms, and medication. Our research objective<br />

was to assess the effect of these three requirements on the <strong>in</strong>tegral ecological impact of Dutch organic egg production. We approached<br />

this objective <strong>in</strong> three steps. In step 1 we compared life cycle assessment (<strong>LCA</strong>) results of egg production with and without<br />

an organic <strong>et</strong>hical framework. In step 2 we identified ma<strong>in</strong> ecological issues of current Dutch organic egg production by means of<br />

<strong>LCA</strong>. In step 3 we explored options to reduce <strong>in</strong>tegral ecological impact of Dutch organic egg production with<strong>in</strong> the boundaries of<br />

the organic <strong>et</strong>hical framework, i.e. replace s<strong>in</strong>gle-tiered with multi-tiered loose hen hous<strong>in</strong>g and replace imported with regional di<strong>et</strong><br />

<strong>in</strong>gredients.<br />

Comparison of battery cage with barn egg production shows that the requirement of loose hen hous<strong>in</strong>g results <strong>in</strong> a 12% to 176%<br />

higher impact for the ecological issues studied, except for phosphorus (P) deficit which was equal (Table 1). This higher impact is<br />

ma<strong>in</strong>ly expla<strong>in</strong>ed by a higher conversion of feed to eggs of loose housed hens (2.33 kg feed kg -1 egg) compared with hens <strong>in</strong> battery<br />

cages (1.99 kg feed kg -1 egg) (Dekker <strong>et</strong> al., 2011b). A second reason for the higher acidification potential of loose hen hous<strong>in</strong>g was<br />

that reduction of ammonia emission by dry<strong>in</strong>g and removal of manure <strong>in</strong> loose lay<strong>in</strong>g hen houses is problematic. Comparison of barn<br />

with free range egg production shows that the requirement of access to an outdoor run results <strong>in</strong> a relative small, i.e. 0% to 10%,<br />

<strong>in</strong>crease of the ecological impact (Table 1). Comparison of free range and organic egg production shows that the requirement of<br />

limited use of external resources results <strong>in</strong> a 10% lower global warm<strong>in</strong>g potential, a 15% lower energy use, a 93% lower fossil P use,<br />

a 108% lower nitrogen (N) surplus and a 114% lower P surplus, but a 82% higher land occupation, a 68% higher acidification potential,<br />

a 1767% higher N surplus and a 900% higher P deficit (Table 1). We found that differences <strong>in</strong> the ecological impact of egg<br />

production systems with and without limited use of external resources resulted ma<strong>in</strong>ly from differences <strong>in</strong> type and amount of fertilisation<br />

and conversion of feed to eggs. Multi-tiered hous<strong>in</strong>g to dry and remove manure (mitigation hous<strong>in</strong>g <strong>in</strong> Table 1; Dekker <strong>et</strong> al.,<br />

2011a) and production of di<strong>et</strong> <strong>in</strong>gredients and eggs <strong>in</strong> the same region to assure availability of manure and <strong>in</strong>crease yields (mitigation<br />

di<strong>et</strong> <strong>in</strong> Table 1; Dekker <strong>et</strong> al., <strong>2012</strong>b), have potential to reduce the ecological impact of organic egg production with<strong>in</strong> the <strong>et</strong>hical<br />

boundaries of organic egg production. If these mitigation options are applied we predict a lower energy use, fossil P use, N surplus<br />

and P surplus, but a higher global warm<strong>in</strong>g potential, land occupation, acidification potential, N deficit and P deficit for organic<br />

compared with battery cage egg production.<br />

We conclude that <strong>in</strong>creases of the ecological impact caused by the organic <strong>et</strong>hical framework ma<strong>in</strong>ly result from <strong>in</strong>efficient N and P<br />

management and <strong>in</strong>efficient conversion of feed to eggs. Issues <strong>in</strong> the current egg production cha<strong>in</strong> regard<strong>in</strong>g manure management<br />

are: (1) a lack of regionally available manure (Dekker <strong>et</strong> al., 2011b), (2) unbalanced application and N-P ratios of manure fertiliser,<br />

(3) high N-emissions from faeces <strong>in</strong> loose hous<strong>in</strong>g systems, and (4) loss of N and P from manure <strong>in</strong> the outdoor run (Dekker <strong>et</strong> al.,<br />

2011b; Dekker <strong>et</strong> al., <strong>2012</strong>a). The higher conversion of feed to eggs may be caused by: (1) a higher body mass of loose housed hens,<br />

(2) <strong>in</strong>creased freedom of movement, (3) prohibited use of external resources, caused by a worse am<strong>in</strong>o acid profile of the di<strong>et</strong>, (4)<br />

limited use of medication, and (5) a smaller number of hens per m 2 <strong>in</strong> the hen house, which generally results <strong>in</strong> a lower <strong>in</strong>door temperature<br />

(Van Knegsel and van Krimpen, 2008; Dekker <strong>et</strong> al., <strong>2012</strong>b; Dekker <strong>et</strong> al., 2011a). Research is required to d<strong>et</strong>erm<strong>in</strong>e<br />

wh<strong>et</strong>her <strong>in</strong>efficient N and P management and <strong>in</strong>efficient conversion of feed to eggs <strong>in</strong> organic egg production must be accepted as an<br />

implication of the organic <strong>et</strong>hical framework or can be further reduced with<strong>in</strong> the boundaries of the organic <strong>et</strong>hical framework.

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