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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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GROUP 4, SESSION B: CROP 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 />

118. Allocat<strong>in</strong>g environmental burdens from fertilisation to crops <strong>in</strong> a<br />

rotation<br />

Alice Gueud<strong>et</strong> 1,* , Hervé Bossuat 1 , Marilys Pradel 2 , Afsaneh Lellahi 3 , Aurélie Tailleur 3<br />

1 ACTA, le réseau des <strong>in</strong>stituts des filières animales <strong>et</strong> végétales, 149 rue de Bercy – Paris, F-75595, <strong>France</strong>,<br />

2 Irstea, UR TSCF Technologies <strong>et</strong> systèmes d'<strong>in</strong>formation pour les agrosystèmes, Doma<strong>in</strong>e des Palaqu<strong>in</strong>s –<br />

Montoldre, F-03150, <strong>France</strong>, 3 ARVALIS-Institut du végétal, Service Agronomie Economie Environnement,<br />

Boigneville, F-91720, <strong>France</strong>, Correspond<strong>in</strong>g author. E-mail: alice.gueud<strong>et</strong>@acta.asso.fr<br />

Allocation is a complex issue for <strong>LCA</strong> practitioners. Due to many allocation m<strong>et</strong>hods, the choice b<strong>et</strong>ween<br />

them can have a significant impact on the results. It is particularly relevant when apply<strong>in</strong>g <strong>LCA</strong> to assess<br />

fertilisation impacts as all nutrients brought by fertilisers are not all taken up by the crop <strong>in</strong> the system under<br />

study but rema<strong>in</strong> available for future crops <strong>in</strong> rotation. Crop residues also produce nutrients which r<strong>et</strong>urn to<br />

soil after harvest. Hence, these nutrients can be considered as co-products from the crop.<br />

Fertilisation contributes highly to different potential impacts for crops: it <strong>in</strong>duces <strong>in</strong> particular 30-60% of the<br />

primary energy consumption, 60-80% of the global warm<strong>in</strong>g potential, 90% of the eutrophication potential,<br />

80-90% of the acidification potential (personal communication from ARVALIS and UNIP). Thus, allocation<br />

m<strong>et</strong>hod used to allocate fertilisers to crops can be decisive for the <strong>LCA</strong> outcomes.<br />

Allocat<strong>in</strong>g burdens from fertilisation is a subject of concern s<strong>in</strong>ce the beg<strong>in</strong>n<strong>in</strong>g of agricultural <strong>LCA</strong> and<br />

different reports dealt with this issue (Audsley <strong>et</strong> al. 2003; Gac <strong>et</strong> al., 2006). Recently, a work<strong>in</strong>g group (Agri<br />

Footpr<strong>in</strong>t M<strong>et</strong>hod, Blonk 2010) made recommendations to take <strong>in</strong>to account m<strong>in</strong>eral and organic nutrients<br />

from synth<strong>et</strong>ic fertilisers, manure and crop residues. However, these references rarely lead to common accepted<br />

rules <strong>in</strong> term of m<strong>et</strong>hodology or their suggestions are not always easy to apply because of data availability.<br />

In the framework of a project aim<strong>in</strong>g at assess<strong>in</strong>g environmental impacts of crop fertilisation by <strong>LCA</strong>, a bibliography<br />

review has been conducted to identify the different solutions <strong>in</strong>volved <strong>in</strong> <strong>LCA</strong> literature regard<strong>in</strong>g<br />

allocation rules for PK nutrients <strong>in</strong> synth<strong>et</strong>ic fertilisers, N from manure and N from crop residues (Table 1).<br />

Consider<strong>in</strong>g this large range of choices, allocation rules have been selected <strong>in</strong> order to be tested on study<br />

cases which will simulate levers to reduce impacts from fertilisation such as cover crops <strong>in</strong>troduction and the<br />

use of different types of fertilisers (m<strong>in</strong>eral and organic). These simulations will assess the rules feasibility<br />

and identify the most consistent. This work will result <strong>in</strong> recommendations about cropp<strong>in</strong>g plan allocation<br />

for m<strong>in</strong>eral and organic N, P, K nutrients and for crop residues, regard<strong>in</strong>g the aim of the study and the data<br />

availability.<br />

References<br />

Audsley <strong>et</strong> al. 2003, Harmonisation of environmental life cycle assessment for agriculture, f<strong>in</strong>al report DG<br />

VI Agriculture 2003, 101p.<br />

Blonk <strong>et</strong> al. 2010, M<strong>et</strong>hodology for assess<strong>in</strong>g carbon footpr<strong>in</strong>ts of horticultural products - A study of m<strong>et</strong>hodological<br />

issues and solutions for the development of the Dutch carbon footpr<strong>in</strong>t protocol for horticultural<br />

products Blonk Milieu Advies p.36-40<br />

European Commission 2010, ILCD Handbook, General Guide for Life Cycle Assessment – d<strong>et</strong>ailed guidance,<br />

394p.<br />

Gac <strong>et</strong> al. 2006, GES’TIM Guide méthodologique pour l’estimation des impacts des activités agricoles sur<br />

l’eff<strong>et</strong> de serre, Version 1.2, 156p.<br />

William <strong>et</strong> al. 2006, D<strong>et</strong>erm<strong>in</strong><strong>in</strong>g the environmental burdens and resource use <strong>in</strong> the production of agricultural<br />

and horticultural commodities. Defra project report IS0205, 97p.<br />

831

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