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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 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 />

27. A multi-scale m<strong>et</strong>hod for assess<strong>in</strong>g ecological <strong>in</strong>tensification <strong>in</strong><br />

aquaculture systems<br />

Aurélie Wilfart 1,2,* , Jéhane Prudhomme 1,2,3 , Jean-Paul Blanch<strong>et</strong>on 3 , Joël Aub<strong>in</strong> 1,2<br />

1 INRA, UMR1069 Sol Agro <strong>et</strong> hydrosystème Spatialisation, F-35000 Rennes, <strong>France</strong>, 2 AGROCAMPUS<br />

OUEST, F-35000 Rennes, <strong>France</strong>, 3 IFREMER, Laboratoire de Recherche Piscicole de Méditerranée,<br />

Chem<strong>in</strong> de Maguelone, 34250 Palavas-les-Flots, <strong>France</strong>, Correspond<strong>in</strong>g author. E-mail: aurelie.wilfart@rennes.<strong>in</strong>ra.fr<br />

To me<strong>et</strong> the challenges of produc<strong>in</strong>g more while lower<strong>in</strong>g impacts on ecosystems, new farm<strong>in</strong>g systems have<br />

to be designed. To def<strong>in</strong>e development strategies, a multi-scale assessment m<strong>et</strong>hod that estimates the tradeoff<br />

b<strong>et</strong>ween human demand and natural services, as well generates consistent performance <strong>in</strong>dicators on utilisation<br />

of natural resources and environmental emission levels based on the same s<strong>et</strong> of <strong>in</strong>put data is needed.<br />

<strong>LCA</strong> estimates resource use and potential environmental impacts throughout a product’s life cycle at global<br />

and regional scales (ISO, 2006) but does not consider the provision of ecosystem services or products (Ulgiati<br />

<strong>et</strong> al., 2006). Emergy account<strong>in</strong>g (EA) is an ecology-based tool developed to <strong>in</strong>tegrate all system <strong>in</strong>puts<br />

(environmental and economic values) us<strong>in</strong>g a common unit, solar emergy joule (Odum, 1996). EA <strong>in</strong>serts the<br />

productive cycle <strong>in</strong>to a local environmental context and quantifies the energy flows b<strong>et</strong>ween the environment<br />

and the production system. Through three contrast<strong>in</strong>g fish-farm<strong>in</strong>g systems, we attempted to demonstrate the<br />

<strong>in</strong>terest of a comb<strong>in</strong>ation of <strong>LCA</strong> and EA to def<strong>in</strong>e the major components of environmental susta<strong>in</strong>ability<br />

and ecological <strong>in</strong>tensification of fish farm<strong>in</strong>g and more globally of agricultural systems.<br />

The first system is a recirculat<strong>in</strong>g system (RSF) of Atlantic salmon depend<strong>in</strong>g highly on external <strong>in</strong>puts (feed<br />

and energy). The second one is extensive fish polyculture <strong>in</strong> a pond (PF1) with few external <strong>in</strong>puts. The last<br />

one is a small pond farm with use of external feeds. These systems were assessed accord<strong>in</strong>g the ISO standards<br />

for attributional <strong>LCA</strong> dur<strong>in</strong>g one production year. The assessment covered farm operations and transportation<br />

at all stages. Local emissions of nutrients were estimated us<strong>in</strong>g nutrient balance model<strong>in</strong>g and pond<br />

emissions were ref<strong>in</strong>ed to <strong>in</strong>clude nitrogen-fate factors. <strong>LCA</strong> results are presented as traditional midpo<strong>in</strong>t<br />

<strong>in</strong>dicators accord<strong>in</strong>g CML 2 basel<strong>in</strong>e 2001and are expressed by tonne of fish produced. Emergy account<strong>in</strong>g<br />

[3] is based on <strong>LCA</strong> system def<strong>in</strong>ition but <strong>in</strong>cludes also the contributions of natural systems (sun, ra<strong>in</strong>,<br />

groundwater, <strong>et</strong>c.) and provide <strong>in</strong>dicators to evaluate the efficiency of energy use and its quality dur<strong>in</strong>g the<br />

lifecycle. The chosen Emergy <strong>in</strong>dicators are: Percentage of renewability (%R); the Emergy Yield Ratio<br />

(EYR, ability to rely on local resources; Environmental Load<strong>in</strong>g Ratio (ELR, level of exploitation of nonrenewable<br />

resources compared to renewable ones).<br />

For 1 tonne of liv<strong>in</strong>g fish, RSF had higher potential impacts for NPPU and all the Emergy <strong>in</strong>dicators (Fig. 1).<br />

PF2 had higher potential impacts <strong>in</strong> comparison with PF1 except for water dependence. However, RSF had<br />

lower potential impacts for climate change, eutrophication, land comp<strong>et</strong>ition and water dependence than<br />

ponds, which reflects the level of <strong>in</strong>tensification of the systems. The consumption of energy (calculated by<br />

<strong>LCA</strong>, Figure 2) was similar for RSF and PF1 and higher for PF2. But, the contributors to this impact differed<br />

among the systems (direct energy use for ponds and feeds and direct energy used for RSF). The difference<br />

<strong>in</strong>%R b<strong>et</strong>ween systems was due to water orig<strong>in</strong>: for RSF water was pumped whereas for ponds it came essentially<br />

from ra<strong>in</strong> and water run-off. PF1 has a higher EYR, which means that it depends less on mark<strong>et</strong><br />

resources than RSF. The RSF higher value of ELR (7.98) <strong>in</strong>dicates a moderate environmental impact.<br />

The comb<strong>in</strong>ation of <strong>LCA</strong> and Emergy account<strong>in</strong>g on contrast<strong>in</strong>g systems provides a perspective of what<br />

ecological <strong>in</strong>tensification could mean <strong>in</strong> aquaculture: a decrease <strong>in</strong> potential impacts per unit mass of f<strong>in</strong>al<br />

products, especially for global warm<strong>in</strong>g, eutrophication and acidification; a decrease <strong>in</strong> dependence on mark<strong>et</strong>-based<br />

and external resources; and an <strong>in</strong>crease <strong>in</strong> the use of renewable natural resources and <strong>in</strong>put efficiency.<br />

This is particularly true for choices regard<strong>in</strong>g feed <strong>in</strong>gredients and the orig<strong>in</strong> of energy sources.<br />

References<br />

ISO, 2006. Environmental Management -Life Cycle Assessment- Pr<strong>in</strong>ciples and Framework. ISO 14040.<br />

Odum HT. Environmental Account<strong>in</strong>g: Emergy and Environmental Decision Mak<strong>in</strong>g. New York: Wiley;<br />

1996.<br />

Ulgiati S, Raugei M, Bargigli S., 2006. Overcom<strong>in</strong>g the <strong>in</strong>adequacy of s<strong>in</strong>gle-criterion approaches to Life<br />

Cycle Assessment. Ecol. Modell., 190:432-42.<br />

693

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