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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 6B: FISHIERIES, SOIL, AND EMERGY METHODS 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 />

Regionalised m<strong>et</strong>hod to assess soil erosion <strong>in</strong> <strong>LCA</strong><br />

Montse Núñez 1,2,* , Assumpció Antón 1,3 , Pere Muñoz 1 , Joan Rieradevall 4<br />

1 IRTA, Sostenipra. Centre de Cabrils 08348 Cabrils, Barcelona, Spa<strong>in</strong><br />

2 INRA-LBE, Avenue des Etangs 11000 Narbonne, <strong>France</strong><br />

3 Departament d’Eng<strong>in</strong>yeria Química, Universitat Rovira i Virgili 43003 Tarragona, Spa<strong>in</strong><br />

4 ICTA, Sostenipra. Universitat Autònoma de Barcelona 08193, Bellaterra, Barcelona, Spa<strong>in</strong><br />

Correspond<strong>in</strong>g author. E-mail: montse.nunez@supagro.<strong>in</strong>ra.fr<br />

ABSTRACT<br />

One of the most relevant and endangered ecosystem services worldwide due to land use change and <strong>in</strong>appropriate land use practices<br />

is the capacity of ecosystems to stabilize soils by prevent<strong>in</strong>g soil erosion. This research was meant to develop a m<strong>et</strong>hod to <strong>in</strong>clude the<br />

assessment of soil erosion <strong>in</strong> <strong>LCA</strong> on a global scale. The m<strong>et</strong>hod deals with land occupation impacts. As soil erosion depends on<br />

local conditions, characterisation factors were regionalised on a 5 arc-m<strong>in</strong>utes grid-cell level resolution. Two endpo<strong>in</strong>t <strong>in</strong>dicators<br />

cover<strong>in</strong>g the areas of protection damage to resources and damage to ecosystem quality were proposed. The m<strong>et</strong>hod was applied to the<br />

agricultural stage of five agricultural crop rotations. Further research efforts should aim at apply<strong>in</strong>g the m<strong>et</strong>hod beyond the agricultural<br />

stage and to identify a feasible and relevant spatial scale at which to aggregate characterisation factors to cope with data gaps on<br />

location of processes.<br />

Keywords: ecosystem services, land use, soil erosion, spatial differentiation, USLE<br />

1. Introduction<br />

Ecosystem services (ES) are resources and processes that are supplied by natural ecosystems. Despite<br />

their fundamental role <strong>in</strong> susta<strong>in</strong><strong>in</strong>g ecosystem function<strong>in</strong>g and human activities, they have been traditionally<br />

disregarded <strong>in</strong> life cycle oriented m<strong>et</strong>hods such as life cycle assessment (<strong>LCA</strong>), a m<strong>et</strong>hod that is meant to<br />

encourage environmental susta<strong>in</strong>ability. This oversight can lead to improper decisions. One of the most relevant<br />

and endangered ES worldwide due to land use change and unsusta<strong>in</strong>able land use management practices<br />

is the capacity of ecosystems to stabilise soils and to prevent soil sediment accumulation downstream. Soil<br />

erosion leads to a reduction of soil quality, as usually a large amount of nutrients is lost tog<strong>et</strong>her with the<br />

topsoil. Nutrient impoverished soils are less capable to provide ecosystem services. D<strong>et</strong>ached soil nutrients,<br />

such as phosphorous, organic matter and heavy m<strong>et</strong>als lead to pollution of water courses and lost particles to<br />

contam<strong>in</strong>ation of the air. Annually, humans cause de loss of 50 to 75 billion m<strong>et</strong>rics of soil (Harvey and Pimentel,<br />

1996). Agricultural lands account for 75% of the soil erosion worldwide, though it also occurs <strong>in</strong><br />

other human-modified ecosystems, such as dur<strong>in</strong>g the construction of roads and build<strong>in</strong>gs. Several m<strong>et</strong>hods<br />

deal with the issue of erosion <strong>in</strong> <strong>LCA</strong>. Cowell and Clift (2000) proposed a non-spatially-explicit <strong>in</strong>dicator,<br />

thus one generic characterisation factor (CF), for assessment of soil depl<strong>et</strong>ion, the static reserve life (years).<br />

The LANCA® calculation tool (Beck <strong>et</strong> al., 2010), based on Baitz (2002)’s m<strong>et</strong>hod, allows assess<strong>in</strong>g soil<br />

loss for specific cases of land use that can be used with<strong>in</strong> life cycle <strong>in</strong>ventory (LCI) databases. Saad <strong>et</strong> al.,<br />

(2011) adopted the LANCA® modell<strong>in</strong>g approach to derive CFs of land occupation and land transformation<br />

for Canada at different spatial scales. Van Zelm <strong>et</strong> al., (2011) proposed CFs for erosion due to agricultural<br />

land occupation for the world at the country level. The m<strong>et</strong>hods by Saad <strong>et</strong> al., (2011) and Van Zelm <strong>et</strong> al.,<br />

(2011) are spatially-resolved, that is, CFs <strong>in</strong>clude site-specific geospatial <strong>in</strong>formation, because land use impacts<br />

are highly <strong>in</strong>fluenced by local conditions regard<strong>in</strong>g climate, soil properties and landscape. So far, even<br />

though some proposals already exist for <strong>LCA</strong> to <strong>in</strong>tegrate soil erosion, approaches are still <strong>in</strong> its <strong>in</strong>fancy and<br />

the discussion on its characterisation is far from be<strong>in</strong>g s<strong>et</strong>tled.<br />

The objective of this research was to go one step further towards the <strong>in</strong>tegration of ES <strong>in</strong> <strong>LCA</strong> by develop<strong>in</strong>g<br />

a regionalised m<strong>et</strong>hod for the world to <strong>in</strong>clude land occupation impacts of any type of human activity<br />

on the erosion regulation ES. To show the applicability of the m<strong>et</strong>hod, erosion and environmental impacts<br />

from grow<strong>in</strong>g agricultural rotations with food and energy crops <strong>in</strong> Spa<strong>in</strong> were assessed.<br />

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

Two endpo<strong>in</strong>t <strong>in</strong>dicators cover<strong>in</strong>g the areas of protection (AoP) damage to resources and damage to ecosystem<br />

quality were def<strong>in</strong>ed. CFs for the two modelled impact pathways were regionalised on a 5 arcm<strong>in</strong>utes<br />

(approximately 10*10 km 2 ) resolution grid, without further aggregation on broader scales.<br />

523

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