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LCA Food 2012 in Saint Malo, France! - Manifestations et colloques ...

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PLENARY SESSION 3: METHODS FOR BIODIVERSITY AND SOIL QUALITY 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 />

Assess<strong>in</strong>g land use impacts on biodiversity on a regional scale: the case<br />

of crop production <strong>in</strong> Kenya<br />

Laura de Baan 1* , Michael Curran 2 , Stefanie Hellweg 2 , Thomas Koellner 3<br />

1 NSSI, Institute for Environmental Decisions, ETH Zurich, Universitätstr. 22, 8092 Zurich, Switzerland<br />

2 ESD, Institute for Environmental Eng<strong>in</strong>eer<strong>in</strong>g, ETH Zurich, Schafmattstr. 6, 8093 Zurich, Switzerland<br />

3 Professorship of Ecological Services, University of Bayreuth, Universitätsstr. 30, 95440 Bayreuth, Germany<br />

Correspond<strong>in</strong>g author. E-mail: laura.debaan@<strong>et</strong>hz.env.ch<br />

ABSTRACT<br />

In current Life Cycle Impact Assessment (LCIA), impacts of land use on biodiversity are often assessed at a local (e.g. field) scale.<br />

The relevance of these local impacts is often limited, as species that are not able to survive on agricultural land may persi st <strong>in</strong> adjacent<br />

undisturbed areas. However, if habitat is scarce on a regional scale, the risk of regional or even global ext<strong>in</strong>ction <strong>in</strong>creases. Here,<br />

we present a m<strong>et</strong>hod to upscale local land use impacts <strong>in</strong> LCIA to the ecoregional scale us<strong>in</strong>g an adapted species-area relationship<br />

model. This model is applied to land use <strong>in</strong> Kenya, where conversion of natural habitats to small and large-scale farms is threaten<strong>in</strong>g<br />

areas of high biodiversity value. As we use globally available data as a start<strong>in</strong>g po<strong>in</strong>t, this m<strong>et</strong>hod is potentially applicable to other<br />

world regions and provides a more environmentally relevant assessment of the land use impacts of agricultural products.<br />

Keywords: biodiversity, land use, regional assessment, Kenya, spatial scales<br />

1. Introduction<br />

Agricultural production occupies about one third of the global terrestrial surface. This causes major<br />

impacts on ecosystems and biodiversity at multiple spatial scales (e.g. local, regional and global). To<br />

evaluate options for reduc<strong>in</strong>g these impacts, decision-support tools such as life cycle assessment (<strong>LCA</strong>)<br />

should help decision-makers to obta<strong>in</strong> the relevant environmental <strong>in</strong>formation related to their product or<br />

product system. In many life cycle impact assessment (LCIA) m<strong>et</strong>hods for land use, local impacts on<br />

biodiversity are assessed (e.g. de Baan <strong>et</strong> al., <strong>2012</strong>), which reflect the direct impacts on the used piece of land<br />

(e.g. by remov<strong>in</strong>g forest-species to cultivate crops). These local impacts are traditionally assessed as<br />

potentially disappeared fraction of species (PDF), represent<strong>in</strong>g relative changes <strong>in</strong> species richness b<strong>et</strong>ween<br />

a used piece of land and a reference situation (e.g. undisturbed natural veg<strong>et</strong>ation). However, these local<br />

assessment m<strong>et</strong>hods do not provide the <strong>in</strong>formation relevant for decisions-makers concerned about<br />

conservation of species at larger scales, i.e. the absolute loss of species <strong>in</strong> a region or globally. Local<br />

extirpation of species from a used piece of land can be fully reversible if the species can survive <strong>in</strong> adjacent<br />

wild areas, and thus recolonize the field after its abandonment. As local conversion of habitat cont<strong>in</strong>ues,<br />

ext<strong>in</strong>ction risk <strong>in</strong>creases to an extent that there is not enough habitat rema<strong>in</strong><strong>in</strong>g at a regional or global level,<br />

lead<strong>in</strong>g to regional or global ext<strong>in</strong>ction, respectively. Global ext<strong>in</strong>ction is fully irreversible and thus of<br />

highest environmental concern. An assessment that <strong>in</strong>corporates both local and regional factors requires<br />

additional <strong>in</strong>formation on the landscape surround<strong>in</strong>g the agricultural field, and is thus more data demand<strong>in</strong>g.<br />

In this paper, we present a m<strong>et</strong>hod to upscale impacts from local to regional scale and to transform<br />

relative <strong>in</strong>to absolute species losses. We apply the m<strong>et</strong>hod <strong>in</strong> a prelim<strong>in</strong>ary case study of agricultural<br />

production and mammal species diversity <strong>in</strong> Kenya, us<strong>in</strong>g globally available data.<br />

1.1. The case: agricultural production <strong>in</strong> Kenya<br />

Previous land use LCIA m<strong>et</strong>hods have been mostly developed for the European (e.g. De Schryver <strong>et</strong> al.,<br />

2010; Koellner and Scholz 2008) or North American context (e.g. Geyer <strong>et</strong> al., 2010), and to our knowledge,<br />

only one study has focused on the African cont<strong>in</strong>ent (Burke <strong>et</strong> al., 2008). We chose Kenya as a case study to<br />

assess regional impacts on biodiversity because it harbours biodiverse areas at threat from human encroachment.<br />

Kenya hosts two global biodiversity hotspots that have already lost more than 70% of their natural<br />

habitats due to human activities. This largely results from an overlap <strong>in</strong> agricultural suitability and biological<br />

value, which are both concentrated <strong>in</strong> South-Central and Western Kenya, and have attracted a dense and<br />

grow<strong>in</strong>g population caus<strong>in</strong>g cont<strong>in</strong>ued land use change or <strong>in</strong>tensification and encroachment of protected<br />

areas. Large shares of species rich ecosystems have been converted to small-holder and large-scale agricultural<br />

land to produce subsistence or export-orientated cash crops such as tea, coffee, cashews, and flowers. A<br />

strong dependence of the often poor rural populations on ecosystems for food, fuel and graz<strong>in</strong>g land, coupled<br />

with <strong>in</strong>creas<strong>in</strong>g population densities puts further pressures on ecosystems (Biggs <strong>et</strong> al., 2004). A more recent<br />

threat to biodiversity comes from an <strong>in</strong>crease <strong>in</strong> land excisions and sales to foreign <strong>in</strong>vestors for the purpose<br />

of large-scale, export-oriented farm<strong>in</strong>g for food and biofuels production (Odhiambo 2011).<br />

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