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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 />

Figure 2. Rema<strong>in</strong><strong>in</strong>g share of natural<br />

habitat <strong>in</strong> and around Kenya<br />

(country marked as white l<strong>in</strong>e)<br />

344<br />

Figure 3. Modelled loss of nonendemic<br />

mammals<br />

Figure 4. Modelled loss of endemic<br />

mammals<br />

4. Discussion<br />

In this paper we assessed absolute regional land use impacts (i.e. numbers of species that potentially disappear<br />

regionally due to land use) by upscal<strong>in</strong>g local relative impacts (i.e. the potential fraction of locally<br />

disappeared species). Absolute and regional characterisation factors are b<strong>et</strong>ter suited to compare land use<br />

impacts across ecosystems and across land use types. In contrast to local relative impacts, the presented regional<br />

absolute characterisation factors reflect differences of land use impacts occurr<strong>in</strong>g <strong>in</strong> species rich or<br />

species poor ecosystems with high or low levels of endemism, or of land use impacts occurr<strong>in</strong>g <strong>in</strong> highly<br />

disturbed or prist<strong>in</strong>e ecosystems. In addition, they directly reflect conservation targ<strong>et</strong>s that aim to prevent<br />

regional (occupation and transformation impacts) and global ext<strong>in</strong>ction (permanent impacts).<br />

The presented approach used globally available data to allow transferr<strong>in</strong>g the approach to other world regions.<br />

However, the accuracy of such global data <strong>in</strong> the regional context still has to be further assessed. B<strong>et</strong>ter<br />

regional land use maps, more region- and taxon-specific habitat suitability scores and b<strong>et</strong>ter data on restoration<br />

times would improve the credibility of the results. Modell<strong>in</strong>g species ext<strong>in</strong>ction at regional and global<br />

scales for use <strong>in</strong> <strong>LCA</strong> improves the <strong>in</strong>terpr<strong>et</strong>ability of results, but also <strong>in</strong>troduces many uncerta<strong>in</strong>ties. The<br />

validity of the matrix-SAR model still has to be further tested, as many important factors driv<strong>in</strong>g ext<strong>in</strong>ction<br />

risk were not considered here (e.g. h<strong>et</strong>erogeneity with<strong>in</strong> ecoregions, temporal dynamics, connectivity of<br />

habitats).<br />

5. Conclusion<br />

Upscal<strong>in</strong>g local land use impacts to regional impacts provides more environmentally relevant <strong>in</strong>formation<br />

to policy makers on the effects of land use on biodiversity. The presented m<strong>et</strong>hod can potentially help to<br />

b<strong>et</strong>ter evaluate the environmental impacts of globally traded agricultural goods orig<strong>in</strong>at<strong>in</strong>g from Kenya or<br />

other world regions. As we use globally available data as a start<strong>in</strong>g po<strong>in</strong>t, this m<strong>et</strong>hod can be applied to other<br />

world regions. However, the robustness and validity of the presented characterisation factors still needs to be<br />

evaluated and tested aga<strong>in</strong>st more d<strong>et</strong>ailed data and techniques <strong>in</strong> a vari<strong>et</strong>y of s<strong>et</strong>t<strong>in</strong>gs.<br />

6. References<br />

Biggs, R., Bohensky, E., Desanker, P. V., <strong>et</strong> al., , 2004. Nature Support<strong>in</strong>g People: The Southern African Millennium Ecosystem<br />

Assessment. Integrated report. Pr<strong>et</strong>oria, South Africa: Council for Scientific and Industrial Research.<br />

Burke, A., Kyläkorpi, L., Rydgren, B., Schneeweiss, R., 2008. Test<strong>in</strong>g a scand<strong>in</strong>avian biodiversity assessment tool <strong>in</strong> an African<br />

desert environment. Environ. Manage. 42: 698–706.<br />

de Baan, L., Alkemade, R., and Koellner, T., <strong>2012</strong>. Land use impacts on biodiversity <strong>in</strong> <strong>LCA</strong>: a global approach. Int. J. Life Cycle<br />

Assess. (onl<strong>in</strong>e first).<br />

De Schryver, A. M., Goedkoop, M. J., Leuven, R. S. E. W., and Huijbregts, M. A. J., 2010. Uncerta<strong>in</strong>ties <strong>in</strong> the application of the<br />

species area relationship for characterisation factors of land occupation <strong>in</strong> life cycle assessment. Int. J. Life Cycle Assess. 15:<br />

682-691.<br />

Drakare, S., Lennon, J., and Hillebrand, H., 2006. The impr<strong>in</strong>t of the geographical, evolutionary and ecological context on speciesarea<br />

relationships. Ecol L<strong>et</strong>t 9: 215-227.<br />

ESA, 2009. GlobCover land cover map, v2.3. European Space Agency.

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