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Landscapes Forest and Global Change - ESA - Escola Superior ...

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T. Höbinger et al. 2010. Impact of changing cultivation systems on the l<strong>and</strong>scape structure of La Gamba<br />

61<br />

compact shaped l<strong>and</strong>scape patches (O’Neill et al. 1988). With exception of section Bonito 2 all<br />

rural sections had higher fractal dimensions than forests. Due to the inclusion of linear<br />

l<strong>and</strong>scape elements these high values indicate rather a high density of linear elements than a<br />

high complexity of the matrix. The comparison of AREA <strong>and</strong> PD clearly showed differences in<br />

the configuration of the patch types. Primary forests had the biggest extend, but comprised only<br />

few patches. Secondary forests were characterized by a much smaller AREA <strong>and</strong> clearly higher<br />

PD because most of these forests were formerly used as pastures. Riparian vegetation covered<br />

only smaller areas, but showed a relatively high PD because many small patches <strong>and</strong> strips of<br />

remnant riparian forests were present along the riversides.<br />

The expansion of oil palm plantations causes considerable changes in the l<strong>and</strong>scape matrix.<br />

Pasture-dominated parts were richer in ecologically valuable elements such as live fences <strong>and</strong><br />

riparian vegetation, while within <strong>and</strong> along oil palm plantations mainly ecologically futile<br />

elements such as roads <strong>and</strong> drainage ditches were found. Compared to pastures plantations had a<br />

bigger AREA, but lower PD which reflects that they are labor-intensive permanent cultures of<br />

great extend. The l<strong>and</strong> use map (see Figure 1) shows that, conversely to pastures, oil palm<br />

plantations were never divided <strong>and</strong> scarcely bordered by live fences. Hence, the expansion of<br />

these plantations involves the risk of a simplification of l<strong>and</strong>scapes <strong>and</strong> the loss of small natural<br />

l<strong>and</strong>scape elements in agricultural areas. This can lead to a significant reduction or shift of the<br />

biodiversity in tropical ecosystems affected by oil palm plantations.<br />

Oil palms are a globally rapidly exp<strong>and</strong>ing crop which has already replaced large areas of<br />

natural forest in many tropical countries such as Malaysia or Indonesia <strong>and</strong> this progress is still<br />

going on. These plantations entail many other problems such as habitat fragmentation, pollution,<br />

loss of biodiversity <strong>and</strong> soil destruction. Because oil palms are unsuitable habitat for most forest<br />

species they can act as severe barrier to animal movement (Fitzherbert et al. 2008). To maintain<br />

the exchange of plants <strong>and</strong> animals between the forest areas surrounding the village La Gamba,<br />

the conservation of live fences <strong>and</strong> other natural habitats is of great importance. As the mean<br />

patch area of pastures was relatively big (2.52 ha) <strong>and</strong> the density of live fences was rather low<br />

(20.0 m per ha farml<strong>and</strong>) more live fences could be established by dividing pastures into smaller<br />

paddocks (Höbinger 2010). This measure would improve the connectivity of forest patches,<br />

increase the tree cover within farml<strong>and</strong>, <strong>and</strong> provide a high conservation value of the<br />

agricultural l<strong>and</strong>scape mosaic in its unconnected gallery forests (Seaman <strong>and</strong> Schulze 2009).<br />

References<br />

Botequilha Leitão, A.B., Miller, J., Ahern, J. <strong>and</strong> McGarigal, K., 2006. Measuring <strong>L<strong>and</strong>scapes</strong>.<br />

A Planner's H<strong>and</strong>book. Isl<strong>and</strong> Press, Washington DC, 272 p.<br />

Cushman, S.A., McGarigal, K. <strong>and</strong> Neel, M.C., 2008. Parsimony in l<strong>and</strong>scape metrics: Strength,<br />

universality, <strong>and</strong> consistency. Ecological Indicators, 8: 691–703.<br />

Fitzherbert, E.B, Struebig, M.J., Morel, A., Danielsen, F., Brühl, C.A., Donald, P.F., <strong>and</strong><br />

Phalan, B., 2008. How will oil palm expansion affect biodiversity Trends in Ecology <strong>and</strong><br />

Evolution, 23: 538-545.<br />

Harvey, C.A., Guindon, C.F., Haber, W.A., Hamilton DeRosier, D. <strong>and</strong> Murray, K.G., 2008a.<br />

La importancia de los fragmentos de bosque, los árboles dispersos y las cortinas<br />

rompevientos para la biodiversidad local y regional: el caso de Monteverde, Costa Rica.<br />

In: Harvey C.A. <strong>and</strong> Saénz J.C. (Eds.). Evaluación y conservación de biodiversidad en<br />

paisajes fragmentados de Mesoamérica. Santo Domingo de Heredia, Cosa Rica: Instituto<br />

Nacional de Biodiversidad. Costa Rica. INBio: 289-325.<br />

Harvey, C.A., Sáenz, J.C. <strong>and</strong> Montero, J., 2008b. Conservación de la biodiversidad en<br />

agropaisajes de Mesoamérica: ¿que hemos aprendido y qué nos falta conocer In: Harvey<br />

C.A. <strong>and</strong> Saénz J.C. (Eds.). Evaluación y conservación de biodiversidad en paisajes<br />

<strong>Forest</strong> <strong>L<strong>and</strong>scapes</strong> <strong>and</strong> <strong>Global</strong> <strong>Change</strong>-New Frontiers in Management, Conservation <strong>and</strong> Restoration. Proceedings of the IUFRO L<strong>and</strong>scape Ecology<br />

Working Group International Conference, September 21-27, 2010, Bragança, Portugal. J.C. Azevedo, M. Feliciano, J. Castro & M.A. Pinto (eds.)<br />

2010, Instituto Politécnico de Bragança, Bragança, Portugal.

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