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

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C. Carvalho-Santos 2010. Fine-scale mapping of High Nature Value farml<strong>and</strong>s<br />

185<br />

farml<strong>and</strong>). The objective is thus not to identify HNVf vs. non-HNVf areas, but instead to<br />

provide a hierarchic zoning of nature value. The parish-level HNVf map is obtained from the<br />

area-weighted mean value of farml<strong>and</strong> patches inside the parish, <strong>and</strong> the final score is expressed<br />

without considering the total extent of each parish.<br />

3.3. Testing the new framework in Northern Portugal<br />

The region chosen to test the methodology was the Baixo Tâmega, in the north of Portugal, a<br />

mosaic of different agrarian systems <strong>and</strong> l<strong>and</strong>scapes that have, in most cases, been suffering<br />

ab<strong>and</strong>onment in the last few decades. Nonetheless, there are some areas with more specialized<br />

<strong>and</strong> intensive agricultural systems, mostly related to wine production along the Douro <strong>and</strong><br />

Tâmega valleys. There are also non-cultivated areas, mostly in mountain areas, with seminatural<br />

vegetation associated with extensive grazing.<br />

Due to the regular presence of semi-natural vegetation types, most of these farml<strong>and</strong>s are<br />

classifiable as HNVf areas (Andersen et al. 2003). The final maps (figure 2) provide<br />

complementary views of HNVf distribution in the area. In fact, the patch-level map identifies<br />

HNVf areas in most of the study area except for the eastern mountain areas (where forestry<br />

prevails), but the parish-level map identifies small farml<strong>and</strong> areas in these mountains as the ones<br />

with the highest nature value.<br />

4. Discussion<br />

The concept of HNVf, areas associated with low intensity farming, has become very important<br />

regarding agrobiodiversity protection under the Rural Development Programs. It is already used<br />

in many European countries from different perspectives, <strong>and</strong> is starting to be more <strong>and</strong> more<br />

included in the political agricultural context. This could mean economic support to these areas,<br />

through European financial instruments.<br />

L<strong>and</strong> cover, farming characteristics <strong>and</strong> species distribution data are the central datasets in the<br />

common approach to the identification of HNVf at European <strong>and</strong> national levels. The<br />

availability <strong>and</strong> the quality of farming <strong>and</strong> species datasets is a recurrent problem. In fact,<br />

mapping methodologies using l<strong>and</strong> cover datasets at different scales can provide very distinct<br />

HNVf maps.<br />

A new refined methodology based on l<strong>and</strong> cover data, l<strong>and</strong>scape features, farming attributes <strong>and</strong><br />

natural value/conservation data was designed to map HNVf at a local scale. The use of datasets<br />

on nature value including information on the valuation of ecosystem services inferred from<br />

l<strong>and</strong>-use dataset is considered an advantage. In the literature, HNVf is stressed to promote<br />

biodiversity in agroecosystems. In our novel methodology, we suggest a stronger emphasis on a<br />

l<strong>and</strong>scape perspective <strong>and</strong> on the ecosystem services provided by semi-natural areas close to<br />

cropl<strong>and</strong>.<br />

This methodology appears as an important instrument in the identification of HNVf areas to<br />

support policy implementation in the framework of agrobiodiversity protection. It can be used<br />

either spatially, comparing the extent of potential HNVf areas among different regions, or<br />

temporally, comparing changes in extent of HNVf in one region at different times as a<br />

monitoring effort. Additionally, we expect with future research to check the possibility to adapt<br />

this methodology in other EU countries, where local l<strong>and</strong> cover datasets are usually available.<br />

References<br />

Andersen E., Baldock D., Bennet H., Beaufoy G., Bignal E., Brouwer F., Elbersen B., Eiden G.,<br />

Godeschalk F., Jones G., MaCracken D., Nieuwenhuizen W., Eupen M., Hennekens S.<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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