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7th Workshop on Forest Fire Management - EARSeL, European ...

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ASSESSMENT OF POST FIRE VEGETATION RECOVERING IN PORTUGAL<br />

Abstract: The years of 2003 and 2005 were the two worst in the historical<br />

record of wildfires in Portugal. In 2003, the country was hit by the most<br />

devastating sequence of large fires, resp<strong>on</strong>sible for a total burnt area of 450<br />

000 ha, representing about 5% of the Portuguese mainland (Trigo et al.,<br />

2006). However, in 2005, Portugal suffered again str<strong>on</strong>g damages from forest<br />

fires that affected an area of 300 000 ha of forest and shrub. The years<br />

of 2003 and 2005 are of particular interest since they are both associated<br />

to extreme events, namely the heat wave episode of August 2003 and the<br />

severe drought of 2005.<br />

Based <strong>on</strong> m<strong>on</strong>thly values, from 1999 to 2008, of the normalized difference<br />

vegetati<strong>on</strong> index (NDVI), at the 1km x 1km spatial scale, as obtained from<br />

the VEGETATION instrument, a methodology is presented that allows identifying<br />

large burnt scars in Portugal and m<strong>on</strong>itoring vegetati<strong>on</strong> recovery<br />

throughout the pre and the post fire periods.<br />

1 - Introducti<strong>on</strong><br />

C. Gouveia<br />

Escola Superior de Tecnologia de Setúbal (EST)<br />

Instituto Politécnico de Setúbal, Setúbal, Portugal, cmgouveia@fc.ul.pt<br />

CGUL, IDL, University of Lisb<strong>on</strong>, Lisb<strong>on</strong>, Portugal<br />

C. DaCamara & R. Trigo<br />

CGUL, IDL, University of Lisb<strong>on</strong>, Lisb<strong>on</strong>, Portugal<br />

cdcamara@fc.ul.pt, rmtrigo@fc.ul.pt<br />

<strong>Fire</strong> represents <strong>on</strong>e of the main disturbances in Mediterranean ecosystems<br />

(Whelan, 1995), having a key role in the dynamics and structure of plant<br />

and animal communities (Gill et al., 1981), that are very inflammable and<br />

have low moisture c<strong>on</strong>tents. Plant communities in these ecosystems have<br />

high elasticity after fire because the species are able to regenerate by<br />

means of resprouting from fire resistant structures (B<strong>on</strong>d and Midgley,<br />

2001), or by germinati<strong>on</strong> of fire protected seeds stored in the soil or in the<br />

canopy (Lloret, 1998). Successi<strong>on</strong> after fires usually begins with herbaceous<br />

species, which often recover quickly as a result of the ‘mineral flush’<br />

after fires and their ability to col<strong>on</strong>ize open spaces (Christensen, 1994).<br />

Plant communities frequently evaluate to shrub-dominated populati<strong>on</strong>s<br />

with isolated trees, becoming dense forests in the end stage (Röder et al.,<br />

2008). Frequent fires may prevent plants from reaching sexual maturity<br />

237

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