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

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M. Ortega et al. 2010. Monitoring vulnerability of the Spanish forest l<strong>and</strong>scapes: the SISPARES approach<br />

388<br />

2.1 Data analysis<br />

In each square FLV has been calculated as:<br />

FLV=FLF*RD/100 (1)<br />

Where RD is road density in the square <strong>and</strong> FLF is an index of forest l<strong>and</strong>scape fragility, which<br />

has been calculated as:<br />

FLF=IJI*WFN (2)<br />

Where IJI is an index of interspersion <strong>and</strong> juxtaposition that considers the neighbourhood<br />

relations between patches. Each patch is analysed for adjacency with all other patch types <strong>and</strong><br />

measures the extent to which patch types are interspersed i.e. equally bordering other patch<br />

types. The IJI is a relative index that represents the observed level of interspersion as a<br />

percentage of the maximum possible given the total number of patch types (McGarigal et al.<br />

1995).<br />

m = number of patch types,<br />

(3)<br />

E ik = length of edge between patch type i <strong>and</strong> patch type k.<br />

IJI approaches 0 when the distribution of adjacencies among unique patch types becomes<br />

increasingly uneven. IJI = 100 when all patch types are equally adjacent to all other patch types<br />

(i.e., maximum interspersion <strong>and</strong> juxtaposition.<br />

WFN in equation 2 is the contrast between forest <strong>and</strong> non forest areas in the square <strong>and</strong> is<br />

measured as:<br />

(1-| <strong>Forest</strong> area – Non <strong>Forest</strong> area|)/100 (4)<br />

A l<strong>and</strong>scape square will be more fragile when a higher WFN <strong>and</strong> a higher IJI have.<br />

Besides if the square has a higher road density it will be a high value of vulnerability.<br />

Fragstat software was used to calculate the IJI index. Repeated measures ANOVA was used to<br />

analyse FLV, FLF, IJI, WFN <strong>and</strong> RD of 206 squares of SISPARES in three dates: 1956, 1984<br />

<strong>and</strong> 1998 by means of Statistica softhware.<br />

3. Results <strong>and</strong> discussion<br />

FLV index showed a significant increase in Spain along the study period (F=3.36; p=0.04) as it<br />

is observed in the figure 1. The increase between 1956 <strong>and</strong> 1984 was 2% <strong>and</strong> during the last 24<br />

years of this study period the mean number of forest fires was 3,940 per year (Table 2).<br />

Between 1984 <strong>and</strong> 1998 data, the increase of FLV was 12% more <strong>and</strong> only during these 14<br />

years the mean number of forest fires was 15,844 per year. In the same way the burnt areas were<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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