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

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S.R. Freitas et al. 2010. The effect of highways on native vegetation <strong>and</strong> reserve distribution in the State of São Paulo<br />

676<br />

by them. Between the ecoregions (Olson et al. 2001), Serra do Mar coastal forests were the most<br />

affected by roads (51%). However, in relation to its cover, mangroves have more of its cover<br />

affected by roads (16%). About 55% of nature nature reserves were affected by roads. Five of<br />

them showed more than 30% of their territory affected by roads.<br />

There is more native vegetation cover as road distance increases (Figura 1). This relationship<br />

was nearly logistic for expressways (Figure 1).<br />

4. Discussion<br />

The State of São Paulo has a lower road density (0.15 km/km 2 ) than that considered as<br />

maximum for sustain populations of big predators (0.60 km/km 2 ; Forman <strong>and</strong> Alex<strong>and</strong>er 1998).<br />

However, those roads affect the distribution of native vegetation <strong>and</strong> threat the efficiency of<br />

nature reserves. Near roads could cause a significant increase of mortality rates for many<br />

wildlife populations, even overcoming hunting (Forman <strong>and</strong> Alex<strong>and</strong>er 1998).<br />

Almost 10% of State of São Paulo is ecologically affected by roads. Forman (2000) found a<br />

double proportion (about 20%) to United States of America. However, the State of São Paulo<br />

has a very lower road density than USA (0.41 km/km 2 ; Forman 2000), indicating that more<br />

native vegetation is under threat of roads in our study area. Even many states of USA have<br />

higher road densities than State of São Paulo (0.15 km/km 2 ): Misouri (1.89 km/km 2 ), Arkansas<br />

(1.23km/km 2 ) <strong>and</strong> Oklahoma (1.18 km/km 2 ; La Rue <strong>and</strong> Nielsen 2008).<br />

Laurance et al. (2009) state that non-paved roads represent a lower impact on vegetation <strong>and</strong><br />

wildlife in tropical forests than paved roads because they usually are inaccessible during raining<br />

season (summer). However, our study showed that non-paved <strong>and</strong> paved roads affect more than<br />

highways <strong>and</strong> expressways because they are more abundant <strong>and</strong> spread all over the territory,<br />

showing higher densities (0.06 km/km 2 <strong>and</strong> 0.07 km/km 2 respectivelly) than highways (0.01<br />

km/km 2 ) <strong>and</strong> expressways (0.01 km/km 2 ).<br />

As expected, the dominant vegetation type - Serra do Mar Coastal <strong>Forest</strong>s - was the most<br />

affected by roads. Serra do Mar Coastal <strong>Forest</strong>s is distributed along coastline as well as many of<br />

road network in Brazil, representing one of the most important connection axis for national<br />

transportation (north-south). However, in proportion mangroves are highly affected by roads for<br />

the same reason.<br />

Half of natural reserves is affected by roads. Five of them have more than 30% <strong>and</strong> three of<br />

them have more than 60% of their territory affected by roads, which represents a threat for their<br />

biodiversity. Roads facilitate hunter access <strong>and</strong> increase the probability of collision by vehicles<br />

(Laurance et al. 2009). Nature reserves near roads are probably under more conflicts with<br />

human population <strong>and</strong> more vulnerable to environmental degradation.<br />

There is more native vegetation as far as the road is. Roads act as atractor to l<strong>and</strong> use <strong>and</strong><br />

deforestation (Nagendra et al. 2003; Freitas et al. 2010). For instance, in the Amazon <strong>Forest</strong>,<br />

about 95% of deforestation occurred at most 50 km far from roads (Laurance et al. 2009).<br />

Expressways are not too densely distributed as other road types, however they show a nearly<br />

logistic relationship to native vegetation cover indicating a strong negative effect to the nearby<br />

native vegetation. Thus, road distance could be used as indicator to predict the distribution of<br />

native vegetation in the future. We suggest that in order to improve conservation <strong>and</strong> restoration<br />

strategies, the effect of highways should be carefully considered, prioritizing remote areas.<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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