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Riconquistiamo il paesaggio - ACCA software SpA

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184<br />

CAPITOLO III - Paesaggi d’Italia<br />

We did not directly measured any relationship among land-use/land-cover changes and biodiversity<br />

patterns over the entire Italy but considering their geographical distribution, the pattern<br />

of changes in land-use/land-cover that we measured show interesting relations to concurrent<br />

and important changes of biodiversity patterns. From 1960 to 2000, the Alps and the Apennines<br />

showed a substantial increase in FOREST, wh<strong>il</strong>e agriculture and human population dropped.<br />

As a result of land abandonment, the floristic species richness is decreasing in higher successional<br />

stages and, depending on the altitude, the structural diversity of the landscape is changing<br />

(Höchtl et al. 2005). In the same time period and in the same area, Italy has experienced a real<br />

“renaissance” of large vertebrates: wolves increased from about 100 individuals in the 1970s<br />

– localized in the central Apennines – to more than 500 individuals in 2000, spreading from the<br />

southern Apennines to the central Alps (Boitani & Ciucci 2000); w<strong>il</strong>d ungulate populations increased<br />

both in numbers and distribution (Boitani et al. 2003); brown bears (Ursus arctos) were<br />

successfully reintroduced in the eastern Alps wh<strong>il</strong>e the central Italy subspecies (U. arctos<br />

marsicanus) has seemingly increased its range (Boitani et al. 2003); temperate forest birds are<br />

following the same pattern, increasing their ranges throughout the mountain areas of the Mediterranean<br />

region (Preiss et al. 1997; Laiolo et al. 2004; Tellini-Florenzano 2004).<br />

Almost the opposite situation can be found in Sardinia, Sic<strong>il</strong>y and in the coastal areas, among the<br />

most important portions of the Mediterranean hotspot for biodiversity conservation (Blondel<br />

& Aronson 1999; Méda<strong>il</strong> & Quézel 1999). Here total agriculture increased (Sardinia) or remained<br />

stable (Sic<strong>il</strong>y and coastal areas), wh<strong>il</strong>e FOREST remained stable (coastal areas) or increased<br />

(Sic<strong>il</strong>y and particularly Sardinia). ARTIFICIAL sharply increased indicating a substantial increase<br />

of human presence, mainly linked to an increase in tourist activities. In Sardinia and the coastal<br />

areas, the drastic decrease of PASTURE followed the decrease in traditional sheep grazing, and<br />

represents an important conservation problem: the little bustard (Tetrax tetrax), a species of<br />

open spaces, is disappearing from continental Italy and its numbers are critically low in Sardinia<br />

(de Juana & Martinez 2001; Wolff et al. 2001); the griffon vulture (Gyps fulvus), dependent on<br />

traditional pasture, has completely disappeared from continental Italy (Dentesani et al. 1996),<br />

and has drastically dropped in number in Sardinia; the Egyptian vulture (Neophron percnopterus)<br />

dropped drastically in number and distribution from 1970 to 1990 following the reduction<br />

of traditional cattle husbandry techniques (Liberatori & Penteriani 2001), typical Mediterranean<br />

bird and plant species, usually restricted to the earlier stages of ecological successions (Blondel<br />

& Farré 1988), are decreasing in range and population sizes, following the decrease of<br />

Mediterranean forests and open areas and the intensification of agriculture (Farina 1991; Farina<br />

1997; Preiss et al. 1997; Brotons et al. 2004).<br />

Even though the Italian landscape is not representative of the entire Mediterranean hotspot<br />

(Vallejo et al. 2005), we suggest that our results may provide an important insight into conservation<br />

planning in the entire region. In fact, many of the ecological and socio-political processes<br />

that have occurred in Italy during the past few decades are already occurring or expected to<br />

occur over most of the Mediterranean region. The transition from traditional to mechanized<br />

agriculture and the intensive development of tourism along the coastal areas are likely to lead<br />

towards situations which are broadly sim<strong>il</strong>ar to Italy today.<br />

Protected areas cannot be eas<strong>il</strong>y adapted to follow these patterns: Italian protected areas already<br />

cover 11% of the territory (Maiorano et al. 2006); most of them are located in mountain<br />

regions (where land-use/land-cover changes favor reforestation and the increase of large vertebrate<br />

populations) wh<strong>il</strong>e only few (mostly small ones) can be found in coastal areas, where<br />

the Mediterranean forest, woodlands and scrubs are concentrated and where human pressure<br />

is high. Much more can be done for the Mediterranean hotspot where protected areas cover

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