Arcipelago Toscano National Park

Arcipelago Toscano National Park

Location: Portoferraio, Tuscany    Map

Area: 746.63 km2 (288.28 sq mi)

Arcipelago Toscano National Park that protects an area of Archipelago Toscano is located near town of Portoferraio, Tuscany province of Italy. Arcipelago Toscano National Park covers an area of 746.63 km2 (288.28 sq mi). The most famous island of the Toscano Archipelago is island of Elbe. In 1814 Napoleon Bonaparte was exiled here with a personal guard of 600 men after being defeated by Russian Emperor Alexander I and his allies. He did not stick around to enjoy the beautiful landscape and Mediterranean sea. He returned to France to seize back his power for about 100 days before being completely defeated at the battle of Waterloo.

 

Territory

The park has an area of 16,856 hectares on land and 56,766 at sea and is composed of:
all the main islands of the Tuscan Archipelago
Island of Gorgona
Capraia Island
Elba island
Pianosa Island
Montecristo Island
Lily island
Giannutri Island
smaller islets in the Piombino Channel:
Palmaiola Island
Cerboli Island
smaller islands in the Tyrrhenian Sea
Ants of Grosseto
some rocks:
Meloria in the Ligurian Sea;
Elba: Formiche della Zanca, Ogliera, Scoglio della Triglia, Corbella Island, Gemini Islands, Ortano Island, Topi Island and Portoferraio Scoglietto
Giglio: the island of the cape, Le Scole
Pianosa: the Scarpa and La Scola;
Capraia: the Peraiola
Montecristo: the Rock of Africa

Lily island/ Isola del Giglio

The island of Giglio, composed of rocky coasts with cliffs of high naturalistic value, in addition to being part of the National Park, is a protected area both as a site of regional interest (SIR) and as a special protection area (SPA), and it has also been proposed as a site of community importance (pSIC).

Geomorphology
As a prevalent environmental typology, the island is mainly granite, with heterogeneous vegetation cover, more or less evolved formations of Mediterranean scrub and its degradation stages (garrigue and annual meadows) prevail, due to fires. Significant areas are occupied by pine trees and recolonization shrubs on abandoned agricultural areas. Large presence of terracing.

SIR
The main critical elements within the SIR are:
Mass summer tourism affects the landscape and vegetation of the island, leading to high levels of anthropization.
Considerable presence of roads, in the northern portion of the island, with very high traffic in the summer months.
Strong anthropogenic disturbance, in the summer months, on the entire coastal development.
Frequent fires.
Abandonment of traditional forms of land use and consequent reduction of environmental heterogeneity.
Increase in the breeding population of herring gulls (Larus cachinnans).
Presence of terrestrial predators introduced by humans (dogs, cats, rats).
Diffusion of non-native plant and animal species.

The main critical elements external to the site are:
Presence of conspicuous tourist settlements (in expansion) in some coastal stretches, with strong artificialization of the areas with sandy coast.
Coastal landfills that favor the increase of the herring gull.
Direct and indirect impact of fishing on seabirds.

The main cynoservation measures to be adopted are:
Preservation of endemics exclusive to flora and fauna (EE).
Maintenance / recovery of priority habitats (grasslands) and rare floristic species (EE).
Maintenance of high levels of naturalness in less populated areas (EE).
Protection of the Corsican gull (EE).
Maintenance / increase of the levels of environmental diversity, favoring the presence of the different stages of vegetation succession and the permanence of agricultural areas (E).
Eradication / control of invasive alien species (M).

Indications for conservation measures:
Verification and limitation of further development programs for tourist settlements, roads, etc., with particular attention to the protection of less populated areas, the coastal strip and endemic species (EE).
Analysis of the impact of fishing on seabirds and adoption of any necessary measures (EE).
Monitoring of the location of the colonies of Larus audouinii and adoption of any conservation measures deemed necessary (prohibition of landing, prohibition of anchoring in areas close to the colony, specific awareness-raising actions) (EE).
Incentive / promotion of low-impact agricultural activities, verifying, in particular, the possibility of restoring livestock activities that allow the maintenance of grasslands and garrigue (E).
Since some of the main causes of deterioration / disturbance depend on environmental pressures originating in the context outside the site, the impact assessment tool (E) must be appropriately applied to these.
Protection of the most advanced vegetation formations, in particular of broad-leaved and sclerophyll woods, and start-up of management interventions (including through contractual measures) aimed at increasing their levels of maturity (E).
Activation of eradication / control actions of invasive exotic plant species (in particular black locust) and control of the presence of feral dogs and cats (E).
Protection of residual strips of sandy coast with the presence of psammophilous vegetation (M).
Activation of a comprehensive plan for the limitation of the herring gull (Larus cachinnans) (M).

 

Common
Campo nell'Elba, Capoliveri, Marciana, Marciana Marina, Porto Azzurro, Portoferraio, Rio; Capraia Isola; Grosseto; Lily island; Livorno

 

Flora

The Mediterranean and island climate are the main factors that influence the vegetation of the Tuscan Archipelago. In this area there are massively present evergreen plants and plants with very small leaves such as gorse. In the environment of the archipelago you can find large holm oak forests of which only a few coppice and chestnut woods survive today. The most widespread plant formation in the park today is the Mediterranean scrub: strawberry trees, mastic trees, Phoenician juniper, myrtle, heather, rosemary, lavender, broom and rock rose.

Some endemic species are exclusive to the Tuscan archipelago or the Sardinian-Corsican area.

Lily island
On the site of the Isola del Giglio, the predominantly silicic flora is quite rich, with rare and endemic Tyrrhenian species. Among the other relevant environmental typologies are agricultural areas (mainly vineyards), sclerophyll woods and, in the cooler aspects, broad-leaved trees, rocky coasts, sandy coasts, small historical centers and tourist settlements.

Among the plant species present: the prostrate cabbage (Brassica procumbens), a species with North African and South European distribution, present in Europe in two localities (Corsica and Isola del Giglio), probably the European stations are of adventitious origin; the Gagea granatellii, a rare species, reported in Elba (M. Capanne), Pianosa and Giglio. Floristic populations of rocky coasts with endemic species or of high conservation interest are also worth mentioning.

 

Fauna

Among the mammals it is worth noting the presence of martens and wild rabbits, as well as mouflons and wild boars, which, however, have been introduced for hunting purposes. The birdlife is rich: various migratory birds, including shearwaters and Corsican gulls, the latter also symbols of the park. Among reptiles and amphibians: the venturone, the Tyrrhenian gecko, the Tyrrhenian tree frog, the Sardinian discoglossus and the sordone.

The Municipality of Marciana on the island of Elba, with resolution no. 26 of 30 April 1976, ordered the acquisition - for the total sum of 672,000 lire - of three specimens of mouflon from the Ugo Baldacci estate in Montecatini Val di Cecina to be placed on Monte Perone, declaring that the introduction of the specimens constituted a "Contribution of the Municipality to the repopulation and reconstitution of the fauna [...] in order to obtain a restocking of game in the suitable areas of the island."

However, in May 2016, the Governing Council of the Tuscan Archipelago National Park took the decision to "eradicate" the mouflon from the island. The crackdown comes after years in which the Park has tried to limit the heads of ungulates in the Elban territory: an action that, evidently, was not enough to manage the emergency caused by the mouflons, responsible together with the wild boars for numerous damage to the crops and biodiversity, especially with regard to the red lily, the star lily, the holly and the butcher's broom.

Lily island
In the SIR of the Isola del Giglio it is worth noting the presence of the rare chiroptera Tadarida teniotis.

Presence of rare marine nesting ornithic species, linked to rocky habitats and Mediterranean garrigue; important for the stopover of migratory birds. Among them: the Sardinian magnanine (Sylvia sarda) recently reported as a breeder; the Sardinian common willow (Sylvia conspicillata), recently reported as a breeder. Presence of endemic forms, exclusive to the Giglio or the Tuscan Archipelago, and numerous other elements of biogeographical interest (for example, Sardinian-Corsican forms). Consistent nesting populations of threatened bird species, linked to complex environmental mosaics and traditional agricultural landscapes.

Presence among the reptiles of Phyllodactylus europeus, belonging to a genus which is otherwise tropical and among the amphibians, of Discoglossus sardus, endemic species of the Tyrrhenian area.

Numerous endemic invertebrate species.