Accona Desert
Accona desert refers to a hilly area in the Siena province of Italy, within the municipality of Asciano often enlarged to include the biancana site of Le Fiorentine - Leonina . The term desert is inappropriate from a physical and climatic point of view, rather the climate is Mediterranean with a hot dry summer and almost 800 mm/y of rain. A real desert has never existed here, unless “desert” was a way of describing severely eroded areas, more properly called “badlands”, even if temporary ones.
Two main types of badlands can be found in the area of the Crete Senesi, the Valdorcia and the Volterra areas of Tuscany: biancana and calanco. Both are linked to processes of gully erosion, the former intermingled mainly with subsurface erosion and the latter with mass movements. Biancanas can be found also in Basilicata and in Calabria. The calanco landscape is common all along the Apennines and in many parts of the Alps. Both calancos and biancanas were used as grazing ground, with an almost annual burning of the vegetation in order to remove brush and favour herbaceous cover more palatable for sheep, goats and cattle. Both practices were abandoned in the 1990s to favour measures to preserve biodiversity and geoforms under the EU Natura 2000 programme. Conservation has almost stopped erosion in both types of badlands and vegetation now covers the majority of the once bare slopes. As there is a strong interrelationship between vegetation biodiversity and erosion/deposition processes, biodiversity is also currently threatened and the biancana landscape is forecast to disappear completely within 20–40 years as brush cover expands. Spots where the traditional forms can still be observed are dispersed in the Crete Senesi and the Valdorcia, included within the quadrangle of vertices , , , . Leonina and Lucciola Bella are two of the best sites for walking through the biancanas, while Chiusure - Monte Oliveto Maggiore and Radicofani host the most impressive calancos.
History
Archaeological maps of Siena province show that all the Crete Senesi area was inhabited in Etruscan and Roman Times as almost every slope contains remnants of that period. The periods of the Barbarian invasions, the Gothic wars and the Justinian plague caused a demographic decline which reduced the anthropic impact on the environment and favoured the natural reforestation of the area. Nevertheless in the seventh century Asciano was already a Curtis Regia, hence a village with a territory where agriculture and animal husbandry coexisted with hunting reserves used by the Lombard lords. In the tenth century documents show Leonina too as Curtis. Other documentation, even if fragmentary, testifies to the existence of a stable settlement in Leonina. At the time of the Black Death, Leonina’s population halved from more than 150-160 to about 60 at the beginning of 1400. This fate was common to Siena, Asciano and the whole territory of the Sienese Republic: Siena’s population fell from about 50,000 before the Black Death to 14-16,000 in 1400-1450 and returned to pre-plague levels only at the end of twentieth century.Asciano, with its surroundings, was a major town in the Sienese territory for a long time and contributed to the Republic’s economy in a substantial way, gaining Sienese citizenship in 1369.
A few kilometers south of Asciano the small town of Chiusure grew around the seventh century church of Sant’Angelo in Luco, despite the fact that the hill on which the village is located would have been threatened by the approach of the heads of large gully systems retreating upslope. It had an economy mainly based on agriculture and animal husbandry. Chiusure's importance is due mainly to its proximity to Accona about 1 km away. The members of three leading Sienese families founded in 1313 what became the Benedictine monastery of Monte Oliveto Maggiore on the site of the Tolomei’s Accona podere. Pius II visited the monastery during his papacy and described the area as rich in olive trees, fruit trees, almonds, vines, orchards, small cypress woods, oaks and junipers. Furthermore, Pius II added, there was water: a perennial spring, wells, tanks, cisterns.
From this time until 1796 the monastery played a spiritual and economical leadership role in the area with its churches, monasteries and farms. Then, under French rule from 1797 all the Church possessions were confiscated and sold. Only after the Restoration did the Olivetan Benedictines recover the Monastery of Monte Oliveto and slowly resume their role as local leaders.
The environment and the anthropic influence
The Crete Senesi lie over plio-pleistocene silty-clay overconsolidated marine deposits, rich in sodium. Deep, narrow cracks cut the deposits to about 10m from the surface, favouring localized water infiltration and the excavation of subterranean tunnels. In natural, unstressed conditions, soils can develop as deep as 1.5 m, with removal of sodium by the leaching action of infiltration water. The present situation is characterized by the presence of eroded or poorly developed soils especially in the badlands. Intense animal activities and anthropic activities favour surface soil erosion, causing the generation of small rivulets, rills and gullies. The rate of soil erosion varies from zero to 1-2 mm of soil removed yearly. If gullies are excavated by concentrating overland flow, erosion values in a field can attain 2-4 mm of soil loss in a single rain event. Excessive animal grazing facilitates gully erosion, soil slips and mass movements. Cropland management requires tillage and sometimes large earth movements. All these activities cause a net movement of soil from the upslope side of the field to the downslope side. Soil in the upslope side of the field is lost at rates between 1 and 4 cm yearly. For medieval tilling techniques, the estimated erosion rate would have been around 2 cm/year. Considering an alternation of years with and without ploughing then 300 years would have been enough to expose the subsoil still rich in sodium. Sodium gives dispersive characteristics to the clay, making it very erodible, hence increasing the velocity of rain-induced erosion.The first half of the fourteenth century was characterized by social unrest due to the transformation from farmers who owned their land to large land holdings with the property subdivided into poderi each managed by a farmer and his family living on the fields in a cropsharing system. At the same time foreign armies passing through the Sienese territory interfered with normal activities in the countryside. Hence, erosion and floods are testified in several documents, in the Lorenzetti’s Buongoverno frescos, that show biancanas, while severe floods are reported. Also the climate was characterized by droughts and extreme events that led to a shortage of food in Italy and necessitated imports from abroad. This forced Siena to invest a large part of its wealth in facing these difficulties, thus diverting funds from other priorities such as flood prevention.
The second half of the fourteenth century the abrupt and large demographic decrease due to the plagues resulted in the farming population of small owners and mezzadri having to manage twice as much livestock and land per capita. With no resources for maintenance activity, the only use for a severely eroded field was animal grazing. Hence, the eroded fields became irrecoverable. The lack of personnel persisted for about two centuries during which the eroded areas expanded, reaching a maximum in the nineteenth century.
This picture is substantially confirmed by soil denudation rates as estimated using average erosion in the basin of the river Ombrone which drains the area and on the denudation rates of the two largest biancanas of the Leonina site and the gully in between.
Biancana badlands reclamation began at the end of the XIXth century and ended during the second half of the twentieth century when bulldozers removed almost all the biancanas and some of the smallest calancos, encouraged by EU subsidies then available under the Common Agricultural Policy. Thus it can be said that damage mainly due to an epidemic was eventually solved by the EU-CAP of 1960-2000.