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Part C - Italy - Commonality (July, 05 2010) - State and Impact
Even though the land changes that occurred between 2000 and 2006 only affected about 1 % of the country, a comparison of Corine Land Cover (CLC) layers shows a general increase of artificial surfaces to the detriment of agricultural and forest lands. Figure 1 shows the status of land cover in Italy using the second level of the CLC 2006 analysis.
Comparing the data shown in Figure 2 with those for 1990-2000 (Figures 3 and 4), the change in the natural environment trend becomes evident. Although there was a general increase of forest and semi/natural areas for 1990-2000, in 2000-2006 these decreased by about 105 km2.
Land take due to the expansion of artificial areas and the related infrastructures, which can lead to the total loss of large areas of land often characterised by soils with a high agricultural value, is the biggest driver of land cover change. Land degradation occurs especially on agricultural and semi-natural areas at the urban fringe and on rural lands close to cities and subjected to peri-urbanisation processes.
The result is an increase of soil sealing, totally preventing soil from performing its vital functions, especially near urban areas and along main road axes. In particular, the problem is taking on worrying proportions in large plain areas, where urbanisation is coupled with intensive farming, and in coastal areas where the coastal economy is linked to tourist pressure (Figure 5).
Land take and soil sealing assessments have been executed on the basis of a national land monitoring network managed by ISPRA. This network is aimed at estimating diachronically the soil – thematic cartography, aerial photographs, remote sensing, archive materials and field visits. The analysis was completed over a long-term period, 1956-2006, showing the rapid growth of the sealed surface areas, with higher rates found in northern Italy (Table 1).
Table 1 Percentage of soil sealing in Italy, 1956-2006)
|
Source: ISPRA
By comparing the variation of soil consumption with resident population over fifty years, it is possible to distinguish a clear decoupling between soil sealing and population growth (Figure 6).
As a consequence of all these pressures, desertification is also becoming an evident problem especially in Sardinia, Sicily, Apulia, Basilicata and Calabria.
For a detailed treatment of topics addressed above, see key topics at
http://annuario.apat.it/capitoli/Ver_6/en/Soil%20and%20land.pdf )
Land cover flows Analysis
Table 2 shows the changes grouped according to so-called flows of land cover that are classified according to major land use processes:
Table 2 Land cover flows, 1990-2006
|
|
|
Changes |
average annual changes
|
||
|
|
|
1990-2000 |
2000-2006 |
1990-2000 |
2000-2006 |
|
|
|
km2 |
km2 |
||
Formation of Artificial surfaces |
868,5 |
573,4 |
86,9 |
95,6 |
||
LCF1 Urban land management: Internal transformation of urban areas |
29,3 |
86,8 |
2,9 |
14,5 |
||
|
lcf11 |
Urban development/ infilling |
0,8 |
2,4 |
0,1 |
0,4 |
|
lcf12 |
Recycling of developed urban land |
27,9 |
81,4 |
2,8 |
13,6 |
|
lcf13 |
Development of green urban areas |
0,6 |
3,0 |
0,1 |
0,5 |
LCF2 Urban residential sprawl |
498,8 |
133,3 |
49,9 |
22,2 |
||
|
lcf21 |
Urban dense residential sprawl |
4,4 |
0,8 |
0,4 |
0,1 |
|
lcf22 |
Urban diffuse residential sprawl |
494,4 |
132,5 |
49,4 |
22,1 |
LCF3 Sprawl of economic sites and infrastructures |
340,4 |
353,3 |
34,0 |
58,9 |
||
|
lcf31 |
Sprawl of industrial and commercial sites |
233,9 |
198,1 |
23,4 |
33,0 |
|
lcf32 |
Sprawl of transport networks |
7,7 |
17,2 |
0,8 |
2,9 |
|
lcf33 |
Sprawl of harbours |
1,7 |
1,0 |
0,2 |
0,2 |
|
lcf34 |
Sprawl of airports |
1,3 |
3,8 |
0,1 |
0,6 |
|
lcf35 |
Sprawl of mines and quarrying areas |
51,1 |
48,1 |
5,1 |
8,0 |
|
lcf36 |
Sprawl of dumpsites |
1,9 |
2,0 |
0,2 |
0,3 |
|
lcf37 |
Construction |
24,8 |
66,2 |
2,5 |
11,0 |
|
lcf38 |
Sprawl of sport and leisure facilities |
18,1 |
16,8 |
1,8 |
2,8 |
Formation of Agricultural areas |
538,6 |
234,0 |
53,9 |
39,0 |
||
LCF4 Agriculture internal conversions |
508,9 |
200,3 |
50,9 |
33,4 |
||
|
lcf41 |
Extension of set aside fallow land and pasture |
235,1 |
65,7 |
23,5 |
10,9 |
|
lcf42 |
Internal conversions between annual crops |
82,7 |
39,9 |
8,3 |
6,6 |
|
lcf43 |
Internal conversions between permanent crops |
0,0 |
0,0 |
0,0 |
0,0 |
|
lcf44 |
Conversion from permanent crops to arable land |
112,0 |
23,9 |
11,2 |
4,0 |
|
lcf45 |
Conversion from arable land to permanent crops |
79,1 |
70,9 |
7,9 |
11,8 |
|
lcf46 |
Conversion from pasture to arable and permanent crops |
0,0 |
0,0 |
0,0 |
0,0 |
|
lcf47 |
Extension of agro-forestry |
0,0 |
0,0 |
0,0 |
0,0 |
LCF5 Conversion from forested & natural land to agriculture |
29,6 |
33,7 |
3,0 |
5,6 |
||
|
lcf51 |
Conversion from forest to agriculture |
26,5 |
23,4 |
2,7 |
3,9 |
|
lcf52 |
Conversion from semi-natural land to agriculture |
0,4 |
0,3 |
0,0 |
0,0 |
|
lcf53 |
Conversion from wetlands to agriculture |
2,4 |
3,8 |
0,2 |
0,6 |
|
lcf54 |
Conversion from developed areas to agriculture |
0,4 |
6,2 |
0,0 |
1,0 |
Formation of Forested or open natural surfaces |
2.423,3 |
1.430,3 |
242,3 |
238,4 |
||
LCF6 Withdrawal of farming |
842,4 |
26,0 |
84,2 |
4,3 |
||
|
lcf61 Withdrawal of farming with woodland creation |
269,7 |
15,4 |
27,0 |
2,6 |
|
|
lcf62 Withdrawal of farming without significant woodland creation |
572,7 |
10,7 |
57,3 |
1,8 |
|
LCF7 Forests creation and management |
1.580,8 |
1.404,2 |
158,1 |
234,0 |
||
|
lcf71 Conversion from transitional woodland to forest |
888,0 |
246,0 |
88,8 |
41,0 |
|
|
lcf72 Forest creation, afforestation |
558,9 |
648,4 |
55,9 |
108,1 |
|
|
lcf73 Forests internal conversions |
3,5 |
2,5 |
0,4 |
0,4 |
|
|
lcf74 Recent felling and transition |
130,4 |
507,3 |
13,0 |
84,6 |
|
Formation of Wetlands and Water surfaces |
28,2 |
41,2 |
2,8 |
6,9 |
||
LCF8 Water bodies creation and management |
28,2 |
41,2 |
2,8 |
6,9 |
||
|
lcf81 Water bodies creation |
23,9 |
41,1 |
2,4 |
6,8 |
|
|
lcf82 Water bodies management |
4,3 |
0,1 |
0,4 |
0,0 |
Source: ISPRA
Table 2 clearly illustrates one of the most evident phenomena about the decrease of farming, especially in the Apennines, that has harmed rural communities as the mountains were abandoned because traditional agriculture was no longer profitable, leading to a lack of job opportunities. In Italy, the number of farm workers was slashed from 48.43 % of the population in 1936 to just 5.7 % in 2000.
It is also important to reflect on the conversion between farming types –internal conversions – mainly due to the transformation of the old methods of farming to industrialised agriculture.
The decrease in farmland, especially between 1990 and 2000, may also explain the major part of the conversion of transitional woodland to forest.
Also notable is the steady growth of artificial areas in the 1990-2006 period. Between 1990 and 2000, the urban residential sprawl – land uptake by residential buildings together with associated services and urban infrastructure from non-urban land – was rapid, but slowed after 2000, while the internal transformation of urban areas and the sprawl of economic sites and infrastructures increased.
For references, please go to https://www.eea.europa.eu/soer/2010/countries/it/land-use-state-and-impacts-italy or scan the QR code.
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