|
|
Cataloging of the territory, mapping systems, GIS, planning and town-planning
Ideas, themes and suggestions on method
Guideline
Territorial planning is a rather generic term to define all those technical and normative instruments aimed at its correct management.
The territory, however, is a complex whole which can be compared to a four-dimensional matrix (the three spatial dimensions + time) which is alive, evolves and becomes modified following the laws of thermodynamics.
These laws regulate, in an inseparable way, those processes which are at the base of all relationships in the ecosystem, relations between the biotic and abiotic systems, the very evolution of the dynamics of life.
Knowing the characteristics of the territory is the starting point for its correct use, the capacity to discriminate between its basic units is the starting point for its long term management, following the principles of Sustainable Development (Brundtland report, 1987). All modern doctrine on territorial planning, field plans, town planning models etc. can not ignore the correct way of cataloguing all the properties of the territory.
It must be pointed out that in the energy model of the future, the use of territorial resources will be increasingly under a system of monitoring and checks, seeing that the characteristic of being renewable will be a fundamental principle of sustainable development.
The processes of territorial planning, of any kind, will have to be sustained by systems of cataloguing, if possible dynamic ones (through GIS), and guarantee the professionalism of Doctors of Agronomy, Doctors of Forestry, Botanists, and experts in general, in cataloguing and classifying flora and fauna.
The need for a base of shared information which can be accessed at any time by different operators requires a system of standard procedures, without which the management of “Territorial Properties” becomes somewhat problematic.
At a European level, the CORINE (COoRdination de l’INformation sur l’Environnement) project was started by the Council of the European Community in 1985. Its primary aim is to verify, in a dynamic way, the state of the environment in the Community area in order to guide European policy, check its effect and propose any possible corrections.
Secondary aims, yet not in the least less worthy, include the formation and distribution of common standards and methodologies and the promotion of contacts and international exchanges in order to facilitate the development of initiatives within the community.
The CORINE Land Cover project aims to map land surface on a scale of 1:100,000, with a legend containing 44 entries on three hierarchical levels referring to homogeneous spatial areas, or composed of areas of elements belonging to the same class, which have a significant area of land with respect to the scale, which are clearly distinct from the areas surrounding them and which are sufficiently stable to be assigned to the gathering of more detailed information.
Given this premise, the minimum surface which can be mapped (on the scale of 1:100,000) is represented by 25 hectares and corresponds, on the selected scale of representation, to a square 5mm in length or a circle with a radius of 2,8 mm.
The final map, in numerical form, constitutes the basis for geographic and thematic reference in the CORINE Information System.
The project further aims to supply local operators with the cultural and methodological instruments needed for an initial elaboration and for successive updates.
The operational methodology adopted is constituted by 5 phases:
1. Preliminary work
2. Preparation for satellite images (usually Landsat D-TM Spot-HRV) in false colour, or, at most, in combination, for the Thematic Mapper of the band 4,5,3, which is the one that allows the best discrimination of the objects identified in the legend.
3. Photographic interpretations aided by a calculator. Delimitation-identification of the objects.
Validation of the interpretation.
4. Digitalisation
5. Validation of the data bank.
For maps of greater detail (1:25,000; 1:10,000) a new hierarchy of the obtained data can be produced with a quarter level. Successively, an example of this is obtained for the Agricultural Areas (2) and for the Forests and semi-natural areas (3).
The following table shows the three levels examined in the Corine program plus a fourth level whose hierarchy is greater, for example, for an Agricultural and Forestry Study.
In any case, any fourth level must have its origin in the corresponding class of the previous level.
The principal levels are:
1-Artificial surface; 2- Agricultural areas; 3- Forests and semi-natural areas; 4- Humid lands; 5-Bodies of
water.
|
Level
2
|
Level
3
|
Level
4
|
|
1.1-
social fabric
|
1.1.1-
social fabric, continuous
|
|
|
|
1.1.2-
social fabric, discontinuous
|
|
|
1.2-areas
of commercial industries and transport
|
1.2.1-
industrial or commercial areas
|
|
|
|
1.2.2-
road networks and binary and tertiary associates
|
|
|
|
1.2.3-port
areas
|
|
|
|
1.2.4-
airports
|
|
|
1.3-
mines, dumps and building sites |
1.3.1-
areas of mineral extraction
|
|
|
|
1.3.2-
dumps
|
|
|
|
1.3.3-
construction sites
|
|
|
1.4-
areas with artificial vegetation
|
1.4.1-
green urban areas
|
|
|
|
1.4.2-
sport and free time structures
|
|
|
2.1-
Sowed areas
|
2.1.1-
non-irrigated sowed areas
|
2.1.1.1-
intensive cultivation
|
|
|
|
2.1.1.2-
extensive cultivation
|
|
|
2.1.2-
permanently irrigated land
|
|
|
|
2.1.3-
rice fields
|
|
|
2.2-
permanent crops
|
2.2.1-
vineyards
|
2.2.1.1-
vineyards
|
|
|
2.2.2-orchards
and minor fruits
|
2.2.2.1-
almond groves
|
|
|
|
2.2.2.2-
apple groves
|
|
|
|
2.2.2.3-
pear groves
|
|
|
|
2.2.2.4-
citrus fruit groves
|
|
|
|
2.2.2.5-
nut groves
|
|
|
|
2.2.2.6-
etc.
|
|
|
2.2.3-
olive groves
|
|
|
2.3-
pasture
|
2.3.1-
pasture
|
|
|
2.4-
heterogeneous agricultural areas
|
2.4.1-
annual crops associated to permanent cultivations
|
|
|
|
2.4.2-complex
cultivation
|
|
|
|
2.4.3-
land occupied principally by agriculture
|
|
|
|
2.4.4-
areas of cultivation on land and forests
|
|
|
3.1- forests
|
3.1.1-
forests of broad-leaved trees
|
3.1.1.1-
with a prevalence of holm-oak or cork oak
|
|
|
|
3.1.1.2-
with a prevalence of deciduous oaks
|
|
|
|
3.1.1.3-
mixed, with a prevalence of
mesophile and mesothermophile broad-leaves
|
|
|
|
3.1.1.4-
with a prevalence of chestnuts
|
|
|
|
3.1.1.5-
with a prevalence of beech
|
|
|
|
3.1.1.6-
with a prevalence of species of hydric plants
|
|
|
|
3.1.1.7-
plantations with a prevalence of non-native broadleaves
|
|
|
3.1.2-
forests of conifers
|
3.1.2.1-
woods with a prevalence of Mediterranean pines
|
|
|
|
3.1.2.2-
woods with a prevalence of oromediterraneo mountain pines and
|
|
|
|
3.1.2.3-
woods with a prevalence of white and/or red firs
|
|
|
|
3.1.2.4-
woods with a prevalence of larches and/or stone pines
|
|
|
|
3.1.2.5-
woods and plantations with a prevalence of non-native conifers
|
|
|
3.1.3-
mixed forests
|
|
|
|
3.1.3.2
mixed woods with a prevalence of conifers
|
|
|
|
|
3.1.3.1.1
-Mixed woods consisting of conifers and broadleaves with a
prevalence of holm oaks or cork oaks
|
|
|
|
3.1.3.1.2-
Mixed woods consisting of conifers and broadleaves with a
prevalence of deciduous
oaks
|
|
3.2-
Grassy and/or shrubby areas
|
3.2.1-
natural prairie
|
3.1.3.1.3-
Mixed woods consisting of conifers and broadleaves with a
prevalence of mesophile and mesothermophile broad-leaves
|
|
|
3.2.2-
moors and heaths
|
3.1.3.1.4-
Mixed woods consisting of conifers and broadleaves with a
prevalence of chestnuts
|
|
|
3.2.3-
schlerophyll vegetation
|
3.1.3.1.5-
Mixed woods consisting of conifers and broadleaves with a
prevalence of beeches
|
|
|
3.2.4-
transition between woody and shrubby land
|
3.1.3.1.6-
Mixed woods consisting of conifers and broadleaves with a
prevalence of species hydric plants
|
|
3.3-
open spaces with little or no vegetation
|
3.3.1-
beaches, dunes and sand plains
|
3.1.3.2.1-
Mixed woods consisting of conifers and broadleaves with a
prevalence of Mediterranean pines
|
|
|
3.3.2-
bare rock
|
3.1.3.2.2-
Mixed woods consisting of conifers and broadleaves with a
prevalence of oromediterraneo mountain pines and
|
|
|
3.3.3-
areas with hardly any vegetation
|
3.1.3.2.3-
Mixed woods consisting of conifers and broadleaves with a
prevalence of white and/or red firs
|
|
|
3.3.4-
burnt areas
|
3.1.3.2.4-
Mixed woods consisting of conifers and broadleaves with a
prevalence of larches and/or stone
pines
|
|
|
3.3.5-
glaciers and areas of perennial snow
|
3.1.3.2.5-
Mixed woods consisting of conifers and broadleaves with a
prevalence of non-native conifers
|
|
4.1-
inland humid lands
|
4.1.1-
inland marshland
|
|
|
|
4.1.2-
peat-bogs
|
|
|
4.2-
humid coastal lands
|
4.2.1-
salt marshes
|
|
|
|
4.2.2-
salt pans
|
|
|
|
4.2.3-
intertidal plains
|
|
|
5.1-
inland water areas |
5.1.1-
rivers and streams |
|
|
|
5.1.2-
bodies of water |
|
|
5.2-
seafront waters |
5.2.1-
coastal lagoons |
|
|
|
5.2.2-
estuaries |
|
|
|
5.2.3-
seas |
|
It
is clear that to a territorial study geared to a programme of
territorial planning or a revision of town-planning must be added a
series of further research which can be summarised in the following
table:
Further
maps and elaborations can give a more complete picture of the work
in question but they must always be correlated to the particular
aims set by the study.
Suggested
rates of reference
|
Analyzed Territory
|
Euro
Rates
|
|
Ha
|
Euro
for Ha
|
Total
|
|
Until
to
|
500
|
27
|
13.500
|
|
“
|
1.000
|
20
|
20.000
|
|
“
|
2.000
|
13
|
26.000
|
|
“
|
5.000
|
8
|
40.000
|
|
“
|
10.000
|
5
|
50.000
|
|
Until
to and >
|
20.000
|
4
|
80.000
|
To
the aforesaid honoraria they go added repayable expenses according
to the tariff official.
In
the case in which a greater detail is demanded, for the calculation
of the following honorarium it is proceeded applying to the previous
increases table:
Scale 1: 5.000 - more 30 %;
Scale 1: 2.000 - more 50 %.
The intermediate values are estimated obviously for linear
interpolation.
Guido
Bissanti
Bibliography
A.A.VV.
(1999) - Il Governo del territorio - modello di pianificazione -
Atti del I Congresso dei Dottori Agronomi e Forestali della Sicilia.
Altavilla Milicia (PA) 21 Maggio 1999 -
AA. VV. (1997) - Lo sviluppo rurale sostenibile - Atti del X
Congresso Nazionale dei Dottori Agronomi e Forestali. Vieste 12 - 14
Giugno 1997 -
Agnelli P. Foggi B. Rossi R. Sposino P. Tarducci F. (1993) - Analisi
e Cartografia dell’ecologia del paesaggio. Genio Rurale n° 9:
9-17. Settembre 1993. Edagricole Bologna
Bagnaresi U. (1997) - Pianificazione e gestione ecologica del
territorio agro-forestale. Genio
Bissanti G. (1999) - Sviluppo rurale e rinascimento politico - Nuova
Ipsa Palermo.
Brullo S., C. Marceno: Contributo alla conoscenza della classe
Quercetea ilicis in Sicilia - Not. Fitosociologico n. 19 (11) 1984
Brullo S. 1984: Contributo alla conoscenza della vegetazione delle
Madonie (Sicilia settentrionale).
Bollettino Accademico Gioenia Scienze Naturali 16(322): 351-420
Catalano M. (1995) - Caratterizzazione agro-ecologica di zone
mediterranee - Metodologia.
Catalano M. Rubino P. (1995) - Caratterizzazione agro-climatica di
zone mediterranee.
Curatolo G. (1998) – La Programmazione Territoriale – L’EPOS
Palermo.
De Nardo A. Dal Sasso P. (1995) - La cartografia nell’analisi e
pianificazione dei sistemi agricolo forestali. Genio Rurale n° 10:
33-52. Ottobre 1995 - Edagricole Bologna.
Di Giulio A. (1995) - Gli indicatori rurali: strumenti per
l’analisi delle politiche di gestione del territorio. Genio Rurale
n° 5: 51 - 55. Maggio 1995 - Edagricole Bologna
Genio Rurale n° 12: 55-62. Dicembre 1992. Edagricole Bologna.
Genio Rurale n° 7/8: 59 - 66. Luglio-Agosto 1995. Edagricole
Bologna.
Genio Rurale n° 6: 61 - 64. Giugno 1997 - Edagricole Bologna.
Genio Rurale n° 9: 40 - 44. Settembre 1997 - Edagricole Bologna.
Gentile S. (1968): Memorie illustrative della carta della
vegetazione naturale potenziale della Sicilia.
Guerrieri G. e Nardi V. (1997) - Le politiche internazionali e
nazionali sullo sviluppo sostenibile del bacino mediterraneo con
particolare riferimento alla lotta alla desertificazione.
INEA - Lo sviluppo rurale - L’ambiente come risorsa per lo
sviluppo integrato delle aree rurali. Quaderno informativo n. 5. -
Gennaio 1997 –
Ist. Botanico lab. critt. Università di Pavia - Quaderno 40: 1-114
La Mantia A., Gianguzzi L., 1999 – La Quercia spinosa in Sicilia
– Sicilia Foreste (6) 21/22: 2-10, Azienda Foreste Demaniali della
Regione Siciliana. Palermo.
Marcenò C., Raimondo F.M., 1972 - Sulla presenza della Quercus
calliprinos Webb nella Sicilia nord-occidentale. - Nuovo giornale
botanico italiano, 106: 290-291.
Pignatti - Flora d’Italia – Ed agricole
Raimondo F.M., Fici S., Gianguzzi L., Lentini F., Mazzola P., Miceli
G., Not R., Ottonello D., Romano S., Schicchi R., 1986 – Atlante
iconografico delle piante endemiche o rare della Riserva naturale
orientata dello Zingaro. – A.F.D.R.S., pp. 84, Palermo.
Raimondo F.M., Gianguzzi L., Ilardi V., 1994 – Inventario delle
specie "a rischio" nella flora vascolare nativa della
Sicilia. – Quad. Bot. Ambientale Appl., 3 (1992): 65-132.
Toccolini A. Angileri V. (1992) - I sistemi informativi per la
pianificazione del territorio.
|
|
|