This article was downloaded by: [Bernardino Romano] On: 22 July 2014, At: 10:32 Publisher: Taylor & Francis Informa Ltd Registered in England and Wales Registered Number: 1072954 Registered office: Mortimer House, 37-41 Mortimer Street, London W1T 3JH, UK

Journal of Land Use Science Publication details, including instructions for authors and subscription information: http://www.tandfonline.com/loi/tlus20 Land urbanization in Central : 50 years of evolution Bernardino Romanoa & Francesco Zulloa a Department of Civil Engineering, Architecture and Environment (DICEAA), University of L’Aquila, Campo di Pile, L’Aquila, Italy Accepted author version posted online: 04 Dec 2012.Published online: 06 Feb 2013.

To cite this article: Bernardino Romano & Francesco Zullo (2014) Land urbanization in Central Italy: 50 years of evolution, Journal of Land Use Science, 9:2, 143-164, DOI: 10.1080/1747423X.2012.754963 To link to this article: http://dx.doi.org/10.1080/1747423X.2012.754963

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Land urbanization in Central Italy: 50 years of evolution Bernardino Romano* and Francesco Zullo

Department of Civil Engineering, Architecture and Environment (DICEAA), University of L’Aquila, Campo di Pile, L’Aquila, Italy (Received 29 June 2012; final version received 28 November 2012)

The increasingly fast pace in urban conversion of land over the past 50 years in Italy is a phenomenon that is still difficult to quantify reliably owing to the chronic lack of knowledge at every territorial level, from national to municipal. This article describes the results of a study on the features of urbanization in the 1950s in the peninsular regions of Central Italy, based on uniform historical maps of the entire country. The historical data were compared from a qualitative and quantitative viewpoint with the present-day geography of settlements. Interesting information has emerged on possi- ble significant thresholds in the relationship between demography and urban use of land, in addition to data on landscape effects to be construed as signs of specific trends underway today and scarcely taken into account by land management tools. Keywords: urbanization impact; land-use change; land-use planning; land uptake

1. Introduction The purpose of this study is to elaborate data on the quantitative and qualitative evolution of land urbanization in Central Italy from the post-war period (1949–1956) to the first decade of the twenty-first century. According to consolidated scientific opinions, land use caused by urbanization is one of the main causes of political and social conflicts (Plotkin, 1987) and altered environmental quality of land (Ellis & Ramankutty, 2008; Sala et al., 2000). The aspects involved, either directly or indirectly, in urban conversion of land include the following:

Downloaded by [Bernardino Romano] at 10:32 22 July 2014 Economic and energetic field:

• diseconomies in transport • waste of energy • reduced agricultural produce

Hydro-geo-pedologic field:

• geological destabilization • irreversible use of land • alteration of underground and surface watercourses.

*Corresponding author. Email: [email protected]

© 2013 Taylor & Francis 144 B. Romano and F.Zullo

Physico-climatic field:

• increased thermal reflection and climate change • reduced emission absorption capacity • effects on carbon sequestration • spatial propagation of physicochemical disturbances

Ecobiological field:

• physical erosion and destruction of habitats • ecosystem fragmentation • dystrophy of ecological and biological processes • penalization of the ecosystem services of the environment • reduction in overall ecological ‘resilience’

Some European countries that are more sensitive to the foregoing consequences have already adopted regulations to curb the phenomenon and one of the most significant expe- riences is the German one (Bundesregierung, 1985; Illy, Hornych, Schwartz, & Rosenfeld, 2009). There are not many studies in the international literature on the Italian case (Bonifazi & Capello, 2001; Heins, 2001) and very few regions (only 3 out of 20) have vector infor- mation on land use over the past 50 years. There are also very few cases in which data covering a shorter time span are available (1970s–2000) regarding both overall magnitude of urbanization and statistically significant historical series and there are no coordinated survey activities among local governments (regions, provinces, and municipalities). The negative aspects of this phenomenon are still considered only marginally by sci- entific, communication, and land governance agencies (Emiliani, 2007; Mercalli, 2009; Pileri, 2007). Some contributions on ecological networks and the threats on the biodiversity due to urbanization are in Battisti (2011). Some Universities (, , Pavia, and L’Aquila) have studied the relationship between land-use change and decreasing of ecosystem quality (Gambino & Romano, 2004, Malcevschi, 2010; www.planeco.org). In other countries, information and publications are far more numerous (Bockstael, 2007; Garcia-Call, 2011; Hall, Gracey, Drewett, & Thomas, 1973; Hauri, Steiner, &

Downloaded by [Bernardino Romano] at 10:32 22 July 2014 Vinzens, 2006; Irwin & Zaninetti, 2006; Mellor, 1983; Yanitsky, 1986). Only recently has the need emerged to set up mechanisms to monitor urban transformation dynamics, but we are still far from having systematic and consistent data collection that would make credi- ble comparisons and assessments possible (Batty, 2008;Lowry,1990; Sharma, Pandey, & Nathawat, 2012). One of the most recent initiatives in this regard is the one taken by the National Land Use Observatory, set up by the Polytechnic and INU (Urban Planning National Institute) (http://www.inu.it/attivita_inu/ONCS_2.html) which however makes use of rel- atively recent information bases (end of the 1970s) and has very little data available. Toward the end of the 1980s, other authors highlighted landscape change modalities using large-scale national databases (1:250,000) (Astengo & Nucci, 1990; CNR-IPRA, 1988)or European standards such as Corine Land Cover (CLC) (APAT, 2005; Bossard, Feranec, & Otahel, 2000; Comber, 2008) derived from satellite remote sensing on a nominal scale of 1:100,000 (Berdini, 2009; Falcucci & Maiorano, 2008). Some international organizations, such as the European Environmental Agency (EEA, 2006), have estimated, in the case Journal of Land Use Science 145

Table 1. Differential test based on the surveys of urbanized areas taken from CLC and those obtained from technical maps or regional land use maps (CUS) after 2000. Urbanized area Urbanized area difference Regions CLC 2000 (ha) CUS 2000 (ha) %

Abruzzo 23,250.13 36,740.00 0.58 Campania 71,145.88 101,163.93 0.42 Emilia-Romagna 97,985.00 206,369.06 1.11 Friuli-Venezia Giul 49,529.01 69,719.61 0.41 Lazio 88,415.77 132,078.31 0.49 Liguria 18,900.41 31,047.42 0.64 Lombardia 215,942.87 304,765.80 0.41 Marche 38,634.30 50,580.37 0.31 Molise 4286.21 12,028.05 1.81 Puglia 71,797.89 128,190.03 0.79 Sardegna 54,130.35 78,061.88 0.44 23,989.49 30,124.74 0.26 Valle d’Aosta 3237.94 4709.35 0.45 Veneto 132,041.36 246,298.58 0.87 Total 893,286.63 1,431,877.14 0.60

of Italy, that approximately 8000 ha/year were artificialized between 1990 and 2000, again based on CLC satellite remote sensing. Other data have been processed by ISTAT (National Institute of Statistics) and the information derives from the census which this Institute con- ducts nationwide (ISTAT, 2009) and, in particular, referred to businesses operating in the agricultural sector. Table 1 shows a differential test on urbanized areas conducted in some Italian regions based on CLC satellite remote sensing and data taken from regional land use maps (Carte regionali di Uso del Suolo – CUS) drawn up over the past 10 years by all Italian regions by means of photo interpretation with levels of detail ranging between 1:10,000 and 1:5000 (far more reliable than CLC as they plot scattered and minute built-up areas too). As may be noted, there is considerable variability and huge differences, sometimes in excess of 80% too, which force technical and scientific operators to be extremely cautious in making diagnoses and outlining problematic scenarios. Out of the sample of 14 regions shown in

Downloaded by [Bernardino Romano] at 10:32 22 July 2014 Table 1, actual urbanized areas (surveyed by CUS) are 60% greater on average than the same areas surveyed by CLC remote sensing. In our article, urbanized areas in the 1950s have been extrapolated from uniform his- torical maps of the entire country, using an appropriate Geographical Information System (GIS) technique, in order to obtain comparable values for all Italian regions. Two years of studies were needed to produce these data and we expect to obtain data for the entire country in three years’ time.

2. Methodology As mentioned previously, in order to develop a reliable national evolutionary picture of urban conversion of land from the second post-war period to the present day, it is necessary to use cartographic bases that are homogenous for the period across the entire country and with a sufficient scale of detail to highlight even the most scattered and fragmented urbanized parts. 146 B. Romano and F.Zullo

This is why, in the study presented in this article we used Italian maps published on a scale of 1:25,000 by the Italian Military Geographical Institute (IGMI) between 1949 and 1962, as our reference time source for the 1950s. These maps are part of the 25V Series, plotted on a scale of 1:20,000, organized in 3545 elements (tables) 730 longitude and 5 latitude in size, in Gauss’s conformal representation and part of the national geodetic system (international ellipsoid oriented to Monte Mario – ED40) with a kilometric grid in the Universal Transverse of Mercator conformal projection (ED50 European data). From these maps, available in raster version, it is possible to extrapolate urbanized areas in the 1950s, formed by areas covered by buildings plus all ancillary areas (parking areas, streets within neighborhoods, goods storage and handling areas, and various other structures) (Figure 1). Within the framework of this study, we developed a GIS technical procedure capa- ble of semi-automating vector extraction of urbanized areas from historical raster maps (Romano & Zullo, 2010). Then, the overall parts corresponding to urban functions (built Downloaded by [Bernardino Romano] at 10:32 22 July 2014

Figure 1. Detail of the representation of an urban area on the IGM 1:25,000 map of the 1950s. Journal of Land Use Science 147

and ancillary areas) were isolated and tested using additional topological devices. The results obtained from this study on 1:25,000 maps were then compared with those of urban- ized areas available in vector format from regional maps generally derived from photo interpretation on a nominal scale of 1:10,000 or 1:5000. The regions presented in this article are those of Central Italy, namely Umbria, Marche, Abruzzo, Molise, and Lazio. The territories in these regions include the highest mountain- ous areas in the Apennine, with the highest peak in peninsular Italy (the Corno Grande 2914 m above sea level), as well as considerable hilly expanses and over 350 km of coastal strip. This is why the relationship between morphology and settlements is so close and has given rise to historically highly diversified phenomena, which however have become more homogenous since the post-war period to the present day, as described later.

3. Results 3.1. Urbanization in the 1950s The regions analyzed have a very diverse territorial history. Prior to the unification of Italy in 1861, Marche, Umbria, and northern Lazio were part of the State of the Church, while the Abruzzo and Molise and some areas of southern and eastern Lazio belonged to the Kingdom of . Geoclimatic features and political administration have had a varied impact on land transformation from both a town planning and a agricultural perspective. For centuries, the prevailing hilly morphology of Umbria and Marche, the abundant watercourses, and a particularly favorable temperate climate have fostered profitable farming based above all on the specialized production of wine and oil. Farming in these regions was marked by the sharecropping model (Reid & Joseph, 1975; Shaban, 1987; Singh, 1989) which was widely used in other Italian regions too, such as Tuscany, Emilia Romagna, and Veneto and strongly developed in the fourteenth and fifteenth centuries. It persisted until the 1960s, when law no. 756/64 put an end to new sharecropping contracts. This form of agricultural production, through which the landowner and the farmer team up to farm an estate in order to share produce and profits, has led to very evident results in the landscapes of the regions in question. The utmost care of the land, made evident by the accurate layout of fields and canals, is the consequence of the sharecropper’s need to produce everything his family needs by tapping the potentialities of the estate as much as possible. The average expanse of farming estates ranging between 6 and 9 ha (250–300 m

Downloaded by [Bernardino Romano] at 10:32 22 July 2014 square block), where the house of the sharecropper’s family and outbuildings were situated, has led to the significant spread of settlements with highly scattered buildings that clearly distinguish the regions of Umbria and Marche from all the others considered in the study sample. In the Abruzzo, Molise, and Lazio farming was historically based on an entirely differ- ent model, that of the latifundium (Cardoza, 1994), that is to say large landed estates, sometimes even in excess of 1000 ha (the famous record of 14,000 ha being held by the Torlonia family in Abruzzo) owned by nobles or the ecclesiastic aristocracy used to farm traditional crops, but more frequently as grazing land, by the farmhands hired by the landowners. In Western Europe, this system, typical of the Ancien Régime, was overcome only between the eighteenth and nineteenth centuries, due to the spread of capitalism in the running of farms. In these large landed estates, not much attention was paid to innovation and the owner was only interested in obtaining a good rent and neglected farming details. This is why 148 B. Romano and F.Zullo

the type of farming practiced in large landed estates was often extremely backward. This latifundistic model did not require a dense system of settlements on the territory and, as a result, urbanized centers are historically far more clustered. This phenomenon is very clear when examining Figure 2 and represented analytically by the urban dispersion index (UDI), which is calculated as follows:

Nuc UDI = A

where Nuc is the number of urbanized nucleus and A is the regional area (km2). Table 2 shows a very high UDI in the 1950s for Umbria and Marche (values rang- ing between 4 and 7), while it is far lower in the regions of Lazio, Abruzzo, and Molise (between 1.6 and 1.3). In the 2000s, the regions of Umbria and Marche are still marked by dispersion, with values significantly on the rise too, while the other regions showed a clustering trend of urbanized areas, mainly linear along the valley lines, with reductions even in excess of one-half of the original urban nucleus.

3.2. Comparison between the 1950s and the year 2000 The regions studied are marked by great differences in urbanization between the 1950s and after the year 2000 for reasons tied undoubtedly to the aforementioned prevailing territorial policies over the years and their climatic, geographical, morphological, and productive features. The variations in question are, however, quantitatively significant (Figure 2 and Table 3), with minimum increase rates of about 100% in the case of Umbria, over 200% in Marche, and over 400% in Lazio, Molise, and Abruzzo. In Molise, one of the smallest Italian regions, land has been urbanized at an average pace of over half a hectare per day, while in Umbria the rate of conversion was slightly lower than 1 ha/day. Abruzzo and Marche showed decisively higher rates with over 1.7 ha/day, while Lazio (the region containing Rome) ranked first with over 5 ha/day. Overall in the regions studied, urban areas have increased threefold on average with an increment of almost 200,000 ha in approximately 50 years, that is to say an artificial- ized surface equal to that of a large European national park. Daily land uptake refers to varying survey periods, but the average value amounts to about a total of over 10 ha/day. Considering that the territories in the regions analyzed account for 17% of the entire coun-

Downloaded by [Bernardino Romano] at 10:32 22 July 2014 try, if these values were extended to 100% of the Italian territory, we would have an average daily conversion surface of about 60 ha/day. If this land transformation trend should per- sist in the future too, we would have a scenario of almost 500,000 ha of built surfaces in the next 20 years, which may be roughly represented as a square of over 70 km per side (almost half of the average width of the Italian peninsula between the Tyrrhenian sea and the Adriatic sea). Table 4 gives us a very effective dynamic image of the actual scope of the process analyzed. In the last post-war period, the regions studied had very low urbanization density values: Molise, Abruzzo, and Marche were below 7‰, while the other regions ranged between 1% and 2%. All these values varied their order of magnitude significantly in the 50 years observed: Umbria, Abruzzo, and Molise reached 3%, Marche rose and exceeded 5%, while Lazio came close to 8%. As far as the per capita value is concerned, in Molise and Abruzzo it has increased almost fivefold, while the lowest values are found in Umbria with an increment factor of less than 3 (even though in the 1950s these two regions had the highest per capita values). Journal of Land Use Science 149

(a) Pesaro

Urbino

Ancona

Macerata

Perugia

Ascoli piceno

km Teramo 0200400 Ter ni

L'aquila Viterbo Chieti

Roma

Frosinone Isernia Campobasso

Latina Urbanized area 1950s

0 20 40 80 120 160 km (b) Pesaro

Urbino

Ancona

Macerata

Perugia

Ascoli piceno

Teramo

Ter ni Pescara

L’aquila Viterbo Rieti Chieti Downloaded by [Bernardino Romano] at 10:32 22 July 2014

Roma

Frosinone Isernia Campobasso

Latina Urbanized area noughties

0 20 40 80 120 160 km

Figure 2. Urbanization maps of the (a) 1950s and of (b) 2000.

In the overall territory investigated which, as mentioned earlier, is a sample accounting for over 17% of the entire national surface, urbanization density has increased fivefold on average between the mid-twentieth century and the early twenty-first century, while the per capita values of the areas converted to urban functions have increased threefold. 150 B. Romano and F.Zullo

Table 2. Territorial dispersion index of urban nucleus. Number urbanized Number urbanized UDI UDI Regions Area (km2) centers (1950s) centers (noughties) (1950s) (noughties)

Umbria 8461.07 35,109 58,892 4.15 6.96 Marche 9749.54 74,487 87,675 7.64 8.99 Lazio 17,226.28 28,302 16,886 1.64 0.98 Abruzzo 10,830.15 15,366 6057 1.42 0.56 Molise 4461.03 5720 7553 1.28 1.69 Total and 50,728.07 158,984 177,063 3.13 1.11 average

Table 3. The analytical result of the study for the sample of Italian regions investigated. Difference Urbanized 1950s- Land uptake area 1950s Urbanized area noughties Increasing speed Regions (ha) noughties (ha) (ha) rate (m2/day)

Umbria 15,750.51 30,124.74 14,374.23 0.91 8561 (1956–2002) Molise 2316.00 12,028.05 9712.05 4.19 5784 (1956–2002) Abruzzo 7242.98 36,740.00 29,497.02 4.07 17,568 (1956–2002) Marche 16,454.41 50,580.37 34,125.96 2.07 17,641 (1954–2007) Lazio 26,356.00 132,078.31 105,722.31 4.01 53,639 (1956–2004) Sum and 68,119.90 261,551.47 193,431.57 3.05 103,193 average

Table 4. Regional and per capita urbanization density values in the time span considered. Urbanization per

Downloaded by [Bernardino Romano] at 10:32 22 July 2014 Urbanization capita Resident inhabitants density (%) (m2/inhabitant) Regional Regions area (km2) 1951 2001 1950s Noughties 1950s Noughties

Umbria 8461.07 803,918 853,676 0.019 0.036 195.92 352.88 (1956–2002) Molise 4461.03 406,823 347,628 0.005 0.027 56.93 346.00 (1956–2002) Abruzzo 10,826.99 1,277,207 1,328,832 0.007 0.034 56.71 276.48 (1956–2002) Marche 9727.70 1,362,863 1,469,826 0.017 0.052 120.73 344.12 (1954–2007) Lazio (1956–2004) 17,206.40 3,340,798 5,089,737 0.015 0.077 78.89 259.50 Sum and average 50,683.19 7,191,609 9,089,699 0.013 0.045 101.84 315.80 Journal of Land Use Science 151

It is interesting to observe that, although per capita values of urbanization were very different in the 1950s, there was a realignment of all the regions at about 300 m2/inhabitant in the 2000s, thus marking an urbanized area requirement constant at regional level in contemporary society. In confirmation of this, the per capita quantity in the year 2000 has a standard deviation of 13% of the average for the five regions, while this deviation exceeded 57% of the average in the 1950s and moreover seems to be independent from demographic changes and the varying number of industries and services present in the regions. As a matter of fact, in the 50 years considered, there has been substantial demographic stability (Table 4) in Umbria, Marche, Abruzzo, and Molise (the average yearly rate is about 1‰, while Molise touched −3%). The only region with a significant rise in population has been Lazio (with an average yearly rate of 8%), but in this regard, it is important to clarify that for decades the region containing Rome has received a larger number of migrants from Central and southern Italy, attracted by the many job opportunities offered by the metropolitan area of the capital. Despite these differences, the present-day per capita urbanization value has reached similar levels. The correlation analysis carried out on a municipal basis between urbanization and population variation rates in the 50 years considered (Figure 3) still shows significant dif- ferences between the two groups of regions Marche–Umbria and Abruzzo–Lazio–Molise. In the first group, common aspects include the scarce dependence between the two vari- ables (R2 not greater than 0.27) and limited increase in urbanization (between 1% and 1.5%) in the case of demographic stability during that time span. In the other three regions, the regression curve is very different: the dependence between the variables (R2 between 0.31 and 0.37) is significantly higher, while the increase in urbanization corresponding to a zero-rate demographic rise is of about 5%. In these cases, the angular coefficient of the regression curves is much higher, suggesting that even modest demographic variations have been followed by significant increases in urbanized areas. This confirms what we stated earlier regarding the ‘run-up’ phenomenon of per capita levels of urbanization that has occurred in the group of three regions Abruzzo– Lazio–Molise and that in half a century has led them to conform with the ‘standard’ average level of 300 m2/inhabitant of urbanization which Marche and Umbria were far closer to already back in the 1950s. The regions considered are formed by 1155 municipalities of which the majority, as evidenced by Figure 3, have witnessed a demographic decline in the 1956–2000 period. In the entire territory examined, only two of these municipalities in the 1950s were urban-

Downloaded by [Bernardino Romano] at 10:32 22 July 2014 ized beyond 20%, while approximately 700 did not even reach 1%. After the year 2000, municipalities urbanized beyond the 20% threshold were 32, while over 350 were around 5%, and only 175 remained below the level of 1% (Figures 4 and 5). Figure 6 shows that the phenomenon is more intense in some inland areas of Lazio and Abruzzo, but above all along the coasts of the Tyrrhenian and Adriatic seas. Considering a coastal strip 500 m in width, over the past 50 years, the overall urbanization growth values along it amount to almost 350% for the Tyrrhenian side and approximately 300% for the Adriatic side, thus evidencing the important transformations that have occurred along the coasts. In the last post-war period, urbanization along the coastline of the Lazio region barely exceeded 1500 ha, but the situation changed drastically after the year 2000, when urbanized areas along the coast reached almost 5500 ha. Analyzing the 390 km coastline of Molise, Abruzzo and Marche from a historical perspective has shown that urbanization along the coastal strip has risen from just over 10% in the 1950s to over 30% today, with Marche reaching a peak of 41% (Table 5). It is also interesting to note that the daily urbanization rate of this strip over the past 50 years, assessed as surface and linear 152 B. Romano and F.Zullo

(a) Umbria region

R2 = 0.2746 Urbanization variation rate variation Urbanization

–0.3 –0.2 –0.1 0 0.1 0.2 0.3 0.4 Demographic variation rate

(b) Molise region

R2 = 0.3705 Urbanization variation rate variation Urbanization

–0.3 –0.2 –0.1 0 0.1 0.2 0.3 Demographic variation rate

(c) Lazio region 2 R = 0.3447 Downloaded by [Bernardino Romano] at 10:32 22 July 2014 Urbanization variation rate variation Urbanization

Area del tracciato

–0.3 –0.2 –0.1 0 0.1 0.2 0.3 0.4 Demographic variation rate

Figure 3. Correlation analysis between urban increasing rate and demographic variation rate (1950s–2000s) on a municipal basis. Journal of Land Use Science 153

(d) Abruzzo region

R2 = 0.3199 Urbanization variation rate variation Urbanization

–0.3 –0.2 –0.1 0 0.1 0.2 0.3 0.4 Demographic variation rate

(e) Marche region

R2 = 0.1401 Urbanization variation rate variation Urbanization

–0.3 –0.2 –0.1 0 0.1 0.2 0.3 0.4 Demographic variation rate

Figure 3. (Continued).

distance, is very similar (about 2100 m2/day and around 2 km/year) on both the Adriatic Downloaded by [Bernardino Romano] at 10:32 22 July 2014 and Tyrrhenian coasts. In addition to the coastal strips in the regions of Central Italy, urban growth has also had a significant impact on inland low-hilly areas and basins where the main towns of the provinces are situated that have always sought economic conditions comparable to those of coastal areas (Figure 6). The policies pursued to this end for decades have always led to an excessive number of public and private services and regular incentives for residential and productive building activities, regardless of the population load and what the places in question were actually suitable for. Regarding demographic trends, Figure 7 shows the distribution, on a municipal basis, of the values of the demo-urban increment index (DUI). This parameter has been obtained as follows:

urb −   = (01 51) 2/ DUI m inhabitant pop(01−51) 154 B. Romano and F.Zullo

Pesaro

<1% Urbino

1–5% Ancona 5–10% 10–20% Macerata

>20% Perugia

Ascoli piceno

Teramo

Ter ni Pescara

Viterbo L'aquila Rieti Chieti

Roma

Isernia Frosinone Campobasso

Latina

0 20 40 80 120 160 km

Figure 4. Map of percentage of urbanization in municipalities in the 1950s.

Pesaro

<1% Urbino

1–5% Ancona 5–10% 10–20% Macerata

>20% Perugia

Ascoli piceno

Teramo

Ter ni Downloaded by [Bernardino Romano] at 10:32 22 July 2014 Pescara

Viterbo L'aquila Chieti Rieti

Isernia Frosinone Campobasso

Latina

0204080120160 km

Figure 5. Map of percentage of urbanization in municipalities in the 2000s. Journal of Land Use Science 155

Pesaro

Urbino

<100% Ancona 100–200% 200–350% Macerata

350–500% Perugia 500–800% 800–1200% Ascoli piceno

1200–2500% Teramo Ter ni >2500% Pescara

Viterbo L'aquila Chieti Rieti

Roma

Isernia Frosinone Campobasso

Latina

0 20 40 80 120 160 km

Figure 6. Increased rate of urbanized areas between the 1950s and 2000.

where urb(01–51) is the difference between urbanized areas in municipalities between the 1950s and the early 2000s and pop(01–51) is the variation in the population residing in municipalities between the 1950s and the early 2000s. Figure 7 shows only the positive DUI values, i.e. the values of those municipal ter- ritories where stable or increased urbanized surfaces are matched by a population rise, and a classification based on per capita increased urbanized surfaces (the amount of land consumed per inhabitant acquired by the municipality in the period considered). The map shows that average-sized and big cities are mostly in this condition (main cities of provinces or regions) and their surrounding hinterland, as well as coastal strips owing to the driving

Downloaded by [Bernardino Romano] at 10:32 22 July 2014 effects of agricultural, industrial, and tourist economies. Almost all the areas resulting from the aforementioned selection had DUI values at the highest levels of the assessment scale (over 500 m2/inhabitant in urbanized surface increase). Another index examined, complementary to the DUI, is the demo-urban contradiction index (DUC), which is calculated as follows:

urb −   = (01 51) 2/ DUC − m inhabitant lost pop(01−51)

where urb(01–51) is the difference between urbanized areas in municipalities between the 1950s and the 2000s and −pop(01–51) is the demographic drop in municipalities between the 1950s and the 2000s. In this case, we selected only municipalities with a negative demographic balance between 1951 and 2001 and calculated the increase in urbanized land between the 1950s and the year 2000, later checking the quantity of the urbanized land corresponding to every 156 B. Romano and F.Zullo / day) 2 126.36 702.82 2069.37 1154.48 2185.92 2185.92 Land uptake speed (m (%) increasing Urban area 1950s-noughties Urban % noughties 1950s Urban % increasing (ha) Urbanized area noughties (ha) Urbanized area Downloaded by [Bernardino Romano] at 10:32 22 July 2014 1950s (ha) Urbanized area 6209.94 292.15 1472.18 1180.03 4.07 23.71 503.91 8721.09 1414.23 3647.57 2233.34 16.22 41.82 257.92 1782.81 59.87 272.03 212.16 3.36 15.26 454.37 area (ha) 33,365.71 1583.26 5412.99 3829.73 4.75 16.22 341.89 Coastal belt Table 5. Differences per region in urbanized areas along coastal strips having a width of 500 m. Regions Marche Abruzzo Molise Lazio Adriatic coastTirrenian coast 16,713.84 33,365.71 1766.25 1583.26 5391.78 5412.99 3625.53 3829.73 10.57 4.75 32.26 16.22 305.27 341.89 Journal of Land Use Science 157

Pesaro

Urbino

<200% Ancona 200–300 300–500 Macerata

500–800 Perugia >800 Ascoli piceno

Teramo

Ter ni Pescara L'aquila Viterbo Rieti Chieti

Roma

Frosinone Isernia Campobasso

Latina

02040 80 120 160 km

Figure 7. Map to select the positive values of the DUI.

inhabitant lost. The geographical outcome is extremely varied (Figure 8), but shows a sig- nificant trend toward urban growth even in places subject to major population drops, with concentrations of the highest values (over 800 m2 more urbanized surfaces for every inhabi- tant lost) in the mid-hilly strips, but also in inland mountainous and submountainous areas. The tourist models applied to mid-mountainous areas, based on holiday homes, are cer- tainly the main cause of this, but undoubtedly the policies pursued for decades to provide economic support to so-called ‘marginal areas’ have contributed to this too. The propensity of municipalities to collect taxes and dues to support public services is hardly negligible, but a significant thrust comes from the tendency, over the past 30 years, of privates to invest

Downloaded by [Bernardino Romano] at 10:32 22 July 2014 in real property to offset either reduced the economic convenience or high risks of other forms of investment.

4. Effects on landscape An effective interpretation of landscape effects of urban sprawl over the past 50 years is the one based on the 37 types of physiographic landscape units censused by the National Institute for Environmental Protection and Research (ISPRA, 2004). In the post-war period, the ‘intramountainous plateaus’ had the highest urbanization rates, with almost 6% of artificialized land, while coastal, open, and valley-line plains were well below 2%. The urbanization analyzed at the year 2000 shows a clear reversal in the value of this index: coastal plains have soared from the previous 2% to over 16%, just like the category of coastal elevations which have seen their urbanization rate reach values in excess of 18%, while the other types of plains have increased well beyond 4% and even 5%. However, it is particularly interesting to note that the ranking of hilly areas, scarcely or not at all 158 B. Romano and F.Zullo

Pesaro

Urbino <100 Ancona 100–200

200–500 Macerata 500–800 Perugia >800%

Ascoli piceno

Teramo

Ter ni Pescara L'aquila Viterbo Rieti Chieti

Roma

Frosinone Isernia Campobasso

Latina

0 20 40 80 120 160 km

Figure 8. Map of the DUC.

encroached upon by constructions in the 1950s, has risen. Hilly areas of all types have shown a significant increase in their urbanization rate which, from their original level rang- ing between 0% and 5%, now exceeds 2% by far and in some cases even 8%, that is to say closer to the values of plains. In a country like Italy which lacks plains that may be easily saturated (approximately 23% of the national territory), these are clear signs that denote a trend of massive ‘attacks’ of hilly areas by settlements, with considerable risks of altering agricultural landscapes, among the finest in Europe, and significantly deteriorating ecosystems, since over 40% of Nature 2000 Sites of the European ecological network (SCIs) are found in hilly areas.

Downloaded by [Bernardino Romano] at 10:32 22 July 2014 While in the 50 years considered, plains were replaced by settlements at an average pace of over 18 ha/day, for hilly areas the rate has been of almost 6 ha/day, but this could merely be the sign of the trigger for subsequent and more vigorous development (Figures 9–11). Figure 12 shows a simulation made throughout the national territory by applying the urbanization rate recorded in the past 50 years in the regions studied to the landscape units (Figure 9). The results highlight national sensibility concentrated essentially in some sensitive areas which, in addition to having suffered urban events over the past 50 years, still have a significant predisposition toward additional increases even today.

5. Conclusions The research conducted in the regions of Central Italy has highlighted some fundamental aspects: first, the average regional per capita urbanization value is about 300 m2/inhabitant for any type of territory, which suggests that this may be a standard need of present-day society. This value, reached spontaneously in half a century in various regions starting from Journal of Land Use Science 159

Figure 9. Difference in the urbanization rate of Italian landscape units between the 1950s and after the 2000s (data referred to sample of regions studied). Downloaded by [Bernardino Romano] at 10:32 22 July 2014

Figure 10. Variation of the urbanization rate in Italian landscape types between the 1950s and after the 2000s (data referred to sample of regions studied).

very diverse bases, may be considered a reference threshold for future planning beyond which other land should not be used for urban functions. Second, we have observed that the increase in urbanized areas is scarcely correlated to demographic trends, either positive or negative. In other words, the development of urban areas over the past 50 years has been marked by a huge dispersion in diffused forms scarcely governed by interpretable rules, leading to the systematic reproduction of a city model ‘lacking town planning’. The third point concerns the relationship with the landscape, that is to say the signs of urban sprawl from the plains to the hills with adverse effects on the agro- and ecosystems, the most valued agricultural productions and rural landscape. 160 B. Romano and F.Zullo

Figure 11. Average rate of daily urban conversion of land per type of landscape (m2/day) for the sample of regions studied.

In this regard, it is important to note that in Italy, the contact between city and countryside has never been clear-cut, but rather nuanced between consolidated fabric, non- consolidated fabric, dispersed and degraded fabric, urbanized countryside, and agricultural areas. The periurban areas are always marked by forms suggesting their precarious state of pre-urbanization. These reasons have led to anarchy in the layout of Italian territories, where residential settlements are always scattered and have a chaotic and metastatic organization from a developmental point of view (Figure 13), as evidenced by the values of the UDI in the case of Marche and Umbria. The ensuing urban structure is lacking in public spaces and related services, profoundly devastating for the agricultural landscape, the integrity, and

Downloaded by [Bernardino Romano] at 10:32 22 July 2014 ecological efficiency of natural habitats and gradually exacerbates all the adverse effects of uncontrolled urbanization described in the Introduction to this article. Low-density rural settlement, especially when tied to an urban lifestyle, is a source of major organizational difficulties for services and transport. As a matter of fact, especially in Central and southern Italy, ‘hub-and-spoke’ (Babcock, 2002) public mobility models are almost inapplicable, owing to the failure to meet the necessary user and distance thresholds. A territorial organization of this kind inevitably forces the residing population to depend on private transport means, with all the ensuing consequences for environmental sustainability and quality of life. The information emerging from this study may serve as a reference for town planning coordination tools so that they may help stabilize the amount of artificialized areas and reorganize forms and functions of urban spaces. In this respect, some positive signals come from Lombardia and Umbria regions that issued laws about regional ecological networks, where the land uptake is controlled, but with tools that should be improved (Malcevschi, 2010; Romano, 2009). Journal of Land Use Science 161 Downloaded by [Bernardino Romano] at 10:32 22 July 2014

Figure 12. Simulation, extended to landscape units across the national territory, of the percentage variation of urbanization calculated on the sample regions in the course of the past 50 years.

Desirable territorial governance policies should be geared mainly toward the system- atic implementation of actions for the functional recovery and reconversion of abandoned urbanized areas. In order to do this, local governments need to have technical and admin- istrative monitoring tools based on actual data on the evolution of land transformation at appropriate details scale. 162 B. Romano and F.Zullo Aggregate growth t t t 1 2 3 Time ‘Metastatic like’ growth

Figure 13. Differential chart, urban development in seamless aggregates, very frequent in northern Europe, and the generalized, metastatic-like urban development in Italy.

In Italy, at present these tools do not exist and every municipality works independently as far as the size and distribution of urban areas of any kind are concerned. Moreover, struc- tured communication links between regions and municipalities about land-use changes are not formalized in current legislation. A so disconnected land planning system makes impossible any quantitative control of transformations on a regional scale. Therefore, one of the first essential steps to be taken toward regulation involves the setting up of Regional Observatories and Land Registers which can be used to monitor the development of the phenomenon at different levels (municipal and regional) and on different scales, using advanced GIS technology.

Acknowledgments We thank the Region of Umbria (Biodiversity and Landscape Observatory) for economic sup- port of this research. We are also grateful to WWF Italia Onlus and the Environmental Engineers Downloaded by [Bernardino Romano] at 10:32 22 July 2014 Manuele Cargini, Doriana Febo, Consuelas Giuliani, and Cristina Iezzi for their collaboration for data providing and elaboration. Thanks are due to the editor and the anonymous reviewer for their comments.

References APAT. (2005). La realizzazione in Italia del progetto europeo Corine Land Cover 2000 (Rapporti 36/2005). Roma: APAT. Astengo, G., & Nucci, C. (Eds.). (1990). It.Urb.80, Rapporto sullo stato dell’Urbanizzazione in Italia. Quaderni Di Urbanistica Informazioni (Vol. 8). Roma: INU. Babcock, B. A. (2002). Making sense of cities: A geographical survey (pp. 63–94). London: Arnold. Battisti, C. (2011). Ecological network planning, from paradigms to design and back: A cautionary note. Journal of Land Use Science. doi:10.1080/1747423X.2011.639098 Batty, M. (2008). The size, scale and shapes of cities. Science, 319, 769–771. Berdini, P. (2009). Il Consumo Di Suolo in Italia: 1995–2006. Democrazia E Diritto, 1, 60–73. Bonifazi, C., & Heins, F. (2001). Dynamics of urbanisation in Italy. Proceedings of XXIV general population conference, IUSSP, Salvador, Brazil, August 18–24, 2001 (pp. 1–26). IUSSP: Paris. Journal of Land Use Science 163

Bossard, M., Feranec, J., & Otahel, J. (2000). Corine land cover technical guide (EEA Technical Report 40), p. 105. Copenhagen: EEA. Bundesregierung. (1985). Unterrichtung durch die Bundesregierung. Bodenschutzkonzepte der Bundesregierung. Deutscher Bundenstag, Drucksache 10.2977, Bonn. Capello, R. (2001). Urban growth in Italy: Economic determinants and socio-environmental conse- quences. International symposium in urban design on “Urban systems and public place”, Umeå, Sweden, June 7–8, 2001, CERUM, Report 10 (pp. 1–37). CERUM: Sweden. Cardoza, A. L. (1994). The large landed aristocracy of piedmont, retreat and adaption 1880–1930. In P. P. D’Attorre & A. de Bernardi (Eds.), Studi Sull’agricoltura Italiana (pp. 65–88). Milan: Feltrinelli. CNR-IPRA. (1988). Interaction and competition between urban systems and agriculture for land use purposes (IPRA doc. XXV). : Pitagora. Comber, A. J. (2008). Land use or land cover? Journal of Land Use Science, 3(4), 199–201. EEA. (2006). Urban sprawl in Europe: The ignored challenge. Copenaghen: Directorate general Joint Research Center. Ellis, C. E., & Ramankutty, N. (2008). Putting people in the map: Anthropogenic biomes of the world. Frontier in Ecology and the Environment, 6(8), 439–447. Emiliani, V. (2007, October). Il consumo di suolo in Italia e in Europa. Atti Convegno Nazionale Comitato per la bellezza, Roma. Falcucci, A., & Maiorano, L. (2008). Land use and misuse: Landscape changes in Italy since 1950. In C. Teofili & S. Clarino (Eds.), Riconquistare Il Paesaggio, La Convenzione Europea Del Paesaggio E La Conservazione Della Biodiversità in Italia (pp. 176–187). Roma: MIUR. Gambino, R., & Romano, B. (2004). Territorial strategies and environmental continuity in mountain systems, the case of the Apennines (Italy). In D. Harmon & G. Worboys (Eds.), Managing moun- tain protected areas: Challenges and responses for the 21st century (pp. 65–77). Andromeda: IUCN. Garcia-Call, A. (2011). The process of residential Sprawl in Spain: Is it really a problem? Urban Research and Practice, 4(3), 250–263. Hall, P., Gracey, H., Drewett, R., & Thomas, R. (1973). The containment of urban England (Vol. I, pp. 9–58). London: Allen & Unwin. Hauri, E., Steiner, V.,& Vinzens, M. (2006). Human settlement in Switzerland, spatial development and housing. Housing Bulletin, 78, 1–80. Illy, A., Hornych, C., Schwartz, M., and Rosenfeld, M. T. W.(2009). Urban growth in Germany – The impact of localization and urbanization economies. (IWH discussion papers 19:1–53). Atlanta, GA: Halle Institute for Economic Research. Irwin, E. G., & Bockstael, N. E. (2007). The evolution of urban sprawl: Evidence of spatial heterogeneity and increasing land fragmentation. PNAS, 104(52), 20672–20677. ISPRA. (2004). Carta dei tipi e delle unità fisiografiche d’Italia scala 1:250.000. Retrieved from http://www.isprambiente.gov.it/site/it-it/Servizi_per_l’Ambiente/Sistema_Carta_della_Natura/ Carta_della_Natura_alla_scala_1_250.000. ISTAT. (2009). Rapporto Annuale La situazione del Paese nel 2008. Roma: ISTAT. Downloaded by [Bernardino Romano] at 10:32 22 July 2014 Lowry, I. S. (1990). World urbanization in perspective. Population and development review, 16, 148–176. Malcevschi, S. (2010). Reti ecologiche polivalenti:Infrastrutture e servizi ecosistemici per il governo del territorio. Milano: Il Verde. Mellor, R. (1983). The urbanization of Britain, a review. IJURR, 7(3), 380–403. Mercalli, L. (2009). Che Tempo Che Farà. Breve Storia Del Clima Con Uno Sguardo Al Futuro. Milan: Rizzoli. Pileri, P. (2007). Compensazione Ecologica Preventiva. Milan: Carocci. Plotkin, S. (1987). Property, policy and politics: Towards a theory of urban land-use conflict. IJURR, 11(3), 382–404. Reid, Jr., & Joseph, D. (1975). Sharecropping in history and theory. Agricultural History, 49(2), 426–440. Romano, B. (2009). Le interferenze insediative. In Ragni, B. (Ed.), RERU, Rete Ecologica Regionale dell’Umbria (pp. 65–110). Petruzzi: Regione Umbria. Romano, B., & Zullo, F. (2010). Tecniche di rilevamento e valutazione del fenomeno di conver- sione urbana dei suoli. Atti della Sesta Conferenza Nazionale INPUT 2010, Potenza (Vol. I, pp. 327–337). Potenza: Università della Basilicata. 164 B. Romano and F.Zullo

Sala, E. O., Chapin, F. S., Armesto, J. J., Berlow, E., Bloomfield, J., Dirzo, R., . . . Wall, D. H. (2000). Global biodiversity scenarios for the year 2100. Science, 287(5459), 1770–1774. Shaban, R. A. (1987). Testing between competing models of sharecropping. Journal of Political Economy, 95(5), 893–920. Sharma, L., Pandey, P. C., & Nathawat, M. S. (2012). Assessment of land consumption rate with urban dynamics change using geospatial techniques. Journal of Land Use Science, 7(2), 135–148. Singh, N. (1989). Theories of sharecropping. In P. Bardhan (Ed.), The economic theory of agrarian institutions (pp. 33–72). Oxford: Clarendon Press. Yanitsky, O. (1986). Urbanization in the USSR, theory, tendencies and policy. IJURR, 10(2), 265–287. Zaninetti, J. M. (2006). Urban sprawl in France, a regional typology of urbanization trends and its demographics and economy background. Bulletin of Geography, 5, 5–20. Downloaded by [Bernardino Romano] at 10:32 22 July 2014