Abstract
Assuming landscape transformations as a process fueling the local level of vulnerability to wildfires, this work investigates the spatial distribution of selected land-use classes for two years (1975 and 2018) in a metropolitan region of the Mediterranean basin (Athens, central Greece). Built-up settlements and cropland expanded moderately over time, facing a slight decline in forests and semi-natural areas. These changes resulted in the inherent growth in local vulnerability to wildfires estimated using a composite indicator, namely the Fire Risk (FR) index developed in the framework of the MEDALUS international research project financed by the European Commission. Crop mosaics and discontinuous settlements were the classes contributing the most to FR growth. The empirical findings of our work suggest how the conversion of fringe landscapes toward simplified (and, likely, low-quality) cropland and pasture land, as well as the inherent fragmentation of natural/semi-natural landscape patches, is detrimental to environmental quality, increasing the potential exposure to peri-urban fires.
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1 Introduction
Suburban landscapes include a variety of land-use types reflected in fragmented morphologies and heterogeneous functions (Antrop, 2004; Duvernoy et al., 2018). Recent landscape transformations determined new elements and landscape structures superimposed upon the traditional (urban–rural) landscape mosaics (Alberti, 2010; Allen, 2003; Coluzzi et al., 2022; Delfanti et al., 2016Mc Donnell et al., 1997). These phenomena may reduce the intrinsic environmental quality of entire districts, determining an increased fragility of habitats, especially when located in ecologically sensitive areas (Foster et al., 2003; Imbrenda et al., 2022a; Jim, 2004; Johnson, 2001; Nickayin et al., 2022; Salvati et al., 2008; Zambon et al., 2018).
Mediterranean metropolises were affected by intense landscape transformations at the fringe, thanks to the rapid expansion of settlements observed since the 1950s and following the post-war demographic boom (Carlucci et al., 2018; Salvati, 2014; Salvati & Carlucci, 2016). These trends determined (and sometimes consolidated) a land take causing an irreversible loss in soil resources and cultural/natural heritages (Antrop, 2004; Atmis et al., 2007; Bianchini et al., 2021; Catalàn et al., 2008; Chorianopoulos et al., 2010; De Marco et al., 2019; Economidou, 1993; Nickayin et al., 2021; Salvati et al., 2012a; Santarsiero et al., 2022). Urbanization of already natural land with olive groves, vineyards, annual crops or shrublands, pastures and woodlots was largely documented along the fringe of Mediterranean cities (Barbati et al., 2013; Biasi et al., 2015; Cecchini et al., 2019; Paul & Tonts, 2005; Salvati et al., 2013a, Simoniello et al., 2022).
Less knowledge is however available on how landscape elements evolve, creating new structures and original patterns of functions (Imbrenda et al., 2022b; Kosmas et al., 2016; Marull et al., 2009), that may impact environmental quality at large (Falcucci et al., 2007; Salvati & Zitti, 2007, 2009; Zambon et al., 2017). In such contexts, wildfires shape the ecological fragility of Mediterranean fringe landscapes determining environmental degradation (e.g., on sloping/rocky/arid land, see Kosmas et al., 2000a, 2000b; Simeonakis et al., 2007; Salvati & Bajocco, 2011; Pignatti et al., 2015; Santarsiero et al., 2020; Nolè et al., 2020; Samela et al., 2022). Based on these premises, we assume land-use change as exerting a negative impact on the ecological fragility of a given territory fueling the intrinsic vulnerability to wildfires, likely determined by, e.g., modifications in plant cover and vegetation composition (Bajocco et al., 2015, 2016; Fares et al., 2017; Smiraglia et al., 2015).
A complete survey of land-use changes over 43 years (1975–2018) allowed us to estimate the spatiotemporal variation in a composite index of vulnerability to wildfires in a metropolitan region of Southern Europe (Athens, Greece) experiencing comparatively high exposure to fires than other metropolises in the macro-region, thus representing a sort of ‘worst scenario’ for other socioeconomic contexts in the same European quadrant. The explicit knowledge stemming from our study may support strategic planning containing wildfires and mitigating soil degradation and habitat fragmentation along urban fringes.
2 Methodology
The investigated area covers more than 3000 km2, a large part of the administrative region of Attica, Central Greece (Fig. 1). The area was partitioned into 115 mainland municipalities (58 forming Athens’ conurbation that extends 430 km2), including two municipalities on Salamina island close to Piraeus harbor, and excluding the remaining municipalities in the other islands of Argosaronic Gulf, Aegean Sea. The area consists of mountains with the highest elevation in Mount Parnitha, 25 km far away from downtown Athens (1413 m on the sea level). Three coastal plains (Messoghia, Marathon and Thriasio) are located immediately outside Athens’ conurbation (Ciommi et al., 2019; Di Feliciantonio et al., 2018; Salvati et al., 2012b, 2013b). The population living in the area amounted to 1.6 million people in 1951, increasing to 2.7 million people in 1971 (approximately 900 inhabitants/km2) and reaching 3.7 million people in 2021 (nearly 1200 inhabitants/km2). Urban population in total population declined from the peak of 92% observed in 1971 to 80% in 2021 (Gavalas et al., 2014).
The spatial distribution of selected land-use classes was investigated over two years (1975 and 2018) based on (i) the LaCoast (LC) digital cartography available for 1975 at 1:100,000 scale and covering the European coastal areas (Perdigao and Christiansen, 2000) and (ii) the Corine Land Cover (CLC) pan-European digital cartography available at the same spatial scale for 2018 (Büttner et al., 2017).
These two geospatial sources were regarded as comparable digital maps covering the study area homogeneously in the two-time points, in line with the nomenclature of the CLC project. Being coordinated by the European Environmental Agency (EEA), this initiative provided land-use maps multiple times for the whole of Europe with an inventory based on satellite images as the primary information source, with spatial scale (1:100.000), geometric resolution (minimum mapping unit of 25 ha), and minimum width of linear elements (100 m) reflecting the trade-off between production costs and level of detail of land cover information. By providing a comprehensive description of the landscape in the study area (Economidou, 1993), the standard CLC nomenclature includes 44 land classes (Salvati & Bajocco, 2011) grouped into a three-level hierarchy (1: artificial surfaces, 2: agricultural areas, 3: forests and semi-natural areas, 4: wetlands, and 5: water bodies).
The vulnerability of plant cover to fires was derived, composing the information from the two maps described above following the rules dictated by a quantitative approach developed in the Environmentally Sensitive Area (ESA) methodology of the Medalus II (Mediterranean Desertification and Land Use) international cooperative research project (Kosmas et al., 1999). Being explicitly validated on the field in several target sites (Brandt, 2005), this framework was applied at both the regional and local scale in Mediterranean regions displaying locally differentiated environmental conditions (Imbrenda et al., 2021; Lanfredi et al., 2022; Pace et al., 2023).
Vegetation vulnerability to fires was estimated by attributing a score between 1 and 2 to each land-use class and leading to a final indicator named FR (‘Fire Risk’: Salvati & Bajocco, 2011). The approach was supported by a preliminary analysis (Kosmas et al., 2000a) developed to define the correlation between each land-use type and fire vulnerability based on literature review and field research mostly collected in the framework of Medalus projects (e.g., Basso et al., 2000; Brandt, 2005; Kosmas et al., 2000b). The results of a sensitivity analysis and a focus group allow for confirming the most valid, low-cost, and efficient score set (Kosmas et al., 1999). Ranging from 1 (the lowest vulnerability to wildfires) to 2 (the highest vulnerability to wildfires), FR indicated zero values assigned to land-use classes that were excluded from the analysis, namely compact urbanization (Salvati & Zitti, 2012).
The spatial distribution of the FR index was mapped for 1975 and 2018 using the same spatial resolution of CLC maps. Land changes and the related variations in FR were studied at the first CLC-class level. This analysis gave information on the positive (or negative) contribution of each class to FR. Changes over time (1975–2018) in the average FR score were quantified separately for each municipality of the study area (n = 115) by using the ‘intersect’ tool provided with ArcGIS software (ESRI Inc., Redwoods, USA) after the overlap between the FR map in 1975 (or 2018) and the shapefile depicting the municipality’s boundaries.
3 Results
Basic land-use changes between 1975 and 2018 were delineated in Table 1 and indicate that built-up areas and cropland expanded into other lands, although with different rates of increase, whereas forest/semi-natural landscape matrices decreased slightly. These changes resulted in a global rise of the FR index (0.1% per year – from 1.42 in 1975 to 1.44 in 2018). ‘Complex cultivation patterns’ contributed the most to the increase of the FR index (4.3% more than the average increase); ‘land principally occupied by agriculture, with significant areas of natural vegetation’ was the second contributor (2.0%). The highest negative contribution to FR came from ‘sparsely vegetated areas’ (−3.4%), ‘olive groves’ (−3.1%) and ‘mixed woodlands’ (−2.5%). At the aggregate level, however, urbanization (e.g., discontinuous, low-density settlements) contributed to FR more (0.75%) than cropland (+0.3%).
The spatial distribution of the FR index in 2018 was illustrated in Fig. 2. The districts with a high vulnerability to wildfires are concentrated in the Athens fringe. At large, plant cover vulnerability does not seem correlated with the distance from downtown Athens (Spearman rank correlation test, p > 0.05). Changes in the FR index along the 43 observation years were mapped at the municipal scale (Fig. 3). The increase in the FR index was spatially heterogeneous, concentrating in suburban municipalities North and East of Athens; these areas experienced low-density urban expansion. Few municipalities at the fringe also showed a moderate reduction in the FR index over time possibly due to the loss in forest cover caused by recurrent fire events in the last decades.
4 Discussion
Transforming fringe landscapes into low-quality cropland and fragmented forest mosaics is detrimental to environmental quality, exalting the ecological fragility of land (Corona, 2018; Corona et al., 2016; Nocentini et al., 2017; Recanatesi et al., 2016). As a possible response to urban sprawl, a rising vulnerability to wildfires was recorded in Attica, although with a mostly heterogeneous spatial pattern that suggests how suburbs between 15 and 30 km from downtown Athens are mostly endangered. Results also support the relevance of an ecological spiral of human pressure resulting in the increase of local vulnerability to wildfires. The recurrent fires in Attica (Salvati et al., 2012a, 2012b) have likely represented an additional engine of land-use changes. Coupled with the increasing events of droughts and the asynchronous distribution of rainfall across large areas (Coluzzi et al., 2020; Lanfredi et al., 2020), the synergistic impact of wildfires and landscape transformations have consolidated the local vulnerability to wildfires (Cillis et al., 2022; Salvati et al., 2013a, 2013b).
These trends can be assessed continuously by integrating remote sensing, geospatial information sources (e.g., Corine Land Cover maps), and field surveys estimating the environmental impact of urban sprawl (European Environment Agency, 2016). Altering landscape patterns and fragmenting high-quality vegetation covers, urban sprawl fueled the intrinsic divergence in ‘extensive’ and ‘intensive’ land uses, exacerbating the spatial polarization in high- and low-quality vegetation areas and thus increasing the local vulnerability of vegetation cover to wildfires (Pickett et al., 2001). The increase of vegetation vulnerability to fires because of inherent homogenization in species composition, disruption of the hydrological systems, and modification of energy flow and nutrient cycling (e.g., Alberti, 2010; Foster et al., 2003; Johnson, 2001) should be also monitored extensively in the framework discussed in our work.
5 Concluding Remarks
Sustainable land management in fringe districts is made more urgent with climate change and requires appropriate assessment methodologies and conservation strategies focusing on relict, high-quality vegetation cover (Chelleri et al., 2015; Ciommi et al., 2018; Perrin et al., 2018). Efforts are finally needed to effectively integrate ecological studies and socioeconomic disciplines in a comparative, local-scale perspective informing fire science and the prevention/suppression cycle in suburban areas.
References
Alberti, M. (2010). Maintaining ecological integrity and sustaining ecosystem functions in urban areas. Current Opinion in Environmental Sustainability, 2, 178–184.
Allen, A. (2003). Environmental planning and management of the peri-urban interface: Perspectives on an emerging field. Environment & Urbanization, 15(1), 135–147.
Antrop, M. (2004). Landscape change and the urbanization process in Europe. Landscape and Urban Planning, 67(1–4), 9–26.
Atmiş, E., Özden, S., & Lise, W. (2007). Urbanization pressures on the natural forests in Turkey: An overview. Urban Forestry & Urban Greening, 6(2), 83–92.
Bajocco, S., Ceccarelli, T., Smiraglia, D., Salvati, L., & Ricotta, C. (2016). Modeling the ecological niche of long-term land use changes: The role of biophysical factors. Ecological Indicators, 60, 231–236.
Bajocco, S., Dragoz, E., Gitas, I., Smiraglia, D., Salvati, L., & Ricotta, C. (2015). Mapping forest fuels through vegetation phenology: The role of coarse-resolution satellite time-series. PLoS ONE, 10(3), e0119811.
Barbati, A., Corona, P., Salvati, L., & Gasparella, L. (2013). Natural forest expansion into suburban countryside: Gained ground for a green infrastructure? Urban Forestry & Urban Greening, 12(1), 36–43.
Basso, F., Bove, E., Dumontet, S., Ferrara, A., Pisante, M., Quaranta, G., & Taberner, M. (2000). Evaluating environmental sensitivity at the basin scale through the use of geographic information systems and remotely sensed data: An example covering the Agri basin - Southern Italy. CATENA, 40, 19–35.
Bianchini, L., Egidi, G., Alhuseen, A., Sateriano, A., Cividino, S., Clemente, M., & Imbrenda, V. (2021). Toward a dualistic growth? Population increase and land-use change in Rome, Italy. Land, 10(7), 749.
Biasi, R., Brunori, E., Smiraglia, D., & Salvati, L. (2015). Linking traditional tree-crop landscapes and agro-biodiversity in Central Italy using a database of typical and traditional products: A multiple risk assessment through a data mining analysis. Biodiversity and Conservation, 24(12), 3009–3031.
Brandt, J. (2005). Desertification information system to support National Action Programmes in the Mediterranean (DISMED). DIS4ME, Desertification Indicator System for Mediterranean Europe. https://esdac.jrc.ec.europa.eu/public_path/shared_folder/projects/DIS4ME/using_dis4me/dismed.htm. Accessed on January 2023.
Büttner, G., Kosztra, B., Soukup, T., Sousa, A., & Langanke, T. (2017). CLC2018 technical guidelines. European Environment Agency, 25.
Carlucci, M., Chelli, F. M., & Salvati, L. (2018). Toward a new cycle: Short-term population dynamics, gentrification, and re-urbanization of Milan (Italy). Sustainability, 10(9), 3014.
Catalàn, B., Sauri, D., & Serra, P. (2008). Urban sprawl in the Mediterranean? Patterns of growth and change in the Barcelona Metropolitan Region 1993–2000. Landscape and Urban Planning, 85(3–4), 174–184.
Cecchini, M., Zambon, I., Pontrandolfi, A., Turco, R., Colantoni, A., Mavrakis, A., & Salvati, L. (2019). Urban sprawl and the ‘olive’ landscape: Sustainable land management for ‘crisis’ cities. GeoJournal, 84(1), 237–255.
Chelleri, L., Schuetze, T., & Salvati, L. (2015). Integrating resilience with urban sustainability in neglected neighborhoods: Challenges and opportunities of transitioning to decentralized water management in Mexico City. Habitat International, 48, 122–130.
Chorianopoulos, I., Pagonis, T., Koukoulas, S., & Drymoniti, S. (2010). Planning, competitiveness and sprawl in the Mediterranean city: The case of Athens. Cities, 27, 249–259.
Cillis, G., Lanorte, A., Nolè, G., Santarsiero, V., & Ronco, F. (2022). Fire planning of urban-rural interface in open source GIS environment: Case study of the Apulia Region (southern Italy). The International Archives of Photogrammetry, Remote Sensing and Spatial Information Sciences, 48, 97–102.
Ciommi, M., Chelli, F. M., Carlucci, M., & Salvati, L. (2018). Urban growth and demographic dynamics in southern Europe: Toward a new statistical approach to regional science. Sustainability, 10(8), 2765.
Ciommi, M., Chelli, F. M., & Salvati, L. (2019). Integrating parametric and non-parametric multivariate analysis of urban growth and commuting patterns in a European metropolitan area. Quality & Quantity, 53(2), 957–979.
Coluzzi, R., Bianchini, L., Egidi, G., Cudlin, P., Imbrenda, V., Salvati, L., & Lanfredi, M. (2022). Density matters? Settlement expansion and land degradation in Peri-urban and rural districts of Italy. Environmental Impact Assessment Review, 92, 106703.
Coluzzi, R., Fascetti, S., Imbrenda, V., Italiano, S. S. P., Ripullone, F., & Lanfredi, M. (2020). Exploring the use of sentinel-2 data to monitor heterogeneous effects of contextual drought and heatwaves on Mediterranean forests. Land, 9(9), 325.
Corona, P. (2018). Communicating facts, findings and thinking to support evidence-based strategies and decisions. Annals of Silvicultural Research, 42, 1‒2. https://doi.org/10.12899/ASR-1617
Corona P., Cutini A., Chiavetta U., & Paoletti E. (2016). Forest-food nexus: A topical opportunity for human well-being and silviculture. Annals of Silvicultural Research, 40, 1‒10. https://doi.org/10.12899/ASR-1181
De Marco, A., Proietti, C., Anav, A., Ciancarella, L., D’Elia, I., Fares, S., Fornasier, M. F., Fusaro, L., Gualtieri, M., Manes, F., Marchetto, A., Mircea, M., Paoletti, E., Piersanti, A., Rogora, M., Salvati, L., Salvatori, E., Screpanti, A., Vialetto, G., … Leonardi, C. (2019). Impacts of air pollution on human and ecosystem health, and implications for the National Emission Ceilings Directive: Insights from Italy. Environment International, 125, 320–333.
Delfanti, L., Colantoni, A., Recanatesi, F., Bencardino, M., Sateriano, A., Zambon, I., & Salvati, L. (2016). Solar plants, environmental degradation and local socioeconomic contexts: A case study in a Mediterranean country. Environmental Impact Assessment Review, 61, 88–93.
Di Feliciantonio, C., Salvati, L., Sarantakou, E., & Rontos, K. (2018). Class diversification, economic growth and urban sprawl: Evidences from a pre-crisis European city. Quality & Quantity, 52(4), 1501–1522.
Duvernoy, I., Zambon, I., Sateriano, A., & Salvati, L. (2018). Pictures from the other side of the fringe: Urban growth and peri-urban agriculture in a post-industrial city (Toulouse, France). Journal of Rural Studies, 57, 25–35.
Economidou, E. (1993). The Attic landscape throughout the centuries and its human degradation. Landscape and Urban Planning, 24, 33–37.
European Environment Agency. (2016). Urban sprawl in Europe—Joint EEA-FOEN report, EEA, Luxembourg, Report No 11/2016.
Falcucci, A., Maiorano, L., & Boitani, L. (2007). Changes in land-use/land-cover patterns in Italy and their implications for biodiversity conservation. Landscape Ecology, 22(4), 617–631.
Fares, S., Bajocco, S., Salvati, L., Camarretta, N., Dupuis, J. L., Xanthopoulos, G., Guijarro, M., Madrigal, J., Hernando, C., & Corona, P. (2017). Characterizing potential wildland fire fuel in live vegetation in the Mediterranean region. Annals of Forest Science, 74, 1–12. https://doi.org/10.1007/s13595-016-0599-5
Foster, D., Swanson, F., Aber, J., Burke, I., Brokaw, N., Tilman, D., & Knapp, A. (2003). The importance of land-use legacies to ecology and conservation. BioScience, 53(1), 77–88.
Gavalas, V. S., Rontos, K., & Salvati, L. (2014). Who becomes an unwed mother in Greece? Sociodemographic and geographical aspects of an emerging phenomenon. Population, Space and Place, 20(3), 250–263.
Imbrenda, V., Coluzzi, R., Di Stefano, V., Egidi, G., Salvati, L., Samela, C., Simoniello, T., & Lanfredi, M. (2022a). Modeling spatio-temporal divergence in land vulnerability to desertification with local regressions. Sustainability, 14(17), 10906.
Imbrenda, V., Lanfredi, M., Coluzzi, R., & Simoniello, T. (2022b). A smart procedure for assessing the health status of terrestrial habitats in protected areas: The case of the natura 2000 ecological network in Basilicata (Southern Italy). Remote Sensing, 14(11), 2699.
Imbrenda, V., Quaranta, G., Salvia, R., Egidi, G., Salvati, L., Prokopovà, M., Coluzzi, R., & Lanfredi, M. (2021). Land degradation and metropolitan expansion in a peri-urban environment. Geomatics, Natural Hazards and Risk, 12(1), 1797–1818.
Jim, C. Y. (2004). Green-space preservation and allocation for sustainable greening of compact cities. Cities, 21(4), 311–320.
Johnson, M. P. (2001). Environmental impacts of urban sprawl: A survey of the literature and proposed research agenda. Environment and Planning A, 33(4), 717–735.
Kosmas, C., Danalatos, N. G., & Gerontidis, S. (2000a). The effect of land parameters on vegetation performance and degree of erosion under Mediterranean conditions. CATENA, 40, 3–17.
Kosmas, C., Gerontidis, S., & Marathianou, M. (2000b). The effect of land use change on soil and vegetation over various lithological formations on Lesvos. CATENA, 40, 51–68.
Kosmas, C., Karamesouti, M., Kounalaki, K., Detsis, V., Vassiliou, P., & Salvati, L. (2016). Land degradation and long-term changes in agro-pastoral systems: An empirical analysis of ecological resilience in Asteroussia-Crete (Greece). CATENA, 147, 196–204.
Kosmas, C., Kirkby, M., & Geeson, N. (1999). The Medalus project: Mediterranean desertification and land use. Manual on key indicators of desertification and mapping environmentally sensitive areas to desertification. European Commission, Brussels.
Lanfredi, M., Coluzzi, R., Imbrenda, V., Macchiato, M., & Simoniello, T. (2020). Analyzing space–time coherence in precipitation seasonality across different European climates. Remote Sensing, 12(1), 171.
Lanfredi, M., Egidi, G., Bianchini, L., & Salvati, L. (2022). One size does not fit all: A tale of polycentric development and land degradation in Italy. Ecological Economics, 192, 107256.
Marull, J., Pino, J., Tello, E., & Cordobilla, M. J. (2009). Social metabolism, landscape change and land-use planning in the Barcelona Metropolitan Region. Land Use Policy, 27(2), 497–510.
Nickayin, S. S., Coluzzi, R., Marucci, A., Bianchini, L., Salvati, L., Cudlin, P., & Imbrenda, V. (2022). Desertification risk fuels spatial polarization in ‘affected’and ‘unaffected’landscapes in Italy. Scientific Reports, 12(1), 1–11.
Nickayin, S. S., Salvati, L., Coluzzi, R., Lanfredi, M., Halbac-Cotoara-Zamfir, R., Salvia, R., Quaranta, G., Alhuseen, A., & Gaburova, L. (2021). What happens in the city when long-term urban expansion and (Un) sustainable fringe development occur: The case study of Rome. ISPRS International Journal of Geo-Information, 10(4), 231.
Nocentini S., Buttoud G., Ciancio O., & Corona P. (2017). Managing forests in a changing world: the need for a systemic approach. A review. Forest Systems, 26(1), eR01. https://doi.org/10.5424/fs/2017261-09443
Nolè, G., Santarsiero, V., Lanorte, A., Tucci, B., Capurso, V. A., Ronco, F. V., & Murgante, B. (2020). Model of post fire erosion assessment using RUSLE method, GIS tools and ESA sentinel DATA. In Computational Science and its Applications–ICCSA 2020: 20th International Conference, Cagliari, Italy, July 1–4, 2020, Proceedings, Part V 20 (pp. 505–516). Springer International Publishing.
Pace, L., Imbrenda, V., Lanfredi, M., Cudlín, P., Simoniello, T., Salvati, L., & Coluzzi, R. (2023). Delineating the intrinsic, long-term path of land degradation: A spatially explicit transition matrix for Italy, 1960–2010. International Journal of Environmental Research and Public Health, 20(3), 2402.
Paul, V., & Tonts, M. (2005). Containing urban sprawl: Trends in land use and spatial planning in the Metropolitan Region of Barcelona. Journal of Environmental Planning and Management, 48(1), 7–35.
Perdigao, V., & Christensen, S. (2000). The Lacoast atlas: Land cover changes in European coastal zones. Joint Research Centre, Ispra.
Perrin, C., Nougarèdes, B., Sini, L., Branduini, P., & Salvati, L. (2018). Governance changes in peri-urban farmland protection following decentralisation: A comparison between Montpellier (France) and Rome (Italy). Land Use Policy, 70, 535–546.
Pickett, S. T. A., Cadenasso, M. L., Grove, J. M., Nilon, C. H., Pouyat, R. V., Zipperer, W. C., & Costanza, R. (2001). Urban ecological systems: Linking terrestrial ecological, physical, and socioeconomic components of metropolitan areas. Annual Review in Ecology and Systematics, 32, 127–157.
Pignatti, S., Acito, N., Amato, U., Casa, R., Castaldi, F., Coluzzi, R., De Bonis, R., Diani, M., Imbrenda, V., Laneve, G. and Matteoli, S., & Cuomo, V. (2015). Environmental products overview of the Italian hyperspectral prisma mission: The SAP4PRISMA project. In 2015 IEEE International Geoscience and Remote Sensing Symposium (IGARSS) (pp. 3997‒4000). IEEE.
Recanatesi, F., Clemente, M., Grigoriadis, E., Ranalli, F., Zitti, M., & Salvati, L. (2016). A fifty-year sustainability assessment of Italian agro-forest districts. Sustainability, 8(1), 32.
Salvati, L., De Angelis, A., & Bajocco, S. (2012a). A satellite-based vegetation index as a proxy for land cover quality in a Mediterranean region. Ecological Indicators, 23, 578–587.
Salvati, L. (2014). Towards a polycentric region? The socio-economic trajectory of Rome, an ‘Eternally Mediterranean’ City. Tijdschrift Voor Economische En Sociale Geografie, 105(3), 268–284.
Salvati, L., & Zitti, M. (2007). Territorial disparities, natural resource distribution, and land degradation: A case study in southern Europe. GeoJournal, 70(2), 185–194.
Salvati, L., & Bajocco, S. (2011). Land sensitivity to desertification across Italy: Past, present, and future. Applied Geography, 31(1), 223–231.
Salvati, L., & Carlucci, M. (2016). Patterns of sprawl: The socioeconomic and territorial profile of dispersed urban areas in Italy. Regional Studies, 50(8), 1346–1359.
Salvati, L., Ciommi, M. T., Serra, P., & Chelli, F. M. (2019). Exploring the spatial structure of housing prices under economic expansion and stagnation: The role of socio-demographic factors in metropolitan Rome, Italy. Land Use Policy, 81, 143–152.
Salvati, L., Gemmiti, R., & Perini, L. (2012b). Land degradation in Mediterranean urban areas: An unexplored link with planning? Area, 44(3), 317–325.
Salvati, L., Petitta, M., Ceccarelli, T., Perini, L., Di Battista, F., & Scarascia, M. E. V. (2008). Italy’s renewable water resources as estimated on the basis of the monthly water balance. Irrigation and Drainage: THe Journal of the International Commission on Irrigation and Drainage, 57(5), 507–515.
Salvati, L., Sateriano, A., & Bajocco, S. (2013a). To grow or to sprawl? Evolving land cover relationships in a compact Mediterranean City Region. Cities, 30, 113–121.
Salvati, L., & Zitti, M. (2009). Substitutability and weighting of ecological and economic indicators: Exploring the importance of various components of a synthetic index. Ecological Economics, 68(4), 1093–1099.
Salvati, L., & Zitti, M. (2012). Monitoring land use quality and its management in a Mediterranean Urban Region. Applied Geography, 32(2), 896–903.
Salvati, L., Zitti, M., & Sateriano, A. (2013b). Changes in city vertical profile as an indicator of sprawl: Evidence from a Mediterranean urban region. Habitat International, 38, 119–125.
Samela, C., Imbrenda, V., Coluzzi, R., Pace, L., Simoniello, T., & Lanfredi, M. (2022). Multi-decadal assessment of soil loss in a Mediterranean Region characterized by contrasting local climates. Land, 11(7), 1010.
Santarsiero, V., Nolè, G., Lanorte, A., Tucci, B., Cillis, G., & Murgante, B. (2022). Remote sensing and spatial analysis for land-take assessment in Basilicata Region (Southern Italy). Remote Sensing, 14(7), 1692.
Santarsiero, V., Nolè, G., Lanorte, A., Tucci, B., Saganeiti, L., Pilogallo, A., Scorza, F., & Murgante, B. (2020). Assessment of post fire soil erosion with esa sentinel-2 data and rusle method in Apulia region (Southern Italy). In Computational Science and Its Applications–ICCSA 2020: 20th International Conference, Cagliari, Italy, July 1–4, 2020, Proceedings, Part IV 20 (pp. 590‒603). Springer International Publishing.
Simeonakis, E., Calvo-Cases, A., & Arnau-Rosalen, E. (2007). Land use change and land degradation in Southeastern Mediterranean Spain. Environmental Management, 40(1), 80–94.
Simoniello, T., Coluzzi, R., D’Emilio, M., Imbrenda, V., Salvati, L., Sinisi, R., & Summa, V. (2022). Going Conservative or Conventional? Investigating Farm Management Strategies in between Economic and Environmental Sustainability in Southern Italy. Agronomy, 12(3), 597.
Smiraglia, D., Ceccarelli, T., Bajocco, S., Perini, L., & Salvati, L. (2015). Unraveling landscape complexity: Land use/land cover changes and landscape pattern dynamics (1954–2008) in contrasting peri-urban and agro-forest regions of Northern Italy. Environmental Management, 56(4), 916–932.
Zambon, I., Benedetti, A., Ferrara, C., & Salvati, L. (2018). Soil matters? A multivariate analysis of socioeconomic constraints to urban expansion in Mediterranean Europe. Ecological Economics, 146, 173–183.
Zambon, I., Colantoni, A., Carlucci, M., Morrow, N., Sateriano, A., & Salvati, L. (2017). Land quality, sustainable development and environmental degradation in agricultural districts: A computational approach based on entropy indexes. Environmental Impact Assessment Review, 64, 37–46.
Acknowledgements
This study was supported by MULTIFOR “Multi-scale observations to predict Forest response to pollution and climate change” PRIN 2020 Research Project of National Relevance funded by the Italian Ministry of University and Research (prot. 2020E52THS).
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Imbrenda, V. et al. (2024). Vulnerability to Wildfires and Peri-urban Areas: An Integrated Socioenvironmental Assessment. In: Rodrigo-Comino, J., Salvati, L. (eds) Fire Hazards: Socio-economic and Regional Issues. Springer, Cham. https://doi.org/10.1007/978-3-031-50446-4_8
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