1. Introduction
Wildfires are becoming more harmful, with recent events occurred in Southern Europe, South America, USA and Australia showing their potential destructive power [
1,
2,
3]. In Portugal, wildfire is one of the most impactful hazards, with the extreme events occurred in 2017 causing the most devastating consequences ever recorded, including the loss of over 100 human lives [
4,
5]. Especially in the inner part of the territory, the combination between the abundance of flammable forest and shrub-dominated land cover, the warm and dry summers typical of Mediterranean-type climates, and the irregular topography, creates a particularly challenging fire-prone landscape [
6,
7,
8,
9]. Historical data also shows that, between 1980 and 2018, Portugal had the highest average number of annual wildfires and the second largest annual burnt area among the top affected countries of southern Europe (Portugal, Spain, France, Italy and Greece) despite having the smallest territory [
5]. Most of the damage occurs in the summer months as the consequence of a relatively small number of large fires [
9,
10,
11,
12].
Like other natural hazards, wildfires can be approached from a disaster risk reduction (DRR) perspective [
13,
14,
15]. The DRR approach conceives risk as a multi-dimensional phenomenon, that not only includes the characteristics of natural hazards and of the environment in which they occur, but also the degree to which populations, infrastructure and livelihoods are exposed to these hazards, as well as their level of vulnerability to their destructive and disruptive effects [
15]. This integrated perspective enables organizations of local to global scope to act upon specific dimensions of risk, armed with the foreknowledge that a reduction in any one of them will lead to a reduction in the total risk associated with a given hazard. Available measures for such purpose are of numerous types, including economic, structural, legal, social, health, cultural, educational, environmental, technological, political, and institutional [
16].
Adopting the risk assessment definitions proposed by the United Nations, wildfire hazard can be defined, for a certain area, in terms of the probability, frequency and intensity that characterize wildfires [
17]. This broad definition allows for contrasting means of quantification and statistical techniques, depending on the purpose and application. For example, burn probability maps can be obtained by simulation approaches [
18], to support operational decisions regarding fuel treatments and suppression activities [
19], or instead, they can be based on historical fire data to provide a structural perspective of the propensity to burn based on terrain conditions [
20,
21], to define long-term prevention strategies.
Exposure evaluates the elements, or assets, which are located in areas where hazardous events may occur [
15,
22,
23]. Based on the spatial intersection with the fire hazard level, potentially affected elements located in the area are analysed, among which are built-up areas, forests, agricultural lands, protected areas, infrastructures, and human communities [
24,
25,
26].
The third component of wildfire risk is vulnerability, which represents the propensity of exposed elements to suffer adverse effects when affected by wildfires [
15,
27,
28,
29]. Given the diversity among the potentially exposed elements, this risk component has been subject to various approaches, for example focused on physical elements such as vegetation types [
30], environmental elements such as ecosystems [
31], social elements [
29,
32,
33], and often on combinations of these elements [
34,
35,
36,
37,
38]. Along with contrasting ways to quantify them individually, the components of risk have also been articulated in different ways to produce risk indexes, which can be hazard-specific or not. For instance, the Inform-Index For Risk Management [
39] proposes three essential dimensions: hazard/exposure, vulnerability (which refers to the fragility of the socio-economic system), and lack of coping capacity (which refers to the lack of resilience to cope and recover). This index draws a strong conceptual influence from the work of Cardona and Carreño [
40]. A contrasting example is the World Risk Index [
14], which proposes two main risk dimensions, or spheres: the hazard sphere and the vulnerability-social sphere. The first aims to identify the diverse entities exposed and prone to be affected by a hazard event (such as communities, resources, infrastructure, or ecosystems). The vulnerability-social sphere is subdivided into three components: susceptibility (the likelihood of suffering harm in the case of a hazardous event, defined by factors such as nutrition or economic capacities), coping capacity (the ability to respond directly to the impact of a hazardous event), and adaptive capacity (the capacity for implementing long-term strategies for societal change). Neither of the above is hazard-specific, and therefore they can be adapted to any hazard or combination thereof. A wildfire-specific example is the wildfire risk assessment framework proposed by [
41], in which wildfire risk for a given area is seen as the combination of wildfire hazard (in terms of likelihood and intensity), exposure, and expected effects (the expected changes in value, expressed in percentage). Other examples are the Wildland Fire Decision Support System (WFDSS) [
42], in which fire spread probability (fire behaviour) is combined spatially with the nature and location of elements at risk (resource assessment), in order to facilitate rapid decision-making in a context of escaped wildfires (in this case, the expected degree of damage, i.e., the physical vulnerability, is not explicitly taken into consideration). Another example is the fire risk assessment framework proposed by Chuvieco et al. [
43], in which risk is the result of the combination between the probability of fire initiation and propagation, and its potential damage. Although exposure is not explicitly included in the framework, it is implicit in its GIS-based implementation, as each pixel represents an exposed spatial unit.
In Portugal, Parente and Pereira quantified wildfire risk at the national scale, considering only damage to vegetation [
30]. Using raster data, wildfire hazard was estimated as the combination of wildfire probability (quantified for each pixel as the percentage of years from the study period in which that pixel burned) and terrain susceptibility (defined as the propensity of the terrain to be burned as a function of its inherent properties, such as land cover or slope). The potential damage (corresponding to the dimensions of exposure and vulnerability) was quantified using the economic value by hectare of existing vegetation types, and their expected degree of loss in case of burning. Antunes et al. [
44] used a similar approach to calculate wildfire risk for a single municipality in central-north Portugal, additionally assessing risk with a focus on scenically valuable landscape units. More recently, Oliveira et al. [
28] assessed wildfire risk specifically for human settlements (villages) within a civil parish in central Portugal, combining burn probability scenarios with exposure and vulnerability levels. The latter was based on a cluster analysis of the social characteristics of resident population; in addition, coping capacity factors were also integrated, namely the time required to reach a potential fire shelter and the distance of each village to the nearest fire station.
In this work, we employ a new detailed parish-scaled approach to characterize a regional-sized study area in central mainland Portugal with respect to the three dimensions of wildfire risk: hazard, exposure, and vulnerability, the latter considered in its social dimension. We then combine the three individual dimensions into an integrated wildfire risk index, based on an adaptation of the INFORM framework [
39]. This adaptation was recently applied with success by Santos et al. [
45] and Pereira et al. [
46], albeit to other hazards (floods and landslides, respectively) and was chosen due to its simple structure and its versatility, being applicable with varying degrees of complexity depending on the availability of data regarding each of the dimensions of risk. Cluster analysis is subsequently used to aggregate the 972 parishes into groups sharing similar wildfire risk dimensions, allowing for a nuanced perspective over the study area. Finally, we discuss the limitations of the index, as well as its potentialities in a risk management context. Our objectives are thus threefold: (1) to characterize the parishes in the study area in terms of wildfire hazard, exposure, and social vulnerability; (2) to quantify wildfire risk within the study area by means of an integrated index; (3) to identify wildfire risk profiles within the study region, by investigating the combination patterns of the components of wildfire risk among the different parishes.
4. Discussion
The proposed risk index (
Figure 10D) allows for a general and integrative perspective over the spatial patterns and variations of wildfire risk throughout the study area. This perspective is invaluable in a context of regional-level to country-level spatial planning and risk management. However, the applicability and value of this index can only be fully grasped in relation to its hierarchical structure in three increasing levels of detail and specificity: the final integrated level, the level of the individual dimensions of wildfire risk (hazard/exposure/social vulnerability), and the level of their individual sub-components (in the cases of exposure and social vulnerability) (
Figure 3). Organizations and individuals responsible for risk management at municipal and sub-municipal scales can implement measures adjusted to the dimensions that influence wildfire risk levels in their areas, avoiding untailored, generalist and less efficient approaches. For instance, a risk manager in a municipal administration can allocate financial and human resources to early detection and suppression of wildfires in hazard-dominated parishes within the municipality (such as those in clusters 2, 3 and 4;
Figure 11A), while privileging measures such as the promotion of neighbour support networks or rapid evacuation capabilities in social vulnerability-dominated parishes (such as those in cluster 5). Prior studies have shown the importance of identifying priority measures in exposed areas, regarding fuel and fire management options [
28,
57], as well as to engage in proactive and collaborative management to prevent wildfire losses [
58]. Other studies have shown that people’s characteristics and social context are paramount to understand their perception regarding wildfires, and how it influences their relations with fire occurrence and their ability to apply protective measures [
28,
59]. Moreover, social context and local conditions are crucial to define suitable mitigation and adaptation strategies to increase communities’ safety and resilience [
60,
61].
Furthermore, in the case of parishes where the main driving dimensions result from the combination of more than one component (exposure and vulnerability), risk managers can resort to the third level of detail—that of the sub-components—to support their decision-making. For example, it is expectable that similar social vulnerability values among parishes will result in some cases from a particularly high criticality, and in others from a particularly low support capability. A consideration at this third and most detailed level would allow risk managers to focus their policies and measures on the more relevant constituents of the more relevant dimension of risk within each parish.
Regarding spatial scale, the use of the individual parish as unit of analysis allowed for a high level of detail to represent wildfire risk and its dimensions, that can be either directly used or adapted to any level of territorial management. At the municipal level, the results allow risk managers to differentiate parishes within a given municipality, thus informing their planning decisions. At higher levels of spatial planning (e.g., region, association of municipalities), results can be adjusted to a municipal scale of representation, for example by using area-weighted averages of the values of the parishes within each municipality. Our choice of the parish as spatial unit of analysis is in accordance with the considerations put forward by the authors of the Inform index [
39], which indicate that the index can be applied at any spatial scale for which information is available. In our case, spatial data was available with a 25 m pixel, and most of the statistical data were available at the parish level. The exceptions were nine of the variables used as input for quantifying support capability, which were only available at the municipal scale (
Table 3). Nevertheless, the index can be applied to spatial units of any level: municipal, regional, or national (for multi-country assessments).
A similar consideration can be made regarding temporal scale. Although we employed a structural approach to assess wildfire hazard by using wildfire factors that change only on a multi-year scale [
21], the applied wildfire risk methodology could be focused on summer-specific wildfire risk, if summer-specific wildfire hazard data were available. In this respect, this index could be combined with a seasonal approach to wildfire hazard such as that recently proposed by [
20].
In parallel to the potential advantages of using this wildfire risk index, some limitations to our approach need also to be considered. The dimension of exposure was expressed using two variables only: total number of residents per parish, and percentage of resident population outside of urban areas by parish, due to the high collinearity with other variables focused on residential buildings. In practice, the first variable quantifies both the number of people and residential infrastructures exposed to wildfires, whereas the second expresses the degree of isolation that these elements are subject to in each parish, adding to their level of exposure. Given the variety of elements that can be at risk within the territory besides people and buildings, our approach excluded elements such as non-residential structures (e.g., cultural, industrial, collective equipment such as hospitals) and economic activities, as well as agricultural lands, forest areas and ecosystems. It also excluded the temporary residents or seasonal visitors that are present only during summertime, when wildfires are more frequent. Future work should be dedicated to diversifying the elements represented within the exposure dimension. A good example in this respect is the HANZE exposure database [
62], which included land cover classes and the estimation of their economic value. Further examples are the works of Salis et al. [
25] and Thompson et al. [
26], in which diverse types of exposed elements (e.g., wildland-urban interfaces, vineyards and orchards, various infrastructure types, areas of ecologic value such as wildlife habitats) are spatially differentiated.
Like exposure, the dimension of vulnerability should also be made more comprehensive in future work. Our approach was focused solely on its social component, and therefore on the characteristics of the residents. Features such as the expected level of destruction of physical structures [
63] and land use parcels (e.g., forests), as well as their estimated economic value [
30,
44] would make the quantification of vulnerability more realistic. Such changes would require the consideration of expected wildfire severity in the methodology, as well as reliable and accessible estimations of the economic value and potential recovery costs of the different elements, which may vary depending on the country or region. Risk is inherently multidimensional, and any application of a risk index will be more effective the more detailed and exhaustive the available data are for each of its dimensions and sub-dimensions.
5. Conclusions
A comprehensive wildfire risk index was proposed and applied to a region in central Portugal. The index was complemented with the division of the 972 parishes studied, by means of cluster analysis, into groups characterized by similar relations between the three wildfire risk dimensions: hazard, exposure, and social vulnerability.
The hierarchical structure of the index, which is based in the INFORM framework, allows approaching wildfire risk management in different levels. At the most generalized, the final index values allow for a general perspective over the distribution of wildfire risk throughout the study area. Results suggest four distinct spatial patterns, with the highest risk parishes being evidently concentrated in the centre-south of the study area, where mitigation measures should be applied first. At the level of the three dimensions of risk, results can inform the decisions of wildfire risk managers, allowing them to more efficiently allocate resources to the major dimension (or dimensions) that are more relevant in each parish. In this respect, the five defined clusters illustrate different risk profiles, with three of them being dominated by hazard (although with values of differing magnitude), and the other two being dominated, respectively, by exposure together with social vulnerability, and social vulnerability only. At the most detailed, sub-dimension level, available only in the cases of exposure and social vulnerability, risk managers can focus their attention on the most relevant factors behind these dimensions, further adjusting policies and measures to the specific reality within each parish.
The proposed index provides an integrated and spatially detailed perspective of wildfire risk that is relevant for disaster risk reduction approaches. It can be easily applied to other study areas, using any spatial unit for which spatial and statistical data are available.