Skip to main content
PLOS ONE logoLink to PLOS ONE
. 2015 Dec 29;10(12):e0144468. doi: 10.1371/journal.pone.0144468

Weather-Related Flood and Landslide Damage: A Risk Index for Italian Regions

Alessandro Messeri 1,2,*, Marco Morabito 1,3, Gianni Messeri 3,4, Giada Brandani 1,2, Martina Petralli 1,2, Francesca Natali 1,2, Daniele Grifoni 3,4, Alfonso Crisci 3,4, Gianfranco Gensini 5, Simone Orlandini 1,2
Editor: Moncho Gomez-Gesteira6
PMCID: PMC4694658  PMID: 26714309

Abstract

The frequency of natural hazards has been increasing in the last decades in Europe and specifically in Mediterranean regions due to climate change. For example heavy precipitation events can lead to disasters through the interaction with exposed and vulnerable people and natural systems. It is therefore necessary a prevention planning to preserve human health and to reduce economic losses. Prevention should mainly be carried out with more adequate land management, also supported by the development of an appropriate risk prediction tool based on weather forecasts. The main aim of this study is to investigate the relationship between weather types (WTs) and the frequency of floods and landslides that have caused damage to properties, personal injuries, or deaths in the Italian regions over recent decades. In particular, a specific risk index (WT-FLARI) for each WT was developed at national and regional scale. This study has identified a specific risk index associated with each weather type, calibrated for each Italian region and applicable to both annual and seasonal levels. The risk index represents the seasonal and annual vulnerability of each Italian region and indicates that additional preventive actions are necessary for some regions. The results of this study represent a good starting point towards the development of a tool to support policy-makers, local authorities and health agencies in planning actions, mainly in the medium to long term, aimed at the weather damage reduction that represents an important issue of the World Meteorological Organization mission.

Introduction

The frequency of natural hazards has been increasing in the last decades in Europe, and more specifically in the Mediterranean regions, due to climate change [1, 2, 3, 4, 5, 6, 7]. Heavy precipitation events can lead to disasters through interaction between exposed and vulnerable people and the natural systems [8, 9, 10]. In particular, floods and landslides are considered important natural disasters with significant effects in terms of the number of people affected and the economic losses [11]. The impacts of floods and landslides are determined not just by their magnitude, but also by human and societal choices related to infrastructures, behaviors and other factors [12, 13, 14, 15, 16]. The immediate and direct impacts of these events on human health include drowning, heart attacks, various injuries, and hypothermia. Furthermore, indirect impacts, such as infections, water-borne infectious diseases, mental health disorders, respiratory diseases and allergies in both the medium and long term, should also be considered as significant effects [17, 18, 19, 20, 21]. In Italy, it has been estimated that over 68% of the municipalities are at high hydrogeological risk [22] and in recent decades, intense rainfall events have caused severe disruptions [23, 24].

In addition, the risk of natural disasters in Italy is still rising due to the increased population density, progressive urbanization, abandonment of mountainous areas, unauthorized buildings, ongoing deforestation, and lack of maintenance of the slopes and waterways [25]. The effects of floods and landslides are often underestimated because of the lack of an inventory system and damage cataloging [26, 27]. Consequently, investigation of the historical effects of these natural hazards is fundamental for the temporal reconstruction of the events and for assessing their potential frequency and consequent effects [28, 29]. For this purpose, the “Inventory of areas affected by landslides and floods in Italy Project” (AVI), commissioned by the Department of Civil Protection and created by the National Research Council, has enabled the development of a detailed Italian database of surveys and damage caused by landslides and floods, from the early 1900s until today.

The increase in the frequency of these events calls for prevention planning to preserve human health and reduce economic losses. Prevention should mainly be carried out with more adequate land management, also supported by the development of an appropriate risk prediction tool based on weather forecasts[30].

However, warnings for severe meteorological events potentially able to cause landslides and floods are only issued a few hours before the event (now casting) or with 2–3 days' notice. This is because weather forecast services only have high reliability in the short-medium term. Nonetheless, the safety operation of major risk situations often requires several days or even weeks' preparedness and a few days warning might not be sufficient.

Several innovative warning tools would therefore be very useful for this purpose. Seasonal climate forecast models are used increasingly across a range of application sectors and could be implemented in new procedures to support health prevention. These models have been developed from ensembles of integrations of numerical climate models [31] and offer good probabilistic reliability. Weather-circulation type (WT) classification could represent a useful tool for improving the reliability of seasonal weather forecasts. The application of WT is a well-established approach in synoptic and applied climatology, ranging from support for weather forecasting to climate model validations or downscaling [32, 33, 34, 35].

The main aim of this study is to investigate the relationship between WT and the frequency of floods and landslides that have caused damage to properties, personal injuries, or deaths in the Italian regions over recent decades. In addition, specific risk indexes (WT-FLARI) have been developed for each WT at a national and regional scale.

The result of this work represent a good starting point towards the development of a tool to support policy-makers, local authorities and health agencies in planning actions, mainly in the medium to long term, aimed at the reduction of disasters. Disasters reduction represents an important issue of the World Meteorological Organization mission [36]. Actions to be taken on the eve on an emergency will nevertheless still predominantly managed through the use of deterministic models able to better locate the phenomena, but in the medium to long term (months), the WT approach could instead make possible a better use of seasonal forecasts, which, although in gradual improving, will unlikely be able to provide deterministic forecasts, on the contrary could provide useful information on the prevailing WT.

Materials and Methods

The study was carried out with an analysis of the connection between atmospheric circulation types and the damage caused by landslides and floods in Italy during the 1948–2003 period. The analysis was based on the following datasets:

  1. The NCEP/NCAR Reanalysis 1 (NCEP1) global grilled dataset [37, 38] was used to create a national weather type classification for the investigated period, 1948–2003. The NCEP1 data, on 2.5°x2.5°, are available at http://www.cdc.noaa.gov/cdc/reanalysis.

  2. A database of the most common weather and circulation types (WTs) in Europe by using the cost733class software package to create, compare, visualize and evaluate weather and circulation-type classifications [34,39]. Data sources are freely available at http://cost733.met.no/. The NCEP reanalysis data were utilized on a latitude-longitude grid (30N-70N, 30W-30E) and then the Principal Component in T mode (PCT) was implemented, using a geopotential height at 500htp [40, 41, 42, 43]. According to Philipp et al [34], there is no clear statistical reason to prefer any of the classified methods of COST733 software package. Consequently no new classification was created and implemented specifically for this study.Therefore, we used an existing classification already applied both for operative-forecast purpose (LAMMA-IBIMET) that for scientific study [34, 35]. The weather-type classification was set to eight classes as representative of the main circulation types prevailing over the Italian Peninsula (Fig 1, Table 1).

  3. A database of landslide and flood events that caused damage created by the National Group for Prevention of Hydrological Hazards (GNDCI) of the National Research Council (CNR) with regard to the AVI Project commissioned by the Department of Civil Protection. The AVI Inventory is a homogeneous and updated archive with a detailed spatial representation of landslides and floods. This is an important tool for hazard-risk analysis and land-use planning. In particular, landslides and floods that caused damage from the early 1900s until today were collected and organized. Furthermore, within this study, the “Inventory of Landslide Phenomena in Italy” [44] was taken into account. However, in this study only years with more reliable data starting from late forties were considered (http://avi.gndci.cnr.it/welcome_en.htm). All data used in this work are available on https://github.com/meteosalute/weather_landslide.

Fig 1. 500hPa geopotential height for each weather types (WT) classified by LAMMA-IBIMET for the period 1948–2011.

Fig 1

Table 1. The most common Weather Types (WT) in Europe and prevailing circulation in Italy.

WT number Characteristics of circulation
1 Marked northward expansion of the Azores anticyclone with blocked anticyclonic circulation over the North Atlantic and northerly winds over Italy
2 Moderate northward expansion of the Azores anticyclone with cyclonic circulation over south Scandinavia and north-westerly winds over Italy
3 Marked cyclonic circulation over Iceland with anticyclonic circulation over northern central Europe accompanied with increased precipitation over Italy, generated by intermittent Atlantic perturbations
4 Cyclonic circulation over the North Atlantic and cyclonic circulation over west Mediterranean Europe and central Mediterranean Europe with decreased precipitations over central Mediterranean Europe
5 Cyclonic circulation over the north-west Atlantic with marked anticyclonic circulation over west Mediterranean Europe and central Mediterranean Europe, inducing warm and dry conditions over Italy
6 Anticyclonic circulation over Iceland and cyclonic circulation over central Europe, with higher precipitation over Tuscany by intrusions of artic and polar continental air
7 South westerly flow over the North Atlantic with ridging over the British Isles towards Scandinavia, with easterly wind over central Mediterranean Europe resulting in very cold dry conditions
8 Cyclonic circulation over west Europe with a ridge over the eastern Mediterranean

Flood and landslide events were organized and processed separately for each region, in order to obtain a detailed overview of the number of events per day from 1948 to 2003. Therefore, a comprehensive database for each Italian region was created on a daily basis including the occurrence of WTs and of landslide/flood events which then were aggregated on a seasonal and annual basis and expressed as relative frequency for each WT.

A non-parametric test [45] was used to compare the number of events for each WT between seasons in the period 1948–2003.

These events together with exposure and vulnerability layers, represented by the population density (inhabitants per km2), river surface (km) and non-plain surface (km2) were used as input data to create a specific WT-related Flood and LAndslide Risk Index (WT-FLARI) calibrated at both annual and seasonal level.

The study design focused on “Crichton’s Risk Triangle” hazard-risk assessment methodology [46] developed in the field of the ASCCUE (Adaptation Strategies for Climate Change in the Urban Environment) project. The workflow of the hazard risk analysis employed to develop the final mapping of the WT-FLARI is shown (Fig 2).

Fig 2. Work-flow of the Weather Type-related Floods and Landslides Risk Index (WT-FLARI) assessment.

Fig 2

The risk concept is represented by harmful consequences on human health and the territory resulting from the interaction between three components that form a triangle: hazard, exposure, and vulnerability. The risk is defined as a function of these three components.

More specifically, a normalization procedure, followed by a weighted-layer combining procedure was applied for each Italian region. By means of the normalization procedure events occurrence, exposure and vulnerability layers were rescaled from 0 to 1. The following step was the combination of the normalized layers through a weighting procedure. The exposure and vulnerability layers, (Table 2), were renormalized in a single “exposed and vulnerable layer” where each variable was weighted at 33.3%.

Table 2. Population density, river surface and non-plain surface for each Italian Region.

Country Population density (Pop. per km 2 ) River surface(km) Non-plain surface (km 2 )
Abruzzo 121 4671 10831
Basilicata 57 5550 9267
Calabria 129 9504 15221
Campania 422 6147 11675
Emilia Romagna 195 10587 11720
Friuli Venezia Giulia 155 4005 4866
Lazio 322 9464 13803
Liguria 289 3943 5416
Lombardia 410 10289 12623
Marche 164 5594 9401
Molise 70 2414 4460
Piemonte 172 15077 18684
Puglia 207 4395 9145
Sardegna 68 15104 19641
Sicilia 194 11122 22164
Toscana 161 15098 21056
Trentino Alto Adige 76 7355 13605
Umbria 105 5214 8464
Veneto 265 7553 8025

Following, the “exposed and vulnerable” layer (weighted at 25%) was combined with the event layer (weighted at 75%) to obtain the final WT-FLARI varying between 0 and 1 (Fig 2). The final annual and seasonal mapping visualization of RI was carried out via identification of specific thresholds indicating the actual ongoing risk. The threshold identification was performed using quantiles, with particular reference to the values over 90% [47]:

  • very high risk (RI> 99%)

  • high risk (95%<RI< 99%)

  • medium risk (90%<RI< 95%)

  • low risk (RI< 90%).

Extreme-value statistics describe the probabilities associated with a quantity exceeding a given threshold value according to a Poisson distribution [48, 49, 50, 51].

The thresholds were only identified for the annual risk index and then applied to a seasonal level instead, in order to obtain a risk assessment that also considered the weight given to each WT in each season.

Results

Weather type distributions

The weather configuration characterized by the presence of the Azores High Pressure over the Mediterranean Basin (WT5) showed the highest annual WT frequency (25%, Table 3), followed by WT2 (22%) characterized by partial displacement of the Azores High Pressure to Northern Atlantic Ocean resulting in the flow of maritime polar air masses towards Central Europe and partly in the Mediterranean basin.

Table 3. Seasonal distribution of weather types and flood and landslide events from 1948 to 2003.

WT1 WT2 WT3 WT4 WT5 WT6 WT7 WT8
WT Frequency 10% 22% 11% 12% 25% 0% 11% 9%
N. E N. E N. E N. E N. E N. E N. E N. E
Season
A 506 27 960 158 574 150 511 219 1601 285 1 0 458 123 480 504
Sp 613 27 989 76 584 37 782 45 958 71 2 0 565 60 659 90
Su 272 25 1381 97 626 29 730 29 1199 100 0 0 601 50 343 136
W 675 70 1073 156 538 83 489 72 1309 99 15 2 550 63 383 119
ANOVASig. E p<0.01 p<0.001 p<0.001 p<0.001 p<0.001 p = 0.905 p<0.01 p<0.001

WT = Weather Type; N = the specific WT frequency; E = number of events related to a specific WT; Su = summer; A = autumn; W = winter; Sp = spring; p = a non parametric method of the analysis of variances [45] was used to compare the number of events for each WT between season.

Annual frequencies ranging from 9% to 12% were observed when WT1, WT3, WT4, WT7 and WT8 were considered. The weather configuration characterized by a large high pressure block in Northern Europe and the Atlantic Ocean with cold air masses in Mediterranean Basin and Central Europe (WT6) showed the lowest frequency with very few cases (18) during the period studied. The predominance of WT2 and WT5 was also confirmed in all seasons (Table 3), with frequencies often greater than 20%. In addition, other high frequencies were also observed for the subtropical high pressure (WT4) in summer (14%) and spring (15%), and for WT1 and WT3 in winter (13%) and autumn (11%) respectively.

WT- related flood and landslide events

Almost half the flood and landslide events occurred in autumn (49%) followed by winter (22%), summer (15%) and springer (14).

A statistical analysis (kruskal wallis test) showed that the weather type significantly discriminate the frequency of events in each season (Autumn P<0.001, Summer P<0.001, Winter P<0.001, Spring P<0.01). In particular WT8 is the weather type that has the highest frequencies in each season (data not shown).

No significant seasonal events variations were observed when WT1 and the rare WT6 were considered (Table 3). However, in these weather conditions the highest frequency of events was observed in winter.

The other WTs always showed significantly higher values in autumn than the other seasons (Table 3). Other significant variations were also observed in winter with significantly higher values than spring and summer when WT2 and WT3 occurred.

In particular, WT8 showed the highest frequency during autumn (34% of autumnal frequencies of events), summer (29%) and spring (22%). During winter the highest frequency was observed when WT2 (23%) occurred, followed by WT8 (18%). Other high frequencies (>15% of seasonal frequencies) were observed in summer for WT5 (22%) and WT2 (21%); in autumn for WT5 (19%) and WT4 (15%); in spring for WT2 (19%) and WT5 (18%).

Several WTs caused damage, especially in northern Italy, while others occurred in central and southern regions (Table 4).

Table 4. Percentage of events for each region and for each WTs.

Region WT1 WT2 WT3 WT4 WT5 WT6 WT7 WT8
Abruzzo 0.24 0.16 0.17 0.08 0.14 5.56 0.46 0.32
Basilicata 0.29 0.48 0.56 0.36 0.39 0 0.60 0.21
Calabria 0.39 0.34 0.65 0.24 0.45 5.56 0.64 0.16
Campania 0.92 1.79 1.68 1.15 1.44 0 1.20 2.31
Emilia Romagna 0.15 0.27 0.30 0.28 0.18 0 0.32 0.86
Friuli Venezia Giulia 0.15 0.32 0.39 0.12 0.10 0 0.18 0.97
Lazio 0.44 0.77 0.43 0.84 0.45 0 0.60 1.77
Liguria 0.29 0.23 0.60 0.84 0.26 0 0.09 1.23
Lombardy 0.05 0.48 0.65 1.07 0.49 0 0.23 2.68
Marche 0.24 0.20 0.17 0.08 0.20 0 0.51 0.38
Molise 0.05 0.07 0.04 0.04 0.06 0 0.05 0.11
Piedmont 0.10 0.27 0.60 0.64 0.47 0 0.37 2.47
Puglia 0.63 0.36 0.43 0.24 0.53 0 0.78 0.59
Sardinia 0.44 0.64 1.12 0.56 0.79 0 0.78 1.39
Sicily 0.73 0.36 0.39 0.44 0.49 0 1.01 0.64
Toscany 0.34 0.61 0.69 0.52 0.28 0 0.37 1.34
Trentino Alto Adige 0.24 0.55 0.47 0.32 0.28 0 0.32 1.45
Umbria 0.44 0.45 0.13 0.12 0.12 0 0.18 0.54
Veneto 0.34 0.59 0.43 0.28 0.28 0 041 1.45

For example, WT8 caused a greater number of events in central and northern Italian regions, particularly Lombardy, Piedmont and Lazio, as well as Campania. Conversely, WT6 and WT7 determined effects, especially in Abruzzo, Calabria, Campania, Apulia, Sardinia and Sicily. Campania showed the highest frequency of flood and landslide events when almost all WTs occurred, with the exception of WT6 and WT8, where the records were held by Calabria and Lombardy respectively. The region which showed the lowest frequency of events for each WTs was Molise.

Exposure and vulnerability layer distributions

Among all regions, Liguria had the highest values of Exposed and Vulnerable Layers (Fig 3), especially due to non-plain surface and the high number of rivers in relation to regional surface. Even Campania showed very high values determined primarily by the high population density. The lowest values were in Apulia, Veneto, Emilia Romagna and Friuli Venezia Giulia where the contribution of the non-plain surface is very low.

Fig 3. Incidence of normalized features for each Italian region.

Fig 3

The annual WT-related flood and landslide Risk Index

The WT8 is the most dangerous meteorological configuration at an annual Italian level (Fig 4).

Fig 4. Mapping of the annual WT-related Floods and LAndslides Risk Index (WT-FLARI).

Fig 4

WT (Weather Type). WT-FLARI levels: red = Very High (WT-FLARI > 99th perc.); orange = High (95th perc. > WT-FLARI > 99th perc.); yellow = Moderate (95th perc. > WT-FLARI > 90th perc.); white = Low (WT-FLARI < 90th perc.)

Piedmont and Lombardy are the regions that reached the “very high” WT-FLARI level (red in Fig 4), followed by Tuscany, Campania and Veneto, which showed the “high” risk level (orange in Fig 4). A “moderate” risk level was observed in Lazio, Trentino Alto Adige and Friuli Venezia Giulia (yellow in Fig 4).

WT2, WT3 and WT5 only showed a “moderate” risk level in Campania.

WT4 determined a “high” risk level in Piedmont, while the risk level was “moderate” in Lombardy. Conversely, WT4 showed a “low” risk level for all central and southern Italian regions which were generally protected by high pressure whenever WT4 occurred.

The very rare WT6 had the greatest effects on southern Italian regions. A “high” risk level (Fig 4) was observed in the Marche and Calabria, which are more exposed to the eastern airflow that often determines a low depression between the Adriatic Sea and the Ionian Sea. On the other hand, there were no risk conditions for WT1 and WT7, which were also characterized by a predominant Eastern circulation.

Seasonal WT-related flood and landslide Risk Index

Varying seasonal WT-FLARI patterns were recorded. In autumn (Fig 5), the hazardous risk levels (“Very High” and “High”), which were always associated with WT8 and WT4, prevailed in the northern regions.

Fig 5. Mapping of the autumn WT-related Floods and LAndslides Risk Index (WT-FLARI).

Fig 5

WT (Weather Type). WT-FLARI levels: red = Very High (WT-FLARI > 99th perc.); orange = High (95th perc. > WT-FLARI > 99th perc.); yellow = Moderate (95th perc. > WT-FLARI > 90th perc.); white = Low (WT-FLARI < 90th perc.)

In particular, the most dangerous risk level was concentrated in the north (Lombardy and Veneto) and one central region (Tuscany) for WT8, and in the northwest (Lombardy) for WT4.

The “High” risk was only observed in northern regions when WT8 occurred. The “Moderate” risk was prevalently observed in the northeast and associated with WT8, and in one southern region (Campania) for WT8 and WT2. “Moderate” risk was also observed in several northern regions (Liguria and Lombardy) when WT4 and WT3 occurred.

In spring (Fig 6), the most dangerous risk level only affected one northwestern region (Lombardy) when WT8 occurred. Conversely, the “High” risk level only occurred in southern regions, especially Campania when WT2, WT3, WT4, WT5, WT6 occurred, while for Molise was only associated with WT7. The “Moderate” risk for northern regions was only associated with WT8 (Liguria and Piedmont) and WT4 (Liguria), in central regions with WT8 (Tuscany and Lazio) and WT3 (Tuscany), and in southern regions with WT1 and WT8 (Campania) and WT7 (Campania and Sicily).

Fig 6. Mapping of the spring WT-related Floods and LAndslides Risk Index (WT-FLARI).

Fig 6

WT (Weather Type). WT-FLARI levels: red = Very High (WT-FLARI > 99th perc.); orange = High (95th perc. > WT-FLARI > 99th perc.); yellow = Moderate (95th perc. > WT-FLARI > 90th perc.); white = Low (WT-FLARI < 90th perc.)

In summer (not shown), the risk was strongly downsized and localized because the perturbed Atlantic flow generally affected northern and central Europe and only occasionally Italy, above all, the northwestern regions. In particular, the “very high” risk level was only observed in Piedmont and associated with WT8. No “High” risk was observed, while the “Moderate” only involved one central region (Tuscany) when WT1 occurred.

In winter (Fig 7), the most dangerous risk level was recorded in central and southern Italian regions when WT6 and WT8 occurred. In particular, the “Very High” risk level was associated with WT6 in Abruzzo and Calabria and with WT8 in Campania. The “High” risk was observed in one central region (Lazio) with WT8 and in one southern region (Campania) with WT2, WT3, WT4 and WT5. The “Moderate” risk was observed in northern regions associated with WT4 (Liguria and Lombardy) and WT8 (Veneto); in central regions with WT2 (Lazio), WT7 and WT8 (Marche), and in one southern region (Sardinia) with WT8.

Fig 7. Mapping of the winter WT-related Floods and LAndslides Risk Index (WT-FLARI).

Fig 7

WT (Weather Type). WT-FLARI levels: red = Very High (WT-FLARI > 99th perc.); orange = High (95th perc. > WT-FLARI > 99th perc.); yellow = Moderate (95th perc. > WT-FLARI > 90th perc.); white = Low (WT-FLARI < 90th perc.)

Discussion

The main finding of this study is that the weather type that generally determines more perturbed flows on the Italian peninsula (WT8) is associated with the highest impact in terms of damage. The greatest effects were observed during autumn, when WT8 determined a deepening of a low depression over the Gulf of Genoa with abundant rainfall in northern Italian areas. However, other weather patterns might also have important effects with variations among seasons and regions. In particular, this study revealed that the effects of each WT on a heterogeneous country such as Italy differ greatly between the northern and southern regions. The effects can even be very different between neighboring regions.

For example, in the winter period, the meteorological configurations that determined a cold easterly or north easterly flows generated rainfall primarily in the central and southern regions due to being the sites of contrast between cold air masses from the northern latitudes and warmer Mediterranean air [52, 53, 54]. For this reason, central and southern regions in particular, experienced WT-FLARI from moderate to very high risk levels. Conversely, the northern regions, despite with lower temperatures, were not affected by heavy rainfall and hence the level of risk is generally very low.

During the warm season, Italy is mainly affected by stable configurations of Azorean or African High Pressure. Moreover, in summer, but also during the intermediate seasons, the increased latent energy generated by high levels of solar radiation is potentially capable of generating strong convective precipitation even with a slight geopotential decrease [55, 56, 57]. Consequently, apparently unexpected risk conditions may be generated. This explains the occurrence of dangerous events during weather patterns characterized by high pressure. For example, weather types 4 and 5, although characterized by Azorean or subtropical high pressure in the Mediterranean basin, determined high risk conditions in some northern Italian regions during the autumn, even though few atmospheric disturbances were present.

Nevertheless, this article highlights the fact that the contribution of the “Exposure and Vulnerability layers” is essential for risk calculation. In regions where there is a high population density, a large number of rivers and little flat territory, the basic risk is generally higher. Campania is the most striking case, and in spring and winter, WT-FLARI is high for most weather types. The highest risk observed in Campania was mainly due to the great vulnerability of the territory and the high population density.

It must also be noted that this work has some limitations. In fact, the risk index was calculated according to the weather type for the event (E) day. However, the occurrence of floods or landslides was influenced by the weather conditions occurring on the days immediately preceding the event that caused the damage. Consequently, particularly prolonged rainy periods are often an aggravating factor [58, 59, 60] because pre-existing wet ground causes an increased risk of landslides. Moreover, river floods are also caused more frequently by prolonged rainy periods [61].

Further research will also study the weather types in a time lag of a few days prior to the event. This will ensure greater accuracy in calculating the risk index that will also take the persistence of the weather type into account. With the increasing reliability of seasonal forecasts, further calibration of WT-FLARI could allow for obtaining a very useful tool for preventing, or attempting to reduce, the impact of extreme rainfall events that are becoming more and more frequent [7, 62].

The World Health Organization (WHO), World Meteorological Organization (WMO), European Commission (EC), European Environmental Agency (EEA) and other important organizations encourage the development and evaluation of more effective and efficient interventions, such as early warning systems and in general, adaptation strategies to reduce negative impacts [3, 63, 64, 65, 66, 67, 68].

Conclusions

In recent decades, the number of natural disasters caused by weather events has increased with great economic losses and a large number of deaths. For example, between 2002 and 2014 there were 293 deaths in Italy and in 2013 alone, a total of 351 landslide and flood events were recorded [22].

This study has identified a specific risk index associated with each weather type, calibrated for each Italian region and applicable to both annual and seasonal levels. The risk index represents the seasonal and annual vulnerability of each Italian region and indicates that additional preventive actions are necessary for some regions.

The result of this work represent a good starting point towards the development of a tool to support policy-makers, local authorities and health agencies in planning actions, mainly in the medium to long term, aimed at the reduction of disasters. Disasters reduction represents an important issue of the World Meteorological Organization mission [36]. Actions to be taken on the eve on an emergency will nevertheless still predominantly managed through the use of deterministic models able to better locate the phenomena, but in the medium to long term (months), the WT approach could instead make possible a better use of seasonal forecasts, which, although in gradual improving, will unlikely be able to provide deterministic forecasts, on the contrary could provide useful information on the prevailing WT. It is still necessary to reiterate that the basis of a proper land policy remains the prevention to be made in the very long term (years) taking into account the changing climate and the need to adapt infrastructures and behaviors in order to prevent the occurrence of disasters. However, this index is in the experimental stage and it doesn’t take into account the man made environmental change (for example land use, overbuilding, river flow, etc). Further investigations are required concerning the choice of "exposure and vulnerability layers" that could impact on the results. WT-FLARI will be further tested and calibrated, specifically to consider a time lag during the days immediately preceding the catastrophic event. It would also be interesting to investigate the frequency of the events and how the weather types have changed over past decades. Changes in weather patterns will be one of the principal effects of climate change and may also give rise to a different frequency of extreme weather events.

Acknowledgments

The authors wish to thank AVI Project(Inventory of areas affected by landslides and floods in Italy), carried out by CNR, which allows data consultation available at http://avi.gndci.cnr.it/welcome_en.htm. Our study was funded by the European Project Horizon 2020 (H2020-DRS-2014) Culture And RISkmanagement in Man-made And Natural Disasters (CARISMAND—G.A. 635748—Horizon 2020). Thank you also the Regional MeteoSalute Project and the Regional Health System of Tuscany.

Data Availability

All relevant data are within the paper and in a specific public repository (https://github.com/meteosalute/weather_landslide).

Funding Statement

This study was funded by the European Project Horizon 2020 (H2020-DRS-2014) Culture And RISkmanagement in Man-made and Natural Disasters (CARISMAND—G.A. 635748—Horizon 2020).

References

  • 1. Kunkel KE, Pielke JR, Changnon SA (1999) Temporal fluctuations in weather and climate extremes that cause economic and human health impacts: a review. Bull. A M. Meteorol Soc 80:1077–1099. doi:101175/1520-0477(1999)080-1077:TFIWAC-2.0.CO [Google Scholar]
  • 2. Kharin VV, Zwiers FW, Zhang X, Hegerl GC (2007). Changes in temperature and precipitation extremes in the IPCC ensemble of global coupled model simulations. Journal Clim 20: 1419–1444. 10.1175/JCLI4066.1 [DOI] [Google Scholar]
  • 3.Harmeling S (2010) Global climate risk index 2010. Who is most vulnerable? Weather-related loss events since 1990 and how Copenhagen needs to respond. Bonn, Germany, Germanwatch Breafing Paper. 20pp
  • 4. WHO (2010) Report Climate Change, extreme weather events and public health Copenaghen, WHO Regional Office for Europe; 37pp [Google Scholar]
  • 5. Trenberth KE (2011) Changes in precipitation with climate change. Contribution to CR Special 25 “Climate services for sustainable development” 47: 123–138. doi: 103354/cr00953 [Google Scholar]
  • 6. Armstrong WH, Collins MJ, Snyder NP (2012). Increased frequency of low-magnitude floods in New England. J. Am. Water Res 48: 306–320. doi:101111/j1752-16882011.00613.x [Google Scholar]
  • 7.IPCC (2013) Report Intergovernmental Panel on Climate Change. Climate Change 2013. The Physical Science Basis. Working group I contribution to the fifth assessment report of the intergovernmental panel on climate change. 10.1017/CBO9781107415324 [DOI]
  • 8. Kumpulainen S (2006) Vulnerability concepts in hazard and risk assessment. Natural and technological hazards and risks affecting the spatial development of European regions. Geol Surv Finl 42: 65–74 [Google Scholar]
  • 9. Dilley M (2006) Setting priorities: global patterns of disaster risk. Phil Trans R Soc A 364: 2217–2229. 10.1098/rsta.2006.1823 [DOI] [PubMed] [Google Scholar]
  • 10. Vorosmarty CJ, Guenni LB, Wollheim WM, Pellerin B, Bjerklie D, Cardoso M, et al. (2013) Extreme rainfall, vulnerability and risk: a continental-scale assessment for South America. Phil Trans R Soc 371 10.1098/rsta.2012.0408 [DOI] [PubMed] [Google Scholar]
  • 11. Lowe D, Ebi KL, Forsberg B (2013) Factors Increasing Vulnerability to Health Effects before, during and after Floods. International Journal of Environmental Research and Public Health 10: 7015–7067. doi: 103390/iJerph10127015 10.3390/ijerph10127015 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 12. Cartwright L (2005). An examination of flood damage data trends in the Unites States. J Cont Water Res Educ 130: 20–25. doi:101111/j.1936-704x.2005.mp130001004.x [Google Scholar]
  • 13. Svensson C, Hannaford J, Kundzewicz AW, Marsh TJ (2006) Trends in river floods: why is there no clear signal in observations? In frontiers in flood research. IAHS Pubblications 305:1–18. Wallingford, UK: IAHS Press ISBN 1-901502-63-5 [Google Scholar]
  • 14. Neumayer E, Barthel F (2011) Normalizing economic loss from natural disaster: a global analysis. Glob Environ Change 21: 13–24. 10.1016/j.gloenvcha.2010.10.004 [DOI] [Google Scholar]
  • 15.Colon L (2013) Sources of Societal Vulnerability to Extreme Weather. Master’s Thesis, City College of New York, City University of New York. 226pp
  • 16. WHO (2013) Report Floods in the WHO European Region: health effects and their prevention World Health Organization. Bettina Menne and Virginia Murray Public Health England; 146pp [Google Scholar]
  • 17. Galea S, Nandi A, Vlahov D (2005) The epidemiology of post-traumatic stress disorder after disasters. Epidemiologic Reviews 27: 78–91 [DOI] [PubMed] [Google Scholar]
  • 18. Ahern M, Kovats S (2006) The health impacts of floods In: Few R., Matthies F, eds Flood hazards and health: responding to present and future risks. London, Earthscan; 28–53 [Google Scholar]
  • 19. Adeola F (2009) Mental health and psychological distress Sequelae of Katrina. Human Ecology Review 16: 195–210 [Google Scholar]
  • 20. Jakubicka T et al. (2010) Health impacts of floods in Europe: data gaps and information needs from a spatial perspective A MICRODIS report, Brussels, Centre for Research on the Epidemiology of Disasters; [Google Scholar]
  • 21. Milojevic A, Armostrong B, Kovats S, Butler B, Hayes E, Leonardi G, et al. (2011) Long-term effects of flooding on mortality in England and Wales, 1994–2005: controlled interrupted time-series analysis. Environmental Health 10:11 10.1186/1476-069X-10-11 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 22. ISPRA (2013) Linee Guida per la valutazione del dissesto idrogeologico e la sua mitigazione attraverso misure e interventi in campo agricolo e forestale. ISPRA Manuali e Linee guida, ISBN 978-88-448-0586-9 [Google Scholar]
  • 23. Few R, Ahern M, Matthies F, Kovats S (2004) Floods, health and climate change: a strategic review Tyndall Centre for Climate Change Research, November 2004 [Google Scholar]
  • 24. Michelozzi P, Francesca D (2014) Cambiamenti climatici, alluvioni e impatto sulla salute. Prog Med 105: 48–50 [DOI] [PubMed] [Google Scholar]
  • 25.EASAC and Norwegian Meteorological Institute (2013) Extreme Weather Events in Europe: preparing for climate change adaptation. ISBN 978-82-7144-100-5. Available online at www.easac.eu
  • 26. Jonkman SN, Kelman I (2005) An analysis of the causes and circumstances of flood disaster deaths. Disasters 29: 75–97 [DOI] [PubMed] [Google Scholar]
  • 27. EM-DAT (2010) The international disaster database Brussels, Centre for Research on the Epidemiology of Disasters, Online available at http://www.emdat.be/ [Google Scholar]
  • 28.Maynard-Ford MC, Phillips EC, Chirico PG (2008) Mapping vulnerability to disasters in Latin America and the Caribbean., 1900–2007. USG Open-File Report 2008–1924, available online at http://pubs.usgs.gov/of/2008/1924. US Geological Survey, Reston, Virginia 30pp;
  • 29. Guha-Sapir D, Rodriguez-Lianes JM, Jakubicka T (2011) Using disaster footprints, population database and GIS to overcame persistent problems for human impact assessment in flood events. Natural Hazards 58: 845–852 [Google Scholar]
  • 30. Hawley K, Moench M, Sabbag L (2012) Understanding the economics of flood risk reduction: a preliminary analysis Boulder, CO; Institute for Social and Environmental Transition; [Google Scholar]
  • 31. Weisheimer A, Palmer TN (2014) On the reliability of Seasonal Climate Forecast. R Soc Interface 6 July 2014, vol 11: 9620131162. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 32. Beck C, Jacobeit J, Jones PD (2007) Frequency and within-type variations of large scale circulation types and their effects on low-frequency climate variability in central Europe since 1780. Int J Climatol 27: 473–491 [Google Scholar]
  • 33. Huth R, Beck C, Philipp A, Demuzere M, Ustrnul Z, Cahynova M et al. (2008) Classifications of atmospheric circulation patterns: recent advances and applications. Ann N Y Acad Sci 1146: 105–152 10.1196/annals.1446.019 [DOI] [PubMed] [Google Scholar]
  • 34. Philipp A, Beck C, Huth R, Jacobei J (2014) Development and comparison of circulation type classifications using the COAST 733 dataset and software. International Journal of Climatology. 10.1002/joc.3920; [DOI] [Google Scholar]
  • 35. Salinger M.J., Baldi M., Grifoni D., Jones G., Bartolini G., Cecchi S, et al. ,(2015). Seasonal differences in climate in the Chianti region of Tuscany and the relationship to vintage wine quality. Int. J. Biometeorol. 10.1007/s00484-015-0988-8; [DOI] [PubMed] [Google Scholar]
  • 36.WMO (2013) Report Provisional Statement on Status of the Climate in 2013. On-line available at www.wmo.int/pages/mediacentre/press_releases/documents/ProvisionalStatementStatusClimate2013.pdf
  • 37. Kalnay E, Kanamitsu M, Kistler R, Collins W, Deaven D, Gandin L, et al. (1996) The NCEP/NCAR 40-year Reanalysis Project. Bulletin of the American and Meteorological Society 437–471 [Google Scholar]
  • 38. Uppala SM, Kallberg PW, Simmons AJ, Andrae U, Bechtold VDC, Fiorino M et al. (2006) The ERA-40 re-analysis. Q J Roy Meteorol Soc 131: 2961–3012 [Google Scholar]
  • 39. Philipp A, Bartholy J, Beck C, Erpicum M, Esteban P, Huth Fettweis R et al. (2010) Cost 733cat–a database of weather and circulation type classifications. Phys Chem Earth 35: 360–373 [Google Scholar]
  • 40.Huth (2000) A circulation classification scheme applicable in GCM studies. Theor Appl Climatol 67: 1–18 [Google Scholar]
  • 41. Christiansen B (2007) Atmospheric circulation regimes: Can cluster analysis provide the number? J Clim 20: 2229–2250 [Google Scholar]
  • 42.Erpicum M, Mabille G, Fettweiss X (2008) Automatic synoptic weather circulation types classification based on the 850hpa geopotential height. In abstracts COST 733 Mid.term Conference, Advances in Weather and Circulation Type Classifications & Applications 22a”25 October 2008 Krakow, Poland, 33
  • 43. Philipp A (2009) Comparison of principal component and cluster analysis for classifying circulation pattern sequences for the European domain. Theor Appl Climatol 31–41 [Google Scholar]
  • 44.ISPRA (2008) Landslides in Italy. Special Report 2008. ISBN: 978-88-448-0355-1
  • 45. Kruskal W.H., Wallis W.A., (1952). Use of ranks in one-criterion variance analysis. Journal of the American Statistical Association n.47, 583–621 [Google Scholar]
  • 46. Crichton D (1999) The Risk Triangle Ingleton J. (ed.), Natural Disaster Management, Tudor Rose, London: 102–103; [Google Scholar]
  • 47. Deser C, Knutti R, Solomon S, Phillips AS (2012) Communication of the role of natural variability in future North American climate. Nature Climate Change 2: 775–779 [Google Scholar]
  • 48. Selvin S (1991) Statistical analysis of epidemiology data Oxford University Press; 499. ISBN 0-19-517280-9 [Google Scholar]
  • 49. Gentle JE (2007) Matrix Algebra Theory. Computations and applications in statistics. ISBN 970-0-387-72836-0 [Google Scholar]
  • 50. Benestad RE, Nychka D, Mearns LO (2012a) Spatially and temporally consistent prediction of heavy precipitation from mean values. Nature Climate Change 2: 544–547 [Google Scholar]
  • 51. Benestad RE, Nychka D, Mearns LO (2012b) Specification of wet-day daily rainfall quintiles from the mean value. Tellus Series A Dynamic Meteorology and Oceanography 64 10.3402/tellusa.v64i0.14981 [DOI] [Google Scholar]
  • 52. Alpert P, Neeman BU, Shay ELY (1990a) Climatology analysis of Mediterranean cyclones using ECMWF data. Tellus 42A: 65–67 [Google Scholar]
  • 53. Alpert P, Neeman BU, Shay ELY (1990b) Intermonthly variability of cyclone tracks in the Mediterranean. Journal of Climate 3: 1474–1478 [Google Scholar]
  • 54. Maheras P, Flocas HA, Patrikas I, Anagnostopoulou CHR 2001. A 40 year objective climatology of surface cyclones in the Mediterranean region: spatial and temporal distribution. International Journal of Climatology 21: 109–13o [Google Scholar]
  • 55. Brooks HE (2009) Proximity soundings for severe convection for Europe and the United States from reanalysis data. Atmospheric Research 93: 546–553 [Google Scholar]
  • 56. Dotzek N, Groenemeijer P, Feuerstein B, Holzer AM (2009) Overview of ESSL’s severe convective storms research using the European Severe Weather Database ESWD. Atmospheric Research 93: 575–586 [Google Scholar]
  • 57. Kunz M, Sander J, Kottmeier C (2009) Recent trends of thunderstorm and hailstorm frequency and their relation to atmospheric characteristics in southwest Germany. International Journal of Climatology 29: 2283–2297 [Google Scholar]
  • 58. Dankers R, Feyen L (2009) Flood hazard in Europe in an ensemble of regional climate scenarios. Journal of Geophysical Research 114: D16–27. 10.1029/2008JD011523 [DOI] [Google Scholar]
  • 59. Hannan DM, Demuth S, Van Lanen HAJ, Looser U, Prudhomme C, Rees G et al. (2011) Large-scale river flow archives: importance, current status and future needs. Comment Hydrol Proc 25:1191–1200. 10.1002/hyp.7794 [DOI] [Google Scholar]
  • 60. Wynne-Evans E et al. (2011) Mapping of European flooding events 200–2009. Chemical Hazards and Poisons Report 20: 44–49. [Google Scholar]
  • 61. Fewtrell L, Kay D (2008) An attempt to quantify the health impacts of flooding in the United Kingdom using an urban case study. Public Health 122: 446–451 10.1016/j.puhe.2007.09.010 [DOI] [PubMed] [Google Scholar]
  • 62. Kundzewicz ZW, Radziejewski M, Pinskwar I (2006) Precipitation extremes in the changing climate of Europe. Climate Research 31: 51–58 [Google Scholar]
  • 63. United Nations Development Programme (2004) Report Reducing disaster risk: a challenge for development New York, NY: United Nations Development Programme, Bureau for Crisis Prevention and Recovery; 146pp [Google Scholar]
  • 64. Kirch W, Menne B, Bertollini R (2005) Extreme Weather Events and Public Health Responses. Springer E-book; XLVI: 303. ISBN 978-3-540-28862-6 [Google Scholar]
  • 65. Field CB, Barros V, Stocker TF, Qin D, Dokken DJ, Ebi KL et al. (2012) Managing the risks of extreme events and disasters to advance climate change adaptation A special report of working groups I and II of the intergovernmental panel on climate change. Cambridge University Press, Cambridge, UK, and New York, NY, USA: [Google Scholar]
  • 66.Cemaden, (2013) Report Centro National de Monitoramento e Alertas de Desastres Naturais (CEMADEN). Available online at www.cemaden.gov.br
  • 67.Integracao (2013) Sistema Integrado de Informacoes sobre Desastres-S2ID. Available online http://s2id.integracao.gov.br
  • 68. Wang L, Liao Y, Yang L, Li H, Ye B, Wang W (2014) Emergency Response to and Preparedness for Extreme weather Events and Environmental Changes in China. Environmental Changes in China. Asia Pacific Journal Public Health. 10.1177/1010539514549763 [DOI] [PubMed] [Google Scholar]

Associated Data

This section collects any data citations, data availability statements, or supplementary materials included in this article.

Data Availability Statement

All relevant data are within the paper and in a specific public repository (https://github.com/meteosalute/weather_landslide).


Articles from PLoS ONE are provided here courtesy of PLOS

RESOURCES