the Creative Commons Attribution 4.0 License.

the Creative Commons Attribution 4.0 License.

# Temporal evolution of flow-like landslide hazard for a road infrastructure in the municipality of Nocera Inferiore (southern Italy) under the effect of climate change

### Marco Uzielli

### Guido Rianna

### Fabio Ciervo

### Paola Mercogliano

### Unni K. Eidsvig

In recent years, flow-like landslides have extensively affected pyroclastic covers in the Campania region in southern Italy, causing human suffering and conspicuous economic damages. Due to the high criticality of the area, a proper assessment of future variations in event occurrences due to expected climate changes is crucial. The study assesses the temporal variation in flow-like landslide hazard for a section of the A3 “Salerno–Napoli” motorway, which runs across the toe of the Monte Albino relief in the Nocera Inferiore municipality. Hazard is estimated spatially depending on (1) the likelihood of rainfall-induced event occurrence within the study area and (2) the probability that the any specific location in the study area will be affected during the runout. The probability of occurrence of an event is calculated through the application of Bayesian theory. Temporal variations due to climate change are estimated up to the year 2100 through an ensemble of high-resolution climate projections, accounting for current uncertainties in the characterization of variations in rainfall patterns. Reach probability, or defining the probability that a given spatial location is affected by flow-like landslides, is calculated spatially based on a distributed empirical model. The outputs of the study predict substantial increases in occurrence probability over time for two different scenarios of future socioeconomic growth and atmospheric concentration of greenhouse gases.

In recent years, eminent scholars have debated about the main features of “shallow” and “deep” uncertainties in the assessment of natural hazards (Stein and Stein, 2013; Hallegatte et al., 2012; Cox, 2012). Shallow uncertainties are associated with reasonably knowing the probabilities of outcomes (Stein and Stein, 2013), while deep uncertainties are associated with (1) several possible future worlds without known relative probabilities, (2) multiple conflicting but equally reasonable world views, and (3) adaptation strategies with remarkable feedbacks among the sectors (Hallegatte et al., 2012).

As stressed in these works, climate change and its impacts can be considered paradigmatic of very deep uncertainty. Given the extent of potential impacts on communities (United Nations, 2015), including their economic dimension (Stern, 2007; Nordhaus, 2007; Chancel and Piketty, 2015), considerable effort has been made in recent years to assess the variations in frequency and magnitude of weather-induced hazards in a changing climate (Seneviratne et al., 2012). A variety of strategies have been devised and implemented with the aim of detecting the main sources of uncertainty and their extents (Wilby and Dessai, 2010; Cooke, 2014; Koutsoyiannis and Montanari, 2007; Beven, 2015).

Investigations of future trends in the occurrence and consequences of weather-induced slope movements and of the uncertainties in their estimation have received relatively limited interest (Gariano and Guzzetti, 2016; Beven et al., 2018). The paucity of investigations could be due to the mismatch between the usual scale of analysis for landslide case studies and the much coarser horizontal resolutions of climate projections currently available as well as the difficulty in generalizing findings to other contexts, given the relevance of site-specific geomorphological features.

## 1.1 Previous studies of flow-like movements in pyroclastic soils in Campania

In an attempt to address the above limitations, several recent studies have focused on future variations in the occurrence of flow-like landslides, or more generally, flow-like movements affecting pyroclastic covers mantling the carbonate bedrock in the Campania Region in southern Italy. Flow-like movements in granular materials such as pyroclastic terrain are among the most destructive mass movements due to their velocity and the absence of warning signs (Hutchinson, 2004; Cascini et al., 2008).The aforementioned studies focused on a number of sites, namely Cervinara (Damiano and Mercogliano, 2013; Rianna et al., 2016), Nocera Inferiore (Reder et al., 2016; Rianna et al., 2017a, b), and Ravello (Ciervo et al., 2016). Several aspects differentiate the case studies and, consequently, the respective investigations. The depth, stratigraphy, and grain size of pyroclastic covers are fundamentally regulated by slope, distance to volcanic centers (Campi Flegrei and Somma-Vesuvio), and the wind direction and magnitude during the eruptions; therefore, the critical rainfall pattern inducing the slope failure varies according to these differences (e.g., intensity and the length of antecedent precipitation time window). Indeed, at some locations (Cervinara and Nocera Inferiore), the triggering event is recognized as being characterized by daily duration (also acting jointly with wet antecedent conditions), while in other locations (Ravello), events in shallower covers or covers formed by coarser materials require heavy rainfall lasting several hours. Consequently, two different approaches are followed (for the scope of such a data elaboration) based on the considered duration. Relative to daily durations, the former modifies daily observations according to projected anomalies (Damiano and Mercogliano, 2013) or simulated data through statistical bias correction approaches (adopted for the Cervinara and Nocera Inferiore test cases). In the latter case, a stochastic approach is coupled with bias-corrected climate data to provide assessments at an hourly scale (adopted for the Ravello test case). Some studies (Reder et al., 2016; Ciervo et al., 2016; Rianna et al., 2017b) make use of expeditious statistical approaches referring to rainfall thresholds to assess slope stability conditions, while other studies employ physically based approaches (Damiano and Mercogliano, 2013; Rianna et al., 2017a).

## 1.2 Objective of the study

This study focuses on the quantitative estimation of the temporal evolution of hazard for rainfall-triggered flow-like movements affecting a stretch of a national motorway in the municipality of Nocera Inferiore. Flow-like landslide runout is probabilistically investigated through a frequentist estimate of “reach probability” (Rouiller et al., 1998; Copons and Vilaplana, 2008) performed in a GIS environment, thus allowing for the seamless mapping of landslide hazard under current and future climate change scenarios.

The study presents significant elements of novelty. For instance, through a Bayesian approach, it characterizes precipitation values cumulated for two time windows as proxies for the triggering of flow-like movements in pyroclastic covers in the Lattari mountain range. The resulting quantitative model returns temporal variations in triggering probability, thus accounting for the effect of climate change on rainfall trends. Uncertainties in variations in rainfall patterns are taken into account by means of the EURO-CORDEX ensemble. Projections provided by climate simulations are bias-adjusted, allowing for the comparison with available physically based rainfall thresholds while adding further assumptions and uncertainties in simulation chains. The analysis also relies on rainfall data from the rain gauges located in Gragnano and Castellammare di Stabia. The location of the three towns in Italy and in the Campania region is illustrated in Fig. 1.

## 2.1 Geographic and geomorphological description

Most of the territory of the Nocera Inferiore municipality belongs geomorphologically to the Sarno River valley. The most urbanized area of the town is located at the toe of the northern slopes of the Mount Albino relief, pertaining to the Lattari mountain range (Fig. 2, sector A); other more sparsely populated areas are located at the foot of the Torricchio hills (Fig. 2, sector B). These reliefs are constituted by carbonate rocks covered by air-fall pyroclastic deposits originating from volcanic eruptions (Somma-Vesuvio complex) during the last 10 000 years (Pagano et al., 2010). Such covers in loose pyroclastic soils have historically been affected by multiple types of rainfall-induced flow movements, including Gragnano (in 1997), Sarno and Quindici (in 1998), Nocera (in 2005), and Ischia (in 2006). The complete list of events affecting the area considered in the study in the period 1960–2015 is given in Table 2. Movement types include (a) “hyper-concentrated flows” (flows in the transition from mass transport to mass movement) that are generally triggered by washing away and/or progressive erosive processes along rills and inter-rill areas, (b) “channelized debris flows” (channelized flow-like mass movements) that are generated by slope failure in “zero order basin” (ZOB) areas (Dietrich et al., 1986; Cascini et al., 2008) and funnel into stream channels (the propagation process is laterally confined by the stream channel), and (c) “un-channelized debris flows” (un-channelized flow-like mass movements; Costa, 1984; Hutchinson et al., 2004), which are locally triggered on open-slope areas and propagate as debris avalanches (the propagation process is not laterally confined). The third type characterized the most recent event that affected the town in March 2005, causing three fatalities and extensive damage to buildings and infrastructure (Pagano et al., 2010; Rianna et al., 2014). This study focuses specifically on a section of the A3 “Salerno–Napoli” motorway, which runs across the toe of the Monte Albino relief, as shown in Fig. 3.

In the disaster risk management discipline, the term “hazard” has been linked to multiple definitions and operational guidelines, depending on the scope, technical approach employed, and available data and models. Fell et al. (2008) distinguish “susceptibility zoning” from “hazard zoning” on the basis that the former involves the spatial distribution and rating of the terrain units according to their propensity to produce landslides, while the latter should include, wherever possible, the quantitative estimation of the frequency of landsliding. In situations where this estimation is difficult to pursue, some approximate guidance on frequency should be provided. Corominas et al. (2015) defined hazard as “a condition that expresses the probability of a particular threat occurring within a defined time period and area”, with no explicit reference to frequency. In this study, calculated hazard levels refer to the frequency of the occurrence of at least one landslide event within the study area in 30-year periods. In the more specific context of the case study presented herein, the geologic hazard mapping web page of ISPRA, the Italian National Institute for Environmental Protection and Research, states that landslide prediction models “usually address where an event is expected to occur and with which probability, without explicitly estimating return periods and intensities”.

Operationally, the study is conducted by coupling mathematical software with GIS to obtain spatially referenced estimates of hazard and its mapping. A digital terrain model (DTM) of the study area, having a resolution of 15×15 m, was built for the purpose of the GIS-based modeling of runout. The original resolution adopted for the Campania region's ORCA project in 2004 was 5×5 m. A variety of DTM resolutions were tested for the case study. The adopted resolution proved to be sufficient to adequately represent the surface morphology and runout as detailed in Sect. 6. Hazard is estimated quantitatively for each cell in the GIS-generated grid through the following model:

where *P*_{L} is the probability of event occurrence and
*P*_{R} is the reach probability for the cell. Occurrence probability
defines the likelihood of the occurrence of at least one event in the study
area as a consequence of the attainment of given thresholds of cumulative
rainfall and of the likelihood of triggering given the occurrence of such
thresholds. Reach probability describes the probability that a given cell
will be reached by a moving soil mass, assuming that flow-like landslides
have been triggered in one or more potential source areas. Occurrence
probability and reach probability are distinct parameters that depend on
different factors and are computed separately.

Occurrence probability is partly related to the likelihood of triggering given the attainment of specific rainfall thresholds, which is assumed to be an inherent, time-invariant attribute of the area, and it is partly related to climate change through the time-dependent probability of the exceedance of such rainfall thresholds, as described in Sect. 5. Reach probability is not related to climate change, as it parameterizes the probability of spatial occupation during runout, assuming that triggering has occurred. Reach probability depends solely on terrain factors and is thus amenable to the concept of susceptibility, as defined by Fell et al. (2008), among others. Occurrence and triggering probabilities are related to rainfall parameters and, thus, are assumed to be spatially invariant and uniform for the entire area (but are time-dependent), while reach probability depends on geomorphological factors and is thus cell-specific and spatially variable (but is time-invariant) within the area. These aspects are explained in detail later in the paper. The study is conducted according to the operational flowchart shown in Fig. 4. The modular approach initially involves the disjoint estimation of occurrence probability (including its temporal variation), as described in Sect. 5, and of reach probability, as detailed in Sect. 6. Subsequently, hazard is calculated in Sect. 7 using the model described above.

## 4.1 Observed precipitation data

Observed datasets are used to identify time windows used as proxies for flow-like landslide triggering to implement the Bayesian approach described in Sect. 5.2. Subsequently, data from the Nocera Inferiore station are used for the bias adjustment of climate projections estimating occurrence probability (Sect. 5.3). Although the study focuses on Nocera Inferiore flow-like movements, data from the neighboring towns of Gragnano and Castellammare di Stabia are considered in order to increase the size of the event database, thus increasing the statistical significance of the approach. At both sites, events affecting pyroclastic covers were observed to be very similar to those of the Nocera Inferiore slopes (De Vita and Piscopo, 2002) as described in Sect. 4.2.

The dataset related to daily precipitation spans across the time window from 1 January 1960 to 31 December 2015. Unfortunately, no weather stations were in operation throughout the entire period for any of the three towns. Consequently, the dataset was reconstructed by merging data provided by different weather stations. Prior to 1999, the network of monitoring stations was managed by Servizio Idrografico e Mareografico Nazionale (SIMN – Hydrographic and Tidal National Service) network at the national level. In that period, the selected reference weather station is that which is located within the town and is identified with the town's name, as can be found in the SIMN yearbooks. Subsequently, the management was delegated to regional level, with the regional civil protection managing the dataset for the Campania region. Since 1999, the reference weather stations have been selected as some of those adopted for the towns in regional early warning systems against geological and hydrological hazards (2005). Checks for the homogeneity of time series and for the unwarranted presence of break points between the two periods were carried out for this study through the Pettitt (1979) and CUSUM (CUmulative sum; Smadi and Zghoul, 2006) tests. Source weather stations, their locations, installation times, and main (i.e., at least 4 months in a year) out-of-use periods are reported in Table 1.

## 4.2 Flow-like movements inventory

The inventory was compiled using three main references: Vallario (2000), De Vita and Piscopo (2002), and, for the more recent events, the “Event Reports” drafted by the regional civil protection. The multiple sources used for reconstructing the inventory provide quite different details. De Vita and Piscopo (2002), for example, report the cumulative rainfall values inducing the events on time spans up to 60 days for events in the same geomorphological context. Vallario (2000) provides brief descriptions about the events (also for the other natural hazards affecting the region), including the number of fatalities and injured people. “Event Reports”, drafted by the regional civil protection, contain exhaustive descriptions about the weather patterns inducing the triggering event and the main consequences for the affected communities. It is worth recalling that only events affecting pyroclastic covers have been considered and included in the dataset. Sixteen events were observed in the period 1960–2015, as detailed in Table 2.

## 4.3 Climate projections

The generation of climate projections was conducted for Nocera Inferiore as a
preliminary step in the quantitative characterization of the temporal
evolution of occurrence probability, since the latter depends partly on the
frequency with which specific rainfall thresholds are attained. The adopted
simulation chain includes several elements. Firstly, scenarios about future
variations in the concentrations of atmospheric gases inducing climate
alterations are assessed through socioeconomic approaches including
demographic trends and land use changes. IPCC (Intergovernmental Panel on
Climate Change) defined Representative Concentration Pathways (RCP)
in terms of increases in radiative forcing in
the year 2100 (compared to preindustrial era) of about 2.6, 4.5, 6.0, and
8.5 W m^{−2}. Such scenarios force global climate models (GCM). These are
recognized for their reliable representation of the main features of the
global atmospheric circulation but fail to reproduce weather conditions at
temporal and spatial scales of relevance for assessing impacts at the
regional and local scale. In order to bridge such a gap, GCMs are usually
downscaled through regional climate models (RCMs). These are climate models
nested on GCMs, from which they retrieve initial and boundary conditions, but
work at higher resolutions (including a non-hydrostatic formulation) on a
limited area. The dynamic downscaling from GCMs to RCMs allows for a better
representation of surface features (orography, land cover, etc.) and of
associated atmospheric dynamics (e.g., convective processes). Nevertheless,
persisting biases can hinder the quantitative assessment of local impacts.

In order to cope with such shortcomings, a number of strategies can be adopted. For instance, to characterize uncertainty associated to future projections, a climate multi-model ensemble can be utilized where different combinations of GCM and RCM run on fixed grid and domain. Furthermore, statistical approaches (e.g., Maraun, 2013; Villani et al., 2015; Lafon et al., 2013) can be pursued to reduce biases assumed as systematic in simulations. More specifically, quantile mapping approaches have been applied for impact studies with satisfactory results in recent years. In these applications, the correction is performed to ensure that “a quantile of the present-day simulated distribution is replaced by the same quantile of the present-day observed distribution” (Maraun, 2013). However, limitations and assumptions associated to these approaches should be clear to practitioners (Ehret, 2012; Maraun and Widmann, 2015).

In the present study, climate simulations included in EURO-CORDEX multi-model ensemble at 0.11' (approximately 12 km) are considered under the RCP4.5 and RCP8.5 scenarios, as described in Table 3 (Giorgi and Gutowski, 2016). Climate simulations are adjusted for bias through an empirical quantile mapping approach (Gudmundsson et al., 2012) using data from Nocera Inferiore weather stations from the period 1981–2010.

In Fig. 5, the variations expected in monthly cumulative values (5a) and maximum daily precipitation (5b) are displayed, assuming 1981–2010 as the reference period and splitting the period 2010–2100 into three 30-year periods. More specifically, the upper part of Fig. 5a shows the expected variations in monthly cumulative variations for RCP 4.5 (continuous line) and RCP8.5 (hatched line) as returned by bias-corrected projections in the short-term (green; 2011–2040 vs. 1981–2010), medium-term (blue; 2041–2070 vs. 1981–2010) and long-term (red; 2071–2100 vs. 1981–2010). The bottom part of Fig. 5a shows the observed annual cycle of monthly cumulative precipitation (in mm). Fig. 5b shows the mean values of maximum daily precipitation in the reference observed period (1982–2009) projected onto short-term (green: 2011–2040 vs. 1981–2010), medium-term (blue: 2041–2070 vs. 1981–2010) and long-term (red: 2071–2100 vs. 1981–2010) periods. Filled and dashed bars correspond to results for RCP4.5 and RCP8.5, respectively.

The ensemble mean values from EURO-CORDEX optimally overlap the actual
values (data not displayed) for the same time span. Concerning future time
periods, reductions of up to 45 % (under RCP8.5) are expected in the summer
season. From this perspective, the decreases are mainly regulated by the
severity of concentration scenarios. Values generally lower than the current
ones are also estimated in spring (approximately −10 %) and in the first
part of fall (approximately −5 %). These predictions are characterized by
a fluctuating signal. An increase is expected in the remaining seasons, with
few exceptions (i.e., short term 2011–2040 under RCP4.5). Higher increases
could exceed 20 % in November and 15 % in January. These evolutions could
primarily induce variations in the timing of flow-like movements affecting
pyroclastic covers in the area. Such events especially tend to occur in the
second part of winter (or first part of spring), following the increase in
antecedent precipitation. On the contrary, the likelihood of occurrence
reduces during fall and in the first part of winter. It is also worth
noting that the expected increase in temperature (not taken into account in
this approach) could lead to a higher atmospheric evaporative demand and,
thus, to lower values of soil water content within the pyroclastic covers.
Regarding precipitation triggering events, the variations in maximum daily
precipitation are displayed in Fig. 4b. Under both scenarios, increases
with respect the reference value (about 90 mm day^{−1}), ranging from 5 % and 15 %
and as high as 20 % for a “mid-way” scenario are expected under RCP8.5 for
the intermediate time horizon.

## 5.1 Calculation method

Flow-like landslide occurrence probability was estimated quantitatively as a
function of two cumulative rainfall thresholds, namely, the 1-day rainfall
*β*_{01} and the 59-day rainfall *β*_{59}. Several studies have
stressed the prominent role of antecedent precipitation for the occurrence of
movements in pyroclastic covers; De Vita and Piscopo (2002) used 59-day
rainfall for the same geomorphological context, and Napolitano et al. (2016)
defined different intensity–duration (I–D) rainfall thresholds for dry and
wet seasons for the Sarno area. Comegna et al. (2017) stated through a
statistical framework that the effective precipitation period for the
area of the Lattari Mountains could be 3 months long. Fiorillo and Wilson (2004) suggested a
simplified approach to evaluate the attainment of soil moisture states that
could act as triggering factors. Pagano et al. (2010), interpreting the 2005
events in Nocera Inferiore, suggested that antecedent precipitation should
be considered for at least 4 months for those events. Reder et al. (2018)
stressed the role of soil–atmosphere water exchanges during the entire
hydrological year, also accounting for the effect of evaporation losses. They
also stated that the effective length of effective antecedent precipitation
window is highly dependent on local conditions: cover depth, pumice lenses,
and bottom hydraulic conditions.

In this study, cumulative rainfall parameters were calculated using a moving
window procedure associated with each day from 1 January 1960 to 31 December 2015 from
the observed precipitation data described in Sect. 4.1. The
number of events observed for each day at the Nocera Inferiore, Gragnano and
Castellammare di Stabia, as reported in the inventory, were associated with the
rainfall data. Figure 6 plots the pairs of *β*_{01} and *β*_{59}
recorded daily in the period 1960–2015, along with the indication of
the occurrence (by site) or non-occurrence of flow-like landslide events.

The probability of event occurrence is given by

where ${\mathit{\beta}}_{\mathrm{01}}^{\left(i\right)}$ is the *i*th value of
cumulative rainfall *β*_{01} (*i*=1, …, ${N}_{{\mathit{\beta}}_{\mathrm{01}}})$,
${\mathit{\beta}}_{\mathrm{59}}^{\left(j\right)}$ is the *j*th value of cumulative rainfall
*β*_{59} (*j*=1,…, ${N}_{{\mathit{\beta}}_{\mathrm{59}}})$, and ${P}_{T}^{\left(ij\right)}=P\left(T\mathrm{|}{\mathit{\beta}}_{\mathrm{01}}^{\left(i\right)},{\mathit{\beta}}_{\mathrm{59}}^{\left(j\right)}\right)$ is the conditional probability of
triggering of a flow-like landslide given the simultaneous occurrence of
${\mathit{\beta}}_{\mathrm{01}}^{\left(i\right)}$ and ${\mathit{\beta}}_{\mathrm{59}}^{\left(j\right)}$.

The joint probability $P\left({\mathit{\beta}}_{\mathrm{01}}^{\left(i\right)},{\mathit{\beta}}_{\mathrm{59}}^{\left(j\right)}\right)$ of the simultaneous occurrence of ${\mathit{\beta}}_{\mathrm{01}}^{\left(i\right)}$ and ${\mathit{\beta}}_{\mathrm{59}}^{\left(j\right)}$ is obtained as the frequentist ratio of the number of days in which the simultaneous occurrence of ${\mathit{\beta}}_{\mathrm{01}}^{\left(i\right)}$ and ${\mathit{\beta}}_{\mathrm{59}}^{\left(j\right)}$ was recorded to the total number of days for which observations at the rain gauges are available. While $P\left({\mathit{\beta}}_{\mathrm{01}}^{\left(i\right)},{\mathit{\beta}}_{\mathrm{59}}^{\left(j\right)}\right)$ is assumed to be temporally variable due to the climate-change-induced variations in rainfall patterns over time, the triggering probability is assumed to be an inherent, temporally invariant characteristic of the study area, as it parameterizes, in terms of probability, the susceptibility of the triggering of flow movements in the area in response to the attainment of specific rainfall thresholds. It accounts implicitly and empirically for all physical factors affecting triggering mechanisms. The triggering probability is calculated as described in the following section.

## 5.2 Triggering probability calculation method

The conditional probability ${P}_{T}^{\left(ij\right)}$ of the triggering of a flow-like landslide given the simultaneous occurrence of ${R}_{\mathrm{01}}^{\left(i\right)}$ and ${R}_{\mathrm{59}}^{\left(j\right)}$ is estimated using a Bayesian approach as suggested by Berti et al. (2012). The procedure refers to Bayes' theorem, formulated as follows:

where, in the Bayesian glossary, $P\left({\mathit{\beta}}_{\mathrm{01}}^{\left(i\right)},{\mathit{\beta}}_{\mathrm{59}}^{\left(j\right)}\mathrm{|}T\right)$ is the likelihood,
i.e., the conditional joint probability of the simultaneous occurrence of ${\mathit{\beta}}_{\mathrm{01}}^{\left(i\right)}$ and ${\mathit{\beta}}_{\mathrm{59}}^{\left(j\right)}$ if an event
is triggered in the reference area, and *P*(*T*) is the prior probability, i.e.,
the probability of triggering in the reference area, regardless of the
magnitude of *β*_{01} and *β*_{59}.

Let *N*_{β} represent the total number of rainfall events recorded during a given reference time
period, *N*_{L} the total number of flow-like landslides occurred during the given reference time
period,
${N}_{{\mathit{\beta}}_{\mathrm{01}}^{\left(i\right)}}$ the number of rainfall events of a given magnitude
of *β*_{01} recorded during the given time reference,
and ${N}_{{\mathit{\beta}}_{\mathrm{59}}^{\left(j\right)}}$
the number of rainfall events of a given magnitude of *β*_{59} recorded during the given time
reference.

The likelihood can be calculated as the product of the marginal conditional probabilities of attainment of ${\mathit{\beta}}_{\mathrm{01}}^{\left(i\right)}$ and ${\mathit{\beta}}_{\mathrm{59}}^{\left(j\right)}\phantom{\rule{0.125em}{0ex}}$given the occurrence

The above Bayesian probabilities can be computed in terms of relative frequencies as follows:

where ${N}_{{\mathit{\beta}}_{\mathrm{01}}^{\left(i\right)}\mathrm{|}T}$ is the number of rainfall events of a magnitude of at least ${\mathit{\beta}}_{\mathrm{01}}^{\left(i\right)}$ recorded during the given time reference that resulted in the triggering of flow-like landslides, and ${N}_{{\mathit{\beta}}_{\mathrm{59}}^{\left(j\right)}\mathrm{|}T}$ is the number of rainfall events of a magnitude of at least ${\mathit{\beta}}_{\mathrm{59}}^{\left(j\right)}$ recorded during the given time reference that resulted in the triggering of flow-like landslides.

Figure 7 plots triggering probability *P*_{T} as a function of 1-day and
59-day cumulative rainfall, as estimated through the Bayesian approach.
Possible future variations in land use and land cover features are assumed not to
significantly affect proxy values. This is a simplistic hypothesis, as local
conditions could substantially modify the susceptibility of the areas to
event occurrence (e.g., fires destroying vegetation). Should substantial
variations in physical factors occur in the study area, a re-evaluation of
triggering probability is warranted.

## 5.3 Occurrence probability outputs

Following the quantitative estimation of the site-specific triggering probability as described above, flow-slide occurrence probability was calculated using Eq. (2) for each of the 10 EURO-CORDEX ensemble models and for 10 sets of 30-year intervals from 1981–2010 to 2071–2100 for both the RCP4.5 and RCP 8.5 scenarios.

A quantitative statistical analysis was conducted with the aim of analyzing
ensemble outputs. The first module of the analysis consisted of the
second-moment statistical characterization of the output samples. Such
characterization involved the calculation of the mean, standard deviation, and
sample coefficient of variation (given by the ratio of the latter to the
former) for the 10-valued sets of ensemble model outputs for each of the 10
30-year intervals. Figure 8 plots the temporal variation of *P*_{L}
for 10 sets of 30-year intervals from 1981–2010 to 2071–2100 and for the
RCP4.5 and RCP 8.5 scenarios, more specifically, model outputs and ensemble
means for RCP4.5 (8a), RCP8.5 (8b), and for both concentration
scenarios (8c). Figure 8d plots the sample coefficient of variation for both
scenarios.

For the RCP4.5 scenario, considering the running 30-year averages, a visual inspection of Fig. 8 suggested that all available projections predict a moderate increase in occurrence probability. A higher spread among the models is recognizable at the middle of the twenty-first century, as parameterized by the peak in the sample coefficient of variation. Such an increased spread is mainly due to the outputs of two models constantly representing the upper and bottom boundaries of the ensemble throughout the entire period investigated. For the RCP8.5 scenario, one of the 10 ensemble models yields occurrence probability values that progressively increase with respect to the other models over time. This leads to a marked increase in the scatter as parameterized by the sample coefficient of variation.

The second module of the statistical analysis consisted of the assessment of
the existence and strength of a temporal statistical trend in occurrence
probability values for the comprehensive set of output of the 10 models in
the CORDEX ensemble for the 10 sets of 30-year periods. This analysis was
conducted by means of two non-parametric statistical tests aimed at
assessing the statistical independence between occurrence probability and
time (as parameterized by a 30-year interval to which a specific
occurrence probability value pertains) through the calculation of rank
correlation statistics and related *p* values that parameterize the
significance level at which the null hypothesis of statistical independence
can be accepted. Spearman's test (Spearman, 1904) entails the calculation of
Spearman's rank correlation coefficient *ρ*, which measures rank
correlation on a $-\mathrm{1}:\mathrm{1}$ scale (−1 is the full negative rank correlation, 0 is no rank
correlation, and 1 is the full rank correlation) for an associated *p* value. The
output values of *ρ* were 0.351 for RCP4.5 and 0.381 for RCP8.5. The
associated *p* values were calculated as $\mathrm{3.45}\times {\mathrm{10}}^{-\mathrm{4}}$ for RCP4.5
and $\mathrm{9.22}\times {\mathrm{10}}^{-\mathrm{5}}$ for RCP8.5, attesting to a very low
significance level for the rejection of the null hypothesis of statistical
independence between the time and occurrence probability. Kendall's test
(Kendall, 1938) entails the calculation of the statistic *τ*, which
measures rank correlation on a $-\mathrm{1}:\mathrm{1}$ scale (−1 is the full negative rank
correlation, 0 is no rank correlation, 1 is the full rank correlation) for an
associated *p* value. The output values of *τ* were 0.245 for RCP4.5 and
0.277 for RCP8.5. The associated *p* values were calculated as $\mathrm{5.42}\times {\mathrm{10}}^{-\mathrm{4}}$ for RCP4.5 and $\mathrm{9.07}\times {\mathrm{10}}^{-\mathrm{5}}$ for RCP8.5, again
attesting to a very low significance level for the rejection of the null
hypothesis. The non-parametric analysis thus assessed the existence of a
strong statistical dependency of occurrence probability from time, thereby
confirming the influence of climate change on flow-like movement hazard.

The third module consisted of the concise formulation of occurrence probability through the fitting of analytical models. The purpose of this model was to allow for a more concise forward estimation of triggering probability. In this study, the fitting of analytical models was conducted with the aim of relating analytically calculated values to specific levels of the likelihood of exceeding the occurrence probability. This was achieved through quantile regression.

Quantile regression is a type of regression analysis often used in statistics and econometrics. Whereas the method of least squares results in estimates that approximate the conditional mean of the response variable given certain values of the predictor variables, quantile regression aims at estimating any user-defined quantile of a response variable in this case of triggering probability (Yu et al., 2003). Quantile regression implements a minimization algorithm and yields model parameters that define the analytical model for user-defined regression quantiles (corresponding to a likelihood of non-exceedance). The use of quantile regression enables us to address explicitly different levels of conservatism in the output models, with higher quantiles corresponding to higher levels of conservatism. Quantiles of 0.50 and 0.90 were considered, corresponding to 50 % and 10 % likelihoods of exceedance, i.e., to scenarios of medium and high conservatism, respectively.

In applying quantile regression, a variety of analytical models were adapted to the dataset, including the linear, power, logarithmic, and modified geometric models. Among those, the third displayed the best goodness of fit. The modified geometric model employed in this study is given by

where *p*_{1} and *p*_{2} are the model parameters to be estimated using
quantile regression and *t*_{30}=1 … 10 is an auxiliary discrete
natural variable referring to the ordinality of the 30-year averaging
interval (e.g., 1981–2010 is interval “1” and 2071–2100 is interval “10”).
Fig. 9a and b show the quantile regression-based fits of the
modified geometric model to the samples of occurrence probability values for
likelihoods of exceedance of 50 % (*Q*_{50}) and 10 % (*Q*_{90}) for
RCP4.5 and RCP8.5, respectively.

The output model parameters for RCP4.5 were ${p}_{\mathrm{1}}=\mathrm{1.38}\times {\mathrm{10}}^{-\mathrm{3}}$ and
${p}_{\mathrm{2}}=-\mathrm{0.087}$ for *Q*_{50} and ${p}_{\mathrm{1}}=\mathrm{1.71}\times {\mathrm{10}}^{-\mathrm{3}}$ and ${p}_{\mathrm{2}}=-\mathrm{0.156}$
for *Q*_{90}. For RCP8.5, ${p}_{\mathrm{1}}=\mathrm{1.37}\times {\mathrm{10}}^{-\mathrm{3}}$ and ${p}_{\mathrm{2}}=-\mathrm{0.110}$ for
*Q*_{50} and ${p}_{\mathrm{1}}=\mathrm{1.83}\times {\mathrm{10}}^{-\mathrm{3}}$ and ${p}_{\mathrm{2}}=-\mathrm{0.190}$ for *Q*_{90}. While
the plots show a continuous fitted model for the sake of visual appreciation
of the quantile regression outputs, it must be noted that *t*_{30} is a
discrete variable that can only take integer values between 1 and 10.
Table 4 illustrates the values of occurrence probability as calculated from
the modified geometric models for *Q*_{50} and *Q*_{90}. The ratios of
occurrence probability of a given interval to those of the observed data
(1981–2010) are also provided to provide a quantitative measure of the
effect of climate change over time. The findings displayed comparable
increases under both RCPs, with no clear increases for the more severe
scenario. Such results are consistent with variations shown in Fig. 4, where
monthly anomalies and future expected values in maximum daily precipitation
are reported. While decreases during the dry season are clearly more
remarkable under RCP8.5, increases during the fall and winter seasons do
not return clear patterns regulated by scenarios or time horizons. In this
perspective, no significant differences between RCPs are observed.

It is worth recalling that the present approach neglects several dynamics (e.g., effects of evapotranspiration reducing the soil moisture), which could play a significant role because of increased warming. For any given time interval and level of conservatism, occurrence probability is assumed to be spatially uniform within the study area, since the database that is used to develop the Bayesian method refers to the entire area itself. As detailed in a similar study by Berti et al. (2012), the quantitative output of empirical methods such as the one developed in the paper implicitly accounts for the spatial variability (if any) of rainfall characteristics within the area. In this study, three distinct reference weather stations were used for the three towns. The analysis of Nocera relies only on the local weather station, whose data were also used for bias correction purposes. Given the limited geographical extension of the area, the component of epistemic uncertainty due to spatial variability is not expected to be significant.

Investigation of the spatial variability of flow-like landslide hazard entails the modeling of its downslope propagation (runout). Reach probability is the probability (from 0, certainty of no reach, to 1, certainty of reach) of each point in the spatial domain being affected by the event during the runout process. Several morphologically, empirically, and physically based approaches are available for quantitative runout analysis (Hürlimann et al., 2008). Each of these may present advantages or weaknesses in relation to site- and/or phenomenon-specific attributes, data availability, and the scale of the analysis. Consistent with the methods previously used to define rainfall-triggering scenarios, the approach used to define downslope runout scenarios is based on an algorithm involving stochastic modeling.

## 6.1 Reach probability calculation method

Reach probability was computed spatially using Flow-R, a DTM-based
distributed empirical model developed in the
Matlab^{®}
environment (Horton et al., 2013). Due to the large geographical scale of
the area and to the deep complexity of the analyzed phenomena, an approach that was not highly
parameter-dependent was deliberately adopted. A variety of DTM
resolutions were tested for the case study, and a 15×15 m resolution was
chosen. Comparing the DTM with the real current morphological shape of the
areas both numerically and by expert judgment, the adopted resolution is
deemed to represent the channelized shape and the fan
areas with good accuracy, confirming the Horton et al. (2013) observations. The flow-slide
spreading is controlled by a flow direction algorithm that reproduces flow
paths (Holmgren, 1994) and by a persistence function to consider inertia and
abruptness in change of the flow direction (Gamma, 2000). In the setting used in this study
(*x*=1, see Eq., 3 in Horton et al., 2013), the flow direction algorithm proposed by Holmgren (1994) is similar to the multiple D8 of
Quinn et al. (1991, 1995). The multiple D8 distributes the flow to all
neighboring downslope cells weighted according to slope. The algorithm tends
to produce more realistic-looking spatial patterns than the simple D8
algorithm by avoiding concentration in distinct lines (Seibert and McGlynn,
2007). The maximum possible runout distances are computed by means a
*simplified friction-limited model* based on a unitary energy balance
(Horton et al., 2013).

One-run propagation simulation provides possible flow-paths generated from previously identified triggering or source areas. In this work, source areas were identified by means of the official geomorphological map of the “Campania Centrale” River Basin Authority (PSAI, 2015). The set of source areas coincides with the union of the “zero order basin” (ZOB) and current “niche/failure” areas, as shown in Fig. 10. This hypothesis is in accordance with the requirement of consistency with accounts of historical events and with the aim of considering the most pessimistic possible triggering scenarios (i.e., those with maximum mass potential energy).

The reach probability for any given cell *P*_{R} is calculated by the
following equation:

where *u* and *v* are the flow directions, *p*_{u} is the probability value
in the *u*th direction, ${p}_{u}^{\mathrm{fd}}$ is the flow proportion according to the
flow direction algorithm, ${p}_{u}^{p}$ is the flow proportion according to
the persistence function, and *p*_{0} is the probability determined
in the previous cell along the generic computed path. The values are
subsequently normalized. Runout routing is stopped when (1) the angle of
the line connecting the source area to the most distant point reached by the
flow slide along the generic computed path is smaller than a predefined
*angle of reach* (Corominas, 1996) and (2) the velocity exceeds a user-fixed maximum value
or is below the value corresponding to the maximum energy lost due to
friction along the path. The values that do not fit the aforementioned
requirements are redistributed among the active cells to ensure the conservation
of the total probability value.

## 6.2 Reach probability outputs

The propagation routine was applied to the DTM described in Sect. 3. An
*angle of reach* of 4^{∘} was calibrated based on the
geomorphological information (i.e., the extension of the slope fan
deposition) and the official hazard maps of the Landslide Risk Management
Plan of the River Basin Authority (PSAI, 2015) shown in Fig. 10, considering
a “paroxysmal” event. Consistent with the mean values reported by the
scientific literature (Faella and Nigro, 2001; Revellino et al., 2004) for
the same phenomena and in the same region, the maximum runout velocity was
set at 10 m s^{−1}. Figure 11 illustrates the spatial distribution of
reach probability at the hillslope scale. Source areas are also indicated. The
runout characteristics of the event types considered (types “b” and “c”;
see Sect. 2.1) can be significantly different. Nevertheless, the same set of
parameters (reach angle and velocity) satisfies both event conditions
adequately. It may be noted that one un-channelized event (March 2005) was
considered in this study.

In this area, the highway runs mostly on a soil embankment. The road level is generally elevated with respect to the paths of the downslope flows. The propagation impacts the embankment and stops in front of – or laterally continues according to – the topographic information and the model setting. Differently, in some points, the highway runs approximately at the same level of the fans, thereby allowing the propagating flow to run onto the road. In both cases, damage or disruptions may be caused to the infrastructure. In order to overcome this distinction and to cover both scenarios, only flow propagation to the upstream boundary of the infrastructure is considered in the study. An illustrative example is shown in the magnified focus area in Fig. 12. Due to the reasons mentioned above, the road's surface is only partially affected by the flow slides. This study focuses on a 400 m stretch of the infrastructure (from point A to point B in Fig. 12), the runout values to be considered in the risk assessment should be taken along the section A–B (Fig. 12). The results shown in Fig. 13 attest to the marked spatial variability of reach probability along the investigated section of the A3 motorway infrastructure.

Once occurrence probability and reach probability have been estimated as illustrated in Sects. 5 and 6, respectively, it is possible to calculate hazard using Eq. (1). Hazard is temporally variable, because occurrence probability displays temporal variability as a consequence of climate change, as shown in Sect. 5.3. Reach probability is assumed to be temporally invariant, as it is deterministically related to terrain morphology. This entails that the reach probability outputs obtained in Sect. 6.2 are valid only for the current terrain morphology. Should significant variations in terrain morphology occur, for instance, in case of the occurrence of flow-like landslides, reach probability would need to be reassessed, as described in Sect. 6.1.

To complete the flowchart shown in Fig. 4, an example calculation of hazard
is provided for the section A–B. Figure 14 shows the spatially and
temporally variable hazard profile for time intervals 1991–2020 and
2071–2100, for both quantiles *Q*_{50} and *Q*_{90} and for RCP4.5 and RCP
8.5. The occurrence probability values used to multiply the reach probability
values shown in Fig. 13 are taken from Table 4. Thus, the estimated
variations primarily reflect changes in occurrence probability due to
expected climate change. In this regard, an increase is estimated under both
concentration scenarios, Trends in the increase are related to the severity
of scenario (the more severe, the higher the increase) and the investigated
percentile (the less frequent, the higher the increase). In spatial terms,
more pronounced increases in hazard are detectable in the current peak reach
probability, which increases from $\mathrm{4}\times {\mathrm{10}}^{-\mathrm{4}}$ to $\mathrm{5}\times {\mathrm{10}}^{-\mathrm{4}}$.

This paper has illustrated an innovative methodology for the quantitative estimation of rainfall-induced flow-like movement hazard. An example of the application of the proposed method was conducted for a short section of a motorway. The quantitative approach to hazard estimation was pursued through the implementation of models that are capable of simulating both deposition and entrainment, similar to other notable literature contributions (e.g., Deangeli, 2008; Rosatti and Begnudelli, 2013; Frank et al., 2015; Stancanelli et al., 2015; Cuomo et al., 2016; Gregoretti et al., 2018). Despite the limited extension of the study area, the results displayed a marked temporal and spatial variability of hazard. The temporal variability of hazard is a consequence of climate change as parameterized through quantitative projections for concentration scenarios RCP4.5 and RCP8.5. Significant temporal variability was assessed for both concentration scenarios. The considerable spatial variability resulting from the case study stems from the spatial variability of reach probability, as modeled in the runout analysis.

The calculation of occurrence probability, specifically in the triggering probability calculation phase, relies on a Bayesian approach that replicates the one provided by Berti et al. (2012). This study replicates the hypotheses and glossary introduced by these researchers and shares the implications and possible limitations of such an approach. For instance, the modeling hypothesis by Berti et al. (2012) is adopted, in which multiple flow-like landslides are counted as one single event. Hence, the Bayesian method presented in the paper quantifies the probability of occurrence of a landslide scenario (defined as “at least one event in the proximity area”) in a well-defined time period (30 years). This definition of scenario is semantically consistent with the one provided by Corominas et al. (2015) Reach probability, as estimated quantitatively in the study, is consistent with this definition, as it is calculated from the superposition of all possible runout paths from all events potentially occurring from all source areas. Hazard, as calculated using the above hypotheses, is thus a conservative, upper-bound estimate related to a specific rainfall scenario involving specific values of 1-day and 59-day cumulative rainfall. From a semantic standpoint, hazard as defined herein is also consistent with the reference glossary provided by Corominas et al. (2015).

The quantitative estimates of hazard as obtained in this paper are pervaded by significant uncertainty. Among the main sources of uncertainty are the climate change projections, the runout model, and the Bayesian model developed to quantify triggering probability. These uncertainties are epistemic in nature, as they stem from the inherent difficulty in compiling climate change projections, the inevitable degree of approximation and imperfection in runout modeling capabilities, and the limited rainfall and flow-like landslide occurrence data used to develop triggering probability curves. As such, increased modeling capability and improved databases could reduce the magnitude of uncertainty associated with hazard estimation.

The hazard outputs obtained by the method can be used directly in the quantitative estimation of risk. The latter also requires the quantitative estimation of the vulnerability of human-valued assets (i.e., vehicles, persons, etc.) and the exposure (i.e., the number and/or degree of presence) of the assets themselves in the study area in a referenced time period.

Notwithstanding the above uncertainties and limitations, the quantitative estimation and assessment of the spatial and temporal variability of hazard provide an important decision support tool in the disaster risk management cycle, specifically in the planning and prioritization of hazard mitigation and risk mitigation measures. The availability of quantitative methods allows for a more rational decision-making process in which the costs and effectiveness of risk mitigation can be compared and assessed.

Campanian pyroclastic covers are characterized by several specific features (high porosity, significant water retention capacity, and intermediate saturated hydraulic conductivities) playing a relevant role for triggering (e.g., role of antecedent precipitation or the persistency and/or magnitude of a potential triggering event). Moreover, stratigraphic details like the actual grain size distribution, the presence of pumice lenses, or the depth of pyroclastic deposits regulated by the distance from the eruptive centers and wind direction or magnitude during the eruptions also make generalizations within the same Campania region complex. Nevertheless, the framework developed for the pyroclastic covers on the northern side of the Lattari Mountains (where Nocera Inferiore is located) appears easily transferable to other contexts where precipitation observations and details about the timing of flow-like movements are available. Similarly, the climate simulation chain follows the state-of-the-art analysis of impacts potentially induced by climate change. Finally, the estimated increases in hazard were consistent with the results reported in several works investigating the variation in frequency of events in coarse-grained soils (Gariano and Guzzetti, 2016).

EURO-CORDEX input data are freely available on the EURO-CODEX website platform. The data underlying the research are available on request by contacting corresponding author.

MU contributed the reference hazard framework (Sect. 3), the calculation of occurrence and triggering probabilities (Sect. 5), and the calculation of hazard (Sect. 7). GR and FC provided the background about the investigated landslide dynamics and contributed the description and modelling of the study area (Sect. 2); GR and PM performed data stocktaking for the reference rainfall and landslide inventory datasets and carried out the proper analysis of climate projections (Sect. 4). GR wrote the Introduction (Sect. 1). FC contributed the calculation of reach probability (Sect. 6). UKE contributed to the definition of the general hazard framework (Sect. 3) and to the calculation of occurrence and triggering probabilities (Sect. 5). All authors contributed jointly to the definition of the general layout of the paper and the concluding remarks (Sect. 8).

The authors declare that they have no conflict of interest.

This article is part of the special issue “Landslide early warning systems: monitoring systems, rainfall thresholds, warning models, performance evaluation and risk perception”. It is not associated with a conference.

The research leading to these results has received funding from the European
Union Seventh Framework Program (FP7/2007-2013) under grant agreement
no. 606799. The support is gratefully acknowledged.

Edited by: Paolo Tarolli

Reviewed by: three
anonymous referees

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- Abstract
- Introduction
- Description and modeling of the study area
- Hazard: glossary and model
- Source datasets
- Occurrence probability
- Reach probability
- Calculation of hazard
- Concluding remarks
- Data availability
- Author contributions
- Competing interests
- Special issue statement
- Acknowledgements
- References

- Abstract
- Introduction
- Description and modeling of the study area
- Hazard: glossary and model
- Source datasets
- Occurrence probability
- Reach probability
- Calculation of hazard
- Concluding remarks
- Data availability
- Author contributions
- Competing interests
- Special issue statement
- Acknowledgements
- References