Abstract
Floods affected more than 2 billion people worldwide from 1998 to 2017 and their occurrence is expected to increase due to climate warming, population growth and rapid urbanization. Recent approaches for understanding the resilience of transportation networks when facing floods mostly use the framework of percolation but we show here on a realistic highresolution flood simulation that it is inadequate. Indeed, the giant connected component is not relevant and instead, we propose to partition the road network in terms of accessibility of local towns and define new measures that characterize the impact of the flooding event. Our analysis allows to identify cities that will be pivotal during the flooding by providing to a large number of individuals critical services such as hospitalization services, food supply, etc. This approach is particularly relevant for practical risk management and will help decision makers for allocating resources in space and time.
Introduction
Floods are the most frequent and lifethreatening natural hazards related disasters^{1,2,3,4} and are expected to increase in occurences and damages due to a large variety of factors such as climate warming with intensification of precipitation extremes, population growth, and rapid urbanization^{5,6,7,8,9,10,11,12}. As other natural disasters, floods reduce accessibility and serviceability of the road transportation network, which is one of our most valuable infrastructure assests^{13}. These disruptive effects on the road system are intimately related to the vulnerability and resilience of the transportation network and are traditionally analysed with a number of methodologies, such as systems dynamics models, stochastic and optimization processes^{14}, network science^{14,15,16,17}, demand and supply models^{16,17}, and approaches based on traffic data^{15}.
Network science is a multidisciplinary field^{18,19,20,21} which offers robust and elegant tools and measures to investigate the topological features and properties of a network^{22,23}. In network science, a wellestablished framework for assessing the robustness of any kind of disrupted network is percolation theory^{20,24,25}, which was recently applied to road networks, to investigate the disruptive effects of earthquakes^{26,27,28,29} and traffic congestion^{30,31,32,33}, as well as of flooding events^{34,35,36,37,38,39,40,41,42,43,44}. Abdulla et al.^{34} modelled the flood propagation over one of the neighborhoods road network of Houston, US, as a percolation mechanism. In the proposed process, they randomly removed (flooded) the network’s nodes based on their elevation and their vicinity to already flooded nodes (using Baye’s rule). Despite they mentioned to simulate a percolation process, which would traditionally include the computation of the giant connected component, they actually calculated the Latora and Marchiori’s global efficiency^{45} as a measure of network connectivity. Both Abdulla and Birgisson^{35} and Abdulla et al.^{36} investigated the potential failure of the Houston road network undergoing fluvial floods, by employing different removal sequences of nodes in a floodrelated percolation process. For the entire set of nodes they first calculated four centrality measures, i.e. degree, betweenness, closeness and eigenvector centrality, which then served to rank their nodes. Following the nodes ranking from the highest to the lowest rank, the authors performed the nodes’ removal sequence for each centrality measure and measured the network connectivity through the giant component size. Eventually, they found that the greatest damage to the network was caused by the removal sequence associated to the betweenness centrality measure, in agreement with results about the resilience of airtransportation weighted networks (see for example Dall’Asta et al.^{46}). Abdulla et al.^{36} also presented a flood diffusion model and investigated the effects of the initial conditions of the flood diffusion on the road network connectivity. To mimic different initial conditions of the flood, the authors performed the flood diffusion from different sets of nodes, correspondent to those nodes which ranked the highest values of centrality measures, i.e. degree, betweenness, closeness and eigenvector centrality. By measuring the size of the giant component for each fraction of removed (flooded) nodes, they found that the road networks connectivity was particularly vulnerable to the flood propagation which started from nodes with high values of betweenness. However, their framework did not include any hydrological or hydraulic model, nor was validated. Abdulla and Birgisson^{37} examined the impact of random and targeted disruptions on the Houston road network. To represent the perturbative action of floods on the road network they used the same mechanism of targeted disruption as in Abdulla et al.^{34}. Through the calculation of the giant component size, they compared the disruptive effects of targeted and random failure on the road network. For low percentage of nodes removal (i.e. between 15 and 30%), they found that the network was more robust against targeted failure than towards random one, while for a higher percentage of nodes removal (i.e. between 30 and 70%), the network was instead more robust against random failure than targeted disruptions. The also found similar connectivity profiles (giant components size) by varying the road network size. They concluded by emphasizing the suitability of the giant component in assessing the robustness of road networks. Fan et al.^{38} presented a percolationbased diffusion model of flood propagation and recession, similar to the susceptible–exposed–infected–recovered (SEIR) disease transmission model. However, their model was not built up directly over the road network, but over an overlapping “network grid”, composed of squared cells and each of them containing a different number of road segments. Therefore, the flood propagation occurred among grid cells, with a probability of flooding proportional to the number of neighbouring flooded cells and to a constant transmission rate. With a similar idea, they also simulated the recession phase of the flood. Despite the mention to a percolationbased process, the authors did not calculated the giant connected component or the equivalent size of outbreak^{20}, but they characterised the entire process of flood diffusion mainly by calculating the fraction of flooded cells. In addition, all the model parameters, i.e. the transmission rate, the recovery rate, and the exposed rate were estimated through a curve fitting with real data. Farahmand et al.^{39} proposed a probabilistic approach to the failure of road networks (inversely proportional to the distance between roads and channels network, and directly proportional to a channel’s vulnerability function), which was assessed through the calculation of the giant component size of the network. During the process of nodes removal, they found dramatic decreases (leaps) in the connectivity profile represented by the giant component size, suggesting the presence of critical roads. Dong et al.^{28} proposed a probabilistic links removal to mimic earthquakesinduced failures and addressed the corresponding effects on the Portland (USA) road network through a nonconventional percolation process. Instead of using the traditional giant connected component, they introduced ‘robust components’ defined as the union of connected components in a network, containing at least one critical facility (as a hospital), showing a twophase transition. In their perspective, the giant connected component does not fairly represent the functionality of a network undergoing such a disaster, claiming that measures of network’s robustness should consider critical infrastructures. In another work, Dong et al.^{40} employed the same idea of robust component for assessing the robustness of a road network affected by a flood, resulting in an almost gradual transition. They simulated the fluvial flood in the entire county by assigning a probability of failure to each link, which was proportional to the distance between the link and the floodway (but not considering any flood depth). For each value of link removal probability, they calculated the robust component and observed a complete shutter of the robust component at a threshold of \(p_c=0.8\). They also reported a sudden drop of the robust component when \(2\%\) of the roads were inundated (\(p=0.02\)), resulting in a loss of accessibility to hospitals for a \(22\%\) of the network. Even if the papers related to the “robust components” might apparently represent a step towards nonpercolation approaches, these authors are still removing gradually an increasing fraction of nodes from zero to one and monitor a cluster size for each fraction of removed nodes. Instead of monitoring the size of the largest connected cluster as in the traditional percolation, they monitor the size of the disjoint union of all clusters containing at least a hospital and consider it as if it were a single large component. The hospitals serve uniquely in this work as markers for constructing the clusters that will constitute the robust component. Dong et al.^{41} proposed to apply a standard percolation process, i.e. with a random removal of the network nodes, for assessing the robustness of twelve U.S. cities and three states’s road networks, when subject to disasterinduced failures. For all the cities and states networks, they showed a discrepancy between the results generated with a simulationbased approach and an analytical one, i.e. the generating function formalism^{47,48}, due to the spatially embedded nature of the road networks (indeed, by decreasing the node degree assortativity, the discrepancy diminished). Therefore, they claimed about the inadequacy of the generating functions formalism for assessing the robustness of road networks. However, the Dong et al.^{41} study and conclusions were limited to the random failure mechanism of the network, which is far from real disruptive processes observed in some natural disasters, as floods. Inspired by percolation theory, Ganin et al.^{42} analysed the increase of traffic delay in six US cities’s road networks with the increased severity of the road links disruptions, by employing a mechanism of random links removal. A low, medium and high percentage of disrupted road links represented, respectively, accidents (low), power failures or sever flooding events (medium), and snow, ice, or dust storms (high). The authors, therefore, used the traffic delay for assessing the towns resilience, as alternative quantity to the traditional giant component size. Wang et al.^{43} compared three types of disruptions to both USA and China’s road networks: random, floodinduced and localized failures. They presented the floodinduced failure as a new typology of network disruption, with intermediary features between a random and a localized disruption, and resulting in an abrupt firstorder phase transition. Yadav et al.^{44} studied different failure scenarios on the London Rail Networks (LRN) system, both as a suprasingle network and a multilayer interdependent network^{49,50}. The failure mechanisms included a random failure of the overall network, a local random failure, a targeted failure based on centrality measures and one scenario representing a flood event. The floodlike failure consisted in dividing the nodes into three groups based on their proximity to the river Thames and, within each group, randomly removing them from the network.
In most of these previous studies related to the application of percolationbased flood modeling on the road system^{34,35,36,37,38,39,40,41,42,43,44}, the network’s functionality was expressed through the size of the largest connected component \(P_\infty \) and its evolution when roads are removed. A summary of those studies and their key features related to the percolationbased process is provided in Table 1. However, \(P_\infty \) is an aggregated quantity that does not capture the entire network’s information and more importantly, does not reflect the local reality. Therefore, more precise information is necessary, in particular at a local scale, for a realistic evaluation of the disruption’s effects. Here, we present a realistic and extreme flood scenario^{51} based on physically plausible rainfall scenarios and a high spatiotemporal resolution, and show that it cannot be described adequately by a percolation transition and the behavior of the giant component. Indeed, the giant component size \(P_{\infty }\) never reaches zero during the flooding process and the percolation threshold is never reached. This demonstrates the need for alternative useful measures of the impact of flooding events on the road network. Here we propose such measures and partition the network into towns, through a Voronoi tessellation, which allows us to extend the concept of network’s functionality to the entire network and at a local level. This approach led us to define timedependent measures alternative to percolation, both at a local and at a global scale, which provide a realistic assessment of a floodinduced disruptive event on a transportation network. In order to demonstrate the relevance of these new measures, we use them on a realistic flood simulation and also compare the results to a null random model.
Results
Flooding is not a percolation transition
In order to test our approach and our new metrics, we will consider a portion of the Swiss road network built up from the swissTLM3D dataset^{52} and shown in Fig. 1a. This area comprises the major towns of Bern, Thun, Interlaken and Brienz and two Swiss lakes, the Thun Lake and the Brienz Lake. This portion of road network was selected in such a way to include the largest extension of the disrupted zone, represented by the blue flooded roads, and a surrounding area (limited by the green perimeter) where the effects of the disruptions were expected to occur as well. We use a realistic flood model^{51} based on physically plausible rainfall scenarios, with a high spatiotemporal resolution (a spatial resolution of 50 m and temporal resolution of a hour) and we model the impact of the rainfall in a deterministic way, based on physical laws and ground morphology and properties. In addition, this model takes into account both flood protection’s works and the elevation difference between the river’s water surface and the bridge over it. In contrast to other simplified models such as in^{34,35,36,37,38,39,40,41,42,43,44}, the model here takes into account all the relevant field features (additional information in the “Flood failure”). The flooded roads (in blue in Fig. 1a) result from these simulations^{51}, while both the green and red external borders were created from an alphashape perimeter of the flooded roads (with shrinking factor 0.5) by broadening the perimeter outwards over a distance of 5000 m and 1000 m, respectively (see Fig. 1a). We compare our results to a random null model where we remove the roads at random, i.e. by randomly reshuffling the water levels simulated by Zischg et al.^{51} over the entire set of roads. In this way, the null model has the same number of flooded roads per hour as in the reallike floods, allowing the comparison between the (timedependent) randomlike flood and the reallike one. In the following, we will coin the simulation result as a reallike flood and the null model as a random flood.
For these flooding processes, we first monitor the quantity \(P_\infty \) (see Fig. 1b), defined as the fraction of nodes that belongs to the giant connected component. The simulations start at time \(t_0=0\) h where there is no flood, the network is intact and \(P_\infty \) is maximum and equal to 1. During the flooding, an increasing number of roads is covered by water until the maximum flood extension (MFE) is reached at \(t_{MFE}=75\) h. After this peak, the flood withdraws and the flooded roads eventually dry up, becoming accessible again. We monitor this “recovery” phase until \(t=166\;h \approx 1\) week. Note that not all flooded roads were removed from the network, but only those ones covered by more than 0.3 m, which corresponds to the height at which vehicles start to float^{56}. The results presented in Fig. 1b first show that the magnitude of the \(P_\infty \)’s variations is affected by the choice of the border delimiting the flooded area, which points to the problem of defining the area of study. Nevertheless, the \(P_\infty \)’s minimum is reached at the same time \(t_{MFE}\) for all choices of borders and for both flood scenarios. A recovery phase then follows, characterised by a slow growth of \(P_\infty \), which yet does not reach the initial stage of \(p_\infty =1\). The curves corresponding to the random flood grow faster that those ones obtained for the reallike flood, mostly due to the retention effect of lakes which slows down the flood withdrawal. Indeed, the flood duration for the roads adjacent to the lakes is higher than for those ones which are only affected by river flooding. Although we added additional time to the simulations to consider the slow process of lake emptying, the full recovery would need more time. Focusing on the reallike case, we observe jumps of \(P_\infty \) during the flooding process (\(t<t_{MFE}\)), which are due to the presence of natural elements, such as lakes or mountains, that constrain the road network. Flooding of those constrained roads has then a dramatic impact on the giant component size and creates these discontinuities in \(P_\infty \). The existence of these discontinuities depends obviously on the border definition: for the 5000 m case, the behavior of \(P_\infty \) is much smoother as there are multiple paths connecting nodes in this larger network. Again, this rises the question on the choice of the embedding region when studying a percolation related quantity such as \(P_\infty \). Also, we observe that these discontinuities are washed out in the random case, leading to an artificially smooth evolution of the giant component size. We do not see jumps in the recovery phase since those roads whose disruption would cause the jumps in the flood’s growing phase have not been dried up yet (or completely) at the last time step of the simulations. In previous studies where floods were considered in the framework of percolation, as in^{37,39,40,43}, we note that the authors reported a complete (or nearly complete) disintegration of the giant connected component, showing the decrease of \(P_\infty \) (or RC in^{40}) from one to zero. This process was carried out by removing a fraction of nodes from zero to one in^{37,39,40} and from zero to around 0.8 in^{43}. This is in sharp contrast with our observations for both reallike and random floods, where \(P_\infty \) undergoes a reduction of less than \(30\%\) (depending on the choice of borders). This would suggest that percolation might not be the correct framework, and \(P_\infty \) not the most relevant quantity, for understanding the impact of flooding on transportation networks.
In addition, we note that a flood event displays different dynamics. Indeed, during the simulation we can also compute for each hour the number of flooded roads, F(t), which resulting curve is shown in Fig. 2a. The curve displays a peak at the maximum flood extension \(t_{MFE}\) and divides the flood into two phases, the growing phase ranging from \(t=0\) to \(t_{MFE}\) and the recovery phase (or flood’s withdrawal phase) for \(t>t_{MFE}\). Interestingly enough, we note that the fraction of disconnected nodes is smaller than \(7\%\), which is significantly smaller than what is usually assumed in percolation type approaches. The beginning of the growing phase can be well fitted by an exponential function with a time scale of order 14 h. The end of this phase displays a saturation effect and is better fitted by a generalized logistic function (see Supplementary Table 1 for details on the various fits and “Supplementary Text” for details on the generalised logistic function). These results suggests that the evolution of the number of flooded roads could be described—at least in the first phase—by a generalized Verhulst’s equation^{57} of the form
where the intrinsic growth rate is here \(\beta _1\approx 0.145\). The recovery phase is well fitted by an exponential decay with a time scale of order 75 h, consistent with the observed slow decay. It would be interesting to construct a simple model for deriving these equations and results, to better understand the critical parameters governing these time scales. Indeed, the form of these equations might suggest a more complex flood propagation model on road networks than those ones presented in^{36,38}. In addition, the Abdulla et al.^{36} model does not include any hydrological or hydraulic component, nor a validation, while the Fan et al.^{38} model, which is applied to grid cells instead of roads, does not consider the water depth, nor the difference in height among the nodes (in their flooding probability). Another related measure is the number of disconnected nodes in the whole network, \(N_\infty (t)\) (defined in Eq. (6) in the “Methods”), which time evolution is shown in Fig. 2b for both flood scenarios. Despite the amount of flooded roads per hour is the same in both flood scenarios, we observe a faster increase of \(N_\infty (t)\) during the growing phase and a slower decrease during the recovery phase in the reallike flood, than in the random flood. This difference is due to the retention effect of the lakes, which implies a storage of flood water and a consequent time lag in releasing the same water. Therefore, important roads located along the right and left shorelines of both lakes (and connecting the upstream with downstream areas) are inundated earlier in time than the rest of the basin and are drying up much later because the lakes are going back to their normal level very slowly (much more slowly than the river floodplains). These differences highlight once again the danger of using simple random model for describing floods.
Realistic measures of the local impact of flooding
We saw above that describing the flooding process by percolation could actually be misleading and that the results could depend on a variety of factors such as the choice of borders for example. Maybe more importantly, we note that during floods, individuals will tend to reach the closest town centers where they can find (at least the basic) supplies, services or assistance. When the closest town cannot be reached anymore due to flooding, individuals will have to reroute to the next closest town in order to fulfill their needs. The rerouting process from a town to another can be viewed as a varying “attraction basin” of the neighbouring town, as illustrated in Fig. 3. Some towns will see their attraction basin decrease, while others will gain some nodes and attract additional individuals. In order to capture these important effects that occur during disruptive events, we first identify the nodes that correspond to towns and identify their attraction basin as their Voronoi cell (for details, see “Methods”). The Voronoi cell of a town c will be denoted as \(K_c(t)\) and is defined as \(K_c(t) \doteq \{ i \mid \min \limits _{c'} (d_{i c'} (t)) = d_{ic} (t) \}\) (its size is denoted by \(K_c(t)\)). The shortest distance \(d_{ic}(t)\) from a node i to the town c is computed using Dijkstra’s algorithm over the graph of nonflooded roads at time t. We can then define the town’s loss \(L_c(t)=1K_c(t)/K_c(t_0)\) (see “Methods” for details on these metrics). These metrics are shown in Fig. 4a–c for each of the 67 towns composing the network.
The evolution of \(K_c(t)\) over the entire flood period (Fig. 4a) displays both losses of nodes for certain towns and an increase of their attractivity for others. In order to visualize in Fig. 4a which towns undergo a size reduction or increase, we represent them in different colors according to their behavior. We find that about half of the towns (\(54\%\)) are not affected by the flood, about \(31\%\) undergo an overall size reduction, and about \(15\%\) display an overall size increase. Although we do not have any spatial information from Fig. 4a, the distribution of non affected towns indicates that the flood impact on the transportation network is limited within the area defined in Fig. 1 (i.e. within a perimeter of 5000 m), and does not involve the entirety of the network here considered. A second information we can infer from the affected towns is about their mechanism of size variation. Indeed, Fig. 4a shows clearly that this mechanism is a mutual process among towns (at least two), as illustrated by two neighbouring towns, Thun and Thierachern, shown in Fig. 4a,b. Although the maximum size variation of Thun involves about twice as many nodes as for Thierachern, the two \(K_c(t)\) curves are partially mirrored, which means many nodes lost by Thun are acquired by Thierachern. A third interesting point is related to the types of dynamics of \(K_c(t)\). We observe towns exhibiting large size variations, reaching a sharp peak (maximum or minimum), and towns displaying smaller jumps and plateaus (e.g. Bern). Also, the maximum size changes can occur at times \(t \ne t_{MFE}\), even during the phase of flood withdrawal, as for the case of Thun and Thierachern. This is probably an effect of the spatiotemporal variability, implying that local peaks of road closures can occur earlier or later than the overall peak (whole river basin). In the case of Thun and Thierachern, this is an effect of the time lag of the lake Thun which needed to be filled first before being able to trigger inundations along the shorelines.
Figure 4b shows \(L_c(t)\) for all the 67 towns. As seen above, this measure can reach negative values, meaning that a town can gain nodes from neighboring ones, due to the rerouting mechanism. As in the previous plot, we group the \(L_c(t)\) curves into three categories for better readability: towns undergoing losses, incorporating new nodes, or constant. Both prior to the flood onset and after the recovery phase, \(L_c(t)\) is expected to be zero or close to zero, while in the interval between these two extremes, \(L_c(t)\) is expected to take values \(0<L_c(t)<1\) (for a town loss) or \(1<L_c(t)<0\) (for a town gain). Although this behaviour is observed for most of the towns in Fig. 4b, some of them (dotted lines) do not show the same tendency for \(L_c(t)\) to return to zero during the flood’s recovery phase, i.e. \(\lim _{t \rightarrow t_{end}} L_c \ne 0\). Indeed, the lake levels do not return to the initial level during the timeframe of the simulations but need a few days longer and some streets remain interrupted until the end of the simulation period. Also, Fig. 4b confirms the finding of Fig. 4a that the largest size variations of each town (the largest values of \(L_c(t)\), both positive and negative) do not always occur at the maximum flood extension. For example, the largest positive value of \(L_c(t)\), recorded among all the towns, occurs around \(t=60\) h and belongs to the town of Gelterfingen, around halfway between Bern and Thun. The largest negative value, instead, was recorded for the town of Thierachern a few hours after the maximum flood extension. This means that emergency services and assistance should be dynamically allocated over the flood timespan. In this specific example, Gelterfingen would have a priority over Thierachern, or Thun, which both peak later. We also note the order of magnitude of the variations of \(L_c\) which for some cities can reach values as large as \(60\%\). Such a large increase potentially represents a very large logistic burden during the flood, a crucial information that needs to be integrated in risk management.
The quantity \(L_c(t)\) is a quantity which changes over time, and we define the expansion/shrinking rate as \(\zeta _c(t)=L_c(t_{MFE})\) (see “Methods” for detail). This quantity can be used for each town as an overall indicator of the size variation during the flood’s growing phase, and gives an aggregated and more concise information about the impact of the flood on a given city. We show in Fig. 4c the value of this indicator and we thus observe that some cities will indeed experience an important growth which is of utmost importance for preparation planning as they will constitute a set of resilient towns serving a large number of individuals. We also note that there are some small discrepancies between \(L_c(t)\) and \(\zeta _c\) which are due to the peaks (or in general to the largest values) of \(K_c\) which can occur at a different time than \(t_{MFE}\). For example, the two towns which exhibit the largest values of \(L_c(t)\), both positive and negative, i.e. Gelterfingen and Thierachern, do not score the largest values of \(\zeta _c\) (see Fig. 4c).
Rerouting entailed by a road disruption generally results in a longer path than the initial one (see Fig. 3). In other words, for a node i, the distance to its closest town \(c'\) at time t, i.e. after rerouting, is longer than the distance to its closest town at \(t_0\): \(d_{ic'}(t) \ge d_{ic}(t_0)\). A simple way to characterise the detour experienced by an individual living close to a city c is then to compute the quantity \(\eta _i(t) = \frac{d_{ic'}(t)}{d_{ic}(t_0)}1\), in analogy to the ‘detour index’^{59,60}. The larger \(\eta _i(t)\), and the larger the rerouting for connecting the node i to its closest town’s center \(c'\) (which is different from the initially assigned town’s center c). At each time t of the disruptive event, the average rerouting from an initially assigned town center to a new closest one, can be captured by the average detour defined as
where m is the number of nodes. This quantity, Eq. (2), is a measure of the global cost or (in)efficiency of a network undergoing a disruptive event, since the rerouting would represent a time consuming and costly workaround to roads blockage. The global metrics \({\overline{\eta }}(t)\) and the loss averaged over all cities, \({\overline{L}}(t)=1/n\sum _{c=1}^nL_c(t)\), are shown in Fig. 4(d, top) and Fig. 4(d, bottom), respectively. Both these metrics are global indicators of the entire network performance, and, in contrast with \(P_{\infty }\), they encode the local information coming from the entire network. Large values of \({\overline{\eta }}(t)\) and \({\overline{L}}(t)\) correspond to a large rerouting and a large loss of nodes for most towns. Ideally, the most efficient and robust network would therefore display a value \({\overline{\eta }}(t)  {\overline{\eta }}(t_0) = 0\), and \({\overline{L}}(t)  {\overline{L}}(t_0) = 0\), for all t. Despite sudden and abrupt variations of \({\overline{\eta }}(t)\) during the reallike flood, the network shows a significant higher efficiency than in a random flood scenario which causes large and gradual variations of \({\overline{\eta }}(t)\) over the entire flooding event. Surprisingly, the high efficiency of the network in the reallike flood appears simultaneously with a lower robustness (represented by \({\overline{L}}(t)\)) than in the random flood which suggests that a low rerouting can be achieved through a larger redistribution of the town’s Voronoi cells. However, the difference in \({\overline{L}}(t)\) between the two types of floods is not so pronounced as for \({\overline{\eta }}(t)\). A last remarkable difference between the two flood scenarios can be observed in the latest hours of the recovery phase: in the random flood, \({\overline{L}}(t)\) and \({\overline{\eta }}(t)\) tend to zero (even though \({\overline{\eta }}(t)\) does not arrive to zero), while in a reallike flood, they reach a nonzero positive value (and a peak shifted in time). Basically, this is due to the retention effect of lakes that causes flooding on roads later in time, and which lasts for a few additional days up to return of the lakes’ water levels to their initial ones.
Discussion
The discussion on a realistic flood simulation presented here allowed us to show the inadequacy of percolation theory for evaluating the robustness of a transportation network, when subject to a realistic flooding event. The standard percolation process is characterised by a simultaneous and independent potential removal, usually using a probability \(1p\), of the entire set of edges. This means that all the edges undergo the removal process given by a probability \(1p\), and not just a subset. In this framework, the size of the giant component, \(P_{\infty }\) is a decreasing function of the growing fraction of removed nodes (or links) up to a certain threshold that depends on the specific network and where \(P_{\infty }=0\). In a reallike flooding, instead, the process of water propagation through the network can be thought as a localized attack both in time and space, where only a subset of the network’s edges can be affected. Therefore, the network cannot be completely disrupted if it is larger than the flooded area. The realistic simulation of the flooding shows that, in general, we do not observe \(P_{\infty }=0\), even in an extreme event and at the peak of the flooding. Possible uncertainties in a flood propagation would not affect our observation, since a realistic mechanism of edges removal would not lead to \(P_{\infty }=0\), if the considered network is large enough. Therefore, the absence of an observed transition limits severely the relevance of percolation for studying this type of catastrophic event. In addition, we showed that the relevance of the giant component is debatable and we introduced metrics based on the idea that the crucial point for individuals during a disaster is the possibility to reach a town, even if it is not the closest one in the normal regime (see Supplementary Figure 1 for a representative visual comparison between the percolation approach and one of the proposed metrics).
The approach presented here answers questions relevant to flood risk management such as the spatiotemporal aspects of the flood’s impacts and where and when resources should be allocated during a flooding event. Our study displays the whole dynamics of the flooding and the sequence of important events, the location and time of the first relevant impact, how the road closures spread, which towns become less accessible, etc. In addition, our metrics about the dynamics of rerouting and rising/shrinking towns contains the relevant information for risk management decision makers, in order to allocate resources in space and time (e.g. hospitalization services, food supply, etc.). Already at the earliest moments of the flood, it could be beneficial to transfer resources to towns with a low potential of inundation and a large expansion/shrinking ratio \(\zeta _c\).
Our study showed that the standard percolation approach might have limits of applicability to realworld systems, such as in this case of floodinduced disruption of a single road network. Future studies might investigate whether such limits could occur in other realworld scenarios and potentially provide a more general theory of percolation or a more formal description of its limits of applicability. For example, still in transportation networks, what happens if we apply the percolation framework to disrupted multilayer networks^{49,50} which include road networks? Also, how can we address the issue related to the border size selection? Indeed, the size of the border determines the number of opportunities for deviating routes: a tiny border would eliminate many alternative routes, whereas a large border would enable a large number of possible alternatives. Therefore, future studies could investigated how far or how close the system can be delimited without losing potential routing alternatives. Also, the influence of the network topography on the flood’s impact could be further investigated in the future. Indeed, in our case, we studied the flood impacts on a road network situated in mountainous and hilly regions, while other authors considered quite flat areas, as Abdulla et al.^{34,35,36,37} with the Houston road network. Another direction for future works is related to a simple model for deriving Eq. (1) and understanding its parameters. Such a simple mechanistic model might include basic principles of hydrology and hydrodynamics and, at least, should account for the difference in height among each pair of nodes, in order to provide the water flows directions. This simple model might also fulfil the criteria of universality, i.e. being applicable to a vast variety of scenarios and road networks. Indeed, so far, the Abdulla et al.^{36} and Fan et al.^{38} models of flood propagation (in a road network) seem to be casedependent, and their parameters have to be estimated for any network and scenario. Another limitation that could be addressed in future studies is related to the use of realistic timevarying travel times. Indeed, travel times and the distribution of traffic congestion change during a flood and the corresponding network weights (represented by travel times) should be updated at each time step, in order to get more reliable results.
Methods
Definition of town center on a transportation network
The definitions of the new proposed measurements (alternative to percolation) are built up around the concept of town center (or city center), which could be intuitively thought as the core area of a town, for social, business, and cultural activities. Despite the common idea of an extended area, the town center was here redefined as a node of a road network, as representative spot for the town center. For each Swiss municipality, two entities were employed for selecting the proxy node of a town center, i.e. the road network and polygons called (town or city) central zones by the Swiss Federal Office^{61}. Since several Swiss towns included a multitude of those polygons, which were all named as central zones, the largest polygon was selected as town center, often corresponding to the historical town center, while the other smaller polygons were neglected. The largest polygon was chosen by assuming it could include the largest quantity of services, useful for a population. Then, the roads overlapping and intersecting the largest polygon were selected, and the centroid of their endpoints was employed to infer the proxy node. The node representing the town center, was defined as the closest node to the roads endpoints’ centroid, calculated from the roads which overlapped the largest polygon. Obviously, other definitions of town center’s node are possible and can be used. For example, the small central zones and their overlapping roads could be also included in calculating the roads endpoints’ centroid, but with the risk of obtaining a centroid far from the largest polygon.
Definition of town and temporal evolution of a flood on a transportation network
The town centers’ nodes previously described in “Definition of town center on a transportation network” represent an essential ingredient for the new metrics definitions. All those metrics are indeed based on the shortest distances \(d_{ic}\) and on the quickest paths \(\tau _{ic}\) among all the pairs of inodes of the road network and cnodes of the town centers. At each time, we thus have matrices \(d_{ic}\) and \(\tau _{ic}\) where \(i = 1,\ldots ,m\), \(c = 1,\ldots ,n\). The quantities m and n represent the total numbers of road network’s nodes and town center’s nodes, respectively. The shortest distances and the quickest travel times were calculated with the Dijkstra algorithm^{62}, by employing singleroad lengths \(d_{road}\) [m] and singleroad travel times \(\tau _{road}\) [s] as network weights (see Fig. 3a). The singleroad lengths were collected from the Swisstopo database^{52}, while the singleroad travel times were approximated by the following formula:
where, \(f=0.8\) is the reduction speed factor which considers the relationships between speed limits and traffic flows^{63}, \(v_{lim}\) is the speed limit (km/h) from Supplementary Table 2, and the number 3.6 was used to convert \(v_{lim}\) from (km/h) into (m/s). Once the elements \(d_{ic}\) and \(\tau _{ic}\) are computed, the minimum value in each row of the corresponding matrices D and T is selected, i.e. the town center’s node with minimum distance to the ithnode. This corresponds to assign an ithnode to the closest town center’s node, at \(t_0\). As a consequence, at time \(t_0\), all nodes in the network are associated to their closest town centers’ nodes (Fig. 3(b, top)), creating n sets of nodes \(K_c(t_0) = \{ i \mid \min \limits _{c'} (d_{i c'} (t_0)) = d_{ic} (t_0) \}\). These sets, \(K_1,K_2,\ldots ,K_n\), correspond to Voronoi cells on the network and could be written also for travel times \(\tau _{i c}\). We defined the generic cth town as:
such that \(\bigcup _{c=1}^{n} K_{c} = m\). During the flood, the elements of D and T could change due to the disruptions of the road network and we recompute them at each time step \(t_0,t_1, t_2,\ldots \), where \(t_0\) is the time just before the flood start, with no disruptions (Fig. 3(b, top)), and \(t_1\) is the first time with disruptions (Fig. 3(b, middle)). During the flood, some roads are disconnected and some nodes have to be rerouted, resulting in a reorganization of the Voronoi cells of each town. We indicate the size of a town c which can be variable by
New metrics
Detour index
Rerouting entailed by a road disruption generally results in a longer path than the initial one, i.e. \(d_{ic'}(t) \ge d_{ic}(t_0)\), where \(c' \ne c\) is the closest town’s center at time t, to which the inode would be reassigned. Then, one of the simplest ways to measure the deviation of a path’s distance at time t from its original value at \(t_0\), would be straightforwardly the ratio between the two distances, or the detour, \(\eta _i(t) = \frac{d_{ic'}(t)}{d_{ic}(t_0)}1\), in analogy to the “detour index”^{59,60}. Since \(d_{ic'}(t) \ge d_{ic}(t_0)\), we would measure \(\eta _i(t) \ge 0\) \(\forall i\), with \(\eta _i(t) = 0\) indicating the absence of rerouting to the closest neighbouring town. Therefore, the larger the \(\eta _i(t)\), the larger the rerouting for connecting the inode to the closest town’s center \(c'\) (which is different from the initially assigned town’s center c). At each time t of the disruptive event, the average rerouting from an initially assigned town center to a new closest one, can be captured by the average detour, defined as in Eq. (2). We would consider Eq. (2) as a measure of global (in)efficiency of a network undergoing a disruptive event, since the rerouting would represent a time consuming and costly—i.e. inefficient—workaround to roads blockage. However, \({\overline{\eta }}(t)\) would differ from the wellestablished Latora and Marchiori’s^{45} or from the Vragović’s^{64} global network efficiencies, which are basically averages of \(\frac{1}{d_{ij}}\) and \(\frac{d_{ij}^{Euclid.}}{d_{ij}}\), respectively, over all pairs of nodes. Indeed, the average in Eq. (2) would be only over those pairs of nodes which include the towns’ center nodes, and not over all pairs of nodes.
Disconnected nodes
The distances and their variations over time, as well as the relative travel times, can also be employed to quantify the total number of disconnected nodes in the entire network:
Town loss
Our understanding of the flood’s effects can be further enriched by metrics related to the size’s variations of each town, \(K_c(t)\). The size reduction of a town during a flood is intuitively expected and can be expressed, analogously to \(\eta _i(t)\) for the distances, through a ratio between the size of the damaged (and diminished) town at time t, and the original size at time \(t_0\):
For example, we can have a reduction of the town size from an initial \(K_c=2500\) nodes to \(K_c(t)=2000\) nodes at time t, or rather a size loss equal to \(L_c(t)=0.2\), i.e. a \(20\%\) less than the initial size at time \(t_0\). In parallel to \(\eta _i(t)\), we can also define a global measure for \(L_c(t)\), the average town loss, simply by averaging \(L_c(t)\) over all towns:
Expansion/shrinking ratio
While Eq. (7) provides information at each time t during the entire flood event, the size variations of every town can be even characterized by a single representative value, which relates the town size at the time of the maximum flood extension, \(t_{MFE}\), to the town size at \(t_0\). We call it the expansion/shrinking rate:
Although we would expect the maximum network’s disruption at \(t_{MFE}\), where the flood reaches the maximum extension, it might be that some towns could reach their maximum disruption at another time \(t \ne t_{MFE}\). Therefore, \(\max \limits _{t} \left( K_c(t)\right) \) might be different from \(K_c(t_{MFE})\), and Eqs. (7) and (9) could eventually indicate different size variations for the same town.
Flood failure
A realistic and extreme flood scenario^{51} based on physically plausible rainfall scenarios and a high spatiotemporal resolution was used to generate the road network disruptions. The spatiotemporal patterns of rainfall of a 3day probable maximum precipitation event were generated with a Monte Carlo procedure that considers only physically plausible patterns. The hydrological model simulated the outflows from the subcatchments. A 1D hydrodynamic flood model simulated the water fluxes from the tributaries through the main river network and the lakes. The 1D hydrodynamic model provided the boundary conditions for the 2D flood simulation models that had been set up for each floodplain. The 2D hydrodynamic model had a spatial resolution of 50 m and computed the flood depths for each timestep (hourly) and thus provided the necessary information for the impact model. The impact model simulated the water depths at the road edges. The model considers the location of the bridges in the third dimension, i.e., road bridges located above the simulated water surface elevation are considered as not affected by the flood. In addition, the model has been validated with historic events.
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Acknowledgements
S.L. thanks Alexander Krok, Maria Arduca and Riccardo Turin for useful discussions. S.L. thanks the Mobiliar Lab for Natural Risks for funding and supporting this research project.
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S.L., A.Z., M.K. and M.B. designed research; S.L. performed research; S.L., E.S.G., A.Z., M.K. and M.B. analyzed data; S.L. and M.B. wrote the paper.
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Loreti, S., SerGiacomi, E., Zischg, A. et al. Local impacts on road networks and access to critical locations during extreme floods. Sci Rep 12, 1552 (2022). https://doi.org/10.1038/s41598022049273
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DOI: https://doi.org/10.1038/s41598022049273
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