1. Introduction
Inundations are caused by random natural phenomena (river overflows, snow melting and rain, groundwater table rising above the terrain level due to infiltration, marine storms, and volcanic eruptions), accidents (dam or dike damages, wrong or faulty handling of spillways and bottom outlet facilities of dams during floods, and the sudden sliding of the mountainsides into a reservoir), or human activities (excessive or rapid filling/emptying of reservoirs and improper drainage of irrigation systems).
Due to its specific climate, Romania is frequently impacted by inundations, mainly provoked by floods occurring on rivers. They usually occur during spring due to snow melting and heavy rains. However, they may occur also in summertime due to severe storms. Over a period of 30 years at the end of the 20th century, Romania faced three catastrophic inundations, in 1970, 1975, and 1991, and smaller ones in 1983 and 1988, leading to a loss of human life and important socio-economic damages (estimated to be about RON 10 billion/year in the currency of that period) [1]. Therefore, an extensive flood defense system was built, which proved its capacity to prevent, avoid, limit, or mitigate the impact of extreme hydrologic events that occurred after its construction. One of the main Romanian rivers with a high flood risk is Buzău [2].
In the context of climate change [3], particularly in regions exposed to intensified extreme weather events and more recurring storms, the values of the design floods for which different types of flood control facilities were built are frequently exceeded. In this regard, researchers recommend considering a so-called climate change factor to modify design floods and adopting a continual review of flood risk management strategies based on updated information [4,5,6]. For the existing flood defense facilities, increased runoff volumes can trigger the risk of their failure, with severe consequences for property and human life. Since the inundated areas can cover various types of land uses, in certain cases, flooding can also release significant volumes of undesired harmful pollutants [4,7,8,9].
The worst consequences, including loss of human lives, are caused by dam failures. Catastrophic examples of dam break accidents include the Malpasset arch dam in France (1959) [10]; the Vajont double-curved, thin-arch dam in Italy (1963) [11]; the Teton earthen dam in United States (1976) [12]; the Belci earthen dam in Romania (1991) [1]; the Gouhou concrete-faced rockfill dam in China (1993) [13]; and the 14 de Julho dam in Brasil (2024), built using roller-compacted concrete [14].
A study conducted by Costa (1985) [15] indicates that about 34% of dam failures are due to overtopping, 30% are due to foundation defects, and 28% are due to internal erosion (piping). Furthermore, the likelihood of overtopping failures will potentially rise given climate change trends that will bring about significant variability in precipitation patterns.
Adamo et al. (2020) indicate that about 77% of all built dams at the global level are embankment dams, of which 13% are rockfill dams and 64% are earth fill dams [16]. Their failure is strongly influenced by the materials and configuration of the structure, acting forces, and different environmental causes [17]. Understanding the failure mechanism and breach processes of this earthen dam category is of significant relevance to setting up realistic scenarios for developing numerical models.
Hydraulic models that simulate the catastrophic consequences of dam break accidents are indispensable tools to assess the time and space evolution of the inundation caused by the flood wave released through the breach, useful outputs for further development of risk management, and mitigation measures for such disastrous events [18,19]. Various numerical modeling packages are used for this type of simulation, such as TUFLOW FV, Mike 21, Telemac 2D, Delft3D Flow, SOBEK 2DFLOW, InfoWorks 2DHEC-RAS 5 and 6, LISFLOOD-FP 8.0, and DIVAST-TVD.
Most of them use 2D approximation to integrate shallow water equations (SWEs) through either finite difference or finite volume numerical methods. These equations include a mass conservation equation and two depth-averaged momentum equations to describe water flowing from one computation cell to another and compute the local values of depth and the averaged velocity components along the two horizontal directions [20].
Numerical models developed to study the problems associated with dam break accidents have recently demonstrated notable advances in the field. Based on diverse complex computational techniques, such models are used to mimic the dynamics of dam failures, to analyze the progression of the flood wave released following the breach of the dam, to evaluate flood hazards and risks, and to assess sediment transport. These developments contributed to deepening the understanding of the hydrodynamics of such phenomena that occur in various circumstances. Maranzoni and Tomirotti [21] presented studies using 3D models to simulate flood wave rooting over irregular topography. The benefits and limitations of the three-dimensional models compared to the two-dimensional depth-averaged approaches are emphasized using case studies for their validation [21]. Aureli et al. [22] give a comprehensive review of dam failure accidents benefiting from existing data sets, stressing the use of numerical models validated against real-field data. Furthermore, the article also presents studies exploring dam break flood routing using physical models designed to replicate actual topographies. Issakhov et al. [23] developed a 3D model to evaluate dam break flows over fixed and movable beds. To simulate the movement of the free surface of water and mud, the authors combined Newtonian and non-Newtonian fluid models, whereas the solid macroscopic particles’ movement was performed using the discrete phase and macroscopic particle models. These features facilitate the enhancement of existing models to approach real dam break problems. Federico and Cesali, C. [24] studied the impacts of the hypothetical failure of the Sciaguana embankment in Sicily on downstream flood routing, considering piping and overtopping breaching mechanisms and using the 2D unsteady flow simulation in HEC RAS. The paper highlights the importance that inundation maps have for dealing with risks and mitigating the consequences of a dam failure. As well, Mattas et al. [25] assessed the flood hazard of the potential Papadia dam break in Greece using the HEC-RAS 2D capability. The computations were run in two failure scenarios, namely, overtopping and piping, and were carried out by varying the mesh size and breach parameters to evaluate their influence on the results of the model [25].
When it was commissioned in 1994, the Siriu Dam on the Buzău River in Romania was the second largest embankment dam in Romania and the fifth of this kind in Europe. The Siriu embankment dam has rockfill materials and a clay core and is ranked in first class of importance and category B of risk, according to the Romanian legislation in the field [26,27]. Given its rank, design particularities, and scale, as well as location, the present study aims to provide a valuable analysis of the consequences of such undesirable accidents.
The research involves numerical simulations using a 2D hydraulic model in HEC-RAS. An analysis of flood wave routing, considering multiple cases of hypothetical dam failure of the Siriu Dam, is made. Chosen scenarios consider extreme precipitation events and failure modes (overtopping and piping). For each case, the study provides as results the following hazard parameters, in locations of interest, necessary to assess the impact on downstream life and property: depth, velocity, and flooded area.
Most numerical studies for clay-core dam breach cases either deal with the mechanics of the failure [28] or compute the depth and velocity maps downstream the dam to quantify the flood hazard [29]. Unlike those, the present study adds as an important contribution the analyses of the flood routing and the dam break wave characteristics (the travel time, travel velocity, flooded width, maximum velocities and depths, and depth × velocity) as functions of the scenario parameters and specific site features, such as the terrain topography, river channel width, built dikes, and hydropower facilities. Another new aspect is that simulation scenarios take into consideration a time breach progression curve based on the failure mechanism for this clay core type of embankment dam. To quantify the hazard useful in the development of risk maps and flood management plans, a new depth × velocity product is proposed to be used in Romania, instead of simply either the depth or velocity, as currently used. And lastly, a flood hazard analysis for this type of accident has not been published so far for this important dam.
The obtained results of the hazard parameters are prerequisites for developing flood risk maps and appropriate measures to mitigate the impact of such a catastrophic event [30].
2. Materials and Methods
2.1. Study Area and Data
The Buzău River is one of the main rivers in Romania, with a length of 308 km and a catchment area of 5 264 km2 (Figure 1). Geographically, Buzău watershed lies between 11° 48′ N–11°57′ N latitude and 37° 28′ E–37° 40′ E longitude. Due to its torrential regime along the upper stretch, the river has faced significant floods over the time [31]. While the multi-annual average flow rate of Buzău River in the dam cross-section is = 9.6 m3/s, the peak flow rates of the synthetic floods with the exceedance probabilities of 1%, 0.1%, and 0.01% are of 1100 m3/s, 1765 m3/s, and 2420 m3/s, respectively [32,33] (flood characteristics are shown in Table 1 and Figure 2). To defend the vulnerable inhabited areas along the Buzău Valley from flooding, many flood protection works were constructed in recent decades, such as dikes and another reservoir (at Cândești, about 70 km downstream from the Siriu Dam). The study river reach has a length of 100 km downstream of the dam to Buzău City, which has a population of about 100,000 citizens and an area of 81 km2.
The Siriu Dam (Figure 3) was built across the upstream Buzău River during a period of 20 years (between 1974 and 1994). It is located 10 km upstream of Nehoiu City, at 19 km from the most active epicenter of Romania, Vrancea, and about 200 km from the second most active epicenter of Făgăraș-Câmpulung. Vrancea is the source of the two main catastrophic earthquakes that took place in Romania during the last century: in November 1940 and March 1977, with magnitudes of 7.4 and 7.2 degrees on Richter scale [34]. The dam has a spillway equipped with two 14 × 12 m Tainter gates and a bottom outlet equipped with two 4 × 6 m gates.
The characteristic data of the dam (cross-section in Figure 4) are shown in Table 2. The materials used for the central inclined core of the dam combine local clay with ballast. The dry weight ratios of clay and ballast varied between 20 and 30% to obtain a material with a granular skeleton filled with fine material and having a relative humidity around 812%. This corresponds to the range of relative humidity for optimal compaction [35].
The downstream Nehoiaș 1 hydropower plant has an installed power of 42 MW for a maximum discharge of 32 m3/s. The dam’s canal-type spillways, bottom outlets, and water intake are designed to evacuate the reservoir incoming flows during floods [33].
The reservoir serves multiple uses: flood control, water supply, irrigation, electricity production, and tourism. Its main characteristics are presented in Table 3 and Figure 5. The designed normal operating pool—NOP—level of 579 m above sea level (a.s.l.) has been lowered to a restricted level of 565 m.a.s.l. due to previous safety issues of the dam, and a safety surveillance program has been undertaken.
The methodological framework of the study refers to the development of the hydraulic model, the selection of the dam failure scenarios, the description of the used equations, and the quantification of flood hazard.
2.2. Development of the 2D Hydraulic Model
The geometry of the 2D hydraulic model (Figure 6) was developed in Ras-Mapper, the GIS interface of HEC-RAS software, version 6.6 [36,37], using the national Stereo-70 projection.
The topographic data consist of a 5 × 5 m digital terrain model (DTM) downloaded from Romanian National Agency for Cadaster and Land Registration of Romania [38] for the Buzău drainage basin. The DTM was built from two different data sources as follows: LiDAR data were used for the river valley (channel and floodplain) and for the lower third of the bottom slopes, whereas for the rest of the area, up to the drainage divide, the contour lines from the highest resolution available topographic maps were vectorized. Processed terrain from DTM was modified to include the dikes protecting Buzău City.
The contour of the 2D computation area was delineated downstream of the dam, around Buzău River, to cover the potential flooded surface over at least 100 km distance from the Siriu Dam to the South-East of Buzău City. A polygon-based computational mesh with a finer average cell size of 25 × 25 m in the river channel and a coarser one, of 50 × 50 m in the floodplain, was built, leading to about 500,000 cells (Figure 6). River channel and thalweg line were defined using ortophotomaps of the study area. The roughness coefficient was taken from the 100 m CORINE Land Cover (CLC) map layer of 2018 (from Copernicus database, EU [39]). The 13 thematic classes encountered in the study area with associated values of the Manning’s coefficient, n, in s/m1/3, are shown in Figure 7.
The Siriu reservoir perimeter was outlined and considered as a storage area with the associated storage–elevation curve in Figure 5, whereas the dam with the spillways was inserted as a connection between the water reservoir storage and the 2D computational area.
As upstream boundary condition at the reservoir tail, the flood inflow hydrograph was considered. At the downstream boundary of the 2D computation area, a normal flow condition with the water surface slope equal to the average terrain one was chosen. Given that no bathymetric data were available, no initial water was considered in the downstream river channel and floodplain prior to the dam break. This hypothesis can be justified by considering the dam break discharges are huge compared to the usual river flows.
The computation time step, Δt, was adjusted (on the order of seconds) for reasons of numerical stability based on the Courant–Friedrichs–Lewy (CFL) condition so that its characteristic Courant number
(1)
was maintained between 0.45 and 1.5. and Δ are the mesh/grid cell sizes along the two directions.2.3. Dam Failure Scenarios
A statistical assessment conducted before 1974 and including 534 dam failures that occurred in 43 countries revealed that earth-rock dam failures rank first [13]. Earth dam failure types can be classified into three main categories [40,41]: hydraulic, seepage, and structural.
Hydraulic failures account for over 40% of the earth dam accidents and are triggered by uncontrolled water flows. These may be caused by overtopping, erosion of the upstream face, cracks induced by frost and defrost cycles, erosion of the downstream face due to gully formation produced by heavy rains, and erosion of the downstream toe initiated by cross currents coming from the spillway or by tailwater.
About 33% of the earth dam failures are caused by seepage. Uncontrolled or intensive seepage through the dam body or through its foundation can generate piping or sloughing failure mode. Piping is triggered by the erosion provoked by the formation of a concentrated flow at a high gradient, flow that creates hollows through the foundation or the body of the dam, while sloughing is due to the erosion of the downstream toe of the dam when this becomes saturated. Therefore, a miniature slide with a nearly steep surface is generated that becomes saturated by the seepage and collapses again, leading to an unstable and weakened downstream face of the dam. This face becomes unable to withstand the horizontal water pressure and consequently causes the dam to collapse.
Approximately 25% of dam accidents are associated with structural failures, such as sliding of the foundation and of the embankment sides.
A database involving 593 earth dam failure cases around the world without China was set up by Zang et al. [42]. To perform a statistical analysis of their failure modes, the earth dams were divided into four main categories: homogeneous, zoned, with core walls, and concrete faced. For a total of 61 earth dams covering the four embankment types, of which 12 fall in the earth dams with core walls category, data show that 66.7% of the failure modes occured through overtopping, 16.7% through piping through the foundation or the dam body, and the remaining 16,6% through other failure modes.
Thus, for an earth dam in clay core category, the overtopping failure mode seems to be of greater importance. This can be explained by the major function of the core wall in preventing piping through the foundation or the body of the dam [43]. It has been reported that erosion begins on the downstream slope of the embankment when overtopping occurs at dams built with a concrete, steel, or clay wall core (Figure 8). The deterioration initiates in the form of surface erosion or headcut migration and proceeds until it arrives at the core, impacting its stability, and finally its potential failure through sliding, bending and/or overturning [17].
Even though clay core embankment failures through piping are statistically less common than those induced by overtopping [43], the simulations for the present study were performed under both failure modes: (i) overtopping (O) and (ii) piping (P) [44]. In both cases, the assumptions are that the spillway and bottom outlet gates are blocked due to a blackout or a mechanical failure. Also, the following hypotheses are considered:
For the overtopping failure mode, two extreme inflow scenarios are considered: S1 as the 10,000-year flood and S2 as the 1000-year flood. The reservoir fills up from NOP to the dam crest, which is subsequently overtopped. The breach starts when the water surface elevation exceeds the dam crest by 0.3 m. The water flowing through the trapezoidal breach washes out the downstream rockfill face (Figure 8b), and the dam core cracks along a horizontal plane. Next, it slides horizontally, as shown in Figure 8a,b. A time–breach progression curve (defined as a fraction of total breach progression as a function of the total time) is proposed and shown in Figure 8c. It was customized similarly to the one given by [43]. The breach shape is trapezoidal in Figure 8d, and therefore, the outflow is computed with the trapezoidal broad crested weir equation.
For the piping failure mode, an erosive action of water is considered that had already initiated through the embankment when an earthquake or an act of sabotage occurs in the absence of a flood (sunny day scenario). The reservoir is full either to NOP (S3) or EFL (S4) levels. In this case, the triggering event generates, at a specific time, a rectangular closed channel (Figure 8e) in the clay core embankment (piping phase). The initial elevation of the hole was considered at 560 m.a.s.l.) The seepage flow through this initial pipe leads to a ceiling collapse [45] and transitions into a trapezoidal broad-crested weir (the overtopping phase). Therefore, the dam break outflow is computed with the orifice equation for the pipe stage and with the weir equation for the overtopping stage. In this failure mode, the same time–progression shape curve was considered as for the overtopping case [45] to analyze the influence of the other parameters on the results. The reservoir inflow is considered to be constant and equal to the multi-annual average flow rate
The breach parameters were estimated based on the dam construction data and Froehlich (1995) recommendations, one of the four sets of empirical relationships implemented in the HEC-RAS software [36,37]. The others belong to MacDonald et al. (1984), Froehlich (2008), and Von Thun & Gillete (1990) [36,37]. The considered final breach elevation, the initial pool level in the reservoir, and the other chosen parameters of the breach (bottom width Wb, side slopes H:V, and breach development time Tb) for the four scenarios in the study are given in Table 4.
2.4. Equations
The 2D Shallow Water Equation (SWE) was integrated in HEC-RAS software through the Eulerian–Lagrangian Method (SWE-ELM) under boundary and initial conditions. These are given by a nonlinear system of two partial differential equations [36] formed by the continuity equation:
(2)
and the full momentum equation, which projected on the and directions:(3)
where the following apply:is the bottom elevation in each computation cell, known from the given topography (considered fixed in time, which means no erosion or deposition occur);
is the computed water depth;
is the computed water surface elevation relative to the datum;
and are the computed depth-averaged velocity components in the and directions, respectively;
is a source/sink flux term;
is the horizontal eddy viscosity coefficient;
and are the horizontal bed shear stresses;
the hydraulic radius.
In terms of numerical method, a combination of finite-difference and finite-volume methods are used by HEC-RAS, on an unstructured polygonal mesh with subgrid bathymetry. This gives a good stability and allows for larger time steps without sacrificing precision and stability.
The horizontal bed shear stresses are given by
(4)
with indicating the drag coefficient, and indicating the magnitude of the velocity vector. The drag coefficient can also be written as a function of the Manning coefficient and hydraulic radius, R, as(5)
The most important terms in the momentum equations in the case of dam break wave propagation are the ones due to gravity (first terms on the right-hand side of Equation (3)), local acceleration and inertia (left-hand side), and bed resistance (last terms on the right-hand side).
Routing the inflow hydrograph through the reservoir is performed with the simplified level pool method. This approach neglects the backwater effects, considering that for any time step, the water surface in the reservoir is horizontal. The continuity equation is used to compute the water storage (volume) (t) in the reservoir [46], in terms of inflow I(t) and outflow O(t), for any computational time.
(6)
where the outflow (t) at any moment is the discharge over the dam break considered as a trapezoidal weir, , given by Equation (2). The water elevation in the reservoir at the next time step is given by its volume–elevation curve (Figure 4) in terms of the storage.2.5. Hazard Quantification
Flood hazard may be quantified in terms of depth, velocity, inundation area, or a combination of depth and velocity [47]. Different thresholds of velocity, depth, or flooded area may be used for a hazard classification [48]. So far, a multiple threshold separate categorization of depth and velocity is used in Romania to display the flood hazard maps [49] (Table 5). However, the depth–velocity product (sometimes called inundation intensity) may influence the flood risk more than each parameter itself, since both factors are dangerous for people and their assets [50,51,52]. Another combination of depth and Froude number is employed by Aureli et al. (2008) [53] to quantify the flood hazard.
Therefore, a new 4 stage-classification for quantifying hazard is proposed in Table 6 based on the depth and velocity product and safety for people, vehicles, and buildings.
3. Results
Knowledge of all the flood characteristic parameters, such as local discharge, depth, velocity, travel time, flooded area, wave travel velocity, residence time, etc., are critical for the development of flood emergency plans, better preparedness, and mitigation measures that can reduce losses associated with such a disaster.
The results of the simulations showed the dam broke after 13 h for scenario S1 and 14:20 h for scenario S2, since the beginning of the incoming flood. It must be noted that for both scenarios, the peak discharge of the inflow hydrographs occurs at 16:00 h from the beginning of the formation of the breach. This means the breach occurs only 3 h before the reservoir inflow reaches its peak for scenario S1 and 1:40 h for scenario S2, respectively. For scenarios S3 and S4, the breach starts 2 h from the beginning of the simulations.
Computed parameters are investigated in eight cross-section profiles, delineated in Figure 6, close to the inhabited locations shown in Table 7.
The computed dam breach hydrograph and how it routes downstream the river valley is one of the most important results of the simulation (Figure 9).
Upstream of Buzău City, corresponding to XS profile 7, the released flood wave reaches over 5 000 m3/s in all scenarios, indicating the exceedance of the design flow for the dikes (of 2440 m3/s, with a 0.5% exceedance probability) and, therefore, the flooding of the northern part of the city. Also, in XS 8 corresponding to downstream Buzău City, the maximum discharge is still over 5 000 m3/s in scenarios S1, S2, and S3. Compared to scenario S4, in these three cases, there are important additional water volumes in the reservoir that are released downstream at the breach start time.
The stage hydrographs upstream (US) of the dam show how the reservoir is filled and emptied over time, whereas the stage hydrographs downstream (DS) of the dam show the time evolution of water elevation in the section immediately DS of the dam (Figure 10). The dam breaks 1:20 h sooner for scenario S1 compared to S2, even though the breach initiates at the same water elevation over the deck. This time lag can be attributed to the increased volume of water entering the reservoir for S1. Also, an increased water surface elevation downstream the dam for S1 compared to S2 can be observed.
The travel time of the dam wave front is depicted in Figure 11. These curves are very useful for developing the emergency action plans in the region. While the flood wave leaves the mountain area about 2 h after the dam break, it reaches the plain area in about 5 h and Buzău City within 6 to 7 h for all four scenarios. The travel time depends more on the incoming flow than on the initial reservoir elevation. In Figure 11a, one may see that a difference in the incoming flow between 2440 and 1760 m3/s for scenarios S1 and S2 leads to a difference of 0.5–1 h in terms of the front wave travel time in the specified locations. The lag time increases after the stream leaves the Subcarpathian region, and the floodplain enlarges. This is due to the increased inertia component of the acceleration (terms B in momentum Equation (2)). Figure 11b (for piping scenarios S3 and S4) shows that 9 m more of initial water surface elevation in the reservoir leads to the flood wave arriving 1h sooner 80 km downstream of the dam. In Buzău City, the difference is also 1 h.
Figure 12 shows that the front wave travel velocity increases along the Carpathians region, reaching maximum values (between 12 and 14 m/s) in the Subcarpathians, followed by a slight decrease at the entrance in the plain zone. The trends depicted by the wave travel velocity are similar for both scenarios S1 and S2, with higher velocities of about 2 km/h for scenario S1 than for scenario S2 (Figure 12a). This is obviously due to the additional water volume released from the dam in the case of S1.
Likewise, for the piping scenarios S3 and S4, the wave travel velocities follow the same variation pattern downstream the dam as in the overtopping scenarios (Figure 12b). However, they are marked by lower values than in S1 and S2, and the difference between the wave travel velocities decreases, on average, at about 1 km/h. Since the flow velocity depends on the product of hydraulic radius and energy slope and their individual trend along the river is to increase and decrease, respectively, this might explain the plateau of the velocity along the middle reach.
By displaying the maximum velocity over the entire simulation period in each grid cell for different cross sections along the river (Figure 13), one may see that these velocity values drop from 15 to below 5 m/s, where the sinuous stream leaves the mountain region, and it begins to develop its braiding/wandering planform pattern [47]. Also, the shape of the maximum velocity profile plots in XS1 and XS4 (details in Figure 13) show the stream flows only through a main channel along its Carpathian course. Then, 65 km from Siriu dam, where the valley enlarges into a floodplain, there is another small dam with a narrow reservoir (Cândești), upstream/downstream of which the water flows in parallel through both the hydropower plant feeder/tailrace canals and the natural river channel, as the velocity profile shapes from XS6 and XS7 show (Figure 13).
The plots of the maximum depth and velocity (over the simulation time) along the thalweg line and in each of the eight study cross-sections (Figure 14a,b) show a similar decreasing trend for all four scenarios.
Maximum depths are very high along the first 20 km from the dam (in the mountain region, where the Buzău River Valley is narrow), in the range of 15–25 m. They drop to values below 10 m at distances over 20 km.
Maximum velocities drop similarly from huge values of 10–12 m/s to smaller values below 6 m/s as the river enters the plain region. While the decrease in depths with the distance from the dam is due to flood wave attenuation, the velocity reduction could be attributed to both attenuation and thalweg slope, as seen in the longitudinal profile of the river in Figure 14c. This slope drops from 0.9% over the mountain reach to 0.3% over the Subcarpathians and to 0.17% over the plain reach, with an average value of 0.4% over the entire 100 km reach.
At the same time, the inundation boundary width in the studied cross-sections increases with the distance from the dam (Figure 14c) from hundreds to thousands of meters, showing its largest value at the entrance in Buzău City (XS7, at 80 km from the dam). In this location, the current splits (due to the topography) and floods the Western and Southern part of the city at high discharge values, as in the case of scenarios S1 and S3.
An example of the inundation boundary for scenario S4 is presented in Figure 15 with details of an inhabited area downstream Siriu dam (bottom-left corner) and of a flooded dike near Buzău City (top-right corner). Depths and velocities in the city from the corresponding hazard maps are under 1 m, and velocities are under 2 m/s.
The flooded areas of Buzău City were computed as a percentage of the total surface by intersecting the computed inundation boundaries in all four scenarios with the contour of the city in QGIS software version 3.10.9 (Figure 16). One may see that the first two scenarios lead to similar flooding areas irrespective of the incoming flow, whereas a higher initial water elevation in the reservoir entails much greater damage (38% compared to 15% flooded area). However, this result does not take into consideration the water depth and velocity.
In Figure 17a,b, example details of the depth x velocity map are shown in the North-East of Buzău City for scenarios S3 and S4 9 h after the initiation of the dam break. Values of the product (up to 20 m2/s) are classified according to the proposed quantification method from Table 6. One may see the highest values are in the river channel, and the choice of the scenario is a major factor of influence in terms of the potential flood damage. This hazard quantification method may be used in the future for the development of risk maps and flood emergency plans.
To see the inhabited area in the city affected by flooding, the results were exported to Google Earth (with the option of 3D buildings activated). Details of the computed water level with respect to building heights are shown in the bottom-left corner of Figure 17 for the flooded Orizont district from Buzău City. This Google Earth facility might be very useful for educating citizens about the hazard of such an accidental flood.
4. Discussion
The findings of the study are marked by the specific location of the dam in terms of topography and the particular physical environment. Table 8 summarizes the results of similar approaches to the present paper obtained by researchers who numerically investigated the impact of embankment dam break waves on downstream inhabited regions to provide an insight into the scale and severity of a possible disaster.
For all studies, the peak values of the maximum depths and velocities were found to occur within the few km downstream of the dam, mainly in highland reaches with steep longitudinal slopes.
Chen and Carpat [54] compared their numerical results for the Teton earthen dam break wave characteristics, obtained for non-uniform valleys, with the surveyed ones. The water depth showed a similar decreasing trend to that in Figure 14a), from about 29 m at the dam to 7 m at 100 km downstream of the dam for a peak dam break discharge of nearly 47,000 m3/s.
Also, a peak value of 33,000 m3/s, having the same order of magnitude as the peak discharges in Figure 9, was obtained numerically by [55] for the overtopping failure mode of the 116 m high Atasu rock fill-type dam in Turkey.
Doğan et al. [56] developed a numerical model to study the possible failure of another dam with rockfill and clay core in Turkey, the Gökçe Dam (62 m in height), using different sets of breaching parameters. The peak outflows for the overtopping and piping scenarios were 12,000 and 6000 m3/s, respectively. The results showed maximum velocities of 14.6 m/s and 22 m/s along the first 2 km downstream of the dam in these two scenarios, respectively, comparable to the ones for the Siriu Dam. For a mean longitudinal slope of the river of about 0.78%, the computed travel time of the flood wave along a reach length of 8 km was between 5 and 10 km/h. These values are in the same range as the ones obtained along the mountain area for the present study.
Researchers who published [56,57,58] obtained larger peak flows for overtopping than for piping failure scenarios, like for the Siriu dam break. However, a paper studying the failure of the Sattarkhan dam [59] did not provide any value for the outflow discharges. The only case that provided a piping peak discharge greater than the overtopping one is [60].
The largest peak discharges were obtained by [58] for the Hidkal Dam in India. Further comparisons of other dam break wave parameters are difficult to be made, since studies do not offer the same type of results. Also, the uniqueness of the sites and dam particularities make such a comparison even more challenging.
5. Conclusions
This study examines the consequences of a possible failure accident of the Siriu clay-core embankment dam from Romania. The selection of the case study was based on some important criteria, including its location in a region subject to earthquakes and high flood risk, dam type, and previous dam problems that determine the need to implement a safety surveillance program. Four hypothetical breach scenarios were chosen, two for overtopping and two for piping failure modes. The breach parameter values were calculated using empirical formulas developed previously by other authors.
The main objective of this study was to analyze flood wave routing and hazard characteristics in terms of chosen scenarios and site-specific features. To achieve this objective, a fully dynamic 2D hydraulic model was developed under HEC-RAS.
The computed results include details about the dam flood wave and its progression downstream, the stage hydrographs upstream and downstream of the dam, and the hazard characteristics. The last ones consist of depth, velocity, inundation boundary, and depth × velocity maps. As expected, water depths and the flow velocity decrease along the 100 km study river reach from 20–25 m and 15–20 m/s downstream the dam to about 3 m and 3 m/s, respectively, in Buzău City, while inundated width increases from several hundreds to several thousands of m, over the same distance. The simulated dam break flood wave reaches Buzău City in 7–8.5 h, depending on the scenario involved. The incoming flow and initial water level in the reservoir were proved to be the determining factors for the travel time, front wave velocity, and inundation depth. Details of the flooded area of the City of Buzău were provided as a function of the scenario. A new hazard quantification method for Romania was proposed based on the water depth and velocity product.
The accuracy of the findings is certainly influenced by different factors, such as the resolution and precision of the digital terrain model, the chosen Manning roughness parameters (since such models cannot be calibrated on previous data from similar events), and the selection of breach scenarios.
The results of the current study could contribute to the selection of optimal adaptation measures to be taken to limit the impact of such catastrophic dam break events to mitigate the flood risk, prepare inhabitants, and increase the resilience of the affected communities.
Conceptualization, C.-S.I. and D.-E.G.-N.; methodology, D.-E.G.-N., C.A.B., A.C., I.M. and L.B.; resources, C.A.B. and L.B.; data curation, A.C.; writing—original draft preparation, C.-S.I. and D.-E.G.-N.; writing—review and editing, D.-E.G.-N., C.-S.I., C.A.B., A.C., I.M. and L.B. All authors have read and agreed to the published version of the manuscript.
Topographical data are made publicly available by the National Agency for Cadastre and Land Registration, NACLR (In Romanian). They are available online:
The authors declare no conflicts of interest.
Footnotes
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Figure 1. Buzău drainage basin with river network, gauging stations, Siriu reservoir, and dam.
Figure 2. Synthetic characteristic check and design flood inflow for the Siriu reservoir.
Figure 3. Siriu Dam: (a) view from downstream; (b) view from upstream, left bank.
Figure 4. Siriu Dam cross-section profile (1—inclined concrete-clay core; 2—filters; 3—sealing wells; 4—drainage blanket; 5—ballast; 6—cofferdam; 7—rockfill; 8—riprap broken stone protection; 9—consolidation drills; 10—sealing wells; 11—stability bench).
Figure 6. The geometry of the hydraulic model with the DTM, river network, 2D computation flow area, boundary conditions lines, cross-section profiles for the results, and contour of Buzău City.
Figure 7. CORINE land cover [39] for the study area. (Numbers in the legend correspond to the thematic classes given in table; Manning coefficient unit measure is s/m1/3.)
Figure 8. Dam breach evolution for the case of the Siriu earth dam with concrete–clay core: Overtopping (a) separation of the failure body; (b) dam displacement volumes associated with the failure stages; (c) breach–progression curve, (d) trapezoidal breach shape, (e) piping phase before ceiling collapse and transition into the overtopping phase.
Figure 9. Dam break wave routing along the Buzău River Valley in the 4 considered scenarios. The locations downstream of the dam correspond to cross-section profiles from Figure 6.
Figure 10. Time variation of reservoir water elevation upstream (US) of the dam and stage downstream (DS) of the dam for the four scenarios.
Figure 11. Travel time of the dam break wave front along Buzău River for the four simulation scenarios: (a) overtopping, S1 and S2 and (b) piping, S3 and S4.
Figure 12. Travel velocity of the dam break wave front along Buzău River Valley for scenarios (a) S1 and S2 and (b) S3 and S4.
Figure 13. Maximum velocity in each cell of the grid over the simulation time for the worst-case scenario, S1. In the plots, examples of the maximum velocity profile shape in XS1 and XS4 on the upper river course and in XS6 and XS7 on the lower river course are shown. In the detailed window: the natural river course and the constructed hydropower feeder canal next to each other.
Figure 14. Maximum values of (a) depth, (b) velocity, and (c) inundated width and thalweg elevations along the river in each of the cross-sections and along the thalweg line over the entire simulation time for all 4 scenarios.
Figure 15. Inundation boundary in Scenario S4, with details of an inhabited area downstream of Siriu dam (bottom-left corner) and the flooding of the Buzău City dike with the maximum water surface elevation (top-right corner).
Figure 17. Details of the depth x velocity map from scenarios (a) S3 and (b) S4, 9 h after the beginning of dam break. In the bottom-left corner of (a)—the depth map exported to Google Earth with 3D buildings on (Orizont district in Buzău City).
Characteristics of the Siriu reservoir check and design flood inflows.
Case | Exceedance Probability | Return Period, | Total Duration (h) | ||
---|---|---|---|---|---|
1 | 2420 | 16 | 0.01% | 10,000 | 69 |
2 | 1765 | 16 | 0.1% | 1000 | 69 |
Characteristic features of Siriu Dam.
Current No. | Characteristic Feature | Value (Meas. Unit) |
---|---|---|
1 | Dam height | 121 m |
2 | Length at deck (top) | 570 m. |
3 | Length at the bottom | 824 m. |
4 | Deck (crest) elevation | 588 m.a.s.l. |
5 | Top of the gates’ elevation | 575 m.a.s.l. |
6 | Spillway elevation | 575 m.a.s.l. |
7 | Width at deck | 12 m |
6 | Average upstream slope (H:V) | 1:2.5 |
7 | Downstream slope (H:V) | 1:2.25 |
8 | Initial thalweg elevation at dam | 482 m.a.s.l. |
9 | Design peak discharge 0.1% | 1765 m3/s |
10 | Verification peak discharge 0.01% | 2420 m3/s |
11 | Density of the central core | 2039 kg/m3 |
12 | Volume of embankment material | 8.3 mil. m3 |
Characteristic features of Siriu reservoir.
Current No. | Characteristic Feature | Value (Measure Unit) |
---|---|---|
1 | Normal Operating Pool—NOP Level (or Full Reservoir Level—FRL) | 579 m.a.s.l. |
2 | Exceptional Flood Level—EFL | 587 m.a.s.l. |
3 | Minimum Operating Pool (mOP) Level | 523 m.a.s.l. |
4 | Total volume at NOP level | 111.38 (mil. m3) |
5 | Total volume at EFL level | 146 (mil. m3) |
6 | Restricted level | 565 m.a.s.l. |
Breach characteristics for the scenarios.
Scenario | Overtopping | Piping | ||
---|---|---|---|---|
S1 | S2 | S3 | S4 | |
Peak flood inflow, Q (m3/s) | 2420 | 1765 | 9.6 | 9.6 |
Initial level in reservoir (m.a.s.l.) | 579 | 579 | 587 | 579 |
Initial volume in reservoir (mil. m3) | 111.38 | 111.38 | 146 | 111.38 |
Breach width at base, W (m) | 150 | 150 | 100 | 100 |
Initial breach elevation (m.a.s.l.) | 588.3 | 588.3 | 560 | 560 |
Breach formation time, Tb (h) | 2 | 2 | 2 | 2 |
Breach slope H:V | 0.85 | 0.85 | 0.85 | 0.85 |
Final breach elevation (m.a.s.l.) | 540 | 540 | 540 | 540 |
Dam breach area/total (%) | 24 | 24 | 18 | 18 |
Present classification of hazard in Romania based on depth and velocity thresholds.
Parameter | |||
---|---|---|---|
Hazard Classification | |||
Low (H1) | < 0.45 | < 1.5 | |
Caution (H2) | 0.45 ÷ 0.8 | 1.5 ÷ 1.6 | |
Moderate (H3) | 0.8 ÷ 1 | 1.6 ÷2 | |
Significant (H4) | 1 ÷ 2 | 2 ÷3 | |
Severe (H5) | 2 ÷ 5 | 3 ÷ 5 | |
Extreme (H6) | >5 | >5 |
Proposed classification of hazard based on depth × velocity thresholds.
Parameter | ||
---|---|---|
Hazard Classification | ||
Low (H1) | < 2 | |
Moderate (H2) | 2÷4 | |
Severe (H3) | 4÷6 | |
Extreme (H4) | > 6 |
Cross-section profile names, where results are investigated.
Cross-Section (XS) Profile No. | Location | Distance from Dam(km) |
---|---|---|
1 | DS dam | 0 |
2 | Nehoiu | 10 |
3 | Pătârlagele | 25 |
4 | Cislău | 36 |
5 | Măgura | 50 |
6 | Berca | 65 |
7 | Buzău US | 80 |
8 | Buzău DS | 100 |
Specific characteristics of numerical embankment dam break studies.
Dam, | Type of Dam | Failure Mode | Dam Height | Max. Depth | Max. Vel. | Travel Velocity | Ref. No. | |
---|---|---|---|---|---|---|---|---|
O/P | m | m3/s | m | m/s | Km/h | |||
Siriu, Romania | Clay core | O | 122 | 40 | 22–25 | 12 | 5–14 | - |
Teton | Clay core | P | 93 | 47 | 29 | 54 | ||
Atasu, | Rock fill | O | 116 | 33 | 40 | 10 | - | 55 |
Gökçe, Turkey | Clay core | O | 62 | 12 | 8 | 14.6 | 5.2 | 56 |
Al Wala | Clay core | O | 52 | 16.5 | 24.6 | - | - | 57 |
Hidkal | Earth | O | 53.3 | 78.45 | 35 | - | 5.3 | 58 |
Sattarkhan, | Clay core | O | 59 | - | 3.8 | 4.3 | - | 59 |
Gumara, Ethiopia | Clay core | O | 33 | 19.7 | 15 | 11.5 | - | 60 |
References
1. Șelărescu, M.; Podani, M. Protection Against Floods (In Romanian–Apărarea Împotriva Inundațiilor); Editura Tehnică: Bucharest, Romania, 1993.
2. Popa, M.C.; Peptenatu, D.; Drăghici, C.C.; Diaconu, D.C. Flood hazard mapping using the flood and flash-flood potential index in the Buzău river catchment, Romania. Water; 2019; 11, 2116. [DOI: https://dx.doi.org/10.3390/w11102116]
3. Martel, J.L.; Mailhot, A.; Brissette, F. Global and regional projected changes in 100-yr subdaily, daily, and multiday precipitation extremes estimated from three large ensembles of climate simulations. J. Clim.; 2020; 33, pp. 1089-1103. [DOI: https://dx.doi.org/10.1175/JCLI-D-18-0764.1]
4. Norwegian Meteorological Institute. Extreme Weather Events in Europe: Preparing for Climate Change Adaptation. 2013; Available online: https://real.mtak.hu/8366/1/EASAC_EWWG_Extreme_weather_report.pdf (accessed on 15 June 2024).
5. Drobot, R.; Draghia, A.F.; Dinu, C.; Sîrbu, N.; Chendeș, V.; Mazilu, P. Adaptive Operating Rules for Flood Control of a Multi-Purpose Reservoir. Hydrology; 2024; 11, 147. [DOI: https://dx.doi.org/10.3390/hydrology11090147]
6. Cea, L.; Costabile, P. Flood Risk in Urban Areas: Modelling, Management and Adaptation to Climate Change. A Review. Hydrology; 2022; 9, 50. [DOI: https://dx.doi.org/10.3390/hydrology9030050]
7. Zhang, Y.; Li, Z.; Ge, W.; Wang, J.; Guo, X.; Wang, T.; Zhang, H. Evaluation of the water pollution risk of dam and dike-break floods in the inundated area. Environ. Sci. Pollut. Res. Int.; 2022; 29, pp. 76365-76377. [DOI: https://dx.doi.org/10.1007/s11356-022-20742-9]
8. Gogoașe-Nistoran, D.E.; Popescu, D.M.; Panaitescu, V. Use of hydraulic modeling for river oil spills. 1. Travel time computation for quick response. UPB Sci. Bull. Ser. D; 2008; 70, pp. 263-270. Available online: https://www.scientificbulletin.upb.ro/rev_docs_arhiva/full46116.pdf (accessed on 10 August 2024).
9. Popescu, D.-M.; Nistoran Gogoaşe, D.-E.; Panaitescu, V. Use of Hydraulic Modeling for Oil Spills. 2. Influence of response methods on travel time in a case study, & Panaitescu V. UPB Sci. Bull. Ser. D; 2008; 70, pp. 271-278. Available online: https://www.scientificbulletin.upb.ro/rev_docs_arhiva/full63206.pdf (accessed on 10 August 2024).
10. Duffaut, P. The Traps Behind the Failure of Malpasset Arch Dam, France, in 1959. J. Rock Mech. Geotech. Eng.; 2013; 5, pp. 335-341. [DOI: https://dx.doi.org/10.1016/j.jrmge.2013.07.004]
11. Superchi, L.; Floris, M.; Ghirotti, M.; Genevois, R.; Jaboyedoff, M.; Stead, D. Technical Note: Implementation of a geodatabase of published and unpublished data on the catastrophic Vajont landslide. Nat. Hazards Earth Syst. Sci.; 2010; 10, pp. 865-873. Available online: www.nat-hazards-earth-syst-sci.net/10/865/2010 (accessed on 12 September 2024). [DOI: https://dx.doi.org/10.5194/nhess-10-865-2010]
12. Graham, W. The Teton Dam Failure: An Effective Warning and Evacuation. ASDSO Annual Conferenc. Indian Wells: Association of State Dam Safety Officials. Available online: https://damfailures.org/wp-content/uploads/2015/07/075_The-Teton-Dam-Failure.pdf (accessed on 20 September 2024).
13. You, L.; Chen, L.; Xu, M.; Tong, X. Review of dam-break research of earth-rock dam combining with dam safety management. Procedia Eng.; 2012; 28, pp. 382-388. [DOI: https://dx.doi.org/10.1016/j.proeng.2012.01.737]
14. Partial Dam Failure Reported at 14 de Julho Hydroelectric Project in Brazil. 5 March 2024. Available online: https://www.hydroreview.com/dams-and-civil-structures/dam-safety/partial-dam-failure-reported-at-14-de-julho-hydroelectric-project-in-brazil/ (accessed on 20 May 2024).
15. Costa, J.E. Floods from Dam Failures. Open-File Rep. No. 85-560; USGS: Denver, CO, USA, 1985; Available online: https://pubs.usgs.gov/of/1985/0560/report.pdf (accessed on 3 June 2024).
16. Adamo, N.; Al-Ansari, N.; Sissakian, V.; Laue, J.; Knutsson, S. Dam safety problems related to seepage. J. Earth Sci. Geotech. Eng.; 2020; 10, pp. 191-239.
17. ASCE/EWRI Task Committee on Dam/Levee Breaching. Earthen Embankment Breaching. J. Hydraul. Eng.; 2011; 137, pp. 1549-1564. [DOI: https://dx.doi.org/10.1061/(ASCE)HY.1943-7900.0000498]
18. Aureli, F.; Maranzoni, A.; Petaccia, G. Advances in dam-break modeling for flood hazard mitigation: Theory, numerical models, and applications in hydraulic engineering. Water; 2024; 16, 1093. [DOI: https://dx.doi.org/10.3390/w16081093]
19. Gogoașe Nistoran, D.E.; Ionescu, C.S.; Simionescu Șt, M. Assessing the impact of an arch-dam breach magnitude and reservoir inflow on flood maps. J. Hydroinform.; 2024; 26, pp. 33-50. [DOI: https://dx.doi.org/10.2166/hydro.2023.301]
20. Gogoașe Nistoran, D.E.; Ionescu, C.S.; Simionescu Șt, M. Influence of dam break scenarios on flood wave characteristics. Case study–Paltinu Dam, Romania. IOP Conf. Series. Earth Environ. Sci.; 2023; 1136, 012031. [DOI: https://dx.doi.org/10.1088/1755-1315/1136/1/012031]
21. Maranzoni, A.; Tomirotti, M. Three-Dimensional Numerical Modelling of Real-Field Dam-Break Flows: Review and Recent Advances. Water; 2023; 15, 3130. [DOI: https://dx.doi.org/10.3390/w15173130]
22. Aureli, F.; Maranzoni, A.; Petaccia, G. Review of Historical Dam-Break Events and Laboratory Tests on Real Topography for the Validation of Numerical Models. Water; 2021; 13, 1968. [DOI: https://dx.doi.org/10.3390/w13141968]
23. Issakhov, A.; Abylkassymova, A.; Issakhov, A. Numerical study of the dam-break flood over natural rivers with macroscopic rocks on movable beds. Comput. Geotech.; 2023; 164, 105793. [DOI: https://dx.doi.org/10.1016/j.compgeo.2023.105793]
24. Federico, F.; Cesali, C. Effects of Dam Failure Mechanisms on Downstream Flood Propagation. Dam Breach Modelling and Risk Disposal. ICED 2020. Springer Series in Geomechanics and Geoengineering; Zhang, J.M.; Zhang, L.; Wang, R. Springer: Cham, Switzerland, 2020; [DOI: https://dx.doi.org/10.1007/978-3-030-46351-9_13]
25. Mattas, C.; Karpouzos, D.; Georgiou, P.; Tsapanos, T. Two-Dimensional Modelling for Dam Break Analysis and Flood Hazard Mapping: A Case Study of Papadia Dam, Northern Greece. Water; 2023; 15, 994. [DOI: https://dx.doi.org/10.3390/w15050994]
26. Standard No. 4273-83 Importance Class Ranking, Romanian Standard (In Romanian, Incadrarea in Clase de Importanță). Available online: https://magazin.asro.ro/ro/standard/14319 (accessed on 31 January 2025).
27. Methodology for Establishing the Potential Risk Classification of Dams (In Romanian) (2002)-Metodologia Privind Stabilirea Categoriilor de Importanţă a Barajelor NTLH-021. Available online: https://www.mdlpa.ro/userfiles/reglementari/Domeniul_XXV/25_11_NTLH_021.pdf (accessed on 18 May 2024).
28. Zhong, Q.; Chen, S.; Deng, Z. A simplified physically-based model for core dam overtopping breach. Eng. Fail. Anal.; 2018; 90, pp. 141-155. [DOI: https://dx.doi.org/10.1016/j.engfailanal.2018.03.032]
29. Musolino, G.; Ahmadian, R.; Falconer, R.A. Comparison of flood hazard assessment criteria for pedestrians with a refined mechanics-based method. J. Hydrol. X; 2020; 9, 100067. [DOI: https://dx.doi.org/10.1016/j.hydroa.2020.100067]
30. Tsai, C.W.; Yeh, J.J.; Huang, C.H. Development of probabilistic inundation mapping for dam failure induced floods. Stoch. Environ. Res. Risk Assess.; 2019; 33, pp. 91-110. [DOI: https://dx.doi.org/10.1007/s00477-018-1636-8]
31. Ialomița-Buzău River Basin Administration. Preliminary Flood Risk Assessment (In Romanian: Evaluarea Preliminară a Riscului la Inundaţii). 2022; Available online: https://inundatii.ro/wp-content/uploads/2022/07/PFRA_Report_RO5_Buzau-Ialomita.pdf (accessed on 17 May 2024).
32. Diaconu, D.C. Siriu Reservoir, Buzau River (Romania). Lakes Reserv. Ponds; 2008; 1–2, pp. 141-149. Available online: https://www.limnology.ro/Lakes/2008/20081215.pdf (accessed on 6 June 2024).
33. Buzău-Ialomiţa Water Basin Administration. Flood Risk Management Plan (In Romanian: Planul de Management al Riscului la Inundaţii. 2022; Available online: https://www.mmediu.ro/app/webroot/uploads/files/RO5_FRMP_PMRI_BUZAU_IALOMITA.pdf (accessed on 17 May 2024).
34. Georgescu, E.S.; Pomonis, A. New archival evidence on the 1977 Vrancea, Romania earthquake and its impact on disaster management and seismic risk. Seismic Hazard and Risk Assessment; Vacareanu, R.; Ionescu, C. Springer Natural Hazards; Springer: Cham, Switzerland, 2018; [DOI: https://dx.doi.org/10.1007/978-3-319-74724-8_19]
35. Popovici, A. Dams for Water Storage (In Romanian–Baraje Pentru Acumulari de Apă. Vomumul 2); Editura Tehnică: Bucharest, Romania, 1992; Volume 2.
36. USACE-US Army Corps of Engineers. Hydraulic Engineering Center–River Analysis System, HEC-RAS, Hydraulic Reference Manual. 2022; Available online: https://www.hec.usace.army.mil/confluence/rasdocs/ras1dtechref/6.3/performing-a-dam-break-study-with-hec-ras/estimating-dam-breach-parameters/estimating-breach-parameters (accessed on 20 October 2024).
37. USACE-US Army Corps of Engineers. Hydraulic Engineering Center–River Analysis System, HEC-RAS Software, Version 6.6. 2022; Available online: https://www.hec.usace.army.mil/software/hec-ras/download.aspx (accessed on 20 October 2024).
38. NACLR-National Agency for Cadastre and Land Registration (In Romanian: Agenția Națională de Cadastru și Publicitate Imobiliară-ANCPI). Available online: https://geoportal.ancpi.ro/portal/apps/webappviewer/index.html?id=50289a41aafc4e01aefd131c2105e374 (accessed on 18 June 2024).
39. Corine Land Cover 2018 Vector Dataset 100m, Copernicus, EU. Available online: https://land.copernicus.eu/en/map-viewer?dataset=0407d497d3c44bcd93ce8fd5bf78596a (accessed on 5 November 2024).
40. Athani, S.S.; Solanki, C.H.; Dodagoudar, G.R. Seepage and Stability Analyses of Earth Dam Using Finite Element Method. Aquat. Procedia; 2015; 4, pp. 876-883. [DOI: https://dx.doi.org/10.1016/j.aqpro.2015.02.110]
41. Santos, K.G. Irrigation Engineering and Hydraulic Structures; 19th revised ed. Khanna Publishers: Delhi, India, 2005.
42. Zhang, L.M.; Xu, Y.; Jia, J.S. Analysis of earth dam failures: A database approach. Georisk Assess. Manag. Risk Eng. Syst. Geohazards; 2009; 3, pp. 184-189. [DOI: https://dx.doi.org/10.1080/17499510902831759]
43. Zhong, Q.; Wang, L.; Chen, S.; Chen, Z.; Shan, Y.; Zhang, Q.; Ren, Q.; Mei, S.; Jiang, J.; Hu, L. et al. Breaches of embankment and landslide dams-State of the art review. Earth-Sci. Rev.; 2021; 216, 103597. [DOI: https://dx.doi.org/10.1016/j.earscirev.2021.103597]
44. Normative on the Analysis and Assessment of Risk Due to Dams. (In Romanian: Normativ Privind Analiza și Evaluarea Riscului Asociat Barajelor), NP 132-2011. 2011; Available online: https://www.mdlpa.ro/userfiles/reglementari/Domeniul_XIX/19_17_NP_132_2011.pdf (accessed on 18 May 2024).
45. Chen, S.S.; Zhong, Q.M.; Shen, G.Z. Numerical modeling of earthen dam breach due to piping failure. Water Sci. Eng.; 2019; 12, pp. 169-178. [DOI: https://dx.doi.org/10.1016/j.wse.2019.08.001]
46. Ionescu, C.S.; Gogoaşe Nistoran, D.E. Influence of reservoir shape upon the choice of Hydraulic vs. Hydrologic reservoir routing method, Conf. on Sustainable Solutions for Energy and Environment (EENVIRO 2018), Cluj Napoca, ROMANIA, OCT 09-13, 2018. Book Series: E3S Web of Conferences; EDP Sciences: Les Ulis, France, 2019; Volume 85, 07001. [DOI: https://dx.doi.org/10.1051/e3sconf/20198507001]
47. Grecu, F.; Ioana-Toroimac, G.; Molin, P.; Dramis, F. River channel dynamics in the contact area between the Romanian Plain and the Curvature Subcarpathians. Rev. Geomorfol.; 2014; 16, pp. 5-12.
48. Ennouini, W.; Fenocchi, A.; Petaccia, G.; Persi, E.; Sibilla, S. A complete methodology to assess hydraulic risk in small ungauged catchments based on HEC-RAS 2D Rain-On-Grid simulations. Nat. Hazards; 2024; 120, pp. 7381-7409. [DOI: https://dx.doi.org/10.1007/s11069-024-06515-2]
49. Flood Risk Management in Romania (In Romanian). Available online: https://harticiclul2.inundatii.ro/[email protected],26.1489528,12z (accessed on 20 November 2024).
50. Ferrari, A.; Vacondio, R.; Mignosa, P. High-resolution 2D shallow water modelling of dam failure floods for emergency action plans. J. Hydrol.; 2023; 618, 129192. [DOI: https://dx.doi.org/10.1016/j.jhydrol.2023.129192]
51. Australian Institute for Disaster Resilience, Australian Government. Flood Hazard 2017. Available online: https://knowledge.aidr.org.au/media/3518/adr-guideline-7-3.pdf (accessed on 2 February 2025).
52. Roșu, C.; Crețu, G. Accidental Floodings (In Romanian–Inundații Accidentale); H*G*A* Publishing House: Bucharest, Romania, 1998.
53. Aureli, F.; Maranzoni, A.; Mignosa, P.; Ziveri, C. 2D numerical modelling for hydraulic hazard assessment: A dam-break case study 2D numerical modelling for hydraulic hazard assessment: A dam-break case study. Proceedings of the International Conference on Fluvial Hydraulics River Flow 2008; Izmir, Turkey,, 3–5 September 2008.
54. Chen, T.Y.K.; Capart, H. Kinematic wave solutions for dam-break floods in non-uniform valleys. J. Hydrol.; 2020; 582, 124381. [DOI: https://dx.doi.org/10.1016/j.jhydrol.2019.124381]
55. Marangoz, H.O.; Anilan, T. Two-dimensional modeling of flood wave propagation in residential areas after a dam break with application of diffusive and dynamic wave approaches. Nat. Hazards; 2021; 110, pp. 429-449. [DOI: https://dx.doi.org/10.1007/s11069-021-04953-w]
56. Doğan, E.; Temiz, T.; Sönmez, O.; Demirci, B.; Spor, P.; Cumhur, A. Dam failure analysis according to different methods in HEC-RAS, Gökçe Dam, Turkey. Acta Sci.; 2024; 46, e64391. [DOI: https://dx.doi.org/10.4025/actascitechnol.v46i1.64391]
57. Al-Fugara, A.; Mabdeh, A.N.; Alayyash, S.; Khasawneh, A. Hydrological and Hydrodynamic Modeling for Flash Flood and Embankment Dam Break Scenario: Hazard Mapping of Extreme Storm Events. Sustainability; 2023; 15, 1758. [DOI: https://dx.doi.org/10.3390/su15031758]
58. Beza, M.; Fikre, A.; Moshe, A. Dam breach modeling and downstream flood inundation mapping using HEC-RAS model on the proposed Gumara Dam, Ethiopia. Adv. Civ. Eng.; 2023; 11, 78. [DOI: https://dx.doi.org/10.1155/2023/8864328]
59. Hosseinzadeh-Tabrizi, S.A.; Ghaeini-Hessaroeyeh, M.; Ziaadini-Dashtekhaki, M. Numerical simulation of dam-breach flood waves. Appl. Water Sci.; 2022; 12, 100. [DOI: https://dx.doi.org/10.1007/s13201-022-01623-5]
60. Bharath, A.; Shivapur, A.V.; Hiremath, C.G.; Maddamsetty, R. Dam break analysis using HEC-RAS and HEC-GeoRAS: A case study of Hidkal dam, Karnataka state, India. Environ. Chall.; 2021; 5, 100401. [DOI: https://dx.doi.org/10.1016/j.envc.2021.100401]
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Abstract
Flood hazard studies for dam break cases are of utmost importance for understanding potential risks and minimizing the impact of such accidents. Siriu Dam, which has a clay core, is ranked as the third highest embankment dam in Romania. A fully dynamic 2D hydraulic numerical model was developed using HEC-RAS software to simulate the routing of the flood waves formed by breaching this dam. Four different failure scenarios were considered: two for overtopping and two for piping. The breach parameters were chosen based on the dam characteristics in accordance with appropriate empirical relationships. The flood hazard was quantified and analyzed in terms of depths, velocities, depth x velocity values, and flooded areas. The results provide useful information concerning flood risk mitigation, such as the dam break wave routing, peak discharges, arrival time, travel velocity, and inundation boundary. The influence of the scenario and site characteristics (topography, river morphology, and constructions) on the results was analyzed. Depths and velocities over 10 m and 15 m/s, respectively, were obtained close to the dam, while those in Buzău City (90 km away) were under 1 m and 2 m/s, respectively. The city was flooded 7–8.5 h after the breach (depending on the scenario), and over 15 to 50% of its total area was affected. Moreover, the flood hazard parameters were compared for the different scenarios, providing the practical details necessary to develop flood risk management plans and the associated response measures for the inhabited areas. This is the first numerical study to simulate the impact of a potential break accident that can occur for this dam.
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1 Faculty of Energy Engineering, National University of Science and Technology Politehnica Bucharest, 060042 Bucharest, Romania;
2 Bucharest-National Agency for Cadastre and Land Registration, National Center for Cartography, 060022 Bucharest, Romania;