Simulation of Flood Hazard Risk for Naban Reservoir Safety Management: A Comprehensive Assessment
Abstract:
Safety of reservoir dams remains pivotal for societal stability, underscoring the significance of efficient emergency management strategies. This investigation focuses on Naban Reservoir, where the BREACH model was employed to simulate potential dam failures. By integrating one-dimensional and two-dimensional modeling approaches, a mathematical representation was developed to scrutinize flood progression in the adjacent region. Correlation coefficients for the devised model ranged from 0.945 to 0.986, with relative errors of -13.72%, -0.23%, -17.41%, and -15.44%. Comparisons indicated that observed flow rates align closely with simulated rates. Notably, significant land slippages surrounding the reservoir were not detected, implying that an enhanced downstream surge due to an upstream collapse is unlikely. Nevertheless, a breach in the main dam could result in catastrophic outcomes for downstream zones, particularly affecting infrastructure and communities along the Shangsi and Zaimiao Basins. Critical observation zones, such as Siyang Town in Shangshi County, Zaimiao Town in Shangshi County, and Nakan Town in Ningming County, were identified, emphasizing the need for enhanced precautionary measures to safeguard human lives, property, and societal stability. This research has paved the way for a novel flood early warning system tailored for the Naban Reservoir, ensuring timely predictions and alerts. Such advancements augment the disaster prevention capacity, offering valuable insights for mitigating risks in small to medium-sized reservoirs.
1. Introduction
Situated within a monsoon climate zone, China is routinely subjected to high rainfall intensities during the flood season. Consequently, floods are recognized as the most prevalent natural disasters in the region [1]. The grave threat they pose to the safety of life and property underscores the imperative of flood prevention and mitigation measures [2], [3], [4].
Central to these mitigation strategies are reservoirs, pivotal hydraulic infrastructures, designed with three-fold functionality: flood control, water supply, and irrigation. Yet, a concerning observation has been made. Many existing reservoirs, having been constructed several years ago, now fall short of current flood risk management standards, presenting numerous safety hazards. In the unfortunate event of dam failures following flood disasters, the resultant devastation in downstream regions can be monumental [5], [6].
The potential severity of these consequences has led to the institution of specialized early warning systems. These systems are believed to considerably enhance the safety profile of reservoirs, concurrently reducing their vulnerability to water hazards, thus contributing significantly to disaster prevention and mitigation [7], [8], [9]. Enabled by advanced GIS technology, artificial intelligence, and machine learning techniques, these early warning systems adeptly analyze vast flood datasets, facilitating real-time flood prognostications [10], [11]. A notable impact of such systems is evident in certain underdeveloped nations where significant declines in mortality rates, attributable to natural calamities, have been recorded following the implementation of flood early warning systems [12]. Emphasizing their importance, the establishment of technology-aided flood early warning systems is now prioritized in flood prevention and mitigation agendas [13], [14].
Integral to these systems is the ability to undertake quantitative flood hazard risk evaluations and devise strategies for hazard minimization [15], [16]. The undertaking of flood hazard risk assessments is not only pivotal to flood risk management but also vital for reservoir safety governance [17], [18]. Several methods, ranging from the indicator system and historical flooding methods to hydrological-hydraulic model simulations, have been employed for these assessments [19], [20], [21]. However, it's noteworthy that the driving factors of floods—such as climate, hydrology, topography, land use, and soils—inject inevitable uncertainties into these evaluations, necessitating a multidimensional approach [22], [23]. The traditionally employed flood assessment methodologies, although comprehensive, often grapple with data insufficiencies and multiple constraints. Thus, a shift towards more pragmatic and streamlined flood models is discernible, with these models progressively superseding the conventional methods to deliver rapid and precise flood simulations [24], [25], [26]. Such advancements in early warning systems fortify reservoirs, enabling them to pre-empt water disasters, which, in turn, reinforces their safety management competencies.
A review of current literature reveals a range of models, including the MIKE series, SHUD, SWMM, and HEC-HMS, which have been utilized for simulating flood dynamics [27], [28], [29], [30]. Several empirical studies serve as exemplars. For instance, in a study by Yang et al. [31], a hybrid model integrating SWMM and MIKE21 was developed to ascertain the implications of rainfall irregularities on urban flooding. Similarly, Barreiro et al. [32] harnessed a combination of one-dimensional SWMM and two-dimensional MOHID models, yielding a more nuanced urban flooding model that provided a better representation of stormwater effects. In a distinct effort, Wang et al. [33] extrapolated current and future river flood dispersions and localized flood inundations using the MIKE FLOOD model, affirming its potential in guiding the scientific planning of urban infrastructures. Furthermore, Lu et al. [34] relied on the MIKE FLOOD model to execute a quantitative analysis of present-day land use, topographical parameters, and flood containment capacities, thereby offering invaluable technical backing for the digitization and precision-targeted watershed flood management.
However, a glaring research gap persists. While flood modeling research predominantly targets urban or flat terrains, scant attention has been accorded to its application in the domains of reservoir water hazard risk and safety management. This oversight is particularly concerning given the vast populations whose lives and assets are intertwined with the safety of these reservoirs. Addressing this deficit, the present study endeavors to provide a meticulous quantitative assessment of the flood dynamics of the Naban Reservoir, especially under dam failure scenarios. The research focus is centered on the Naban Reservoir, strategically located in the Ming River's mainstream. Employing a combination of one-dimensional (MIKE11 river network model) and two-dimensional (MIKE21 surface model) coupled models, flood inundations under varying flood magnitudes are simulated. The fusion of these models aims to comprehensively capture the hydrological nuances of the reservoir's surrounding basin, ensuring superior simulation accuracy. Concurrently, the study introduces a reservoir flood warning model, synthesized using the aforementioned coupled models, to facilitate real-time flood predictions, thereby bolstering reservoir disaster prevention and mitigation capabilities.
In summation, this research is poised to furnish valuable data insights and scientific references, potentially guiding reservoir water hazard risk studies and shaping reservoir emergency strategy formulations.
2. Geographical and Climatic Profile of the Naban Reservoir Area
Naban Reservoir is situated within Shangsi County of Fangchenggang City, in the Guangxi Zhuang Autonomous Region. It is geographically positioned at 108°00'E longitude and 22°08'N latitude, as delineated in Figure 1. Nestled in the Ming River basin — the predominant tributary of the Zuojiang River basin — the reservoir is strategically located in the upper reaches of the Ming River [35].
The Ming River has its origins at the northern foothills of Guangxi's 100,000 mountains. It courses from the southwest to the northeast, spanning a distance of 315 km, and draining a watershed area encompassing 6379 km2. Notably, the Tuolin River, the Gongan River, and the Pailian River are identified as its principal tributaries. The watershed experiences a subtropical monsoon climate, characterized by ample precipitation and sunshine. Within the basin, an average annual temperature of 21.3℃ is recorded. Additionally, an average annual evaporation of 1,647 mm and a relative humidity of approximately 81 percent are observed.
Flowing through multiple townships in Fangchenggang City, including Shangsi County, Si Yang, and Jiao An, the Ming River basin sustains a populace exceeding one million. It envelopes over 400,000 acres of cultivated land and is critical for the protection of vital infrastructures such as the 100 km stretch of the Xianggui Railway and 3 km of the 311 Provincial Highway. Shangsi County, where the reservoir is anchored, is renowned for its bountiful natural resources, being designated as both a forestry and sugar-producing county.
Primarily established for irrigation, Naban Reservoir also facilitates power generation and urban water supply. Historically, it has been assailed by numerous typhoon events and flooding hazards, leading to considerable damages both to governmental infrastructure and the local populace, as cataloged in Table 1. Essential technical parameters of the reservoir, encompassing watershed area, multi-year average rainfall, multi-year average runoff, characteristic water level, and reservoir capacity, are detailed in Table 2. These parameters are subsequently employed as foundational data during the modeling phase.

Starting Moment | End Moment | Rising Water Level (m) | Maximum Water Level(m) | Average Rainfall in Reservoir Area (mm) | Flood Peak Flow (m³/s) | Total Amount of Flood Water (billion m3) |
1994-7-14 18:00 | 1994-7-23 4:00 | 211.09 | 219.88 | 476 | 1300 | 2.3 |
1997-8-22 8:00 | 1997-8-27 8:00 | 213.99 | 219.72 | 356 | 3600 | 1.7 |
1998-6-25 6:00 | 1998-7-8 8:00 | 208.98 | 220.59 | 643 | 2300 | 3.0 |
2001-7-2 2:00 | 2001-7-4 12:00 | 215.81 | 222.76 | 457 | 4009 | 2.5 |
(Pearl River Basin above, Yellow Sea Basin below) | ||||||
2013-11-10 5:00 | 2013-11-12 5:00 | 219.63 | 222.64 | 334 | 3200 | 1.2 |
2014-9-8 6:00 | 2014-9-20 22:00 | 215.15 | 221.2 | 441 | 3800 | 2.1 |
Name | Unit | Numerical Value |
Watershed area | km2 | 490 |
Multi-year average rainfall | mm | 1229 |
Multi-year average runoff | m3 | 63072×104 |
Normal water storage level | m | 220.57 |
Design Flood Level | m | 227.98 |
Calibration flood level | m | 229.68 |
Stagnant water level | m | 209.57 |
Dead storage capacity | m3 | 1.64×108 |
Flood control reservoir capacity | m3 | 4.00×108 |
Xingli storage capacity | m3 | 2.64×108 |
Total storage capacity | m3 | 8.28×108 |
3. Methodology: Model Construction and Validation
Given the intricate terrains present in the Ming River basin, encompassing forests, grasslands, clearings, settlements, and roadways, a flood simulation model has been developed, integrating both one- and two-dimensional modules. The one-dimensional module serves as the river network model, whereas the two-dimensional module functions as the terrestrial surface representation.
Within this context, the riverine flooding of the Ming River is depicted through the one-dimensional model, while the two-dimensional model emulates the inundation and lateral flow patterns adjacent to the riverbanks. To enhance the accuracy of riverine flood representation, and the complex terrains within the Ming River basin of the Naban Reservoir, the coupling of MIKE11 and MIKE21 was employed. This coupling optimally captures the hydrodynamics of the river and the surrounding terrain, aiming to diminish discrepancies between simulated and observed phenomena.
The underlying mathematical representation is rooted in the one-dimensional non-constant flow Saint-Venant equation set, which facilitates the depiction of the river's flow state. Generated outputs from this model encompass pivotal data such as inundation depths, flow rates, and velocities, which subsequently are utilized to formulate flood risk maps.
The governing Saint-Venant equations are articulated as:
where, $A$ denotes the cross-sectional area ($\mathrm{m}^2$), $Q$ represents the flow rate ($\mathrm{m}^3/s$), $x$ signifies the distance coordinate (m), $t$ is the time coordinate (s), $h$ refers to the water level (m), $q$ is the lateral inflow rate ($\mathrm{m}^3/s$), $C$ is associated with the Xie Cai coefficient, $R$ stands for the hydraulic radius (m), and $g$ encapsulates gravitational acceleration ($\mathrm{m}^3/s$).
Reservoir dam failures can be attributed to various causative agents such as extreme flood events, inadequacies in reservoir scheduling management, and seismic activities surpassing anticipated intensities. Through the analysis of dam-breach operations, breach modeling, and discharge computations, speculative insights into the reservoir breach format can be formulated. In this study, two primary dam-failure flood scenarios were deliberated upon. The initial scenario postulated a high-water level of 229.68m due to a 5000-year calibration flood, which, compounded with abnormal water seepage, led to an external slope failure. Conversely, the second scenario proposed dam failure at a normal storage elevation of 220.57m due to abrupt incidents.
Naban Reservoir's dam, a homogenous construct of earth and rock, undergoes progressive breaches. For the estimation of such gradual dam breaches, the BREACH model was employed. Fundamental parameters of the reservoir were incorporated into this model (refer to Table 3). These parameters, when juxtaposed with the water level-reservoir capacity relationship curve ( Figure 2), enabled the derivation of the dam-break flow process for Naban Reservoir, as depicted in Figure 3.
Working Condition 1 | Working Condition 2 | |||
Serial number | Parameter Name | Parameter Value | Parameter Name | Parameter Value |
1 | Inlet flow (m3 /s) | 2870 | Inlet flow rate (m3/s) | 653 |
2 | Water surface elevation | 229.68 | Water surface elevation (m) | 220.57 |
3 | Reservoir capacity | 7.89 | Storage capacity | 4.28 |
4 | Elevation of the top of the dam (m) | 232.56 | Elevation of the top of the dam (m) | 232.56 |
5 | Material density (g/cm3 ) | 2490.2 | The density of dam material (g/cm3 ) | 2490.2 |
6 | The angle of internal friction of matter (°) | 30 | The angle of internal friction of the dam material (°) | 30 |
7 | Matter cohesion (kPa) | 13 | The cohesion of dam material (kPa) | 13 |
8 | D50 (m) | 1.1 | D50 (m) | 1.1 |
9 | D30 (m) | 1.12 | D30 (m) | 1.12 |


Following a thorough analysis of the dam-breach flow process, it was discerned that the peak flood flow for the first scenario amounted to 128,000 m3/s, whilst the second scenario culminated in a peak flow of 80,000 m3/s. Notably, the peak for the first scenario exceeded that of the second. Furthermore, the peak flow for the first case was attained at 1.5 hours, whereas the second scenario reached its zenith at 2.0 hours, rendering a temporal difference of 0.5 hours for peak emergence. However, the propagation durations were found to be nearly identical.
In accounting for the direst potential outcome of a Naban Reservoir dam failure, the dam-failure flood trajectory was based on the calibration level of the first scenario. This trajectory was subsequently introduced as the open boundary condition for numerical computations. Emphasis was placed on contemplating the most adverse circumstances during the formulation of flood contingency plans. As a result, three computational scenarios were established in this study. Depending on reservoir inflow rates under varying frequencies, reservoir spillway discharge processes for 100-year, 500-year, and 5000-year intervals were delineated according to scheduling principles and in conjunction with antecedent hydrological computations of the reservoir. These values were introduced as the inflow boundary conditions for open boundary computations.
The computational segment of Naban Reservoir's Ming River main course spans from the dam site to the concluding segment of the downstream Ming River Shangsi, a total expanse of 73,350 m (as shown in Figure 4). To satisfy boundary prerequisites, it became essential to incorporate the configurations of power stations, gates, and dams situated throughout the river's course. Within the one-dimensional model of Naban Reservoir, upstream processes included flood discharge trajectories and dam-failure flows for each determined frequency. In contrast, downstream processes encapsulated the relationship between water level and flow. Time series files were generated from the flood discharge trajectories and dam-failure flows for each frequency, serving as upstream boundary conditions. Meanwhile, the downstream water level-flow relationship was directly input to the lower boundary, as tabulated in Table 4.

River Name | Starting Mileage (m) | End Mileage (m) | Upstream Boundary Conditions | Downstream Boundary Conditions |
Ming River | 0 | 73350 | Flooding process of Naban Reservoir at each frequency and dam failure flooding process | Cross-sectional water level - flow relationship |
Field studies of the Ming River basin and Naban Reservoir were conducted, and hydrological data were subsequently collected and analyzed to determine and validate the model rates. By assimilating the typical annual flood conditions of both the Ming River basin and Naban Reservoir, the parameters of the coupled model were calibrated and validated.
It has been previously indicated that both boundary conditions and riverbed roughness play intricate roles in determining flood evolution uncertainties [36]. Here, streambed roughness refers to the texture of the streambed surface, which inherently influences energy losses during floodwater progression. The roughness of the one-dimensional model parameters was calculated using flood control engineering data from the Ming River and adjacent waterways. Initial values for the roughness of each segment were provisionally established between 0.03 and 0.05.
The two-dimensional hydrodynamic model was simulated with a temporal resolution of one second. The process of designating roughness was informed by land-use data and remote sensing imagery from the flanks of the Ming River. The roughness file was represented using Manning's value. Different land types were ascribed specific roughness values as detailed in Table 5.
Lower pad surface | Place of Residence | Trees | Dry Field | Water Field | Roads | Open Space | River |
Roughness (n) | 0.07 | 0.065 | 0.06 | 0.05 | 0.035 | 0.035 | 0.025-0.035 |
For the validation phase, measured flood data from the Ming River, dated 18 September 2014, was utilized (as shown in Figure 5 and Table 6). This data set was sourced from the Naban Reservoir Management Centre. A juxtaposition of the simulated outcomes with the actual measured values exhibited correlation coefficients spanning between 0.945 and 0.986. The observed relative errors were -13.72%, -0.23%, -17.41%, and -15.44%, respectively. Notably, flow values from both simulated and actual measurements remained broadly aligned, and the simulation discrepancies fell within the acceptable error threshold (less than 20%). Consequently, it can be inferred that the developed model is reflective of real-world conditions within the Ming River.

Frequency | Average Measured Flow/m3 -s-1 | Average Simulated Flow/m3 -s-1 | Absolute Error/m3 -s-1 | Relative Error/% | Relativity Eoefficient R |
5000a | 2164.89 | 2461.95 | 297.06 | -13.72 | 0.986 |
500a | 1630.68 | 1634.43 | 3.75 | -0.23 | 0.946 |
100a | 1240.73 | 1502.29 | 261.56 | -17.41 | 0.945 |
20a | 882.04 | 1018.23 | 136.19 | -15.44 | 0.955 |
4. Analysis of Simulation Results
Based on the design, construction, safety evaluation report, and risk-mitigation data of Naban Reservoir, as well as observations from the reservoir site, two potential flood emergencies were identified: over-standard flooding events and dam-break floods. Historical data from Naban Reservoir floods informed the consideration of three operational scenarios: floods with return periods of 5000 years, 500 years, and 100 years. For the dam-break flood, the most adverse reservoir conditions associated with a 5000 years check flood, and the implications of unusual high-water level leakage were taken into account. The flood evolution process in the Ming River's lower reaches was assessed based on three parameters: peak flood level, maximum water depth, and flood arrival time. The subsequent sections delve into the flood impacts associated with the Naban Reservoir.
Model simulations provided the peak flood level, maximum water depth, and flood arrival time progressions for the Ming River under the conditions of Naban Reservoir's flood discharge and dam break (refer to Figure 6). As delineated in subgraph (a) of Figure 6, a general decline in the peak flood water level of Naban Reservoir along the Ming River was noted for both the overtopping release and dam-break flood events. The largest peak flood water level was observed during a dam breach at the 5000 years calibration level, while the smallest occurred during the 100 years flood event. This disparity is attributed to the maximal flow during the former dam breach and the minimal flow during the latter flood release. Remarkably, the end peak flood levels for all four emergencies were convergent, suggesting minimal threat to the inhabitants and their properties along the river, from Naban Reservoir's dam site to the Ming River's Shangsi section.
The maximum water depths, from the dam site to the terminating cross-section, were tabulated, as displayed in subgraph (b) of Figure 6. A generalized declining trend in maximum water depth was observed for all flood emergencies in the Naban Reservoir. However, a slight increase in maximum water depth was discerned 20,000 m from the dam site for the three overtopping flood conditions, attributable to the more subtle topography and consequently slower floodwaters, resulting in increased water levels.
According to subgraph (c) of Figure 6, four scenarios were examined for flood occurrences near the Naban Reservoir dam site. The order of flood front arrivals were: a dam breach at the 5000 years check level, a 5000 years flood, a 500 years flood, and a 100 years flood. It was observed that the flood from the 5000 years check level breach was the earliest to manifest, whereas the 100 years flood was the latest. This trend suggests a correlation between the flood's onset and its velocity, with higher flow rates corresponding to faster velocities and earlier flood front arrivals.
The simulation outcomes from the aforementioned scenarios indicate that, within the Ming River Basin of the Naban Reservoir, the most significant water disaster impact stems from a dam failure during the 5000-year calibration flood. This situation presents the most considerable challenge to the flood prevention and mitigation capacities of the downstream areas. When subjected to a dam failure of the 5000-year calibrated flood, the peak flood level attained was 199.12m, with inundation depths reaching up to 30.57m in downstream regions. This flood event propagated rapidly from the reservoir site, eventually submerging the downstream area.

Within the context of the Ming River basin pertaining to the Naban Reservoir, the populace affected by the inundation range under various flooding frequencies was quantified (as depicted in Figure 7). The data revealed that for flood occurrences with return periods of 100 years, 500 years, and 5000 years during standard release, 10,668, 28,491, and 33,664 individuals were affected respectively. A significant portion of this population was located in Siyang town, with the urban sector being the most impacted.

In the unfortunate event of a dam failure at the calibration level within the Naban Reservoir, key parameters, such as the inundation depth, flood flow rate, and flood front arrival time, were assessed downstream (refer to Figure 8 and Figure 9 and Figure 10). The inundation depth serves as a pertinent metric for flood risk assessment, facilitating the categorization of water hazard levels based on depth measurements. When subjected to a dam breach at a 5000-year calibration level, the volume of water released was found to be 864.38 million m3. The resultant inundated area was 83.12 km2, excluding river zones. Depths of inundation varied from 5 m to 15 m, affecting a land area of 39.90 km2. The peak inundation depth varied between 11.28 m and 30.57 m over an area of 14.56 km2. The primary areas of inundation were identified downstream of both the Naban and Nianlun Reservoirs, especially at confluences with rivers like the Tuopin, Baibao, and Phoenix. This inundation affected an estimated 100,000 individuals and submerged around 210,000 mu of arable land. Dam failure would result in catastrophic impacts, especially in regions downstream of the Shangsi and Zaimiao basins. Notably, the town of Siyang in Shangsi County, situated approximately 4 km linearly from the dam, was highlighted as being at substantial risk.



The analysis of the flood front's arrival time during a dam breach at the 5000-year calibration level (illustrated in Figure 10) demonstrated that waters quickly inundated the areas downstream of Nianlun Reservoir along the Tuopin River. Siyang town, located along the Ming River, was the initial region to experience the flood impacts with a response time of less than 0.5 hours. Conversely, in regions downstream of the Dinggou and Baibao rivers, flood front arrival times in Siyang town and Callan town ranged between 0.5 to 1 hour. For areas in Siyang near the Baibao River and in the downstream sections of Dinggou, flood front arrival times extended from 1 to 3 hours. Given the rapid progression of the flood, evacuation and property relocation measures would face stringent time constraints. It is imperative to establish a swift response and dispatch mechanism, amplifying residents' awareness of protective measures and emergency responses to maximize the preservation of lives and property.
Based on the outcomes derived from model simulations, several strategic measures are advocated for enhancing the safety management of Naban Reservoir.
(1) Risk analyses related to reservoir water disasters should be conducted proactively. Potential safety concerns for the Naban Reservoir ought to be detected and addressed with early warning systems to enable timely interventions.
(2) The structural integrity of the reservoir, especially components that might harbor latent vulnerabilities, should be rigorously evaluated. Documentation of these assessments should be systematically maintained and disseminated at consistent intervals.
(3) Given that the flood front's approach to the downstream area is typically recorded within a three-hour window, it is imperative that a diversified communication strategy be employed. Information dissemination through public broadcasts, television news, mobile text alerts, and online platforms can expedite the notification process. Such methods can effectively maximize the available time frame for safe evacuations.
(4) In the face of imminent disasters, the seamless operation of communication channels becomes paramount. Collaborations with communication departments might be necessitated to deploy emergency communication apparatus and ensure uninterrupted connectivity in the vicinity of the reservoir.
(5) Logistical preparations are vital for executing large-scale evacuations. Provisions should be made to offer sustenance and support, especially in locales likely to face power or water outages.
(6) Emphasis should be placed on raising the flood disaster awareness and preparedness levels of the resident population. By ensuring that residents are well-informed and educated on best practices, the adverse impacts of potential flood disasters can be substantially mitigated.
5. Conclusion
This study focused on the Ming River basin of the Naban Reservoir located in the Guangxi Zhuang Autonomous Region. Utilizing a one-two-dimensional coupled model, a flood model of the Naban Reservoir was constructed. Investigations were centered on flood evolution, flood inundation by discharge, and flood inundation resultant from dam failure during instances of 100-year, 500-year, and 5000-year floods in regular discharge, alongside a 5000-year calibration water level scenario.
Key findings from this research are as follows:
(1) Roughness calibration was achieved using observed data from the Ming River. For river roughness values ranging between 0.025 and 0.035, with a settlement value of 0.07 and an open space roughness of 0.035, deviations between the coupled model’s predicted and observed values were minimal, indicating high accuracy. All simulation outcomes remained within the permissible error range.
(2) Minimal impact on the downstream shoreline was observed during routine flooding of Naban Reservoir across varied frequencies. However, a significant alteration was noted when the reservoir underwent a 5000-year calibration level dam failure. In this scenario, the dam failure volume was estimated at 864.38 million m3, leading to an inundated area of 83.12 km2. The compromised zone spanned 39.90 km2, with a maximum inundation depth ranging from 11.28 m to 30.57 m, impacting an area of 14.56 km2. Predominantly, the inundated regions were located downstream of the reservoir and its adjacent river. Over 100,000 residents were affected, and an estimated 210,000 mu of arable land was submerged. Such a dam failure would inflict catastrophic damage to the downstream Shangsi and Zaimiao Basins, with Siyang Town being the most susceptible.
(3) Variability in the flood front's arrival time was recorded across different regions following the dam's failure. Siyang Town emerged as the initial recipient of the flood, presenting an alarmingly short emergency response time of fewer than 0.5 hours. Absence of prior alerts poses challenges in ensuring comprehensive and safe evacuations. Inhabitants along both sides of the downstream Ming River are advised to relocate before the impending flood. Authorities are urged to devise a swift response and dispatch mechanism, while concurrently enhancing residents' cognizance of emergency protocols to curtail water disaster threats.
(4) Through the integration of MIKE11 and MIKE21 models, a flood warning system for the Naban Reservoir was developed. This system enabled real-time flood predictions and advance warnings, augmenting the reservoir's disaster prevention and mitigation potential. It is posited that the findings from the Naban Reservoir flood model can be extrapolated to other small and medium-sized reservoirs, offering valuable data insights and scholarly benchmarks for flood disaster risk investigations in similar environments.
(5) Given the intricate nature of enacting flood prevention and mitigation policies, this study abstains from delving into detailed procedural implementations. Subsequent research endeavors might explore government strategies in streamlining response mechanisms, elevating public awareness surrounding flood prevention, and pinpointing optimal timelines for early evacuations.
Not applicable. The data in this paper was also used in other scientific projects where the data was not applicable because of confidentiality agreements.
The authors declare that they have no conflicts of interest.
