Flash floods present a significant risk to urbanized arid regions, and assessing their inundation patterns is crucial for effective disaster management. Extreme hydrologic events due to aridity and climate change are shaping human lives and major activities in numerous countries at an unprecedented pace. This study aims to assess flash floods from extreme storm events in an arid catchment using high-resolution data. The study applied two models on the event of a single storm, namely the IHACRES and AHP models. The observed flow was used for models' validation. The average flow output determined with the IHACRES model was approximately 0.47 m3/s while the flow output resulting from the AHP model was 0.45 m3/s. The efficiency showed that the IHACRES performed better in evaluating extreme events with an average of 0.88 while the AHP model showed an efficiency of 0.68. The quantitative simulation of both models is likely to have good applicability for simulating single storm events in arid catchments. The validated IHACRES and AHP models offer valuable tools for simulating flash flood. The study's outcomes have implications for flood management policy and infrastructure planning, ensuring a more resilient response to extreme flood events in arid regions globally.

  • Modelling flash flood was conducted based on high-resolution hydrologic data of a single storm event in an arid catchment.

  • The models IHACRES and AHP are likely to have good applicability for simulating single storm events in arid catchments.

  • The efficiency of applied models is based on parameter sensitivity.

  • The simulation of a single storm event provides valuable insights into the characteristics of hydrologic events.

Flash floods are complex natural hazards that result from very intensive and localized rainfall storms among hydrometeorological, geomorphological, and anthropic complexities. While water assessments, management, and planning are important issues in urbanized communities, water scarcity is a major dilemma in arid regions and may damage their local economic growth. Extreme events such as drought and flash floods due to increasing or decreasing temperature trends lead to more heavy rainfall in a short time interval (El Kasri et al. 2021; Abushandi & Al Ajmi 2022). Therefore, there is a need to understand the hydrological processes that occur in arid regions although the lack of hydrological data and the difficulties of access to some areas make the task much more challenging. Reliable flash flood modelling requires sufficient, continuous, and high-intensity interval records not only for several years but even for a single storm event. Generally, governmental efforts have focused on strengthening water facilities through the establishment of dams for groundwater recharge and surface storage. Groundwater represents the main water resource that feeds various regions of the Sultanate of Oman. Networks and stations have also been established to monitor the water conditions in the Sultanate and to understand the characteristics of rainfall; these represent an essential input in hydrologic modelling. The behaviour of rainfall differs from storm to storm according to several factors, including:

  • 1.

    Cloud diameter and thickness

  • 2.

    Wind speed and direction

  • 3.

    Rainfall intensity

  • 4.

    Temperature gradients

Accurate rainfall estimates are crucial for accurate flood forecasting. A deep-learning-based Long Short-Term Memory (LSTM) model was introduced by Chen et al. (2022) to forecast monthly rainfall data. The model improved accuracy and efficiency in forecasting rainfall under different climatic conditions, making it a promising approach for rainfall forecasting in various global regions. Numerous studies have investigated the behaviour of single extreme storm events and their impact on the water sector. Using a three-dimensional computational fluid dynamics (CFD) model, Feng et al. (2022) studied flood behaviour during extreme storm events revealing the sensitivity of the flow distribution. Abdulla et al. (2002) modelled the hydrographic runoff for a single rainfall event in an arid basin using limited available meteorological and hydrological data. The results showed that the hydrographic simulation of the runoff was similar to the observed records. Abushandi & Merkel (2013) developed a new framework using two models – the HEC-HMS (hydrologic modelling system) and the IHACRES (Institute of Hydrology Center for Resource and Environmental Studies) – to assess a single runoff event for an arid catchment in Jordan. The results showed that both models could be used to calculate the flow volume. Primarily, the results of hydrological models are based on soil moisture antecedent conditions. Singh et al. (2022) proposed two hybrid Machine Learning-based Pedotransfer Functions (ML-PTFs), combining Genetic Algorithm with Multilayer Perceptron (MLP-GA) and Support Vector Machine (SVM-GA), to estimate saturated hydraulic conductivity (Ks) in soils. Tan et al. (2008) studied the performance of rainfall-runoff models from single storms for small catchments. The authors found that continuous-event calibration performed better in evaluating the overall shape of a hydrograph, the peak flow volume, and the delay time. Hossain et al. (2019) used an event-based stormwater management model (EPA-SWMM) performing continuous simulations for calculating individual runoff volumes. The calibration parameters were based on the physical characteristics of catchments such as Manning's roughness, saturated hydraulic conductivity, and unsaturated zone moisture contents. However, modelling flood events may overestimate reference data by up to 200% due to method uncertainties (Valeriya et al. 2019). A limited number of hydrologic models are currently capable of predicting short-duration runoff occurring during 30-minute-long storm events (Du et al. 2007; Abushandi & Merkel 2013). The simulated runoff in these models demonstrated close agreement with the observed events and a relative error of less than 10%.

The integration of remotely sensed data to complement the scarcity of ground hydrologic data has been a major modelling concern over the last 10 years. Chen et al. (2021) conducted a study using satellite estimates and sub-pixel changes in precipitation in a semi-arid region. The authors used the infrared (IR) method to detect clouds that produced rain through a multi-infrared channel and revealed that the spatial variations of precipitation depended on both the spatial scale and the type of precipitation. Massari et al. (2019) used a model conditional processor (MCP) to combine satellite precipitation products through a precipitation dataset. The method was developed for the forecasting of specific flooding events. Furthermore, Abushandi & Merkel (2013) developed a new framework using global satellite mapping of precipitation (GSMaP-MVK+) to feed two models, namely the HEC-HMS and IHACRES. The models were able to determine a single runoff volume for an arid catchment in Jordan. Croke et al. (2005) have also previously used the IHACRES to model rainfall-runoff for arid and semi-arid catchments. To reduce the parameter uncertainty, these authors developed a non-linear loss module which had stronger physical descriptors.

However, modelling rainfall-runoff in arid catchments is associated with difficulties in defining a threshold because the information commonly contains a large number of zero data points. Ali et al. (2019) conducted a study to examine the capability of the analytic hierarchy process (AHP) for flood vulnerability mapping incorporating geographic information systems (GIS). Seven factors were used for this purpose, namely land elevation, slope angle, topographic wetness index, rainfall deviation, land use land cover, clay contents in soil, and distance from rivers. The most important factor determining the occurrence of floods in the AHP model according to Souissi et al. (2020) was the elevation (22.5%); around 75% of the observed flood areas were located in moderate to very high elevation districts. Similarly, a flood susceptibility map generated using an AHP based on the elevation factor has previously shown that flood potential (moderate to very high classes) is generally concentrated in low-altitude areas (Hammami et al. 2019). The simplicity, flexibility, and ability to mix multi-criteria in the final decision framework make the AHP method much more popular (Pohekar & Ramachandran 2004).

Isolation of specific hydrologic events allows for a more detailed investigation (Bermúdez et al. 2017), such as storm duration, intensity, and distribution which can significantly influence the flood magnitudes and dynamics. In addition, analysing single storm events enables the collection of high-resolution data. These detailed datasets explain how the catchment responds to the rapid changes in hydrological conditions during the storm. However, analysing individual storm events allows us to identify the critical factors that trigger flash floods in arid catchments and determine the thresholds of rainfall and soil antecedent conditions that lead to flash flooding (Abushandi & Merkel 2013). Modelling individual storm events provides an opportunity to validate hydrological models and refine the sensitive parameters, making the models more reliable and accurate tools for predicting and managing flash floods in arid regions.

A combination of the Google Earth Engine (GEE) platform, the AHP, and GIS has been used to generate susceptibility maps (Swain Singha & Nayak 2020) showing that major floods may accumulate preferentially in zones with lower elevations. Lallam et al. (2018) applied the AHP to identify surface runoff coefficients based on three different criteria, namely soil type, slope, and vegetation cover. The Wadi Al Jizzi arid catchment has been experiencing flash floods almost every year, causing significant damage to infrastructure, human and animal losses, and erosion of fertile soils. This paper aims to assess flood magnitudes for a single storm event that occurred on 4 May 2021, using the AHP and IHACRES models.

The Wadi Al Jizzi arid catchment is located in the northern part of the Sultanate of Oman, specifically in Sohar, the country's second major city. The total area of the catchment basin is around 870.6 square kilometres. The catchment is one of the most famous Wadis and feeds groundwater aquifers in Sohar over a length of 260 km. The climate in the region is arid and the average precipitation is less than 100 mm per year. The catchment is subjected to seasonal rainstorms and tropical cyclones in the months of March, April, and May, which lead to the flash flooding of Wadi Al Jizzi for a short time following these events. The predominant soil type in Wadi Al Jizzi is loamy alluvial with moderate infiltration rates (Abushandi & Al Sarihi 2022). However, its downstream areas are rich in lime and often contain high proportions of clays. The infiltration rate in the downstream area is relatively lower than in other areas in the catchment. Figure 1 shows the location of the catchment, where 50% of the catchment is located over the Al Hajar Al Gharbi mountains with a maximum elevation of 1,200 m above sea level. The mountains are covered by basaltic rocks, whose impermeability increases the recurrence of floods in the catchment.
Figure 1

Location of the Wadi Al Jizzi catchment (Google Earth).

Figure 1

Location of the Wadi Al Jizzi catchment (Google Earth).

Close modal
Rainfall is usually correlated with minimum temperatures and topographic elevations. Figure 2 presents the annual rainfall rates for the Wadi Al Jizzi catchment according to the tropical rainfall measuring mission (TRMM). The highest rainfall rates are commonly recorded at higher topographic elevations while the coastal areas receive much less rainfall. It is, however, an advantage to use remote TRMM data as the ground meteorological stations are located in accessible areas where most of the mountainous areas are not fairly monitored due to accessibility difficulty. The slopes in these mountains are very steep and, therefore, they are impossible to access and install monitoring devices on (Figure 3).
Figure 2

Annual rainfall distribution for the Wadi Al Jizzi arid catchment.

Figure 2

Annual rainfall distribution for the Wadi Al Jizzi arid catchment.

Close modal
Figure 3

Slope distribution for the Wadi Al Jizzi arid catchment.

Figure 3

Slope distribution for the Wadi Al Jizzi arid catchment.

Close modal
Wadi Al Jizzi is characterized by flash flooding which can generally be defined as overland flows that usually inundate dry areas or ephemeral streams. The average flow in the catchment is about 0.95 m3/s while the average duration of a rainstorm is around 45 min. Around 85% of effective rainfall is generated from mountainous areas. Figure 4 shows a very high tendency of flow records for the years between 1986 and 2007. In addition, the number of flood events per month shows that the highest frequency of floods has historically occurred in the month of February (Figure 5).
Figure 4

Wadi Al Jizzi catchment flow records for 26 events from the year of 1996 to 2007.

Figure 4

Wadi Al Jizzi catchment flow records for 26 events from the year of 1996 to 2007.

Close modal
Figure 5

Flood events frequency in Wadi Al Jizzi for the years between 1996 and 2007.

Figure 5

Flood events frequency in Wadi Al Jizzi for the years between 1996 and 2007.

Close modal

A diver data logger for water level measurements was used to collect high-resolution temporal data at 10 min intervals with a memory capacity of 0.5 million records. These instruments are generally used for groundwater table monitoring rather than for the monitoring of surface water levels. The device required calibration and proper installation in the Wadi. The device was used to measure the water pressure column and therefore, the cross-sectional area of the Wadi was also measured to determine the water volume per unit time (flow).

IHACRES model description

The IHACRES is a hydrograph unit model that derives a time series of runoff from the duration of rainfall and temperature. The IHACRES model was developed by the Center for Resource and Environmental Studies, Australian National University (Ye et al. 1997) and it only requires a small number of input data, namely on the rainfall and temperature. Therefore, it has been used for a large number of arid catchments where hydrologic data are limited (e.g., Ye et al. 1997; Croke & Jakeman 2008; Abushandi & Merkel 2013; Abushandi & Al Sarihi 2022). The model also has an advantage in that it can be used to relate parameters to landscape attributes (Croke & Jakeman 2008). Moreover, it contains a non-linear module that can simulate effective rainfall from input rainfall and temperature data, and two linear modules quick and slow. The first stage in the model's performance is the determination of a drying rate τw and the catchment moisture index Sk at each time step. The drying rate represents the rate at which the catchment wetness declines in the absence of rainfall. This step can be conducted with the following equations:
(1)
(2)
where is the drying rate ; is the temperature at time step k; f is a temperature modulation parameter (C−1); c is the adjustment parameter and controls the amount by which increases during a rainfall event, and is the rainfall during a time step .
Finally, the determined effective rainfall (rk) and then effective rainfall are converted into streamflow (Qk) by
(3)
(4)
(5)
where is the effective rainfall, are the quick and slow stream flow components, is the delay between the rainfall and the stream flow response, are the recession rates for quick and slow storage, and are the fractions of effective rainfall.

AHP model description

The AHP model was used here to compare its performance with that of the IHACRES one. The principles of the AHP method were developed by Saaty (1977) which yielded a relative prioritization of the qualitative and quantifiable multi-criteria. The method synthesizes the relative priorities into global priorities leading to the selection of a final decision (Kostagiolas 2012). The AHP model is based on organizing and analysing complex decisions by forming a hierarchical structure and making pairwise comparisons. To reduce flood estimation uncertainties, all relevant parameters impacting runoff were determined and their importance degree was defined (Table 1). Figure 6 shows the main steps of each model according to the mathematical stages.
Table 1

Comparison and evaluation of the importance of the criteria (Saaty 1990)

Degree of importanceDefinitionExplanation
The two criteria are equally important Both criteria contribute to one objective in the same way 
One criterion is less important than the other Experience and personal appreciation slightly favour one criterion over the other 
High or significant importance Experience and personal appreciation highly favour one criterion over the other 
Very high and corroborated importance One criterion is strongly favoured and its dominance is supported in practice 
Absolute importance Evidence supporting one criterion over the other is as convincing as possible 
2,4,6,8 Values related to intermediate judgements When a compromise is required 
Degree of importanceDefinitionExplanation
The two criteria are equally important Both criteria contribute to one objective in the same way 
One criterion is less important than the other Experience and personal appreciation slightly favour one criterion over the other 
High or significant importance Experience and personal appreciation highly favour one criterion over the other 
Very high and corroborated importance One criterion is strongly favoured and its dominance is supported in practice 
Absolute importance Evidence supporting one criterion over the other is as convincing as possible 
2,4,6,8 Values related to intermediate judgements When a compromise is required 
Figure 6

Flowchart of the AHP and IHACRES models used in this study.

Figure 6

Flowchart of the AHP and IHACRES models used in this study.

Close modal

Five parameters used in the AHP model affected the runoff volume, namely the slope, soil group, rainfall intensity, temperature, and land cover type. Accordingly, the comparison matrix was created based on several important evaluations defined as numbers. This step consisted of assigning weights, checks, and parameter balances to ensure that ratios were consistent when comparing the relative importance of the criteria. A matrix was created for all the factors affecting the flow as shown in Table 2. Each entry in the column was then divided by the column sum to yield its normalized score. The indices of each column were calculated, and the results are listed in Tables 3 and 4.

Table 2

Comparison matrix of input parameters to AHP

ParameterSlopeSoil groupRainfall intensityTemperatureLand cover type
Slope 
Soil group 0.142857 
Rainfall intensity 0.111111 0.2 
Temperature 0.25 0.25 0.111111 
Land cover type 0.166667 0.25 0.25 0.5 
ParameterSlopeSoil groupRainfall intensityTemperatureLand cover type
Slope 
Soil group 0.142857 
Rainfall intensity 0.111111 0.2 
Temperature 0.25 0.25 0.111111 
Land cover type 0.166667 0.25 0.25 0.5 
Table 3

Average number for each column, consistency measure, and consistency index

ParameterSlopeSoil groupRainfall intensityTemperatureLand cover typeAverageConsistency measureConsistency index (CI)Random index (RI)Consistency ratio (CR)
Slope 0.598574793 0.804597701 0.585895122 0.216216216 0.352941176 0.511645 7.857338 0.402992 1.11 0.363056 
Soil group 0.085510599 0.114942529 0.32549729 0.216216216 0.235294118 0.195492 8.262792 
Rainfall intensity 0.066508244 0.022988506 0.065099458 0.486486486 0.235294118 0.175275 6.269488 
Temperature 0.149643698 0.028735632 0.007233266 0.054054054 0.117647059 0.071463 5.037192 
Land cover type 0.099762665 0.028735632 0.016274864 0.027027027 0.058823529 0.046125 5.633036 
ParameterSlopeSoil groupRainfall intensityTemperatureLand cover typeAverageConsistency measureConsistency index (CI)Random index (RI)Consistency ratio (CR)
Slope 0.598574793 0.804597701 0.585895122 0.216216216 0.352941176 0.511645 7.857338 0.402992 1.11 0.363056 
Soil group 0.085510599 0.114942529 0.32549729 0.216216216 0.235294118 0.195492 8.262792 
Rainfall intensity 0.066508244 0.022988506 0.065099458 0.486486486 0.235294118 0.175275 6.269488 
Temperature 0.149643698 0.028735632 0.007233266 0.054054054 0.117647059 0.071463 5.037192 
Land cover type 0.099762665 0.028735632 0.016274864 0.027027027 0.058823529 0.046125 5.633036 
Table 4

Random index (RI) for each number of criteria

N12345678910
Random index 0.55 0.89 1.11 1.25 1.35 1.4 1.45 1.49 
N12345678910
Random index 0.55 0.89 1.11 1.25 1.35 1.4 1.45 1.49 

In the next stage, the consistency index (CI) and consistency of the matrix were determined with the following equations (Saaty 1977):
(6)
(7)
where n is the number of criteria, represents the average values of the consistency factor, CR is the consistency ratio, CI is the consistency index, and RI is the random index which depends on the number of factors used in the pairwise matrix.
Thus, the coefficient of surface runoff can be established using the following equation:
(8)
where Ps, Pc, Pr, PT, and PL are the weights of the criteria, i.e., the slope, soil group, rainfall intensity, temperature, and land cover type, respectively. Likewise, Ns, Nc, Nr, NT, and NL represent the degrees of influence of the same criteria, respectively.
The model performance evaluation was based on the Nash–Sutcliffe efficiency (Ef) and the index of agreement (IoA). The Ef is widely used in hydrologic modelling evaluations to assess the goodness-of-fit measures for modelled versus observed ones. The Ef values range between −1 and +1. An Ef value of +1 indicates a perfect correspondence between observed and simulated records. The Ef can be expressed by the following equation (Nash & Sutcliffe 1970):
(9)
where is the observation flow value; is the modelled flow value, and is the average of the observation values.
The IoA reformulation of Willmott's index of agreement was developed by Willmott (1981) and ranges from −1 to +1. Values approaching +1 depict a better model performance. The values of IoA can be expressed by the following equation (Willmott et al. 2011):
(10)
where is the observation value, is the forecast value, and is the average of the observation values.
While the Ef and IoA represent traditional performance metrics, the Kling-Gupta efficiency (KGE) (Gupta et al. 1998) was used to ensure models performance. The KGE is based on a separation of the Ef into its constituent components (Pearson correlation, variability bias, and mean bias) (Knoben et al. 2019), as shown in Equation (10):
(11)
where CC is the Pearson coefficient value, rm is the average of the observed values, cm is the average of the forecast values, rd is the standard deviation of the observation values, and cd is the standard deviation of the forecast values.
Pearson correlation was used in KGE based on the following formula:
(12)

The values of Pearson correlation always range between −1 and 1, and if the relation between the observed and simulated records is weak, the correlation approaches zero.

Arid areas are highly sensitive to any hydrologic changes and, therefore, the simulation of a single storm event is very challenging. The recorded storm considered here started at 8:40 PM and finished at 1:00 AM. Figure 7 shows the rainfall record of the selected storm on 4 May 2021, measured at 10 min intervals. The soil was assumed to have been dry prior to the storm event. The highest amount of rain recorded during the storm was 11 mm after 90 min out of the total duration of 170 min 08:40 PM. Similar to the annual rainfall spatial distribution, the highest rainfall magnitudes occurred in the higher altitude during the month of May (Figure 8). The rainfall event started from the western part of the catchment and gradually decreased towards the south. However, the rainfall reached its maximum rate 3 h after the start of the storm. Over 60% of the catchment area commonly receives very little rainfall with an average of four rainy days per year. The upper catchment, on the other hand, experiences most of the rainstorms and flooding, as it has around seven rainy days per year. In other words, around 77.8% of the flood magnitudes occurred in the upper catchment area. The temperature during the storm is about 15.3 °C, while the average temperature during the month of May is 24.7 °C.
Figure 7

Rainfall (mm) in Wadi Al Jizzi for the recorded storm.

Figure 7

Rainfall (mm) in Wadi Al Jizzi for the recorded storm.

Close modal
Figure 8

Average rainfall distribution in May in the Wadi Al Jizzi arid catchment.

Figure 8

Average rainfall distribution in May in the Wadi Al Jizzi arid catchment.

Close modal

The results obtained from the two models showed their ability to estimate a single flood event in arid areas, and the accuracy of the results ranged from satisfactory to very good. The IHACRES method has been successfully used for arid catchments, i.e. Jordan, Saudi Arabia, Oman, and Australia where the major advantage of using this model is the few data inputs it requires. However, the IHACRES model was not able to simulate flooding when rainfall was less than 1 mm due to a high infiltration rate. Therefore, as an initial stage to run the model, the rainfall records were divided into two categories: low (5 mm or less) and high (more than 5 mm). The calibrated parameters of the IHACRES model are summarized in Table 5.

Table 5

IHACRES input parameter values for the low and high cateogries

Low
High
ParametersValueParametersValue
 0.00680000  0.01000000 
 2.500  1.000 
 0.060  0.020 
 0.800  0.030 
 0.340  0.030 
 0.570  0.700 
 0.301000  0.291000 
Area 870.6 Area 870.6 
Delay Delay 
Low
High
ParametersValueParametersValue
 0.00680000  0.01000000 
 2.500  1.000 
 0.060  0.020 
 0.800  0.030 
 0.340  0.030 
 0.570  0.700 
 0.301000  0.291000 
Area 870.6 Area 870.6 
Delay Delay 

The total volumes of runoff generated by the IHACRES and AHP models agreed well with the observed volume (Figure 9). However, all IHACRES model parameters were sensitive to the amount of rainfall in both the low and high categories. The effects of the drying rate ( and temperature modulation parameter of the low category were increasing due to higher temperature gradients during the initiation of the storm, whereas the adjustment parameter (parameter c) was decreasing. Similar results have been reported by Abushandi & Al Sarihi (2022) for 26 flood events in the Wadi Al Jizzi catchment.
Figure 9

Simulated flow using the IHACRES and AHP models in comparison with observed flows for a single storm on 4 May 2021.

Figure 9

Simulated flow using the IHACRES and AHP models in comparison with observed flows for a single storm on 4 May 2021.

Close modal

Based on further analyses, the IHACRES maximum flow rate was 2.09 m3/s while that obtained with the AHP model was 2.10 m3/s. Both models were able to capture the peak flow with a longer response delay for the AHP model.

Although the AHP model used more input data, the IHACRES performed better for this event. The main advantage of applying the AHP model is that it allows the consideration of numerous criteria based on pairwise comparisons for estimating the runoff volume. The AHP method was moreover highly efficient for modelling floods in arid areas based on multi-criteria decision-making (MCDM) tools. It was noted that the rainfall intensity and the type of soil had a clear effect on the surface runoff in the study area. In general, the results of the three efficiency methods (Ef, IoA, and KGE) depicted a better performance of high category rainfall events (Table 6).

Table 6

Efficiency proxies showing the accuracy of the IHACRES and AHP prediction models

Efficiency ProxyIHACRES
AHP
LowHigh
Nash–Sutcliffe 0.74 0.95 0.56081 
Index of agreement 0.91 0.97 0.867 
Kling-Gupta 0.80 0.91 0.617 
Efficiency ProxyIHACRES
AHP
LowHigh
Nash–Sutcliffe 0.74 0.95 0.56081 
Index of agreement 0.91 0.97 0.867 
Kling-Gupta 0.80 0.91 0.617 

A reliable assessment of short-term flood risk using the multi-criteria analysis model with the AHP-entropy method by Wu et al. (2022) showed similar storm spatial characteristics as the long flood risk with a correlation coefficient of more than 0.9.

According to the results obtained by Lallam et al. (2018) who investigated the effects of the AHP operative criteria, the vegetation cover had the greatest impact on runoff volume simulations. Generally, the AHP model is subjected to expert judgement of ranking importance while consistency measures are the reference to compare the selected criteria. Accordingly, the error propagation due to the expert judgement may have caused uncertainties in the model outputs (Fernández & Lutz 2010). Similarly, nature-based solutions (NBSs) are increasingly being utilized to mitigate flood risks in diverse areas, but the lack of quantitative assessment approaches limits their acceptance; however, NBS performance assessment provides valuable guidance for flood mitigation (Pugliese et al. 2021).

Peleg et al. (2022) studied high-resolution individual rainfall storms coupled with the future climate scenario. The spatial and temporal patterns of extreme rainfall storm will be increased by 20–30%.

Here, the application of hydrologic models using numerical quantification provided a better understanding of the behaviour of flood events. The results of both IHACRES and AHP models allowed us to predict a single storm event albeit with some limitations. Extreme rainfall magnitudes in the upper parts of the catchment were not recorded due to their topographic complexity. Mountains cover around 68% of the catchment area and, therefore, spatial rainfall distributions cannot be monitored by meteorological stations. However, the satellite images from TRMM used here indicated the presence of a stormy area extending from the western part of the catchment southward of the Wadi Al Jizzi catchment. The two models applied to the study area were able to reproduce the important hydrologic and geo-physical features associated with flood events in arid areas. The average flows determined using the IHACRES and AHP models were 0.47 and 0.45 m3/s, while the average observed flow was 0.55 m3/s using the AHP model. Efficiency measures provide a good tool for comparing model performances. In this paper, the three efficiency proxies (Ef, IoA, and KGE) concluded that the IHACRES model performed better in evaluating the single storm event. The proposed research framework is evolutionary and can be adapted to different climatic areas.

The study relies on limited datasets collected from three weather stations, which may not fully represent the region's climatic diversity. Expanding the data collection to include more meteorological stations and extending the study period could enhance the accuracy and representativeness of the results. Additionally, the study primarily focuses on temperature and rainfall trends, leaving room for further exploration of other climatic parameters and factors influencing extreme events, such as land use changes and socioeconomic drivers.

The authors are thankful to the Directorate General of Regional Municipalities and Water Resources in Al Batina North/Oman, particularly to the Surface Water Unit in Sohar for providing hydrologic data.

All relevant data are included in the paper or its Supplementary Information.

The authors declare there is no conflict.

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