Event-based rainfall-runoff mechanism modeling is a very useful process for flood forecasting, in particular at the level of the dam watersheds in semi-arid regions. In this regard, this paper presents a flood modeling application in the Sidi Mohammed Ben Abdellah (SMBA) dam watershed in Morocco, using the HEC-HMS model. The Soil Conservation Service (SCS) Curve Number (CN), the SCS Unit hydrograph, and the Recession were chosen as loss, transform, and baseflow methods respectively. The various frequency floods entering the SMBA dam were simulated using the elaborated model. The results show that it is possible to estimate the volumes of water generated during floods satisfactorily with errors of 6–11%, while the error in peak flow is around 20%. The median NSE, during validation, is 0.58 and the R2 is about 0.67. Sensitivity analysis shows that the runoff volume, the peak flow, and the NSE were found to be more sensitive to lag time and CN parameters. The developed event-based model will make it possible to carry out several simulations allowing the assessment of the North to South Water Transfer Project operation, in particular, the SMBA dam reservoir management during the flood periods.

  • HEC-HMS has proved its ability to simulate the floods at the SMBA dam watershed.

  • Tlag and CN are the most influential parameters on the elaborated model outputs.

  • Frequency floods entering the SMBA dam were simulated using the validated model.

  • The resulted model will allow optimal SMBA dam-reservoir management.

Under the combined effect of growing water needs and decrease of the global water resources due to climate change, integrated and sustainable water resources management has become a major priority (Luo et al. 2019; Şen 2021). This challenge is most felt in areas with an unequal spatio-temporal distribution of water resources. To deal with this stressful situation, dams constitute an important means to alleviate the problems linked to the temporal heterogeneity of water resources. Thus, water transfers from the surplus areas to the deficit ones make it possible to remedy the uneven spatial distribution of water (Liu et al. 2019; Laassilia et al. 2021).

Since the 1960s, Morocco has opted for a policy of building dams to secure water supply for domestic purposes and to accompany the economic development of the country. In recent years, water transfer projects between the surplus basins in the North and the deficit ones in the South are under study (Laassilia et al. 2019). The effectiveness of this kind of projects is linked to the understanding of the rainfall-runoff mechanism in the watersheds concerned by the water transfer. The estimation of the runoff produced within a given catchment will make it possible to optimize the sizing and the management of the water transfer whether under current or future climatic conditions.

Hydrologic models are often used as a tool for a wide range of tasks, such as the modeling of flood events, the long-term water resources assessment, or the prediction of floods (Jia et al. 2009). The type of the modeling approach normally depends on the study purpose, data availability, and ease of use (Tassew et al. 2019). Known as a powerful tool to model the hydrologic mechanism in the various climatic context, the HEC-HMS model was selected for the concretization of the rainfall-runoff relationship at the level of the SMBA dam watershed, considered as one of the main components of the North to South Water Transfer Project (NSWTP) in Morocco. The HEC-HMS model was chosen for its adequacy with the study aims, its applicability in the semi-arid zones as Morocco, and availability of the input data.

Previous studies on HEC-HMS proved its ability to simulate and forecast streamflow based on different datasets and catchment types (Chu & Steinman 2009). In this regard, Joo et al. (2013) carried out a comparison of two event-based flood models (ReFH and HEC-HMS). The authors concluded that the ReFH model shows the limitations in the simulation of peak flow, while HEC-HMS shows good simulations in the studied catchments. De Silva et al. (2014) used the HEC-HMS for the modeling of events and continuous flow hydrographs in the Kelani River Basin (Sri Lanka). The results depict the capability of HEC-HMS to reproduce stream-flows in the basin to high accuracy with averaged computed Nash-Sutcliffe efficiencies of 0.91 for event-based simulations and 0.88 for continuous simulations. Ramly & Tahir (2016) applied HEC-HMS as rainfall-runoff model for flood simulation. The study had produced an illustrative and comprehensive representation of the sub-basin with reasonable accuracy indicated by the Nash-Sutcliffe coefficient of 0.86. Natarajan & Radhakrishnan (2019) applied HEC-HMS for the simulation of extreme event-based rainfall-runoff process in an urban catchment area. As a result, the frequency storm method has a Nash value of 0.7, which is higher than the value obtained from the specified hyetograph process, and it is chosen as a better model for generating food peak and volume for different return periods in the basin. Katwal et al. (2021) validated an event-based and a continuous flood modeling in Zijinguan watershed, Northern China. The authors found that the performance of SCS-CN model is more satisfactory than that of SMA model. In the semi-arid Moroccan context, many authors have validated rainfall-runoff models, using HEC-HMS, in several catchments of the country (Khaddor et al. 2016; Khattati et al. 2016; Ahbari et al. 2018; Elhassnaoui et al. 2019).

It is worth mentioning that the Bouregreg basin was the subject of several studies dealing with the various hydro-climatic aspects. However, the rainfall-runoff modeling of this catchment using the HEC-HMS model has not yet been carried out. Therefore, this paper aims to validate an event-based rainfall-runoff model to assess the magnitude of the floods in this basin and their impact on SMBA dam reservoir management. In relation with the NSWTP, this developed hydrological model will make it possible to carry out several simulations allowing the assessment of the NSWTP operation, in particular, SMBA dam reservoir management during the flood periods.

Presentation of the SMBA dam watershed (Figure 1)

The SMBA dam, located at the north-central of Morocco, was commissioned in 1974 to ensure the domestic and industrial water supply for the coastal zone of Rabat–Casablanca, and to protect the Bouregreg Valley against floods. Its watershed area is about 9 600 km2. The yearly inflow volume is estimated at 540 Mm3 (1975–2020), with a maximum of 2,600 Mm3 in 2010. The climate is semi-arid. The average annual rainfall is around 420 mm and the temperature varies between 11 and 27 °C. The main rivers are Bouregreg (125 km), Grou (260 km), and Mechra (93 km).

Figure 1

Map of the Bouregreg watershed and the meteorological gauges used.

Figure 1

Map of the Bouregreg watershed and the meteorological gauges used.

Close modal

Data used

Available instantaneous rainfall and runoff data are presented in the Table 1. To verify certain incomplete records, the intensity-duration-frequency (IDF) curves available for the Rabat city were used. These IDF curves were developed on the basis of instant rainfall by the Directorate of National Meteorology in Morocco. The comparison between the cumulative instantaneous rainfalls and the cumulative daily rainfalls was also carried out.

Table 1

Rainfall and runoff data used for Bouregreg basin modeling

Rain gaugesElevation (m)Instantaneous runoff
Instantaneous rainfall
BeginningEndBeginningEnd
Aguibat Ezziar 130 25/03/1977 31/01/2018 21/07/2009 18/07/2017 
Ras Elfathia 161 25/03/1977 31/01/2018 04/08/2009 18/07/2017 
S. M. Cherif 299 01/11/1972 31/01/2018 10/07/2009 18/07/2017 
Lala Chafia 227 01/09/1980 31/01/2018 10/07/2009 18/07/2017 
Ain Loudah 273 01/10/1972 31/01/2018 27/06/2009 18/07/2017 
Tsalat 692 01/03/1977 31/01/2018 26/07/2009 18/07/2017 
Sidi Jabeur 232 17/12/1971 31/01/2018 15/07/2009 18/07/2017 
Ouljat Haboub 552 01/11/1972 31/01/2018 01/03/2012 18/07/2017 
Tamdroust 312 01/09/1974 31/01/2018 25/06/2009 18/07/2017 
Rain gaugesElevation (m)Instantaneous runoff
Instantaneous rainfall
BeginningEndBeginningEnd
Aguibat Ezziar 130 25/03/1977 31/01/2018 21/07/2009 18/07/2017 
Ras Elfathia 161 25/03/1977 31/01/2018 04/08/2009 18/07/2017 
S. M. Cherif 299 01/11/1972 31/01/2018 10/07/2009 18/07/2017 
Lala Chafia 227 01/09/1980 31/01/2018 10/07/2009 18/07/2017 
Ain Loudah 273 01/10/1972 31/01/2018 27/06/2009 18/07/2017 
Tsalat 692 01/03/1977 31/01/2018 26/07/2009 18/07/2017 
Sidi Jabeur 232 17/12/1971 31/01/2018 15/07/2009 18/07/2017 
Ouljat Haboub 552 01/11/1972 31/01/2018 01/03/2012 18/07/2017 
Tamdroust 312 01/09/1974 31/01/2018 25/06/2009 18/07/2017 

As regards the selected events, we have chosen the most important events in terms of the peak flow. About 9–11 events, for each sub-basin, were used for the calibration and validation of the model. Table 2 lists the flood characteristics of samples events used in this study. The analysis of the events used for the model calibration and validation made it possible to draw certain observations. Indeed, most of the recorded events took place between October and March, which corresponds to the rainy period in Morocco. In addition, there has been a very remarkable reduction in the amount of precipitation over the past decade, which has been reflected by a decrease in the flows recorded at the various gauges. Also, the magnitude of floods varies from one sub-basin to another. Indeed, the Aguibat Ezziar basin (3,640 km2) receives significant amounts of precipitation, sometimes exceeding 80 mm/day, which has generated very immense floods whose flow exceeds 1,300 m3/s (events 1, 5, and 6). The neighboring sub-basin, Ras lFathia (2,100 km2), is marked also by significant flows, but less pronounced compared to the Aguibat Ezziar sub-basin. The peak flows recorded varied from 400 to 883 m3/s. The small SM Cherif and Ain Loudah sub-basins are marked by modest events, which rarely exceed 200 m3/s with a low base flow (less than 20 m3/s at the start of the events). The variation in the flood extent recorded at the various sub-basins is mainly due to the amounts of precipitation received by these different sub-basins, which depend to the area surface and the climatic context, and its physiographical characteristics namely the land use, the soil types, the altitude, and the slopes. Furthermore, the amount of precipitation having generated event 1, in the Aguibat Ezziar sub-basin, is slightly greater than that relating to event 5. However, the peak flow of the latter is greater than that of the former (event 1). This can be explained, on the one hand, by the variation in the soil moisture at the start of each event, and by the rain intensity corresponding to the various events, on the other hand. The same explanation can be granted to events 4 and 7 of the Ras Lfathia sub-basin.

Table 2

Sample events characteristics used for calibration and validation of the model

Sub-basinsEventsBaseflow (m3/s)Date of StartDate of endDuration (h)Peak flow (m3/s)Peak timeTotal rainfall (mm)
Aguibat Ezziar AZ 1 84 23/12/2009
20:00 
26/12/2009
14:00 
66 1,347 25/12/2009
06:00 
86.5 
AZ 3 142 20/02/2010
20:00 
23/02/2010
02:00 
54 1,187 22/02/2010
03:00 
81.27 
AZ 5 123 09/03/2010
02:00 
11/03/2010
05:00 
51 1,574 09/03/2010
16:00 
80.8 
AZ 6 32 29/11/2010
21:00 
02/12/2010
12:00 
63 1,771 01/12/2010
04:00 
92 
AZ 7 6.7 30/10/2012
07:00 
03/11/2012
12:00 
97 866 01/11/2012
14:00 
56 
AZ 9 26 13/03/2013
12:00 
16/03/2013
08:00 
68 852 14/03/2013
14:00 
60.7 
Ras El Fathia RE 1 54 24/12/2009
03:00 
26/12/2009
06:00 
51 710 25/12/2009
02:00 
51 
RE 2 70 21/02/2010
06:00 
23/02/2010
20:00 
62 850 22/02/2010
09:00 
53 
RE 4 51 29/11/2010
20:00 
02/12/2010
23:00 
75 883 30/11/2010
22:00 
69.9 
RE 7 59 30/10/2012
12:00 
02/11/2012
23:00 
83 813 01/11/2012
08:00 
77.33 
RE 8 15 06/03/2013
01:00 
08/03/2013
17:00 
64 400 06/03/2013
22:00 
42 
RE 10 9,9 27/11/2014
23:00 
30/11/2014
18:00 
64 697 29/11/2014
01:00 
50 
S. M. Cherif SM 1 12 23/12/2009
12:00 
25/12/2009
18:00 
42 201 24/12/2009
09:00 
54.8 
SM 2 18 07/01/2010
07:00 
09/01/2010
06:00 
47 105 07/01/2010
21:00 
40 
SM 4 19.2 20/02/2010
18:00 
22/02/2010
23:00 
53 193 21/02/2010
12:00 
37.4 
SM 5 7.7 08/03/2010
18:00 
10/03/2010
07:00 
37 216 09/03/2010
07:00 
34 
SM 7 8.2 30/11/2010
01:00 
01/12/2010
23:00 
46 96.5 30/11/2010
20:00 
26.4 
SM 9 7.5 30/11/2012
20:00 
02/12/2012
21:00 
49 80,8 01/12/2012
12:00 
26.5 
Ain Loudah AL 1 19 23/12/2009
10:00 
25/12/2009
23:00 
61 128 24/12/2009
12:00 
40.4 
AL 4 14.6 16/02/2010
08:00 
18/02/2010
20:00 
60 207 17/02/2010
23:00 
37.34 
AL 5 10.4 08/03/2010
18:00 
10/03/2010
12:00 
42 140 09/03/2010
08:00 
32 
AL 7 3.5 29/11/2010
18:00 
01/12/2010
22:00 
52 75 30/11/2010
21:00 
24.8 
AL 8 8.1 30/10/2012
19:00 
01/11/2012
12:00 
41 99,8 31/10/2012
18:00 
29.7 
AL 10 2.1 29/11/2014
21:00 
01/12/2014
23:00 
50 53,6 30/11/2014
22:00 
26.1 
Sub-basinsEventsBaseflow (m3/s)Date of StartDate of endDuration (h)Peak flow (m3/s)Peak timeTotal rainfall (mm)
Aguibat Ezziar AZ 1 84 23/12/2009
20:00 
26/12/2009
14:00 
66 1,347 25/12/2009
06:00 
86.5 
AZ 3 142 20/02/2010
20:00 
23/02/2010
02:00 
54 1,187 22/02/2010
03:00 
81.27 
AZ 5 123 09/03/2010
02:00 
11/03/2010
05:00 
51 1,574 09/03/2010
16:00 
80.8 
AZ 6 32 29/11/2010
21:00 
02/12/2010
12:00 
63 1,771 01/12/2010
04:00 
92 
AZ 7 6.7 30/10/2012
07:00 
03/11/2012
12:00 
97 866 01/11/2012
14:00 
56 
AZ 9 26 13/03/2013
12:00 
16/03/2013
08:00 
68 852 14/03/2013
14:00 
60.7 
Ras El Fathia RE 1 54 24/12/2009
03:00 
26/12/2009
06:00 
51 710 25/12/2009
02:00 
51 
RE 2 70 21/02/2010
06:00 
23/02/2010
20:00 
62 850 22/02/2010
09:00 
53 
RE 4 51 29/11/2010
20:00 
02/12/2010
23:00 
75 883 30/11/2010
22:00 
69.9 
RE 7 59 30/10/2012
12:00 
02/11/2012
23:00 
83 813 01/11/2012
08:00 
77.33 
RE 8 15 06/03/2013
01:00 
08/03/2013
17:00 
64 400 06/03/2013
22:00 
42 
RE 10 9,9 27/11/2014
23:00 
30/11/2014
18:00 
64 697 29/11/2014
01:00 
50 
S. M. Cherif SM 1 12 23/12/2009
12:00 
25/12/2009
18:00 
42 201 24/12/2009
09:00 
54.8 
SM 2 18 07/01/2010
07:00 
09/01/2010
06:00 
47 105 07/01/2010
21:00 
40 
SM 4 19.2 20/02/2010
18:00 
22/02/2010
23:00 
53 193 21/02/2010
12:00 
37.4 
SM 5 7.7 08/03/2010
18:00 
10/03/2010
07:00 
37 216 09/03/2010
07:00 
34 
SM 7 8.2 30/11/2010
01:00 
01/12/2010
23:00 
46 96.5 30/11/2010
20:00 
26.4 
SM 9 7.5 30/11/2012
20:00 
02/12/2012
21:00 
49 80,8 01/12/2012
12:00 
26.5 
Ain Loudah AL 1 19 23/12/2009
10:00 
25/12/2009
23:00 
61 128 24/12/2009
12:00 
40.4 
AL 4 14.6 16/02/2010
08:00 
18/02/2010
20:00 
60 207 17/02/2010
23:00 
37.34 
AL 5 10.4 08/03/2010
18:00 
10/03/2010
12:00 
42 140 09/03/2010
08:00 
32 
AL 7 3.5 29/11/2010
18:00 
01/12/2010
22:00 
52 75 30/11/2010
21:00 
24.8 
AL 8 8.1 30/10/2012
19:00 
01/11/2012
12:00 
41 99,8 31/10/2012
18:00 
29.7 
AL 10 2.1 29/11/2014
21:00 
01/12/2014
23:00 
50 53,6 30/11/2014
22:00 
26.1 

Modeling formalism and initial values estimation

The Bouregreg watershed was divided into four sub-basins (Aguibat Ezziar, Ras Lfathia, S.M. Cherif, and Ain Loudah) following the major Bouregreg rivers or tributaries. The basin model in HEC-HMS is set up for each sub-basin using two hydrologic elements: sub-basin and junction. The sub-basin element handles the infiltration loss and rainfall-runoff transformation process. The junction element comprises the observed flow data that is essentially used to compare the observed flow hydrographs with the simulated one. In this study, we opted for a semi-distributed modeling with an hourly time step. HEC-HMS has nine different loss methods, some of which are designed primarily for simulating events, while others are intended for continuous simulation. It also has seven different transformation methods. The Soil Conservation Service Curve Number (SCS CN) has been selected as a loss method. The SCS Unit hydrograph (SCS UH) and the Recession method were chosen as transform model and baseflow respectively. These methods were chosen on the basis of applicability and limitations of each method, availability of data, suitability for the same hydrologic condition, stability, wide acceptability, and well-established researcher recommendations (Tassew et al. 2019).

SCS CN loss method

The CN was estimated for the sub-basins, based on the hydrologic soil group and the land cover type. After determining the required soil and land cover characteristics, the CN was estimated for each unit of the sub-basin, followed by area-weighting for the whole sub-basin. The tables used for computation are found in the Technical Release Number 55. The retained CN values are 81, 83, 78, and 77 for Aguibat Ezziar, Ras Lfathia, S.M. Cherif, and Ain Loudah sub-basins respectively.

SCS UH transform method

Once excess precipitations is known, it is converted to direct runoff. In this study, the SCS UH model was chosen to transform excess precipitation into the runoff. The lag time (Tlag) is the only input for this method. It is the time from the mass center of excess rainfall to the hydrograph peak, and is calculated for each sub-basin based on the time of concentration Tc, as:
(1)
where Tlag and Tc are in minutes. The time of concentration was calculated by the different methods existing in the literature (Almeida et al. 2015; Azizian 2018). Thus, the retained value of the Tc corresponds to the average of the convergent values (Table 3).
Table 3

Representative Tc and Tlag for different sub-basin of the Bouregreg watershed

Sub-basinTc (min)Tlag (min)
Aguibat Ezziar 515 309 
Ras Lfathia 506 304 
S.M. Cherif 166 100 
Ain Loudah 151 91 
Sub-basinTc (min)Tlag (min)
Aguibat Ezziar 515 309 
Ras Lfathia 506 304 
S.M. Cherif 166 100 
Ain Loudah 151 91 

Recession

Baseflow is the flow component that returns to the stream from underground storage and aquifers. Basic flow knowledge is important for modeling the hydrograph recession after the peak flow, as well as for estimating the volume of the flood. The recession method uses an exponentially declining baseflow developed from standard baseflow separation techniques. However, given unavailability of information to assign an initial value for the recession constant (Rc) and the threshold (Td), and their value can be calibrated, a value from literature has been used until calibration of these parameters (Tramblay 2012; Rihane et al. 2019). The recession constant Rc is set at 0.5 and the threshold Td at 0.3. Only the initial baseflow at the beginning of the episode is necessary.

Calibration, validation, and performance evaluation

Before a hydrological model can be considered to have reliable outputs, it needs to be calibrated and validated using observed stream flow. The simulated stream flow must be compared to the observed stream flow to evaluate the goodness of fit and conclude whether the model is able to predict and present credible results. In this work, the model was calibrated using the identified parameters to achieve good fit between the simulated and observed data. The auto-calibration (through optimization trials) tool available in the HEC-HMS model was used for optimizing the estimates of the model parameters. We choose the weighted root mean square error as the objective function in the calibration process, which has the advantage of considering both the magnitude and temporal synchronization of the flood (Moriasi et al. 2007).

Validation aims to expose a calibrated model to a real phenomenon different from that used for calibration, in order to assess its response and its ability to reproduce the hydrograph shape properly, especially the peak flow. In this study, the model validation was done by simulating other events for each sub-basin.

The HEC-HMS model performance evaluation involves assessing the goodness of fit in the observed and simulated stream flow using statistical techniques such as:

  • 1.
    Percentage error in volume (PEV)
    (2)
    where Volo and Vols are the observed and simulated volumes, respectively.
  • 2.
    The Percentage error in peak flow (PEPF)
    (3)
    where Qo(peak) and Qs(peak) are the observed and simulated flows, respectively.
  • 3.
    The coefficient of correlation (R2)
    (4)
    where Oi and Si are the observed and simulated flows at time i, respectively; and, are the average observed and simulated flows during the calibration period, respectively.
  • 4.
    The index of agreement (d)
    (5)
  • 5.
    The Nash-Sutcliffe model efficiency (NSE)
    (6)
  • 6.
    The root mean squared error (RMSE) - standard deviation ratio (RSR)
    (7)

Lower values of RSR indicate a lower RMSE normalized by the standard deviation of the observations, which indicates the appropriateness of the model simulation.

To interpret the results, Tables 4 was used as a guide.

Table 4

General performance ratings for recommended statistics (Moriasi et al. 2007)

Performance RatingPEV (%)PEPF (%)R2/ NSEdRSR
Very good <± 10 <15 0.75–1.0 0.90–1.0 0.0–0.50 
Good ±10 to ±15 15–30 0.65–0.75 0.75–0.90 0.50–0.60 
Satisfactory ±15 to ±25 30–40 0.50–0.65 0.50–0.75 0.60–0.70 
Unsatisfactory >± 25 >40 <0.50 <0.50 >0.70 
Performance RatingPEV (%)PEPF (%)R2/ NSEdRSR
Very good <± 10 <15 0.75–1.0 0.90–1.0 0.0–0.50 
Good ±10 to ±15 15–30 0.65–0.75 0.75–0.90 0.50–0.60 
Satisfactory ±15 to ±25 30–40 0.50–0.65 0.50–0.75 0.60–0.70 
Unsatisfactory >± 25 >40 <0.50 <0.50 >0.70 

Frequency analysis

Frequency analysis is a statistical prediction method consisting of studying the past events to define the probabilities of future appearance (Meylan et al. 2008). Frequency analysis is used, in particular, to estimate the magnitude of the temporal event associated with a return period. To estimate the probability that a hydro-meteorological event will appear, a series of flows or rainfall over a period of observation must be available. Then, the observed series must be sampled to select the maximum values. Subsequently, this analysis consists of looking for the probability law that best fits our data series after comparing different probability laws and the estimation methods using adequacy tests.

Since the simulations will be done at an hourly time step, the creation of a synthetic hourly hyetograph from the daily rainfall is unavoidable. There are several methods that allow the disaggregation of the daily rainfall to the hourly one (Arnaud & Lavabre 2000; Mendoza-Resendiz et al. 2013; Kossieris et al. 2016). The approach adopted in this study has been demonstrated and validated in several basins in Morocco (Hasnaoui et al. 2015; Bennani-Baiti et al. 2017; Elhassnaoui et al. 2019). It consists of creating the maximum annual data over time steps of 1–10 days. Values for return periods of 2–100 years are determined by the Gumbel distribution. Then for each of the return periods, the parameters of Montana are established to obtain IDF curves that allow the calculation of the critical intensity of rainfall according to its duration and its return period using the following equation:
(8)
where I (t, T) indicates the intensity of the rainfall over time t (min) and return period T (years), a (T) and b (T) the parameters of Montana, t the duration of the rainfall (min) and T the return period (years).

To apply this equation for t < 24 hours, it has been necessary to compare the Montana parameters calculated by the approach described above with those obtained from the short-term observed data. This comparison made it possible to calculate the error order and verify the reliability of the chosen approach. Montana parameters thus corrected were used to establish the synthetic hyetograph of the daily rainfall corresponding to each return period. Indeed, this process was established using the Chicago method (proposed by Keifer & Chu 1957), which uses IDF curves and the equations derived from them. The proposed hyetograph is adjusted from two exponential curves, one before and the other after the rainfall point (for more details, see Lopes-da-Silveira (2016) and Elhassnaoui et al. (2019)).

Sensitivity analysis

Sensitivity analysis (SA), the most important component of hydrologic modeling, helps to simplify the complexities and understand the physical processes of complex hydrologic systems in a comprehensive way. The principal aim of SA is to assess the variability of response surface with respect to significant changes in input factors and to prioritize these factors by finding the non-influential factors. This would simplify the complexity of the model either by omitting a few trivial input parameters or by assigning a constant value to them (Devak & Dhanya 2017). Various SA methods exist, which differ in terms of mathematical approaches, assumptions, availability, cost of application, and applicability. The employment of any SA approach depends on the field of application and the definition.

The selected method consists in running the model with the optimized model parameters obtained after calibration and validation. Next, one parameter at a time method was applied: the value of each parameter was varied from −30% to +30% in increments of 10%, keeping all other parameters constant. The output values (simulated volume, peaks, and NSE) were analyzed to determine variation with respect to the initial estimates of the parameters. The elasticity ratio (e) (Wałega et al. 2014) was used to rank the parameters in descending order from most to the least sensitive. Also called the relative sensitivity, e expresses the relative change in the dependent variable with respect to the independent variable. The elasticity ratio is invariant to the dimensions of the variables and is given by the following formula as proposed by (McCuen 2003):
where O and I are the output and the input variables, respectively. A greater elasticity ratio indicates a more highly sensitive variable.

The elaborated hydrological model results showed a reasonable fit between the simulated and observed flow after optimization; the hydrograph shape and timing of peaks matched well, although the model tended to underestimate the peak flow and slightly overestimate the volumes in the majority of events for the overall sub-basins (Figure 2).

Figure 2

Samples of the simulated and observed hydrographs for the Bouregreg basin during calibration.

Figure 2

Samples of the simulated and observed hydrographs for the Bouregreg basin during calibration.

Close modal

During calibration, four parameters have been optimized: Tlag CN Rc, and Td. For the overall sub-basins, the Tlag mean value was increased while the other parameters mean values were decreased. We note that the Rc values for the Ain Loudah sub-basin were slightly increased after the optimization process (Table 5).

Table 5

Optimized model parameters for the various events used in calibration

Sub-basinsEventsTlagCNRcTd
Aguibat Ezziar AZ 1 467.74 70.80 0.47 0.28 
AZ 2 382.20 80.36 0.40 0.21 
AZ 5 313.34 75.35 0.41 0.27 
AZ 9 440.00 64.80 0.45 0.28 
Mean 400.8 72.8 0.43 0.26 
Median 411.1 73.1 0.43 0.28 
Ras El Fathia RE 3 512 78 0.31 0.18 
RE 4 354 75.8 0.47 0.28 
RE 6 420 79.5 0.42 0.18 
RE 7 356 82 0.52 0.33 
RE 10 301 83 0.46 0.25 
Mean 388.6 79.7 0.44 0.24 
Median 356.0 79.5 0.46 0.25 
S. M. Cherif SM 1 120.32 71.12 0.38 0.32 
SM 3 145.26 66.98 0.44 0.35 
SM 4 109.36 72.39 0.5 0.32 
SM 8 132.8 77.31 0.52 0.37 
SM 9 92.3 75.9 0.43 0.25 
Mean 120.0 72.7 0.45 0.32 
Median 120.3 72.4 0.44 0.32 
Ain Loudah AL 2 93.36 72.3 0.63 0.21 
AL 5 123.2 78.64 0.51 0.36 
AL 6 85.69 79.35 0.62 0.29 
AL 8 106.25 75.7 0.52 0.3 
AL 10 134.3 78.6 0.59 0.31 
Mean 108.6 76.9 0.57 0.29 
Median 106.3 78.6 0.59 0.30 
Sub-basinsEventsTlagCNRcTd
Aguibat Ezziar AZ 1 467.74 70.80 0.47 0.28 
AZ 2 382.20 80.36 0.40 0.21 
AZ 5 313.34 75.35 0.41 0.27 
AZ 9 440.00 64.80 0.45 0.28 
Mean 400.8 72.8 0.43 0.26 
Median 411.1 73.1 0.43 0.28 
Ras El Fathia RE 3 512 78 0.31 0.18 
RE 4 354 75.8 0.47 0.28 
RE 6 420 79.5 0.42 0.18 
RE 7 356 82 0.52 0.33 
RE 10 301 83 0.46 0.25 
Mean 388.6 79.7 0.44 0.24 
Median 356.0 79.5 0.46 0.25 
S. M. Cherif SM 1 120.32 71.12 0.38 0.32 
SM 3 145.26 66.98 0.44 0.35 
SM 4 109.36 72.39 0.5 0.32 
SM 8 132.8 77.31 0.52 0.37 
SM 9 92.3 75.9 0.43 0.25 
Mean 120.0 72.7 0.45 0.32 
Median 120.3 72.4 0.44 0.32 
Ain Loudah AL 2 93.36 72.3 0.63 0.21 
AL 5 123.2 78.64 0.51 0.36 
AL 6 85.69 79.35 0.62 0.29 
AL 8 106.25 75.7 0.52 0.3 
AL 10 134.3 78.6 0.59 0.31 
Mean 108.6 76.9 0.57 0.29 
Median 106.3 78.6 0.59 0.30 

Figure 2 show that the selected events, for the calibration, are marked by an acute peak, materialized by a subvertical rising limb corresponding to a very short rising time and generally a short falling time as well. This can be explained by the significant slope characterizing the studied basin as well as the intensity of the rains that generated these floods. We also note the existence of some events with two peaks (RE 3 & SM1), which can be reflected by the occurrence of two successive rainfall episodes. In addition, the importance of the flood's events in term of peak and volume depends on the extent of each sub-basin, as indicated previously.

Model performance evaluation was conducted for each event. The time series of simulated and observed flows from the results of the simulation run in the HEC-HMS model were analyzed in Microsoft Excel to compute the statistics used for performance evaluation. Table 6 and Figure 3 show the performance evaluation results during the calibration for the different studied sub-basins. According to the simulation’s results for the Aguibat Ezziar sub-basin, and based on the mean values of PEV, PEPF, R2, d, NSE, and RSR calculated, the model performance is evaluated as good to very good. Indeed, the PEV ranges from −15.96 to −11.89, the PEPF ranges from 9.03 to 28.39 depending on the different events, the NSE and the R2 ranges from 0.71 to 0.87, which indicate a good model performance. As for the Ras El Fathia sub-basin, the performance rating of the PEV and PEPF criteria was improved. However, the NSE and R2 criteria, for which the mean values are 0.71 and 0.74, respectively, are slightly decreased compared with the first sub-basin. Nevertheless, the performance evaluation is still good. As for the S. M. Cherif and Ain Loudah sub-basins, we can judge that the simulated hydrologic response is similar for those sub-basins. This is justified by the common physiographic characteristics and the climatic context, as well as the chosen modeling formalism, which is almost identical for the two basins. the mean values of PEV, PEPF, R2, d, NSE, and RSR were found to be −1.32%, 11.21%, 0.67, 0.89, 0.64 and 0.61, respectively for S. M. Cherif, and −2.55%, 12.68%, 0.80, 0.93, 0.72, and 0.49, respectively, for Ain Loudah. The model performances are also good to very good. We note that the NSE and R2 for the event SM 1 was unsatisfactory. This was due to the limited capability of the model to simulate an event with two peaks. Nevertheless, the mean values reflect a good fit between the simulated and observed flow.

Table 6

Performance evaluation of the developed event-based model during calibration

Sub-basinsEventsPEVPEPFR2dNSERSR
Aguibat Ezziar AZ 1 −15.96 9.03 0.81 0.93 0.78 0.54 
AZ 2 −12.7 16.82 0.71 0.88 0.68 0.58 
AZ 5 −14.3 28.39 0.87 0.96 0.84 0.4 
AZ 9 −11.89 24.58 0.85 0.96 0.83 0.41 
Mean −13.71 19.71 0.81 0.93 0.78 0.48 
Median −13.5 20.7 0.83 0.95 0.805 0.48 
Ras El Fathia RE 3 −10.58 15.42 0.69 0.91 0.65 0.6 
RE 4 −14.89 −24.7 0.68 0.9 0.62 0.62 
RE 6 −8.56 18.36 0.71 0.91 0.72 0.52 
RE 7 6.41 24.42 0.8 0.94 0.79 0.46 
RE 10 −25.8 16.33 0.82 0.93 0.77 0.48 
Mean −10.68 9.97 0.74 0.92 0.71 0.54 
Median −10.58 16.33 0.71 0.91 0.72 0.52 
S. M. Cherif SM 1 4.93 8.31 0.49 0.83 0.42 0.76 
SM 3 −12.52 15.39 0.61 0.86 0.58 0.7 
SM 4 10.87 18.03 0.75 0.92 0.73 0.52 
SM 8 −8.36 12.33 0.69 0.89 0.67 0.62 
SM 9 −1.52 1.98 0.82 0.95 0.82 0.43 
Mean −1.32 11.21 0.67 0.89 0.64 0.61 
Median −1.52 12.33 0.69 0.89 0.67 0.62 
Ain Loudah AL 2 −4.92 24.22 0.71 0.91 0.7 0.5 
AL 5 −2.37 −4.79 0.88 0.93 0.61 0.62 
AL 6 −14.62 12.35 0.72 0.91 0.71 0.5 
AL 8 11.55 31.06 0.76 0.92 0.64 0.6 
AL 10 −2.41 0.56 0.95 0.99 0.96 0.21 
Mean −2.55 12.68 0.80 0.93 0.72 0.49 
Median −2.41 12.35 0.76 0.92 0.7 0.5 
Mean −7.07 13.39 0.76 0.92 0.72 0.53 
Median −6.50 14.34 0.74 0.92 0.71 0.51 
Sub-basinsEventsPEVPEPFR2dNSERSR
Aguibat Ezziar AZ 1 −15.96 9.03 0.81 0.93 0.78 0.54 
AZ 2 −12.7 16.82 0.71 0.88 0.68 0.58 
AZ 5 −14.3 28.39 0.87 0.96 0.84 0.4 
AZ 9 −11.89 24.58 0.85 0.96 0.83 0.41 
Mean −13.71 19.71 0.81 0.93 0.78 0.48 
Median −13.5 20.7 0.83 0.95 0.805 0.48 
Ras El Fathia RE 3 −10.58 15.42 0.69 0.91 0.65 0.6 
RE 4 −14.89 −24.7 0.68 0.9 0.62 0.62 
RE 6 −8.56 18.36 0.71 0.91 0.72 0.52 
RE 7 6.41 24.42 0.8 0.94 0.79 0.46 
RE 10 −25.8 16.33 0.82 0.93 0.77 0.48 
Mean −10.68 9.97 0.74 0.92 0.71 0.54 
Median −10.58 16.33 0.71 0.91 0.72 0.52 
S. M. Cherif SM 1 4.93 8.31 0.49 0.83 0.42 0.76 
SM 3 −12.52 15.39 0.61 0.86 0.58 0.7 
SM 4 10.87 18.03 0.75 0.92 0.73 0.52 
SM 8 −8.36 12.33 0.69 0.89 0.67 0.62 
SM 9 −1.52 1.98 0.82 0.95 0.82 0.43 
Mean −1.32 11.21 0.67 0.89 0.64 0.61 
Median −1.52 12.33 0.69 0.89 0.67 0.62 
Ain Loudah AL 2 −4.92 24.22 0.71 0.91 0.7 0.5 
AL 5 −2.37 −4.79 0.88 0.93 0.61 0.62 
AL 6 −14.62 12.35 0.72 0.91 0.71 0.5 
AL 8 11.55 31.06 0.76 0.92 0.64 0.6 
AL 10 −2.41 0.56 0.95 0.99 0.96 0.21 
Mean −2.55 12.68 0.80 0.93 0.72 0.49 
Median −2.41 12.35 0.76 0.92 0.7 0.5 
Mean −7.07 13.39 0.76 0.92 0.72 0.53 
Median −6.50 14.34 0.74 0.92 0.71 0.51 
Figure 3

Correlation between observed and simulated flow during calibration.

Figure 3

Correlation between observed and simulated flow during calibration.

Close modal

After having successfully calibrated the model, four or five different events were selected to validate the model, considering the mean of the optimized parameters as shown in Table 5. In general, the performance of the model in validation is slightly degraded compared to the calibration performance. The results nevertheless remain satisfactory. Figures 4 and 5 showed the simulated and observed hydrographs and their correlation respectively.

Figure 4

Samples of the simulated and observed hydrographs for the Bouregreg basin during validation.

Figure 4

Samples of the simulated and observed hydrographs for the Bouregreg basin during validation.

Close modal
Figure 5

Correlation between observed and simulated flow during validation.

Figure 5

Correlation between observed and simulated flow during validation.

Close modal

The result showed that the simulated values are close to the observed ones for all the events. This was be confirmed by the performance criteria evaluation as shown in Table 7. Indeed, the mean values, for the Aguibat Ezziar sub-basin, of PEV, PEPF, R2, d, NSE, and RSR were found to be −15.36%, 30.46%, 0.64, 0.86, 0.61, and 0.62, respectively. The performance rating is generally satisfactory to good. Similarly for the Ras El Fathia sub-basin, the performance evaluation results are also satisfactory to good, except the events RE2 and RE9, for which the PEV and NSE evaluation is unsatisfactory. Concerning the S. M. Cherif and Ain Loudah sub-basins, the PEV is evaluated as very good and the performance rating of the other criteria is good in general. This can be explained by the small area surface of those sub-basins comparing to the Aguibat Ezziar and Ras El Fathia sub-basins.

Table 7

Performance evaluation of the developed event-based model during validation

Sub-basinsEventsPEVPEPFR2dNSERSR
Aguibat Ezziar AZ 3 −4.21 24.89 0.79 0.94 0.79 0.46 
AZ 4 −25.63 28.3 0.58 0.81 0.52 0.7 
AZ 6 −22.26 30.09 0.61 0.84 0.56 0.67 
AZ 7 −0.38 31.66 0.60 0.86 0.60 0.63 
AZ 8 −24.32 37.36 0.61 0.84 0.57 0.67 
Mean −15.36 30.46 0.64 0.86 0.61 0.62 
Median −22.26 30.09 0.61 0.84 0.57 0.67 
Ras El Fathia RE 1 0.27 29.06 0.68 0.90 0.68 0.57 
RE 2 −38.76 6.68 0.72 0.85 0.43 0.75 
RE 5 −26.32 18.71 0.63 0.87 0.6 0.62 
RE 8 17.83 27.68 0.60 0.84 0.55 0.67 
RE 9 −30.68 15.32 0.54 0.82 0.52 0.71 
Mean −15.53 19.49 0.63 0.85 0.55 0.67 
Median −26.32 18.71 0.63 0.85 0.55 0.67 
S. M. Cherif SM 2 6.33 3.81 0.66 0.88 0.44 0.75 
SM 5 −7.74 21.34 0.79 0.92 0.77 0.48 
SM 6 −12.65 28.52 0.58 0.85 0.57 0.67 
SM7 9.81 24.27 0.62 0.87 0.61 0.63 
Mean −1.06 19.49 0.66 0.88 0.59 0.63 
Median −0.71 22.81 0.64 0.87 0.59 0.65 
Ain Loudah AL 1 9.48 19.38 0.79 0.93 0.73 0.52 
AL 3 −11.63 17.38 0.71 0.83 0.68 0.55 
AL 4 22.04 37.25 0.74 0.86 0.59 0.64 
AL 7 14.12 8.80 0.84 0.94 0.72 0.53 
AL 9 −5.63 28.32 0.68 0.82 0.65 0.56 
Mean 5.67 22.22 0.75 0.87 0.68 0.56 
Median 9.48 19.38 0.74 0.86 0.68 0.55 
Mean −6.57 22.91 0.67 0.87 0.61 0.62 
Median −11.49 21.09 0.64 0.85 0.58 0.66 
Sub-basinsEventsPEVPEPFR2dNSERSR
Aguibat Ezziar AZ 3 −4.21 24.89 0.79 0.94 0.79 0.46 
AZ 4 −25.63 28.3 0.58 0.81 0.52 0.7 
AZ 6 −22.26 30.09 0.61 0.84 0.56 0.67 
AZ 7 −0.38 31.66 0.60 0.86 0.60 0.63 
AZ 8 −24.32 37.36 0.61 0.84 0.57 0.67 
Mean −15.36 30.46 0.64 0.86 0.61 0.62 
Median −22.26 30.09 0.61 0.84 0.57 0.67 
Ras El Fathia RE 1 0.27 29.06 0.68 0.90 0.68 0.57 
RE 2 −38.76 6.68 0.72 0.85 0.43 0.75 
RE 5 −26.32 18.71 0.63 0.87 0.6 0.62 
RE 8 17.83 27.68 0.60 0.84 0.55 0.67 
RE 9 −30.68 15.32 0.54 0.82 0.52 0.71 
Mean −15.53 19.49 0.63 0.85 0.55 0.67 
Median −26.32 18.71 0.63 0.85 0.55 0.67 
S. M. Cherif SM 2 6.33 3.81 0.66 0.88 0.44 0.75 
SM 5 −7.74 21.34 0.79 0.92 0.77 0.48 
SM 6 −12.65 28.52 0.58 0.85 0.57 0.67 
SM7 9.81 24.27 0.62 0.87 0.61 0.63 
Mean −1.06 19.49 0.66 0.88 0.59 0.63 
Median −0.71 22.81 0.64 0.87 0.59 0.65 
Ain Loudah AL 1 9.48 19.38 0.79 0.93 0.73 0.52 
AL 3 −11.63 17.38 0.71 0.83 0.68 0.55 
AL 4 22.04 37.25 0.74 0.86 0.59 0.64 
AL 7 14.12 8.80 0.84 0.94 0.72 0.53 
AL 9 −5.63 28.32 0.68 0.82 0.65 0.56 
Mean 5.67 22.22 0.75 0.87 0.68 0.56 
Median 9.48 19.38 0.74 0.86 0.68 0.55 
Mean −6.57 22.91 0.67 0.87 0.61 0.62 
Median −11.49 21.09 0.64 0.85 0.58 0.66 

Frequency analysis of the daily maximum rainfall annual series was carried out using the data from the rainfall stations inside the studied basin. Statistical adjustment of the data was made by applying the five laws, usually used in frequency analysis of maximum daily rainfall, namely the generalized extreme value (GEV), Gumbel, normal law, lognormal with three parameters, and the Pearson Type III (according to Habibi et al. 2013). Applying the homogeneity, stationarity, and independence tests, Gumbel's law showed a good adjustment to the maximum daily rainfall series of the SMBA dam watershed.

After having computing the frequency rainfall from the various stations for the studied basin (Table 8), we have established the representative synthetic hourly hyetograph of each sub-basin for different return period. The rainfall-runoff simulations have been carried out on the basis of the already elaborated event-based hydrological models. The results show the extent of the floods received by the SMBA dam (Table 9 and Figure 6). Indeed, the peak flow rises from 1,092 m3/s for the return period T2 to 6,097 m3/s for T100. The volumes are also important, they vary between 80 and 438.5 Mm3, according to the return periods.

Table 8

Rainfall depth corresponding to different return periods

Sub-basinsReturn periods (T)
10050201052
Aguibat Ezziar 73.3 67.7 60 53.8 47 36 
Ras Elfathia 64.2 58.5 50.9 45 38.8 29.3 
S. M. Cherif 68.3 62.1 53.9 47.4 40.7 30.4 
Ain Loudah 66.4 60.8 53.3 47.4 41.1 31.2 
Intermediate 59.8 55.2 48.9 43.9 38.4 29.7 
Sub-basinsReturn periods (T)
10050201052
Aguibat Ezziar 73.3 67.7 60 53.8 47 36 
Ras Elfathia 64.2 58.5 50.9 45 38.8 29.3 
S. M. Cherif 68.3 62.1 53.9 47.4 40.7 30.4 
Ain Loudah 66.4 60.8 53.3 47.4 41.1 31.2 
Intermediate 59.8 55.2 48.9 43.9 38.4 29.7 
Table 9

Peak flow and total volume of the frequency floods in the studied basin

Studied basinsT100
T50
T20
T10
T5
T2
PVPVPVPVPVPV
SMBA dam 6.097 438.5 5.053 364.6 3.871 277.6 3.056 219.5 2.233 161 1.092 80 
Studied basinsT100
T50
T20
T10
T5
T2
PVPVPVPVPVPV
SMBA dam 6.097 438.5 5.053 364.6 3.871 277.6 3.056 219.5 2.233 161 1.092 80 

P. Peak flow. V. Total volume.

Figure 6

Frequency flood hydrographs of the SMBA dam watershed.

Figure 6

Frequency flood hydrographs of the SMBA dam watershed.

Close modal

Sensitivity analysis was carried out in order to determine the sensitivity of the error in volume, the computed peak, and the NSE criterion to the model parameters, namely Tlag, CN, Rc, and the Td (Figure 7). The runoff volume was found to be more sensitive to and CN, respectively. While the peak flow was found to be more sensitive to CN and Tlag, respectively. At the same time, the NSE was found to be more sensitive to Tlag and CN. (Table 10). Rc and Td were found to be the least sensitive parameters.

Table 10

The model parameters sensitivity ranking for volume. peak, and NSE

ParametersVolumePeakNSE
Tlag 0.43 0.44 0.17 
CN 0.55 0.25 0.17 
Rc 0.15 0.14 0.14 
Td 0.15 0.16 0.16 
ParametersVolumePeakNSE
Tlag 0.43 0.44 0.17 
CN 0.55 0.25 0.17 
Rc 0.15 0.14 0.14 
Td 0.15 0.16 0.16 
Figure 7

Percentage changes in simulated peak (a), volume (b), and NSE (c) plotted against the percentage variation of each parameter.

Figure 7

Percentage changes in simulated peak (a), volume (b), and NSE (c) plotted against the percentage variation of each parameter.

Close modal

Flood forecasting has become a priority task, especially in a global context influenced by climate change. Knowledge of the extent of the floods is very needed for dam management. Understanding the rainfall-runoff mechanism in a given dam watershed allows improving the management of this reservoir and protecting the downstream against floods.

This paper presents a flood modeling application in the SMBA dam watershed, using the HEC-HMS modeling platform. The event-based models that have been developed make it possible to reproduce, with a reduced number of parameters, the floods in the four main Bouregreg sub-basins and the hydrographs of the frequency of floods entering the SMBA dam. The results show that it is possible to estimate the volumes of water generated during floods satisfactorily with errors of the order of 6–11%, while the error in peak flow is around 20%. The median NSE during validation is 0.58% and the R2 is about 0.67. Sensitivity analysis shows that the runoff volume, the peak flow, and the NSE were found to be more sensitive to Tlag and CN parameters, while the Rc and Td were found to be the least sensitive parameters.

The model could thus operate in real time, fed by data from the stations transmitted to the concentrator station. Such a tool would make it possible to anticipate the hydrological response of the basin during precipitation, with an anticipation time of the order of 10–12 hours, after a rainy episode. Thus, the management of the dam would be improved, making it possible both to maximize the filling of the reservoir and to minimize the risks of spills and flooding downstream.

This hydrological modeling could also be supplemented by hydraulic modeling downstream of the dam to develop floodplain scenarios for different volumes of releases at the SMBA dam.

The authors thank the Water Research and Planning Directorate (Morocco) and the Hydraulic Basin Agency of Bouregreg-Chaouia for data acquisition.

The authors declare no conflict of interest.

Data cannot be made publicly available; readers should contact the corresponding author for details.

Ahbari
A.
,
Stour
L.
,
Agoumi
A.
&
Serhir
N.
2018
Sensitivity of the HMS model to various modelling characteristics: case study of Bin El Ouidane basin (High Atlas of Morocco)
.
Arabian Journal of Geosciences
11
(
18
).
doi:10.1007/s12517-018-3911-x
.
Almeida
I. K.
,
Kaufmann
A. A.
,
Anache
J. A. A.
&
Steffen
J. L.
2015
Estimation on time of concentration of overland flow in watersheds
.
Geociencias
33
(
4
),
661
671
.
Arnaud
P.
&
Lavabre
J.
2000
La modélisation stochastique des pluies horaires et leur transformation en débits pour la prédétermination des crues
.
Journal of Water Science
13
(
4
),
441
462
.
doi:10.7202/705402ar
.
Azizian
A.
2018
Uncertainty analysis of time of concentration equations based on first-order-analysis (FOA) method
.
American Journal of Engineering and Applied Sciences
11
(
1
),
327
341
.
doi:10.3844/ajeassp.2018.327.341
.
Bennani-Baiti
H.
,
Bouziane
A.
,
Ouazar
D.
&
Hasnaoui
M. D.
2017
Storm water management model sensitivity to different design storm types and parameters: the case of tangier experimental Basin, Morocco
.
Journal of Sustainable Watershed Science & Management
,
130
142
.
doi:10.5147/jswsm.2017.0159
.
Chu
X.
&
Steinman
A.
2009
Event and continuous hydrologic modeling with HEC-HMS
.
Journal of Irrigation and Drainage
135
,
119
124
.
https://doi.org/10.1061/(ASCE)0733-9437(2009)135:1(119)
.
De Silva
M. M. G. T.
,
Weerakoon
S. B.
&
Herath
S.
2014
Modeling of event and continuous flow hydrographs with HEC–HMS: case study in the Kelani River Basin, Sri Lanka
.
Journal of Hydrologic Engineering
19
(
4
),
800
806
.
doi:10.1061/(asce)he.1943-5584.0000846
.
Devak
M.
&
Dhanya
C. T.
2017
Sensitivity analysis of hydrological models: review and way forward
.
Journal of Water and Climate Change
8
(
4
),
557
575
.
doi:10.2166/wcc.2017.149
.
Elhassnaoui
I.
,
Moumen
Z.
,
Serrari
I.
,
Bouziane
A.
,
Ouazar
D.
&
Hasnaoui
M. D.
2019
Generation of synthetic design storm hyetograph and hydrologic modeling under HEC HMS for Ziz watershed
.
International Journal of Innovative Technology and Exploring Engineering (IJITEE)
8
(
10
),
2278
3075
.
doi:10.35940/ijitee.J1214.0881019
.
Habibi
B.
,
Meddi
M.
&
Boucefiane
A.
2013
Analyse fréquentielle des pluies journalières maximales Cas du Bassi Chott-Chergui
.
Nature & Technologie, C- Sciences de L'Environnement
08
,
41
48
.
Hasnaoui
M. D.
,
Bouziane
A.
,
Ouazar
D.
,
Alaoui
M.
,
Boudaoud
Y.
&
Hadine
A.
2015
Modélisation de l'impact de la collecte des eaux pluviales sur l'atténuation des crues dans le bassin du Bouskoura et perspectives d'adaptation au changement climatique
.
La Houille Blanche
01
,
56
62
.
doi:10.1051/lhb/2015007
.
Jia
Y.
,
Zhao
H.
,
Niu
C.
,
Jiang
Y.
,
Gan
H.
,
Xing
Z.
&
Zhao
Z. A.
2009
WebGIS-based system for rainfall-runoff prediction and real-time water resources assessment for Beijing
.
Computers & Geosciences
35
,
1517
1528
.
doi:10.1016/j.cageo.2008.10.004
.
Joo
J.
,
Kjeldsen
T.
,
Kim
H. J.
&
Lee
H.
2013
A comparison of two event-based flood models (ReFH-rainfall runoff model and HEC-HMS) at two Korean catchments, Bukil and Jeungpyeong
.
KSCE Journal of Civil Engineering
18
(
1
),
330
343
.
doi:10.1007/s12205-013-0348-3
.
Katwal
R.
,
Li
J.
,
Zhang
T.
,
Hu
C.
,
Rafique
M. A.
&
Zheng
Y.
2021
Event-based and continous flood modeling in Zijinguan watershed, Northern China
.
Natural Hazards
108
(
1
),
733
753
.
doi:10.1007/s11069-021-04703-y
.
Keifer
C. J.
&
Chu
H. H.
1957
Synthetic storm pattern for drainage design
.
Journal of the Hydraulics Division
83
(
4
),
1
25
.
https://doi.org/10.1061/JYCEAJ.0000104
.
Khaddor
I.
,
Achab
M. A.
&
Alaoui
H.
2016
Hydrological simulation (Rainfall-Runoff) of Kalaya watershed (Tangier, Morocco) using Geo-spatial tools
.
Journal of Water Sciences & Environment Technologies
01
,
10
14
.
Khattati
M.
,
Serroukh
M.
,
Rafik
I.
,
Mesmoudi
H.
,
Hassane
B.
&
Bouslihim
Y.
2016
Hydrological modelling of Sidi Jabeur watershed (Morocco) using spatially distributed model ATHYS
.
Journal of Geoscience and Environment Protection
4
,
77
83
.
doi:10.4236/gep.2016.41009
.
Kossieris
P.
,
Makropoulos
C.
,
Onof
C.
&
Koutsoyiannis
D.
2016
A rainfall disaggregation scheme for sub-hourly time scales: coupling a Bartlett-Lewis based model with adjusting procedures
.
Journal of Hydrology
556
,
980
992
.
https://doi.org/10.1016/j.jhydrol.2016.07.015
.
Laassilia
O.
,
Ouazar
D.
,
Bouziane
A.
&
Driss Hasnaoui
M. D.
2019
Particle swarm optimization applied to multi-reservoir operating policy in inter-basin water transfer system, 2019
. In
5th International Conference on Optimization and Applications (ICOA)
. pp.
1
5
,
doi:10.1109/ICOA.2019.8727645
.
Laassilia
O.
,
Ouazar
D.
,
Bouziane
A.
&
Driss Hasnaoui
M. D.
2021
Estimation of excess water in the Sebou basin for an interbasin water transfer
.
Journal of Applied Water Engineering and Research
9
(
1
),
69
87
.
doi:10.1080/23249676.2021.1884616
.
Liu
K.
,
Wang
Z.
,
Cheng
L.
,
Zhang
L.
,
Du
H.
&
Tan
L.
2019
Optimal operation of interbasin water transfer multireservoir systems: an empirical analysis from China
.
Environmental Earth Sciences
78
(
7
).
doi:10.1007/s12665-019-8242-z
.
Lopes da Silveira
A. L.
2016
Cumulative equations for continuous time Chicago hyetograph method
.
Brazilian Journal of Water Ressources
21
(
3
).
http://dx.doi.org/10.1590/2318-0331.011615094
.
Luo
M.
,
Liu
T.
,
Meng
F.
,
Duan
Y.
,
Bao
A.
,
Xing
W.
&
Frankl
A.
2019
Identifying climate change impacts on water resources in Xinjiang, China
.
Science of The Total Environment
.
doi:10.1016/j.scitotenv.2019.04.2
.
McCuen
R. H.
2003
Modeling Hydrologic Change, Statistical Methods
.
CRC Press Company, Ed.; Lewis Publishers
,
Boca Raton, FL
,
USA
.
Mendoza-Resendiz
A.
,
Arganis-Juarez
M.
,
Dominguez-Mora
R.
&
Echavarria
B.
2013
Method for generating spatial and temporal synthetic hourly rainfall in the Valley of Mexico
.
Atmospheric Research
133
,
411
422
.
Meylan
P.
,
Favre
A. C.
&
Musy
A.
2008
Hydrologie fréquentielle: une science prédictive
.
Science et ingénierie de l'environnement
,
France
.
Moriasi
D. N.
,
Arnold
J. G.
,
Van Liew
M. W.
,
Bingner
R. L.
,
Harmel
R. D.
&
Veith
T. L.
2007
Model evaluation guidelines for systematic quantification of accuracy in watershed simulations
.
American Society of Agricultural and Biological Engineers
50
(
3
),
885
900
.
ISSN 0001−2351
.
Natarajan
S.
&
Radhakrishnan
N.
2019
Simulation of extreme event-based rainfall–runoff process of an urban catchment area using HEC-HMS
.
Modeling Earth Systems and Environment
5
(
4
),
1867
1881
.
doi:10.1007/s40808-019-00644-5
.
Ramly
S.
&
Tahir
W.
2016
Application of HEC-GeoHMS and HEC-HMS as rainfall–runoff model for flood simulation
. In:
ISFRAM 2015
.
Springer
,
Singapore
.
https://doi.org/10.1007/978-981-10-0500-8_15
.
Rihane
R.
,
Khattabi
A.
,
Rifai
N.
&
Lahssini
S.
2019
Modeling hydrological functioning of a drainage basin with relation to land use change in the context of climate change: ourika watershed case study
. In:
Geospatial Technologies for Effective Land Governance
.
doi:10.4018/978-1-5225-5939-9.ch012
.
Şen
Z.
2021
Reservoirs for water supply under climate change impact – a review
.
Water Resources Management
.
doi:10.1007/s11269-021-02925-0
.
Tassew
B. G.
,
Belete
M. A.
&
Miegel
K.
2019
Application of HEC-HMS model for flow simulation in the Lake Tana Basin: the case of Gilgel Abay catchment, Upper Blue Nile Basin, Ethiopia
.
Journal of Hydrology
6
(
21
),
1
17
.
doi:10.3390/hydrology6010021
.
Tramblay
Y.
2012
Modélisation des crues dans le bassin du barrage Makhazine, Maroc
.
Institut de Recherche pour le Développement Hydrosciences-Montpellier
,
France
.
Wałega
A.
,
Rutkowska
A.
&
Policht-latawiec
A.
2014
Sensitivity of Beta and Weibull synthetic unit hydrographs to input parameter changes
.
Polish Journal of Environmental Studies
2014
(
23
),
221
229
.
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