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Article

Suspended Sediment Load Simulation during Flood Events Using Intelligent Systems: A Case Study on Semiarid Regions of Mediterranean Basin

1
Research Laboratory of Water Resources, Soil and Environment, Department of Civil Engineering, Faculty of Civil Engineering and Architecture, Amar Telidji University, P.O. Box 37.G, Laghouat 03000, Algeria
2
Vegetable Chemistry-Water-Energy Research Laboratory, Faculty of Civil Engineering and Architecture, Hassiba Benbouali, University of Chlef, B.P. 78C, Ouled Fares, Chlef 02180, Algeria
3
Department of Civil Engineering, College of Engineering, Taif University, Taif 21944, Saudi Arabia
4
Department of Civil and Environmental Engineering, Federal University of Paraíba, João Pessoa 58051-900, Brazil
5
Water Research Center, P.O. Box 74, Shubra El-Kheima 13411, Egypt
*
Authors to whom correspondence should be addressed.
Water 2021, 13(24), 3539; https://doi.org/10.3390/w13243539
Submission received: 14 November 2021 / Revised: 6 December 2021 / Accepted: 8 December 2021 / Published: 10 December 2021

Abstract

:
Sediment transport in rivers is a nonlinear natural phenomenon, which can harm the environment and hydraulic structures and is one of the main reasons for the dams’ siltation. In this paper, the following artificial intelligence approaches were used to simulate the suspended sediment load (SSL) during periods of flood events in the northeastern Algerian river basins: artificial neural network combined with particle swarm optimization (ANN-PSO), adaptive neuro-fuzzy inference system combined with particle swarm optimization (ANFIS-PSO), random forest (RF), and long short-term memory (LSTM). The comparison of the prediction accuracies of such different intelligent system approaches revealed that ANN-PSO, RF, and LSTM satisfactorily simulated the nonlinear process of SSL. Carefully comparing the results, the ANN-PSO model showed a slight superiority over the RF and LSTM models, with RMSE = 67.2990 kg/s in the Chemourah basin and RMSE = 55.8737 kg/s in the Gareat el tarf basin.

1. Introduction

Many significant threats to water resources arise primarily from human activities, including pollution, climate change, urbanization, and landscape changes. Each one has specific impacts, and most are often directly on ecosystems with repercussions on water resources [1]. In sedimentology, sediment transport in a river is a nonlinear and complex phenomenon, is more active during flood periods that cause a more significant amount of sediment, and is very varied in space and time. The geological, hydrological, and morphological parameters of a river basin have substantial implications on the sediment activity inside a river [2]. According to Zounemat-Kermani et al. (2016) [3], suspended sediment load (SSL) and bed sediment load (BSL) are the two significant parts of sediment load. Still, the SSL has a complex behavior compared to BSL and can be considered the most crucial part of the sediment load [4]. In hydraulic engineering, before installing hydraulic structures, such as dams and reservoirs, the study and estimation of the volume of sediment transported constitutes an important issue and is of particular interest in the final decision [2,5]. The economic life of a reservoir is expressed through dead storage by the incoming sediments. A poor estimate of the sediment volume results in insufficient dam capacity [5], requiring maintenance and cleaning procedures, such as dredging. However, those procedures are costly and sometimes even exceed the cost of rebuilding the structure itself. Toumi and Remini (2018) [6] highlight an accumulated silt deposit of more than 650,106 m3 in more than 110 Algerian dams. For example, a silt volume equal to 100 million m3 is currently at the bottom of the Sidi M’hamed Ben Aouda dam (Algeria), representing a filling rate equal to 42%. This value places it among the dams most threatened by siltation [7].
Traditionally, the relationship between discharge and sediment concentration, for example, has been based on setting up a simple linear regression model. This linear relationship based on empirical equations does not represent reality due to the spatiotemporal variability of the data; the notable disadvantage of these equations leads to estimates with a considerable margin of error [8]. Although, since the end of the 1980s, this linear relationship seems to be an up-and-coming technique to model the runoff–sediment load relationship to improve water resources infrastructure planning, a new concept of nonlinear empirical and conceptual models based on artificial intelligence seems to constitute an innovative approach to model complex systems [9]. The success of artificial intelligence techniques to model complex systems, since the first use of classical models of artificial neural networks (ANN), has led researchers to develop robust systems. Some examples are the intelligent hybrid systems that combine optimization and probabilistic reasoning techniques, known universally as soft computing [10]. The significant advantage of these systems is reasoning and learning in an imprecise and uncertain environment [11]. In the context of SSL, the following works can be mentioned: [12,13,14,15,16,17,18,19,20,21,22,23,24,25]. Meshram et al. (2019) [25] used the two-phase feed-forward neuron network particle swarm optimization gravitational search algorithm (FNN-PSOGSA), the single-phase feed-forward neuron network particle swarm optimization (FNN-PSO), feed-forward neuron network (FNN), and adaptive neuro-fuzzy inference system (ANFIS) to estimate monthly sediment load. The authors found that the FNN-PSOGSA model was superior to the other models. Kumar et al. (2016) [26] used the machine learning approach for daily SSL simulation in the Kopili River basin (India). The assessment indicates that the least square support vector regression (LS-SVR) and ANN offer more insight than decision tree models such as the M5 model tree and classification and regression tree (CART). Based on ANN, ANFIS, and support vector machine (SVM) models, SSL in the Coruh River (Turkey) was estimated by Buyukyildiz and Kumcu (2017) [19]. Yilmaz et al. (2019) [23] used hybrid artificial intelligence techniques combining ANN with teaching–learning-based optimization (TLBO) and artificial bee colony (ABC) for SSL prediction. The results of ANN-TLBO and ANN-ABC models are more promising than the classical ANN model for SSL prediction. For suspended sediment concentration (SSC) prediction, Kisi and Yaseen (2019) [21] have documented the effectiveness of the hybrid evolutionary fuzzy (EF) intelligence model. The conjunction between subtractive clustering (SC), grid partition (GP), and fuzzy c-means (FCM) models with an adaptive neuro-fuzzy inference system (ANFIS) indicates the high qualification of the proposed models to be a brilliant approach for SSC prediction. Nourani et al. (2019) [22] used a wavelet-based data mining technique for SSL simulation. The different modeling approaches found that the Wavelet-M5 tree model predicts SSL with high reliability compared with Wavelet-ANN (WANN) and M5 tree models. Adnan et al. (2019) [27] used dynamic evolving ANFIS (DENFIS), ANFIS-FCM, and multivariate adaptive regression splines (MARS) for SSL prediction, in Guangyuan and Beibei (China). The comparison between different approaches demonstrates that the DENFIS can be the best approach for the accurate estimation of SSL. Banadkooki et al. (2020) [28] used ANN models based on ant lion optimization (ALO), bat algorithm (BA) and particle swarm optimization (PSO)for SSL prediction. The results indicates that the ANN-ALO improved the accuracy RMSE of the ANN-BA and ANN-PSO models by 18% and 26%, respectively. In three rivers in Idaho (United States), an assessment of sediment load forecasting using ANN was performed with different sensitivity analysis methods and 263 processed datasets. Applying the nine sediment variables and different measured flows with sensitivity analysis indicated no good relationship between suspended load and predicted bedload [24]. Salih et al. (2020) [4] used newly developed data mining models for river SSL prediction based on M5P, M5Rule (M5R), attribute selected classifier (AS M5P), and K Star (KS). Overall, the results obtained achieved excellent forecasting of the SSL process. The results obtained show good reliability for different use approaches. Kaveh et al. (2020) [29] used long short-term memory (LSTM) for daily SSC prediction in Schuylkill River (United States). The comparison was made between the ANN, ANFIS, and LSTM models. The results show that the LSTM could be very satisfactory for SSC time series prediction.
In Algeria, the population faces a water shortage situation [30], with a capital of less than 500 m3/inhabitant/year [31]. Therefore, it is well below the threshold that separates countries in the red from those with relative sufficiency [31]. Despite the various development programs carried out in the early 2000s, a considerable breakthrough has been achieved in constructing mobilization works, including more than 94 dams in operation, and 5 in progress, for a total capacity of 8.4 billion m3. The situation in terms of the protection and control of storage volumes and dead volumes of these structures, for example, is not under control. This situation requires a national emergency response program to optimize water resource mobilization structures [32]. Suspended sediments transported across rivers are a significant cause of this situation and other environmental impacts, which is well explained by Buyukyildiz and Kumcu (2017) [19]. The studies carried out in the context of SSL at the basin level in Algeria are not sufficient by comparing with its area and the number of dams in operation (e.g., [7,33,34,35,36,37,38]).
For example, in the Sacramento River (California), Nakato (1990) [36] tested a set of sediment-transport formulas, i.e., the Ackers–White Einstein–Brown, Engelund–Fredsoe, Engelund–Hansen, Inglis–Lacey, Karim, Meyer–Peter and Mueller, Rijin, Schoklitsch, Toffaleti, and Yang formulas. The study results clearly show how difficult it is to predict the sediment discharge in natural rivers. In the Yellow River, China, Baosheng et al. (2008) [33] evaluated the applicability of the sediment transport methods developed by Engelund and Hansen, Ackers and White, Yang et al., and van Rijn, and compared with the Wuhan methods. The results show that the best possible predictions were obtained by the Yang et al., Wuhan, and modified Wuhan methods. Acceptably good predictions were also obtained by the van Rijn method. Several studies predict SSL based on artificial intelligence systems, as ANN models are the most widely used intelligent models in this field [39,40,41,42]. This paper assessed four approaches, ANN-PSO, ANFIS-PSO, RF, and LSTM, for estimating SSL at Chemourah and Gueiss wadis. This analysis was performed in an information-scarce environment, which is what the researcher and practitioner suffer in Algeria. Therefore, the main aim of this study was to make essential decisions with scant information.

2. Materials and Methods

2.1. Artificial Neural Networks

ANN can be defined as a reasoning model inspired by biological neural networks based on the human brain. It is a relatively nonlinear technique that belongs to the black box model category. ANN is a set of interconnected artificial neurons that perform nonlinear mathematical functions for information processing. Many distinct neural networks are characterized by their activation function and how interconnection is achieved between neurons. Among these types is the multilayer perceptron (MLP). The MLP is a neural network among the most popular models of ANN [43], and is a feedforward network with multiple layers. It consists of an input layer, one or more hidden layers, and an output layer. Each layer contains neurons’ propagated signals (connections) in a forward direction layer by layer since there is no connection to neurons from the same layer. In Figure 1 is shown the structure of the multilayer perceptron. The learning of MLP is supervised by minimizing the cost function, which is the sum of squared errors that represent the differences between the observed and simulated values of the network. Backpropagation was the selected algorithm for training MLP to measure the difference between the observed and simulated values of the network and propagate. The problem of the slowness of classical backpropagation led to the emergence of several different algorithms. Among these is the Levendberg Marquardt backpropagation (LMBP). In the context of our work, we use the LMBP algorithm because of its efficiency [44,45].

2.2. Neuro-Fuzzy Inference Systems

The adaptive neuro-fuzzy inference system (ANFIS) is an intelligent hybrid model combining ANN and fuzzy inference systems. It is a black box nonlinear mathematical technique capable of forming relationships between the inputs and outputs of a system, which was first introduced by Jang (1993) [46]. ANFIS is an MLP neural network equivalent to a fuzzy system structure, i.e., ANFIS applies the learning mechanism of ANN (backpropagation learning) on fuzzy inference techniques. ANFIS is a neuro-fuzzy inference model of the Sugeno type [47,48]. It can define parameters of membership functions and fuzzy rules (if, then) from the inputs and outputs of the system, as described in Figure 2a.
Rule   1 :   If   x   is   A 1   and   y   is   B 1 ,   then   Z 1 = a 1 x + b 1 y + c 1
Rule   2 :   If   x   is   A 2   and   y   is   B 2 ,   then   Z 2 = a 2 x + b 2 y + c 2
where A i and B i are fuzzy sets and a i , b i , and c i are the consequent parameters determined during the learning process [49,50].
As shown in Figure 2b, the architecture of the ANFIS model has five layers: the fuzzification layer, the rules layer, the normalization layer, the defuzzification layer, and the summation layer.

2.3. Particle Swarm Optimization

Particle swarm optimization (PSO) is a metaheuristic optimization algorithm that is somewhat similar to evolutionary computations. It was first invented by Kennedy and Eberhart (1995) [51]. PSO is an optimization algorithm that relies on a population of candidate solutions (called particles) to develop the optimal solution of the problem. It was initially inspired by the living world, specifically by simulating the social behavior of animals, such as flocks of birds, fish, or bees. This algorithm aims to graphically simulate the graceful and unpredictable choreography of bird individuals. Each individual in the swarm is represented by a vector in the multidimensional search space. This vector also has a custom vector that defines the subsequent movement of the particle, called the velocity vector. In addition, each particle contains a memory that allows it to remember its best performance in value and location and the best performance achieved by neighboring particles.
At the start of the algorithm, each particle is placed in the search space. The movement of particles for each iteration is affected by three components:
  • The current velocity.
  • The best performance.
  • The best performance in its neighborhoods.
The general principle of PSO functioning is illustrated in Figure 3.

2.4. Random Forest

Random forests (RF) or forest of decision trees are techniques that provide predictive models for classification and regression. To do this, they combine many decision trees in a bagging-type approach. This technique was introduced by Leo Breiman [52], who suggested it earlier under the name of CART trees (1984). RF implements binary decision trees (CART). It performs parallel learning on multiple decision trees built randomly and trained on different data subsets. In statistical terms, if the trees are decorrelated, it helps reduce the forecasts’ variance. The working principle of the RF technique is illustrated in Figure 4.
The following equation represents the output of the regression model, which is the average of all the predicted values of the decision trees:
h ( X ) = 1 K k = 1 K h ( x , θ k )
where K is the number of regression trees (k = 1, 2, …, K), x is a subset of the training dataset X (input series), θ are normally distributed random variables (with zero mean and unity variance) of the combined classifier, and h(x, θk) is the generated decision tree based on x and θk.

2.5. Long Short-Term Memory Networks

Long short-term memory networks (LSTM) (Figure 5) are an extension for recurrent neural networks (RNN), which expands their memory. Therefore, they are well suited for learning from essential experiences, which have very long delays in between. The units of an LSTM that have internal memory are used as building units for the layers of an RNN, which is then often referred to as an LSTM network. This unit consists of a numeric value that the network can drive based on situations.
An LSTM neuron comprises an internal memory controlled by three gates: an input gate, an output gate, and a forget gate. The input gate decides whether or not to let a new entrance input, and the forget gate decides whether to delete the information and reset the unit contents to 0. The output gate determines whether the unit contents must influence the neuron’s output at the current time. Figure 4 shows a schematic of an LSTM neuron. The type of algorithm for learning LSTM is backpropagation through time (BPTT), as in classic recurrent networks, by unfolding the recurrent network over time.

2.6. Data Sources

For a good SSL estimation, several parameters must be used. In this study, a great lack of necessary information and data was faced. However, it was possible to use the liquid flow and solid flow data recorded during flood periods.
The flows and SSL data were obtained from Foum El Gueiss and Chemourah gauging stations in the Gareat el tarf and Chemorah basins, respectively, provided by the National Agency of Hydraulic Resources. Foum El Gueiss gauging station provides 26 years of data, and the Chemourah station provides only 13 years of data recorded during flood periods.

3. Study Area

The Gareat el tarf and Chemorah basins are located in the northeastern part of Algeria, at the extreme east of the high steppe plains between the Tellian Atlas in the north and the Saharan Atlas in the south. It is a part of the basins of Constantine’s highlands, according to the National Agency of Hydraulic Resources (ANRH). The Gareat el tarf basin is located between the northern latitudes 35°22′ and 35°56′ and the eastern longitudes 06°49′ and 07°34′, where Oued Chemora is situated at 35°39′52″ N and 6°38′41″ E. The Gareat el tarf basin covers an area of 2432 km2 [53], whereas the Chemorah basin has an area of 755 km2.
The Gareat el tarf and Chemorah basins (Figure 6) are limited to the north by the Sidi Reghis and Aamamet El Kebir massifs, to the south by the Feraoun, Aurès, and El Aoud mountains, to the east by the Fedjidjet, Bou Tokhma, Tafrennt, and Chettaia massifs, and to the west by the Fedjoudj and Tarf mountains. The Gareat el tarf basin constitutes a pervasive and relatively high endorheic depression, about 960 m, receiving all the erosion inputs from the surrounding reliefs. Most of the rivers in the basin flow towards the lake of Gareat el tarf. In general, two types of climate characterize the Gareat el tarf basin: The north is covered by a semiarid climate, and the south is affected by cold and humid air currents from the Aurès, resulting in a temperate climate [53]. The Chemorah basin has almost the same characteristics as the Gareat el tarf basin, as they are affected by a semiarid Mediterranean climate with a cold and wet winter and dry and hot summer.
In this study, we used the hydrometric series of gauging stations of Foum El Gueiss coded 07-07-02 by ANRH. The data correspond to 1002 observations of flows and SSL of the Gueiss River during the flood events from 17 September 1971 to 11 January 1996, whereas the hydrometric series of the gauging station of Chemorah basin coded 07-04-03, also during the flood period, are from 17 August 1985 to 11 June 1997. Table 1 shows an example of the data used in this research. Note that the flow (Ql) is obtained from the rating curve and the SSL (Qs) is the product of Ql by the corresponding suspended sediment concentration. The main statistical parameters for the data used in this study are presented in Table 2. According to Table 2, it can be said that the statistical characteristics of the data represented by the mean, standard deviation (STD), coefficient of variation (CV), minimum value (Min), and maximum value (Max) are relatively similar, with a slight difference in both Chemorah and Gareat el tarf basins.

4. Evaluation Criteria

Models are generally evaluated in the training and validation phases by calculating the error between simulated and observed values using statistical parameters. The statistical parameters used in this research are root mean square error (RMSE), Theil’s inequality coefficient (U2) [54], the Nash–Sutcliffe efficiency coefficient (E) [55], and the correlation coefficient (R) [56]. The following equations define these criteria:
RMSE = i = 1 N ( Q s i Q ^ s i ) 2 N
U ² = i = 1 N ( Q s i Q ^ s i ) 2 i = 1 N Q s i 2
E = 1 i = 1 N ( Q s i Q ^ s i ) 2 i = 1 N ( Q s i Q ¯ s i ) 2
R = i = 1 N ( Q s i Q ¯ s i ) ( Q ^ s i Q ˜ s i ) i = 1 N ( Q s i Q ¯ s i ) 2 i = 1 N ( Q ^ s i Q ˜ s i ) 2
where Q s i is the measured value of SSL; Q ^ s i is the calculated SSL by the model; Q ¯ s i is the measured average SSL; Q ˜ s i is the calculated average SSL, and N is the number of data points.

5. Models Development

In this study, the neuro-particle swarm (ANN-PSO), neuro-fuzzy-particle swarm (ANFIS-PSO), RF, and LSTM models were used to estimate the SSL in the Gueiss and Chemourah rivers. Due to the lack of sufficient information in this study, flows with lag time t, t −–1, and t − 2 (Ql(t), −Ql(t − 1) and −Ql(t − 2)) and SSL with lag time t − 1 (Qs(t − 1)) were used as input vectors for the models, which are values observed during periods of flood events. The outputs of the models are the current calculated SSL (Qs(t)) using water discharge and suspended sediment concentration.
The available database was divided into two sets to adjust model parameters and achieve optimal performance: a set for the training phase contains 70% of the data, and a set for the validation phase includes 30% of the data. Table 3 illustrates the combinations of the proposed input vectors to simulate the SSL by the ANN-PSO, ANFIS-PSO, RF, and LSTM models. For the ANN-PSO and ANFIS-PSO models, MLP and ANFIS were used in conjunction with the PSO optimization algorithm, as shown in Figure 3.
ANN-PSO development is carried out by determining the optimum number of neurons in the hidden layer for different combinations of the proposed input vectors. This procedure was carried out by error testing by modifying the number of hidden neurons to obtain the structure that gives maximum performance. ANFIS-PSO was developed by performing error tests with variations in the number of rules for the input vector combinations provided. The rules that produced the slightest performance error were chosen to develop ANFIS-PSO to estimate SSL. We used the early stopping algorithm to avoid the over-fitting and under-fitting problem for the models used in this research (ANN-PSO and ANFIS-PSO). The early stopping algorithm determines the number of iterations and stops learning before the algorithm converges. It involves specifying the number of iterations used in training, checking for errors based on validation, and stopping training as soon as the error begins to increase. We follow the same process by error-testing the validation dataset of different sets of combinations input vectors proposed to develop RF and LSTM models to obtain the best possible performance for estimating SSL.

6. Results and Discussion

After developing ANN-PSO, ANFIS-PSO, RF, and LSTM models for different combinations of input vectors, they were evaluated according to RMSE error. In Chemourah basin, the ANN-PSO and LSTM models gave the lowest values for RMSE with a combination of input vectors (4 vectors). In contrast, the ANFIS-PSO model gave the highest values of RMSE for input vectors (4 vectors) for the two basins (Figure 7a). According to Figure 7b, in the Gareat el tarf basin, ANN-PSO and LSTM models had the lowest RMSE values with a combination of 4 input vectors, while RF and ANN-PSO models showed the lowest values for the combination of 2 and 3 input vectors, respectively.
Table 4 presents the results obtained by the optimal models of ANN-PSO, ANFIS-PSO, RF, and LSTM in the training and validation phases. According to Table 4, the ANN-PSO model provided the best results in estimating the SSL for both basins in the validation phase, i.e., RMSE = 67.2990 kg/s in Chemourah basin and RMSE = 55.8737 kg/s in Gareat el tarf basin. In contrast, the ANFIS-PSO model provided the worst results in both basins, i.e., RMSE = 158.2035 kg/s in Chemourah basin and RMSE = 165.3653 kg/s in Gareat el tarf basin. The RF and LSTM models always gave acceptable results in the validation phase. In Chemourah basin, the RF model gave RMSE = 74.5747 kg/s and the LSTM model gave RMSE = 69.4178 kg/s, while in the Gareat el tarf basin the RF model gave the result of RMSE = 58.9957 kg/s and the LSTM model gave RMSE = 64.8888 kg/s. According to Kaveh et al. (2021) [29], the LSTM algorithm could satisfactorily predict SSC compared to ANN and ANFIS. Al Dahoul et al. (2021) [57] reported that LSTM outperformed other models such as linear regression, MLP, and extreme gradient boosting for SSL prediction. Sharafati et al. (2020) [58] applied new ensemble machine learning models for daily SSL prediction based on gradient boost regression (GBR), AdaBoost regression (ABR), and RF regression. This shows that the RF model has a slight lead in prediction performance.
Figure 8 and Figure 9 show the superiority of the ANN-PSO, RF, and LSTM models over the ANFIS-PSO model. This superiority is translated by the results reported for the RMSE, U2, E, and R statistical parameters (Table 4). In an in-depth comparison, the ANN-PSO model provides the best performance compared with the other models with low values of RMSE and U2, and high values of E and R. Similarly, Mohammadi et al. (2021) [59] concluded that ANN-PSO is the best algorithm in terms of accurate prediction of SSL with a lower number of input parameters compared to radial basis function (RBFNN) and SVM. Hanoon et al. (2021) [60] revealed that ANN provided a superior performance to that of the gradient boost regression (GBT), RF, and SVM for SSL prediction for some case studies in Malaysia. Idrees et al. (2021) [61] concluded that the ANN is better compared to the ANFIS, RBFNN, SVM , and GP in terms of SSL prediction capabilities. Nhu et al. 2020 [62] tested the predictive ability of a random subspace (RS), RF, two SVM models using a radial basis function kernel (SVM-RBF) and a normalized polynomial kernel (SVM-NPK) model for monthly SSL estimation. The results show the superiority of the RS model compared to SVM-RBF, SVM-NPK, and RF models. Ehteram et al. 2021 [63] optimized ANN by multi-objective whale algorithm (MOWA) for predicting daily SSL. The ANN-MOWA model showed the best accuracy for predicting daily SSL, compared with other models. The main statistical characteristics of mean, standard deviation (STD), coefficient of variation (CV), minimum value (Min), and maximum value (Max) of the observed and estimated SSL by the optimum models of ANN, ANFIS, ANN-GA, and ANN-PSO in the training and validation phases are shown in Table 5. Figure 10 and Figure 11 show comparisons between observed and estimated SSL values using the optimal ANN-PSO, ANFIS-PSO, RF, and LSTM models (training and validation phases). These figures demonstrate the efficacy and superiority of the ANN-PSO, RF, and LSTM models compared to ANFIS-PSO. The poor results obtained by ANFIS-PSO are due to the complexity of the fuzzy rules, which led the model to not find a well-defined relationship between inputs and outputs.
From Table 4 and Figure 10 and Figure 11, the ANN-PSO model has provided more efficient results than the RF, LSTM, and ANFIS-PSO models for estimating SSL. Comparing the obtained results with those presented by Bouzeria et al. (2017) [64], using data from northeastern Algeria to predict sediment loads in the Mellah catchment with an ANN, the present results are very satisfactory, despite the lack of sufficient information and the use of only recorded flood data.

7. Conclusions

In this study, four different machine learning approaches, ANN-PSO, ANFIS-PSO, RF, and LSTM, were examined for estimating SSL in the Chemourah and Gareat el tarf basins using observation data of flood events of the Chemourah and Gueiss rivers. This paper also shows that the ANN-PSO, RF, and LSTM models have given a better accuracy of simulations compared to the ANFIS-PSO model. Model performances were measured using RMSE, U2, E, and R, between the estimated and observed SSL values. The results indicate that the ANN-PSO model is slightly better than the RF and LSTM models for estimating SSL in the Chemourah and Gareat el tarf basins. We concluded from this study that the ANN-PSO, RF, and LSTM models can always give good results compared with the ANFIS-PSO model. The ANN-PSO, RF, and LSTM models can decrease the complexity of runoff and SSL relationships and increase the estimation accuracy. These encouraging results lead us to experiment and use other machine learning systems and hybrid models to estimate SSL in rivers, and encourage the installation of flumes that enable more accurate measurements in the basin outlet sections to take even more advantage of such new computational techniques.

Author Contributions

Z.A., B.Z., M.A. and M.C. conceived the framework of this research, processed data, designed the experiments, plots, and map preparation, validated the processing results, and wrote the manuscript. C.A.G.S. and E.E.H. gave feedback on the written manuscript and helped to analyze and edit the manuscript for proper English language, grammar, punctuation, spelling, and technical improvements. All authors have read and agreed to the published version of the manuscript.

Funding

This research was funded by Taif University, Researchers Supporting Project, grant number TURSP-2020/324.

Institutional Review Board Statement

Not applicable.

Informed Consent Statement

Not applicable.

Data Availability Statement

The data that support the findings of this study are available from the corresponding author Bilel Zerouali, upon reasonable request.

Acknowledgments

Authors would like to acknowledge the financial support provided from Taif University Researchers Supporting Project, grant number TURSP-2020/324. The authors gratefully thank the Directorate General for Scientific Research and Technological Development and the National Agency of Water Resources (ANRH) of Algeria who gave us the needed data to realize this research.

Conflicts of Interest

The authors declare no conflict of interest.

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Figure 1. Structure of multilayer perceptron neural networks.
Figure 1. Structure of multilayer perceptron neural networks.
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Figure 2. (a) Sugeno fuzzy reasoning and (b) architecture of ANFIS.
Figure 2. (a) Sugeno fuzzy reasoning and (b) architecture of ANFIS.
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Figure 3. Structure of the ANN-PSO and ANFIS-PSO models.
Figure 3. Structure of the ANN-PSO and ANFIS-PSO models.
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Figure 4. Flowchart of the RF functioning.
Figure 4. Flowchart of the RF functioning.
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Figure 5. Flowchart of the LSTM functioning.
Figure 5. Flowchart of the LSTM functioning.
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Figure 6. Geographic location of (a) Northern Algeria and (b,c) the main basins used in this study.
Figure 6. Geographic location of (a) Northern Algeria and (b,c) the main basins used in this study.
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Figure 7. Evaluation of RMSE based on the different combinations of input vectors s for ANN-PSO, ANFIS-PSO, RF, and LSTM models in the validation phase.
Figure 7. Evaluation of RMSE based on the different combinations of input vectors s for ANN-PSO, ANFIS-PSO, RF, and LSTM models in the validation phase.
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Figure 8. Violin diagram of different machine learning models in the training and validation phases.
Figure 8. Violin diagram of different machine learning models in the training and validation phases.
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Figure 9. Taylor diagram of different machine learning models in the training and validation phases.
Figure 9. Taylor diagram of different machine learning models in the training and validation phases.
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Figure 10. Comparison between observed and estimated SSL of Chemourah basin by the different machine learning models in the training and validation phases.
Figure 10. Comparison between observed and estimated SSL of Chemourah basin by the different machine learning models in the training and validation phases.
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Figure 11. Comparison between observed and estimated SSL of Gareat el tarf basin by the different machine learning models in the training and validation phases.
Figure 11. Comparison between observed and estimated SSL of Gareat el tarf basin by the different machine learning models in the training and validation phases.
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Table 1. Example of the data used in this research.
Table 1. Example of the data used in this research.
YearMonthDayHourHeight (m)Ql (m3/s)Qs (kg/s)
197252419:153227.30025.662
197252506:30170.9660.985
197261005:00170.2701.220
197261106:00170.2700.837
197261206:5090.2700.772
197271705:4080.0980.632
197271806:1570.0790.021
197271919:00320.0620.786
Table 2. The statistical characteristics of river flow and SSL used in the study.
Table 2. The statistical characteristics of river flow and SSL used in the study.
BasinStatistical
Parameters
MeanSTDCVMinMax
ChemourahQl (m3/s)4.72829.43491.9955074.3000
Qs (kg/s)71.1296150.12952.11060955.0040
Garaet el tarfQl (m3/s)3.42257.34792.1470069.5000
Qs (kg/s)64.3165162.97722.53400957.6070
Table 3. The combinations of the proposed input vectors for ANN-PSO, ANFIS-PSO, RF, and LSTM.
Table 3. The combinations of the proposed input vectors for ANN-PSO, ANFIS-PSO, RF, and LSTM.
Input ModelsNumber of InputOutput
(1) Ql(t)1Qs(t)
(2) Ql(t) and –Qs(t − 1)2Qs(t)
(3) Ql(t) and −Ql(t − 1)2Qs(t)
(4) Ql(t), −Ql(t − 1) and −Qs(t − 1)3Qs(t)
(5) Ql(t), −Ql(t − 1) and −Ql(t − 2)3Qs(t)
(6) Ql(t), −Ql(t − 1), −Ql(t − 2) and −Qs(t − 1)4Qs(t)
Table 4. The results obtained by ANN-PSO, ANFIS-PSO, RF, and LSTM for the training and validation phases.
Table 4. The results obtained by ANN-PSO, ANFIS-PSO, RF, and LSTM for the training and validation phases.
BasinModelsPhasesRMSEU2ER
ChemourahANN-PSOTraining78.11930.18280.76630.8755
Validation67.29900.32740.63460.8003
ANFIS-PSOTraining201.59121.2171−0.55610.0051
Validation158.20351.8090−1.0195−0.0012
RFTraining77.10060.17800.77240.8845
Validation74.57470.40200.55130.7458
LSTMTraining62.04050.11530.85260.9239
Validation69.41780.34830.61120.7824
Garaet el tarfANN-PSOTraining88.78520.20090.75640.8706
Validation55.87370.29040.69710.8392
ANFIS-PSOTraining239.52961.4647−0.7753−0.0235
Validation165.36532.5346−1.6440−0.0394
RFTraining80.18850.16390.80130.8974
Validation58.99570.32370.66240.8157
LSTMTraining68.63530.12010.85440.9273
Validation64.88880.39160.59150.7706
Table 5. Characteristics of statistical parameters of observed and estimated SSL for ANN-PSO, ANFIS-PSO, RF, and LSTM.
Table 5. Characteristics of statistical parameters of observed and estimated SSL for ANN-PSO, ANFIS-PSO, RF, and LSTM.
BasinModelsPhasesFlowMeanSTDCVMinMax
ChemourahANN−PSOTrainingObserved85.2852161.90961.89840955.0040
Simulated87.2012142.59011.63520.0567819.1319
ValidationObserved37.9759111.81702.94440647.2060
Simulated42.699182.33021.92820.1968500.3120
ANFIS−PSOTrainingObserved85.2852161.90961.89840955.0040
Simulated71.0791120.72541.6985−0.0036884.2506
ValidationObserved37.9759111.81702.94440647.2060
Simulated56.9000109.93961.93220.0252670.2476
RFTrainingObserved85.2852161.90961.89840955.0040
Simulated81.5454127.49401.56350.0486622.4522
ValidationObserved37.9759111.81702.94440647.2060
Simulated42.540377.02341.81060.0486365.7755
LSTMTrainingObserved85.2852161.90961.89840955.0040
Simulated84.1479144.42131.7163−52.7124843.7532
ValidationObserved37.9759111.81702.94440647.2060
Simulated41.451887.94882.1217−17.5058512.4590
Garaet el tarfANN−PSOTrainingObserved82.9021180.01032.17140957.6070
Simulated89.6066154.66801.72610.0427859.5337
ValidationObserved21.0568101.70524.83010909.5410
Simulated27.290479.45572.91150.0310776.1455
ANFIS−PSOTrainingObserved82.9021180.01032.17140957.6070
Simulated64.5640153.19412.3727−111.9880931.0246
ValidationObserved21.0568101.70524.83010909.5410
Simulated45.9378124.28112.7054−0.06951.1821
RFTrainingObserved82.9021180.01032.17140957.6070
Simulated82.6496150.04501.81540.0721687.6447
ValidationObserved21.0568101.70524.83010909.5410
Simulated26.322481.12123.08180.0721641.6942
LSTMTrainingObserved82.9021180.01032.17140957.6070
Simulated79.1898154.04211.9452−32.8914739.1696
ValidationObserved21.0568101.70524.83010909.5410
Simulated21.277073.53153.4559−39.5889711.1299
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Abda, Z.; Zerouali, B.; Alqurashi, M.; Chettih, M.; Santos, C.A.G.; Hussein, E.E. Suspended Sediment Load Simulation during Flood Events Using Intelligent Systems: A Case Study on Semiarid Regions of Mediterranean Basin. Water 2021, 13, 3539. https://doi.org/10.3390/w13243539

AMA Style

Abda Z, Zerouali B, Alqurashi M, Chettih M, Santos CAG, Hussein EE. Suspended Sediment Load Simulation during Flood Events Using Intelligent Systems: A Case Study on Semiarid Regions of Mediterranean Basin. Water. 2021; 13(24):3539. https://doi.org/10.3390/w13243539

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Abda, Zaki, Bilel Zerouali, Muwaffaq Alqurashi, Mohamed Chettih, Celso Augusto Guimarães Santos, and Enas E. Hussein. 2021. "Suspended Sediment Load Simulation during Flood Events Using Intelligent Systems: A Case Study on Semiarid Regions of Mediterranean Basin" Water 13, no. 24: 3539. https://doi.org/10.3390/w13243539

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