Abstract
Renewable energy sources have been used for desalination by employing different technologies and mediums due to the limitations of fossil fuels and the environmental issues related to their consumption. Solar energy is one of the most applicable types of renewable sources for desalination in both direct and indirect ways. The performance of solar desalination is under effects of different factors which makes their performance prediction difficult in some cases. In this regard, data-driven methods such as artificial neural networks (ANNs) would be proper tools for their modeling and output forecasting. In the present article, a comprehensive review is provided on the applications of different data-driven approaches in performance modeling of solar-based desalination units. It can be concluded that by employing these methods with proper inputs and structures, the outputs of the solar desalination units can be reliably and accurately forecasted. In addition, several recommendations are produced for the upcoming work in the relevant areas of the study.
Introduction
Fresh water is absolutely essential for human societies since they rely on it for development and survival (Zheng, 2017). Around 71% of the earth is covered with water; however, about 96.5% of this water is in the brackish form or saline, which means that it cannot be directly used for irrigation and drinking, and just less than 1% of fresh water resources are within human reach (Tiwari et al., 2003; ). Regarding the uneven distribution of fresh water in different regions of the world, the increase in demand due to population growth, and the essence of water for human survival and activities, desalination has gained more importance in recent years. Desalination is known as a treatment process of water that includes salt removal from saline water to make it appropriate for drinking (). Desalination of water with the salinity more than normal levels is one of the ways (Tzen and Morris, 2003), and probably the most applicable one, to overcome the mentioned problems related to the unavailability of fresh water. The nature of the desalination process is energy-consuming, and it is crucial to properly supply the required energy. Improving the efficiency of the systems and utilizing the renewable energy sources are recommended to solve the problems related to the energy demand of desalination systems. Renewable energy sources can be used for desalination in direct and indirect ways. In direct approaches, thermal energy is mainly used for water evaporation and reducing the salinity of water, while renewable energies can be used for indirect desalination by producing electricity and applying the power in reverse osmosis (RO) technologies (). Among the renewable energy sources, solar energy is attractive for the desalination purpose since it can be used in different ways such as thermal technologies or photovoltaic/RO systems.
Numerous studies have been performed on the various kinds of solar-based desalination systems to find the influential factors and improve their performance (). Depending on the type of solar desalination, the factors affecting the performance can be differed. Solar radiation is one of the most important factors on the output of the systems. For instance, found that by increasing the solar radiation from 400 W/m2 to 900 W/m2, the efficiency of a single-stage solar desalination system increased from 15 to 26%. In addition to solar radiation, the components of the system and their configuration affect the performance of these systems. As an example, investigated the performance of a solar still composed of two parabolic troughs and two rectangular absorbers under different working conditions. They found that the rim angle of the troughs can influence the productivity of the desalination. Moreover, it was observed that reducing the pressure could remarkably improve the productivity of the desalination system. In another work, investigated the performance of an RO system powered by a solar dish Stirling engine. They found that by an increment in the temperature of the absorber, productivity of water increased, while there was an optimum temperature at which the exergy efficiency of the system reached its maximum value. In addition to the technical aspects, solar desalinations have been investigated from the economic point of view. For instance, carried out techno-economic assessment on large-scale solar powered desalination systems in Morocco by considering photovoltaics (PVs) and concentrated solar power (CSP) for supplying energy. They found that using the PV/RO system without a storage unit is the cheapest configuration today and by 2030. In another work (Zheng and Hatzell, 2020), solar thermal desalination was thermo-economically analyzed, and it was found that construction costs of solar collectors were the largest total investments of the system. Other types of desalination systems have been modeled by using data-driven methods. For instance, Faegh et al. () applied different artificial neural network (ANN)-based methods to model the gain output ratio and heat transfer rate of the evaporator and evaporative condenser of a heat pump-assisted desalination system and found that the R-squared of the models were more than 0.91 for all the outputs.
As mentioned in the previous paragraph, the performance of desalination units is affected by several elements such as the applied technology, operating conditions, and the properties of the saline or brackish water. Since the experimental works are costly and time-consuming, it would be useful to propose models for performance prediction and assessment of the desalination systems. Data-driven methods, with outstanding ability in modeling of complex systems, would be attractive options for performance forecasting of desalination systems (; ; ). These methods have shown their outstanding performance in a wide variety of applications such as predicting the properties of materials (; ), fault diagnosis (Venkatasubramanian and Chan, 1989), etc. (). Current works focus on providing a comprehensive review on the applications of data-driven methods in modeling the performance of various solar desalination systems, which is performed for the first time. In addition, a table is prepared that summarizes the main findings of the reviewed works, inputs of the proposed models, applied approaches, and algorithms, which will be useful for the scholars working on the similar fields of study. Finally, according to the knowledge of the authors and the investigation of the previous studies, some suggestions are recommended for future works in the relevant subjects. The findings and information represented in this study will facilitate upcoming works to concentrate on the modeling of desalinations systems, especially the ones using solar energy.
Mostly Used Data-Driven Methods
There are different data-driven methods used in modeling of energy systems. The mostly used approaches in energy system modeling are multilayer perceptron (MLP) ANN, adaptive neuro-fuzzy inference system (ANFIS), radial basis function (RBF), and support vector machines (SVMs). In this regard, these approaches are briefly described in the following subsections.
Multilayer Perceptron Artificial Neural Network
The structure of MLP is shown in Figure 1. As shown in this figure, there are three main layers in the simplest form of this network including input, hidden, and output. However, the hidden layer may be composed of more layers. In each node of this network, a weight vector is used to make connection between the current node and the ones in the upcoming layer. In the primary layer of the network, the summation of the values is sent to the next layer, which plays a role as inputs of that layer. Assuming that the vector of X is the model input and nj is applied as the jth node, the input in the upcoming layer is written as Eq. 1where , and K are the threshold of the jth node, the weight value of the node, and the number of nodes, respectively. Subsequently, f as a transfer function is applied to provide the overall inputs in the upcoming layer as represented in Eq. 2
FIGURE 1
Different functions can be used in this step with its own features and characteristics. By multiplying the linking weight and the output of the hidden layer, the output of the nodes will be determined. It should be noted that the architecture of the network including the number of hidden layers and neurons is dependent on the problem complexity, the noise of data, and the shares of data used for the test and validation of the model (
Adaptive Neuro-Fuzzy Inference System
The schematic of ANFIS in a simple form with two inputs and one output is illustrated in Figure 2. In this architecture, five layers are considered. The first layer of this model is applied in order to change the inputs to fuzzy sets and projects the variables on fuzzy membership in the range between 0 and 1. In the second layer, the signals of the input are generated; furthermore, values of membership function weight will be checked. In the next layer of this network, normalized firing strength of each node is obtained. Subsequently, the outputs are changed to crisp sets in the fourth layer. Finally, the outputs are determined in the last layer of the proposed network. This layer of the network contains one node which is used to sum up the input signals provided by the prior layer.
FIGURE 2

Structure of the ANFIS model (
There are some advantages in the ANFIS method such as its ability in capturing the nonlinear structure of a procedure and fast learning capacity. In addition, this approach has both linguistic and numerical knowledge. In comparison with MLP ANN, ANFIS is more transparent for the users and results in less memorization error (
Radial Basis Function
The RBF network has some advantages such as fast performance, a simple structure, and high estimation. The structure of this network is shown in Figure 3. Similar to MLP, there are three main layers in this network. The nodes are connected to the previous one in each layer of the network. In the first layer, input variables are assigned to the nodes. Subsequently, they are transferred to the next layer. At the final stage, the weighted links are used to transfer the data to the third layer. In the hidden layer of these networks, RBF plays the role of activation functions to produce the vector distance multiplied by the corresponding bias.
FIGURE 3

Structure of the RBF model (
In the second layer of the mentioned network, the input vector will be projected to a new space (Zendehboudi and Tatar, 2017). To determine the output of the jth neurons, Eq. 3 is applied as follows:
In Eq. 3, is the weight factor, X is the input vector, Z is the RBF, and To calculate the standard deviation, the following equation is used:
In Eq. 4, is the maximum distance between the centers and refers to number of centers. In the last layer of the network, weights of the signals are obtained by using the previous layer dataIn Eq. 5, refers to the value of the weight vector determined in the training process. Despite some advantages of RBF networks compared with MLP ANN such as a faster training process, their accuracy in modeling the test data may be lower compared with MLP ANN (
Support Vector Machine
SVM can be applied for regression and prediction in different systems (Sreedhara et al., 2019). By considering that is the number of data set samples and the inputs of and K = 1,2,…,N and the outputs are , the SVM formulation is as follows (
In Eq. 6, b and w are the bias and weight, respectively (
In Eq. 7, γ and ek are the regularization parameter and error value, respectively (
In this equation, two parameters including and Lagrange multipliers must be determined. One of the main advantages of SVM methods for modeling is their ability in providing nonlinear solutions, while the main problem associated with this approach is the requirement for knowledge about the kernel that must be used.
Generally, mean square error (MSE) and R-squared are used in evaluation of regression and predictive models, which are as follows:where ns is the number of samples used in regression.
Applications of Data-Driven Methods in Solar Desalinations
There are three main principle approaches used for desalination, which are thermal, pressure, and electrical. Thermal distillation can be considered as the oldest approach in which water with high salinity is boiled and the generated steam is collected. The condensed form of the collected steam can now be used as fresh water. In the electrical approach, electrical current is applied to separate the salt and water. In these types of desalination units, a permeable membrane is used, in which ions move across it by use of electric current as a driving force. In the RO type of desalination, pressure acts as a driver for moving water through a selectively permeable membrane, leaving the salt behind (
The applied method and algorithm are among the most important factors that influence the exactness of the data-driven methods in forecasting the outputs of solar stills (
In modeling the system with data-driven methods, it is essential to consider all the effective elements as inputs. In this regard, some models have included more inputs to reach better accuracy or improved the comprehensiveness. As an example,
Solar desalination can be integrated with other components to reach higher productivity. Data-driven methods are applicable for performance forecasting of these systems (
FIGURE 4

Solar desalination system with a collector, heater, and PV (
Data-driven methods are employable for modeling the dynamic performance of solar desalination systems. In a study carried out by
Utilizing nanofluids in solar stills can improve their performance. Intelligent methods can be applied for accurate evaluation of these solar stills.
The outputs of the ANN-based model can be used for designing an optimal condition for the performance of the desalination systems (
To sum up the findings of the study, it can be declared that the accuracy of the models is under the influence of the applied method, optimization algorithm, etc. Generally, intelligent methods such as ANNs are preferred in terms of accuracy due to their more complex structures which enable them to model complicated systems with higher accuracy. In addition, it is found that applying optimization algorithms and coupling them with the intelligent methods improve the accuracy since the parameters affecting the exactness are used in their optimum values. In addition to the abovementioned factors, the considered inputs influence the exactness. Considering more influential factors as the inputs will provide more accurate models (
TABLE 1
| Reference | System | Method | Inputs | Findings |
|---|---|---|---|---|
| Stepped solar still | Long short-term memory (LSTM) ANN | – | R2 of the provided model was 0.9752. | |
| Zarei and Behyad (2019) | Solar greenhouse desalination (humidification–dehumidification) | ANN | Width and length of the seawater greenhouse, front evaporator height, and the roof transparency | Using one hidden layer with nine neurons led to the model with the maximum exactness with R2 of 0.997. |
| Single-slope solar still | ANN | Time, solar radiation, temperatures of ambience, glass, water, and basins | Using the ICA optimization approach led to significant reduction in the error of the predicted values (up to a 54.30% reduction in mean absolute error of the model used for water productivity estimation). The maximum R2 value of the model for water productivity was 0.9924 | |
| Inclined passive solar still | ANN and MLR | Relative humidity, ambient temperature, solar radiation, wind speed, feed temperature and its total dissolved solids, and feed mass flow rate | ANN outperformed the MLR in performance prediction of the system. The maximum absolute errors of the ANN and MLR were 8% and 35%, respectively. The R2 value of the model with ANN was 0.949, while it was 0.739 for MLR. | |
| Solar still | ANFIS and multiple nonlinear regression | Relative humidity, solar radiation, flow rate of the feed, total dissolved solids of the feed and brine. | The applied function in ANFIS affects the outputs of the model. The maximum value of R2 for training data sets was 0.999 for the ANFIS-based model. | |
| Solar still | ANN and stepwise regression | Relative humidity, ambient temperature, total dissolved solids in feed water, rate of feed flow, solar radiation, and wind speed | The model based on ANN had higher accuracy compared with stepwise regression. The mean absolute relative error of the stepwise regression was around 2.5 times higher than that of the ANN-based model. R2 for ANN was 0.960, while it was 0.902 under optimal conditions of the SWR model. | |
| Solar still | ANN | Julian day, relative humidity, ambient temperature, total dissolved solids in the feed and brine water, rate of feed flow, solar radiation, wind speed, and temperature of brine water | Using Levenberg– Marquardt as a learning function led to higher accuracy (R = 0.99437) compared with resilient backpropagation (R = 0.9853) and conjugate gradient backpropagation with Fletcher–Reeves restarts (R- = 0.98941). | |
| Solar still | ANFIS | Total dissolved solids in the feed and brine water, solar radiation, relative humidity, and feed flow rate | The membership function affects the accuracy of the forecasted data. The coefficient of correlation was 0.99 under the most accurate conditions. | |
| Solar still | ANFIS | Total dissolved solids in the feed and brine water, solar radiation, relative humidity, and feed flow rate | The membership function of the model influences the exactness of the predicted values. The R2 value in the most accurate case was 0.999. | |
| Wang et al. (2021) | Tubular solar still | ANN, RF, and multilinear regression | Time, solar radiation intensity, wind speed, temperatures of feed water, basin plates, salt water, cover, and ambient temperature | The proposed model based on RF had the highest exactness with a mean absolute error of 5.21%. The R2 value in the most accurate case was 0.9758, while it was 0.9745 for RF and 0.9614 for ANN. |
| Active solar still | ANN, ANN/Harris Hawks, and SVM | Ambient temperature, time, speed of wind, solar irradiance, and velocity of vapor | Using the optimizer in the ANN increased R2 of the model from about 0.970 to around 0.983. | |
| Solar still | ANFIS with different membership functions | Dissolved solids of the feed and brine, feed flow rate, relative humidity, and solar radiation | The membership function affects the exactness of the proposed models based on ANFIS. The value of R2 under optimal conditions was 0.9999. | |
| Inclined stepped solar still | ANN, linear model, and regression | Cloud cover, day and month numbers, number of hours per day, difference between the temperatures of inner and outer surfaces of glass, ambient temperature, solar radiation, humidity, wind speed, and temperatures of water, basins, and vapor | Using ANN provided a model with the highest accuracy (RMSE = 22.48). R2 for ANN and the regression were approximately 0.98 and 0.905, respectively. | |
| Solar still with a battery, heater, PV, and collector | ANN and first principle models | Temperatures of water, basins, insulation, ambience, and glass, solar intensity, and speed of wind | Using ANN provided more accurate prediction. In the case of modeling water mass, R2 of ANN and first principle models were 0.9998 and 0.9978, respectively. | |
| – | ANN | Temperatures of water, basins, and glass | R2 of the provided model was 0.993. | |
| Solar still with improved design | FF, BP, and RBF ANNs | wind speed, ambient temperature, received radiation from the Sun, and water depth in the basin | RBF and FF showed the highest accuracy in forecasting water temperature and hourly water production, respectively. The R2 values for FF, BP, and RBF networks were 0.9631, 0.9425, and 0.9567, respectively. | |
| Double-slope solar still with nanofluids | SVR, Linear SVR, ANN, and FR | Air ambient temperature, solar radiation, wind speed, vapor temperature, basin temperature, and temperatures at the glass inlet and outlet | Using RF led to the highest accuracy. The R2 values for train data sets of SVR, linear SVR, ANN, and RF were 0.9905, 0.9569, 0.9867, and 0.9971, respectively. | |
| Nanofluidic solar stills coupled with a thermoelectric | ANN with ICM and GA | Time, solar radiation, ambient temperature, power of the applied fan, concentration of the nanofluid, and temperatures of water, glass, and basins | Using ICM led to more enhancement in the accuracy of the ANN-based model compared with GA. The R2 values of training data sets for MLP, GA-MLP, and ICM-MLP were 0.9458, 0.9495, and 0.9865, respectively. | |
| Nanofluidic solar stills coupled with a thermoelectric | PSO-ANFIS and PSO-ANN | Time, solar radiation, ambient temperature, power of the applied fan, concentration of the nanofluid, and temperatures of water, glass, and basins | Using PSO-ANFIS provided the predictions with the highest accuracy with an R-squared of 0.9884 for training data sets. | |
| Solar still | MLR and ANN | Julian day, ambient temperature, relative humidity, solar radiation, wind speed, ambient temperature, feed water temperature, and total dissolved solids of brine and feed water | ANN provided a model with higher exactness compared with MLR. The mean value of coefficient of correlation for ANN was 11.23% higher than the corresponding value of MLR. The values of R2 for training data sets of MLR and ANN were 0.856 and 0.996, respectively. | |
| Solar-powered membrane distillation unit | ANN | Radiation, rate of feed flow inlet temperature of the cold channel | A control system was proposed based on the ANN model to reach maximum productivity. The R value of the network for training data sets was 0.975. | |
| Inclined passive solar still | ANN, ANFIS, and MR | Solar radiation, relative humidity, feed flow rate, and total dissolved solids of brine and the feed | ANN showed superior performance compared with the other approaches with a coefficient of correlation equal to 0.98. |
Important findings of the studies on applications of data-driven methods in solar desalination systems.
Suggestions for Upcoming Studies
Despite the fact that there are several works on utilization of data-driven methods in performance prediction of solar desalination systems, there are some limitations in modeling the outputs of solar desalination systems. For instance, it is difficult to propose comprehensive models with applicability for different types of solar-assisted desalination systems. For this purpose, the type of desalination must be defined as a meaningful variable. In addition, different working conditions may affect the performance of the systems, which must be distinguished and considered in inputs of the models. Furthermore, since the experimental data are used for modeling, it may cause some problems due to different accuracies of measuring systems. Despite the mentioned problems and limitations, there are some recommendations that can improve the upcoming studies. First of all, the majority of the works are on thermal desalination modules, while these methods can be developed for the solar-powered RO systems and other desalination systems powered by solar-based hybrid systems such as solar/geothermal or solar/wind. In addition, most of the proposed models are applicable for just one type of solar desalination, while their comprehensiveness can be improved by considering more inputs. For instance, using the dimensions of desalination systems is one of the ways that can be used to extend the application of the models. Furthermore, in the case of nanofluidic solar desalination, using the properties of nanofluids such as their concentration and properties of particles can lead to proposing a model with a higher level of applicability. Another point that must be considered in the future works is utilizing more recent optimization approaches to reach higher exactness. In this regard, hybrid optimization algorithms would be attractive options. Furthermore, it would be useful to use data-driven methods for other purposes such as modeling systems from economic and environmental points of view. In addition, the majority of the studies have focused on water productivity as the output of the model, while it would be useful and beneficial to model other technical criteria such as energy and exergy efficiency of the systems. Finally, it is suggested to compare different approaches in terms of the required time for the training process.
Conclusion
In the provided article, applications of data-driven methods in solar desalination system modeling are provided. Different variables have been used as the inputs in the models proposed for solar desalination systems including solar radiation, ambient conditions, etc. The main findings of this review article are as follows:
• Compared with the correlation, intelligent methods can model the solar desalination systems more accurately.
• Different parameters such as productivity, energy, and exergy efficiency can be modeled by using the intelligent methods.
• The accuracy of the suggested models is influenced by different elements such as the applied method and algorithm and the considered inputs.
• Coupling optimization methods with the models will improve the accuracy due to adjusting the hyperparameters to their optimum values.
• In addition to the applied method for modeling, the type of the optimization algorithm influences the exactness of the models.
• Operating conditions such as solar radiation and relative humidity in addition to the properties of the feed and saline water are among the most important factors that must be used as inputs.
• The outputs of the models, obtained by intelligent methods, can be used to optimize the systems.
• Most of the studies have considered water productivity as the output of the model, while it would be beneficial to consider other technical criteria such as energy and exergy efficiency of the system.
• In addition to technical criteria, considering other factors such as environmental and economical parameters as outputs of the models would be useful.
• It is suggested to compare the intelligent models in terms of required time and calculations for the training process with different algorithms and approaches.
• Applying hybrid optimization algorithms, with more proper ability in finding optimal solutions, can lead to more precise models.
Statements
Author contributions
MA and MS have designed the work and contributed in writing and implementation of the work. IM and KY have contributed in implementation of the work and edition. BM edited the manuscript and contributed in writing.
Funding
This work was partially supported by Universiti Sains Malaysia under Short-term grant No. 304/PELECT/6315330.
Conflict of interest
The authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.
Publisher’s note
All claims expressed in this article are solely those of the authors and do not necessarily represent those of their affiliated organizations or those of the publisher, the editors, and the reviewers. Any product that may be evaluated in this article or claim that may be made by its manufacturer is not guaranteed or endorsed by the publisher.
Abbreviations
ANFIS, adaptive neuro-fuzzy inference system; ANN, artificial neural network; BP, backpropagation; FF, feed forward; GA, genetic algorithm; ICM, imperialist competition method; MLP, multilayer perceptron; MLR, multiple linear regression; PSO, particle swarm optimization; PV, photovoltaic; RBF, radial basis function; RF, random forest; RO, reverse osmosis; SVM, support vector machine.
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Summary
Keywords
solar desalination, artificial neural network, data-driven methods, renewable energies, review
Citation
Alhuyi Nazari M, Salem M, Mahariq I, Younes K and Maqableh BB (2021) Utilization of Data-Driven Methods in Solar Desalination Systems: A Comprehensive Review. Front. Energy Res. 9:742615. doi: 10.3389/fenrg.2021.742615
Received
21 July 2021
Accepted
02 September 2021
Published
07 October 2021
Volume
9 - 2021
Edited by
Mamdouh El Haj Assad, University of Sharjah, United Arab Emirates
Reviewed by
Willy Villasmil, Lucerne University of Applied Sciences and Arts, Switzerland
Muhammad Ahmad Jamil, Northumbria University, United Kingdom
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© 2021 Alhuyi Nazari, Salem, Mahariq, Younes and Maqableh.
This is an open-access article distributed under the terms of the Creative Commons Attribution License (CC BY). The use, distribution or reproduction in other forums is permitted, provided the original author(s) and the copyright owner(s) are credited and that the original publication in this journal is cited, in accordance with accepted academic practice. No use, distribution or reproduction is permitted which does not comply with these terms.
*Correspondence: Mohamed Salem, salemm@usm.my
This article was submitted to Process and Energy Systems Engineering, a section of the journal Frontiers in Energy Research
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