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Article

Estimation of Reference Evapotranspiration in Semi-Arid Region with Limited Climatic Inputs Using Metaheuristic Regression Methods

by
Saad Sh. Sammen
1,
Ozgur Kisi
2,3,*,
Ahmed Mohammed Sami Al-Janabi
4,
Ahmed Elbeltagi
5 and
Mohammad Zounemat-Kermani
6,*
1
Department of Civil Engineering, College of Engineering, Diyala University, Baquba 32001, Iraq
2
Department of Civil Engineering, Technical University of Lübeck, 23562 Lübeck, Germany
3
Department of Civil Engineering, Ilia State University, 0162 Tbilisi, Georgia
4
Department of Civil Engineering, Cihan University-Erbil, Kurdistan Region, Erbil 44001, Iraq
5
Agricultural Engineering Department, Faculty of Agriculture, Mansoura University, Mansoura 35516, Egypt
6
Department of Water Engineering, Shahid Bahonar University of Kerman, Kerman 93630, Iran
*
Authors to whom correspondence should be addressed.
Water 2023, 15(19), 3449; https://doi.org/10.3390/w15193449
Submission received: 28 August 2023 / Revised: 25 September 2023 / Accepted: 27 September 2023 / Published: 30 September 2023

Abstract

:
Different regression-based machine learning techniques, including support vector machine (SVM), random forest (RF), Bagged trees algorithm (BaT), and Boosting trees algorithm (BoT) were adopted for modeling daily reference evapotranspiration (ET0) in a semi-arid region (Hemren catchment basin in Iraq). An assessment of the methods with various input combinations of climatic parameters, including solar radiation (SR), wind speed (WS), relative humidity (RH), and maximum and minimum air temperatures (Tmax and Tmin), indicated that the RF method, especially with Tmax, Tmin, Tmean, and SR inputs, provided the best accuracy in estimating daily ET0 in all stations, while the SVM had the worst accuracy. This work will help water users, developers, and decision makers in water resource planning and management to achieve sustainability.

1. Introduction

Evapotranspiration is an important factor in the hydrological cycle and is used in water resource management for irrigation [1,2], drought estimation and monitoring [3,4,5], and in estimation of crop production [6,7]. Evapotranspiration (ET) could be defined as the amount of water that is transferred from the Earth’s surface to the atmosphere, and it plays a significant role in the world’s ecosystem that is related to water, energy, and carbon cycles [8,9]. ET is affected by different factors, including precipitation, temperature, relative humidity, wind speed, and solar radiation [10]. In addition, there is a common consent that terrestrial ET around the world has been changed as a result of climate change and human activity in the last decades [11,12,13,14,15]. Therefore, in order to calculate terrestrial ET, it is necessary to recognize the roles of water management, the hydrological cycle, and the impact of climate change [16,17].
Reference evapotranspiration (ET0) can be estimated using different methods and approaches, including statistical or empirical methods, remote-sensing methods, and physical model-based methods [11]. In the first method, ET0 is estimated using flux tower observations [18,19], while in the second method, ET0 is calculated using the integration of remote-sensing data with experimental observations [20,21], the surface energy balance equation [22,23], Penman–Monteith or Priestley–Taylor equations [24,25,26], and data assimilation methods [27,28,29]. In the third method, ET0 is estimated using a physical model alone or integrated with data-simulation algorithms [30,31,32]. Although several studies have used these methods globally, the daily estimation of ET0 using these methods comes with some uncertainty [33]. Relative variation between the observed and estimated values was found to range from 14% to 44% [34,35]. On the other hand, Lysimeters provide more precise measurements of ET values, and many researchers estimate ET by employing the measurements of Lysimeters [36,37]. Unfortunately, the use of Lysimeters has some drawbacks such as the cost of installation and maintenance, in addition to environmental impacts. Additionally, the restricted number of Lysimeters impedes the observation of ET at specific locations [38]. Based on the above, the development of new adequate methods to estimate reference evapotranspiration (ET0) with more accuracy and low cost is important and necessary.
In the last decades, the use of machine learning (ML) has received more attention in the field of water resource management around the world, including ET0 estimation. ML has been applied to estimate the parameters of hydrology [39,40,41,42,43,44,45], hydraulics [46,47,48,49], and water quality by many researchers [42,50,51,52,53]. Several previous studies have reported the capability of ML techniques in estimating ET0 [54]. A comparative study using two ML techniques, namely generalized regression neural networks (GRNN) and radial basis function neural networks (RBFNN), in addition to empirical methods for ET0 estimation in Algeria, is presented in [55]. It concluded that for ET0 estimation, the results obtained from the use of GRNN are better than those obtained from using the RBF. Another ML model, which is the support vector machine (SVM) model, was developed for ET0 estimation in [56] using limited climatic data. They used different parameters such as maximum and minimum temperature, wind speed, and solar radiation with several input combinations. The results acknowledged that the SVM is useful for ET0 estimation with acceptable accuracy. A comparison between an artificial neural network (ANN) with empirical approaches to estimate ET0 using the daily meterological data has also been conducted [57]. It used two types of ANN with three empirical approaches that included Priestley–Taylor, Makkink, Hargreaves, and mass transfer. In [58], different machine learning techniques were used for ET0 estimation with more actual and precise limited meteorological variables. The results generalized the relation between the various meteorological parameters. Moreover, the performance of ten ML techniques was evaluated in [59]. It used three statistical indices that included RMSE, R2, and bias to evaluate the modeling results. In [60], a deep neural network (DNN) model was developed for ET0 estimation using four meteorological stations in Turkey. In that study, the results of DNN were compared with results of ANN. The study revealed that the output of DNN was more accurate compared to that of ANN. In [61], eight ML techniques were evaluated in estimating ET0 using temperature data only. Additionally, the results were compared with the Hargreaves–Samani equation (a temperature-based equation). It was concluded that the accuracy of the developed models varied with various scenarios. Five machine learning models to predict daily ET0 across ten meteorological stations in China were developed in [62]. The results from comparison showed that the CAT model outperformed the other models. The overall findings of the previous studies indicate that the use of soft computing techniques for modeling the evaporation process is very promising, and further studies incorporating these techniques are recommended [63].
In this research, seven scenarios with different climate variables were evaluated by employing four regression-based ML techniques. To the best of the authors’ knowledge, these regression-based ML methods have not been previously compared in estimating ET0 in a semi-arid region.

2. Materials and Methods

2.1. Study Area

The catchment area of the Diyala River is at the eastern border of Iraq towards Iran. The northern part of it (within Iran) is mostly of mountainous character, with about 3000 m height. The Hemren Basin, a large catchment area located in the northeast of Iraq within the Diyala governorate, extends between (33°53′13.00″ to 35°25′41.61″ Northern latitude) and (44°30′47.68″ to 45°48′39.59″ Eastern longitude) inside Iraqi land, and it is located about 120 km northeast of Baghdad, the capital city in Iraq (Figure 1).
The relief of study area is characterized with topographic differences, their elevation ranges vary from 225 to 900 m above M.S.L. Therefore, the area was divided into three main regions. The length of the Diyala River within the catchment area is about 150 km, with an average gradient of 1 m per kilometer. Meanwhile, the Alwand River, which is the main tributary on the left side of the Diyala River, has a gradient of 2 m/km. It drains an area of 3974 km2, and without the part in Iranian land, the area is 1974 km2. The Narin River, which is the largest tributary on the right side, has a small gradient with a catchment area of 2344 km2, and empties into the Diyala River near Hemren Mountains. Moreover, the downstream part of the catchment area, located between Derbendi Khan and Hemren, has lower altitudes and gradients.

2.2. Employed Data

In the present study, the capability of four regression-based machine learning methods, SVM, RF, BoT and BaT, was investigated for ET0 estimation. Seven input scenarios were considered in this study using six climatic parameters, namely solar radiation (SR), wind speed (WS), relative humidity (RH), and maximum, mean, and minimum air temperatures (Tmax, Tmin, Tmean) as model inputs. The data were collected daily from five stations in Iraq, namely Mandali, Kalar, Iran–Iraq Border, Qarah-Tapah, and Adhim stations. Table 1 shows the statistical properties of the meteorological stations. The daily climate data during the period of 1979–2014 were collected from the study area and used for model development.

2.3. Machine Learning Models

This section briefly explains the input combinations and machine leaning methods used in this study. ET mainly depends on temperature and other climate variables as stated by previous studies. The idea in this study was creating some scenarios including temperature as the first variable and then combining it with other variables to select which scenario was the best for predicting ET0.
Support Vector Machines (SVM) are widely recognized as powerful machine learning (ML) models that yield valuable outcomes in both classification and regression problems. The SVM methodology employs structural risk minimization during the training process, which results in several effective features for simulating complex problems [46]. These features include the sparse presentation of solutions, good generalization ability, and the ability to avoid trapping in local minima. It is worth noting that the term Support Vector Regression (SVR) is commonly used for regression-based problems.
In this method, the input vector x is transformed into a higher-dimensional space through nonlinear mapping, where linear regression is applied to the input vector. Considering a solution space with x as the independent vector and y as the dependent vector variables for the dataset having N number of data pairs, the linear regression function can be written as:
f x = n = 1 N w n φ n x + b
where φ(x) represents a non-linear function that maps the low input space to the high output space; w represents the weights vector, while b denotes the threshold.
Unlike the SVR model, the other three ML models, RF, BaT, and BoT, are based on the concepts of decision and regression tree models that employ ensemble learning techniques. Decision tree learning is a supervised learning approach that is used to solve both classification and regression problems. Examples include Classification and Regression Tree (CART) models. In a decision tree model such as CART, each decision node in the tree represents a test on some input variables. Ensemble learning is a prosperous ML paradigm that merges a group of learners, rather than relying on a solitary learner, to forecast unfamiliar target attributes. It has been proven that using ensemble learning can improve the simulating and predicting results of individual models [64]. In this respect, two types of ensemble learning methodologies, namely bagging (here for the Bat and RF models) and boosting (here for the BoT model), are applied.
As indicated by [65], the BoT model incorporates important advantages of tree-based methods and has unique features. Its performance is based on an ensemble for training new samples. On the other hand, the bagging technique, also known as bootstrap aggregated, is an early ensemble method, which has numerous trees designed to improve the stability and accuracy of models. In the BaT, multiple independent decision trees can be constructed simultaneously on different segments of the training samples by utilizing distinct subsets of accessible characteristics.
Random forests are one of the most popular machine learning algorithms. They are so successful because they provide in general good predictive performance, low over-fitting, and easy interpretability. This interpretability is given by the fact that it is straightforward to derive the importance of each variable on tree decision. In other words, it is easy to compute how much each variable is contributing to the decision. The RF model acts similar to the BaT by constructing different decision trees. However, it uses a classification methodology for combining multiple trees to arrive at a conclusive outcome using the voting technique. Consequently, the RF classifier exhibits a robust ability to generalize. The RF can be considered as a specified type of the Bootstrap model. In each stage, the system has two subdivisions as unconnected segments to reduce the mean squared error values.
Feature selection through the random forest (RF) is categorized as an embedded method. Embedded methods encompass the advantages of both filter and wrapper techniques, as they rely on algorithms with built-in feature selection capabilities. Embedded methods offer several advantages, including:
High accuracy: They yield precise results.
Improved generalization: They enhance the model’s ability to apply learned patterns to new data.
Interpretability: They provide insights into the significance of selected features.
Random forest comprises multiple decision trees, each constructed using a random subset of observations and a random subset of features from the dataset. This means that not every tree processes all the features or observations. This design ensures that the trees are uncorrelated, reducing the risk of overfitting. Each tree is essentially a sequence of binary questions based on individual or combined features. At each node (corresponding to each question), the tree partitions the dataset into two groups, each containing observations that are more similar to each other and dissimilar to those in the other group. Consequently, the importance of each feature is determined by how “pure” each of these partitioned groups becomes.

2.4. Evaluation of Models’ Performance

The most important step in using machine-learning models is evaluating their accuracy. Performance evaluation of the four soft computing models was conducted based on regression analysis using four statistical indices, namely mean absolute error (MAE), root mean square error (RMSE), mean square error (MSE), and coefficient of determination (R2).

3. Results

The utilized input scenarios for daily ET0 estimation are presented in Table 2. From the table, the first Scenario (M1) used full variables as inputs, while the seventh Scenario (M7) had only two variables, Tmean and SR. The performance metrics of the employed methods in estimating daily ET0 of the five stations are presented in the following sections.

3.1. Qarah-Tapah Station

From Figure 2 and Table 3, the performance metrics of the employed methods in estimating the daily ET0 of the Qarah-Tapah station shows that the RF method had R2, MSE, RMSE, and MAE ranges from 0.86 (RF-5) to 1 (RF-1), from 0.05 (RF-2) to 0.414 (RF-5), from 0.074 (RF-2) to 0.643 (RF-5), and from 0.055 (RF-2) to 0.487 (RF-5), respectively. It is evident from the metrics’ ranges that the RF method was generally more successful in estimating the daily ET0 of the Qarah-Tapah station. Another finding is that for the RF method, there was a small difference between the first and second scenarios, and the second one produced the best accuracy. The other methods behaved differently, for example, the first and second input combinations provided the same accuracy for the BoT method. The M1 scenario had slightly better accuracy than the M2 for the SVM method, while the first scenario performed worse compared to latter for the BaT. This difference can be explained by the different working principles of the four implemented methods. The best estimates belonged to the RF method, followed by the BaT methods, while the SVM generally produced the worst ET0 estimates.

3.2. Mandali Station

The test performances of the RF, SVM, BoT, and BaT methods in estimating ET0 of the Mandali Station are reported in Figure 3 and Table 4. Here, it was also clear that the RF-2 model had the lowest MSE (0.024), RMSE (0.156), and MAE (0.059) followed by those of the RF-1 and BaT-2 models, while SVM produced the worst estimates, similar to the previous station.

3.3. Kalar Station

Figure 4 and Table 5 present the test performances of the implemented four methods in estimating ET0 of the Kalar Station. Similarly to Qarah-Tapah and Mandali stations, the RF-2 model provides the best performance with the lowest MSE (0.022), RMSE (0.148), and MAE (0.056) and the highest R2 (0.998), followed by those of RF-1 and BaT-2 models. In this station, the BaT and BoT ranked second and third, while the SVM was the least accurate model.

3.4. Iraq–Iran Station

Figure 5 and Table 6 give the performance metrics of the four methods in the test period of the Iraq–Iran Border station. In this station, RF-2 also ranked first by providing the lowest MSE (0.020), RMSE (0.143), and MAE (0.055) and the highest R2 (0.998), followed by those of the RF-1 and BaT-2 models. Here as well BoT and BaT performed superior to the SVM method. Again, the fifth scenario provided the worst results, while the first and second input scenarios had the best ET0 estimates.

3.5. Adhim Station

The performance measures of the RF, SVM, BoT, and BaT methods in estimation at the Adhim Station are presented in Figure 6 and Table 7. The RF-2 model had the lowest MSE (0.006), RMSE (0.078), and MAE (0.058), followed by those of the RF-1 and BaT-2 models. SVM generally produced the worst estimates, while BaT and BoT methods followed the RF in accuracy for estimating the daily ET0. Models including the first and/or scond scenarios perform the best, while models with the fifth combination had the worst results. In this station, BoT-1 had better accuracy than BoT-2 did; however, this difference was marginal.
Overall, the RF method, especially with the Tmax, Tmin, Tmean, and SR inputs, provided the best accuracy in estimating the daily ET0 of all stations. Its accuracy was followed by that of the BaT and BoT methods, while SVM had the worst accuracy. In most cases, the second input scenario provided the best accuracy in estimating the daily ET0. It is also worth noting that the seventh input scenario, having only Tmean and SR inputs, performed superior to the fourth, fifth, and sixth input scenarios. These results are contrary to those of [56], where a support vector machine (SVM) model was developed for ET0 estimation using limited climatic data (i.e., maximum and minimum temperature, wind speed, and solar radiation). The results in that study acknowledged that the SVM was useful for ET0 estimation with acceptable accuracy.
On the other hand, [66] used two machine-learning methods, random vector functional link (RVFL) and relevance vector machine (RVM), in modeling ET0 using limited climatic data, Tmax, Tmin, and extraterrestrial radiation with various input combinations and three data split scenarios. The study indicated that using only the temperature input (Tmin, Tmax) provided the worst ET0 estimations. Other studies also acknowledged similar results [67,68]. Another study found that temperature-based models involving temperature and Ra inputs offer promising results [61].
Figure 7 and Figure 8 illustrate the time variation and scatter plots of the best model (RF-2) estimates. It is clear from Figure 7 that the ET0 estimates by RF-2 were closely following the observed values. The models’ ranks from the best to worst are presented in Table 8. From Table 8, we can say that the first or second input scenarios, inlcuding Tmax, Tmin, Tmean, SR, WS, and RH; and Tmax, Tmin, Tmean and SR variables, respectively, generally provided the best estimates, while the fifth scenario, involving RH, WS, and Tmax, gave the worst ET0 estimates. The main reason of this might be the fact that the SR input is very effective for ET0, and not having it in this combination (fifth) and involving the WS parameter may worsen the estimation accuracy. Adding some input variables may negatively affect the variance and cause worse model accuracy in machine learning modeling. Here, adding WS might deteriorate the model’s performance, as this can be observed from the first and second input cases. From Table 8 it can also clearly be seen that for the Kalar Station, the first and second scenarios produced the best estimates, whereas the fifth scenario had the worst results. As clearly seen from Figure 8, the fit line of RF-2 overlapped the ideal line (1:1 line), and it had a high correlation for all stations. All these results highly recommend the RF method in estimating daily ET0.

4. Discussion

Evapotranspiration plays a significant role in the hydrological cycle and finds applications in water resource management, including irrigation, as well as in the assessment and surveillance of drought conditions [69,70,71,72,73,74,75,76]. Four different regression-based machine learning methods were compared for modeling daily reference evapotranspiration (ET0) for a semi-arid region (the Hemren catchment basin in Iraq). The comparison statistics indicated that the random forest method with Tmax, Tmin, Tmean, and SR inputs performed superior to the other methods in estimating the daily ET0 at all stations, while the SVM had the worst accuracy. Random forest (RF) is a popular machine-learning algorithm known for its strong predictive performance, minimal overfitting, and ease of interpretability. RF constructs multiple decision trees and combines them using a voting mechanism, resulting in robust generalization capabilities. One key feature of RF is its use of embedded methods for feature selection, which combines the strengths of filter and wrapper methods. Embedded methods are known for their high accuracy, excellent generalization, and interpretability. RF builds multiple decision trees, each using a random subset of data observations and features. This ensures that the trees are uncorrelated and less prone to overfitting. Each tree consists of a series of questions based on features, with each question dividing the data into two groups based on their similarity, ultimately determining the importance of each feature. In summary, RF is a powerful machine learning algorithm valued for its predictive abilities, robustness, and interpretability, making it a popular choice in various applications.
In [55], ET0 estimation was carried out using radial based artificial neural networks (RBNNs) and generalized regression artificial neural networks (GRNNs). The inputs for this estimation included daily mean relative humidity, sunshine duration, maximum and minimum air temperatures, mean air temperature, and wind speed. The study yielded the best R2 values of 0.868 and 0.889 for the RBNN and GRNN, respectively. Granata and Nunno [77] adopted two deep learning methods, NARX and LSTM, to model ET0. They experimented with various input combinations, including solar radiation, mean air temperature, sensible heat flux, relative humidity, and lagged ET0 values. The results showed R2 values of 0.687 and 0.837 as the best performance achieved by the LSTM and NARX models, respectively. The table data in Table 3, Table 4, Table 5, Table 6 and Table 7 clearly demonstrate that the proposed methods achieved remarkable success in modeling ET0.

5. Conclusions

In this study, the applicability of four different regression-based machine learning methods in estimating ET0 was investigated. Climatic data from five stations located in a semi-arid region of Iraq was used as inputs to the models. According to comparison statistics (R2, MSE, RMSE, and MAE) and graphical inspection, the random forest model offered the best ET0 estimates in all stations, while the SVM provided the worst accuracy. Employing various combinations of climatic inputs revealed that the models with Tmax, Tmin, Tmean, and SR inputs produced the best estimations. The best random forest model with Tmax, Tmin, Tmean, and SR improved the estimation accuracy of the SVM, BoT, and BaT models by 94%, 83%, and 38% for Qarah-Tapah, by 68%, 50%, and 8% for Mandali, by 73%, 49%, and 8% for Kalar, by 72%, 51%, and 9% for Iran–Iraq Border, and by 93%, 81%, and 73% for Adhim with respect to RMSE in the test period, respectively. The outcomes of the study recommend random forest for estimating ET0 in a semi-arid region. The study used data from one region, and more data can be used to assess the regression-based machine learning methods in future studies. The regression-based methods considered in this study may be compared with more complex machine learning methods.

Author Contributions

Conceptualization: S.S.S., A.M.S.A.-J., O.K., and A.E.; data creation: O.K. and S.S.S.; formal analysis: O.K. and S.S.S.; investigation: O.K. and A.M.S.A.-J.; methodology: S.S.S. and A.M.S.A.-J.; software: A.E. and O.K.; validation: S.S.S. and O.K.; writing—original draft: O.K., A.M.S.A.-J. and S.S.S.; writing—review and editing, S.S.S., A.M.S.A.-J., O.K., A.E and M.Z.-K. All authors have read and agreed to the published version of the manuscript.

Funding

This research received no external funding.

Data Availability Statement

It will be available on request.

Conflicts of Interest

The authors declare no conflict of interest.

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Figure 1. Location of the study area.
Figure 1. Location of the study area.
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Figure 2. The effectiveness of the applied models in daily ET0 estimation at the Qarah-Tapah station.
Figure 2. The effectiveness of the applied models in daily ET0 estimation at the Qarah-Tapah station.
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Figure 3. The effectiveness of the applied models in daily ET0 estimation at the Mandali station.
Figure 3. The effectiveness of the applied models in daily ET0 estimation at the Mandali station.
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Figure 4. The effectiveness of the applied models in daily ET0 estimation at the Kalar station.
Figure 4. The effectiveness of the applied models in daily ET0 estimation at the Kalar station.
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Figure 5. The effectiveness of the applied models in daily ET0 estimation at the Iraq–Iran Border station.
Figure 5. The effectiveness of the applied models in daily ET0 estimation at the Iraq–Iran Border station.
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Figure 6. The effectiveness of the applied models in daily ET0 estimation at the Adhim station.
Figure 6. The effectiveness of the applied models in daily ET0 estimation at the Adhim station.
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Figure 7. The temporal distribution of observed vs. estimated monthly ET0 values yielded by the best RF-2 model corresponding to M2 at (a) Qarah-Tapah, (b) Mandali, (c) Kalar, (d) Iraq–Iran Border, and (e) Adhim stations during the testing period.
Figure 7. The temporal distribution of observed vs. estimated monthly ET0 values yielded by the best RF-2 model corresponding to M2 at (a) Qarah-Tapah, (b) Mandali, (c) Kalar, (d) Iraq–Iran Border, and (e) Adhim stations during the testing period.
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Figure 8. Scatter plots of the best RF-2 model corresponding to M2 for monthly ET0 estimation at (a) Qarah-Tapah, (b) Mandali, (c) Kalar, (d) Iraq–Iran Border, and (e) Adhim stations during the testing period.
Figure 8. Scatter plots of the best RF-2 model corresponding to M2 for monthly ET0 estimation at (a) Qarah-Tapah, (b) Mandali, (c) Kalar, (d) Iraq–Iran Border, and (e) Adhim stations during the testing period.
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Table 1. Details of meteorological stations used in this study.
Table 1. Details of meteorological stations used in this study.
Station NameStation LocationTemperature (°C)Relative Humidity (%)Solar Radiation (MJ/m2)Wind Speed (m/s)
Lon.Lat.Max.Min.Max.Min.Max.Min.Max.Min.
Mandali45.3133.8851.18−8.76963.232.20.8112.70.7
Kalar45.3134.5050.31−4.69983.532.650.310.250.72
Iraq–Iran Border45.6334.1948.82−11.6796.63.6233.280.5611.130.63
Adhim44.6834.1852.23−3.45993.732.050.310.820.66
Table 2. Scenarios of input combinations used for daily ET0 estimation at study stations.
Table 2. Scenarios of input combinations used for daily ET0 estimation at study stations.
Scenario CodeInputsTechnique
RFSVMBoTBaT
M1Tmax, Tmin, Tmean, SR, WS, and RH××××
M2Tmax, Tmin, Tmean, and SR××××
M3Tmean, SR, and WS××××
M4SR, WS, RH, andTmin××××
M5RH, WS, and Tmax××××
M6Tmax, RH, and Tmin××××
M7Tmean and SR××××
Table 3. The effectiveness of the applied models in daily ET0 estimation at the Qarah-Tapah station during the testing period.
Table 3. The effectiveness of the applied models in daily ET0 estimation at the Qarah-Tapah station during the testing period.
ModelML AlgorithmPerformance Metric
R2MSE (mm/day)2RMSE (mm/day)MAE (mm/day)
M1RF-11.000.0060.0770.061
SVM-10.970.0770.2800.230
BoT-10.990.0290.1720.135
BaT-10.990.0190.1410.085
M2RF-20.9980.0050.0740.055
SVM-20.970.0860.2930.239
BoT-20.990.0290.1720.135
BaT-21.000.0080.0910.052
M3RF-30.990.0290.1700.125
SVM-30.970.0890.2990.241
BoT-30.980.0440.2110.161
BaT-30.980.0530.2290.163
M4RF-40.990.0430.2080.149
SVM-40.960.1050.3250.258
BoT-40.980.0540.2320.174
BaT-40.990.0290.1710.122
M5RF-50.860.4140.6430.487
SVM-50.870.3670.6060.488
BoT-50.900.2970.5450.439
BaT-50.900.2970.5450.428
M6RF-60.900.2880.5360.395
SVM-60.910.2670.5160.421
BoT-60.920.2410.4900.398
BaT-60.920.2290.4780.372
M7RF-70.990.0310.1760.129
SVM-70.970.0920.3030.245
BoT-70.980.0450.2120.161
BaT-70.990.0260.1620.119
Table 4. The effectiveness of the applied models in daily ET0 estimation at the Mandali station during the testing period.
Table 4. The effectiveness of the applied models in daily ET0 estimation at the Mandali station during the testing period.
ModelML AlgorithmPerformance Metric
R2MSE (mm/day)2RMSE (mm/day)MAE (mm/day)
M1RF-10.990.0250.1570.067
SVM-10.980.0650.2550.206
BoT-10.980.0480.2200.146
BaT-10.990.0360.1890.090
M2RF-20.9980.0240.1560.059
SVM-20.970.0750.2740.223
BoT-20.980.0480.2200.146
BaT-20.990.0260.1610.066
M3RF-30.980.0560.2370.150
SVM-30.970.0880.2960.237
BoT-30.980.0690.2630.180
BaT-30.970.0770.2780.181
M4RF-40.970.0740.2720.176
SVM-40.960.1090.3300.262
BoT-40.970.0800.2830.195
BaT-40.980.0550.2360.147
M5RF-50.850.4250.6520.492
SVM-50.870.3600.6000.481
BoT-50.890.3100.5560.442
BaT-50.890.3090.5560.431
M6RF-60.890.3160.5620.414
SVM-60.900.2630.5130.418
BoT-60.910.2590.5090.406
BaT-60.910.2500.5000.385
M7RF-70.980.0630.2510.162
SVM-70.970.0930.3040.244
BoT-70.970.0710.2660.182
BaT-70.980.0540.2340.148
Table 5. The effectiveness of the applied models in daily ET0 estimation at the Kalar station during the testing period.
Table 5. The effectiveness of the applied models in daily ET0 estimation at the Kalar station during the testing period.
ModelML AlgorithmPerformance Metric
R2MSE (mm/day)2RMSE (mm/day)MAE (mm/day)
M1RF-10.990.0220.1490.062
SVM-10.970.0710.2680.216
BoT-10.980.0440.2100.138
BaT-10.990.0340.1860.087
M2RF-20.9980.0220.1480.056
SVM-20.970.0800.2840.231
BoT-20.980.0430.2090.137
BaT-20.990.0240.1550.060
M3RF-30.980.0460.2150.132
SVM-30.970.0870.0290.238
BoT-30.980.0580.2420.162
BaT-30.980.0690.2630.169
M4RF-40.980.0610.2480.157
SVM-40.960.1040.3220.257
BoT-40.970.0690.2630.178
BaT-40.980.0470.2170.131
M5RF-50.850.4120.6410.484
SVM-50.880.3430.5860.476
BoT-50.890.3020.5490.439
BaT-50.890.3000.5480.429
M6RF-60.900.2880.5360.390
SVM-60.910.2430.4930.403
BoT-60.910.2440.4940.395
BaT-60.910.2300.4800.368
M7RF-70.980.0470.2170.134
SVM-70.970.0890.2990.242
BoT-70.980.0580.2420.163
BaT-70.980.0420.2060.124
Table 6. The effectiveness of the applied models in daily ET0 estimation at the Iraq–Iran Border station during the testing period.
Table 6. The effectiveness of the applied models in daily ET0 estimation at the Iraq–Iran Border station during the testing period.
ModelML AlgorithmPerformance Metric
R2MSE (mm/day)2RMSE (mm/day)MAE (mm/day)
M1RF-10.990.0210.1450.062
SVM-10.970.0640.2530.204
BoT-10.980.0410.2030.133
BaT-10.990.0320.1780.084
M2RF-20.9980.0200.1430.055
SVM-20.970.0710.2660.216
BoT-20.980.0410.2030.133
BaT-20.990.0220.1510.059
M3RF-30.980.0420.2050.125
SVM-30.970.0780.2790.225
BoT-30.980.0550.2370.157
BaT-30.980.0600.2460.156
M4RF-40.980.0580.2410.154
SVM-40.960.0930.3060.242
BoT-40.970.0670.2590.175
BaT-40.980.0450.2130.130
M5RF-50.840.4010.6330.478
SVM-50.870.3290.5740.466
BoT-50.880.2870.5360.427
BaT-50.880.2860.5340.418
M6RF-60.890.2640.5140.375
SVM-60.910.2300.4800.390
BoT-60.910.2280.4770.383
BaT-60.910.2170.4660.358
M7RF-70.980.0450.2130.132
SVM-70.970.0800.2830.228
BoT-70.980.0560.2370.158
BaT-70.980.0410.2020.121
Table 7. The effectiveness of the applied models in daily ET0 estimation at the Adhim station during the testing period.
Table 7. The effectiveness of the applied models in daily ET0 estimation at the Adhim station during the testing period.
ModelML AlgorithmPerformance Metric
R2MSE (mm/day)2RMSE (mm/day)MAE (mm/day)
M1RF-11.000.0060.0820.061
SVM-10.970.0750.2750.222
BoT-10.990.0310.1780.140
BaT-10.990.0330.1840.093
M2RF-20.9980.0060.0780.058
SVM-20.970.0820.2870.234
BoT-20.990.0320.1790.140
BaT-20.990.0220.1480.059
M3RF-30.990.0340.1850.134
SVM-30.970.0860.2940.234
BoT-30.980.0530.2310.173
BaT-30.980.0680.2610.173
M4RF-40.980.0470.2180.156
SVM-40.970.1030.3210.253
BoT-40.980.0580.2410.182
BaT-40.990.0310.1770.127
M5RF-50.860.4050.6360.481
SVM-50.880.3670.6060.485
BoT-50.900.2960.5440.434
BaT-50.900.2920.5410.422
M6RF-60.890.3190.5650.415
SVM-60.900.3010.5480.443
BoT-60.910.2530.5030.404
BaT-60.920.2430.4930.381
M7RF-70.980.0440.2110.152
SVM-70.970.0900.3000.239
BoT-70.980.0570.2390.178
BaT-70.980.4910.2210.143
Table 8. Ranks of ML models based on the five stations.
Table 8. Ranks of ML models based on the five stations.
ModelML AlgorithmModels’ Ranks Based on Stations
Qarah-TapahMandaliKalarIraq–Iran BorderAdhim
M1RF-122222
SVM-1168888
BoT-1615161515
BaT-1423232324
M2RF-211111
SVM-2179999
BoT-2716151616
BaT-2322222222
M3RF-383333
SVM-31810101010
BoT-31217171717
BaT-31426262626
M4RF-4115555
SVM-42012121212
BoT-41519191919
BaT-4925252523
M5RF-5287777
SVM-52714141414
BoT-52621212121
BaT-52528282828
M6RF-6246666
SVM-62313131313
BoT-62220202020
BaT-62127272727
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MDPI and ACS Style

Sammen, S.S.; Kisi, O.; Al-Janabi, A.M.S.; Elbeltagi, A.; Zounemat-Kermani, M. Estimation of Reference Evapotranspiration in Semi-Arid Region with Limited Climatic Inputs Using Metaheuristic Regression Methods. Water 2023, 15, 3449. https://doi.org/10.3390/w15193449

AMA Style

Sammen SS, Kisi O, Al-Janabi AMS, Elbeltagi A, Zounemat-Kermani M. Estimation of Reference Evapotranspiration in Semi-Arid Region with Limited Climatic Inputs Using Metaheuristic Regression Methods. Water. 2023; 15(19):3449. https://doi.org/10.3390/w15193449

Chicago/Turabian Style

Sammen, Saad Sh., Ozgur Kisi, Ahmed Mohammed Sami Al-Janabi, Ahmed Elbeltagi, and Mohammad Zounemat-Kermani. 2023. "Estimation of Reference Evapotranspiration in Semi-Arid Region with Limited Climatic Inputs Using Metaheuristic Regression Methods" Water 15, no. 19: 3449. https://doi.org/10.3390/w15193449

APA Style

Sammen, S. S., Kisi, O., Al-Janabi, A. M. S., Elbeltagi, A., & Zounemat-Kermani, M. (2023). Estimation of Reference Evapotranspiration in Semi-Arid Region with Limited Climatic Inputs Using Metaheuristic Regression Methods. Water, 15(19), 3449. https://doi.org/10.3390/w15193449

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