Evapotranspiration Estimation in the Arab Region: Methodological Advances and Multi-Sensor Integration Framework
Abstract
1. Introduction
1.1. ET Concepts
1.2. ET Estimation Methods
Method | Data Requirements | Strengths | Limitations | Source |
---|---|---|---|---|
Penman-Monteith | Full meteorological data (T, RH, wind, radiation) | High accuracy, widely validated | Needs comprehensive data | Sun et al. [12] |
Hargreaves-Samani | Mainly temperature | Simple, minimal data required | Underestimates ET, needs local calibration | Azzam et al. [10] |
Thornthwaite | Temperature | Simple, easy to apply | Less accurate in arid climates | Aschonitis et al. [17] |
Remote Sensing (SEBS, etc.) | Satellite data (LST, NDVI, etc.) | Large-scale, spatially continuous, multi-sensor | Requires validation, complex processing | Xue et al. [6] |
- Physics-based Penman-Monteith principles for physical consistency.
- Satellite-derived NDVI, surface temperature, and radiation for spatial precision.
- Machine learning models (e.g., Random Forest, LSTM networks) to estimate missing parameters.
2. Methodological Framework
2.1. Bibliometric Analysis of ET Studies
2.2. Application of Fusion-Based ET Estimation
3. Results and Discussion
3.1. Evapotranspiration Research Distribution Across Arab Countries
- Data constraints: The lack of long-term, high-quality meteorological and land-use data restricts researchers’ ability to conduct comprehensive ET assessments, hindering model calibration and accuracy. Commonly missing datasets in the Arab region include, for example, long-term rainfall records, radiation, and temperature data. El-Shirbeny et al. [4] employed simulated meteorological datasets to compensate for the spatial and temporal limitations of ground-based weather observations across the Arab region. Aieb et al. [22] identified missing climatic data as a persistent challenge in climatology and proposed a regression-based imputation framework to reconstruct daily rainfall records in Algeria’s Soummam watershed. In Sudan, soil moisture estimates from the Climate Prediction Center deviated by up to 106% from ground measurements, largely due to mismatches in spatial resolution and rainfall variability. Similarly, the Climate Research Unit’s (CRU) potential ET estimates underestimated values by about 7–37%, affecting water balance accuracy [23]. Technical and expertise gaps: ET studies demand advanced hydrological modelling, meteorological precision, and environmental science expertise, fields that remain underdeveloped in many Arab research institutions. Persistent technical and institutional gaps continue to hinder effective drought and ET monitoring across the MENA region. Bouhioui & Loudyi [24] highlight a significant disparity in modern drought monitoring techniques, largely driven by data inadequacies and insufficient early warning systems, despite growing research interest. These limitations reflect broader challenges in hydrometeorological modeling, environmental data integration, and regional capacity for climate resilience planning. El-Shirbeny et al. [4] highlight persistent technical limitations in ET monitoring across the Arab region, including sparse and unevenly distributed ground meteorological data, limited integration of GIS-based modeling frameworks, and reliance on cloud platforms such as Google Earth Engine to compensate for infrastructural constraints. The validation of satellite-derived ET estimates using only 35 ground stations further underscores the region’s restricted capacity for GIS-enabled monitoring and multi-source data fusion. Low research prioritisation: Socio-economic challenges divert national focus away from environmental research, leading to limited investment in hydrology and climate-related studies.
3.2. Common Methods Used in Arab Countries
- FAO Penman-Monteith Method (PM): Widely regarded as the standard approach. The PM method has been widely adopted in approximately 14% of evapotranspiration (ET) studies conducted in Arab countries, reflecting its robustness and reliability. Its application is particularly prominent in Egypt (18%), Saudi Arabia (15%), and Morocco (11%) (Table 2 and Table 3).
- Hargreaves-Samani Equation (HS): This empirical method is commonly used when comprehensive meteorological data are unavailable. It has been used in less than 2% of ET studies conducted across Arab countries, especially in Iraq (21%) and Morocco (16%). Integrating wind speed into the HS equation, coupled with an optimised coefficient set, significantly enhances its predictive reliability across diverse Iraqi regions, including high-altitude areas [22,26]. Ahmed et al. and Hadria et al. [23,27] claimed that the HS equation demonstrated moderate agreement with the PM method across Morocco’s arid and semi-arid zones. While practical in data-scarce settings, its accuracy declined in high-altitude or variable-climate regions. Recent calibration efforts of the HS equation across the Arab region emphasize the necessity of empirical refinement and contextual sensitivity in reference ET modeling. In Egypt, Anwar et al. [28] integrated a recalibrated HS formulation into the RegCM4 framework, demonstrating strong agreement with ERA5-derived PET estimates. Notably, modifying the radiation coefficient from 0.0135 to 0.0105 yielded superior bias reduction compared to adjustments in the temperature coefficient (17.8), particularly enhancing performance in arid and semi-arid zones with limited station data. Complementing this, Al-Alsadi et al. [26] assessed three HS variants across 103 Iraqi stations, revealing that the default global coefficients were inadequate for reliable ET0 estimation. The wind-adjusted variant also achieved full calibration and validation success. Collectively, these findings underscore the value of region-specific calibration, especially when incorporating local climatic drivers such as wind speed, in strengthening the operational reliability of HS-based ET0 estimation under data-scarce conditions across the Arab domain.
- Hargreaves Equation: This simplified empirical method estimates evapotranspiration using only temperature and extraterrestrial radiation, making it especially suitable for regions where meteorological data are scarce or incomplete. This equation has been used in approximately 3% of ET studies conducted across Arab countries, particularly in Iraq (17%), Morocco (14%), and Saudi Arabia (14%). In Morocco’s semi-arid region, unlike Priestley–Taylor and Makkink, which underestimated ET0, Hargreaves showed minimal bias, proving effective under data-scarce conditions [24,29].
- Thornthwaite Equation (TH): This temperature-based empirical method estimates potential ET using only mean monthly air temperature and latitude [17]. This model has been used in about 1% of ET studies conducted across Arab countries, particularly in Morocco (1.4%), Algeria (2.3%), and Sudan (1.9%). The TH equation was evaluated alongside other temperature-based models for estimating ET0 in Al-Baha, Saudi Arabia. While it offered simplicity, its performance was less accurate than the Linacre method (a temperature-based model), highlighting the need for local calibration under arid conditions [30]. The TH equation produced consistently higher evapotranspiration (ET0) estimates than the Blaney–Criddle, Pan evaporation, and Penman methods under desert conditions of Qatar [31]; during winter, TH values ranged from 2.3 to 6.2 mm/day, exceeding the 0.67 to 3 mm/day range observed in the other methods. Similarly, in summer, TH estimates spanned 11.1 to 12.9 mm/day, compared to 5.2 to 7.9 mm/day for the remaining approaches. These results highlight the tendency of the TH method to overestimate ET0, particularly under arid conditions, reinforcing the need for regional calibration [31].
- Remote Sensing Approaches: Given the sparse and uneven distribution of ground-based meteorological stations in many Arab countries, remote sensing methods have become increasingly important. Common satellite sources include MODIS, Landsat-8, and Sentinel-2. Validation protocols typically involve field observations and benchmarking against the FAO–Penman–Monteith method. Validation protocols involve field observations and the PM model [4,32,33]. These remote sensing-based models are effective for regional-scale ET mapping and have been validated using ground-based PM estimates in 24% of all ET studies in Arab countries, with extensive validation in Morocco (32%), Egypt (12%), Sudan (10%), and Tunisia (9%). Using Landsat-8 imagery and the SEBAL model, actual ET for winter wheat in Sudan’s central clay plain was accurately estimated [34].
- Machine Learning (ML): Machine learning techniques are increasingly used to estimate evapotranspiration (ET) by identifying complex, non-linear patterns in environmental data. ML approaches, including decision trees, support vector machines, and neural networks, offer high flexibility and can outperform conventional methods in data-rich environments. However, they require large, well-curated datasets and careful calibration to prevent overfitting, and their performance can vary depending on the model type and regional characteristics. Machine learning (ML) has been applied in only approximately 4% of evapotranspiration (ET) studies conducted in Arab countries. Notably, Morocco (25%), Egypt (18%), and Iraq (18%) account for the highest shares of these applications. However, nearly 50% of Arab countries have yet to produce a single ML-based ET study, indicating significant regional disparities and untapped research potential. Ahmed et al. [23] applied a bagging machine learning algorithm to assess evapotranspiration dynamics across Sudan, revealing a declining trend in actual evapotranspiration (AET) at −0.2% per year since 1960. This reduction, linked to rising temperatures and recurrent droughts, underscores the need for adaptive water management strategies. Despite the growing interest in ML for satellite-based ET modeling, its adoption remains limited due to several technical challenges. Overfitting is a persistent concern, particularly when models are trained on region-specific datasets with sparse ground truth, leading to poor generalization across diverse climatic zones [4,35]. Data preprocessing also poses a significant hurdle, as satellite inputs from MODIS, Landsat-8, and Sentinel-2 require rigorous cloud masking, radiometric correction, and temporal harmonization to ensure consistency [36]. Furthermore, the interpretability of complex ML models, especially deep learning architectures, remains a barrier to institutional and policy uptake, as black-box outputs lack transparency and hinder stakeholder trust [37]. Computational constraints further limit experimentation, particularly in resource-constrained settings where access to cloud platforms or GPU clusters is restricted [4]. Lastly, temporal drift due to climate variability challenges model robustness, as shifting vegetation dynamics and land-use patterns require frequent retraining to maintain predictive accuracy. Addressing these barriers through explainable AI, standardized preprocessing pipelines, and scalable validation frameworks is essential for advancing ML integration in ET monitoring across arid and semi-arid regions.
- Artificial Intelligence (AI): AI-based methods for estimating evapotranspiration (ET) utilise advanced computational algorithms that surpass traditional rule-based or empirical models. AI models offer high predictive accuracy when trained with robust, high-resolution data; however, they can be computationally intensive and require careful validation to ensure generalizability across diverse environmental conditions [4,38]. The application of AI methods in ET research in Arab countries remains in its infancy, accounting for only 1% of the total studies. Among these, Egypt, Iraq, and Saudi Arabia each contribute approximately 18%, reflecting early but concentrated efforts in select regions. Deep learning models, such as LSTM and GRU, demonstrated strong predictive performance for daily ET0 estimation in Sudan’s coastal Red Sea region, especially when combined with pseudo-labelling [39]. Explainability techniques such as SHAP and LIME, i.e., two widely adopted post-hoc interpretability methods, are increasingly recognized as critical enablers of policy uptake in AI-driven evapotranspiration (ET) modeling. By attributing model predictions to specific input features, such as vegetation indices, surface temperature, and net radiation, these tools provide transparent, instance-level insights into model behavior. This interpretability not only enhances stakeholder confidence but also facilitates regulatory validation and integration into national water governance frameworks. As highlighted by Linardatos et al. [37], such transparency is essential for managing uncertainty and ensuring the responsible deployment of complex AI and ML systems in sensitive environmental domains.
- Other Empirical and Semi-Empirical Methods: Additional approaches, such as the Blaney-Criddle, Priestley-Taylor, Kimberly-Penman, and Pan Evaporation methods, are also referenced in about 51% of ET studies across Arab countries. While less commonly used, these techniques are often adapted to specific local conditions or applied when data availability is constrained [30], particularly in Egypt (16%) and Tunisia (16%). A comparison of ET0 estimation methods against the PM standard found that the Makkink and Priestley–Taylor models could serve as viable alternatives under semi-arid conditions in Tunisia [40]. However, in Morocco’s Tensift Al Haouz region, both models significantly underestimated ET0, highlighting the location-dependent nature of their performance [29]. This variability underscores the need for regional calibration and adaptation when applying empirical ET models across diverse climatic zones. A cross-regional comparison of empirical ET0 models reveals significant variability in their performance under semi-arid conditions. In Tunisia, Latrech et al. [41] found that the Makkink and Priestley–Taylor models closely aligned with the FAO-PM standard, yielding high R2 values (0.80 and 0.89) and low RMSE values (0.93 and 1.04 mm day−1), indicating strong predictive reliability. However, in Morocco’s Tensift basin, Er-Raki et al. [29] observed substantial underestimation by the same models, 18% for Makkink and 20% for Priestley–Taylor, when using default coefficients. Calibration of the empirical parameters α and Cm via linear regression changed the bias in relative humidity to 4% and 9%, respectively, improving model accuracy by up to 76%. These findings underscore the necessity of localized calibration when applying radiation-based ET0 models across diverse Mediterranean semi-arid zones.
Model | Inputs | Strengths | Limitations | Typical Applications | Reference |
---|---|---|---|---|---|
Penman-Monteith | Full meteorological data | Physically robust; internationally standardized | Requires complete, quality-controlled data | Irrigated agriculture; climate zones with full data | Allen et al. [5] |
Hargreaves–Samani | Minimum and maximum temperature, extraterrestrial radiation | Simple, low data demand; suitable for arid regions with sparse observations | Sensitive to calibration; less accurate in humid climates | Regional climate modeling, data-scarce environments | Pandey and Pandey [42] |
Makkink | Solar radiation, air temperature | Good performance in temperate climates; fewer inputs than Penman–Monteith | Less reliable in arid zones; assumes constant psychrometric conditions | Irrigation scheduling, temperate zone hydrology | Zhang et al. [43] |
Priestley–Taylor | Net radiation, temperature, humidity | Strong performance in humid regions; physically grounded | Overestimates ET0 in arid zones; assumes ample moisture availability | Wetland hydrology, humid climate ET0 estimation | Xie et al. [44] |
Thornthwaite | Mean monthly temperature, latitude | Minimal data requirement; useful for long-term climatological studies | Oversimplified; poor accuracy in arid and tropical climates | Historical reference ET trends, water balance studies | Song et al. [45] |
Remote Sensing (RS) | Satellite data (LST, NDVI, albedo, etc.) | Scalable; spatially continuous; multi-sensor integration | Requires validation; complex processing | Regional ET mapping; crop monitoring | Elnashar et al. [46] |
Machine Learning (ML) | Multi-variable datasets; RS + meteorological | Captures non-linear patterns; flexible | Needs large training datasets; risk of overfitting | ET prediction in data-rich zones; fusion modeling | Amani et al. [38] |
Artificial Intelligence (AI) | Big data; RS inputs; climate variables | High precision; dynamic modeling | Computationally intensive; limited regional adoption | Climate resilience modeling; urban hydrology | Goyal et al. [47] |
Fusion (RS + ML/AI) | RS imagery + ground data + ML algorithms | High-resolution; reduces error; scalable | Sparse adoption; requires interdisciplinary expertise | ET monitoring in arid zones; policy integration | Guzinski et al. [21] |
3.3. Fusion
3.4. ET Implications for Climate Resilience and Agricultural Sustainability in the Arab Region
3.4.1. ET Research Addressing Climate Change in Arab Countries
3.4.2. ET Research in the Context of Food Security in Arab Countries
3.5. Strategic Alignment of Evapotranspiration (ET) Research with Research and Development Investment in the Arab Region
- Research priorities—Many Arab countries prioritise food security over long-term climate adaptation, given immediate socio-economic challenges.
- Policy misalignment—While agricultural innovation is widely supported, climate-focused ET studies often lack dedicated funding mechanisms and institutional backing.
- Data scarcity issues—Climate change research, particularly ET modelling for adaptation strategies, requires high-resolution, long-term datasets, which are limited across the Arab region, thereby restricting the study scope.
- Technological accessibility—AI-driven ET fusion models for climate adaptation are cost-intensive and require advanced expertise, leading to slower adoption and fewer studies in climate resilience domains.
- Increase targeted funding for ET-based climate resilience studies.
- Integrate ET research into national climate policies, bridging the gap between food security and environmental sustainability.
- Enhance regional collaboration to facilitate shared research efforts and cross-country adaptation initiatives.
- Improve data collection and accessibility to support AI-driven ET modelling and advanced fusion techniques.
4. Conclusions
Author Contributions
Funding
Data Availability Statement
Conflicts of Interest
Appendix A
Scale | PM | HGS | HG | THW | RS | ML | AI | Fusion | Other |
---|---|---|---|---|---|---|---|---|---|
Algeria | 16 | 2 | 3 | 2 | 12 | 7 | 2 | 0 | 40 |
Bahrain | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 1 |
Comoros | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
Djibouti | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 5 |
Egypt | 32 | 2 | 5 | 1 | 37 | 11 | 3 | 0 | 103 |
Iraq | 18 | 4 | 7 | 0 | 16 | 10 | 3 | 0 | 29 |
Jordan | 12 | 0 | 3 | 1 | 17 | 1 | 0 | 0 | 42 |
Kuwait | 6 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 12 |
Lebanon | 2 | 0 | 0 | 0 | 17 | 3 | 0 | 5 | 23 |
Libya | 3 | 1 | 2 | 0 | 0 | 0 | 1 | 0 | 3 |
Mauritania | 2 | 0 | 0 | 0 | 2 | 0 | 0 | 0 | 2 |
Morocco | 19 | 3 | 6 | 3 | 97 | 14 | 2 | 0 | 74 |
Oman | 5 | 0 | 0 | 0 | 5 | 1 | 0 | 0 | 18 |
Palestine | 1 | 0 | 0 | 0 | 3 | 0 | 0 | 0 | 8 |
Qatar | 4 | 1 | 3 | 0 | 1 | 0 | 1 | 0 | 4 |
Saudi Arabia | 26 | 2 | 6 | 1 | 28 | 3 | 3 | 1 | 55 |
Somalia | 0 | 0 | 0 | 0 | 3 | 0 | 1 | 0 | 8 |
Sudan | 13 | 2 | 3 | 2 | 30 | 4 | 1 | 1 | 49 |
Syria | 3 | 0 | 0 | 1 | 3 | 1 | 0 | 0 | 55 |
Tunisia | 12 | 2 | 4 | 0 | 28 | 0 | 0 | 0 | 103 |
UAE | 2 | 0 | 0 | 1 | 6 | 2 | 1 | 0 | 5 |
Yemen | 2 | 0 | 0 | 0 | 0 | 0 | 0 | 1 | 9 |
Arab countries | 0 | 0 | 0 | 0 | 1 | 0 | 0 | 0 | 0 |
MENA | 6 | 0 | 1 | 0 | 2 | 2 | 1 | 0 | 7 |
Arabian Peninsula | 1 | 0 | 2 | 0 | 6 | 1 | 1 | 0 | 23 |
North Africa | 6 | 1 | 1 | 2 | 13 | 1 | 2 | 0 | 69 |
SSA | 5 | 0 | 0 | 2 | 15 | 2 | 0 | 0 | 0 |
Appendix B
Scale | ET-Climate Change | ET-Food Security | Funded |
---|---|---|---|
Algeria | 37 | 5 | 2 |
Bahrain | 1 | 0 | 0 |
Comoros | 0 | 0 | 0 |
Djibouti | 2 | 1 | 1 |
Egypt | 48 | 15 | 14 |
Iraq | 40 | 1 | 1 |
Jordan | 21 | 7 | 6 |
Kuwait | 3 | 1 | 0 |
Lebanon | 12 | 3 | 2 |
Libya | 5 | 1 | 0 |
Mauritania | 1 | 0 | 1 |
Morocco | 64 | 9 | 0 |
Oman | 7 | 2 | 3 |
Palestine | 2 | 1 | 1 |
Qatar | 9 | 2 | 8 |
Saudi Arabia | 26 | 4 | 1 |
Somalia | 7 | 6 | 0 |
Sudan | 30 | 11 | 5 |
Syria | 11 | 4 | 1 |
Tunisia | 37 | 3 | 3 |
United Arab Emirates | 2 | 1 | 1 |
Yemen | 7 | 1 | 0 |
Arab countries | 0 | 0 | |
MENA | 16 | 1 | 2 |
Arabian Peninsula | 19 | 0 | 1 |
North Africa | 58 | 7 | 2 |
Sub-Saharan Africa | 4 | 2 | 7 |
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Scale | PM | HGS | HG | TH | RS | ML | AI | Other |
---|---|---|---|---|---|---|---|---|
Algeria | 9 | 11 | 7 | 17 | 4 | 12 | 12 | 6 |
Bahrain | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
Comoros | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
Djibouti | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 1 |
Egypt | 18 | 11 | 12 | 8 | 12 | 19 | 18 | 16 |
Iraq | 10 | 21 | 17 | 0 | 5 | 18 | 18 | 4 |
Jordan | 7 | 0 | 7 | 0 | 6 | 2 | 0 | 6 |
Kuwait | 3 | 0 | 0 | 0 | 0 | 0 | 0 | 2 |
Lebanon | 1 | 0 | 0 | 0 | 6 | 5 | 0 | 4 |
Libya | 2 | 5 | 5 | 0 | 0 | 0 | 6 | 0 |
Mauritania | 1 | 0 | 0 | 0 | 1 | 0 | 0 | 0 |
Morocco | 11 | 16 | 14 | 25 | 32 | 25 | 12 | 11 |
Oman | 3 | 0 | 0 | 0 | 2 | 2 | 0 | 3 |
Palestine | 1 | 0 | 0 | 0 | 1 | 0 | 0 | 1 |
Qatar | 2 | 5 | 7 | 0 | 0 | 0 | 6 | 1 |
Saudi Arabia | 15 | 11 | 14 | 8 | 9 | 5 | 18 | 8 |
Somalia | 0 | 0 | 0 | 0 | 1 | 0 | 6 | 1 |
Sudan | 7 | 11 | 7 | 17 | 10 | 7 | 6 | 8 |
Syria | 2 | 0 | 0 | 8 | 1 | 2 | 0 | 8 |
Tunisia | 7 | 11 | 10 | 0 | 9 | 0 | 0 | 16 |
UAE | 1 | 0 | 0 | 8 | 2 | 4 | 6 | 1 |
Yemen | 1 | 0 | 0 | 0 | 0 | 0 | 0 | 1 |
Average | 5 | 5 | 5 | 4 | 5 | 5 | 5 | 4 |
Standard deviation | 5 | 6 | 6 | 7 | 7 | 7 | 7 | 5 |
Coefficient of variation (%) | 113 | 140 | 126 | 174 | 157 | 159 | 134 | 111 |
Metric | Value | What It Means |
---|---|---|
MAE | 215 mm | On average, there is a 215 mm/year difference between ML-fused and traditional ET. |
RMSE | 531 mm | Sensitive to outliers—high values in some regions create larger deviations. |
r | 0.86 | Strong positive relationship—ML fusion follows the same spatial trend as traditional, but with improved precision. |
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Ahmed, S.M.; Biro Turk, K.G.; Ahmed, A.E.; Elbushra, A.A.; Aldhafeeri, A.A.; Darrag, H.M. Evapotranspiration Estimation in the Arab Region: Methodological Advances and Multi-Sensor Integration Framework. Water 2025, 17, 2702. https://doi.org/10.3390/w17182702
Ahmed SM, Biro Turk KG, Ahmed AE, Elbushra AA, Aldhafeeri AA, Darrag HM. Evapotranspiration Estimation in the Arab Region: Methodological Advances and Multi-Sensor Integration Framework. Water. 2025; 17(18):2702. https://doi.org/10.3390/w17182702
Chicago/Turabian StyleAhmed, Shamseddin M., Khalid G. Biro Turk, Adam E. Ahmed, Azharia A. Elbushra, Anwar A. Aldhafeeri, and Hossam M. Darrag. 2025. "Evapotranspiration Estimation in the Arab Region: Methodological Advances and Multi-Sensor Integration Framework" Water 17, no. 18: 2702. https://doi.org/10.3390/w17182702
APA StyleAhmed, S. M., Biro Turk, K. G., Ahmed, A. E., Elbushra, A. A., Aldhafeeri, A. A., & Darrag, H. M. (2025). Evapotranspiration Estimation in the Arab Region: Methodological Advances and Multi-Sensor Integration Framework. Water, 17(18), 2702. https://doi.org/10.3390/w17182702