SWAT Model and Drought Indices: A Systematic Review of Progress, Challenges and Opportunities
Abstract
1. Introduction
2. Materials and Methods
Data Acquisition
3. Results and Discussion
3.1. Analysis of Scientific Production
3.2. Analysis of Keywords and Their Co-Occurrences
3.3. Critical Appraisal of Literature
3.4. Research Gaps and Future Directions
3.5. Challenges and Advances in Tropical Regions: The Case of Brazil and the Future Research Agenda
4. Final Considerations
Author Contributions
Funding
Data Availability Statement
Acknowledgments
Conflicts of Interest
References
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| Ref. * | Research Focus | Calibration Accuracy | Advances | Limitations |
|---|---|---|---|---|
| [10] | To evaluate how the impact of climate change manifests differently in meteorological, agricultural, and hydrological droughts, and to assess the reliability of climate projections in estimating these droughts. | The SWAT model was calibrated in previous studies. | - Different GCM-RCM generate distinct results, underscore the importance of model selection; - Integrated assessment of climate change impacts on meteorological, agricultural, and hydrological droughts. | - Uncertainties inherent in GCM projections significantly impact the drought forecast and subsequent analysis; - The relatively short 10-year period used for data analysis limits the robustness of the results, limiting the capacity to capture long-term climatological variability required for high-confidence drought predictions. |
| [59] | To evaluates the effectiveness of different drought indices to improve monitoring in the Upper Blue Nile Basin, Ethiopia. | - R2 from 0.83 to 0.93 and NSE from 0.84 to 0.91. Calibrated variable: streamflow | - Historical monitoring of drought events in the Upper Blue Nile Basin; - The combination of multiple drought indices improves drought detection accuracy. | - Data period available (1970–2010), which may affect the accuracy of drought estimates. |
| [67] | To propose a new non-stationarity hydrological drought index, which incorporates the climate-driven and human-induced non-stationarities in streamflow | - It was considered that the sub-basin was calibrated when it simultaneously presented, ENS > 0.5; R2 > 0.7, PBIAS < ±25% Calibrated variable: streamflow | - Development of the Non-stationary Standardized Streamflow Index (NSSI), which incorporates changes in the hydrological regime driven by both climate variability and human activities. | - Difficulty in distinguishing between climatic and anthropogenic effects. It remains impossible to fully separate the impacts of climate change and human activities on streamflow, as doing so would require complex statistical analyses involving a wide range of variables. |
| [56] | To investigate the combined influence of climate, catchment, and morphological variables on hydrological drought in the Savannah River Basin | - NSE from 0.45 to 0.87; R2 from 0.54 to 0.88; p-factor from 0.84 to 0.89, and R-factor from 0.66 to 0.82. Calibrated variable: streamflow | - Integration of hydrological and statistical models to predict hydrological droughts at multiple timescales; - Use of decision tree (CART) to identify variable thresholds influencing short-, medium-, and long-term droughts. | - Drought drivers vary by scale (global vs. regional); findings are most relevant at the basin level; - Applying the method in ungauged basins may rely on indirect estimates. |
| [68] | To reveal the future impacts of extreme events and their potential consequences for local livelihoods and human well-being in the Srepok River basin | KGE from 0.80 to 0.84; NSE from 0.71 to 0.76 | - Identification of changes in intensity, frequency, and timing of future hydro-climatic extremes in the Transboundary Srepok River Basin; - Scientific support for adaptation strategies and disaster-risk management. | - Anthropogenic influences (e.g., reservoir operations) not fully represented; - Land use considered stationary in future projections. |
| [57] | To assess the impacts of climate change on drought occurrence across five major river basins in Virginia using hydrological modeling (SWAT), multiple drought indices, and future climate projections. | - NSE from 0. 41 to 0.66; R2 from 0.48 to 0.67 Calibrated variable: streamflow | - Combined high-resolution climate projections, hydrological modeling (SWAT), and multiple drought indices to evaluate future droughts from different perspectives (meteorological and agricultural). | - The divergence in results (SSI projections increased drought vs. MSDI/MPDSI projecting decreased drought) limits the reliability of any single index. This highlights the need for cautious interpretations and the use of multi-approach to capture the drought. |
| [58] | To develop and validate a high-resolution, watershed-scale framework for assessing, monitoring, and forecasting drought severity using stratified soil moisture | - NRMSE from 0.03 to 0.21; R2 from 0.18 to 0.68; WI from 0.16 to 0.7 Calibrated variable: streamflow | - Innovate methodology for near-real-time drought monitoring and forecasting based on soil moisture simulated by SWAT model. | - The study did not incorporate the effect of local edaphic and biophysical factors which are known to influence the soil profile’s response to drought. |
| [60] | Analysis of meteorological, agricultural, and hydrological droughts using the Drought Hazard Index (DHI) derived from the SWAT model for historical and near-future periods. | - NS from 0.13 to 0.67; bR2 from 0.38 to 0.67; p-factor from 0.52 to 0.75, and R-factor from 0.66 to 1.08. Calibrated variable: streamflow | - Comparison of multiple drought indices enables more effective monitoring of the spatiotemporal characteristic of drought. | - The accuracy of drought indices is highly dependent on the calibration and performance of the SWAT model, which may introduce uncertainties in future projection results. |
| [48] | To assess the impacts of climate change on streamflow and their effects on ecosystems. | - Monthly: NS = 0.81; R2 = 0.83 Daily: NS = 0.62; R2 = 0.63 Calibrated variable: streamflow | - Provides conservation strategies focused on habitat restoration and enhancing ecosystem resilience | - The downscaling approach was identified as a key factor influencing the projected climatic variables. |
| [62] | To assess future changes in meteorological, hydrology and agricultural droughts under the impact of changing climate in the Srepok River Basin. | - Monthly: ENS from 0.62 to 0.84; R2 from 0.88 to 0.94; PBIAS from −2 to −14; Daily: ENS from 0.52 to 0.76; R2 from 0.77 to 0.90; PBIAS from −2 to −14; Calibrated variable: streamflow | - In the Srepok River Basin, SSWI (Standardized Soil Moisture Index) and SRI (Standardized Runoff Index) are more sensitive to climate change than SPI. - The correlations of the meteorological drought with the hydrological and agricultural droughts increase as the accumulation periods are increased | - The reliability of the results depends on the data used/regional application. - The climate change assessment is confined to a relatively short-term period (2016–2040). This period may be insufficient to capture long-term climate variability. |
| [69] | The combination of trend assessment for both past decades and future projections, evaluation of climate change impacts on hydrological extremes, and the implications for both meteorological and hydrological drought. | - NS from 0.40 to 0.81; R2 from 0.40 to 0.83; PBIAS from −17.90 to 21.50 p-factor from 0.25 to 0.87; r-factor from 0.52 to 1.15. Calibrated variable: streamflow | - Detailed analysis of historical trends and projections for temperature, precipitation, and streamflow. | - Analyses restricted to the intermediate emissions scenario, limiting the assessment of more severe or more optimistic scenarios |
| [61] | To characterize and reconstruct the different types of droughts (meteorological, agricultural, and hydrological) in the Upper Kafue River Basin, Zambia | - Monthly: ENS from 0.71 to 0.75; R2 from 0.71 to 0.75; Daily: ENS = 0. 70; R2 = 0.70 Calibrated variable: runoff | - Characterization of drought using a comprehensive approach with standardized indices and hydrological modeling. | - The local characteristics of the basin may have influenced the interactions between temperature, precipitation, and runoff, leading to different results compared to other regions. |
| [63] | To combine drought indices and hydrological modeling to forecast future drought impacts | -NSE from 0.63 to 0.87; R2 from 0.69 to 0.77; PBIAS from −9 to 12 Calibrated variable: streamflow ** | - The combination of different approaches, such as multiples indices and hydrological modeling, provides a valuable foundation for improving drought risk management in Mediterranean context | - The analysis relies on projection from only one GCM, which limits the assessment of overall climate change uncertainty. |
| [54] | To analyze spatiotemporal changes in hydrometeorological variables and investigate the underlying mechanisms of contrasting soil dryness/wetness patterns across the West River Basin, a mega-watershed in southern China. | -NSE from 0.86 to 0.95; R2 from 0.89 to 0.95; PBIAS from −2.5 to 10.9 Calibrated variable: streamflow | - Identification of a climate change pattern and its impacts on hydrological variables (surface runoff and baseflow); - Spatial assessment of flood and drought risks across the studied watershed. | - Regional focus (watershed with a monsoon climate); - The analysis does not quantify the direct and indirect socioeconomic impacts of the hydrological changes. |
| [53] | To assess the frequency, affected areas, and severity of drought events, using hydrological simulations and drought indices. To develop a nine-month seasonal drought forecast to improve drought prediction and management in the region. | - NS from 65 to 0.86 Calibrated variable: streamflow | - Use of SWAT and CFSv2 (Coupled Forecast System Model version 2) for drought forecasting; | - Seasonal forecasting may not fully account for the complexities of future drought dynamics, especially in the context of changing climate conditions. |
| [35] | To develop a drought forecasting method using VIC (Variable Infiltration Capacity) and SWAT models, along with CFSv2 (Climate Forecasting System version 2) meteorological forecasts, to provide up to nine-month drought predictions for the CONUS (Contiguous United States) | - The SWAT model was not calibrated; only the VIC model was calibrated in previous studies. | - The study successfully integrated the SWAT and VIC models with CFSv2 to simulate and forecast drought conditions for the CONUS, improving real-time drought predictions; - The proposed method provides weekly forecasts, enhancing the frequency and timeliness of drought information. | - The forecasting accuracy decreases remarkably after an eight-week leas time. - Drought forecasting using only one variable showed poor prediction performances even for the first eight weeks. |
| [70] | To assess the potential impacts of climate change on hydrometeorological variables and drought characteristics in the Ethiopian Bilate watershed | - NSE = 0.75; R2 = 0.86; RSR = 0.50 Calibrated variable: streamflow | - The study evaluated future climate impacts on drought characteristics using three drought indices (SPI, SDI, and RDI); SDI (Streamflow Drought Index), RDI (Reconnaissance Drought Index). | - Lack of investigation into the combined impacts of land use and land cover changes and climate changes and their effects on water resources |
| [71] | Projecting drought characteristics for the Cheongmicheon watershed using RCP4.5 (CMIP5) and SSP2–4.5 (CMIP6) climate scenarios with ACCESS1–3 and ACCESS CM2 models. | - NSE = 0.786; R2 = 0.95 Calibrated variable: streamflow | - Comparison of distinct climate scenarios (RCP 4.5 and SSP 2–4.5), allowing the assessment of variations in drought estimates based on different climate projection scenarios. | - Use of only two climate models (one from CMIP5 and one from CMIP6) and uses only one scenario (RCP4.5 and SSP2–4.5), which may limit the reliability of the results |
| [55] | To analyze drought propagation including drought and groundwater drought. | - Monthly: ENS = 0.89; R2 = 0.89; Daily: ENS = 0.66; R2 = 0.67 Calibrated variable: streamflow | - Identification of drought propagation patterns (meteorological drought does not always result in agricultural or hydrological drought) | - Human activities were excluded from the analysis; Uncertainties in thresholds and selection of drought events. |
| [50] | To analyze the spatiotemporal characteristics of drought in the Wei River Basin (WRB) in northwest of China | - NSEln from 0.71 to 0.88; R2 from 0.73 to 0.89; PEV from 80% to 92% Calibrated variable: streamflow | - Development of the PSDI_SWAT drought index, which demonstrates a good ability to capture drought events and represent the spatiotemporal variations in soil moisture | - Discrepancies in the description of drought propagation among different indices when using PDSI_SWAT. |
| Abbreviation | Drought Index Name | Country/Region | Drought Type | References |
|---|---|---|---|---|
| SPI | Standardized Precipitation Index | China, Vietnam, Malaysia, Poland, Thailand, Ethiopia, Iran, USA, Italy, Canada, Brazil, India, South Africa, Southern Africa Kenya, Morocco, South Korea, Argentina, Sudan, East Africa, Peru | Meteorological | [10,48,55,58,59,60,61,62,63,64,68,70,71,77,79,80,81,83,84,85,86,87,88,89,90,91,92,93,94,95,96,97,98,99,100,101,102,103,104,105,106,107,108,109,110,111,112,113,114,115,116,117,118] |
| SPEI | Standardized Precipitation–Evapotranspiration Index | Canada, China, Kenya, Poland, South Africa, Southern Africa, Thailand, Ethiopia, Portugal, Tunisia, USA, India | Meteorological | [51,52,59,61,69,71,77,79,85,86,87,88,107,115,119,120,121,122,123,124,125,126,127] |
| SSI | Standardized Streamflow Index | Afghanistan, Brazil, Colombia, China, Thailand, Malaysia, Poland, Vietnam, Pakistan | Hydrological | [51,55,64,67,68,82,84,87,101,105,115,124,128,129,130,131] |
| SSI | Soil moisture Stress Index | India | Agricultural | [103] |
| MSDI | Multivariate Standardized Drought Index | China, USA, India | Multivariate | [35,53,57,80,103,132] |
| PDSI | Palmer Drought Severity Index | China, Iran, USA | Meteorological | [46,54,58,60,85,133,134] |
| SMI | Standardized Soil Moisture Index | Poland | Agricultural | [115] |
| SSI | Standardized Soil Moisture Index | China, USA, Southern Africa | Agricultural | [35,52,53,57,61,80,95,132] |
| SSMI | Standardized Soil Moisture Index | China, Thailand, Poland | Agricultural | [77,81,85,104,120,122,135,136] |
| SRI | Standardized Runoff-discharge index | Ethiopia | Hydrological | [59] |
| SRI | Standardized Runoff Index | China, India, Italy, Iran, South Korea, Thailand, USA, Poland, East Africa, Southern Africa, Vietnam, Cambodia | Hydrological | [10,11,55,56,60,61,62,78,85,95,96,98,103,104,106,110,120,123,135,137,138,139,140,141,142,143] |
| SWSI | Standardized Water Streamflow Index | China | Hydrological | [85] |
| SWYI | Standard Water Yield Index | China | Soil | [81] |
| RDI | Reconnaissance Drought Index | China, Ethiopia, Iran | Meteorological | [70,79,91,144,145,146] |
| SDI | Streamflow Drought Index | China, India, Iran, Kenya, Morocco, Vietnam, Thailand, Greece, Ethiopia, South Korea, USA | Hydrological | [47,63,69,70,88,91,99,100,108,144,145,146,147,148,149,150] |
| SDI | Standardized Stream flow Drought Index | China | Hydrological | [52] |
| SDI | Standardized Streamflow Index | South Korea | Hydrological | [71] |
| SPAEI | Standardized Precipitation Actual Evapotranspiration Index | India, China | Meteorological | [125,135] |
| SWI | Soil Water Index | South Africa | Hydrological | [86] |
| PERCI | Percolation Index | South Africa | Hydrological | [86] |
| RFI | Runoff Index | South Africa | Hydrological | [86] |
| WYLDI | Water Yield Index | South Africa | Hydrological | [86] |
| SMDI | Soil Moisture Deficit Index | Canada, Colombia, Ethiopia | Agricultural | [59,82,92] |
| NJHDI | Non-linear Joint Hydrological Drought Index | China | Hydrological | [122] |
| EDDI | Evaporative Demand Drought Index | China | Meteorological | [98] |
| scPDSI | Self-Calibrated Palmer Drought Severity Index | Canada | Meteorological | [92] |
| ETDI | Evapotranspiration Deficit Index | Canada, Ethiopia, Tanzania | Agricultural | [59,92,151] |
| aSPI | Agricultural Standardized Precipitation Index | Ethiopia | Agricultural | [145,146] |
| SDI | Stream Drought Index | Vietnam, Pakistan | Hydrological | [93,152] |
| SSDI | Standardizes Supply-demand water Index | China | Vegetation | [111] |
| MPDSI | Modified Palmer Drought Severity Index | China, USA | Meteorological | [53,57,132] |
| SSWI | Standardized Soil Moisture Index | Vietnam | Agricultural | [62] |
| J | The Drought Index | Vietnam | Meteorological | [90] |
| Ped | The Ped Index | Vietnam | Meteorological | [90] |
| KDrought | Hydrological Drought Index | Vietnam | Hydrological | [90] |
| SBI | Standardized Baseflow Index | USA | Hydrological | [35] |
| ADI | Aggregate Drought Index | Ethiopia | Multivariate | [59] |
| SSWI | Standardized Soil Water Index | USA, Iran | Agricultural | [10,60] |
| PHDI | Palmer Hydrological Drought Index | USA | Hydrological | [58] |
| MAHDI | Meteorology Agriculture Drought Index | China | Meteorological, Agricultural | [52] |
| SWI | Standardized Soil Moisture Indes | China | Agricultural | [87] |
| SRI | Streamflow Response Index | China | Hydrological | [153] |
| NSSI | Non-stationary Standardized Streamflow Index | China | Hydrological | [67] |
| ESI | Evaporative Stress Index | China | Meteorological | [154] |
| IDI | Integrated Drought Indicator | China | Agricultural, Hydrological, Meteorological | [155] |
| SDI | Stream Drying Index | South Korea | Hydrological | [156] |
| SWSI | Surface Water Supply Index | Iran | Hydrological | [157] |
| Theme | Gaps | Future Perspectives |
|---|---|---|
| Observational data | – Scarcy and limited quality of precipitations, temperature, and streamflow data, especially in vulnerable or/and developing regions; – Reliance on reanalysis products without local validation; – Uncertainties associated with GCM projections. | – Establish standardized validation protocols for reanalysis products and GCMs. – Improve the estimation of reanalysis datasets and develop statistical techniques to support their validation. |
| Soil data | – Low resolution and limited discussion regarding the quality of soil maps. – Direct influence on the simulation of agricultural drought processes. | – Improve the accuracy of soil datasets by incorporating remote sensing techniques and advanced digital soil mapping approaches. |
| Harmonization of drought indices | – Large number of different indices (47 identified). – Identical acronyms used for different indices (e.g., SSI). – Difficulties in conducting regional or global comparative assessments. | – Standardize nomenclature, calculation procedures, and interpretation guidelines. – Develop international recommendations for selecting and applying drought indices. |
| Statistical approaches | – Limited use of non-stationary statistical models. – Insufficient evaluation of suitable probability distributions for regional applications. – Minimal incorporation of machine learning approaches. | – Expand the use of non-stationary methods. – Integrate ML and multivariate approaches into drought estimation and prediction. |
| SWAT model calibration | – Calibration focused almost exclusively on streamflow – Lack of standardization in performance metrics; NSE often used as the sole criterion. | – Adopt multi-criteria calibration and evaluation frameworks. – Develop a standardized protocol for model performance metrics in drought-related studies. |
| Drought propagation analysis | – Few studies quantify how drought propagates across meteorological, agricultural, and hydrological stages. | – Develop integrated frameworks to analyze drought propagation cascades and their associated impacts. |
| Multivariate approaches | – Dominance of univariate drought indices that capture only part of drought complexity. | – Incorporate multiple variables (soil moisture, ET, temperature, land cover, groundwater) into drought indices and hydrological modeling. |
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Martins, L.L.; Martins, W.A.; Ferreira, M.E.C.; Moraes, J.F.L.d.; Bolfe, É.L.; Blain, G.C. SWAT Model and Drought Indices: A Systematic Review of Progress, Challenges and Opportunities. Water 2026, 18, 41. https://doi.org/10.3390/w18010041
Martins LL, Martins WA, Ferreira MEC, Moraes JFLd, Bolfe ÉL, Blain GC. SWAT Model and Drought Indices: A Systematic Review of Progress, Challenges and Opportunities. Water. 2026; 18(1):41. https://doi.org/10.3390/w18010041
Chicago/Turabian StyleMartins, Letícia Lopes, Wander Araújo Martins, Maria Eduarda Cruz Ferreira, Jener Fernando Leite de Moraes, Édson Luis Bolfe, and Gabriel Constantino Blain. 2026. "SWAT Model and Drought Indices: A Systematic Review of Progress, Challenges and Opportunities" Water 18, no. 1: 41. https://doi.org/10.3390/w18010041
APA StyleMartins, L. L., Martins, W. A., Ferreira, M. E. C., Moraes, J. F. L. d., Bolfe, É. L., & Blain, G. C. (2026). SWAT Model and Drought Indices: A Systematic Review of Progress, Challenges and Opportunities. Water, 18(1), 41. https://doi.org/10.3390/w18010041

