Freshwater availability is a very determining issue, especially in semiarid and arid regions, for sustainable development and secured food production. In this premise, the detection and assessment of water stress are of utmost importance. In this study, the satellite-based Potential Available Water Storage (PAWS) index is used to test its feasibility for a basin-scale analysis of water stress in the Western Mediterranean Basin (WMB) in Türkiye. The coarse-resolution GRACE (Gravity Recovery And Climate Experiment) estimates were downscaled based on the Random Forest (RF) model and then were integrated with fine-resolution precipitation data to derive fine-resolution PAWS values. The accuracy of the index was validated against the net water flux (NWF) and water storage deficit (WSD) values over the basin. The results revealed a good performance for the PAWS index for a local scale evaluation of water stress. The PAWS variations turned out to be highly correlated with the NWF (r = 0.72) and WSD (r = 0.66). The PAWS indicates that the WMB has suffered from a critical hydrological situation from 2003 to 2020 during which the basin has been under stress with the most critical situation in 2018 when the per capita water has fallen below 500 m3 suggesting an absolute water stress status.

  • The PAWS index is capable of revealing water stress status at local scales.

  • The Western Mediterranean Basin (WMB) has a critical situation regarding its water resources.

  • There is a descending trend in water storage variations of the basin.

  • The per capita water availability of the WMB is less than 500 m3 in 2018.

Climate change is one of the main challenges of human beings in recent history which invites a real menace to different aspects of human life as well as nature. It has had perceptible ramifications for the agricultural sector in many regions of the world which jeopardizes the food safety of the residents (Gregory et al. 2005). Climate change is fundamentally manifested as changes in the established norms of climatic parameters such as precipitation (P), temperature (T), evapotranspiration (ET), etc. in a region (McCarty 2001; Dore 2005). The decreasing P and rising T and ET accompanied by increased population put tremendous pressure on water resources (Richey et al. 2015). The deterioration of the hydrological balance between inputs and outputs in a region due to natural and anthropogenic drivers engenders a gap between water supply and demand which is defined as water scarcity (Hasan et al. 2019). Water stress is regarded as a potential driver of regional insecurity that can contribute to regional unrest (Richey et al. 2015).

The spatiotemporal dynamics between human and natural water systems can be understood easily through water stress analysis. To date, different approaches have been followed by researchers to characterize and analyze water stress which yielded various water stress indicators. Water Resources Availability (Yang et al. 2003); Watershed Sustainability Index (Chaves & Alipaz 2006); Green–Blue Water Scarcity (Rockström et al. 2009); Water Scarcity Function of Water Footprint (Hoekstra et al. 2011); Water Use Availability Ration (Alcamo & Henrichs .2002); Local Relative Water Use and Reuse (Vorosmarty et al. 2005); Water Poverty Index (Lawrence et al. 2002); and Water Supply Stress Index (McNulty et al. 2010). Although these indices have made good strides in assessing water stress status, their optimal use is shackled by some restrictions mainly due to their inability to integrate all forms of ‘available water’, particularly, soil moisture and groundwater due to data dearth (Hasan et al. 2019).

To overcome the aforementioned handicap, Hasan et al. (2019) proposed a new water stress index based on the Gravity Recovery And Climate Experiment (GRACE)'s Terrestrial Water Storage (TWS) estimates and precipitation data from the Tropical Rainfall Measuring Mission (TRMM). The GRACE-observed TWS is a composite hydrological parameter consisting of different water cycle components such as surface water, soil moisture, snow water, canopy water, and groundwater (Rodell et al. 2018). Therefore, it encompasses all forms of water storage and its application for water stress assessment gives a clear insight into the total water availability in a region (Hasan et al. 2019). In their recent study, Hasan et al. (2019) tested the feasibility of the Potential Available Water Storage (PAWS) indicator to determine water stress in African countries and reported good performance. They applied this approach over a large scale (country level) because of two reasons; first, the coarse resolution (ranging from 200,000 km2 at low latitudes to 90,000 km2 near the poles) (Rodell et al. 2018) of the GRACE data hinders its applications over smaller scales. Moreover, they validated their results against the water availability statistics retrieved from the AQUASTAT dataset (a global water information system of the Food and Agriculture Organization (FAO)) which is available only on country scales. The novelty of this study lies in its application of the PAWS index for a smaller scale (basin level) which is more required for hydrological analysis and applications. In this premise, the GRACE-derived TWS was downscaled to 10 km of spatial resolution based on Random Forest (RF) machine learning. The downscaled TWS later was integrated with satellite precipitation estimates from the CHIRPS (Climate Hazards Group InfraRed Precipitation with Station data) mission to derive the PAWS index.

The Western Mediterranean Basin (WMB) is located in the south-west of Türkiye (Figure 1). The surface water flow of the basin discharges to the Aegean and the Mediterranean Sea. Encompassing four provinces of the country including Antalya, Burdur, Denizli, and Muğla. The WMB's surface area is about 21,224 km2, which accounts for about 2.72% of Türkiye's land (Çelekli & Lekesiz 2020). The dominant climate of the basin is of the Mediterranean type with dry and hot summer days and mild and rainy winter days. The mean annual precipitation is approximately 876 mm (Çelekli & Lekesiz 2020). The population of the basin, which was approximately 1.2 million in 2000, increased to 2.0 million in 2022. The average population growth rate of the basin is 2.23%.
Figure 1

The geographical location of the Western Mediterranean Basin (WMB) in the southwest of Türkiye.

Figure 1

The geographical location of the Western Mediterranean Basin (WMB) in the southwest of Türkiye.

Close modal
Several steps were followed in conducting the analysis and evaluation of the results. In the first step, data acquisition and preprocesing were conducted using TWS from the GRACE satellites, hydro-meteorological data from the Famine Early Warning Systems Network Land Data Assimilation System (FLDAS) model, and population statistics. In the next step, fine-resolution TWS data were estimated using the RF model. Then, the PAWS index was calculated. Finally, the results were validated against P, ET, and water storage deficit (WSD) values. Figure 2 details the link between each step and the procedure which is detailed as follows.
Figure 2

The schematic flow of the study analysis.

Figure 2

The schematic flow of the study analysis.

Close modal

GRACE TWS

The GRACE is a twin satellite remote sensing project, working in tandem to gather the gravitational signals of the Earth (Rodell et al. 2007). The GRACE has been providing the public end-users with data on the monthly anomalies of TWS processed by different centers (Khorrami et al. 2022). Mass Concentration (Mascon) blocks are the latest data format of the mission, which are post-processed and ready to use. Moreover, the Mascon solutions are global and not tailored toward a particular application, and hence, can be utilized for all scientific topics of interest (Save et al. 2016). Therefore, the latest release of the GRACE/GRACE-FO JPL Mascon solutions with a spatial resolution of 50 km was utilized in this study. The TWS data can be downloaded from https://earth.gsfc.nasa.gov/geo/data/grace-mascons.

FLDAS model

The FLDAS model is a large-scale hydrology model within which two Land Surface Models (LSMs) are used to simulate different hydrometeorological variables through integrated in situ, modeled, and satellite-derived observations at different resolutions (Loeser et al. 2020). The FLDAS makes simulations under the Variable Infiltration Capacity (VIC), and the Noah models (McNally et al. 2017) with a spatial resolution of 25 and 10 km, respectively. In this study, the different hydro-meteorological parameters such as P, ET, T, soil moisture storage, snow water storage, and runoff were extracted from the Noah model of the FLDAS mission via https://disc.gsfc.nasa.gov/datasets?keywords=FLDAS.

CHIRPS precipitation

CHIRPS dataset is a relatively new quasi-global, high-resolution, daily/monthly precipitation dataset. The multisource CHIRPS project combines three different datasets (global climatology, satellite estimates, and in situ observations) to generate gridded precipitation data. Being known as one of the most potent gridded representatives of the rainfall field (Ray et al. 2022), CHIRPS is often used as an alternative source of precipitation measurements, especially where sufficient measurements are not accessible (Paca et al. 2020). The CHIRPS monthly precipitation data with a resolution of 0.05 degrees can be downloaded from http://chg.geog.ucsb.edu/data/chirps/.

MODIS ET

MOD16 is an algorithm used by MODIS (Moderate Resolution Imaging Spectroradiometer) mission to generate high-resolution ET data by integrating MODIS observations and MERRA meteorological data (Souza et al. 2019). In this study, ET data from the MOD16A2 products with a spatial resolution of 500 m and the temporal resolution of 8 days were used. MOD16A2 ET estimates are freely available at https://modis.gsfc.nasa.gov/data/dataprod/mod16.php.

Random forest

The coarse spatial resolution of the GRACE data remains a handicap for local studies with a spatial extent of less than the GRACE resolution (Wang et al. 2019; Khorrami & Gunduz 2021a). Recent developments in downscaling techniques make GRACE data suitable to assess the local scale variations in water storage (see e.g., Chen et al. 2019; Ali et al. 2021; Arshad et al. 2022; Yin et al. 2022; Khorrami et al. 2023b). In this study, the RF machine learning technique, which is proven to be a very successful downscaling technique for the GRACE data (Chen et al. 2019), was applied to enhance the spatial footprint of the GRACE TWS from to over the entire country. The RF benefits from the average values obtained from decision trees generated based on a set of homogenous subsets of random predictors (Rahaman et al. 2019). The spatial downscaling is implemented as follows: (i) All the input variables were aggregated to the spatial resolution of the GRACE-JPL Mascon (50 km), and then the statistical associations between the TWS, geospatial variable (elevation), and FLDAS-derived variables (soil moisture, snow water, rainfall, surface runoff, ET) at 10 km resolution were evaluated by developing the RF model to predict TWS. Later, (ii) the residual values were calculated by deducing the model-derived TWS from the GRACE-derived TWS. Afterward, (iii) the developed model was applied to the hydrological and geospatial variables at a spatial resolution of 10 km to attain the estimated 10 km TWS. Finally, (iv) the residual correction was performed at 10 km by adding residuals to the estimated TWS at 10 km to obtain the downscaled TWS.

Water storage deficit

WSD expresses the water surplus or deficit in terms of deviations of monthly TWS estimates from monthly climatology values (Wang et al. 2020). The WSD was calculated by subtracting the climatology (long-running mean monthly) TWS from the monthly TWS in each corresponding month (Equation (1)) (Khorrami & Gunduz 2021b) where negative WSD values indicate water storage depletion and positive WSD suggests storage surplus.
(1)
where defines the value of TWSA for the month j of the year i. The climatology value of each month is given by .

Potential available water storage index

The PAWS is a satellite-derived hydrological index proposed by Hasan et al. (2019) to investigate water stress status at large scales. The PAWS is calculated as follows:

First, TWS change () is estimated as the temporal derivative of the GRACE-observed TWS for 2 consecutive months (Forootan et al. 2017) (Equation (2)).
(2)
Second, Internal Water Storage (IWS) is estimated based on the integrated and P. The IWS represents the water availability in all forms (i.e. surface and subsurface storage). In this study, P values were used from the CHIRPS dataset. Since there is a 3-month of temporal lag between TWS and P in the WMB, the monthly IWS was estimated in mm as the difference between the P estimate of the month (i) and the ΔTWS of the consecutive month (i + 3) both in mm of water (Equation (3)).
(3)
And finally, the PAWS was estimated (in m3 per capita) by dividing the basin-average monthly IWS by its population density (PD) (Equation (4)).
(4)

The water stress level of the basin based on the PAWS threshold was determined according to the classification given in Table 1.

Table 1

The water stress threshold (Falkenmark & Widstrand 1992)

Threshold/capitaStress level
> 1,700 Occasional or local water stress (no stress) 
1,700–1,000 Regular water stress (vulnerable) 
1,000–500 Chronic water shortage (stressed) 
< 500 Absolute water scarcity (scarcity) 
Threshold/capitaStress level
> 1,700 Occasional or local water stress (no stress) 
1,700–1,000 Regular water stress (vulnerable) 
1,000–500 Chronic water shortage (stressed) 
< 500 Absolute water scarcity (scarcity) 

Performance of downscaling model

The results of the downscaling model were verified through comparison of the basin-wise variations of the original and predicted (downscaled) TWS values. According to the results (Figure 3), with a correlation of coefficient (CC) of 0.87, and RMSE of 2.3 mm, the RF model turned out to be successful in modeling the finer resolution TWS over the study area.
Figure 3

The multiyear (2003–2020) temporal associations between the GRACE-TWS and downscaled RF-TWS.

Figure 3

The multiyear (2003–2020) temporal associations between the GRACE-TWS and downscaled RF-TWS.

Close modal

Fluctuations of TWS

To depict the temporal fluctuations of TWS over the WMB, the basin-wise values were extracted from the downscaled TWS. According to the variations of the mean TWS (Figure 4) negative storage variations are seen from 2007 to 2010, 2013 to 2014, 2016, and 2018 to 2020. The maximum storage loss happened on August 2008 with a of equivalent water height which is equal to . On the other hand, positive variations in the water storage of the basin are observed from 2003 to 2006, 2011 to 2013, 2015, and 2019. The maximum storage surplus of 21.95 cm occurred in March 2012 which is equivalent to of water storage. Overall, the long-term variations (Jan 2003–Dec 2020) of TWS indicate that the basin has experienced decreasing water storage variations with an annual storage loss of equal to . The multiyear trend of the TWS (Figure 5) suggest that the water storage of the basin diminishes from the west to the east.
Figure 4

The multiyear (2003–2020) temporal fluctuations of TWS.

Figure 4

The multiyear (2003–2020) temporal fluctuations of TWS.

Close modal
Figure 5

Multiyear (2003–2020) annual trend of TWS.

Figure 5

Multiyear (2003–2020) annual trend of TWS.

Close modal

Associations between TWS and climatic parameters

As the main hydrological input and output forces, the variations of P and ET over the basin and their associations with the TWS were investigated. The P and ET values were, respectively, extracted from the CHIRPS and MODIS datasets. The annual ET and P of the basin were estimated as and , respectively. To draw a rational analogy between the variables, the P and ET anomalies were calculated based on the same baseline (mean of Jan 2004–Dec 2009) of the GRACE mission (Moghim 2020). The results (Figure 6) indicated that the variations of P and ET were associated with lagged TWS over the basin where there was a correlation of between TWS and P and ET.
Figure 6

Multiyear (2003–2020) associations of TWS with P and ET anomalies.

Figure 6

Multiyear (2003–2020) associations of TWS with P and ET anomalies.

Close modal

Variations of IWS and PAWS

The basin-wise variations of the IWS and PAWS are given in Figures 7 and 8, respectively. The variations of IWS over the WMB are associated with those of TWS with a correlation of 0.59. The annual IWS is also associated with the PAWS with a correlation of 0.65. In Figure 8, the PAWS time series suggests that the amount of available water per capita is the minimum in 2018 with of available water suggesting absolute water scarcity this year. The maximum water is available in 2003 with of available water per capita which demonstrates no water stress in the basin.
Figure 7

Temporal variations of Internal Water Storage (IWS) and its associations with TWS.

Figure 7

Temporal variations of Internal Water Storage (IWS) and its associations with TWS.

Close modal
Figure 8

Temporal variations of PAWS and the annual IWS.

Figure 8

Temporal variations of PAWS and the annual IWS.

Close modal

Validation

To validate the accuracy of the results, the variations of PAWS were validated against the WSD and the net water flux (NWF) in the basin. NWF is calculated as precipitation minus ET and describes the effective flux of water between the atmosphere and the earth's surface (Khorrami et al. 2023a) and therefore provides important information regarding the interaction of the atmosphere with the land surface. This parameter is also important from a hydroclimatic perspective because it is a measure of water stress (Gao & Giorgi 2008). Decreasing NWF signals water scarcity thus diminishing available water in a basin. Therefore, higher NWF corresponds to a condition where water is more available for other compartments of the hydrological cycle. In this study, the annual ET was subtracted from the annual P to estimate the NWF over the study area.

The results (Figure 9) demonstrate a high association between the PAWS index variations and those of NWF and WSD from 2003 to 2020 with a correlation of 0.72 and 0.66, respectively. The high interactions between PAWS and NWF demonstrate the great influence of the climatic situation on the availability of water during the study period in the basin. Where increasing NWF implies more water availability and thus more freshwater accessibility for use and vice versa. The WSD variations also indicate that the basin has experienced a harsh hydrological situation with negative WSD in most of the years suggesting the WSD. The highest storage deficit of the basin is seen in 2008 with a water storage.
Figure 9

Associations among the annual net water flux (NWF), Water Storage Deficit (WSD), and Potential Available Water Storage (PAWS).

Figure 9

Associations among the annual net water flux (NWF), Water Storage Deficit (WSD), and Potential Available Water Storage (PAWS).

Close modal

Spatial evolution of water stress

The spatial status of the water stress is given in Figure 10. According to the results, it can be stated that the basin has had an overall water scarcity from 2003 to 2020. Excluding 2003 and 2004 for which partial stressless areas detected over the basin, during the remaining years the basin has been stressed out hydrologically. The situation is more exacerbated in 2016 and 2018 when the WMB suffered from absolute water scarcity, especially in 2018 when the majority of the basin was stressed out.
Figure 10

Water stress of the WMB according to the long-term (2003–2020) mean PAWS.

Figure 10

Water stress of the WMB according to the long-term (2003–2020) mean PAWS.

Close modal

The WMB is one of the basins most susceptible to drought in Türkiye (Özüpekçe 2021). The recent water stress status of the basin was investigated based on the PAWS index. According to the results, The WMB has suffered from diminishing water storage from 2003 to 2020 with a storage loss of 0.09 km3 per annum which is equal to 1.62 km3 of total water storage loss during the last 18 years. Since the GRACE signals are more sensitive to agricultural and hydrological droughts (Okay Ahi & Jin 2019), the results can be interpreted taking the drought analysis results into account. The critical storage loss of the basin in 2007, 2008 2018, and 2020 can be ascribed to the harsh country-wise drought incidents (Türkeş et al. 2009; Kurnaz 2014; Özüpekçe 2021; Khorrami & Gündüz 2022). The hydrologic status of the WMB has been in particular very critical in 2008 during which the basin lost −1.79 km3 of its water storage. This is justified by taking the drought analysis results of the region into consideration. Özüpekçe (2021) reported extremely dry conditions for the basin in 2008 and stated that the wetlands of the basin had been in peril of complete disappearance due to the drought side effects as well as anthropogenic impacts.

The basin-wise PAWS results reveal that except in 2003, the WMB has had a critical status with a per capita available water of less than 1,200 m3. Since the water stress threshold is 1,700 m3, it can be inferred that the basin has been under great pressure from 2004 onward. Although the GRACE estimates reflect the impacts of both natural and anthropogenic forces on the variations of water storage (Mandea et al. 2020), in light of the high associations between the PAWS and NWF over the basin, it can be inferred that the variations of water storage and thus water stress in this basin are fundamentally ascribed to climate change consequences.

The prevalent impacts of climate change and population increase have culminated in the detriment of the hydrological balance in many regions of the world. As a result, water resources were put under exorbitant pressure challenging the availability of freshwater, especially in the regions with semiarid to arid climates. Since water availability plays a crucial role in sustaining the world food supply and socio-economic development, investigation of water availability and analysis of water stress are very important. Remote sensing observations provide a good alternative for the traditionally used field data with their global coverage, affordability, and acceptable accuracy. The PAWS is a new index developed based on the GRACE estimates and satellite precipitation data to investigate water stress. In this study, downscaled GRACE data and fine-resolution precipitation from the CHIRPS mission were integrated to evaluate water stress at a local scale. The results suggested a very good performance of the index for a local scale analysis. The PAWS agrees well with the NWF and WSD in the basin suggesting the reliability of the index for basin-wise assessments of water stress.

This research did not receive any specific grant from funding agencies in the public, commercial, or not-for-profit sectors.

All relevant data are available from an online repository at https://figshare.com/s/c0899ea7796c74810e83.

The authors declare there is no conflict.

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