Central Asia (CA) is one of the most arid regions with serious water shortages. To understand the impacts of climate change on the regional water storage in CA, we introduce the terrestrial water storage (TWS) as a comprehensive water resource indicator and evaluate its spatial -temporal variation by regional coupled simulation. In this study, the performance of the Weather Research Forecasting (WRF) model in TWS simulation is evaluated. To consider the uncertainties and study the sensitivity of TWS to model schemes, two microphysics, two planetary boundary layers, and three cumulus schemes are combined in the numerical experiments at 25 km horizontal resolution. The results show that the modeled TWS by WRF agrees well with the satellite-based TWS in high correlation and consistent trends. The simulated TWS has larger variability than that of the satellite-based TWS, but a weaker decreasing trend due to lack of human activities consideration. Overall, the modeled TWS is mainly influenced by the precipitation and soil moisture, and insensitive to the physical schemes on monthly scale in CA. This can serve as a basic tool for water resource assessment in CA by the stable model performance, especially after the consideration of human activities in the future.

  • WRF can reproduce the spatial–temporal variations and the decreasing trend of TWS well in CA, but the variability is smaller than the Gravity Recovery and Climate Experiment (GRACE)-based TWS without considering human activities.

  • In the period 2004–2008, the precipitation and evaporation are the primary factors impacting the TWS in CA.

  • The TWS simulated by WRF is insensitive to the physical schemes combination, and WRF can capture the water balance stably in CA.

Located in the middle part of the Asian and European continents, Central Asia (referred to as CA) covers an area of over 4,000,000 km2 with complex topography and diverse climates (Qiu et al. 2022). CA is considered to be one of the driest areas in the world with extreme water shortage and a fragile ecosystem because it is far away from the oceans (Oki & Kanae 2006). Thus, the region is also among the most vulnerable and sensitive to climate change, which can have a great influence on the regional water storage and resources in CA. Both climate–ecosystem and human society are highly dependent on the distribution and variation of water resources, and over 70% of the development-related problems were caused by water shortage in CA (Severskiy 2004). Because of the extremely limited water conditions by rare precipitation and strong evapotranspiration, the water balance is particularly sensitive and vulnerable to climate change in CA. Numerous studies and reports have indicated that the water resource shortage is a very serious international water problem in CA influenced by climate change (Yao et al. 2016; Yang et al. 2017; Qiu et al. 2022).

Therefore, the water resources are closely related to regional climate change and have complex interactions in CA. During the past century, CA has experienced a significant warming period at a rate of 0.16 °C/10 yr (Chen et al. 2009), especially in the recent 30 years (Hu et al. 2017). The precipitation has also increased under the accelerated water cycle of the warmer climate, and the trend seems to be continuing in the future (Hu et al. 2017; Jiang et al. 2020; Qiu et al. 2022), which may bring more extreme climatic events in CA, along with more severe water resource conditions and more challenges to ‘The Belt and Road Initiative’.

To consider the water resource evaluation under the climate change background in CA, a comprehensive indicator that can not only directly reflect the water resource condition but is also closely connected with climate change is greatly needed for investigation in CA. The terrestrial water storage (TWS), which contains all the water content stored in the vegetation, entire soil profile, glacier, snow and underground aquifers, has been considered a better indicator for water resource assessment than the traditional single variable, e.g., soil moisture, runoff, and streamflow, in recent studies (Tapley et al. 2004; Scanlon et al. 2015; Zhang et al. 2015). Unfortunately, due to the harsh environment and expensive construction and maintenance costs, there were few ground-based TWS observations in CA. The spatial representation of the observations in CA was extremely limited because of the complex terrain, the huge mountains and the sparsely distributed sites. The detailed spatial pattern of TWS was very difficult to obtain.

In March 2002, the launch of the Gravity Recovery and Climate Experiment (GRACE) mission jointly by the US and German academicians facilitated the monitoring of the large-scale TWS directly (Swenson et al. 2003; Syed et al. 2008; Famiglietti & Rodell 2013), which can provide highly accurate monthly solutions for the Earth's gravity field at an approximately 100 km scale by a twin satellite in identical Earth orbit at a distance of ∼220 km. Then the Earth's gravity field can be solved by the change of this distance after removing the effects of nongravitational accelerations (Swenson et al. 2003). With these advantages, the GRACE-based TWS can provide a more direct, continuous, and comprehensive way to estimate TWS than ground-based observations, especially in an area such as CA. A number of related studies have show remarkable prospects and obvious effects of global/regional hydrological research and water resource assessment based on GRACE-based TWS products (Long et al. 2014, 2015; Scanlon et al. 2016, 2018; Rodell et al. 2018; Ma et al. 2021; Zheng et al. 2022; Rodell & Li 2023).

Another effective method of obtaining distributed TWS is coupled numerical regional simulation. As we know, the climate system is coupled with a variety of physical processes including microphysical, radiation, land surface, atmospheric boundary layer, and hydrological processes. Along with the rapid development of theoretical atmospheric science and computing technologies during recent years, these processes were comprehensively parameterized in global and regional coupled climate models. As an outstanding representation, the Weather Research and Forecasting (WRF) Model has been widely used in regional climate and weather simulation, land–atmosphere interaction investigation, urbanization effects’ evaluation, and hydrological processes and water resource estimation with different combinations of physical parameterizations (Cesana et al. 2017). The physical parameterizations in WRF can be divided into specific classes such as microphysics (MP), radiation, land surface model (LSM), planetary boundary layer (PBL), and cumulus scheme (CU), which can generate thousands of combinations (Cesana et al. 2017). According to previous studies, different physical parameterization combinations could contribute to considerable influences and disparities in simulation results. For example, Wang et al. (2019) made use of different radiation schemes in WRF simulation over China and found that the New Goddard and Community Atmosphere Model (CAM) schemes are suitable for longtime simulation without nesting and nudging options, and different PBL schemes showed different performances for different observation and meteorological parameters, which can have a substantial influence on land–atmosphere energy balance (Xie et al. 2012; Wang et al. 2019; Xu et al. 2019). The LSM, which connects the land surface and lower atmosphere, also plays an important role in weather forecasting (Chen & Dudhia 2001), climate prediction (Barlage et al. 2015), water cycle simulation (Li et al. 2015; Qiu et al. 2017), and regional urbanization (Wang et al. 2012).

Based on the previous studies mentioned above, water resources’ evaluation is also an important application field of the WRF model, especially in areas with scarce water resources, serious water crisis, and limited ground-based observations. Although previous studies indicated that the WRF model had good performance in areas with complex mountain terrain (Feng et al. 2015; Qiu et al. 2017; Salamanca et al. 2018; Chen et al. 2019; Constantinidou et al. 2019), uncertainties still exist in both model simulation in the water cycle and GRACE products in the area of CA. The water balance in CA is sensitive and vulnerable to climate change, and different selections and combinations of schemes in WRF may affect the regional water resource evaluation. The questions mentioned above still need more attention in water resource evaluation in CA. This paper aims to evaluate the TWS evaluation over CA from coupled climate–land surface simulation by the WRF model with different combinations of MP, CU, and PBL schemes for further inter-comparison. To give more detailed descriptions of groundwater processes, we introduced the multi-parameterizations of Noah LSM (Noah-MP) as the land surface scheme in experimental design. Compared to original Noah LSM, the greatest advantage of the Noah-MP is that it can improve simulation effects and achieve model optimization for specific regions by combining different schemes of vegetation, soil moisture, runoff, and other land surface process (Jiang et al. 2009; Niu et al. 2011; Cai et al. 2014; Gao et al. 2017; Chen et al. 2019). Here, in the experimental design, we take the combination of Noah-MP that was presented by Wang et al. (2020) in CA as the land surface scheme. For the model description, an experimental design is shown in Section 2. The results’ analyses are presented in Section 3. Finally, the conclusions are summarized and discussed in Section 4.

Model description

In this study, the WRF v4.0.1 is used to simulate the TWS variation in CA (Figure 1) during the period 2004–2008. The horizontal resolution of the domain is 25 km. The simulations began on 1 December 2003, with a warm start based on the restart and WRF output files of previous experiments (WRF cold start from 1 January 2023), and the first month of the results was used for model spin-up. The initial and boundary conditions of the atmosphere are from the National Centers for Environmental Prediction Final reanalysis data (NCEP-FNL) with the spatial and temporal resolution of 1° and 6 h, respectively. The model output time resolution is 6 h.
Figure 1

The WRF model domain and the topography map of CA (the purple rectangle).

Figure 1

The WRF model domain and the topography map of CA (the purple rectangle).

Close modal

GRACE-based TWS products

The GRACE-based TWS used in this study are retrieved from GRACE monthly mass grid-land datasets, which are based on the RL05 products with 1° spherical harmonics (SH) (Scanlon et al. 2015) and 0.5° mass concentration (Mascon) (Scanlon et al. 2016; Zhang et al. 2020) solutions. The GRACE-based products are obtained from the Center for Space Research (CSR) at the University of Texas at Austin, the German Research Centre for GeoForschungsZentrum (GFZ), and Jet Propulsion Laboratory (JPL) at National Aeronautics and Space Administration (NASA). These TWS products are used for the comparison and validation of WRF modeling results which intended to guide historical and future longer estimation of regional TWS in CA, which represent the TWS deviation for that month relative to the baseline average from 2004 to 2008. The RL05 products are considered more accurate than previously released GRACE products and are much less noisy than RL04 because of describing procedures applied to the data. Therefore, RL05 needs less spatial smoothing than earlier products.

Experimental design

In all design simulations, the Rapid Radiative Transfer Model for GCM (RRTMG) long-wave and short-wave radiation scheme and the LSM scheme Noah-MP (Niu et al. 2011) are used. To evaluate the performance of different physical schemes on WRF/Noah-MP in simulating the Earth–atmosphere interaction in CA, nine sets of experiments are conducted, namely, two PBL schemes, MYJ and YSU PBL schemes; two microphysical schemes, Thompson and WDM6 microphysical schemes; and three CUs, KF, Tiedtke (TDK), and the new Tiedtke (NewTDK). All the different physical scheme combinations are listed in Table 1.

Table 1

The physical schemes employed in the WRF/Noah-MP in this study

Thomp-KF-YSUThomp-NewTDK-MYJThomp-NewTDK-YSUThomp-TDK-MYJThomp-TDK-YSUWDM6-TDK-MYJWDM6-TDK-YSUWDM6-NewTDK-MYJWDM6-NewTDK-YSU
MP Thompson Thompson Thompson Thompson Thompson WDM6 WDM6 WDM6 WDM6 
CU Kain Fritsch New Tiedtke New Tiedtke Tiedtke Tiedtke Tiedtke Tiedtke New Tiedtke New Tiedtke 
PBL YSU MYJ YSU MYJ YSU MYJ YSU MYJ YSU 
Thomp-KF-YSUThomp-NewTDK-MYJThomp-NewTDK-YSUThomp-TDK-MYJThomp-TDK-YSUWDM6-TDK-MYJWDM6-TDK-YSUWDM6-NewTDK-MYJWDM6-NewTDK-YSU
MP Thompson Thompson Thompson Thompson Thompson WDM6 WDM6 WDM6 WDM6 
CU Kain Fritsch New Tiedtke New Tiedtke Tiedtke Tiedtke Tiedtke Tiedtke New Tiedtke New Tiedtke 
PBL YSU MYJ YSU MYJ YSU MYJ YSU MYJ YSU 

The spatial resolution with 0.25° × 0.25° precipitation data from European Centre for Medium-Range Weather Forecasts Reanalysis 5 (ERA5) precipitation (Hersbach et al. 2020) is used to verify the simulated precipitation.

The spatial distribution of TWS

CA is the heartland of the Asian and European continent, far away from the sea, and is a typical inland region. Water resources are an important factor in national development and a sensitive topic in the relations between countries (Deng et al. 2010). The total amount of water resources in CA is large, but it mainly exists in the form of mountain glaciers and deep groundwater, and the real usable water resources are mainly surface waters such as river water and lake water (Yao et al. 2016; Yang et al. 2017). Due to global warming in recent years, many rivers in CA are close to exhaustion, lakes have shrunk sharply, groundwater levels have continued to fall, and water pollution has become more and more serious (Yang et al. 2017). Therefore, the distribution of water resources in CA is both spatially and temporally uneven. The GRACE-based and WRF-simulated spatial distributions of TWS anomalies from 2004 to 2008 over CA are plotted in Figure 2. We can see that the GRACE-based SH solutions show similar spatial characteristics of TWS over CA, and the high-value areas are mainly located in the west of the Caspian Sea, the northern region of Xinjiang province in China, the western Iran plateau, and areas along the Himalayas. The regional heterogeneities in SH solutions are relatively small and much larger in Mascon solutions, especially in the JPL-Mascon products with the highest TWS anomaly over 5.0 cm. The southern part of Xinjiang is the area with negative TWS anomaly due to the shortage of water storage in the desert.
Figure 2

The spatial distribution of the GRACE and simulated TWS.

Figure 2

The spatial distribution of the GRACE and simulated TWS.

Close modal

The coupled model WRF can provide much more detailed regional information about spatial TWS distributions. Consistent with the distribution of GRACE-based products, the simulated high-value areas of TWS are still located around the Himalayas in all numerical experiments and with higher positive anomalies than GRACE-based TWS except JPL-Mascon. This could be attributed to the higher horizontal resolution of the WRF model, which can reproduce more detailed processes of water transfer and the dominant effect of terrain in lifting the water vapor and generating precipitation. The range of TWS values in most areas is between −2.0 and 2.0 cm, which is consistent with the values monitored by GRACE satellites. However, in the south of the study domain and around the Caspian Sea, there are inconsistent areas of spatial TWS where the negative anomalies are modeled by WRF while positive values are in GRACE-based products. Insufficient descriptions of the groundwater scheme in this complex topography area and shot spin-up period for the experiments are possible reasons for this phenomenon. Overall, the WRF simulation can basically reproduce the spatial characteristics of TWS in CA, especially in the eastern part of the study domain.

The trend of GRACE and simulated TWS

CA is one of the largest dry lands in the northern hemisphere with little rainfall and large evaporation. The economy of CA is heavily dependent on agriculture, especially affected by changes in the local hydrological cycle. In recent decades, this semi-arid/arid region has experienced increasing water scarcity and related conflicts. A comprehensive understanding of the changes in the water cycle in this area is essential for agriculture, ecosystems, and the economy. From the regional time series from GRACE-based products, we can see a significant downward trend of TWS in CA during the study period, especially in 2008 (Figure 3(a)). The decline rate of ensemble mean TWS in CA can be as high as −19.54 mm/yr, which indicates huge water loss. The five averaged GRACE-based TWS products are generally consistent on the regional scale. The annual water loss rates are all over −10.00 mm/yr, as shown by these 5 GRACE-based products (Table 2) and all the trends are at 0.01 significance level. The regional time series simulated by WRF can also reflect the annual cycle and the decrease trends of TWS in CA but with relatively smaller decrease rates (Figure 3(b) and Table 3). In this study, the experiments with the WDM6 microphysical scheme performed better than those with the Thompson microphysical scheme on trend detection, and only the experiment group ‘Thompson-TDK-MYJ’ modeled the opposite trend. The differences in trend values may be due to the cause of human activities in CA, which can comprehensively be reflected in GRACE-based products while they are not considered in WRF simulation yet in this study. Similar situations also occur in the Yellow River and Haihe River Basins in northern China, which was demonstrated by previous studies (Pan et al. 2017; Lv et al. 2019). The correlation coefficients of simulated and monitored TWS are all around 0.80 (Table 3), which indicates good agreement between them. Overall, the WRF model can reproduce the temporal evolution of TWS at the regional scale well and capture the decreasing trend in CA, but the decline rates are relatively small due to the lack of consideration of human activities.
Table 2

The annual trends of regional averaged TWS from GRACE-based products

GRACE-based productTrend (mm/yr)
CSR −13.59 
CSR_Mascon −13.63 
GFZ −10.03 
JPL −13.65 
JPL_Mascon −15.29 
GRACE-based productTrend (mm/yr)
CSR −13.59 
CSR_Mascon −13.63 
GFZ −10.03 
JPL −13.65 
JPL_Mascon −15.29 
Table 3

The annual trends of regional TWS modeled by WRF and their correlation coefficients with the GRACE ensemble mean

Trend (mm/yr)Correlation coefficient vs. GRACE
Thomp-KF-YSU −1.94 0.80 
Thomp-NewTDK-MYJ −1.45 0.79 
Thomp-NewTDK-YSU −1.67 0.79 
Thomp-TDK-MYJ 0.59 0.78 
Thomp-TDK-YSU −0.81 0.78 
WDM6-NewTDK-MYJ −1.73 0.79 
WDM6-NewTDK-YSU −2.86 0.80 
WDM6-TDK-MYJ −2.04 0.79 
WDM6-TDK-YSU −3.20 0.80 
Trend (mm/yr)Correlation coefficient vs. GRACE
Thomp-KF-YSU −1.94 0.80 
Thomp-NewTDK-MYJ −1.45 0.79 
Thomp-NewTDK-YSU −1.67 0.79 
Thomp-TDK-MYJ 0.59 0.78 
Thomp-TDK-YSU −0.81 0.78 
WDM6-NewTDK-MYJ −1.73 0.79 
WDM6-NewTDK-YSU −2.86 0.80 
WDM6-TDK-MYJ −2.04 0.79 
WDM6-TDK-YSU −3.20 0.80 
Figure 3

The regional averaged TWS series over CA from 2004 to 2008 of (a) GRACE-based, (b) WRF-simulated, and (c) the box plots.

Figure 3

The regional averaged TWS series over CA from 2004 to 2008 of (a) GRACE-based, (b) WRF-simulated, and (c) the box plots.

Close modal

A box plot is a statistical chart that is often used to display data dispersion information. The dominant advantage of the box plot is that it is not affected by outlier values and can accurately and steadily depict the discrete distribution of the data. Figure 3(c) is the box plot of the TWS, the up and down box represents 75% value and 25% value, while the top line and bottom line are the maximum and minimum values. As can be seen from the figure, the reproduced TWS have larger ranges than the GRACE, either from the maximum (minimum) value or percentage values. The GRACE shows that the average value is the same as the 50th percentage value, which is a positive value. There was more water storage in CA during the period 2004–2008 compared to the baseline years’ average (2003–2009). However, the simulated average value is larger than the 50th percentage value; therefore, the simulation presents less water storage in the CA. Among the three options, the PBL has an impact on the up and down percentage values, the CUs have little effect on the 50th percentage, and the MP schemes have the least impact on the box plot.

The spatial distribution of rainfall, soil evaporation, and soil moisture

Since the 1950s, CA has shown rapid warming and drying trends in summer, consistent with the observed increase in evaporation and decrease in soil moisture (Jiang et al. 2020). As mentioned above, there are large spatial differences in precipitation in CA, as shown by the average in the 2004–2008 average spatial distribution of the ERA5 from 2004 to 2008 in Figure 4. The monthly average difference between the nine simulations and observations of ERA5 is used to describe the simulated features. First, the combination of WDM6 microphysical schemes is reproduced similarly to the Thompson microphysical combinations, except for the experiment using the Thompson scheme with the KF CU scheme, and the precipitation in the main countries in CA, which are located in the center of the study area, is underestimated. Then, the MYJ and YSU PBL schemes' results also present a small impact, while the MYJ scheme shows more precipitation than the ERA5 in the mountain areas. As can be seen from Figure 4, the precipitation in CA is more in the east than in the west, and the large amount of precipitation area is located in the Pamir Plateau, Tianshan Mountains, and around Astana. Because CA is deep inland, it is difficult for seawater vapor to reach the area, so the precipitation amount is small. However, because it is covered in the westerly wind zone, the west wind from the Atlantic Ocean transports water vapor to western CA, which is a relatively flat plain, and the westward European terrain is also plain, so the west wind can take some water vapor to the eastern part of CA, which is blocked by the Pamir Plateau and Tianshan area, then forming a certain amount of terrain rain. Therefore, the precipitation in this mountainous area has a great relationship with the terrain and seems less impacted by the change of physical schemes in WRF.
Figure 4

The spatial distribution of the precipitation over CA.

Figure 4

The spatial distribution of the precipitation over CA.

Close modal
Soil evaporation is the process of water diffusion into the atmosphere in the form of water vapor, which is one of the most important processes of material and energy exchange between land and atmosphere (Ma et al. 2017; Ye et al. 2017). And also, soil evaporation is an integral part of surface heat balance and water balance and is one of the most directly accepted influences of land use and climate change in the water cycle. Judged from the spatial distribution of the evaporation from 2004 to 2008 in the CA (Figure 5), most of the area has a value of less than 0.6 mm/day, which affirms that the vapor is in deficit in this area. The vegetation in the CA is dominated by grasslands and deserts, including the Karakum Desert, which is in a typical temperate desert and grassland continental climate. Soil evaporation is not only interdependent on precipitation, it is also related to rivers on the ground. In extremely arid areas, precipitation is minimal. Its actual evaporation is equal to precipitation. Although soil evaporation is generally dominated by water conditions, some previous studies demonstrated that it can also be affected by the variation of vegetation and canopy, except for regional precipitation in CA and some other plateau areas (Ma & Zhang 2022). Referring to the physical option influences in this study, different from the precipitation results, the microphysical scheme shows the least impact on the soil evaporation, and the PBL and CU schemes have a larger impact on the evaporation simulation. Especially for the PBL schemes, the turbulence of different PBL options can affect the horizontal and vertical transport of the vapor near the surface and then influence the evaporation simulation in high-value areas in the southern part.
Figure 5

The spatial distribution of the evaporation over CA.

Figure 5

The spatial distribution of the evaporation over CA.

Close modal
Soil moisture refers to the amount of water stored in unsaturated soil, which plays an important role in the land energy and water cycle. The influence of soil moisture on climate is manifested in its possible changes in the surface albedo, the thermal capacity of the soil, the evaporation of the surface, and the growth of vegetation. The result of the above effects eventually leads to the redistribution of surface energy and water; finally, those changes affect the climate (Xiao et al. 2017; Koster et al. 2024). The relationship between soil moisture and evaporation is strongest in arid and semi-arid regions because evaporation in arid and semi-arid regions is mainly limited by humidity (Lawrence & Slingo 2005). The spatial distribution of soil moisture in all the soil layers (the integrated volumetric soil water content from all four soil layers in Noah-MP) of the different physical options (Figure 6) demonstrates that the relatively high values are in the northern part and mountain areas; the central parts and deserts are the areas with lowest water content values. Among the three options, the CU and PBL schemes present the least impact on the soil moisture, while the MP schemes have the largest influence. The soil moisture values were over 0.02 m3/m3 in the northern and southeastern parts of CA per the WDM6 MP scheme used, and the change of CU and PBL schemes reproduced similar soil moisture spatial patterns with the same MP schemes. Generally, the spatial-temporal of soil moisture in CA can be affected by many factors such as temperature, air humidity, radiation, evaporation, precipitation, infiltration, and groundwater level. At the same time, soil moisture is also closely related to human activities, especially in recent decades. Therefore, more detailed land use and land cover change information and typical human activities modules should be considered in the WRF simulation in the future work.
Figure 6

The spatial distribution of moisture of all the soil layers over CA.

Figure 6

The spatial distribution of moisture of all the soil layers over CA.

Close modal

In most atmospheric models, sub-grid scale processes that are not explicitly resolved by the model are represented by parameterization schemes. For example, cloud MP schemes are used to model the microphysical processes that govern cloud particle formation, growth, and dissipation on small scales. The effect of sub-grid scale clouds is represented by cumulus parameterization schemes. The short- and long-wave radiation schemes provide the atmospheric heating profiles and the estimation of net radiation for the ground heat budget. The surface layer schemes are used to calculate the friction velocity and exchange coefficients that enable the estimation of heat, momentum, and moisture fluxes by the LSM. Finally, the PBL schemes determine the flux profiles within the convective boundary layer and the stable layer, and thus provide atmospheric tendencies of temperature, moisture, and momentum in the entire atmospheric column (Shrivastava et al. 2015).

The main problem in climate change research over CA is the lack of observational data, which can create some limitations for precipitation validation and optimization by other statistical and machine learning techniques. Since precipitation is the most important indicator for TWS and water resource evaluation and prediction, the numeric model coupled with the data assimilation module (WRF-DA) will be used in future studies for precipitation simulation improvement once sufficient high-quality observations or satellite products are collected in CA. Also, the intense human activities in CA are another important factor that needs to be considered. Human activities have affected the appearance of the land surface, changing the roughness, reflectivity, and water–heat balance of the land surface, causing local climate changes. With the development of human society, the breadth and depth of its influence have increased, and the influence of human activities has become increasingly important. From the perspective of water resources, the most important human activity in CA is water consumption for agricultural irrigation, which was not considered in the numerical experiments yet in this study. In the next step, the water use module and irrigation scheme in the LSM need to be activated to not only obtain the human-induced TWS results but also to quantify the impact of human activities on TWS and regional water resources. In the past 100 years, the temperature in the arid region of CA has increased significantly, with a magnitude of 1.6 °C, which is much higher than the warming in the northern hemisphere. With the intensified global warming in the future, the temperature increase in the arid region of CA will generally be higher than the global average, likely leading to the warming of the core area of Eurasia. Another important factor for regional TWS is lake water storage variation (Ma et al. 2017), which can be solved by introducing the dynamical land use/land cover change with temporal variation and activating the lake module in the land surface scheme to enhance the description of lake effects in numerical experiments. So, future work of TWS in CA needs to clarify the contributions of natural forcing, internal variation, different human activities, and land use/land cover change.

Nine sets of simulation experiments using WRF v4.0.1 at a horizontal resolution of 25 km during 2004–2008 were carried out in CA. The dominant study variables in this study are TWS and precipitation, which are evaluated based on GRACE products and ERA5 data. In comparison with the GRACE data, all the simulations basically capture the spatial features of TWS in CA but with more detailed regional information, especially in the east part of the study domain. From the regional time series of the TWS, the WRF reproduces a downward trend in CA, but the rate of decline is relatively small due to the lack of consideration of human activities such as irrigation. The box plot shows the simulated TWS has larger variability compared to the GRACE. The different physical options and combinations present less difference and small variances in the TWS simulation. This situation may be attributed to the relatively short simulation period, and thus, longer simulation periods and finer spatiotemporal resolution are required for further research. Using the TWS products provided by both GRACE and GRACE-FO missions over longer spatiotemporal scales to achieve more statistically significant and more reliable simulation results will be the key focus of the future work. Conversely, the results indicate that the TWS in CA may be insensitive to WRF physical scheme combinations, although the model can capture the regional water balance stably. In the future, we will pay more attention to the evaluation of different physical options for the water cycle components, e.g., the precipitation, the soil water evaporation, and moisture variation, and try to consider the effects of human activities in detail, lake processes, and the utilization of data assimilation modules on regional TWS investigations in CA.

This study was jointly funded by the Second Tibetan Plateau Scientific Expedition and Research Program (STEP) (No. 2019QZKK0903-02), the International Partnership Program of the Chinese Academy of Sciences (No. 060GJHZ2022057MI), the Natural Science Foundation of China (No. 42375176), and the Iran National Science Foundation (INSF, No. 4006075). We also thank for the technical support of the National Large Scientific and Technological Infrastructure “Earth System Numerical Simulation Facility” (https://cstr.cn/31134.02.EL, EarthLab, No. 2023-EL-PT-000205). The datasets used in this study are derived from European Centre for Medium-Range Weather Forecasts (https://www.ecmwf.int/en/forecasts/datasets/reanalysis-datasets/era5), National Centers for Environmental Prediction (https://rda.ucar.edu/datasets/ds083.2/), and the GRACE data centers of JPL and CSR (https://grace.jpl.nasa.gov/data/get-data/monthly-mass-grids-land/, https://grace.jpl.nasa.gov/data/get-data/jpl_global_mascons/, and http://www2.csr.utexas.edu/grace/RL06_mascons.html). In addition, we also thank the anonymous reviewers for their detailed and helpful comments.

All relevant data in this study are available from an online repository or repositories. Due to the large volume of the numerical model results, we uploaded one group of model results and all the GRACE-based TWS products. The data link is: https://pan.baidu.com/s/1v90DNZ2Znu2dO57ohCSXHQ, and the pw code is: dfxx. If the reader has further in-depth interest in the datasets mentioned in this article, please feel free to contact the corresponding author Ziyan Zheng ([email protected]) to obtain the complete datasets.

The authors declare there is no conflict.

Barlage
M.
,
Tewari
M.
,
Chen
F.
,
MiguezMacho
G.
,
Yang
Z.
&
Niu
G.
(
2015
)
The effect of groundwater interaction in North American regional climate simulations with WRF/Noah-MP
,
Clim. Change
,
129
(
3–4
),
485
498
.
Cai
X.
,
Yang
Z.
,
Xia
Y.
,
Huang
M.
,
Wei
H.
,
Leung
L. R.
&
Ek
M. B.
(
2014
)
Assessment of simulated water balance from Noah, Noah-MP, CLM, and VIC over CONUS using the NLDAS test bed
,
J. Geophys. Res.
,
119
(
24
),
13751
13770
.
Cesana
G.
,
Suselj
K.
&
Brient
F.
(
2017
)
On the dependence of cloud feedbacks on physical parameterizations in WRF aquaplanet simulations
,
Geophys. Res. Lett.
,
44
(
20
),
10762
10771
.
Chen
F. H.
,
Wang
J. S.
,
Jin
L. Y.
,
Zhang
Q.
,
Li
J.
&
Chen
J. H.
(
2009
)
Rapid warming in mid-latitude Central Asia for the past 100 years
,
Front. Earth Sci. China
,
3
,
42
.
https://doi.org/10.1007/s11707-009-0013-9
.
Chen
L.
,
Li
Y. P.
,
Chen
F.
,
Barlage
M.
,
Zhang
Z.
&
Li
Z. H.
(
2019
)
Using 4-km WRF CONUS simulations to assess impacts of the surface coupling strength on regional climate simulation
,
Clim. Dyn.
,
53
,
6397
6416
.
Deng
M. J.
,
Long
A. H.
,
Zhang
Y.
,
Li
X. Q.
&
Lei
Y.
(
2010
)
Assessment of water resources development and utilization in the five Central Asia countries
,
Advances in Earth Science
,
25
(
12
),
1347
1356
.
doi: 1001-8166(2010)12-1347-10. (in Chinese).
Famiglietti
J. S.
&
Rodell
M.
(
2013
)
Water in the balance
,
Science
,
340
(
6138
),
1300
1301
.
Feng
J. M.
,
Wang
Y. L.
&
Ma
Z. G.
(
2015
)
Long-term simulation of large-scale urbanization effect on the East Asian monsoon
,
Clim. Change
,
129
(
3–4
),
511
523
.
Hersbach, H., Bell, B., Berrisford, P., Hirahara, S., Horányi, A., Muñoz-Sabater, J., Nicolas, J., Peubey, C., Radu, R., Schepers, D., Simmons, A., Soci, C., Abdalla, S., Abellan, X., Balsamo, G., Bechtold, P., Biavati, G., Bidlot, J., Bonavita, M., De Chiara, G., Dahlgren, P., Dee, D., Diamantakis, M., Dragani, R., Flemming, J., Forbes, R., Fuentes, M., Geer, A., Haimberger, L., Healy, S., Hogan, R., Hólm, E., Janisková, M., Keeley, S., Laloyaux, P., Lopez, P., Lupu, C., Radnoti, G., Rosnay, P., Rozum, I., Vamborg, F., Villaume, S. & Thépaut, J.
(
2020
)
The ERA5 global reanalysis
,
Q. J. R. Meteorol. Soc.
,
146
,
1999
2049
.
https://doi.org/10.1002/qj.3803
.
Hu
Z. Y.
,
Zhou
Q. M.
,
Chen
X.
,
Qian
C.
,
Wang
S. S.
&
Li
J. F.
(
2017
)
Variations and changes of annual precipitation in Central Asia over the last century
,
Int. J. Climatol.
,
37
,
157
170
.
https://doi.org/10.1002/joc.4988
.
Jiang
X.
,
Niu
G.-Y.
&
Yang
Z.-L.
(
2009
)
Impacts of vegetation and groundwater dynamics on warm season precipitation over the Central United States
,
J. Geophys. Res.
,
114
(
D6
),
D06109
.
Jiang
D. B.
,
Hu
D.
,
Tian
Z. P.
&
Lang
X. M.
(
2020
)
Differences between CMIP6 and CMIP5 models in simulating climate over China and the East Asian Monsoon
,
Adv. Atmos. Sci.
,
37
,
1102
1118
.
https://doi.org/10.1007/s00376-020-2034-y
.
Koster
R. D.
,
Feldman
A. F.
,
Holmes
T. R. H.
,
Anderson
M. C.
,
Crow
W. T.
&
Hain
C.
(
2024
)
Estimating hydrological regimes from observational soil moisture, evapotranspiration, and air temperature data
,
J. Hydrometeor.
,
25
,
495
513
.
https://doi.org/10.1175/JHM-D-23-0140.1
.
Long
D.
,
Shen
Y.
,
Sun
A.
,
Hong
Y.
,
Longuevergne
L.
,
Yang
Y.
,
Li
B.
&
Chen
L.
(
2014
)
Drought and flood monitoring for a large karst plateau in Southwest China using extended GRACE data
,
Remote Sens. Environ.
,
155
,
145
160
.
Long
D.
,
Longuevergne
L.
&
Scanlon
B. R.
(
2015
)
Global analysis of approaches for deriving total water storage changes from GRACE satellites
,
Water Resour. Res.
,
51
(
4
),
2574
2594
.
Ma
N.
&
Zhang
Y. Q.
(
2022
)
Increasing Tibetan Plateau terrestrial evapotranspiration primarily driven by precipitation
,
Agric. For. Meteorol.
,
317
,
108887
.
https://doi.org/10.1016/j.agrformet.2022.108887
.
Ma
N.
,
Niu
G.-Y.
,
Xia
Y.
,
Cai
X.
,
Zhang
Y.
,
Ma
Y.
&
Fang
Y.
(
2017
)
A systematic evaluation of Noah-MP in simulating land-atmosphere energy, water, and carbon exchanges over the continental United States
,
J. Geophys. Res.-Atmos.
,
122
,
12,245
12,268
.
https://doi.org/10.1002/2017JD027597
.
Ma
N.
,
Szilagyi
J.
&
Zhang
Y.
(
2021
)
Calibration-free complementary relationship estimates terrestrial evapotranspiration globally
,
Water Resour. Res.
,
57
,
e2021WR029691
.
https://doi.org/10.1029/2021WR029691
.
Niu
G.-Y.
,
Yang
Z.-L.
,
Mitchell
K. E.
,
Chen
F.
,
Michael
B. E.
,
Barlage
M.
,
Kumar
A.
,
Manning
K.
,
Niyogi
D.
,
Rosero
E.
,
Tewari
M.
&
Xia
Y. L.
(
2011
)
The community Noah Land Surface Model with multiparameterization options (Noah-MP): 1. Model description and evaluation with local-scale measurements
,
J. Geophys. Res.
,
116
(
D12
),
D12109
.
Oki
T.
&
Kanae
S.
(
2006
)
Global hydrological cycles and world water resources
,
Science
,
313
(
5790
),
1068
1072
.
Pan
Y.
,
Zhang
C.
,
Gong
H. L.
,
Yeh
P. J. F.
,
Shen
Y. J.
,
Guo
Y.
,
Huang
Z. Y.
&
Li
X. J.
(
2017
)
Detection of human-induced evapotranspiration using grace satellite observations in the Haihe River Basin of China
,
Geophys. Res. Lett.
,
44
(
1
),
190
199
.
Qiu
Y.
,
Hu
Q.
&
Zhang
C.
(
2017
)
WRF simulation and downscaling of local climate in Central Asia
,
Int. J. Climatol.
,
37
,
513
528
.
Qiu
Y.
,
Feng
J.
,
Yan
Z.
&
Wang
J.
(
2022
)
HCPD-CA: high-resolution climate projection dataset in Central Asia
,
Earth Syst. Sci. Data
,
14
,
2195
2208
.
https://doi.org/10.5194/essd-14-2195-2022
.
Rodell, M. & Li, B. (
2023
)
Changing intensity of hydroclimatic extreme events revealed by GRACE and GRACE-FO
,
Nat. Water
,
1
,
241
248
.
https://doi.org/10.1038/s44221-023-00040-5
.
Rodell, M., Famiglietti, J. S., Wiese, D. N., Reager, J. T., Beaudoing, H. K., Landerer, F. W. & Lo, M.-H.
(
2018
)
Emerging trends in global freshwater availability
,
Nature
,
557
,
651
659
.
https://doi.org/10.1038/s41586-018-0123-1
.
Salamanca
F.
,
Zhang
Y.
,
Barlage
M.
,
Chen
F.
,
Mahalov
A.
&
Miao
S.
(
2018
)
Evaluation of the WRF-Urban modeling system coupled to Noah and Noah-MP land surface models over a semiarid urban environment
,
J. Geophys. Res.-Atmos.
,
123
(
5
),
2387
2408
.
Scanlon
B. R.
,
Zhang
Z.
,
Reedy
R. C.
,
Pool
D. R.
,
Save
H.
,
Long
D.
,
Chen
J.
,
Wolock
D. M.
,
Conway
B. D.
&
Winester
D.
(
2015
)
Hydrologic implications of GRACE satellite data in the Colorado River Basin
,
Water Resour. Res.
,
51
,
9891
9903
.
Scanlon
B. R.
,
Zhang
Z.
,
Save
H.
,
Wiese
D. N.
,
Landerer
F. W.
,
Long
D.
,
Longuevergne
L.
&
Chen
J.
(
2016
)
Global evaluation of new GRACE mascon products for hydrologic applications
,
Water Resour. Res.
,
52
,
9412
9429
.
Scanlon
B. R.
,
Zhang
Z.
,
Save
H.
,
Sun
A. Y.
,
Schmied
H. M.
,
van Beek
L. P.
,
Wiese
D. N.
,
Wada
Y.
,
Long
D.
,
Reedy
R. C.
&
Longuevergne
L.
(
2018
)
Global models underestimate large decadal declining and rising water storage trends relative to GRACE satellite data
,
Proc. Natl. Acad. Sci. USA
,
115
(
6
),
E1080
E1089
.
Swenson
S.
,
John
W.
&
Milly
P. C. D.
(
2003
)
Estimated accuracies of regional water storage variations inferred from the Gravity Recovery and Climate Experiment (GRACE)
,
Water Resour. Res.
,
39
(
8
),
1
13
.
doi: 10.1029/2002wr001808
.
Syed
T. H.
,
Famiglietti
J. S.
,
Rodell
M.
,
Chen
J.
&
Wilson
C. R.
(
2008
)
Analysis of terrestrial water storage changes from GRACE and GLDAS
,
Water Resour. Res.
,
44
,
W02433
.
Tapley
B. D.
,
Bettadpur
S.
,
Ries
J. C.
,
Thompson
P. F.
&
Watkins
M. M.
(
2004
)
GRACE measurements of mass variability in the Earth system
,
Science
,
305
(
5683
),
503
505
.
Wang
J.
,
Feng
J. M.
,
Yan
Z. W.
,
Hu
Y. H.
&
Jia
G. S.
(
2012
)
Nested high-resolution modeling of the impact of urbanization on regional climate in three vast urban agglomerations in China
,
J. Geophys. Res.-Atmos.
,
117
(
D21
),
D21103
.
Wang
Y. L.
,
Feng
J. M.
,
Zheng
Z. Y.
&
Jin
S. F.
(
2019
)
Sensitivity of the weather research and forecasting model to radiation schemes in China
,
J. Trop. Meteorol.
,
25
,
201
210
.
Xiao
Y.
,
Ma
Z. G.
&
Li
M. X.
(
2017
)
Evaluation of the parameterizations of soil moisture influence on evapotranspiration in land surface models
,
Chin. J. Atmos. Sci.
,
41
(
1
),
132
146
.
(in Chinese)
.
Xie
B.
,
Fung
J. C. H.
,
Chan
A.
&
Lau
A.
(
2012
)
Evaluation of nonlocal and local planetary boundary layer schemes in the WRF model
,
J. Geophys. Res.-Atmos.
,
117
(
D12
),
D12103
.
Yang
S. T.
,
Yu
X. Y.
,
Ding
J. L.
,
Zhang
F.
,
Wang
F.
&
Ma
L. G.
(
2017
)
A review of water issues research in Central Asia
,
Acta Geogr. Sin.
,
72
(
1
),
79
93
.
(in Chinese)
.
Yao
J. Q.
,
Yang
Q.
,
Mao
W. Y.
,
Xu
X. B.
&
Liu
Z. H.
(
2016
)
Evaluation of the impacts of climate change and human activities on the hydrological environment in Central Asia
,
J. Glaciol. Geocryol.
,
38
(
1
),
222
230
.
(in Chinese)
.
Ye
D.
,
Zhang
S. W.
,
Wang
F.
,
Mao
F.
&
Yang
X.
(
2017
)
The applicability of different parameterization schemes in semi-arid region based on Noah-MP land surface model
,
Chin. J. Atmos. Sci.
,
41
(
1
),
189
201
.
(in Chinese)
.
Zhang
Z. Z.
,
Chao
B. F.
,
Chen
J. L.
&
Wilson
C. R.
(
2015
)
Terrestrial water storage anomalies of Yangtze River Basin droughts observed by grace and connections with Enso
,
Global Planet. Change
,
126
,
35
45
.
Zhang
L.
,
Tang
H.
,
Chang
L.
&
Sun
W.
(
2020
)
Performance of GRACE mascon solutions in studying seismic deformations
,
J. Geophys. Res. B: Solid Earth
,
125
,
e2020JB019510
.
https://doi.org/10.1029/2020JB019510
.
Zheng
Z. Y.
,
Ning
L. K.
,
Dai
D. Q.
,
Chen
L.
,
Wang
Y. L.
,
Ma
Z. G.
,
Yang
Z.-L.
&
Zhan
C. S.
(
2022
)
Water budget variation, groundwater depletion, and water resource vulnerability in the Haihe River Basin during the new millennium
,
Phys. Chem. Earth A/B/C
,
126
,
103141
.
https://doi.org/10.1016/j.pce.2022.103141
.
This is an Open Access article distributed under the terms of the Creative Commons Attribution Licence (CC BY 4.0), which permits copying, adaptation and redistribution, provided the original work is properly cited (http://creativecommons.org/licenses/by/4.0/).