Research papersEvaluation of GRACE derived groundwater storage changes in different agro-ecological zones of the Indus Basin
Introduction
Groundwater use provides distinct benefits and chances for human development (Velis et al. 2017). It is approachable to a wide number of consumers (Sakthivadivel 2007) and can be utilized based on its depth, the reason for which it is extracted, the relationship between recharge rate against withdrawals, and the distance between wells. When not tainted by human interference, the main advantage of groundwater is its high microbiological purity, which stems from its underground location and the natural protection by the soil and geological layers and filtration during flow (Calow et al. 1997). Globally, the rate of groundwater depletion rose from 126 ± 32 km3 year−1 to 283 ± 40 km3 year−1 between 1960 and 2000, respectively (Wada et al. 2010). According to Zektser and Everett (2004), 20% of the global irrigation withdrawals, around 40% of total commercial activities, and 50% of total urban activities are supported with withdrawals from groundwater. Thus, depletion in groundwater resources will cause a significant interruption of their societal and ecological functions (Danielopol et al., 2003). In both Afghanistan and Pakistan, the population’s reliance on groundwater abstraction for municipal, agricultural, and industrial purposes is growing day by day. As a result, groundwater levels are falling, prompting the consumers in both countries to respond sustainably and adaptively. There is a massive withdrawal of groundwater in the region of the Indus Basin (IB); according to Uhl (2006), the Kabul River Basin (KRB) experiences a withdrawal of 450 million m3 against recharge of 380 million m3. Similarly, Pakistan is experiencing a mean annual recharge of 83.88 km3 against a groundwater withdrawal of 55 km3 (Bhutta 2005).
More comprehensive groundwater governance is required to ensure the protection of groundwater resources. This should include spatial resolution mapping of groundwater aimed at detecting changes in water level and volume, which has largely been overlooked thus far (Megdal et al. 2015). To effectively estimate the groundwater resources and associated fluctuations, it is necessary to establish an effective groundwater-monitoring network (Wu 2004). There are various tools and methodologies that could be used at different spatial and temporal scales to assess the changes in groundwater. Usually, the groundwater observation wells are mostly used to indirectly extract the groundwater use information. It gives point-based measurements of water levels to higher accuracy, and so far the observation wells, both in Afghanistan and Pakistan, are sparsely installed and their spatial and temporal maintenance and monitoring have not been systematically managed either. In Pakistan, the groundwater observations are taken twice a year, e.g. pre-and post-monsoon season (Shahzad et al. 2020). The systematic errors may be avoided but measurements must be performed exclusively by personnel who have received adequate training (Rau et al. 2019). In addition to systematic errors in the measurements, the representativeness of the site selection for the monitoring points is a very important issue to minimize systematic errors. For example, a location close to main irrigation canals or drainage collectors might systematically influence or disturb the representativeness of measurements. Yet, this approach is practically not cost-effective when dealing with large river basins, countries, or continental geographies. Instead, there is a need to use a system/tool/method which is less expensive, yet accurate and capable to cover larger spatial extents with appropriate time-steps. Therefore, accurate and periodic long-term measurements of aquifer levels are important to track the storage of groundwater and its changes over space and time (Taylor and Alley 2001).
Recently, Gravity Recovery and Climate Experiment (GRACE) based groundwater storage (GWS) variation, both in space and time and in complex aquifer systems in large heterogeneous river basins has been very instructive (Singh and Saravanan, 2020, Iqbal et al., 2016). The GRACE satellite project provides new insights into mass redistribution within the Earth structure and establishes new hydrological viewpoints (Tapley et al., 2004a, Tapley et al., 2004b). The GRACE satellite tracks Spatio-temporal changes with an unparalleled resolution in the Earth’s gravity field and facilitates the analysis of mass changes within hydro-systems. The detailed estimation of the GWS changes derived from the GRACE satellite could be used for a decision support system in maintaining the recharge and discharge strategies within a catchment or basin. Since GRACE measures terrestrial water storage (TWS), deriving GWS change out of the TWS column requires to be validated with in-situ measurements of groundwater levels before being used for water resources management initiatives under local circumstances (Neves et al., 2020, Zhong et al., 2018, Yin et al., 2018).
The objective of this study was thus (i) to evaluate the GRACE’s performance in two different agro-ecological zones of the IB, as well as (ii) to quantify the trend of groundwater abstraction over 15 years (i.e., 2002–2017). The KRB (in Afghanistan) and the Lower Bari Doab Canal (LBDC) command area (in Pakistan) were the two distinct agro-ecological zones that were rigorously examined under the auspices of this study. The KRB and LBDC distinctly differ from each other not only in terms of geomorphologic features but also in terms of having large changes in the irrigation infrastructure, elevation, slope, climatic conditions as well as management hierarchies that undergo transboundary dissociated up-and-downstream interactions too. The addition of such an agro-ecological heterogeneity component to the evaluation of GRACE’s performance is an innovative part of this study concerning previous research in the two regions. The detailed Spatio-temporal estimates of GRACE-based GWS were also validated against in-situ groundwater levels; Furthermore, groundwater storage anomalies (GWSA) were cross-correlated with precipitation data to determine how variations in GWS respond to precipitation.
Section snippets
Study area
The IB (Fig. 1) is a trans-Himalayan river basin located in South Asia with an area of around 1.12 million km2 shared between Pakistan (47%), India (39%), China (8%), and Afghanistan (6%) (FAO/Aquastat, 2011). IB hosts one of the world’s biggest contiguous irrigation systems, i.e. the IB Irrigation System. The key rivers network of the IB includes the Kabul, Indus, Jhelum, Chenab, Ravi, Beas, and Sutlej rivers. Snowmelt and monsoon precipitation, received at the different elevation ranges of
Variation of the groundwater storage anomalies in monthly time-steps
In Fig. 4, the temporal analysis of the GWS anomalies in LBDC reveals that throughout the year, a decrease in the GWS starts from February till June; recharging the aquifers starts from July onwards, coinciding with the start of the monsoon season of June to October. Overall, with −56.97 ± 79.8 mm the LBDC experienced the highest decrease in GWS in June. Conversely, in the KRB, a decrease in the GWS starts in August onwards; KRB experienced the highest mean depletion in GWS in February which
Summary and conclusion
The groundwater aquifers are the key sources of freshwater across the IB. There has been increasing dependency on the groundwater resources not only for municipal and agricultural consumption but a heavy amount is being additionally exploited by the industrial sector. The quantification of the withdrawal of groundwater by sector is still not clear across the IB. Meanwhile, there are fewer or almost no facilities to replace the ever-increasing usage of groundwater for industrial and agricultural
CRediT authorship contribution statement
Fazlullah Akhtar: Conceptualization, Data curation, Visualization, Methodology, Writing – original draft. Rana Ali Nawaz: Methodology, Formal analysis, Writing – review & editing. Mohsin Hafeez: Conceptualization, , Writing – review & editing. Usman Khalid Awan: Conceptualization, Writing – review & editing. Christian Borgemeister: Supervision, Writing – review & editing. Bernhard Tischbein: Formal analysis, Methodology, Writing – review & editing.
Declaration of Competing Interest
The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.
Acknowledgment
The corresponding author of this research paper is supported by the SDG fellowship of the University of Bonn (Germany).
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