The natural systems are under considerable threat because of rise in temperatures and consequent global shifts in precipitation patterns(IPCC, 2014) .This threat will get more worse and socio-economic systems will be severely affected by these changes by the end of this century (Ding et al., 2016). A global rise in temperature between 0.3oC to 4.8 oC is predicted by the end of this century in 5th Assessment Report (AR5) of the Intergovernmental Panel on Climate Change (IPCC), due to the emissions of greenhouse gases (GHG)(IPCC, 2013) .
High altitude areas are more fragile to climate change(Buytaert et al., 2010) and are easily affected by climatic changes. These changes affect the services provided by these regions including water supply for hydropower and crop production etc. Increased warming trends over high altitudes have been predicted by Mountain Research Initiative(MRI, 2015) and (Gerlitz et al., 2016). These climatic changes endanger the overall hydrological equilibrium upstream and aggravate the issues associated with water management downstream. It is therefore of the utmost importance to investigate the likely impacts of climate change on the future water availability from the mountainous watersheds.
The upper Indus basin (UIB—Figure 1), contributes approximately half (Hasson et al., 2017) of the surface water availability in Pakistan, thereby ensuring the continued existence of the immediate downstream Tarbela reservoir, which is the major water storage structure in the country.
The future water availability is strongly dependent upon the future climate projections under different greenhouse gas (GHG) emissions. Since the agricultural sector of Pakistan's economy is highly dependent on erratic water supplies from the Hindukush-Karakoram-Himalayan (HKH) watersheds of the Indus basin, it is of the utmost importance to conduct a realistic evaluation of the future water availability from these watersheds in order to ensure the socioeconomic development of the country in a manner that is sustainable.
An awareness of the likely variations in precipitation and temperature that may occur in the future is important to explore the impact on water resources and livelihoods. It will be helpful in the process of creating and putting into action appropriate adaptation strategies on a river basin scale.
Many researchers have used Global Climate Models (GCMs) and Representative Concentration Pathways (RCPs) to forecast future climate change. However, because of the relatively coarse computational cells that they use, GCMs are not suitable for direct application to sub-grid or local scale impact studies (Fowler et al., 2007). So, these GCMs need to be downscaled either using statistical downscaling (SD) or dynamical downscaling (DD). DD can be achieved by using the regional climate model (RCM) embedded in a larger GCM. RCMs use the boundary conditions of the GCMs and dynamically downscale them to the limited area of interest with more detailed output(Abiodun & Adedoyin, 2016). Because of their ability to capture weather phenomena at various spatial and temporal scale, RCMs are now widely used to simulate the future climate along with assessing the impacts of climate on water resources and predicting extreme hydrological events(Kim et al., 2020; Lee & Cha, 2020). Coordinated Regional Downscaling Experiment (CORDEX) consists of a range of RCMs which have been used worldwide by many researchers. Bukovsky et.al(2020) have used multi model ensemble of NA-CORDEX RCMs to project temperature and precipitation. Luhunga et.al.(2018) have used CORDEX RCMs to project climate changes for Tanzania. Fotso-Nguemo et. al(2019) have used multi model ensemble of CORDEX to predict the impact of climate change on extreme precipitation indices over Central Africa. Chapagain et.al (2021)have used CORDEX-SA for future projection of climate indices under low and high emission scenarios for Nepal. EURO-CORDEX and MED-CORDEX has been used by(Baronetti et al., 2022) to predict drought events in northern Italy.
RCMs can be further downscaled to the point data of gauging station using SD techniques. The SD technique establishes statistical links between large scale weather and local scale weather. Extensive research on downscaling of GCMs have been carried out. However, there are only a few studies on downscaling of RCMs.
The SD techniques are regarded to be among the most popular since they have the advantages of being computationally affordable and being able to provide comprehensive station-specific data (Trzaska & Schnarr, 2014). Karam et.al (2022)have used sch technique to downscale CORDEX RCM to assess hydrological extremes in Congo basin. One example of SD technique is the Long Ashton Research Station Weather Generator (LARS-WG6) (Semenov et al., 2002). It has been adopted by various researchers and studies have shown that it is able to simulate future climate with reasonable skills (Hashmi et al., 2011) and (Bayatvarkeshi et al., 2020). It has been used successfully in numerous studies to downscale climate variables such as in the and Koshi River Basin in Nepal (Agarwal et al., 2014), Gujrat, India (Sarkar et al., 2015), Nile River Basin (Fenta Mekonnen & Disse, 2018) and Northeastern China(Sha et al., 2019).
Many studies have been conducted on the use of downscaled GCMs based on various RCP scenarios for evaluating potential climate changes and their impact on UIB hydrology (Lutz et al., 2016; Ougahi et al., 2022; Pomee & Hertig, 2021). Few researchers have used RCMS for Upper Indus Basin including (Khan et al., 2015; Hassan et al., 2019 and Shah et al., 2020). Among these, some has either used only one RCM, or have used set of RCMs for end century and only for one RCP scenario. Keeping in view the significance of the UIB for Pakistan, it is absolutely necessary to conduct a more in-depth study that investigates concerns regarding an uncertain future by taking into account climate predictions from a greater number of RCMs, additional RCPs, and more than one future time period in the twenty-first century. In this perspective, the goals of the current research are as follows: (a) to examine the capability of LARS-WG6 for downscaling RCMs in the UIB; and (b) to project the climate changes for two selected future time periods[2041–2070 (2050s)] and [2071–2100 (2080s)] under RCP4.5 and RCP8.5 scenarios. These findings will be valuable in environmental planning and risk reduction initiatives on a local scale, particularly those pertaining to water resources and extreme hydrological events.