Next Article in Journal
The Impact of Meteorological Factors on Stroke Incidence in the Transdanubian Region of Hungary
Previous Article in Journal
A Comparison between Radar Variables and Hail Pads for a Twenty-Year Period
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Article

Quantifying Climate Change Variability for the Better Management of Water Resources: The Case of Kobo Valley, Danakil Basin, Ethiopia

by
Mengesha Tesfaw
1,*,
Mekete Dessie
1,
Kristine Walraevens
2,
Thomas Hermans
2,
Fenta Nigate
3,
Tewodros Assefa
4 and
Kasye Shitu
5
1
Faculty of Civil and Water Resources Engineering, Bahir Dar Institute of Technology, Bahir Dar University, Bahir Dar P.O.Box 26, Ethiopia
2
Laboratory for Applied Geology and Hydrogeology, Department of Geology, Ghent University, 9000 Ghent, Belgium
3
School of Earth Sciences, Bahir Dar University, Bahir Dar P.O.Box 79, Ethiopia
4
Department of Irrigation and Water Resource Engineering, Hawassa Institute of Technology, Hawassa, Ethiopia
5
Department of Natural Resource Management, Mekdela Amba University, Tulu-Awlia, Ethiopia
*
Author to whom correspondence should be addressed.
Climate 2024, 12(10), 159; https://doi.org/10.3390/cli12100159
Submission received: 4 August 2024 / Revised: 9 September 2024 / Accepted: 10 September 2024 / Published: 6 October 2024

Abstract

:
Alterations in the hydrological cycle due to climate change are one of the key threats to the future accessibility of natural resources. This study used 12 GCM climate models from CMIP6 to evaluate future climate change scenarios by applying model performance measures and trend analysis in Kobo Valley, Ethiopia. The models were ranked based on their ability to analyze the historical datasets. The result of this study showed that the outputs of the FIO-ESM-2-0 CIMP6 model had a good overall ranking for both precipitation and temperature. After bias correction of the model-based projections with the observed data, the average annual precipitation in the average scenario (SSP2-4.5) decreased by 4.4% and 13% in 2054 and 2084, respectively. Similarly, in the worst-case scenario (SSP5-8.5), by the end of 2054 and 2084, decreases of 4% and 12.8%, respectively, were predicted. The average annual maximum temperature under the SSP2-4.5 scenario increased by 1.5 °C in 2054 and by 2.1 °C in 2084. The average annual maximum temperature under the worst-case (SSP5-8.5) scenario increased by 1.7 °C in 2054 and by 3.2 °C in 2084. In the middle scenario (SSP4.5), the average annual minimum temperature increased by 2.2 °C in 2054 and by 3 °C in 2084. The average annual minimum temperature under the worst-case (SSP5-8.5) scenario increased by 2.6 °C in 2054 and by 4.3 °C in 2084. The seasonal variability in precipitation in the studied valley will decrease in the winter and increase in the summer. A decrease in precipitation combined with an increase in temperature will strengthen the risk of drought events in the future.

1. Introduction

Global climate change encompasses changes in the atmospheric composition as well as changing interactions between the atmosphere and other various geological, chemical, and biological factors within Earth’s system [1,2,3,4]. According to [5], global climate change is driven by natural or human forces that can lead to changes in the likelihood of the strength of extreme weather and climate events. Changes in climate variables have additional influences on Earth’s system, such as changes in land use/land cover, water resource availability, and environmental hazards [6,7,8].
The results of human-induced pressure can directly or indirectly alter the composition of the atmosphere, and consequently, the natural climate variability is observed over comparable referenced time scales [9]. Natural processes such as volcanic eruptions [10] and human activities such as land use and deforestation [11] can have a significant role in changing greenhouse gases. Different natural and anthropogenic factors are responsible for changing precipitation patterns [12]. Greenhouse gas concentrations are used as input statistics for General Circulation Models (GCMs) [13].
According to the Intergovernmental Panel for Climate Change (IPCC) 2013 reports, changes in rainfall and temperature in many parts of Africa are causing fluctuations in freshwater and affecting the quality and quantity of water accessibility. The GCM and analyses of their products provide historical and projected values of climate variables.
Several meteorological stations lack any recorded data or their records are over short periods. Therefore, satellite data have reduced the challenges associated with the shortage of station observations and enhanced the spatial and temporal continuity in meteorological data in data-scarce regions, thereby creating great progress in the study and understanding of climate change. After the 1990s, satellite data entered data assimilation systems, which further improved the accuracy of meteorological data [14]. Currently, many scholars have used satellite or reanalysis products to represent the spatiotemporal variability in climate change across the world. In this study, we used satellite-based data, reanalysis models, and the combination of satellite data with reanalysis products to investigate the spatiotemporal variability in climate change in Kobo Valley.
The global climate change projections were carried out using GCMs, which provide future climate change variables at large spatial scales. The Intergovernmental Panel for Climate Change (IPCC) released five series of reports on climate change. However, the CMIP6 models are more advanced in terms of modeling groups, the number of projection scenarios, and the number of various experiments involved [15,16,17,18,19]. The CMIP6 models have a broader range of complexity as compared with the previous assessment phases due to several improved physical processes and their spatial resolution. Climate change scenarios provide critical results in climate models through their description and the involvement of human-induced as well as natural processes for emissions trajectories [20].
The Intergovernmental Panel for Climate Change (IPCC) released their sixth assessment report (AR6) based on the latest CMIP6 models [21]. A significant improvement in the CMIP6 models compared with the previous CMIP5 models is the inclusion of socioeconomic development factors with GHG emission scenarios (representative concentration pathways (RCPs)) [22]. The CMIP6-GCMs present aspects of improvement over previous generations, such as higher spatial resolution and better parameterization schemes of the physical and biogeochemical processes of the climate system [3].
General Circulation Models (GCMs) are one of the primary tools for understanding future climate projections. Shared Socioeconomic Pathways (SSPs) characterize a more realistic socioeconomic development by considering different social, economic, technological, and political scenarios [23]. Several studies have revealed that CMIP6 models show better simulation performance in terms of hydrological responses and impact assessment [17,24,25,26,27,28,29]. However, the spatial scale of these GCMs is generally hundreds of kilometers in order to represent the Earth’s system, including land, oceans, and the atmosphere. Therefore, capturing local-scale details should be improved in order to generate promising results for users working on regional-scale studies [30].
The seasonal and hydrological variability in climate change has been experienced in different parts of Ethiopia [31,32,33,34]. However, different studies have identified varying scales and magnitudes of their impacts. For example, the precipitation projections in ref. [31] show a slightly (statistically insignificant) increasing trend for the near (long)-term periods in the Upper Blue Nile Basin. Natural resources in Ethiopia are highly vulnerable to climate variability because of their topography and anthropogenic factors such as land degradation, increasing population, and natural resource management practices [35,36].
Most studies conducted in Ethiopia have used a single GCM selection criterion and thus may not provide accurate model selection and impact assessment. Moreover, the climate change variability in the Danakil Basin has not been studied with an appropriate climate model projection. Therefore, in this study, we used several model selection criteria to select the best representative models for seasonal and annual hydrological variability. Minimizing model discrepancies is important and was conducted in this study by using multi-model selection criteria of GCMs with the most recent naval approach (state-of-the-art) to evaluate the individual CMIP6 models. The accurate evaluation of an individual model’s performance before selecting the representative GCMs for a particular impact assessment is also important. In this regard, comprehensive studies are required to select improved CMIP6 models for simulating climate change variability over various spatiotemporal scales.
In recent times, extreme events like momentary devastating floods, prolonged droughts, and water scarcity that limit agricultural activities and socioeconomic activities have become frequent phenomena in Kobo Valley. The variability in hydrometeorological processes is worth investigating using the global climate model. This investigation could also evaluate the climate models’ reliabilities, identifying their strengths and restrictions, as well as identifying the best-performing model for a specified location and time. The new set of investigations will also help to evaluate the applications of machine learning potentials for climate change prediction that would suggest a range of strengths and limitations for a specified location.
Therefore, the objective of this study is to quantify the variability and trends in climatic variables in Kobo Valley. In this study, (a) the correlations and biases of four reanalyzed meteorological variables from reanalysis products (ERA5, MERRA-2, JAR-55-mdl-iso, 20CRv3), satellite (CHIRPS), and merged products of the Climate Prediction Center (CPC) are compared based on the daily weather variable data obtained from 12 ground meteorological stations from 1985 to 2014 and (b) the meteorological variables from CMIP6 models are projected to determine future possible trends. Moreover, a comprehensive set of statistical indicators is used to assess how the calculated climate variables from the reanalysis and merged products compare with the corresponding observational data.

2. Material and Methods

2.1. Area Description

Kobo Valley is located in the Danakil Basin, Ethiopia. The valley has an altitude ranging from 1136 m to 3970 m above sea level. It is found on the intermountain plain between 11.84° and 12.34° north and 39.34° and 39.84° east. The area covers 1228 km2. Figure 1 shows the location of Kobo Valley.

2.2. Dataset

The observed daily temperature and precipitation data were collected from the Ethiopian Meteorological Agency. However, in the Danakil Basin, there is limited data availability and various gaps in the time series data. The installation and accessibility periods of the gauged stations were divided into three groups as follows: Group 1, precipitation stations with 30 years (1985–2014) of records, Group 2 with 16 years (1998–2014) of records, and Group 3 with 9 years (2006–2014) of records.
In this study, the average monthly, seasonal (summer, winter), and annual data were derived from the daily meteorological datasets. The summer season starts in June and ends in September (JJAS), while winter begins in March and lasts until May (MAM). The satellite data, the Reanalysis model, and the merged results of satellite data with reanalysis model products were analyzed and compared with historical meteorological data. Table 1 shows the meteorological stations used for this study and the grouping based on measurement periods.
Several gauging stations have a lack of consistency in their measured data. Various spatial interpolation techniques are available today with varying degrees of complexity to fill data gaps and maintain consistency. The inverse distance method is the most widely used method for filling missing data [37]. In this method, the weights for each sample are inversely proportional to its distance from the point being estimated [38]. We used the inverse distance method to complete the missing precipitation data of stations that have other stations nearby, using the following equation (Equation (1)):
Px = i = 1 N 1 di 2 Pi i = 1 N 1 di 2
where Px = estimate of rainfall for the ungauged station in mm, Pi = rainfall values of rain gauges used for estimation in mm, di = distance from each location to the point being estimated in km, and N = No. of surrounding stations.
The historical precipitation, maximum, and minimum temperature of the satellite and merged products over the study area (Kobo Valley) were retrieved from the Royal Netherlands Meteorological Institute Climate Explorer website (https://climexp.knmi.nl/) accessed on 28 March 2023. The reanalysis data were retrieved from the Collaborative Reanalysis Technical Environment Intercomparing Project (CREATE-IP) under the designation in the Earth System Grid Federation (ESGF) website (https://esgf-node.llnl.gov/projects/create-ip/) accessed on 28 March 2023.
The satellite products of the Climate Hazards Group InfraRed Precipitation with Station (CHIRPS) data, and the reanalysis products of European Community Medium-range Weather Forecasts v5 (ECMWF-ERA5), NASA Modern Reanalysis Evaluation (NASA-MERRA v2), Japanese Meteorological Agency (JRA-55-mdl-iso), and Twentieth Century Reanalysis V3 (20CRv3) were used. The satellite, reanalysis model, and CPC merged products were used and validated by the observational data for the baseline period (1985–2014). The following table (Table 2) shows the data products, resolutions, and their sources for the selected variables.

Estimation of Potential Evapotranspiration (PET)

The other important hydrological variable is evapotranspiration, which is governed by several factors, where the most important are temperature, humidity, and the availability of water [39]. There are different methods to quantify the potential evapotranspiration of a given watershed. The FAO (Food and Agriculture Organization) recognized that the Penman–Monteith method (PM) is a standard and widely acceptable method for potential evapotranspiration (PET) estimation. However, because of detailed input meteorological datasets, the application of the Penman–Monteith method (PM) is often limited in many regions. The model requires several climate variables, including the air temperature (Tmax and Tmin), relative humidity (RH), solar radiation (Rs), and wind speed at 2 m height (U2). Most of these climate variables are not available at the meteorological stations in many regions in Ethiopia. In such cases, selecting an alternative method with similar efficiency to that of the standard technique has to be identified [40].
The Hargreaves method is an alternative method for estimating PET if insufficient meteorological data are available and is recommended by the FAO [41]. The Hargreaves method is a simple evapotranspiration model that requires a few input parameters. For this study, the PET was simulated by using the Hargreaves method in Standardized Precipitation–Evapotranspiration Index (SPEI) packages written in R [42]. The Hargreaves equation requires input data on radiation and temperature. The advantage of this method is that no radiation has to be measured since the model works with calculated extra-terrestrial radiation. Equation (2) represents the potential evapotranspiration estimation using the Hargreaves method.
PET = 0.0135 Rs Conv ( T + 17.8 )
where PET is potential evapotranspiration (mm day−1), T is the mean temperature of the day (°C), Rs is solar radiation (MJ m−2 day−1), and Conv is conversion to the ET factor (m2 mm MJ−1). This method uses nearest neighbor interpolation to simulate the spatiotemporal distribution of potential evapotranspiration.

2.3. Future Scenarios

The temperature and precipitation data were extracted from the World Climate Research Programme’s (WCRP’s) CMIP6 under a medium forcing scenario (SSP2-4.5) and a strong forcing scenario (SSP5-8.5). For future climate scenarios, the monthly weather data were investigated for 30-year time intervals for the baseline period (1985–2014), the near term (2025–2054), and the long term (2055–2084).
The selection of future projections was based on historical data and was considered in three time steps, which are average monthly, seasonal (JJAS, MAM), and annual. This allowed us to grasp all statistical analyses of the time series climate data for the selected individual model. The primary operations were the analysis of CMIP6-driven weather datasets and the evaluation/calibration with station data. Overall, 12 global climate models were obtained from the WCRP platform (https://esgf-node.llnl.gov/search/cmip6/). The CMIP6 model products were accessed on 28 March 2023. We used several criteria to evaluate the individual model results in terms of the monthly basis, the grid level (gn), the nominal resolution (100 km), the type of source (AOGCM), and the variant level (r1i1p1f1). The selected individual CMIP6 products (acronyms, resolutions, countries, and references) are summarized in Table 3.
The process started with extracting the individual outputs of GCMs by location and period. The extraction process was performed with CDO (Climate Data Operator). Since all climate models have coarse resolution, spatial downscaling was performed considering the outputs of the GCM as grid points. The Inverse Distance Weighting (IDW) method was used to extract four surrounding grid points for each GCM output to the observed station.
The individual GCM outputs were evaluated based on their statistical relationships to the observed datasets on time levels of average monthly, seasonal, and annual bases, followed by identifying the best possible probability distributions and their trends. Bias correction methods were applied after the extraction of GCM outputs. Various bias correction methods are available [43]. In this study, the quantile mapping method was applied to minimize errors. The outputs of individual GCMs are biased because of the lack of parameters, inadequate length of recorded data, and low spatial resolution.

2.4. Model Performance

2.4.1. Statistical Analysis

Model performance and trend studies were applied using multiple statistical analyses. We used the correlation coefficient, the root mean square error, the mean absolute error, probability distributions, and trend analysis. The mathematical expressions of these indexes are given below (Equations (3)–(5)) [44]. The correlation coefficient is a value that indicates the strength of the relation between variables, and it ranges from −1 to 1.
R   = n ( ( x y ) ( x ) ( y ) ) [ n x i 2 ( x ) 2 ] [ n y 2 ( y ) 2   ]
where R is the correlation coefficient, n is number of given datasets, x is the observed variable, and y is the model variable.
The root mean square error (RMSE) is a frequently used measure of the difference between values predicted by a model and the values observed from the environment that is being modeled.
RMSE = 1 n i = 1 n ( Xobs , i Xmodel , i ) 2
where n is the number of observations, (Xobs, i) is the observed value, and (Xmodel, i) is the model value.
The mean absolute error (MAE) is the absolute value of the difference between the model value and the observed value. The mean absolute error measures accuracy of continuous variables.
AE = 1 n i = 1 n | Oi Pi |
where n is the number of observations and |Oi − Pi| is the absolute error. Both the mean absolute error and the root mean square error express average model prediction error in units of the variable of interest. The mean absolute error and the root mean square error can range from 0 to ∞ and are indifferent to the direction of errors. It is noteworthy that the lower the value of RMSE and MAE, the more reliable the prediction of the data.

2.4.2. Trend Test Analysis

The trends in the time series datasets were detected using parametric or non-parametric tests. The Mann–Kendall (MK) test is a widely used method for non-parametric tests because of its independence on the distribution of the data and because it is not affected by missing datasets and their outliers [45]. Non-parametric methods are alternatives that require few assumptions to be made about the data. These methods are most often used to analyze data that do not meet the distributional requirements of parametric methods. To apply the non-parametric MK test, the data time series does not need to be normally distributed, but it must be serially independent and randomly ordered.

2.4.3. Probability Distributions

The climate data were analyzed to identify the best-fit probability distribution for each time level in the study area. Several studies have investigated precipitation analysis and identified the best-fit probability distribution functions such as Normal, Lognormal, Gumbel, Weibull, and Pearson-type distributions [46]. Probability distributions are selected based on Akaike Information Criteria (AIC) and its distribution type (DT). The smaller the AIC value, the better is the model fit [47]. For the observed data and the individual climate models, the best likely probability distributions were selected with the help of the “gamlss” package in R [48]. In this approach, probability distributions of the observed and reanalysis results were analyzed using “fittest” in R packages.

3. Results

3.1. Data Quality Checking

The observed precipitation and temperature data quality were checked by both distribution types and their trends. Table 4 shows the distribution type of the observed, satellite data, reanalysis, and merged products at different time levels.
The trend test results can evaluate the reanalysis products by considering the similarity in their trends. The merged (CPC) products of the precipitation follow the same trend as the observed datasets at all time levels. Table 5 shows the trend analysis of the observed, satellite, reanalysis, and merged products at different time levels.
The merged (CPC) products of the precipitation follow the same trend as the observed datasets at all time levels. Figure 2 shows the results of the comparison between observed, satellite, and reanalysis products for average monthly precipitation data. The unit of measurement for precipitation is mm.
The historical temperature datasets were compared to the reanalysis products. Figure 3 shows the comparison results between the observed and reanalysis products for the average monthly maximum and minimum temperature datasets. The unit of measurement for temperature is degree centigrade.
The historical potential evapotranspiration (PET) datasets were compared to the reanalysis products. Figure 4 shows the results of the comparison between observed and reanalysis products of the average potential evapotranspiration. The unit of measurement for PET is mm.
Meteorological stations represent the area of the specific locations that are near and around the measured point. The spatial interpolation technique was used to estimate meteorological parameters for other neighboring locations. The Inverse Distance Weight (IDW) method was selected from the spatial interpolation methods available in ArcGIS. Figure 5 shows the spatial distribution of the climate variables over the valley.

3.2. Selection of the Future Climate Model

The selected projected GCMs were evaluated by their distribution type, statistical characteristics, and trends in the observed/historical data of average monthly, seasonal, and annual time intervals.

3.2.1. Identification of Distribution

The observed average monthly, seasonal (summer, winter), and annual precipitation data were identified to have Normal (NO), Normal (NO), Reverse Gamble (RG), and Normal (NO) distributions, respectively. The MRI-ESM2-0, CESM2-WACCM, and FIO-ESM-2-0 models for precipitation and the FIO-ESM-2-0 model for maximum temperature have top ranks among the selected CMIP6 models. Table 6 shows the results of observed and historical CMIP6 model distributions.

3.2.2. Trend Test Results

The trend test was also performed at three different levels for the distribution analysis. For the precipitation data series, the CanESM5 model has the same trend as the observed data in all four levels, while the ACCESS-ESM1-5 model has a better fit for three time levels except in JJAS. CS-ESM2-0 has the same trends as the observed data for maximum temperature datasets, while CAS-ESM2-0 and FIO-ESM-2-0 have similar trends as the observed/historical minimum temperature series for all time levels.
The significance was determined based on the p-values at a significance level of 0.05. Table 7 shows the results of the trend tests of the observed/historical data and the individual CMIP6 models.

3.2.3. Model Performance Measurement

The model performance measures were also calculated at three different levels. For the precipitation data datasets, the TaiESM1 model has a better overall model performance at all time levels. The CMCC-ESM2 products have a better model performance with the observed datasets for maximum temperature, while MRI-ESM2-0 has a good overall performance with the historical data series for minimum temperature at all time levels. The correlation, RMSE, and MAE of the observed/historical data and the individual GCM outputs are given in Table 8. Each model is scored a rank.
The final ranks for the correlation (R), root mean square error (RMSE), and mean absolute error (MAE) of the observed/historical data and the CMIP6 climate models are given in Table 9.
The FIO-ESM-2-0 model has the top rank among the selected CMIP6 models for precipitation. Table 10 shows the summary of probability distribution functions (PDFs), model performance measures (MPMs), and trend (MK-tests) for the selected variables from the CMIP6.
The FIO-ESM-2-0 model has the top rank among the selected CMIP6 models for temperature. Table 11 shows the sum of ranks for maximum and minimum temperatures from the CMIP6 models.
Based on the selected multi-model selection criteria, the FIO-ESM-2-0 model has the best overall model performance for all climate variables.

3.3. Bias Correction and Future Scenarios

After bias correction of the results of each GCM, the average annual precipitation in the middle scenario (SSP2-4.5) shows a decrease of 4.4% and 13% in 2054 and 2084 respectively. Similarly, in the worst-case scenario (SSP5-8.5), in 2054, there is a decrease in precipitation by 4%, and in 2084, by 12.8%. The average annual maximum temperature under the SSP2-4.5 scenario increases by 1.5 °C in 2054 and by 2.1 °C in 2084. The average annual maximum temperature under the worst case (SSP5-8.5) scenario increases by 1.7 °C in 2054 and by 3.2 °C in 2084. In the middle scenario (SSP4.5), the average annual minimum temperature increases by 2.2 °C in 2054 and by 3 °C in 2084. The average annual minimum temperature under the worst case (SSP5-8.5) scenario increase by 2.6 °C in 2054 and by 4.3 °C in 2084. Figure 6 presents the projected precipitation in the medium and worst-case scenarios derived from FIO-ESM-2-0. In all projection scenarios, the unit of measurement for the monthly precipitation and potential evapotranspiration is mm, while for temperature, it is degree centigrade.
Figure 7 presents the probable monthly maximum temperature in the medium and worst-case scenarios derived from FIO-ESM-2-0.
Figure 8 presents the probable monthly minimum temperature in the medium and worst-case scenarios derived from FIO-ESM-2-0.
Figure 9 presents the probable monthly potential evapotranspiration in the medium and worst-case scenarios derived from FIO-ESM-2-0.

4. Discussion

The results of this study quantify climate change variability for better management of water resources under medium and worst-case scenarios. Reanalysis, satellite, and merged (satellite and reanalysis) climate data products were evaluated using historical observed datasets. The merged products of the Climate Prediction Center (CPC) have a similar distribution as the observed precipitation on seasonal and annual bases. The reanalysis products of maximum temperature from MERRA-2 and 20CRv3 have the same trend test results as the observed datasets at all time levels.
We observed that the MERRA-2 product overestimates the precipitation data and underestimates temperature datasets at all time levels. The ERA5 product has the best fit with the simulated evapotranspiration using the Hargreaves method. The 20CRv3 product is the best-fitted model for maximum temperature.
The timing and magnitude of projected future climate changes are uncertain because of different ambiguities in anthropogenic and natural conditions, and climate sensitivity can change the predicted results. The results of this study showed that the outputs of the FIO-ESM-2-0 CIMP6 model have a good overall ranking for both precipitation and temperature.
This study evaluates the climate change model’s potential for analyzing climate variables and their trends. The merging of satellite data with model products reproduces best the historical observed meteostation data. Climate change scenarios can provide information on how future human-induced factors are expected to alter the composition of the atmosphere and how this may affect global climate conditions. The projected precipitation derived from the FIO-ESM-2-0 CIMP6 model will decrease in the medium and worst-case scenarios, while the projected temperature will increase.

5. Conclusions and Recommendations

The outputs of CMIP6 are preferred over CMIP5 because of several improved climate projection scenarios. Several improvements have been provided by CMIP6 such as better resolution, the number of parameterizations involved, and considering various emission scenarios. The model evaluation criteria are important for appropriate model selection. The GCMs are at a coarse resolution, and spatial downscaling should be performed before analyzing the climate change effects at a watershed level. Appropriate bias correction methods are important to reduce errors in CMIP6 model results. Because of some uncertainty in the variables, the projected climate change trends and their variability may change over time in the study area. Based on the statistical analysis, the FIO-ESM-2-0 model has the best performance for both weather datasets under the selected SSP scenarios.
The average annual precipitation in the middle scenario (SSP2-4.5) shows a decrease of 4.4% and 13% in 2054 and 2084, respectively. The worst-case scenario (SSP5-8.5) shows a decrease in precipitation by 4% in 2054 and by 12.8% in 2084. The average annual maximum temperature under the SSP2-4.5 middle scenario increases by 1.5 °C in 2054 and by 2.1 °C in 2084. Under the worst-case (SSP5-8.5) scenario, it increases by 1.7 °C in 2054 and by 3.2 °C in 2084. In the middle scenario (SSP2-4.5), the average annual minimum temperature increases by 2.2 °C in 2054 and by 3 °C in 2084, while in the worst-case scenario, it increases by 2.6 °C in 2054 and by 4.3 °C in 2084.
The results of the predicted climate variables using the CMIP6 under SSP scenarios also predict an increase in annual average temperature in the future. Moreover, the seasonal amount of precipitation will decrease in the winter but slightly increase in the summer. This will be accompanied by an increase in the annual potential evapotranspiration rate. The conclusions of this research have crucial importance for impact studies of climate change scenarios. These results can support hydrological impact studies based on the CMIP5 projections and would benefit from updating the CMIP6 ensemble to obtain more confident estimations of future hydrological conditions [49].
We obtained satisfactory results for the predicted climate change variability using three model selection criteria. However, some limitations have been observed such as the spatial resolution of the CMIP6 model result, which is coarser. Some studies revealed that CMIP6 models showing the highest warming are unlikely to be representative of the real world, and CMIP6 projections of global surface temperature should not be exclusively relied on for policy-relevant decisions [50]. Several improvements should be made to avoid drawbacks, such as addressing cloud effects, carbon budgets, and net-zero emission objectives. If the model selection criteria were modified, the probability of selecting another CMIP6 model as the optimal one would be high, and the projected results would be different.
A decrease in the estimation errors of CMIP6 projection products will be obtained using daily time steps. Moreover, studies are needed to combine a daily basis future data series to select the appropriate models for future predictions.

Author Contributions

Conceptualization, M.T.; methodology, M.T. and M.D.; software, M.T.; validation, K.W., T.H., F.N. and K.S.; formal analysis, M.D., K.W., T.H. and T.A.; resources, K.W. and F.N.; data curation, T.A. and K.S.; writing—original draft, M.T.; writing—review and editing, M.T., M.D., T.H., K.W., T.A. and K.S.; visualization, T.H.; supervision, M.D., K.W. and T.H.; funding acquisition, K.W. All authors have read and agreed to the published version of this manuscript.

Funding

This research received no external funding.

Data Availability Statement

The Ethiopian National Meteorological Agency provided climatic data. We acknowledge the World Climate Research Programme’s Working Group on Coupled Modelling and all the modeling groups that performed the simulations and made their data available. The reanalysis, monthly observations, and CMIP6 results are openly available through the KNMI Climate Explorer website at https://climexp.knmi.nl/start.cgi, and https://esgf-node.llnl.gov/search/cmip6/, accessed on 28 March 2023.

Acknowledgments

The authors acknowledge the support of the ITP project SULAMA (Sustainable Land Management) (VLIR-UOS reference BE2022ITP246A103), in the framework of the International Training Programme (ITP), as part of the “Higher Education & Science for Sustainable Development” (HES4SD) of VLIR (Flemish Interuniversity Council)-UOS (University Development Cooperation), in which the first author was trained at Ghent University.

Conflicts of Interest

The authors declare no conflicts of interest.

References

  1. Müller-Hansen, F.; Schlüter, M.; Mäs, M.; Donges, J.F.; Kolb, J.J.; Thonicke, K.; Heitzig, J. Towards representing human behavior and decision making in Earth system models—An overview of techniques and approaches. Earth Syst. Dyn. 2017, 8, 977–1007. [Google Scholar] [CrossRef]
  2. Flato, G.M. Earth system models: An overview. Wiley Interdiscip. Rev. Clim. Chang. 2011, 2, 783–800. [Google Scholar] [CrossRef]
  3. Eyring, V.; Bony, S.; Meehl, G.A.; Senior, C.A.; Stevens, B.; Stouffer, R.J.; Taylor, K.E. Overview of the Coupled Model Intercomparison Project Phase 6 (CMIP6) experimental design and organization. Geosci. Model Dev. 2016, 9, 1937–1958. [Google Scholar] [CrossRef]
  4. Stepanenko, V.M.; Repina, I.A.; Fedosov, V.E.; Zilitinkevich, S.S.; Lykossov, V.N. An Overview of Parameterezations of Heat Transfer over Moss-Covered Surfaces in the Earth System Models. Izv.—Atmos. Ocean Phys. 2020, 56, 101–111. [Google Scholar] [CrossRef]
  5. Trenberth, K.E.; Fasullo, J.T.; Shepherd, T.G. Attribution of climate extreme events. Nat. Clim. Chang. 2015, 5, 725–730. [Google Scholar] [CrossRef]
  6. Näschen, K.; Diekkrüger, B.; Evers, M.; Höllermann, B.; Steinbach, S.; Thonfeld, F. The Impact of Land Use/Land Cover Change (LULCC) on Water Resources in a Tropical Catchment in Tanzania under Different Climate Change Scenarios. Sustainability 2019, 11, 7083. [Google Scholar] [CrossRef]
  7. Kaushal, S.S.; Gold, A.J.; Mayer, P.M. Land use, climate, and water resources-global stages of interaction. Water 2017, 9, 815. [Google Scholar] [CrossRef]
  8. Talib, A.; Randhir, T.O. Climate change and land use impacts on hydrologic processes of watershed systems. J. Water Clim. Chang. 2017, 8, 363–374. [Google Scholar] [CrossRef]
  9. Colorado-Ruiz, G.; Cavazos, T.; Salinas, J.A.; De Grau, P.; Ayala, R. Climate change projections from Coupled Model Intercomparison Project phase 5 multi-model weighted ensembles for Mexico, the North American monsoon, and the mid-summer drought region. Int. J. Climatol. 2018, 38, 5699–5716. [Google Scholar] [CrossRef]
  10. Ward, P.L. Sulfur dioxide initiates global climate change in four ways. Thin Solid Film. 2009, 517, 3188–3203. [Google Scholar] [CrossRef]
  11. Onoja, U.S.; Dibua, U.M.E.; Enete, A.A. Climate Change: Causes, Effects And Mitigation Measures—A Review. Glob. J. Pure Appl. Sci. 2011, 17, 469–479. Available online: www.globaljournalseries.com (accessed on 8 September 2024).
  12. Kuttippurath, J.; Murasingh, S.; Stott, P.A.; Balan Sarojini, B.; Jha, M.K.; Kumar, P.; Nair, P.J.; Varikoden, H.; Raj, S.; Francis, P.A.; et al. Observed rainfall changes in the past century (1901–2019) over the wettest place on Earth. Environ. Res. Lett. 2021, 16, 024018. [Google Scholar] [CrossRef]
  13. Jaagus, J.; Mändla, K. Climate change scenarios for Estonia based on climate models from the IPCC Fourth Assessment Report. Est. J. Earth Sci. 2014, 63, 166–180. [Google Scholar] [CrossRef]
  14. Eyre, J.R.; Kelly, G.A.; McNally, A.P.; Andersson, E.; Persson, A. Assimilation of TOVS radiance information through one-dimensional variational analysis. Q. J. R. Meteorol. Soc. 1993, 119, 1427–1463. [Google Scholar] [CrossRef]
  15. Chen, X.; Wang, L.; Niu, Z.; Zhang, M.; Li, C.; Li, J. The effects of projected climate change and extreme climate on maize and rice in the Yangtze River Basin, China. Agric. For. Meteorol. 2020, 282–283, 107867. [Google Scholar] [CrossRef]
  16. Magang, D.S.; Ojara, M.A.; Yunsheng, L.; King, P.H. Future climate projection across Tanzania under CMIP6 with high—Resolution regional climate model. Sci. Rep. 2024, 14, 1–21. [Google Scholar] [CrossRef]
  17. Do, H.X.; Le, T.H.; Le, M.H.; Nguyen, D.L.T.; Do, N.C. Future Changes in Hydro-Climatic Extremes across Vietnam: Evidence from a Semi-Distributed Hydrological Model Forced by Downscaled CMIP6 Climate Data. Water 2024, 16, 674. [Google Scholar] [CrossRef]
  18. Arfasa, G.F.; Sekyere, E.O.; Doke, D.A. Temperature and precipitation trend analysis using the CMIP6 model in the Upper East region of Ghana. All Earth 2024, 36, 1–14. [Google Scholar] [CrossRef]
  19. Gebisa, B.T.; Dibaba, W.T.; Kabeta, A. Evaluation of historical CMIP6 model simulations and future climate change projections in the Baro River Basin. J. Water Clim. Chang. 2023, 14, 2680–2705. [Google Scholar] [CrossRef]
  20. Gidden, M.J.; Riahi, K.; Smith, S.J.; Fujimori, S.; Luderer, G.; Kriegler, E.; Van Vuuren, D.P.; Van Den Berg, M.; Feng, L.; Klein, D.; et al. Global emissions pathways under different socioeconomic scenarios for use in CMIP6: A dataset of harmonized emissions trajectories through the end of the century. Geosci. Model Dev. 2019, 12, 1443–1475. [Google Scholar] [CrossRef]
  21. Pörtner, H.O.; Roberts, D.C.; Masson-Delmotte, V.; Zhai, P.; Tignor, M.; Poloczanska, E.; Mintenbeck, K.; Alegría, A.; Nicolai, M.; Okem, A.; et al. The Ocean and Cryosphere in a Changing Climate: Special Report of the Intergovernmental Panel on Climate Change; Cambridge University Press (CUP): Cambridge, UK, 2022; ISBN 9781009157964. [Google Scholar]
  22. Fan, X.; Duan, Q.; Shen, C.; Wu, Y.; Xing, C. Evaluation of historical CMIP6 model simulations and future projections of temperature over the Pan-Third Pole region. Environ. Sci. Pollut. Res. 2022, 29, 26214–26229. [Google Scholar] [CrossRef] [PubMed]
  23. Li, X.; Tan, L.; Li, Y.; Qi, J.; Feng, P.; Li, B.; Li Liu, D.; Zhang, X.; Marek, G.W.; Zhang, Y.; et al. Effects of global climate change on the hydrological cycle and crop growth under heavily irrigated management—A comparison between CMIP5 and CMIP6. Comput. Electron. Agric. 2022, 202, 107408. [Google Scholar] [CrossRef]
  24. Ali, Z.; Iqbal, M.; Khan, I.U.; Masood, M.U.; Umer, M.; Lodhi, M.U.K.; Tariq, M.A.U.R. Hydrological response under CMIP6 climate projection in Astore River Basin, Pakistan. J. Mt. Sci. 2023, 20, 2263–2281. [Google Scholar] [CrossRef]
  25. de Souza Ferreira, G.W.; Reboita, M.S.; Ribeiro, J.G.M.; de Souza, C.A. Assessment of Precipitation and Hydrological Droughts in South America through Statistically Downscaled CMIP6 Projections. Climate 2023, 11, 166. [Google Scholar] [CrossRef]
  26. Andrade, C.; Fonseca, A.; Santos, J.A.; Bois, B.; Jones, G.V. Historic Changes and Future Projections in Köppen–Geiger Climate Classifications in Major Wine Regions Worldwide. Climate 2024, 12, 94. [Google Scholar] [CrossRef]
  27. Ideki, O.; Lupo, A.R. Evaluation of Bias-Corrected GCM CMIP6 Simulation of Sea Surface Temperature over the Gulf of Guinea. Climate 2024, 12, 19. [Google Scholar] [CrossRef]
  28. Anil, S.; Anand Raj, P.; Vema, V.K. Catchment response to climate change under CMIP6 scenarios: A case study of the Krishna River Basin. J. Water Clim. Chang. 2024, 15, 476–498. [Google Scholar] [CrossRef]
  29. Rettie, F.M.; Gayler, S.; Weber, T.K.D.; Tesfaye, K.; Streck, T. High-resolution CMIP6 climate projections for Ethiopia using the gridded statistical downscaling method. Sci. Data 2023, 10, 442. [Google Scholar] [CrossRef] [PubMed]
  30. Ougahi, J.H.; Cutler, M.E.J.; Cook, S.J. Modelling climate change impact on water resources of the Upper Indus Basin. J. Water Clim. Chang. 2022, 13, 482–504. [Google Scholar] [CrossRef]
  31. Alaminie, A.A.; Tilahun, S.A.; Legesse, S.A.; Zimale, F.A.; Tarkegn, G.B.; Jury, M.R. Scenarios for the UBNB (Abay), Ethiopia. Water 2021, 13, 2110. [Google Scholar] [CrossRef]
  32. Feyissa, T.A.; Demissie, T.A.; Saathoff, F.; Gebissa, A. Evaluation of General Circulation Models CMIP6 Performance and Future Climate Change over the Omo River Basin, Ethiopia. Sustainability 2023, 15, 6507. [Google Scholar] [CrossRef]
  33. Climate, S.; Outputs, M.; Balcha, Y.A.; Malcherek, A.; Alamirew, T. Understanding Future Climate in the Upper Awash Basin. Climate 2022, 10, 185. [Google Scholar] [CrossRef]
  34. Berhanu, D.; Alamirew, T.; Taye, M.T.; Tibebe, D.; Gebrehiwot, S.; Zeleke, G. Evaluation of CMIP6 models in reproducing observed rainfall over Ethiopia. J. Water Clim. Chang. 2023, 14, 2583–2605. [Google Scholar] [CrossRef]
  35. Mosello, B.; Calow, R.; Tucker, J.; Parker, H.; Alamirew, T.; Kebede, S.; Alemseged, T.; Gudina, A. Building Adaptive Water Resources Management in Ethiopia; ODI: London, UK, 2015; Available online: https://odi.org/en/publications/building-adaptive-water-resources-management-in-ethiopia/ (accessed on 8 September 2024).
  36. Costa, D.; Zhang, H.; Levison, J. Impacts of climate change on groundwater in the Great Lakes Basin: A review. J. Great Lakes Res. 2021, 47, 1613–1625. [Google Scholar] [CrossRef]
  37. Silva, R.P.; Dayawansa, N.D.K.; Ratnasiri, M.D. A Comparison of methods used in estimating missing rainfall data. Univ. Perad. 2007, 3, 101–108. [Google Scholar] [CrossRef]
  38. Li, L.; Revesz, P. Interpolation methods for spatio-temporal geographic data. Comput. Environ. Urban Syst. 2004, 28, 201–227. [Google Scholar] [CrossRef]
  39. Tran, A.P.; Rungee, J.; Faybishenko, B.; Dafflon, B.; Hubbard, S.S. Assessment of spatiotemporal variability of evapotranspiration and its governing factors in a mountainous watershed. Water 2019, 11, 243. [Google Scholar] [CrossRef]
  40. Lang, D.; Zheng, J.; Shi, J.; Liao, F.; Ma, X.; Wang, W.; Chen, X.; Zhang, M. A comparative study of potential evapotranspiration estimation by eight methods with FAO Penman–Monteith method in southwestern China. Water 2017, 9, 734. [Google Scholar] [CrossRef]
  41. Berti, A.; Tardivo, G.; Chiaudani, A.; Rech, F.; Borin, M. Assessing reference evapotranspiration by the Hargreaves method in. Agric. Water Manag. 2014, 140, 20–25. [Google Scholar] [CrossRef]
  42. Slavková, J.; Gera, M.; Nikolova, N.; Siman, C. Standardized Precipitation and Evapotranspiration Index Approach for Drought Assessment in Slovakia—Statistical Evaluation of Different Calculations. Atmosphere 2023, 14, 1464. [Google Scholar] [CrossRef]
  43. Package, T.; Gudmundsson, A.L. Package ‘Qmap’. 2016. Available online: https://cran.r-project.org/web/packages/qmap/index.html (accessed on 8 September 2024).
  44. Yimer, S.M.; Bouanani, A.; Kumar, N.; Tischbein, B.; Borgemeister, C. Assessment of Climate Models Performance and Associated Uncertainties in Rainfall Projection from CORDEX over the Eastern Nile Basin, Ethiopia. Climate 2022, 10, 95. [Google Scholar] [CrossRef]
  45. Hu, Z.; Liu, S.; Zhong, G.; Lin, H.; Zhou, Z. Modified Mann-Kendall trend test for hydrological time series under the scaling hypothesis and its application. Hydrol. Sci. J. 2020, 65, 2419–2438. [Google Scholar] [CrossRef]
  46. Mohita Anand, S.; Jai Bhagwan, S. Use of Probability Distribution in Rainfall Analysis. N. Y. Sci. J. 2010, 3, 40–49. [Google Scholar]
  47. Cong, R.G.; Brady, M. The interdependence between rainfall and temperature: Copula analyses. Sci. World J. 2012, 2012, 405675. [Google Scholar] [CrossRef] [PubMed]
  48. Rigby, R.A.; Stasinopoulos, D.M.; Lane, P.W. Generalized additive models for location, scale and shape. J. R. Stat. Soc. Ser. C Appl. Stat. 2005, 54, 507–554. [Google Scholar] [CrossRef]
  49. Martel, J.L.; Brissette, F.; Troin, M.; Arsenault, R.; Chen, J.; Su, T.; Lucas-Picher, P. CMIP5 and CMIP6 Model Projection Comparison for Hydrological Impacts Over North America. Geophys. Res. Lett. 2022, 49, e2022GL098364. [Google Scholar] [CrossRef]
  50. Forster, P.M.; Maycock, A.C.; McKenna, C.M.; Smith, C.J. Latest climate models confirm need for urgent mitigation. Nat. Clim. Chang. 2020, 10, 7–10. [Google Scholar] [CrossRef]
Figure 1. Location map of Kobo Valley.
Figure 1. Location map of Kobo Valley.
Climate 12 00159 g001
Figure 2. Comparison between observed, satellite, and reanalysis products for precipitation (in mm).
Figure 2. Comparison between observed, satellite, and reanalysis products for precipitation (in mm).
Climate 12 00159 g002
Figure 3. Comparison between the observed and reanalysis products for temperature (°C).
Figure 3. Comparison between the observed and reanalysis products for temperature (°C).
Climate 12 00159 g003aClimate 12 00159 g003bClimate 12 00159 g003c
Figure 4. Comparison between the observed and reanalysis products for PET (in mm).
Figure 4. Comparison between the observed and reanalysis products for PET (in mm).
Climate 12 00159 g004aClimate 12 00159 g004b
Figure 5. Spatial distribution of climate variables in Kobo Valley.
Figure 5. Spatial distribution of climate variables in Kobo Valley.
Climate 12 00159 g005aClimate 12 00159 g005b
Figure 6. Projected precipitation under middle and worst-case scenarios.
Figure 6. Projected precipitation under middle and worst-case scenarios.
Climate 12 00159 g006
Figure 7. Projected maximum temperature under the middle and worst-case scenarios.
Figure 7. Projected maximum temperature under the middle and worst-case scenarios.
Climate 12 00159 g007
Figure 8. Projected minimum temperature under the middle and worst-case scenarios.
Figure 8. Projected minimum temperature under the middle and worst-case scenarios.
Climate 12 00159 g008aClimate 12 00159 g008b
Figure 9. Projected PET under the middle and worst-case scenarios.
Figure 9. Projected PET under the middle and worst-case scenarios.
Climate 12 00159 g009aClimate 12 00159 g009b
Table 1. Available meteorological stations in Kobo Valley.
Table 1. Available meteorological stations in Kobo Valley.
NoName of the StationLocation (WGS)
LatitudeLongitudePrecipitation Temperature
Group 1
1Alamata12.4239.71****
2Waja12.3039.60****
3Korem12.5139.51****
4Lalibela 12.0439.04****
5Sirinka11.7539.61****
Group 2
6Kobo12.1339.63****
7Zobel12.1739.75****
8Kulmesk 11.9439.20**
Group 3
9Dilb11.9639.43**
10Sanka 11.8939.48****
11Hara 12.6741.42****
12Robit12.0139.62**
** Selected for both variables.
Table 2. Data sources of satellite, reanalysis, and merged products.
Table 2. Data sources of satellite, reanalysis, and merged products.
No Name Data ProductResolution Source
Precipitation
1CHIRPSSatellite 0.25° × 0.25°NOAA
2ERA5Reanalysis 0.25° × 0.25°ECMWF
3MERRA-2Reanalysis0.5° × 0.625°NASA
4JRA-55-mdl-isoReanalysis0.5625° × 0.5625°JMA
5CPCMerged 0.25° × 0.25°NOAA
Temperature (Tmax, Tmin)
1ERA5Reanalysis0.25° × 0.25°ECMWF
2MERRA-2Reanalysis0.5° × 0.625°NASA
320CRv3Reanalysis1° × 1°NOAA
Evapotranspiration
1ERA5Reanalysis0.25° × 0.25°ECMWF
Table 3. Selected CMIP6 climate model products.
Table 3. Selected CMIP6 climate model products.
No CMIP6 ModelResolution Country
1ACCESS-ESM1-5 1.875°× 1.25° Australia
2BCC-ESM1 (**)1.1° × 1.1°China
3CAMS-CSM1-01.1° × 1.1°China
4CanESM52.8° × 2.8°Canada
5CAS-ESM2-0 (**)1° × 1°China
6CESM2-WACCM1.3° × 0.9°USA
7CMCC-ESM2 (**) 0.9° × 1.25° Italy
8FIO-ESM-2-0 (**) 0.9° × 1.25° China
9MIROC61.4° × 1.4°Japan
10MRI-ESM2-0 (**)1.1° × 1.1°Japan
11NorESM2-LM 1.9° × 2.5° Norway
12TaiESM1 0.9° × 1.25 ° Taiwan
** Selected CMIP6 models for both variables.
Table 4. Distribution type of the observed, satellite, reanalysis, and merged products.
Table 4. Distribution type of the observed, satellite, reanalysis, and merged products.
DatasetsAverage MonthlyJJASMAMAnnual
Precipitation
AICDTAICDTAICDTAICDT
Observed 226.01NO372.61NO350.56RG375.12NO
CHIRPS 220.49SEP2374.79PE326.68RG369.58SEP2
ERA5255.42SEP2361.03SEP3370.07NO403.44SEP2
MERRA-2286.94LO417.73RG409.13RG436.03LO
JAR-55-mdl-iso277.42SN2384.14RG376.94RG426.53SN2
Merged (CPC)229.62NO362.63NO339.98RG378.72NO
Evapotranspiration
Observed 236.01NO368.61NO358.56RG379.12NO
ERA5254.18NO312.45NO 369.56SEP3403.28NO
AIC—Akaike Information Criteria, DT—distribution type, NO—Normal, LO—Logistic distribution, SN2—Skew Normal Type 2, SEP2 and SEP3—Skew Power exponential 1-4, RG—Reverse Gumbel, PE—Power Exponential distributions. The shaded color indicates that the data sources have a similar distribution type to the observed data.
Table 5. Trend test results of the observed, satellite, reanalysis, and merged products.
Table 5. Trend test results of the observed, satellite, reanalysis, and merged products.
DatasetAverage MonthlyJJASMAMAnnual
Precipitation
TTRDirTTRDirTTRDirTTRDir
Observed NS-NS+NS-NS-
CHIRPS NS+NS+NS-NS+
ERA5SDNS+SDSD
MERRA-21NS-NS+SDNS-
JAR-55-md l-isoSDSDSDSD
Merged (CPC)NS-NS+NS-NS-
Maximum Temperature
Observed SISISISI
ERA5NS+SISISI
MERRA-2SISISISI
20CRv3SISISISI
Minimum Temperature
Observed SISISISI
ERA5SISISISI
MERRA-2SISISISI
20CRv3SISINS+SI
Evapotranspiration
Observed SISSSSSS
ERA5SISSSSSS
TTR—trend test result, Dir—direction, S—significant, NS—non-significant, I—increasing, D—decreasing, + and – represent the sign.
Table 6. Probability distributions of observed and CMIP6 products.
Table 6. Probability distributions of observed and CMIP6 products.
Parameter Average MonthlyJJASMAMAnnual
AICDTAICDTAICDTAICDT
Precipitation
Observed 226.01NO372.61NO350.56RG375.12NO
ACCESS-ESM1-5245LO368.69RG323.79SEP3394.64LO
BCC-ESM1195.07RG336.31RG309.1RG344.17RG
CAMS-CSM1-0236.61LO386.66RG274.86SN2385.70LO
CanESM5198.03SN2324.01ST2316.99SN2347.12SN2
CAS-ESM2-0300.99SEP3405.43SEP4425.80SN2450.09SEP3
CESM2-WACCM228.04NO334.50SEP3363.33RG377.14NO
CMCC-ESM2218.37RG356.51SN2300.02SN2367.47RG
FIO-ESM-2-0212.07NO325.88LO328.30RG361.17NO
MIROC6260.69LO386.23NO365.01RG409.79LO
MRI-ESM2-0264.18NO382.45NO 389.56SEP3413.28NO
NorESM2-LM226.41SN2338.30RG356.48SN2375.50SN2
TaiESM1225.76GU381.12NO 316.49RG374.85GU
Maximum Temperature
Observed 67.44SHASH55.41NO78.19SHASH49.74SEP2
CMCC-ESM257.80GU98.29GU76.85SEP263.42GU
BCC-ESM154.75SN282.04GU68.89NET32.45SEP3
MRI-ESM2-0102.55SEP379.39NET129.3RG82.77NO
CAS-ESM2-055.71RG66.93RG83.78NO41.10LO
FIO-ESM-2-070.56GU74.67NO88.46GU49.46NO
Minimum Temperature
Observed −12.99SEP228.37LO46.64GU27.92LO
CMCC-ESM273.59LO71.91NO85.28SEP264.45LO
BCC-ESM151.69NO45.17NO74.41NO42.50NO
MRI-ESM2-040.35NO11.94GU29.32LO−0.36SN2
CAS-ESM2-036.35NO25.73NO49.65NO17.42NO
FIO-ESM-2-056.56PE34.39SEP368.57GU48.75GU
DT—distribution type, GU—Gumbel, SHASH—Sinh–Arcsinh, NET—Normal Exponential t, ST—Skew t distributions, NO—Normal, LO—Logistic distribution, SN2—Skew-normal, SEP2 and SEP3—Skew Power exponential 1-4, RG—Reverse Gumbel, PE—Power Exponential distributions. The shaded color indicates that the CMIP6 model results have similar distributions to the observed datasets.
Table 7. Trend test of the observed and GCM outputs.
Table 7. Trend test of the observed and GCM outputs.
ParameterAverage MonthlyJJASMAMAnnual
TTRDirTTRDirTTRDirTTRDir
Precipitation
Observed NS-NS+NS-NS-
ACCESS-ESM1-5NS-NS-NS-NS-
BCC-ESM1NS+NS+NS+NS+
CAMS-CSM1-0NS-NS-SINS-
CanESM5NS-NS+NS-NS-
CAS-ESM2-0NS+NS+NS-NS+
CESM2-WACCMNS+NS+NS-NS+
CMCC-ESM2NS-NS-NS+NS-
FIO-ESM-2-0NS+NS+NS+NS+
MIROC6NS+NS+NS+NS+
MRI-ESM2-0NS+NS+NS-NS+
NorESM2-LMNS+NS+NS+NS+
TaiESM1NS+NS+NS-NS+
Maximum Temperature
Observed SISISISI
CMCC-ESM2NS+NS+NS+NS+
BCC-ESM1NS+NS+NS+NS+
MRI-ESM2-0NS-NS-NS+NS+
CAS-ESM2-0SISISISI
FIO-ESM-2-0NS+NS+NS+NS+
Minimum Temperature
Observed SISISISI
CMCC-ESM2SISINS+SI
BCC-ESM1NS+NS+SISI
MRI-ESM2-0SISINS+SI
CAS-ESM2-0SISISISI
FIO-ESM-2-0SISISISI
NB: TTR—trend test result, Dir—direction, S—significant, NS—non-significant, I—increasing, + and – represent the sign.
Table 8. The model performance results.
Table 8. The model performance results.
ModelsMonthlyJJASMAMAnnual
RRMMARRMMARRMMARRMMA
Precipitation
ACCESS-ESM1-5104410336331144
BCC-ESM13883771087388
CAMS-CSM1-081212552781012
CanESM5910104101015591010
CAS-ESM2-021212212124121221212
CESM2-WACCM1771188512177
CMCC-ESM2766666799866
FIO-ESM-2-012337448211233
MIROC6511118111111111171111
MRI-ESM2-045512291010555
NorESM2-LM11999991266499
TaiESM1621511344621
Maximum Temperature
CMCC-ESM2211111333322
BCC-ESM1333233222133
MRI-ESM2-0544444544544
CAS-ESM2-0155355155255
FIO-ESM-2-0422522411411
Minimum Temperature
CMCC-ESM2255355555355
BCC-ESM1511522311511
MRI-ESM2-0322111422422
CAS-ESM2-0144244144144
FIO-ESM-2-0433433233233
R is correlation, RM is the root mean square error, and MA is the absolute mean error. The integer numbers in the table represent the ranks of each model.
Table 9. Overall ranks of statistical tests.
Table 9. Overall ranks of statistical tests.
CMIP6 ModelRRMSEMAESum RankTotal Rank
Precipitation
ACCESS-ESM1-5371414655
BCC-ESM1193130807
CAMS-CSM1-0321417633
CanESM5233535939
CAS-ESM2-010484810611
CESM2-WACCM182324655
CMCC-ESM2282727828
FIO-ESM-2-0391211622
MIROC631444411912
MRI-ESM2-0192222633
NorESM2-LM36333310210
TaiESM12097361
Maximum Temperature
CMCC-ESM2977231
BCC-ESM181111303
MRI-ESM2-0191616515
CAS-ESM2-072020474
FIO-ESM-2-01766292
Minimum Temperature
CMCC-ESM2132020535
BCC-ESM11855282
MRI-ESM2-01277261
CAS-ESM2-051616374
FIO-ESM-2-0121212363
Table 10. Results of the overall model performance measures.
Table 10. Results of the overall model performance measures.
Model PDFMPMTrendSum RankTotal Rank
Precipitation
ACCESS-ESM1-5752146
BCC-ESM1672157
CAMS-CSM1-0732125
CanESM5791178
CAS-ESM2-071122012
CESM2-WACCM15284
CMCC-ESM2782178
FIO-ESM-2-012251
MIROC641221810
MRI-ESM2-013262
NorESM2-LM71021911
TaiESM141273
Maximum Temperature
CMCC-ESM221251
BCC-ESM123273
MRI-ESM2-025295
CAS-ESM2-024173
FIO-ESM-2-012251
Minimum Temperature
CMCC-ESM215172
BCC-ESM132384
MRI-ESM2-031372
CAS-ESM2-0343105
FIO-ESM-2-013151
Table 11. Ranks for temperature dataset.
Table 11. Ranks for temperature dataset.
Model TmaxTminSum Rank Final Rank
CMCC-ESM21232
BCC-ESM13473
MRI-ESM2-05273
CAS-ESM2-03585
FIO-ESM-2-01121
Disclaimer/Publisher’s Note: The statements, opinions and data contained in all publications are solely those of the individual author(s) and contributor(s) and not of MDPI and/or the editor(s). MDPI and/or the editor(s) disclaim responsibility for any injury to people or property resulting from any ideas, methods, instructions or products referred to in the content.

Share and Cite

MDPI and ACS Style

Tesfaw, M.; Dessie, M.; Walraevens, K.; Hermans, T.; Nigate, F.; Assefa, T.; Shitu, K. Quantifying Climate Change Variability for the Better Management of Water Resources: The Case of Kobo Valley, Danakil Basin, Ethiopia. Climate 2024, 12, 159. https://doi.org/10.3390/cli12100159

AMA Style

Tesfaw M, Dessie M, Walraevens K, Hermans T, Nigate F, Assefa T, Shitu K. Quantifying Climate Change Variability for the Better Management of Water Resources: The Case of Kobo Valley, Danakil Basin, Ethiopia. Climate. 2024; 12(10):159. https://doi.org/10.3390/cli12100159

Chicago/Turabian Style

Tesfaw, Mengesha, Mekete Dessie, Kristine Walraevens, Thomas Hermans, Fenta Nigate, Tewodros Assefa, and Kasye Shitu. 2024. "Quantifying Climate Change Variability for the Better Management of Water Resources: The Case of Kobo Valley, Danakil Basin, Ethiopia" Climate 12, no. 10: 159. https://doi.org/10.3390/cli12100159

APA Style

Tesfaw, M., Dessie, M., Walraevens, K., Hermans, T., Nigate, F., Assefa, T., & Shitu, K. (2024). Quantifying Climate Change Variability for the Better Management of Water Resources: The Case of Kobo Valley, Danakil Basin, Ethiopia. Climate, 12(10), 159. https://doi.org/10.3390/cli12100159

Note that from the first issue of 2016, this journal uses article numbers instead of page numbers. See further details here.

Article Metrics

Back to TopTop