Greenhouse gases affect climate system disturbances. This research employs sixth generation CMIP6 models in the SSP5.85 scenario and extends the use of the neural wavelet network to predict precipitation variations for the future (2025–2065). Kendall's trend test is used to assess changes in precipitation trends for observed and projected periods. An analysis of variance (ANOVA) validates models under SSP5.85 by comparing observed precipitation with model predictions. A multi-layer perceptron neural network assesses climate change's impact on future precipitation. Findings indicate future precipitation is projected to fluctuate from −0.146 to over −2.127 mm compared to the baseline period. The observed period showed a significant 3.37% monthly precipitation decrease within the watershed. The CanESM5 model predicts a 3.916 reduction in precipitation with 95% confidence, while INM-CM4-8 and MRI-ESM2-0 models are less certain. The minor difference between CanESM5's predicted (−5.91) and observed (−5.05) precipitation suggests a slight variance. On the other hand, the wavelet neural network (WNN) model predicts that precipitation in this region will increase in the future. In general, this study predicts a decrease in precipitation for the Aji-Chay watershed in Iran over the next decade, could lead to serious issues like lower crop yields, rising food prices, and even droughts.

  • This research stands as a beacon of progress in climate science. Through its use of cutting-edge modeling, innovative methodology, statistical rigor, and policy-relevant conclusions, it thoroughly investigates the critical issue of climate change's impact on rainfall and its broader implications for water resources.

The climate system has been disturbed by greenhouse gas-induced climate shifts, emphasizing the need to investigate how climate change affects hydrological elements, particularly precipitation. To forecast forthcoming rainfall changes crucial for water resources, this study has employed CMIP6 models and wavelet neural network (WNN) to predict rainfall variations in the Aji-Chay watershed from 2065 to 2025. Climate change is causing concerning alterations in precipitation patterns, which are vital components of the Earth's hydrological cycle and essential for human activities like agriculture (Sun et al. 2006). These changes, including increased frequency and intensity of droughts, disrupt the intricate link between precipitation intensity and frequency. This disruption further impacts human activities, particularly in vulnerable regions like the Aji-Chay watershed. Climate change is expected to exacerbate these problems in the Aji-Chay watershed, making analysis and prediction of future precipitation trends crucial for informed decision-making. Climate change has led to observable changes in both the quantity and patterns of rainfall. The exacerbation of drought due to climate change is a global phenomenon. It is predicted that this trend will lead to substantial alterations in climate, spatio-temporal patterns, and hydrometeorological factors, such as precipitation. Therefore, the evaluation of global climate models (GCMs) and the detection of uncertainties and biases in the simulation of climate models are important steps toward understanding their application and potential for climate impact assessment studies (Raghavan et al. 2018; Zazulie et al. 2018; Rivera & Arnould 2019). The exacerbation of drought due to climate change is a global phenomenon. It is predicted that this trend will lead to substantial alterations in climate, spatio-temporal patterns, and hydrometeorological factors, such as precipitation. Accurate climate models are vital for understanding the impact of climate change on precipitation. Accurate climate models are vital for understanding the impact of climate change on precipitation. Previous studies have explored these impacts, however, limitations exist due to the use of older models and a lack of investigation under specific scenarios. Hessar & Ghazavi (2015) analyzed time series models and artificial neural networks in the field of climate scenarios. Yaghoubi et al. 2017 conducted a research to evaluate the effects of climate change between 2016 and 2099 on the runoff of the Gavharud watershed, considering the uncertainty. They analyzed meteorological data generated by the Hadley Center Coupled Model, version 3 (HadCM3) and the general circulation model under the A2 climate change scenario. Pour (2016) examined the effects of climate change on temperature, precipitation, and variations in the flow of the Qareh Soo River in the Qareh Soo watershed located in the Kermanshah province, one of the vital sub-basins of the Karkeh watershed.

Nazaripouya et al. (2016) using the comparison of HadCM3 model and Integrated Precipitation and Climate Model version 4 (IPCM4) under scenarios A2 and B1, the uncertainty of the effects of climate change on temperature, precipitation and runoff in the Ekbatan Dam watershed for the period of 2045–2065 evaluated. Jahanbakhsh Asl et al. (2016) utilized the statistical model of the Long Ashton Research Station–Climate Generator (LARS-WG) to examine the impacts of climate change on temperature and precipitation in the Urmia-Chai watershed under three scenarios (A1, B1, A1B) for the period 2011–2030. Azizabadi Farahani et al. (2017) initially estimated precipitation and temperature variables from 1983 to 2012 and Canadian Earth System Model, version 2 (CanESM2) model outputs under three Representative Concentration Pathway (RCP) scenarios (2.6, 4.5, 8.5) for the period 2019–2048. They used drought indices and a conditional return period approach. The study revealed diverse changes in monthly precipitation and temperature variables across different scenarios in the future period. For a drought event with a severity level of 10 lasting up to 6 months, the return period changed from 5 years in the base period to 21, 17, and 4 years under RCP 2.6, 4.5, and 8.5 scenarios, respectively. Mansouri et al. (2018) investigated inflow variations to the Karun 4 Dam for 2050–2021 using HadCM3 model outputs (B1, A2) from the fourth report and combined outputs (RCP 2.6, RCP 8.5) from the fifth report. Artificial neural networks were used for runoff estimation. Precipitation in studied stations increased by 15% (B1) and 5% (RCP 2.6) while decreasing by 8% (A2) and 6% (RCP 8.5) annually. Sadeghi & Deen Pjooh (2019) employed statistical downscaling with LARS-WG6 to predict precipitation in the Tabriz region for three future periods (2021–2040, 2041–2060, and 2061–2080) using RCP4.5 and RCP8.5 scenarios with the Max Planck Institute – Earth System Model, version MR (MPI-ESM-MR) model. The findings indicated an increase in winter precipitation for all periods in both scenarios, while spring and autumn precipitation is projected to decrease under the RCP8.5 scenario. Omidvar et al. (2019) assessed the simulation of climate change effects on the behavior of precipitation and temperature at the Synoptic Station of Sirjan in Kerman Province. Initially, the performance of an artificial neural network model for downscaling climate variables predicted by the CanESM2 general circulation model was tested. Salahi et al. (2019) conducted a study to examine the impact of climate change on the planting time and the growth period of rainfed wheat in the Ardabil region. To achieve this, they first assessed the occurrence of climate change in the region using statistical downscaling. They used output data from the CanESM2 model and the Statistical Downscaling Model (SDSM) software under the RCP 4.5 scenario. They simulated maximum temperature, minimum temperature, and precipitation parameters for the future period (2011–2040). Senatore et al. (2022) assessed the hydrological impact of climate change under RCP scenarios by combining multiple global and regional climate models and making corrections. In this study, they investigated model uncertainties using analysis of variance (ANOVA). Few studies have been conducted on the impacts of climate change on various sectors of the economy in northwest Iran, particularly in the Aji-Chay watershed, utilizing the latest CMIP6 models and updated Shared Socioeconomic Pathways (SSP) scenarios from the Intergovernmental Panel on Climate Change (IPCC). Comprehensive studies based on the latest data are crucial to fully understand the impacts of climate change and to develop informed long-term policies in areas such as agriculture, water resources management, and industry. Due to the location of the Aji-Chay watershed in a semi-arid and arid region, as well as the continuous exploitation of groundwater in this area, conducting comprehensive research is essential for climate change. The main objective of this study is to evaluate the changes in precipitation patterns under the influence of climate change using CMIP6 models and the SSP5.85 scenario. The Aji-Chay watershed encounters various challenges categorized into water resource issues (such as decreased rainfall, drought, water quality decline, and overexploitation of groundwater), agricultural concerns (like outdated methods and reduced efficiency in irrigation), pasture degradation, air pollution, among others. Addressing these challenges necessitates thorough planning and collaboration among all pertinent institutions. The innovation of this research is the use of the ANOVA method to demonstrate the uncertainty of rainfall prediction models. In most previous studies, traditional methods such as mean comparison or root mean square error (RMSE) have been used to evaluate the uncertainty of models, the analysis was conducted using the neural wavelet network method to examine the data from 2025 to 2065. The analysis was carried out using the neural wavelet network method to examine data from 2025 to 2065. To conduct this study, the most suitable model was selected to estimate precipitation variables using a variety of time series models. Historical rainfall data from 1961 to 2010 collected from synoptic stations in the Urmia, the Tabriz, and the Khoi was used to predict variable values for the following 18 years (2011–2029). This can help researchers and policymakers choose the appropriate model for rainfall prediction.

The Aji-Chay watershed, located in northwestern Iran, is one of the most important sub-basins of Lake Urmia. It is situated geographically between latitudes 37°42′–38°30′ North and longitudes 45°40′–47°53′ East. In this research, data from the Tabriz synoptic station, which is one of the stations within the Aji-Chay watershed, were used. This watershed originates from the southern and southwestern slopes of the Sabalan Mountains at an altitude of about 3,400 meters, approximately 33km from Sarab County, and, after passing north of Tabriz, it terminates in the west of Azarshahr at an altitude of 1,370m, where it flows into Lake Urmia. The area of this watershed is approximately 12,790km2 (Figure 1).
Figure 1

Location of Aji-Chay area of Tabriz.

Figure 1

Location of Aji-Chay area of Tabriz.

Close modal

This study utilized two sets of data. The initial set comprises daily precipitation records for the Aji-Chay watershed spanning from 1981 to 2021 AD (at least 40 years). These data served as foundational/historical information for assessment and modeling, sourced from the National Meteorological Organization. The second category includes climate scenario data from the Coupled Model Intercomparison Project Phase 6 (CMIP6) GCMs, which have been freely accessible to researchers since 2022 via the https://climate-scenarios.canada.caM website. In this study, these data have been evaluated as prediction data from 2022 to 2065 AD. The reason for selecting the SSP5-8.5 scenario in this study is the highest greenhouse gas emissions and increased utilization of fossil fuels, along with the adoption of resource-intensive energy technologies worldwide. In this research, historical predictions of the sixth assessment report models are compared with reconstructed data in a similar period, and models with acceptable statistical performance are considered for predicting precipitation changes in the study area. The model data used in this research for the study region have horizontal resolutions of 100 and 250km. Statistical downscaling techniques are applied to the chosen models. The study is divided into two time frames: a historical period (1975–2014) and a future period (2025–2065) focusing on the precipitation parameter. Furthermore, the Kendall rank correlation test is used to determine the concordance of observed and predicted precipitation trends. In addition, ANOVA is used for verifying the accuracy between observed precipitation and the models under the SSP5-8.5 scenario, and this test is conducted using the MATLAB software environment.

Climate models and emission scenarios

The ensemble of CMIP6 climate models, a collaborative effort across multiple organizations to standardize general circulation model design and model distribution, has become a pivotal component in guiding global-scale climate research. CMIP6's primary objective is to address three fundamental questions: how Earth's structure responds to various influences, the origins and consequences of quantifiable changes in climate models, and the uncertainty associated with scenarios. Notably, CMIP6 models feature an improved number of vertical layers compared to CMIP5 models, resulting in more precise stratosphere simulations. Moreover, CMIP6 encompasses a significantly broader range of future scenarios. New scenarios introduced in CMIP6 include SSP1.1-9, SSP4-3.4, and SSP3-7.0, with updates to SSP1-2.6, SSP2-4.5, SSP4-6.0, and SSP5-8.5. The SSPs are designed to offer a comprehensive analysis of future climate conditions, vulnerabilities, impacts, as well as strategies for adaptation and mitigation. These pathways were developed by the scientific community. The SSP5.85 scenario represents a high greenhouse gas emission scenario, indicating the maximum levels of emissions (Figure 2). This scenario predicts that greenhouse gas emissions will surpass current levels by more than tenfold by the year 2100. This substantial increase in emissions is expected to result in a significant global temperature rise and noteworthy changes in weather patterns.
Figure 2

Common economic-social scenarios, and the corresponding concentration pathways for each scenario (Ahmadi et al. 2023 : 81).

Figure 2

Common economic-social scenarios, and the corresponding concentration pathways for each scenario (Ahmadi et al. 2023 : 81).

Close modal

In this study, data from three CMIP6 climate models were initially acquired from the database at https://climate-scenarios.canada.ca (see Table 1). Subsequently, relevant information and model characteristics were extracted using ArcGIS 10.8 and are briefly summarized in Table 2. It is important to note that this research adopts a pessimistic scenario.

Table 1

Characteristics of climate general circulation models (GCMs) for climate change (https://esgf-node.llnl.gov/search/cmip6)

Emission scenarioSpatial accuracyResearch institute developing modelsModel name
SSP5-8.5 (Canada) 2.8 × 2.8 Commonwealth Scientific and Industrial Research Organization (CSIR), Canadian CanESM5 
SSP5-8.5 (Russia) 2 × 1.5 The model was run by the Institute for Numerical Mathematics, Russian Academy of Science, Moscow 119,991, Russia (INM) in native nominal resolutions INM-CM4-8 
SSP5-8.5 (Japan) 0.3 × 0.5 Version 2.2.0.0 Japan Meteorological Agency (JMA) merged satellite and in situ Data Global Daily SST MRI-ESM2-0 
Emission scenarioSpatial accuracyResearch institute developing modelsModel name
SSP5-8.5 (Canada) 2.8 × 2.8 Commonwealth Scientific and Industrial Research Organization (CSIR), Canadian CanESM5 
SSP5-8.5 (Russia) 2 × 1.5 The model was run by the Institute for Numerical Mathematics, Russian Academy of Science, Moscow 119,991, Russia (INM) in native nominal resolutions INM-CM4-8 
SSP5-8.5 (Japan) 0.3 × 0.5 Version 2.2.0.0 Japan Meteorological Agency (JMA) merged satellite and in situ Data Global Daily SST MRI-ESM2-0 
Table 2

Statistical characteristics of CMIP6 climate change data

1° × 1° curvilinear grid Data type 
Regular geographic longitude–latitude grid Design 
varies among models Horizontal coverage 
Single levels, pressure levels (1 to 1,000 hectopascals) Vertical coverage 
1,850–2,300 (shorter for some scenarios) Temporal coverage 
Monthly, daily, fixed (no temporal resolution) Temporal resolution 
NetCDF4 File format 
Climate and forecast (CF) Conventions 
The latest data versions are provided up to the year 2022. Versions 
1° × 1° curvilinear grid Data type 
Regular geographic longitude–latitude grid Design 
varies among models Horizontal coverage 
Single levels, pressure levels (1 to 1,000 hectopascals) Vertical coverage 
1,850–2,300 (shorter for some scenarios) Temporal coverage 
Monthly, daily, fixed (no temporal resolution) Temporal resolution 
NetCDF4 File format 
Climate and forecast (CF) Conventions 
The latest data versions are provided up to the year 2022. Versions 

The criteria for selecting three models

INM-CM4-8 model (Institute for Numerical Mathematics)

The selection of this model is based on its Equilibrium Climate Sensitivity (ECS), which measures the Earth's warming response to a doubling of carbon dioxide (CO2) concentration in the atmosphere. ECS is a critical parameter in climatology, providing insights into how Earth reacts to changes in greenhouse gas concentrations (Gettelman et al. 2019: 46). The INM-CM4-8 model exhibits high sensitivity to ECS, with a range of ECS changes from 1.1 to 1.4. This range surpasses more than half of the ECS variation range observed in CMIP6 models (Tiedtke 1993: 3051). The model is characterized by a complex cloud system that includes various cloud types with distinct characteristics. The model's demonstration of ECS sensitivity to variations in cloud parameterization aids scientists in gaining a better understanding of the mechanisms governing cloud evolution (Volodin 2021: 5).

The Meteorological Research Institute Earth System Model version 2.0, (MRI-ESM2 model)

Overall, demonstrates a proficient ability to replicate global and regional precipitation patterns, encompassing areas with both intense rainfall and arid conditions (Reddy & Saravanan 2023: 47119). However, the simulation of intense and unforeseen rainfall continues to pose a challenge for all climate models, MRI-ESM2-0 included (Dione et al. 2023: 355).

CanESM5 model

The CanESM5 model is adept at simulating one of the essential climatic features, precipitation. This model is applied for forecasting climate patterns over the century and is also employed to create seasonal and decadal predictions. Serving as a predictive tool, it aids in formulating optimal strategies for water resource management and decisions related to watersheds (Swart et al. 2019: 4855).

The change factor (CF) method is a common approach for error correction, often used to reduce the discrepancies between GCM outputs and observational data (Chen et al. 2011; Ouyang et al. 2015). The procedure works by calculating the delta values for precipitation in each of the 12 months of the year. It involves dividing the average of each month in the future climate by the average of the corresponding month in the baseline climate (Equation (1)):
(1)

The provided formula is utilized for examining variations in precipitation over time. It serves as a tool for comparing precipitation levels between two distinct time periods, enabling the investigation of precipitation changes over the designated duration (Gallé & Katzenberger 2023 : 14). In this expression, At signifies the precipitation amount during a future time interval, while A(t1) denotes the precipitation value in the baseline period (t1).

Trend analysis using the non-parametric Mann–Kendall test

Governing equations

Trend analysis is conducted to examine the underlying trend in the time series of the studied variable since climate change can potentially alter the regime governing many hydrological variables (Sen 1968; Mohammadpour Khoie & Nasseri 2022). In this study, trend analysis is performed on both observational time series and the models under the SSP5.85 scenario.

The Mann–Kendall test is a non-parametric test used to determine the presence of a trend and was proposed by (Kendall & Stuart 1973). Since this method does not make assumptions about the distribution of input data, it has been widely used for detecting statistically significant positive or negative trends in hydrological and climatic variables (Gocic & Trajkovic 2013; Pirnia et al. 2019).

The steps for calculating the statistic of this test are as follows:

Calculating the difference between individual observations and applying the sign function to extract parameter S is as follows in the Equation (2):
(2)
where xi and xj are consecutive data values for years or months i and j, n number of serial data and sgnθ function Sign and θ difference of two values recorded in each of the variables under study are determined as follows becomes:
(3)
This formula subtracts negative values from positive values for all numbers. For large samples (N > 10), this test uses the normal distribution (Z-statistic). The mean and variance are obtained from Equation (4):
(4)
VAR(S) for calculating the Z-statistic are determined according to Equation (5):
(5)

The final stage involves hypothesis testing. The null hypothesis suggests the absence of a trend and its randomness, indicated by non-statistically significant Z. This null hypothesis is upheld when −Za/2 < Z < Za/2, with Za/2 values representing standard normal deviations (Z-table). Conversely, the alternative hypothesis indicates the presence of a significant trend, with statistically significant Z. In this study, a significance level of α = 0.05 is used, making the Z-table value 1.96 (Gan 1998). In climate change studies, two general approaches have garnered attention: utilizing a single model (Teixeira et al. 2013) and combining outputs from multiple models (Tebaldi & Knutti 2007; Gohari et al. 2014; Majone et al. 2016; Zamani et al. 2017). In addition to addressing the uncertainty associated with GCM models and employing model ensembles, evaluating the performance of these models is crucial. Utilizing models with superior capabilities in simulating climate variables for a specific region can help reduce uncertainties further. This study focuses solely on uncertainties related to Atmosphere–Ocean General Circulation Model (AOGCM) models. The effectiveness of each AOGCM is assessed using the ANOVA method.

After assessing the trends in precipitation changes at the Aji-Chay station during a future time period, in order to ensure the accuracy of the models under examination and to identify variations in mean precipitation values during that period, a one-way ANOVA was employed, and the relevant hypotheses were tested. However, as ANOVA assumes equal variances between groups, the Levene test for variance equality was conducted as well. Furthermore, to compare means between two time periods with unknown population variances, an independent samples t-test was utilized. This test essentially conducts multiple independent sample t-tests with a shared error level. As mentioned earlier, it determines whether there are significant pairwise differences among the models under examination.

The objectives of ANOVA include testing for statistical differences in the means of a continuous variable among two or more groups, assessing statistical differences in the means of a continuous variable within two or more time intervals, and examining statistical differences in the means of a continuous variable among two or more treatments (Javankhah Amiri & Khatami 2005: 13). In its simplest form, ANOVA offers a statistical test that assesses the equality of means among different groups without specifying which groups differ from one another. Therefore, the Tukey test was used to identify distinct groups.

Tukey's test for pairwise comparison of means

In this test, comparisons between means are made against a fixed value, irrespective of the specific means under examination. Statistical significance between two means is established when their difference surpasses the predetermined constant value. The response variable needs to be quantitative and measured on a relative interval scale, while the independent variable must be qualitative, with at least two levels or categories. The distribution of the quantitative variable within each level of the qualitative variable (groups or treatments) should be normal. Homogeneity among the variables should also be ensured, and this can be assessed using tests such as the Hartley and Levene tests (which evaluate the independence of one sample selection from other selections) (Rezai & Shoberiri 2015).

This test, commonly referred to as honestly significant difference (HSD) test, introduces a scale that enables the pairwise examination of the means of each group. The null and alternative hypotheses for this test are represented by Equation (6):
(6)

The assumptions for the Tukey test are as follows:

  • 1.

    Independence: Populations I and j should be independent of each other.

  • 2.

    Equal variances: The variances of both populations should be equal (Amiri & Karami 2012: 505).

Artificial neural networks are a well-known evolutionary model inspired by the neural networks found in the human body (Kothari & Gharde 2015; Tahani et al. 2016). This model can identify and simulate relationships between input and output variables. Artificial neural networks are a suitable model for simulating both linear and non-linear relationships, which is why they have been considered as a suitable simulation model in a wide range of environmental studies (Wang et al. 2006; Kothari & Gharde 2015; Noori & Kalin 2016; Prasad et al. 2017).

The integration of wavelet and artificial neural network introduces a groundbreaking paradigm within artificial intelligence, recognized as the WNN. This model emerges as a feasible substitute for recurrent neural networks (RNNs), demonstrating the ability to effectively employ any desired non-linear function. The governing algorithm of this network encompasses two fundamental processes: the self-organization of the network and error reduction. In the initial stage, the network's structure is delineated by employing the wavelet as an activation function. Through this iterative procedure, network parameters are adjusted, maintaining the network's framework and advancing to the next phases. In the following stage, the network estimator addresses simulation inaccuracies by utilizing algorithms embedded within the neural network design. Each hidden layer unit, which integrates a wavelet as its activation function and a time square window, adjusts its parameters by following optimization principles. This inherent flexibility enables the wavelet to function similarly to a behavior function. Through this transformative process, the original signal can be decomposed into its constituent basis signals.

Wavelet transform (WT)

According to the definition, a wavelet is a small wave with its energy concentrated in a small region and is a suitable tool for the analysis of transient phenomena. A wavelet has minimal oscillation that tends toward zero, and this descent must be limited in both positive and negative directions within its domain. This characteristic makes wavelets flexible and capable of behaving like a function. Recent findings have shown that wavelet transforms are suitable for data analysis and denoising. Wavelets are mathematical functions that provide a time-scale representation of time series and their relationships, which is useful for the analysis of non-stationary time series (Adamowski et al. 2009; Chou 2011). The advantage of wavelet transforms lies in their ability to provide information in terms of time, location, and frequency of a signal. Using this transform, the original signal can be decomposed into its constituent basis signals. There are two types of wavelet transforms: 1 Continuous Wavelet Transform (CWT), and 2 Discrete Wavelet Transform (DWT), which are expressed by one of the wavelet Equations (7) and (8) (Polikar 1996):
(7)
(8)
Equation (8) represents a function of two variables, s and τ. Here, τ represents translation, and s denotes scale (inverse of frequency), and the * sign represents complex conjugation. Both s and τ are real numbers, and s is always positive and may take continuous or discrete values. In continuous wavelet transforms, s and τ have continuous values, while in discrete wavelet transforms, they have discrete values. ψ(t) is the mother wavelet function. The term ‘mother’ is used because various functions are generated based on scale and translation parameters, all derived from the mother wavelet function. All the functions created from the mother function are called daughter wavelets, as derived in Equation (9). The scale coefficient is denoted by one of the letters a or s (Lau & Weng 1995):
(9)
The following statistical metrics were used to evaluate the simulations. All the metrics were assessed between historical models and the reference before and after fine-scale exponentiation and correction using the delta method in MATLAB software. The data generated by the neural network were evaluated using the correlation coefficient (R), the coefficient of determination (R2), the mean squared error (MSE), the mean absolute error (MAE), in the MATLAB environment (Equations (10)–(14)):
(10)
(11)
(12)
(13)
(14)

In which Xi and Yi represent the ith observed and simulated data, respectively, and are the overall means of Yi and Xi in the population, and n is the total number of samples evaluated (Panahi & Khormabad 1398: 148). A smaller value for statistical metrics such as RMSE, Mean Bias Error (MBE), and MAE being closer to zero is better. The values of R2 and R range from zero to one, and the closer they are to one, the better the data fit (Ahmadi et al. 1398: 278).

As shown in Table 3 and Figures 36, trends in hydrological time series can be caused by gradual natural changes, climate variability, or human activities. The findings of this study are consistent with the findings of other studies on the impact of human activities on rainfall patterns. For example, the IPCC study (2023) has shown that global warming increases the probability of drought in semi-arid and arid regions. It is important to note that demonstrating the statistical significance of a trend in a time series of precipitation alone cannot serve as conclusive evidence of climate change in a region. Considering the aforementioned, a significant decrease in precipitation has been observed in the study area.
Table 3

Comparison of observed and predicted precipitation changes in the study period

 
 

Throughout this text, certain symbols are used to denote the strength of the statistical evidence.

*A finding is significant with 90% confidence, meaning there's a 90% chance the finding is true and not due to random variation.

** 95% confidence level.

*** Strongest evidence at a 99% confidence level.

Figure 3

Dispersion of the monthly average total precipitation in the baseline period.

Figure 3

Dispersion of the monthly average total precipitation in the baseline period.

Close modal
Figure 4

Dispersion of the monthly average total precipitation in the CanESM5 model.

Figure 4

Dispersion of the monthly average total precipitation in the CanESM5 model.

Close modal
Figure 5

Dispersion of the monthly average total precipitation in the INM-CM4 model.

Figure 5

Dispersion of the monthly average total precipitation in the INM-CM4 model.

Close modal
Figure 6

Dispersion of the monthly average total precipitation in the MRI-ESM2 model.

Figure 6

Dispersion of the monthly average total precipitation in the MRI-ESM2 model.

Close modal

Figure 3 illustrates a notable decrease in precipitation during the study period, particularly in February. This decrease is significantly larger than the historical average variability for the region, indicating a deviation from expected seasonal patterns. For instance, the average February precipitation for the baseline period (1981–2010) was 38.54 mm. However, in February 2024, the observed precipitation was only 35.24 mm, representing an 8.59% decrease. This decline is statistically significant, with a 99% confidence level, suggesting that it is unlikely to be due to natural variability alone. This observed deviation from historical trends aligns with concerns about the impact of climate change on regional precipitation patterns. Global warming is expected to lead to increased aridity in some regions, and the observed decrease in February precipitation could be an early manifestation of this trend.

To further investigate this possibility, future research should focus on analyzing long-term precipitation data and comparing the data with climate model projections for the region. This will help to determine whether the observed decrease is part of a long-term trend and whether it can be attributed to climate change. As seen in Figures 5 and 6, the downward trend of rainfall in July and August during the study period is clearly visible. This is in line with predictions about the effect of global warming on rainfall patterns.

Furthermore, a twofold decreasing trend is noticeable in June during the observational period and in the CanESM5 model for the future period (2025–2065) under the SSP5.85 scenario, indicating the presence of a drought trend in the region. On the other hand, the CanESM5 model simulates an increase in average rainfall during March and April compared to the baseline period. These increases are predicted to be 1.90 and 2.035 mm for March and April, respectively. The observed trends imply potential alterations in the seasonal weather patterns of the study region. This could impact the amount and characteristics of precipitation throughout the year, potentially as a result of global warming. These results align with the research conducted by Azizi-Ebrahim et al. (2023) and provides strong evidence of the impact of climate change on rainfall patterns in the study area. Both the INM-CM4 and MRI-ESM2 climate models project a decrease in April precipitation exceeding 1% for the near future under the SSP5.85 scenario. MRI-ESM2 predicts a more substantial decline of 1.98 mm (13.76%), whereas INM-CM4 suggests a decrease of 2.035 mm (7.08%). Compared to historical data (baseline period), future projections using the SSP5.85 scenario in the studied climate models suggest varying decreases in precipitation across the study area for the 2025–2065 period. These projected changes range from a slight decrease of 0.146 mm to a more substantial decline exceeding 2.127 mm.

Exploring the uncertainty of monthly precipitation estimation by models

First, we defined a historical period (baseline) to serve as a reference point. Then, we compared the precipitation levels during this period with those expected in the future. This comparison forms the basis for our key findings. A statistical technique called ANOVA was used to assess the uncertainties associated with the climate models employed in this study. Our analysis revealed a statistically significant decline of 3.37% in monthly precipitation across the watershed area during the observation period. This decrease is considered significant with a confidence level of 95%. Notably, the CanESM5 model projects an even steeper decline of 3.916% in watershed precipitation with 95% confidence, highlighting the potential severity of these future changes.

Interestingly, the INM-CM4-8 and MRI-ESM2-0 models exhibited a higher level of confidence in their projections compared to historical data (baseline period) at a 95% confidence level. This suggests lower uncertainty in their predictions. However, the CanESM5 model stood out with the highest level of confidence when forecasting precipitation under scenario 5.85 for the study period (2025–2065). These findings highlight the exceptional ability of the CanESM5 model to simulate precipitation patterns within the watershed area (refer to Table 4 for details).

Table 4

Summary of factorial analysis of variance

 
 

The CanESM5 model predicts slightly more rainfall (−5.91 mm) for the future compared to that observed in the past (−5.05 mm). This difference might be because real-world rainfall data mainly reflect geographic aspects such as latitude and altitude. The CanESM5 model, however, is more complex and considers additional factors such as ocean currents, air circulation patterns, and even climate change. Interestingly, the similarity between the observed baseline rainfall and the CanESM5's projection for the future might be attributed to their shared utilization of geographical factors to simulate rainfall. These factors include latitude, altitude, and distance to the ocean, all of which can significantly impact precipitation levels.

In contrast, the WNN model predicts a 5.92% increase in future rainfall for this region, contradicting the CanESM5 model's prediction. This difference in forecasts might be due to the way each model simulates climate. CanESM5 is a global model that utilizes complex equations to represent various climate processes on a large scale. Conversely, the WNN model focuses on a specific region and utilizes an artificial neural network, which is a type of machine learning, to simulate climate processes. In simpler terms, CanESM5 learns from global weather data, while WNN learns from data specific to this region.

Different climate models predict diverse changes in future rainfall, as illustrated by the box plot. However, a measure known as the Standardized Coefficients index indicates that the CanESM5 model is the most accurate in simulating rainfall patterns. Compared to other models, CanESM5's predictions are much closer to past weather data (observed data). This is further supported by the boxplot's position closer to the axis, indicating high confidence at a 95% significance level. Overall, the CanESM5 model best reflects historical trends. Looking at Figure 7, we observe that the average monthly precipitation across the study area exhibits a decreasing trend for the period 2025–2065 (under scenario SSP5.8.5) compared to the past (observational period).
Figure 7

Box plot comparing the standardized coefficients between selected models for the future period with the observational period.

Figure 7

Box plot comparing the standardized coefficients between selected models for the future period with the observational period.

Close modal
The scientists examined the ability of the climate models to replicate the natural variability in monthly rainfall, both historically (observational period) and for the future (95% confidence interval). This variation is a key statistic for understanding rainfall patterns. Figure 8 shows the results for the selected watershed. Two models, INM-CM4-8 and MRI-ESM2-0, did not capture this variation as effectively as the other models. Their predictions fall outside the shaded area (95% confidence interval), indicating that they may not be suitable for simulating rainfall in this area.
Figure 8

A comparison of the behavior of monthly precipitation during the observational period compared to the predicted period.

Figure 8

A comparison of the behavior of monthly precipitation during the observational period compared to the predicted period.

Close modal

Table 5 presents the results of a statistical test (Tukey test) comparing rainfall data from historical observations (1987–2020) with predictions from future models (2025–2065) for the study area. The test results are significant, indicating their reliability at a 95% confidence level. According to the table, only the CanESM5 model shows acceptable variation in rainfall predictions for March and April compared to historical data (observational period). These indicate that the CanESM5 model's predictions for these months are statistically similar to past observations. Furthermore, when comparing the simulation results of the CanESM5 model under the SSP5-8.5 scenario for the period 2025–2065 to the period 1987–2020, these results are consistently validated at a monthly scale. The performance of the INM-CM4-8 and MRI-ESM2-0 models is considered acceptable; however, their performance in replicating the frequency distribution of the observational period is weaker. Despite this, their performance in evaluating the impacts of climate change on averages at all time scales remains adequate. Consequently, the evaluation results for the INM-CM4-8 and MRI-ESM2-0 models are considered less reliable.

Table 5

Partial output of the interaction effect of precipitation from the observational period relative to the study models of the future period in Tukey HSD test

 
 

Neural networks require careful preparation of rainfall data for accurate predictions. The recommended approach involves cleaning the historical data by removing outliers and standardizing it for consistency. These preprocessed data are then divided into two sets: training data and testing data. The training data help the neural network learn patterns between past and future precipitation. Finally, the unseen testing data are used to evaluate the model's accuracy in predicting future rainfall.

After splitting the data into two groups (training and testing), the larger portion (80%) becomes the training data. These data are fed into the neural network, similar to showing examples to a student for learning. The neural network analyzes these examples and constructs a model to predict future rainfall. The remaining 20% of the data are the testing data. Once the model is built using the training data, these new examples are presented to the model for testing. This helps us evaluate how well the model performs on unseen data, similar to how a teacher might give a student a new problem to solve. This process of training and testing continues until all the testing data have been used. By analyzing the results, scientists can determine whether the model accurately predicts future rainfall. In this study, we utilized preprocessed data transformed using DWT as inputs to the neural network to improve its accuracy. Specifically, we used the DWT MIR wavelet as inputs. This approach enables the extraction of both fine and coarse features from the time series signal, ultimately enhancing the model's accuracy. As shown in Figure 9, the daily rainfall time series signal is decomposed into its constituent basis signals using the DWT MIR with a decomposition level of 3. As depicted in the figure, the MIR wavelet has decomposed the signal S into one approximation wavelet (a2) and two detail wavelets (d1, d2) (Equation (15)):
(15)
Figure 9

The original time series and decomposed by damped wavelet in the period 2001–2000.

Figure 9

The original time series and decomposed by damped wavelet in the period 2001–2000.

Close modal

The results of these predictions are provided in Table 6. It is evident from this table that the performance and accuracy of the models, obtained through the MIR wavelet decomposition, have improved due to their similarity to the rainfall signal and its inherent complexity. The high accuracy achieved by the neural network-wavelet model can be attributed not only to the preprocessing and wavelet-based segmentation of sub-signals but also to the amplification of the relative weight of each sub-signal's influence through the decomposition process.

Table 6

Results of prediction

(Test)(Validation)(Training)The number of delays
MAERMSER2RMAERMSER2RMAERMSER2R
0.0023 0.001 0.92 0.96 0.003 0.0002 0.86 0.93 0.006 0.003 0.88 0.94 
0.004 0.001 0.87 0.935 0.006 0.003 0.72 0.85 0.01 0.0004 0.84 0.92 
0.062 0.004 0.84 0.92 0.005 0.002 0.67 0.82 0.02 0.0005 0.86 0.93 
0.0075 0.003 0.82 0.91 0.006 0.0003 0.75 0.87 0.01 0.0006 0.84 0.92 
(Test)(Validation)(Training)The number of delays
MAERMSER2RMAERMSER2RMAERMSER2R
0.0023 0.001 0.92 0.96 0.003 0.0002 0.86 0.93 0.006 0.003 0.88 0.94 
0.004 0.001 0.87 0.935 0.006 0.003 0.72 0.85 0.01 0.0004 0.84 0.92 
0.062 0.004 0.84 0.92 0.005 0.002 0.67 0.82 0.02 0.0005 0.86 0.93 
0.0075 0.003 0.82 0.91 0.006 0.0003 0.75 0.87 0.01 0.0006 0.84 0.92 

Wavelet decomposition, a technique for analyzing complex signals, significantly improved the accuracy of neural network predictions for monthly rainfall. This method breaks down the rainfall data into simpler components, enabling the neural network to learn the intricacies of the signal. The resulting neural wavelet model achieved a high correlation coefficient (0.94), demonstrating its effectiveness in capturing and simulating monthly rainfall patterns compared to traditional methods. This approach offers a promising advancement in predicting future precipitation (Figure 10).
Figure 10

Comparison of monthly precipitation and precipitation values by the WNN method with damped wavelet.

Figure 10

Comparison of monthly precipitation and precipitation values by the WNN method with damped wavelet.

Close modal

Table 7 illustrates the precipitation change predictions for the upcoming decade at the Aji-Chay station. This table is divided into two sections. The first section presents forecasts from the CMIP6 models analyzed during the baseline period over the past three decades (1975–2014). In the MRI-ESM2 model, the annual precipitation amounted to 337.57 mm; in the CanESM5 model, it was 290.61 mm, and in the INM-CM4 model, it reached 344.42 mm. For the subsequent four decades (2025–2065), the projected annual precipitation is 313.11 mm in the MRI-ESM2 model, 274.14 mm in the CanESM5 model, and 316.14 mm in the INM-CM4 model. This pattern indicates a decreasing trend in precipitation over these four decades compared to the previous three decades. In the next decade (2025–2035), this trend, observed across all CMIP6 models under the SSP5.85 scenario, shows a reduction of more than 5%. Specifically, this reduction is equivalent to 5.0%. Consequently, it implies an anticipation of an average annual precipitation decrease of more than 5% at the Aji-Chay station in the next decade.

Table 7

Average annual rainfall predicted by different models over the next two decades at Tabriz Synoptic Station

 
 

In the upcoming decade (2025–2065), the projected precipitation amount for the Aji-Chay station is 322.23 mm, as indicated in the first section of the table. The recorded precipitation for this station in the preceding decade (1981–2020) was 304.22 mm. Consequently, based on the findings of the examined CMIP6 models, the estimated percentage decrease in precipitation for the next decade at the Aji-Chay station is approximately 5%.

The second section provides the forecasts generated by the WNN.

For the upcoming decade (2025–2035), the projected value for the WNN is 5.04%. This figure indicates an expected average annual precipitation increase of about 5.04% at the Aji-Chay station in the next decade.

Neural network models are sensitive to input data, which can lead to variations in their outcomes. In this investigation, precipitation data from 1981 to 2020 were used to train the neural network model in the Aji-Chay watershed. Not all factors influencing precipitation changes in this watershed were accounted for in the analysis. Consequently, relying solely on the presented precipitation percentage values, the WNN (5.92%) and CanESM5 (5.40%) models demonstrate proximity to each other. This underscores the model's satisfactory performance in replicating the climate of the examined region. The study forecasts a significant reduction in precipitation for the Aji-Chay watershed under the SSP5.85 scenario. This decline in precipitation could have severe implications, such as diminishing agricultural productivity due to reduced rainfall, resulting in lower crop yields and an increase in food prices. The reduced precipitation also increases the risk of drought in the Aji-Chay watershed, which could potentially result in significant economic and environmental consequences.

Rainfall, a crucial element of the planet's water cycle, has a profound impact on human endeavors. The effects of rainfall are intricately linked to both its volume and characteristics, with alterations in precipitation amounts and patterns being significantly influenced by shifts in climate. This research aimed to forecast changes in precipitation within the Aji-Chay watershed between 2025 and 2065 by comparing models from the CMIP6 under the SSP5-8.5 scenario with a WNN. Furthermore, to evaluate the uncertainty related to CMIP6 models, an ANOVA was utilized. The results indicated that, in the models analyzed, there was a decrease in precipitation for the future period compared to the baseline period. The decrease ranged from −0.146 to more than −2.127 mm under the SSP5.85 scenario for the years 2025–2065. During the observational period, a statistically significant decreasing trend of 3.37% in monthly watershed precipitation was identified at a significance level of 0.05. The CanESM5 model highlighted this trend by predicting a decrease in precipitation in the watershed at a rate of 3.916. There is a 95% confidence level associated with this prediction. The accuracy evaluation of the CMIP6 models indicated that the CanESM2 model performed well in simulating precipitation in the study area, consistent with previous studies that identified it as the optimal model for the Aji-Chay watershed. Furthermore, the simulated precipitation using the hybrid WNN model at the Tabriz station for the period 2025–2065 was lower than that of the CanESM5 model. However, for the period 2025–2065, the simulated precipitation of the INM-CM4 and MRI-ESM2 models exceeded that of the CanESM5 model.

One of the limitations of this study is that it only measured changes in rainfall over time. Meanwhile, other factors such as changes in temperature, vegetation and land use can also affect changes in rainfall. This study did not consider these factors and can be proposed as a suggestion for future studies.

In general, the results of this study highlight several key findings. Firstly, it is evident that the precipitation parameters have been effectively downscaled by the fine-scale model. The modeling and downscaling capabilities of the past climate at the study station are generally well established. Furthermore, the results indicate that the downscaled data from CanESM5 closely match the actual climate parameters of the region. This suggests that these downscaled data can be employed to provide more accurate future climate projections at the station level. Utilizing statistical models in conjunction with these data can significantly contribute to enhanced resource management, particularly in the context of water resources.

Considering the non-stationary and non-linear characteristics of precipitation time series, the utilization of a WNN is essential for accurate prediction and simulation. The wavelet transformation separates the signal into high and low-frequency components, providing access to multi-scale signal features and significantly enhancing the accuracy of the model. Additionally, in the hybrid model, the accuracy of peak precipitation prediction, which holds great significance in precipitation modeling, is notably enhanced.

Another important point to consider is that an increase in the delay in the output signal can decrease the accuracy of predictions in the WNN model. The use of the Morlet wavelet has been shown to enhance the prediction accuracy of the model. ANOVA results show both homogeneity and non-homogeneity of precipitation indices, with the predicted precipitation demonstrating homogeneity at a 99% confidence level, indicating it is part of a statistical population. This highlights the high accuracy of the prediction method, which can be credited to the complex wavelet shape of the Morlet wavelet. By breaking down the signal into simpler wave components, the model can better model random data, resulting in improved prediction accuracy compared to traditional methods.

All relevant data are included in the paper or its Supplementary Information.

The authors declare there is no conflict.

Adamowski
K.
,
Prokoph
A.
&
Adamowski
J.
2009
Development of a new method of wavelet aided trend detection and estimation
.
Hydrological Processes: An International Journal
23
(
18
),
2686
2696
.
Ahmadi
M. A.
,
Baqeri Moghadam
N.
,
Abbaspour
M.
&
Nazemi Ashani
A.
2023
Analysis of population, economic growth, and science and technology indicators in scenarios (common economic-social paths)
.
Science and Technology Policy Quarterly
13
(
1
),
76
90
.
Amiri
M.
&
Karami
S.
2012
Quality Control and Statistical Analysis with Minitab 16
.
Tehran, Iran. Kian Rayaneh Sabz Publications
.
Azizabadi Farahani
M.
,
Bakhtiari
B.
,
Kadri
K.
&
Rezapour
M.
2017
Investigation of the effect of climate change on drought-duration-frequency curves of Qarahsoo catchment using detailed functions
.
Iranian Soil and Water Research
47
(
4
),
754
743
.
Azizi-Ebrahim
M.
,
Salehghe
M.
,
Naserzadeh
M. H.
&
Alijani
B.
2023
The role of climate change in the displacement of climatic seasons in Iran
.
Applied Geography Research (Geographical Sciences)
22
(
64
),
1
16
.
Chen
J.
,
Brissette
F. P.
&
Leconte
R. J.
2011
Uncertainty of downscaling method in quantifying the impact of climate change on hydrology
.
Journal of Hydrology
401
,
190
202
.
Chou
C. M.
2011
Complexity analysis of rainfall and runoff time series based on sample entropy in different temporal scales
.
Stochastic Environmental Research and Risk Assessment
6
,
1401
1408
.
Dione
P. M.
,
Faye
C.
&
Sadio
C. A. A. S.
2023
Hydrological impacts of climate change (Rainfall and temperature) and characterization of future drought in the aga foua djilas watershed
.
Indonesian Journal of Social and Environmental Issues (IJSEI
4
(
3
),
353
375
.
Gallé
J.
&
Katzenberger
A.
2023
Indian agriculture under climate change: The competing effect of temperature and rainfall anomalies (No. 1002). RWI-Leibniz-Institut für Wirtschaftsforschung, Ruhr-University Bochum, TU Dortmund University, University of Duisburg-Essen.
Gettelman
A.
,
Hannay
C.
,
Bacmeister
J. T.
,
Neale
R. B.
,
Pendergrass
A. G.
&
Danabasoglu
G.
2019
High climate sensitivity in the community earth system model version 2 (CESM2)
.
Geophysical Research Letters
46
,
83298337
.
https://doi.org/10.1029/2019gl083978
.
Gohari
A.
,
Madani
K.
,
Mirchi
A.
&
Bavani
A. M.
2014
System-Dynamics Approach to Evaluate Climate Change Adaptation Strategies for Iran's Zayandeh-Rud Water System
.
World Environmental and Water Resources Congress 2014, Portland, Oregon, Sponsored by the Environmental and Water Resources Institute of ASCE
. pp.
1598
1607
.
Hessar
S. B.
&
Ghazavi
R.
2015
Comparison of TS and ANN models with the results of emission scenarios in rainfall prediction
.
Journal of Water and Soil
9
(
4
),
943
953
.
Hosseini
S. M.
&
Khormabadi
F.
2023
Predicting hazardous heat waves in east Azerbaijan using the CMIP6 model
.
Geography and Environmental Hazards
12
(
2
),
125
145
.
Intergovernmental Panel on Climate Change (IPCC), 2023: Climate Change
2023
Synthesis Report. Contribution of Working Groups I, II and III to the Sixth Assessment Report of the Intergovernmental Panel on Climate Change [Core Writing Team, H. Lee and J. Romero (eds.)]. IPCC, Geneva, Switzerland
, pp.
35
115
.
Jahanbakhsh Asl
S.
,
Khorshiddoust
A.
,
Alinejad
M. H.
&
Pourasghr
F.
2016
Impact of climate change on precipitation and temperature by taking the uncertainty of models and climate scenarios (case study: Shahrchay basin in Urmia)
.
Hydrogeomorphology
3
(
7
),
107
122
.
Javankhah Amiri
S.
&
Khatami
H.
2005
Investigating the relationship between future air quality index parameters in Tehran using regression analysis in 1384
.
Human and Environment
10
(
1
),
15
28
.
Kendal
M. G.
&
Stuart
A.
1973
The Advanced Theory by Statistics
.
Griffin
,
London
.
Kothari
M.
&
Gharde
K. D.
2015
Application of ANN and fuzzy logic algorithms for streamflow modeling of Savitri catchment
.
Journal of Earth System Science
124
(
5
),
933
943
.
Lau
K. M.
&
Weng
H. Y.
1995
Climate signal detection using wavelet transform. How to make time series sing
.
Bulletin of the American Meteorological Society
76
,
2391
2402
.
Majone
B.
,
Villa
F.
,
Deidda
R.
&
Bellin
A.
2016
Impact of climate change and water use policies on hydropower potential in the south-eastern Alpine region
.
Journal of Hydrology
543
,
965
980
.
Mohammadpour Khoie
M. M.
&
Nasseri
M.
2022
Evaluation of unstationary and extreme value patterns of precipitation over Iran considering impacts of climate change
.
Journal of Climate Research
1401
(
49
),
131
148
.
(In Persian)
.
Nazaripouya
H.
,
Kardavany
P.
&
Rad
A. R. F.
2016
Assessing climate change impacts on hydro-climatic parameters in the Dam Basin of Ekbatan
.
Hamedan. Iranian Journal of Eco Hydrology
3
(
2
),
181
194
.
Omidvar
E.
,
Rezaei
M.
&
Pirnia
A.
2019
Performance evaluation of artificial neural network models for downscaling and predicting of climate variables
.
Journal of Watershed Management Research
9
(
18
),
80
90
.
Ouyang
F.
,
Zhu
Y.
,
Fu
G.
,
H.
,
Zhang
A.
,
Yu
Z.
&
Chen
X.
2015
Impacts of climate change under CMIP5 RCP scenarios on streamflow in the Huangnizhuang catchment
.
Stochastic Environmental Research and Risk Assessment
29
,
1781
1795
.
Pirnia
A.
,
Golshan
M.
,
Darabi
H.
,
Adamowski
J.
&
Rozbeh
S.
2019
Using the Mann–Kendall test and double mass curve method to explore stream flow changes in response to climate and human activities
.
Journal of Water and Climate Change
10
(
4
),
725
742
.
Polikar
R.
1996
Fundamental Concepts and Overview of the Wavelet Theory
, 2nd edn.
The Wavelet Tutorial Part I, Rowan University, College of Engineering Web Servers, 15
.
Pour
O. M. R.
2016
The effect of climate change on streamflow used statistical downscaling of HADCM3 model and Artificial Neural Networks
.
Water and Soil Conservation
23
(
3
),
317
326
.
Raghavan
S. V.
,
Liu
J.
,
Nguyen
N. S.
,
Vu
M. T.
&
Liong
S. Y.
2018
Assessment of CMIP5 historical simulations of rainfall over Southeast Asia
.
Theoretical and Applied Climatology
132
(
3–4
),
989
1002
.
Reddy
N. M.
&
Saravanan
S.
2023
Extreme precipitation indices over India using CMIP6: A special emphasis on the SSP585 scenario
.
Environmental Science and Pollution Research
30
(
16
),
47119
47143
.
Rezai
M.
&
Shoberiri
S. M.
2015
Analysis of the role of strategic planning in training sustainable development with an emphasis on environmental aspects
.
Journal of Environmental Science and Technology
16
(
Special Issue
),
409
419
.
Sadeghi
A.
&
Deen Pjooh
Y.
2019
Preview of precipitation and its changes under climate change conditions in future periods (Case study: Tabriz)
.
Environment and Water Engineering
5
(
4
),
0
33935
.
Salahi
B.
,
Nohegar
A.
&
Behrouzi
M.
2019
Estimation of future temperature and precipitation fluctuations in Ardebil plain in order to manage and planning the beginning of cultivation and the length of wheat growth period
.
Quarterly of Geography (Regional Planning)
9
(
4
),
277
288
.
Sen
P. K.
1968
Estimates of the regression coefficient based on Kendall's tau
.
Journal of the American Statistical Association
63
(
324
),
1379
1389
.
Senatore
A.
,
Fuoco
D.
,
Maiolo
M.
,
Mendicino
G.
,
Smiatek
G.
&
Kunstmann
H.
2022
Evaluating the uncertainty of climate model structure and bias correction on the hydrological impact of projected climate change in a Mediterranean catchment
.
Journal of Hydrology: Regional Studies 42, 101120
.
Sun
Y.
,
Solomon
S.
,
Dai
A.
&
Portmann
R. W.
2006
How often does It rain?
Journal of Climate
19
,
916
934
.
https://doi.org/10.1175/JCLI3672.1
.
Swart
N. C.
,
Cole
J. N.
,
Kharin
V. V.
,
Lazare
M.
,
Scinocca
J. F.
,
Gillett
N. P.
,
Anstey
J.
,
Arora
V.
,
Christian
J. R.
,
Hanna
S.
,
Jiao
Y.
,
Lee
W. G.
,
Majaess
F.
,
Saenko
O. A.
,
Seiler
C.
,
Seinen
C.
,
Shao
A.
,
Sigmond
M.
,
Solheim
L.
,
von Salzen
K.
,
Yang
D.
&
Winter
B.
2019
The Canadian earth system model version 5 (CanESM5. 0.3)
.
Geoscientific Model Development
12
(
11
),
4823
4873
.
Tahani
M.
,
Vakili
M.
&
Khosrojerdi
S.
2016
Experimental evaluation and ANN modeling of thermal conductivity of graphene oxide nanoplatelets/ deionized water nanofluid
.
International Communications in Heat and Mass Transfer
76
,
358
365
.
Tebaldi
C.
&
Knutti
R.
2007
The use of the multi-model ensemble in probabilistic climate projections
.
Proceedings of the National Academy of Sciences
365
,
2053
2075
.
Teixeira
E. I.
,
Fischer
G.
,
Van Velthuizen
H.
,
Walter
C.
&
Ewert
F.
2013
Global hot-spots of heat stress on agricultural crops due to climate change
.
Agriculture, Ecosystems & Environment
170
,
206
215
.
Tiedtke
M.
1993
Representation of clouds in large-scale models
.
Monthly Weather Review
121
,
3040
3061
.
https://doi.org/10.1175/1520–04
.
Wang
W.
,
Van Gelder
P.
,
Vrijling
J. K.
&
Ma
J.
2006
Forecasting daily streamflow using hybrid ANN models
.
Journal of Hydrology
324
(
1–4
),
383
399
.
Yaghoubi
B.
,
Hosseini
S. A.
&
Nazif
S.
2017
Hydrological impact of climate change on the GavehRud Watershed as affected by the parameter uncertainty
.
Water Engineering 10 (32), 71–86
.
Zamani
R.
,
Akhond-Ali
A.-M.
,
Roozbahani
A.
&
Fattahi
R.
2017
Risk assessment of agricultural water requirement based on a multi-model ensemble framework in the southwest of Iran
.
Theoretical and Applied Climatology
129
,
1109
1121
.
Zazulie
N.
,
Rusticucci
M.
&
Raga
G. B.
2018
Regional climate of the Subtropical Central Andes using high-resolution CMIP5 models. Part II: Future projections for the twenty-first century
.
Climate Dynamics
51
,
2913
2925
.
https://doi.org/10.1007/s00382–017–4056
.
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/).