A nonlinear programming model was developed for optimizing cropping patterns with two objectives: maximizing farming revenue and minimizing irrigation water consumption. After determination of dominant crops in the study area, the water requirement of each crop was calculated by CROPWAT. Next, the volume of water used by farmers to irrigate the crops was computed. Based on the costs of agricultural inputs and farming operations and the price of products, the profit earned by farmers was calculated. The calculations were carried out for current and future climate conditions. For the future periods, input data to CROPWAT was obtained by simulating the climate parameters in the general circulation model (Hadley Centre Coupled Model version 3) under three emission scenarios, namely, A2, B1, and A1B. Then, the Long Ashton Research Station Weather Generator statistical model was used for the downscaling of data from the general circulation model. Finally, an NLP optimization model was developed in LINGO-20 to optimize the cropping pattern. The results indicated that by optimizing the cropping pattern, the farming revenue increased up to 65% on average compared with the existing (nonoptimal) cropping pattern, while at the same time, the agricultural water consumption was reduced by 5%.

  • A nonlinear model was developed in LINGO for the optimization of cropping patterns.

  • CROPWAT was used to calculate the crop water requirement in the study area.

  • Three global climate model emission scenarios (A2, B1, and A1B) were applied for future modelling.

  • The farming revenue increased up to 65% on average.

  • The agricultural water consumption was reduced by 5%.

Today, the rapid growth of the global population has increased the demand for agricultural products. Agricultural productivity is highly dependent on reliable sources of water, which itself is seriously influenced by climate change. Accordingly, for sustainable agricultural development, any long-term fluctuations of climatic variables (climate change) and their impact on agricultural activities should be considered in macro-economic decisions and policies. Therefore, special attention should be paid to the selection of optimum cropping patterns and optimal use of water resources under climate change. Selecting the optimal cropping pattern while minimizing water consumption can increase irrigation efficiency, increase crop yields, improve soil properties, increase farmers’ income levels, prevent the migration of families from rural to urban areas, and promote the agricultural, social, and economic development of a country. Therefore, cropping pattern optimization is an important step towards sustainable agriculture. Designing an optimum cropping pattern is a complex process influenced by a variety of factors and analysing them requires the gathering of large amounts of data and information. Solving such complex problems requires a robust and efficient method.

Previous researchers suggested different methods to optimize the cropping pattern. Zhenmin (1994) used a simple linear optimization model in the Yellow River Chengai irrigation project in China and reported that this optimization model could increase the production level while saving irrigation water. Darwish et al. (2007) optimized the cropping pattern in northern Lebanon by a linear programming (LP) method with the purpose of increasing farmers' profits. Regarding the several limitations of LPs, which make them unable to optimize complex engineering problems, nonlinear programming (NLP) methods have demonstrated promising results in such problems. Garibay-Rodriguez et al. (2017) proposed a mathematical NLP model for sustainable water management in treatment units in macroscopic systems. Aljanabi et al. (2018) developed a mixed-integer NLP optimization model to optimize the agricultural reclaimed water allocation over 84 agricultural farms in Iraq. They documented that irrigation with reclaimed water has the potential to increase agricultural and economic activities. Grové (2019) presented an NLP model to formulate deep percolation and evapotranspiration (ET) as functions of the soil-moisture content. The results of this study demonstrated that ignoring the increasing efficiencies may overestimate the impact of deficit irrigation on maize yields by a maximum of 2.2 tons/hectare. Li et al. (2019) proposed an NLP-based integrated model for the sustainable management of agricultural water–energy–food nexus under uncertainty and successfully employed the developed model for a real case study in northwest China. Cervantes-Gaxiola et al. (2020) proposed a multi-period mixed-integer NLP model for optimal crop allocation for several planting cycles based on future crop price and freshwater availability. The results demonstrated that the optimal allocation can be determined by the optimal relationship between the crop price, water availability, and costs by employing mass water integration. Barati et al. (2020) used a system dynamics approach by Vensim-Pro and multi-objective mathematical programming to optimize the cropping pattern in an agricultural region in Iran. The results showed that the ratio of the benefit to the consumed water in the optimized condition was always higher than in the nonoptimal condition. Yan et al. (2021a) successfully used a cloud-based dual-objective NLP model for the irrigation water allocation in northwest China. The results showed that the net economic profit and irrigation system efficiency are influenced by evapotranspiration more than surface water availability. Yan et al. (2021b) developed a stochastic multi-objective NLP model for irrigation water allocation under uncertainty and reported that the developed model can generate solutions that save irrigation water while ensuring net economic benefit. Marzban et al. (2022) developed a multi-objective NLP model to optimize the cropping pattern in Lorestan, Iran, for maximization of the net profit and minimization of the consumed energy. Akbari et al. (2022) linked the Soil and Water Assessment Tool to the well-known MODFLOW model to simulate agricultural production and groundwater-level variation in the Eshtehard watershed in Iran and used the particle swarm algorithm to optimize the cropping pattern. They reported that in the optimal cropping pattern, the dramatic rate of groundwater depletion was reduced. Ajudiya & Yadav (2023) utilized an artificial intelligence (AI) model to derive the optimal policies for a multi-reservoir system in a semi-arid river basin in India with the purpose of maximizing the net benefits subject to the land and water allocation. They validated the proposed model with the results of the LP model. The result revealed that the proposed AI model was superior. Mardani Najafabadi & Ashktorab (2023) developed a multi-objective fractional LP to determine the optimal cropping pattern under uncertainty. They reported that the consumption of fertilizers and chemical pesticides decreased by 5.9% and 8.19%, respectively, in the optimal cropping pattern. Darzi-Naftchali et al. (2024) provided a sustainable cropping pattern by developing a multi-objective model that maximizes profit while minimizing environmental problems and raising social indicators. The results of their study indicated that by sustaining a cropping pattern, the proposed model can help reduce social conflict while generating a synergy between economic and environmental benefits.

As seen, during recent years, special attention has been dedicated to cropping-pattern optimization. In this way, less attention has been paid to the effect of climate change on the cropping pattern. Climate change directly impacts the irrigation water requirement and crop yields. Investigating the effects of climate change on agriculture is essential for addressing food security and the sustainable use of water. Accordingly, Harmsen et al. (2009) investigated the impact of climate change on the relative yield of crops in the three regions of west Puerto Rico and found that climate change impacted the crop yield in some emission scenarios. Jamshidpey & Shourian (2021) used the well-known MODSIM, IHACRES, and Hadley Centre Coupled Model version 3 (HadCm3) models to obtain the optimal amount of irrigation water and cultivation areas under two conditions, namely, the status quo and the climate-change-affected streamflow for the Zayandeh-roud River in Iran. They reported that the agricultural net benefit will decrease by up to 17.5% in the investigated climate-change scenarios. Chen et al. (2022) developed a multi-objective model for the optimization of cropping patterns in the Jinxi Irrigation District in China under climate-change with two goals: environmental pollutants' reduction and the economic benefit increment. They found that by adjusting the acreage of rice, maize, and soybean, the degree of harmony of the economy–society–environment system increased by 10.7% compared with the nonoptimal condition. More recently, Rudraswamy & Umamahesh (2024) employed the CROPWAT model to investigate the impact of future climate change on the irrigation and crop water requirements of Bhadra and Tungabhadra areas in India. The results showed that the future climate projections from the best global climate model indicate a consistent increasing trend from 2023 to 2100 in both areas under the two shared socioeconomic pathways. Kumari et al. (2024) investigated the impacts of climate change on the irrigation water requirements in the Lower Mahanadi Basin in India utilizing a CMIP6-based spatio-temporal analysis and future projections. They documented that the study region may experience more extreme weather events in the future, potentially leading to increased challenges in water management. They reported the importance of optimal water allocation and management scenarios to sustain agricultural activities in the study area.

As reviewed, climate change may pose significant challenges to agricultural productivity, global food security, and water resources (Reshmidevi et al. 2018). This highlights the urgency of the optimal cropping pattern and adaptive water-management strategies considering climate-change scenarios. Despite its great importance, limited studies have been conducted on this topic. In most of the related studies, such as those mentioned above, a holistic view that considers both natural (water) and human (farmer) resources considering the uncertainties (climate change) was not evident. Accordingly, there is still a great need for further research on this topic.

The objective of this study was to develop a framework for optimization of the cropping pattern in an agricultural region. The optimization procedure in the proposed framework was defined in such a way that the amount of agricultural water consumption was reduced while the farmer's revenue from the sale of agricultural products was increased. In the optimization model, several constraints regarding the available water resources, accessible cultivable areas, and food-security compliance for the indigenous people were considered.

Study area

Baft agriculture area is located in Kerman province in south-eastern Iran (Figure 1) with an area of over 6,494 km2 and an annual precipitation of 249.7 mm. According to Demarton's climate classification system, it has a semi-arid climate with average minimum and maximum temperatures of 2.4 and 24.7 °C, respectively (Table 1). In recent years, declining precipitation and rising air temperatures, along with long-term droughts, have created several challenges for agricultural activities and crop production in the region. Since in most parts of the region the surface water is fed by precipitation, in the hot seasons of the year the lack of precipitation has forced farmers to obtain the water they require by extracting groundwater through wells. This has, over time, reduced the groundwater levels dramatically and negated the water balance in most parts of the study area. In such situations, the optimization of cropping patterns (considering the effect of climate change) for the optimal use of existing water resources is necessary.
Table 1

Climate variables and specifications of Baft synoptic station

Station latitude/longitude 29.23°N/56.60°E 
Station altitude (MASL) 2,280 
Average annual precipitation (mm) 249.7 
Average minimum temperature (°C) 2.4 
Average maximum temperature (°C) 24.7 
Average real evapotranspiration (MCM) 108.8 
Station latitude/longitude 29.23°N/56.60°E 
Station altitude (MASL) 2,280 
Average annual precipitation (mm) 249.7 
Average minimum temperature (°C) 2.4 
Average maximum temperature (°C) 24.7 
Average real evapotranspiration (MCM) 108.8 
Figure 1

Location of the study area: Baft city in Iran.

Figure 1

Location of the study area: Baft city in Iran.

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In this study, a new framework was proposed for the optimization of the cropping pattern considering the effect of climate change. To investigate the effect of climate change and its future impacts, global climate models (GCMs) are the most appropriate tool (Rudraswamy & Umamahesh 2024). The GCM projections directly are not suitable for capturing climate at a local scale (Baft agricultural area) due to their coarse spatial resolutions (Anandhi et al. 2013). So, it is necessary to downscale the coarse GCM projections to a high-resolution scale that can characterize a representative condition (Tamang et al. 2023). In this study, the Long Ashton Research Station Weather Generator (LARS-WG) model (Semenov & Barrow 2002) as a stochastic weather generator was used to extract the local-scale future daily climate data from the selected GCMs (downscaling). To implement the LARS-WG model, the daily data in the base period, including the minimum and maximum temperatures, the precipitation, and the solar radiation, were used. These data were employed as the base-period climate and to simulate the future climate. The reproduced climate data were used as input to the CROPWAT model (Swennenhuis 2009) for estimating the irrigation water requirement of the study area and calculating the amount of agricultural water consumption. Next, a nonlinear optimization model was developed in LINGO to optimize the cropping pattern in the study area in such a way that while the farmer's revenue increases, the agricultural water consumption decreases. In the following sections, a brief introduction of the utilized models and the modelling procedure are provided.

Utilized models

LARS-WG: LARS-WG is a stochastic weather generator that can be used for the simulation of weather data under current and future climate conditions. These data are in the form of daily time-series, including the precipitation, maximum and minimum temperatures, and solar radiation. The first version of this model, LARS, was developed in Budapest in 1990, and a modified version (current version) of this weather generator, LARS-WG, was introduced in 2005. It is a robust model capable of generating synthetic weather data for a wide range of climates. It has been well validated in diverse climates around the world (Sha et al. 2019; Bayatvarkeshi et al. 2020; Ahmadi et al. 2021; Roushangar & Abdelzad 2023). The process of generating synthetic weather data includes three phases, namely, model calibration, model validation, and synthetic weather data generation. During the model calibration, the observed weather data are analysed to determine their statistical characteristics. In the model validation step, the statistical properties of the observed and synthetic weather data are analysed to specify if there are any statistically significant differences. In the final step, the parameters derived from the observed data during the calibration procedure are employed to produce synthetic data having similar statistical properties to the observed data but differing on a day-to-day basis. Synthetic data related to specific climate-change scenarios may also be produced based on GCMs, which have been used in the Sixth Assessment Report of the Intergovernmental Panel on Climate Change (Kikstra et al. 2022). In this study, the daily data of minimum temperature, maximum temperature, precipitation, and solar radiation in a 17-year statistical period from 2007 to 2023 have been used as the base-period data, and the prediction of these variables has been performed for the period of 2024–2054 under three IPCC emission scenarios, namely, A2, B1, and A1B. The A family of scenarios (here, A2 and A1B) describes a future world of very rapid economic growth, a global population that peaks in mid-century and declines thereafter, and the rapid introduction of new and more efficient technologies. The A1B is distinguished by its technological emphasis on a balance across all sources of energy. The B1 scenario family describes a convergent world with the same global population as in the A1 scenario but with rapid changes in economic structures towards a service and information economy, with reductions in material intensity and the introduction of clean and resource-efficient technologies. The emphasis is on global solutions to economic, social, and environmental sustainability, including improved equity, but without additional climate initiatives (IPCC 2000). The details of each scenario can be found in Kikstra et al. (2022). The LARS-WG weather generator has been widely used by many researchers (Mohebbi et al. 2024; Tikuye et al. 2024) because of its several advantages, e.g. it is computationally inexpensive, it provides climate scenarios that match the statistical properties of observed weather, and it furnishes daily-scale meteorological variables while preserving statistical interrelationships between variables.

CROPWAT: This is a decision support tool for the calculation of crop water requirements based on rainfall, crop, soil, and climate data. It was developed by the Land and Water Development Division of the Food and Agriculture Organization (FAO). This model can improve the computations of a scheme's water supply for different crop patterns under different irrigation schedules. Due to its simplicity and accuracy compared with other models, CROPWAT has been widely used and recommended by many researchers for estimating crop evapotranspiration, crop water requirement, irrigation water requirement, and irrigation scheduling (Mwanga et al. 2024; Niromand Fard et al. 2024; Yerli 2024).

CROPWAT uses the FAO Penman–Monteith equation (Equation (1)) for the calculation of the reference evapotranspiration (ETo), as follows:
(1)
where ETo is the reference evapotranspiration (mm day−1), Rn is the net radiation at the crop surface (MJ m−2 day−1), G is the soil heat flux density (MJ m−2 day−1), T is the air temperature at 2 m height (°C), U2 is the wind speed at 2 m height (m s−1), es is the saturation vapour pressure (kPa), ea is an actual vapour pressure (kPa), esea indicates saturation vapour pressure deficit (kPa), Δ indicates the slope vapour pressure curve (kPa °C−1), and γ is a psychrometric constant (kPa °C−1).

LINGO: The LINGO optimization model, developed by Lindo Systems Inc., is a comprehensive tool for efficiently building and solving a variety of linear, nonlinear, and integer optimization problems. It has a friendly environment for building and editing optimization models and a collection of fast built-in solvers. Also, it has several other prominent features, such as its high capability for modelling optimization problems, enjoying various mathematical, statistical, and stochastic functions, and the ability to read information from other files, including Excel (Tulett & Ke 2023). LINGO has a comprehensive language to facilitate all the optimization models in a wide range of engineering fields. Due to the mentioned advantages and features, it has been widely used and accepted in several optimization studies (Mirzaei et al. 2024; Shoaib et al. 2024; Zečević & Jevremović 2024).

Modelling procedure

This research was conducted in two periods, namely, the base period (2007–2023) and projecting years (2024–2054). The available data in the study area were from 2007, and the authors did not have access to older data. Accordingly, the year 2007 was considered the starting year of the base period. In addition, 30-year data are required when making decisions concerning future climate or for determining how the climate will change at a specific location (Scherrer et al. 2024). Accordingly, the future period was considered a 30-year period from 2024 to 2054. The 30-year (1993–2023) climate data (minimum and maximum temperatures, sunshine hours, wind speed, relative humidity, and rainfall) were obtained from the Iran Meteorological Organization. Using the base-period data, CROPWAT was used to estimate the crops' water requirements. The crops' phenology and growth-stage data were obtained from the Kerman Agricultural Research Center. The soil data were obtained from the Kerman Agricultural Jihad Organization. Also, the required data for the optimization model (the existing cropping pattern, the socioeconomic status of the region, the regional nutritional requirements, the crops' planting, cultivation and harvesting cost, the selling price of crops, and the amount of available water) were obtained from the Kerman Agricultural Jihad Organization and the Kerman Regional Water Authority. Using such data, the CROPWAT model calculates the crops' water requirement for the regional crops (wheat, barley, alfalfa, beans, and maize) and estimates the total irrigation water requirement in the study area. In this study, the surface irrigation efficiency was considered as 30% (Chaudhari et al. 2020). Then, an NLP model was programmed in LINGO to optimize the cropping pattern in such a way that while the farmers' profit from the selling of agricultural products increases, the water usage for irrigation of crops decreases. In the NLP model, the considered crops were selected from those that are already available in the region. The objective function in the optimization model was defined as follows:
(2)
where the variable i is related to each crop, as follows: wheat (i = 1), barley (i = 2), beans (i = 3), maize (i = 4), alfalfa (i = 5); t is the time period (t = 1, 2, …, 17; for 2007, 2008, … 2023, respectively); Ai,t is the crop area (ha) of crops in different years; CWi,t is the crop water requirement during the growing season (m3) in different years; and Ni,t is the net profit of each crop/hectare, which is different for each year and is derived from the following equation:
(3)
where Pi is the price of each crop, Yi,t is the yield per hectare (kg), and Ci is the cost of production of each crop/hectare. The constraints of the optimization model for this study were defined as follows:
(4)
(5)
(6)
(7)
(8)
(9)
(10)
These constraints (Equations (4)–(8)) were defined based on the farmers' strategy in the base period. For example, during the base period, the area under wheat cultivation was never less than 35% of the total area. This may have been due to several factors such as the region's nutritional needs and the desirability of wheat cultivation for farmers. Accordingly, a similar constraint (Equation (4)) was considered for the cultivated area of this crop. Equation (9) states that the total cultivation area devoted to the five crops (At) in the optimal cropping pattern should be equal to the total cultivation area devoted to the five crops in the nonoptimal (existing) cropping pattern. Figure 2 shows a framework of the modelling procedure in the base period.
Figure 2

Framework of the procedure for optimizing the cropping pattern in the base period in the study area.

Figure 2

Framework of the procedure for optimizing the cropping pattern in the base period in the study area.

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For the future period (2024–2054), the methodology was similar to the base period, except that the input data of the utilized models would be predicted. To this purpose, the meteorological variables were predicted using the LARS-WG by HadCM3 under the three IPCC emission scenarios of A2, B1, and A1B. Since the LARS-WG model could only predict four meteorological variables (minimum temperature, maximum temperature, precipitation, and sunshine hours) and the CROPWAT model requires the two further variables of relative humidity and wind speed to calculate the crop water requirement, an artificial neural network model was also used with three layers and seven neurons per layer to predict these two variables. For the future period, it was assumed that the productivity of each crop would remain at its highest value (the highest value seen in the base period), and the cost of production and the price of crop yield would increase annually by the average rate of annual inflation over the past ten years, according to Iranian Central Bank data. The objective function in this case was considered as Equations (1)–(9) as well, in which i = 1, 2, … , 5 (five crops) and t = 1, 2, … , 30 (30 years). These equations state that the total area under cultivation of the five crops should not exceed the total arable area of the region (76,100 ha). At is the total cultivation area of the five crops and equals 76,100. Figure 3 illustrates the framework of the modelling procedure for future periods.
Figure 3

Framework of the procedure for optimizing the cropping pattern in the future period in the study area.

Figure 3

Framework of the procedure for optimizing the cropping pattern in the future period in the study area.

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Calibrating results of the LARS-WG

Figure 4 shows the observed precipitation values compared with the predicted precipitation by LARS-WG. The left chart indicates the average precipitation values for each month. As seen, the highest precipitation occurred from January to March, which was in accordance with the predictions of the LARS-WG model. In addition, the lowest precipitation was observed in September, which was also very close to the prediction of the LARS-WG model. In other months as well, the predicted values by LARS-WG were in close agreement with the measured values at the meteorological station. This revealed that the LARS-WG model had relatively accurate predictions in all months, even in extreme values. The right chart demonstrates the observed precipitation values versus the simulated precipitation values by LARS-WG with a 45° bisector line. In this chart, the higher concentration of points around the 45° line indicates the higher accuracy of the predictions. As seen, the points are very close to the 45° line, which means that the LARS-WG model had significant accuracy in predicting the precipitation values. The values of the statistical indices (R2: coefficient of determination, RMSE: root mean square error, and MAE: mean absolute error) were obtained (R2 = 0.996, RMSE = 1.91, and MAE = 1.35), respectively, which confirms the excellent performance of LARS-WG in predicting the climate variables in the calibration process.
Figure 4

Comparison of observed and simulated precipitation in the base period; average values in each month (left), simulated versus predicted values on a 45° line (right).

Figure 4

Comparison of observed and simulated precipitation in the base period; average values in each month (left), simulated versus predicted values on a 45° line (right).

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After the successful calibration of LARS-WG, this model was employed for the prediction of meteorological data in the future period (2024–2054) under the three IPCC emission scenarios of A2, B1, and A1B. In Figure 5, the predicted values of the precipitation and the average minimum temperature are presented on a monthly scale. As seen, depending on which emission scenario is considered, the values of climatic variables (here, the precipitation and the average minimum temperature) may increase in some months or decrease in other months in the future compared with the base period. For example, in all three investigated emission scenarios, it is anticipated that the average precipitation in January and April will decrease in the future, but it will increase significantly in December and June (compared with the base period). This reveals that the trend of future changes in climatic variables will largely depend on the selected GCM emission scenario. Similar reports have been provided by other researchers as well (Kumari et al. 2024).
Figure 5

The long-term average precipitation (upper diagram) and minimum temperature (lower diagram) predicted by the LARS-WG model in the future period (2024–2054) under the three emission scenarios of A2, B1, and A1B versus the base period.

Figure 5

The long-term average precipitation (upper diagram) and minimum temperature (lower diagram) predicted by the LARS-WG model in the future period (2024–2054) under the three emission scenarios of A2, B1, and A1B versus the base period.

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Results of crops’ water requirement calculations

In this study, the water requirements of each crop in the region in both base and future periods were calculated for all the three IPCC emission scenarios of A2, A1B, and B1. The results showed that in all the investigated scenarios, the highest water requirement was for wheat and the least for bean. For the alfalfa, the highest water requirement was observed in June and the lowest in December. The reason for this is the decline of the precipitation in the study area during these months. For the bean and barley crops with the same planting and harvesting dates, the highest water requirement was observed in January and the lowest water requirement in April. Wheat had the highest water demand in June and the lowest water demand in November. Also, maize had the highest water demand in July and the lowest in September.

Optimal cropping pattern in the base period

This section presents the cultivation area of each crop in the optimal cropping pattern compared to the existing cropping pattern (the farmer's selected cropping pattern) from 2007 to 2023. By maximizing the objective function (Equation (2)), the NLP optimization model calculated the best cropping pattern to provide the highest revenue for the farmers while the least irrigation water is consumed. Figure 6 shows the selected cropping pattern by farmers (existing cropping pattern) versus the optimal cropping for two years, that is, 2011 and 2020, as an example. As shown, in the existing cropping pattern, alfalfa had the largest cropping area (38%, 52% of the total area) in 2011 and 2020, respectively, and wheat (35%, 35%), barley (13%, 13%), bean (13%, ∼0%), and maize (1%, ∼0%) had smaller cultivation areas correspondingly. In the optimal cropping pattern, the cultivation area in the same years for alfalfa (17%, 17%), wheat (45%, 37%), barley (35%, 43%), bean (2%, ∼0%), and maize (1%, 3%) was changed in such a way that each farmer's income was increased while less water was consumed. From the analysis, it was found that the optimization model tends to increase the cultivation area of barley and, by contrast, to decrease the cultivation area of alfalfa. It was concluded that, in the optimal cropping pattern, the cultivation area of plants that bring higher income to the farmer and consume relatively less water had been increased significantly. For example, in 2020, the area of alfalfa in the optimal cropping pattern was decreased by 35% while the area of barley was increased by 30% compared with the existing cropping pattern.
Figure 6

Cropping area in the existing cropping pattern (left) compared to the optimal cropping pattern (right) in the study area in the two years of 2011 and 2020.

Figure 6

Cropping area in the existing cropping pattern (left) compared to the optimal cropping pattern (right) in the study area in the two years of 2011 and 2020.

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Figure 7 shows the changes in cultivation area of each crop in different years of the base period. As shown, a constant trend was not observed during the different years. In fact, the optimum cultivation area of each crop depends on several factors, such as the climatic conditions, available water, production costs, crop yield, and the crop price. From the figure, the cultivation area of wheat, barley, and maize increased significantly in all years in the optimal cropping pattern compared with the existing cropping pattern, but for the two crops of bean and alfalfa, the changes in cultivation area were less.
Figure 7

Cropping area under the existing cropping pattern (yellow background) compared with the optimal cropping pattern (green background) for each crop in the base period (2007–2023).

Figure 7

Cropping area under the existing cropping pattern (yellow background) compared with the optimal cropping pattern (green background) for each crop in the base period (2007–2023).

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Farmers’ profit in the existing and optimal cropping patterns

Figure 8 shows the farmers' relative profit (profit earned in the optimal cropping pattern divided by profit earned in the existing cropping pattern) in the years of the base period. As shown, the profit of farmers in the optimal cropping pattern is on average 1.65 times more than in the existing cropping pattern in the base period. The highest relative profit was obtained in 2009 (green bar) and the lowest relative profit in 2020 (brown bar). This shows that if farmers follow the optimum cropping pattern, they will get more profit anyway. This result, which proves the importance of optimizing the cropping pattern in improving the economy of agricultural activities, has also been reported by Barati et al. (2020), Daghighi et al. (2017), and Darzi-Naftchali et al. (2024).
Figure 8

Comparison of the relative profit (profit in optimal cropping pattern/profit in existing cropping pattern) for the base period.

Figure 8

Comparison of the relative profit (profit in optimal cropping pattern/profit in existing cropping pattern) for the base period.

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Water consumption in the existing and optimal cropping patterns

Figure 9 illustrates the percentage of water savings in the optimal cropping pattern compared with the existing cropping pattern in the base period. It demonstrates that, for example, in 2019, by optimizing the cropping pattern, the agricultural water consumption decreased by 3.5% compared with the existing cropping pattern. As seen, in almost all the studied years, the water consumption was reduced by optimizing the cropping pattern, while the revenue of farmers significantly increased in the optimal cropping pattern. For example, in 2011, the volume of water used for irrigation of farmlands in the optimal cropping pattern decreased by 71.3 Mm3 compared with the existing cropping pattern, but the profits received by the farmer increased by 1.9 times. This indicates higher profits with less water consumption.
Figure 9

The percentage of water saving in the optimal cropping pattern compared with the existing cropping pattern in the base period: for example, in 2009, by optimizing the cropping pattern, agricultural water consumption decreased by 4.8% compared with the existing cropping pattern.

Figure 9

The percentage of water saving in the optimal cropping pattern compared with the existing cropping pattern in the base period: for example, in 2009, by optimizing the cropping pattern, agricultural water consumption decreased by 4.8% compared with the existing cropping pattern.

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Optimal cropping pattern in the future period

One of the main goals of this study was to suggest the optimal cropping pattern for future years considering climate-change conditions. Figure 10 demonstrates the cultivation area of each crop in the future years in the optimal cropping pattern. The results showed that the maize and bean crops have the least changes in the cultivation area in the future. The barley crop also has low fluctuations in its cultivation area. Most of the changes in the cultivation area were observed in alfalfa and wheat crops. This indicates that among the crops, alfalfa will be more profitable because it requires less water, and therefore, in the coming years, alfalfa will be one of the dominant crops in the region. Based on the results of the optimization model, in the future period, most of the agricultural lands should be devoted to the cultivation of three crops: alfalfa, wheat, and barley.
Figure 10

Cultivation area of each crop in the optimal cropping pattern in the future period predicted by the optimization model.

Figure 10

Cultivation area of each crop in the optimal cropping pattern in the future period predicted by the optimization model.

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Climate change has led to extreme pressure on water resources and agricultural activities in the world. Optimization of cropping patterns considering climate change is an essential step towards sustainable agriculture. The purpose of this study was to optimize the cropping pattern considering climate change to reduce agricultural water consumption as well as to improve the farmers' economic conditions in Baft agricultural area in Iran. For this purpose, after the identification of the dominant crops in the study area, the water requirement of each crop was predicted by the CROPWAT model through the FAO – Penman–Monteith method, and thereafter, the total volume of water used by farmers to irrigate the agricultural areas was calculated for both base and future climate-conditions. Next, regarding the yield, price, and production costs of the crops, the total gross profit earned by the farmers was calculated. The calculations were carried out for two periods: current (2007–2023) and future (2024–2054). For the future period, the CROPWAT input data was obtained by simulating the climatic parameters using HadCM3 under the three IPCC emission scenarios of A2, B1, and A1B. For the downscaling of GCM data, the LARS-WG statistical model was used. Finally, a nonlinear optimization model was developed in LINGO-20 to optimize the cropping pattern. In the optimal cropping pattern, the farmer can achieve more profit while consuming less water to irrigate the crops. The results indicated that by applying the optimal cropping pattern, the farmer's profit could be increased up to 1.65 times compared with the nonoptimal cropping pattern, while the amount of agricultural water consumption could be decreased by 5%. It should be noted that the assumptions and uncertainties in the utilized data and modelling procedure may impact model performance, so it is recommended that the sensitivity of the utilized models to such error sources be investigated in future studies. Future directions for this study include the utilization of comparative models such as the water evaluation and planning system for projecting the irrigation water requirements under different climate-change scenarios, the statistical downscaling model for assessing the local climate-change impacts, remote sensing and geographic information system for acquiring huge amounts of spatiotemporal crop data from satellite information, and evolutionary algorithms for efficient optimization of cropping patterns.

N.B. collected the data, designed the model, carried out the simulations, and prepared the original draft. N.S. conceived the original idea, reviewed the paper, and supervised the project. B.B. reviewed the paper and contributed to the interpretation of the results. M.R.M. proofread the paper, analysed the data, and contributed to the interpretation of the results. All authors reviewed the results and approved the final version of the paper.

All authors have given their consent to participate in this work.

All authors have given their permission to publish this work.

This work has not received any funding.

Data cannot be made publicly available; readers should contact the corresponding author for details.

The authors declare there is no conflict.

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