Next Article in Journal
Observed Trends of Climate and River Discharge in Mongolia’s Selenga Sub-Basin of the Lake Baikal Basin
Next Article in Special Issue
Estimation of River Management Flow Considering Stream Water Deficit Characteristics
Previous Article in Journal
Experimental Optimization of Gate-Opening Modes to Minimize Near-Field Vibrations in Hydropower Stations
Previous Article in Special Issue
Optimal Allocation of Water Resources from the “Wide-Mild Water Shortage” Perspective
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Article

Multiperiod Optimisation of Irrigated Crops under Different Conditions of Water Availability

by
Mathias Kuschel-Otárola
1,*,
Diego Rivera
1,2,
Eduardo Holzapfel
1,2,
Cristian D. Palma
3 and
Alex Godoy-Faúndez
2,3
1
Department of Water Resources, School of Agricultural Engineering, University of Concepción, Chillán 3812120, Chile
2
Water Research Center for Agriculture and Mining (CRHIAM), CONICYT/FONDAP-15130015, Chillán 3812120, Chile
3
Centro de Sustentabilidad y Gestión Estratégica de Recursos (CiSGER), Facultad de Ingeniería, Universidad del Desarrollo, 4040418 Concepción, Chile
*
Author to whom correspondence should be addressed.
Water 2018, 10(10), 1434; https://doi.org/10.3390/w10101434
Submission received: 10 August 2018 / Revised: 30 September 2018 / Accepted: 9 October 2018 / Published: 12 October 2018

Abstract

:
We propose a nonlinear optimisation model which maximises profits by resource allocation on a monthly time scale, considering a monthly crop yield model. The proposed model was applied to six management scenarios (two seasonal and four monthly), nine conditions of water availability, and two situations of resource availability under Chilean conditions. These situations provided the same seasonal amount of resources, but different distributions over time. The model included improvements in water resource management such as water storage and water transactions, being the latter a monthly decision variable that can increase farmers’ profits. According to our results, monthly scenarios gave high profits, even better with appropriate resource distribution. When water costs are high, water transactions allow loss reduction of up to 50%. Regarding labour, the lack of availability is more critical than the wages.

1. Introduction

Current world population is around 7.5 billion, but by 2025 there will be an expected nine billion people [1]. To feed this population, the worldwide irrigated area should increase in 30 M ha, with 40% higher water and energy demand for the next 20 years [2]. According to McMichael et al. [3], agriculture has depleted natural resources, contributing to water scarcity. To face this problem, strategies have been proposed such as increasing water use efficiency [4], desalination [5,6], water transactions [7,8], use of infrastructure for water storage [9,10], and optimisation of resources [11,12,13,14].
Optimisation assigns resources among competitive activities, subject to some restrictions and solved through mathematical algorithms [15]. In agriculture, optimisation has been employed for resource management, especially regarding water allocation and cropping patterns. Models have been developed in the literature to maximise profits by optimal cropping patterns. For example, Sethi et al. [16] considered groundwater management through linear programming to maximise profits. Mishra et al. [17] developed a multiobjective optimisation model to determine optimal cropping pattern and optimal size of an auxiliary storage reservoir. Fasakhodi et al. [18] used a multiobjective fractional goal programming method to find the optimal cropping pattern and sustain water availability. Ponce et al. [19] developed a nonlinear water supply model for analysing the economic impacts of changes in crop yields due to climate change. Su et al. [20] improved agricultural water use efficiency and the proportion of green water utilization by multiobjective optimisation. Das et al. [21] developed a menu-driven user friendly software based on a linear programming model for optimal land and water allocation. Tan et al. [22] developed a multiobjective fuzzy robust programming model for allocation of water and land resources and Varade and Patel [23] determined an optimal cropping pattern to maximise the net annual returns in order to conserve natural resources. On the other hand, there are researches that have included crop production functions that relate yield reduction as a result of the relative loss in evapotranspiration [24]. In these studies, the equation proposed by Doorenbos and Kassam [25,26,27,28] and polynomial regressions were considered [11,29,30]. Moreover, there are investigations which include multiperiod crop yield functions related to crop yield reduction as a result of the water stress at an intraseasonal timescale [31]. These studies considered the multiplicative approach of the equation proposed by Doorenbos and Kassam [25,32,33,34] and Jensen [13,35,36,37,38].
Considering the importance of sub-seasonal management in food production, we formed the following research question: What is the method to cope with seasonal changes, and how does variability affect profits for a given number of resources? None of the mentioned studies included a monthly optimisation model subject to monthly constraints, such as labour and capital (separately) and the possibility of including improvements in water resource management such as water transactions and water storage. Therefore, the principal objective was to develop and test nonlinear optimisation models at seasonal and monthly time scales and then compare them under Chilean conditions. This started with developing a monthly crop yield equation based on the multiperiod model proposed by Raes et al. [31] which depends mainly on crop features and sowing date. A monthly optimisation model allows adequate resource allocation due to monthly demand for labour and capital, often reported by technical-economic reports. Improvements in water resource management such as water storage and water transactions, are also monthly decision variables that can increase profits.

2. Methodology

Our proposed nonlinear optimisation model consists of an objective function which includes a monthly crop yield function and constraints on a monthly basis for resources. The objective is to maximise profits by the allocation of water and land to be cultivated on a monthly time scale.

2.1. Multiperiod Crop Yield Function

For planning with limited data availability, a simple equation was proposed by Doorenbos and Kassam [25], which describes crop yield reduction due to water scarcity:
1 - Y i Y m i = K y i 1 - E T a i E T c i
where i represents crop type. Y i and Y m i (in yield unit ha−1) are the actual and maximum crop yields, respectively. K y i is the yield response factor, which has been documented by Doorenbos and Kassam [25] for many crops at different stages and corresponds to the slope of the yield reduction due to a decrease of applied water (Figure 1a). E T a i and E T c i (both in mm) are the actual and crop evapotranspiration for the whole growing period, respectively. Later, Raes et al. [31] proposed a multiperiod crop yield equation at constant time scales smaller than growth periods.
Y i Y m i = k = 1 t 1 - K y i , s 1 - E T a i , k E T c i , k Δ t i , k / L i , s
where t is the number of periods, K y i , s is the yield response factor at growth stage s, E T a i , k and E T c i , k are the actual and crop evapotranspiration at time k; Δ t i , k is the length of time (in days) of each step during the growth stage s (1 if daily) and L i , s is the growth stage length (in days). Figure 1b represents the daily yield response to water [31] for maize, where relative yield stays constant when water demand is satisfied, and decreases when it is not. We propose modification to this equation for this research for monthly time steps, considering a parameter Δ t i , k * as an array which maintains the number of the days in each month while the crop is growing (instead of considering it as scalar); and L i , k * as a fit parameter when it compared to the relative yield at daily time step:
L i , k * = Δ t i , k * l n Y i , d Y i , k - 1 l n 1 - K y i , k 1 - E T a i , k E T c i , k
where Y i , d is the actual crop yield at day d which is equivalent to the difference of the last day of the month k, and the sowing day for the first month and the last day of each month for the following months while the crop is growing. For example, if the sowing and harvest day of crop i are 15 November and 3 March, respectively, d corresponds to 15 for November, 46 for December (15 + 31), 77 for January, 105 for February, and 108 for March (105 + 3). Finally, the monthly crop yield equation has the following form:
Y i Y m i = k = 1 t 1 - K y i , k 1 - E T a i , k E T c i , k Δ t i , k * / L i , k *
A comparison between the daily and monthly approach for maize is illustrated in Figure 1c. Here, yield reduction is due to seasonal water shortage as a function of time, showing that there are not significant differences between the approaches.

2.2. Optimisation of Irrigated Crops

The objective function to maximise has the following form:
M a x U = i = 1 n P i A i Y i - i = 1 n k = 1 t A i C i , k
where P i is the price per crop i (in US$ yield unit−1), A i is the area to be cultivated with crop i (in ha), and C i , k represents the production costs per unit area (in US$ ha−1). Some components of C i , k are [29]: labour and other costs such as seed, fertiliser and pesticides.
Thus, the complete form of the objective function is:
M a x U = i = 1 n P i A i Y m i k = 1 t 1 - K y i , k 1 - E T a i , k E T c i , k Δ t i , k * / L i , k * - L C i = 1 n k = 1 t A i N L i , k - i = 1 n k = 1 t A i O C i , k - W c r k = 1 t W r k - W c b k = 1 t V w b k + W c s k = 1 t V w s k
where L C is the labour cost (in US$ person-day−1), N L i , k is the labour needed per unit area (in person-day ha−1 month−1), O C i , k corresponds to other costs, and W r k is the amount of water rights in month k (in m3 month−1) with its respective cost ( W c r ) (in US$ m−3). If farmers have the possibility to buy water (to increase the area to be irrigated) and to sell water (when not using it), they can obtain higher profits. Therefore, the monthly amounts of water to buy ( V w b k ) and to sell ( V w s k ) are also included, with the corresponding costs to buy ( W c b ) and to sell ( W c s ) water (in US$ m−3).
Constraints of resources on a monthly basis are as follows:
  • Water availability: Assuming that the farmer has the infrastructure to store water at monthly scale ( R c m3 of capacity), available water is defined as:
    0 k = 1 k W r k + V w b k - 10 i = 1 n A i E T a i , k A E i + V w s k R c , k
    where A E i is the application efficiency of the irrigation system for crop i. It is important to mention that E T a i , k refers to the water contained in the soil after applied an initial volume of water E T a i , k / A E i , where there are losses due to irrigation system efficiency. This variable is multiplied by 10 for conversion to m3 per hectare.
  • Land availability: This constraint defines the area to be cultivated.
    i = 1 n A i A t
    where A t is the land availability (in ha).
  • Labour availability: Assuming that the labour availability can change for each month, this constraint is defined as:
    i = 1 n A i N L i , k L a k , k
    where L a k is the labour availability at month k (in person-d month−1).
  • Capital availability: Assuming that farmers can save money if it is not spent, the monthly capital availability is considered as:
    k = 1 k W c r · W r k + W c b · V w b k + L C i = 1 n A i N L i , k + i = 1 n A i O C i , k k = 1 k C a k , k
    where C a k is the economic capital availability at month k (in US$ month−1).
  • Crop area considerations: It is necessary to consider agricultural, market and productive diversity management criteria to restrict the maximum or minimum crop areas. This is due to marketing situations, rotations, or other agricultural limitations. These constraints are expressed as:
    m i n S i A i m a x S i , i
    where m i n S i and m a x S i are the minimum and maximum areas assigned to farm with crop i, respectively.
  • Complementary considerations: To force the crop water requirement to be zero when the cultivated area is also zero, the constraint is expressed as:
    K z · A i - k = 1 t E T a i , k 0 , i
    where K z is a positive constant ( K z = 10,000 mm ha−1). In order to not apply more water than required by the crop, the following constraint is also considered:
    E T a i , k E T c i , k , i , k
    Finally, there are non-negativity constraints expressed as:
    A i , E T a i , k , V w b k , V w s k 0

2.3. Case Study

Our proposed model was applied to conditions characteristic of the Central Valley of Chile (Figure 2). Annual mean precipitation for this area is about 1025 mm, and the average high and low temperatures are 20.6 and 7.6 °C, respectively [39]. This sector contains about 28% of the national crop production surface. Some of the most produced crops are wheat (34.3%), maize (11.6%), and sugar beets (6%), which contribute to the national planted surface with 27.9, 22.5, and 60%, respectively. On the other hand, fodder crops represent 6.1% of the regional cultivated area (11% national) [40], alfalfa being the most common, mainly destined to intensive dairy farming.

2.3.1. Model Inputs

In this research, alfalfa, maize, wheat, and sugar beets were the crops considered for the case study. Crop yield parameters ( K y and L) were extracted from the database of CROPWAT 8.0 [41,42]. Then, values were fitted to the study area according to crop sowing date, as recommended by Faiguenbaum [43]. This gave the monthly parameters of crop yield equations presented in Table 1. Price, costs, and maximum yield for each crop considered in Equation (6) (Table 2) were extracted from technical-economic reports from the Office of Agricultural Studies and Policies (ODEPA) and the National Institute of Agricultural Research (INIA). Prices were adjusted to May 2017 using the Consumer Price Index (CPI) calculator which is available on the National Statistics Institute (INE) website. A value of 575 Chilean Pesos (CLP) per US dollar $ was considered for this study as the long-term mean. Monthly water demand for each crop was determined using the ASCE Standardised Reference Evapotranspiration Equation [44]. Monthly water availability was estimated using streamflow data from distribution channels. Then, a decile analysis was carried out to assess different conditions of water availability. Deciles 1 and 9 represented the driest and wettest conditions, respectively.

2.3.2. Model Application

The model was applied to two situations that provided the same seasonal amount of resources (for labour and capital) but different distributions in time (Figure 3). The seasonal availability of resources (labour and capital) was the same for both situations, but its distribution differed. Moreover, the model was applied to six scenarios, and their features can be summarised as follows:
  • Scenario 1: Optimisation subject to seasonal constraints. This scenario assumes that resources are available for the season, but does not consider intraseasonal variability. In this scenario, for the whole growing period, only one value of K y and E T a for each crop i was considered. Water storage and water transactions were not considered.
  • Scenario 2: Optimisation subject to seasonal constraints. For the whole growing period, monthly values of K y and E T a for each crop i were considered. In this scenario, water storage and water transactions were not considered.
  • Scenario 3: Optimisation subject to monthly constraints, i.e., water and other resources availability at a monthly scale are considered. In this scenario, water storage and water transactions were not considered.
  • Scenario 4: Optimisation subject to monthly constraints with water transactions.
  • Scenario 5: Optimisation subject to monthly constraints with water storage.
  • Scenario 6: Optimisation subject to monthly constraints with water storage and transactions. This scenario is the most complete, considering all possible factors involved in the process.
A summary of the equations considered in the optimisation algorithm is presented in Table 3 for each scenario. Figure 4 summarises the aforementioned methodology, where parameters such as price received for crop and its maximum yield, monthly demand and supply of water, labour, and economic capital are available in the database. The six scenarios described above were assessed by the model proposed by Doorenbos and Kassam [25] for scenario 1, and by the monthly proposed crop yield equation (scenarios 2 through 6), subject to seasonal constraints (scenarios 1 and 2), and monthly constraints (scenarios 3 through 6).
The model was run using the General Algebraic Modelling System (GAMS) [48] software, Version 24.7, and solved with the CONOPT 3 solver.
For implementation of the six scenarios, the following values were considered:
For the whole scenarios, A t was 25 ha, W c r was 0.0016 US$ m−3, and L C was 20 US$ person-day−1 [47]. In this study, it was considered that alfalfa, maize, and sugar beet were watered by sprinklers ( A E i = 0.75) and wheat by furrow ( A E i = 0.60). For scenario 1, K y i values of 1.00, 1.25, 1.15, and 1.10 were considered for alfalfa, maize, wheat, and sugar beet, respectively, according to the recommended values by Doorenbos and Kassam [25] (Figure 1a). For scenarios 2 through 6, the values considered are shown in Table 1. For scenarios where water transactions were considered (4 and 6), W c b and W c s corresponded to 0.0018 and 0.0014 US$ m−3, respectively. On the other hand, for scenarios where water storage was considered (5 and 6), R c assumed a value of 30,000 m3.
On the other hand, the same amount of resource availability (labour and capital) was considered for both situations, but at different distributions in time, where labour and capital availability was 300 person-days and 80,000 US$, respectively.
To test the effectiveness of the optimisation model once it reached an optimum irrigated cropping pattern and water allocation, a sensitivity analysis was conducted. This analysis included scenario 1 and 6. The sixth scenario was evaluated considering both situations of resource distribution (a and b) (Figure 3). The analysis was conducted considering land, labour, capital, and mean water availability (25 ha, 300 person-d, 80,000 US$, and 357,334 m3 for the whole season, respectively). The analysis tested the variation in profits by changing export prices, crop area, irrigation systems, water and labour costs, labour availability and other costs, as well as capital availability.

3. Results and Discussion

3.1. Seasonal Use of Resources and Profits

Seasonal use of resources and profits are presented in the form of radar charts (Figures 6 and 7) in which each axis corresponds to a decile of a probability (DI) of water availability for each scenario. Each ring represents a resource index, organised as follows (from inside to outside): Land, water, labour, capital used, and profit (Figure 5). These resources were relativized to consider an index number from 0 to 1, and this was carried out in the following manner: (1) For land used, an index of 1 was considered to represent 25 ha of land, which is the available resource for this case study. (2) For water used, an index of 1 depended on the seasonal amount of water of every decile. (3) For labour used, an index of 1 was considered to represent the whole labour availability (300 person-day) distributed at monthly time scales. (4) For capital used, an index of 1 was considered to represent the whole capital availability (80,000 US$) also distributed at monthly time scales. (5) For profit, an index of 1 was considered to represent the maximum profit obtained from the runs (46,269 US$).

3.1.1. Situation a

Figure 6 shows profits and seasonal use of resources at situation a. Scenarios 1 and 2 present the highest profits because these scenarios are subject to seasonal constraints, i.e., it is not relevant how resources are divided up in time. In these scenarios, restrictions are scalars instead of arrays, in contrast to monthly scenarios (3, 4, 5, and 6). Water is the limiting resource for these scenarios in decile 1, while capital from decile 2. The third scenario is subject to monthly constraints, and the higher the water supply, the higher the profits. In the fourth scenario, which considers water transactions, the area to be sowed does not increase as water supply increase, because of being limited mainly the labour availability in September, October, and March (Figure 10). Under the fifth scenario, which considers water storage, a similar behaviour is presented as in scenario 3, showing slightly greater profits, but lower than the fourth scenario, which includes water transactions. According to Arnell [49], De Vries and Weatherhead [50], Luo et al. [51], Xu et al. [52], water markets are regarded as an effective way for improving water-use benefits. The sixth scenario, which factors in both improvements in water resources management (water transactions and water storage) shows greater profits than the fifth scenario because it includes water markets.

3.1.2. Situation b

Figure 7 shows profits and seasonal use of resources under situation b. Scenarios 1 and 2 present the same values as situation a. As mentioned before, because these scenarios are subject to seasonal constraints, it is not relevant how resources are divided over time. Regarding the third and fifth scenarios, more water availability means the higher the area to sow, water, labour, and capital used, as well as profits. As far as the fourth and sixth scenarios, profits are as high as seasonal scenarios (1 and 2) and in some cases, even better (in decile 1). Due to capital limitations, profits do not increase, in spite of having the chance to buy, sell, and store water. Carvallo et al. [29] found that by reducing labour availability, profits were affected by almost 5%, compared to their optimum cropping pattern.

3.2. Crop Allocation

Figure 8 and Figure 9 show the crop allocation suggested by the runs to obtain the highest profit.

3.2.1. Situation a

Figure 8 shows crop allocation for situation a. Scenarios 1 and 2 present the same results, sowing only sugar beet is the best choice, which requires low labour but high capital (Figure 3). Regarding the third and fifth scenario, sowing maize is the best choice for the first four deciles due to the low water availability and the sowing date of this crop (1 November). From decile 5, there is enough water in September, the month when sugar beet starts to grow. From the sixth decile, the area to plant with sugar beet continues to increase and the area to sow with alfalfa appears as an option, being a better choice than maize because this crop demands less capital (Figure 3). On the other hand, in the fourth and sixth scenarios, sugar beet is the main crop suggested because there is enough water for irrigation.

3.2.2. Situation b

Figure 9 shows crop allocation for situation b. Scenarios 1 and 2 present the same results as situation a. In the third and fifth scenarios, there is not enough water before decile 5. Compared to the situation a, there is lower labour availability in November, the month when maize could be sowed (Figure 3). However, after decile 5, there is enough water to irrigate sugar beet. As far as the fourth and sixth scenarios, sugar beet is the only suggested crop because of the possibility of having more water (water transactions and water storage).

3.3. Monthly Limiting Resource

Figure 10 and Figure 11 present resource availability for each month in order to find the monthly limiting resource. Labour and capital are relativized to consider an index number from 0 to 1. An index of 1 is used to represent the labour (300 person-day) and capital availability (80,000 US$). However, water availability indices depend on different scenarios. Regarding the third scenario which does not consider improvements in water resource management, an index of 1 represents the seasonal amount of water for every decile. For the fourth scenario, an index of 1 is considered to represent the maximum difference between income (water rights and water to buy) and outcome fluxes (water applied and water to sell). Regarding the last two scenarios, an index of 1 is considered to represent the maximum capacity of the reservoir (30,000 m3).

3.3.1. Situation a

Figure 10 shows the monthly limiting resource presented as water, labour, and capital availability for situation a. Regarding the third scenario, which does not consider improvements in water resource management, water is the limiting resource in September for the first four deciles of water supply. For this reason, the model does not recommend establishing sugar beet. Also, during September, October, and March labour is the limiting resource for the most deciles of water supply.

3.3.2. Situation b

Figure 11 shows the monthly limiting resources presented as water, labour, and capital availability under situation b. In the third scenario, water is a limiting resource for the first four deciles of water supply. On the other hand, labour is also a limiting resource after October (as well as in scenarios 4, 5, and 6), which is a reason not to sow maize in this scenario (Figure 3). Analysing the capital, this resource is limiting for decile 9. For the fourth scenario, which considers water transactions, water and capital are limiting resources. The water constraint equation (Table 3), does not consider storage. Regarding the fifth scenario, which factors in water storage, water is the limiting resource in September. Moreover, starting from decile 4, water availability increases due to the capacity to store water; but because of the labour constraints, it is not feasible to increase profits. Regarding the sixth scenario, capital is the limiting resource. Therefore, under this scenario, profits do not increment in spite of higher water availability.

3.4. Sensitivity Analysis

Sensitivity analysis was carried out to test the proposed optimisation model. This analysis included the first (seasonal) and the sixth scenario (the monthly scenario which considers water transactions and storage). This latter was assessed by both situations of resource distribution (a and b).

3.4.1. Scenario 1

Table 4 shows the sensitivity analysis for the scenario 1. The best profit, according to the local conditions, corresponds to 45,917 US$, allocating only sugar beet. Under this regime, capital is the limiting resource. Changes in export prices do not affect profits when maize and wheat decrease and increase their values, respectively. A reduction of 50% in the export price of sugar beet means that the farmer must only establish maize. Consequently, profits reduce by about 42%. An increase of 50% in the export price of alfalfa means that this crop and sugar beet share the available land, raising profits by 13%. When the crop area consideration is taken into account, all crops share the available area. Although profits are reduced by 9%, it is recommended to sow more than one crop due to marketing, rotations, or other agricultural limitations [21,23,26,27,29,30,36,53]. By changing the irrigation system, i.e., sugar beet irrigated by furrow (AE = 0.60) instead of sprinkler (AE = 0.75), and wheat by sprinkler instead of furrow, profits are not affected due to that the model still suggests establish only sugar beet. Moreover, water is not the limiting resource, but capital. Consequently, water use increases by 25%. An increase in water costs means that profits are reduced by almost 60%. Here, the model recommends sowing only sugar beet. In this case, improvements in water resource management such as water transactions [7,8] and water storage [9,10] can be useful to mitigate this problem. An increase in labour costs does not considerably affect profits (4%) in comparison to the lack of labour availability. The latter reduces profits by 17%. Therefore, according to Carvallo et al. [29], it is recommended to increase wages to avoid the lack of labour availability. Changes in other costs do not considerably affect profits when maize and wheat increase and decrease their values, respectively. An increment of 50% in the values for sugar beet means that the farmer sows only maize. Consequently, profits are reduced by about 43%. The same response happens when export prices for this crop decrease in 50%. A reduction of 50% in the export price for alfalfa means that this crop and sugar beet share the available land, raising profits by 10%. A decrease in capital availability reduces profits by more than 50%. For this reason, the model suggests sowing only sugar beet when capital is the limiting resource.

3.4.2. Scenario 6, Situation a

Sensitivity analysis for scenario 6, considering the distribution of resources for situation a is presented in Table 5. According to local conditions, the best choice is to allocate 3, 4, and 6 ha of alfalfa, maize, and sugar beet, respectively, resulting in profits of 18,754 US$. Changes in export prices considerably affect profits; sugar beet decreases its value by 50%, and consequently, profits are reduced by 85%. A decrease of 50% in the export price for maize means that alfalfa and sugar beet should be sowed, decreasing profits by almost 9%. When alfalfa price increases by 50%, this situation involves planting the same cropping pattern as the previous situation (reduction of 50% in the export price for maize) but profits increase by almost 20%. The reason is that the price of one of the recommended crops (alfalfa) increases, despite having the same resources consumption. When crop area is taken into account, all crops share the available area, but as a result, profits are reduced by 12%. By changing the irrigation system, profits are not considerably affected. Water use, however, increases by 12%. When water costs are high, profits are reduced by 33%. As mentioned before, an increase in labour costs does not considerably affect profits (6%) in comparison to the lack of labour availability (67%). Changes in other costs do not considerably affect profits when maize and wheat increase and decrease their values, respectively. A 50% increment of this value for sugar beet suggests that the farmer only sows 10 ha of maize, reducing profits by 44%. A 50% reduction in the export price of alfalfa leads to a rise in profits of 10%. When capital availability decreases by 50%, profits are reduced by nearly 12%. In this case, the model suggests sowing 3 and 6 ha of alfalfa and sugar beets, respectively.

3.4.3. Scenario 6, Situation b

Table 6 shows the sensitivity analysis for scenario 6, considering the resources distribution for situation b. The best profits, according to the local conditions are 46,177 US$, 0.57% higher than the seasonal scenario and 146% higher than the situation a. The latter is due to the monthly distribution of resources. According to the resource distribution of labour and capital, sugar beet is the only feasible crop to be sowed. Therefore, a reduction of 50% in the export price of this crop results in no positive returns due to costs of water rights, which farmers must pay if they use them or not. When crop area is taken into account, the model suggests establishing a minimum of 3 ha of each crop, reducing profits by 84%. However, this is an infeasible solution; sugar beet is the only feasible crop to be established for this situation of resource distribution. When water costs are high, profits decrease by 30%. That is only 50% compared to scenario 1, which does not consider water transactions. An increment of labour costs does not considerably affect profits (5%) in comparison to the lack of labour availability (18%). On the other hand, if other costs of sugar beet increase by 50%, profits decrease by almost 90%. As in the first scenario, a decrease in capital availability reduces profits by more than 50%.

4. Conclusions

We developed a monthly optimisation model to obtain an optimum cropping pattern and monthly water allocation for irrigated agriculture under Chilean conditions. The objective function included a monthly crop yield model, which was developed from the Raes et al. [31] equation, being a valid alternative for handling resources on a monthly timescale. This model also included monthly water transactions as a decision variable (besides cropping pattern and monthly water allocation for crops), giving the possibility to farmers to buy water (to increase the irrigated area) and to sell water (when not using it) to improve their profits. Regarding our results, optimizing resources on a monthly basis attained higher profits as it allowed farmers to tailor their management practices and manage costs to cope with less available resources.
Scenarios based on single run optimisation at the beginning of the season assume that how resources are distributed in time is not significant, or that resources will be available. However, this approach does not account for intraseasonal changes. Thus, in seasonal-based scenarios, water is the limiting resource when available water is less than the requirements for the whole season. In the studied monthly scenarios, which include improvements in water resource management (such as water transactions and water storage), the model not only attains higher profits (even better than the seasonal approaches), but also decreases uncertainty and improves risk management. The main advantage of considering a multiperiod model is that is the best option for coping with seasonal changes because income is received from crop production and water transactions. When water transactions are taken into account, labour is the main limiting resource. According to sensitivity analysis, it is not always feasible to consider crop area criteria due to resource distribution (Table 6). On the other hand, when water costs are high, water transactions could reduce losses by up to 50%. As far as labour, the lack of availability is more critical than wages. Future studies should focus on the estimation of the yield response factor ( K y ) under local conditions in order to include them in the proposed monthly optimisation model.
Seasonal scenarios for crop management are highly beneficial because they consider that certain resources are only available at the start of the season (the timescale “growing season” is longer than monthly). On the other hand, monthly scenarios increase profits when they consider improvements in water resource management, such as water transactions and water storage.

Author Contributions

Conceptualization, M.K.-O., D.R., E.H., C.D.P. and A.G.-F.; Data curation, M.K.-O., D.R. and E.H.; Formal analysis, M.K.-O.; Investigation, M.K.-O., D.R., E.H., C.D.P. and A.G.-F.; Methodology, M.K.-O., D.R., E.H. and C.D.P.; Software, M.K.-O.; Supervision, D.R., E.H., C.D.P. and A.G.-F.; Visualization, M.K.-O.; Writing—original draft, M.K.-O.

Funding

The research leading to this report was supported by the National Commission for Scientific and Technological Research (CONICYT) through CONICYT-PCHA/National Doctorate/2015-21150463, the project FONDAP 15130015: Water Research Center for Agriculture and Mining (CRHIAM) and FONDECYT 1160656: Hillslope Water Storage And Runoff Processes: Linking Climate Variability And Interannual Storage.

Acknowledgments

Authors thank the project FONDAP 15130015: Water Research Center for Agriculture and Mining (CRHIAM) and the Laboratory of Investigation and Technologies to the Water Management in the Agriculture (ItecMA2). Special thanks to GAMS Technical Support for all the constructive suggestions.

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. Al-Ansari, T.; Korre, A.; Shah, N. Integrated modelling of the energy, water and food nexus to enhance the environmental performance of food production systems. In Proceedings of the 9th International Conference on Life Cycle Assessment in the Agri-Food Sector (LCA Food 2014), San Francisco, CA, USA, 8–10 October 2014; pp. 1–10. [Google Scholar]
  2. FAO; IFAD; WFP. The State of Food Insecurity in the World 2015. Meeting the 2015 International Hunger Targets: Taking Stock of Uneven Progress; FAO: Rome, Italy, 2015. [Google Scholar]
  3. McMichael, A.J.; Powles, J.W.; Butler, C.D.; Uauy, R. Food, livestock production, energy, climate change and health. Lancet 2007, 370, 1253–1263. [Google Scholar] [CrossRef]
  4. Gohari, A.; Mirchi, A.; Madani, K. System dynamics evaluation of climate change adaption strategies for water resources management in central Iran. Water Resour. Manag. 2017, 31, 1413–1434. [Google Scholar] [CrossRef]
  5. Assouline, S.; Russo, D.; Silber, A.; Or, D. Balancing water scarcity and quality for sustainable irrigated agriculture. Water Resour. Res. 2015, 51, 3419–3436. [Google Scholar] [CrossRef] [Green Version]
  6. Harmancioglu, N. Overview of water policy developments pre- and post- 2015 development agenda. Water Resour. Manag. 2017, 31, 3001–3021. [Google Scholar] [CrossRef]
  7. Garrick, D.; Siebentritt, M.; Aylward, B.; Bauer, C.; Purkey, A. Water markets and freshwater ecosystem services: Policy reform and implementation in the Columbia and Murray-Darling Basins. Ecol. Econ. 2009, 69, 366–379. [Google Scholar] [CrossRef]
  8. Erfani, T.; Binions, O.; Harou, J.J. Simulating water markets with transaction costs. Water Resour. Res. 2014, 50, 4726–4745. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  9. Cosgrove, W.J.; Loucks, D.P. Water management: Current and future challenges and research directions. Water Resour. Res. 2015, 51, 4823–4839. [Google Scholar] [CrossRef] [Green Version]
  10. Iglesias, A.; Sánchez, B.; Garrote, L.; López, I. Towards adaptation to climate change: Water for rice in the coastal wetlands of Doñana, souther Spain. Water Resour. Manag. 2017, 31, 629–653. [Google Scholar] [CrossRef]
  11. Maneta, M.P.; Torres, M.O.; Wallender, W.W.; Vosti, S.; Howitt, R.; Rodrigues, L.; Bassoi, L.H.; Panday, S. A spatially distributed hydroeconomic model to assess the effects of drought on land use, farm profits, and agricultural employment. Water Resour. Res. 2009, 45. [Google Scholar] [CrossRef]
  12. Liu, D.; Chen, X.; Lou, Z. A Model for the Optimal Allocation of Water Resources in a Saltwater Intrusion Area: A Case Study in Pearl River Delta in China. Water Resour. Manag. 2010, 24, 63–81. [Google Scholar] [CrossRef]
  13. Homayounfar, M.; Lai, S.; Zomorodian, M.; Sepaskhah, A.; Ganji, A. Optimal crop water allocation in case of drought occurrence, imposing deficit irrigation with proportional cutback constraint. Water Resour. Manag. 2014, 28, 3207–3225. [Google Scholar] [CrossRef]
  14. Zhu, T.; Marques, G.F.; Lund, J.R. Hydroeconomic optimization of integrated water management and transfers under stochastic surface water supply. Water Resour. Res. 2015, 51, 3568–3587. [Google Scholar] [CrossRef] [Green Version]
  15. Hillier, F.; Lieberman, G. Introduction to Operations Research; McGraw Hill: New York, NY, USA, 2001. [Google Scholar]
  16. Sethi, L.; Kumar, D.; Panda, S.; Mal, B. Optimal crop planning and conjuctive use of water resources in a Coastal river basin. Water Resour. Manag. 2002, 16, 145–169. [Google Scholar] [CrossRef]
  17. Mishra, A.; Adhikary, A.; Panda, S. Optimal size of auxiliary storage reservoir for rainwater harvesting and better crop planning in a minor irrigation project. Water Resour. Manag. 2009, 23, 265–288. [Google Scholar] [CrossRef]
  18. Fasakhodi, A.; Nouri, S.; Amini, M. Water resources sustainability and optimal cropping pattern in farming systems: A multi-objective fractional goal programming approach. Water Resour. Manag. 2010, 24, 4639–4657. [Google Scholar] [CrossRef]
  19. Ponce, R.; Blanco, M.; Giupponi, C. The economic impacts of climate change on the chilean agricultural sector: A non-linear agricultural supply model. Chil. J. Agric. Res. 2014, 74, 404–412. [Google Scholar] [CrossRef]
  20. Su, X.; Li, J.; Singh, V. Optimal Allocation of Agricultural Water Resources Based on Virtual Water Subdivision in Shiyang River Basin. Water Resour. Manag. 2014, 28, 2243–2257. [Google Scholar] [CrossRef]
  21. Das, B.; Singh, A.; Panda, S.; Yasuda, H. Optimal land and water resources allocation policies for sustainable irrigated agriculture. Land Use Policy 2015, 42, 527–537. [Google Scholar] [CrossRef]
  22. Tan, Q.; Zhang, S.; Li, R. Optimal use of agricultural water and land resources through reconfiguring crop planting structure under socioeconomic and ecological objectives. Water 2017, 9, 488. [Google Scholar] [CrossRef]
  23. Varade, S.; Patel, J. Determination of Optimum Cropping Pattern Using Advanced Optimization Algorithms. J. Hydrol. Eng. 2018, 23, 05018010. [Google Scholar] [CrossRef]
  24. Steduto, P.; Hsiao, T.; Fereres, E.; Raes, D. Crop Yield Response to Water. FAO Irrigation and Drainage Paper 66; Food and Agriculture Organization of the United Nations: Rome, Italy, 2012; p. 503. [Google Scholar]
  25. Doorenbos, J.; Kassam, A. Yield Response to Water; FAO: Rome, Italy, 1979. [Google Scholar]
  26. Mainuddin, M.; Das Gupta, A.; Raj Onta, P. Optimal crop planning model for an existing groundwater irrigation project in Thailand. Agric. Water Manag. 1997, 33, 43–62. [Google Scholar] [CrossRef]
  27. Prasad, A.S.; Umamahesh, N.V.; Viswanath, G.K. Optimal irrigation planning under water scarcity. J. Irrig. Drain. Eng. 2006, 132, 228–237. [Google Scholar] [CrossRef]
  28. Banihabib, M.; Zahraei, A.; Eslamian, S. Dynamic programming model for the system of a non-uniform deficit irrigation and reservoir. Irrig. Drain. 2017, 66, 71–81. [Google Scholar] [CrossRef]
  29. Carvallo, H.; Holzapfel, E.; López, M.; Mariño, M. Irrigated cropping optimization. J. Irrig. Drain. Eng. 1998, 124, 67–72. [Google Scholar] [CrossRef]
  30. Singh, A. Optimal Allocation of Resources for the Maximization of Net Agricultural Return. J. Irrig. Drain. Eng. 2012, 138, 830–836. [Google Scholar] [CrossRef]
  31. Raes, D.; Geerts, S.; Kipkorir, E.; Wellens, J.; Sahli, A. Simulation of yield decline as a result of water stress with a robust soil water balance model. Agric. Water Manag. 2006, 81, 335–357. [Google Scholar] [CrossRef]
  32. Karamouz, M.; Zahraie, B.; Kerachian, R.; Eslami, A. Crop pattern and conjuctive use management: A case study. Irrig. Drain. 2010, 59, 161–173. [Google Scholar] [CrossRef]
  33. Moghaddasi, M.; Araghinejad, S.; Morid, S. Long-term operation of irrigation dams considering variable demands: case study of Zayandeh-rud reservoir, Iran. J. Irrig. Drain. Eng. 2010, 136, 309–316. [Google Scholar] [CrossRef]
  34. Garg, K.; Dadhich, S. Integrated non-linear model for optimal cropping pattern and irrigation scheduling under deficit irrigation. Agric. Water Manag. 2014, 140, 1–13. [Google Scholar] [CrossRef]
  35. Jensen, M. Water consumption by agricultural plants. In Water Deficits in Plant Growth; Academic, P., Kozlowski, T., Eds.; Academic Press: New York, NY, USA, 1968; Chapter 1; pp. 1–22. [Google Scholar]
  36. Kipkorir, E.; Sahli, A.; Raes, D. MIOS: A decision tool for determination of optimal irrigated cropping pattern of a multicrop system under water scarcity constraints. Irrig. Drain. 2002, 51, 155–166. [Google Scholar] [CrossRef]
  37. Sadati, S.; Speelman, S.; Sabouhi, M.; Gitizadeh, M.; Ghahraman, B. Optimal irrigation water allocation using a genetic algorithm under various weather conditions. Water 2014, 6, 3068–3084. [Google Scholar] [CrossRef] [Green Version]
  38. Zhang, D.; Guo, P. Integrated agriculture water management optimization model for water saving potential analysis. Agric. Water Manag. 2016, 170, 5–19. [Google Scholar] [CrossRef]
  39. DGA. Diagnóstico y Clasificación de los Cursos y Cuerpos de agua Según Objetivo y Calidad; Cuenca del río Itata.: Santiago, Chile, 2004. [Google Scholar]
  40. ODEPA. Región del Biobío: Información Regional 2018; Technical Report; Oficina de Estudios y Políticas Agrarias (ODEPA): Santiago, Chile, 2018.
  41. FAO. “CROPWAT 8.0” Databases and Software; FAO: Rome, Italy, 2017. [Google Scholar]
  42. Allen, R.G.; Pereira, L.S.; Raes, D.; Smith, M. Crop Evapotranspiration: Guidelines for Computing Crop Water Requirements; FAO: Rome, Italy, 1998; Volume 300. [Google Scholar]
  43. Faiguenbaum, H. Labranza, Siembra y Producción de los Principales Cultivos de Chile; Vivaldi y Asociados: Santiago, Chile, 2003; p. 760. [Google Scholar]
  44. Allen, R.G.; Walter, I.A.; Elliott, R.; Itenfisu, D.; Brown, P.; Jensen, M.E.; Mecham, B.; Howell, T.A.; Snyder, R.; Eching, S.; Spofford, T. Task Committee on Standardization of Reference Evapotranspiration; ASCE: Reston, VA, USA, 2005. [Google Scholar]
  45. INIA. Antecedentes Económicos de la Producción de Forrajes en Suelos Regados de la VIII Región; Technical Report; Instituto de Investigaciones Agropecuarias (INIA): Santiago, Chile, 2005. [Google Scholar]
  46. ODEPA. Boletin de Cereales; Technical Report; Oficina de Estudios y Políticas Agrarias (ODEPA): Santiago, Chile, 2017.
  47. ODEPA. Estudio: Identificación y Análisis del Impacto Económico del uso de Variedades y/o Híbridos Transgénicos de Maíz (Zea mays), Raps (Brassica Napus) y Remolacha (Beta Vulgaris), para los Agricultores en Chile: Informe Final; Technical report; Oficina de Estudios y Políticas Agrarias (ODEPA): Santiago, Chile, 2011.
  48. Brooke, A.; Kendrick, D.; Meeraus, A.; Raman, R. GAMS User’s Guide; The Scientific Press: Washington, DC, USA, 2014. [Google Scholar]
  49. Arnell, N. Climate change and global water resources: Sres emissions and socio-economics scenarios. Glob. Environ. Chang. 2004, 14, 31–52. [Google Scholar] [CrossRef]
  50. De Vries, T.; Weatherhead, E. Adapting to irrigation water scarcity due to climate changes in eastern England. Impacts of global climate change. In World Water and Environmental Resources Congress; ASCE: Reston, VA, USA, 2005; pp. 1–6. [Google Scholar]
  51. Luo, B.; Maqsood, I.; Gong, Y. Modeling climate change impacts on water trading. Sci. Total Environ. 2010, 408, 2034–2041. [Google Scholar] [CrossRef] [PubMed]
  52. Xu, T.; Zheng, H.; Liu, Y.; Wang, Z. Assessment of the water market in the Xiying irrigation district, Shiyang River Basin, China. Water Resour. Plan. Manag. 2016, 142, 04016021. [Google Scholar] [CrossRef]
  53. Singh, A. Land and water management planning for increasing farm income in irrigated dry areas. Land Use Policy 2015, 42, 244–250. [Google Scholar] [CrossRef]
Figure 1. Representation of crop yield reduction, where (a) is the seasonal crop yield reduction function proposed by Doorenbos and Kassam [25] where K y is the slope; (b) is the daily crop yield reduction for maize proposed by Raes et al. [31] where relative yield stays constant when the water demand is satisfied and decreases when it is not; and (c) represents daily and monthly approaches for maize.
Figure 1. Representation of crop yield reduction, where (a) is the seasonal crop yield reduction function proposed by Doorenbos and Kassam [25] where K y is the slope; (b) is the daily crop yield reduction for maize proposed by Raes et al. [31] where relative yield stays constant when the water demand is satisfied and decreases when it is not; and (c) represents daily and monthly approaches for maize.
Water 10 01434 g001
Figure 2. Study area location. The right-bottom panel shows available water based on streamflow records of a distribution channel.
Figure 2. Study area location. The right-bottom panel shows available water based on streamflow records of a distribution channel.
Water 10 01434 g002
Figure 3. Monthly demand and supply of resources using collated data. Deciles 1 and 9 are the driest and the wettest conditions, respectively. Distribution of labour and capital are provided by the situation a (black bar) and b (white bar). Seasonal amount of labour and capital availability is 300 person-day and 80,000 US$, respectively. See ODEPA [46], ODEPA [47], and INIA [45] for more detailed sources of information.
Figure 3. Monthly demand and supply of resources using collated data. Deciles 1 and 9 are the driest and the wettest conditions, respectively. Distribution of labour and capital are provided by the situation a (black bar) and b (white bar). Seasonal amount of labour and capital availability is 300 person-day and 80,000 US$, respectively. See ODEPA [46], ODEPA [47], and INIA [45] for more detailed sources of information.
Water 10 01434 g003
Figure 4. Methodology used for this research. The six scenarios were assessed by two situations of time and resource distribution.
Figure 4. Methodology used for this research. The six scenarios were assessed by two situations of time and resource distribution.
Water 10 01434 g004
Figure 5. Interpretation of radar plots (Figures 6 and 7) showing profits and seasonal use of resources for each scenario at a situation of resource distribution. Each ring represents a resource index organised as follows (from inside to outside): Land, water, labour and capital used, and profit; each slice corresponds to a decile of water availability (DI).
Figure 5. Interpretation of radar plots (Figures 6 and 7) showing profits and seasonal use of resources for each scenario at a situation of resource distribution. Each ring represents a resource index organised as follows (from inside to outside): Land, water, labour and capital used, and profit; each slice corresponds to a decile of water availability (DI).
Water 10 01434 g005
Figure 6. Profits and seasonal use of resources obtained from the optimisation process for each scenario at situation a. Each ring represents a resource index organised as follows (from inside to outside): Land, water, labour and capital used, and profit; each slice corresponds to a decile of water availability (DI).
Figure 6. Profits and seasonal use of resources obtained from the optimisation process for each scenario at situation a. Each ring represents a resource index organised as follows (from inside to outside): Land, water, labour and capital used, and profit; each slice corresponds to a decile of water availability (DI).
Water 10 01434 g006
Figure 7. Profits and seasonal use of resources obtained from the optimisation process for each scenario at situation b. Each ring represents a resource index organised as follows (from inside to outside): Land, water, labour and capital used, and profit; each slice corresponds to a decile of water availability (DI).
Figure 7. Profits and seasonal use of resources obtained from the optimisation process for each scenario at situation b. Each ring represents a resource index organised as follows (from inside to outside): Land, water, labour and capital used, and profit; each slice corresponds to a decile of water availability (DI).
Water 10 01434 g007
Figure 8. Crop allocation as a result of the optimisation processes for each decile of water supply and for each scenario at the situation a.
Figure 8. Crop allocation as a result of the optimisation processes for each decile of water supply and for each scenario at the situation a.
Water 10 01434 g008
Figure 9. Crop allocation as a result of the optimisation processes for each decile of water supply and for each scenario at the situation b.
Figure 9. Crop allocation as a result of the optimisation processes for each decile of water supply and for each scenario at the situation b.
Water 10 01434 g009
Figure 10. Monthly limiting resources presented as water, labour, and capital availability for each decile of water supply (DI) and for each monthly scenario (from 3 to 6) for situation a (see Section 3.3).
Figure 10. Monthly limiting resources presented as water, labour, and capital availability for each decile of water supply (DI) and for each monthly scenario (from 3 to 6) for situation a (see Section 3.3).
Water 10 01434 g010
Figure 11. Monthly limiting resources presented as water, labour, and capital availability for each decile of water supply (DI) and for each monthly scenario (from 3 to 6) for situation b (see Section 3.3).
Figure 11. Monthly limiting resources presented as water, labour, and capital availability for each decile of water supply (DI) and for each monthly scenario (from 3 to 6) for situation b (see Section 3.3).
Water 10 01434 g011
Table 1. Parameters used for monthly crop yield functions based on the CROPWAT 8.0 database and the sowing date recommended by Faiguenbaum [43].
Table 1. Parameters used for monthly crop yield functions based on the CROPWAT 8.0 database and the sowing date recommended by Faiguenbaum [43].
CropParameterMonthSowing
SepOctNovDecJanFebMar
Alfalfa K y 1.01.01.01.01.01.01.001-Sep
Δ t * 30.031.030.031.031.028.015.0
L * 49.049.049.049.049.049.049.0
Maize K y --0.50.71.20.50.101-Nov
Δ t * --30.031.031.028.05.0
L * --28.435.135.634.333.4
Wheat K y 0.40.60.70.50.1--01-Sep
Δ t * 30.031.030.031.08.0--
L * 30.030.932.532.68.5--
Sugar beet K y 0.60.81.01.00.90.6-01-Sep
Δ t * 30.031.030.031.031.07.0-
L * 29.531.535.237.338.838.4-
Table 2. Price and maximum yield for each crop.
Table 2. Price and maximum yield for each crop.
CropPriceMaximum YieldSource
ValueUnitsValueUnits
Alfalfa5.1US$ bale−1400bales ha−1INIA [45]
Maize22.3US$ qqm−1150qqm ha−1ODEPA [46]
Wheat22.5US$ qqm−170qqm ha−1ODEPA [46]
Sugar beet62.7US$ ton−1100ton ha−1ODEPA [47]
Table 3. Objective functions and constraints used in each scenario.
Table 3. Objective functions and constraints used in each scenario.
Function or ConstraintEquationScenarios
Objective M a x U = i = 1 n P i A i Y m i 1 - K y i 1 - E T a i E T c i - L C i = 1 n k = 1 t A i N L i , k - i = 1 n k = 1 t A i O C i , k - W c r k = 1 t W r k 1
M a x U = i = 1 n P i A i Y m i k = 1 t 1 - K y i , k 1 - E T a i , k E T c i , k Δ t i , k * / L i , k * - L C i = 1 n k = 1 t A i N L i , k - i = 1 n k = 1 t A i O C i , k - W c r k = 1 t W r k 2, 3, 5
M a x U = i = 1 n P i A i Y m i k = 1 t 1 - K y i , k 1 - E T a i , k E T c i , k Δ t i , k * / L i , k * - L C i = 1 n k = 1 t A i N L i , k - i = 1 n k = 1 t A i O C i , k - W c r k = 1 t W r k - W c b k = 1 t V w b k + W c s k = 1 t V w s k 4, 6
Capital W c r k = 1 t W r k + L C i = 1 n k = 1 t A i N L i , k + i = 1 n k = 1 t A i O C i , k k = 1 t C a k 1, 2
k = 1 k W c r · W r k + W c b · V w b k + L C i = 1 n A i N L i , k + i = 1 n A i O C i , k k = 1 k C a k , k 3–6
Water 10 i = 1 n A i E T a i A E i k = 1 t W r k 1
10 i = 1 n k = 1 t A i E T a i , k A E i k = 1 t W r k 2
10 i = 1 n A i E T a i , k A E i W r k , k 3
10 i = 1 n A i E T a i , k A E i + V w s k W r k + V w b k , k 4
0 k = 1 k W r k - 10 i = 1 n A i E T a i , k A E i R c , k 5
0 k = 1 k W r k + V w b k - 10 i = 1 n A i E T a i , k A E i + V w s k R c , k 6
Table 4. Sensitivity analysis for scenario 1.
Table 4. Sensitivity analysis for scenario 1.
Crop AllocationUse of Resources
AlfalfaMaizeWheatSugar BeetLandWaterLaborCapitalProfits
(ha)(ha)(m3)(Person-d)(US$)(US$)
1. Optimum cropping pattern0002020167,47712080,00045,917
2. Export prices
  2.1 Decrease in 50% for sugar beet0250025172,41726757,11426,671
  2.2 Decrease in 50% for maize0002020167,47712080,00045,917
  2.3 Increase in 50% for alfalfa8001725201,62319280,00051,708
  2.4 Increase in 50% for wheat0002020167,47712080,00045,917
3. Agronomic management
  3.1 Minimum area to be sowed corresponds to 3 ha3331625196,75417879,57841,695
4. Application efficiency of the irrigation system
  4.1 Sugar beet is irrigated by furrow ( A E = 0 . 60 ) and
         wheat by sprinkler ( A E = 0 . 75 )0002020209,34612080,00045,917
5. Water costs
  5.1 Costs of water rights increase to 0.05 US$/m30001616131,0109480,00018,500
6. Labour
  6.1 Costs increase to 30 US$/person-d0002020164,97411980,00044,036
  6.2 Availability decreases to 100 person-d0001717139,01510066,50238,017
7. Other costs
  7.1 Increase in 50% for sugar beet0250025172,41726757,11426,671
  7.2 Increase in 50% for maize0002020167,47712080,00045,917
  7.3 Decrease in 50% for alfalfa6001925203,01418480,00050,321
  7.4 Decrease in 50% for wheat0061925198,64314680,00047,781
8. Capital
  8.1 Availability decreases to 50%000101083,1366040,00022,506
Table 5. Sensitivity analysis for scenario 6, situation a.
Table 5. Sensitivity analysis for scenario 6, situation a.
Crop AllocationUse of Resources
AlfalfaMaizeWheatSugar BeetLandWaterLaborCapitalProfits
(ha)(ha)(m3)(Person-d)(US$)(US$)
1. Optimum cropping pattern34061396,21210936,00018,754
2. Export prices
  2.1 Decrease in 50% for sugar beet5000537,9955880982805
  2.2 Decrease in 50% for maize50061189,8359532,68717,122
  2.3 Increase in 50% for alfalfa50061189,8359532,68722,349
  2.4 Increase in 50% for wheat345416114,62512536,68719,046
3. Agronomic management
  3.1 Minimum area to be sowed corresponds to 3 ha343514107,85411936,43416,578
4. Application efficiency of the irrigation system
  4.1 Sugar beet is irrigated by furrow ( A E = 0 . 60 ) and
         wheat by sprinkler ( A E = 0 . 75 )340613108,04010936,00018,737
5. Water costs
  5.1 Costs of water rights increase to 0.05 US$/m334061396,21210953,35012,505
6. Labour
  6.1 Costs increase to 30 US$/person-d34061396,21210937,09117,662
  6.2 Availability decreases to 100 person-d1102432,0713612,3806204
7. Other costs
  7.1 Increase in 50% for sugar beet010201281,74411525,68310,416
  7.2 Increase in 50% for maize50061189,8359532,68717,122
  7.3 Decrease in 50% for alfalfa34061396,21210934,03220,722
  7.4 Decrease in 50% for wheat34061396,21210936,00018,754
8. Capital
  8.1 Availability decreases to 50%30061079,0357830,92216,577
Table 6. Sensitivity analysis for scenario 6, situation b.
Table 6. Sensitivity analysis for scenario 6, situation b.
Crop AllocationUse of Resources
AlfalfaMaizeWheatSugar BeetLandWaterLaborCapitalProfits
(ha)(ha)(m3)(Person-d)(US$)(US$)
1. Optimum cropping pattern0002020167,46012080,00046,177
2. Export prices
  2.1 Decrease in 50% for sugar beet0000000572−71
  2.2 Decrease in 50% for maize0002020167,46012080,00046,177
  2.3 Increase in 50% for alfalfa0002020167,73912180,00046,224
  2.4 Increase in 50% for wheat0002020167,76012179,95846,135
3. Agronomic management
  3.1 Minimum area to be sowed corresponds to 3 ha333514101,80311336,3957464
4. Application efficiency of the irrigation system
  4.1 Sugar beet is irrigated by furrow ( A E = 0 . 60 ) and
         wheat by sprinkler ( A E = 0 . 75 )0002020209,29212080,00046,108
5. Water costs
  5.1 Costs of water rights increase to 0.05 US$/m30001717143,13310377,49332,014
6. Labour
  6.1 Costs increase to 30 US$/person-d0002020163,87011879,36343,920
  6.2 Availability decreases to 100 person-d0001616137,5589965,81537,919
7. Other costs
  7.1 Increase in 50% for sugar beet0001314112,4518279,2775221
  7.2 Increase in 50% for maize0002020167,43312179,98846,074
  7.3 Decrease in 50% for alfalfa0002020168,25612279,98046,268
  7.4 Decrease in 50% for wheat0002020168,25612279,98046,268
8. Capital
  8.1 Availability decreases to 50%000101083,0746039,97222,872

Share and Cite

MDPI and ACS Style

Kuschel-Otárola, M.; Rivera, D.; Holzapfel, E.; Palma, C.D.; Godoy-Faúndez, A. Multiperiod Optimisation of Irrigated Crops under Different Conditions of Water Availability. Water 2018, 10, 1434. https://doi.org/10.3390/w10101434

AMA Style

Kuschel-Otárola M, Rivera D, Holzapfel E, Palma CD, Godoy-Faúndez A. Multiperiod Optimisation of Irrigated Crops under Different Conditions of Water Availability. Water. 2018; 10(10):1434. https://doi.org/10.3390/w10101434

Chicago/Turabian Style

Kuschel-Otárola, Mathias, Diego Rivera, Eduardo Holzapfel, Cristian D. Palma, and Alex Godoy-Faúndez. 2018. "Multiperiod Optimisation of Irrigated Crops under Different Conditions of Water Availability" Water 10, no. 10: 1434. https://doi.org/10.3390/w10101434

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

Article Metrics

Back to TopTop