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Article

Estimation of Yield Response Factor for Each Growth Stage under Local Conditions Using AquaCrop-OS

by
Mathias Kuschel-Otárola
1,*,
Niels Schütze
2,
Eduardo Holzapfel
1,3,
Alex Godoy-Faúndez
3,4,
Oleksandr Mialyk
2 and
Diego Rivera
3,4
1
Department of Water Resources, School of Agricultural Engineering, University of Concepción, 3812120 Chillán, Chile
2
Institute of Hydrology and Meteorology, Technische Universität Dresden, 01062 Dresden, Germany
3
Water Research Center for Agriculture and Mining (CRHIAM), 3812120 Chillán, Chile
4
Centro de Sustentabilidad y Gestión Estratégica de Recursos (CiSGER), Facultad de Ingeniería, Universidad del Desarrollo, 7610658 Las Condes, Chile
*
Author to whom correspondence should be addressed.
Water 2020, 12(4), 1080; https://doi.org/10.3390/w12041080
Submission received: 16 February 2020 / Revised: 22 March 2020 / Accepted: 4 April 2020 / Published: 10 April 2020
(This article belongs to the Special Issue Crop Water Stress and Deficit Irrigation)

Abstract

:
We propose a methodology to estimate the yield response factor (i.e., the slope of the water-yield function) under local conditions for a given crop, weather, sowing date, and management at each growth stage using AquaCrop-OS. The methodology was applied to three crops (maize, sugar beet, and wheat) and four soil types (clay loam, loam, silty clay loam, and silty loam), considering three levels of bulk density: low, medium, and high. Yields are estimated for different weather and management scenarios using a problem-specific algorithm for optimal irrigation scheduling with limited water supply (GET-OPTIS). Our results show a good agreement between benchmarking (mathematical approach) and benchmark (estimated by AquaCrop-OS) using the Normalised Root Mean Square Error (NRMSE), allowing us to estimate reliable yield response factors ( K y ) under local conditions and to dispose of the typical simple mathematical approach, which estimates the yield reduction as a result of water scarcity at each growth stage.

1. Introduction

Water is the main factor for crop development. Globally, irrigation in agriculture uses about 70% of the available fresh water resources [1] and so, improving irrigation management will increase the water use efficiency (WUE), which is defined as the amount of water necessary to achieve a given yield [2]. According to Saccon [3], the effective planning and management of water for crop production requires a deep knowledge of the system, as experimental results are generally site-specific and are not applicable to different weather, soil, crop, and management conditions. Furthermore, carrying out field experiments is expensive, laborious [4], and time-consuming.
To address the above concerns, the Food and Agriculture Organization (FAO) of the United Nations has developed the AquaCrop model [5]. This model simulates attainable yields of crops as a function of water consumption under rain-fed, supplemental, deficit, and full irrigation conditions, and has been used to accurately determine crop yields in maize [6,7,8], wheat [9,10,11], sugar beet [4,12,13], potatoes [14,15], barley [16], quinoa [17], and rice [18]. AquaCrop has also been linked to crop production functions [19,20,21,22,23,24,25,26,27] which relate yield reduction as a result of the relative loss in evapotranspiration [28].
For yield reduction due to water stress, Doorenbos and Kassam [20] proposed:
1 Y Y m = K y 1 E T a E T c ,
where Y and Y m are the actual and maximum crop yields, respectively; E T a and E T c correspond to actual and maximum evapotranspiration, respectively; and the coefficient K y denotes the yield response factor, which relates the yield reduction ( 1 Y / Y m ) to the water stress ( 1 E T a / E T c ) for a given environment [23].
In the literature, researchers have developed a multiplicative approach to the equation proposed by Doorenbos and Kassam [20,23,27,29]. This approach relates the crop yield reduction as a function of the water stress at specific growth stages. According to Shrestha et al. [30], with the rise in average yields and an increase in crop sensitivities to water stress, the K y coefficients need to be updated. In the literature, K y values have been estimated for maize, wheat, and sugar beet. For maize, Kresović et al. [31] have assessed the effects of different irrigation amounts, estimating grain yield functions depending on seasonal irrigation and water consumption. The latter depends seasonally on K y . Djaman et al. [32] have measured and evaluated crop response to several variables under different levels of irrigation, quantifying seasonal values of K y . With respect to sugar beet, Kiymaz and Ertek [33] have determined the effect of different irrigation and nitrogen levels on yield and other components, obtaining K y for two growing seasons. Tarkalson et al. [34] have quantified the yield response to water input and actual evapotranspiration; they also obtained K y for two growing seasons. Regarding wheat, Bandyopadhyay et al. [35] have analysed the effect of different combinations of sprinkler and surface flooding on crop production functions, obtaining K y for each irrigation treatment and Liu et al. [36] have evaluated the performance of winter wheat under different irrigation amounts, estimating K y for four growing seasons.
Foster et al. [37] developed the AquaCrop-OS model, an open-source code written in MATLAB, providing the opportunity to link it with other concepts to assess farming scenarios. Considering the importance of the sub-seasonal application of water in food production, we defined the following research question: Is it possible to incorporate the multiplicative approach of Doorenbos and Kassam [20] into AquaCrop-OS, in order to estimate K y at each growth stage? Therefore, the main objective of our research was to develop and test a methodology to estimate K y under local conditions for a given crop, soil, weather, sowing date, and management at each growth stage using AquaCrop-OS. Reliable K y values under local conditions for each growth stage allow farmers to decrease uncertainty and improve risk management due to intraseasonal changes.

2. Methodology

Our proposed methodology aims to include the AquaCrop-OS model into the multiplicative approach of Doorenbos and Kassam [20], with the objective of determining K y under local conditions (i.e., for a given crop, soil, weather, sowing date, and management) at each growth stage.

2.1. Crop Yield Equation

The multiplicative approach of the equation proposed by Doorenbos and Kassam [20] (Equation (1)) is:
Y Y m = n = 1 N 1 K y n 1 E T a n E T c n ,
where n is an index representing each growth stage and N corresponds to the number of functions between the square brackets [23].

2.2. Estimation of K y Using AquaCrop-OS

This section was developed in MATLAB and is split into two parts: A benchmark definition and a benchmarking (Figure 1).
As a benchmark definition, we started with a database of historical weather scenarios for a given area in which, for each year, the water-yield functions (WYF) have been determined using AquaCrop-OS [37] and a problem-specific algorithm for optimal irrigation scheduling with limited water supply. This is named the Global Evolutionary Technique for OPTimal Irrigation Scheduling (GET-OPTIS) [24]. The main objective of GET-OPTIS is to maximise the crop yield (Y) by finding an optimal irrigation schedule (S) composed of a date ( d i ) and an irrigation depth ( v i ) (Figure 2):
Y = m a x Y S : S = s i i = 1 n = d 1 , v 1 , , d i , v i , , d n , v n n , d i N ; v i R .
This process required high computational effort, as building 34,020 scenarios (21 points for 45 years, 3 crops, and 12 soil types) was required. So, we used the parallel run mode in MATLAB R2017a [38]. Parallel computing allows us to carry out many calculations simultaneously, accelerating the computing speed. Once the WYFs were built, the K y values (i.e., the slopes of the WYFs) were estimated, by considering Equation (2), through the least square method at each growth stage: (1) emergency or transplant recovery, (2) vegetative stage, (3) flowering stage, and (4) yield formation and ripening [39]. Finally, we considered discrete mean values of K y every 5 years. It should be noted that there were no measured data used in this case, and the simulation results from AquaCrop-OS were used as the comparison benchmark for evaluation.
Benchmarking was carried out by determining crop yield using Equation (2), considering the K y values for each combination of crop, soil type, and weather scenario for each year. Different statistical indices were used, such as Normalised Root Mean Square Error (NRMSE) and linear regression, for comparison of the results obtained from AquaCrop-OS and those estimated using the proposed methodology. The NRMSE (in %) was calculated according to Loague and Green [40]:
NRMSE = s = 1 S Y A O S , k Y P r o p , k 2 S × 100 Y A O S , k ¯ ,
where Y A O S , k and Y P r o p , k correspond respectively to the crop yield estimated by AquaCrop-OS and the proposed methodology for the year k and Y A O S , k ¯ represents the mean value of the crop yields estimated by AquaCrop-OS for the year k. A simulation is considered excellent if its NRMSE is less than 10%, good if its NRMSE is greater than 10% and less than 20%, fair if its NRMSE is greater than 20% and less than 30%, and poor if its NRMSE is greater than 30% [41].

2.3. Case Study

Our proposed model was applied to conditions characteristic of the Central Valley of Chile (see Figure 3). The annual mean precipitation in this area is about 1025 mm, and the average maximum and minimum temperatures are 20.6 and 7.6 C, respectively [42]. This region contains about 28% of the national cropping area. Some of the most-produced crops are wheat (34.3%), maize (11.6%), and sugar beet (6%), which contribute to 27.9%, 22.5%, and 60% of the national planted surface, respectively [43]. The soils are formed from volcanic ashes (Andisols) deposited over an unrelated substrate of andesitic tuff and fluvioglacial materials. The texture is predominately silty clay loam, silty loam, and loam, and the bulk density ranges from 0.71 to 1.35 Mg m−3 [44,45,46].

2.4. Model Inputs

Sowing dates for maize, wheat, and sugar beet for each year correspond to the first day of November, September, and August, respectively [47]. A weather database from 1970 to 2014 (Figure 4) was extracted from the Explorador Climático website (http://explorador.cr2.cl/). Reference evapotranspiration was estimated according to Allen et al. [48]. Crop parameters from the AquaCrop-OS [37] database were considered (see Table 1). On the other hand, soil hydraulic parameters (Table 2) were extracted from Granda et al. [45] and saturated hydraulic conductivity (Ks) was estimated using the RETC model [49]. Soils in the area of study are mainly derived from volcanic ashes, with strong vertical and horizontal variability. The data in Table 2 are based on field studies (see Granda et al. [45] and Kuschel-Otárola [50]), such that the Ks values lie in the range of variation and provide realistic values for representative soils. However, we draw attention to the fact that andesitic soils are less-studied soils and show high variability in hydraulic parameters, despite having similar texture. Moreover, agricultural operations have effects on changes in bulk density which are not always accounted by pedotransfer functions. For soils, the numbers 1, 2, and 3 correspond to low, medium, and high bulk density, respectively. Each growing season started with 50% of the total available water. Regarding fertilisation, there was no differentiated management to not alter the water management conditions.

3. Results and Discussions

3.1. Yield Response Factor for Each Growth Stage

The K y values for each growth stage (emergency or transplant recovery, vegetative stage, flowering stage, and yield formation and ripening) are presented in form of box plots for maize, sugar beet, and wheat, in Figure 5, Figure 6 and Figure 7, respectively. These figures represent K y as a discrete mean value over 5 years for benchmarking (i.e., 1970–1974, 1975–1979, 1980–1984, 1985–1989, 1990–1994, 1995–1999, 2000–2004, 2005–2009, and 2010–2014) for different soil types in the study area with low (1), medium (2), and high (3) bulk densities (Table 2) considering optimal irrigation scheduling (GET-OPTIS). In each box, the central mark indicates the median, and the bottom and top edges of the box indicate the 25 th and 75 th percentiles, respectively. The whiskers extend to the most extreme data points not considered as outliers, and the outliers are plotted individually using the “+” symbol.

3.1.1. Yield Response Factor For Maize

Figure 5 shows the K y values for maize at each growth stage and for soils with low (1), medium (2), and high (3) bulk densities. According to Steduto et al. [28], K y > 1 implies that the crop is very sensitive to water deficits, K y < 1 means that it is more tolerant to water deficits, and K y = 1 corresponds to a direct proportion of yield reduction to reduced water use. The K y value for the first growth stage was close to zero for all soil types. On the other hand, K y always reached its maximum in the third growth stage (flowering). Its values ranged from 0.9 to 1.4, indicating that maize is very sensitive to water deficits in this stage. Thus, water stress during this stage incurs larger reductions than in other stages [20,28]. For clay loam soil, the higher the bulk density, the lower the value of K y was in the third growth stage. With the exception of the fourth growth stage, the obtained values were lower than those proposed by the FAO [51].

3.1.2. Yield Response Factor for Sugar Beet

Figure 6 shows the K y values for sugar beet at each growth stage and for each soil type. Similarly to the results obtained for maize (Figure 5), the K y value in the first growth stage was close to zero for all soil types, indicating that yield is not affected when there is enough water in the soil profile. It reached its maximum value in the third growth stage for most soil types; except for clay loam soil with high bulk density, where this value was the lowest (compared with the other soil types). Furthermore, this soil type presented the highest values for the second and fourth growth stage. The obtained values were lower than those proposed by the FAO [51], for each growth stage.

3.1.3. Yield Response Factor For Wheat

Figure 7 shows the K y values for wheat for each growth stage and for each soil type. Similarly to the results obtained for maize (Figure 5) and sugar beet (Figure 6), the K y value in the first growth stage was close to zero, except for loam soil with medium bulk density ( K y = 0.15). Regarding the value for the third growth stage, this value was relatively low when compared to maize and sugar beet. The lowest value for the third growth stage was presented in loam soil with medium bulk density ( K y = 0.73); this soil type also presented a value over the 70 th percentile for the second growth stage ( K y = 0.30). With the exception of the third growth stage, the obtained values were lower than those proposed by the FAO [51]. Soils with high bulk density (index number 3) showed lower differences, with respect to the values proposed in the literature.

3.2. Benchmarking of the Proposed Methodology

3.2.1. Benchmarking for a Specific Year

Figure 8 shows the comparison between the dry yield obtained by AquaCrop-OS (red line 1:1) and the estimates obtained by the proposed methodology (blue dots). There was generally a good agreement between the results obtained by AquaCrop-OS and the proposed methodology, with NRMSE values ranging from 1.62% (wheat in a silty loam soil) to 15.80% (sugar beet in a loam soil). The K y values used in this case were extracted from the benchmark between 2010–2014 (see Table 3). According to Steduto et al. [28], sugar beet (Beta vulgaris) is a biennial plant which produces a large storage root as a part of its tap root, containing 14–20% sucrose on a fresh mass basis; thus, the crop yield values of sugar beet can reach 80–120 t ha−1.

3.2.2. Benchmarking for All Years

The benchmarking for all years was carried out by determining the Normalised Root Mean Square Error (NRMSE) for every year. Figure 9 shows the NRMSE values for each year for maize (a), sugar beet (b), and wheat (c), for all soil types, where the lowest and highest values are presented in blue and red, respectively. According to the classification suggested by Jamieson et al. [41], the values are ranged from 0% to ≥ 30%. It can be seen that wheat presented the best performance.
On the other hand, Figure 10 shows a comparison of the frequency of NRMSE values, as suggested by Jamieson et al. [41]. Local estimation of the K y values presented better performance, compared to the values reported in the literature [20,51], as they were not specific to a particular soil type or management. Local estimation increased the frequency of the best performance (excellent) in maize (from 0 to 67%), sugar beet (from 0 to 35%) and wheat (from 46 to 82%). Wheat, however, presented the best performance, considering the K y values suggested by the FAO [51].

4. Conclusions

We developed and assessed a methodology to estimate the K y value under local conditions for a given crop, soil, weather, sowing date, and management, as well as for each growth stage, using AquaCrop-OS under Chilean conditions. The proposed methodology presented a good agreement; excellent simulation of 67%, 35%, and 82% was observed for maize, sugar beet, and wheat, respectively (Figure 10), allowing us to estimate the K y values under local conditions and to dispose of the typical simple mathematical approach in which yield reduction is estimated as a result of water scarcity at each growth stage.
Most irrigation managers consider resources to be available over the whole season. However, at sub-seasonal time scales—weekly, monthly, or even daily—irrigation managers and farmers must make decisions and take action based on new information regarding climate drivers and resource availability. Thus, the K y value could be used to tailor water management strategies under changing conditions [27]. Future studies should focus on the estimation of K y under a more diverse range of management scenarios.

Author Contributions

Conceptualization, M.K.-O., N.S., E.H., A.G.-F., O.M., and D.R.; Data curation, M.K.-O., N.S., E.H., O.M., and D.R.; Formal analysis, M.K.-O.; Investigation, M.K.-O., N.S., E.H., A.G.-F., O.M., and D.R.; Methodology, M.K.-O. and N.S.; Resources, D.R.; Software, M.K.-O., N.S., and O.M.; Supervision, N.S., E.H., A.G.-F., and D.R.; Visualization, M.K.-O.; Writing—original draft, M.K.-O. All authors have read and agreed to the published version of the manuscript.

Funding

The research leading to this report was supported by the National Agency for Research and Development (ANID) through ANID-PCHA/National Doctorate/2015-21150463, the project ANID/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 ANID/FONDAP/15130015: Water Research Center for Agriculture and Mining (CRHIAM), the Laboratory of Investigation and Technologies to the Water Management in the Agriculture (ItecMA2) and the Institute of Hydrology and Meteorology of the Dresden University of Technology.

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. FAO. AQUASTAT Website. FAO’s Information System on Water and Agriculture; Food and Agriculture Organization of the United Nations: Rome, Italy, 2016. [Google Scholar]
  2. Hubick, K.T.; Farquhar, G.D.; Shorter, R. Correlation between water use efficiency and carbon isotope discrimination in diverse peanut (Arachis) germplasm. Aust. J. Plant Physiol. 1986, 13, 803–816. [Google Scholar] [CrossRef]
  3. Saccon, P. Water for agriculture, irrigation management. Appl. Soil Ecol. 2017. [Google Scholar] [CrossRef]
  4. Malik, A.; Shakir, A.; Ajmal, M.; Khan, M.; Khan, T. Assessment of AquaCrop model in simulating sugar beet canopy cover, biomass and root yield under different irrigation and field management practices in semi-arid regions of Pakistan. Water Resour. Manag. 2017, 31, 4275–4292. [Google Scholar] [CrossRef]
  5. Steduto, P.; Hsiao, T.; Raes, D.; Fereres, E. AquaCrop—The FAO crop model to simulate yield response to water: I. Concepts and underlying principles. Agron. J. 2009, 101, 426–437. [Google Scholar] [CrossRef] [Green Version]
  6. Paredes, P.; de Melo-Abreu, J.; Alves, I.; Pereira, L.S. Assessing the performance of the FAO AquaCrop model to estimate maize yields and water use under full and deficit irrigation with focus on model parameterization. Agric. Water Manag. 2014, 144, 81–97. [Google Scholar] [CrossRef] [Green Version]
  7. Nyakudya, I.W.; Stroosnijder, L. Effect of rooting depth, plant density and planting date on maize (Zea mays L.) yield and water use efficiency in semi-arid Zimbabwe: Modeling with AquaCrop. Agric. Water Manag. 2014, 146, 280–296. [Google Scholar] [CrossRef]
  8. Heng, L.K.; Hsiao, T.; Evett, S.; Howell, T.; Steduto, P. Validating the FAO AquaCrop model for irrigated and water deficient field maize. Agron. J. 2009, 101, 488–498. [Google Scholar] [CrossRef] [Green Version]
  9. Toumi, J.; Er-Raki, S.; Ezzahar, J.; Khabba, S.; Jarlan, L.; Chehbouni, A. Performance assessment of AquaCrop model for estimating evapotranspiration, soil water content and grain yield of winter wheat in Tensift Al Haouz (Morocco): Application to irrigation management. Agric. Water Manag. 2016, 163, 219–235. [Google Scholar] [CrossRef]
  10. Mkhabela, M.S.; Paul, R.B. Performance of the FAO AquaCrop model for wheat grain yield and soil moisture simulation in Western Canada. Agric. Water Manag. 2012, 110, 16–24. [Google Scholar] [CrossRef]
  11. Andarzian, B.; Bannayan, M.; Steduto, P.; Mazraeh, H.; Barati, M.E.; Barati, M.A.; Rahnama, A. Validation and testing of the AquaCrop model under full and deficit irrigated wheat production in Iran. Agric. Water Manag. 2011, 100, 1–8. [Google Scholar] [CrossRef]
  12. Alishiri, R.; Paknejad, F.; Aghayari, F. Simulation of sugarbeet growth under different water regimes and nitrogen levels by AquaCrop. Int. J. Biosci. 2014, 4, 1–9. [Google Scholar]
  13. Stricevic, R.; Cosic, M.; Djurovic, N.; Pejic, B.; Maksimovic, L. Assessment of the FAO AquaCrop model in the simulation of rainfed and supplementally irrigated maize, sugar beet and sunflower. Agric. Water Manag. 2011, 98, 1615–1621. [Google Scholar] [CrossRef]
  14. Montoya, F.; Camargo, D.; Ortega, J.; Córcoles, J.; Domínguez, A. Evaluation of AquaCrop model for a potato crop under different irrigation conditions. Agric. Water Manag. 2016, 164, 267–280. [Google Scholar] [CrossRef]
  15. Garcia-Vila, M.; Fereres, E. Combining the simulation crop model AquaCrop with an economic model for the optimization of irrigation management at farm level. Eur. J. Agron. 2012, 36, 21–31. [Google Scholar] [CrossRef] [Green Version]
  16. Araya, A.; Habtu, S.; Hagdu, K.M.; Kebede, A.; Dejene, T. Test of AquaCrop model in simulating biomass and yield of water deficient and irrigated barley (Hordeum vulgare). Agric. Water Manag. 2010, 97, 1838–1846. [Google Scholar] [CrossRef]
  17. Geerts, S.; Raes, D.; Garcia, M.; Miranda, R.; Cusicanqui, J.A.; Taboada, C.; Mendoza, J.; Huanca, R.; Mamani, A.; Condori, O.; et al. Simulating yield response of quinoa to water availability with AquaCrop. Agron. J. 2009, 101, 499–508. [Google Scholar] [CrossRef]
  18. Maniruzzaman, M.; Talukder, M.S.U.; Khan, M.H.; Biswas, J.C.; Nemes, A. Validation of the AquaCrop model for irrigated rice production under varied water regimes in Bangladesh. Agric. Water Manag. 2015, 159, 331–340. [Google Scholar] [CrossRef]
  19. Jensen, J. Water consumption by agricultural plants. In Water Deficit and Plant Growth; Kozlowski, T., Ed.; Academic Press: New York, NY, USA, 1968; pp. 1–22. [Google Scholar]
  20. Doorenbos, J.; Kassam, A. Yield Response to Water; FAO: Rome, Italy, 1979. [Google Scholar]
  21. Carvallo, H.O.; Holzapfel, E.A.; Lopez, M.A.; Mariño, M.A. Irrigated cropping optimization. J. Irrig. Drain. Engin. ASCE 1998, 124, 67–72. [Google Scholar] [CrossRef]
  22. 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]
  23. 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]
  24. Schütze, N.; de Paly, M.; Shamir, U. Novel simulation-based algorithms for optimal open-loop and closed-loop scheduling of deficit irrigation systems. J. Hydroinform. 2012, 14, 136–151. [Google Scholar] [CrossRef]
  25. Singh, A. Optimal Allocation of Resources for the Maximization of Net Agricultural Return. J. Irrig. Drain. Eng. 2012, 138, 830–836. [Google Scholar] [CrossRef]
  26. 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] [Green Version]
  27. 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. [Google Scholar] [CrossRef] [Green Version]
  28. Steduto, P.; Hsiao, T.C.; 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]
  29. 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]
  30. Shrestha, N.; Geerts, S.; Raes, D.; Horemans, S.; Soentjens, S.; Maupas, F.; Clouet, P. Yield response of sugar beets to water stress under Western European conditions. Agric. Water Manag. 2010, 97, 346–350. [Google Scholar] [CrossRef]
  31. Kresović, B.; Tapanarova, A.; Tomić, Z.; Životić, L.; Vujović, D.; Sredojević, Z.; Gajić, B. Grain yield and water use efficiency of maize as influenced by different irrigation regimes through sprinkler irrigation under temperate climate. Agric. Water Manag. 2016, 169, 34–43. [Google Scholar] [CrossRef]
  32. Djaman, K.; Irmak, S.; Rathje, W.R.; Martin, D.L.; Eisenhauer, D.E. Maize evapotranspiration, yield production function, biomass, grain yield, harvest index, and yield response factors under full and limited irrigation. Trans. ASABE 2013, 56, 273–293. [Google Scholar]
  33. Kiymaz, S.; Ertek, A. Yield and quality of sugar beet (Beta vulgaris L.) at different water and nitrogen levels under the climatic conditions of Kirsehir, Turkey. Agric. Water Manag. 2015, 158, 156–165. [Google Scholar] [CrossRef]
  34. Tarkalson, D.D.; King, B.A.; Bjorneberg, D.L. Yield production functions of irrigated sugarbeet in an arid climate. Agric. Water Manag. 2018, 200, 1–9. [Google Scholar] [CrossRef]
  35. Bandyopadhyay, K.K.; Misra, A.K.; Ghosh, P.K.; Hati, K.M.; Mandal, K.G.; Moahnty, M. Effect of irrigation and nitrogen application methods on input use efficiency of wheat under limited water supply in a Vertisol of Central India. Irrig. Sci. 2010, 28, 285–299. [Google Scholar] [CrossRef]
  36. Liu, X.W.; Shao, L.W.; Sun, H.Y.; Chen, S.Y.; Zhang, X.Y. Responses of yield and water use efficiency to irrigation amount decided by pan evaporation for winter wheat. Agric. Water Manag. 2013, 129, 173–180. [Google Scholar] [CrossRef]
  37. Foster, T.; Brozovic, N.; Butler, A.; Neale, C.; Raes, D.; Steduto, P.; Fereres, E.; Hsiao, T. AquaCrop-OS: An open source version of FAO’s crop water productivity model. Agric. Water Manag. 2017, 181, 18–22. [Google Scholar] [CrossRef]
  38. MathWorks. Parallel Computing Toolbox: User’s Guide; Technical Report; The MathWorks, Inc.: Natick, MA, USA, 2017. [Google Scholar]
  39. Raes, D.; Steduto, P.; Hsiao, T.C.; Fereres, E. Reference Manual: AquaCrop Plug-in Program (Version 4.0); Technical Report; FAO: Rome, Italy, 2012. [Google Scholar]
  40. Loague, K.; Green, R.E. Statistical and graphical methods for evaluating solute transport models; overview and application. J. Contam. Hydrol. 1991, 7, 51–73. [Google Scholar] [CrossRef]
  41. Jamieson, P.D.; Porter, J.R.; Wilson, D.R. A test of the computer simulation model ARC-WHEAT1 on wheat crops grown in New Zealand. Field Crop. Res. 1991, 27, 337–350. [Google Scholar] [CrossRef]
  42. DGA. Diagnóstico y Clasificación de los Cursos y Cuerpos de Agua Según Objetivo y Calidad; Cuenca del río Itata: Santiago, Chile, 2004. [Google Scholar]
  43. ODEPA. Región del Biobío: Información Regional 2018; Technical Report; Oficina de Estudios y Políticas Agrarias (ODEPA): Santiago, Chile, 2018. [Google Scholar]
  44. Rivera, D.; Granda, S.; Arumí, J.L.; Sandoval, M.; Billib, M. A methodology to identify representative configurations of sensors for monitoring soil moisture. Environ. Monit. Assess. 2011, 184, 6563–6574. [Google Scholar] [CrossRef]
  45. Granda, S.; Rivera, D.; Arumí, J.L.; Sandoval, M. Monitoreo continuo de humedad con fines hidrológicos. Tecnolog. Cienc. Agua 2013, 4, 189–197. [Google Scholar]
  46. Rivera, D.; Sandoval, M.; Godoy, A. Exploring soil databases: A self-organizing map approach. Soil Use Manag. 2015, 31, 121–131. [Google Scholar] [CrossRef]
  47. Faiguenbaum, H. Labranza, Siembra y Producción de los Principales Cultivos de Chile; Vivaldi y Asociados: Santiago, Chile, 2003; p. 760. [Google Scholar]
  48. Allen, R.G.; Walter, I.A.; Elliott, R.; Itenfisu, D.; Brown, P.; Jensen, M.E.; Mecham, B.; Howell, T.A.; Snyder, R.; Eching, S.; et al. Task Committee on Standardization of Reference Evapotranspiration; SCE: Reston, VA, USA, 2005. [Google Scholar]
  49. Van Genuchten, M.T.; Leij, F.J.; Yates, S.R. The RETC Code for Quantifying the Hydraulic Functions of Unsaturated Soils; EPA/600/2-91/065; U.S. Environmental Protection Agency: Ada, OK, USA, 1991; p. 85.
  50. Kuschel-Otárola, M. Estimación de Flujos de Agua en un Andisol Usando Datos de Humedad. Bachelor’s Thesis, Universidad de Concepción, Chillán, Chile, 2014. [Google Scholar]
  51. FAO. “CROPWAT 8.0” Databases and Software; FAO: Rome, Italy, 2017. [Google Scholar]
Figure 1. The methodology used for this research to estimate the K y value at each growth stage under local conditions (i.e., for a given crop, soil, weather, sowing date, and management) using AquaCrop-OS.
Figure 1. The methodology used for this research to estimate the K y value at each growth stage under local conditions (i.e., for a given crop, soil, weather, sowing date, and management) using AquaCrop-OS.
Water 12 01080 g001
Figure 2. Water-yield functions (left side) and optimal irrigation schedules (right side) for maize (a), sugar beet (b), and wheat (c) under clay loam soil conditions.
Figure 2. Water-yield functions (left side) and optimal irrigation schedules (right side) for maize (a), sugar beet (b), and wheat (c) under clay loam soil conditions.
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Figure 3. Study area location.
Figure 3. Study area location.
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Figure 4. Minimum and maximum temperature ( T m i n and T m a x ), reference evapotranspiration ( E T r ), and precipitation ( P P ) for the study area, presented as mean values from 1970 to 2014.
Figure 4. Minimum and maximum temperature ( T m i n and T m a x ), reference evapotranspiration ( E T r ), and precipitation ( P P ) for the study area, presented as mean values from 1970 to 2014.
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Figure 5. Yield response factor ( K y ) obtained for maize for every soil type, considering the benchmark process. Circles represent K y values proposed by the FAO [51].
Figure 5. Yield response factor ( K y ) obtained for maize for every soil type, considering the benchmark process. Circles represent K y values proposed by the FAO [51].
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Figure 6. Yield response factor ( K y ) obtained for sugar beet for every soil type, considering the benchmark process. Circles represent K y values proposed by the FAO [51].
Figure 6. Yield response factor ( K y ) obtained for sugar beet for every soil type, considering the benchmark process. Circles represent K y values proposed by the FAO [51].
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Figure 7. Yield response factor ( K y ) obtained for wheat for every soil type considering the benchmark process. Circles represent K y values proposed by the FAO [51].
Figure 7. Yield response factor ( K y ) obtained for wheat for every soil type considering the benchmark process. Circles represent K y values proposed by the FAO [51].
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Figure 8. Crop yield (Y) obtained from the benchmarking for maize, sugar beet, and wheat in various soil types considering the mean value of bulk density in the year 2014. Red lines present the benchmark estimated by AquaCrop-OS, while each blue dot corresponds to the crop yield estimated by the proposed methodology.
Figure 8. Crop yield (Y) obtained from the benchmarking for maize, sugar beet, and wheat in various soil types considering the mean value of bulk density in the year 2014. Red lines present the benchmark estimated by AquaCrop-OS, while each blue dot corresponds to the crop yield estimated by the proposed methodology.
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Figure 9. Normalised Root Mean Square Error (NRMSE) for maize (a), sugar beet (b), and wheat (c), for every soil type, from 1970 to 2014.
Figure 9. Normalised Root Mean Square Error (NRMSE) for maize (a), sugar beet (b), and wheat (c), for every soil type, from 1970 to 2014.
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Figure 10. Comparison of the frequency of NRMSE values obtained by the proposed methodology and recommended by CROPWAT database [51].
Figure 10. Comparison of the frequency of NRMSE values obtained by the proposed methodology and recommended by CROPWAT database [51].
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Table 1. Conservative (constant) and generally applicable parameters for maize, sugar beet, and wheat in the Central Valley of Chile.
Table 1. Conservative (constant) and generally applicable parameters for maize, sugar beet, and wheat in the Central Valley of Chile.
ParameterCrop
MaizeSugar BeetWheat
Conservative (generally applicable)
Base temperature ( C)8.005.000.00
Cut-off temperature ( C)30.0030.0026.00
Canopy cover per seedling at 90% emergence (CCo)6.501.001.50
Canopy growth coefficient (CGC)1.251.050.50
Maximum canopy cover (CCx)96.0098.0096.00
Crop coefficient for transpiration at CC = 100%1.051.101.10
Decline in crop coef. after reaching CCx0.300.150.15
Canopy decline coefficient (CDC) at senescence1.000.390.40
Water productivity, normalised to the year 2000 (WP*)33.7017.0015.00
Leaf growth threshold (Pupper)0.140.200.20
Leaf growth threshold (Plower)0.720.600.65
Leaf growth stress coefficient curve shape2.903.005.00
Stomatal conductance threshold (Pupper)0.690.650.65
Stomata stress coefficient curve shape6.003.002.50
Senescence stress coefficient (Pupper)0.690.750.70
Senescence stress coefficient curve shape2.703.002.50
Considered to be conservative but can or may be cultivar-specific
Reference harvest index (HIo)487048
GDD from 90% emergence to start of anthesis8008421100
Duration of anthesis, in GDD1800200
Coefficient, inhibition of leaf growth on HI7410
Coefficient, inhibition of stomata on HI3-7
Maximum yield (t ha−1) (more details in Kuschel-Otárola et al. [27])151007
Table 2. Bulk density ( ρ a ), saturation ( θ s ), field capacity ( θ f c ), permanent wilt water content ( θ p w p ), and saturated hydraulic conductivity ( K s ) representative of the Central Valley of Chile. A constant soil depth of 2.3 m was considered and there was no influence from the water table.
Table 2. Bulk density ( ρ a ), saturation ( θ s ), field capacity ( θ f c ), permanent wilt water content ( θ p w p ), and saturated hydraulic conductivity ( K s ) representative of the Central Valley of Chile. A constant soil depth of 2.3 m was considered and there was no influence from the water table.
SandSiltClay ρ a θ s θ fc θ pwp K s
Soil(%)(g cm−3)(m3 m−3)(mm day−1)
ClayLoam 12248300.720.730.450.303415.9
ClayLoam 23538270.970.640.570.33269.1
ClayLoam 33928331.390.470.340.26132.4
Loam 13442240.710.730.440.283517.8
Loam 23146231.070.600.590.4069.5
Loam 34137221.130.570.550.34110.3
SiltyClayLoam 11052380.780.700.460.322382.0
SiltyClayLoam 21152370.810.690.500.321903.3
SiltyClayLoam 31549360.860.680.500.361534.2
SiltyLoam 12750230.710.730.440.283571.7
SiltyLoam 22251270.980.630.590.38183.9
SiltyLoam 32451251.030.610.590.4476.3
Table 3. Yield response factor ( K y ) obtained for maize, sugar beet, and wheat in various soil types considering the mean value of bulk density, valid for the years 2010–2014.
Table 3. Yield response factor ( K y ) obtained for maize, sugar beet, and wheat in various soil types considering the mean value of bulk density, valid for the years 2010–2014.
CropSoil1st2nd3rd4thTotal
MaizeClayLoam0.000.291.040.481.07
Loam0.000.050.970.731.01
SiltyClayLoam0.000.220.860.581.10
SiltyLoam0.000.471.050.151.10
Sugar beetClayLoam0.000.591.020.001.16
Loam0.000.120.820.211.13
SiltyClayLoam0.000.510.960.001.15
SiltyLoam0.000.411.000.001.16
WheatClayLoam0.000.001.010.231.05
Loam0.160.400.730.261.09
SiltyClayLoam0.000.001.010.251.09
SiltyLoam0.000.001.020.251.04

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Kuschel-Otárola, M.; Schütze, N.; Holzapfel, E.; Godoy-Faúndez, A.; Mialyk, O.; Rivera, D. Estimation of Yield Response Factor for Each Growth Stage under Local Conditions Using AquaCrop-OS. Water 2020, 12, 1080. https://doi.org/10.3390/w12041080

AMA Style

Kuschel-Otárola M, Schütze N, Holzapfel E, Godoy-Faúndez A, Mialyk O, Rivera D. Estimation of Yield Response Factor for Each Growth Stage under Local Conditions Using AquaCrop-OS. Water. 2020; 12(4):1080. https://doi.org/10.3390/w12041080

Chicago/Turabian Style

Kuschel-Otárola, Mathias, Niels Schütze, Eduardo Holzapfel, Alex Godoy-Faúndez, Oleksandr Mialyk, and Diego Rivera. 2020. "Estimation of Yield Response Factor for Each Growth Stage under Local Conditions Using AquaCrop-OS" Water 12, no. 4: 1080. https://doi.org/10.3390/w12041080

APA Style

Kuschel-Otárola, M., Schütze, N., Holzapfel, E., Godoy-Faúndez, A., Mialyk, O., & Rivera, D. (2020). Estimation of Yield Response Factor for Each Growth Stage under Local Conditions Using AquaCrop-OS. Water, 12(4), 1080. https://doi.org/10.3390/w12041080

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