Characterizing spatial and temporal trends in drought patterns of rainfed wheat (Triticum aestivum L.) across various climatic conditions: A modelling approach
Graphical abstract
Introduction
Drought was recognized as one of the most common and challenging environmental stresses in the agricultural sectors worldwide (Hu et al., 2020; Lamaoui et al., 2018; Watson et al., 2017). Drought stress can result in substantially lower crop production -21 % in wheat and 40 % in maize (Daryanto et al., 2016), and globally 9–10 % in cereals (Lesk et al., 2016). By an annual production of ∼12 million tons, Iran is the second largest producer of wheat in the Middle East (FAO, 2017). Wheat is cultivated on 5.5 million ha, of which 62 % is rainfed and the rest irrigated. The average yield of rainfed wheat is 1.03 t ha-1 and that of irrigated wheat is 4.3 t ha-1 for the period of 2010–2016 (Anonymous, 2017). The huge difference between irrigated and rainfed systems due to the grain yield could be related to the lack of the knowledge of drought patterns (DP) that occurs across the rainfed agro-ecosystems in these regions. The drought pattern is not only related to the rainfall trends, but also to the rainfall concentration and monthly rainfall heterogeneity (Thomas and Prasannakumar, 2016).
Drought stress reduces the crop yield by reducing the stomatal conductivity, growth and grain development (Fahad et al., 2017; Farooq et al., 2014). Both severity and duration of drought stress also define the extent of yield loss by reducing the duration of growth and grain filling (Mohammadi-Ahmadmahmoudi et al., 2020; Fahad et al., 2017) and decreasing the yield components and seed set (Alqudah et al., 2011). To deal with drought stress, there are some strategies including drought escape or avoidance by which plants can alleviate the negative effects of drought stress by completing their life-cycle during the short period of favorable conditions (Shavrukov et al., 2017). However, using top-mentioned strategies requires a deep understanding of drought stress nature including the severity and duration of drought due to the spatial and temporal dimensions. Understanding the seasonal pattern of drought events in the target environments has focused by many researchers looking to improve the rainfed crop yields in drought-prone environments (Touzy et al., 2019; Chenu et al., 2013; Kholová et al., 2013; Heinemann et al., 2008). In one simulation study, for example, Chenu et al. (2013) identified four DPs (drought patterns) as the environment types for rainfed wheat across the Australian Wheatbelt, where severe drought patterns or DP4 (i.e. drought starts during the vegetative period and generally lasts until maturity) occurred 44 % of time. In another simulation study, Heinemann et al. (2019) analyzed the changes in drought effects on the upland rice cropping systems for cultivars representing three decades of breeding (1980s, 1990s, and 2000s) in the Brazilian savannas using ORYZA v3 rice crop model and observed a mean increase of 12 % in the drought effect (0.35 % per year) from the 1980s to the 2000s.
Characterizing the spatial and temporal trends in the DPs for any particular environment is essential for the breeding programs can deal with drought. It helps the researchers and breeders introduce the genotypes better adapted to each environment (e.g. Heinemann et al., 2019; Touzy et al., 2019; Chenu et al., 2013; Chapman et al., 2000). Some genotypes are well adapted to severe drought patterns while others are suitable for moderate to light drought patterns (i.e. no drought stress or drought stress occurring only at post-flowering) (Chenu et al., 2013). Moreover, depending on drought pattern type, the best combination of G × E (genotype × environment) could be chosen. For this purpose, modelling approaches were pragmatically applied to assess G × E combinations and to take advantage of the genetic and environmental resources more efficiently regarding drought patterns in each environment (Casadebaig et al., 2016). Hammer et al. (2014), for instance, indicated that the multi-year drought stress risk in sorghum for a given region could be decreased by the adoption of better G × M ("local G" and "local M") compared to using the combination of "global G" and "global M". Touzy et al. (2019) used modelling and statistical approaches to identify the specific drought tolerant QTLs in the breeding wheat and reported that the environmental clustering improved understanding of drought impact on wheat grain yields which explained 20 % of G × E interaction. Moreover, they claimed that their results enable the breeders to introduce drought-resistant genotypes to specific environmental conditions. In another modelling study, Lake et al. (2016) used the APSIM crop model to simulate the effect of 3905 E (71 locations × 55 years from 1958 to 2013) in order to assess the patterns of water stress and temperature for Australian chickpea production. The researchers identified four DPs accounting for 87 % of total variation. Hence, they concluded that the significant spatial variation in the drought patterns was highly associated to the efforts conducted in breeding programs for decades.
To date, neither short-term nor long-term country-wide assessments were conducted to characterize the spatial and temporal trends of drought patterns in rainfed wheat agro-ecosystems across the different climatic conditions in Iran. Moreover, an assessment was needed to quantify long-term seasonal drought patterns and their relationship with grain yield using a modelling approach. Considering these contexts, this study aimed (1) to cluster seasonal drought patterns across various rainfed wheat agro-ecosystems; (2) to analyze the frequency of drought patterns for each climate zone and selecting the representative genotypes of wheat differentiated by earliness; and (3) to identify the optimal wheat genotypes well adapted to each climatic region based on the drought patterns.
Section snippets
Study sites and regions
To represent the drought pattern (DP) across the rainfed wheat agro-ecosystems of Iran, 69 sites were chosen based on the climatic diversity and area under cultivation which cover two million ha of rainfed wheat agro-ecosystems in the country (Table 1). The sites were divided into 16 regions based on the climatic methodology followed by the Iran Meteorological Organization (http://www.irimo.ir/far/index.php) (Table 1 and Fig. 1). According to the methodology, the regions were classified based
APSIM model precisely captured grain yield and soil water balance under rainfed conditions based on the model calibration and validation
In the model calibration step, the results indicated that the model reasonably predicted the days to flowering, days to maturity and grain yield under different regions and years (Table 3, Table 5). The difference between the simulated and observed values for days to flowering was 4 days, the difference in days to maturity was 1.88 days and the difference in grain yield was 0.5 t ha−1 (Table 5). NRMSE and d values were 3.18 % and 0.96 for days to flowering, 2.15 % and 0.97 for days to maturity,
Simulated rainfed grain yield was highly associated to the occurrence of drought patterns
APSIM model could precisely simulate the growth, development, grain yield as well as soil water balance in drought-prone wheat agro-ecosystems in a wide range of climatic conditions (across regions and years) with various management practices (Tables 3,4 and 5 and Fig. 3). Previous studies showed APSIM model accuracy to simulate the grain yield under potential (with no biotic and abiotic stresses) and water-limited situations in Iranian soil and climatic conditions for analyzing yield gap (
Conclusion
The result of model evaluation showed that the APSIM crop model could accurately simulate rainfed wheat growth and grain yield for various climate types under drought-prone conditions. The impact of drought pattern (from light to severe stress) and genotype on grain yield were also accurately addressed by the modelling approach under a wide range of climatic classes (from very rainy cold regions to very warm regions with very low rainfall).
Simulation results indicated water stress was dominant
Availability of data and material
Data available within the article.
Funding
The authors did not receive support from any organization for the submitted work.
Authors contributions
Sajjad Rahimi-Moghaddam: Conceptualization, Formal analysis, Investigation, Model evaluation
Reza Deihimfard: Conceptualization, Writing Original draft preparation, Methodology
Khosro Azizi: Supervision and Reviewing, Data curation, Software
Mozaffar Roostaei: Handling soil, management, and climate data
Declaration of Competing Interest
The authors report no declarations of interest.
Acknowledgments
The authors thank Masoud Haghighat at the Agricultural Meteorological Organization of Iran and Dr. Hamed Eyni-Nargeseh at Technical and Vocational University of Ahvaz to provide some weather and soil data. We also thank Hamid Reza Amiri at Ministry of Agriculture Jihad for providing some information regarding farmer’s local management practices. A special thanks to Iran's Dryland Agricultural Research Institute for its generous contribution to data collection for evaluating the crop model.
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