1. Introduction
Drought management is a highly relevant global problem. Bread wheat (
Triticum aestivum L.) is an essential source of calories and proteins, and plays a crucial role in global nutrition. Adapted to the Mediterranean climate, characterized by dry summers and wet winters, common wheat plays a significant role in agricultural systems and food security in Morocco [
1,
2,
3]. This crop is particularly prominent in the regions of Gharb, Saïss, and Haouz, where favorable agro-climatic conditions and advanced agricultural practices contribute to high yields [
1,
2,
3,
4].
Bread wheat (
Triticum aestivum L.) cultivation is of paramount importance in the semi-arid regions of Morocco, as it covers a significant area and contributes to national food security. Approximately 1.5 million hectares are dedicated to bread wheat cultivation, representing a substantial proportion of the country’s agricultural land [
5]. In these regions, irregular rainfall and frequent drought periods pose major challenges to wheat production. In response, farmers have adopted optimized agricultural practices, such as using drought-resistant wheat varieties and efficient irrigation techniques, such as drip irrigation, applying approximately 50 to 60 mm of water per irrigation cycle [
6].
With water resources being limited, average annual rainfall of 200 to 400 mm is insufficient to meet crop water needs, leading to a significant decline in groundwater levels of more than 0.5 m per year in some areas [
7]. Groundwater accounts for approximately 50% of the total irrigation water supply, providing significant economic benefits and playing a crucial role in supporting local livelihoods [
8]. The application of fertilizers, particularly nitrogen, is also essential for stabilizing production and improving crop resilience. However, inefficient nitrogen management can lead to leaching losses, contributing to water pollution and greenhouse gas emissions [
9]. Nitrogen (N) management in wheat cultivation through crop modeling and irrigation methods is crucial for optimizing water consumption and nitrogen application, thus enabling efficient resource use [
10,
11]. Research conducted in China has shown that optimal nitrogen fertilization rates not only increase yields, but also improves nitrogen use efficiency under various climatic conditions [
12]. Furthermore, different nitrogen management practices significantly affect greenhouse gas emissions and wheat yields in conservation agriculture systems, with integrated nitrogen management reducing emissions while maintaining high yields [
13]. Optimized management practices can enhance agronomic and environmental outcomes in arid regions through adequate irrigation and nitrogen fertilization [
14]. Nitrogen (N), along with water supply and other nutrients such as phosphorus, is a critical factor limiting agricultural productivity. Applying nitrogen fertilizers is the most effective method increasing nitrogen accumulation in plants. The yield and quality of wheat grains strongly depend on nitrogen availability and uptake. High yields of high-quality grains can only be achieved with high nitrogen uptake rates [
15,
16]. Among the nutrients applied to crops, nitrogen is typically the most expensive for growers [
17]. Over the past five decades, the external application of mineral nitrogen fertilizers has increased sevenfold, whereas agricultural food production has only doubled [
18]. Unabsorbed nitrogen can be lost to water and the atmosphere, contributing to water pollution and greenhouse gas emissions [
19,
20,
21,
22,
23,
24,
25,
26,
27,
28,
29]. Enhancing nitrogen use efficiency (NUE) in wheat not only reduces costs for growers but also addresses environmental issues associated with nitrogen runoff and denitrification in wheat-growing regions [
21].
Genetic selection plays a crucial role in developing of more nitrogen-efficient varieties; however, achieving this objective remains a challenge. Breeding programs to date have aimed not only to improve wheat crop yields but also enhance nitrogen use efficiency (NUE) [
23]. Environmental factors, such as light, temperature, and water supply, significantly influence wheat grain yield response to nitrogen fertilizer application [
24]. These variables, which vary across sites and years, play crucial roles in the response of wheat genotypes to nitrogen fertilizer application [
25]. Additionally, soil parameters, including water retention capacity and soil type, influence wheat grain yields [
26]. The positive correlation between high nitrogen application rates and soil moisture highlights the importance of water for optimal wheat production. Variations in soil water-holding capacity, such as in sandy and clay soils, significantly affect wheat grain yield by influencing water availability to plants throughout the growing season [
27].
Wheat plants have developed several adaptive mechanisms to survive drought. These mechanisms include the accumulation of osmolytes such as proline, which helps maintain the osmotic balance of plant cells. Stomatal closure is another key response that reduces water loss via transpiration. Wheat roots can also grow deeper to access groundwater reserves, and significant new variations in root architecture related to grain production have been detected in Moroccan varieties [
28]. Additionally, leaves may develop thicker cuticles to reduce evaporation [
29,
30].
Drought negatively affects several essential physiological processes in wheat. Photosynthesis is often reduced because of stomatal closure, which limits CO
2 entry. Additionally, water stress can lead to a decrease in chlorophyll content and alter the chloroplast structure, thereby reducing photosynthetic efficiency. Oxidative stress is another major consequence of the accumulation of free radicals, which damage cell membranes, proteins, and DNA [
31,
32,
33].
Environmental factors are crucial in selecting wheat genotypes adapted to various soil and climatic conditions while maintaining good to moderate yields and efficient nitrogen use. However, researchers must also address the challenges posed by climate change, which affects nitrogen fertilization. Heat and drought are the primary obstacles to wheat yield [
34]. Additionally, extreme weather events such as floods, storms, and extreme temperatures significantly impact wheat production and pose substantial challenges for agriculture [
35,
36,
37].
To evaluate crop variety yields, it is essential to consider genetic variability (G), environmental factors (E) such as climate (including annual variability), and geography, as well as farm management of nitrogen fertilizer (N). The combination of these factors and their interactions (G × E × N) determines sustainable and secure crop yields [
38]. To date, wheat breeding programs have focused on addressing challenges related to yield potential, quality, and stress tolerance, both biotic and abiotic, through the development of predominantly higher-yielding varieties [
38]. We hypothesize that increased nitrogen fertilization and irrigation practices will synergistically enhance the yield and biomass production of selected wheat varieties.
This study aims to evaluate the effect of irrigation, environmental factors, nitrogen fertilization, and genotype on wheat yield, biomass production, and yield components. It seeks to comprehensively understand the complex interactions between these factors. Over two years (2019–2021), this research was conducted under two irrigation systems: irrigated and rainfed. We focused on six Moroccan varieties of bread wheat: three new varieties (“Snina”, “Kharouba”, and “Malika”) and three older cultivars (“Achtar”, “Amal”, and “Arrehane”). The objectives of this study were: (i) to evaluate the impact of irrigation on bread wheat yield, (ii) to analyze the effect of nitrogen fertilization on productivity and assess the performance of different varieties, and (iii) to determine the influence of environmental factors and study the interactions between genotypes, nitrogen fertilization, and environmental conditions in both irrigation systems.
3. Results
3.1. Combined Impact of Genotype, Environment and Nitrogen on the Productivity of Moroccan Bread Wheat under Different Irrigation Systems
The combined ANOVA analysis (
Table 3) reveals that the performance characteristics of Moroccan bread wheat, including biomass, yield, thousand-kernel weight, number of spikes, and number of grains, are significantly influenced (
p ≤ 0.001) by multiple factors. These factors include varieties, environments (site and years), nitrogen dose, and their interactions under both rainfed and irrigated conditions. This highlights the necessity of thoroughly understanding these factors to optimize production.
A significant observation concerns the interaction between genotypes and nitrogen doses. In the rainfed system, there is a highly significant difference (p ≤ 0.001) for biomass, number of grains and number of spikes, while no significant difference was detected in yield and thousand-kernel weight. In the irrigated system, significant differences were observed for yield (p < 0.01) and number of grains per square meter (p < 0.01). Additionally, a significant difference was observed for thousand-kernel weight (p < 0.05), although no significant difference was noted in yield. This suggests that the response of bread wheat varieties to nitrogen application can vary depending on water availability, highlighting the complexity of genotype-environment interactions.
In both systems, the interaction between genotypes and nitrogen doses revealed a significant difference for biomass in the irrigated system (p ≤ 0.001), but not in the rainfed system. Yield showed a significant difference in the irrigated system (p < 0.01), but not in the rainfed system. Thousand-kernel weight showed a significant difference in the irrigated system (p < 0.05), but not in the rainfed system. The number of spikes showed a significant difference in the irrigated system (p ≤ 0.001), but not in the rainfed system. Finally, the number of grains (exhibited significant differences in both systems (p ≤ 0.001 in irrigated and p < 0.01 in rainfed). This finding has practical implications for nitrogen management, emphasizing the necessity of tailored management strategies based on environmental conditions.
Similarly, the interaction between genotypes and environments showed a significant difference in biomass, yield, number of spikes, and number of grains in both systems (p ≤ 0.001). However, the thousand-kernel weight did not show a significant difference in either system. Understanding these genotype-environment interactions is crucial for selecting varieties adapted to specific agro-climatic regions, thereby maximizing yield potential and resource use efficiency.
The results of this study (
Table 3) show that the interactions between genotypes, environments, and nitrogen doses significantly influence the agronomic performance of Moroccan bread wheat. In the rainfed system, significant differences were observed for biomass (
p ≤ 0.001), yield (
p ≤ 0.001), number of spikes (
p ≤ 0.001), number of grains (
p ≤ 0.001), and thousand-kernel weight (
p < 0.05). In the irrigated system, only biomass and the number of grains showed significant differences (
p ≤ 0.001). These results underscore the importance of adapting nitrogen management strategies based on specific environmental conditions to optimize production. Understanding these interactions is crucial for choosing varieties adapted to different agro-climatic regions, thereby maximizing yield potential and resource use efficiency.
3.2. Genotypic Effects on Yield and Yield Components
During the two-year research period from 2019/2020 and 2020/2021, a significant upward trend was observed: new varieties’ yields were generally higher than that of older ones (
Table 3). Among the studied varieties, ‘Snina’ exhibited a notable biomass production, yielding 2340 kg/ha and 5490 kg/ha in rainfed and irrigated systems, respectively, and producing biomasses of 7570 kg/ha and 15,370 kg/ha, respectively. ‘Malika’ and ‘Kharouba’ also achieved impressive results. ‘Malika’ yields were 1940 kg/ha in the rainfed system and 4930 kg/ha in the irrigated system, with biomasses of 6500 kg/ha and 13,240 kg/ha, respectively. Similarly, ‘Kharouba’ produced yields of 1790 kg/ha in the rainfed system and 4450 kg/ha in the irrigated system, with biomasses of 5670 kg/ha and 12,130 kg/ha under the respective conditions. These results underscore the potential of newer and moderately recent varieties to enhance agricultural production.
Additionally, older varieties such as ‘Arrehane’, ‘Achtar’, and ‘Amal’ also demonstrated competitive performance. For instance, ‘Arrehane’ yields were 1610 kg/ha and 4100 kg/ha in rainfed and irrigated systems, respectively, with biomasses of 5150 kg/ha and 10,740 kg/ha. ‘Achtar’ produced yields of 1430 kg/ha and 3660 kg/ha, with biomasses of 4530 kg/ha and 9800 kg/ha under the same conditions. ‘Amal’ also produced respectable yields of 1170 kg/ha and 3180 kg/ha, with biomasses of 3700 kg/ha and 8500 kg/ha.
Overall, all varieties averaged a biomass of 5520 kg/ha in rainfed conditions and 11,630 kg/ha in irrigated conditions, with average yields of 1710 kg/ha in rainfed conditions and 4290 kg/ha in irrigated conditions. These results underscore the importance of new varieties in enhancing agricultural productivity while recognizing the enduring value of older varieties under specific conditions.
Moreover, the analysis of grain size through thousand-kernel weight is a crucial measure for evaluating crop quality. In this study, the variance analysis revealed a highly significant difference between varieties (p ≤ 0.001) under both irrigated and rainfed conditions. This indicates that the observed variations in TKW are influenced by differences between the varieties themselves.
Among the examined varieties, ‘Snina’ emerged as the best performer in terms of TKW, displaying the highest values in both systems, with 34.9 g in the rainfed system and 43.7 g in the irrigated system. These results suggest that ‘Snina’ produces larger grains compared to the other varieties evaluated. In contrast, ‘Amal’ had the lowest TKW among the examined varieties, measuring 27.9 g in rainfed conditions and 34.3 g in irrigated conditions. Although this may indicate lower performance in terms of grain size for ‘Amal’, the TKW analysis highlights significant differences between the studied varieties. ‘Snina’ stands out as the variety with the largest grains, while ‘Amal’ shows comparatively smaller grain size performance.
Analysis of variance also reveals significant variability among grains for the performances of different varieties in terms of the number of spikes per square meter (spikes/m2) under both natural precipitation and irrigated conditions (p ≤ 0.001). The variety ‘Achtar’ stands out by displaying the highest number of spikes per square meter under natural precipitation (599 spikes/m2), while under irrigation, the variety ‘Snina’ had the highest value (794 spikes/m2). Conversely, ‘Snina’ exhibits the lowest number of spikes under rainfed conditions, with 333 spikes/m2, while under irrigation, the variety ‘Amal’ had the lowest number of spikes, with 502 spikes/m2. Additionally, the average plant density across all varieties is significantly higher under irrigation (626 spikes/m2) than under natural no irrigation (450 spikes/m2).
Regarding grains per square meter, the variety ‘Amal’ showed the highest productivity under rainfed conditions, yielding the most grains per square meter at 4974 grains/m2, while ‘Snina’ achieved the highest yield under irrigation with 13,676 grains/m2. In contrast, the variety ‘Malika’ exhibited the lowest number of grains per square meter, recording 4130 grains/m2 under rainfed conditions, while ‘Amal’ had the lowest grains/m2 under irrigation with 7874 grains/m2. Across all varieties and treatments, the average grainsm2 was 5226 grains per square meter under rainfed conditions and 11,197 grains per square meter under irrigation.
The significant difference between rainfed and irrigated conditions suggests that water availability is a factor in determining the productivity of these varieties. The high performance of ‘Snina’ under irrigation and the poor performance of ‘Malika’ and ‘Amal’ under rainfed conditions indicate that some varieties are more dependent on additional water for optimum growth. It underscores the importance of selecting appropriate varieties, based on local water availability and irrigation practices, in order to obtain the best possible yields. These results underline the need to adopt targeted agricultural practices and allocate resources to improve crop productivity under variable environmental conditions.
3.3. Effect of Nitrogen on Yield and Yield Components
The analysis results revealed a significant impact of nitrogen on two key aspects of trial production: yield and its components. Across crops grown under both rainfed and irrigated conditions, nitrogen exhibited a significant effect on yield and its components (
p ≤ 0.001) (
Table 3). These findings underscore the crucial importance of nitrogen for these parameters.
Under rainfed conditions, application of 120 kg/ha of nitrogen resulted in the highest yield, reaching 2430 kg/ha, whereas no nitrogen application led to the lowest yield of only 1210 kg/ha. For the irrigated trial, the maximum yield was achieved following the application of 100 kg/ha of nitrogen, reaching 4690 kg/ha, while the minimum yield was observed without nitrogen application, at 3950 kg/ha.
Additionally, nitrogen also demonstrated a significant effect on biomass production. In the rainfed treatment, the application of 120 kg/ha of nitrogen resulted in the highest biomass, averaging 7000 kg/ha, whereas no nitrogen application led to the lowest biomass of 4250 kg/ha. In the irrigated treatment, the highest biomass was observed with 100 kg/ha of nitrogen, averaging 12,710 kg/ha, while the absence of nitrogen resulted in reduced biomass, averaging 10,670 kg/ha.
Additionally, the thousand-kernel weight showed significant differences between nitrogen rates in both systems. For crops under rainfed conditions, applying 120 kg/ha of nitrogen resulted in the highest thousand-kernel weight of 32.3 g, whereas without nitrogen, it was lowest at 30.2 g. In irrigated conditions, applying 100 kg/ha of nitrogen resulted in the highest TKW of 46.9 g, compared to the lowest TKW of 39.5 g observed without nitrogen.
Furthermore, the analysis of variance results indicated significant differences in the effect of nitrogen on the number of spikes per square meter (spikes/m2) in both cultivation systems. Under rainfed conditions, applying 120 kg/ha of nitrogen resulted in the highest number of spikes at 583 spikes/m2, while no nitrogen application led to the lowest number of spikes at 435 spikes/m2. In the irrigated treatment, applying 100 kg/ha of nitrogen resulted in the highest number of spikes at 717 spikes/m2 compared to 551 spikes/m2 without nitrogen.
Regarding grains per square meter, applying 120 kg/ha of nitrogen under rainfed conditions resulted in the highest number of grains per square meter at 5195 grains/m2, whereas the absence of nitrogen led to the lowest number of grains (3695 grains/m2). In irrigated conditions, applying 100 kg/ha of nitrogen resulted in the maximum number of grains (11,999 grains/m2), with a lower number observed without nitrogen application (10,482 NG/m2). Overall, the yields of different varieties under two irrigation regimes (rainfed and irrigated) and three levels of nitrogen fertilization levels (N0, N1, AND N2) consistently increased with higher nitrogen doses, indicating a positive response to fertilization.
Under rainfed conditions, yields increased proportionally with nitrogen dose for all varieties, reaching maximum values with N2 (
Figure 2). The most notable increases were observed in the Kharouba (1408 kg/ha) and Achtar (1174 kg/ha) varieties. In contrast, under irrigated conditions, although overall yields were higher, a trend of nutrient saturation was observed with high nitrogen doses, as evidenced by yield decreases between N1 and N2 for the Amal (reduction of 805 kg/ha) and Achtar (reduction of 470 kg/ha) varieties. Snina exhibited the largest yield difference between rainfed and irrigated conditions (3088.3 kg/ha), indicating a strong dependence on irrigation and a high sensitivity to water stress. Malika closely followed with a yield difference of 3011.0 kg/ha. In contrast, Achtar and Amal show less pronounced increases (2279.4 kg/ha and 2011.7 kg/ha, respectively), indicating a certain tolerance to water stress. These
Figure 2a,b underscore the importance of tailored irrigation management and nitrogen application strategies to optimize yields, while considering varietal specificities and water availability.
3.4. Effect of Environment (Site × Year) on Biomass, Yield, and Components
The results from the rainfed and irrigated systems at the experimental stations Afourar (AFR) and Sidi El Aidi (SEA) between 2019 and 2021 reveal significant differences in yields and variability. The data indicated consistently higher median yields in the irrigated system compared to the rainfed system across all studied years and sites (
Table 3 and
Figure 3).
In the rainfed system at the AFR experimental station, median yields increased from 1500 kg/ha in 2020 to 3000 kg/ha in 2021, showing a notable improvement. Specifically, data for AFR were 1300 kg/ha in 2020 and 3650 kg/ha in 2021, indicating an increasing trend. Similarly, at the SEA experimental station, median yields in the rainfed system were 1000 kg/ha in 2020 and 2000 kg/ha in 2021. Specifically, results for SEA were 2580 kg/ha in 2020 and 5190 kg/ha in 2021, demonstrating significant variability but overall increasing yields.
For the irrigated system, median yields were more stable and higher, increasing from 3500 kg/ha in 2020 to 5000 kg/ha in 2021 at the AFR station, and from 3500 kg/ha in 2020 to 4500 kg/ha in 2021 at the SEA station. Specifically, yields for AFR were 3690 kg/ha in 2021 and 1010 kg/ha in 2020, slightly lower than the observed medians but indicating improvement. Furthermore, for SEA, yields were 1960 kg/ha in 2020 and 4650 kg/ha in 2021, showing a significant increase.
In addition to yields, several other agronomic parameters were measured and compared. Biomass was generally higher at the AFR station compared to SEA for both years, with a significant increase observed between 2020 and 2021 at both sites. For instance, at Afourar, biomass increased from 3870 kg/ha in 2020 to 8530 kg/ha in 2021, while at Sidi El Aidi, it increased from 3010 kg/ha in 2020 to 6660 kg/ha in 2021.
Moreover, the thousand-kernel weight (TKW) shows an increasing trend between 2020 and 2021 at both sites, with the highest values observed at AFR in 2021 at 141.1 g. Specifically, TKW at Afourar increased from 99.7 g in 2020 to 141.1 g in 2021, and at Sidi El Aidi, it increased from 101.8 g in 2020 to 122.6 g in 2021.
Additionally, the number of spikes per square meter (spikes/m2) remained relatively stable between years, with a slight increase observed in 2021 at both sites. The highest values were recorded at AFR in 2021 with 593 spikes/m2. Specifically, at Afourar, the number of spikes increased from 442 spikes/m2 in 2020 to 593 spikes/m2, showing an increase from 442 spikes/m2 in 2020. Similarly, at Sidi El Aidi, spikes increased from 440 spikes/m2 in 2020 to 587 spikes/m2 in 2021.
Finally, a general trend of increasing grains per square meter (grains/m2) was observed between 2020 and 2021. The highest values were recorded at SEA in 2021 with 4924 grains/m2, while at AFR, it increased from 4340 grains/m2 in 2020 to 4987 grains/m2 in 2021.
3.5. Comparative Analysis of Wheat Varieties under Varied Nitrogen Application Rates: Two-Year Study in Rainfed and Irrigated Systems
In the rainfed system, which depends on precipitation, our research focused on evaluating the performance of different wheat varieties under various nitrogen application levels. This approach allowed us to understand how these varieties respond to fluctuations in rainfall and soil moisture, providing insights into their adaptability to climate change.
3.5.1. Effect of Nitrogen Fertilization and Wheat Varieties in the Rainfed System (2019–2020)
The 2019–2020 study examined the effect of nitrogen fertilization (N0, N1, AND N2) and wheat varieties (Achtar, Amal, Arrehane, Kharouba, Malika, and Snina) on several agronomic parameters: biomass, grain yield, thousand-kernel weight, number of spikes per square meter and number of grains per square meter.
First, the results (
Table 4) demonstrate that nitrogen fertilization significantly influences all parameters. Biomass increased from 2780 kg/ha without nitrogen to 4380 kg/ha with 120 kg/ha of nitrogen. Grain yield increased from 890 kg/ha without nitrogen to 1550 kg/ha with 120 kg/ha. TKW increased from 29.1 g without nitrogen to 31.7 g with 120 kg/ha. The number of spikes per m
2 increased from 355 to 532, and the grains/m
2 from 3 125 to 3 904, with all these differences being significant.
Next, the wheat varieties exhibited diverse performances. Particularly, Snina, showed high values of biomass and grain yield, reaching 5160 kg/ha and 1750 kg/ha, respectively, with 120 kg/ha of nitrogen. TKW varied from 25.80 g for Amal without nitrogen to 36.5 g for Snina with 120 kg/ha. Arrehane had the highest number of spikes with 695 spikes/m
2 under 120 kg/ha. The differences between varieties were significant (
Table 4).
Moreover, the interaction between variety and fertilization did not show significant differences for most parameters, suggesting a similar response to fertilization among the varieties (
Table 4).
In conclusion, increasing the nitrogen dose resulted in a significant increase in biomass, grain yield, TKW, and the number of spikes per square meter. Snina and Malika stood out due to their high performances. With the consistent effect of fertilization across all varieties, these results are crucial for optimizing agricultural practices and maximizing wheat productivity.
3.5.2. Effect of Nitrogen Fertilization and Wheat Varieties in the Rainfed System (2020–2021)
The 2020–2021 study continued to explore the effect of nitrogen fertilization (N0, N1, AND N2) and wheat varieties on various agronomic parameters. The results (
Table 5) revealed a significant effect of nitrogen fertilization on all parameters. Biomass increased from 5670 kg/ha without nitrogen to 9790 kg/ha with 120 kg/ha. Grain yield increased from 1530 kg/ha without nitrogen to 3290 kg/ha with 120 kg/ha. TKW also increased from 31.0 g without nitrogen to 33.3 g with 120 kg/ha. The number of spikes per m
2 increased from 413 to 549, and the number of grains per square meter from 3811 to 5767, with all these differences being statistically significant. Furthermore, the varieties exhibited diverse performances. Snina maintained high levels of biomass and yield, reaching 12,240 kg/ha and 4240 kg/ha, respectively, with 120 kg/ha. TKW varied from 27.0 g for Amal without nitrogen to 36.2 g for Snina with 120 kg/ha. The differences between the varieties were significant. Additionally, the interaction between variety and fertilization was not significant for most parameters, indicating a similar response among the varieties.
In conclusion, the results for 2020–2021 indicate that an increase in nitrogen application results in a significant increase in biomass, grain yield, TKW, and the number of spikes per square meter. Snina and Kharouba stood out for their high performances. With the consistent effect of fertilization across all varieties, these results are crucial for optimizing agricultural practices and maximizing wheat productivity.
In the irrigated system, which depends on a controlled water supply, our research shifted focus to evaluate the performance of various Moroccan bread wheat under different nitrogen application levels. This approach helped us understand how these varieties respond to fluctuations in water availability and soil moisture, providing valuable insights into their ability into their adaptation to changing climatic conditions.
3.5.3. Effect of Nitrogen Fertilization on Wheat Varieties’ Yield, and Grain Characteristics in an Irrigated System (2019–2020)
The analysis of data for the 2019–2020 agricultural year in an irrigated system revealed the effects of different nitrogen doses (N0, N1, AND N2) on six wheat varieties in terms of yield and their components (
Table 6). Biomass showed a significant increase with higher nitrogen doses. For N0, the average biomass was 9250 kg/ha, which increased to 10,860 kg/ha under N1 and 10,130 kg/ha under N2. The Snina variety had the highest biomass values under all doses, reaching a peak of 13,340 kg/ha under N1. This increase in biomass is attributed to improved nitrogen availability, which promotes vegetative growth.
Grain yield also increased with nitrogen doses. The average yields were 3670 kg/ha for N0, 3910 kg/ha for N1, and 3720 kg/ha for N2. The varieties Malika and Snina showed particularly high yields, with Snina reaching 4570 kg/ha under N1 and 4420 kg/ha under N2. These results indicate that irrigation, combined with adequate nitrogen fertilization, optimizes grain production.
Thousand-kernel weight (TKW) varied among varieties and nitrogen doses. Average values were 36.3 g for N0, 39.8 g for N1, and 39.0 g for N2. The Snina variety exhibited the highest TKW across all nitrogen doses, reaching 45.7 g under N2. This suggests that higher nitrogen doses can improve grain quality by increasing their weight. The number of spikes per square meter showed significant variations among different varieties and nitrogen doses. Under N0, the average was 593 spikes/m2, increasing to 730 spikes/m2 under N1, and slightly decreasing to 652 spikes/m2 under N2. Varieties Amal and Malika showed the highest number of spikes, particularly under N1, suggesting a positive response to irrigation and nitrogen fertilization.
The number of grains per square meter also varied with nitrogen doses, with averages of 8842 grains/m2 for N0, 10,470 grains/m2 for N1, and 9811 grains/m2 for N2. The Amal variety exhibited notably high grain numbers across all nitrogen doses, reaching 12,565 grains/m2 under N1, highlighting its productivity under ideal irrigation and fertilization conditions.
Additionally, the analysis of variance revealed that the effects of nitrogen doses and varieties on the measured parameters (biomass, yield, TKW, spikes/m2, and grains/m2) were significant (p < 0.001), except for the variety × nitrogen interaction, which was not significant (ns). This indicates that while varieties and nitrogen doses individually have a significant impact on performance, their interactions did not show significant variations.
3.5.4. Impact of Nitrogen Fertilization on Wheat Varieties’ Yield, and Grain Characteristics in an Irrigated System (2020–2021)
The analysis of data for 2020–2021 in an irrigated system shows the impact of nitrogen doses (N0, N1, AND N2) on six wheat varieties (Achtar, Amal, Arrehane, Kharouba, Malika, and Snina) regarding biomass, yield, thousand-kernel weight, number of spikes per square meter (spikes/m
2), and number of grains per square meter (grains/m
2). Increasing nitrogen significantly improves biomass, yield, and TKW. The average biomass increased from 12,290 kg/ha (N0) to 14,430 kg/ha (N1), with N2 showing a statistically significant difference at 128.3 kg/ha, despite no significant difference between N1 and N3. Grain yield increased from 4460 kg/ha (N0) to 5440 kg/ha (N1) and 4850 kg/ha (N2). Snina and Malika showed the best performances, with Snina reaching the highest values. The TKW varied from 37.3 g (N0) to 39.8 g (N1) and 38.2 g (N2), with Snina display the highest values. The number of spikes also increased with nitrogen, reaching 819 spikes/m
2 (N1). The number of grains per square meter increased to 13.418 grains/m
2 (N1), with Snina showing the best performance. The analysis of variance showed significant effects of nitrogen dose and variety, but not their interaction (
Table 7).
3.6. Correlation Analysis: Yield, Yield Components
The Pearson correlation matrices for irrigated and rainfed systems (
Figure 4) reveal interesting differences and similarities in the factors influencing yield.
In both systems, biomass exhibits a very strong positive correlation (R = 0.88; p ≤ 0.001) with yield, underscoring its importance as a key indicator of increased yields regardless of irrigation conditions. This robust relationship can be attributed to biomass effectively reflecting the overall health and productivity of crops.
Additionally, thousand-kernel weight shows a moderate positive correlation with yield in both systems (R = 0.55 in irrigated and R = 0.51 in non-irrigated) with (p ≤ 0.001). This highlights that heavier grains are associated with better yields, emphasizing the critical role of grain quality in achieving high yields. However, this correlation is slightly weaker in the non-irrigated system, possibly due to water stress conditions impacting grain development and maturation.
The number of spikes per square meter and the number of grains per square meter (NG) behave differently depending on the system. In the irrigated system, spikes shows a low positive correlation with yield (R = 0.33; p ≤ 0.001), suggesting that a higher number of spikes can positively influence overall yield. However, this correlation is negligible in the non-irrigated system (R = 0.18), indicating that under water stress conditions, the number of spikes per unit area has minimal impact on yield.
Similarly, NG demonstrates a weak but significant correlation with yield in the irrigated system (R = 0.33; p ≤ 0.001) and a moderate correlation in the non-irrigated system (R = 0.40; p ≤ 0.001). This implies that in the absence of irrigation, the number of grains per spike becomes a more crucial determinant of yield. Under water stress, a plant’s ability to increase the number of grains per spike can compensate for the reduction in total spike count, thereby sustaining satisfactory yields.
In conclusion, while biomass remains the primary determinant of yield in both systems, the relative importance of thousand-kernel weight and the number of grains per spike varies with irrigation levels. Thousand-kernel weight retains significance in both systems, albeit with slightly diminished influence under water stress. Conversely, the number of grains per spike assumes greater importance in non-irrigated conditions, underscoring the need to tailor crop management strategies according to irrigation conditions to maximize yields.
3.7. Principal Component Analysis (PCA) of Agronomic Characteristics of Wheat under Rainfed and Irrigated Conditions
Principal component analysis conducted on the agronomic characteristics of wheat under rainfed conditions provides a comprehensive overview of the variance explained by each component, the correlations between variables, and the influence of different environments, varieties, and nitrogen doses (
Figure 4).
The scree plot (
Figure 5A) illustrates the variance explained by each principal component. The first principal component (Dim1) accounts for 59.6% of the total variance, followed by the second principal component (Dim2) with 22.4%. Together, these components capture 82% of the total variance, indicating their substantial explanatory power. The third, fourth, and fifth components contribute less to the variance, with 13.6%, 3%, and 1.4%, respectively.
In the correlation circle (
Figure 5B), variables such as TKW (thousand-kernel weight), biomass, and yield exhibit strong correlations with Dim1, while NG (number of grains) and SPK (spikes) are more closely linked to Dim2. The length and direction of the vectors indicate the magnitude and direction of each variable’s contribution to the principal components.
The biplot (
Figure 5C) illustrates how different environments (AFR 2020, AFR 2021, SEA 2020, SEA 2021) are distributed in the space of the first two principal components. AFR 2020 and AFR 2021 are closely grouped, indicating similar environmental conditions or responses, whereas SEA 2020 and SEA 2021 show greater dispersion, suggesting variability across these environments.
In the biplot (
Figure 5D), different wheat varieties (Achtar, Amal, Arrehane, Kharouba, Malika, and Snina) are represented based on the first two principal components. Varieties such as Kharouba and Snina show significant differentiation along Dim1, while others are more clustered. The vectors indicate how variables like TKW, biomass, yield, NG, and SPK contribute to distinguishing between the varieties.
The biplot (
Figure 5E) displays the distribution of nitrogen doses (N0, N1, AND N2) along the first two principal components. The N2 dose exhibits a distinct separation along Dim1, indicating a strong response of wheat varieties to higher nitrogen doses. Variables such as yield and biomass are prominently associated with Dim1, emphasizing their sensitivity to nitrogen levels.
These analyses provide a comprehensive understanding of how agronomic characteristics, environments, wheat varieties, and nitrogen levels interact and contribute to the variability observed in the dataset.
A scree plot (
Figure 6A) illustrates the proportion of total variance explained by each principal component. The first principal component accounts for 57.3% of the total variance, followed by the second component at 28.1%. Together, these first two principal components capture 85.4% of the total data variance. This distribution indicates that the first two dimensions effectively summarize most of the information in the data, justifying their use in subsequent PCA analyses.
Figure 6B displays a correlation circle highlighting the contribution of different variables (TKW, biomass, yield, SPK, NG) to the first two principal components. Vectors representing TKW, biomass, and yield align in the same direction, indicating a strong positive correlation among these variables. The vectors for SPK and NG show positive and negative correlations, respectively, with the other variables. The cos2 plot confirms that all variables are well represented by the first two dimensions, underscoring their significance in the analysis.
Figure 6C presents a PCA biplot illustrating the distribution of samples based on environments (AFR 2020, AFR 2021, SEA 2020, and SEA 2021). The distinct environmental groups show minimal overlap, suggesting significant environmental impacts on the measured variables. SEA environments appear to exert a stronger influence on TKW, biomass, and yield, while AFR environments affect NG and SPK more prominently. This indicates that specific environmental conditions at each experimental station affect the measured parameters differently.
In
Figure 6D, a PCA biplot represents various wheat varieties (Achtar, Amal, Arrehane, Kharouba, Malika, and Snina). The dispersion of varieties in the first two dimensions indicates considerable variability among them. Varieties like Achtar, Amal, Kharouba, and Snina show significant influence on TKW, biomass, and yield, whereas NG and SPK are influenced more by varieties such as Arrehane. This dispersion reflects the genetic and phenotypic diversity of the varieties in their response to the measured variables.
Figure 6E presents a PCA biplot for different nitrogen doses (N0, N1, AND N2). The overlapping groups corresponding to nitrogen doses suggest similar effects of different doses on the measured variables. Increasing nitrogen doses appears to promote biomass and yield production while potentially impacting other variables differently.
This comprehensive PCA analysis provides insights into how different variables, environments, wheat varieties, and nitrogen doses interact and contribute to the observed data variability.