Genotypic variability and AMMI analysis of green fodder yield and quality traits in fodder cowpea
In a study aimed at addressing the impacts of climate change, 26 cowpea genotypes were evaluated over three growing seasons. The results, as shown in Fig 2 and detailed in Table 4, revealed highly significant differences among the genotypes across various environmental conditions. Analysis across three environments revealed notable variability in green fodder yield per plant (GFY), crude fiber content (CFB) and crude protein content (CPR), underscoring the influence of environmental factors. In E1, GFY ranged from 192.67 g/plant for EC 467380 (G12) to 277.54 g/plant for GETC 23 (G20), with CFB peaking at 25.34% in GETC 15 (G17). CPR reached its highest at 22.14% for CO (FC)8 (G24). In E2, GFY achieved a high of 354.92 g/plant for GETC 40 (G21), while EC 467380 (G12) peaked in CPR at 23.56%, indicating favourable conditions for both yield and protein accumulation. E3 recorded a more balanced performance, with GFY up to 350.48 g/plant for EC 240806 (G13) and moderate fluctuations in CFB and CPR, reflecting consistent environmental conditions.
The AMMI analysis of variance for green fodder yield per plant (GFY) and quality traits-crude fibre content (CFB) and crude protein content (CPR)-revealed significant contributions (p<0.01) from environmental factors (E), genotypic variation (G) and genotype-by-environment (GEI) interactions (Table 5). Environmental effects had the most substantial impact, with the highest variance observed in GFY (184,183), while the lowest variance was seen in residuals across all traits. Among the genotypes, GFY showed the greatest variability (4,902.25), indicating considerable genetic diversity, while CPR exhibited the least variability (3.23). The genotype-by-environment interaction was most prominent for GFY (3,734.23) and CFB also showed significant interaction variance (2.50), with CPR having the lowest (2.13). Principal components analysis highlighted that PC1 captured the most variance in GFY (6,324.63) and CFB (4.23). At the same time, PC2 contributed significantly to CPR (1.57), underscoring the substantial variability driven by environmental factors, genetic differences and their interactions.
Genotype performance analysis via AMMI biplots for GFY and quality traits
The pooled mean (Table 6) green fodder yield per plant (GFY) among genotypes ranged from 210.7 g/plant G5 to 298.4 g/plant G21. Among environments, E3 showed the highest mean GFY (296.2 g/plant), while E2 was lowest (199.2 g/plant), indicating substantial environmental influence. The AMMI 1 biplot (Fig 3) identified G10, G19 and G25 as being broadly adapted and stable, combining above-average yields with low PC1 scores. In contrast, G12, G14 and G22 showed high positive PC1 values, indicating specific adaptation to environments with strong positive interactions, such as E2. Genotypes G1, G3 and G8 had high negative PC1 scores, reflecting adaptation to environments with negative interaction forces (E1 and E3). All environments exhibited large absolute PC1 values, confirming their highly discriminating nature for GEI in GFY.
The AMMI 2 biplot (PC1 vs. PC2; Fig 3) further clarified these interaction patterns. Genotypes near the origin (G10, G11, G15 and G17) were stable, while those distant from the origin, such as G21 (high positive PC1 and PC2) and G9 (high absolute PC2), exhibited pronounced, environment- specific responses. G21 was located far along the positive PC1 and PC2 axes, indicating strong adaptation to E2, which itself was positioned at the extreme positive PC1. On the negative side, G1, G3, G5 and G8 aligned with E1 and E3, each distinguished by negative PC1 values and differentiated further by their PC2 scores. Collectively, these results demonstrate that the AMMI 2 biplot effectively distinguishes both stable and specifically adapted genotypes and highlights each environment’s unique discriminative power for green fodder yield.
The pooled mean (Table 6) for CFB ranged from G5 (21.2%) to G17 (23.5%), with E2 showing the highest mean environment value (23.7%) and E3 the lowest (20.6%). The AMMI 1 biplot (Fig 4) indicated that genotypes G1, G11 and G24 had PC1 values near zero, signifying broad adaptability and stable performance across environments; notably, G24 combined this stability with above-average CFB. In contrast, genotypes G23 and G14 exhibited high positive PC1 values, reflecting specific adaptation to E1 (PC1 = 1.6), while G26, G4 and G25 showed high negative PC1 values, indicating specific adaptation to E2 (PC1 = -1.8). Among environments, E1 and E2 had the largest absolute PC1 scores, marking them as highly discriminating, while E3, with a low PC1 (0.2) but a notable PC2 (-1.2), demonstrated discrimination based on secondary interaction effects.
The AMMI 2 biplot (PC1 vs. PC2; Fig 4) further differentiated genotype responses: G14, G12 and G23 occupied positions near the origin, confirming their stability and moderate-to-high mean CFB, whereas G1 and G20, located further along the PC2 axis, reflected greater environmental sensitivity driven by secondary interaction components. Overall, environments were distinctly separated along the PC1 and PC2 axes, with E1 and E2 providing strong discrimination for identifying specific adaptations and E3 uniquely distinguishing genotypes according to secondary interaction patterns.
The pooled mean (Table 6) of crude protein content (CPR) values among genotypes ranged from G26 (18.96%) to G22 (21.18%) and G21 (21.17%), while environment means spanned from a high of 22.46% in E2 to a low of 18.59% in E3. The AMMI 1 biplot (Fig 5) identified G14, G16, G17 and G18 as genotypes with low PC1 values and above-average CPR, highlighting stable, broadly adapted performance. In contrast, G26 and G1 exhibited pronounced negative PC1 scores, indicating specific adaptation to environments with negative PC1 values (such as E3), while genotypes G12, G13, G21 and G22 showed positive PC1 values and thus specific adaptation to E2 (PC1 = 1.69), which exerts the strongest positive interactive force.
The AMMI 2 biplot (Fig 5) further distinguished genotype responses: G14, G16 and G17 were positioned near the origin, confirming exceptional stability across environments, while G26, G1 and G23 appeared much further from the origin, reflecting heightened sensitivity and stronger genotype-by-environment interaction effects. Regarding environments, E2 and E3 occupied positions with strong PC1 scores, thus acting as major discriminators among genotypes, whereas E1 was characterized by a large PC2 value, indicating that this environment primarily differentiated genotypes according to secondary, rather than primary, interaction effects.
Multi-trait stability index (MTSI)
In Fig 6, the MTSI radar chart distinctly marks genotypes G16, G7, G19 and G11 in red on the outermost circuit, highlighting their superior stability and adaptability across different environmental conditions. These genotypes exhibit the highest stability index values, making them particularly favourable for breeding programs focused on resilience and performance. Conversely, G26 is positioned near the centre, indicating the lowest stability, suggesting that its performance is less consistent across environments. This visualization effectively aids in identifying and prioritizing genotypes for further research and development.
The escalating threat of global warming necessitates the development of climate-resilient crops to ensure agricultural sustainability and food security
(Muchero et al., 2011; Samireddypalle et al., 2017). Fodder cowpea, a drought-adapted legume, stands as a critical component of livestock feed, particularly in resource-limited regions
(Mbeyagala et al., 2021; Abiriga et al., 2020). This study aimed to quantify the phenotypic stability of fodder cowpea germplasm across diverse environments, focusing on green fodder yield per plant (GFY), crude fiber content (CFB) and crude protein content (CPR), thereby identifying climate-resilient genotypes for sustainable fodder production.
The highly significant differences observed among genotypes, environments and their interaction (GEI) (Table 4, Table 6) confirm that fodder cowpea performance is a complex interplay of genetic potential and environmental influence. This aligns with extensive research on the critical role of GEI in crop breeding
(Carvalho et al., 2017; Raza et al., 2019). The overwhelming contribution of the environment to performance variation, especially for GFY, underscores the profound impact that factors like moisture and temperature have on productivity and validates the necessity of the multi-environment trial approach used here (
Slafer, 2003;
Fageria et al., 2011).
Our analysis revealed two distinct adaptation strategies among the genotypes: Specific adaptation and broad stability. For instance, the high yield of GETC 40 (G21) was realized exclusively under the favorable conditions of E2, suggesting it is a specialist genotype. This indicates that while its yield potential is high, it may lack the physiological plasticity to buffer against suboptimal conditions, possibly due to a less robust root system or higher moisture requirements
(Iqbal et al., 2024; Kebede et al., 2023). In contrast, the consistent performance of genotypes like FD 1067 (G10) for yield and CO (FC) 8 (G24) for fiber content across all environment’s points to broad stability. This suggests these genotypes possess superior homeostatic capabilities, likely conferred by robust physiological traits such as efficient water uptake or superior stomatal control, which are key markers for drought resilience
(Kuruma et al., 2019; Kindie et al., 2022).
A crucial outcome of this study was the identification of genotypes that break the common trade-off between yield and quality under stress. The AMMI analysis identified K-13-CP42 (G14), G16 (GETC 10) and G17 (GETC 15) as exceptionally stable for high crude protein, making them invaluable genetic resources
(Suvadra et al., 2025; Cardona-Ayala et al., 2021). By integrating these complex traits, the Multi-Trait Stability Index (MTSI) provided a holistic solution, conclusively identifying G16 (GETC 10), G7 (FD 711), G19 (GETC 21) and G11 (FD 1259) as the most superior genotypes overall. This approach is essential because selecting for yield alone can inadvertently lead to reduced nutritional value, thereby failing to address the regional fodder quality deficit (
Omomowo and Babalola, 2021;
Singh, 2023).
While studies like
Popoola et al., (2024) have demonstrated significant GEI in cowpea across diverse continents, our research provides a high-resolution view within the specific hot, semi-arid eco-region of Southern India. It confirms that substantial genotype re-ranking occurs even due to seasonal variations at a single location. The successful application of the AMMI model via the metan package (
Olivoto and Lucio, 2020) reinforces the robustness of this contemporary analytical approach, aligning our work with numerous studies that have used it to identify superior genotypes
(Mekonnen et al., 2022).
The practical implications for regional breeding are significant. The stable, high-performing genotypes identified-such as G10 for green fodder yield per plant and G14, G16 and G17 for crude protein content-can be immediately integrated into breeding pipelines as elite parental material to develop new climate-resilient varieties
(Fasahat et al., 2015; Shekhawat et al., 2024). Furthermore, the highly discriminative environments E1, E2 and E3 can be strategically used as testing laboratories to efficiently screen germplasm for specific strengths and weaknesses, accelerating the development of varieties tailored to distinct agro-ecological zones
(Gauch et al., 2008; Kang, 2020). Theoretically, this study reinforces that GEI analysis is a vital tool for making informed breeding decisions that can build more productive and sustainable agricultural systems in the face of climate change (
Pour-Aboughadareh et al., 2022).
However, certain limitations must be acknowledged. This study was conducted at a single location over two years, meaning its findings are most applicable to this specific agro-ecological zone (
Pour-Aboughadareh et al., 2022;
Malosetti et al., 2013). Broader validation across multiple locations is needed. Additionally, while we focused on key agronomic and quality traits, other factors critical for climate resilience, such as disease resistance and water use efficiency, were not assessed
(Balapure et al., 2016).
Future research should prioritize multi-location trials to confirm the stability of the elite genotypes identified. Molecular characterization of G10, G14, G16 and G17 could help identify the quantitative trait loci (QTLs) governing stability, paving the way for more efficient marker-assisted breeding
(Malosetti et al., 2013). Finally, investigating the underlying physiological mechanisms of these stable genotypes will provide deeper insights into their resilience and help develop the next generation of climate-smart fodder crops.