Introduction

Chilli (Capsicum annuum L.) holds immense value among various crops due to its wide consumption, versatile usage, and crucial role in culinary traditions worldwide. However, enhancing the yield remains challenging as conventional approaches to analyzing the genotype performance often overlook the significant effects and interactions that profoundly influence crop yield and selection1. The productivity and quality of chili pepper are influenced by agronomic factors, which are subjected to the impacts of cultivar selection and environmental variability across diverse environments. The genotype × environment interaction (G × E), a phenomenon where the response of a plant variety varies depending on several factors such as soil type, temperature, irrigation management, photoperiod, and pathogenic disease2,3,4 is also known as genotype-by-environment interaction (GEI). This GEI involves variations in genetic makeup that affect traits or gene expression levels in different environmental conditions5 or specialized for specific planting conditions6, posing challenges for plant breeders in introducing new cultivars and recommending superior genotypes. Concurrently, stability analysis emerges as an equally vital tool, assessing the adaptability of genotypes across various environments and contributing to a more comprehensive understanding of crop performance7,8,9 emerges as an equally vital tool, assessing the adaptability of genotypes across various environments and contributing to a more comprehensive understanding of crop performance5,10. The screening and selection of cultivars by plant breeders frequently involve the utilization of yield performance and phenotypic expression. Therefore, the primary focus of crop technology is to mitigate risk, promote yield stability, reduce costs, and increase profitability7,11.

Incorporating soilless planting systems into this framework is increasingly important. Soilless cultivation offers controlled environments that can mitigate some of the variability and unpredictability associated with traditional soil-based agriculture12. These systems allow for a more precise study of G × E interactions by minimizing external environmental variables, leading to a clearer understanding of genetic influences on yield and quality. Furthermore, soilless systems can be key in developing and selecting cultivars that are not only high-yielding but also resilient to a range of environmental conditions addressing issues of food security and sustainable agricultural practices13.

The analysis of variance (ANOVA) is a widely used statistical technique to analyze multi-environmental yield trials, aiming to detect genotype-by-environment interaction by assessing the variation among random and fixed factors such as replication, genotype, site, season, and year. However, it is important to note that ANOVA has certain limitations when detecting genotypic differences in non-additive expression, commonly referred to as G × E interaction14. Numerous statistical approaches have been developed to assess genotype stability, capturing different aspects of genotype-by-environment interaction. These methods can help identify genotypes that exhibit consistent performance across different environments which includes the stability analysis techniques deviation from regression (S2d), regression slope (bi), Wricke ecovalance (Wi2), and Shukla stability variance (σi2). Stability under a broad range of environmental conditions is observed when the genotypes’ regression coefficient (bi) approach unity in conjunction with a high trait mean.

Over the last three decades, several statistical techniques have been devised to evaluate the consistency of cultivars across different testing locations. Among the most crucial analytical techniques, biplot analysis provides a comprehensive graphical tool for visualizing and assessing G × E interactions in plant breeding and agricultural research to help researchers identify genotypes with stable performance across diverse environments and select superior cultivars. Biplot analysis has proven valuable in various crops, including cereals, legumes, vegetables, and fruits, enabling breeders to make informed decisions in cultivar development and selection15,16,17. Incorporating G × E data into biplots, researchers gain a deeper understanding of the complex interplay between genotypes and environments, leading to improved breeding strategies, interest trait improvement, and the development of resilient cultivars. AMMI (Additive Main Effects and Multiplicative Interaction) biplots and GGE (Genotype plus Genotype by Environment) biplots are the two types of biplot analysis frequently utilized18,19,20. The AMMI biplot visually represents the relationships between genotypes, environments, and the G × E interaction patterns. In an AMMI biplot, genotypes are represented as vectors, similar to other biplots. The vectors’ length and direction indicate the genotypes’ performance and direction. The GGE model characterizes the Genotype by Environment (G × E) interaction as a composite of the genotype’s main effect and the interaction between the genotype and environment. The GGE biplot identifies mega-environments, groups of similar environments where genotypes perform similarly. This help determines the ideal genotypes for specific mega-environments and assesses the adaptability and stability of genotypes across these mega-environments21. Therefore, this study aims to determine the stability analysis of yield and yield attributes in different soilless planting systems of chilli.

Conversely, genotypes displaying low mean performance for a trait signify inadequate adaptation to all environments. Furthermore, genotypes exhibiting a bi value exceeding unity demonstrate a heightened sensitivity to environmental fluctuations, indicative of below-average stability, while showcasing a more pronounced adaptability to conditions favoring high yields. The assessment of genotype stability involves examining the statistical significance of deviation from regression (S2d). Genotypes characterized by low Wricke ecovalance (Wi2) and Shukla stability variance (σi2) are considered stable, indicating their reliability in various conditions.

Materials and methods

Planting materials

The seeds from Chilli Bangi 3 (B3) and Chilli Bangi 5 (B5) were initially acquired from the Seeds Company, Bangi, Selangor, Malaysia. These seeds were then subjected to gamma irradiation in the greenhouse facility at the Malaysian Nuclear Agency Bangi, 43000 Kajang, Selangor, Malaysia, utilizing Caesium-137 (137Cs) as a source of chronic gamma irradiation22 to obtain a M1 parent. The commercial varieties (Co), on the other hand, were obtained from local agricultural supplier companies in Seri Kembangan, Selangor as detailed in Table 1. For this study, a total of 19 mutant lines (M6 generation) and 11 commercial genotypes were selected to undergo trials in four soilless planting systems: fertigation, HydroStock (commercial hydrogel), BioHydrogel (biodegradable hydrogel), and a hydroponic in two planting cycles (2020–2022). The irrigation system was installed in the rain shelter following MARDI’s System Manual (first edition). The plants were manually supplied daily with a copper standard formulation fertilizer containing (mg L−1) Mo 0.2, N 200, P 60, Ca 170, K 300, Mg 50, Mn 2, Fe 12, B 1.5, Zn 0.1, and Cu 0.1, with electron conductivity (EC) readings ranging from 0.6 to 2.5 according to the growth stage.

Table 1 List of chilli genotypes used in the study.

Field experiments

The research was organized using a split-plot Randomized Complete Block Design (RCBD), with each planting system replicated five times across two cropping cycles. The experiment was conducted under an experimental glasshouse located at Field 15, Universiti Putra Malaysia Serdang, with an average temperature ranging from 25 to 33 °C, average humidity of 75%.

Preparation of soilless planting systems

For the fertigation system, the 16″ × 16″ polybag was filled with cocopeat, ensuring adequate space at the top for watering and further planting procedures. Seedlings were then planted in the cocopeat within the polybag by making a small hole in its centre, placing the seedling inside, and gently covering it with the medium. Following planting, the polybag was positioned in an area that provided the plants with the requisite sunlight.

The process for preparing the commercial hydrogel known as HydroStock was adhered to as per the supplier's instructions. An amount of 20 g of the dry hydrogel was combined with 1.5 L of water. After a swelling period of 30 min, the hydrogel was ready to be incorporated with cocopeat.

The solidified BioHydrogel was soaked in distilled water with initial pH of 12–13 and electrical conductivity over 20.00 mScm−1. It was kept at room temperature and the water was changed daily for 6–10 days until the pH reached a neutral 7.0–7.5 and conductivity fell to 0.2–0.5 mScm-1. The time needed for neutralization varied based on the hydrogel's size and water volume. Post-neutralization, the hydrogel was crushed into smaller fragments, each 2–5 mm in diameter, to maximize surface area, preparing it for use as an amendment in cocopeat for field deployment.

The Nutrient Film Technique hydroponic system, established in a complex glasshouse, was organized using a randomized complete block design. Seedlings, aged 21 days, were transplanted into the system, ensuring that all roots were submerged in the nutrient solution. Throughout the growth period, the Electrolytic Conductivity (EC) of the solution was carefully maintained between 0.5 and 2.0 Ms cm-1. Oxygenation was provided by pumps attached to the nutrient tank, enhancing aeration. To ensure optimal nutrient availability, the nutrient stock in the tank was refreshed every time an adjustment in EC levels was made.

Stability analysis

The G × E interaction was examined utilizing the R-studio software23,24,25. The output from the G × E analysis contained univariate stability results, including the Linn and Binn (Pi), regression coefficient (bi), deviation from regression (Sd2), Shukla stability variance (σi2), Wricke’s ecovalance (Wi2), adjustments in trait means (M) and least significant differences (L.S.D.) across the planting cycles and systems for the genotype. A GGE biplot and AMMI were employed for multivariate stability to interpret the G × E interaction visually. This approach incorporates two main components, the GGE (Genotype and Genotype by Environment) and the biplot26,27, and was analyzed using R-studio software packages of ggplot2 and Agricolae23,25.

Complies with international, national and/or institutional guidelines

Experimental research and field studies on plants (either cultivated or wild), comply with relevant institutional, national, and international guidelines and legislation.

Results

“Which won where” polygon view of GGE biplot

The polygon view of the GGE biplot (Fig. 1) demonstrates significant variation in the genotype and genotype-by-environment interaction, accounting for 91%, 85%, 92%, and 93% of the variation in the yield per plant (g), number of fruits, fruit length, and fruit width respectively. The environmental markers are segmented into single, two, two, and three sectors for these traits, with unique genotypes taking the lead in each section. This pattern affirms the presence of gene-environment interactions across all the traits studied. Genotypes located at the vertex of sectors containing environmental markers indicate superior performance in yield and adaptability in those specific environments. However, the genotypes at the vertex, where no environment falls within the sector, demonstrated consistently inferior performance across all environments. Conversely, the genotypes within the polygon exhibited less responsiveness to the environment than the corner genotypes, indicating that the corner genotypes possess a superior adaptive capability across diverse environments compared to those within the polygon.

Figure 1
figure 1

Polygon view of GGE biplot (which–won–where) showing the (G + G × E) interaction effect of 30 chilli genotypes within four planting systems for (A) yield per plant, (B) the number of fruits, (C) Fruit’s length, (D) Fruit’s width. The biplot was based on Scaling = 0, Centering = 2, S.V.P. = 3. Bio = BioHydrogel, Hydros = HydroStock.

Polygon view of AMMI2 biplot

The AMMI2 analysis is a valuable graphical instrument that utilizes the information in the first two principal components (PC1 and PC2) to unravel the gene-environment interactions (GEIs), including characterizing the major environments and pinpointing genotypes that exhibit broad or specific adaptability. The distribution of the first two principal component interactions in this model account for 88.3%, 87.7%, 83.3%, and 83.2% of the variation in yield per plant, number of fruits, fruit length, and width, respectively, further substantiating the occurrence of GEI (Fig. 2A–D). These figures suggest that the primary two PCs effectively predicted the interactions among the 30 chilli genotype trials conducted across four different environmental systems, thus, providing a comprehensive understanding of how genotypes perform in varying environments. These suggested that the first two PCs of genotypes predicted the interaction of the 30 chilli genotypes trials in four environment systems.

Figure 2
figure 2

Polygon view of Additive main effects and multiplicative interaction 2 (AMMI2) biplot of the first two principal components (PC1 and PC2) showing the (G + G × E) interaction effect of 30 chilli genotypes in two planting cycles and four planting systems for (A) Yield per plant, (B) Number of fruits, (C) Fruit’s length, (D) Fruit’s width. The biplots were based on Scaling = 0, Centering = 0, and SVP = 2.

In Fig. 2, the biplot can be divided into four distinct sectors by vertical and horizontal lines that pass through the center (0, 0). Similar to the GGE biplot approach, the genotypes positioned at the polygon’s vertices are identified as the winning cultivars within the specific sectors associated with the respective environments. The spatial arrangement of the environment and genotype vectors, originating from the central point of the biplot diagram, provides a visual representation of the dynamic interaction between the environment and genotypes. The further these vectors extend from the origin, the more significant the magnitude of this interaction is likely to be. This study revealed that the sectors corresponding to yield per plant, number of fruits, fruit length, and width consist of five, seven, six, and nine distinct segments, respectively, with different genotypes winning each sector.

Genotype evaluation

The significant G × E interaction in this current study justified our evaluation of chilli genotypes for yield-attribute stability across the planting systems (Table 2). The result of the mean comparison presented in Table 3 showed that genotypes G30, G27, and G7 had the highest yield per plant, while genotypes G22 and G8 had the lowest yield per plant. While for the number of fruits, genotypes G20 and G29 recorded the highest number of fruits and contrary to G19 and G21, which revealed the lowest number of fruits.

Table 2 Analysis of variance (mean square) for yield attributes on 30 Capsicum annuum L. genotypes.
Table 3 Mean comparison of yield attributes on 30 Capsicum annuum L. genotypes within different soilless systems. The means followed by similar letters within the column for each parameter were not significantly different at P ≤ 0.05 based on the LSD multiple mean comparisons.

Genotype stability and interaction of chilli genotype for yield and yield attributes (Univariate stability methods)

For the stability analysis and the G × E interaction, the chilli genotypes are evaluated based on the yield per plant, number of fruits, fruit length, and width, which showed a positive relationship with the yield per plant. The genotypes with the lowest Pi value are considered the most superior. Hence the genotype with low Pi and high mean yield is considered stable and can be ranked from G30 > G27 > G7 > G13 > G26 > G21 > G11 > G15 > G17 > G16. Genotypes with large Pi values are considered unstable, as recorded by G22, G8, G28, G29, and G20. Genotypes with small Wi values are less affected by the environmental or planting system. The genotypes with small values were ranked as follows: G22 > G8 > G29 > G28 > G20 > G18 > G19 > G2 > G1 > G14. The most unstable genotype for yield per plant was G30, G7, G21, G13, and G11 (Table 4). For the number of fruits, genotypes with low Pi and high mean for the number of fruits are ranked from G20 > G29 > G28 > G7 > G17 > G30 > G22 > G16 > G13 > G8. Genotypes with large Pi stability values are considered unstable, as recorded by G19, G26, G14, G23, and G21. The genotypes with small Wi values for the number of fruits were ranked as G19 > G26 > G27 > G14 > G21 > G23 > G9 > G10 > G1. The most unstable genotype for the number of fruits were G20, G29, G28, G7, and G30 (Table 5). The genotype with low Pi and high mean for fruit’s length is ranked as G30 > G23 > G26 > G27 > G25 > G7 > G6 > G12 > G21 > G13. While genotypes with large Pi stability values are considered unstable, as recorded by G8, G28, G22, G29, and G18. The genotypes with small Wi values for the fruit’s length were ranked as follows: G28 > G29 > G20 > G8 > G22 > G18 > G24 > G19 > G2. The most unstable genotype for the fruit’s length was G30, G23, G26, G27, and G17 (Table 6). The stable genotype with low Pi and high mean for fruit’s width is ranked from G25 > G24 > G13 > G15 > G23 > G30 > G10 > G6 > G14 > G3. While genotypes with large Pi stability values are considered unstable, as recorded by G22, G20, G29, G2, and G8. The genotypes with small Wi values for the fruit’s width were ranked as follows: G22 > G2 > G20 > G29 > G8 > G28 > G18 > G17 > G19 > G21. The most unstable genotype for the fruit’s width were G15, G25, G30, G10, and G24 (Table 7).

Table 4 Means (corrected by least squares) (M), Linn and Bin (Pi), Regression coefficient (bi), Shukla’s stability variance (σ2i), Wricke’s ecovalence (Wi2), deviation from regression (S2d), and Annicchiarico (Wi) yield per plant planted in 4 different planting systems.
Table 5 Means (corrected by least squares) (M), Linn and Bin (Pi), Regression coefficient (bi), Shukla’s stability variance (σ2i), Wricke’s ecovalence (Wi2), deviation from regression (S2d), and Annicchiarico (Wi) the number of fruits planted in 4 different planting systems.
Table 6 Means (corrected by least squares) (M), Linn and Bin (Pi), Regression coefficient (bi), Shukla’s stability variance (σ2i), Wricke’s ecovalence (Wi2), deviation from regression (S2d), and Annicchiarico (Wi) for fruit’s length planted in 4 different planting system.
Table 7 Means (corrected by least squares) (M), Linn and Bin (Pi), Regression coefficient (bi), Shukla’s stability variance (σ2i), Wricke’s ecovalence (Wi2), deviation from regression (S2d), and Annicchiarico (Wi) for fruit’s width planted in 4 different planting systems.

Genotype ranking

A biplot with concentric circles presents the genotype ranking or “comparison with ideal genotype”. The ideal genotype always occupies the central position, with the arrowhead in concentric circles (Fig. 3A–D). Those genotypes closer to the center are more desirable than those outside the circle. In the current study, G30 falls within the inner circle, making this genotype suitable for all planting systems environments regarding yield per plant. The G20 is selected for the number of fruits, G30 for the fruit’s length and width. A genotype closer to the ideal genotype is more favorable. Thus, based on proximity to the ideal, the genotype hierarchy for yield per plant is G30 > G26 > G7 > G13 > G27.

Figure 3
figure 3

The genotypes comparison with the ideal genotype view showing the (G + G × E) interaction effect of 30 chilli genotypes in two planting cycles and four planting systems (A) Yield per plant, (B) Number of fruits, (C) Fruit’s length, (D) Fruit’s width. An ideal genotype is represented by a circle within the innermost concentric circles on average environment coordinate (AEC) –abscissa, which passes through biplot origin.

Mean vs. stability

A mean vs. stability biplot is one way to visualize G × E interactions, often used in plant breeding and genetics. The biplot’s horizontal axis (x-axis) typically represents the genotypes’ mean performance. Genotypes to the right on this axis have higher mean performance across all environments. The vertical axis (y-axis) usually represents stability. Genotypes further from the horizontal axis (either above or below) are less stable, meaning their performance varies more across different environments.

Conversely, genotypes close to the horizontal axis are more stable because their performance is consistent across different environments. In this current study, the GGE biplot analysis was employed to assess the mean versus stability perspective in explaining the variation in genotypic and genotype by environment effects for yield-related traits, namely yield per plant, number of fruits, fruit length, and width. The results, illustrated in Fig. 4, indicated that the GGE biplot analysis accounted for substantial proportions of the total variation in these traits, specifically 88%, 84%, 92%, and 94% for yield per plant, number of fruits, fruit length, and width, respectively.

Figure 4
figure 4

The mean vs. stability view showing the (G + G × E) interaction effect of 30 chilli genotypes in two planting cycles and four planting systems for (A) Yield per plant, (B) Number of fruits, (C) Fruit’s length, and (D) Fruit’s width.

The directional arrows in the biplot provided valuable insights into the ranking of genotypes based on their performance in relation to higher trait values, as indicated on the A.E.C. abscissa. Among the genotypes assessed, G30 exhibited the highest yield per plant, followed by G27, while G8 and G22 demonstrated the lowest yield per plant. Regarding the number of fruits, G20 and G29 displayed the highest fruit yield, whereas G19 exhibited the lowest fruit count. G30 and G27 showed the highest mean values for fruit length, while G13 and G23 exhibited the widest fruit girth among the genotypes. Genotype vectors projected from the AEC vertical axis offer insights into stability, with the most stable genotypes often positioned on the AEC abscissa (horizontal axis) or having the shortest projection from the AEC vertical axis.

Consequently, G26 and G30 emerged as the most stable genotypes for yield per plant, as evidenced by their shortest genotype vectors from the AEC vertical axis. For the number of fruits per plant, G16, G22, and G30 were considered stable genotypes. Similarly, G30, G23, and G26 exhibited stability in terms of fruit length. Finally, G10, G6, and G30 were identified as the most stable fruit-width genotypes. The GGE biplot analysis provided comprehensive insights into the mean versus stability perspective for evaluating genotypic and genotype by environment effects on yield-related traits. The results identified specific genotypes that excelled in trait performance and stability, thereby contributing to the understanding and improving crop breeding programs.

Additive main effects and multiplicative interaction 1 (AMMI1)

In the context of AMMI1 analysis, the first principal component (PC1) and the main trait effect are represented by the horizontal (abscissa) and vertical (ordinate) axes of the biplot, respectively. The AMMI model decomposes the effects of genotypes and environments into two primary components: additive effects and multiplicative effects. Figure 5 illustrates that all genotypes exhibited differences not only in their means but also in their interactions. For each yield-related attribute, none of the planting system scores were near zero, indicating the presence of significant interaction between the genotypes and the planting system. These suggest that genotypes are more specific to certain environments or planting systems rather than showing consistent performance across different conditions. However, noteworthy is that genotypes such as G20 and G24 (for yield per plant), G15 and G16 (for the number of fruits), G12, G23, and G30 (for fruit length), and G28 and G21 (for fruit width) displayed nearly zero scores on the first principal component (PCA1), which suggests environmental conditions relatively less influences these genotypes.

Figure 5
figure 5

The Additive Main Effects and Multiplicative Interaction 1 (AMMI1) biplot displays the principal components’ impact (PC1) on 30 chilli genotypes across two planting cycles and four systems, showcasing variations in yield per plant (A), number of fruits (B), fruit length (C), and fruit width (D).

Despite their reduced sensitivity to environmental effects, these genotypes exhibited mean values below average for yield per plant. Since plant breeders prioritize genotypes with high yield and relative stability, alternative genotypes must be considered. In this regard, for yield per plant, fruit length, and fruit width, genotypes G26 and G30 were recommended as relatively stable genotypes with nearly general adaptation to various environments Fig. 5.

Discriminative and representative ability of locations

Figure 6 presents the GGE biplot vector view to determine the discriminative ability of the tested locations. The length of the location vector in the biplot indicates the degree of discriminative ability each location possesses. In the current study, HydroStock and BioHydrogel demonstrated the highest level of informativeness or discrimination among the four planting systems evaluated for yield per plant. In contrast, fertigation and hydroponic systems exhibited lower discriminative abilities (Fig. 6). The representativeness of individual locations was assessed based on the proximate angle between the location vector and the AEC (average environment coordinate). A smaller angle indicates a higher level of representativeness for the tested location. The planting systems amended with hydrogel, specifically BioHydrogel for the number of fruits and HydroStock for the fruit’s length, were identified as the most representative locations within each mega-environment.

Figure 6
figure 6

The ‘discriminating power vs. representativeness’ view of the GGE biplot of 30 chilli genotypes planted in four soilless planting systems in two planting cycles of (A) Yield per plant, (B) Number of fruits, (C) Fruit’s length, and (D) Fruit’s width.

Discussion

This study is the first to document the contribution of genotype and environment to the morpho-physiological traits and yield and yield-related attributes of chilli genotypes across different soilless planting systems. Generally, the yield-related are conducted in different locations to determine the performance of the ideal genotypes in the specific location. The yield from the multi-soilless planting system trial enables quantification of the planting systems and the genotype by environment interaction influences. However, the evaluation of the genotypes and the planting systems or environments cannot be described by analysis of variances solely but require full exploration of G × E that can be achieved through univariate and multivariate analysis8. This study offers critical insights into the genotype and genotype-by-environment interaction dynamics of thirty chilli genotypes cultivated across four soilless systems. The observed significant variations in the yield per plant, number of fruits, fruit length, and fruit width, as illustrated by the GGE biplot (Fig. 1), underline the complex interplay between genotypes and their environments16. These variations hint at the profound influence of individual planting systems on the measured traits of chilli, with the Genotype (G), Environment (E), and G × E interactions showing high significance (P < 0.001) for all yield and yield-related attributes.

A key aspect of this genotype-environment interaction is highlighted by the differential positioning of the environmental markers across sectors on the biplot. This pattern sheds light on the unique performance of each genotype in their respective environments, which aligns with previous research underscoring the prevalence of gene-environment interactions across diverse traits. The differential positioning of the environmental markers across sectors further illuminates the unique performance of genotypes in respective environmental contexts, echoing previous research affirming the prevalence of gene-environment interactions across diverse traits27,28. Environmental factors such as nutrient availability, temperature, and humidity during the planting cycles also play a critical role in these interactions29. These observations of G × E interactions resonate with previous studies on the pronounced environmental impact on crop traits like those seen in chilli and wheat15,30. However, it’s important to note that variance analysis doesn’t entirely capture the G × E interactions’ complexity, with genotypic diversity inferred from a large sum of squares, suggesting significant differences among genotypic means and trait variability5.

Further, the study highlights the adaptability of specific genotypes across different planting systems. Genotypes G27 and G30, for instance, display superior yield across all planting systems, signifying their potential for widespread cultivation. These insights are crucial for enhancing agricultural practices, improving yields, and guiding effective selection. The GGE biplot’s utility becomes evident in this context, capturing a significant proportion of the genotype and genotype-by-environment variation for the studied traits, thereby effectively illustrating the genotype-environment interactions10. The AMMI2 analysis employed in our study proves instrumental in dissecting the complex genotype by environment interaction (GEI) in agronomy and plant breeding, consistent with prior research30,31. The significant variation explained by the first two principal components (PCs), amounting to 88.3%, 87.7%, 83.3%, and 83.2% for yield per plant, number of fruits, fruit’s length, and fruit’s width, respectively, highlights the importance of these components in capturing the GEI. This supports the argument that the performance of genotypes can vary significantly across different environments or planting systems11,32.

In the AMMI2 biplot model, positioning environmental markers and genotype vectors and identifying mega-environments partitioned into the first two PCs further demonstrated this GEI. This indicates that the environment, encompassing factors like nutrient availability and climatic conditions, is vital in influencing the genotypes’ performance across different planting systems31. Concurrently, our findings identify unique environmental sectors and genotypes showing high adaptability within these sectors, mirroring similar observations in previous research28,33. In chilli cultivation, various agronomic traits, such as the number of fruits, and fruit dimensions (length and width), significantly influence yield per plant. This yield is notably subject to variation with changes in planting environments, highlighting the relevance of genotype by environment (G × E) analysis in understanding environmental impacts on genotype expression5.

Genotype evaluation across diverse planting systems allows quantification and comparison of genotypic performance, aiding breeders in identifying superior performers for targeted selection and breeding efforts11. It also assists in discerning genotypes with broad or specific adaptability, as portrayed by the GGE biplot. The differential performance, as represented by genotypes G30, G27, and G7, which had the highest yield per plant, contrasts with genotypes G22 and G8, which yielded the least (Table 4). Likewise, genotypes G20 and G29 produced the most fruits, while G19 and G21 had the fewest. These variations underscore the significance of selecting appropriate genotypes to optimize yield across diverse environments, reaffirming the pivotal role of G × E interactions in shaping crop performance15. Therefore, a comprehensive understanding of G × E interactions is imperative for informed decisions on crop improvement strategies30.

The regression slope coefficient (bi) represents the change in the performance of a genotype in response to changes in environmental conditions to quantify the genotype’s responsiveness to different environments. A genotype with a ‘bi’ value less than 1.0 measures greater resistance to environmental change (above-average stability) and therefore increases the specificity of adaptability to low-yielding environments. In contrast, a cultivar with a ‘bi’ value of more than 1.0 is more prone to environmental changes and may not perform as well in challenging or unfavorable conditions. However, it may exhibit higher adaptability and productivity in environments that yield better results than those with a ‘bi’ value of exactly 1.0, present average stability, and be adaptable to all environments34. From the current finding for the yield per plant, the bi value is ranged between − 1.15 and 0.04. The genotype is expressed as stable when it is shown the regression coefficient of unity (bi = 1).

Although high mean yield is a desirable attribute but not an indicator of yield stability, thus the deviation from regression (S2d) value can help to quantify the portion of the variation that cannot be accounted for by the genotype–environment interaction35. The value explains the genotype stability across different planting systems or environmental conditions. A smaller value of S2d suggests lower variability of observed genotype performance, indicating greater stability, and more consistency across diverse environments, suggesting that environmental fluctuations less influence their performance. On the other hand, larger values of S2d indicate higher variability in genotype performance, indicating greater instability or sensitivity to environmental changes.

The univariate stability model is the commonly used method to measure and estimate stability1,36, including Shukla’s stability variance (σ2i), which is the method to measure the stability rather than the mean performance37, and Wricke’s ecovalence (Wi2), which is the estimation on the contribution of each genotype to the G × E interaction sum of squares. The genotypes were considered stable if the genotype had low Wi2 and σ2i values.

The mean vs. stability diagram features an average-environment axis (AEA), depicted by a continuous single arrow line that represents the average performance of genotypes across the environment, which helps breeders to understand which genotypes perform better on average. On the other hand, the SVP line is typically drawn perpendicular to the AEA to assess genotype stability across different environments. Genotypes closer to the SVP line are more stable (their performance is more consistent across varying environments). In contrast, those further from the SVP line are less stable (their performance varies more across different environments)38.

Discriminative and representative: a discriminative analysis helps elucidate the performance variations among genotypes across various environmental conditions, their average performances, and stability.A discriminating ability of test location is measured by the length of location vectors, which is approximately the standard deviation within each location38. A representative location should effectively identify superior genotypes adapted to the whole environment or planting system. According to the result of this study, HydroStock and BioHydrogel were identified as superior planting systems due to their more discriminative and representativeness. Evaluating test locations based on their ability to discriminate and representativeness delivers important information about the efficiency of each location in recommending cultivars suited to specific or broad adaptation39.

Conclusion

The study has effectively revealed the interactions between genotype and environment in chilli cultivation using various soilless planting systems. It demonstrated that these interactions significantly impact crop yield and other related traits, leading to the categorization of genotypes into three distinct groups: high-yielders, low-yielders, and stable performers. The study utilized advanced analytical tools like the GGE biplot and AMMI2 analysis to understand genotype performance and stability. Key findings include the identification of certain genotypes that excel in yield and fruit production, as well as those that show consistent performance across different environmental conditions. The research also revealed that among the planting systems evaluated, HydroStock and BioHydrogel were particularly effective in maximizing yield. These insights are crucial for guiding future crop breeding programs and optimizing agricultural practices. The study underscores the importance of selecting high-performing and stable genotypes and effective planting systems to enhance fruit productivity, contributing significantly to our understanding of genotype-environment interactions in fruit production. Further research is suggested to explore those high performing and stable genotypes under different environmental condition including the field trial to validate the findings and further expand our understanding og genotype–environment interactions.