Pooled ANOVA for stability of seed yield tonnes per hectare is given in Table 2. Genotype × environmental interaction as per
Eberhart and Russell’s (1966) model indicated that, Environment linear component was highly significant for seed yield
, whereas, G × E (linear) interaction was non-significant for the character. These findings are in agreement with the earlier findings of
Ghodke (1992) obtained non significant G × E for majority of the traits. Further, higher value of mean squares due to environment (linear) as compared to genotype × environment (linear) displayed that linear response of environments accounted for the most of total variation for the trait under study. Similar findings in this regard were obtained by
Kumara et al., (2015). As regard to pooled deviation (nonlinear portion of variance), which is unpredictable portion of G × E interaction was highly significant for the trait under study. This demonstrated that genotypes respond differently to variation in environmental condition, indicated that the deviation from linear regression also contributed substantially toward the differences in stability of genotypes. The results are in accordance with
Balakrishna and Natarajratnam (1989);
Sawargaokar et al., (2011); Pawar et al., (2013); Patel and Tikka (2014);
Kumara et al., (2015); Singh et al., (2015); Meena et al., (2017); Ramesh et al., (2017) and
Deepak Pal et al., (2020).
As indicated in the Table 3, the genotype GRG-177 showed highest seed yield (1.18 t/ha). While, IBTDRG-4 less seed yield (0.54 t/ha) and population mean over three environments was 0.93 t/ha. All the genotypes showed non-significant value for regression coefficient and deviation from regression. The 23 genotypes
viz., GRG-177, GRG-152, ICPH-3762, TS-3R (check), ICPL-20108, Asha (check), ICPH-2671, ICPH-2740, ICPL-99050, RVSA-15-5, ICPL-20116, LRG-105, BDN-2011-1, RVSA-15-10, IBTDREG-3, ICPL-20098, BDN-2013-45, TDRG-58, IBTTDRG-5, AGL-1603-4, IBTDRG-6, ICPH-3933 and TDRG-60 were found to have higher mean value than population mean with non significant bi and S2di values.
The genotype GRG 177 though showed highest yield, it exhibited nonlinear regression indicating highly sensitiveness to different environments. The genotype GRG 152 had second highest mean yield with positive regression (0.52) and non significant deviation from regression co-efficient indicating the its specific suitability to unfavorable environments. Considering all stability parameters the genotype ICPL 20108 considered as stable and high yielding because it had high mean yield (1.07 t/ha), regression coefficient around unity (bi=0.94) and non significant deviation from S
2d
i. In addition to stable performance of the variety ICPL 20108, it had ideal agronomic traits like medium maturity (160 days) and test weight (10.6 g/100 seeds). The average performance of genotypes for agronomic traits over three years is presented in Table 4. The genotypes ICPL 20098 and AGL-1603-4 (0.94 t/ha) had average yield above population mean, regression around unity and non significant deviation from S
2d
i indicating stableness of these genotypes across the environments. The agronomic characters of these genotypes also found ideal (Table 4). The check entry TS 3R and the hybrid ICPH 2740 had high mean with bi value less than one (
i.e around zero) and non asignificant S
2d
i. Indicating their suitability to unfavorable or low input environments. Referring to the ancillary traits (Table 4), the genotypes TDRG 60, IBTTDRG-5 and BDN-2013-45 were early maturing and had average yield above population mean. The entry LRG 41 was bold seeded genotype.
Environmental index (EI) refers to a variety that has response across environments that is parallel to the mean response of all genotypes in the trial (
i.e. the mean regression on the environmental index). The regression of genotypes for seed yield (t/ha) across environments and stability parameters is presented in Fig 1. As indicated by EI, the genotypes TDRG 60, AGL 1603-4, ICPH 2671, JKM 189 (Ch), RVSA-15-5 and BDN-2013-45 had linear regression over the environments. These findings are in accordance with
Shoran et al., (1981); Muthiah and Kalaimagal (2005);
Vannirajan et al., (2007); Patel et al., (2009); Sreelakshmi et al., (2010); Thanki et al., (2010); Sawargaonkar et al., (2011); Niranjan Kumar (2013);
Muniswamy et al., (2017); Ramesh et al., (2017) and
Manish Sharma et al., (2020).