J. Agric. Environ. Sci. Vol. 7 No. 1 (2022) ISSN: 2616-3721 (Online); 2616-3713 (Print)
Publication of College of Agriculture and Environmental Sciences, Bahir Dar University 43
Genotype by Environment Interaction and Yield Stability of Drought Tolerant Mung
Bean [Vigna radiata (L.) Wilczek] Genotypes in Ethiopia
Tekle Yoseph*
1
, Firew Mekbib
2
,
Berhanu Amsalu
3
, and Zerihun Tadele
4
1
Southern Agricultural Research Institute, Jinka Agricultural Research Centre, Jinka, Ethiopia
2
Haramaya University, School of Plant Sciences, Dire Dawa, Ethiopia
3
International Livestock Research Institute, Addis Ababa, Ethiopia
4
University of Bern, Institute of Plant Sciences, Altenbergrain 21, 3013 Bern, Switzerland
*Corresponding author: tekleyoseph486@gmail.com
Received: May 4, 2022 Accepted: June 14, 2022
Abstract: A multi-environment evaluation of mung bean genotypes was conducted in six environments across
Ethiopia to select promising genotypes. This study was conducted to estimate the magnitude of genotypes by
environment interaction (GEI) and seed yield stability of the selected drought-tolerant mung bean genotypes
across different environments. A total of fifteen mung bean genotypes were used. Out of these, two released
varieties were used as standard checks. The field experiments were conducted during the 2019 main cropping
season at six locations namely Humbo, Gofa, Melkassa, Konso, Jinka, and Kako using a randomized complete
block design with three replications. Data were subjected to analysis of variance, Additive Main Effects and
Multiplicative Interaction (AMMI), and GGE bi-plot analysis. A combined analysis of variance revealed
significant variations among the genotype, environments, and GEI for yield and yield-related traits, indicating
that seed yield was significantly affected by these factors. Analysis of variance from the AMMI model indicated
the contribution of environment, genotype, and GEI was 59.6%, 16.8%, and 14.8% of the total variation in seed
yield, respectively. Sum squares of the first and the second interaction principal component axis (IPCA)
explained 47.4% and 7.4% of the GEI variation, respectively. The IPCA1 mean square was highly significant
(P≤0.01) and that of IPCA2 was significant (p≤0.05), indicating the adequacy of the AMMI model with the first
two IPCAs for cross-validation of the seed yield variation. The magnitude of the GEI sum squares was 4.4 times
that of the genotypes sum squares for seed yield, indicating the presence of substantial differences in genotypic
responses across the environments. The results for the AMMI, Yield stability index (YSI), AMMI Stability Value
(ASV), and GGE biplot, analyses depicted that the genotypes G6 (NLLP-MGC-24), G13 (Acc006), and G3
(NLLP-MGC-15) were identified as stable and high yielders across the environments and should be considered
for variety release. AMMI1 biplot showed Kako was the potential and favorable environment for mung bean
production, while Humbo was an unfavorable for mung bean production.
Keywords: AMMI Stability Value, GGE biplot, Kako, Gofa, Yield Stability Index
This work is licensed under a Creative Commons Attribution 4.0 International License
1. Introduction
Mung bean [Vigna radiata (L.) Wilczek] is an
important self-pollinated pulse crop of Asia and
can be grown in sandy and loam soils, with a pH
range of 6.2 to 7.2. Multi-environment trials allow
breeders to select the best-performing genotype for
their target areas by assessing the relative
performance of genotypes under a variety of
locations and environmental conditions (Zu, 2010).
Genotypes tested in different locations and over
years have significant fluctuations in yield due to
variations in soil fertility, unpredicted rainfall, and
the presence of other biotic and abiotic stresses
(Kang, 1993). Differential response of genotypes to
different environmental conditions is termed
genotype by environment interaction (GEI). In this
context, genotypes across environments may be
classified as stable when the classification of
genotypes remains constant in various
environments and there is significant interaction
due to the differences in the magnitude of the
responses; or complex when the classification of
the genotypes is different from one environment to
another, which is quite common and has greater
importance in plant breeding (Mohammadi and
Amri, 2013). The magnitude of an environment,
genetics, and their interaction effects are a serious
problem for the yield and stability of genotype
J. Agric. Environ. Sci. Vol. 7 No. 1 (2022) ISSN: 2616-3721 (Online); 2616-3713 (Print)
Publication of College of Agriculture and Environmental Sciences, Bahir Dar University 44
across environments because it reduces the
efficiency of the genetic gain. Comestock and Moll
(1993) suggested that GE interaction reduces the
genetic progress in plant breeding programs by
minimizing the association between phenotypic and
genotypic values. Hence, GE interaction must be
either exploited by selecting a superior genotype
for each specific target environment or avoided by
selecting a widely adapted and stable genotype
across a wide range of environments (Ceccarelli,
1996).
Genotypes x environment interactions exist, when
the responses of the genotypes to different levels of
environmental factors fail to respond similarly
(Allard and Bradshaw, 1964). Major constraints in
breeding pulses such as mung beans are the high
genotype x environment (GxE) interactions and the
low genetic diversity in the primary gene pool
(Jitendra et al., 2011). Researchers working in the
area of plant breeding have the trend of evaluating
genotypes in multi-environments, representing
favorable and unfavorable growing conditions, to
estimate and understand the stability of the
genotype across environments. Hence, Tiwari et al.
(2000) and Mehla et al. (2000) suggested testing
varieties over a large number of environments is
necessary to observe GEI effects
Grain yield performance is not the only parameter
for selection as a genotype with the highest grain
yield and would not be necessarily stable and
adaptable across locations and years. The plant
breeders need to identify adaptable and stable high-
yielding genotypes with other desirable traits under
varying environmental conditions as a desirable
variety (Showemimo et al., 2000; Mustapha et al.,
2001).
In Ethiopia, G x E interaction studies have been
conducted on different food legumes, thus on
cowpea (Tariku et al., 2018), common bean (Asrat
et al., 2008; Nigussie et al., 2012), soybean (Asrat
et al., 2009), faba bean (Gemechu et al., 2002;
Gemechu and Musa, 2002; Musa and Gemechu,
2004; Gemechu et al., 2006; Mulusew et al., 2008;
Tamene et al., 2015; Asnakech et al., 2017; Tadele
et al., 2017; Tekalign et al., 2019), field pea
(Mulusew et al., 2009; Mulusew et al., 2014), and
mung bean (Asrat et al., 2012). However,
information on the effect of genotype,
environment, and GEI on mung bean yield with
drought-tolerant traits is limited in Ethiopia. There
have been only limited studies on the use of the
GGE biplot study for mung bean genotypes
evaluation in Ethiopia. In these areas, more studies
are needed to help mung bean farmers choose the
right genotypes. Therefore, the present study was
conducted to estimate the magnitude of genotypes
by environment interaction effect and to evaluate
the performance and stability of promising
drought-tolerant mung bean genotypes for wider
and /or specific recommendations for cultivation
under farmers’ conditions in Ethiopia.
2. Materials and Methods
2.1. Description of the study areas
The field experiments were conducted during the
2019 main cropping season at six locations namely
Humbo, Gofa, Melkassa, Konso, Jinka, and Kako.
The geographical locations and mean rainfall and
temperatures of the study area over several years
(2009 to 2019) are presented in Table 1. The
weather data were collected from the nearby
stations, respective woreda, and zonal Bureau of
Agriculture and research centers (Personal
Communication).
2.2. Experimental materials
A total of fifteen selected genotypes were used. Out
of these, two released varieties were used as
standard checks and thirteen genotypes were
selected from the drought experiment where 60
genotypes were tested (Table 2). Genotypes were
sourced from Melkassa Agricultural Research
Center as well as our collections from southern
Ethiopia.
2.3. Experimental design and procedures
The experiments were laid out using a randomized
complete block design with three replications.
During planting, blended NPSB fertilizer at the rate
of 100 kg ha
-1
was applied. Agronomic
management practice namely, weeding was carried
out uniformly for all experimental units.
Experiments were planted from early June to early
July of the 2019 cropping season at each location.
The plot size was 4 m long, 0.3 m between rows,
and 0.05 m between plants. Each experimental plot
had an area of 6.0 m
2
. It consists of five rows
accommodating 80 plants per row. The distance
between plots and replications was 1 m and 2 m,
respectively. The data were collected from the
middle three rows, which have a 3.6 m
2
net plot
area.
J. Agric. Environ. Sci. Vol. 7 No. 1 (2022) ISSN: 2616-3721 (Online); 2616-3713 (Print)
Publication of College of Agriculture and Environmental Sciences, Bahir Dar University 45
Table 1: Description of the experimental sites
Experimental
sites
Soil Type
Geographical location
Rainfall
(mm)
Temperature (°C)
Altitude
(m.a.s.l)
Latitude
(N)
MinT (°C)
MaxT (°C)
Humbo
Vertisols
1390
6° 39'
710-1337
18.3
21.0
Gofa
Cambisols
1276
6°19′
800-1200
17.5
20.0
Melkassa
Andosols
1550
8°30'
763
15.73
27.31
Konso
Vertisols
1432
5°23'
787
18.4
30.70
Jinka
Cambisols
1420
5° 47'
1381
16.61
27.68
Kako
Cambisols
1407
5° 39'
637.3
23.1
38
Table 2: List of genotypes used
Genotypes
Genotypes code
NLLP-MGC-01
G1
NLLP-MGC-12
G2
NLLP-MGC-15
G3
NLLP-MGC-20
G4
NLLP-MGC-22
G5
NLLP-MGC-24
G6
NLLP-MGC-27
G7
VC1973A
G8
NM94 (VC6371-94)
G9
VC6368(46-40-4)
G10
NLLP-MGC-06
G11
Acc002
G12
Acc006
G13
N-26 (Standard check)
G14
NVL-1 (Standard check)
G15
2.4. Data collection
The quantitative data were collected according to
the descriptor of the mung bean developed by the
International Board for Plant Genetic Resources
(IBPGR, 1980). The data collected on the plot basis
were; days to flowering (days), days to maturity
(days), hundred seed weight (g), and seed yield per
hectare (kg). The data collected on a plant basis
were; plant height (cm), number of pods per plant,
five plant pod numbers, and number of seeds per
pod.
2.5. Data analysis
Different statistical packages were used to analyze
the data. GenStat Software 16
th
edition (GenStat,
2014) was used for the analysis of variance of the
individual location and the combined data over
locations, AMMI, and GGE biplot analysis. GEA-
R (Genotypic by Environment Analysis with R for
Windows) Version 4.1 was also used (Angela et
al., 2016). The AMMI model was used based on
the recommendation of Choukan (2010) who
suggested that the additive main effects and
multiplicative interaction (AMMI) are an effective
alternative method for assessing the suitable
genotype. The author also proposed that the GGE
biplot is an effective tool for the Mega-
environment analysis (which-won-where pattern),
genotype evaluation, mean performance and
stability, and environment evaluation to
discriminate among genotypes in the targeted
environment.
2.5.1. Analysis of variance
The analysis of variance of each location and
combined data over location were performed using
a mixed linear model to assess the differences
among genotypes as per Gomez and Gomez
(1984). The combined analysis of variance across
the environment was analyzed by using GenStat
Software 16
th
edition (GenStat, 2014) to determine
the differences between genotypes across the
environment, among environments, and their
interaction. Bartlett's test was used to assess the
homogeneity of error variances before combined
analysis over the environments (Bartlett, 1947). In
the combined analysis of variance, the location was
used as random while genotypes were a fixed
variable.
2.5.2. additive main effect and multiplicative
interaction model analysis
The Additive Main effect and Multiplicative
Interaction (AMMI) model analysis proposed by
Zobel et al. (1988) was used for analyzing the
magnitudes of GEI. The seed yield data were
J. Agric. Environ. Sci. Vol. 7 No. 1 (2022) ISSN: 2616-3721 (Online); 2616-3713 (Print)
Publication of College of Agriculture and Environmental Sciences, Bahir Dar University 46
analyzed using this model because AMMI
partitions the sum of squares into the interaction
principal component (IPC) axis. The AMMI
analysis of variance summarizes most of the
magnitude of GEI into one or a few interaction
principal component axes (IPCA). The AMMI
model equation is indicated below [1].
   
 
 


  

 

[1]
Where

=
the observed yield of genotype i in
environment j
µ = grand mean

= additive effect of the ith genotype
(genotype means minus the grand
mean)

= additive effect of the jth environment
(environment mean
deviation)
= eigenvalue of the interaction
principal component (IPCA) axis n



= scores for the genotype i and
environment j for the PCA axis n

= residual for the first n multiplicative
components

= error
2.5.3. GGE biplot analysis
The GGE biplot has many visual interpretations
that additive main effects and multiplicative
interaction do not have; particularly it allows
visualization of any crossover G x E interaction.
GGE biplot is close to the best additive main
effects and multiplicative interaction model in most
cases (Yan and Ma, 2006). Moreover, the GGE
biplot is more logical for biological objectives in
terms of explaining the first principal component
score, which represents the genotypic level rather
than the additive level (Yan et al., 2000). The GGE
biplot is built on the first two major components of
a principal component analysis (PCA) using the
Site Regression (SREG) model. When the first
component is highly correlated with the main effect
of the genotype, the proportion of the yield is
considered to be due only to the characteristics of
the genotype. The second component represents the
part of the yield due to the G×E (Yan, 2011). The
model for a GGE biplot (Yan, 2002) is based on
singular value decomposition of the first two
principal components [2].
Yij ì âj = ël îil çjl + ë2 îi2 çj2 + εij [2]
Where
Yij = the measured mean of genotype i in
environment j
Ì = grand mean
Âj = main effect of environment j,
ì+âj = mean yield across all genotypes in
environment j
ë1 and ë2 = singular values for the first
and second principal components,
respectively
îi1 and îi2 = eigenvectors of genotype i for
the first and second principal components,
respectively
ç1j and ç2j = eigenvectors of environment
j for the first and second principal
components, respectively
åij= residual associated with genotype i in
environment j.
2.5.4. Stability analysis
The AMMI stability parameters (Guach and Zobel,
1988; Zobel et al., 1988) and GGE biplot by using
GenStat Software 16
th
edition (GenStat, 2014) were
computed for grain yield and the GEI analyses of
variance. Accordingly, regression coefficient (bi)
and deviation from linear regression (S
2
di) from
Eberhart and Russell‟s (1966) model and
interaction principal component axes (IPCA) scores
of genotype and environment and AMMI Stability
Value from the AMMI model were computed as
per the established standard procedures for each
model. The pooled deviations mean square was
tested against the pooled error mean square by F-
test to evaluate the significance of the differences
among the deviations of genotypes from their
expected performances. Hence, to test whether
there is a significant difference among the
genotypes concerning their mean grain yields,
genotypes mean square and regression mean square
were tested against the pooled error mean square
using the F-test.
2.5.5. AMMI stability value (ASV)
Since the AMMI model does not make provision
for a quantitative stability measure that guides us to
rank genotypes in terms of their yield stability. The
AMMI stability values (ASV) were calculated to
study the stability of genotypes across the
environments following the formula of Purchase
(1997) expounded by Purchase et al. (2000) was
applied to quantify and rank genotypes according
J. Agric. Environ. Sci. Vol. 7 No. 1 (2022) ISSN: 2616-3721 (Online); 2616-3713 (Print)
Publication of College of Agriculture and Environmental Sciences, Bahir Dar University 47
to their yield stability. Therefore, AMMI stability
value (ASV) was computed to quantify and rank
genotypes according to their yield stability by using
Microsoft office excel 2007. The larger the
absolute value of IPCA, the greater the adaptability
of a specific variety for a certain environment.
Conversely, lower ASV values indicate greater
stability in different environments (Farshadfar et
al., 2011).
ASV =





[3]
Where
ASV = AMMI's stability value
SS = sum of squares
IPCA1 = interaction of principal
component analysis one
IPCA2 = interaction of principal
component analysis two.
The ASV is the distance from zero in a two-
dimensional scatter graph of IPCA1 (Interaction
Principal Component Analysis Axis 1) scores
against IPCA2 (Interaction Principal Components
Analysis Axis 2) scores. Since the IPCA1 score
contributes more to the GEI sum of squares; it has
to be weighted by the proportional difference
between IPCA1 and IPCA2 scores to compensate
for the relative contribution of IPCA1 and IPCA2
to the total GEI sum of squares.
2.5.6. Yield stability index (YSI)
YSI incorporates both mean yield and stability in a
single criterion. Low values of both parameters
show desirable genotypes with high mean yield and
stability (Bose et al., 2014; Tumuhimbise et al.,
2014). The yield stability index was calculated
using the following formula below [4].
    [4]
Where
RASV = the ranking of the AMMI
stability value
R = the ranking of mung bean genotypes
yields in all environments.
3. Results and Discussion
3.1. Combined analysis of variance across
environments
The combined analysis of variance showed
significant differences in the environment,
genotype, and genotype-by-environment
interactions (Table 3). The result revealed that there
were significant variations among genotype,
environments, and GEI for yield and yield-related
traits, indicating that the environment had a great
impact on seed yield potentials of the tested
genotypes.
As presented in Table 3, days to maturity, five
plant pods, seeds per pod, and a hundred seed
weights were significantly (P ≤0.01) influenced due
to genotype, environments, and genotype x
environment interaction. Pods per plant and seed
yield per hectare were significantly (P ≤0.01)
affected due to genotype. The environment had
exerted a significant (P≤0.01) effect on days to
flowering. The results also depicted that GEI for
days to flowering, days to maturity, plant height,
five plants pod number, number of pods per plant,
hundred seed weight and seed yield per hectare
were highly significant (P ≤0.01), while it had
brought significant (P ≤0.05) effect on plant height,
indicating that the environment had a great impact
on the seed yield potential of the tested genotypes
(Table 3). Generally, the result signifies that the
studied phenological and other yield-related traits
of mung bean genotypes were influenced by
environmental factors and it also indicated the
presence of genetic variability among the tested
genotypes. This result agreed with the previous
findings of Lal et al. (2010) on fifteen mung bean
genotypes at 10 locations and found that the
genotype by environment interaction and both
variances due to genotypes and environments were
significant, which coincides with the reports of
several researchers (Dhillion et al., 2009; Tyagi
and Khan, 2010) on soybean, Kan et al. (2010) on
chickpea, Nigussie et al. (2015) on common bean,
Yeyis et al. (2014) on field pea, Akande (2009),
and Tariku et al. (2018) on cowpea genotypes.
Moreover, this study revealed that the magnitudes
of the GEI sum square were about 4.4 times that of
the genotypes sum squares for seed yield,
indicating that there were considerable differences
in genotypic responses across environments
thereby differential responses of genotypes across
environments were observed. This result agreed
with the work of Dyulgerova and Dyulgerov
(2019), who reported that the magnitude of the GEI
sum of squares was two times larger than that of
genotypes, indicating that there was a substantial
difference in genotypic response across
environments. The larger sum of squares of GEI
J. Agric. Environ. Sci. Vol. 7 No. 1 (2022) ISSN: 2616-3721 (Online); 2616-3713 (Print)
Publication of College of Agriculture and Environmental Sciences, Bahir Dar University 48
compared to the genotype indicated larger
differences in genotypic response across
environments, indicating that there was a
considerable variance in genotypic response across
environments. Therefore, GEI complicates the
selection process as GEI reduces the usefulness of
genotypes by confounding their yield performance
and minimizing the association between genotypic
and phenotypic values (Crossa, 1990). The GEI in
the current analysis was a cross-over type whereby
a change in the ranking of genotypes for a target
environment because of the difficulty to interpret
seed yield based on genotype and environment
means alone. This finding is in line with the
previous report of Asrat et al. (2009) on soybean.
3.2. Comparison of mean seed yield across the
environments
The average environmental seed yield across
genotypes ranged from 507 kg ha
-1
at E2 (Humbo)
to 2081 kg ha
-1
at E4 (Kako) with the overall
environmental mean yield of 1164 kg ha
-1
, while
the average genotype seed yield across
environments ranged from 696 kg ha
-1
for the
genotype (G4) to 1375 and 1580 kg ha
-1
for G13
and G8, respectively (Table 4). This indicates that
the tested genotypes had inconsistent performance
across the tested environments. In this study, most
of the tested genotypes gave relatively good seed
yield performance and could be suggested that
there is an opportunity to get high-yielding mung
bean genotypes for future variety development. The
large variation due to the environments in our study
also confirmed the high diversity of weather
conditions during growing seasons and also the
locations had different soil types, temperatures, and
rainfall as well as altitude, directly affecting the
performances of the genotypes. Hence, the
selection and development of mung bean varieties
in the future should follow environment-specific
approaches.
The results of the present study are in agreement
with the work of Tariku et al. (2018) on the cowpea
genotype, who reported that the performance of
cowpea genotypes was different from location to
location, similar to that of Aremu et al. (2007) in
cowpea. Ranking based on the genotype-focused
scaling assumed that stability and mean yield was
equally important (Yan, 2002). The best candidate
genotypes were expected to have a high mean seed
yield with stable performance across all test
locations. However, such genotypes are very rare to
find in practice. Therefore, high-yielding and
relatively stable genotypes can be considered as a
reference for genotype evaluation (Yan and Tinker,
2006).
In this study, the mean values of seed yield and
yield-related traits are presented in table 5. The
highest mean seed yield (1580 kg ha
-1
) was
recorded for the genotype (G8) and the least (696
kg ha
-1
) was recorded for the genotype (G4), with
an overall mean of (1164 kg ha
-1
). Overall mean
values for days to flowering ranged from 40.42
days for the genotype (G5) to 59.77 days for the
genotype (G14). Days to maturity ranged from
66.72 to 98.98 days. Genotypes (G6, G13, G14,
and G15), respectively took 96.33, 98.98, 97.72,
and 98.39 days to attain their physiological
maturity. Plant height ranged from 37.57 cm for
(G8) to 48.79 cm for (G15). The number of pods
per five plants ranged from 38.5 for (G11) to 96.6
for (G3). In this study, the maximum pods per five
plants of 96.6, 94.9, and 88.7, respectively were
also recorded for the genotypes (G3, G2, and G8)
while the minimum number of pods per five plants
of 38.5 and 44 were recorded for G11 and G15,
respectively. Pods per plant varied from 14.03 for
G13 to 25.14 for G5. Seeds per pod ranged from
9.29 for G11 to 12.35 for G1. Hundred seed weight
ranged from 3.66 g for the genotype (G5) to 5.94 g
for G11.
Table 3: Mean square of combined ANOVA for eight traits of 15 mung bean genotypes
Source
DF
DTF
DTM
PH
FPP
PPP
SPP
HSW
SY
Genotype (G)
14
581.04**
3307.60**
147.34**
6180.2**
232.0*
11.613**
6.3254**
743921*
Environment
(E)
5
32.70*
26.993**
751.17**
4840.3**
978.6**
45.428**
2.6136**
15313847**
GEI
70
0.01**
0.004**
151.14*
242.1**
50.9**
1.449**
0.0272**
655105**
Error
178
25.54
3.524
20.95
642.1
118.1
3.163
0.3648
561079
*, ** = significant at 5% and 1% probability level, respectively, SV = source of variation, DF = Degree of freedom, GEI =
genotype by environment interaction, DTF= days to flowering, DTM days to maturity, PH= plant height, FPP= five plants
pod, PPP= number of pods per plant, HSW= hundred seed weight, SPP= the number of seeds per pod
J. Agric. Environ. Sci. Vol. 7 No. 1 (2022) ISSN: 2616-3721 (Online); 2616-3713 (Print)
Publication of College of Agriculture and Environmental Sciences, Bahir Dar University 49
Table 4: Mean Seed yield (kg ha
-1
) of 15 mung bean genotypes at six environments and stability indicators of AMMI
analysis
Genotype
E1
E2
E3
E4
E5
E6
Mean
IPCAg[1]
IPCAg[2]
G1
939
421
1101
3143
421
939
1161
-19.98967
5.99378
G2
1072
572
1237
2922
572
1072
1241
-14.48429
7.06782
G3
1320
791
1289
1509
1325
1320
1259
11.77525
17.02819
G4
944
364
583
979
364
944
696
11.49340
7.04205
G5
1709
446
1584
878
446
1709
1129
21.74822
-8.60742
G6
1437
593
1011
2499
760
1437
1290
-5.21787
1.15422
G7
2037
633
911
1237
633
1704
1192
16.79039
-11.77015
G8
1550
693
1112
3881
693
1550
1580
-25.16245
-3.87765
G9
1301
584
999
1979
584
1301
1125
1.11140
2.62966
G10
1453
557
1484
813
557
1453
1053
21.12314
0.73750
G11
1188
454
1111
904
587
1188
905
16.64242
6.21678
G12
1063
459
1022
2201
459
1063
1044
-4.66412
5.19843
G13
2098
306
1276
2833
306
1432
1375
-9.17042
-21.46960
G14
1071
457
1315
3298
457
1071
1278
-20.64006
3.65807
G15
1612
275
1188
2138
275
1278
1128
-1.35534
-11.00170
Mean
1386
507
1148
2081
563
1297
IPCAe[1]
13.36480
8.13392
8.80096
-54.21802
10.28095
13.63738
IPCAe[2]
-25.23624
13.09221
2.23948
-2.14545
20.72911
-8.67911
E1 = Gofa, E2 = Humbo, E3 =Jinka, E4 = Kako, E5 =Konso, E6 = Melkassa, G1 = NLLP-MGC-01, G2 = NLLP-MGC-12,
G3 = NLLP-MGC-15, G4 = NLLP-MGC-20, G5 = NLLP-MGC-22, G6 = NLLP-MGC-24, G7 = NLLP-MGC-27, G8 =
VC1973A, G9 = NM94 (VC6371-94), G10 = VC6368(46-40-4), G11 = NLLP-MGC-06, G12 = Acc002, G13 = Acc006,
G14 = N-26, G15 = NVL-1
Table5: Mean values of seed yield and yield-related traits of 15 mung bean genotypes
Genotypes
DF
DM
PH
FPP
PPP
SPP
HSW
SYLD
G1
42.56
69.39
42.98
53.9
14.86
12.35
4.528
1161
G2
53.22
67.72
42.02
94.9
20.19
11.07
4.028
1241
G3
45.22
67.72
40.06
96.6
22.36
10.24
4.25
1259
G4
40.69
69.39
37.82
63.2
14.81
10.63
4.667
696
G5
40.42
68.39
40.77
59.4
25.14
11.57
3.656
1129
G6
51.38
96.33
43.49
47.4
15.47
10.51
4.089
1290
G7
44.31
66.72
40.28
62
20.36
10.74
4.694
1192
G8
45.22
68.12
37.57
88.7
23.64
10.07
3.683
1580
G9
51.22
68.39
40.08
79.9
20.25
10.96
4.294
1125
G10
45.36
69.39
41.27
74.4
20.86
11.35
4.333
1053
G11
41.56
66.72
38.63
38.5
17.47
9.29
5.944
905
G12
42.69
68.727
38.69
75.4
15.31
9.63
4.52
1044
G13
57.56
98.98
43.74
61.5
14.03
10.24
4.222
1375
G14
59.77
97.72
41.74
47.5
15.36
11.51
4.639
1278
G15
55.56
98.39
48.79
44
20.36
10.18
5.361
1128
Mean
47.78
76.14
41.20
65.82
18.70
10.69
4.46
1164
SD
4.48
1.71
4.18
23.12
9.92
1.62
0.55
8.27
CV (%)
2.3
2.5
11.1
28.5
16.4
16.6
13.6
28.3
CV = Coefficient of variation, SD = standard deviation, G = genotype, DF = days to flowering, DM = days to maturity, PH =
plant height, FPP = five plants pod, PPP = number of pods per plant, HSW = hundred seed weight, SPP = seed per pod. G1 =
NLLP-MGC-01, G2 = NLLP-MGC-12, G3 = NLLP-MGC-15, G4 = NLLP-MGC-20, G5 = NLLP-MGC-22, G6 = NLLP-
MGC-24, G7 = NLLP-MGC-27, G8 = VC1973A, G9 = NM94 (VC6371-94), G10 = VC6368(46-40-4), G11 = NLLP-MGC-
06, G12 = Acc002, G13 = Acc006, G14 = N-26, G15 = NVL-1.
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Publication of College of Agriculture and Environmental Sciences, Bahir Dar University 50
3.3. Stability analysis
3.3.1. Additive main effects and multiplicative
interaction analysis
The AMMI analysis of variance for seed yield (kg
ha-1) of 15 mung bean genotypes tested at six
environments is presented in Table 6. Considering
the additive component of the analysis, genotype
had brought significant (P≤0.01) effects on seed
yield, while the environment significantly
(P≤0.001) affected seed yield. A similar result was
reported by Kocaturk et al. (2019) on soybean
genotypes, who reported that significant (P≤0.01)
effects were observed due to environment,
genotype, and G×E interaction for the seed yield
and yield components. In this study, the
environment accounted for the largest part of the
variation in seed yield (59.6%) followed by
genotype (16.8%). This finding is supported by the
works of (Asrat et al., 2009; Kocaturk et al., 2019)
on soybean, and Tamene et al. (2013) on field pea,
that demonstrating the environment accounted for
the largest part of the variation in seed yield
followed by the genotype. Similarly, Yan and Kang
(2003) reported the environment was considered as
the predominant source of variation. In the current
study, the largest variation in seed yield was
explained by environments, which indicated the
presence of different environments that can be sub-
grouped into mega-environments. This result is in
agreement with the work of Dessalegn et al. (2018)
on finger millet, who reported that the difference in
seed yield across environments implies that the
environments are highly variable. This indicated
the presence of different environments that can be
sub-grouped into mega-environments, since, the
largest variation in seed yield was explained by
environments.
Regarding the multiplicative component, genotype
by environment interaction significantly (P≤0.01)
influenced seed yield. According to the result of
AMMI, (14.8%) was explained due to GEI effects
on the variation in the total sum of squares (Table
6). This finding conforms to the report of Kocaturk
et al. (2019) on soybean, who reported that the GE
interaction explained (20.84%) of the total
variation. The highest share of the total sum
squares was contributed by environment and
genotype total sums of squares as compared to the
GEI, with large differences among environmental
means causing most of the variation in seed yield
of mung bean. This finding also coincides with the
previous works on cowpea (Akande, 2009;
Sarvamangala et al., 2010; Nunes et al., 2014;
Tariku et al., 2018), Zali et al. (2012) in chickpea
who reported that the larger contribution of GEI
than genotype effect for the observed yield
variation was due to large contribution of the
environment in GEI.
The AMMI model extracted two significant
Interaction Principal Component Axis (IPCAs)
from the interaction component (Table 6). The
multiplicative component of the AMMI further
revealed that the mean squares were highly
significant (P≤0.01) for the first interaction
principal component axis (IPCA1) and significant
(P≤0.05) for the second interaction principal
component axis (IPCA2). Hence, these two IPCAs
(IPCA1 and IPCA2) captured 47.4% and 7.4% of
the interaction of sum squares, respectively
accounting for a total of 54.8% of the total GEI
sum of squares. Moreover, the IPCA1 mean square
was greater than that of IPCA2, indicating the
presence of differences in seed yield performance
of the genotypes as a result of GEI. This finding is
in agreement with the previous reports by Tamene
et al. (2013) for field pea, Hagos and Fetien (2013)
for bread wheat, and Ashraf et al. (2016) on flax.
The first and the second IPCA together explained
54.8% of the variability in seed yield of mung
beans due to GEI. This indicated that the first two
IPCAs had exerted a significant contribution to the
variations in GEI.
In this study, the two IPCA's accounted for greater
than 50% of the interaction of sum square and were
significant. Therefore, the AMMI model with the
first and second multiplicative terms was adequate
for cross-validation of seed yield variation
explained by GEI that can easily be visualized with
the aid of the biplot whereas, the residual was
considered as noise. The results were in agreement
with the several authors who took the first two
IPCAs for GGE biplot analysis for different crops
(Zobel et al., 1988; Mohammadi and Mahmoodi
2008; Asrat et al., 2009; Hagos and Fetien, 2013;
Tamene et al., 2013; Kilic, 2014; Pržulj et al.,
2015; Dyulgerova and Dyulgerov, 2019) which
showed a similar magnitude of GEI variance
revealed by the first two principal components of
GEI and indicated that AMMI with the first two
multiplicative terms was the best predictive model.
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Publication of College of Agriculture and Environmental Sciences, Bahir Dar University 51
Table 6: AMMI ANOVA for seed yield (kg ha
-1
) of 15 mung bean genotypes
Source
DF
SS
MS
Sum of squares
explained (%)
GxE Interaction
explained (%)
Cumulative
explained (%)
Total
269
238218571
885571
Treatments
89
132841482
1492601***
33.6
Genotypes
14
10414899
743921**
16.8
Environments
5
76569237
5313847***
59.6
Block
12
30842052
2570171ns
5.79
Interactions
70
45857346
655105**
14.8
IPCA 1
18
37882199
2104567**
47.4
47.4
IPCA 2
16
5250316
328145*
7.4
54.8
Residuals
36
2724831
75690*
1.7
Error
168
74535037
443661
E = Environments, G = Genotypes, SS = Sum of Squares, MS = Mean Squares, DF = Degree of Freedom, IPCA1 =
Interaction Principal Component Analysis Axis 1 scores, IPCA2 = Interaction Principal Components Analysis Axis 2 scores.
3.3.2. GGE biplot analysis
The GGE biplot displays the genotypic main effect
(G) and genotype by environment (G x E)
interaction of a genotype by the environment data
set (Yan et al., 2000). The application of the biplot
for partitioning through GGE biplot analysis
showed that PC1 and PC2 accounted for 75.22%
and 14.06% of the GGE sum of squares,
respectively (Figure 1).
3.3.3. Mean performance and stability of
genotypes
Desirable genotypes are those located close to the
ideal genotype. Genotypes G8, G6, and G15 can be
thus used as benchmarks for the evaluation of
mung bean genotypes since they are placed near the
ideal genotype and found near the first concentric
circle, and thus are desirable genotypes. This
finding is in line with the reports by Muez et al.
(2015), who found outstanding genotypes near to
the ideal genotype in wheat. Based on the average
environmental coordination (AEC) method,
genotypes (G4, G10, and G11) were the most
unstable and undesirable genotypes across the
tested environment since these genotypes had a
larger distance from the origin of the biplot and
were found far distant from the first concentric
circle (Figure 1).
The ideal genotype is the one presenting high
means and is identified based on the length of the
vector; thus, the longer the PC1 and PC2 without
projections and the closer to the concentric circle,
the better the genotype (Santos et al., 2017). Such
an ideal genotype is defined by having the greatest
vector length of the high-yielding genotypes and
with zero GE, as represented by the small circle
with an arrow pointing to it (Yan, 2001). Thus,
starting from the middle concentric circle pointed
with arrow concentric circles were drawn to help
visualize the distance between genotypes and the
ideal genotype (Yan and Tinker, 2006). Based on
this, the genotype (G13) was considered the ideal
genotype and was followed by the genotype (G6).
Genotypes were classified in the following order
according to their performances: Genotype (G13) >
(G6) (G8) > (G15) > (G9) (G2) (G14)
(G7) > (G1) (G12) (G3) > (G5) > (G10) >
(G11) > (G4). A position in either direction away
from the biplot origin, on this axis, indicates
greater GEI and reduced stability (Yan, 2002).
Genotypes (G8, G6, and G15) are located on the
next consecutive concentric circles, and these
genotypes are considered the most desirable
genotypes. On the other hand, undesirable
genotypes were those very far distant from the first
concentric circle; namely, genotypes (G4, G10, and
G11) in Figure 1.
The ranking of fifteen mung bean genotypes based
on their mean yield and stability performance is
shown in Figure 2. The line passing through the bi-
plot origin is called the average tester coordinate
(ATC), which is defined by the average PC1 and
PC2 scores of all environments (Yan and Kang,
2003). The ordinate of the AEC is the line that
passes through the origin and is perpendicular to
the AEC abscissa indicating a greater G×E
interaction effect and reduced stability in either
direction away from the biplot origin and separates
genotypes with below-average means from those
with above-average means (Bhartiya et al., 2017).
For selection, the ideal genotypes are those with
both high mean yield and high stability. The
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average yield of a genotype is approximated by the
projections of their markers on the AEC x-axis
while the stability is determined by the projection
onto the AEC ordinate line (y-axis) (Yan and
Rajcan, 2002). As shown in Figure 2, the genotypes
further along the average tester axis (ATA), away
from the biplot origin and in direction of the arrow
(to the left), exhibited higher mean performance.
Therefore, the genotypes that gave higher yield
values were in the order of (G8) > (G13) > (G6) >
(G14) > (G15); while the lowest yielding genotype
was (G4). Generally, in the bi-plot, as shown in
Figure 2, the genotypes G6 (NLLP-MGC-24), G15
(NVL-1), and G8 (VC1973A) can be considered as
genotypes with both high yield and stable
performance since these genotypes are close to the
origin and have the shortest vector from the ATC.
The genotypes with the highest yielding
performance but relatively low stability were G7
(NLLP-MGC-27), whereas the genotype with low
yield and low stability were G5 (NLLP-MGC-22)
and G10 (VC6368 (46-40-4)). The other genotypes
on the left side of the line with no arrow have yield
performance greater than the mean yield and the
genotypes on the right side of this line had yields
less than the mean yield.
As indicated in the bi-plot (Figure 2) the genotypes,
G6 (NLLP-MGC-24), G15 (Acc0013), and G8
(VC1973A) were the most stable genotypes with
better mean yield performance. The genotypes G1
(NLLP-MGC-01), G14 (N-26), G10 (VC6368 (46-
40-4)), G12 (Acc002), G7 (NLLP-MGC-27), and
G5 (NLLP-MGC-22) can be recommended for
specific adaptation, whereas genotypes G6 (NLLP-
MGC-24), G9 (NLLP-MGC-09), G8 (NLLP-
MGC-08), G15 (NVL-1), G11 (NLLP-MGC-06),
G4 (NLLP-MGC-20), G13 (Acc006), and G3
(NLLP-MGC-15) can relatively be recommended
for wider adaptation.
Figure 2: GGE biplot-based genotype-focused scaling for comparison of the genotypes with the stable genotype
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Figure 2: The AEC Views of the GGE Biplot Based on Environment-focused Scaling for the Mean Performance and
Stability of Genotypes
Figure 3: Mean and stability view of the GGE bi-plot for mung bean genotypes evaluated at six environments
PC1 (75.22 %)
PC2 (14.06 %)
G1
G10
G11
G12
G13
G1
G15
G2
G3
G4
G5
G6
G7
G8
G9
Gofa
Humbo
Jinka
Kako
Konso
Melkassa
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3.3.4. 'Which-Won-Where' patterns of genotypes and
environments
As indicated in Table 6, the residual mean square
for seed yield was significant (P≤0.05), suggesting
that the importance of constructing an AMMI
biplot is very low or good for nothing. The polygon
view of the GGE biplot is the best way the
identification winning genotypes by visualizing the
interaction patterns between genotypes and
environments (Yan et al., 2000; Yan and Kang,
2003). Therefore; the GGE biplot has been used in
a variety of trials to identify the best-performing
genotype(s) across environments, and categorize
the best genotypes for specific environments,
whereby specific genotypes can be recommended
to specific environments (Yan and Kang, 2003;
Yan and Tinker, 2006).
Therefore, it was necessary to construct a GGE
biplot for visual observation to understand which
genotypes were best performed in which
environment or which genotypes were stable and
unstable (Figure 4). A polygon view of GGE was
formed by connecting the vertex genotypes with
straight lines and the rest of the genotypes were
placed within the polygon. Genotypes (G8, G13,
G7, G5, G4, and G1) were the vertex genotypes,
having the largest distance from the origin and
were more responsive to environmental changes
and gave high yield except G4 were considered as
specially adapted genotypes. The genotypes located
on vertices of polygon performed either best or
poorest in one or more environments. Therefore,
these genotypes are best in the environment lying
within their respective sector in the polygon view
of the GGE-biplot (Yan and Tinker, 2006); thus
these genotypes are considered specifically
adapted. The vertex genotypes in each sector are
the best genotype in environments whose markers
fall into the respective sector. If a genotype at an
angular vertex of the polygon falls within one
sector with an environment marker (or with several
markers), that means that the yield capacity of this
genotype was the highest in this particular
environment. Environments within the same sector
share the same winning genotypes and
environments in different sectors have different
winning genotypes. Genotypes (G8 and G13)
performed well at Kako while genotypes (G5 and
G7) performed well at Gofa and Melkassa and were
moderately adapted to Jinka. Two vertex
genotypes, G1, and G4 had the highest yield in
none of the environments (Figure 4). Genotypes
close to the origin of axes have wider adaptation
(Fetein and Bjornstand, 2009). In this study, the
genotypes (G3, G9, G2, G12, G15, G6, G11, and
G14) were located within the polygon and were
less responsive. This finding is supported by the
previous works (Yan et al., 2001; Yan and Tinker,
2006), who reported that the genotypes within the
polygon and nearer to origin were less responsive
than the vertex genotypes.
The polygon view of the GGE-biplot analysis in
(Figure 4) helps to detect cross-over and non-
crossover genotype-by-environment interaction and
to analyze possible mega environments in multi-
location yield trials (Yan et al., 2007). The
perpendicular lines were equality lines between
adjacent genotypes on the polygon, which facilitate
visual comparison of them. Line 1 is between G8
and G13 and line 2 is perpendicular to side G13
and G7; line 3 is perpendicular to side G7 and G5;
lines 4 and 5 are perpendicular to side G10 and
G11; similarly, line 6 is perpendicular to side G4
and G1; while, line 7 is perpendicular to side G1
and G8. The environments fall into two quadrants
while the genotypes are into four quadrants. In the
GGE biplot, the vectors from the biplot center
divided the graph into seven sectors.
The GGE biplot presented in Figure 4, indicating
that the best performing genotypes for a specific
environment and the group of environments. This
finding is following the results of (Yan et al., 2007;
Dessalegn et al., 2018) who reported that when
different environments fell into different sectors; it
shows that they had different high-yielding
cultivars for those sectors, and also the presence of
a cross-over interaction. The rays of the bi-plot
divided the plot into seven sections. The
environments appeared in three of them, revealing
two mega environments. The vertex families for
each quadrant represented the genotypes with the
highest yield in the specific environment hence the
highest yielding genotypes were identified for each
sector. This finding is in agreement with the
previous reports on soybean genotypes (Bhartiya et
al., 2017; Ramos et al., 2017; Kocaturk et al.,
2019), who reported that the GGE biplot created
for soybean genotypes in seed yield was divided
into six or eight sectors. When using the first two
principal components, two clusters of environments
(mega-environments) were formed using the GGE
biplot methodology, indicating the environmental
groupings, which suggests the possible existence of
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different mega-environments. The polygon view of
the GGE biplot indicated the presence of a
crossover G x E interaction as the environments
fell in different sectors of the polygon view and had
different high-yielding genotypes (Yan and Kang,
2003). The current test locations could be grouped
into two different mung bean-growing mega-
environments. Thus, in our studies, the first mega-
environment consists of environments Jinka,
Humbo, Konso, Gofa, and Melkassa whereby
genotypes (G5 and G7) in Gofa and Melkassa
produce the highest yield (Figure 4), while the
genotypes (G8 and G13) are producing the highest
yield in Jinka, Humbo, and Konso.
3.3.5. Discriminating and representativeness of
the test environments
The IPCA scores of the genotype in the AMMI
analysis signify the adaptability of the genotypes
across environments and the relationship between
genotypes and environments. This is supported by
the reports of (Zobel et al., 1988; Gauch and Zobel,
1996). Therefore, genotypes with small scores
close to zero have low interactions and were stable,
whereas, genotypes with large scores have high
interactions and were unstable. In the present
investigation, IPCA1 alone and despite positive or
negative signs, genotypes (G6, G9, and G12) had
small scores close to zero and were stable, while
the genotypes (G10, G3, G5, G7, G8, G11, G1, and
G14) had large IPCA1 scores and far from zero
were unstable (Figure 5). The genotype (G9) had a
small and positive sign of IPCA1 scores and thus
this genotype was stable across the environments.
Oliveira et al. (2014) and Tariku et al. (2018)
reported that the genotypes with lower IPCA1
scores would produce lower E interaction
effects than those with higher IPCA1 scores and
have less variable yields or more stable across
environments. In the present study G3, G13, G8,
G5, G7, G1, G14, and G10 had more responsive
since they were away from the origin whereas the
genotypes G4, G11, and G15 were close to the
origin and hence they were less sensitive to
environmental interactive forces while genotypes
G6, G9 and G12 were closest to the origin and
hence had almost no interaction forces. Genotypes
(G9, G11, and G4) had a positive sign of IPCA1
scores and had a shorter vector to the origin. Here
the genotype (G9) is adapted to Jinka while
genotypes (G4 and G11) are adapted to Humbo,
genotypes (G5 and G7) are adapted to Gofa and
Melkassa, while genotype (G3) is adapted to
Konso. In contrast, the genotype (G8 and G13) was
adapted to Kako with a larger and negative IPCA1
score.
As shown in Figure 5, the discriminating ability
and representativeness of test environments, Kako,
Konso, and Gofa were more discriminating
environments with longer vectors and larger angles
which provides much information about differences
among genotypes. These environments cannot be
used for selecting superior mung bean genotypes,
but are useful in culling out unstable genotypes.
Environments with longer vectors are more
discriminating with the genotypes whereas
environments with very short vectors are little or
not informative on the genotype difference (Yan,
2002; Yan et al., 2007). On the other hand, if the
marker of a test environment is close to the biplot
center, having a short vector, all genotypes in it are
similar, and this environment is not informative
about their differentiation. Environments with
short spokes do not exert strong interactive forces
while those with long spokes exert strong
interaction.
In this study, Jinka, Humbo, and Melkassa had
relatively short vectors and were close to the origin,
indicating that all genotypes performed similarly
and therefore it might provide little or no
information about the genotypes' differences. The
ideal environment is representative and has the
highest discriminating power (Yan and Tinker,
2006). Therefore, it should not be used as a test
environment for mung bean genotypes. As
suggested by Yan and Tinker (2006), though,
identification and removal of non-informative test
environments as well as identification of test
environments for yield evaluation trials require
multiyear data. If budgetary constraints allow only
a few test environments, these test environments
would be the first choice. The cosine of the angle
between environment vectors is used for the
assessment of approximation between
environments; the smaller the angle between
environment vectors; the larger the correlation
between them (Yan and Holland, 2010). The
smaller the angle, the more representative the
environment is (Yan and Tinker, 2006; Yan et al.,
2007). Representativeness of the test environment
is visualized by the angle formed between the
environment vector and abscissa of the average
environment axis. Correspondingly, there is a
strong correlation between environments Humbo
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Publication of College of Agriculture and Environmental Sciences, Bahir Dar University 56
and Konso since the cosine of the angle between
these two environment vectors is small. As
suggested by Yan (2001), discriminating ability
and representativeness are the important properties
of test environments. An ideal environment should
be highly differentiating for the tested genotypes
and is also representative (Yan and Kang, 2003).
Thus, environments Kako, Konso, and Gofa with
long vectors had high discriminating power, and
environments Jinka, Humbo, and Melkassa were
characterized by low discriminating power (Figure
5). Hence, environments Kako, Gofa, and Konso
exerted strong interaction forces while the rest
three (Jinka, Humbo, and Melkassa) did less.
Therefore, the tested environments, Kako, Gofa,
and Konso were more discriminating environments
with longer vectors and larger angles which
provides more information about differences
among genotypes. Contrastingly, Jinka, Humbo,
and Melkassa had relatively short vectors and were
close to the origin and all genotypes performed
similarly and therefore provide little or no
information about the genotypes' differences
(Figure 5). On the contrary, the genotypes near the
origin are not sensitive to environmental interaction
and those distant from the origins are sensitive and
have large interaction.
Figure 4: Polygon view of GGE biplot showing the relationship among environments and the specific ideal niches of
the tested genotypes
J. Agric. Environ. Sci. Vol. 7 No. 1 (2022) ISSN: 2616-3721 (Online); 2616-3713 (Print)
Publication of College of Agriculture and Environmental Sciences, Bahir Dar University 57
Figure 5: Discriminating power and representativeness of test environments
3.3.6. AMMI stability value (ASV) and yield stability
index (YSI)
According to the ASV model, genotypes (G9),
(G15), and (G12) were stable and high yielders
among the tested genotypes, indicating that the
yield performance and stability had the same trend
in the present study (Table 7). Similarly,
Annicchiarico (2002) noted the dynamic of stable
genotype and yield response that is always parallel
to the mean response of the tested environments.
Such findings have been observed by Getachew et
al. (2015) in chickpea, Nigussie et al. (2015) in
common bean and Tariku et al. (2018) in cowpea.
However, genotypes G10, G8, and G14 were the
most unstable. These genotypes are adapted to
specific and favorable environments. Likewise,
Lotan et al. (2014) reported genotypes with the
higher IPCA score and AMMI stability values were
more specifically adapted to a certain environment.
The principles of stability alone might not be the
only selection parameter because the most stable
genotypes would not necessarily give the best yield
performance. Therefore, as per the suggestion
(Hassan et al., 2012; Lotan et al., 2014), the
stability per se should however not be the only
parameter for selection because the most stable
genotypes would not necessarily give the best yield
performance.
Therefore, there is a need for approaches that
incorporate both mean yield and stability in a
single index. To this end; the yield stability index
(YSI) method incorporates both yield and stability
into a single index, reducing the problem of using
only yield stability as the single criteria for the
selection of genotypes. Genotypes with the least
YSI values are considered the most stable with a
high grain yield (Bose et al., 2014; Lotan et al.,
2014). Genotypes G6 and G13 were the most stable
with low YSI values and high mean performance.
Therefore, the yield stability index (YSI)
discriminated genotypes G6 and G13 with high
adaptability and high grain yield (Table 7). Thus,
according to the YSI method, the most desirable
genotypes which can be considered as widely
adapted and with seed yield above the grand mean
(1164 kg ha
-1
) among 15 mung bean genotypes are
presented in Table 7. Similarly, Hassan et al.
(2012) indicated that both yield and stability should
be considered simultaneously to exploit the useful
effect of GE interaction and to make the selection
of the genotypes for a diverse environment.
Conversely, genotypes like G1, G4, G5, G9, G10,
G11, G12, and G15 had high YSI values and below
the grand mean (1164 kg ha
-1
) seed yield
performance, which indicates instability of the
genotypes across the tested environments.
Table 7: Mean seed yield (kg ha
-1
) of fifteen mung bean genotypes, AMMI stability values (ASV), Ranks, yield
stability index, IPCA1, and IPCA2 scores
J. Agric. Environ. Sci. Vol. 7 No. 1 (2022) ISSN: 2616-3721 (Online); 2616-3713 (Print)
Publication of College of Agriculture and Environmental Sciences, Bahir Dar University 58
Genotypes
IPCA1
IPCA2
ASV
R
a
MSY
R
y
YSI
G1
-19.98967
5.99378
6.89
11
1161
8
19
G2
-14.48429
7.06782
5.55
8
1241
6
14
G3
11.77525
17.02819
4.89
7
1259
5
12
G4
11.49340
7.04205
4.87
6
696
15
21
G5
21.74822
-8.60742
6.95
12
1129
9
21
G6
-5.21787
1.15422
3.68
4
1290
3
7
G7
16.79039
-11.77015
5.84
9
1192
7
16
G8
-25.16245
-3.87765
8.60
14
1580
1
15
G9
1.11140
2.62966
1.56
1
1125
11
12
G10
21.12314
0.73750
10.82
15
1053
12
27
G11
16.64242
6.21678
6.12
10
905
14
24
G12
-4.66412
5.19843
3.06
3
1044
13
16
G13
-9.17042
-21.46960
4.47
5
1375
2
7
G14
-20.64006
3.65807
7.60
13
1278
4
17
G15
-1.35534
-11.00170
2.08
2
1128
10
12
Grand Mean
1164
ASV = AMMI Stability Value, R
a
= rank of ASV, MSY = means of seed yield, R
y
= rank of seed yield, YSI = Yield Stability
Index, G1= NLLP-MGC-01, G2 = NLLP-MGC-12, G3 = NLLP-MGC-15, G4 = NLLP-MGC-20, G5 = NLLP-MGC-22, G6
= NLLP-MGC-24, G7 = NLLP-MGC-27, G8 = VC1973A, G9 = NM94 (VC6371-94), G10 =, VC6368(46-40-4), G11 =
NLLP-MGC-06, G12 = Acc002, G13 = Acc006, G14 = N-26, G15 = NVL-1
4. Conclusion
Combined analysis of variance shows that
genotype, environment, and G x E interaction are
highly significant, which indicate the existence of a
wide range of variation between the genotypes,
environments, and interactions.
According to AMMI and GGE biplot methods, G6,
G13, and G3 were identified as stable and high
yielder genotypes across the environments.
Besides, the results of the yield stability index and
AMMI stability values identified genotypes G6,
G13 and G3 as high yielding with stable
performance across the environments and be
recommended for diverse environments. Therefore,
genotype G13, which fell into the center of
concentric circles, was the ideal genotype in terms
of higher yield ability and stability, compared with
the rest of the genotypes. Also, genotypes, G6, G8
and G15 can be considered as desirable genotypes.
In this study, genotype G13, which fell in the first
concentric circle, was the ideal genotype in terms
of higher-yielding ability and can be used as a
benchmark for evaluation of mung bean variety
development in future breeding programs.
However, G1, G4, G5, G9, G10, G11, G12, and
G15 were identified as least stable with high YSI
and ASV values that can be recommended for
specific environments.
In general, this study has provided highly valuable
information on the yield stability status of the
mung bean genotypes and the best environments
for future improvement programs in Ethiopia.
Therefore, the mung bean improvement strategy in
Ethiopia should be based on the performance of the
genotypes across environments. Generally, GGE
biplot analysis, AMMI, and Eberhart and Russell's
model revealed that genotype G13 was stable and
high yielding.
Acknowledgment
The authors extend their gratitude to the Southern
Agricultural Research Institute for the financial
support of this research. Also, the authors' deep
gratitude and acknowledgment go to Melkassa
Agricultural Research Center for providing the
mung bean genotypes for this study. The authors
also recognize Jinka Agricultural Research Center
for its administrative facilitation during the
implementation of this research.
Conflict of interest
The author declares that there is no conflict of
interest.
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