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. 2021 Jan 19;7(1):e05973. doi: 10.1016/j.heliyon.2021.e05973

Environmentally stable common bean genotypes for production in different agro-ecological zones of Tanzania

Mashamba Philipo 1,, Patrick Alois Ndakidemi 1, Ernest Rashid Mbega 1
PMCID: PMC7820561  PMID: 33521356

Abstract

Genotype by environment interaction (GxE) complicates the process of selecting genotypes suitable for quantitative traits like seed yield in beans, hence slows down the development and release of varieties by breeding programs. GxE study on seed yield in beans enables identification of stable genotypes across sites and best site(s) for discriminating the tested genotypes in terms of seed yield. The purpose of this study was to evaluate the influence of the environment, genotype, and genotype by environment interaction on seed yield stability and adaptability of common bean landraces, lines, and improved varieties across three different agro-ecologies in Tanzania. The 99 common bean genotypes (Landraces, lines, and improved varieties) were planted following alpha lattice design in three replications each contained five blocks with 20 plots. Soil properties from the experimental sites, days to 75% flowering, Seed yield, 100 seed weight, number of seeds/pod, and number of pods/plant were recorded. Data on seed yield and its components were analyzed using Additive main effect and multiplicative interaction (AMMI), genotype main effects plus genotype × environment interaction (GGE), and yield stability index (YSI). The AMMI revealed very highly significant (P ≤ 0.001) effects of genotypes, environmental, and genotype × environment interaction on all the traits. AMMI analysis revealed that genotype main effects accounted for 39.3% of the total sum square of seed yield, whereas the environment and genotype × environmental interaction accounted for 31.4% and 26.8 % respectively. Genotype main effects largely influenced the variation in days to 75% flowering (55.5%), number of pods/plant (49.2%), number of seeds/pod (73.3%), and 100 seed weight (71.2%). Among soil properties recorded, available soil phosphorus, soil pH, soil exchangeable K, Ca, and Na had a strong positive association with common bean seed yield, while soil organic carbon and total nitrogen exhibited a strong negative association with seed yield. GGE revealed that E1 (TARI-Selian) was the most discriminative and representative site for common bean genotypes seed yield. Based on the yield stability index, the most stable and high seed yielding genotypes were ACC 714, Selian 14, Selian 9, Katuku, and Msolini. The identified high seed yielding and stable genotypes can be further tested in participatory variety selection involving farmers and later on released as varieties and can also be used for different breeding purposes in different agro-ecologies of Tanzania.

Keywords: Common bean, Genotype by environment interaction, AMMI, GGE, Yield stability index


Common bean, Genotype by environment interaction, AMMI, GGE, Genotype stability index.

1. Introduction

Common bean (Phaseolus vulgaris L.) is a tropical diploid (2n = 22), self-pollinating crop, and a member of the Fabaceae family [1]. It contains vegetable protein, minerals (Ca, Cu, Fe, Mg, Mn, and Zn), vitamins (folate), and essential amino acids [2]. Common bean performs well in environmental conditions with a temperature of 15 °C–30 °C, rainfall of 300 mm–600 mm, and well-drained, loamy soils with pH ranging from 5.5 to 7.0 [3,4]. In Tanzania, common bean is mainly grown in altitudes above 1000 m.a.s.l. for home consumption and incomes [5]. Worldwide Tanzania is ranked number seven and the largest producer of common beans in Africa followed by Uganda and Kenya. It is mostly grown in the Lake zone, Southern highlands, Northern and Western Tanzania [6]. The total common bean production in Tanzania is 1,158,039 tonnes, produced within the area of 1,118,406 ha. The crop ranks number three and number five among staple crops grown in Tanzania in terms of production and area of production respectively [7].

Despite the importance of common bean for food and incomes in Tanzania, the crop has been reported to be affected by extreme environmental conditions including i) very low or very high rainfall (below 300ml or above 600 ml) as such conditions result in intermittent and or terminal drought, which negatively affects photosynthesis, causing a reduction in plant sugars, energy, quality, and yield [8, 9]. Too much rainfall, results in water logging, causing poor gas exchange between root and soil pore spaces, it also causes foliar diseases and root rot, thus reduces yield [10]. ii) High temperatures, such as day temperature of above 30 °C and night temperature above 20 °C as these conditions cause flower bud, flower, and pod abortion resulting in common bean seed yield reduction [1, 11, 12]. iii) Poor soil fertility, such as low nitrogen and available phosphorus causes a reduction in common bean yield through the reduction in nitrogen fixation activities and photosynthesis [9]. Too acidic soils lead to aluminum toxicity which also reduces bean yield [13].

As a result of those environmental factors, common bean production and productivity in Tanzania continue to be very low 1,035.4 kg/ha [7], compared to the potential yield of 1500–3000 kg/ha (the majority of non-climbing cultivars) [14] or up to 6000 kg/ha for some climbing bean cultivars [15]. Nevertheless, the performance of beans and reaction to different environmental conditions vary between genotypes [16]. Thus there is a strong need to screen different bean genotypes so as to identify those with stability in performances irrespective of varied environmental conditions. This study was aimed at assessing the performance of different bean genotypes in different environments and identify a few with superior stabilities in yield and yield components across agro-ecologies for use in plant breeding programs targeting bean varietal development and release.

2. Materials and methods

2.1. Common bean genotypes

This study used ninety nine common bean genotypes to evaluate the effect of three different agro-ecologies on seed yield and yield components. Fifty nine local varieties were obtained from randomly selected farmers of the largest bean producer regions in the country; namely Morogoro, Mbeya, Arusha, and Kagera. Whereas thirty two improved cultivars that are recommended for cultivation in a wide range or specific environment and nine lines were obtained from research institutions, which include; Sokoine University of Agriculture (SUA), located in Morogoro, Tanzania Agricultural Research Institute (TARI) Uyole, Selian and Maruku stations found in Mbeya, Arusha and Kagera respectively. Geographical and weather description of Morogoro region [17, 18], Mbeya region [19, 20], Arusha region [20], and Kagera region [21] are presented in Table 1.

Table 1.

Geographical information and weather conditions of regions where seeds were obtained.

Region Geographical position
Mean annual rainfall (mm) Mean annual temperature (°C)
Latitudes Longitudes
Morogoro 05°58′- 09°32′S 35°25′- 38°30′E 500–2200 18–30
Mbeya 07°00′- 09°35′S 32°00′- 35°00′E 650–2600 16–25
Arusha 02°00′- 06°00′S 35°00′- 38°00′E 250–1200 21–26
Kagera 01°00′- 02°45′S 30°25′- 32°40′E 500–2000 20–28

2.2. Description of test locations

The three field experiments of this study were planted at agricultural research stations (Selian and Uyole) of the Tanzania Agricultural Research Institute (TARI) and Sokoine University of Agriculture (SUA) (Figure 1). Geographical positions and altitude, where the field trials were planted at each test location are presented in Table 2.

Figure 1.

Figure 1

Map of Tanzania showing Agro-ecological zones [25], and the experimental sites (TARI-Selian, SUA, and TARI-Uyole).

Table 2.

Geographical information of the test locations.

Test Location Latitude Longitude Altitude (m.a.s.l)
TARI-Selian station 3° 22‘ S 36° 37‘ E 1430.0
SUA 6° 50‘ S 37° 39‘ E 541.7
TARI-Uyole station 8° 55' S 33° 30' E 1772.0

m.a.s.l = meters above sea level.

2.3. Test locations field soil collection and analysis

Soil samples were collected at each test location field at a depth of 20 cm before planting. The soil samples were air-dried, ground, sieved using a 2.0 mm mesh and used in laboratory determination of soil physical and chemical characteristics. Texture of the soils were obtained using the hydrometer method whereas soil pH was determined on 2.5:1 water to soil suspension [22]. After soil pH determination, available phosphorus (AP) for TARI-Selian experimental field soil (basic) was determined using the Olsen method while that of SUA and TARI-Uyole soils (acidic), was determined using Bray 1 method [23]. Exchangeable bases (Ca, Mg, Na, and K) were extracted using ammonium acetate and determined by atomic absorption spectrophotometry. Walkley-Black wet combustion method was used to determine organic carbon (OC), whereas total nitrogen (TN) was measured using the Kjeldahl method [24].

2.4. Field trial details

The field experiments at all three test locations (TARI-Selian, SUA, and TARI-Uyole) were laid out in alpha lattice design with three replications, each replication containing five blocks of 20 plots. Every experimental plot was planted with one common bean genotype in two rows of 1.5 m length spaced at 50 cm apart. Within rows plants were spaced at 10 cm from one plant to another. Planting at TARI-Uyole and Selian station, was done on March 2018 and harvested on July 2018, whereas common bean genotypes planting at SUA was done on May 2018 and harvested on August 2018.

2.5. Data collection

Days to 75 % flowering in each genotype were observed and recorded during flowering time. At harvesting, all plants in a plot were harvested and heaped at the center of a plot. Ten plants were randomly selected and the number of pods in each of the selected plants was counted and recorded to determine the number of pods per plant. The number of seeds per pod was counted and recorded from twenty randomly selected pods. Pods were shelled and air-dried for three days, the weight of 100 seeds (g/100 seeds), and all seeds per plot (g/plot) were measured and recorded. The weight of seeds per plot was later converted into kg/ha. Besides, weather information recorded during the planting season at each experimental site was obtained from Tanzania meteorological authority (TMA).

2.6. Statistical analysis

Analysis of variance (ANOVA) on days to 75 % flowering, yield, and yield components from each test location, was performed using GenStat 15th edition statistical package, to determine significant variability among genotypes for yield and yield components. Common bean genotypes seed yield and yield components means were separated using Duncan's new multiple range test (DNMRT) methods at a 5% level of probability while Pearson's correlation was used to determine the relationship between the variables at a 5% level of probability.

Additive main effects and multiplicative interaction (AMMI) model [26] using GenStat 15th edition statistical package (equation 1), was used to assess the effect of genotype by environment interaction, analyze the ability of common bean genotype(s) to become well suited to an environment rather than modifying the environment (adaptability) and genotype's capability of performing more or less similar across several environments (stability).

Yge= μ + αg+ βe+ Σnλnγgnδen+ ρge (1)

Where Yge is the yield for genotype g in environment e, μ is the grand mean, μg the mean for genotype g (over environments), and μe the mean for environment e (over genotypes), αg = μg - μ is the genotype deviation and βe = μe - μ is the environment deviation, λn the singular value for n component, γgn be the eigenvector value for genotype g and let δen be the eigenvector value for environment e, ρge is the residual term. AMMI Stability Value (ASV) as explained by [27] was used to quantify and rank the common bean genotypes based on their yield stability (equation 2).

ASV=SSIPC1SSIPC2(IPC1)2+(IPC2)2 (2)

Where SSIPC1 is the interaction principal component one sum of the square, SSIPC2 is the interaction principal component two sum of the square, IPC1 and IPC2 are interaction principal component 1 and 2 respectively.

Yield Stability Index (YSIi) of each common bean genotype in terms of yield was calculated based on the rank of the ith genotype across environments based on AMMI Stability Value (RASVj) and rank of the ith genotype based on mean yield across environments (RYi) [28, 29] as

YSIi = RASVi + RYi (3)

The genotype main effect and genotype by environment interaction effect (GGE) biplot analysis was performed using PB Tools version 1.4. GGE biplot is based on tester centered data that is tester (environment) main effects (E) are removed, while the genotypes main effects (G) and genotypes by environment interaction main effects are retained and combined [30]. This study used GGE biplot analysis to visualize the correlation among the test locations and evaluate the discriminating power and representativeness of the test locations for the common bean genotypes in terms of seed yield and yield components.

3. Results

3.1. Test locations weather and soil physico-chemical characteristics

All the test locations received enough rainfall above 300 mm, though at different rates during common bean growing period. The crop requires rainfall above 300 mm for it to perform well. The other monthly weather parameters during the growing season are as presented in Table 3. The highest rainfall was recorded at TARI-Selian, followed by SUA, while the lowest rainfall was recorded at TARI-Uyole. The highest temperatures were recorded at SUA, Morogoro followed by TARI-Selian whereas TARI-Uyole recorded the lowest temperatures. The highest relative humidity at TARI-Selian and SUA was recorded in April, while TARI-Uyole recorded highest relative humidity in March. All the test locations recorded the lowest relative humidity in August.

Table 3.

Test locations weather information during experimental period.

Month TARI-Selian
SUA
TARI-Uyole
Max Temp (°C) Min Temp (°C) Rain (mm) Rh (%) Max Temp (°C) Min Temp (°C) Rain (mm) Rh (%) Max Temp (°C) Min Temp (°C) Rain (mm) Rh (%)
March 28.9 19.3 302.7 83.0 30.4 21.2 186.7 82.0 23.4 14.6 156.7 92.6
April 24.3 17.5 195.3 88.0 28.9 21.1 228.6 87.0 23.7 14.8 149.9 84.8
May 22.9 17.4 137.5 87.0 28.4 19.9 111 86.0 23.6 11.2 29.5 74.2
June 22.3 14.5 7.4 83.0 28.3 17.1 6.4 80.0 22.5 7.9 0.0 71.0
July 22.1 14.3 0.8 78.0 27.1 16.8 33 76.0 21.9 8.9 0.0 72.0
August 23.4 13.4 1.8 76.0 28.5 16.5 0.0 71.0 24.7 7.8 0.0 70.0

Test locations soil characteristics are presented in Table 4. Analysis of variance revealed no significant difference (P ≤ 0.05) in sandy soil particles, whereas there was a significant difference (P ≤ 0.05) in clay and silt soil particles among the test location soils. Soils at TARI-Uyole and TARI-Selian were classified as sandy clay loam while soils at SUA were classified as clay. Significant variations (P ≤ 0.05) among the test location soils were observed in total nitrogen (TN), organic carbon (OC), and available phosphorus (P), a highly significant variation (P ≤ 0.01) was observed in exchangeable calcium (Ca), magnesium (Mg), potassium (K), and sodium (Na) among the test location soils. Furthermore, soils from the test locations had no significant difference (P ≤ 0.05) in soil pH.

Table 4.

Characteristics of the test locations soils.

Soil Properties Location
Mean Optimal levels CV% LSD (0.05) P-value
Selian SUA Uyole
Soil pH 7.15a 6.00a 5.84a 6.33 5.5–7.5 6.2 1.69 0.132
% Clay 28.12b 52.12a 30.12b 36.79 5.9 9.29 0.013
% Silt 22.92a 9.92b 22.92a 18.59 11.6 9.30 0.04
% Sand 48.96a 37.96a 46.96a 44.63 4.8 9.30 0.064
Soil textural class SCL SCL C
TN % 0.16b 0.25a 0.15b 0.19 0.25–0.5 4.4 0.04 0.011
OC % 2.21b 4.52a 1.92b 2.88 >2 8.2 1.01 0.013
P (mg/kg) 23.93a 2.24c 13.26b 13.14 20–100 15.9 9.01 0.018
Ca2+ (CmolKg−1) 22.14a 8.14b 8.05b 12.78 >10 5.5 3.02 0.004
Mg2+ (CmolKg−1) 5.15a 4.98a 2.61b 4.25 >1.5 2.8 0.52 0.004
Na+ (CmolKg−1) 1.03a 0.48c 0.58b 0.70 <1.5 1.2 0.04 0.001
K+ (CmolKg−1) 5.58a 0.96c 1.54b 2.69 0.6–2.0 0.8 0.09 0.001

C = Clay, SCL = Sand clay loam, Different letters among samples = significant differences by Duncan's new multiple range test (p ≤ 0.05).

3.2. Genotypes seed yield and yield components variation

The highest common bean seed yield was recorded at TARI-Selian, followed by TARI-Uyole and lastly SUA. Seed yield at TARI-Selian, ranged from 1252.1 to 5121.9 kg/ha with a mean of 2336.0 kg/ha, while at SUA, seed yield ranged from 668.5 to 2499.4 kg/ha with a mean yield of 1347.7 kg/ha, and at TARI-Uyole it has a range of 903.4–2773.1 kg/ha with mean yield of 1579.4 kg/ha. The large variation in seed yield among the common bean genotypes was observed at TARI-Selian due to the larger interquartile range of the box plot compared to the rest experimental sites (Figure 2D). TARI-Selian recorded the highest 100 seed weight compared to other experimental sites. Weight of 100 seeds per genotype at TARI-Selian had a range of 20.3–66.0 g with a mean of 42.9 g. At SUA, the weight of 100 seeds ranged from 15.6 to 44.9 g with a mean of 30.1 g, whereas at TARI-Uyole, the weight of 100 seeds had a range of 17.0–50.1 g with a mean of 32.7 g. There was greater variability in the weight of 100 seeds among genotypes at TARI-Selian compared to other sites. Most of the tested bean genotypes weighted 100 seeds below the mean in all sites (Figure 2C). The highest number of pods per plant and the largest variability among bean genotypes were recorded at TARI-Selian compared to other sites. Most of the bean genotypes at TARI-Selian and SUA had the number of pods per plant greater than their site means (Figure 2A). TARI-Selian recorded the largest variation and highest number of seeds per pod among the experimental sites (Figure 2B).

Figure 2.

Figure 2

Distribution and comparison of 99 common bean genotypes seed yield and yield components across sites (TARI-Selian, SUA and TARI-Uyole); (A) Number of pods per plants; (B) Number of seeds per pod; (C) 100 seed weight; (D) Seed yield.

The highest seed yielding genotype at TARI-Selian was Cheupe, closely followed by Uyole 84 and Selian 05. Among the common bean genotypes harvested at SUA, Jabeyila recorded the highest seed yield, followed by Cheupe and Mwamikola. At Uyole-Mbeya, the highest seed yielding genotypes was Selian 14, followed by DOOR 500 and Selian 15 (Table 5).

Table 5.

Test locations seed yield mean and ranking of 99 common bean genotypes based on seed yield, AMMI stability value (ASV), and yield stability index (YSI).

GN Genotype Common bean seed yield (kg/ha)
Common bean genotypes ranking
Selian Uyole SUA Mean IPCA1 IPCA2 ASV RASVi RYi YSIi RYSIi
1 ACC 714 2629no 1888g-l 1639h-m 2052j-n 0.06 0.24 0.4 1 22 23 1
2 Bagara Ompigize 2041xyz 1681j-t 1278o−A 1667w−E 3.09 2.76 15.6 43 43 86 35
3 Bangaya Akatebe 1863A−D 1029CF 893H−M 1261R–W -0.22 -1.33 1.7 2 92 94 45
4 Bilfa 4 1708E−J 1507m-z 811KLM 1342M−T 2.97 6.71 16.2 45 86 131 77
5 Bilfa Uyole 2400qrs 1347s−C 919F−M 1555D−K -4.26 2.06 21.2 51 57 108 58
6 Buji 1694FK 1414m−B 1358m-y 1489F−M 6.01 -1.53 29.9 69 64 133 78
7 Burushu 2637n 1096A−F 1542j-p 1758t−A -4.04 -9.75 22.3 55 39 94 44
8 CAL 96 1884ABC 903F 1456k-t 1414KS 2.42 -10.27 15.8 44 71 115 66
9 Calima Uyole 1403O−R 1141y−F 1239p−E 1261R–W 7.13 -3.45 35.5 76 93 169 96
10 Cheupe 5122a 1957f-l 2353ab 3144a -21.19 -11.50 105.7 96 1 97 49
11 Chumba Neroza 3175hi 1602l-x 1260p−B 2012k-o -9.14 0.19 45.3 86 23 109 60
12 CODMLB 033 2518n-q 1645k-v 1732f-k 1965n-q 0.72 -4.21 5.5 9 27 36 6
13 DOR 500 3012jk 2772a 1137u−J 2307fgh -3.12 18.54 24.1 60 16 76 27
14 Fibea 2490pqr 1728h-q 1245p−C 1821q-w -1.57 3.18 8.4 19 35 54 15
15 Jabeyila 2536n-q 2393bcd 2499a 2476de 8.41 -3.38 41.9 84 10 94 43
16 Jesca 1467M−P 1328t−D 1243p−D 1346M−S 7.30 -0.96 36.2 78 84 162 92
17 KAB o6F2-8-35 1758CH 1446m−A 854J−M 1353M−S 2.43 5.21 13.1 32 81 113 62
18 KAB o6F2-8-36 2312stu 1428m−B 1093x−L 1611z−H -1.94 1.12 9.7 25 52 77 28
19 Kabanima 1768C−G 1257x−F 936C−M 1321NU 2.01 1.50 10.1 26 87 113 64
20 Kabumburi 1836B−E 1171y−F 1477j-t 1495F−M 4.21 -6.68 21.9 53 61 114 65
21 Kachele 2498opq 1607l-x 1225q−F 1777s-y -2.29 1.70 11.5 27 37 64 20
22 Kaempu 2413qrs 1762h-o 1421l-v 1865o-u 0.43 1.54 2.6 3 33 36 9
23 Kainja 1628H−L 1357q−C 1106w−L 1364L−S 4.93 0.95 24.5 62 79 141 85
24 Kaisho kamugole 2824lm 1609l-x 858I−M 1764t-z -7.90 5.90 39.6 82 38 120 67
25 Kakaritusi 1969yzA 1604l-x 1301o-z 1624y−G 3.63 1.48 18.1 47 49 96 48
26 Kamoshi 2093wxy 1455m−A 1116v−K 1555D−K 0.59 1.53 3.3 7 56 63 19
27 Kamosi 2212uvw 1671k-t 1531j-q 1805r-x 2.80 -0.85 13.9 35 36 71 25
28 Kanade 3260gh 2160c-g 1759f-j 2393ef -4.58 1.64 22.8 56 11 67 21
29 Kashule 1559KN 940EF 942C−M 1147VW 2.84 -2.77 14.4 36 98 134 80
30 Kasukari 2145vwx 1660k-u 1097x−L 1634y−G 0.82 4.60 6.1 10 46 56 16
31 Katuku 2833lm 1954f-l 1692g-l 2160ijk -1.44 0.19 7.2 15 19 34 4
32 Katuku2 4270e 2063d-i 820KLM 2384ef -21.16 10.68 105.5 95 12 107 56
33 Kibugu 1734D−I 1281v−E 1114v−K 1376L−S 3.55 -0.37 17.6 46 75 121 71
34 Kigoma 1598I−M 1400n−B 1333m-y 1444I−Q 6.80 -1.27 33.8 75 68 143 86
35 Kikobe 3316fg 2311b-e 2011def 2546d -2.98 0.49 14.8 38 9 47 11
36 Kilindi 1658G−K 1246x−F 1221q−F 1375L−S 4.83 -2.12 24.0 59 76 135 81
37 Kinyobya 1562KN 1141y−F 1066y−L 1256SW 4.44 -1.49 22.1 54 94 148 87
38 Kipapi 1775C−G 1511m-y 1487j-s 1591B−J 6.37 -1.92 31.6 71 54 125 73
39 Kisapuri 2364rst 1395o−C 1110v−L 1623y−G -2.52 0.36 12.5 31 50 81 30
40 Kitebe 2520n-q 1998e-k 1242p−D 1920n-s -0.72 6.98 7.8 17 31 48 12
41 Kituntunu 2900kl 1188y−F 1073x−L 1720u−C -9.20 -2.89 45.7 87 41 128 74
42 Kyababikira 1782C−G 1398n−B 1297o-z 1493F−M 4.66 -1.11 23.1 58 62 120 68
43 Kyakaragwe 2424qrs 1184y−F 1178r−H 1595A−I -3.65 -3.58 18.4 49 53 102 52
44 Lyamungo 85 1682FK 1720i-r 1467j-t 1623y−G 8.12 1.44 40.3 83 51 134 79
45 Lyamungo 90 1356PS 1265w−E 892H−M 1171UVW 6.06 2.77 30.2 70 96 166 95
46 Maharage Kamba 2764m 1882g-l 1167t−I 1938n-r -4.21 5.93 21.7 52 29 81 29
47 Maharage Mbeya 2209uvw 1891g-l 1887e-h 1996l-o 5.93 -2.23 29.5 68 25 93 41
48 Malirahinda 2038xyz 1427m−B 1222q−F 1562CK 1.67 -0.12 8.3 18 55 73 26
49 Masusu 3110ij 1719i-s 2186bcd 2338e-h -2.36 -9.80 15.3 40 14 54 14
50 Meupe Uyole 1706E−J 1427m−B 1225q−F 1453HP 5.14 0.32 25.5 64 67 131 76
51 Mshindi 1415OPQ 1063BF 1370m-y 1283Q−V 7.46 -6.23 37.5 80 90 170 97
52 Msolini 2812lm 2035e-j 2098b-e 2315fgh 1.58 -3.77 8.7 21 15 36 5
53 Mwami Kola 2214uvw 1886g-l 2329abc 2143i-l 8.53 -7.92 43.0 85 20 105 55
54 Ngoma za bahaya 2150vwx 1630l-w 1208r−G 1663x−E 1.32 2.76 7.1 14 44 58 17
55 Ngwakungwaku 2892klm 1511m-y 2295abc 2232ghi -0.33 -13.80 13.9 34 17 51 13
56 Njano fupi 1945zAB 1150y−F 1181r−H 1426K−R 1.20 -3.40 6.8 13 70 83 33
57 Njano Uyole 1456NOP 1477m-z 1103x−L 1345M−S 7.21 2.95 35.9 77 85 162 93
58 Nyeupe Kubwa 4356e 2440bc 1886e-h 2894b -13.98 2.37 69.4 91 4 95 46
59 Nyeupe ndogo 2469pqr 1769h-n 1538j-p 1925n-s 0.60 0.06 3.0 6 30 36 7
60 Pasi 2501opq 1712i-s 1439k-u 1884o-t -0.58 0.48 2.9 4 32 36 8
61 Pesa 1805CF 1504m-z 1571i-o 1627y−G 6.54 -3.12 32.6 73 48 121 70
62 Raja 1960y−B 1604l-x 854J−M 1473G−N 1.03 7.17 8.8 22 65 87 36
63 Rojo 1280RS 1409n−B 1416l-w 1368L−S 10.63 -1.73 52.7 88 77 165 94
64 Rosenda 1791C−G 1429m−B 668M 1296OV 0.91 7.28 8.6 20 88 108 59
65 Rozikoko fupi 1615I−L 1209y−F 981A−L 1268R–W 3.66 0.47 18.2 48 91 139 84
66 Ruondera 4548d 2237c-f 1933d-g 2906b -16.56 -1.38 82.1 93 3 96 47
67 RWR 2154 2642n 2053e-i 1119v−K 1938n-r -2.50 9.14 15.4 42 28 70 23
68 Selian 05 4831b 1313t−D 1988def 2711c -23.17 -15.57 115.9 97 7 104 54
69 Selian 06 4785bc 1385p−C 958B−M 2376efg -28.61 -1.43 141.9 99 13 112 61
70 Selian 10 1763CH 1639k-v 1070y−L 1491F−M 4.53 5.20 23.1 57 63 120 69
71 Selian 11 2893klm 2144c-g 1543j-p 2193hij -2.15 4.69 11.6 28 18 46 10
72 Selian 12 1293QRS 1253x−F 901G−M 1149VW 6.71 2.59 33.4 74 97 171 98
73 Selian 13 1669FK 1249x−F 941C−M 1286PV 3.03 1.46 15.1 39 89 128 75
74 Selian 14 3429f 2773a 2132b-e 2778bc -1.43 5.33 8.9 23 5 28 2
75 Selian 15 4678c 2588ab 1993def 3086a -16.02 2.63 79.5 92 2 94 42
76 Selian 9 2775lm 1782h-m 1844e-i 2134i-m -0.67 -4.07 5.3 8 21 29 3
77 Selian 94 1520L−O 1258x−F 1430k-u 1403KS 7.58 -4.40 37.8 81 72 153 88
78 Selian 97 1766CH 1460m−A 818KLM 1348M−S 2.20 5.87 12.4 30 83 113 63
79 Selundo 2259tuv 1672k-t 2066cde 1999l-o 5.55 -7.68 28.6 67 24 91 39
80 Sinon 1760CH 1637k-v 1265o−B 1554D−K 5.73 2.71 28.5 66 58 124 72
81 SMC 17 1514L−O 1366p−C 1176s−H 1352M−S 6.57 0.36 32.6 72 82 154 89
82 SMC 18 1982yzA 1155y−F 946C−M 1361L−S -0.59 -0.39 2.9 5 80 85 34
83 Soya 1857A−D 1309t−D 932D−M 1366L−S 1.28 2.15 6.7 12 78 90 38
84 Soya Mbeya 4343e 2081d-h 1614h-n 2680c -17.04 0.75 84.5 94 8 102 51
85 SUA 90 1278RS 1333t−D 945C−M 1185T−W 7.48 3.17 37.2 79 95 174 99
86 Tema 2245tuv 1512m-y 802LM 1520E−L -2.64 6.09 14.4 37 60 97 50
87 Tikiumba Nyama 2060xyz 1671k-t 1489j-r 1740t−B 4.12 -0.09 20.4 50 40 90 37
88 Urafiki 1393O−R 975DEF 969A−M 1112W 4.89 -2.37 24.3 61 99 160 91
89 Uyole 03 2575nop 1500m-z 1432k-u 1836p-v -2.31 -2.56 11.7 29 34 63 18
90 Uyole 04 2201uvw 1135z−F 1322n-y 1553D−K -0.67 -5.76 6.7 11 59 70 24
91 Uyole 16 2087wxy 1500m-z 1480j-s 1689v−D 3.04 -2.44 15.3 41 42 83 32
92 Uyole 18 1581J−N 1220y−F 2090b-e 1630y−G 10.77 -13.38 55.1 89 47 136 82
93 Uyole 84 5116a 1736h-p 1313n-y 2722c -28.37 -1.44 140.7 98 6 104 53
94 Uyole 94 1787C−G 1291u−E 1071y−L 1383L−S 2.78 0.23 13.8 33 74 107 57
95 Uyole 96 2296stu 1634l-w 1001z−L 1644y−F -1.44 5.23 8.9 24 45 69 22
96 Uyole 98 2124vwx 1323t−D 929E−M 1458HO -1.44 1.99 7.4 16 66 82 31
97 Wanja 1663G−K 1351r−C 1185r−H 1400KS 5.01 -0.18 24.9 63 73 136 83
98 Wifi Nyegela 2211uvw 2391bcd 1363m-y 1988m-p 4.91 11.47 26.9 65 26 91 40
99 Zawadi 1252S 1650k-v 1385m-x 1429J−R 11.78 2.12 58.5 90 69 159 90

Different letters among genotype values = significant differences by Duncan's new multiple range test (DNMRT) (p ≤ 0.05), GN = Genotype number, IPC1 and IPC2 are interaction principal component 1 and 2 respectively, ASV = AMMI Stability Value, RASV = rank of the genotype across environments based on AMMI Stability Value, YSI = Yield Stability Index, RY = rank of the genotype across environments based on mean yield across environments, RGSI = rank of the genotype based on Yield Stability Index.

At TARI-Selian, the highest number of pods per plant was recorded from Cheupe followed by Ruondera and Kaisho kamugole. Cheupe also recorded the highest number of pods per plant at SUA, closely followed by Jabeyila and Mwamikola, whereas Wifi nyegela had the highest number of pods per plant at TARI-Uyole, followed by Kikobe and DOOR 500. In terms of the number of seeds per pod, Malirahinda, Cheupe, and Ngoma za bahaya were the best three genotypes at TARI-Selian. At SUA the best three genotypes in the number of seeds per pod were Kaempu, Kikobe, and Kyakaragwe, whereas Cheupe, kamosi, and kaempu had the highest number of seeds per pod at TARI-Uyole (Table 6). The highest 100 seed weight-containing common bean genotypes at TARI-Selian were Lyamungo 90, CAL96, and Msolini, Whereas Lyamungo 90, Msolini, and Selian 15 recorded the highest 100 seed weight at SUA. At TARI-Uyole Selian 15, Msolini and Uyole 94 were the highest 100 seed weight-containing common bean genotypes. The earliest flowering 3 common bean genotypes at TARI-Selian were Jesca, Kigoma, and Selian 12, whereas Pesa, Rojo, and Zawadi flowered early at SUA. At Uyole Calma Uyole, Kigoma, and Kintuntunu were observed as the earliest flowering common bean genotypes (Table 7).

Table 6.

The best 20 common bean genotypes at each experimental site in terms of number of pods per plant and seeds per pod.

Number of pods per plant
Number of seeds per pod
Genotype Selian Genotype SUA Genotype Uyole Genotype Selian Genotype SUA Genotype Uyole
Cheupe 45.9a Cheupe 25.9a Wifi Nyegela 35.0a Malirahinda 7.3a Kaempu 6.9a Cheupe 7.1a
Ruondera 40.1b Jabeyila 25.1a Kikobe 27.3b Cheupe 7.3a Kikobe 6.6ab Kamosi 7.0a
Kaisho kamugole 37.2c Mwami Kola 21.8b DOR 500 26.3bc Ngoma za bahaya 7.0ab Kyakaragwe 6.5abc Kaempu 7.0a
Katuku2 35.5d Selian 9 20.5bc Ruondera 23.9cd Selian 11 7.0ab Kachele 6.5a-d Wifi Nyegela 7.0a
Kikobe 35.3d Kikobe 19.7bcd Jabeyila 23.0de Maharage Kamba 6.9ab Kaisho kamugole 6.4a-e Kanade 6.3b
Selian 05 34.3e Ruondera 18.9cde Kaempu 22.4def Kachele 6.7bc Kamoshi 6.4a-e Maharage Kamba 6.3b
Selian 14 34.2e Wifi Nyegela 18.7c-f Soya Mbeya 21.3d-g Kaempu 6.7bc Kasukari 6.3a-f Selian 9 6.3b
Selian 11 32.6f Bagara Ompigize 18.1c-g Kachele 20.8d-h Kamosi 6.7bcd Malirahinda 6.2b-f Malirahinda 6.1b
Maharage Kamba 32.3f Kachele 18.1c-h Pasi 20.5d-i Selian 10 6.5cde Mwami Kola 6.1b-g Kaisho kamugole 6.1bc
Uyole 84 32.1f Kamosi 17.7c-i Nyeupe Kubwa 20.2e-i Kakaritusi 6.4c-f Ngoma za bahaya 6.1b-h DOR 500 6.0bcd
Soya Mbeya 31.7f Selian 05 17.5d-i Bagara Ompigize 20.1e-i Selian 9 6.4c-f Selian 10 6.1b-h Jabeyila 6.0bcd
Kachele 30.7g Nyeupe ndogo 17.1d-j Selian 11 19.3f-i DOR 500 6.3c-g Cheupe 6.0b-i Kamoshi 6.0bcd
Tema 29.7h Kaempu 16.7e-j Kaisho kamugole 19.0f-j Kamoshi 6.3c-g Kakaritusi 6.0b-i Kasukari 6.0b-e
Kamosi 28.7i Masusu 16.7e-j Kamosi 19.0f-j Kasukari 6.3d-h Chumba Neroza 5.9c-ij Kitebe 6.0b-e
Masusu 27.8j Kanade 16.5e-j Katuku 18.7f-k Wifi Nyegela 6.2e-i Uyole 84 5.9c-j Ngoma za bahaya 6.0b-e
DOR 500 27.5j CODMLB 033 16.1e-k Mwami Kola 18.5g-l Bangaya Akatebe 6.1e-j Wifi Nyegela 5.9c-j Ruondera 6.0b-e
Kamoshi 27.4j Msolini 16.1e-k Selian 9 18.3g-l Kikobe 6.1e-j Kamosi 5.9d-k Selian 10 6.0b-e
Nyeupe Kubwa 27.3jk Selian 15 16.0e-k Kanade 18.0g-m Kitebe 6.1e-j Selian 05 5.8e-l Selian 14 5.9b-f
Selundo 26.4kl Katuku 15.9f-k Selian 15 18.0g-n Selian 06 6.1e-j Kituntunu 5.7f-l Chumba Neroza 5.9b-f
Pasi 26.1lm Uyole 18 15.9f-k Maharage Kamba 17.7g-o Nyeupe Kubwa 6.1e-k Bangaya Akatebe 5.7f-m ACC 714 5.9b-f

Different letters among genotype values = significant differences by Duncan's new multiple range test (p ≤ 0.05).

Table 7.

The best 20 common bean genotypes in terms of 100 seed weight and earliest flowering 20 genotypes at each experimental site.

Weight (g) of 100 seeds
Days to 75% flowering
Genotype Selian Genotype SUA Genotype Uyole Genotype Selian Genotype SUA Genotype Uyole
Lyamungo 90 66.0a Lyamungo 90 44.9a Selian 15 50.1a Jesca 34.3a Pesa 33.0a Calima Uyole 36.0a
CAL 96 65.0b Msolini 44.5ab Msolini 47.0b Kigoma 35.0b Rojo 33.0ab Kigoma 36.0a
Msolini 64.0c Selian 15 44.2ab Uyole 94 46.7bc Selian 12 35.0b Zawadi 33.3abc Kituntunu 36.0ab
Selian 15 63.7c Lyamungo 85 43.6bc Rosenda 46.6bc CAL 96 35.3b SUA 90 33.7a-d Selian 05 36.0abc
Bilfa Uyole 62.0d Rosenda 43.1c Masusu 46.0cd Soya 35.3b Buji 34.0a-e Wifi Nyegela 36.0a-d
Fibea 62.0d Buji 41.8d Lyamungo 90 45.9cd Kilindi 36.0c Selian 13 34.0a-e Kabumburi 37.0a-e
Lyamungo 85 62.0d Bilfa Uyole 41.2d Wanja 45.3de Kisapuri 36.0c Uyole 16 34.0a-f Maharage Mbeya 37.0a-f
Uyole 03 62.0d Fibea 41.2d Fibea 45.0e Masusu 36.0c Kilindi 34.3c-g Msolini 37.0a-g
Calima Uyole 61.3d Selian 14 41.2d CAL 96 44.0f Mshindi 36.0c Selian 12 34.7d-g Uyole 18 37.0a-h
Wanja 59.3e Uyole 96 41.2d Meupe Uyole 43.4fg Pesa 36.0c Kibugu 35.0egh Jesca 38.0e-i
Selian 14 59.0ef Masusu 40.7d Ngwakungwaku 43.2g SUA 90 36.0cd Kigoma 35.0e-h KAB o6F2-8-35 38.0e-i
Uyole 94 58.3fg Kipapi 40.7d Tikiumba Nyama 43.0gh Buji 36.3cde Kipapi 35.0e-h Kaisho kamugole 38.0e-i
Uyole 96 58.0g Ngwakungwaku 39.5e Selian 14 43.0gh Kabumburi 36.3c-f Njano fupi 35.0e-i Kashule 38.0e-i
Meupe Uyole 57.7g Sinon 38.7ef Uyole 96 42.3hi Ngwakungwaku 36.3c-g Tikiumba Nyama 35.0e-j Kipapi 38.0e-i
Buji 56.3h Njano fupi 38.7ef Lyamungo 85 41.8ij Njano fupi 36.3c-h Wanja 35.0e-j Mwami Kola 38.0e-i
Masusu 56.0h Wanja 38.6ef Ruondera 41.8ijk Urafiki 36.3c-i Jesca 36.0hk Nyeupe ndogo 38.0e-i
Ngwakungwaku 56.0h CODMLB 033 38.4fg CODMLB 033 41.8i-l Wanja 36.3c-j Kitebe 36.0h-l Selian 13 38.0e-i
Sinon 56.0h Meupe Uyole 38.3fg Uyole 18 41.3j-m Zawadi 36.3c-k Mshindi 36.3klm Selian 97 38.0e-i
Rosenda 55.0i Uyole 16 37.7fgh Kipapi 41.0jlm Kinyobya 36.7c-l Selian 9 36.3klm Soya 38.0e-i
Uyole 16 55.0i CAL 96 37.7fgh Selundo 41.0j-m Bangaya Akatebe 37.0lm CAL 96 37.0k-n SUA 90 38.0e-i

Different letters among genotype values = significant differences by Duncan's new multiple range test (p ≤ 0.05).

Across locations, there was highly significant (P < 0.001) effects of genotypes, environments, and genotype by environment interaction on the days to 75% flowering, number of pods per plant, number of seeds per pod, the weight of 100 seeds and seed yield (kg/ha). Mean seed yield across sites ranged from 1085.2 to 3068.7 kg/ha with a grand mean of 1736.9 kg/ha. AMMI analysis showed that the main effects of genotypes and environment accounted for 39.3 % and 31.4 % of seed yield treatment some of the squares respectively, whereas genotype × environment interaction effect represented 26.8 % of seed yield treatment some of the squares. The two interaction principal component axes (IPCA 1 and IPCA 2) were both highly significant (P ≤ 0.001) for seed yield and accounted for 83.2 and 16.8 % respectively of the genotype by environment interaction for seed yield (Table 8).

Table 8.

AMMI analyses of variance for seed yield of common bean genotypes across sites.

Source of Variation DF SS MS F P-value. %TSS %GEISS
Total 890 506262438 568834
Treatments 296 493659622 1667769 82.8 <0.001 97.5
Genotypes 98 199047377 2031096 100.84 <0.001 39.3
Environments 2 158873571 79436785 627.26 <0.001 31.4
Block 6 759843 126640 6.29 <0.001 0.2
Interactions 196 135738674 692544 34.38 <0.001 26.8
IPCA 99 112960007 1141010 56.65 <0.001 83.2
IPCA 97 22778667 234832 11.66 <0.001 16.8
Error 588 11842974 20141

DF = degree of freedom, SS = sum of square, MS = mean sum square, F = F value, P-value. = F probability, %TSS = percentage of total sum square and %GEISS = percentage of genotype by environment interaction sum square.

The main effects of genotypes, environment, and genotype × environment interaction accounted for 55.5%, 5.5%, and 36.7% of the days to 75% flowering treatment some of the squares respectively. The two interaction principal component axes (IPCA 1 and IPCA 2) were both highly significant (P ≤ 0.001) for days to 75 flowerings and accounted for 67.8 and 32.1% respectively of the genotype by environment interaction for days to 75% flowering. Genotype main effect accounted for 49.2%, while environmental main effect and genotype by environment interaction accounted for 26.0% and 21.9% of the number of pods/plant total sum square respectively. Of the interaction, IPCA1 accounted for 74.6% of the interaction sum of squares while IPCA2 accounted for 25.4% (Table 9).

Table 9.

AMMI analyses of variance for days to 75% flowering and number of pods/plant of common bean genotypes across sites.

Source of Variation DF Days to 75% flowering
Number of pods per plant
SS MS F P-value %TSS %GEISS SS MS F P-value %TSS %GEISS
Total 890 6851 7.7 44930 50.5
Treatments 296 6696 22.6 89.5 <0.001 97.7 43574 147.2 68.9 <0.001 97.0
Genotypes 98 3804 38.8 153.6 <0.001 55.5 22094 225.5 105.5 <0.001 49.2
Environments 2 376 188.1 167.2 <0.001 5.5 11660 5829.8 350.4 <0.001 26.0
Block 6 7 1.1 4.5 <0.001 0.1 100 16.6 7.8 <0.001 0.2
Interactions 196 2516 12.8 50.8 <0.001 36.7 9820 50.1 23.4 <0.001 21.9
IPCA 99 1707 17.3 68.3 <0.001 67.8 7324 74 34.6 <0.001 74.6
IPCA 97 808 8.3 33.0 <0.001 32.1 2495 25.7 12.0 <0.001 25.4
Error 588 149 0.3 1257 2.1

DF = degree of freedom, SS = sum of square, MS = mean sum square, F = F value, P-value. = F probability, %TSS = percentage of total sum square and %GEISS = percentage of genotype by environment interaction sum square.

The contribution of genotype main effect on the number of seeds/pod and 100 seed weight total sum square was larger 73.3% and 71.2% respectively, compared to environmental main effect which contributed 2.4% of the number of seeds per pod total sum of a square and 22.9% of 100 weight total sum of the square. Genotype by environment effect accounted for 18.7% of the number of seeds per pod total sum square and 5.8% of 100 seed weight total sum square. IPCA1 and IPCA2 for both 100 seed weight and the number of seeds/pod were highly significant difference (P ≤ 0.001) (Table 10).

Table 10.

AMMI analyses of variance for number of seed/pod and 100 seed weight of common bean genotypes across sites.

Source of Variation DF Number of seeds per pod
100 seed weight (g)
SS MS F P-value %TSS %GEISS SS MS F P-value %TSS %GEISS
Total 890 933.4 1.1 119863 135
Treatments 296 881.1 3.0 34.5 <0.001 94.4 119705 404 1532.7 <0.001 99.9
Genotypes 98 684.5 7.0 80.9 <0.001 73.3 85390 871 3302.4 <0.001 71.2
Environments 2 22.3 11.2 45.7 <0.001 2.4 27393 13696 34089.6 <0.001 22.9
Block 6 1.5 0.2 2.8 0.01 0.2 2 0 1.5 0.168 0.0
Interactions 196 174.3 0.9 10.3 <0.001 18.7 6922 35 133.9 <0.001 5.8
IPCA 99 100.2 1.0 11.7 <0.001 57.5 5819 59 222.8 <0.001 84.1
IPCA 97 74.1 0.8 8.8 <0.001 42.5 1103 11 43.1 <0.001 15.9
Error 588 50.8 0.1 155 0

DF = degree of freedom, SS = sum of square, MS = mean sum square, F = F value, P-value = F probability, %TSS = percentage of total sum square and %GEISS = percentage of genotype by environment interaction sum square.

3.3. AMMI stability value and yield stability index for seed yield

The AMMI-1 biplot (Figure 3) elaborates genotypic and environmental additive main effects against their corresponding first interaction principal component axis (IPCA1). Common bean genotypes placed on the right-hand side of the midline have higher seed yield compared to those on the left-hand side of Figure 3. Genotype G74 (Selian 14) and G35 (Kikobe) had low IPCA1 scores close to zero and high seed yield. This indicates that the genotypes were less involved in genotype by environment interaction, therefore these were the most stable and high yielding genotypes. On the other hand, genotype G93 (Uyole 84), G69 (Selian 06), and G68 (Selian 05) exhibited the highest positive genotype by environment interaction while G99 (Zawadi) and G62 (Raja) expressed the highest negative genotype by environment interaction. Among the three environments, Uyole-Mbeya (E3) had a low contribution to genotype by environment interaction, whereas Selian-Arusha (E1) and SUA-Morogoro (E2) showed larger environmental main effects with high contributions to genotype by environment interaction.

Figure 3.

Figure 3

AMMI-1 model biplot for seed yield (kg/ha) presenting the means of ninety nine genotypes (G) and three environments (E) against their corresponding IPCA-1 scores.

Based on additive main effects and multiplicative interaction (AMMI) stability value (ASV) on seed yield of the harvested 99 common bean genotypes across locations, the genotypes were ranked based on least scores, whereby, low score indicates the most stable genotype. ASV ranked ACC 714 as the most stable genotype due to the lowest ASV followed by Bangaya akatebe, Kaempu, Pasi, and SMC 18. Selian 06 was ranked the most unstable genotype due to the highest ASV. The sum of seed yield and AMMI stability rankings also known as Yield Stability Index (YSI) ranked ACC 714 as the highest seed yielding and stable common bean genotypes across sites, followed by Selian 14, Selian 9, Katuku, and Msolini. SUA 90 was ranked the most unstable common bean genotypes based on YSI (Table 5).

3.4. Experimental sites discriminating power and representativeness on genotypes seed yield

The GGE biplot (Figure 4) shows the discriminating power and representativeness of the experimental sites on the seed yield of the common bean genotypes. An experimental site with a longer vector from the origin of the biplot had a larger discriminating ability for superior seed yield genotypes, while those with a shorter vector had low discriminating power. The experimental site vector with a small angle from the average environmental axis (AEA), is described as more representativeness site for the common bean genotypes seed yield evaluation experiment. E1 (TARI-Selian) with a longer vector from the biplot origin had good discriminating ability compared to the other experimental sites, while E3 (TARI-Uyole) with a shorter vector had poor discriminating ability compared to other experimental sites. E3 (TARI-Uyole) vector had a small angle with the AEA, thus more representative compared to the other sites, whereas E2 (SUA) had a larger angle with the AEA and therefore the least representative site among the experimental sites.

Figure 4.

Figure 4

GGE biplot showing experimental sites discriminating power and representativeness on common bean genotypes seed yield.

3.5. Association between common bean seed yield and yield components with test locations soil chemical properties

Pearson correlation analysis revealed that there was a strong positive significant (P ≤ 0.001) relationship between common bean seed yield (kg/ha) with soil available phosphorus, soil pH, soil exchangeable potassium, sodium, and calcium. A strong negative significant (P ≤ 0.001) correlation between seed yield and total soil nitrogen and organic carbon was observed. A week positive significant (P ≤ 0.001) correlation between seed yield and soil exchangeable magnesium was observed. A strong positive significant (P ≤ 0.001) relationship was obtained between the number of pods/plant and available soil phosphorus, soil pH, exchangeable soil potassium, sodium, and calcium. A moderate negative significant (P ≤ 0.001) relationship between the number of pods/plant with total soil nitrogen and soil organic carbon was obtained, whereas a weak significant (P ≤ 0.001) association was observed between the number of pods/plant and soil exchangeable magnesium. A moderate positive significant (P ≤ 0.001) association was observed between 100 seed weight (g) and available soil phosphorus, soil pH, exchangeable soil potassium, sodium, and calcium, whereas exchangeable magnesium had a weak positive significance (P ≤ 0.001) influence on 100 seed weight. A negative weak significant (P ≤ 0.001) association was observed between 100 seed weight with total soil nitrogen and soil organic carbon (Table 11).

Table 11.

Association of common bean seed yield and yield components with soil properties.

Soil Property Seed yield (kg/ha) Days to 75% flowering Number of pods/plant Number of seeds/plant 100 seed weight (g)
Soil N -0.54∗∗∗ 0.03ns -0.47∗∗∗ -0.12∗∗∗ -0.29∗∗∗
Soil P 0.71∗∗∗ -0.15∗∗∗ 0.64∗∗∗ 0.15∗∗∗ 0.45∗∗∗
Soil OC -0.52∗∗∗ 0.02ns -0.45∗∗∗ -0.12∗∗∗ -0.28∗∗∗
Soil K 0.68∗∗∗ -0.21∗∗∗ 0.63∗∗∗ 0.15∗∗∗ 0.48∗∗∗
Soil Mg 0.13∗∗∗ -0.19∗∗∗ 0.15∗∗∗ 0.02ns 0.18∗∗∗
Soil Na 0.69∗∗∗ -0.20∗∗∗ 0.64∗∗∗ 0.15∗∗∗ 0.48∗∗∗
Soil Ca 0.65∗∗∗ -0.22∗∗∗ 0.61∗∗∗ 0.14∗∗∗ 0.47∗∗∗
Soil pH 0.62∗∗∗ -0.23∗∗∗ 0.58∗∗∗ 0.13∗∗∗ 0.46∗∗∗

∗∗∗ = significant at P ≤ 0.001, and ns = not significant (P > 0.05).

Pearson correlation analysis for common bean seed yield and yield components (Table 12) showed that there was a strong positive significant (P ≤ 0.001) relationship between seed yield and number of pods/plant. The number of seeds/pod exhibited a weak positive significant (P ≤ 0.001) relationship with seed yield, whereas a moderate positive significant (P ≤ 0.001) association was observed between 100 seed weight and seed yield. No significance (P ≤ 0.001) relationship was observed between days to 75% flowering and seed yield and 100 seed weight with the number of pods/plant. Moderate negative significant (P ≤ 0.001) associations were observed between 100 seed weight with days to 75% flowering and the number of seeds/pod.

Table 12.

Association of common bean seed yield and yield components.

Yield component Days to 75% flowering Number of pods/plant Number of seeds/pod 100 seed weight Seed yield (kg/ha)
Days to 75% flowering 1.00 0.12∗∗∗ 0.27∗∗∗ -0.34∗∗∗ -0.003ns
Number of pods/plant 0.12∗∗∗ 1.00 0.43∗∗∗ 0.06ns 0.79∗∗∗
Number of seeds/pod 0.27∗∗∗ 0.43∗∗∗ 1.00 -0.48∗∗∗ 0.27∗∗∗
100 seed weight -0.34∗∗∗ 0.06ns -0.48∗∗∗ 1.00 0.33∗∗∗
Seed yield (kg/ha) -0.003ns 0.79∗∗∗ 0.27∗∗∗ 0.33∗∗∗ 1.00

∗∗∗ = significant at P ≤ 0.001, and ns = not significant (P > 0.05).

4. Discussion

Yield and yield components of common bean genotypes were strongly influenced by the genetic makeup of bean genotypes, environmental conditions of the sites, and their interactions. in common bean, the influence of genotype, environment, and genotype by environment interaction has been reported [31]. Common bean genotypes particularly the landraces which were high yielding in specific sites can be used for improving varieties specific for locations where they have performed better. The highest seed yield was recorded at TARI-Selian followed by TARI-Uyole and lastly SUA-Morogoro, this may have been caused by well-distributed rainfall and soil properties. The high variations of common bean genotypes within location form the basis for selection on the respective bean traits [16].

AMMI analysis revealed that common bean seed yield was largely influenced by the genotype main effect (39.3%) compared to the environmental main effect (31.4). This indicated that the genotypes and experimental sites used were diverse and good for specific and general genotype adaptability studies. Similarly [32] determined a large contribution of cowpeas genotypes (38.0%) in seed yield compared to environmental effects (5.0%), and [26] reported 41.3 % genotype main effect on rice seed yield compared to the environmental main effect (31.9%). In contrast to this study [33], reported a larger contribution of environmental effect (78.2%) compared to the genotype main effect (6.5%). The difference in genotype main effect reported by this study may be due to a difference in the number of common bean genotypes and location used, whereby the current study used 99 diverse bean genotypes while [33] used 14 all white bean genotypes. Due to nearly equal environmental influence and genotype main effect on seed yield, this trait selection needs to be done in several environments to have a genotype that can be grown across several agro-ecological zones and perform more or less the same. From this preliminary one year result, days to 75% flowering, number of pods/plant, number of seeds/pod, and 100 seed weight were observed to be largely influenced by genotypes than environment and genotype by environment interaction, thus these traits are easy to select and breed for compared to seed yield. To confirm the results, the experiment needs to be repeated in other more sites and years.

There are several adaptabilities and stability analysis procedures that are used by plant breeders in the selection of plant genotypes that performs more or less similar across environments [31, 32]. Additive main effects and multiplicative interaction (AMMI) stability value (ASV) is one of the modern methods used for the identification and selection of plant genotypes that are stable across environments. Plant genotypes with low ASV closer to zero are thought to be more stable whereas those with great values are influenced by environmental effects [32]. Some of the bean genotypes that were ranked as stable by ASV had very low yield, this is because stability doesn't care about high or low yielding genotypes [35]. Thus yield stability index (YSI) was used to identify high seed yielding and stable bean genotypes, as it combines both stability and high yielding traits into a single index, that is used in the selection of genotypes [29, 34]. Genotypes with lower YSI are more useful as they have high mean yield and stability traits [28]. Thirty high seed yield and stable common bean genotypes were identified in this study based on YSI.

The concentric circles help in the visualization of the ideal experimental site, which has both high discriminating ability of superior genotypes and representativeness of the experimental sites [37]. Experimental site E1 (TARI-Selian), has both the high discriminating ability of superior common bean genotypes and representativeness of other experimental sites, thus it is an ideal site for a selection of the widely adapted common bean genotypes, as this site provided more information on seed yield performance of the tested genotypes. The experiment can be further conducted into other sites to provide more information on this, as this was a one-season field experiment, [38] used GGE biplot to determine the discriminating power and representativeness of the experimental sites on sorghum genotypes yield.

The influence of individual soil properties on common bean performance indicated a strong positive effect of available soil phosphorus on seed yield and number of pods per plant also moderate 100 seed weight. Thus available soil phosphorus was the most important soil-plant nutrient to increase bean productivity and therefore needs to be considered carefully when growing beans. TARI-Selian which had optimum available soil phosphorus level had higher seed yield compared to TARI-Uyole and SUA which had low soil available phosphorus. The phosphorus influence and limiting factor for common bean seed yield was also been reported [39].

Total soil nitrogen and soil organic carbon influenced common bean seed yield negatively compared to the study [13], where soil organic carbon and nitrogen influenced seed yield in common bean positively. The negative influence of total soil nitrogen on common bean yield and its components may be due to low rainfall at SUA which recorded higher total soil nitrogen compared to other sites. [40] reported that, total soil nitrogen availability is positively influenced by precipitation, thus the availability of the measured total high soil nitrogen at SUA prior–planting may have been decreased by low rainfall during bean growing season. In all sites, soil organic carbon was optimum, therefore its influence on bean seed yield maybe it is the function of other soil and weather parameters. In all experimental sites, soil exchangeable potassium, magnesium, and sodium were adequate for common bean growth, and the highest levels of these were recorded at TARI-Selian, whereas soil exchangeable calcium was adequate and highest at TARI-Selian and low in other sites. All the measured exchangeable bases were positively and strongly correlated with seed yield.

5. Conclusion

All the common bean traits under this study were significantly influenced by genotype by environment interaction, thus a need to plant multilocation trials when selecting for these traits. Days to 75% flowering, number of pods/plant, number of seeds/plant, and 100 seed weight are largely influenced by genotype main effect, while seed yield is almost equally influenced by genotype and environmental main effects. Among 20 identified high seed yielding and stable common bean genotypes across sites, 17 had larger seed yield mean than grand mean, these genotypes includes ACC 714, Selian 14, Selian 9, Katuku, Msolini, CODMLB 033, Nyeupe ndogo, Pasi, Kaempu, Selian 11, Kikobe, Kitebe, Ngwakungwaku, Masusu, Fibea, Uyole 03 and Kichele. These genotypes can further be tested into other several bean-growing areas involving farmers and other common bean stakeholders for participatory variety selection, recommendation, and release. The genotypes can also be used for different breeding purposes in different agro-ecologies of Tanzania. The number of pods/plant can be used in the selection of high seed yielding common bean genotypes, as among the yield component traits, it was observed to associate strongly and positively with seed yield and was less influenced by environmental effect compared to seed yield.

Declarations

Author contribution statement

Mashamba Philipo: Conceived and designed the experiments; Performed the experiments; Analyzed and interpreted the data; Wrote the paper.

Patrick Alois Ndakidemi: Conceived and designed the experiments; Contributed reagents, materials, analysis tools or data; Wrote the paper.

Ernest Rashid Mbega: Conceived and designed the experiments; Analyzed and interpreted the data; Contributed reagents, materials, analysis tools or data; Wrote the paper.

Funding statement

This work was supported by the Centre for Research, agricultural Advancement, Teaching Excellence and Sustainability in Food and Nutritional Security (CREATES) at NM-AIST.

Data availability statement

Data included in article/supplementary material/referenced in article.

Declaration of interests statement

The authors declare no conflict of interest.

Additional information

No additional information is available for this paper.

Appendix A. Supplementary data

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Raw Data - Copy
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References

  • 1.Singh M., Bisht I.S., Dutta M. Springer India; 2014. Broadening the Genetic Base of Grain Legumes. [Google Scholar]
  • 2.Acosta-Gallegos J.A., Kelly J.D., Gepts P. Prebreeding in common bean and use of genetic diversity from wild germplasm. Crop Sci. 2007;47:44–59. [Google Scholar]
  • 3.Ossom E., Zwane S., Rhykerd R. Plant population effects on ecological characteristics of field bean (Phaseolus vulgaris L.) in Swaziland. Trans. Ill State Acad. Sci. 2006;99:1–15. http://scholar.google.com/scholar?hl=en&btnG=Search&q=intitle:Plant+Population+Effects+on+Ecological+Characteristics+of+Field+Bean+(+Phaseolus+vulgaris+L+.)+in+Swaziland#0%5Cnhttp://scholar.google.com/scholar?hl=en&btnG=Search&q=intitle:Plant+population+e [Google Scholar]
  • 4.Salcedo J.M. CGIAR System-wide Genetic Resource Programme; Rome, Italy: 2008. Regeneration Guidelines: Common Bean. [Google Scholar]
  • 5.Musimu J.J. Sokoine University of Agriculture; 2018. Economics of Small Holder Common Beans Production in Mbeya, Tanzania. [Google Scholar]
  • 6.Ministry of Agriculture . 2010. Agriculture Basic Data.http://www.kilimo.go.tz/index.php/en/resources/view/agriculture-basic-data-2005-2006-2009-2010 [Google Scholar]
  • 7.FAOSTAT, crops. 2016. http://www.fao.org/faostat/en/#data/QC
  • 8.Ntukamazina N., Onwonga R.N., Sommer R., Mukankusi C.M., Mburu J., Rubyogo J.C. Effect of excessive and minimal soil moisture stress on agronomic performance of bush and climbing bean (Phaseolus vulgaris L.) Cogent Food Agric. 2017;3 [Google Scholar]
  • 9.Diaz L.M., Ricaurte J., Tovar E., Cajiao C., Terán H., Grajales M., Polanía J., Rao I., Beebe S., Raatz B. QTL analyses for tolerance to abiotic stresses in a common bean (Phaseolus vulgaris L.) population. PloS One. 2018;13:1–26. doi: 10.1371/journal.pone.0202342. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 10.Beebe S.E., Rao I.M., Blair M.W., Acosta-Gallegos J.A. Phenotyping common beans for adaptation to drought. Front. Physiol. 2013;4 doi: 10.3389/fphys.2013.00035. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 11.De la Peña R.C., Ebert A.W., Gniffke P.A., Hanson P., Symonds R.C. 2011. Genetic Adjustment to Changing Climates: Vegetables. [Google Scholar]
  • 12.De Ron A.M., Rodiño A.P., Santalla M., González A.M., Lema M.J., Martín I., Kigel J. Seedling emergence and phenotypic response of common bean germplasm to different temperatures under controlled conditions and in open field. Front. Plant Sci. 2016;7:1–12. doi: 10.3389/fpls.2016.01087. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 13.Chekanai V., Chikowo R., Vanlauwe B. Response of common bean (Phaseolus vulgaris L.) to nitrogen, phosphorus and rhizobia inoculation across variable soils in Zimbabwe. Agric. Ecosyst. Environ. 2018;266:167–173. doi: 10.1016/j.agee.2018.08.010. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 14.Namugwanya M., Tenywa J.S., Otabbong E., Mubiru D.N., Masamba T.A. Development of common bean (phaseolus vulgaris L.) production under low soil phosphorus and drought in sub-saharan Africa: a review. J. Sustain. Dev. 2014;7:128–139. [Google Scholar]
  • 15.Williams H. Swedish University of Agricultural Sciences; 2016. Soil Factors Affecting Plant Performance of Climbing Beans (Phaseolus vulgaris L ) in South Western Kenya. [Google Scholar]
  • 16.Acquaah G. second ed. 2013. Principles of Plant Genetics and Breeding. Malden, USA. [Google Scholar]
  • 17.PLC R.C. 1997. Morogoro Region Socio-Economic Profile.http://www.tzonline.org/pdf/Morogoro.pdf [Google Scholar]
  • 18.Kahimba F.C., Mbaga S., Mkoko B., Swai E., Kimaro A.A., Liingilie A. Trans-SEC Consortium: Müncheberg; Germany: 2015. Analysing the Current Situation Regarding Biophysical Conditions and Rainfed Crop - , Livestock - and Agroforestry Systems, A Baseline Report; 031A249A. [Google Scholar]
  • 19.PLC R.C. 1977. Mbeya Region Socio-Economic Profile.http://www.tzonline.org/pdf/Mbeyareg.pdf [Google Scholar]
  • 20.Chuwa A.A. United Republic of Tanzania National sample census of agriculture. Natl. Bur. Stat. 2012;III:41–44. www.nbs.org [Google Scholar]
  • 21.PLC R.C. 1998. Kagera Region Socio-Economic Profile.http://www.tzonline.org/pdf/kagera.pdf [Google Scholar]
  • 22.Okalebo R.J., Gathua K.W., Paul L W. second ed. Sacred Africa; Nairobi: 2002. Laboratory Methods of Soil and Plant Analysis : A Working Manual. [Google Scholar]
  • 23.Estefan J., Sommer R., Ryan John. Third Edit, ICARDA; Beirut, Lebanon: 2013. Methods of Soil, Plant, and Water Analysis: A Manual for the West Asia and North Africa Region.http://infosiap.siap.gob.mx/aagricola_siap_gb/icultivo/index.jsp [Google Scholar]
  • 24.va Reeuwijk P.L. Sixth Edit, ISRIC; Wageningen, Netherlands: 2002. Procedures for Soil Analysis. [Google Scholar]
  • 25.Ministry of Agriculture Food Security and Cooperatives . 2014. The United Republic of Tanzania Agriculture Climate Resilience Plan.http://extwprlegs1.fao.org/docs/pdf/tan152483.pdf [Google Scholar]
  • 26.Balakrishnan D., Subrahmanyam D., Badri J., Raju A.K. Genotype × environment interactions of yield traits in backcross introgression lines derived from Oryza sativa cv . Swarna/Oryza nivara. Front. Plant Sci. 2016;7:1–19. doi: 10.3389/fpls.2016.01530. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 27.Purchase J.L., Hatting H., Van Deventer C.S. Genotype × environment interaction of winter wheat ( Triticum aestivum L .) in South Africa : II . Stability analysis of yield performance. S. Afr. J. Plant Soil. 2000;17:101–107. [Google Scholar]
  • 28.Bose L.K., Jambhulkar N.N., Pande K., Singh O.N. Use of AMMI and other stability statistics in the simultaneous selection of rice genotypes for yield and stability under direct-seeded conditions. Chil. J. Agric. Res. 2014;74:3–9. [Google Scholar]
  • 29.Adjebeng-danquah J., Manu-aduening J., Gracen V.E., Asante I.K., Offei S.K. AMMI stability analysis and estimation of genetic parameters for growth and yield components in cassava in the forest and Guinea savannah ecologies of Ghana. Int. J. Agron. 2017;2017 [Google Scholar]
  • 30.Gauch H.G., Piepho H., Annicchiarico P. 2008. Statistical Analysis of Yield Trials by AMMI and GGE : Further Considerations. [Google Scholar]
  • 31.Barili L.D., Martins N., Lelis A., Eustáquio J., Carneiro D.S. Genotype-environment interaction in common bean cultivars with carioca grain cultivated in Brazil in the last 40 years, Crop Breed. Appl. Biotechnol. 2015;15:244–250. [Google Scholar]
  • 32.Horn L., Shimelis H., Sarsu F., Mwadzingeni L., Laing M.D. ScienceDirect Genotype-by-environment interaction for grain yield among novel cowpea ( Vigna unguiculata L .) selections derived by gamma irradiation ☆. Crop J. 2017;6:306–313. [Google Scholar]
  • 33.Tadesse T., Tekalign A., Mulugeta B., Sefera G. Evaluation of the effect of genotype , environment and genotype X environment interaction on white common bean varieties using additive main effect and multiplicative interaction ( AMMI ) analysis in the mid- altitude of Bale zone. Southeastern Ethiopia. 2018;13:338–344. [Google Scholar]
  • 34.Milioli A.S., Zdziarski A.D., Woyann L.G., Santos R., Rosa A.C., Madureira A. Yield stability and relationships among stability parameters in soybean genotypes across years. Chil. J. Agric. Res. 2018;78:299–309. [Google Scholar]
  • 35.Rono J.K., Cheruiyot E.K., Othira J.O., Njuguna V.W., Macharia J.K., Owuoche J., Oyier M., Kange A.M. Adaptability and stability study of selected sweet sorghum genotypes for ethanol production under different environments using AMMI analysis and GGE biplots. Sci. World J. 2016;2016:1–23. doi: 10.1155/2016/4060857. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 37.Tena E., Goshu F., Mohamad H., Tesfa M., Seife A. Genotype × environment interaction by AMMI and GGE-biplot analysis for sugar yield in three crop cycles of sugarcane ( Saccharum officinirum L .) clones in Ethiopia Genotype × environment interaction by AMMI and GGE-biplot analysis for sugar yield in thre. Cogent Food Agric. 2019;5:1–14. [Google Scholar]
  • 38.Mare M., Manjeru P., Ncube B., Sisito G. GGE biplot analysis of genotypes by environment interaction on Sorghum bicolor L . ( Moench ) in Zimbabwe. Afr. J. Plant Sci. 2017;11:308–319. [Google Scholar]
  • 39.Mourice S.K., Tryphone G.M. Evaluation of common bean ( phaseolus vulgaris L .) genotypes for adaptation to low phosphorus. ISRN Agron. 2012;2012:9. [Google Scholar]
  • 40.Nie X., Xiong F., Yang L., Li C., Zhou G. Soil nitrogen storage , distribution , and associated controlling factors in the Northeast Tibetan plateau shrublands. Forests. 2017;8:1–13. [Google Scholar]

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