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a Inst. of Plant Breeding, Seed Science, and Population Genetics, Univ. of Hohenheim, D-70593 Stuttgart, Germany
b International Crops Research Institute for the Semi-Arid Tropics (ICRISAT), B.P. 320, Bamako, Mali
* Corresponding author (presterl{at}uni-hohenheim.de)
| ABSTRACT |
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Abbreviations: AMMI, additive main effects and multiplicative interaction GY, grain yield ICRISAT, International Crops Research Institute for the Semi-Arid Tropics IPC, ICRISAT pollinator collection PP, panicles per plant SY, dry stover yield TF, time to flowering TG, thousand-grain weight
| INTRODUCTION |
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In the dry areas of western Rajasthan, farmers use diverse strategies to improve their own landraces (Weltzien, 2000; Christinck, 2002). These strategies include the introgression of modern cultivars with high yield potential into well-adapted landraces. Information about combining ability and heterotic pattern of the current breeding materials can be used, on the one hand, to optimize farmer breeding; it could, on the other hand, help conventional on-station breeding programs to create new source populations for hybrid and population breeding with increased genetic variability and to combine adaptation with yield potential.
The objectives of this study were to evaluate the performance of six elite breeding populations and three landraces in contrasting environments and to determine the heterotic pattern among diallel crosses of those populations. Through this analysis, the most promising ways to use these materials in population improvement programs for the arid zone environments of Rajasthan are explored.
| MATERIALS AND METHODS |
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Elite Populations
EC-C6:
Early Composite Cycle 6, based largely on Indian breeding materials, mostly originating from the Gujarat pearl millet-breeding program. New early-maturing breeding lines from other ICRISAT composites were introgressed in every selection cycle.
EC II:
Early Composite II, developed by random-mating early-flowering progenies from ICRISAT's medium-maturity breeding populations, which draw on African, including some Iniadi landraces, and Indian germplasm. It was originally called the Early Gene Pool.
EC 87:
Early Composite 87, developed by random mating EC II, with two cultivars from the Bold Seeded Early Composite (BSEC) and one cultivar from EC-C6. The BSEC is based mainly on landrace germplasm from Togo and Ghana.
EC 89: Early Composite 89, a population cross of EC-C6 with BSEC.
Elite High-Tillering Populations
HiTiP 88 and HiTiP 89:
High Tillering Population 88 and 89, respectively. The parental materials of these populations were mainly high-tillering pollinator lines from the ICRISAT pollinator collection (IPC). The IPC parents of HiTiP 88 differ from those of HiTiP 89.
Landrace Populations
WRajPop C2:
Western Rajasthan Population based on 13 landrace accessions from northwestern India. This population has been improved by two cycles of S1progeny selection for downy mildew resistance (Weltzien R. and King, 1995).
PakLR 74:
A landrace from Pakistan (ICRISAT genebank IP 18065), collected in a region where cultivation follows flash floods (Weltzien and Bhatti, 1991).
LRE 128:
A landrace from western Rajasthan (ICRISAT genebank IP 3425).
A detailed description of the materials, except the landraces PakLR 74 and LRE 128, is given by Yadav and Weltzien (1998). To analyze the heterotic pattern, 36 crosses among the nine parental populations were produced according to a diallel mating scheme. A minimum of 50 panicles was pollinated with pollen bulked from a minimum of 25 panicles every day for a minimum of 14 d. Crossing continued during the core flowering period of each population and a minimum of 200 plants were pollinated for each cross. Reciprocal crosses were made, and seed was bulked to exclude maternal effects. Crossing was done during the dry post-rainy season, when good seed quality is assured.
Field Experiments
The nine populations, along with their 36 crosses, were evaluated in eight environments (Table 1) during the rainy seasons (July to September) of 1991, 1992, and 1993. The test locations were subdivided into three groups according to their latitude, mean GY of the trials, and environmental conditions (rainfall, fertilizer input, and soil type). These groups were: (i) the arid zone environments of northwestern India at the Rajasthan Agricultural University research station in Fatehpur-Shekhawati and at the Central Arid Zone Research Institute in Jodhpur; (ii) the more favorable production environments of northwestern India at the Haryana Agricultural University Farm at Hisar, Haryana, and (iii) the test environments at ICRISAT at Patancheru near Hyderabad in Andhra Pradesh.
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Field design for the experiments at Rajasthan, Hisar 1991, and Patancheru 1991 was an 8 by 8 lattice with four replications including populations, population crosses, and check cultivars. The experiments at Hisar (1992) and Patancheru (1992 and 1993) were laid out as an 11 by 11 lattice with four replications.
The experiments in all environments were machine-planted in four-row plots of 4-m length with an interrow distance between 45 cm (Hisar 1992) and 75 cm (all others). Experiments were overplanted and thinned to a final plant density between four (Rajasthan) and nine plants per square meter (Patancheru and Hisar). Plant densities were adjusted according to the water availability of the different environments. Before planting, 10 to 18 kg ha-1 N and 20 to 40 kg ha-1 P (P2O5) fertilizers as diammonium phosphate were banded below the rows, following the standard cultural practices of the respective experimental station. An additional application of 12 to 46 kg N ha-1 in the form of urea was side-dressed
20 d after emergence. The plots were kept free from weeds manually and by cultivation.
The following traits were recorded or calculated for each plot: Time to flowering, recorded as the number of days from planting date until 50% of the plants of each plot had stigma emergence in main shoot panicles, number of panicles per plot recorded at maturity, and panicles per plant (PP) calculated for each plot. At maturity, all panicles in the central 3 m of the four rows were harvested by hand. The panicles were dried, weighed, threshed, and the grain weighed to determine GY (g m-2). The stover was cut at ground level and fresh weight of the stover was recorded. A subsample was taken, weighed, dried, and reweighed to determine moisture percentage. Dry stover yield (g m-2) was calculated from fresh weight and moisture percentage. Thousand-grain weight (TG, g) was determined from the mean weight of two 100-seed samples.
Statistical Analyses
Lattice analyses of variance were performed for each location. Lattice-adjusted means and effective error mean squares were used in the combined analyses across environments (Cochran and Cox, 1957). Year and location combinations were considered as random and populations and their crosses were considered as fixed effects.
Gardner and Eberhart's (1966) Analysis II was used to estimate genetic effects and their variances by fitting the lattice-adjusted means of the nine parental populations and their 36 crosses to the following linear model:
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= 0 when i = j, and
= 1 when i
j. As described by Gardner and Eberhart (1966), the sums of squares, which contribute to each parameter, were estimated by fitting successively more complex models. Midparent heterosis was calculated as the difference between the performance of the cross and the mean of the parents, relative to the mean performance of the parents. Significance of heterosis for each cross was tested with a t test, comparing the midparent and the population cross mean.
Entry x environment interaction effects for GY were analyzed using the AMMI (additive main effects and multiplicative interaction) model (Crossa et al., 1990). This method estimates interaction effects in standard ANOVA with entries (populations and crosses) and environments as main factors, and subsequently fits the interaction effects in a principal component analysis.
Analyses of variance were computed with the GENSTAT software package (1993, Version 5, Release 3, VSN International Ltd., Hemel Hempstead, U.K.). The AMMI analysis was calculated using the PROC IML algorithm of the software package SAS (Release 6.03, SAS Institute, Cary, NC). The SAS code for calculating the AMMI analysis was kindly provided by Dr. B. Schill and is described in Link et al. (1996).
| RESULTS |
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Mean GYs in Patancheru were double to threefold those in the Rajasthan environments and 50% higher than mean GYs in Hisar. These yield levels correspond to contrasting growing conditions during the experimental period and confirm the subdivision of the test environments into the three groups. Stover yield was highest at Hisar, but differences between location means were less distinct than those for GY. At Patancheru, flowering was on average 7 d earlier, plants had 43% more PP, and TG was 26% higher than in the Rajasthan environments. The difference in flowering was in part caused by the longer daylengths in Rajasthan, and in part by the effects of the severe early droughts, particularly in 1991, which caused delayed flowering of all genotypes.
Performance of Parents and Population Crosses
The GY of the elite populations was distinctly higher compared with the landraces (Table 2) and corresponded to their high population effects in the Gardner and Eberhart Analysis II (data not shown). Population EC II had the highest GY across all eight environments as well as across Rajasthan environments, while EC 87 was the highest-yielding population across the three Patancheru environments (Table 2, Table 3). The two elite high-tillering populations showed an intermediate GY performance, which was most apparent at Patancheru. Stover yield of elite materials was of the same magnitude as SY of landraces in Rajasthan and Patancheru. The three landraces flowered on average 4 d earlier and tillered more, with double the number of PP compared with the elite parents. Reduction of number of panicles under stress conditions was more pronounced with the elite populations than with the landraces. Mean thousand-grain weights of the landraces and the elite high-tillering populations were lower, 7.4 and 8.0 g, respectively, compared with the elite parents (10.5 g).
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For SY, mean superiority of population crosses over their parents was significantly positive and higher than for GY (Table 1). The magnitude of differences, however, was also variable across environments, and significant only in four out of eight environments. The highest heterosis values were observed in the marginally drought stressed environment, Jodhpur (1992), and in the favorable environment of Patancheru (1992).
Average heterosis for TF was generally low and significant only in the Jodhpur (1992) and the Patancheru (1993) experiments. The number of PP showed significant negative heterosis in the lowest yielding environment, Jodhpur (1991), and significant positive heterosis in the highest yielding environment. Thousand-grain weight showed a mean superiority of population crosses over parents of 4.35%, and significant heterosis was observed in all three groups of environments [Jodhpur (1991,1992), Hisar (1991), and Patancheru (1992)].
Gardner and Eberhart's Analysis II revealed, for all traits, highly significant variation for population and heterosis effects when computed across all environments (Table 5). Contributions of heterosis effects to the entry sum of squares were generally low, ranging from 5 to 12%, except for SY, where the proportion of heterosis effects accounted for 44% of the entry sum of squares.
When the analyses of variance were computed separately for each of the three groups of environments, GY showed significant or highly significant population effects (Table 6). Variation of heterosis effects for GY was also significant when combined across the Rajasthan environments and 51% of the entry sum of squares could be explained by heterosis effects. The subdivision of heterosis into average, population, and specific heterosis showed that most of this variation could be attributed to specific heterosis effects. A different pattern was observed in the analyses of GY across the Patancheru environments. Although heterosis was highly significant in Patancheru, it accounted only for 5% of the entry sum of squares and the variation among entries was mainly caused by population effects. The variation of heterosis was nonsignificant combined across the two Hisar environments.
The SY population and heterosis effects were nonsignificant in the Rajasthan and Hisar groups of environments, but highly significant in Patancheru. As in the case of GY, specific heterosis was more important than population heterosis at Patancheru.
Relationships among Traits
The number of PP was negatively correlated with GY, whereas late flowering and high TG were positively associated with GY (Table 7). These correlations were strongest in the highest yielding Patancheru environments and only moderate to nonsignificant in the more stress-prone environments. Stover yield showed significant correlations only with GY in Rajasthan and TF in Patancheru. The magnitude and sign of the correlation among traits of crosses and traits of parents were generally comparable, although especially in the Patancheru environments, the correlations between traits of crosses were smaller compared with associations between traits of parent populations (data not shown).
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| DISCUSSION |
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In the present study, average level of heterosis across environments was low, mainly because positive and negative heterosis values balanced each other out. The parent populations differed widely in their plant architecture and origin. Therefore, insufficient genetic diversity could not explain the low average heterosis and the occurrence of negative heterosis, especially in the wide crosses between landraces and elite materials. The elite populations differed in their content of African and Indian germplasm, but there was no obvious heterotic pattern related to the origin of the elite populations. The landrace parents originated from the dry areas of northwestern India and Pakistan, and the elite parents were developed in the Patancheru environment. Therefore, adaptation to different local conditions could be one reason for the comparatively low heterosis values, and could be explained through coadapted genes, at many loci, interacting in an epistatic manner. When such populations are crossed, the F1s are adapted to neither of the different environments (Moll et al., 1965; Geiger, 1988; Falconer and MacKay, 1996). The present study was not designed to estimate such epistatic effects.
For GY, expression of heterosis in this set of materials depended on the environmental conditions, and more positive heterosis values occurred under drought stress in the Rajasthan environments. Haussmann et al. (1998) obtained similar results with sorghum lines and hybrids in Kenya. Pethani and Dave (1992) reported that levels of heterosis for pearl millet in different environments changed. Bidinger et al. (1994) and Yadav et al. (2000) evaluated topcross hybrids between elite male-sterile lines and landraces as pollinators in different environmental zones of Rajasthan and under terminal drought conditions in Patancheru. Heterosis was calculated as the superiority of the hybrid over its landrace pollinator. Average heterosis for most of the traits tended to be greater under drought stress conditions than in the environments with only mild stress. For GY, results depended on the male-sterile parent. Crosses with one male-sterile line showed greater heterosis under drought stress, whereas hybrid superiority of the crosses with the other line was greater under more favorable conditions. Highest estimates for heterosis were, however, obtained under conditions of terminal drought. This could be partly caused by the lack of adaptation of landraces to the Patancheru environment.
The population crosses, especially those involving landrace parents, expressed a relatively high number of panicles with unusually poor seed set (data not shown). Subsequent observations of some of the same populations in test crosses with male-sterile lines indicated that this poor seed was caused by chromosome translocations segregating in these populations. This could partially explain the low levels of heterosis, and its high level of specificity, but not the variability across different groups of environments.
Midparent heterosis for SY was on average higher than for GY and significant across environments, which is in contrast to the study of Yadav et al. (2000). It was also variable across environments but followed a different pattern than heterosis for GY. Heterosis tended to be higher than for GY in all favorable environments, including Jodhpur in 1992, the year with the higher seasonal rainfall within the Rajasthan environments. The Gardner and Eberhart Analysis II across all environments showed a much higher percentage of sum of squares explained through heterotic effects for SY (44%) than for GY (7%). All three components of heterosis were significant, with the largest contribution of specific effects. When individual analyses were performed for the different groups of environments, however, heterotic effects were only significant in Patancheru, and specific effects dominated. Burton (1968) tested 106 pearl millet F1 hybrids from inbred lines in three years for their total annual forage yield (three to four cuttings per year). In contrast to our results, the hybrids outyielded their inbred parents by a greater margin in a year with strong environmental stress conditions (73%) than in a favorable growing season (53%).
Drought escape through early flowering is advantageous in growing seasons with terminal drought stress. On the other hand, later anthesis can be beneficial in escaping early season drought stress (Bidinger et al., 1987; van Oosterom et al., 1996). Heterosis for earliness is common in pearl millet and has also been reported by Bidinger et al. (1994) and Yadav et al. (2000). In a study with topcross hybrids on extremely early male-sterile lines, the greatest yield superiority of hybrids over landrace parents was observed in a terminal stress environment where the hybrids escaped drought stress via earlier flowering (Yadav et al., 2000). In the present study, population crosses flowered on average 0.4 d later than their parents, resulting in a slightly positive heterosis for TF, and possibly a yield advantage at the three Rajasthan locations, where early season drought occurred.
Usefulness of Population Crosses
The aims of pearl millet breeding programs for arid-zone environments are good adaptation to variable drought stress to minimize the risk of crop failure in unfavorable years, high yield potential for both grain and SY, and high food and fodder quality. The landraces showed good adaptation to the local environments of Rajasthan. Their plant type differed considerably from that of elite breeding populations, in being high-tillering, small-seeded, and early-flowering. The early flowering would seem to maximize grain fill by escaping terminal drought stress. Unfortunately, during the 3 yr of this study, only early season drought stress was observed. The high tillering capacity enables the formation of new tillers in response to continuing or intermittent rainfall. These are characteristics that farmers associate with good adaptation to severe stress conditions (van Oosterom et al., 1996; vom Brocke et al., 2000).
Many of the population crosses did combine productivity traits of the elite populations and the adaptive traits of the landraces. Among the 10 superior crosses in Rajasthan, three involved a landrace parent. These three crosses showed not only good grain and stover productivity but also were the earliest flowering and had the highest number of PP among the 10 highest-yielding crosses. Eight of the 10 highest-yielding crosses in Rajasthan were combinations of high-tillering materials (landraces and elite high-tillering populations) with elite populations. In contrast, at Patancheru, only five such populations were among the top 10 and none of them was derived from a cross with a landrace. In Rajasthan, however, only two of the population crosses derived from high-tillering materials expressed an above-average number of PP (EC-C6 x LRE 128 and EC 87 x LRE 128).
Livestock are a very important part of the agricultural production systems in arid-zone environments. Therefore, in addition to using pearl millet grain as human food, SY and quality are of great economic importance for farmers. As mentioned before, heterosis for SY was significant and important when analyzed across all environments. A moderate positive correlation between stover and GY occurred in Rajasthan, and among the 10 highest yielding population crosses were five populations with SY ranks among the top 10. It is interesting that the three highest grain yielding landrace crosses were also superior in SY. It should, therefore, be possible to combine high potential for grain and SY in one population. Two of these landrace crosses were also higher tillering than the elite populations, which is an indicator of stover quality often used by farmers in Rajasthan (Christinck et al., 2000).
Implications for Pearl Millet Breeding Programs in Arid-Zone Environments
Choosing the right germplasm is an important prerequisite for a successful breeding program. Basic materials for breeding should have a high mean performance and high genetic variability to maximize gains from selection (Schnell, 1983). High genetic variability can be expected in population crosses showing high levels of heterosis. The three population crosses involving landrace parents (EC 89 x WRajPop C2, EC-C6 x LRE 128, and EC 87 x LRE 128) did express high means and high levels of heterosis for GY. These three populations were also superior in SY and two of them had above average tillering potential. Earliness of the three populations should be improved because the population crosses of LRE 128 were
3 d later compared with their landrace parent (data not shown). Therefore, these crosses could be used to widen the germplasm base and to combine the high yield potential of elite materials with the good adaptation of the landraces.
In another study, subsequent recurrent selection efforts in populations based on the highest-yielding crosses between landrace and elite parents did show the expected gains in yield stability (Yadav and Weltzien-Rattunde, 1998). The improved populations outyielded landrace cultivars in early and late season stress years, as well as in favorable years. Selection in landrace populations alone did not result in productivity gains across a broad range of more favorable conditions.
Our results indicate the great value of local landraces as genetic resources for pearl millet breeding programs targeting arid environments. The suitability of source populations, however, varied depending on the specific interaction among these source populations and on their reaction to the environment. In practice, information about the usefulness of such resources regarding quantitative characteristics, such as adaptation, yield potential, or heterotic pattern is lacking for most cases. To improve the usefulness of such genetic resources, detailed evaluations of landraces collected from farmers' fields would be highly desirable and should be performed in the target environments.
Implications for Farmer Participatory Breeding Programs
Farmers in Rajasthan have developed strategies to improve productivity and to increase diversity within their landraces through introgression of modern cultivars (Dhamotharan et al., 1997; Weltzien R. et al., 1998; vom Brocke et al., 2000, 2002). Farmers expect that the mixed and outcrossed populations increase the adaptive range of their seed stocks by maintaining specific landrace plant types, well adapted to stress, and adding elite plant types that respond better to improved growing conditions. Population crosses between elite and landrace materials showing high heterosis are one way to broaden genetic variability in farmer-maintained landraces. Our study supports farmers' experiences. This study also showed, however, that not all combinations between landraces and elite materials had the same benefits. While many of the elite x landrace crosses showed GY considerably above the best landrace parent, only three crosses had a high GY performance and a high level of heterosis. Thus, only these crosses offer good chances for increased gains from selection (also by farmers). To support the farmers' breeding efforts, it could be helpful to test their landraces in combination with a range of improved materials. One could identify those elite materials offering the greatest benefits to farmers, who are interested in mixing, crossing, and selecting in diversified landrace populations.
The analysis of the environment x entry interaction effects also showed clearly that only the landrace parents and the landrace x landrace crosses clustered near the stress environments. All the elite x landrace crosses, as well as the improved landrace population (WRajPop C2) clustered with the intermediate Hisar environments. Thus, there seems to be a clear loss of adaptation associated with these type of wide crosses. This confirms reports from poor farmers who have to grow pearl millet under the most severe stress conditions. They observed a loss of adaptation of such crossed materials they received from better-off farmers (Dhamotharan et al., 1997, Christinck, 2002). Vom Brocke et al. (2002) confirmed these observations by comparing farmer-managed seed stocks in field experiments. It remains to be explored if selection within these population crosses in the target environment can recover some of this adaptation to stress, while maintaining responsiveness to good growing conditions. Routine evaluations of such populations in on-station trials of selection done on the research station indicated that this is possible (Yadav and Weltzien R., 1998). Thus, population crosses do offer opportunities for exploiting heterosis through population breeding, in conjunction with a suitable selection strategy to meet farmers' needs for adaptation, responsiveness, and quality traits.
| ACKNOWLEDGMENTS |
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Received for publication March 25, 2002.
| REFERENCES |
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