|
|
||||||||
Agricultural Research Station, Virginia State Univ., P.O. Box 9061, Petersburg, VA 23806
* Corresponding author (tmebraht{at}vsu.edu)
| ABSTRACT |
|---|
|
|
|---|
| INTRODUCTION |
|---|
|
|
|---|
Corn earworm is the most serious insect pest of soybean in much of the Mid-Atlantic and southern coastal plain of the USA (Stinner et al., 1980). The adult is attracted to soybean at the time of flowering (Johnson et al., 1975) where it prefers to oviposite on developing new foliage (Eckel et al., 1992). Small larvae tend to be found in greater density in young foliage, perhaps because of protection provided by rolled leaves (Kraemer et al., 1997). Late migration of older larvae to the developing pods and pod feeding may cause severe economic loss. Several management schemes to reduce CEW populations during or before the first two generations have been suggested (Fife and Graham, 1966; Knipling and Stadelbacher, 1983; Wiseman et al., 1984; Mueller et al., 1984). Another management approach is to control CEW on the third generation hosts through the use of minimal pesticides in combination with cultural control (Bradley and Van Duyn, 1980), biological control, and insect resistant cultivars. Even though insecticides provide adequate control of CEW, the use of host plant resistance would be an economically and ecologically better management technique. The genetic base from which most soybean breeders have selected for resistance to insect defoliation is narrow. Most lines selected for resistance are derived from one of three plant introductions (PIs), 171451, 227687, or 229358, that were identified by Van Duyn et al. (1971) as resistant to Mexican bean beetle (Epilachna varivestis Mulsant). These lines were later shown to have resistance to many other defoliating insects, including CEW (Hatchett et al., 1976; Luedders and Dickerson, 1977; Turnipseed and Sullivan, 1976; and Clark et al., 1972).
Breeding program decisions commonly rely on knowledge of the genetic structure of breeding populations and an understanding of the relative importance of genotype x environment interactions (GEI). This interaction is a common concern in plant breeding programs and germplasm evaluation trials. For plant breeders, it is often desirable to find genotypes that show little interaction with environments. Such genotypes may be regarded as stable. Stability is the ability of a genotype to avoid substantial fluctuation in injury over a range of environments, and is a breeding objective difficult to achieve. The cause of CEW injury stability could be due to physiological, morphological, and phenological mechanisms that impart stability. The objectives of this study were to determine the magnitude of genotype x year interaction (GYI) of antibiosis to CEW and to identify genotypes with stable performance.
| MATERIALS AND METHODS |
|---|
|
|
|---|
|
,
,
-trifluoro-2,6-dinitro-N, N-dipropyl-p-toluidine, 0.56 kg a.i./ha) herbicide (Treflan HFP, manufactured by DOW, AgroSciences, LLC, Indianapolis, IN) was incorporated at the recommended rate prior to planting. Foliage was collected when plants had reached R1 development stage (Fehr et al., 1971). Half to fully expanded terminal trifoliolates were excised, placed in plastic self-sealing bags, and transported to the laboratory in a cooler. The trifoliolates were separated into leaflets with petioles removed and placed into 150- by 15-mm plastic Petri dishes lined with moistened #2 filter paper. Four Petri dishes were used per genotype per replication, making a total of 12 Petri dishes per genotype. Two neonate CEW larvae were placed on the foliage in each Petri dish to allow for possible first instar mortality unrelated to leaf antibiosis (Kraemer et al., 1997; Kraemer, 2001). The Petri dishes were incubated in an environmental chamber at 25°C and 14:10 (light:dark) photoperiod. Although relative humidity within the environmental chamber was not controlled (5060%), the filter paper within each Petri dish was kept moist by applying approximately 1 mL of water every other day. The number of larvae per Petri dish was reduced to one after 4 to 5 d. After 10 d, the larvae were weighed and mortality was determined. When more than one CEW larvae was found in a Petri dish, probably from eggs brought in on the foliage, the largest larva was selected for analysis.
Statistical Analysis
The data for each year were analyzed by (SAS,1996) as a randomized complete block design. After testing the homogeneity of error variance, combined data over years analysis was conducted by a genotype x year interaction (GYI) model. Year was tested for significance using replication within year (rep[yr]) as the error term, genotype was tested with GYI as the error term, and GYI was tested by means of the pooled error term. Means were separated by least significant difference (LSD) at the 5% probability level as described by Steel and Torrie (1980).
The number of replications (R) required to show specific differences between genotypes is given by the following formula modified from Mendenhall and Scheaffer (1973):
![]() |
/2 is the t-values associated with significance level of the t-test (
= 0.05 for our calculation) and are dependent on the degree of freedom (df) of sample variance. t
is the t-value associated with accepting a false null hypothesis based on the t-test (ß = 0.05 for our calculation),
2 is the error variance, d is the true difference between two genotypes.
The previous formula can be modified to determine the number of environments (E) required to show specific differences between genotypes with different levels of GYI
![]() |
2GE is the interaction variance component. The rational for determining the number of replication or environments to detect specific difference between treatment means rather than overall treatment effects has been discussed by Carter et al. (1983) and Reese et al. (1988). Both GYI and cultivar superiority performance measure (CSPM) methods of analyses were used for the data. The CSPM values estimated are the mean squares of the differences between an entry mean and the maximum mean of a location, summed and divided by twice the number of locations (Lin and Binns, 1998). The genotype CEW larval means generated by GYI were ranked in descending order from 1 to 35. One being with the highest value and 35 being with the lowest CEW larval weight. Similarly the values generated by the CSPM were ranked from 1 to 35. The genotype with the lowest CSPM value was given a score of 1 and the genotype with the highest value was given a rating of 35. A Spearman's rank correlation was used to determine the association of rank scores generated by G x E analysis with the mean ranking of CSPM scores.
| RESULTS AND DISCUSSION |
|---|
|
|
|---|
0.01) among the genotypes tested were found for CEW larval weight for each growing season. In 1996 and 1998, the genotypic variances exceeded that of error variance, while in 1997, they did not. The significant genotypic differences indicated that genetic variation exists for CEW resistance among the tested genotypes. This offers promise for selection and improvement through breeding and selection. A significant GYI was observed. This interaction was the result of a change in the magnitude and rank of the differences among the genotypes in the different years. The significant GYI observed suggests that the performance or response of the genetic materials used in this study were not stable from one growing season to another. A stable genotype is defined as a genotype able to avoid substantial fluctuation in CEW resistance over a range of environments, a breeding objective that is difficult to achieve. Stability could be due to physiological, morphological, and/or phenological mechanisms.
The sum of squares of the sources of variation expressed as percentages revealed the relative contribution of each source to the total variance. The pooled error variances contributed proportionally the highest (55%) to the total variability, followed by replication within year (19%), and genotype (11%). The proportional contribution of year to the total variation was only 9%. The GYI contributed 6% to the total variation. Among the major components, the interaction component contributed the least. The pooled error sum of squares on the other hand contributed proportionally more than genotype and GYI to the total sum of squares.
The number of replications required to detect a 10, 20, 30, 40, and 50% difference of magnitude between means of genotypes for CEW larval weight (
= 0.05, ß = 0.50) were 181, 45, 20, 11, and 7, respectively. If the power of the test was increased to 0.9 (1 - ß), then the number of replications required to show specific genotypic differences would increase 2.5 fold. The number of environments required to show specified differences in CEW larval weight between two genotypes was calculated assuming
2GE = 0.1
2 (Table 2)
. Detection of 40% difference of the mean between two genotypes would require four and three environments with four and five replications per environment, respectively. However, if the specified difference between two genotypes was 50% of the mean, then four and three environments, respectively for two and three replications are required or two environments with four replications per environment.
|
The CEW larva mean weight distribution in 1997 was similar to 1996 in that 37% had lower values than the overall mean, 26% were equal to the overall mean, and 37% had higher values than the overall mean. In 1997, lines that registered the lowest CEW larval weight mean values were VS94-05, VS94-11, VS94-12, VS94-44, VS94-45, and V91-0613. The mean larvae weight in 1998 revealed that about 46%, had CEW mean larval weight lower than the overall mean, 26% had weights about equal to the mean, and about 28% of the genotypes had weights higher than the overall mean. The lines resulting in the lowest CEW larval weights were VS94-11, VS94-12, VS94-16, VS94-17, VS94-18, and VS94-26. The mean larval weight was higher in 1996 than 1997 and 1998. The susceptible checks, Essex and PI 399055, had 156 and 170 mg overall mean larval weights, respectively, which were significantly higher than the 81 mg mean of L76-0049, a resistant check.
In comparing genotypic CEW larval weight values averaged over the 3 yr, we found about 29% with lower values than the overall mean, 11% with equal values to the mean and the largest group about, 66%, had weights higher than the overall mean. The overall CEW mean larval weight of the genotypes ranged from 55 mg for VS94-12 to 169 mg for PI 399055 with a mean of 124 mg (Table 3) . The mean of the top 10 high ranking genotypes ranged from 169 to 139 mg. The genotypes with CEW larval weights significantly higher (0.05) than overall mean were PI 399055, VS94-42, V89-2623, Essex, and VS94-13. Over three growing seasons three lines, VS94-11, VS94-12, and VS94-26, consistently showed lower CEW mean larval weights than the other genotypes. These results suggest that the expression of CEW resistance in these three lines is relatively less affected by environmental fluctuations. They could serve as genetic resources in a breeding program aimed at reducing CEW larval foliage damage in soybean. In each of the three growing seasons and in the overall average results, the susceptible checks, Essex and PI 399055, exhibited higher values than the overall genotypic means, whereas the resistant check, L76-0049, was significantly lower than the overall genotypic means.
|
The Spearman's rank correlation between the combined over years mean ranks and CSPM ranks was 0.985 (
0.01), and between the overall rank average was 0.996 (
0.01). Moreover, the rank of the overall mean and the rank average was 0.995 (
0.01). These high correlation values indicated that either GYI or CSPM methods of analyses are ideal in identifying genotypes that are significantly resistant to CEW and stable.
The mean CEW larval weight of the two susceptible standard genotypes, PI 399055 and Essex, were 169 and 157 mg, respectively. The resistant standard (L76-0049) had a CEW larval weight of 81 mg which was significantly lower than both the susceptible checks, PI 399055 and Essex. In this study, we found VS94-12 to have 33% lower CEW larval weight than L76-0049. The other genotypes that are higher than L76-0049 by less than 5, 14, 17, and 28% were VS94-11, VS94-21, VS94-16, and VS94-26, respectively. This suggested that first, the screening technique used was adequate to make a clear demarcation between the CEW resistant and susceptible lines and second that sufficient variability exists among the genotypes tested to make further improvement possible through selection and hybridization.
The broad range of resistance exhibited by PIs 171451, 227687, and 229358 have enhanced their usefulness in breeding programs. However, they are all from late maturity groups (MGs) VII and VIII and represent a relatively narrow genetic base from which to select for resistance. The addition of the new breeding lines VS94-11, VS94-12, VS94-16, VS94-21, and VS94-26 includes some additional resistant parentage that may increase genetic diversity. Breeding lines VS94-11 and VS94-12 were selected from a L76-0049 x Essex cross. The resistant parent of L76-0049 is from one of the old resistant standards, PI 171451. However, breeding lines VS94-21, VS94-26, and VS94-16 were selected from York x PI 416937, Bay x PI 416937, York x PI 416925 crosses, respectively. Plant introductions 416937 and 416925 are from MG VI and were reported to have resistance to Mexican bean beetle defoliation (Kraemer et al. 1990). PI 416937 is also resistant to drought and tolerant of aluminum (Carter and Ruffy, 1992). The four breeding lines VS94-12, VS94-16, VS94-21, and VS94-26 belong to MG VI and VS94-11 belongs to MG V. All these lines were entered into Mid-Atlantic cooperative yield test during 1994 and produced seed yield equal to the standard checks Brim and Twiggs.
Determining the GEI is common in plant breeding programs and germplasm evaluation trials because it is often desirable to find genotypes that show little interaction with the environment. While some lines had a stable level of resistance over environments, others did not. Because the GYI was significant, tests in multiple years will be required to adequately evaluate resistance to CEW. Selections among these genotypes for CEW resistance would be different in each growing season.
The resistance measured by Petri dish assays is of the antibiosis type (Painter, 1951). Resistance resulting from nonpreference was not evaluated and could also be a factor in the field. However, resistance based on antibiosis is more reliable because nonpreference may vary with the type of alternative plant hosts in the area. Petri dish bioassays have been shown to correlate well with field evaluations (Kraemer 2001). The results of our study also demonstrated that the Petri dish assay technique was reliable to separate susceptible from resistant genotypes. On the basis of the resource allocation estimates, we found that the larval weight differences between genotypes of 40% of the experimental mean can be detected with three environments and five replications per environment using this bioassay. The data for this study could assist researchers in the design and resource allocation for future experiments involving CEW antibiosis study. Moreover, these results suggested that sufficient genetic variation exists among genotypes to make improvement through breeding. The advantage of using host plant resistance to reduce yield losses to CEW over the use of alternative methods generally outweighs its limitation. Economic benefits offered by host resistance are its ease of adaption and reduction of variable costs. From an ecological perspective, the main benefits of host plant resistance are its specificity and compatibility with integrated pest management (IPM).
| ACKNOWLEDGMENTS |
|---|
| NOTES |
|---|
|
|
|---|
Received for publication October 1, 2001.
| REFERENCES |
|---|
|
|
|---|
This article has been cited by other articles:
![]() |
T. Mebrahtu and M. Kraemer Registration of VS94-11, VS94-12, and VS94-21 Soybean Germplasm Lines Resistant to Corn Earworm Foliar Damage Crop Sci., March 1, 2004; 44(2): 701 - 702. [Full Text] |
||||
| ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
| HOME | HELP | FEEDBACK | SUBSCRIPTIONS | ARCHIVE | SEARCH | TABLE OF CONTENTS |
| The SCI Journals | Agronomy Journal | Vadose Zone Journal | |||
| Journal of Plant Registrations | Soil Science Society of America Journal | ||||
| Journal of Natural Resources and Life Sciences Education |
Journal of Environmental Quality |
||||