Abstract
Perennial ryegrass (Lolium perenne) is the most widely grown temperate grass species globally. Intensive plant breeding in ryegrass compared to many other crops species is a relatively recent exercise (last 100 years) and provides an interesting experimental system to trace the extent, impact and trajectory of undomesticated ecotypic variation represented in modern ryegrass cultivars. To explore germplasm dynamics in Lolium perenne, 2199 SNPs were genotyped in 716 ecotypes sampled from 90 European locations together with 249 cultivars representing 33 forage/amenity accessions. In addition three pseudo-cross mapping populations (450 individual recombinants) were genotyped to create a consensus genetic linkage map. Multivariate analyses revealed strong differentiation between cultivars with a small proportion of the ecotypic variation captured in improved cultivars. Ryegrass cultivars generated as part of a recurrent selection programme (RSP) are strongly associated with a small number of geographically localised Italian ecotypes which were among the founders of the RSP. Changes in haplotype frequency revealed signatures of selection in genes putatively involved in water-soluble carbohydrate (WSC) accumulation (a trait selected in the RSP). Retrospective analysis of germplasm in breeding programmes (germplasm dynamics) provides an experimental framework for the identification of candidate genes for novel traits such as WSC accumulation in ryegrass.
Plant species encounter a diverse set of selective pressures as they spread into new ecosystems, leading to changes in disease resistance, growth habit, production or partitioning of metabolites and gross morphology. Ecotypic material thus represents an important source of adaptive genetic variation which can be maintained by gene banks for use in conservation efforts or plant breeding. With the availability of high-density genotyping systems, this variation can be studied on a genome wide basis– both for understanding the genes which underpin adaptive traits, and also to facilitate their incorporation into plant breeding programmes for crop species1,2. These natural accessions can provide a source of useful traits which may have been lost to genetic erosion during the domestication process, and which can be reintroduced via introgression. This approach has been used to great success in long-domesticated species, such as rice, by breeding with wild relatives2. In more recently-domesticated species, there is the potential to investigate the impact of domestication on genetic diversity as well as identifying the genes underlying natural variation which has been incorporated into breeding programmes3. The forage grass Lolium perenne, has only recently (past 100 years) been subjected to selective breeding4 and provides an interesting experimental system to explore the dynamics and impact of domestication on genetic diversity in a recently evolved crop.
Lolium perenne (perennial ryegrass) is the most widespread grass species in temperate regions globally due to its rapid establishment, persistence and nutritional value to ruminants. It is outbreeding and exhibits extensive genetic variation for morphological growth characteristics5,6, extreme climate tolerance7,8, disease and pest resistance9,10 and soil mineral composition11,12. This variation is represented in ecotypes that are maintained in germplasm collections that can be characterised and utilised in breeding programmes to develop improved cultivars that are adapted to a range of biotic and abiotic stresses.
Due to the range of phenotypic traits exhibited by perennial ryegrass, it is commercially important as both a forage and amenity (recreational/turfgrass) species. Forage varieties of L. perenne are favoured due to their quick establishment, long growing season and high dry matter yield that is highly digestible to ruminants13,14,15. In contrast, amenity varieties are selected for the short growth habit, thicker sward from the increased tillering, persistence and resilience to close cutting16,17,18,19. Whilst the phenotypic differences between these functional groups are readily apparent, a genome wide analysis of the extent of differentiation and the biological pathways or genes under selection has not been previously reported.
The creation of a publically available genotyping array for Lolium perenne with over 2,000 validated markers provided the opportunity to interrogate germplasm in new ways20. The ability to genotype individuals with the same SNPs allows the comparison of large number of individuals, accessions, populations and meta-studies. Reproducible and comparable estimates of diversity and linkage disequilibrium will also allow the identification of genomic regions that are under selection and help guide the judicious choice of genetic diversity in breeding programmes. As part of ongoing studies to characterise ecotypic variation in perennial ryegrass, Blackmore et al.20 described and quantified genetic diversity detected in a sample of European ecotypes that reflected the geographic distribution and origin of the accessions. A large East-West cline was observed together with further genetic sub-structure that is related to latitudinal differences. Extensive genetic variation was detected in unimproved ecotypes that highlighted the opportunity to exploit this variation in ryegrass breeding.
In this study we exploit the Infinium array described previously20 to quantify the levels and patterns of genetic variation in commercial cultivars of forage and amenity grasses relative to that observed in ecotypes. We also show the capture of ecotypic variation from founders into a recurrent selection programme and observe the effects of selection on haplotypes of candidate genes for water-soluble carbohydrate (WSC) within this programme.
Results
Genetic Diversity
To evaluate levels of diversity and divergence, summary statistics were calculated within different groups of germplasm. Observed heterozygosity for each cultivar group was greater than the expected heterozygosity based on HW expectations, which was similar to the ecotype accessions (Table 1, Supplementary Tables S1 and S2). Consequently the fixation index was negative across all groups. The percentages of polymorphic loci were greatest in the OA and OF groups, and comparable to the ecotypes. This had only reduced to 76% in AF and 79% in ARSP. All cultivars showed similar levels of polymorphism, however, some had percentages of polymorphic loci below 70%, such as AF3 (Aurora), AF1 (S23-1970), OA8 (Bartwingo), AA1 (AberImp) and AA2 (AberSprite) (Supplementary table S2). Of which, Aurora and S23-1970 had less than 3 individuals genotyped.
Table 1. Summary of heterozygosity and F-statistics across different variety groups.
Ho | He | F | Polymorphic loci (%) | Fis | Fit | Fst | ||
---|---|---|---|---|---|---|---|---|
European ecotypes | Mean | 0.324 | 0.291 | −0.106 | 80.28 | −0.112 | 0.135 | 0.223 |
SE | 0.005 | 0.004 | 0.011 | 0.99 | 0.002 | 0.002 | 0.001 | |
AA | Mean | 0.273 | 0.255 | −0.069 | 67.39 | −0.065 | −0.010 | 0.052 |
SE | 0.004 | 0.003 | 0.005 | 0.86 | 0.006 | 0.006 | 0.002 | |
OA | Mean | 0.314 | 0.296 | −0.060 | 82.50 | −0.061 | 0.126 | 0.176 |
SE | 0.001 | 0.001 | 0.002 | 1.93 | 0.003 | 0.003 | 0.002 | |
AF | Mean | 0.328 | 0.294 | −0.113 | 76.48 | −0.109 | 0.149 | 0.235 |
SE | 0.002 | 0.002 | 0.003 | 4.45 | 0.004 | 0.005 | 0.003 | |
(ARSP) | Mean | 0.329 | 0.305 | −0.077 | 79.47 | −0.071 | 0.091 | 0.154 |
SE | 0.003 | 0.002 | 0.004 | 2.23 | 0.005 | 0.005 | 0.002 | |
OF | Mean | 0.336 | 0.310 | −0.081 | 85.07 | −0.082 | 0.072 | 0.142 |
SE | 0.002 | 0.001 | 0.002 | 1.31 | 0.004 | 0.004 | 0.002 |
AA–Aberystwyth bred amenities, OA–Other commercial amenities, AF- Aberystwyth bred forages, ARSP–Recurrent selection programme varieties, OF–Other commercial forages. Ho = Observed Heterozygosity = No. of Hets/N, He = Expected Heterozygosity = 1-sum pi^2, F = fixation index = (he- ho)/He = 1- (he/He). Fis = (Mean He-Mean Ho)/Mean He, Fit = (Ht-Mean Ho)/Ht, Fst = (Ht-Mean He)/Ht.
An analysis of molecular variance (AMOVA) was conducted to examine the patterns of diversity between and within germplasm groups (Table 2). As expected for an outbreeding species most diversity was detected within populations although there were differences detected between the different germplasm groups. The lowest PhiPT value for the groups was seen in the AA group. AA shows little diversity, however, there are only 16 individuals representing 2 cultivars included in this group. OF has the second lowest value indicating less diversity between accessions than other groups. Despite the selective breeding program in Aberystwyth, AF showed the largest PhiPT value.
Table 2. Summary of AMOVA results between ecotypes or commercial varieties.
Group | No. of individuals | Number of accessions | Among pops (%) | Within pops (%) | PhiPT | P value |
---|---|---|---|---|---|---|
Ecotypes | 716 | 90 | 30 | 70 | 0.298 | 0.001 |
AA | 16 | 2 | 8 | 92 | 0.078 | 0.001 |
OA | 119 | 15 | 23 | 77 | 0.230 | 0.001 |
AF | 45 | 7 | 28 | 72 | 0.283 | 0.001 |
(ARSP) | 32 | 4 | 25 | 75 | 0.247 | 0.001 |
OF | 69 | 9 | 18 | 82 | 0.180 | 0.001 |
AA–Aberystwyth bred amenities, OA–Other commercial amenities, AF- Aberystwyth bred forages, ARSP–Recurrent selection programme varieties, OF–Other commercial forages. 999 pairwise populations and permutations. PhiPT = AP/(WP + AP) = AP/TOT where AP = Est. Var. Among Pops, WP = Est. Var. Within Pops.
Population structure in cultivars and ecotypes of L. perenne
In order to understand the distribution of genetic diversity contained in cultivars in comparison to the variation across European ecotypes, an unbiased principal component analysis (PCA) was performed on the allele frequency for each of the 2199 SNPs within each of the 90 sample locations (accession) in addition to the 33 cultivars (Fig. 1a). As previously reported20, the ecotypes are distributed in close alignment to their geographical origin. Together, the cultivars occupy a limited proportion of the genetic variation observed across Europe with most of the cultivars clustering in the central part of the PCA plot with forage varieties grouped apart from amenity, revealing that the genetic variation in Lolium perenne germplasm reflects their history of breeding for specific end user needs. Outliers from the central clusters were Aberystwyth’s amenity varieties, AberImp and AberSprite, and in the opposite direction on PC2 Aberystwyth’s Aurora and recurrent selection programme (ARSP) varieties (AF4-7; AberElan, AberAvon, AberDart and AberMagic). The ARSP shows progressive movement away from other forages towards 3 Italian ecotypes, IT7, 8 & 10. These ecotypes were, in fact, used in the original polycross with S23 (AF1 & 2) in the development of the ARSP (AF4-7). The breeding programme has focussed on recurrent selection for increased nutritional composition, in particular high WSC. Cultivar Aurora (AF3) is also descended from ecotypic material, CH6. A total of 21 tillers from accession CH6 were polycrossed and the progeny subjected to multiple rounds of crossing/selection for persistence, winter hardiness, early heading, yield and increased WSC, likely explaining the shift of AF3 away from its CH6 founder on Fig. 1a and towards the ARSP group, which shares these traits.
To focus further on the differences between the cultivars, PCA was performed on only the cultivar accessions along with the Italian ARSP founder ecotypes (Fig. 1b). This analysis clearly highlights the distinct genetic difference of the ARSP varieties in comparison to amenities and other forages. The top 20 markers contributing to the distribution of accessions along PC1 are listed at the top of Table 3. Although there are some uncharacterised or predicted proteins, there are 5 markers from 2 L. perenne contigs that have top BLAST hits to succinate dehydrogenase. In addition to which, markers associated to NADH dehydrogenase and hexokinase are also listed. PC2 significantly separates the Aberystwyth amenity varieties and the other commercial amenity varieties; it also discriminates between clusters of the forages and the amenities. The top 20 markers contributing the variation seen on PC2 are shown in the lower half of Table 3. Two markers which exhibit the greatest weight on PC2 are pheophorbide a chloroplast-like protein and aminoacylase-1-like protein. Two markers are associated with cell wall function; NAC secondary wall thickening promoting factor (Nst1) and cellulose synthase, are also identified in the top 20 markers (Table 3). In order to identify the markers and regions that segregate OF and OA, PCA was repeated for the cultivars (as in Fig. 1b), with the exception of the removal of the 2 AA accessions (Supplementary Fig. S1). The top 20 markers on PC2, which separated OF and OA are given in supplementary table S3. These markers have the greatest differentiation between the forage (OF) and amenity (OA) varieties. Pheophorbide a chloroplast like protein, again, had the greatest contribution to the segregation on PC2, indicating it differs between OF and OA. A number of other markers were identified including membrane proteins and stress related proteins, including sugar transporter erd6-like, alkaline/neutral invertase, snRK1-interacting protein I.
Table 3. Top 20 markers contributing segregation in Fig. 2.
Top 20 markers on PC1 (segregation of AA from OF and OA groups) | ||||
---|---|---|---|---|
Marker | LG | Position (cM) | PC1 | BLAST |
3971_540 | 3 | 49.378 | −0.046 | Putative cysteine-rich receptor-like |
9820_93 | U | U | −0.045 | NADH dehydrogenase |
6740_1395 | 4 | 55.018 | −0.045 | PP |
31101_1669 | 3 | 75.576 | 0.045 | Dihydrolipoyl dehydrogenase-like |
41898_129 | 4 | 86.787 | 0.044 | Succinate dehydrogenase |
41898_187 | U | U | −0.044 | Succinate dehydrogenase |
50733_606 | 4 | 86.698 | 0.044 | Succinate dehydrogenase |
40643_1058 | U | U | 0.044 | PP |
6714_511 | U | U | 0.043 | PP |
6714_306 | 1 | 34.656 | −0.043 | PP |
37377_605 | 1 | 44.526 | −0.043 | Farnesyl pyrophosphate synthetase |
17343_359 | U | U | 0.042 | Glyoxysomal fatty acid beta-oxidation multifunctional protein MFP-a |
41281_366 | U | U | 0.042 | Glyoxysomal fatty acid beta-oxidation multifunctional protein MFP-a-like |
6714_427 | 1 | 35.182 | 0.042 | PP |
50733_452 | U | U | 0.042 | Succinate dehydrogenase |
6740_966 | 4 | 54.881 | −0.042 | PP |
50733_371 | 4 | 87.261 | 0.042 | Succinate dehydrogenase |
6855_1933 | 1 | 36.296 | −0.041 | Hexokinase 5 |
7244_936 | U | U | −0.041 | Probable polygalacturonase-like |
41366_306 | 4 | 105.346 | −0.041 | Peptidyl-prolyl cis-trans isomerase h |
Top 20 markers on PC2 (segregation of AA from OF and OA groups) | ||||
Marker | LG | Position (cM) | PC2 | BLAST |
31527_789 | U | U | −0.057 | Pheophorbide a chloroplastic-like |
9552_740 | 7 | 42.603 | 0.056 | Aminoacylase-1-like |
13591_172 | U | U | −0.047 | Chloroplast genome |
47071_67 | 7 | 47.583 | −0.046 | NA |
52864_272 | U | U | −0.045 | Stress Response protein, Nst1 |
32698_400 | 6 | 13.684 | 0.045 | Alcohol dehydrogenase class 3 |
22583_156 | 6 | 74.525 | −0.045 | Alkaline/neutral invertase |
41908_1026 | U | U | 0.043 | Cellulose synthase catalytic subunit 12 |
43527_131 | U | U | 0.043 | PP |
34965_397 | 4 | 74.959 | −0.041 | Cysteine desulfurase chloroplastic-like |
34965_538 | U | U | 0.041 | Cysteine desulfurase chloroplastic-like |
40640_795 | U | U | 0.041 | 1-deoxy-D-xylulose 5-phosphate reductoisomerase |
40920_284 | 7 | 48.169 | −0.041 | Trigger factor-like |
34965_1344 | 4 | 59.347 | 0.040 | Cysteine desulfurase chloroplastic-like |
8982_1259 | 6 | 62 | −0.040 | Acetolactate synthase amino acid binding protein |
13979_375 | U | U | 0.040 | Cyclin-like f-box |
32206_1218 | 7 | 23.072 | −0.040 | Enolase 1-like |
53366_177 | U | U | −0.040 | Cyclin-like f-box |
7528_1208 | 7 | 43.297 | 0.039 | Auxin response factor 7b |
6762_1533 | U | U | −0.039 | 2-oxoglutarate/malate translocator |
PP–predicted protein. U–Unmapped. NA- not available.
Genomic regions under selection
In order to identify regions of the genome that have been under directional selection, a consensus linkage map was constructed from three distinct mapping populations that were genotyped with the Infinium array. Each mapping population generated its own linkage map with 1255, 1475 and 745 markers for the amenity x forage, AberMagic x Aurora and a F2 populations, respectively. Upon combining these three maps, 1386 markers of the 2199 validated markers were included in an integrated consensus map (supplementary Fig S2; Table 4). The markers were distributed evenly across all 7 linkage groups (LG), with the exception of LG5 where only 109 markers, against an average of 198 per linkage group, were assigned (Table 4). Across all linkage groups, 98% of the markers were less than 4cM apart.
Table 4. Summary of consensus genetic linkage map.
Linkage Group | Number of mapped markers | LG size (cM) | Average distance between markers |
---|---|---|---|
1 | 171 | 91.918 | 0.54 |
2 | 197 | 128.305 | 0.65 |
3 | 199 | 123.870 | 0.50 |
4 | 279 | 131.229 | 0.47 |
5 | 109 | 89.227 | 0.78 |
6 | 208 | 114.036 | 0.52 |
7 | 223 | 105.950 | 0.46 |
Total | 1386 | 784.535 | 0.54 |
Genetically mapped markers were used to determine the extent of linkage disequilibrium (LD) in natural Lolium perenne populations across Europe (Fig. 2a). LD across the genome (all linkage groups combined) was seen to rapidly breakdown in ecotypes (LOWESS curve did not extend up to r2 = 0.2). The genetic distance was slightly greater in commercial varieties (Fig. 2b). To focus further on the effect of a recurrent selection on a breeding programme, LD in ARSP was also plotted (Fig. 2c). ARSP included 4 forage cultivars (AberElan, AberAvon, AberDart, AberMagic) that are part of the recurrent selection programme with a focus on increasing WSC content. The greatest amount of LD was seen in this group, compared to varieties (Fig. 2b) and ecotypes (Fig. 2a). However, the LOWESS curve remained low and did not extend up to r2 = 0.2, highlighting that some regions have much greater levels of LD, but in general LD remains very low across the genome, as would be expected for an outbreeding, SI species. Examining LD for each LG found slightly elevated LD in LG1, 2, 4, 6 and 7.
In order to genetically locate regions under selection for functional use (amenity or forage), the top 20 markers with the highest loading in the PCA plot (Fig. 1b) are identified on the consensus linkage map (Fig. 3). Strikingly, the markers contributing to the differentiation of ARSP from OA and OF are located on LG1, 3 and 4, with a cluster of markers on LG1 and 4. Markers with the greatest loading on PC2 are shown in tables 3 and supplementary Table 3 and are localised on LG6 and 7, identifying regions discriminating between amenity and forage groups.
Of particular interest is the cluster of 3 SNPs at 86cM on LG4 from 2 different contigs that both BLAST to succinate dehydrogenase. These 2 contigs have a total of 5 markers on the array, with 2 currently unmapped. These 5 markers are all in the top 20 markers contributing to the loading on PC1, and therefore differentiating ARSP from OF and OA. SNP- based haplotype analysis was performed on these 5 markers for the ecotypes, Italian founders of the ARSP and other groups of interest (Fig. 4). This identified 12 haplotypes which were all present in the ecotypes (ecotypes + founders). Haplotype “12111” had a disproportionately high frequency in the founders, compared to the other ecotypes and other commercial varieties (OA and OF). The founders were used in conjunction with S23 (AF1-2) and recurrently selected in ARSP with an emphasis for increased WSC. Haplotype “12111” has been preferentially selected for in the ARSP, with the frequency of this haplotype increased to >90%, compared to ~31% in ecotypes (excluding the founders).
Discussion
This study of natural variation in L. perenne is the largest, to date, in terms of individuals genotyped with a comprehensive, genomewide array of 2199 SNPs. It therefore provides insight into the extent and distribution of genetic diversity available in European ecotypes of Lolium perenne and how this variation has been incorporated and exploited in breeding programmes. As the most economically and agriculturally important temperate forage crop, understanding patterns and distribution of genetic variation will help breeders respond to the new challenges of sustainable intensification21.
The European ecotype sample previously described20 enabled a comparison with commercial forage and amenity synthetic varieties. Observed heterozygosity (Ho) was previously reported to be greater than expected heterozygosity (He) in all ecotypes20. The same observation was made in varieties (Supplementary Table S4). Explanation due to technical bias was excluded by comparison of observed heterozygote numbers in a biparental mapping population where both parents had been genotyped, and therefore the expected number of heterozygotes could be calculated. Variation of observed heterozygotes around the expected values was seen in the markers, but no deviation from 0 was found as an average across all the markers (Supplementary Table S4). Previously, when observed only in the ecotypes, this was proposed to result from polycrossing within accession to provide seed for germplasm bank storage at Aberystwyth, and the influence of self-incompatibility (SI) loci under these conditions20. Commercial cultivars are produced from a number of parental genotypes that may vary from 4 to hundreds22,23,24,25, however the observed excess of heterozygosity remains fairly constant across all accessions. As far as we know, this appears to be the first documented observation of this increase in heterozygosity in Lolium perenne. The effect at individual loci is non-significant and it is only due to the large number of markers and populations studied that the general effect is visible. We propose this effect arises from the action of SI and warrants further investigation.
Although the commercial varieties together capture a reasonable range of the genetic diversity observed across Europe, there was a surprising “geographic” divide seen between amenity and forage varieties genotypes. The amenities captured a greater expanse of the European ecotype diversity, with the forages forming a tight cluster on the PCA plot (Fig. 1a). This figure highlights ecotypic diversity that remains uncaptured by commercial breeding programmes. While this might be because these ecotypes lack key traits for amenity or forage use, this diversity may equally represent novel genetic resources for inclusion in present or future breeding programmes. LD analysis shows no significant increase in the magnitude of LD within cultivated ryegrass versus ecotypic material, again confirming that the genetic diversity within breeding programmes has not been unduly affected.
The ARSP genepool is differentiated from the other commercial forages, demonstrating the power of directional selection with a focus on increasing WSC. An individual from each of the ecotype accessions IT7, IT8 and IT10 were originally polycrossed with S23 and Ba9633 between 1978–1980. Recurrent selection of this population has led to a number of award-winning varieties, renowned for their increased WSC14,26. Genetic variation for WSC has previously been reported27 and has allowed the continued increase in WSC, from an average of 205 g/KG dry matter in AberDart to 237 g/KG in AberMagic from 7 cuts over 5 years. The benefits of increasing WSC have been shown to increase animal productivity and reduce nitrogen excretion28. PCA showing only the varieties highlights the progression of these cultivars away from the other forages on PC1 (Fig. 1b). The SNP markers contributing to the greatest difference in genetic variation show movement toward allele fixation in the ARSP, culminating in AberMagic (AF7). A number of interesting BLAST hits were found for the contigs in which the markers resided (Table 3). A common function of most of these candidates is their role in a stress response in plants, as well as energy metabolism. Five SNPs in 2 different contigs matched succinate dehydrogenase, which is associated with photosynthesis and stress responses in Arabidopsis thaliana and Oryza sativa29,30. NADH dehydrogenase has links with oxidative stress, increased growth and biomass31,32. Hexokinase 5 has been reported to be involved in fructan mobilisation in Lolium perenne33. Dihydrolipoyl dehydrogenase-like protein also has a role in photosynthesis and photorespiration34. Ryegrasses store their energy as fructans, and thus, during periods of stress would draw on these reserves until more favourable conditions return. Due to the similarity in the function of these markers’ BLAST matches, it is proposed that pathways in which energy metabolism and response to stress are controlled in the ARSP plants differ to other varieties, both forage and amenity type. Of the markers that had been assigned consensus map positions, two clusters of markers were observed. Three mapped markers (across 2 contigs) for succinate dehydrogenase grouped ~86cM on LG4, suggesting that these contigs are part of the same gene or two tightly linked gene copies. Haplotype construction from these markers highlighted the unique increased frequency of haplotype “12111” in the 3 Italian ecotypes that were used as founders of the ARSP population, along with S23. This haplotype has been favourably selected in the recurrent breeding programme for increased WSC to now account for >90% of the haplotype frequency. The marker for hexokinase (contig6855) and 2 markers in contig 6714 also grouped together at 35cM on LG1. Turner et al.27 have previously reported QTL for WSC on LG1 and LG6. These are not the same regions identified in this study and may reflect the polygenic nature of WSC and the high environmental component contributing to this complex trait. As might be expected, LD increases in the ARSP compared to the ecotypes and other varieties due to the recurrent nature of the breeding programme, but remains low compared to inbreeding species such as barley35.
Amenity varieties are selected for their suitability for lawns, sports pitches and recreation, requiring a tough sward that thrives on maintenance at a short sward height. This contrasts to forages that need to be highly digestible to animals and have rapid growth yields for grazing or cutting. The contrasting phenotypic traits and the genetic control of these can be dissected by the use of genetic markers. The differentiation between forage and amenities in Fig. 1b can also be used to begin to identify markers that may be associated with traits that differentiate both functional groups (Table 3). However, this is confounded on PC2 by the presence of amenity cultivars bred in Aberystwyth and those of other commercial breeders. There are some striking differences in allele frequencies seen between the OA and AA groups, although the number of accessions included in the OA group greatly outnumbers that of the AA (15 vs 2). As with the ARSP, contributing markers (where mapped) formed two large clusters (~74cM on LG6 and ~46cM on LG7). Two markers contributed a greater weighting to PC2 than others. Pheophorbide A chloroplast-like has been associated with chlorophyll breakdown and senescence in Arabidopsis36. Prolonging the colour of varieties used for amenity purposes would be more aesthetically desirable to the turf industry37,38. In contrast, aminoacylase has been associated to Phytophthora infestans resistance in Nicotiana39: it is known that AberImp and AberSprite are susceptible to crown rust infection (D. Thorogood, pers. comm). Two other markers, NAC secondary wall thickening promoting factor 1 and cellulose synthase were also identified in the top 8 markers differentiating OA, AA and OF. This is unsurprising given the differences in cell wall robustness required from forages and amenity varieties. Forages need to be easily digested in contrast to amenities that need to tolerate frequent trampling.
In summary, this study has allowed quantification of genetic variation in ecotypes and cultivars of L. perenne and the identification of key regions of the genome that are strongly associated with the differentiation of forage and amenity forms. In addition candidate genes implicated in the control of WSC accumulation have been identified based on a combination of multidimensional and haplotype analysis of genetic variation in ecotypes and commercial breeding germplasm, illustrating the power of crop diversity to both improve nutritional composition and the underlying genetic basis of WSC in ryegrass.
Methods
Plant material
Leaf tissue from 249 individuals from 33 accessions of commercial varieties of Lolium perenne was collected. These represented 9 accessions from commercial forage varieties (OF) and 7 accessions from Aberystwyth University’s forage breeding programme (AF), in addition to 15 accessions of commercial amenity varieties (OA) and 2 accessions of Aberystwyth amenity varieties (AA) (Supplementary Table 5). DNA was extracted using QIAGEN 96 plant tissue extraction kit.
For a more accurate representation of the effect of a recurrent selection breeding programme on the genetic diversity contained within a cultivar, the AF group was subsetted to Aberystwyth Recurrent Selection Programme (ARSP). The ARSP group contains the 4 most recent forage varieties generated by the programme (AF4-7; Supplementary Table 5) genotyped and recurrently selected with emphasis on increasing WSC. AF3 is also a high sugar variety (Aurora), however, this is not part of the same recurrent selection breeding program as AF4-AF7.
In addition to the cultivars, 716 individual Lolium perenne ecotypes as previously described20 were also included in this study. Briefly, this included 8 individuals from 90 different geographic locations across Europe (Supplementary Table S1).
In order to generate a robust consensus linkage map, three mapping populations were genotyped. The first population was a back-cross mapping family of 162 individuals was derived from an initial cross between contrasting amenity-type (ex cv AberImp) and forage-type (accession Ba12142 ex Cardigan Island [Wales, UK]) ecotype collection (grid ref 52.1167 -4.6833) genotypes, followed by backcrossing of a single F1 genotype to the amenity type parent40. The second population involved 192 F1 progeny from a cross between Aurora and AberMagic41. A F2 mapping population of 96 individuals derived from a single hybrid self-pollinating plant obtained from crossing cultivars ‘Perma’ and ‘Aurora’ formed the third mapping population42.
Genotyping
All cultivars (n = 249), ecotypes (n = 716) and 3 mapping populations (n = 450), were genotyped using our custom Illumina Infinium iSelect array across 3425 SNPs. The cluster file trained using the diverse European ecotype panel (as reported and verified in20) was applied to the commercial varieties and mapping populations generating genotype calls for 2501 SNPs. Markers with more than 10% missing data (n = 4) and/or a minor allele frequency of less than 5% (n = 225) were excluded. In addition to which, markers which had incorrect heritability in the AberMagic x Aurora mapping population (n = 43) or a probability of less than 0.5 for observed heterozygosity excess in each of the accessions (n = 34, GenePop43) were also excluded to minimise technical genotyping errors. In order to verify the technical robustness of the array, the expected number of heterozygotes based on the parental genotypes for the AberMagic x Aurora population were calculated and compared to the observed values. No bias was observed across all markers (Supplementary Table S4). Following these exclusion parameters that had also been applied in Blackmore et al.20, a final validated marker set of 2199 SNPs spanning 1615 contigs were used for analysis.
Genetic diversity analysis
Diversity measures were calculated within each of the accessions using GenAlEx44 using accession as a population (8 individuals per accession) for the ecotypes and varieties. A summary of values for the varieties was calculated based on the commercial type; amenity or forage. Allele frequency for each marker within an accession was calculated, with up to 8 individuals from each accession used as detailed in Blackmore et al.20. Principal component analysis (PCA) was performed using the R package. Haplotype frequency was performed using the EM algorithm to estimate maximum likelihood frequencies at the haplotype level in Arlequin 3.5.2.145.
Construction of a genetic linkage map for Lolium perenne
From the genotyping data of the three individual mapping families, genetic linkage maps were created using JoinMap v4.046. Of the 2199 SNP markers, 1161, 1275 and 691 informative markers were mapped in the Amenity x Forage, AberMagic x Aurora and F2 mapping populations respectively. LOD thresholds of 6.0 and 5.0 were able to separate seven distinctive groups representing the seven chromosomes of Lolium perenne in the Amenity x Forage and F2 mapping populations. In the AberMagic x Aurora population LOD threshold of 4.0 was able to separate all but two of the linkage groups. A LOD threshold of 8.0 was required to separate out linkage groups 2 and 4. Groups were assigned to linkage groups that align to those determined for the seven Hordeum vulgare chromosomes47 and are standardised for all members of the Triticeae family. This was done by BLASTing a small number of contig sequences from markers on each linkage group against Brachypodium and rice genomes using the Gramene database48 and assigning linkage groups based on comparative genomics of the Triticeae family with these model species (see for example Pfeifer et al.49). Once assigned to groups, markers with identical genotype scores were excluded and map order was determined using the weighted least squares (linear regression) method50 using marker linkages with a recombination threshold of 0.4 and a LOD threshold of 1.0 with map distances calculated from recombination frequencies using Haldane’s mapping function. Three rounds of mapping were employed. An integrated map was then produced by combining the linkage groups of the three maps using the same recombination frequency, LOD score threshold and mapping functions as used for mapping the separate mapping families. Text-based map files were exported to the program MapChart51 for production of map images.
Linkage Disequilibrium
Linkage disequilibrium (LD) was calculated for both the ecotypes and the varieties using PopGen (1.0–3) package in R project and plotted against the genetic map distances between markers as generated from the consensus linkage map. LD was calculated for each linkage group, and then combined to produce genome wide LD plots. A LOWESS curve was included in each plot. This was repeated for the ecotypes, varieties (all cultivars) and ARSP.
Additional Information
How to cite this article: Blackmore, T. et al. Germplasm dynamics: the role of ecotypic diversity in shaping the patterns of genetic variation in Lolium perenne. Sci. Rep. 6, 22603; doi: 10.1038/srep22603 (2016).
Supplementary Material
Acknowledgments
This work was conducted with the financial support of strategic funding from the BBSRC. We would like to thank Ianto Thomas for detailed records and maintenance of the seed bank for ecotypic populations, John Harper and Dagmara Gasior for maintenance of the plants and Rattan Yadav for providing tissue from the AberMagic x Aurora mapping population.
Footnotes
IBERS receives a mixture of public and private funding for the breeding of perennial ryegrass varieties, some of which are included in this paper. IBERS is committed to the concept of “public good plant breeding”.
Author Contributions T.B. conducted the genotyping, data analysis and bulk of manuscript writing. M.H. designed the Infinium assay and assisted with manuscript generation, data analysis and experimental design. R.M. provided advice on genetic diversity and structure. D.T. and L.S. constructed the genetic maps and consensus map. W.P. assisted with experimental design and manuscript production.
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