Souza Et Al., 2018
Souza Et Al., 2018
0.02 for wild populations), a large number of evenly spaced SNPs would be needed to
perform genome-wide association studies in rubber tree, and the wilder the genotypes
used, the more difficult the mapping saturation.
Keywords: linkage mapping, genetic diversity, population structure, non-random association, genome-wide
association study, Hevea
prior to this publication (Souza et al., 2013; Rosa et al., Population Structure and Genetic
unpublished). Genomic DNA was extracted from leaves using Diversity
the DNeasy
Plant Mini Kit (QIAGEN, Germany) according
R
which 350,965 SNPs (germplasm) and 66,453 SNPs (mapping by a drastic decline starting at K = 3, suggesting that the
population) were biallelic. After excluding markers showing (1) optimal K value was 2. The assignment results for K = 2 showed
more than 20% missing data or (2) a MAF ≤ 0.05, the whole that some of the sampled individuals exhibited admixtures
dataset was reduced to 77,660 and 21,283 SNPs in the germplasm from two gene pools (Figure 2A): group 1 (red bars) mainly
and mapping populations, respectively. The SNP frequencies consisted of accessions originating from the Mato Grosso and
were one biallelic SNP every 20.7 kb for the mapping population cultivated genotypes, and group 2 (green bars) consisted entirely
and every 3.9 kb for the germplasm. of wild accessions from Amazonas, Rondônia, Para, and Acre
Sequence data are deposited under EMBL-EBI accession (identified as IS – Ilha Solteira). Twenty-one accessions showing
PRJEB26962. a membership probability (Q value) below 0.70 were defined as
admixed and were removed from subsequent analyses.
Saturation of the Linkage Map With SNPs As a second analysis of differentiation, we employed PCoA
From 21,283 SNPs, a total of 14,852 markers were selected based on a similarity matrix that explained 22.8 and 16.7%
after applying the chi-square test (P ≤ 0.05), which revealed of the genetic variation with the first and second PCoA
segregation ratios of 1:2:1 and 1:1. Markers exhibiting statistically axes, respectively. Plotting the two first PCoA axes separated
significant segregation distortion were excluded from further the germplasm into two clusters, though some overlap was
analysis to obtain accurate genetic linkage maps. The data present between the wild germplasms and cultivated genotypes
analyses were performed using SNPs with a maximum of 5% (Figure 2). On the first axis, most of the breeding genotypes were
missing data, resulting in a linkage map with 1,062 markers separated from the other genotypes. On the second axis, the wild
presenting 348 SSR markers (Souza et al., 2013; Mantello, 2014), germplasm samples were clustered together, but some accessions
576 SNPs from GBS (Supplementary Table S2) and 138 SNPs from the Amazon were isolated in their own subdivision.
markers genotyped using the Sequenom MassARRAY
platform R
(AgenaBio, San Diego, CA, United States) and the Fluidigm
R Evaluation of LD
platform (South San Francisco, CA, United States), developed Based on population genetic structure, accessions could be
from de novo transcriptome assemblies (Mantello et al., 2014; divided into two distinct groups (cultivated and wild group)
Salgado et al., 2014) and from EST full-length libraries (Silva et al., (Figure 2), and pairwise LD estimates were performed within the
2014). gene pool of each of these groups. To visualize LD throughout
The genetic map was organized according to the numbers the genome, heat maps were produced based on pairwise r2
obtained from the map previously developed by Rosa et al. estimates, and corresponding p-values were calculated using
(unpublished). Eleven markers were removed after data diagnosis permutations for all marker pairs (Supplementary Figure S1).
using heat map graphs, thereby permitting the visualization of These heat maps were employed to identify variations in LD
the recombination fraction and LOD scores from markers, to between the cultivated and wild rubber tree germplasm groups.
group the SNPs in the LGs without changing the order of the base In 16,025 pairwise combinations, we identified 186 (1.2%) and
map. Only LG18 was further divided into subgroups “A” and “B” 592 (3.7%) statistically significant associations that were in LD
(Figure 1). (P < 0.05) in the cultivated and wild germplasms, respectively. Of
Thus, a genetic map was generated spanning a cumulative these significant associations, 78 and 64 were intrachromosomal
length of 4,693 cM (Figure 1), distributed among all the in the cultivated and wild germplasms, respectively, accounting
chromosomes. The LGs ranged from 23.8 cM (LG18B) for 0.5 and 0.4% of the total possible intrachromosomal
(Supplementary Table S3) with 14 markers to the largest group correlations. Among the unlinked loci, the proportions of LD
with 404.6 cM (LG10) with 85 markers (of which 78 were from were 0.7 and 3.3% for the cultivated and wild germplasms,
GBS), and the average interval size between two adjacent markers respectively. In both clusters, an uneven distribution of LD
was 4.4 cM. among the 18 chromosomes was observed.
The maximum gap size was 36.4 cM (LG11), which was The strength of LD (P < 0.05) was very different between
maintained from the previous map. Furthermore, some regions two clusters, as reflected by the mean r2 values of 0.49 and 0.02
could not be sampled using the selected restriction enzyme; in obtained for the cultivated and wild germplasms, respectively.
LG16, for example, only two GBS-based markers were added. The 346 SNPs that were localized in the integrated map were
used for the estimation of LD decay among the different LGs.
LD decay was estimated across the germplasms and was found
Genetic Relationships Among to be more pronounced in the wild germplasms, with the range
Populations being dependent on the chromosome group (Supplementary
The germplasm collection was selected in a prior work by de Figure S2). Using a fixed baseline r2 value of 0.1 for the wild
Souza et al. (2015) examining the population structure with SSR germplasm, LD decay ranged from 2.3 cM (LG9) to 11.4 cM
markers. To confirm the population structure of the sample of (LG17). In contrast, in the cultivated accessions, this decay was
selected individuals, we performed a new analysis as performed slower, ranging from 4.3 cM (LG8) to 50 cM (LG17), with
with the SNPs from GBS genotyping. Only mapped SNPs that average values of 5.6 cM and 19.6 cM for the wild and cultivated
were common in the germplasm collection were used. Clustering germplasms, respectively (Figure 3). The patterns of LD can also
inference performed with K values ranging from 1 to 10 showed be visualized across the genome from the diagonal of the heat
that the model likelihood increased steeply at K = 2, followed maps (Supplementary Figure S1).
FIGURE 1 | Linkage map of the rubber tree. Markers in blue represent SNPs obtained using the genotyping-by-sequencing technique, and markers in black were
obtained from the previous map (Rosa et al., unpublished).
FIGURE 2 | Estimated genetic structure of the wild population and breeding population of rubber tree based on PCoA (A) and STRUCTURE analysis
(B). All analyses are based on the genetic variability of 438 SNP loci.
FIGURE 3 | Decay of LD (r 2 ) as a function of genetic distance (cM) between pairs of loci on all chromosomes. Only r 2 values with P < 0.05 are shown.
genome is challenging, owing in part to the presence of highly Tang et al. (2016) to map the SNPs. The SNPs positioned on the
repetitive DNA sequences, which introduce ambiguity during map are named in reference to the location of alignment with the
genome reconstruction. We used the genome published by genome.
Repetitive regions account for 71% of the Hevea genome and differences in mapping strategies, the mapping software and
(Tang et al., 2016), posing a major challenge for the de novo the ratio between the number of markers and the population size
assembly, particularly when exclusively short-read data are used. (Knox and Ellis, 2002).
This phenomenon might explain the prevalence of tags that Genetic mapping of the population (PR255 × PB217)
aligned to more than one unique region (59.78% to the mapping was initiated in the first publication by Souza et al. (2013)
population and 67.38% to the germplasm) (Tang et al., 2016). using microsatellite markers. These first LGs were organized
Based on the properties of the reference genome (characterized according to the numbers obtained from the map previously
by a great accumulation of repetitive sequences, primarily in developed by Lespinasse et al. (2000), and information from
heterochromatic regions) (Rahman et al., 2013), the restriction other maps (unpublished) consisting of microsatellites in
enzyme EcoT22I was selected because it is partially sensitive to common was used to identify syntenic markers. Subsequently,
methylation and rarely cuts retrotransposons. the PR255 ×PB217 mapping population was saturated with
The frequency of nucleotide substitutions was five times SSR markers and 243 SNPs obtained from platforms such as
higher in the wild (3.9 kb) than in the cultivated (20.7 kb) Sequenom MassARRAY iPLEX technology and KASP genotyping
germplasm sequences. One explanation for this finding is that (Rosa et al., unpublished). The SNPs from GBS used to construct
selection in cultivated breeding programs acts to reduce diversity the new genetic linkage map contributed to reducing the average
and alter allele frequencies in the DNA sequence. Depending interval between two adjacent markers (4.4 cM versus 7.4 cM).
on how LD is increased surrounding these loci; the effects of However, the marker density remained lower than that of the
such a selection may not extend sufficiently far to affect the first rubber tree map (Lespinasse et al., 2000), which presented
overall genome diversity. Rubber tree breeders have had to one marker every 3 or 0.89 cM according to Pootakham et al.
develop cultivars that are appropriate for the specific temperature (2015). LG11 displayed the maximum gap size (36.4 cM), which
and humidity conditions encountered in different cultivation may have been caused by sections of the genome that were
areas, along with various biotic and abiotic stress resistance identical among the parental genotypes and thus an absence
factors. High-density SNPs are also common in non-genetic of polymorphisms, or by recombination hotspots. Large gaps
regions where there is no selection pressure, and the abundance exhibiting a low degree of polymorphisms have also been
of these SNPs will be very useful for future assessments of reported by Shearman et al. (2015).
breeding populations. The high diversity of SNPs is characteristic Genetic maps are important tools not only for QTL mapping
of outbreeding trees; in other studies examining rubber tree, but also for anchoring genome assembly scaffolds into pseudo-
Pootakham et al. (2011) previously identified a frequency of one chromosomes. The draft genome of H. brasiliensis has been
SNP every 1.5 kb, while Pootakham et al. (2015) observed a reported to be highly heterozygous, with 71% of the genome
frequency of one SNP every 308 nucleotides. length comprising repeats (Tang et al., 2016). A total of 21,283
GBS does not require complete genome sequencing; only biallelic SNPs were identified, potentially aligning with 1,926
a targeted sequencing approach is necessary. Due to its high- scaffolds, corresponding to 26% of the total scaffolds of the
throughput efficiency, GBS has been used for SNP identification genome used. However, only 3% of these scaffolds were anchored
and mapping in many plant species (Poland et al., 2012; Rabbi to LGs due to the relatively fragmented scaffold sequences and
et al., 2014; Bekele et al., 2018; Rimbert et al., 2018). In rubber the usage of an insufficient genetic map to anchor the scaffolds.
tree, most of the genetic linkage maps constructed to date Thus, it is important to develop higher-quality genetic maps to
have employed molecular markers such as RFLPs and AFLPs help improve the scaffold anchoring ratio of future rubber tree
(Lespinasse et al., 2000) or microsatellites (SSRs) (Le Guen et al., genome assemblies.
2011; Triwitayakorn et al., 2011; Souza et al., 2013). However, Progress in the development of new molecular markers and
GBS was employed for linkage map construction in rubber tree genetic linkage maps is important for genetic improvement
very recently (Pootakham et al., 2015; Shearman et al., 2015). in rubber tree breeding programs. Despite the economic and
In the present study, we utilized the GBS platform to sequence ecological importance of this crop, restricted genomic resources
a PR255 × PB217 mapping population that was previously are available for rubber tree. Sequencing of the studied family
saturated with SSR markers and SNPs obtained from other allowed the identification and genotyping of many markers in
specific platforms (Souza et al., 2013; Rosa et al., unpublished). an efficient and cost-effective way. The linkage mapping analysis
The linkage map constructed in the present study exhibits resulted in a number of LGs corresponding to the rubber tree
a regular marker distribution. However, the cumulative genetic haploid chromosome number (n = 18) (Ong, 1975; Lespinasse
map is significantly longer (4,693 cM) than would be expected et al., 2000), and the development of GBS methods and genetic
for maps derived from other mapping populations that have maps represents an important advancement of the genomics tools
presented a lower resolution; for example, a map of 2,052 cM available for these crops, which currently lack a good reference
(Pootakham et al., 2015) was obtained using only SNPs, and genome sequence.
a map of 2,441 cM (Le Guen et al., 2011) was obtained using Diversity analyses were performed in a previous work that
both SSRs and AFLPs. Such expansions of the rubber tree included the entire collection of rubber germplasm, analyzing
genetic linkage map have also reported previously (4,160 cM, 1,117 genotypes with 13 microsatellite markers (de Souza et al.,
Shearman et al., 2015). Several factors may be responsible for 2015), and showed a mean observed heterozygosity (Ho) of
this phenomenon, including the numbers and types of mapped 0.64 and higher genetic diversity (He) than Ho in all cases.
loci, the genetic constitution of different mapping populations Wright’s fixation index (F) values were positive, with a mean of
0.16 obtained for the accessions overall. Among a total of 408 wild germplasm (0.02), corroborating the results of Chanroj
observed alleles, 89 represented unique alleles to different groups et al. (2017), who suggested that these results were caused
of accessions, demonstrating the high level of heterogeneity in by high gene flow in the wild Amazonian population. The
these genotypes. To confirm the population structure of the breeding accessions exhibited a notably higher level of LD,
sample of selected individuals based on the work of de Souza suggesting less genetic diversity in this subdivision, perhaps
et al. (2015), a new analysis of the population structure was because of the constraint of genetic variability employed
conducted with SNPs obtained from GBS genotyping. The 1K in breeding programs due to the recurrent process of
values obtained in this study indicated that the rubber tree selection. The low LD detected in the wild germplasm
germplasm could be divided into two groups and showed that in this study was expected because perennial outcrossing
some of the sampled individuals exhibited admixtures from two tree species display a high effective recombination rate,
gene pools, which was also confirmed by plotting the two first which leads to the rapid decay of LD (Krutovsky and Neale,
PCoA axes. 2005).
Recent work using SSR markers has revealed similar results The higher LD level detected in the cultivated group may
to those obtained using SNPs from GBS. For example, Le Guen have been influenced by the partly identical-by-descent of these
et al. (2009) demonstrated a separation between the Acre and genotypes from a limited number of founders of the breeding
Rondônia groups and the Mato Grosso group. One possible programs, with only a few generations between them. Thus,
reason for this separation is that the wild accessions are from many longer pieces of chromosomes have not had time to
geographically distant populations that are not connected by undergo disruptions. Domesticated crop cultivars necessarily
hydrographic networks (Le Guen et al., 2009; Chanroj et al., represent a subset of the genetic variation found in their wild
2017), whereas most of the Wickham clones were collected from ancestors, and the process of crop domestication is responsible
regions that are geographically closer to the Mato Grosso and the for genetic bottlenecks (McCouch, 2004). Although rubber
Tapajós river, enabling rubber seeds to flow from one region to tree breeding programs are very recent, the differences in
another via the river. de Souza et al. (2015) reported a difference LD patterns detected between cultivated and wild germplasms
in genotypes between the two groups, which are in different suggest that plant breeders may have selected for separate
river basins, thus separating the genotypes in the cultivated combinations of genes during the breeding process. Moreover,
and wild groups. Within the group of cultivated genotypes selection for high latex yields and the extensive use of
denoted as Mato Grosso and Wickhan, genotypes collected from particular clones as parents in rubber breeding programs
Mato Grosso were genetically close to genotypes used to initiate have further reduced the genetic diversity of commercial
the Asian breeding programs, denoted Wickhan genotypes in rubber germplasm (Priyadarshan, 2016), which may also
this article. These genotypes were collected by Henry Wickhan affect LD.
in 1976 in the same basin from which the genotypes from LD decay was estimated at 25.7 cM within cultivated
Mato Grosso were sampled (Gonçalves et al., 1990). The results and 5.7 cM within wild germplasm, and significant inter-
obtained by de Souza et al. (2015) corroborate the seminal study chromosomal LD was identified within cultivated in contrast
by Le Guen et al. (2009). to wild germplasm. The distances of LD decay between the
Population genetic structure is a principal factor influencing two groups were most different in LGs 3, 5, 7, 10, and 11,
the generation of false positives and the success of the association suggesting that these chromosomes may carry more genes
or LD mapping (Gupta et al., 2005). These 368 rubber tree related to agronomic traits that have been selected via organized
accessions could be divided into two distinct groups based on breeding of this crop. In previous studies involving Amazonian
population genetic structure: cultivated and wild germplasm. accessions of rubber tree, Chanroj et al. (2017) revealed an
The investigation of LD decay versus genetic distance based on LD decay of more than 0.5–6 cM and suggested that LD
markers is not possible without prior information regarding the estimates were significantly influenced by physical distance,
positions of markers in the genome. Since the information on the with LD decay greater than 2 kbp being observed in the
rubber tree genome is still inaccurate regarding these positions, widespread Amazonian population. These authors showed that
we employed the existing genetic map of the PR255 × PB217 LD decay over genetic distance was different for the 18 different
population to identify the positions of some SNPs and, thus, chromosomes, possibly because of the different recombination
enable a more accurate study of LD decay. rates of the 18 chromosomes. Rapid LD decay has been reported
LD analysis with the mapped SNPs revealed that LD for many other outcrossing tree species, such as Populus nigra, in
varied along the chromosomes, with regions of high LD being which a decay of r2 with distance in the CAD4 gene was observed
interspersed with regions of low LD (Supplementary Figure S1). at approximately 16 bp (Marroni et al., 2011). In Eucalyptus
LD estimation is possible without the positions of molecular globulus, candidate genes for wood quality were analyzed using
markers along the genome and was indeed performed in this SNPs, and LD was estimated to decay rapidly (Thavamanikumar
study. However, these positions are crucial if one is interested et al., 2011). Most LD estimation studies conducted in tree
in determining the decay or extension of LD in relation to the species are based on candidate genes (Krutovsky and Neale,
genetic distance, regardless of by chromosome. 2005).
The average r2 values were found to be very different when LD mapping relies on germplasm samples and, as such,
the two detected groups were compared. This measurement does not require the development of experimental crosses with
was higher in the breeding germplasm (0.49) than in the specific genetic backgrounds, and thus ease of use is an obvious
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Genetic Diversity and Erosion in Plants: Case Histories, eds M. R. Ahuja and
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Priyadarshan, P. M., and Goncalves, P. S. (2003). Hevea gene pool for breeding. open-access article distributed under the terms of the Creative Commons Attribution
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geminiviruses in cassava using genotyping-by-sequencing and its implications practice. No use, distribution or reproduction is permitted which does not comply
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