Skip to main content

ORIGINAL RESEARCH article

Front. Plant Sci., 01 March 2018
Sec. Evolutionary and Population Genetics

Development and Application of Genomic Resources in an Endangered Palaeoendemic Tree, Parrotia subaequalis (Hamamelidaceae) From Eastern China

  • 1College of Life Sciences, Nanjing University, Nanjing, China
  • 2Key Laboratory of Conservation Biology for Endangered Wildlife of the Ministry of Education, College of Life Sciences, Zhejiang University, Hangzhou, China
  • 3College of Life Sciences, Tarim University, Alaer, China
  • 4Asian Natural Environmental Science Center, The University of Tokyo, Tokyo, Japan

Parrotia subaequalis is an endangered palaeoendemic tree from disjunct montane sites in eastern China. Due to the lack of effective genomic resources, the genetic diversity and population structure of this endangered species are not clearly understood. In this study, we conducted paired-end shotgun sequencing (2 × 125 bp) of genomic DNA for two individuals of P. subaequalis on the Illumina HiSeq platform. Based on the resulting sequences, we have successfully assembled the complete chloroplast genome of P. subaequalis, as well as identified the polymorphic chloroplast microsatellites (cpSSRs), nuclear microsatellites (nSSRs) and mutational hotspots of chloroplast. Ten polymorphic cpSSR loci and 12 polymorphic nSSR loci were used to genotype 96 individuals of P. subaequalis from six populations to estimate genetic diversity and population structure. Our results revealed that P. subaequalis exhibited abundant genetic diversity (e.g., cpSSRs: Hcp = 0.862; nSSRs: HT = 0.559) and high genetic differentiation (e.g., cpSSRs: RST = 0.652; nSSRs: RST = 0.331), and characterized by a low pollen-to-seed migration ratio (r ≈ 1.78). These genetic patterns are attributable to its long evolutionary histories and low levels of contemporary inter-population gene flow by pollen and seed. In addition, lack of isolation-by-distance pattern and strong population genetic structuring in both marker systems, suggests that long-term isolation and/or habitat fragmentation as well as genetic drift may have also contributed to the geographic differentiation of P. subaequalis. Therefore, long-term habitat protection is the most important methods to prevent further loss of genetic variation and a decrease in effective population size. Furthermore, both cpSSRs and nSSRs revealed that P. subaequalis populations consisted of three genetic clusters, which should be considered as separated conservation units.

Introduction

The genus Parrotia C. A. Mey. (Hamamelidaceae) contains just two extant species, Parrotia persica (DC.) C. A. Mey. and P. subaequalis (Hung T. Chang) R.M. Hao & H.T. Wei (Dirr et al., 1998; Wang and Xie, 2004; Andrews, 2007; Sefidi et al., 2014; Angiosperm Phylogeny Group, 2016). The former is native to the Alborz Mountain of northern Iran, whereas the latter is restricted to eastern China (Li and Tredici, 2008; Sefidi et al., 2011). Due to their unique exfoliating bark, obovate leaves with gorgeous autumn color, and beautiful apetalous flowers, both species are cultivated as ornamental trees in North America, Europe and East Asia (Nicholson, 1989; Li and Zhang, 2015). P. subaequalis differs from P. persica in its lanceolate stipules and sepals fused into a shallow saucer-shaped calyx (Hao et al., 1996; Li and Tredici, 2008). The two species of Parrotia were estimated to diverge at around 7.5 Mya (Li and Tredici, 2008). This speciation event is attributable to range fragmentation of the widespread Tertiary vegetation, as colder and more arid climates developed shortly after the mid-Miocene (Yin and Harrison, 2000; Sun et al., 2005).

Parrotia subaequalis, the focal species of the present study, is a diploid (2n = 2x = 24), deciduous tree (up to 6–8 m tall) with bisexual and wind-pollinated flowers that turn into woody capsules, dispersed by gravity and water (Li et al., 1999; Li and Tredici, 2008). P. subaequalis grows mainly in a mixed evergreen and deciduous broadleaved forest (c.100–700 m above sea level) on the hillsides and along canyons in subtropical China, where it is presently found in only about 8 known populations from disjunct/montane sites in Anhui, Jiangsu, Zhejiang and Henan provinces of eastern China (Hu et al., 2011; Li and Zhang, 2015). Because of its extremely restricted distribution and very few extant populations, P. subaequalis is classified as “extremely endangered” by the IUCN (International Union for Conservation of Nature; Bhandari, 2012) and Chinese Plant Red Book (Grade I Key protected Wild Plant; Wang and Xie, 2004). The limited geographic range of this species can be ascribed to the species alternate-year fruit production, serious habitat destruction, and increasing anthropogenic disturbance in the form of timber harvesting and clearing forest land for agriculture (Li and Tredici, 2008; Li and Zhang, 2015). Previous studies have focused primarily on germplasm investigation, taxonomy, systematics, population ecology, cultivation and ecophysiology (Li et al., 1999; Yan et al., 2008; Yao et al., 2010; Zhong et al., 2014). However, although genetic information is crucial for conservation and management strategies of a rare species (Frankham, 2010; Nybom et al., 2014), only very few studies have been conducted to assess genetic diversity and population structure of P. subaequalis. For example, the spatial patterns of genetic variation of P. subaequalis were surveyed for five natural populations using inter-simple sequence repeats (ISSRs) (Geng et al., 2015). The results revealed high genetic differentiation (GST = 0.46) and low within-population diversity 0.11 for Nei's gene diversity. However, the dominant nature of ISSR markers precludes estimating small-scale spatial genetic structure and inbreeding coefficient FIS as well as inferring evolutionary/demographic history which are necessary to guide management practices aiming at avoiding inbreeding and assessing future risk of erosion of diversity (Turlure et al., 2014). By contrast, the highly variable co-dominant nuclear microsatellite (SSR) markers are suitable for inferring relatively recent population genetic events and detecting the possible inbreeding (Perdereau et al., 2014). In addition, without the confounding effect of biparental inheritance, the maternally inherited chloroplast (cp) DNA markers could provide information on the migration routes and location of refugia of species (Avise, 2000).

To enable further population genetic and phylogeographic studies in P. subaequalis, we developed polymorphic nSSRs and cpSSRs markers for this species. Compared with traditional SSR development using random enrichment strategies, new methods to identify SSRs from next-generation sequencing (NGS) datasets are less expensive and more efficient (Squirrell et al., 2003; Li et al., 2015, 2017; Stoll et al., 2017; Yang et al., 2017). Here, we performed low-coverage whole genome shotgun sequencing for two P. subaequalis individuals from the northern- and southernmost population on the Illumina HiSeq 2500 platform. The sequencing data of P. subaequalis generated enough reads to assemble the entire chloroplast genome, from which maternally inherited markers, including highly variable regions and cpSSR loci can be developed. Moreover, we identified nSSR loci by searching in scaffolds for SSR motifs from the genomic sequences. The candidate loci were chosen for designing primer pairs, which were further tested for PCR amplification followed by screening for polymorphisms. Finally, we employed 10 cpSSRs and 12 nSSRs to investigate the genetic variation and population structure in six populations sampled throughout most of its natural range. The results here will provide useful resources for further studies on the relative role of historical and contemporary evolutionary processes in determining the contemporary genetic diversity of this Tertiary relict species, and lay a scientific foundation for designing conservation strategies.

Materials and Methods

Plant Samples and DNA Extraction

The fresh leaves of two individuals were collected from the population TX in Anhui Province and the population SJD in Jiangsu Province (China) (Table 1), respectively. They were chosen to represent the northern- and southernmost distribution of P. subaequalis. To evaluate and validate the polymorphism of both the nSSRs and cpSSRs developed from our sequencing data, leaf material of P. subaequalis was collected from single individuals in six populations from across the distribution range of the species in eastern China. From each population, 16 individuals were sampled at least 10 m apart to minimize the likelihood of sampling clones, resulting in a total of 96 individuals (Figure 1, Table 1). The polymorphic nSSRs and cpSSRs were further tested for transferability to five related species in Hamamelidaceae, i.e., Parrotia persica, Parrotiopsis jacquemontana, Sycopsis sinensis, Distylium racemosum, Hamamelis virginiana (Table 1). For each species, three accessions were used. Collected leaf material was dried with silica gel for further DNA extraction. Representative voucher specimens of all populations sampled were deposited in the Herbarium of Zhejiang University (HZU). Total genomic DNA was extracted from the silica-dried leaves with DNA Plantzol Reagent (Invitrogen) following the manufacturer's protocol. The quality of the DNA was determined by band intensity and integrity from electrophoresis on a 0.8% agarose gel stained with 1 × GelRed (Biotium). Besides, the concentration of DNA was tested by an Aglient BioAnalyzer 2100 (Agilent Technologies).

TABLE 1
www.frontiersin.org

Table 1. Voucher information and geographic characteristics of 6 Parrotia subaequalis populations and five related species from Hamamelidaceae.

FIGURE 1
www.frontiersin.org

Figure 1. (A) The distribution range of Parrotia subaequalis in China. (B) Location of the six extant natural populations and geographic distribution of 15 cpSSR haplotypes (H1-H15). The radius of the pie charts is proportional to the number of individuals sampled. (C) Median-joining network showing the relationship of haplotypes. The haplotypes are indicated by circles and the colors correspond with the color of the haplotypes in all populations, and small red circles show median vectors. The size of each pie chart is proportional to the frequency of corresponding haplotype.

Illumina Paired-End Sequencing and Chloroplast DNA Genome Assembly, Validation, and Annotation

Two next-generation sequencing (NGS) DNA libraries were prepared using the low-coverage shotgun sequencing of the whole genome of two P. subaequalis individuals. Firstly, a total of 3 μg of the purified genomic DNA was used for each library construction. Short-insert (500 bp) paired-end libraries were generated in accordance with the Illumina standard protocol. Two libraries with different indexes were then pooled together and sequenced in one lane of HiSeq 2500 platform (Illumina Inc., San Diego, California, USA) at Beijing Genomics Institute (Shenzhen, China). For each individual, about 2.5 Gb of raw data were obtained with pair-end 125 bp read length.

Paired-end reads of P. subaequalis were assembled into whole chloroplast genomes using a combination of both reference guide and de novo assembly approaches (Cronn et al., 2008). First, to obtain the high-quality clean data, all raw reads of two accessions were filtered by removing adapter sequences and low-quality reads (Q < 20, 0.01 probability error) using CLC-quality trim program CLC ASSEMBLY CELL package (http://www.clcbio.com/products/clc-assembly-cell/). Then, for the reference-based mapping, we aligned the trimmed reads to the reference chloroplast genome of Liquidambar formosana Hance (Genbank ID: KC588388) using BOWTIE software (Langmead et al., 2009). De novo assembly of reads were then conducted using CLC GENOMICS WORKBENCH v8 (http://www.clcbio.com) under the following parameters: minimum contig length = 200 bp, bubble size = 98 bp, deletion and insertion costs = 3, mismatch cost = 2, length fraction = 0.9, and similarity fraction = 0.8. All the assembled contigs were aligned and ordered with respect to the reference cp genome of L. formosana through BLAST. Lastly, the top-quality reads were again mapped to the draft cp genomes to yield the complete cp genomes of two P. subaequalis individuals that were visualized in GENEIOUS v10.0.5 (http://www.geneious.com). To confirm accuracy, the four junctions between LSC/IRs and SSC/IRs of the two cp genomes of P. subaequalis were validated via specific primers as described previously (Dong et al., 2013) and PCR-based conventional Sanger sequencing.

Gene annotation of the two cp genomes of P. subaequalis was conducted using the program DUAL ORGANELLAR GENOME ANNOTATOR (DOGMA; Wyman et al., 2004), and checked manually for gene start and stop codons. All protein-coding genes, rRNAs and tRNAs were identified by using the plastid/bacterial genetic code. Intron/exon boundaries were corrected by comparison with homologous genes from L. formosana using MAFFT v7 (Katoh and Standley, 2013). Furthermore, tRNAscan-SE (Schattner et al., 2005) was employed to verify the tRNA genes. Finally, the whole chloroplast genome maps were generated using Organellar Genome DRAW (Lohse et al., 2013), with subsequent manual editing. Codon usage and relative synonymous codon usage (RSCU, Sharp and Li, 1987) value were estimated for all protein-coding genes via the program CODONW v1.4.2 (http://codonw.sourceforge.net/).

Identification of Microsatellite Loci and Highly Variable Regions

To exploit simple sequence repeats (SSRs) within the cp genomes, we applied the MISA perl script (Thiel et al., 2003) with the following repeat thresholds settings: 10 repeat units for mononucleotide SSRs, 5 for dinucleotide SSRs, 4 for trinucleotide SSRs, and 3 for tetra-, penta-, and hexa-nucleotide SSRs. Additionally, in order to identify the nuclear genome database, we firstly removing the contigs used for the assembly of the two cp genomes and then the mitochondria-contained contigs were further removed from the assembled genome database using the mitochondrial genomes of Heuchera parviflora var. saurensis (Genbank ID: KR559021) and Vitis vinifera (Genbank ID: FM179380) as references. After filtering the cp- and mitochondria-contained contigs, potential polymorphic nSSRs were identified using CandiSSR (Xia et al., 2016) from the remaining scaffolds of the assembled nuclear genome database.

Both coding regions and noncoding regions with total number of mutation (Eta) > 0 and an aligned length > 200 bp were extracted to explore the divergence hotspot regions in P. subaequalis cp genome using MAFFT v7. The sequence divergence for a specific region between two cp genomes was quantified as the nucleotide variability (Pi) and estimated using DNASP v5.10 (Librado and Rozas, 2009).

SSR Primer Design and Polymorphism Assessment

Nuclear and cp SSR primer pairs were designed according to the flanking sequences of the SSR loci using Primer3 package (http://sourceforge.net/projects/primer3/files/primer3/) with the following parameters: 18–25 base pairs (bp) in length, PCR product size of 100–300 bp, annealing temperature of 50°-65°C, and a GC content of 40–60%. After that, according to our potential polymorphic SSRs selection principles, we finally selected 20 chloroplast and 30 nuclear candidates of polymorphic SSRs primer pairs to do the further trials (Tables S5, S7). Potential polymorphic cpSSRs identification criteria were as follows: (1) polymorphic cpSSRs possessed the same repeat units with the different number of repeat units; (2) for the cp mononucleotide repeats, more than ten repeat numbers were far more likely to be polymorphic cpSSRs; whereas for the di-, tri-, or tetranucleotide repeats comprising four or more repeat units is likely to represent a variable locus (Jakobsson et al., 2007; Ebert and Peakall, 2009); (3) polymorphic cpSSRs were located in the homologous non-coding regions. Besides, according to the results of CandiSSR, specific potential polymorphic nSSRs selected standards were as follows: (1) the nSSRs which the missing rate value were equal to zero and the transferability/similarity value were equal to one were chosen; (2) every type of nucleotide repeats motif, such as the di-, tri-, tetra-, penta-, or hexanucleotide repeats were selected; (3) on the premise of the above two principles, for each type of motif, we just chose a few of them to have a further polymorphism test.

Primer pairs were initially screened for amplification success and effectiveness using one randomly selected individual. The polymorphism of each locus was performed then by selecting 12 individuals from six representative geographically distant populations (two individuals were chosen from each population at random). PCR amplifications were performed on a GeneAmp9700 DNA Thermal Cycler (Perkin-Elmer, Waltham, Massachusetts, USA) following the standard protocol of the AmpliTaq Gold 360 Master PCR kit (Thermofisher Biotech Company, Applied Biosystems, Foster City, California, USA) in a final volume of 15 μL, which contained 1 μL of template DNA, 7.5 μL AmpliTaq Gold 360 Master Mix (Thermofisher Biotech Company, Applied Biosystems, Foster City, California, USA), 5.5 μL of deionized water, and 0.5 μL of forward and reverse primers (10 μM). And the procedure of PCR was 5 min initial denaturation at 95°C, 35 cycles of 45 s at 95°C, 30 s annealing at optimal primer temperature (Tables S6, S8) and 30 s synthesis at 72°C, followed by a final 10-min extension step at 72° and a 4°C holding temperature. PCR products were separated on 6.0% (w/v) denaturing polyacrylamide gels (PAGE) and subsequently visualized by silver staining. After the identification of the polymorphism, we used 96 individuals from six representative geographically distant populations to further amplify and character the polymorphic SSR loci. The forward primer of each of the polymorphic primer pairs was labeled with a fluorescent dye (FAM, ROX, HEX, or TAMRA; Tables S6, S8), and SSR loci were amplified using the PCR conditions described above.

Fragment lengths of PCR products were analyzed on an ABI 3730XL DNA Analyzer (Applied Biosystems, Foster City, California, USA) with GeneScan LIZ 500 as an internal reference (Applied Biosystems). Electrophoresis peaks scoring and alleles identification were assayed by using GeneMarker v2.2.0 (SoftGenetics, State College, Pennsylvania, USA). All primer sequences obtained from this study were submitted to GenBank (Tables S6, S8). In addition, transferability among the other five Hamamelidaceae species was assessed using the same PCR conditions described above.

Population Structure and Differentiation at Chloroplast and Nuclear SSR Loci

Each cpSSR was considered a locus at a specific site and length variants were considered as alleles. Different alleles at each of the cpSSR loci in each individual were combined into one haplotype because the cp genome behaves as a single non-recombining locus. For each polymorphic locus, we obtained the number of alleles (NA) and unbiased haploid diversity index (hd) using the program GenAlEx v6.41 (Peakall and Smouse, 2006). For each population, we computed haplotypic diversity (Hcp), the number of effective alleles (NE) using program CONTRIB v1.02 (Petit et al., 1998). Two coefficients of population differentiation, GST and RST, were analyzed using the program PERMUT & CPSSR v2.0 (Pons and Petit, 1996). GST is only based on haplotype frequency, while RST takes into account both haplotype frequencies and haplotype similarities. A significantly higher RST than GST values (1,000 permutations; P < 0.05) implies that genealogically closely related haplotypes are geographically close to each other, indicating the presence of phylogeographical structure (Pons and Petit, 1996). A network of relationship between cpDNA haplotypes was constructed using a median-joining network (MJN, Bandelt et al., 1999) approach implemented in NETWORK v5.0.0.3 (http://www.fluxus-engineering.com/). Analysis of molecular variance (AMOVA) was performed to partition the total genetic variance among populations using the ARLEQUIN v3.11 (Excoffier et al., 2007). Significance tests were made after 1,000 permutations.

For each nSSR locus, the number of alleles (NA), allelic richness (AR), expected heterozygosity (HE), observed heterozygosity (Ho), total genetic diversity (HT), average genetic diversity within populations (HS) and polymorphism information content (PIC) were calculated by using CERVUS v2.0 (Kalinowski et al., 2007) and FSTAT v2.9.3.2 (Goudet, 2001). Deviation from Hardy-Weinberg equilibrium (HWE) for each primer pair was tested using a Markov chain (dememorization 1,000, 100 batches, 1,000 iterations per batch) in GENEPOP v4.0.7 (Rousset, 2008). The frequency of null alleles and their bias on genetic diversity were evaluated based on the expectation maximization method implemented in FREENA (Chapuis and Estoup, 2006). Differentiation between populations (RST; Slatkin, 1995) under a stepwise mutation model (SMM; Kimura and Ohta, 1978) was computed in ARLEQUIN v3.11. All nSSR samples were assigned to genetic clusters (K) by using STRUCTURE v2.3.4 (Pritchard et al., 2000), assuming the admixture model with independent allele frequencies. This program was run 10 times for each K value ranging from 1 to 6 (the number of sampled localities) to determine the maximum value of posterior probability of the data [lnp(D)] (Pritchard et al., 2000). Each run was performed using a burn-in period of 104 and a run length of 105 iterations. In addition, we estimated a parameter (ΔK) that corresponds to the change of lnp(D) between consecutive K values (Evanno et al., 2005). The most likely number of cluster (K) was identified as the one that maximized lnp(D) and/or ΔK. Analysis of molecular variance (AMOVA) was performed to partition the total genetic variance among populations using the ARLEQUIN v3.11.

We tested for a correlation between pairwise population genetic distance (RST) and geographic distance among sampling locations (isolation-by-distance effect) using a Mantel test (Mantel, 1967) in IBDWS (Isolation by Distance Web Service) v3.21 (Jensen et al., 2005) with 10,000 permutations to determine the significance of IBD pattern. Additionally, we calculated the pollen/seed migration ratio (r) using a modified form of an equation of Ennos (1994) and used RST values as estimators of population differentiation following Petit et al. (2005): r = mp/ms = [(1/RST(n)-1)−2(1/RST(c)-1)]/(1/RST(c)-1), where mp and ms correspond to the pollen migration rate and the seed migration ratio, RST(n) is the nuclear RST and RST(cp) is the cytoplasmic RST.

Results

Chloroplast DNA Genome Organization and Structural Features

After filtering the low-quality reads and adaptor sequences, 34,688,769 and 25,632,935 clean reads (of 125 bp length) were produced for P. subaequalis (TX) and P. subaequalis (SJD), respectively. The de novo assembly generated 359,167 contigs with an N50 length of 554 bp for P. subaequalis (TX) and 274,639 contigs with an N50 length of 580 bp for P. subaequalis (SJD) (Table 2). Subsequently, based on total alignment score and percentage sequence identity, three to four initial contigs were identified with greatest similarity to the reference cp genome of L. formosana. They were combined to generate each draft chloroplast genome, with no gaps or missing nucleotids (Ns). Four junction regions in each chloroplast genome were validated using PCR-based sequencing (Table S1). These sequences were found to be identical with the assembled genomes, confirming the accuracy of our genome sequencing and assembly.

TABLE 2
www.frontiersin.org

Table 2. The basic characteristics of two chloroplast genomes of Parrotia subaequalis.

The whole cp genome sequences of two P. subaequalis were 159,280 bp (TX; GenBank: MG252374) and 159,324 bp in length (SJD; GenBank: MG334121) (Table 2, Figure 2). The cp genomes of P. subaequalis exhibited a typical quadripartite structure, consisting of a pair of inverted repeats (IRs) with a length of 26,211 in TX and 26,212 bp in SJD, separated by one large single-copy (LSC) region of 87,927 bp in TX and 87,968 bp in SJD and a small single-copy (SSC) region of 19,031 bp in TX and 18,932 bp in SJD. The gene map is shown in Figure 2. The overall GC content was 38.0%, whereas the GC content in the LSC, SSC, and IR regions were 36.1, 32.4, and 43.1%, respectively (Table 2). Gene content and arrangement were identical in both cp genomes. There were 133 predicted functional genes in both genomes, of which 115 were unique and 18 were duplicated in the IR regions. Among the 115 unique genes, there were 81 protein-coding genes, 30 tRNA genes and 4 rRNA genes, respectively. Nine protein-coding genes (atpF, ndhA, ndhB, petB, petD, rpl2, rpl16, rpoC1, and rps16) and six tRNA genes (trnG-GCC, trnK-UUU, trnL-UAA, trnV-UAC, trnI-GAU, and trnA-UGC) had a single intron, while three protein-coding genes (ycf3, clpP, and rps12) possessed two introns (Table S2). All the protein-coding genes had standard AUG as initiator codon. The gene rps12 was found to be trans-spliced, with the 5′-end exon located in the LSC region and two copies of 3′-end exon and intron in the IR regions. The gene ycf15 was identified as pseudogene because it contained several internal stop codons. The gene ycf1 was located in the boundary regions between SSC/IRb. Incomplete duplication of the normal copy of ycf1 resulted in the ycf1 pseudogene at the SSC/IRa border in all three cp genomes (P. subaequalis (TX): 985 bp; P. subaequalis (SJD): 985 bp; L. formosana: 1,609 bp).

FIGURE 2
www.frontiersin.org

Figure 2. Gene maps of the two Parrotia subaequalis chloroplast genomes. (A) Parrotia subaequalis (TX); (B) Parrotia subaequalis (SJD). Genes shown on the outside of the circle are transcribed clockwise, and genes inside are transcribed counter-clockwise. Genes belonging to different functional groups are color-coded. The darker gray in the inner corresponds to GC content, and the lighter gray corresponds to AT content.

Divergence Hotspot Regions of P. subaequalis

The nucleotide variability (Pi) values in the two cp genomes of P. subaequalis were calculated for the 40 regions showing single-nucleotide polymorphisms (SNPs). The overall average Pi value was 0.00144. For 20 protein coding regions, Pi values ranged from 0.00015 (ycf2) to 0.00407 (psaC), among which psaC, rps4, cemA, petD, ycf1, ndhD, ndhG, ndhI, and ndhA regions showed remarkably higher Pi values (Pi > 0.00144). For the 17 intergenic spacer, Pi-values ranged from 0.00055 (ycf1-trnN) to 0.00369 (ccsA-ndhD), of which matK-trnK, trnT-psbD, trnS-psbZ, psbZ-trnG, psaJ-rpl33, rps18-rpl20, and ccsA-ndhD regions with Pi values exceeding the average value. Besides, for the three intron regions, Pi-values varied between 0.00094 (intron ndhA) and 0.00136 (intron rpoC1) (Figure 3, Table S3).

FIGURE 3
www.frontiersin.org

Figure 3. The nucleotide variability (Pi) values were compared between two Parrotia subaequalis.

Characterization of Chloroplast SSRs and Polymorphism Analysis

In total, 139 perfect cpSSRs, including 104 mononucleotide (A, C, T), 20 dinucleotide (AT, TA, TC), 4 trinucleotide (GAA, TTA), 8 tetranucleotide (ATAC, TGAA, TTCT, TTTC), and 3 pentanucleotide (TATTT, TTCTA) repeats were detected within the two P. subaequalis cp genomes. The mononucleotide A/T repeat units were found to be the most abundant, with 49 in P. subaequalis (TX) and 54 in P. subaequalis (SJD) (Table S4, Figure 4A). Most SSR loci were located in the IGS regions (78.5%), followed by CDS (8.1%) and introns (13.4%) (Table S4, Figure 4B). The cp genomes of P. subaequalis (TX) and P. subaequalis (SJD) contained 71 and 78 SSRs, respectively, of which 30 were potential polymorphic cpSSRs (Table S5). Based on a strict set of criteria employed in this study, 20 candidates of polymorphic SSR loci were selected from the total 30 potential polymorphic cpSSRs to evaluate their amplification and polymorphism in the initial screening with the 12 individuals from the six populations (Table S5). Finally, after excluding those that gave poor amplification or produced a complex pattern with multiple bands, 10 with high polymorphism (Table S6) were genotyped in the 96 individuals from the six populations. The 10 cpSSR loci yielded a total of 43 alleles across the 96 samples. The number of alleles (NA) per locus varied from 2 to 6, while the the unbiased haploid diversity (Hd) per locus ranged from 0.392 to 0.752 (Table 3), representing the different level of genetic diversity in chloroplast genome. Moreover, all cpDNA loci were successfully amplified in all the other five species of Hamamelidaceae (Table 4).

FIGURE 4
www.frontiersin.org

Figure 4. Simple sequence repeats (SSRs) in the two Parrotia subaequalis chloroplast genomes. (A) Numbers of cpSSRs type and length of repeats; (B) Distribution of cpSSR loci. IGS, intergenic spacer region; (C) Overview of the candidate polymorphic nuclear SSRs (nSSRs) detected in the two Parrotia subaequalis.

TABLE 3
www.frontiersin.org

Table 3. Genetic characteristics of the 10 polymorphic cpSSR loci and 12 polymorphic nSSR loci in Parrotia subaequalisa.

TABLE 4
www.frontiersin.org

Table 4. Fragment sizes detected in cross-amplification tests of the 25 newly developed microsatellite markers in the five related species of Hamamelidaceaea.

Characterization of Nuclear SSR Loci and Polymorphism Analysis

A total of 596 P. subaequalis candidates of polymorphic nSSR loci with an average length of 17 bp were detected in the nuclear genome. Among these loci, di-nucleotide repeats (DNRs) were the most abundant repeat type (480; 80.54%), followed by tri- (TNRs; 100; 16.77%), tetra- (TTRs; 12; 2.01%), penta- (PNRs; 2; 0.34%) and hexa-nucleotide repeats (HNRs; 2; 0.34%) (Table S7, Figure 4C). Following a strict set of criteria, 30 candidates of polymorphic SSR loci were selected for further trials. After excluding those that gave poor amplification or produced a complex pattern with multiple bands in an initial polymorphism screening, 15 with high polymorphism (Table S8) were genotyped in the 96 individuals from the six populations. Of the 15 nSSR loci, a high frequency of null alleles was detected in PasN11 and PasN14 (v > 5%), while significant linkage disequilibrium was observed between PasN24 and PasN14. These three loci were excluded from subsequent analyses. Four of the remaining 12 loci deviated significantly from HWE expectations (P < 0.001) in some populations (PasN4 in HBS; PasN7 in ZXC and SJD; PasN10 in TX and HBS; PasN27 in LWS and WFS) as a result of heterozygote deficiency. In total, the 12 polymorphic SSRs yielded 64 alleles with an average of 5.33 alleles and a range of 2 to 14 alleles (NA) per locus. Besides, the observed (HO) and expected (HE) heterozygosity per locus over all populations ranged from 0.073 to 0.990 (with an average of 0.520) and from 0.071 to 0.868 (with an average of 0.558), respectively (Table 3). Eight nSSR loci were successfully amplified in all the other five species of Hamamelidaceae, while seven loci produced PCR fragments in some species (i.e., PasN7 for P. persica, S. sinensis and H. virginiana; PasN8 for P. persica and P. jacquemontana; PasN14 for H. virginiana; PasN21 and PasN10 for P. jacquemontana; PasN27 for S. sinensis and PasN25 for H. virginiana) (Table 4).

Genetic Diversity and Population Structure

For the cpSSR dataset, a total of 15 haplotypes were identified across the 96 individuals from the six populations based on the 10 polymorphic loci (H1–H15; Figure 1, Table 5). High total haplotypic diversity with Hcp = 0.832 at species level. The haplotypic diversity per population (Hcp) ranged from 0.520 (SJD) to 0.862 (HBS), with an average of 0.713 (Table 5). H1, H2, H3, and H4 were the most frequent haplotypes, and almost shared by all the populations. H5 and H6 were shared between LWS and ZXC, H10, H11, and H12 were shared among WFS, TX and HBS. While the remaining 6 haplotypes (40% of the total) were restricted to single populations (Figure 1, Table 5). The relationships between 15 cpSSR haplotypes were analyzed by a median-joining network model (Figure 1). Haplotype H11 occupied the central place of this network. Six median vectors (mv) representing missing intermediates were inferred from the network. The haplotype network displayed a distinct geographic distribution of haplotypes that coincided with certain mountain regions (Figure 1). For example, haplotypes H10 and H12–H14 formed one distinct clade and spanned populations (HBS, WFS and TX) in Dabie Mountain region; haplotypes H5–H9 were recovered as a separate clade and were restricted to Yellow Mountain region. The indices of population structure GST and RST were 0.335 and 0.652 respectively, whereby RST was significantly greater than GST (P < 0.01), indicating the existence of a marked phylogeographical structure at this scale. The AMOVA partitioned genetic variation into 65.45% among six populations and 34.55% was contributed by differences within populations (P < 0.001; Table S9).

TABLE 5
www.frontiersin.org

Table 5. Genetic characteristics of the six Parrotia subaequalis populations studied.

For the nSSR dataset, per locus estimates of the average value of genetic diversity within-populations (HS) among loci was 0.478, with a range of 0.067–0.740; while the total genetic diversity over all populations (HT) ranged from 0.071 to 0.865 and averaged 0.559 (Table 3). At the population level, average estimates of genetic diversity were generally high (AR = 2.274, HE = 0.464, HO = 0.520), being lowest in population HBS (1.814, 0.395, and 0.495) and highest in population TX (2.558, 0.540, and 0.620; Table 5). The nSSR-derived data demonstrated significant population genetic differentiation at the range-wide scale (RST(n) = 0.331, P < 0.001). The hierarchical AMOVA revealed that 16.39% of the total variation was attributed to differences among six populations and that 83.61% was contributed by differences within populations (P < 0.001; Table S9). Mantel tests of IBD revealed no significant correlation between geographical and genetic distances (r = 0.228, P = 0.564). Using the nSSR-derived RST(n) value of 0.331 across the six populations surveyed, and their corresponding value for cpSSR markers, RST(cp) = 0.652, the pollen/seed migration ratio (r) was calculated as 1.78, indicating a slightly higher level of pollen flow as compared to seed flow. STRUCTURE yielded the highest likelihood when samples were clustered into three groups (K = 3). However, all individuals were clearly assigned to non-empty groups when K values ranged from 2 to 4 (Figure 5). Running STRUCTURE and using K = 2, HBS, the southernmost population, was firstly separated from the remaining 5 populations; with K = 3, ZXC, the westernmost population, formed a separate cluster; with K = 4, SJD, the easternmost population, were separated.

FIGURE 5
www.frontiersin.org

Figure 5. Histogram of the STRUCTURE analysis for the model with K = 3 (showing the highest ΔK), K = 2 and K = 4. Each color corresponds to a suggested cluster, and a vertical bar represents a single individual. The x axis corresponds to population codes. The y axis presents the estimated membership coefficient (Q) for each individual in the different clusters.

Discussion

The Mining of Chloroplast and Nuclear SSRs

In the last decade, next-generation high-throughput sequencing technologies have allowed producing genomic resources in a rapid and cost-effective way (Mardis, 2008; Hao et al., 2011). Here, in our study, using the low-coverage whole genome shotgun sequencing data, we successfully assembled the complete chloroplast genomes of P. subaequalis (Figure 2). The cp genomes displayed typical quadripartite structure, which is consistent with previous published plastid genomes of four Saxifragales families (Dong et al., 2013). The genome contains 133 unique genes, 18 of which are duplicated within the IRs. Although there are expansions or contractions of IR regions observed among the cp genomes of P. subaequalis and the other four Saxifragales families of Saxifragales (Dong et al., 2013), they contribute little to the overall size differences in the chloroplast genomes. We found 16 regions of the two cp genomes, which were inferred to already represent polymorphic characters like in the seven intergenic spacers (matK-trnK, trnT-psbD, trnS-psbZ, psbZ-trnG, psaJ-rpl33, rps18-rpl20, and ccsA-ndhD) and the nine genes (psaC, rps4, cemA, petD, ycf1, ndhD, ndhG, ndhI, and ndhA). These regions of the cp genome can be further used to evaluate maternally inherited genomic diversity for phylogeographic and population genetic studies of P. subaequalis. Moreover, based on a comparative analysis of two cp genomes of P. subaequalis, we identified a total of 30 candidates of polymorphic cpSSR loci, for which 20 primer sets were designed to evaluate their amplification and polymorphism in the initial screening with the 12 individuals from the six populations. Of the 20 primer pairs, 10 yielded clear and polymorphic amplification products, confirming that plastome assembly from low coverage genomic sequencing is an ideal method for the development of cpSSR markers. Notably, the 10 polymorphic SSR markers could also be amplified in other five Hamamelidaceae species, indicating that they could be used as cross-species markers within Hamamelidaceae.

Genomic SSRs have traditionally been isolated by hybridizing repeat-enriched molecular probes in genomic libraries (Zalapa et al., 2008), but this method has proven low efficiency, time consuming and costly, and can isolate only the targeted enriched SSR motif types (Zane et al., 2002; Parchman et al., 2010). In addition to the chloroplast SSR loci developmenet, the present work also demonstrated that the use of sequences derived from low-coverage shotgun sequencing of genomic DNA to develop nuclear SSR markers in non-model species is a rapidly and cost-effective approach. As we used two individuals representing the northern- and southernmost distribution of P. subaequalis to construct the sequencing library, based on the two assembled sequences, we identified a total of 576 candidate polymorphic SSRs by means of the program CandiSSR. In agreement with previous reports from many other plant taxa (Jiao et al., 2012; Xia et al., 2016), dinucleotide motifs are found to be the most common in P. subaequalis. A total of 30 designed primer pairs were used for validation of the SSR markers, and 15 primer pairs (50%) were proved to be polymorphic among 96 individuals from the six populations. Such high success ratios indicate that the application of next-generation sequencing (NGS) technologies for SSRs development is possible to develop large numbers of polymorphic SSR markers. For population genetic analyses in P. subaequalis, 13 loci seem to provide a good resource to explore population genetic diversity and structure (see below). Our tests of interspecies transferability of the 15 SSRs from P. subaequalis to other five Hamamelidaceae species yielded transfer success rates of 47% (7) for all species, suggesting an intermediate level of cross-species transferability.

Population Genetic Diversity and Structure

Despite its restricted and highly disjunct distribution range, P. subaequalis exhibits similar or even higher levels of cpDNA haplotype diversity (Hcp = 0.862) as compared to other Chinese endemic flowering plant taxa presented in previous studies by using similar markers (e.g., 0.893 for Davidia involucrata, Ma et al., 2015; 0.627 for Dipteronia dyeriana, Chen et al., 2017). The species-wide levels of haplotype diversity in P. subaequalis were also higher than the mean value of 170 seed plants estimated by maternally inherited markers (mean: hT = 0.67; Petit et al., 2005). Such high total cpDNA gene diversity is generally thought to reflect the long evolutionary histories (Sun et al., 2005) but also suggests restricted gene flow between populations (Varvio et al., 1986; Qiu et al., 2009). In line with the first assumption, the estimated speciation time of around 7.5 Mya for the two extant species of Parrotia qualifies them as Tertiary relicts (Li and Tredici, 2008), indicating a long period of time for which both species have evolved separately in different glacial refugia. In fact, Eastern China has never been directly impacted by Pleistocene glaciations (Axelrod and Fuerch, 1996) and served as one of the most important ancient relict areas for temperate biota throughout the Quaternary (Deng et al., 1992). Therefore, P. subaequalis likely persisted in this long-term refuge, allowing for the maintenance of considerable genetic variation. The estimated value of pollen flow/seed flow (r = 1.78) is at the lower end of the range reported for 93 seed plant species (median r ≈ 17, Petit et al., 2005; Hodgins and Barrett, 2007). Considering the large maternal RST(cp) (0.652) estimated for P. subaequalis, its correspondingly low r estimate likely implies restricted pollen flow in a low-seed disperser rather than a significant role of seed flow in a species for which pollen dispersal is limited. In fact, nSSR-derived RST(n) value of 0.331 suggest a substantial amount of population isolation. Therefore, the reduced levels of contemporary intersite gene flow via pollen and seed agrees well with the second assumption. The above results also accord with field observations indicating that (1) the small (ca 4–5mm) seeds from the two-seeded capsules are ballistically dispersed for a short distance (≤ 18 m) (Deng et al., 1992; Yang, 1994); and (2) the wind-mediated pollen dispersal is severely constrained in P. subaequalis, probably as a consequence of its limitation to mountain streams and slopes as well as often steep temperate-deciduous forest habitats in isolated mountains.

In general, there is increased efficiency of genetic drift in small and isolated populations (Ellstrand and Elam, 1993; Lande, 1999). In this study, a complete absence of IBD, together with the strong population subdivision in both marker systems, suggests that genetic drift had a larger historical role in contemporary population structure and genetic diversity compared to limited pollen and seed flow alone (Hutchison and Templeton, 1999). Our nSSR-measured HE value (HE = 0.464) is comparable to average nSSR-based HS (the equivalent to HE in the present study) in endemic species (HS = 0.42), as reviewed by Nybom (2004). Therefore, the low within-population nSSRs diversity detected in P. subaequalis (in terms of HE) are more likely due to the historical random loss of alleles, possibly following habitat fragmentation, rather than inbreeding. Likewise, historical processes such as long-term isolation and/or habitat fragmentation may have also contributed to the geographic differentiation of P. subaequalis (see also Young et al., 1996). In fact, based on STRUCTURE analyses of nSSRs data, the populations HBS, ZXC (K = 3) and SJD (K = 4) were assigned to a separate cluster, respectively (Figure 5). Moreover, each of the regions Dabie Mountain and Yellow Mountain were also found to contain a set of regional-specific haplotypes (Figure 1). The spatially consistent genetic split between two marginal populations and central populations as registered by both cpSSRs and nSSRs strongly implies a long-term population persistence and isolation in eastern China, possibly before the beginning of the last glacial period. Taken together, geographical distribution patterns of haplotype (Figure 1) and nSSR cluster of P. subaequalis (Figure 5) suggested at least three refugia in Dabie Mountain, Yellow Mountain and central region. Nevertheless, for the central populations, it seems unlikely that ongoing gene flow among them may be existent because the smallest distances between the mountains where this species occur is 99 km (Geng et al., 2015). Thus, the cpDNA haplotypes (e.g., H1, H2, H3, H4) and nSSRs cluster (“red”) shared among populations (Figures 1, 5) may largely reflect common ancestry due to incomplete lineage sorting rather than recurrent gene flow. In fact, based on fossil-based evidence, forests were found to decline during the last 6,000 years in the middle and lower reaches of the Yellow River (Ren and Beug, 2002) and in the Yangtze delta region (Yi et al., 2003) due to the expansion of farming since the Yangshao Culture period (ca. 5,000–6,000 years ago). Such human interference may have contributed to population extinction and/or disruption of recent population connectivity of P. subaequalis. However, it remains to be investigated whether the separation of three clusters resulted from historical fragmentation due to human interference or eco-geographic isolation induced by Pleistocene climate change. However, irrespective of the outcome of such studies, the three genetic clusters of P. subaequalis revealed by both cpSSRs and nSSRs should be considered as separate conservation units in any program.

Conclusions

To enable population genetic and phylogeographic analyses in this species, we performed paired-end shotgun sequencing (2 × 125 bp) of genomic DNA from two individuals of P. subaequalis on the Illumina HiSeq platform. Based on the resulting sequences, we have assembled and characterized the plastome of P. subaequalis. Moreover, we have identified the polymorphic cpSSRs/nSSRs using the new pipeline CandiSSR and mutational hotspots of the P. subaequalis plastome. The present work demonstrates the use of sequences derived from low-coverage shotgun sequencing of genomic DNA to rapidly and cost-effectively explore genomic resources in a genetically understudied plants.

We further used 10 polymorphic cpSSR and 12 polymorphic nSSR loci to investigate the genetic diversity and population structure for six populations sampled across the range of P. subaequalis. Our results revealed that P. subaequalis exhibits abundant genetic diversity (e.g., cpSSRs: Hcp = 0.832; HT = 0.559) and high genetic differentiation; e.g., cpSSRs: RST(cp) = 0.652; nSSRs: RST(n) = 0.331], and is characterized by a low pollen-to-seed migration ratio (r ≈ 1.78). These genetic patterns are attributable to its long evolutionary histories and reduced levels of contemporary intersite gene flow via pollen and seed. In addition, lack of isolation-by-distance pattern, together with the strong population subdivision in both marker systems, suggests that long-term isolation, and/or habitat fragmentation as well as genetic drift may have also contributed to the geographic differentiation of P. subaequalis. Therefore, long-term habitat protection is the most important means to prevent further losses of genetic variation and a decrease in effective population size. Moreover, the three genetic clusters of P. subaequalis revealed by both cpSSRs and nSSRs should be considered as separate conservation units in any program, allowing for the long-term preservation of its genetic resources.

Author Contributions

Y-YZ, Y-XQ, and Z-SW conceived the study; Y-YZ analyzed the data and wrote the manuscript; ES and Z-PY helped to collect samples; Y-YZ and ES performed the experiment; Z-PY and Q-FG provided useful suggestions on the manuscript.

Conflict of Interest Statement

The authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.

Acknowledgments

This research was supported by grants from the State Key Basic Research and Development Plan of China (Grant No. 2017YFA0605104) and the National Natural Science Foundation of China (Grant No. 30970512). We thank Pan Li, Xin Zhuang, and Jie-Han Zhou for their great help in collecting plant materials. We are also grateful to Wu-Qin Xu and Yu Feng for assistance with data analysis.

Supplementary Material

The Supplementary Material for this article can be found online at: https://www.frontiersin.org/articles/10.3389/fpls.2018.00246/full#supplementary-material

References

Andrews, S. (2007). Tree of the Year Parrotia. Kew: International Dendrology Society Press.

Google Scholar

Angiosperm Phylogeny Group (2016). An update of the Angiosperm Phylogeny Group classification for the orders and families of flowering plants: APG IV. Bot. J. Linn. Soc. 181, 1–20. doi: 10.1111/boj.12385

CrossRef Full Text

Avise, J. C. (2000). Phylogeography: the History and Formation of Species. Cambridge: Harvard University Press.

Google Scholar

Axelrod, P., and Fuerch, M. A. (1996). Flight of the deities: Hindu resistance in Portuguese Goa. Mod. Asian Stud. 30, 387–421. doi: 10.1017/S0026749X00016516

CrossRef Full Text | Google Scholar

Bandelt, H. J., Forster, P., and Röhl, A. (1999). Median-joining networks for inferring intraspecific phylogenies. Mol. Biol. Evol. 16, 37–48. doi: 10.1093/oxfordjournals.molbev.a026036

PubMed Abstract | CrossRef Full Text | Google Scholar

Bhandari, M. (2012). International Union for Conservation of Nature. Jersey City, NJ: John Wiley & Sons, Ltd.

Chapuis, M. P., and Estoup, A. (2006). Microsatellite null alleles and estimation of population differentiation. Mol. Biol. Evol. 24, 621–631. doi: 10.1093/molbev/msl191

PubMed Abstract | CrossRef Full Text | Google Scholar

Chen, C., Lu, R. S., Zhu, S. S., Tamaki, I., and Qiu, Y. X. (2017). Population structure and historical demography of Dipteronia dyeriana (Sapindaceae), an extremely narrow palaeoendemic plant from China: implications for conservation in a biodiversity hot spot. Heredity 119, 95–106. doi: 10.1038/hdy.2017.19

PubMed Abstract | CrossRef Full Text | Google Scholar

Cronn, R., Liston, A., Parks, M., Gernandt, D. S., Shen, R., and Mockler, T. (2008). Multiplex sequencing of plant chloroplast genomes using solexa sequencing-by-synthesis technology. Nucleic Acids Res. 36:e122. doi: 10.1093/nar/gkn502

PubMed Abstract | CrossRef Full Text | Google Scholar

Deng, M. B., Wei, H. T., Wang, X. Q., Shu, P., and Jin, Y. X. (1992). On the significance of the discovery of Fothergilleae in China. J. Plant Resour. Environ. 1, 30–35.

Dirr, M. A., Dirr, B., Stephan, M., and Asta, S. (1998). Manual of Woody Landscape Plants: their Identification, Ornamental Characteristics, Culture, Propagation and Uses. Champaign, IL: Stipes Publication Company.

Google Scholar

Dong, W., Xu, C., Cheng, T., Lin, K., and Zhou, S. (2013). Sequencing angiosperm plastid genomes made easy: a complete set of universal primers and a case study on the phylogeny of Saxifragales. Genome Biol. Evol. 5, 989–997. doi: 10.1093/gbe/evt063

PubMed Abstract | CrossRef Full Text | Google Scholar

Ebert, D., and Peakall, R. (2009). Chloroplast simple sequence repeats (cpSSRs): technical resources and recommendations for expanding cpSSR discovery and applications to a wide array of plant species. Mol. Ecol. Res. 9, 673–690. doi: 10.1111/j.1755-0998.2008.02319.x

PubMed Abstract | CrossRef Full Text | Google Scholar

Ellstrand, N. C., and Elam, D. R. (1993). Population genetic consequences of small population size: implications for plant conservation. Annu. Rev. Ecol. Syst. 24, 217–242. doi: 10.1146/annurev.es.24.110193.001245

CrossRef Full Text | Google Scholar

Ennos, R. (1994). Estimating the relative rates of pollen and seed migration among plant populations. Heredity 72, 250–259. doi: 10.1038/hdy.1994.35

CrossRef Full Text | Google Scholar

Evanno, G., Regnaut, S., and Goudet, J. (2005). Detecting the number of clusters of individuals using the software STRUCTURE: a simulation study. Mol. Ecol. 14, 2611–2620. doi: 10.1111/j.1365-294X.2005.02553.x

PubMed Abstract | CrossRef Full Text | Google Scholar

Excoffier, L., Laval, G., and Schneider, S. (2007). Arlequin (version 3.0): an integrated software package for population genetics data analysis. Evol. Bioinform. Online 1, 47–50. doi: 10.1177/117693430500100003

PubMed Abstract | CrossRef Full Text | Google Scholar

Frankham, R. (2010). Where are we in conservation genetics and where do we need to go? Conserv. Genet. 11, 661–663. doi: 10.1007/s10592-009-0010-2

CrossRef Full Text | Google Scholar

Geng, Q., Yao, Z., Yang, J., He, J., Wang, D., and Wang, Z. (2015). Effect of Yangtze river on population genetic structure of the relict plant Parrotia subaequalis in eastern china. Ecol. Evol. 5, 4617–4627. doi: 10.1002/ece3.1734

PubMed Abstract | CrossRef Full Text | Google Scholar

Goudet, J. (2001). FSTAT, a program to estimate and test gene diversities and xation indices (version 2.9.3). My Pub. 21, 13–15. doi: 10.1016/B978-012083522-5/50036-4

CrossRef Full Text | Google Scholar

Hao, R., Wei, H., and Liu, W. (1996). Floral morphology of Shaniodendron (Hamamelidaceae) and its taxonomic significance. J. Plant Res. Environ. 5, 38–42.

Google Scholar

Hao, Y., Tardivo, L., Tam, S., Weiner, E., Gebreab, F., Fan, C., et al. (2011). Next-generation sequencing to generate interactome datasets. Nat. Methods 8, 478–480. doi: 10.1038/nmeth.1597

PubMed Abstract | CrossRef Full Text | Google Scholar

Hodgins, K. A., and Barrett, S. C. (2007). Population structure and genetic diversity in tristylous Narcissus triandrus: insights from microsatellite and chloroplast DNA variation. Mol. Ecol. 16, 2317–2332. doi: 10.1111/j.1365-294X.2007.03314.x

PubMed Abstract | CrossRef Full Text | Google Scholar

Hu, Y. M., Fang, G. F., and Luo, X. M. (2011). Status of Parrotia subaequalis in taxonomy, reasons for its endangerment and protective measures. Anhui. Forestry Sci. Tech. 37, 46–48.

Google Scholar

Hutchison, D. W., and Templeton, A. R. (1999). Correlation of pairwise genetic and geographic distance measures: inferring the relative influences of gene flow and drift on the distribution of genetic variability. Evolution 53, 898–1914. doi: 10.1111/j.1558-5646.1999.tb04571.x

PubMed Abstract | CrossRef Full Text | Google Scholar

Jakobsson, M., Säll, T., Lind-Halldén, C., and Halldén, C. (2007). Evolution of chloroplast mononucleotide microsatellites in Arabidopsis thaliana. Theor. Appl. Genet. 114, 223–235. doi: 10.1007/s00122-006-0425-9

PubMed Abstract | CrossRef Full Text | Google Scholar

Jensen, J. L., Bohonak, A. J., and Kelley, S. T. (2005). Isolation by distance, webservice. BMC Genet. 6:13. doi: 10.1186/1471-2156-6-13

PubMed Abstract | CrossRef Full Text | Google Scholar

Jiao, Y., Jia, H. M., Li, X. W., Chai, M. L., Jia, H. J., Chen, Z., et al. (2012). Development of simple sequence repeat (SSR) markers from a genome survey of Chinese bayberry (Myrica rubra). BMC Genomics 13:201. doi: 10.1186/1471-2164-13-201

PubMed Abstract | CrossRef Full Text | Google Scholar

Kalinowski, S. T., Taper, M. L., and Marshall, T. C. (2007). Revising how the computer program CERVUS accommodates genotyping error increases success in paternity assignment. Mol. Ecol. 16, 1099–1106. doi: 10.1111/j.1365-294X.2007.03089.x

PubMed Abstract | CrossRef Full Text | Google Scholar

Katoh, K., and Standley, D. M. (2013). MAFFT multiple sequence alignment software version 7: improvements in performance and usability. Mol. Biol. Evol. 30, 772–780. doi: 10.1093/molbev/mst010

PubMed Abstract | CrossRef Full Text | Google Scholar

Kimura, M., and Ohta, T. (1978). Stepwise mutation model and distribution of allelic frequencies in a finite population. Proc. Natl. Acad. Sci. U.S.A. 75, 2868–2872. doi: 10.1073/pnas.75.6.2868

PubMed Abstract | CrossRef Full Text | Google Scholar

Lande, R. (1999). “Extinction risks from anthropogenic, ecological and genetic factors,” in Genetics and the Extinction of Species, eds L. F. Landweber and A. P. Dobson (Princeton, NJ: Princeton University Press), 1–22.

Google Scholar

Langmead, B., Trapnell, C., Pop, M., and Salzberg, S. L. (2009). Ultrafast and memory-efficient alignment of short DNA sequences to the human genome. Genome Biol. 10:R25. doi: 10.1186/gb-2009-10-3-r25

PubMed Abstract | CrossRef Full Text | Google Scholar

Li, W., and Zhang, G. F. (2015). Population structure and spatial pattern of the endemic and endangered subtropical tree Parrotia subaequalis (Hamamelidaceae). Flora 212, 10–18. doi: 10.1016/j.flora.2015.02.002

CrossRef Full Text | Google Scholar

Li, J., and Tredici, P. D. (2008). The Chinese Parrotia: a sibling species of the Persian Parrotia. Arnoldia 66, 2–9.

Google Scholar

Li, J., Bogle, A. L., and Klein, A. S. (1999). Phylogenetic relationships of the Hamamelidaceae inferred from sequences of internal transcribed spacers (ITS) of nuclear ribosomal DNA. Am. J. Bot. 86, 1027–1037. doi: 10.2307/2656620

PubMed Abstract | CrossRef Full Text | Google Scholar

Li, P., Lu, R. S., Xu, W. Q., Ohi-Toma, T., Cai, M. Q., Qiu, Y. X., et al. (2017). Comparative genomics and phylogenomics of East Asian Tulips (Amana, Liliaceae). Front. Plant Sci. 8:451. doi: 10.3389/fpls.2017.00451

PubMed Abstract | CrossRef Full Text | Google Scholar

Li, Z. H., Xie, Y. S., Zhou, T., Jia, Y., He, Y. L., and Yang, J. (2015). The complete chloroplast genome sequence of Acer morrisonense (Aceraceae). Mitochondr. DNA 28, 1–2. doi: 10.3109/19401736.2015.1060439

PubMed Abstract | CrossRef Full Text | Google Scholar

Librado, P., and Rozas, J. (2009). DnaSP v5: a software for comprehensive analysis of DNA polymorphism data. Bioinformatics 25, 1451–1452. doi: 10.1093/bioinformatics/btp187

PubMed Abstract | CrossRef Full Text | Google Scholar

Lohse, M., Drechsel, O., Kahlau, S., and Bock, R. (2013). Organellar genome DRAW: a suite of tools for generating physical maps of plastid and mitochondrial genomes and visualizing expression data sets. Nucleic Acids Res. 5, 75–81. doi: 10.1093/nar/gkt289

CrossRef Full Text

Ma, Q., Du, Y. J., Chen, N., Zhang, L. Y., Li, J. H., and Fu, C. X. (2015). Phylogeography of Davidia involucrata (Davidiaceae) inferred from cpDNA haplotypes and nSSR data. Sys. Bot. 40, 796–810. doi: 10.1600/036364415X689267

CrossRef Full Text | Google Scholar

Mantel, N. (1967). Detection of disease clustering and a generalized regression approach. Cancer Res. 27, 209–220.

PubMed Abstract | Google Scholar

Mardis, E. R. (2008). Next-generation DNA sequencing methods. Annu. Rev. Genomics Hum. Genet. 9, 387–402. doi: 10.1146/annurev.genom.9.081307.164359

PubMed Abstract | CrossRef Full Text | Google Scholar

Nicholson, R. G. (1989). Parrotia persica: an ancient tree for modern landscapes. Arnoldia 49, 34–39.

Google Scholar

Nybom, H. (2004). Comparison of different nuclear DNA markers for estimating intraspecific genetic diversity in plants. Mol. Ecol. 13, 1143–1155. doi: 10.1111/j.1365-294X.2004.02141.x

PubMed Abstract | CrossRef Full Text | Google Scholar

Nybom, H., Weising, K., and Rotter, B. (2014). DNA fingerprinting in botany: past, present, future. Invest. Genet. 5:1. doi: 10.1186/2041-2223-5-1

PubMed Abstract | CrossRef Full Text | Google Scholar

Parchman, T. L., Geist, K. S., Grahnen, J. A., Benkman, C. W., and Buerkle, C. A. (2010). Transcriptome sequencing in an ecologically important tree species: assembly, annotation, and marker discovery. BMC Genomics 11:180. doi: 10.1186/1471-2164-11-180

PubMed Abstract | CrossRef Full Text | Google Scholar

Peakall, R., and Smouse, P. E. (2006). GenAlex 6: genetic analysis in population genetic software for teaching and research. Mol. Ecol. Res. 6, 288–295. doi: 10.1111/j.1471-8286.2005.01155.x

CrossRef Full Text | Google Scholar

Perdereau, A. C., Kelleher, C. T., Douglas, G. C., and Hodkinson, T. R. (2014). High levels of gene flow and genetic diversity in Irish populations of Salix caprea L. inferred from chloroplast and nuclear SSR markers. BMC Plant Biol. 14:202. doi: 10.1186/s12870-014-0202-x

PubMed Abstract | CrossRef Full Text | Google Scholar

Petit, R. J., Duminil, J., Fineschi, S., Hampe, A., Salvini, D., and Vendramin, G. G. (2005). Invited review: comparative organization of chloroplast, mitochondrial and nuclear diversity in plant populations. Mol. Ecol. 14, 689–701. doi: 10.1111/j.1365-294X.2004.02410.x

CrossRef Full Text | Google Scholar

Petit, R. J., El Mousadik, A., and Pons, O. (1998). Identifying populations for conservation on the basis of genetic markers. Conserv. Biol. 12, 844–855. doi: 10.1046/j.1523-1739.1998.96489.x

CrossRef Full Text | Google Scholar

Pons, O., and Petit, R. J. (1996). Measuring and testing genetic differentiation with ordered versus unordered alleles. Genetics 144, 1237–1245.

PubMed Abstract | Google Scholar

Pritchard, J. K., Stephens, M., and Donnelly, P. (2000). Inference of population structure using multilocus genotype data. Genetics 155, 945–959. doi: 10.1186/2041-2223-4-22

PubMed Abstract | CrossRef Full Text | Google Scholar

Qiu, Y. X., Guan, B. C., Fu, C. X., and Comes, H. P. (2009). Did glacials and/or interglacials promote allopatric incipient speciation in East Asian temperate plants? Phylogeographic and coalescent analyses on refugial isolation and divergence in Dysosma versipellis. Mol. Phylogenet. Evol. 51, 281–293. doi: 10.1016/j.ympev.2009.01.016

PubMed Abstract | CrossRef Full Text | Google Scholar

Ren, G., and Beug, H. J. (2002). Mapping Holocene pollen data and vegetation of China. Quat. Sci. Rev. 21, 1395–1422. doi: 10.1016/S0277-3791(01)00119-6

CrossRef Full Text | Google Scholar

Rousset, F. (2008). Genepop 007: a complete re-implementation of the genepop software for Windows and Linux. Mol. Ecol. Res. 8, 103–106. doi: 10.1111/j.1471-8286.2007.01931.x

CrossRef Full Text | Google Scholar

Schattner, P., Brooks, A. N., and Lowe, T. M. (2005). The tRNAscan-SE, snoscan and snoGPS web servers for the detection of tRNAs and snoRNAs. Nucleic Acids Res. 33, W686–W689. doi: 10.1093/nar/gki366

PubMed Abstract | CrossRef Full Text | Google Scholar

Sefidi, K., Copenheaver, C. A., Kakavand, M., and Behjou, F. K. (2014). Structural diversity within mature forests in northern Iran: a case study from a relic population of Persian ironwood (Parrotia persica CA Meyer). Forest Sci. 16, 258–265. doi: 10.5849/forsci.13-096

CrossRef Full Text | Google Scholar

Sefidi, K., Mohadjer, M. R. M., Etemad, V., and Copenheaver, C. A. (2011). Stand characteristics and distribution of a relict population of Persian ironwood (Parrotia persica C. A. Meyer) in Northern Iran? Flora 206, 418–422. doi: 10.1016/j.flora.2010.11.005

CrossRef Full Text | Google Scholar

Sharp, P. M., and Li, W. H. (1987). The codon adaptation index: a measure of directional synonymous codon usage bias, and its potential applications. Nucleic Acids Res. 15, 1281–1295. doi: 10.1093/nar/15.3.1281

PubMed Abstract | CrossRef Full Text | Google Scholar

Slatkin, M. (1995). A measure of population subdivision based on microsatellite allele frequencies. Genetics 139, 457–462.

PubMed Abstract | Google Scholar

Squirrell, J., Hollingsworth, P. M., Woodhead, M., Russell, J., Lowe, A. J., and Gibby, M. (2003). How much effort is required to isolate nuclear microsatellites from plants? Mol. Ecol. 12, 1339–1348. doi: 10.1046/j.1365-294X.2003.01825.x

PubMed Abstract | CrossRef Full Text | Google Scholar

Stoll, A., Harpke, D., Schütte, C., Stefanczyk, N., Brandt, R., Blattner, F. R., et al. (2017). Development of microsatellite markers and assembly of the plastid genome in Cistanthe longiscapa (Montiaceae) based on low-coverage whole genome sequencing. PLoS ONE 12:e0178402. doi: 10.1371/journal.pone.0178402

PubMed Abstract | CrossRef Full Text | Google Scholar

Sun, J., Wang, Y., and Zeng, Y. (2005). Characteristics of the soil seed banks in degenerated grasslands under grazing and grazing suspension. Acta Bot. Boreali Occidentalia Sin. 25, 2035–2042. doi: 10.3321/j.issn:1000-4025.2005.10.018

CrossRef Full Text | Google Scholar

Thiel, T., Michalek, W., Varshney, R. K., and Graner, A. (2003). Exploiting EST databases for the development and characterization of gene-derived SSR-markers in barley (Hordeum vulgare). Theor. Appl. Genet. 106, 411–422. doi: 10.1007/s00122-002-1031-0

PubMed Abstract | CrossRef Full Text | Google Scholar

Turlure, C., Vandewoestijne, S., and Baguette, M. (2014). Conservation genetics of a threatened butterfly: comparison of allozymes, RAPDs and microsatellites. BMC Genetics 15:114. doi: 10.1186/s12863-014-0114-7

PubMed Abstract | CrossRef Full Text | Google Scholar

Varvio, S. L., Chakraborty, R., and Nei, M. (1986). Genetic variation in subdivided populations and conservation genetics. Heredity 57, 189–198. doi: 10.1038/hdy.1986.109

PubMed Abstract | CrossRef Full Text | Google Scholar

Wang, S., and Xie, Y. (2004). China Species Red List. Beijing: Higher Education Press.

Wyman, S. K., Jansen, R. K., and Boore, J. L. (2004). Automatic annotation of organellar genomes with dogma. Bioinformatics 20:3252. doi: 10.1093/bioinformatics/bth352

PubMed Abstract | CrossRef Full Text | Google Scholar

Xia, E. H., Yao, Q. Y., Zhang, H. B., Jiang, J. J., Zhang, L. P., and Gao, L. Z. (2016). CandiSSR: an efficient pipeline used for identifying candidate polymorphic SSRs based on multiple assembled sequences. Front. Plant Sci. 6:1171. doi: 10.3389/fpls.2015.01171

PubMed Abstract | CrossRef Full Text | Google Scholar

Yan, C., Wang, Z. S., An, S. Q., Chen, S. N., Wei, N., and Lu, X. M. (2008). Differences in photosynthetic capacity among different diameter-classes of Parrotia subaequalis populations and their implication to regeneration limitation. Acta Ecol. Sin. 28, 4153–4161.

Yang, J., Yue, M., Niu, C., Ma, X. F., and Li, Z. H. (2017). Comparative analysis of the complete chloroplast genome of four endangered herbals of Notopterygium. Genes 8:124. doi: 10.3390/genes8040124

PubMed Abstract | CrossRef Full Text | Google Scholar

Yang, Z. (1994). Maximum likelihood phylogenetic estimation from DNA sequences with variable rates over sites: approximate methods. J. Mol. Evol. 39, 306–314. doi: 10.1007/BF00160154

PubMed Abstract | CrossRef Full Text | Google Scholar

Yao, Z. G., Wang, Z. S., Yan, C., Dong, Z. Y., Xu, W. X., and Wei, N. (2010). The photosynthesis response to different light intensity for the endangered plant Parrotia subaequalis. J. Nanjing Forestry Univer. 34, 83–88. doi: 10.3969/j.issn.1000-2006.2010.03.017

CrossRef Full Text | Google Scholar

Yi, S., Saito, Y., Zhao, Q., and Wang, P. (2003). Vegetation and climate changes in the Changjiang (Yangtze River) Delta, China, during the past 13,000 years inferred from pollen records. Quaternary Sci. Rev. 22, 1501–1519. doi: 10.1016/S0277-3791(03)00080-5

CrossRef Full Text | Google Scholar

Yin, A., and Harrison, T. M. (2000). Geologic evolution of the himalayan-tibetan orogen. Annu. Rev. Earth Planet. Sci. 28, 211–280. doi: 10.1146/annurev.earth.28.1.211

CrossRef Full Text | Google Scholar

Young, A., Boyle, T., and Brown, T. (1996). The population genetic consequences of habitat fragmentation for plants. Trends Ecol. Evol. 11, 413–418. doi: 10.1016/0169-5347(96)10045-8

PubMed Abstract | CrossRef Full Text | Google Scholar

Zalapa, J. E., Brunet, J., and Guries, R. P. (2008). Genetic diversity and relationships among Dutch elm disease tolerant Ulmus pumila L. accessions from China. Genome 51, 492–500. doi: 10.1139/G08-034

PubMed Abstract | CrossRef Full Text | Google Scholar

Zane, L., Bargelloni, L., and Patarnello, T. (2002). Strategies for microsatellite isolation: a review. Mol. Ecol. 11, 1–16. doi: 10.1046/j.0962-1083.2001.01418.x

PubMed Abstract | CrossRef Full Text | Google Scholar

Zhong, T., Zhao, G., Chu, J., Guo, X., and Genyou, L. I. (2014). A study on photosynthetic physiological characteristics of six rare and endangered species. Agr. Sci. Tech. 8, 1265–1270. doi: 10.3969/j.issn.1009-4229.2014.08.005

CrossRef Full Text | Google Scholar

Keywords: Parrotia subaequalis, palaeoendemic tree, chloroplast genome, microsatellites, fragmentation, conservation genetics

Citation: Zhang Y-Y, Shi E, Yang Z-P, Geng Q-F, Qiu Y-X and Wang Z-S (2018) Development and Application of Genomic Resources in an Endangered Palaeoendemic Tree, Parrotia subaequalis (Hamamelidaceae) From Eastern China. Front. Plant Sci. 9:246. doi: 10.3389/fpls.2018.00246

Received: 16 November 2017; Accepted: 12 February 2018;
Published: 01 March 2018.

Edited by:

Renchao Zhou, Sun Yat-sen University, China

Reviewed by:

Zhonghu Li, Northwest University, China
Andrea Coppi, Università degli Studi di Firenze, Italy

Copyright © 2018 Zhang, Shi, Yang, Geng, Qiu and Wang. This is an open-access article distributed under the terms of the Creative Commons Attribution License (CC BY). The use, distribution or reproduction in other forums is permitted, provided the original author(s) and the copyright owner are credited and that the original publication in this journal is cited, in accordance with accepted academic practice. No use, distribution or reproduction is permitted which does not comply with these terms.

*Correspondence: Ying-Xiong Qiu, cXl4aGVyb0B6anUuZWR1LmNu
Zhong-Sheng Wang, d2FuZ3pzQG5qdS5lZHUuY24=

Disclaimer: All claims expressed in this article are solely those of the authors and do not necessarily represent those of their affiliated organizations, or those of the publisher, the editors and the reviewers. Any product that may be evaluated in this article or claim that may be made by its manufacturer is not guaranteed or endorsed by the publisher.