Qi An
Yuanheng Feng1,2,3- 1Guangxi Key Laboratory of Superior Timber Trees Resource Cultivation, Guangxi Zhuang Autonomous Region Forestry Research Institute, Nanning, Guangxi, China
- 2Masson Pine Engineering Technology Research Center of Guangxi, Nanning, Guangxi, China
- 3Key Laboratory of Central South Fast-growing Timber Cultivation of Forestry Ministry of China, Nanning, Guangxi, China
Background: This study aimed at exploring unique population genetic characteristics of Albizia odoratissima (Linn. f) Benth on Hainan Island to provide a scientific basis for its rational utilization and protection.
Methods: It analyzed the genetic diversity and structure of 280 individuals from 10 subpopulations of A. odoratissima from Hainan Island and Baise City using 16 expression sequence markers - simple sequence repeat markers.
Results: The genetic diversity of Hainan population (I = 0.7290, He = 0.4483) was lower than that of the Baise population (I = 0.8722, He = 0.5121). Compared with the Baise population (Nm = 2.0709, FST = 0.1077), the Hainan Island population (Nm = 1.7519, FST = 0.1249) exhibited lower gene flow and higher degree of genetic differentiation. Molecular variance and genetic differentiation analyses showed that the main variation originated from individuals within the subpopulation. There were significant differences in the genetic structure between Hainan and Baise populations. It grouped according to geographical distance, consistent with the Mantel test results (R2 = 0.77, p = 0.001). In conclusion, the genetic diversity of the island A. odoratissima population was lower than that distributed on land, the two populations exhibited obvious genetic structure differences. Both the degrees of inbreeding and genetic differentiation were higher in the island population than in the land population.
Introduction
Albizia odoratissima (Linn. f) Benth is a perennial evergreen tree of Albizia Durazz that belongs to Leguminosae sp., Mimosaceae, commonly found in low-altitude sparse forests (Yuan et al., 2011; Ai, 2016). The plant has no spines, the twigs are initially puberulous; leaflet oblong, apex blunt; the flowers are sessile, yellowish, fragrant, capitulum arranged terminal, open panicles; pod flat, oblong, with 6-12 seeds; flowering period from April to July, fruit period from June to October. This tree species has excellent quality, rapid growth, medicinal value, is a rare fast-growing precious timber tree species (Liang, 2012; Liang, 2020; Wei et al., 2020). However, the A. odoratissima distribution area is shrinking due to human interference, among other reasons, and the threat of endangerment is becoming increasingly serious (Luo et al., 2020). Therefore, population genetics research is needed to effectively protect this precious species.
As a typical monsoonal evergreen broad-leaved forest species, A. odoratissima is mainly distributed in Guangxi, Yunnan, Guizhou, Guangdong, Sichuan, Hainan, and other provinces in China, it had also been reported in India, Vietnam, Malaysia, and other countries (Wei et al., 2020). In China, the natural population of A. odoratissima shows an “island-like” discontinuous distribution, spanning the South subtropical and tropical climate zones. It’s distribution area covers a variety of landforms, such as the Yunnan-Guizhou Plateau, Nanling Mountain, the Hilly area of South China, and Hainan Island Mountain. This distribution pattern is highly likely to hinder the gene exchange between A. odoratissima populations in different regions, resulting in rich genetic variation between them.
Hainan Island is the second-largest island in China. It was completely separated from the Asian mainland owing to the formation of the Qiongzhou Strait in the middle Pleistocene. Since then, it has faced the southernmost end of mainland China across the sea. With an area of 35400 km2 (Wang et al., 2022), the island has a tropical monsoon climate, rich rainfall, and sufficient heat. Known as a “species gene pool” and “natural museum,” it is also the most special distribution area of A. odoratissima. The Hainan population is the only A. odoratissima group distributed in the tropical areas of China. As a typical “continental island,” Hainan Island is an ideal place to study species genetics and evolution (Del Valle et al., 2020). For species with intermittent island and land distributions, the limited island area, long-term geographical isolation, and greatly different climatic conditions lead to obvious genetic differentiation and phenotypic differences between the populations on the island and those on the mainland during evolution. From the formation of unique or even excellent germplasm resources, research different populations of the same species distributed on both islands and the mainland can provide important clues for the intraspecific evolution that determines the early differentiation and recent spread of species (Fernández-Mazuecos and Vargas, 2011).
In general, in order to research the genetic differences between island populations and mainland populations, it is more appropriate to compare the populations in the land distribution area closest to the island. In addition, comparative studies can also be conducted using the core distribution area or origin center area populations on the mainland. The current survey results showed that there is no large-scale distribution of A. odoratissima populations in the Leizhou Peninsula which is closest to Hainan Islandand and the coastal areas of southern China. The Baise population, located in the northwest of Guangxi, China, is adjacent to the two distribution areas of eastern Yunnan and southwest Guizhou, is the closest to Hainan Island among the large-scale distribution areas of A. odoratissima found so far. The geographical distribution area of Baise is 36,000 km2 (Liu et al., 2017), which is similar to Hainan Island. From the perspective of biogeography, Hainan Island was once connected to Guangxi, China (Zhu, 2016). Therefore, selecting the population of Baise area as the control experimental material has good representativeness.
The research of genetic diversity is of great significance for revealing the evolutionary history of species, evaluating their survival status, and predicting their future development trends. At present, research on population genetics of species mostly relies on experimental materials from island or terrestrial populations, while there are relatively few populations from both islands and continents. As a species of important research value distributed on both islands and land, the study of population genetics of A. odoratissima was still limited. Simple sequence repeat (SSR) molecular marker has the advantages of abundant quantity, codominant inheritance, high polymorphism, high specificity, high universality and good repeatability (Garrido-Cardenas et al., 2018). According to their origin, they can be divided into genomic SSR (G-SSR) and expression sequence label SSR (EST-SSR). Compared with G-SSR, EST-SSR has the advantages of simple development process, low cost, high sequence conservation, and inter-species transferability (Manoj et al., 2021). The EST-SSR originates from transcription regions, which is often linked to functional genes, it has obvious advantages in population genetics research and marker-assisted breeding. In view of this, it used EST-SSR molecular markers as a tool to comprehensively evaluate the genetic diversity and structure of A. odoratissima populations in four regions of Hainan Island. Baise population as a representative of terrestrial population. To provide reference for the genetic evaluation of this germplasm resource and the development of high-quality genetic resources.
Materials and methods
Experimental materials of A. odoratissima population
Based on relevant literature, the natural population of A. odoratissima is mainly distributed in the west and southwest Hainan Province (Figure 1). Yingge Ling, Sanya City, Jianfengling, and Bawangling of Hainan Island were selected as the locations for test materials collection, representing the east, south, west, and north of the main distribution area of A. odoratissima. The population of Baise Prefecture in Guangxi were collected from six regions, including Youjiang District, Xilin County, Tianlin County, Tiandong County, Longlin County, and Leye County. At each collection site, according to the standard distance between plants of no less than 30 m, individual plants with normal growth, no obvious defects, diseases, and pests were selected. The top tender tree leaves from the current year were collected, silica gel was used to dry and preserve them. The collection sites for the experimental materials were evenly distributed, showing good representation. A total of 280 samples were collected from each of the ten sites (Table 1).
Figure 1 Geographical distribution of the plant materials.
Table 1 Basic information of natural A. odoratissima populations.
Extraction of genomic DNA from A. odoratissima
Fresh plant tissues (50 – 100 mg) were ground into a powder in liquid nitrogen, and genomic DNA was extracted using an EZ – 10 Spin Column Plant Genomic DNA Purification Kit, which Providing by Sangon Biotech (Shanghai) Co., Ltd.
SSR (simple sequence repeat)-PCR (polymerase chain reaction) amplification and detection of amplification products
Transcriptome sequencing was performed on A. odoratissima leaves. Considering the RNA-seq results, Novofinder software was used to search for SSR loci in the transcriptome Universal Gene of A. odoratissima. The SSR loci were screened following these criteria: sequence length: 18-26 bp and number of nucleotide repeats ≥ 5. 16 pairs of EST-SSR primers were selected for this study (Table 2). All primers were synthesized by Guangzhou Ige Biotechnology LTD, Guangzhou, China.
Table 2 EST-SSR primer information of A. odoratissima.
The PCR system was 10.00 μL, including template DNA (1.00 μL; 50 ng/stock), 10 × buffer (1.00 μL; 1 × Buffer), dNTPs (including Mg2+) (0.20 μL; 0.2 mmol/L), positive and negative primers (0.25 μL; 0.25 μmol/L), Taq DNA enzyme (0.10 μL 0.25 U/stock), and ddH2O (7.20 μL). The PCR procedure was as follows: 94°C pre-denaturation for 4 min; 25 cycles of 94°C denaturation for 15 s, 58°C annealing for 15 s, 72°C extension for 30 s; extension at 72°C for 20 min; and storage at 12°C. The amplified products were separated using 8% polyacrylamide gel electrophoresis.
Data analysis
POPGENE 32 (Yeh et al., 1999) software was used to calculate the following genetic parameters: average number of alleles (A), observed number of alleles (Na) (Fang et al., 2018), effective number of alleles (Ne) (Hartl and Clark, 1989), Shannon’s Information Index (I), and Nei’s gene diversity index (H) (Shannon and Weaver, 1949; Shannon et al., 1950), observed heterozygosity (Ho), expected heterozygosity (He) (Nei, 1973), and Wright’s fixation index (F) could be obtained from the formula 1-FIT = (1-FIS) (1-FST), used to determine FIS, FIT, and genetic differentiation index (FST) (Wright, 1978). Nei’s standard genetic distance (GD) (Nei, 1972), genetic identity, gene flow (Nm) (Slatkin and Barton, 1989), and genetic differentiation coefficient (GST).
STRUCTURE 2.3.4 (Pritchard et al., 2000) software was used to perform Bayesian clustering analysis on individuals from different populations. Subpopulation grouping was determined based on the optimal K value obtained via STRUCTURE Harvester (https://taylor0.biology.ucla.edu/structureHarvester) analysis.
The polymorphism information content (PIC) for each locus was calculated using the online program PIC calc (Botstein et al., 1980).
Arlequin 3.5 (Excoffier and Lischer, 2010) software was used to analyze the molecular variation at different levels within and between populations.
Mantel test was performed using GenAlEx 6.5 (Peakall and Smouse, 2012). The Mantel test was used to assess the correlation between geographic distance and genetic distance.
The UPGMA (unweighted pair-group method with arithmetic means) clustering tree was constructed using NTSYS PC (Rohlf, 2000) software based on Nei’s standard genetic distance.
The ape (Paradis and Schliep, 2019) and ggplot 2 (Wickham, 2016) packages of R 2.3.4 were analyzed for principal coordinates analysis (PCoA).
Results
Screening of EST-SSR primers for A. odoratissima
The results of the previous study showed that among the 243 pairs of developed primers of A. odoratissima, the effective amplification rate in Albizia odoratissima Albizia procera, Albizzia falcataria, Acacia melanoxylon and Erythrophloeum fordii was 63.79%, 33.75%, 45.68%, 41.56% and 14.81% respectively, the polymorphism ratio in them was 23.87%, 12.20%, 9.01%, 3.96% and 2.78% respectively (An et al., 2022). A total of 16 materials were randomly selected from various subpopulations of A. odoratissima in Guangxi and Hainan, the polymorphisms of 155 pairs of effective primers were re-detected. Finally, 16 pairs of primers with good generality, high polymorphism and clear bands were selected for the genetic diversity study of the germplasm resources of A. odoratissima. The polymorphism information content was analyzed, as shown in Table 2. The effective amplification rate of 16 selected primers in Albizia procera, Albizia falcataria and Acacia melanoxylon was 50%, and the proportion of polymorphic primers in effective primers was 50%, 12.5% and 12.50%, respectively. Only one pair of primers can have effective amplification rate and no polymorphism in Erythrophleum fordii. It can be seen that the polymorphic information content of the 16 SSR primers used in this experiment ranged from 0.08 to 0.70, with an average value of 0.48. The 16 pairs of primers selected were all medium-high polymorphic primers, except for AO-194, which was a low polymorphic primer. Indicating that the screened primers could be used for the genetic diversity study of the germplasm resources of A. odoratissima. It had certain universality in Albizia procera, Albizia falcataria, Acacia melanoxylon and Erythrophleum fordii.
Genetic diversity of A. odoratissima population
A total of 52 alleles were amplified by 16 SSR loci in 280 individuals from 10 A. odoratissima subpopulations (Table 3), the number of alleles detected at each site ranged from 2.00 to 5.00.
Table 3 Genetic diversity in 10 populations of A. odoratissima.
In terms of gene abundance (Table 3), 43 and 52 alleles were detected at 16 SSR loci in Hainan and Baise populations, respectively. Compared with the Baise population, the Hainan population had allele deletions at 50.00% of loci and no specific alleles (Table 4). The average number of observed alleles (Na) in Hainan population was 2.69, which was 17.23% lower than that in Baise population. The average number of effective alleles (Ne) in Hainan population was 1.96, which was 12.50% lower than that in the Baise population. To some extent, it showed that after geographical isolation from the mainland, Hainan population were greatly limited in introducing new alleles through gene communication.
Table 4 Allele frequencies of A. odoratissima populations from Hainan and Baise.
The average He, Ho, I, and H values of the Hainan A. odoratissima population were 0.4483, 0.2075, 0.7290, and 0.4452, respectively (Table 3). which were 87.54%, 74.10%, 83.58%, and 87.16% lower than those of Baise population, respectively. Thus, genetic complexity was lower in the Hainan population than in the Baise population. In the four subpopulations of Hainan, Ho ranged from 0.1869 to 0.2246, He ranged from 0.3820 to 0.4150, I ranged from 0.6088 to 0.6537, and H ranged from 0.3706 to 0.4021. In the six subpopulations of Baise, Ho ranged from 0.2542 to 0.3737, He ranged from 0.4436 to 0.4855, I ranged from 0.7261 to 0.7927, and H ranged from 0.4357 to 0.4765. The He, Ho, I and H values of the four Hainan subgroups were all lower than those of the six subgroups of Baise.
There were certain differences in allele frequencies between the two populations at different loci (Table 4), with a maximum of 67.84%, indicating that the two populations have different evolutionary directions due to differences in natural environment.
Population genetic differentiation and genetic variation
The Nm (0.9976) between the two populations of A. odoratissima was lower than that of Hainan (Nm=1.7559) and Baise (Nm=2.0709), respectively. This indicates that gene exchange between the two populations was low, but the degree of gene exchange within the population was relatively high.
The Ho values of both populations were lower than the He value, the inbreeding coefficients of each subgroup were greater than zero, indicating that both populations had a certain degree of homozygosity and inbreeding. Among them, the inbreeding coefficient of the GX-3 subgroup was close to zero, showing that it was closest to the Hardy Weinberg equilibrium.
From the F statistical data (Table 5), it canould be seen that the FST and GST values of the A. odoratissima population in Hainan Province were 0.1249 and 0.1000, respectively, while the population in Baise City were 0.1077 and 0.0980, respectively. Therefore, the genetic differentiation of the Hainan population was higher than that of the Baise population. The genetic variation of the two populations mainly comes from subpopulations.
Table 5 Analysis of molecular variance (AMOVA) for population of A. odoratissima.
Further analysis of variance was performed at the population, subpopulation and individual levels (Table 5). Both populations exhibit within individuals > among individuals Within populations> among populations. It indicated that the genetic variation of A. odoratissima mainly came from the variation between individuals.
Genetic structure of A. odoratissima population
The genetic structure of A. odoratissima was predicted using STRUCTURE software. When K = 2, the ΔK value was the highest (Figures 2A, B), indicating that it was most reasonable to divide 280 samples into two groups of independent evolutionary units (Figure 2C). Based on the Q value, it also plotted the cluster member proportion of each subpopulation when K = 2. The four Hainan subpopulations were composed of individuals with red clusters, and the six Baise subpopulations were composed of individuals with green clusters. The results were consistent with those of UPGMA cluster analysis (Figure 3A) and PCoA (Figure 3B) based on GD. This shows obvious differences in genetic structure between the Hainan and Baise populations of A. odoratissima. It further analyzed the correlation between GD and geographic distance using Mantel test (Figure 4). GD was significantly correlated with geographical distance (R2 = 0.77, p = 0.001), indicating an obvious geographical origin structure or main distance isolation among the investigated populations.
Figure 2 Population genetic structure. (A) Mean log-likelihood [Ln(K)±SD] against the number of K; (B) Relations between the rational groups number K and Estimated value ΔK. (C) Genetic structural plot of 10 A. odoratissima subpopulations based on structure analysis (Each individual is represented by a single vertical bar, which is partitioned into two different colors).
Figure 3 (A) Genetic divergence among 10 subpopulations of A. odoratissima based on UPGMA clustering analysis. (B) Principal coordinate analysis (PCoA) of 10 A. odoratissima subpopulations.
Figure 4 Mantel between genetic distance and geographical distance of 10 A. odoratissima subpopulations.
Discussion
Genetic diversity of the A. odoratissima population
The genetic diversity of trees directly affects their evolutionary potential and adaptability to environmental changes. Higher genetic diversity indicates stronger evolutionary potential and ability to match the environment (Xia, 1999; Booy et al., 2000). The genetic diversity of a species is closely related to its geographical distribution, mating system, gene flow, genetic drift, and human interference (Jaenike, 1973; Fan et al., 2019; Jiang et al., 2019).
This study revealed that the genetic abundance and complexity of the A. odoratissima population in Hainan were lower than those of the Baise population. This phenomenon that the genetic diversity of island population was lower than that of land population also exists in some species such as Mussaenda kwangtungensis (Guangdong) (Hufford et al., 2014; Shi et al., 2020; Hunt et al., 2022). Long-term geographic isolation is probably the main reason explaining the lower genetic diversity of the Hainan population. This phenomenon is related to factors, such as Nm blocking, genetic drift, and small population bottleneck effect allele loss (Avise, 1996; Rieseberg and Swensen, 1996; Balmford et al., 1997).
Compared to the Baise population, allele deletion occurred in more than half of the loci in the Hainan population. It found that the two groups had lower levels of genetic communication. Indicating that the existence of geographical isolation makes it difficult for Hainan population to acquire new genes through gene exchange from land population. In additionthe, population size on Hainan Island was small, which may complicate gene mutation fixing in this population. The geographical distribution area of Baise population is close to Hainan, located at the junction of Guangxi, Guizhou, and Yunnan provinces in China, adjacent to Vietnam to the south. The population size of Baise was large, there were fewer gene exchange barriers between nearby populations, which helps to accept new genes through gene exchange and fix mutated genes. It may also be the main factor why a unique haplotype was not found in the Hainan population. It is also the reason that genetic diversity of Hainan population is lower than that of Baise population.
The genetic diversity of species dominated by outbreeding is generally higher than that of species dominated by self - breeding, the inter - population variation of the former accounts for more than 50% of the total variation (Gao and Li, 2008; Lu et al., 2021). The genetic diversity of the total population (Ho = 0.2615, He = 0.5366) was higher than that of wild soybean (Ho = 0.0310, He = 0.4260) (He et al., 2012), as well as the average of the major self - crossing species (Ho = 0.1200, He = 0.3030) (Hamrick and Godt, 1996). In addition, 18.38% of the genetic variation existed among the subpopulations, it can be reasonably inferred that the breeding system was dominated by out - crossing. The blossoms of A. odoratissima are light yellow, fragrant, terminal, and dispersed panicles, conforming to the characteristics of insect pollination. Affected by the flight distance of insects, the ability of the wild population to spread pollen among subpopulations was limited by distance, terrain, and other factors (Kwon and Morden, 2002).The Hainan population is more about gene exchange among subpopulations on the island, the richness of genetic diversity is lower than that of the Baise population located at the border of the three provinces and in the core distribution area.
Genetic differentiation and genetic structure of the A. odoratissima population
The genetic structure of a population is the result of the interaction between ecological and genetic processes. Related research is of great significance for understanding population genetic characteristics and dynamics, and developing effective protection measures (Leberg, 1990; Cheng et al., 2020). There were significant differences in genetic structure between the Hainan and Baise populations, the genetic variation mainly came from within the population. The coefficient of genetic differentiation between the two populations (FST = 0.2004) was significantly higher than that of Hainan and Baise populations (FST = 0.1249 and FST = 0.1077). In the cluster analysis, six Baise subpopulations were grouped into one cluster, and four Hainan subpopulations were grouped into another cluster. Hainan had different geographical, topographic, water, thermal conditions from Baise. Under the effect of selection, the Hainan population had taken a different evolutionary direction from that of the Baise population in order to accommodative the local environment. The existence of geographical isolation resulted in genetic differentiation between Hainan and mainland populations, while the outcrossing breeding system and the characteristics of insect pollination further intensified the genetic differentiation between island and land populations. In the wild, the A. odoratissima are mainly propagated by seeds, when the seeds mature, the pods crack. Affected by seed weight, wind speed, and media, the seeds generally fall not far from the mother plants, can also spread to further places along rivers. Nevertheless, the long-term geographical isolation makes it difficult for the Hainan population to rely on water flow or some media to break through the geographical isolation barrier and smoothly communicate genes with the land population. The degree of pollen dispersal among long-distance subpopulations was also lower, therefore, the Hainan population is more about gene exchange among subpopulations on the island. The isolation of the sea resulted in a lower degree of gene exchange between island and land populations than within the population, making the genetic differentiation between island and land populations more pronounced (Wright, 1951; Grant, 1986; Manel, 2003; Saro et al., 2015).
In addition, the degree of inbreeding and genetic differentiation were higher in Hainan than in Baise, consistent with the conclusion of Chen et al (Chen et al., 2008). on Ficus pumila. The small size and scattered distribution of the natural A. odoratissima population may be underlying reasons for inbreeding in this population. The resources of A. odoratissima were abundant in Hainan, their distribution range was limited, and the population is smaller than that in Baise. There are many tall mountains on the island, creating a mountain isolation effect greater than natural transportation effect (Frankham, 1998). It prevents gene exchange among subpopulations and facilitating inbreeding between individuals. The existence of inbreeding reduces population heterozygosity and further increases genetic differentiation of the populations.
Conservation and utilization of A. odoratissima genetic resources
Some alleles were found to exist in only a few subpopulations, there was abundant genetic variation among individuals within the populations. However, due to human interference, the number of its natural population is decreasing dramatically. In view of this, it can further expand the select range of superior trees, increase their number, and establish seed orchards with a wider genetic basis than the original. Establishing seed orchards with a wider genetic basis can better preserve A. odoratissima resources. Seeds with better genetic quality can also be produced to establish high -quality A. odoratissima plantations to meet production needs and increase the breeding value of high-quality genetic resources. In addition, the study found that different subpopulations had different levels of genetic diversity, there were rare alleles with allele frequencies less than 0.01 in the A. odoratissima population, indicating that the rare alleles carrying certain genetic variants in the population were likely to exist in only one or a few individuals, these genetic variants were facing loss. Therefore, it is necessary to select some subpopulations with high genetic diversity and establish nature reserves to protect them in situ.
Conclusions
This article used EST-SSR molecular markers as a research tool to comprehensively evaluate the genetic diversity and structure of two A. odoratissima populations from Hainan Island and Baise, Guangxi, China. The genetic variation of the population mainly comes from individual to individual. The A. odoratissima population distributed in Hainan Island has lower genetic diversity than the Baise population, the degree of genetic differentiation. The Hainan Island A. odoratissima population had a 50% loss of alleles compared to the Baise population, and there are no specific alleles. There were significant differences in the genetic structure of the two populations, with different evolutionary directions. These findings have improved our current understanding of the genetic diversity and population genetic structure of A. odoratissima. It can provide a theoretical basis for the improvement of seed orchard, further development, utilization, and protection of this species.
Data availability statement
The datasets presented in this study can be found in onlinerepositories. The names of the repository/repositories and accessionnumber(s) can be found in the article/Supplementary Material.
Author contributions
QA: Conceptualization, Data curation, Formal analysis, Investigation, Validation, Writing – original draft, Writing – review & editing. YF: Conceptualization, Methodology, Validation, Writing – review & editing. ZY: Conceptualization, Data curation, Funding acquisition, Project administration, Validation, Writing – review & editing. LH: Investigation, Validation, Writing – review & editing. DW: Investigation, Validation, Writing – review & editing. GG: Formal analysis, Methodology, Writing – review & editing.
Funding
The author(s) declare financial support was received for the research, authorship, and/or publication of this article. This work was supported by Guangxi Science and Technology Base and Special Funds for Talents (AD19254004), Special Program of Bagui Scholar (2019A026) and National “Thirteenth Five-Year” Key R&D Project (2017YFD0600303).
Acknowledgments
We appreciate senior engineer Jie Jia and engineer Qunfeng Luo for their seedling cultivation assistance, and appreciate Bailin Forest Farm in Baise, Guangxi, China for collection of germplasm resources assistance.
Conflict of interest
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.
Publisher’s note
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.
Supplementary material
The Supplementary Material for this article can be found online at: https://www.frontiersin.org/articles/10.3389/fpls.2024.1369409/full#supplementary-material
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Keywords: Albizia odoratissima, EST-SSR molecular markers, genetic diversity, genetic structure, Hainan Island
Citation: An Q, Feng Y, Yang Z, Hu L, Wu D and Gong G (2024) Differences in Albizia odoratissima genetic diversity between Hainan Island and mainland populations in China. Front. Plant Sci. 15:1369409. doi: 10.3389/fpls.2024.1369409
Received: 12 January 2024; Accepted: 02 April 2024;
Published: 24 April 2024.
Edited by:
Xiyang Zhao, Jilin Agricultural University, ChinaReviewed by:
Kundapura Ravishankar, Indian Institute of Horticultural Research (ICAR), IndiaYuepeng Song, Beijing Forestry University, China
Xiang Li, Ningxia University, China
Copyright © 2024 An, Feng, Yang, Hu, Wu and Gong. 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(s) 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: Zhangqi Yang, eWFuZ3poYW5ncWlAMTYzLmNvbQ==