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Algae > Volume 40(1); 2025 > Article
Song, Zhang, Du, Li, Shen, Lin, Hu, and Duan: Historical climate change influenced the phylogeographical patterns of the brown alga Colpomenia sinuosa in the southern China

ABSTRACT

Historical climate changes significantly influenced the phylogeographical patterns of intertidal macroalgae. The brown alga Colpomenia sinuosa was common in warmer waters worldwide, providing an ideal model for genetic diversity and distribution research. C. sinuosa has abundant biomass in the coastal South China Sea, which is a well-known hotspot on marine biodiversity. Here, we analyzed its population structure and demographic history using mitochondrial cox3, atp6, and chloroplast rbcL. We detected a genetic diversity pattern of high haplotype diversity and low nucleotide diversity at the intraspecific level, and our results revealed 2 main clades within C. sinuosa with obvious genetic differentiation among most populations. Furthermore, we detected 5 genetic lineages in concatenated dataset, and the regional isolation was regarded as dominating factor for genetic differentiation. The demographic history suggested that C. sinuosa was first diverged in late Oligocene, then underwent dynamic changes during the Pleistocene. Historical vicariance caused by Pleistocene glaciation events may account for present phylogeographic pattern. Moreover, ocean current and coastal topography of northern South China Sea might participate in shaping present genetic structure. Utilizing C. sinuosa as a model material, we suggested that Dongfang in southwestern Hainan and Sanya in southern Hainan should be regarded as independent management units and give priorities to seaweed resource conservation. In the future, we’ll enlarge our study range and sample collection, and further investigate the genetic distribution pattern of C. sinuosa at larger scale. Our study enriched insights into the historical glacial influences on seaweed phylogeographical patterns, and provided theoretical evidence for seaweed management of southern China.

INTRODUCTION

The historical climate oscillations are essential for the genetic differentiation and speciation of organisms (Avise 2000). In the age of Quaternary, the drastic climate change and sea level fluctuation caused noteworthy change in the coastal habitats, triggering off the huge impacts on the marine biodiversity distribution patterns (Hewitt 2000, Ni et al. 2014). In the last glacial period of Pleistocene stage, significant glacier expansion led to sea level dropping dramatically, contributing to the topographical transformation and coastal habitat fragmentation (Wang 1999, Clark and Mix 2002). Nevertheless, the surviving coastal marine organisms could preserve populations and diversity within separated refugia, and developed genetic differentiation due to long-term isolation (Stewart et al. 2010, Keppel et al. 2012). Generally, the current genetic makeup of populations and species can reflect past dynamics, aiding the investigation of evolutionary processes through present genetic imprints (Hewitt 2004).
As common marine plant worldwide, benthic macroalgae can provide food, reproduction substrate and shelter for other marine organisms (Hu and Fraser 2016). Many brown algae species (such as giant kelp, Sargassum and Fucales) could make up seaweed beds and ocean forests, which serve as important roles of habitat and carbon sequestration in the coastal marine ecosystem (Tano et al. 2017, Ortega et al. 2019). Moreover, the intertidal macroalgae can be more vulnerable to the marine environmental change due to the complex physical factors and heterogeneous habitat types (Hu and Fraser 2016). Numerous studies have documented that current seaweed flora may be significantly influenced by paleoclimate events and historical isolation (Hoarau et al. 2007, Zhang et al. 2019b, Song et al. 2021). Thus, the macroalgae can be considered as valuable materials to exploring how seaweed responded to the past climate change in the evolutionary history, which holds far-reaching ecological implications. Among rich studies of macroalgae diversity and evolutionary patterns, the question about seaweeds’ genetic response to Quaternary glacial climate changes still remain a hot topic for global researchers (Hoarau et al. 2007, Zhang et al. 2019b, Boo et al. 2023). Studying seaweed spatial genetic structure and population dynamics will be positive to explore its distribution regularities and adaptive evolution, and aids our understanding to manage and conserve the coastal seaweed resources.
As one of the largest worldwide marginal seas, the South China Sea is known as a marine biodiversity hotspot (Liu 2013). It is located in subtropical and tropical region in southern China, characterized by a typical tropical marine monsoon climate, integrating with complicated geological, hydrological and environmental conditions (Morton and Blackmore 2001, Sun 2016). Many researches have demonstrated that present distribution pattern of marine organisms in the South China Sea have been deeply affected by the Pleistocene glacial events. In the last glacial period, the coastal environment of South China Sea underwent extreme changes, such as multiple dropping of the sea level and rushing decrease of the surface temperature, which caused ice sheet contraction and land exposure (Wang 1999), leading to substantial influence on coastal marine population dynamics and genetic diversity. For example, the historical isolation in Pleistocene glacial cycles led to highly differentiation and ancestral lineage division of the coral Pocillopora verrucosa (Li et al. 2022); the present cryptic diversity and geographic distribution of the shell Atrina pectinatawas was related to the demographic expansion in late Pleistocene (Xue et al. 2021); the study for different genetic lineage and dispersal routes of the crab Portunus pelagicus highlighted that land bridge formation in the Pleistocene glacial maximum have influenced the historical expansion and present phylogeographical structure (Lu et al. 2022). Meanwhile, the habitat heterogeneity of coastal South China Sea and ocean environmental conditions (such as sea surface temperature) may also result in the genetic differentiation of marine organisms (Jia et al. 2023, Wang et al. 2024), while the high capacity of dispersal of some marine animals relying on the ocean current have contributed to high genetic connectivity and low differentiation (Chan et al. 2013, Wu et al. 2020).
Although lots of researches have focused on the phylogeographical patterns on the marine organisms in the South China Sea, the complex genetic structure and distribution patterns of intertidal macroalgae in this region are still poorly understood. According to recent studies, under the climate change, the seaweed populations may undergo northward range shift and more genetic loss in the southern coast of China (Song and Li 2023). Therefore, it’s important to enrich the knowledge of the phylogeographical pattern of intertidal macroalgae in the South China Sea, which can provide scientific evidence for the seaweed resource protection.
Colpomenia sinuosa is a cosmopolitan brown alga which occurs in the intertidal or subtidal zones from warm to tropical coast areas (Lee et al. 2013). It’s the type species of the genus Colpomenia, characterized by yellow or brown saccate thalli with a heteromorphic life history (Toste et al. 2003, Guiry and Guiry 2024). Meanwhile, C. sinuosa can be considered as a suitable model of seaweed biogeographical research for two reasons: first, it has a widespread distribution in global coastal waters. Compared to the endangered species, the common and widespread species can provide insight regarding how demographic events have shaped intraspecific biodiversity based on more data basis. Additionally, the widespread species usually harbor geographically structured variation, which can facilitate a deeper understanding of the speciation process (Cloutier et al. 2024). Second, its hollow-like feature allows for its capability of dispersal with waterflow in the ocean, and previous studies have reported that Colpomenia species could spread rapidly with a rate achieving 35 km y−1 through the contribution of the hollow characteristic (Green-Gavrielidis et al. 2019). Some studies have explored the genetic diversity and evolutionary patterns of C. sinuosa at large scale, and suggested that present genetic distribution of C. sinuosa might result from the mixture of modern anthropogenic introduction and ancient relics (Cho et al. 2009, Lee et al. 2013, Martins et al. 2022). Colpomenia sinuosa has abundant biomass in the coast of northern margin of the South China Sea, but the genetic diversity and evolutionary pattern of this alga here is still a knowledge gap.
Here, with the collections of C. sinuosa in the South China Sea, we applied mitochondrial (mt) and chloroplast (cp) markers to analyze its phylogeographical pattern, and explore the likely historical, environmental and hydrographic factors influencing the contemporary distribution pattern. Our data will help to enrich the understanding of seaweed biogeography in Southern China, and give scientific evidence to the conservation and management of coastal seaweed resource in the future.

MATERIALS AND METHODS

DNA extraction and sequencing

We collected 16 populations of C. sinuosa in the northern coast of South China Sea (the latitude range spanning 18–22° N), including 5 populations in Guangxi province, 1 population in Guangdong province, and 10 populations in Hainan Island (Table 1, Fig. 1, Supplementary Fig. S1). The total genomic DNA was isolated using Hi-DNAsecure Plant Kit (TIANGEN, DP350-03) following the manufacturer’s instruction. After quality checking by OD260/OD280 ratio and 1% agarose gel electrophoresis, multiple molecular markers were amplified using these DNA template. The mt cox3, atp6, and cp rbcL partial sequences were amplified with pair primers F49 (5′-CATTTAGTNGAYCCWAGYCCTTGGC-3′)/R20(5′-AACAAARTGCCAATACCAKG-3′), F25P (5′-CCHTTAGAACAATTTBAAATACTYCC-3′)/R754P (5′-GCRTCRTTTATRTARATRCAACTTA-3′)(Leeetal. 2014) and F3 (5′-GCCTGAAGATGTGCAGAATCG-3′)/R1266 (5′-GCCTGAAGATGTGCAGAATCG-3′). The amplification procedures were carried out based on the method in Lee et al. (2013) and Song et al. (2019) as follows: for mt cox3 gene, the polymerase chain reaction (PCR) reactions consisted of an initial denaturation at 94°C for 4 min, followed by 35 amplification cycles containing denaturing at 94°C for 30 s, annealing at 53°C for 45 s, extending at 72°C for 1 min, and a final extension at 72°C for 10 min; for mt atp6 gene, the PCR reactions consisted of an initial denaturation at 94°C for 4 min, followed by 35 amplification cycles containing denaturing at 94°C for 30 s, annealing at 45°C for 30 s, extending at 72°C for 1 min, and a final extension at 72°C for 10 min; for cp rbcL gene, the PCR reactions consisted of an initial denaturation at 94°C for 4 min, followed by 45 amplification cycles containing denaturing at 94°C for 1 min, annealing at 48.5°C for 45 s, extending at 72°C for 1 min, and a final extension at 72°C for 10 min. Purification and sequencing of PCR products were performed using a BigDye Terminator Cycle sequencing kit and an ABI3730 automated sequencer (Applied Biosystems, Foster City, CA, USA).

Molecular diversity and population genetic structure

The obtained sequence datasets were aligned with MUSCLE model in MEGA X, respectively (Kumar et al. 2018). In addition to the datasets for individual genes, we constructed a multi-gene dataset as concatenated cox3-atp6-rbcL. After manual adjusting for false or missing gaps, variable sites and parsimony informative sites in each marker were counted in DnaSP v5.0 (Librado and Rozas 2009). Molecular genetic diversity indices of 16 populations were inferred in Arlequin v3.5.2.2 (Excoffier and Lischer 2010), including haplotype diversity (h) and nucleotide diversity (π).
We reconstructed phylogeographical network of C. sinuosa based on the haplotypes of concatenated cox3-atp6-rbcL, cox3, atp6, and rbcL using Median-Joining algorithm in POPART (Leigh and Bryant 2015). Besides, we assessed the population genetic structure based on the 4 datasets using admixture model in Structure v2.3.4 (Pritchard et al. 2000). The K value of putative clusters was set from 1 to 8. To ensure the reliability and consistency, the analysis carried out 10 repetitive iterations per K with a burn-in of 100,000 Markov chain Monte Carlo (MCMC) chains followed by 500,000 chains using a correlated allele frequencies model (Falush et al. 2003). The log-likelihood LnP(K) and statistic ΔK (Evanno et al. 2005) was estimated to determine most probable K value by online StructureHarvester(http://taylor0.biology.ucla.edu/struct_harvest/). Based on the K results, the analysis of molecular variance (AMOVA) was conducted to explore the genetic differentiation of subdivisions using all datasets in Arlequin. Additionally, the population pairwise differentiation (Fst) was estimated in Arlequin with 1,000 permutations.
To check the population distinctiveness, the principal component analysis (PCoA) was operated in GenAlex v6.5 (Peakall and Smouse 2012) based on the population pairwise genetic distances with all datasets calculated in DnaSP v5.

Isolation by distance / environment

The isolation by distance (IBD) model was estimated in order to assess whether the geographical distance acted as an important factor to influence population genetic structure. The genetic distances between pair populations were calculated measured as Slatkin’s linearized pairwise Fst [Fst = Fst / (1 − Fst)] (Rousset 1997). The log-transformed geographic distances between pair sampling sites along the coastline were estimated with the roadmap tool in QGIS (QGIS Development Team 2024). Also, the isolation by environment (IBE) model was estimated to analyze the correlation about environment variable and population genetics. The total 19 bioclimate variables were obtained in WorldClim 2 (https://worldclim.org/) (Fick and Hijmans 2017). Pearson’s correlation coefficients between bioclimate variables were calculated by “cor” function in R 3.4.1, and the highly correlated variables (|r| > 0.7) were removed, then 5 bioclimate variables (bio2, bio8, bio14, bio32, and bio38) were kept for IBE analysis. The environmental distance matrix was calculated based on pairwise Euclidean distances using ‘vegan’ package (Dixon 2003) in R. Partial mantel test using Pearson’s product-moment correlation were carried out to test the relation between genetic distances, geographical distances, and environmental distances with 10,000 permutations using ‘vegan’ package in R. The multiple matrix regression with randomization (MMRR) was implemented to evaluate the IBD and IBE model using ‘MMRR’ function in R.

Divergence time calculation and demographic history

Due to the lack of direct fossil evidence, we calibrated the molecular clock based on the timeframe proposed by Silberfeld et al. (2010), Choi et al. (2024), and Denoeud et al. (2024). For reckoning the divergence time of Colpomenia, we retrieved 63 sequences of 21 brown algae species in GenBank (Supplementary Table S1) and 3 sequences of an individual (HT1) in this study, and constructed a cox3-atp6-rbcL candidate dataset, aligned as 2,216 bp. We estimated the partition for each codon of the dataset and calculated optimal substitution models using Akaike information criterion in PartitionFinder v2.1.1 (Lanfear et al. 2017). Six partitions were specified and the optimal substitution model for all sites was determined as GTR + I. We reconstructed the time-calibrated phylogeny using log normal relaxed clock implemented in Beast v2.7.5 (Bouckaert et al. 2019). Yule model was selected for the tree prior, and 3 fossil nodes were added to help the divergence time correction: (1) Padina boryana and P. pavonica were set as monophyletic group with an age of Padina genus (99.6–145.5 Ma); (2) the age of Sargassaceae lineage (including Sargassum horneri, S. muticum and S. thunbergii) was taken for 13–17 Ma; (3) a monophyletic group including Nereocystis luetkeana and Pelagophycus porra with the age for 13–17 Ma. The runs of MCMC carried out 108 generations with sampling each 1,000 generations, then 105 samples were saved, and the first 25,000 samples were removed as burn-in. One consensus tree was constructed with maximum clade credibility in TreeAnnotator v2.7.5 (Drummond et al. 2012). The tree was visualized using FigTree v1.4.3 (http://tree.bio.ed.ac.uk/software/figtree/).
To examine the extent of evolutionary selection among populations, we carried out the neutrality test (Tajima’s D and Fu’s Fs) using cox3-atp6-rbcL, cox3, atp6, and rbcL datasets in DnaSP. Besides, we calculated the Tajima’s D and Fu’s Fs based on 5 lineage datasets of concatenated cox3-atp6-rbcL, respectively. To evaluates demographic historical dynamic patterns in different genetic subgroups, the coalescent extended Bayesian skyline plots (EBSPs) analysis was preceded with different genetic lineages in Beast v2.7.5 based on cox3, atp6, and rbcL datasets. Molecular clocks of these three genes were chosen as relaxed clock log normal with calculated substitution rates mentioned in the previous paragraph. MCMC chains were set as 8 × 108 iterations, followed by 2 × 108 iterations discarded as burn-in, with sampling every 80,000 iterations.

RESULTS

Genetic diversity

In the 16 populations of southern Chinese coast, we obtained 233 cox3 sequences (622 bp, 37 haplotypes) (GenBank accession Nos. PQ760306–PQ760342), 294 atp6 sequences (636 bp, 37 haplotypes) (GenBank accession Nos. PQ760184–PQ760220), and 289 rbcL sequences (1,143 bp, 19 haplotypes) (GenBank accession Nos. PQ760221–PQ760239), with 28, 29 and 8 parsimony information sites, respectively. And we established a multi-gene dataset consisting of 219 concatenated cox3-atp6-rbcL sequences (2,401 bp) with 74 haplotypes.
The molecular diversity indices showed that the populations in Guangdong and Hainan exhibited higher diversity (Table 1, Supplementary Table S2), while only 1 population in Guangdong showed higher haplotype diversity in the cp rbcL dataset (Supplementary Table S2). Most populations in Guangxi provinces showed lower haplotype and nucleotide diversity (Table 1, Supplementary Table S2). And 3 populations (Dongfang [DF] and Ledong [LD] in the southwestern Hainan and Wanning [WN] in southeastern Hainan) displayed the highest haplotype diversity by exceeding 0.9 (Table 1).

Population genetic structure

We found two main genetic clusters (Group I and II) and 5 subdivided genetic lineages in concatenated cox3-atp6-rbcL (Fig. 1), in which that Group II contains 3 populations in Sanya of southern Hainan (Xiaodonghai [DH], Luhuitou [HT], and Haitangwan [HW]), and Group I contains the rest 13 populations (Fig. 1A). We noted obvious regionalism to the lineage distribution (Fig. 1B). More precisely, the northern part of the study area was occupied by the lineage 1, and the eastern coast was mostly dominated by the lineage 2, also, the western part was mainly covered by the lineage 1 and 3, and the southern part was majored in the lineage 4 and 5 (Fig. 1B). Furthermore, two genetic clusters were also detected in cox3, atp6; and rbcL datasets (Supplementary Figs S2B, S3B & S4B). Four genetic subdivisions were recognized in mt cox3 (Supplementary Fig. S2C), and five subdivisions were discovered in mt atp6 (Supplementary Fig. S3C). Compared to the concatenated cox3-atp6-rbcL, the genetic distribution of these 2 datasets also showed similar regionalism (Supplementary Figs S2A & S3A). As for the cp rbcL, there were 2 genetic groups found (Supplementary Fig. S4C), consistent with the result of population genetic structure (Supplementary Fig. S4B), in which that one group was mainly distributed in the southwestern and southern Hainan, and the other group contained other populations.
In parallel, the PCoA analyses were conducted for assessing the population partitions and deviations. Consistent with the result of genetic structure (Fig. 1A), there were 2 main genetic groups found in the cox3-atp6-rbcL dataset (Fig. 2B). Three populations of Sanya in southern Hainan consisted of Group II, and other populations consisted of Group I. However, within the genetic groups, it was evident that the populations exhibited various patterns of aggregation and dispersion. In Group I, nine populations in Guangxi and eastern Hainan displayed high levels of aggregation, whereas the three populations in Guangdong and southwestern Hainan (DF, LD, and Guangdong [XW]) remained closely clustered. Conversely, the WN population in southeastern Hainan showed relatively distinctness from other populations. In Group 2, the HW population stood out as a significant outlier. Similarly, the result of mt cox3 and atp6 dataset showed 2 genetic groups among 16 populations (Supplementary Figs S5 & S6), resembling the result of concatenated dataset. Meanwhile, the two populations WN and HW were disjoint in respective genetic groups (Supplementary Figs S5 & S6). In cp rbcL, although there were 2 main genetic groups, the populations contained in each group were different with the other 3 datasets, and the population DF was a specific outlier in Group II (Supplementary Fig. S7).
We examined the genetic differentiations by AMOVA and Fst. The AMOVA analysis of all datasets suggested that the major genetic differentiations occurred among genetic groups and within populations (Supplementary Table S3). The genetic differentiation between populations was examined with all datasets (Fig. 2A, Supplementary Tables S4 & S5). The pairwise Fst values revealed significant differentiations among most populations (Fig. 2A). The populations in Sanya, southern Hainan (HT and DH) showed highest differentiation with other populations (Fig. 2A, Supplementary Tables S4 & S5). Besides, five populations of XW and southwestern Hainan (DF, LD, HW, HT, and DH) showed significant genetic differentiations in cp rbcL dataset (Supplementary Table S5), coincident with the result of population hierarchical structure (Supplementary Fig. S4).

IBD versus IBE

When the significance threshold was specified as 0.01, the mantel test using IBD model showed that |r| = 0.28 and p = 0.001 (Supplementary Fig. S8), while the mantel test using IBE model showed that |r| = 0.18 and p = 0.018 (Supplementary Fig. S9). Consequently, the current population structure of C. sinuosa can be explained by the IBD model, indicating that geographical distance rather than environmental change was the main factor leading to the isolation among populations.

Demographic history deduction

Based on concatenated cox3-atp6-rbcL, we reconstructed the divergence calibration within 21 Phaeophyceae species, and the result was comparable to the timeframe proposed in Choi et al. (2024) and Denoeud et al. (2024). The origin of C. sinuosa may occur at 26.73 Ma (22.52–31.18 Ma) before present, which was dated at the Chattian stage in late Oligocene (Supplementary Fig. S10). According to this divergence time, we compared the genetic distances among 3 Colpomenia species (C. sinuosa, C. peregrina and C. claytoniae), and the molecular clocks of the 3 markers were estimated as 0–635% Ma−1 in cox3 (average 0.255% Ma−1), 0–0.71% Ma−1 in atp6 (average 0.247% Ma−1), and 0–0.25% Ma−1 in rbcL (average 0.082% Ma−1), respectively.
The neutrality tests were examined with Tajima’s D and Fu’s Fs index at population level based on 3 datasets. The D and Fs were negative in most populations, suggesting potential population expansions in the evolutionary process, however, all D and Fs were positive only in population HW in Sanya, southern Hainan, suggesting underlying contraction (Supplementary Table S6). Meanwhile, the neutrality tests were computed at lineage level in concatenated cox3-atp6-rbcL. All the 4 lineages (except lineage 4 containing only 3 individuals) showed expansion possibility within the 2 tests (Supplementary Table S7).
Furthermore, the EBSP showed that all lineages have undergone dynamic expansions in Pleistocene (Fig. 3). The lineage 1 has experienced expansion at about 0.2 Ma ago and expanded more rapidly from about 0.1 Ma ago. There was slight expansion detected in lineage 2 from 0.35 Ma before present. The lineage 3 exhibited apparent expansion from about 0.4 Ma before present and the lineage 5 had slight expansion within a very short time period at about 0.1 Ma before present.

DISCUSSION

Genetic diversity pattern of Colpomenia sinuosa

In this study, most populations displayed the pattern of high haplotype diversity and low nucleotide diversity (Table 1, Supplementary Table S2). According to the thesis proposed by Grant and Bowen (1998), the formation of such diversity pattern suggested that C. sinuosa in northern South China Sea have experienced rapid population growth in a short period because sudden expansion couldn’t support sufficient time to accumulate enough nucleotide mutations. Similarly, the star-like structure of haplotype network implied intraspecific expansion as well (Fig. 1C, Supplementary Figs S2C, S3C & S4C). However, most populations of cp rbcL dataset showed the pattern of low haplotype diversity and low nucleotide diversity (Supplementary Table S2), and compared to mitochondrial datasets, there were not so much subdivided genetic lineages showed (Supplementary Fig. S4). It reinforced that mitochondrial markers of C. sinuosa might have higher resolution in phylogeographic structure delineation than cp gene (Hu et al. 2017).
In this study, the genetic diversity distribution of C. sinuosa exhibited complex picture. Three populations in southwestern and southeastern Hainan (DF, LD, and WN) displayed highest haplotype diversity. Different situation occurs in a coral species Turbinaria peltata that the DF population exhibited lowest genetic diversity due to severe anthropogenic pollution (such as wharf building) (Wu et al. 2021). The contrasting situation suggested that C. sinuosa might have stronger adaptation to resist the negative environmental change compared with other sensitive marine species. The higher diversity pattern in southwestern Hainan appears to be similar with the findings of another brown alga Sargassum polycystum C. Agardh (Hu et al. 2018, Liang et al. 2022), which indicated that the population of LD in southwestern Hainan harbored the richest genetic diversity. In our study, the population of LD also showed high genetic diversity (Table 1, Supplementary Table S2), but the result could be distorted due to the limited sample size, so more extensive sample collection should be conducted for further understanding. Additionally, for S. polycystum, Hu et al. (2018) proposed a hypothesis that a unique historical climate refugium might be located at southwestern Hainan because the population of LD in Hainan had highest genetic diversity and supported the most widespread ancestral haplotypes. Moreover, the Yinggehai Basin in Ledong harbored rich endemic species diversity, and the pockmarks and mudflow gullies in Yinggehai Basin have helped to preserve unique diversity during the sea level dropping in Pleistocene (Hu et al. 2018). In our study, although there was only 1 lineage in the southwestern Hainan in the concatenated dataset, we found that the population of DF in southwestern Hainan held haplotypes of all lineages in genetic Group I in the mt cox3 dataset (Supplementary Fig. S2A). The populations in glacial refugia usually accumulated higher genetic diversity and particular haplotypes than recolonized populations (Maggs et al. 2008). Thus, our results partially supported the hypothesis by Hu et al. (2018). However, it still needs further sample collection and analysis. Moreover, the population of WN in southeastern Hainan had the highest genetic diversity (Table 1). Based on the structure result, this population held genetic compositions of both Group I and II (Fig. 1A, Supplementary Figs S2B, S3B & S4B), and in the PCoA result, the population WN was located in the middle position of 2 genetic groups (Fig. 2B, Supplementary Figs S5 & S6), which suggested that this population might be an intersection of genetic groups. But no haplotypes of lineage 3 has been found in this population (Fig. 1B), so it could be challenging to perceive it as a diversity center. We assumed the situation might result from weak genetic exchange between southwestern and southeastern Hainan.

Phylogeographical patterns of Colpomenia sinuosa derived by Pleistocene glacial cycle

Deep genetic structure and significant differentiation were detected in C. sinuosa datasets in the northern margin of the South China Sea. Two genetic groups were displayed clearly between the populations of southern Hainan and other regions in Guangxi, Guangdong and Hainan (Fig. 1, Supplementary Figs S2 & S3), which indicated that current genetic distribution might originate from different ancestral populations despite monophyletic origin. According to the IBD / IBE results, the genetic differentiation was influenced by geographical isolation rather than environmental variables (Supplementary Figs S8 & S9). Therefore, the current population genetic structure might be a consequence of historical isolation engendered by paleoclimate change. Historical vicariance caused by Pleistocene glaciation events may account for present phylogeographic pattern. During the glacial cycles in Pleistocene, the marginal seas in East Asia have endured huge sea level fluctuation, and the South China Sea became enclosed inland sea, only connected to the Pacific by Bashi Strait in the Last Glacial Maximum (Ni et al. 2014). Thus, we assumed a scenario that current genetic distribution pattern might be a mixture of separated ancestral populations, which were likely isolated due to declining sea levels during the Pleistocene ice age and subsequently expanded in the process of glacial eustasy (Hoarau et al. 2007, Sinclair et al. 2016, Bringloe et al. 2020). Although both EBSP analysis and neutral tests indicated that all the lineages of C. sinuosa have experienced demographic expansion in Pleistocene, the demographic process occurred in different period (Fig. 3), which implied that the ancestral populations in two genetic groups might experience multiple colonization and spread in turbulent historical oscillation, resulting in the sophistication of genetic differentiation. As the most ancestral lineage, lineage 5 maintained relatively long-term demographical stability with a minor expansion in recent 0.1 Ma. The contrasting phylogeographical process might be responsible for significant differentiation with other lineages, suggesting strong endemism and limited dispersal capability. However, this small lineage is restricted at Sanya in southern Hainan with low genetic diversity (Fig. 1). Additionally, although we detected expansion in lineage 5, the HW population in this lineage showed signs of population contraction in the neutrality test (Supplementary Table S6), suggesting potential bottleneck effect in the evolutionary process. Thus, it revealed a potential precarious situation and underscored the importance of seaweed diversity conservation of Sanya. Contrast to the post glacial expansion pattern of other seaweed species (Zhang et al. 2019b, Song et al. 2021, Assis et al. 2023), the C. sinuosa lineages presented pre-LGM (Last Glacial Maximum) demographic dynamics pattern (Fig. 3). Especially, the population expansion of lineage 1 experienced a significant acceleration during recent 0.1 Ma in late Pleistocene. This phenomenon might be attributed to the relatively warm climate during the last interglacial period (1.3–0.5 Ma before present in China) (Wang and Wang 1980), which might facilitate the dispersal and recolonization of C. sinuosa. This pre-LGM demographic pattern was also observed in other seaweed and marine organisms (Coyer et al. 2011, Ni et al. 2014). We assumed that C. sinuosa existed throughout the last glaciation of Pleistocene, and the LGM seemed to have influence only on its distribution and habitat, rather than demographic history. It implicated the importance of insight on pre-LGM tectonic events and marine population demographic genetic shifts.
At present, there were few researches discussing about the phylogeographical pattern of C. sinuosa (Cho et al. 2009, Lee et al. 2013, Martins et al. 2022). Cho et al. (2009) found that C. sinuosa could be divided into 2 genetic groups in northern and southern hemispheres, while Lee et al. (2013) proposed that there were 3 divergent groups at the global scale and C. sinuosa might originate from the large Indo-Pacific region. The phylogeographic studies of C. sinuosa across global oceans highlighted its complex genetic diversity and distribution were likely shaped by historical climate changes and oceanic barriers. Furthermore, Martins et al. (2022) have illustrated that the genetic structure of C. sinuosa along the Brazilian coast might be influenced by Quaternary climate change, coastal habitat heterogeneity and ocean current barriers. Notably, all three studies have also found that Pleistocene glaciation-induced climate change had a significant impact on the current genetic distribution patterns of C. sinuosa, which were comparable with our findings. Although our study is only based on a regional scale, we found more haplotypes than the Brazilian coast (Supplementary Table S2), and the demographic expansions of genetic lineages in northern South China Sea were roughly earlier than that in Brazilian coast (Martins et al. 2022). It might emphasize more intricate evolutionary history in the Western Pacific. In addition, when comparing current released haplotypes worldwide, we found that all the cox3 haplotypes in this study were newly discovered, but several haplotypes were comparable to those from Taiwan in China, the Philippines (Lee et al. 2013), and French Polynesia; similarly, most rbcL haplotypes were newly recorded, but one haplotype was identical with those from the Philippines (Santiañez et al. 2022) and French Polynesia. Therefore, integrating these newly discovered haplotypes into comprehensive study from the global landscape may offer novel insights into the evolutionary history of C. sinuosa. Given the sampling limitation of regional scale studies, it is crucial to study the phylogeographical pattern of C. sinuosa in further large-scale comparative research with integration of these previous research.

Genetic connectivity influenced by ocean currents and other abiotic factors

The dynamic fluid nature of the marine environment promotes connectivity among distinct populations, which helps to shape genetic structure, biogeography and speciation (Cowen and Sponaugle 2009, Assis et al. 2022). Multiple researches have indicated that complex hydrological factor of South China Sea could significantly shape the marine phylogeographical patterns by facilitate the genetic homogeneity (Geng et al. 2021, Sun et al. 2023). Meanwhile, many studies have demonstrated that the ocean currents of South China Sea and adjacent seas have significant impact on the population structure of some Sargassum species, which have strong ability of floating and dispersal (Zhang et al. 2019a). High gene flow in S. thunbergii might be affected by the Kuroshio current and coastal current in China (Li et al. 2017). In addition, the apparent genetic homogeneity of S. polycystum in southeastern Asia might be influenced by the facilitation of complex current system (Chan et al. 2013, Liang et al. 2022). The ocean currents of South China Sea were characterized by seasonal directional changes due to the monsoon effect, and the southwestern currents affected by northeast monsoon in autumn and winter might promote the southward dispersal of S. polycystum (Liang et al. 2022). In this study, since the highly differentiated genetic structure of C. sinuosa, potential dispersal barriers result from the coastal currents and Kuroshio currents in the South China Sea might also play a role on the current distribution pattern of C. sinuosa. In the field work we found the occurrence of C. sinuosa was mainly at the winter and early spring in the northern South China Sea, so we assumed that the gene flow among populations was mostly influenced by the seasonal current in winter and spring by northeastward monsoon. The haplotypes of lineage 1 and 3 were only distributed in the coastal Beibu Gulf (Fig. 1B), which might be related to the limited genetic exchange with eastern side of Hainan, affected by the restriction by semi-closed topography and counterclockwise coastal currents of Beibu Gulf in winter and spring (Supplementary Fig. S11) (Jia et al. 2023, Gao et al. 2024). Also, the westward costal current through the Qiongzhou Strait can block the eastward spread of lineage 1 and 3 (Shi et al. 2002, Yang et al. 2003). Moreover, other lineages might sustain population connectivity promoted by the northeastward Kuroshio current and South China Sea warm current, and we need to enlarge sample collection of C. sinuosa and utilize detailed analysis to study the ocean current’s influences on the seaweed genetic connectivity at larger scale.
Besides, several studies have suggested that environmental heterogeneity, such as sea surface temperature and nutrients variation, can have an impact on the genetic differentiation of marine organism in South China Sea, particularly evident in some coral species (Wu et al. 2021, Li et al. 2022, Jia et al. 2023). In our study, the IBE result indicated that the correlation between genetic variation and environmental variables was not significant. We speculated that C. sinuosa had a broad thermohaline adaption at regional scale compared to more sensitive marine species, thus little affected by the regional environmental changes (Oates 1985, Lee et al. 2014).

Conservation suggestion of the marine flora in the northern South China Sea

As a global marine biodiversity hotspot, the coastal ecosystem of South China Sea has faced severe stress of habitat degradation and biodiversity loss due to recent global climate change and human-mediated disturbances (Juinio-Meñez 2015). In this study, we investigated the genetic diversity of a widely distributed macroalga C. sinuosa and provided some scientific basis of the coastal seaweed diversity conservation in northern South China Sea. Firstly, we found that Sanya in southern Hainan contains two ancestral small lineages with low genetic diversity, which was deeply differentiated with other populations (Table 1, Fig. 1). It revealed that it should be regarded as an independent management unit (MU) and a priority for conservation. Secondly, our findings indicated that Yulinzhou, Dongfang (DF) in southwestern Hainan might serve as a potential central population in the mitochondrial dataset (Supplementary Fig. S2). Additionally, the PCoA result of cp rbcL dataset showed significant deviation from other populations (Supplementary Fig. S7). These results highlighted the importance of seaweed biodiversity conservation in this region. We recommended Yinggehai Basin involved Dongfang in southwestern Hainan as an independent MU, and increase the efforts for marine plant protection with the basis of marine nature reservation. Thirdly, the highest diversity was displayed at Wanning (WN) in southeastern Hainan. So we suggested that it should be involved in the conservation concern of marine plant resource in conjunction with more researches on other marine organism.
In conclusion, we detected deep divergent genetic lineages and complex diversity pattern of C. sinuosa in the northern margin of the South China Sea. Although at regional scale, we found different demographical expansion processes in different lineages in Pleistocene. The phylogeographical pattern might result from the paleoclimatic oscillations and sea level fluctuations in the Pleistocene glacial period, and the ocean currents along the South China Sea could also influence the population genetic structure. Based on the ancestral lineages and high genetic diversity, we proposed Dongfang in western Hainan and Sanya in southern Hainan need extra attention to seaweed diversity conservation and management. In the future, we’ll use C. sinuosa as a good example and shed light on macroalgae phylogeography under historical climate change based on extensive collection work.

Notes

ACKNOWLEDGEMENTS

We thanked Dr. Ruoyu Liu (Fujian Agriculture and Forestry University) and Dr. Zhongmin Sun (IOCAS) for sample collections.

This research was supported by Strategic Priority Research Program of Chinese Academy of Sciences (XDB42030203), International Partnership Program of Chinese Academy of Sciences (133137KYSB20210034), Asia Collaboration Project on the Development of Ecological Marine Ranching, and National Key R & D Program of China (2023YFE0106200).

CONFLICTS OF INTEREST

The authors declare that they have no potential conflicts of interest.

SUPPLEMENTARY MATERIALS

Supplementary Fig. S1
The study area in the whole China (https://www.e-algae/org).
algae-2025-40-2-27-Supplementary-Fig-S1.pdf
Supplementary Fig. S2
Phylogeographic relationships and population genetic structure of Colpomenia sinuosa based on mitochondrial cox3 dataset (https://www.e-algae/org).
algae-2025-40-2-27-Supplementary-Fig-S2.pdf
Supplementary Fig. S3
Phylogeographic relationships and population genetic structure of Colpomenia sinuosa based on mitochondrial atp6 dataset (https://www.e-algae/org).
algae-2025-40-2-27-Supplementary-Fig-S3.pdf
Supplementary Fig. S4
Phylogeographic relationships and population genetic structure of Colpomenia sinuosa based on chloroplast rbcL dataset (https://www.e-algae/org).
algae-2025-40-2-27-Supplementary-Fig-S4.pdf
Supplementary Fig. S5
Principal co-ordinates analysis based on mitochondrial cox3 populations (https://www.e-algae/org).
algae-2025-40-2-27-Supplementary-Fig-S5.pdf
Supplementary Fig. S6
Principal co-ordinates analysis based on mitochondrial atp6 populations (https://www.e-algae/org).
algae-2025-40-2-27-Supplementary-Fig-S6.pdf
Supplementary Fig. S7
Principal co-ordinates analysis based on chroloplast rbcL populations (https://www.e-algae/org).
algae-2025-40-2-27-Supplementary-Fig-S7.pdf
Supplementary Fig. S8
Mantel test using isolation by distance model (https://www.e-algae/org).
algae-2025-40-2-27-Supplementary-Fig-S8.pdf
Supplementary Fig. S9
Mantel test using isolation by environment model (https://www.e-algae/org).
algae-2025-40-2-27-Supplementary-Fig-S9.pdf
Supplementary Fig. S10
Maximum clade credibility coalescent tree based on concatenated cox3-atp6-rbcL (https://www.e-algae/org).
algae-2025-40-2-27-Supplementary-Fig-S10.pdf
Supplementary Fig. S11
Diagram of the major ocean currents flowing through the northern South China Sea (https://www.e-algae/org).
algae-2025-40-2-27-Supplementary-Fig-S11.pdf
Supplementary Table S1
The sequences retrieved in GenBank (https://www.e-algae/org).
algae-2025-40-2-27-Supplementary-Table-S1.pdf
Supplementary Table S2
Populations, sample sizes and genetic diversity indices inferred from cox3, atp6, and rbcL of Colpomenia sinuosa in the South China (https://www.e-algae/org).
algae-2025-40-2-27-Supplementary-Table-S2.pdf
Supplementary Table S3
Analysis of molecular variance (AMOVA) based on 4 datasets (https://www.e-algae/org).
algae-2025-40-2-27-Supplementary-Table-S3.pdf
Supplementary Table S4
Pairwise values of Fst between populations based on mitochondrial cox3 and atp6 (https://www.e-algae/org).
algae-2025-40-2-27-Supplementary-Table-S4.pdf
Supplementary Table S5
Pairwise Fst between 16 populations based on chloroplast rbcL (https://www.e-algae/org).
algae-2025-40-2-27-Supplementary-Table-S5.pdf
Supplementary Table S6
Neutral test of Colpomenia sinuosa populations based on 4 datasets (https://www.e-algae/org).
algae-2025-40-2-27-Supplementary-Table-S6.pdf
Supplementary Table S7
Neutral test of Colpomenia sinuosa lineages based on concatenated cox3-atp6-rbcL (https://www.e-algae/org).
algae-2025-40-2-27-Supplementary-Table-S7.pdf

Fig. 1
Phylogeographic relationships and population genetic structure of Colpomenia sinuosa based on concatenated cox3-atp6-rbcL dataset. (A) STRUCTURE analysis result based on optimal K = 2. The populations were in order from north to south. (B) The geographical distribution of genetic lineages in northern South China Sea. Numbers in the pie chart represented the population size. The grey part represented land and the blue line represented province boundaries. (C) The median-joining network based on haplotypes within C. sinuosa. The pie chart size represented the number of individuals of the haplotype, and the short lines on the connecting lines represented the mutation steps. BG, Beigang, Beihai, Guangxi; ST, Shengtang, Weizhou island, Beihai, Guangxi; HS, Huoshankou Geopark, Weizhou island, Beihai, Guangxi; CT, Wucai beach, Weizhou island, Beihai, Guangxi; WZ, Dishui, Weizhou island, Beihai, Guangxi; XW, Dengloujiao, Xuwen, Zhanjiang, Guangdong; WC, Wenchang, Hainan; TO, Haitou, Danzhou, Hainan; CH, Qizi Bay, Changhua, Changjiang, Hainan; BA, Boao, Qionghai, Hainan; DF, Yulinzhou, Dongfang, Hainan; WN, Wanning, Hainan; LD, Ledong, Hainan; HW, Haitang Bay, Sanya, Hainan; HT, Luhuitou, Sanya, Hainan; DH, Xiaodonghai, Sanya, Hainan.
algae-2025-40-2-27f1.jpg
Fig. 2
The genetic differentiation and deviation at population level based on concatenated cox3-atp6-rbcL dataset. (A) Pairwise Fst between 16 populations. Values less than 0.25 are shown in light yellow block. (B) Principal co-ordinates analysis result based on 16 populations. BG, Beigang, Beihai, Guangxi; ST, Shengtang, Weizhou island, Beihai, Guangxi; HS, Huoshankou Geopark, Weizhou island, Beihai, Guangxi; CT, Wucai beach, Weizhou island, Beihai, Guangxi; WZ, Dishui, Weizhou island, Beihai, Guangxi; XW, Dengloujiao, Xuwen, Zhanjiang, Guangdong; WC, Wenchang, Hainan; TO, Haitou, Danzhou, Hainan; CH, Qizi Bay, Changhua, Changjiang, Hainan; BA, Boao, Qionghai, Hainan; DF, Yulinzhou, Dongfang, Hainan; WN, Wanning, Hainan; LD, Ledong, Hainan; HW, Haitang Bay, Sanya, Hainan; HT, Luhuitou, Sanya, Hainan; DH, Xiaodonghai, Sanya, Hainan.
algae-2025-40-2-27f2.jpg
Fig. 3
Extended Bayesian skyline plot analysis of 4 lineages within Colpomenia sinuosa based on concatenated cox3-atp6-rbcL dataset. The horizontal axis represented the past time in the unit of per million years (Myr), and the vertical axis represented the effective population size. The green intervals represented the 95% confidence posterior density (CPD).
algae-2025-40-2-27f3.jpg
Table 1
Populations, sample sizes and genetic diversity indices inferred from concatenated cox3-atp6-rbcL in the South China Sea
No. ID Locations n H h π (×10−2)
1 BG Beigang, Beihai, Guangxi 16 4 0.44 ± 0.14 0.04 ± 0.03
2 ST Shengtang, Weizhou island, Beihai, Guangxi 12 3 0.32 ± 0.16 0.01 ± 0.01
3 HS Huoshankou Geopark, Weizhou island, Beihai, Guangxi 16 6 0.54 ± 0.14a 0.06 ± 0.04
4 CT Wucai beach, Weizhou island, Beihai, Guangxi 15 2 0.13 ± 0.11 0.03 ± 0.03
5 WZ Dishui, Weizhou island, Beihai, Guangxi 5 2 0.40 ± 0.24 0.13 ± 0.09
6 XW Dengloujiao, Xuwen, Zhanjiang, Guangdong 5 3 0.70 ± 0.22a 0.12 ± 0.09
7 WC Wenchang, Hainan 19 11 0.88 ± 0.06a 0.13 ± 0.07
8 TO Haitou, Danzhou, Hainan 18 11 0.86 ± 0.08a 0.08 ± 0.05
9 CH Qizi Bay, Changhua, Changjiang, Hainan 23 9 0.82 ± 0.06a 0.10 ± 0.06
10 BA Boao, Qionghai, Hainan 15 5 0.68 ± 0.10a 0.03 ± 0.03
11 DF Yulinzhou, Dongfang, Hainan 21 12 0.91 ± 0.04a 0.17 ± 0.10
12 WN Wanning, Hainan 17 12 0.96 ± 0.03a 0.40 ± 0.22
13 LD Ledong, Hainan 7 5 0.90 ± 0.10a 0.11 ± 0.07
14 HW Haitang Bay, Sanya, Hainan 9 3 0.72 ± 0.10a 0.55 ± 0.31a
15 HT Luhuitou, Sanya, Hainan 5 2 0.40 ± 0.24 0.02 ± 0.02
16 DH Xiaodonghai, Sanya, Hainan 16 2 0.13 ± 0.11 0.01 ± 0.01

n, sample size; H, haplotype size; h, haplotype diversity; π, nucleotide diversity.

The populations were numbered in order from north to south.

a Values greater than 0.5 in h and greater than 0.5 × 10−2 in π.

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