Visitors   Views   Downloads

First evidence of asexual recruitment of Pocillopora acuta in Okinawa Island using genotypic identification

View article
First evidence of asexual recruitment of Pocillopora acuta in Okinawa Island using genotypic identification https://t.co/35wr1JwXoN #coralreefs #biodiversity https://t.co/5eQMYtoOoI
First evidence of asexual recruitment of Pocillopora acuta in Okinawa Island using genotypic identification https://t.co/fqQya0aPn8 @thePeerJ https://t.co/EcHGP3xN1m

Introduction

The Nansei Islands, spanning approximately 1,000 km, are located to the north of the coral triangle in the East China Sea and the Pacific Ocean (Fig. 1A). This is relatively high latitude (∼24–31°N) for coral reefs, and includes the northern reef limit in the northern hemisphere (Yamano, 2008). Over 80 coral genera (over 400 species) are abundant in the area (Nishihira & Veron, 1995; The Japanese Coral Reef Society & Ministry of the Environment, 2004). The geographic reef range and coral species diversity appear to be enhanced by the Kuroshio Current and its branch currents that flow from the east side of the Philippines (Nishihira & Veron, 1995). However, like many tropical reefs, coral populations in the Nansei Islands are suffering from anthropogenic disturbances. Since the mass coral bleaching event in 1998, coral bleaching has often been observed in the region (Loya et al., 2001; Hongo & Yamano, 2013; Harii et al., 2014). Erosion of red soil from sugar cane farming has destroyed water quality in coastal waters (Hasegawa et al., 1999), and outbreaks of coral-eating, crown-of-thorns starfish, Acanthaster planci (Acanthaster cf. solaris) have caused further damage to coral reefs (Yamaguchi, 1986; Nakamura et al., 2015). Multiple environmental stresses at global and local scales are expected to degrade coral reefs in the region for the foreseeable future (Harii et al., 2014).

Location, outdoor tank, and coral colonies.

Figure 1: Location, outdoor tank, and coral colonies.

(A) A map of the Nansei Islands and the location of the OIST Marine Science Station, Onna Village Fisheries Cooperative Association, and Zampa in Okinawa Island. Original maps were downloaded from Google Earth. Map data: Google Earth, Image Landsat/Copernicus, Data SIO, NOAA, US Navy, NGA, GEBCO. (B, C) Coral colonies maintained under natural sea water flow in the outdoor tank. (D) Small colonies were discovered in the tank on January, 2018. These photographs in B, C, and D were taken by Yuichi Nakajima.

Population retention and larval recruitment of corals have been studied in the Nansei Islands (Loya et al., 2001; Nakamura & Sakai, 2010; Van Woesik et al., 2011). Monitoring of coral coverage and coral composition over long periods is fundamental to understand the circumstances of living corals and to support future reef conservation efforts. In addition to monitoring numbers and densities of coral colonies, it is also important to assess larval coral recruitment. However, the recruitment process is complex in corals because of multiple reproductive strategies involving both sexual and asexual reproduction (Harrison & Wallace, 1990). The annual spawning season varies among genera/species, even in the same region (Shlesinger & Loya, 1985; Okubo et al., 2013). Among sexually reproducing species, both hermaphroditic taxa, e.g., Acropora, and dioecious species, e.g., Galaxea fascicularis are known (Babcock et al., 1986; Keshavmurthy et al., 2012). However, clonal replicates, produced by fragmentation and asexual planula, may also contribute to reef formation as well (Harrison & Wallace, 1990). Thus, reproductive strategy plays a key role in understanding population retention and maintenance.

Okinawa Island (∼26–27°N) comprises ∼1,200 km2 and is located near the center of the archipelago (Fig. 1A). It is currently home to over 1.3 million people and the population is concentrated in the south and middle sections of the island, which are relatively developed. The central and northwestern coastal area has also been designated as an “Okinawan semi-national coastal park” to conserve geological features and marine coastal fauna, and to limit development of the coast and to ensure the survival of marine species. In July, 2016, Okinawa Institute of Science and Technology Graduate University (OIST) inaugurated the OIST Marine Science Station at Seragaki, Onna, in the central west coast of Okinawa to advance marine research (Fig. 1A). This station possesses indoor and outdoor tanks with a constant flow of natural and sand-filtered sea water to hold various marine organisms. In March, 2017, we started to hold multiple coral species for molecular biological and physiological studies. Ten months after, we found small pocilloporid-like colonies in an outdoor tank. It is difficult to identify coral species morphologically and their plasticity has resulted in taxonomic confusion (Paz-García et al., 2015); hence, genetic markers have been used for classification (Pinzón et al., 2013; Schmidt-Roach et al., 2013). In this study, we validated the classification and clonality of these small colonies by comparing them with adult colonies in the tank using genetic methods, and here we present a coral population dynamics study in a miniaturized, artificial world.

Materials and Methods

Coral keeping and collection of small corals

We started to keep coral colonies of Acropora, Galaxea, Pocillopora, and Stylophora in an outdoor tank with constantly flowing natural sea water, in March, 2017 (Figs. 1B and 1C). These colonies were purchased from Onna Village Fisheries Cooperative (Fig. 1A). Also, we collected and kept morphological Pocillopora verrucosa colonies in Zampa (Fig. 1A), on the west coast of Okinawa Island commencing in May, 2017. The collection of corals was approved by Okinawa prefecture (permit number: 28-80). The list of corals that were kept in the tank is shown in File S1. Although we did not observe spawning of these corals, we spotted small pocilloporid-like corals adhering to the side wall of the tank (Fig. 1D). We confirmed over 40 small colonies on the tank wall in January, 2018. Using a flathead screwdriver, we collected 25 small corals, which were readily accessible on the inner wall of the tank. A tip of mature pocilloporid corals was also collected like as these small corals. However, morphological P. verrucosa colonies from Zampa died before the procedure started. After samples were soaked in a mixture of ATL buffer and Proteinase K in DNeasy Blood & Tissue Kit (Qiagen, Hilden, Germany) for extraction of genomic DNA (see below), we preserved the 25 coral skeletons in ethanol and then dried them for more than a week at room temperature. Then, we measured the maximum width and height of each skeleton using an electronic caliper E-PITA15 (Nakamura Mfg, Matsudo-shi, Japan) and their weight on an Analytical Balance ME54 (Mettler Toledo, Columbus, OH, USA). The sum of individual width and height was calculated for each colony. We calculated the correlation of size (sum of the width and height) with weight by regression analysis using statistical package R ver. 3.4.4 (R Core Team, 2016) and determined the microsatellite multilocus genotypes (see below).

Genotyping of mitochondrial haplotypes

It is impossible to identify these coral species as recruits by eye, due to the complex relationship between morphology and genetic species (Schmidt-Roach et al., 2013; Schmidt-Roach et al., 2014a; Schmidt-Roach et al., 2014b; Nakajima et al., 2017). Genomic DNA from mature pocilloporid colonies and the 25 small colonies was extracted using a DNeasy Blood & Tissue Kit, following the standard protocol. We conducted genotyping using the mitochondrial open reading frame region (mtORF), which is useful for identification of genetic types of pocilloporids (Flot et al., 2008; Flot et al., 2011). Mitochondrial haplotypes were confirmed by sequencing the mtORF region. PCR reaction mixtures (10 µL) contained template DNA (<50 ng/µL), AmpliTaq Gold 360 Master Mix (Thermo Fisher Scientific), and primers (final concentration: 2 µM for each primer) for mtORF: FATP6.1 (5′-TTTGGGSATTCGTTTAGCAG-3′) and RORF (5′-SCCAATATGTTAAACASCATGTCA-3′). The PCR protocol consisted of 94 °C for 1 min, followed by 40 cycles at 94 °C for 30 s, 53 °C for 30 s, and 72 °C for 75 s, with a final extension at 72 °C for 5 min using thermal cycler, Thermal Cycler Dice Touch TP350 (Takara, Kusatsu, Japan). PCR products were cleaned with Exonuclease I (Takara) and Shrimp Alkaline Phosphatase (Takara). Sequencing was performed by Macrogen Japan, and sequences obtained were aligned with mtORF sequences reported in Nakajima et al. (2017) and Flot et al. (2011) to identify the genetic species of Pocillopora and Stylophora, respectively. We could not obtain the sequence of morphological P. verrucosa colonies collected from Zampa, because these colonies had died previously.

Scoring of microsatellite multilocus genotypes

Nine microsatellite loci developed for Pocillopora by Nakajima et al. (2017) were used to investigate the relationship between potential parental colonies and the small coral colonies discovered on the tank wall. These nine loci have perfect repeats (see Table 1 in Nakajima et al., 2017). Information about microsatellite loci is presented in Table 1. For scoring of microsatellite genotypes of each colony, the PCR reaction mixture (5 µL) contained template DNA (<50 ng/µL), AmpliTaq Gold 360 Master Mix, and three primers for each locus: a non-tailed primer (0.5 µM), another primer with a sequence tail of U19 (5′-GGTTTTCCCAGTCACGACG-3′) (0.5 µM), and a U19 primer (0.5 µM) fluorescently labeled with FAM, VIC, or NED. The PCR protocol consisted of 95 °C for 9 min, followed by 35 cycles at 95 °C for 30 s, 56 °C for 30 s, and 72 °C for 1 min, with a final extension at 72 °C for 5 min using the thermal cycler. PCR products were analyzed using an ABI 3130xl capillary DNA sequencer (Thermo Fisher Scientific, Waltham, MA, USA) with GeneScan 600 LIZ size standards (Thermo Fisher Scientific) to identify genotypes by the length of the amplicon. Fragment size and intensity were confirmed using Geneious version 9.0.4 (Biomatters, Auckland, New Zealand). We calculated the probability of identity (PID) value using multilocus genotypes obtained from potential parental colonies and small colonies using GenAlEx ( Peakall & Smouse, 2012) for the possibility of clonal occurrence.

Table 1:
Characteristics of microsatellite loci used in this study.
Locus name, forward and reverse primer sequences, microsatellite genotypes (fragment length), fluorescent dye for U19, and GenBank accession number for each locus in Pocillopora acuta (Type 5 in mtORF) (see Nakajima et al., 2017). One colony consistently displayed two genotypes in the fragment analysis.
Locus Forward primer sequence (5′−3′) Reverse primer sequence (5′−3′) Microsatellite genotypes Fluorescent dye for U19 Accession No.
20 colonies 4 colonies
Psp_02 CTGTGCTGGAATTCCCCTTA U19-AGCCTACGGCGCAATAGTAG 261/281 234/234 FAM LC222432
Psp_16 CCCGCTGCTGAGTAAGAATC U19-AGAGAAACTGCAAAACCGC 181/181 187/188 FAM LC222434
Psp_18 CACACGTTTTATGACAACGGA U19-ATAAGCCGTAGGCCCTGTCT 307/327 275/303 FAM LC222435
Psp_23 ACCATTGCCATCACTGTTCA U19-TTCATTCATTCGTATTGGCG 158/158 157/165 VIC LC222436
Psp_29 TTTCGTACCAAAATCCAGGC U19-TTTTTCAGTCGCAAGAGGC 257/262 257/257 VIC LC222437
Psp_32 AAGCACGCAATTCAGCCTAT U19-AGCCTAAGACGAATCGAGCA 127/147 127/127 VIC LC222438
Psp_33 CCATTTCCCGAATCTCTCTC U19-CTCGTCGCCCAGATATAAA 258/266 256/270 NED LC222439
Psp_39 TCTTTACAGCACAGGAGCCA U19-TTTTTCTTGCGGTCCAATTC 121/121 121/121 NED LC222441
Psp_48 TGTAAATTCAAGAGAATGGGCA U19-GTTTCCTGATGGTGTTCT 183/183 183/191 NED LC222443
DOI: 10.7717/peerj.5915/table-1

Results

Almost all of small colonies collected in the outdoor tank were ≤1 cm in width and height, ranging from 7.02 to 19.42 mm in size (sum of the width and height) and from 0.0287 to 0.1807 g in weight, respectively (Fig. 2, File S2). Size and weight were highly correlated (P < 0.001, R2 = 0.920). All small colonies were identified as Pocillopora corals according to a genetic analysis of mitochondrial haplotype. There were at least three genetic species of potential adult pocilloporid colonies in the tank: Pocillopora Type 1 (Pocillopora meandrina/eydouxi species complex), Type 3 (P. verrucosa), Type 5 (Pocillopora acuta, known as Pocillopora damicornis Type β in Schmidt-Roach et al. (2013), and Stylophora C (see File S1) following the nomenclature of Pinzón et al. (2013) for Pocillopora and Flot et al. (2011) for Stylophora. However, all mtORF sequences of the 25 small coral colonies were Pocillopora Type 5. Only one mtORF haplotype was shared between potential adult colony of P. acuta and the 25 small colonies (GenBank accession number LC390046), and two microsatellite multilocus genotypes were detected (20 colonies of one and four of the other) (Table 1). One small colony matched both multilocus genotypes. Peaks showing four or fewer microsatellite alleles were found per microsatellite locus (File S3). One microsatellite multilocus genotype for 20 colonies matched that of a potential adult colony. The PID value was 2.9e−4 in among the 25 colonies (one potential adult colony, 20 colonies with genotype 1 and four colonies with genotype 2; the colony with both multilocus genotypes was removed). Even in the calculation using only 21 colonies (one potential adult colony and 20 colonies with genotype 1), the PID value was 7.4e−3.

Sizes and weights of 25 colonies collected.

Figure 2: Sizes and weights of 25 colonies collected.

The color of the circle corresponds to the microsatellite genotypes (white circle: multilocus genotype 1 for 20 colonies, black circle: multilocus genotype 2 for four colonies), but one colony had two multilocus genotypes (circle with white and black stripes).

Discussion

This study reports the first evidence for asexual recruitment in Pocillopora corals at Okinawa Island. These Pocillopora colonies probably were not all released synchronously, judging from the size differences among them, even though they shared the same multilocus genotype. The multilocus genotype for the 20 colonies matched that of a colony placed in the tank in March, 2017. From the PIDs of potential parental colonies and small colonies, we assume that coral recruits were derived from asexual reproduction. We tried to estimate the index of PSEX using RClone (Bailleul, Stoeckel & Arnaud-Haond, 2016) to assess the possibility of clonality, but there were only two multilocus genotypes, resulting in such low statistical power that we could not calculate appropriate PSEX values in the population (see also Arnaud-Haond et al., 2007; Nakajima et al., 2016). Meanwhile, another multilocus genotype (for four colonies) could not be assigned to any colony in the tank. One possible explanation is that this multilocus genotype may have been derived from a colony collected in Zampa and identified as P. verrucosa (see File S1); however, it died before it could be genotyped. This explanation is based on the assumption that the deceased colonies were actually P. acuta. However, there is a possibility that recruits came from outside the tank because of natural seawater without filtration. Interestingly, one small colony matched both multilocus genotypes. We suspected contamination and extracted genomic DNA again; however, the result was consistent. Thus, this may have been a chimeric colony resulting from allogeneic fusion of planula larvae from two different colonies that were not fused when branches of adult colonies were tried to be fused in P. damicornis (Hidaka, 1985; Hidaka et al., 1997).

Our data show that the small colonies found in the tank had an asexual origin and they were not produced sexually. This means that P. acuta may be able to spawn clonal offspring rapidly and to adapt to local environments easily. It has been confirmed that P. acuta releases sperm during sexual reproduction (e.g., Schmidt-Roach et al., 2014a; Schmidt-Roach et al., 2014b), but that they also produce clonemates (e.g., Torda et al., 2013; Gélin et al., 2017). Clonality of P. acuta was documented in our previous population genetic analysis for corals in the Nansei Islands. A population at Ueno, Miyako Island showed clonality with only 10 different multilocus lineages, among 29 colonies (Nakajima et al., 2017). Powerful waves during tropical storms may cause fragmentation of P. verrucosa colonies (Aranceta-Garza et al., 2012), but only if fragment branches can survive long enough to reattach on the sea bottom can they give rise to viable new colonies. We have observed that for fragile coral colonies of G. fascicularis, fragmented branches formed colonies of small, clonal-like branches with a original branch. Actually, clonemates of G. fascicularis had been often found in the Nansei Islands (Nakajima et al., 2015; Nakajima et al., 2016). However, in our outdoor tank, most colonies of P. acuta appear to result from asexual planula larvae. If these small colonies had been derived from fragmentation, fragmented branches would have sunk to the bottom, rather than attaching to the side wall, especially near the surface (see Fig. 1D). This result suggests that clonal colonies of P. acuta in Okinawa have been maintained asexually with planula larvae, though the frequency of fragmentation is not yet known. In Eastern Australia, P. acuta also releases brooded asexual larvae (Schmidt-Roach et al., 2013) as do morphological P. damicornis in Western Australia (Stoddart, 1983; Ayre & Miller, 2004) and Taiwan (Yeoh & Dai, 2010). Our research provides additional evidence that clonal reproduction is one of the reproductive strategies adopted by P. acuta.

However, polyp bail-out in Pocillopora must be considered in stressful local environments (P-S Chuang, Y Nakajima & S Mitarai, 2018, unpublished data). Coral polyps are expelled into the water column under extreme stress (Oculina patagonica: Kramarsky-Winter, Fine & Loya, 1997; Seriatopora hystrix: Sammarco, 1982; P. damicornis: Fordyce, Camp & Ainsworth, 2017). It is possible that expelled polyps have settlement competency like that of planula larvae; however, that possibility requires validation. In addition, physiological experiments are needed to estimate the timing and condition of planula release and polyp bail-out. With the data collected here, it is impossible to determine whether these small clonal colonies were from released planula larvae or from bail-out due to environmental conditions. Our observations help to better understand coral physiology and ecology of sustainable coral populations and they provide new data about the reproductive characteristics of corals inhabiting the Nansei Islands.

Conclusion

In this study, we found evidence of asexual recruitment that is supported by genetic analysis. These Pocillopora colonies probably were not released synchronously judging from size differences among the colonies. This is the first report of asexual reproduction in a species of Pocillopora at Okinawa Island. One small colony appeared to be a chimeric colony resulting from the allogeneic fusion of planula larvae. This research improves our understanding of coral physiology and life history, and contributes to sustainability of coral populations in the Nansei Islands.

Supplemental Information

A list of corals kept in the outdoor tank

Mitochondrial DNA types of corals were defined following Nakajima et al. (2016) for Galaxea fascicularis, Pinzón et al. (2013) for genus Pocillopora and Flot et al. (2013) for Stylophora pistillata.

DOI: 10.7717/peerj.5915/supp-1

Size and weight of each colony

Size means sum of maximum width and height of each colony. Bold means maximum or minimum value in the column.

DOI: 10.7717/peerj.5915/supp-2

Microsatellite peaks of colonies including the allogenically fused colony

These peaks were output from Geneious after fragment analysis on an ABI 3130xl capillary DNA sequencer. A: Psp_02 (blue), Psp_23 (green), and Psp_33 (black). B: Psp_16 (blue), Psp_29 (green), and Psp_39 (black). C: Psp_18 (blue), Psp_32 (green), and Psp_48 (black). Specific information for each locus is shown in Table 1.

DOI: 10.7717/peerj.5915/supp-3