Scleractinian corals (Fungiidae, Agariciidae and Euphylliidae) of Pulau Layang-Layang, Spratly Islands, with a note on Pavonamaldivensis (Gardiner, 1905).
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Scleractinian corals (Fungiidae, Agariciidae and Euphylliidae) of Pulau Layang-Layang, Spratly Islands, with a note on Pavona maldivensis (Gardiner, 1905)
Abstract
Layang-Layang is a small island part of an oceanic atoll in the Spratly Islands off Sabah, Malaysia. As the reef coral fauna in this part of the South China Sea is poorly known, a survey was carried out in 2013 to study the species composition of the scleractinian coral families Fungiidae, Agariciidae and Euphylliidae. A total of 56 species was recorded. The addition of three previously reported coral species brings the total to 59, consisting of 32 Fungiidae, 22 Agariciidae, and five Euphylliidae. Of these, 32 species are new records for Layang-Layang, which include five rarely reported species, i.e., the fungiids Lithophyllon ranjithi, Podabacia sinai, Sandalolitha boucheti, and the agariciids Leptoseris kalayaanensis and Leptoseris troglodyta. The coral fauna of Layang-Layang is poor compared to other areas in Sabah, which may be related to its recovery from a crown-of-thorns seastar outbreak in 2010, and its low habitat diversity, which is dominated by reef slopes consisting of steep outer walls. Based on integrative molecular and morphological analyses, a Pavona variety with small and extremely thin coralla was revealed as Pavona maldivensis. Since specimens from Sabah previously identified as Pavona maldivensis were found to belong to Pavona explanulata, the affinities and distinctions of Pavona maldivensis and Pavona explanulata are discussed.
Introduction
Pulau [island] Layang-Layang is a small island standing 2 m high on the southeast rim of a reef known as Swallow Reef (Hancox and Prescott 1995). The reef is an atoll situated at the southern edge of the Spratly Islands in the South China Sea, approximately 300 km northwest of Kota Kinabalu, Sabah, Malaysia. Layang-Layang was reported to have one of the best reefs in East Malaysia in terms of coral cover and diversity and fish life (Ismail et al. 1998; Pilcher and Cabanban 2000).
Being remote, the reef was regarded to be in pristine condition (Pilcher et al. 1999; Pilcher and Cabanban 2000; Zainuddin et al. 2000), although it had experienced disturbances in the past years. In the 1980s, reclamation work was carried out to accommodate a military base, and in the 1990s the island was further extended to construct an airstrip, a resort and a seawall. For the latter developments, coral and sand were mined from the lagoon for building material. A comparative study in 1993 and 1998 showed that the impact of the development on the reef was most evident in the lagoon, with a reduction on live coral cover from 29% to 10% (Mohamed et al. 1994; Zakariah et al. 2007). The outer reefs were not affected by the construction development, except at sites immediate to the island. Here the coral cover averaged 48% at 5 m and 34% at 10 m depth in 1993 (Mohamed et al. 1994). At subsequent independent surveys from 1996 to 1999 in four outer reef sites, mean live coral cover was 73% at 5 m and 58% at 10 m depth (Pilcher and Cabanban 2000).
A massive coral bleaching event during the 1997–98 El Niño event had also affected the reefs of Layang-Layang. Up to 40% of the coral colonies at less than 10 m depth and 25% at 10-20 m depth were bleached at 55 monitoring sites, but by 1999 the corals had recovered or were overgrown with zoantharians and soft corals (Pilcher and Cabanban 2000).
A recent calamity to confront the reefs was an outbreak of the crown-of-thorns (COT) seastar, Acanthaster planci (Linnaeus, 1758), in July 2010. During a 3-day survey, densities of 1,011 COTs were counted in a 7,000 m2 reef area over eight sites, which corresponds to over 1,400 individuals per ha with dominant size class of 21-30 cm (Nasrulhakim et al. 2010). During the time of the survey, reefs in the southwest of the atoll were badly damaged and had dead corals covered by algae. Although damage to the reefs was not quantified, it was noted that COT had started to infest the reefs in the northwest of the atoll and coral mortality was not as extensive as compared to the reefs in the southwest (Nasrulhakim et al. 2010).
While several short research expeditions and surveys have been carried out to collect baseline information on the marine biodiversity of Pulau Layang-Layang (Zakariah et al. 2007), only one checklist of hard coral species is available as reference, with over 140 species reported by Ridzuan et al. (n.d.) cited in Pilcher and Cabanban (2000) (pp 46–47, Suppl. material VI). In the present study, we aim to update the species list of the hard coral families Fungiidae, Agariciidae and Euphylliidae in Layang-Layang, as similarly done for the reefs of Sabah, Malaysia (Waheed and Hoeksema 2013, 2014). These families, together consisting of ~100 species, were selected as a proxy for scleractinian reef coral diversity, as they can be found in a variety of reef habitats and in a wide geographical range within the Indo-Pacific (Veron 2000). At the time of the survey, small, thin and encrusting corals thought to belong to an unknown Pavona species were encountered. Several specimens that were collected for closer inspection of corallite morphology appeared to match with Pavona maldivensis (Gardiner, 1905) despite the unusual growth form of the corallum. For verification, a comparison was made between these Pavona maldivensis specimens and those collected from other localities including its type locality in the Maldives. Samples of Pavona explanulata (Lamarck, 1816) closely resembling Pavona maldivensis were also examined in order to better define the boundaries between these two species.
Methods
Physical setting
Pulau Layang-Layang (7°22'20"N, 113°50'30"E) measures approximately 1,500 m × 200 m (Google Earth 2013). The only infrastructures on the island are buildings of the Royal Malaysian Navy base, the Marine Research Station Layang-Layang (MARSAL) of the Fisheries Department and the Avillion Layang-Layang Resort. An airstrip runs alongside these establishments. The atoll is somewhat oval in shape situated in a SW-NE axis and measures approximately 7 km long and 2 km wide. Its rim is formed by a ring of 13 shallow reefs, which covers an area of over 4 km2 (Musa et al. 2006). The reef circumference is almost 17 km with a sandy cove at the western end and it encloses a shallow lagoon with a maximum depth of 20 m (Pilcher et al. 1999, Sahari et al. 2004, Svrcula 2008). The reefs rise to sea level from around 1,500 m depth forming steep outer reef walls (see Hutchison and Vijayan 2010). The north and northeast reef slopes have a more gradual profile to depths of 20–25 m before plunging down steeply, as compared to the reefs in the south and southwest where the reefs form vertical walls.
Water parameters were measured at 10 m depth of each survey site (Suppl. material 1). The water temperature ranged 28.4–30.0 °C, with a salinity range of 30.1–31.2 ppt. Temperature and salinity measurements were slightly higher in July 2002 (see Ku Yaacob and Ibrahim 2004) in comparison to our readings in March 2013.
Layang-Layang in the South China Sea is influenced by the monsoon system (see Wyrtki 1961). The northeast monsoon dominates between November to March and the southwest monsoon prevails from May to September (Saadon et al. 1999, Morton and Blackmore 2001, Ku Yaacob and Ibrahim 2004, Akhir 2012) while the transitional periods are in April and October (Saadon et al. 1999). The surface current patterns are characterised by the monsoonal system (Akhir 2012). The northeast monsoon causes an anticlockwise circulation pattern in the South China Sea, creating a southwesterly current from the northern rim of the sea, which either departs via the Karimata Straits or turns northeasterly along the west coast of Borneo (East Malaysia) and Palawan, whereas the southwest monsoon reverses the current direction, driving a northward current in the central South China Sea while creating a clockwise gyre above the Spratly Islands (Wyrtki 1961, Morton and Blackmore 2001). The rainy season occurs during the northeast monsoon and due to unpredictable weather Layang-Layang is not accessible for diving. The diving season lasts from March to September annually.
Field sampling
Fieldwork was carried out 24–30 March 2013 on the reefs of Layang-Layang. Due to safety issues, surveys were confined to dive sites designated for tourism around the atoll. A total of 18 sites was surveyed on the outer slope of the reef wall from a maximum depth of 40 m to the shallow reef crest of 1 m using the roving diver technique (Schmitt et al. 2002) (Figure (Figure1,1, Table Table1).1). An additional dive was made at the House Reef (10 m maximum depth) off the resort jetty (7°22'23"N, 113°50'37"E). A checklist of the coral families Fungiidae (sensu Gittenberger et al. 2011, Benzoni et al. 2012a), Agariciidae and Euphylliidae (sensu Veron 2000) was made for each site with photo documentation of each species. Specimens that could not be identified in situ were collected for further examination and are kept at the Borneo Marine Research Institute reference collection, Universiti Malaysia Sabah (UMS) in Kota Kinabalu.
Table 1.
Locality data of survey sites at Pulau Layang-Layang, Spratly Islands.
| Site | Site name | Latitude (N) | Longitude (E) | Date | Max. depth (m) |
|---|---|---|---|---|---|
| 1 | Snapper Ledge | 07°22.048 | 113°48.467 | 24/03/2013 | 31.8 |
| 2 | Dogtooth Lair | 07°22.470 | 113°51.100 | 24/03/2013 | 30.7 |
| 3 | Wrasse Strip | 07°22.557 | 113°47.397 | 25/03/2013 | 30.3 |
| 4 | Shark Cave 1 | 07°22.279 | 113°47.457 | 25/03/2013 | 32.6 |
| 5 | D’Wall | 07°22.191 | 113°47.701 | 25/03/2013 | 33.8 |
| 6 | Gorgonian Forest | 07°22.710 | 113°51.218 | 26/03/2013 | 37.9 |
| 7 | Shark Cave 2 | 07°22.323 | 113°47.321 | 26/03/2013 | 27.9 |
| 8 | Crack Reef | 07°22.876 | 113°48.910 | 26/03/2013 | 29.3 |
| 9 | Coral Café | 07°22.773 | 113°51.144 | 27/03/2013 | 38.5 |
| 10 | Wrasse Strip 2 | 07°22.555 | 113°47.371 | 27/03/2013 | 33.5 |
| 11 | Wreck Point | 07°22.407 | 113°51.032 | 27/03/2013 | 33.3 |
| 12 | Wreck Point 2 | 07°22.197 | 113°50.649 | 28/03/2013 | 40.4 |
| 13 | Navigator Lane | 07°23.110 | 113°49.979 | 28/03/2013 | 36.8 |
| 14 | The Point | 07°22.573 | 113°51.254 | 28/03/2013 | 34.2 |
| 15 | Coral Café 2 | 07°23.013 | 113°50.912 | 29/03/2013 | 36.7 |
| 16 | Mid Reef | 07°22.725 | 113°48.539 | 29/03/2013 | 37.7 |
| 17 | The Valley | 07°22.447 | 113°47.180 | 29/03/2013 | 34.8 |
| 18 | Runway | 07°21.902 | 113°49.778 | 30/03/2013 | 40.3 |
Coral specimens were identified by referring to taxonomic literature (Dinesen 1980, Veron and Pichon 1980, Hoeksema 1989, 2012a, 2012b, 2014, Veron 2000, Ditlev 2003, Licuanan and Aliño 2009, Gittenberger et al. 2011, Benzoni et al. 2012a). Recent molecular studies have led to taxonomic revisions of many scleractinian corals, including the families Agariciidae and Euphylliidae (sensu Veron 2000). The genera Coeloseris, Pachyseris, Catalaphyllia, Nemenzophyllia, Physogyra and Plerogyra are now classified incertae sedis (Fukami et al. 2008, Kitahara et al. 2010, Benzoni et al. 2014). Nevertheless, these genera were included in the checklist for comparison with similar studies previously conducted around Sabah (Waheed and Hoeksema 2013, 2014, Waheed et al. subm).
Specimens of a thin morph of Pavona maldivensis were collected and small fragments were preserved in 95% absolute ethanol for molecular analyses. The specimens were bleached with sodium hypochlorite, rinsed, air-dried and small fragments were taken for morphological examination. The remaining coralla of these specimens are kept in the dry reference collection of the Borneo Marine Research Institute, UMS.
Further examination of Pavona corals
Seven samples of Pavona maldivensis corals collected from Layang-Layang and samples from Banggi, North Sabah (n=1), Ternate, Indonesia (n=1), New Caledonia (n=2) and the Maldives (n=2) were used for further molecular and morphological analyses. Samples of Pavona explanulata collected from Banggi, North Sabah (n=1), Ternate, Indonesia (n=2) and Redang, Peninsular Malaysia (n=1) closely resembling Pavona maldivensis were also included. In total, 17 samples were used in the analyses (Suppl. material 2).
Molecular analyses
Coral samples were sequenced for two markers, namely the mitochondrial intergenic spacer between CO1 and 16S-rRna (IGR for short; Terraneo et al. 2014) and the nuclear internal transcribed spacers 1 and 2 including the 5.8S region (ITS for short; White et al. 1990, Takabayashi et al. 1998). DNA extraction was performed using the DNeasy Blood and Tissue Kit (QIAGEN) following the manufacturer’s protocol for animal tissue. The samples were left to incubate overnight. The extracts had concentrations of between 1 to 3 ng/µl for the PCR, quantified using a NanoDrop ND-1000 Spectrophotometer. The PCR mixture was composed of 2.5 µl CoralLoad Buffer (containing 15 mM MgCl2), 1.0 µl of each primer (10 pmol), 0.5 µl dNTPs (2.5 mM), 0.5 µl Taq polymerase (15 units/ µl), 18.5 µl of extra pure water and 1.0 µl DNA extract. The primer sequences and PCR amplification details are provided in Table Table2.2. The PCR cycles consisted of an initial denaturation step of 95 °C for 2 min, followed by 39 cycles of 95 °C for 30 s, annealing temperature for 1 min, extension step of 72 °C for 1 min and a final elongation step of 72 °C for 5 min. The PCR products were run on a 1% agarose gel electrophoresis, stained with ethidium bromide and visualized on a RedTM Personal Imaging System. Successfully amplified samples were sent to Macrogen Europe for bidirectional sequencing on an ABI Automated Sequencher 3730xl. The sequences were edited and assembled with Sequencher 4.10.1 and the consensus sequences were blasted against GenBank to check for specific amplification or contamination.
Table 2.
Primer pairs, gene region, fragment size, annealing temperature and references of the molecular markers used in this study.
| Name | Primer | Gene region | Fragment size | Annealing temp. | Reference |
|---|---|---|---|---|---|
| AGAH | GCT TGA CAG GGT TTC CAA GA | COI-1-rRNA intron | ~1200 | 54 °C | Terraneo et al. (2014) |
| AGAL | CGC ATT GAA ACA CGA GCT TA | COI-1-rRNA intron | ~1200 | 54 °C | Terraneo et al. (2014) |
| ITS4 | CCT CCG CTT ATT GAT ATG C | ITS1-5.8S-ITS2 | ~700 | 55 °C | White et al. (1990) |
| A18S | GAT CGA ACG GTT TAG TGA GG | ITS1-5.8S-ITS2 | ~700 | 55 °C | Takabayashi et al. (1998) |
Sequences were aligned on the GUIDANCE server using PRANK algorithm (Penn et al. 2010a, b) and pruned in BioEdit 7.2.5 (Hall 1999). Gaps were treated as missing data. Pairwise genetic differences were calculated as uncorrected p-distance in MEGA 6.06 (Tamura et al. 2013). The most appropriate model of nucleotide substitution based on the Akaike Information Criterion (AIC) as determined in jModelTest 2.1.6 (Darriba et al. 2012) was a three-parameter model a proportion of invariant sites (TPM3uf+I) for IGR and a Kimura two-parameter model with a proportion of invariant sites and gamma distributed rates (K80+I+G) for ITS. Phylogenies were reconstructed separately for each marker and for the concatenated dataset partitioned by genes based on three optimality criteria.
Maximum Likelihood (ML) analyses were carried out in Garli 2.0 (Zwickl 2006) with the default configuration settings. Separate runs were made for searching the ML tree (100 replicates of random addition) and bootstrapping (1000 replicates). The bootstrap consensus tree was visualised with SumTrees 3.3.1 of the DendroPy 3.12.0 package (Sukumaran and Holder 2010) with a majority rule consensus that includes branch length information. Maximum Parsimony (MP) analyses were conducted in PAUP* 4.0a136 (Swofford 2002) using heuristic searches with 100 replicates of random addition with a Tree Bisection and Reconnection (TBR) branch swapping method. Branch support was obtained with 1000 bootstrap replicates to produce a majority rule consensus tree. Bayesian Inferences (BI) were made in MrBayes 3.2.2 (Huelsenbeck and Ronquist 2001, Ronquist and Huelsenbeck 2003, Ronquist et al. 2012), whereby four Markov Chain Monte Carlo (MCMC) of 10 million generations were applied in two runs, saving one tree every 100 generations and discarding the initial 25% of the total trees as burnin. The average standard deviation of split frequencies after 10 million generations was 0.001615 for IGR, 0.001679 for ITS and 0.001840 for the concatenated dataset in the Bayesian analyses. For the mtDNA phylogeny, sequences of Pavona maldivensis and Pavona explanulata available on GenBank (Luck et al. 2013) were included in the analyses. In order to root the trees, the closely related species Leptoseris foliosa was selected as outgroup (Benzoni et al. 2012b, Terraneo et al. 2014). Novel sequences were submitted to GenBank (accession numbers KR706116–KR706143).
Morphological analyses
A subset of the Pavona corals was examined under a Leica MZ16 microscope and analysed using scanning electron microscope (SEM). Coral fragments were mounted on SEM stubs using blu-tack and coated with Pd/Au for 8 minutes. Images were taken with a JEOL JSM6490LV scanning electron microscope. Distinguishing characters for species identification include macromorphological features of the corallum and calices as well as micromorphological features of the septocostae, columella and radial elements (terminology according to Dinesen 1980, Budd et al. 2012, Benzoni et al. 2012b). Original species descriptions of Pavona maldivensis and Pavona explanulata as well as descriptions by Wells (1954), Pillai and Scheer (1976), Scheer and Pillai (1983), Veron and Pichon (1980) were used as references.
Results
Coral checklist
The number of scleractinian corals recorded in the study area is 56 species with 31 Fungiidae, 22 Agariciidae and three Euphylliidae (Table (Table3,3, Figures Figures22–8, Suppl. material 3). Thirty-two species were not documented from Layang-Layang before and are considered new records (17 Fungiidae, 14 Agariciidae, and one Euphylliidae). Most coral colonies were small in size, making identification difficult for some specimens. Specimens that could not be identified to species level in situ include corals of three Leptoseris spp. (Figure (Figure9).9). All were encountered once, except Leptoseris sp. 1 at two sites. The House Reef within the lagoon was species-poor in terms of Scleractinia and only one fungiid species, Danafungia horrida, was encountered.
Fungiidae recorded at Pulau Layang-Layang in this study. a Ctenactis albitentaculata b Cycloseris boschmai c Cycloseris costulata d Cycloseris explanulata e Cycloseris mokai f Cycloseris tenuis g Danafungia horrida h Danafungia scruposa.
Euphylliidae recorded at Pulau Layang-Layang in this study. a Euphyllia glabrescens b Euphyllia paraancora c Physogyra lichtensteini.
Undetermined Leptoseris coral species recorded at Pulau Layang-Layang in this study a Leptoseris sp. 1 (registration no. IPMB-C 13.00009) b Leptoseris sp. 2 c Leptoseris sp. 3.
Table 3.
Checklist of hard coral families Fungiidae, Agariciidae and Euphylliidae from 18 sites at Layang-Layang. Species marked with an asterisk (*) are now considered incertae sedis. The number of sites indicate the species occurrence frequencies. The figure number corresponds with photos in Figures Figures22 to to8,8, while a dash (-) denotes no available photo from the surveys. Previous records are indicated as follows: a = Pilcher and Cabanban (2000), b = Abdullah (2005), dash (-) = species not reported before, therefore are considered new records for Layang-Layang.
| Family | No. | Species | No. of sites | Figure no. | Previous records |
|---|---|---|---|---|---|
| Fungiidae | 1 | Ctenactis albitentaculata Hoeksema, 1989 | 1 | 2a | b |
| 2 | Ctenactis crassa (Dana, 1846) | 15 | - | b | |
| 3 | Ctenactis echinata (Pallas, 1766) | 12 | - | a | |
| 4 | Cycloseris boschmai Hoeksema, 2014 | 6 | 2b | - | |
| 5 | Cycloseris costulata (Ortmann, 1889) | 12 | 2c | - | |
| 6 | Cycloseris cyclolites (Lamarck, 1815) | 1 | - | - | |
| 7 | Cycloseris explanulata (Van der Horst, 1922) | 2 | 2d | - | |
| 8 | Cycloseris mokai (Hoeksema, 1989) | 6 | 2e | - | |
| 9 | Cycloseris sinensis Milne Edwards & Haime, 1851 | 1 | - | - | |
| 10 | Cycloseris tenuis (Dana, 1846) | 11 | 2f | - | |
| 11 | Danafungia horrida (Dana, 1846) | 13 | 2g | a | |
| 12 | Danafungia scruposa (Klunzinger, 1879) | 13 | 2h | a | |
| 13 | Fungia fungites (Linnaeus, 1758) | 15 | 3a | a, b | |
| 14 | Halomitra pileus (Linnaeus, 1758) | 5 | 3b | a | |
| 15 | Herpolitha limax (Esper, 1797) | 15 | 3c | a, b | |
| 16 | Lithophyllon concinna (Verrill, 1864) | 13 | - | - | |
| 17 | Lithophyllon ranjithi Ditlev, 2003 | 7 | 3d | - | |
| 18 | Lithophyllon repanda (Dana, 1846) | 17 | 3e | b | |
| 19 | Lithophyllon scabra (Döderlein, 1901) | 12 | 3f | - | |
| 20 | Lithophyllon undulatum Rehberg, 1892 | 4 | 3g | a | |
| 21 | Lobactis scutaria (Lamarck, 1801) | 15 | 3h | b | |
| 22 | Pleuractis granulosa (Klunzinger, 1879) | 12 | 4a | - | |
| 23 | Pleuractis gravis (Nemenzo, 1955) | 5 | 4b | - | |
| 24 | Pleuractis moluccensis (Van der Horst, 1919) | 6 | 4c | a | |
| 25 | Pleuractis paumotensis (Stutchbury, 1833) | 16 | - | - | |
| 26 | Podabacia motuporensis Veron, 1990 | 1 | - | - | |
| 27 | Podabacia sinai Veron, 2000 | 1 | 4d | - | |
| 28 | Polyphyllia talpina (Lamarck, 1801) | 1 | 4e | a, b | |
| 29 | Sandalolitha boucheti Hoeksema, 2012 | 2 | 4f | - | |
| 30 | Sandalolitha dentata Quelch, 1884 | 12 | 4g | - | |
| 31 | Sandalolitha robusta (Quelch, 1886) | 9 | 4h | a, b | |
| Agariciidae | 32 | Coeloseris mayeri Vaughan, 1918* | 3 | 5a | - |
| 33 | Gardineroseris planulata (Dana, 1846) | 7 | 5b | a | |
| 34 | Leptoseris foliosa Dinesen, 1980 | 5 | 5c | - | |
| 35 | Leptoseris glabra Dinesen, 1980 | 17 | 5d | - | |
| 36 | Leptoseris hawaiiensis Vaughan, 1907 | 12 | 5e | - | |
| 37 | Leptoseris incrustans (Quelch, 1886) | 9 | 5f | - | |
| 38 | Leptoseris kalayaanensis Licuanan and Aliño, 2009 | 13 | 5g | - | |
| 39 | Leptoseris mycetoseroides Wells, 1954 | 18 | 5h | a | |
| 40 | Leptoseris scabra Vaughan, 1907 | 12 | 6a | - | |
| 41 | Leptoseris solida (Quelch, 1886) | 6 | 6b | - | |
| 42 | Leptoseris troglodyta Hoeksema, 2012 | 1 | 6c | - | |
| 43 | Leptoseris yabei (Pillai and Sheer, 1976) | 1 | 6d | - | |
| 44 | Pachyseris rugosa (Lamarck, 1801)* | 8 | 6e | a | |
| 45 | Pacyhseris speciosa (Dana, 1846)* | 6 | 6f | a | |
| 46 | Pavona bipartita Nemenzo, 1980 | 3 | 6g | - | |
| 47 | Pavona clavus (Dana, 1846) | 3 | 6h | a | |
| 48 | Pavona duerdeni Vaughan, 1907 | 5 | 7a | - | |
| 49 | Pavona explanulata (Lamarck, 1816) | 6 | 7b | a | |
| 50 | Pavona maldivensis (Gardiner, 1905) | 4 | 7c | - | |
| 51 | Pavona minuta Wells, 1954 | 6 | 7d | a | |
| 52 | Pavona varians Verrill, 1864 | 14 | 7e | a | |
| 53 | Pavona venosa (Ehrenberg, 1834) | 9 | 7f | - | |
| Euphylliidae | 54 | Euphyllia glabrescens (Chamisso & Eysenhardt, 1821) | 1 | 8a | a |
| 55 | Euphyllia paraancora Veron, 1990 | 1 | 8b | - | |
| 56 | Physogyra lichtensteini Milne Edwards & Haime, 1851* | 1 | 8c | a |
Other coral species recorded at Layang-Layang during earlier studies, but not encountered during the present survey are the fungiids Heliofungia actiniformis (Quoy & Gaimard, 1833) and Podabacia crustacea (Pallas, 1766), the agariciids Pavona cactus (Forskål, 1775) and Pavona decussata (Dana, 1846), and the euphylliids Euphyllia ancora Veron & Pichon, 1980 and Plerogyra sinuosa (Dana, 1846) (Pilcher et al. 1999, Pilcher and Cabanban 2000). The presence of Heliofungia actiniformis and both euphylliids was verified by images in Pilcher et al. (1999), thus bringing the total species count to 59 (Table (Table44).
Table 4.
Hard coral species that were not encountered in the present study. Species marked with an asterisk (*) is now considered incertae sedis. Previous records are indicated as follows: a = Pilcher et al. (1999), b = Pilcher and Cabanban (2000). The presence of Heliofungia actiniformis, Euphyllia ancora and Plerogyra sinuosa are verified by images in Pilcher et al. (1999).
| Family | No. | Species | Previous records | Status |
|---|---|---|---|---|
| Fungiidae | 1 | Heliofungia actiniformis (Quoy & Gaimard, 1833) | a, b | Verified |
| 2 | Podabacia crustacea (Pallas, 1766) | b | Unverified | |
| Agariciidae | 3 | Pavona cactus (Forskål, 1775) | b | Unverified |
| 4 | Pavona decussata (Dana, 1846) | b | Unverified | |
| Euphylliidae | 5 | Euphyllia ancora Veron & Pichon, 1980 | a, b | Verified |
| 6 | Plerogyra sinuosa (Dana, 1846)* | a, b | Verified |
Pavona corals – molecular perspective
Sequences were obtained from 11 and 17 Pavona samples for the IGR and ITS markers, respectively. Amplification success for the IGR marker was rather low and the length of the sequences ranged between 432 and 887 bp, shorter than the expected length of ~1200 bp (Terraneo et al. 2014). Tree topologies obtained from the ML, MP and BI analyses for each gene and the concatenated dataset were comparable so only the ML phylogram is shown. There were some differences in the topology between the IGR and ITS phylogeny trees, but the ITS tree was less resolved and has lower support values (Suppl. material 4). The topology of the IGR tree is almost similar with the concatenated sequences tree and has well-supported basal clades, hence we focus on the latter. The final alignment of the concatenated sequences consisted of 1360 characters with 1243 constant, 35 variable and 82 parsimony informative characters. The phylogram consists of four clades (Figure (Figure10).10). Samples of the Pavona maldivensis from Layang-Layang (samples with LAC labels) clustered with those of Pavona maldivensis from other areas (clade I). Clade II consists of a single specimen of Pavona cf. explanulata from Hawaii (Luck et al. 2013). Samples BAN02 from Banggi, North Borneo and TER28 from Ternate, Indonesia, initially identified as Pavona maldivensis during in situ observations from previous studies clustered together with Pavona explanulata samples (clade III). Pavona cf. explanulata from Redang, Peninsular Malaysia formed clade IV. The pairwise genetic difference between clades, although considerably low, were highest between clade II and clade IV (0.073 ± 0.011), followed by clade II and clade III (0.066 ± 0.011) and clade I and clade IV (0.047 ± 0.005). The intraspecific genetic distance within the clades was also very low: 0.004 ± 0.001 for clade I and 0.008 ± 0.002 for clade III.
Maximum likelihood phylogram of Pavona maldivensis and Pavona explanulata based on combined mitochondrial intergenic spacer between CO1 and 16S-rRna and nuclear marker ITS1-5.8S-ITS2 sequences. Support values for maximum likelihood, maximum parsimony (>70) and bayesian posterior probabilities (>80) are given at the nodes. Dashes (-) indicate nodes without statistical support. Letters in parentheses correspond to images a–l in rows L and R. L: coral colonies in situ, R: SEM images of calices. Locality for the coral samples are: LAC = Layang-Layang, LOY = Loyalty Islands, MAL = the Maldives, BAN = Banggi, East Malaysia, TER = Ternate, Indonesia, RED = Redang, Peninsular Malaysia. a–b Pavona maldivensis from Layang-Layang c–d Pavona maldivensis from Loyalty Islands e–f Pavona maldivensis from the Maldives g–h Pavona explanulata from Banggi, Sabah i–j Pavona explanulata from Banggi, Sabah k–l Pavona explanulata from Ternate, Indonesia. Additional samples KF437780 Pavona maldivensis and KF437762 Pavona cf. explanulata are from Pearl and Hermes Atoll, the northwest Hawaiian Islands and O’ahu, Hawaii, respectively (Luck et al. 2013). Outgroup LK934507, HE978501 Leptoseris foliosa is from Prony Bay, New Caledonia (Benzoni et al. 2012b, Terraneo et al. 2014).
Pavona corals – morphology
Macro- and micromorphology features of the Pavona corals support the clades of the molecular analyses (Figure 10a–l, Suppl. material 5). In general, the Pavona maldivensis specimens from Layang-Layang were small in size, the largest measured 11 cm × 8 cm while the smallest was 3.5 cm × 3 cm. All Pavona maldivensis specimens from Layang-Layang had paper-thin coralla (≤1 mm) and were found encrusting the reef wall (e.g. Figure Figure7c).7c). Several specimens had knobs or rounded columns protruding from the corallum (Figure 10a). The specimen from the Maldives has a columnar or club-shaped growth form (Figure 10e). The corallite morphology is variable within the same specimen, largely depending on the position of the corallites in the corallum. Calices at the top of the knobs or columns are small and compact and become larger and widely spaced towards the base or on horizontal plates (see Gardiner 1905). Calices vary from circular, distinctly raised edges (plocoid) (Figure 10d) to broad, flattened edges particularly at the base of the colony (Figure 10f), or a combination of both features (Figure 10b) when inclined towards the margin. Calices with raised walls protrude up to 2–4 mm. The columella is well-developed in the form of a peg (Figure 10b) or a single, rounded or twisted rod (Figure 10d, f).
Agariciidae recorded at Pulau Layang-Layang in this study. a Pavona duerdeni b Pavona explanulata c Pavona maldivensis (registration no. IPMB-C 13.00007) d Pavona minuta e Pavona varians f Pavona venosa.
Specimens of Pavona explanulata were either encrusting (Figure 10g, i), submassive (Figure 10k) or a combination of submassive with plate margins. Corallites may have irregular arrangements and shapes and mostly lack any form of wall (theca), giving the corallum a smooth surface appearance. Veron and Pichon (1980) described the thecae as “synapticulothecate”, if present, which is defined as rod-or bar-like structures extending between the septa (Budd et al. 2012). In plate colonies, the corallites are inclined towards the margin and usually in parallel rows. The columella consists of several fused processes that extend from the radial elements into the fossa (Figure 10h) or a single process, which appears as a twisted rod (Figure 10j, l). Synapticular rings may be visible in this species (Figure 10j, l). The specimen from Redang, Peninsular Malaysia looks superficially like Pavona explanulata, but the morphology differs from the rest of the Pavona explanulata specimens by the deeply seated columella and the widely spaced septa (Figure (Figure11).11). This specimen resembles Pavona cf. explanulata in Veron and Pichon (1980: Fig. 31).
Specimen RED05 Pavona cf. explanulata from Pulau Redang, Peninsular Malaysia. a coral colony in situ at 13 m depth b corallites detail at the plate margin c coral fragment preserved in ethanol d, e SEM images showing calices.
Septocostae of both Pavona species are closely compacted, but in Pavona maldivensis they have denser granulated sides (Figure (Figure12).12). In Pavona explanulata, the order of septa may alternate between thin with rows of fine granules and thick with prominent spines. The upper margin of the septa (forming radial elements) consist of beaded granules in Pavona maldivensis, and in Pavona explanulata it appears to taper into a somewhat straight ridge. The side walls or lateral faces of the septa are covered with granules either in rows or scattered on the surface (e.g. Figure 12a, d). Aligned granulations alongside the lateral faces also known as menianae (Kitahara et al. 2010, Benzoni et al. 2012b, Terraneo et al. 2014), or menianes (Kitahara et al. 2012, Hoeksema 2012b), are more obvious in Pavona explanulata (Figure 12b, d) as compared with Pavona maldivensis, which has short series of menianae, if formed (Figure 12c). Radial elements of Pavona explanulata can have almost smooth margins (e.g. Figure 12b), and this has been described by Veron and Pichon (1980) for the second order septa of this species. A summary of the variation in morphological characters between Pavona maldivensis and Pavona explanulata is given in Table Table55.
Variation of radial elements in Pavona maldivensis (a, c) and Pavona explanulata (b, d). a specimen LAC23 from Layang-Layang, b specimen BAN02 from Banggi, North Borneo, c specimen LOY12 from Loyalty Islands, and d specimen TER28 from Ternate, Indonesia. Lateral faces of septa are covered with granules (g) as indicated in a and d. Aligned granulations along the lateral faces of septa (menianae) are indicated by white arrows in b, c, d.
Table 5.
Summary of variation in morphological characters between Pavona maldivensis and Pavona explanulata.
| Morphological characters | Pavona maldivensis | Pavona explanulata |
|---|---|---|
| Growth form | Encrusting; paper-thin coralla, club-shaped (specimen from the Maldives) | Encrusting, submassive; may have plate margins |
| Corallite (arrangement) | Small and compact (top of the colony), widely spaced (base of the colony) | Irregular spacing and arrangement, in parallel rows towards the margin |
| Corallite (shape) | Circular, plocoid, flattened edges when inclined towards the margin | Irregular shape, but may be somewhat circular |
| Theca | Distinct; plocoid | Mostly lacking, synapticulothecate if present |
| Columella | Well-developed; peg-like, single, rounded or twisted rod | Several fused processes |
| Septo-costae | Compact, dense granulated sides | Compact, septa alternate between thin with fine granules and thick with spines |
| Radial elements | Beaded granules | Tapers into straight ridge, may have smooth margins |
| Lateral faces | Granules in rows or scattered on the surface, may form short series of menianae | With granules and meaninae |
Discussion
Species occurrence
The total number of coral species noted at Layang-Layang is lower than that of other localities in Sabah where similar surveys have been conducted. Nevertheless, the overall species diversity is considered high even for fungiid corals, despite the fact that steep reef walls are hostile environments for free-living mushroom corals, as they can get dislodged from these drop-offs (Hoeksema and Moka 1989). In contrast, agariciid corals of the genus Leptoseris are known to flourish at greater depths (Kahng and Maragos 2006, Rooney et al. 2010, Dinesen et al. 2012, Luck et al. 2013). Based on the three target coral families, there is a decrease in the number of species from the east to the west coast of Sabah, from Semporna (90 species: 44 Fungiidae, 31 Agariciidae, 15 Euphylliidae; Waheed and Hoeksema 2013) to Kudat (84 species: 39 Fungiidae, 30 Agariciidae, 15 Euphylliidae; unpublished data), then Kota Kinabalu (72 species: 35 Fungiidae, 26 Agariciidae, 11 Euphylliidae; Waheed and Hoeksema 2014), and finally offshore Layang-Layang (59 species: 32 Fungiidae, 22 Agariciidae, 5 Euphylliidae) (see inset of Figure Figure1).1). This is concordant with the general pattern of decreasing diversity away from the designated centre of maximum marine biodiversity (Briggs 1974, Hoeksema 2007, 2013, 2015, Bellwood and Meyer 2009), also known as the Coral Triangle, with its present western border at the Sulu Sea (Veron et al. 2009, 2011). However, Huang et al. (2015) demonstrated that there is no significant structure in species diversity on a larger scale from the eastern to the western reefs of the South China Sea, and suggested that local dynamics are at play in driving the species richness and distribution patterns in the area. Based on their coral species composition, the Spratly Islands clustered together with southern Vietnam rather than closer continental localities such as Sabah, Brunei or Palawan, the Philippines (Huang et al. 2015), which implies that the former two localities may have similar reef attributes. For oceanic Layang-Layang with its steep reefs walls, an additional factor for its lower species richness as compared to nearby continental reef areas such as Kota Kinabalu and Kudat could be the lack of habitat heterogeneity, which would be important for supporting species diversity (Done 1982, Best et al. 1989; Cornell and Karlson 1996, 2000, Karlson and Cornell 1998, Hoeksema 2007, 2012c).
Among the new coral records for Layang-Layang are five rarely documented species, i.e., Lithophyllon ranjithi (Figure (Figure3d),3d), Podabacia sinai (Figure (Figure4d),4d), Sandalolitha boucheti (Figure (Figure4f),4f), Leptoseris kalayaanensis (Figure (Figure5g)5g) and Leptoseris troglodyta (Figure (Figure6c).6c). Lithophyllon ranjithi, a mushroom coral previously thought to be endemic to northeast Borneo was encountered at seven sites. The first mention of this species from the South China Sea was from Brunei (Turak and DeVantier 2011), although this record could not be confirmed in a later review (Hoeksema and Lane 2014). This species is usually found on nearshore or coastal reefs (Waheed and Hoeksema 2013) so it was surprising to find it at an offshore and oceanic locality. Conversely, Leptoseris kalayaanensis was anticipated to be present in Layang-Layang. In fact, its type locality, the Kalayaan Islands in the Philippines is located ~ 350 km northeast from the atoll and this species has been reported from three other localities in the South China Sea, two with rather similar reef conditions (Licuanan and Aliño 2009) and one from the coastal area of Nha Trang, Vietnam (Hoeksema et al. 2010). Specimens of Leptoseris kalayaanensis were found at 13 sites along steep reef walls and considered rather common in Layang-Layang. Leptoseris troglodyta, a cavernicolous and azooxanthellate species was encountered only once during the dives. A cluster of about 12 small calices was found on the ceiling of a small cave in a reef wall at 30 m depth (Site 1). This species is widely distributed in the West Pacific (Hoeksema 2012b) and this account is the first record for the South China Sea. Podabacia sinai was previously recorded from the Red Sea (Veron 2000) but meanwhile it has also been found in various other Indo-Pacific localities (Hoeksema unpubl.). Sandalolitha boucheti has been observed in Vanuatu (Hoeksema 2012a) and Semporna, East Sabah (Waheed and Hoeksema 2013). This species was represented on the Layang-Layang reefs by two specimens. The largest of these (Ø ~ 6 cm; Figure Figure4f)4f) was still attached by a very wide stalk while the other was free-living and showed a large detachment scar. It is abnormal for free-living mushroom corals to maintain a long-lasting fixed growth form (Hoeksema and Yeemin 2011), which may hinder their identification.
Fungiidae recorded at Pulau Layang-Layang in this study. a Fungia fungites b Halomitra pileus c Herpolitha limax d Lithophyllon ranjithi e Lithophyllon repanda f Lithophyllon scabra g Lithophyllon undulatum h Lobactis scutaria.
Fungiidae recorded at Pulau Layang-Layang in this study. a Pleuractis granulosa b Pleuractis gravis c Pleuractis moluccensis d Podabacia sinai e Polyphyllia talpina f Sandalolitha boucheti g Sandalolitha dentata h Sandalolitha robusta.
Agariciidae recorded at Pulau Layang-Layang in this study. a Coeloseris mayeri b Gardineroseris planulata c Leptoseris foliosa d Leptoseris glabra e Leptoseris hawaiiensis f Leptoseris incrustans g Leptoseris kalayaanensis h Leptoseris mycetoseroides.
Agariciidae recorded at Pulau Layang-Layang in this study. a Leptoseris scabra b Leptoseris solida c Leptoseris troglodyta d Leptoseris yabei e Pachyseris rugosa f Pacyhseris speciosa g Pavona bipartita h Pavona clavus.
Corals of three Leptoseris spp. could not be identified to species level. Two specimens of encrusting Leptoseris sp. 1 had free margins and small corallites (≤ 1.5 mm in size). One of these corals (Figure (Figure9a)9a) has calices in rows somewhat concentric and parallel with the margin and a central corallite can be discerned. Corallites appear sunken because of the high and continuous carinae. This specimen measures Ø 5 cm, and it is possibly a juvenile Leptoseris mycetoseroides. Further examination of these specimens is required for certainty. Unfortunately, specimens of Leptoseris sp. 2 and 3 were not collected; nevertheless photos have been included for visual record (Figure 9b, c).
Three coral species that have been reported from Layang-Layang but were not observed in the present study are the fungiid Podabacia crustacea and the agariciids Pavona cactus and Pavona decussata (Pilcher and Cabanban 2000). Since there is no photographic evidence or other supporting information to support the presence of these species on the atoll, they have not been included in the current species list. Still, it is very likely that these three species are present on the reef as they are common Indo-Pacific species and their distribution ranges certainly cover across the South China Sea, including the Spratly Islands (see Huang et al. 2015). As a note, Pavona cactus is usually found in turbid and sheltered reef conditions (Veron and Pichon 1980, Veron 2000). However, Pavona cactus and Pavona decussata can also be found in shallow reef environments such as upper reef slopes and lagoons. It is possible that these species are present in the lagoon reefs, which were underexplored in our study, as surveys were only possible around the reef walls of the atoll.
Many coral colonies in Layang-Layang appeared small in size, and most were juveniles. This was consistent across the reef sites for most coral families including those targeted in our study. For example, the largest collected Leptoseris kalayaanensis specimen measured 7.5 cm x 5 cm while the smallest was 4 cm × 3 cm. Also, the initial uncertainty in identifying Pavona maldivensis most likely stemmed from the fact that the specimens were very small in size (collected colonies were between 11 cm × 8 cm and 3.5 cm × 3 cm). This puzzling find can be explained by the fact that corals in the study area are recolonizing after the outbreak of the corallivorous crown-of-thorns (COT) seastar. Surveys during the COT outbreak in July 2010 were conducted down to 10 m depth only (Nasrulhakim et al. 2010), but the damage extends deeper based on our surveys (~ 20 m depth). Preceding this event there was also a COT outbreak on the nearby reefs of Brunei in April-May 2010, and at the same time a report of large numbers of COT at the reefs of the Tunku Abdul Rahman Park in Kota Kinabalu, Sabah on the northwest coast of Borneo (Lane 2012). Following this outbreak, Brunei and Kota Kinabalu reported to have thermally induced bleaching episodes in June-July 2010 (Lane 2011, Aw and Muhammad Ali 2012). There is no account on whether the reefs of Layang-Layang were also affected by this bleaching event, and based on our observations, we are unable to determine if a bleaching episode did occur.
There is no information on the extent of damage caused to the reefs and the rate of recovery from the COT outbreak in 2010, as the reefs of Layang-Layang are not monitored regularly. Many studies have reported the effects of COTs to reefs in terms of coral cover loss and changes in coral assemblage (e.g. Lourey et al. 2000, Pratchett 2010, Lane 2011, 2012, Baird et al. 2013, Bos et al. 2013, Osborne et al. 2011, Saponari et al. 2014). While COTs are known to have a feeding preference for Acropora (De’ath and Moran 1998, Pratchett 2007), they have also been found to feed on many different coral taxa (Glynn 1974, Ormond et al. 1976, Colgan 1987, De’ath and Moran 1998, Pratchett 2007, Pratchett et al. 2009), which includes fungiids (De’ath and Moran 1998, Pratchett 2007, 2010, Pratchett et al. 2009, Scott et al. 2015) and agariciids (Colgan 1987, Pratchett 2007, 2009, 2010) particularly during an outbreak or when food becomes scarce (Moran 1986). Similarly for Layang-Layang, it appears that the COT outbreak resulted in high coral mortality (E Foo, J Bell, R Wahab, Avillon Layang-Layang Resort, pers. comm.). Our study was carried out almost three years after the outbreak and from our observations, the high frequency of coral recruits and small-sized colonies indicate an ongoing recovery of corals. We question whether all coral species (as prior to the outbreak) have re-established on the reefs as coral species such as Euphyllia ancora and Plerogyra sinuosa, both reported as common from previous surveys (NJ Pilcher, pers. comm.), were not observed during the present study. We are unable to draw a conclusion that the absence of certain species previously reported for Layang-Layang is caused by the 2010 COT event. While some baseline data is available for comparison (e.g. Pilcher et al. 1999, Pilcher and Cabanban 2000), there is no specific locality data of species occurrences to refer to. As far as we know, the reefs of Layang-Layang were monitored between 1996 and 1999 (see Pilcher et al. 1999, Pilcher and Cabanban 2000) and since then and prior to that, reef surveys were conducted intermittently. As several studies have impressed upon the importance of utilising long-term monitoring data in order to assess changes to the coral communities (e.g. Brown et al. 2002, Somerfield et al. 2008), there is a need to establish a coral reef monitoring plan for Layang-Layang. With a monitoring plan in place, any changes or disturbance can be detected at the onset so that mitigation measures can be taken if necessary.
Pavona species boundaries
The IGR marker has proven to be successful in resolving species boundaries in the family Agariciidae and the genus Pachyseris (Terraneo et al. 2014). In our small dataset, the IGR marker gave better resolution than the ITS marker in resolving species-level relationships for two Pavona species. Both the IGR and the concatenated gene tree supported two main groups, one of Pavona maldivensis, including specimens from Layang-Layang, and the other of Pavona explanulata.
For all specimens in the Pavona maldivensis clade, the calice size is smaller, the calice walls are raised and distinct, the septocostae spacing is more compact and there is more surface ornamentation on the radial elements as compared to Pavona explanulata. They share some similar features in colony growth form, but Pavona explanulata does not form club-shaped branches. Pavona explanulata specimens also tend to have a smooth surface appearance due to the absent calice wall, but exceptions do occur. The columella is well-developed as a single, rounded or twisted rod for both species, peg-like for Pavona maldivensis and as fused processes in Pavona explanulata. Lastly, synapticular rings are obvious in Pavona explanulata but not so in Pavona maldivensis, though Veron and Pichon (1980) have described them to be obvious on the branch ends.
Upon re-examining the morphological characters of the Pavona specimens identified as Pavona maldivensis in our previous studies (Waheed and Hoeksema 2013, 2014), it was clear that the specimens were more similar to Pavona explanulata instead. However, these specimens have calices with somewhat distinct walls, a feature that is more typical of Pavona maldivensis. This is most likely one of the factors that prompted the misidentification of these specimens. Adding to this, Pavona maldivensis has a wide distribution range in the Indo-Pacific (e.g. Veron and Pichon 1980, Scheer and Pillai 1983, Maragos and Jokiel 1986, Dai and Lin 1992, Nishihira and Veron 1995, Glynn et al. 2007, Pichon 2007, Pichon and Benzoni 2007), and has been reported from the Bodgaya and Sipadan islands in Semporna, Sabah (Wood and Tan 1987); hence, we had expected to find this species in our previous study areas (i.e. Semporna and Kota Kinabalu).
Although Pavona maldivensis and Pavona explanulata may not be considered the most problematic species within Pavona, specimens that closely resemble these species have been collected and analysed. For example, sample KF437762 Pavona cf. explanulata (Luck et al. 2013) clusters basally to Pavona maldivensis rather than with its conspecifics, while sample RED05 Pavona cf. explanulata from Redang clusters basally to the other samples of Pavona explanulata. For the latter, the macro- and micromorphology of this specimen was noticeably different from the rest of the Pavona explanulata samples. These cases indicate that the identity of Pavona explanulata should be carefully re-examined in the future through a larger morpho-molecular study including several specimens from various localities.
Implication of misidentified Pavona maldivensis
Based on the findings of this study, the “true” Pavona maldivensis has only been found in Layang-Layang out of the other localities previously visited in Sabah, Malaysia, i.e. Semporna and Kota Kinabalu (Waheed and Hoeksema 2013, 2014), and the status of this species in those localities remains ambiguous until future data is available. It is highly likely that the misidentified specimens from those previous studies are Pavona explanulata, as was discovered for specimens from Banggi and Ternate utilised in this study, or a variety closely resembling it.
The name Pavona explanulata, like Pavona maldivensis, has been mistakenly used in the past (examples given by Veron and Pichon 1980: 17–36). Furthermore, the type specimen of Pavona explanulata appears to be missing and the original species description is rather vague, so taxonomic literature of this species since when it was first described needs to be re-examined in order to better define its species boundaries.
Conclusions
The coral species list for the families Fungiidae, Agariciidae and Euphylliidae in the present study added 32 new records for Layang-Layang and includes rarely recorded species such as Leptoseris kalayaanensis, which is thus far a South China Sea endemic. The mushroom coral Lithophyllon ranjithi has a wider distribution range than previously thought and can no longer be considered endemic to northeastern Borneo. This is the first record of this species from an oceanic and offshore reef habitat, in contrast to its previously reported habitat preference for coastal and sheltered reef conditions.
An integrative molecular and morphological approach was utilised to determine that specimens identified as Pavona maldivensis from previous surveys are in fact Pavona explanulata. The combination of both techniques have proven to be powerful in addressing species complexes in scleractinians (e.g. Benzoni et al. 2007, 2011, 2014, Kitahara et al. 2012, Arrigoni et al. 2014a, b, c, Kitano et al. 2014), particularly if type specimens and coral samples from the type locality are included in the analyses (Huang et al. 2014), and taxonomic descriptions are consolidated (Benzoni et al. 2010). While the species boundaries between Pavona maldivensis and Pavona explanulata may already be distinct based on morphological descriptions and images in current taxonomic literature, the present study has included SEM images of calices and radial elements of specimens of both species for the first time to further illustrate the previous descriptions. In addition, a specimen closely resembling but dissimilar from Pavona explanulata was also shown. As such, this finding may serve as a stepping stone for further investigations of Pavona.
Acknowledgements
Research permits for Layang-Layang were granted by the Economic Planning Unit and the National Security Council of the Prime Minister’s Department, Malaysia, and the Sabah Biodiversity Council. Travel expenses for Z. Waheed was funded by the A.M. Buitendijkfonds, The Netherlands. We acknowledge the Marine Research Station Layang-Layang (MARSAL) for the visit to the field station at Layang-Layang. We thank the team at Avillon Layang-Layang Resort for living and diving logistics, the managing director Eugene Foo and divemasters Jasper Bell, Rozlan Wahab and Amanda La Brooy for fruitful discussions. Loyalty Island data was collected during the BIBELOT campaign in 2014 onboard RV Alis of IRD at Nouméa. Sampling permits were granted by the Loyalty Islands Province, New Caledonia. BW Hoeksema is grateful to Cecile Fauvelot and Claude Payri for the invitation to join this expedition, and to Francesca Benzoni and Paola Galli for allowing him to participate in the Maldives International Reef Biodiversity Workshop in 2014, which enabled him to obtain data on Pavona maldivensis. Sampling of Pavona explanulata in Ternate, Indonesia was done under Ekspedisi Widya Nusantara (E-Win) co-organised by Naturalis and the Indonesian Institute of Sciences (LIPI) with research permits from LIPI and RISTEK. We thank Erik-Jan Bosch for the map of Layang-Layang. We highly appreciate the constructive comments from Bastian T. Reijnen, Nadiezhda Santodomingo and one anonymous reviewer, which greatly improved the manuscript.
Notes
Citation
Waheed Z, Benzoni F, van der Meij SET, Terraneo TI, Hoeksema BW (2015) Scleractinian corals (Fungiidae, Agariciidae and Euphylliidae) of Pulau Layang-Layang, Spratly Islands, with a note on Pavona maldivensis (Gardiner, 1905). ZooKeys 517: 1–37. 10.3897/zookeys.517.9308
Supplementary materials
Supplementary material 1
Table S1
Data type: measurement
Explanation note: Physical properties of seawater at Pulau Layang-Layang.
Supplementary material 2
Table S2
Data type: specimens data
Explanation note: Coral samples included in the molecular analyses with supporting collection and locality data.
Supplementary material 3
Table S3
Data type: specimens data
Explanation note: Species occurrence of hard coral families Fungiidae, Agariciidae and Euphylliidae at Pulau Layang-Layang.
Supplementary material 4
Figure S1
Data type: molecular data
Explanation note: Maximum likelihood phylogram of Pavona maldivensis and Pavona explanulata. a mitochondrial intergenic spacer between CO1 and 16S-rRna. The sequence alignment consisted of 680 characters with 593 constant, 23 variable and 64 parsimony informative characters, b nuclear marker ITS1-5.8S-ITS2, with 680 characters of 649 constant, 14 variable and 17 parsimony informative characters. Support values for maximum likelihood, maximum parsimony (>70) and bayesian posterior probabilities (>80) are given at the nodes. Dashes (-) indicate nodes without statistical support.
Supplementary material 5
Figure S2
Data type: specimens data
Explanation note: Variation of corallite form and structure in Pavona maldivensis (a, c, e), and Pavona explanulata (b, d, f). a specimen LAC23 from Layang-Layang, b specimen BAN01 from Banggi, North Borneo, c specimen LOY12 from Loyalty Islands, d specimen BAN02 from Banggi, North Borneo, e specimen MAL from the Maldives, and f specimen TER28 from Ternate, Indonesia.
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Coral Reefs at the Northernmost Tip of Borneo: An Assessment of Scleractinian Species Richness Patterns and Benthic Reef Assemblages.
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BioStudies: supplemental material and supporting data
Nucleotide Sequences (Showing 6 of 6)
- (2 citations) ENA - KF437762
- (1 citation) ENA - HE978501
- (1 citation) ENA - KF437780
- (1 citation) ENA - KR706143
- (1 citation) ENA - LK934507
- (1 citation) ENA - KR706116
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