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. 2022 May 20;1102:177–190. doi: 10.3897/zookeys.1102.82228

Scleractinian coral (Cnidaria, Hexacorallia, Scleractinia) diversity of the Mersing Islands, Peninsular Malaysia

Jen Nie Lee 1,2,, Kee Alfian Abd Adzis 2, Lutfi Afiq-Rosli 3,3, Jani T I Tanzil 3, Albert Apollo Chan 4, Md Nizam Ismail 5, Khodzori Fikri Akmal 6, Yang Amri Affendi 7
PMCID: PMC9848869  PMID: 36761156

Abstract

We present a comprehensive checklist of scleractinian (hard) corals for the Mersing Islands, Malaysia based on surveys conducted at 24 reefs across protected and unprotected marine areas. A total of 261 species of corals from 16 families and one incertae sedis (Pachyseris spp.) were recorded, along with ten records that are new for the east coast of Peninsular Malaysia. Compared against the IUCN Red List, 46.7% of coral species found in the Mersing Islands were of Least Concern (LC), 29.5% as Near Threatened (NT) and 16.4% Vulnerable (V). Only one recorded species, Pectiniamaxima (Moll & Best, 1984), was listed as Endangered (EN). Baseline species diversity data are essential for the monitoring and management of marine biodiversity, especially within marine protected areas. With both protected and unprotected coral reef areas in the vicinity of the widely scattered Mersing Islands, the diversity and distribution of coral species can be used as the basis for area-based conservation and management strategies. The diversity and abundance of scleractinian corals of each island or area should be surveyed periodically to ensure the appropriate level of protection is afforded to retain scleractinian biodiversity in this region.

Keywords: Biodiversity, conservation, hard coral, Johor, marine protected area, South China Sea

Introduction

Scleractinian corals, commonly referred to as hard corals, are a group of animals belonging to the order Scleractinia under the Phylum Cnidaria. These organisms are the backbone of coral reefs, which support high species diversity, provide goods and services (e.g., food, coastal protection, tourism), and provide substantive support to people worldwide (Praveena et al. 2012; Huang et al. 2016; Hoegh-Guldberg et al. 2019). Coral reefs in Malaysia are estimated to cover about 4,006 km2 (Praveena et al. 2012), with most reefs found in Sabah and along the east coast of Peninsular Malaysia, and in limited areas in Sarawak and the west coast of Peninsular Malaysia (UNEP 2007). A total of 398 species of scleractinian corals (Huang et al. 2015) and 925 species of reef fishes (Chong et al. 2010) have thus far been recorded from the shallow fringing reefs along the coasts of Peninsular Malaysia alone. These reefs are located at Sunda Shelf, within and near the western edge of the Coral Triangle, a marine biodiversity hotspot that is home to 627 species of zooxanthellate corals (Veron et al. 2015).

Malaysia, as a megadiverse country, is dedicated to fulfilling the Convention on Biological Diversity (CDB) agreement (Tong 2020). With the launch of the National Policy on Biological Diversity in 2016, Malaysia aims to further safeguard both key terrestrial and marine ecosystems, as well as species and genetic diversity (Goal 3) (Ministry of Natural Resources and Environment 2016). Knowledge and data on the biodiversity of Malaysia’s vast marine areas will therefore be crucial for stakeholders and policy makers to identify suitable areas for ecological protection. To date, studies that have reported on the reef-building coral biodiversity around Peninsular Malaysia are somewhat limited. A review by Affendi and Rosman (2011) found only six research articles on scleractinian diversity published for the coral reef-rich areas along the east coast of Peninsular Malaysia, most of which were based on surveys conducted only around highly visited tourist islands that are under the jurisdiction of the Department of Fisheries Malaysia (DOF), e.g., Pulau Redang and Pulau Tioman (e.g., Toda et al. 2007; Akmal et al. 2019).

The Mersing Islands comprise one of the largest archipelagos off the east coast of Peninsular Malaysia. With 58 islands (Said et al. 2021), this region is not only known for its coral reefs but also for its seagrass ecosystems (Ooi et al. 2011; Ponnampalam et al. 2015). Geologically, the Mersing Islands originated ~350 million years ago, and they are currently evaluated as a potential National Geopark for their unique geological and cultural heritage (Said et al. 2021). This elevated status will not only affect the islands but also the surrounding marine life, both in terms of increased protection and increased tourism. Biodiversity data in the area will therefore be extremely valuable to advise any development and/or management plans for the Mersing Islands. A sole report that recorded 155 species of scleractinian corals from four islands (Pulau Dayang, Pulau Pemanggil, Pulau Tinggi and Batu Tikus) (Harborne et al. 2000) was the main literature source for coral biodiversity in the Mersing Islands prior to this study, aims to provide a comprehensive updated species checklist of scleractinian corals for the coral reefs around the Mersing Islands.

Methods

The study area comprised islands on the east coast of Johor, Peninsular Malaysia, referred to as the Mersing Islands. Underwater surveys were carried out during two expeditions, one in 2012 (“Marine Park Biodiversity Expedition)” and one in 2016 (“Johor 8 Islands Expedition”). Parts of the Mersing Islands (Fig. 1) are protected under the unique overlapping protection by both Malaysia’s Federal (known as Johor Marine Park) and Johor State jurisdictions, i.e., these reefs are protected under the Fisheries Act of 1985 (Federal) as well as by the Johor State government, following the establishment of the Johor National Park in 1990. Both authorities promote the protection, preservation and management of the natural breeding ground and habitat of aquatic life. In 2013, the protected area that falls within Mersing Islands was renamed ‘Sultan Iskandar Marine Park’, and entrance and activities within the Marine Park are strictly controlled by Johor National Park Corporation, leading to a significant reduction of tourism activities in the area (Hassan 2013).

Figure 1.

Figure 1.

Survey areas at the Mersing Islands. Johor Marine Park protected area are two nautical miles away from the low tide shoreline of each gazetted island

Coral species diversity surveys were conducted at Pulau Aur, Pulau Pemanggil, Pulau Besar, Pulau Sibu and Pulau Tinggi (Fig. 1) in 2012, when a total of 13 reefs were surveyed (depth range: 3–12 m) using 100 m transects perpendicular to the shoreline, for a total of 19 transects. Further surveys were conducted in 2016 for one reef at Pulau Tinggi using SCUBA timed swims (English et al. 1997), and seven reefs via transects perpendicular to the shoreline (Pulau Lima Kecil, Pulau Lima Besar, Pulau Tokong Rakit, Tokong Gantang, Tokong Chondong, Tokong Belalai and Tokong Chupak) (Fig. 1). The reefs surveyed in 2012 were all part of a larger marine protected area (MPA), whereas the reefs surveyed in 2016 were all outside the MPA (i.e., unprotected, non-MPA).

Corals were identified to species level based on distinct features of their morphological structure according to Veron (2000), using photographs and videos recorded during the survey. All identified species were standardized according to the World Register of Marine Species (Hoeksema and Cairns 2021) to account for synonyms and taxonomic change. The relative abundance and conservation status of each species were gathered from Veron (2000) and the IUCN Red List (IUCN 2019). Conservation categories that were used are Not Evaluated (NE), Data Deficient (DD), Least Concern (CC), Near Threatened (NT), Vulnerable (VU), Endangered (EN) and Critically Endangered (CR).

Results

A total of 261 scleractinian coral species from 16 families and one incertea sedis were recorded during the 2012 (MPA; 243 species) and 2016 (non-MPA; 261 species) expeditions. Table 1 shows the checklist of scleractinian corals from Mersing Islands, with species arranged alphabetically by family and including records (155 species) from the previous survey published by Harborne et al. (2000). The current study found ten new records of scleractinian corals from the Mersing Islands in the larger Peninsular Malaysia east coast area (Fig. 1), i.e. Acroporapectinata (Brook, 1892); Astreoporaexplanata Veron, 1985; Coeloserismayeri Vaughan, 1918; Halomitrapileus (Linnaeus, 1758); Acanthastrearotundoflora Chevalier, 1975; Favitesvasta (Klunzinger, 1879); Paramontastraeaserageldini (Veron, 2000); Seriatoporahystrix Dana, 1846; Gonioporagracilis (Milne Edwards & Haime, 1849); and Pavonadivaricata Lamarck, 1816 (Fig. 2).

Table 1.

Checklist of scleractinian corals from the Mersing Islands according to (a) Harborne et al. (2000); (b) Marine Park Biodiversity Expedition 2012; and (c) Johor 8 Islands Expedition 2016. Species denoted with an asterisk (*) are those considered to represent new records for the east coast of Peninsular Malaysia.

Order Scleractinia (17) a b c Abundance (sensu Veron, 2000) IUCN Status
Family Acroporidae (79)
Acroporaabrotanoides (Lamarck, 1816) / Sometimes common LC
Acroporaanthocercis (Brook, 1893) / Sometimes common VU
Acroporaaspera (Dana, 1846) / / Sometimes common VU
Acroporaaustera (Dana, 1846) / Usually uncommon NT
Acroporacerealis (Dana, 1846) / / Common LC
Acroporaclathrata (Brook, 1891) / / Common LC
Acroporacytherea (Dana, 1846) / / / Common LC
Acroporadigitifera (Dana, 1846) / / / Sometimes common NT
Acroporadivaricata (Dana, 1846) / / / Common NT
Acroporaflorida (Dana, 1846) / / / Common NT
Acroporagemmifera (Brook, 1892) / / Common LC
Acroporaglobiceps (Dana, 1846) / Common VU
Acroporagrandis (Brook, 1892) / Common LC
Acroporahemprichii (Ehrenberg, 1834) / Common VU
Acroporahoeksemai Wallace, 1997 / / / Common VU
Acroporahorrida (Dana, 1846) / / Uncommon VU
Acroporahumilis (Dana, 1846) / / Common NT
Acroporahyacinthus (Dana, 1846) / / / Common NT
Acroporaintermedia (Brook, 1891) / Unknown NE
Acroporalatistella (Brook, 1892) / / / Common LC
Acroporaloripes (Brook, 1892) / / Common NT
Acroporamicrophthalma (Verrill, 1869) / / Common LC
Acroporamillepora (Ehrenberg, 1834) / / / Common NT
Acroporamonticulosa (Brüggemann, 1879) / / Uncommon NT
Acroporamuricata (Linnaeus, 1758) / / / Common NT
Acroporanasuta (Dana, 1846) / / Common NT
*Acroporapectinata Veron, 2000 / Uncommon DD
Acroporarobusta (Dana, 1846) / / Common LC
Acroporasamoensis (Brook, 1891) / / Usually uncommon LC
Acroporasarmentosa (Brook, 1892) / / Common LC
Acroporasecale (Studer, 1878) / Common NT
Acroporaselago (Studer, 1879) / / Sometimes common NT
Acroporasolitaryensis Veron & Wallace, 1984 / / Rare VU
Acroporasubulata (Dana, 1846) / Common LC
Acroporatenuis (Dana, 1846) / Common NT
Acroporavalenciennesi (Milne Edwards, 1860) / Common LC
Acroporavalida (Dana, 1846) / Sometimes common LC
Acroporavaughani Wells, 1954 / Uncommon VU
Acroporayongei Veron & Wallace, 1984 / / Common LC
Alveoporadaedalea (Forskål, 1775) / Uncommon VU
Alveoporaspongiosa Dana, 1846 / Usually uncommon NT
Anacroporaforbesi Ridley, 1884 / Uncommon LC
Anacroporamatthaii Pillai, 1973 / Rare VU
*Astreoporaexplanata Veron, 1985 / Sometimes common NE
Astreoporagracilis Bernard, 1896 / Sometimes common LC
Astreoporalisteri Bernard, 1896 / Usually uncommon LC
Astreoporamyriophthalma (Lamarck, 1816) / / Common LC
Astreoporaocellata Bernard, 1896 / Usually rare LC
Isoporabrueggemanni (Brook, 1893) / / Common VU
Isoporacuneata (Dana, 1846) / Common VU
Isoporapalifera (Lamarck, 1816) / / Common NT
Montiporaaequituberculata Bernard, 1897 / / / Common LC
Montiporacactus Bernard, 1897 / Common VU
Montiporacaliculata (Dana, 1846) / Uncommon VU
Montiporacebuensis Nemenzo, 1976 / / Uncommon VU
Montiporaconfusa Nemenzo, 1967 / Uncommon NT
Montiporadanae Milne Edwards & Haime, 1851 / Common LC
Montiporadelicatula Veron, 2000 / Uncommon VU
Montiporadigitata (Dana, 1846) / Common LC
Montiporaeffusa (Dana, 1846) / Uncommon NT
Montiporaflorida Nemenzo, 1967 / Common VU
Montiporafoliosa (Pallas, 1766) / Common NT
Montiporafoveolata (Dana, 1846) / Seldom common NT
Montiporagaimardi Bernard, 1897 / / Sometimes common VU
Montiporahispida (Dana, 1846) / / / Usually uncommon LC
Montiporainformis Bernard, 1897 / Common LC
Montiporamalampaya Nemenzo, 1967 / Common VU
Montiporamollis Bernard, 1897 / / Common LC
Montiporamonasteriata (Forskål, 1775) / Common LC
Montiporanodosa (Dana, 1846) / Usually uncommon NT
Montiporapalawanensis Veron, 2000 / Uncommon NT
Montiporapeltiformis Bernard, 1897 / Uncommon NT
Montiporastellata Bernard, 1897 / Common LC
Montiporatuberculosa (Lamarck, 1816) / / Common LC
Montiporaturgescens Bernard, 1897 / Common LC
Montiporaturtlensis Veron & Wallace, 1984 / Common VU
Montiporavenosa (Ehrenberg, 1834) / Uncommon NT
Montiporaverrucosa (Lamarck, 1816) / Sometimes common LC
Montiporaverruculosa Veron, 2000 / Uncommon VU
Famili Agariciidae (15)
*Coeloserismayeri Vaughan, 1918 / / Uncommon LC
Gardineroserisplanulata (Dana, 1846) / / Usually uncommon LC
Leptoserisexplanata Yabe & Sugiyama, 1941 / / Uncommon LC
Leptoserisfoliosa Dinesen, 1980 / Uncommon LC
Leptoserishawaiiensis Vaughan, 1907 / Uncommon LC
Leptoserismycetoseroides Wells, 1954 / / Sometimes common LC
Leptoserisscabra Vaughan, 1907 / Usually uncommon LC
Pavonabipartita Nemenzo, 1979 / Uncommon VU
Pavonacactus (Forskål, 1775) / / Common VU
Pavonaclavus Dana, 1846 / Common LC
Pavonadanai (Milne Edwards, 1860) / Uncommon VU
Pavonadecussata (Dana, 1846) / / / Common VU
*Pavonadivaricata Lamarck, 1816 / Unknown NE
Pavonaexplanulata (Lamarck, 1816) / / / Common LC
Pavonavarians Verrill, 1864 / Common LC
Famili Astrocoeniidae (3)
Palauastrearamosa Yabe & Sugiyama, 1941 / Common NT
Stylocoeniellaarmata (Ehrenberg, 1834) / Rare LC
Stylocoeniellaguentheri (Bassett-Smith, 1890) / / Uncommon LC
Famili Dendrophylliidae (10)
Duncanopsammiapeltata (Esper, 1790) / / / Common VU
Tubastraeacoccinea Lesson, 1830 / / Unknown NE
Tubastraeadiaphana (Dana, 1846) / Unknown NE
Tubastraeafaulkneri Wells, 1982 / Unknown NE
Tubastraeamicranthus (Ehrenberg, 1834) / / Unknown NE
Turbinariafrondens (Dana, 1846) / Common LC
Turbinariairregularis Bernard, 1896 / Common LC
Turbinariamesenterina (Lamarck, 1816) / / / Common VU
Turbinariareniformis Bernard, 1896 / / Sometimes common VU
Turbinariastellulata (Lamarck, 1816) / / / Usually uncommon VU
Famili Diploastreidae (1)
Diploastreaheliopora (Lamarck, 1816) / / / Common NT
Famili Euphylliidae (8)
Euphylliacristata Chevalier, 1971 / Uncommon VU
Euphylliaglabrescens (Chamisso & Eysenhardt, 1821) / / Uncommon NT
Euphylliaparaglabrescens Veron, 1990 / Rare VU
Fimbriaphylliaancora (Veron & Pichon, 1980) / / / Seldom common VU
Fimbriaphylliadivisa (Veron & Pichon, 1980) / / Seldom common NT
Fimbriaphylliaparadivisa (Veron, 1990) / Uncommon VU
Galaxeaastreata (Lamarck, 1816) / / Common VU
Galaxeafascicularis (Linnaeus, 1767) / / / Uncommon NT
Famili Fungiidae (20)
Ctenactiscrassa (Dana, 1846) / Usually uncommon LC
Ctenactisechinata (Pallas, 1766) / / / Common LC
Cycloserisexplanulata (van der Horst, 1922) / / Uncommon LC
Cycloserisvaughani (Boschma, 1923) / Rare LC
Danafungiahorrida (Dana, 1846) / Uncommon NE
Danafungiascruposa (Klunzinger, 1879) / Uncommon LC
Fungiafungites (Linnaeus, 1758) / / / Common NT
*Halomitrapileus (Linnaeus, 1758) / / Usually uncommon LC
Heliofungiaactiniformis (Quoy & Gaimard, 1833) / Common VU
Herpolithalimax (Esper, 1792) / / Common LC
Lithophyllonconcinna (Verrill, 1864) / / Common LC
Lithophyllonrepanda (Dana, 1846) / Common LC
Lithophyllonundulatum Rehberg, 1892 / / / Usually uncommon NT
Lobactisscutaria (Lamarck, 1801) / Common LC
Pleuractisgranulosa (Klunzinger, 1879) / Usually uncommon LC
Pleuractismoluccensis (Van der Horst, 1919) / Usually uncommon LC
Pleuractispaumotensis (Stutchbury, 1833) / / Common LC
Podabaciacrustacea (Pallas, 1766) / / / Usually uncommon LC
Polyphylliatalpina (Lamarck, 1801) / / / Common LC
Sandalolitharobusta (Quelch, 1886) / / Common LC
Famili Lobophylliidae (23)
Acanthastreaechinata (Dana, 1846) / / / Usually uncommon LC
Acanthastreahemprichii (Ehrenberg, 1834) / / / Uncommon VU
Acanthastreapachysepta (Chevalier, 1975) / Usually uncommon NT
*Acanthastrearotundoflora Chevalier, 1975 / Usually uncommon NT
Cynarinalacrymalis (Milne Edwards & Haime, 1848) / Seldom common NT
Echinophylliaaspera (Ellis & Solander, 1786) / / / Rare LC
Echinophylliaglabra (Nemenzo, 1959) / Common LC
Homophylliaaustralis (Milne Edwards & Haime, 1848) / / Uncommon LC
Lobophylliaagaricia (Milne Edwards & Haime, 1849) / / / Uncommon LC
Lobophylliacorymbosa (Forskål, 1775) / / Sometimes common LC
Lobophylliadiminuta Veron, 1985 / Uncommon VU
Lobophylliaflabelliformis Veron, 2000 / / Usually uncommon VU
Lobophylliahataii Yabe, Sugiyama & Eguchi, 1936 / / Uncommon LC
Lobophylliahemprichii (Ehrenberg, 1834) / / / Common LC
Lobophylliaradians (Milne Edwards & Haime, 1849) / / / Common LC
Lobophylliarecta (Dana, 1846) / / / Common LC
Lobophylliarobusta Yabe & Sugiyama, 1936 / Uncommon LC
Lobophylliavalenciennesii (Milne Edwards & Haime, 1849) / Uncommon LC
Lobophylliavitiensis (Brüggemann, 1877) / / Usually uncommon NT
Micromussalordhowensis (Veron & Pichon, 1982) / / / Sometimes common NT
Oxyporacrassispinosa Nemenzo, 1979 / Uncommon LC
Oxyporaechinata (Saville Kent, 1871) / / Usually rare LC
Oxyporalacera (Verrill, 1864) / / Common LC
Famili Merulinidae (57)
Astraeosmiliatumida (Matthai, 1928) / / Uncommon NT
Astreacurta Dana, 1846 / / Common LC
Coelastreaaspera (Verrill, 1866) / / Common LC
Cyphastreamicrophthalma (Lamarck, 1816) / / Common LC
Cyphastreaocellina (Dana, 1846) / Rare VU
Cyphastreaserailia (Forskål, 1775) / Common LC
Dipsastraeaamicorum (Milne Edwards & Haime, 1849) / Uncommon LC
Dipsastraeafavus (Forskål, 1775) / / Common LC
Dipsastraeahelianthoides (Wells, 1954) / Sometimes common NT
Dipsastraeamaritima (Nemenzo, 1971) / Uncommon NT
Dipsastraeapallida (Dana, 1846) / Less common LC
Dipsastraeaspeciosa (Dana, 1846) / Common LC
Dipsastraeaveroni (Moll & Best, 1984) / / Rare NT
Echinoporagemmacea (Lamarck, 1816) / / Usually uncommon LC
Echinoporahorrida Dana, 1846 / / Uncommon NT
Echinoporalamellosa (Esper, 1791) / / Common LC
Echinoporamammiformis (Nemenzo, 1959) / / Common NT
Echinoporapacifica Veron, 1990 / / / Usually uncommon NT
Favitesabdita (Ellis & Solander, 1786) / / / Common NT
Favitescomplanata (Ehrenberg, 1834) / Sometimes common NT
Favitesflexuosa (Dana, 1846) / / Sometimes common NT
Faviteshalicora (Ehrenberg, 1834) / / / Usually uncommon NT
Favitesmagnistellata (Milne Edwards & Haime, 1849) / / Usually uncommon NT
Favitesmelicerum (Ehrenberg, 1834) / Rare NT
Favitespentagona (Esper, 1790) / / Sometimes common LC
Favitesvalenciennesii (Milne Edwards & Haime, 1849) / Usually uncommon NT
*Favitesvasta (Klunzinger, 1879) / Uncommon NT
Goniastreaedwardsi Chevalier, 1971 / / Common LC
Goniastreafavulus (Dana, 1846) / / / Uncommon NT
Goniastreapectinata (Ehrenberg, 1834) / / / Common LC
Goniastrearetiformis (Lamarck, 1816) / / Common LC
Goniastreastelligera (Dana, 1846) / / / Common NT
Hydnophoraexesa (Pallas, 1766) / / / Common NT
Hydnophoragrandis Gardiner, 1904 / / Usually uncommon LC
Hydnophoramicroconos (Lamarck, 1816) / / / Uncommon NT
Hydnophorarigida (Dana, 1846) / / Sometimes common LC
Leptoriaphrygia (Ellis & Solander, 1786) / / / Common NT
Merulinaampliata (Ellis & Solander, 1786) / / / Usually common LC
Merulinacylindrica (Milne Edwards & Haime, 1849) / / Uncommon LC
Merulinascabricula Dana, 1846 / / Common LC
Mycediumelephantotus (Pallas, 1766) / / / Common LC
Orbicellaannularis (Ellis & Solander, 1786) / Rare NE
Oulophylliabennettae (Veron, Pichon & Wijsman-Best, 1977) / / Uncommon NT
Oulophylliacrispa (Lamarck, 1816) / / / Uncommon NT
Paramontastraeasalebrosa (Nemenzo, 1959) / Rare VU
*Paramontastraeaserageldini (Veron, 2000) / Rare VU
Pectiniaalcicornis (Saville Kent, 1871) / / Usually uncommon VU
Pectinialactuca (Pallas, 1766) / Common VU
Pectiniamaxima (Moll & Best, 1984) / Uncommon EN
Pectiniapaeonia (Dana, 1846) / / / Common NT
Platygyraacuta Veron, 2000 / Sometimes common NT
Platygyradaedalea (Ellis & Solander, 1786) / / Common LC
Platygyralamellina (Ehrenberg, 1834) / / / Usually uncommon NT
Platygyrapini Chevalier, 1975 / / Usually uncommon LC
Platygyrasinensis (Milne Edwards & Haime, 1849) / / / Usually uncommon LC
Platygyraverweyi Wijsman-Best, 1976 / Usually uncommon NT
Trachyphylliageoffroyi (Audouin, 1826) / Rare NT
Famili Plerogyridae (2)
Physogyralichtensteini (Milne Edwards & Haime, 1851) / / Common VU
Plerogyrasinuosa (Dana, 1846) / / / Usually uncommon NT
Famili Plesiastreidae (1)
Plesiastreaversipora (Lamarck, 1816) / / Unknown LC
Famili Pocilloporidae (7)
Pocilloporadamicornis (Linnaeus, 1758) / / / Common LC
Pocilloporagrandis Dana, 1846 / Common NT
Pocilloporameandrina Dana, 1846 / *Common LC
Pocilloporaverrucosa (Ellis & Solander, 1786) / / Common LC
*Seriatoporahystrix Dana, 1846 / Common LC
Stylophorapistillata (Esper, 1792) / Common NT
Stylophorasubseriata (Ehrenberg, 1834) / / Common LC
Famili Poritidae (21)
Gonioporacolumna Dana, 1846 / / Common NT
Gonioporadjiboutiensis Vaughan, 1907 / Common LC
*Gonioporagracilis (Milne Edwards & Haime, 1849) / Unknown NE
Gonioporalobata Milne Edwards, 1860 / / Common NT
Gonioporanorfolkensis Veron & Pichon, 1982 / Uncommon LC
Gonioporaplanulata (Ehrenberg, 1834) / Usually uncommon VU
Gonioporastokesi Milne Edwards & Haime, 1851 / Uncommon NT
Poritesannae Crossland, 1952 / / / Common NT
Poritesattenuata Nemenzo, 1955 / Common VU
Poritesaustraliensis Vaughan, 1918 / common LC
Poritescylindrica Dana, 1846 / / Common NT
Poritesdensa Vaughan, 1918 / Sometimes common NT
Poritesevermanni Vaughan, 1907 / / / Usually uncommon DD
Poriteslatistellata Quelch, 1886 / Uncommon LC
Poriteslichen (Dana, 1846) / Common LC
Poriteslobata Dana, 1846 / / Common NT
Poriteslutea Milne Edwards & Haime, 1851 / / Common LC
Poritesmonticulosa Dana, 1846 / Common LC
Poritesnigrescens Dana, 1846 / Sometimes common VU
Poritesrus (Forskål, 1775) / / Common LC
Poritessolida (Forskål, 1775) / / / Common LC
Famili Psammocoridae (6)
Psammocoracolumna Dana, 1846 / / / Sometimes common LC
Psammocoracontigua (Esper, 1794) / / Common NT
Psammocoradigitata Milne Edwards & Haime, 1851 / / / Usually uncommon NT
Psammocoraexesa Dana, 1846 / / Common LC
Psammocorahaimiana Milne Edwards & Haime, 1851 / Uncommon LC
Psammocoraprofundacella Gardiner, 1898 / Uncommon LC
Famili Rhizangiidae (1)
Pseudosiderastreatayamai Yabe & Sugiyama, 1935 / Uncommon NT
Famili Leptastreidae (3)
Leptastreaaequalis Veron, 2000 / Rare VU
Leptastreapurpurea (Dana, 1846) / / / Common LC
Leptastreatransversa Klunzinger, 1879 / Uncommon LC
Famili Scleractinia incertae sedis (4)
Pachyserisfoliosa Veron, 1990 / Uncommon LC
Pachyserisgemmae Nemenzo, 1955 / / Rare NT
Pachyserisrugosa (Lamarck, 1801) / / Common VU
Pachyserisspeciosa (Dana, 1846) / / / Common LC

Figure 2.

Figure 2.

New records of scleractinian corals for the east coast of Peninsular Malaysia aAstreoporaexplanatabCoeloserismayericHalomitrapileusdAcanthastrearotundofloraeFavitesvastafParamontastraeaserageldinigGonioporagracilis, and hPavonadivaricata.

Of the 16 families recorded, Acroporidae was the richest with a total of 79 species: 39 Acropora species, 28 Montipora species and four from other genera (Table 1). Six per cent (16) of species from the list were considered ‘rare’ in abundance according to Veron (2000), whereby the species can be common in a specific area but rare overall. According to the IUCN Red List, many coral species we observed were classified as of Least Concern (46.7%), Near Threatened (29.5%) or Vulnerable (18.8%). Only one species, Pectiniamaxima, was categorised as Endangered (EN). The remaining species were Not Evaluated (3.8%) or classified as Data Deficient (0.8%).

Discussions and conclusions

The current study provides an updated species checklist of scleractinian corals from coral reefs around the Mersing Islands. A total of 261 scleractinian species were recorded, including ten new records for the east coast of Peninsular Malaysia, from where 398 species were previously reported (Huang et al. 2015). Compared to previous findings by Harborne et al. (2000) (155 species recorded from a subset of reefs around the Mersing Islands), we find the coral diversity around the Mersing Islands to be comparable, if not slightly higher, than other reefs in the region, i.e., Pulau Tioman with 239 species (Akmal et al. 2019) (i.e., north of the Mersing Islands) and Singapore with 255 species (Huang et al. 2009) (i.e., south of the Mersing Islands). The South China Sea in the Central Indo Pacific holds a high biodiversity of scleractinian corals, with a total recorded number of 571 species. The diversity found around the Mersing Islands represents ~ 45% of the total recorded coral fauna of the South China Sea and ~65% of the total recorded fauna from the east coast of Peninsular Malaysia. Previous records and records from the current study account for a total of 413 scleractinian coral species for reefs along the east coast of Peninsular Malaysia. These include eight new records of coral species at Pulau Tioman and Pulau Redang by Akmal et al. (2019) and the ten (10) new records from this study.

The ten new records of coral species for the east coast of Peninsular Malaysia found during this study are known to be widely distributed in the Indo-West Pacific Ocean (east coast of Africa to Japan and Melanesia) (Veron 2000; Cairns and Hoeksema 2022; GBIF 2022). Two of these species (Acanthastrearotundoflora and Seriatoporahystrix) had previously been reported from Singapore’s southern islands (Huang et al. 2009), whereas another species (Pavonadivaricata) was previously recorded from the west coast of Peninsular Malaysia (Affendi and Rosman 2011). However, we note that all the newly recorded coral species found were rarely observed in our surveys, suggesting that their occurrence along the east coast of Peninsular Malaysia may be relatively low. Given the vastness of the coral reef area around the Mersing Islands and the complexity of reef ecosystems, together with seagrass meadows, such as those at Pulau Tinggi (Ooi et al. 2011) and Pulau Besar (Lee et al. 2010), we posit that the current account of coral diversity in this region may yet be underestimated. Further surveys around the Mersing Islands are likely to yield new findings, as visual surveys have only been conducted once at each study reef site. Although hard scleractinian corals form the basis of coral reef ecosystems, information about other reef-related species’ diversity and abundance is also crucial for marine area planning (e.g., determining management strategies and protection status). Based on the results of the current study, we propose that more surveys should be conducted around the Mersing Islands, extending investigations to other taxa where possible.

Biodiversity and taxonomic studies on the scleractinian corals of Peninsular Malaysia are in their infancy compared to neighbouring regions, e.g., Singapore (Huang et al. 2009) and Sabah, East Malaysia (Waheed and Hoeksema 2013, 2014; Waheed et al. 2015). Given recent findings around the region, such as the new genus and species records of Micromussaanalusensis by Ng et al. (2019), the increased occurrence and records of Pocilloporaacuta (Poquita-Du et al. 2017; Torres and Ravago-Gotanco 2018), and the cryptic speciation in Pachyserisspeciosa (Bongaerts et al. 2021; Feldman et al. 2021), we can expect important scleractinian discoveries for the Mersing Islands (and other coral reefs in Malaysia) should we aim to further explore and examine these underexplored reefs.

Acknowledgements

We thank the Department of Fisheries Malaysia (formally known as Department of Marine Park Malaysia during both expeditions); EKOMAR from Universiti Kebangsaan Malaysia; and Institute of Biological Sciences and Team Sea Habitats from Universiti Malaya for organizing the expeditions. This study was supported by the Department of Fisheries Malaysia. We also express our special thanks to the reviewers and academic editor, who provided comments that helped improve the manuscript.

Citation

Lee JN, Adzis KAA, Afiq-Rosli L, Tanzil JTI, Chan AA, Ismail MN, Akmal KF, Affendi YA (2022) Scleractinian coral (Cnidaria, Hexacorallia, Scleractinia) diversity of the Mersing Islands, Peninsular Malaysia. ZooKeys 1102: 177–190. https://doi.org/10.3897/zookeys.1102.82228

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