Molecular phylogenetics and morphology of Gambierdiscus yasumotoi from tropical eastern Australia

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Molecular phylogenetics and morphology of Gambierdiscus yasumotoi from tropical eastern

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Australia

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Shauna Murray*1,2, Paolo Momigliano*3,4, , Kirsten Heimann3,5, David Blair3

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*These authors contributed equally

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NSW 2007, Australia

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Sydney Institute of Marine Sciences, Chowder Bay Rd, Mosman NSW Australia

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School of Marine and Tropical Biology, James Cook University, QLD 4810, Australia

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Department of Biological Sciences, Macquarie University, North Ryde 2019 NSW,

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Australia

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4810, Australia

Plant Functional Biology and Climate Change Cluster, University of Technology, Sydney

Centre for Sustainable Tropical Fisheries and Aquaculture, James Cook University, QLD

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Corresponding author:

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Paolo Momigliano

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email address: [email protected]

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phone: +61 2 9850 8331

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Abstract

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Here the occurrence of the species Gambierdiscus yasumotoi is reported for the first time

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along a latitudinal gradient spanning more than 1550 km of the Australian Great Barrier Reef

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(GBR), a region with endemic ciguatera fish poisoning. Gambierdiscus yasumotoi was found

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at three tropical and sub tropical coral reef sites, Raine Island (northern GBR) , Nelly Bay

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(central GBR) and Heron Island (southern GBR), indicating a wide-ranging distribution in

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tropical and subtropical eastern Australia. Specimens from Australia broadly fitted the

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original description of Gambierdiscus yasumotoi, but differed in some aspects, showing some

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similarities to G. ruetzleri. Molecular phylogenetic analyses based on nuclear rRNA gene

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sequences and morphological analyses showed specimens to be intermediate between the two

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species Gambierdiscus yasumotoi and Gambierdiscus ruetzleri. The full intraspecific

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diversity of these two species appears to be incompletely known, and these two species may

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represent a species complex. Strains of this species from other sites around the world have

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been found to produce an as yet unknown toxin, possibly an analogue of maitotoxin.

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Keywords: Gambierdiscus, Ciguatera, Great Barrier Reef, Phylogenetics

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1 Introduction

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The genus Gambierdiscus Adachi and Fukuyo (Gonyaulacales, Dinoflagellata, Alveolata) is

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one of more than 550 known genera of dinoflagellates. Species of this genus are the main

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causative agents of Ciguatera Fish Poisoning (CFP), caused by the consumption of fish

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contaminated with toxins produced by these dinoflagellates, which are biomagnified along

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the food web. CFP is the most common non-bacterial seafood poisoning disease in the world

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(Fleming et al., 1998) and mainly occurs in tropical countries. Cases have been reported in

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coral reef areas in Australia (Gillespie et al., 1985; Lewis, 2006), the Pacific and Indian

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oceans as well as the Caribbean (Tosteson, 2004). In Australia, there were more than 1,400

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documented cases between 1965 and 2010, including two fatalities (Gillespie et al., 1985;

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Hamilton et al., 2010).

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Gambierdiscus are epibenthic on seagrass, macroalgae, sand and coral rubble, however, they

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can also occur in the plankton (Nakahara et al., 1996; Parsons et al., 2011). Species of this

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genus have the plate formula: Po, 3', 7", 6c,?s, 5’’', 1p, 2”” (Chinain et al., 1999; Faust, 1995;

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Fraga et al., 2011; Holmes, 1998; Litaker et al., 2009) and are distinguished from one another

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based on characters such as surface patterns, cell flattening (apical or dorso-ventral), size and

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shapes of the plates and of the cells.

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The type species, Gambierdiscus toxicus, was first identified as recently as 1979 (Adachi and

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Fukuyo, 1979), and until 15 years ago, only 3 species were known in the genus. It was

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recognised that the type description of Gambierdiscus toxicus probably incorporated several

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species, and G. toxicus was redescribed more narrowly, based on a lectotype (Litaker et al.,

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2009). Currently, twelve species of Gambierdiscus are recognised: Gambierdiscus australes,

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G. belizeanus, G. caribaeus, G. carolinianus, G. carpenteri, G. pacificus, G. polynesiensis,

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G. ruetzleri, G. toxicus, G scabrosus, G. yasumotoi, and G. excentricus (Chinain et al., 1999;

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Faust, 1995; Fraga et al., 2011; Holmes, 1998; Litaker et al., 2009; Nishimura et al., 2014).

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At least five additional unnamed clades that are clearly genetically distinguishable have been

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found, indicating that further species may be distinguished in future (Litaker et al., 2009;

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Richlen et al., 2008; Xu et al., 2014).

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Published reports initially indicated the presence of only a single species, Gambierdiscus

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toxicus in Australia, from tropical regions of Queensland (Holmes et al., 1990; Holmes et al.,

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1991; Holmes et al., 1994), and more recently, from New South Wales (Murray, 2010).

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Cultures of this taxon from sites in Queensland were made in the 1990s (Babinchak et al.,

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1994; Holmes et al., 1990; Holmes et al., 1991; Holmes et al., 1994) and subsequently lost.

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Since these initial reports, our understanding of the morphological and genetic diversity

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present in the genus Gambierdiscus has increased significantly (Chinain et al., 1999; Fraga et

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al., 2011; Litaker et al., 2009; Nishimura et al., 2014; Richlen et al., 2008; Xu et al., 2014),

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and it is therefore necessary to revisit initial sites in order to assess the presence of these

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species. Recently, a second species of Gambierdiscus, G. carpenteri, has been reported from

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several sites in Australia for the first time (Kohli et al., 2014a; Kohli et al., 2014b).

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The species Gambierdiscus yasumotoi was originally described from Singapore waters

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(Holmes, 1998), and was found to produce an uncharacterised toxin that was lethal to mice,

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producing symptoms similar to those of maitotoxin (Holmes, 1998). This species has since

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been reported from additional sites around the world, including from the Pacific and

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Caribbean waters. Strains isolated from New Zealand were found not to produce known

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analogues of ciguatoxins (CTXs) or maitotoxin (MTX) 1, but were likely to produce an as yet

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uncharacterised analogue of maitotoxin (Rhodes et al., 2014a).

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In this study the presence of Gambierdiscus yasumotoi is shown for the first time along a

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latitudinal gradient of more than 1550 km in waters of the northern, central and southern

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Great Barrier Reef (GBR), Queensland, Australia. Gambierdiscus yasumotoi is described

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from Australia based on scanning electron microscopy of field material, as well as scanning

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electron microscopy and phylogenetic analysis of a culture of G. yasumotoi isolated from the

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central GBR region. The occurrence of two other species of Gamberdiscus is also

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documented: G. carpenteri and G. cf belizeanus.

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2 Materials and Methods

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2.1 Sample collection.

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Between the 3rd-8th December 2003, eight samples were taken at low tide at sites on Raine

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Island (11° 45’.501 S, 144° 02’.309 E), a remote uninhabited tropical coral cay in the

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northern GBR, in the vicinity of the tower end of the beach (Fig 1), as part of annual

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sampling coordinated by the Raine Island Corporation. On 15th June 2003, four samples were

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collected from Heron Island (23°25’ S, 151° 55’ E), a tropical coral cay in the southern GBR

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(Fig 1). Samples were taken from encrusting macroalgae in shallow (less than 30 cm deep)

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tidal pools at low tide.

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Macroalgal samples were obtained from central GBR waters on low tide in the area between

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Townsville (Pallarenda at the mouth of Three Mile Creek, 19° 12' 34'' S, 146° 46' 36'' E) and

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Magnetic Island (Nelly Bay, 1910’ S, 14650’ E; Great Barrier Reef Marine Park Authority

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Permit G06/20234.1) in August 2004 and March 2008 (Fig 1). Macroalgal material was

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washed in filtered (0.45 µm) seawater to flush epiphytic dinoflagellates off their surface and

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the wash water was sequentially concentrated by filtration through 53 and 20 µm nylon mesh

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filters.

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2.2 Culture establishment.

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Dinoflagellates were isolated from Pallarenda and Nelly Bay macroalgal wash waters at the

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North Queensland Algal Identification/Culturing Facility (NQAIF) at James Cook University,

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Townsville, Australia using the microcapillary‐capturing‐technique (Andersen and Kawachi,

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2005) at 10X magnification on an inverted light microscope (Olympus CKK 41, Olympus

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Australia Ltd, Mt Waverley VIC 3149). Cells were dispensed in autoclaved and filtered (0.45

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μm) seawater. Cells were allowed to swim for ten minutes and were then recaptured. This

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procedure was repeated ten times to ensure that nano‐ and pico‐plankton were no longer in

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the vicinity of the cell to be isolated. Cultures of NQAIF116 (Pallarenda) and NQAIF210

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(Nelly Bay) were established in L1 medium (Guillard and Hargraves, 1993) prepared in

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natural seawater and maintained at 24°C, a 12:12 h photoperiod and light intensity of 45

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μmol photons m‐2s‐1 in a Contherm cross‐flow phytoplankton growth chamber. Cultures were

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subcultured in L1 medium every 4 weeks

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2.3 Microscopy.

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Samples were immediately examined using a dissecting light microscope. Individual cells

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were isolated onto 5 µm millipore filtersor 1 cm round glass coverslips that had been treated

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with poly-L-lysine (Marchant and Thomas, 1983), to make preparations to observe in the

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scanning electron microscope. Cells were dehydrated in a series of increasing ethanol

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concentrations (15, 30, 50, 70, 90, and 100%), followed by 50% and 100%

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hexamethyldisilizane (HMDS). The filters were air dried before being sputter coated with

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gold or gold/palladium. They were observed using a Philips 505 scanning electron

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microscope (Philips, Eindhoven, the Netherlands) at 10–15kV and a JEOL JSM-5410LV

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scanning electron microscope (JEOL, Sydney, Australia).

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2.4 DNA extraction and sequencing.

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DNA was extracted from cultures NQAIF210 and NQAIF116 using a modified Chelex®

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protocol (Walsh et al., 1991) as outlined in Momigliano et al. (2013). The near-complete

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nuclear 18S rRNA gene, and the D1-D3 and D8-D10 regions of the 28S rRNA gene were

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amplified and sequenced using the primers listed in Table S1. PCR reactions were set up as

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follows: 1µl of template DNA, 800 µM each DNTPs, 10 pmol of each primer, 1X Green

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GoTaq® Flexi Buffer and 1 unit GoTaq® Flexi Polymerase (Promega, Inc.). PCR reactions

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underwent an initial denaturation of 3 min at 94 °C, followed by 35 cycles of 30 s

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denaturation (94 °C), 30 s annealing (see Table S1 for details), and 1 min extension (72 °C),

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and a final extension of 5 min at 72 °C. PCR products were cleaned by isopropanol

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precipitation and sequenced using a commercial service (Macrogen, Inc.). All sequences

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were deposited in GenBank (accession numbers: KM272970-272974).

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2.5 Sequence alignment and phylogenetic analysis.

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Overlapping fragments of the D1-D3 and D8-D10 regions of the 28S and the near-complete

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18S genes were assembled using the software Chromas Pro (Technelysium Pty Ltd.). The

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sequences obtained from culture NQAIF210 and NQAIF116 were aligned with available

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sequences of Gambierdiscus spp. (for a list of the strains used see Table S2) using Clustal W

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(Thompson et al., 1994) and the alignments were visually refined using BioEdit (Hall, 1999).

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Phylogenetic analysis was performed on the datasets including the D8-D10 region of the 28S

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rRNA and the near complete 18S rRNA gene. Substitution models were selected for each

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dataset in jModelTest2 (Darriba et al., 2012), using Bayesian Information Criterion as a

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measure of the relative quality of the models. Phylogenetic reconstructions were carried out

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using both a Maximum Likelihood (ML) and Bayesian Inference (BI) approach.

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ML trees were produced in PhyML 3.1 (Guindon et al., 2010), using a TrN+G substitution

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model with 4 gamma categories (alpha= 0.46) and a TIM2+G model with 4 gamma

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categories (alpha=0.46) for the D8-D10 region of the 28S gene and the 18S dataset

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respectively, tree improvement by using the best of nearest neighbour interchanges (NNI)

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and subtree pruning and regrafting (NPR), starting with 5 random trees. Bayesian analysis

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was performed in MrBayes 3.2.2 (Ronquist and Huelsenbeck, 2003). The substitution model

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used for the D8-D10 region of the 28S gene was the same as in the ML analysis. However as

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MrBayes does not implement the TIM2 substitution model, we used the next-best available

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model, the HKY+G model. The number of Markov Chain Monte Carlo generations was set to

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2 000 000, but set to automatically stop when the standard deviation of split frequencies fell

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below 0.01. Trees were sampled every 100 generations, and convergence of the 2

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independent runs was checked by analysing the stability of each parameter estimate in the

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software Tracer v1.6.

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In addition, for each locus p-distances for all available strains belonging to the G.

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yasumotoi/ruetzleri clade were estimated in the R statistical environment using the ape

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package (Paradis et al., 2004). The distance matrices were further analysed using Principal

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Coordinates Analysis (PCoA) implemented in the package ade4 (Dray and Dufour, 2007).

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3 Results

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3.1 Phylogenetic analyses.

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The final alignments of the D8-D10 region of the 28S rRNA gene based on 45 sequences

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included 929 unambiguously aligned nucleotides and 348 variable sites, of which 286 were

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parsimony informative. The 18S alignment included 36 sequences, 1746 unambiguously

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aligned nucleotides and 696 variable sites of which 603 were parsimony informative. Both

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phylogenies show strong support for all terminal branches (Figs 2 & 3), and largely support

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previously published phylogenies of the genus Gambierdiscus. Small differences in the trees

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presented here relative to previously published phylogenies are due to the fact that out-group

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taxa were not used in phylogenetic reconstruction and disappear if the trees are rooted with

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the most basal Gambierdiscus clade (G. yasumotoi clade).

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NQAIF210 grouped with high support within the G. ruetzleri/G. yasumotoi clade - Clade I in

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Nishimura et al. (2013) in both phylogenies (Figs 2 & 3 ). NQAIF210 could not be

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unambiguously identified as either G. yasumotoi nor G. ruetzleri based on 18S sequences. In

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the phylogeny reconstructed using the D8-D10 region of the 28S gene, NQAIF210 grouped

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with high support with the New Zealand strain CAWD210, and both NQAIF210 and

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CAWD210 grouped with G. ruetzleri with moderate bootstrap support (Fig 3). The culture

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NQAIF116 consistently grouped with high support within the G. carpenteri clade (Figs 2 &

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3). Representations of p-distance matrices in reduced space (Fig 4) showed that NQAIF210

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and CAWD210 have identical sequences for the D1-D3 region, and have small p-distances

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for the D8-D10 region but the analysis also failed to show any clear grouping of NQAIF210

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with other previously identified strains in this clade, from which NQAIF210 is roughly

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equidistant (Fig. 4) . However, it must be remembered that all sequences of G. yasumotoi

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utilized in the phylogenies and p-distance analyses are clones of the same strain (Gyasu), and

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therefore they cannot be used as a proxy of intra-specific variation. Furthermore, p-distances

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within this clade, and between putative species within it, are very small when compared to

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between-species distances elsewhere in the genus. P-distances between G. yasumotoi and G.

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ruetzleri are as little as 0.01 (D1-D3 and D8-D10 regions of the 28S rRNA gene) and 0.004

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(near complete 18S gene).

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Interestingly, p-distances among clones of the same strain of G. yasumotoi are comparable to

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those observed between clones of G. yasumotoi and strains of G. ruetzleri (Fig 4, particularly

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4A, 4C and 4E).

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3.2 Morphological analyses

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The morphology of Gambierdiscus yasumotoi from field samples and from the cultured strain

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is shown (Figs 5,6,7). Cells from field samples were laterally compressed in ventral view, and

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oval to round in lateral view, with a depth of 57 µm (range 54- 59 µm), width 48 µm (range

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46-50 µm) and length 56 µm (range 53-59 µm) (Figs 6,7). The depth to width ratio was 1.18,

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while the length to width ratio was 1.16. Cultured cells were slightly smaller, more globular

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and less obviously laterally compressed, with a depth of 49 µm (range 44- 54 µm), width 45

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µm (range 40-49 µm) and length 51 µm (range 49-54 µm) (Fig 5). The depth to width ratio

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was 1.08, while the length to width ratio was 1.13 (Table 1).

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The thecal plates were smooth with many small round pores, approximately 0.3 µm diameter

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(Figs 5b, 7a,b). The epicone had the plate formula of Gambierdiscus, with three apical plates

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and seven precingular plates (Figs 5a, 6b,g,h,i). The apical pore plate was tear drop shaped,

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while the pore was long and fish hook shaped at the cell apex, approximately 8-9 µm long,

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with 33-45 pores surrounding (Figs 5b, 6g, 7a). The hypocone consisted of five postcingular

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plates, two antapical plates and one posterior intercalary plate (Figs 5f, g, i, 6f).

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The cingulum was deeply excavated and descending, displaced about 1-2 cingular widths

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(Figs 5c, 6a, b, c, 7b, c, d). Prominent cingular lists were present in all cells,(Figs 5i, 6a, c,

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7b, c, d). In cultured cells, the cingulum was positioned slightly higher than the mid point of

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the cell in left lateral view, approximately in the mid point of the cell in dorsal view, and just

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below the mid point of the cell in right lateral view (Figs 5c, d, e). In cells from field samples,

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the cingulum was positioned higher, approximately 1/3 of the way down the cell from the

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apex in left lateral view, and slightly above the mid point of the cell in right lateral view (Figs

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6a, c, f).

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The sulcus has been reported to consist of seven plates, the Sdp, Sda, Ssp, Ssa, t, Sma and

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Smp (Litaker et al., 2009). Of these, the Ssp, Ssa, Sdp, t and Sda plates were clearly visible in

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this study (Fig. 7b, c, d). The tiny, oval shaped Sma plate, which is adjacent to the Sda plate,

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was also visible in several images (Fig. 7c, d). The Smp plate could not be observed in our

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images. Prominent sulcal lists were present in all cells from the field (Figs 5i, 6a, c, 7b, c, d),

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and some cultured cells (Fig. 5c), but absent in other cultured cells (Fig 5h). The sulcal lists

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consisted of a long list on the left side of the Ssa and Ssp plates, and a shorter list on the right

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side of the Sdp plate (Fig. 7b, c, d). The 2'''' plate was fork shaped and invaded the sulcus

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(Figs 5g, h, i, 6a).

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Substantial plate overlaps, particularly in the hypothecal cells, were found in some cells in the

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cultured material (Fig 5g).

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Two other species of Gambierdiscus were found in field samples: Gambierdiscus cf

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belizeanus, and Gambierdiscus carpenteri. These species were only partially documented

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from the sites, and the morphological information about them is shown in the Supplementary

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Figs.

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4 Discussion

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Gambierdiscus yasumotoi has previously been reported from sub-tropical Japan (Nishimura

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et al., 2013),the Persian Gulf and the Red Sea (Saburova et al., 2013), Singapore (Holmes,

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1998), the Mexican Caribbean (Hernández-Becerril and Almazán Becerril, 2004), and even

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the northern coast of New Zealand (Rhodes et al., 2014a), but not from Australian waters.

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Here the occurrence of G. yasumotoi at three sites along a latitudinal gradient spanning more

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than 1550 km of the Australian GBR is reported, a region with endemic CFP.

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Records of G. yasumotoi in tropical and sub-tropical regions in the Indian, and Pacific

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Oceans, both in the northern and southern hemispheres, suggest that this species has a

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circum-global distribution in tropical and sub-tropical waters. Interesting is the occurrence of

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G. yasumotoi in northern New Zealand, reported by Rhodes et al. (2014a), as sea surface

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temperatures (SST) fall well below 15 º C in this region, the lowest thermal limit for any

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species of Gambierdiscus reported to date (Kibler et al., 2012). However, as (Rhodes et al.,

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2014a) noted, the specimens were collected in summer, when SST was 23 ºC. It is possible

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that the occurrence of G. yasumotoi in New Zealand is seasonal, with cells being transported

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from tropical and sub-tropical Australia during the warmer months via the East Australian

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Current (EAC) and the Tasman Front. The EAC is known to affect phytoplankton

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communities in the eastern Australian coast, transporting tropical species into sub-tropical

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and temperate areas (Armbrecht et al., 2013).

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4.1 Comparison between Gambierdiscus yasumotoi and G. ruetzleri

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Interestingly, most of the strains of G. yasumotoi which have been recently isolated have

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intermediate morphologies between G. yasumotoi and the more recently described G.

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ruetzleri (Table 1). According to the original description of G. ruetzleri, the features that

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distinguish this species from G. yasumotoi are: size (G. ruetzleri is significantly smaller and

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has a cell width less than 42 µm); a smaller, narrower and differently shaped 2’’’’ plate; a

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greater depth to width ratio, meaning they are proportionally narrower; a smaller length to

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width ratio, and a smaller epitheca to hyptheca ratio, as the cingulum is closer to the centre of

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the cell, rather than closer to the cell apex (Litaker et al., 2009).

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There was some variability in these features in both individual cells from the culture, and

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between cells found in field samples as compared to cultured cells (Table 1). Both the field

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and cultured material had L:W and D:W ratios that were more similar to those in the original

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description of Gambierdiscus yasumotoi than that of G. ruetzleri (Table 1). However, the

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epitheca to hypotheca ratios appeared to differ between the field and cultured material. For

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the cultured strain, this ratio seems to be smaller than that reported for G. yasumotoi, but the

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difference is not nearly as pronounced as in the original description of G. ruetzleri (Litaker et

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al., 2009). In previous studies, the D:W and L:W ratios of material from New Zealand were

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most similar to those of G. ruetzleri. However in overall cell size, these specimens more

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closely resembled G. yasumotoi (Rhodes et al. 2014a, Table 1). In the material from Kuwait

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(Saburova et al., 2013), the D:W ratio and epitheca:hypotheca ratio appeared to be most

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similar to those of Gambierdiscus ruetzleri, while the cell width and overall cell size were

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most similar to those of G. yasumotoi.

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In terms of the shape of the 2’’’’ plate, variability was found in the Australian samples. In

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some cells this appeared to have an almost horizontal posterior side (Figs 5f, 6a), similar to

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the shape as described for G. yasumotoi. Other cells had a 2’’’’ plate with a 45° angle on the

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posterior side of this plate (Fig. 6c), a shape more similar to that of G. ruetzleri (Litaker et al.,

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2009).

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Several specimens of Gambierdiscus yasumotoi with aberrant plate pattern have been

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observed among cultured cells (Saburova et al., 2013) and cells with substantial plate

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overlaps were found in this study (Fig 5g), which would tend to distort the plate size or

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shape. For this reason, interpreting species-level differences based on minor differences in

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plate sizes or shapes could be misleading.

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In our molecular analysis, NQAIF210 grouped with high support within the G.

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yasumtoi/ruetzleri clade, but it was not clearly grouped with either based on 18S gene

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sequences (Figs 3,4). The phylogeny constructed using the D8-D10 region of the 28S rRNA

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gene suggests that NQAIF210 and the G. cf. yasumotoi isolated from New Zealand constitute

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a highly supported sub-clade, and the two strains had identical sequences for the D1-D3

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region of the same gene (Fig. 3). The genetic data support the morphological observations,

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suggesting that these strains are indeed very similar. Interestingly, while both strains were

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morphologically closer to the original description of G. yasumotoi, in the D8-D10 phylogeny

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they grouped with high support with G. ruetzleri (Fig. 3). There are now reports of a number

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of strains, including NQAIF210 (this study) , IR4G and Go3 (Nishimura et al., 2013) and

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CAWD210 (Rhodes et al., 2014a), which always group within the G. yasumotoi /G. ruetzleri

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clade, but cannot be clearly identified based on molecular and morphological data as either

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species.

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Our analyses of p-distances among strains (Fig 4) belonging to the Gambierdiscus yasumotoi

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clade suggest that caution is needed in trying to delineate species boundaries within this

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group. Firstly, the erection of G. ruetzleri as a new species was based on a comparison with a

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single strain of G. yasumotoi, the strain used in the original description (Litaker et al., 2009).

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The estimates of within-species p-distances for G. yasumotoi are based on multiple sequences

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from this same strain, and therefore it could be considered a form of pseudo-replication to use

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such differences to recognise G. yasumotoi and G. ruetzleri as distinct, well supported entities

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in the phylogenetic analysis. Furthermore, our PCoA analyses of p-distance matrices for 18S

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and 28S rRNA gene sequences seems to suggest that p-distances among clones of G.

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yasumotoi are in some cases comparable to p-distances between strains of G. yasumotoi and

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G. ruetzleri (Fig. 4). In addition, the genetic differences between these two species are less

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than those determined for within-species divergence for other Gambierdiscus species

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(Nishimura et al., 2013; Rhodes et al., 2014a). Morphological and genetic distances similar

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to, or even larger than the ones reported between putative species within the G.

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yasumoti/ruetzleri clade have been described within species of other dinoflagellate genera,

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such as Coolia (Fraga et al., 2008; Momigliano et al., 2013; Rhodes et al., 2014b) and

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Amphidinium carterae (Murray et al., 2012). Within the G. yasumotoi/ruetzleri clade, the

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discovery of a number of strains which show intermediate morphologies and cannot be

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unambiguously identified as either G. yasumotoi or G. ruetzleri (Nishimura et al., 2013;

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Rhodes et al., 2014a) throws into doubt the status of these as distinct species. It is possible

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that G. yasumotoi and G. ruetzleri are conspecific, and the minor genetic and morphological

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differences reported are at the population level, or that they form an as yet unresolved species

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complex.

334 335

4.2Toxicity

336

In the original description of Gambierdiscus yasumotoi, methanol extracts were found to be

337

toxic to mice with symptoms similar to those of maitotoxins (MTX) (Holmes, 1998). The

338

strain of Gambierdiscus yasumotoi from New Zealand was found by LC-MS analysis not to

339

produce known analogues of MTX or of the monitored analogues of CTXs at detectable

340

levels (Rhodes et al., 2014a). However, a putative MTX analogue which had the same mass

341

as MTX-3 (Holmes and Lewis, 1994; Lewis et al., 1994) was found (Rhodes et al., 2014a). A

342

study using the human erythrocyte lysis assay (HELA) showed significant toxicity in

343

Gambierdiscus ruetzleri (Holland et al., 2013). Experiments which used specific inhibitors

344

of the MTX pathway and purified MTX, Gambierdiscus whole cell extracts, and hydrophilic

345

cell extracts containing MTX, were consistent with MTX as the primary hemolytic

346

compound produced in those studies (Holland et al., 2013). MTX was generally considered

347

not to be related to CFP symptoms, which are thought to be solely caused by ciguatoxins

348

(CTX) (Lewis and Holmes, 1993). However, the propensity for MTX to accumulate in fish

349

flesh following exposure to Gambierdiscus spp has been re-examined experimentally, and its

350

role in fish toxicity remains incompletely known(Kohli et al., 2014c). A strain of G.

351

yasumotoi was recently found to increase mortality and the expression of stress related genes

352

in copepods (Lee et al., 2014)

353 354 355

Acknowledgements

13 356

We thank the Raine Island Corporation for funding the field trip to Raine Island (SM), the

357

Australian Biological Resources Study for additional funding (SM) and the University of

358

Sydney Australian Centre for Microscopy and Microanalysis for access to the scanning

359

electron microscopes (SM). We also thank the Marine and Tropical Sciences Research

360

Facility for funding field work and laboratory work in the central GBR (KH, DB, PM).

361 362

Author contributions

363

Conceived and designed the experiments: PM, SM, KH, DB. Performed the experiments:

364

PM, SM, KH. Analysed the data: PM, SM. Contributed reagents/materials/analytical tools:

365

KH, SM, DB. Wrote the paper: PM, SM. Provided feedback on the manuscript: KH, DB.

366 367 368

References

369

Adachi, R., Fukuyo, Y., 1979. The thecal structure of a marine dinoflagellate Gambierdiscus

370

toxicus gen. et sp. nov. collected in a ciguatera-endemic area. Bull. Jap. Soc. Sci. Fish. 45(1),

371

67-71.

372

Andersen, R.A., Kawachi, M., 2005. Traditional microalgae isolation techniques, In:

373

Anderson, R.A. (Ed.), Algal culturing techniques. Elsevier, Amsterdam, pp. 83-100.

374

Armbrecht, L.H., Roughan, M., Rossi, V., Schaeffer, A., Davies, P.L., Waite, A.M., Armand,

375

L.K., 2013. Phytoplankton composition under contrasting oceanographic conditions:

376

Upwelling and downwelling (Eastern Australia). Cont. Shelf Res.

377

Babinchak, J.A., Moeller, P.D.R., Van Dolah, F.M., Eyo, P.B., Ramsdell, J.S., 1994.

378

Production of ciguatoxins in cultured Gambierdiscus toxicus. Mem. Queensl. Mus. 34, 447-

379

453.

380

Chinain, M., Faust, M.A., Pauillac, S., 1999. Morphology and molecular analyses of three

381

toxic species of Gambierdiscus (Dinophyceae): G. pacificus, sp. nov., G. australes, sp. nov.,

382

and G. polynesiensis, sp. nov. J. Phycol. 35(6), 1282-1296.

14 383

Darriba, D., Taboada, G.L., Doallo, R., Posada, D., 2012. jModelTest 2: more models, new

384

heuristics and parallel computing. Nat. Methods 9(8), 772-772.

385

Dray, S., Dufour, A.-B., 2007. The ade4 package: implementing the duality diagram for

386

ecologist. J. Stat. Softw. 22(4), 1-20.

387

Faust, M.A., 1995. Observation of sand-dwelling toxic dinoflagellates (Dinophyceae) from

388

widely different sites, including two new species. J. Phycol. 31(6), 996-1003.

389

Fleming, L.E., Baden, D.G., Bean, J.A., Weisman, R., Blythe, D.G., 1998. Seafood toxin

390

diseases: issues in epidemiology and community outreach, In: Reguera, B., Blanco, J.,

391

Fernandez, M., Wyatt, T. (Eds.), Harmful Algae. Xunta de Galicia and Intergovernmental

392

Oceanographic Commission of UNESCO, pp. 245-248.

393

Fraga, S., Penna, A., Bianconi, I., Paz, B., Zapata, M., 2008. Coolia canariensis sp. nov.

394

(Dynophyceae), a new nontoxic epiphytic benthic dinoflagellate frm the Canary Islands. J.

395

Phycol. 44(4), 1060-1070.

396

Fraga, S., Rodríguez, F., Caillaud, A., Diogène, J., Raho, N., Zapata, M., 2011.

397

Gambierdiscus excentricus sp. nov.(Dinophyceae), a benthic toxic dinoflagellate from the

398

Canary Islands (NE Atlantic Ocean). Harmful Algae 11, 10-22.

399

Gillespie, N., Lewis, R., Pearn, J., Bourke, A., Holmes, M., Bourke, J., Shields, W., 1985.

400

Ciguatera in Australia. Occurrence, clinical features, pathophysiology and management. Med.

401

J. Aust. 145(11-12), 584-590.

402

Guillard, R., Hargraves, P., 1993. Stichochrysis immobilis is a diatom, not a chrysophyte.

403

Phycologia 32(3), 234-236.

404

Guindon, S., Dufayard, J.-F., Lefort, V., Anisimova, M., Hordijk, W., Gascuel, O., 2010.

405

New algorithms and methods to estimate maximum-likelihood phylogenies: assessing the

406

performance of PhyML 3.0. Syst. Biol. 59(3), 307-321.

407

Hall, T., 1999. BioEdit: a user-friendly biological sequence alignment editor and analysis

408

program for Windows 95/98/NT. Nucl. Acid S. 41, 95-98.

409

Hamilton, B., Whittle, N., Shaw, G., Eaglesham, G., Moore, M.R., Lewis, R.J., 2010. Human

410

fatality associated with Pacific ciguatoxin contaminated fish. Toxicon 56(5), 668-673.

15 411

Hernández-Becerril, D., Almazán Becerril, A., 2004. Especies de dinoflagelados del género

412

Gambierdiscus (Dinophyceae) del Mar Caribe mexicano. Rev. Biol. Trop. 52, 77-87.

413

Holland, W.C., Litaker, R.W., Tomas, C.R., Kibler, S.R., Place, A.R., Davenport, E.D.,

414

Tester, P.A., 2013. Differences in the toxicity of six Gambierdiscus (Dinophyceae) species

415

measured using an in vitro human erythrocyte lysis assay. Toxicon 65, 15-33.

416

Holmes, M.J., 1998. Gambierdiscus yasumotoi sp. nov. (Dinophyceae), a toxic benthic

417

dinoflagellate from southeastern Asia. J. Phycol. 34(4), 661-668.

418

Holmes, M.J., Lewis, R.J., 1994. Purification and characterisation of large and small

419

maitotoxins from cultured Gambierdiscus toxicus. Nat. Toxins 2(2), 64-72.

420

Holmes, M.J., Lewis, R.J., Gillespie, N.C., 1990. Toxicity of Australian and French

421

Polynesian strains of Gambierdiscus Toxicus (Dinophyceae) grown in culture:

422

Characterization of a new type of maitotoxin. Toxicon 28(10), 1159-1172.

423

Holmes, M.J., Lewis, R.J., Poli, M.A., Gillespie, N.C., 1991. Strain dependent production of

424

ciguatoxin precursors (gambiertoxins) by Gambierdiscus toxicus (Dinophyceae) in culture.

425

Toxicon 29(6), 761-775.

426

Holmes, M.J., Lewis, R.J., Sellin, M., Street, R., 1994. The origin of ciguatera in Platypus

427

Bay. Mem. Queensl. Mus. 34, 505-512.

428

Kibler, S.R., Litaker, R.W., Holland, W.C., Vandersea, M.W., Tester, P.A., 2012. Growth of

429

eight Gambierdiscus (Dinophyceae) species: Effects of temperature, salinity and irradiance.

430

Harmful Algae 19, 1-14.

431

Kohli, G.S., Murray, S., Neilan, B.A., Rhodes, L., Harwood, D.T., Smith, K., Mayer, L.,

432

Capper, A., Hallegraeff, G., 2014a. Abundance of the potentially maitotoxic dinoflagellate

433

Gambierdiscus carpenteri in temperate waters of New South Wales, Australia. Harmful

434

Algae 39, 134-145.

435

Kohli, G.S., Neilan, B.A., Brown, M.V., Hoppenrath, M., Murray, S.A., 2014b. Cob gene

436

pyrosequencing enables characterization of benthic dinoflagellate diversity and

437

biogeography. Environ. Microbiol. 16(2), 467-485.

16 438

Kohli, G.S., Papiol, G.G., Rhodes, L.L., Harwood, D.T., Selwood, A., Jerrett, A., Murray,

439

S.A., Neilan, B.A., 2014c. A feeding study to probe the uptake of Maitotoxin by snapper

440

Pagrus auratus. Harmful Algae 37, 125-132.

441

Lee, K.-W., Kang, J.-H., Baek, S.H., Choi, Y.-U., Lee, D.-W., Park, H.-S., 2014. Toxicity of

442

the dinoflagellate Gambierdiscus sp. toward the marine copepod Tigriopus japonicus.

443

Harmful Algae 37, 62-67.

444

Lewis, R.J., 2006. Ciguatera: Australian perspectives on a global problem. Toxicon 48(7),

445

799-809.

446

Lewis, R.J., Holmes, M.J., 1993. Origin and transfer of toxins involved in ciguatera. Comp.

447

Biochem. Physiol., C: Toxicol. Pharmacol. 106(3), 615-628.

448

Lewis, R.J., Holmes, M.J., Alewood, P.F., Jones, A., 1994. Lonspray mass spectrometry of

449

ciguatoxin‐1, maitotoxin‐2 and‐3, and related marine polyether toxins. Nat. Toxins 2(2), 56-

450

63.

451

Litaker, R.W., Vandersea, M.W., Faust, M.A., Kibler, S.R., Chinain, M., Holmes, M.J.,

452

Holland, W.C., Tester, P.A., 2009. Taxonomy of Gambierdiscus including four new species,

453

Gambierdiscus caribaeus, Gambierdiscus carolinianus, Gambierdiscus carpenteri and

454

Gambierdiscus ruetzleri (Gonyaulacales, Dinophyceae). Phycologia 48(5), 344-390.

455

Marchant, H.J., Thomas, D.P., 1983. Polylysine as an adhesive for the attachment of

456

nanoplankton to substrates for electron microscopy. J. Microsc. 131(1), 127-129.

457

Momigliano, P., Sparrow, L., Blair, D., Heimann, K., 2013. The diversity of Coolia

458

spp.(Dinophyceae Ostreopsidaceae) in the central Great Barrier Reef region. PloS one 8(10),

459

e79278.

460

Murray, S., 2010. Benthic dinoflagellates, In: Hallegraeff, G.M., Bolch, C.J.S., Hil, l.D.R.A.,

461

Jameson, I., LeRoi, J.-M., McMinn, A., Murray, S., de Salas, M.F., Saunders, K. (Eds.),

462

Algae of Australia: Phytoplankton flora of temperate coastal waters. CSIRO Publishing,

463

Canberra.

464

Murray, S.A., Garby, T., Hoppenrath, M., Neilan, B.A., 2012. Genetic diversity,

465

morphological uniformity and polyketide production in dinoflagellates (Amphidinium,

466

Dinoflagellata). PloS one 7(6), e38253.

17 467

Nakahara, H., Sakami, T., Chinain, M., Ishida, Y., 1996. The role of macroalgae in

468

epiphytism of the toxic dinoflagellate Gambierdiscus toxicus (Dinophyceae). Phycol. Res.

469

44(2), 113-117.

470

Nishimura, T., Sato, S., Tawong, W., Sakanari, H., Uehara, K., Shah, M.M.R., Suda, S.,

471

Yasumoto, T., Taira, Y., Yamaguchi, H., 2013. Genetic diversity and distribution of the

472

ciguatera-causing dinoflagellate Gambierdiscus spp.(Dinophyceae) in coastal areas of Japan.

473

PloS one 8(4), e60882.

474

Nishimura, T., Sato, S., Tawong, W., Sakanari, H., Yamaguchi, H., Adachi, M., 2014.

475

Morphology of Gambierdiscus scabrosus sp. nov.(Gonyaulacales): a new epiphytic toxic

476

dinoflagellate from coastal areas of Japan. J. Phycol.

477

Paradis, E., Claude, J., Strimmer, K., 2004. APE: analyses of phylogenetics and evolution in

478

R language. Bioinformatics 20(2), 289-290.

479

Parsons, M.L., Settlemier, C.J., Ballauer, J.M., 2011. An examination of the epiphytic nature

480

of Gambierdiscus toxicus, a dinoflagellate involved in ciguatera fish poisoning. Harmful

481

Algae 10(6), 598-605.

482

Rhodes, L., Giménez Papiol, G., Smith, K., Harwood, T., 2014a. Gambierdiscus cf.

483

yasumotoi (Dinophyceae) isolated from New Zealand's sub-tropical northern coastal waters.

484

N. Z. J. Mar. Freshwat. Res.(ahead-of-print), 1-8.

485

Rhodes, L., Smith, K., Papiol, G.G., Adamson, J., Harwood, T., Munday, R., 2014b.

486

Epiphytic dinoflagellates in sub-tropical New Zealand, in particular the genus Coolia

487

Meunier. Harmful Algae 34, 36-41.

488

Richlen, M.L., Morton, S.L., Barber, P.H., Lobel, P.S., 2008. Phylogeography, morphological

489

variation and taxonomy of the toxic dinoflagellateGambierdiscus toxicus(Dinophyceae).

490

Harmful Algae 7(5), 614-629.

491

Ronquist, F., Huelsenbeck, J.P., 2003. MrBayes 3: Bayesian phylogenetic inference under

492

mixed models. Bioinformatics 19(12), 1572-1574.

493

Saburova, M., Polikarpov, I., Al-Yamani, F., 2013. New records of the genus Gambierdiscus

494

in marginal seas of the Indian Ocean. Mar. Biodivers. Rec. 6, e91.

18 495

Thompson, J.D., Higgins, D.G., Gibson, T.J., 1994. CLUSTAL W: improving the sensitivity

496

of progressive multiple sequence alignment through sequence weighting, position-specific

497

gap penalties and weight matrix choice. Nucleic Acids Res. 22(22), 4673-4680.

498

Tosteson, T., 2004. Caribbean ciguatera: a changing paradigm. Rev. Biol. Trop. 52, 109-113.

499

Walsh, P.S., Metzger, D.A., Higuchi, R., 1991. Chelex 100 as a medium for simple extraction

500

of DNA for PCR-based typing from forensic material. BioTechniques 10(4), 506-513.

501

Xu, Y., Richlen, M.L., Morton, S.L., Mak, Y.L., Chan, L.L., Tekiau, A., Anderson, D.M.,

502

2014. Distribution, abundance and diversity of Gambierdiscus spp. from a ciguatera-endemic

503

area in Marakei, Republic of Kiribati. Harmful Algae 34, 56-68.

504 505 506 507 508 509 510 511 512 513 514 515 516 517 518

19 519

Figures Legends

520 521

Figure 1. Map of the sampling sites in Great Barrier Reef (GBR) region, east coast,

522

Queensland, Australia. Inset box, showing the location of the sampling area within Australia.

523

The three regions in which sampling took place: Raine Island in the far northern GBR; Nelly

524

Bay and Pallarenda, Townsville, in the central GBR; Heron Island in the southern GBR.

20

525 526 527

Figure 2. Maximum Likelihood phylogeny of the genus Gambierdiscus based on near-

528

complete 18S gene sequences. Branch support values (ML/BI) represent bootstrap support

529

based on 1000 pseudo-replicate datasets and Bayesian clade credibility values respectively.

530

Branches with 100/100 support are indicated by an asterisk. Scale represents number of

531

changes per nucleotide. Strains isolated in this study are shown in bold.

21

532 533

Figure 3. Maximum Likelihood phylogeny of the genus Gambierdiscus based on the D8-D10

534

region of the 28S rRNA gene. Branch support values (ML/BI) represent bootstrap support

535

based on 1000 pseudo-replicate datasets and Bayesian clade credibility values respectively.

536

Branches with 100/100 support are indicated by an asterisk. Scale represents number of

537

changes per nucleotide. Strains isolated in this study are shown in bold.

538 539 540 541 542 543 544 545

22 546 547

548 549

Figure 4. Principal Coordinate Analyses (PCoA) based on p-distance matrices among

550

sequences within the G. yasumotoi/ G. ruetzleri clade. PCoA based on near complete 18S

551

gene sequences (A & B) and on the D8-D10 (C & D) and D1-D3 (E & F) regions of the 28S

552

rRNA gene. Clones from the same strain are represented by partially transparent symbols

553

with the same colour, allowing visualization of density of points via colour saturation .

554

Eigenvalues of the plotted axes are shown in black.

23

555 556

Figure 5. Scanning electron microscope images of Gambierdiscus yasumotoi from the

557

cultured strain, NQAIF210. Scale bars are shown. A. Apical view, showing the epithecal

558

plate pattern and shape of the epicone. B. The apical pore plate, showing the comma and

559

pores. C. Cell in left lateral view. D. Cell in dorsal view. E. Cell in dorsal view. F. Antapical-

560

ventral view, showing antapical plates and part of the sulcus. G. Antapical view, showing

561

substantial plate overlaps. H. Ventral view, showing the sulcus and a lack of sulcal lists. I.

562

Antapical/lateral view, showing the sulcal lists.

563 564

24

565 566

Figure 6. Scanning electron microscope images of Gambierdiscus yasumotoi from the field

567

material from Raine Island and Heron Island. Scale bars are 10 µm. A. Cell in ventral/lateral

568

view, showing sulcal lists. B. Cell in apical/ventral view, showing part of the epicone. C. Cell

569

in ventral view. D. Cell in right lateral view. E. Cell in left lateral view. F. Cell in left lateral

570

view. G. Cell in apical view, showing the epicone, including the apical pore plate and

571

comma. H. Cell in apical view, showing the epicone. I. Cell in apical view, showing the

572

epicone.

573 574 575

25

576 577

Figure 7. Scanning electron microscope images of Gambierdiscus yasumotoi from the field

578

material from Raine Island and Heron Island, showing the apical pore region, and sulcus.

579

Scale bars represent 10 µm (A) and (B).A. The apical pore plate. B. The sulcal plates,

580

showing the list, and ssa and ssp. C. Showing the sma and sda plates. D. Showing the sma

581

plate and sulcal list.

582

26

Tables Table 1. Cell sizes and comparison of other morphological features of G.yasumotoi, from our data and previous reports.

site

G.

G.

G. cf

G.

G.

G. yasumotoi

G. yasumotoi

G. ruetzleri

yasumotoi

yasumotoi

yasumotoi

yasumotoi

yasumotoi

(Holmes 1998),

(Litaker et al

(Litaker et al

(this study

(this study

(Rhodes et

(Saburova

(Saburova

type description

2009

2009)

field cells)

culture)

al in 2014a

et al 2013

et al 2013

Heron

Townsville northern

Kuwait

Jordan

Island,

New

Raine

Zealand

Singapore

Island Depth

Mean =

Mean = 49

Mean =

Mean=62.9 Mean= 62.6

Mean = 50

Mean = 56.8

Mean = 45.5

57.2

Range 44-

54.8

± 4.4

(n=17)

(n=14)

Range 41-55

Range 54-

54

± 5.7

(n=30)

Mean = 56

Mean= 51

Mean =

Mean=

Mean= 62.9

Mean = 53

Mean= 62.4

Mean = 51.6

Range 53-

Range 49-

59.8 ± 7.5

61.7 ± 6.2,

± 6.8, N=7

(n=17)

(n=14)

45-59.5

59

54

Mean=48

Mean=45

Mean =

Mean=

Mean=

Mean = 44

Mean = 51.7

Mean=37.5

Range 46-

Range 40-

42.5 ± 4.1

54.1 ± 5.1,

54.7± 1.5,

38-50

(n=14)

30.9-42.2

50

49

N=9

N=3

± 6.1, N =7

Range 43-61

59 Length

Width

N = 20

45-63

27

Epitheca

~0.5

~1.0

D:W ratio 1.18

1.08

L:W ratio

1.13

~1.0

0.5-0.6

~1.0

1.29

1.28

1.14

1.13

1.1

1.35

1.41

1.14

1.15

1.20

1.2

1.45

to hypotheca ratio

1.16

28

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