Hosts of the Plio-Pleistocene Past Reflect Modern-Day Coral Vulnerability

Total Page:16

File Type:pdf, Size:1020Kb

Hosts of the Plio-Pleistocene Past Reflect Modern-Day Coral Vulnerability Proc. R. Soc. B (2012) 279, 2448–2456 doi:10.1098/rspb.2011.2621 Published online 15 February 2012 Hosts of the Plio-Pleistocene past reflect modern-day coral vulnerability Robert van Woesik1,*, Erik C. Franklin2, Jennifer O’Leary3, Tim R. McClanahan4, James S. Klaus5 and Ann F. Budd6 1Department of Biological Sciences, Florida Institute of Technology, Melbourne 32901 FL, USA 2Hawaii Institute of Marine Biology, School of Ocean and Earth Science and Technology, University of Hawaii, Kaneohe 96744, HI, USA 3National Center for Ecological Analysis and Synthesis, University of California, Santa Barbara 93101 CA, USA 4Coral Reef Conservation Project, Wildlife Conservation Society, Mombasa, Kenya 5Department of Geological Sciences, University of Miami, Coral Gables 33146 FL, USA 6Department of Geoscience, University of Iowa, Iowa City 52242 IA, USA The risk of global extinction of reef-building coral species is increasing. Weevaluated extinction risk using a bio- logical trait-based resiliency index that was compared with Caribbean extinction during the Plio-Pleistocene, andwithextinctionriskdeterminedbytheInternationalUnionforConservationofNature(IUCN).Through the Plio-Pleistocene, the Caribbean supported more diverse coral assemblages than today and shared consi- derable overlap with contemporary Indo-Pacific reefs. A clear association was found between extant Plio- Pleistocene coral genera and our positive resilience scores. Regional extinction in the past and vulnerability in the present suggests that Pocillopora, Stylophora and foliose Pavona areamongthemostsusceptibletaxato local and regional isolation. These same taxa were among the most abundant corals in the Caribbean Pliocene. Therefore, a widespread distribution did not equate with immunity to regional extinction. The strong relation- ship between past and present vulnerability suggests that regional extinction events are trait-based and not merely random episodes. We found several inconsistencies between our data and the IUCN scores, which suggest a need to critically re-examine what constitutes coral vulnerability. Keywords: biological trait; coral; extinction risk; Plio-Pleistocene; resilience; vulnerability 1. INTRODUCTION with persisting congenerics in the present-day Indo-Pacific Climate change is increasing the severity and the intensity of (Alveopora, Caulastraea, Galaxea, Gardinoseris, Goniopora, thermal stress events on modern coral reefs [1–4]. One of Isopora, Pavona, Pocillopora, Psammocora, Stylophora the primary concerns of conservation biologists and ecosys- and Trachyphyllia), whereas others went globally extinct tem managers is assessing the vulnerability of ecologically (Antillia, Antillophyllia, Hadrophyllia, Pironastrea, Placo- important taxa and mitigating their risk. The risk of global cyathus and Thysanus)[9]. The rates of change towards extinction of coral species is currently assigned by the Inter- regional and global extinction in the Caribbean varied national Union for Conservation of Nature (IUCN) using considerably; some genera gradually declined, whereas population reduction thresholds. For the vast majority of others declined rapidly [10]. coral species, IUCN conservation status is evaluated from In the early Pliocene, large colonies of Pocillopora domi- a weighted average calculated by multiplying the area of nated the shallow reefs along with Stylophora [11,12]. reef, within a species’ distribution range, by the per cent of Stylophora was highly vulnerable to the climate shifts of the total coral cover loss in 17 different geographical regions. Plio-Pleistocene, and went regionally extinct approximately Using this method, the IUCN has documented an increase 1.8 Ma from the Caribbean. By contrast, Pocillopora gradu- in the elevated extinction risk status for coral species from 2 ally diminished over millions of years, shifting from a per cent of 704 species during pre-1998 to 33 per cent by ubiquitous distribution of predominantly large colonies, to 2008 [5]. This approach is currently the only comprehen- a patchy distribution of small colonies, and eventually to sive assessment of coral extinction risk, but it is calculated regional extinction during the last interglacial. The foliose with limited data on species-specific trends, and lacks a Pavona that went extinct in the Caribbean through the historical validation process [6,7]. Plio-Pleistocene was never dominant but diminished over The regional extinctions in the Plio-Pleistocene may shed several million years through repeated isolation [10]. The light on which coral genera may be vulnerable or resistant two Caribbean Acropora species (Acropora palmata and to stress during contemporary ocean warming. During Acropora cervicornis), increased in relative abundance the Plio-Pleistocene turnover, 25 coral genera persisted, through the Pliocene and Pleistocene. The Montastraea while 18 were lost from the Caribbean region (figure 1). annularis complex, Siderastrea and branched Porites changed During this period, some corals went regionally extinct little over this 5 Myr period [10]. If indeed biological traits lead to differences in fitness, then the march to regional extinction during the Plio- * Author for correspondence (rvw@fit.edu). Pleistocene in the Caribbean should be reflected in the Received 15 December 2011 Accepted 27 January 2012 2448 This journal is q 2012 The Royal Society Past reflects modern vulnerability R. van Woesik et al. 2449 extant Caribbean global sea level Caribbean genera (R) extinctions (+) extinctions (‡) –100 0 –50 (m) 50 R R R R R R R R R R R R R R R R R R R R R R R R R R R R R +++++ 0 ++ ‡ ‡ middle ‡ ‡ + ‡ 100 k.y. cycles 100 k.y. Pleistocene + 2 lower onset of NHG 41 k.y. cycles 41 k.y. + ‡ late + + age (Ma) 4 Pliocene closure of early CAS 6 late [8] Miocene Favia Mussa Porites Pavona Antillia Isopora Galaxea Undaria Diploria Agaricia Eusmilia Scolymia Acropora Thysanus Madracis Manicina Isophyllia Helioseris Alveopora Leptoseris Cladocora Goniopora Stylophora Meandrina Siderastrea Pocillopora Solenastrea Pironastrea Dendrogyra Mussismilia Caulastraea Dichocoenia Montastraea Colpophyllia Psammocora Hadrophyllia Placocyathus Antillophyllia Trachyphyllia Isophyllastrea Mycetophyllia Gardineroseris Stephanocoenia Figure 1. Stratigraphic ranges of recorded reef coral genera (total ¼ 43) within the Caribbean region from 6.8 Ma to Recent. Of the 18 genera that went regionally extinct in the Caribbean, 12 persist in the Indo-Pacific today. Key palaeo-environmental events, including closure of the Central American Seaway (CAS) and the onset of Northern Hemisphere glaciation (NHG), are highlighted next to the global sea-level curve of Miller et al.[8]. genealogy of contemporary species in the warming decision-making [16] constituted that the traits and scoring Indo-Pacific. By contrast, if individuals on coral reefs are were purposefully decided a priori (table 1), and that all responding to changing conditions equally and indepen- traits were maintained throughout the analysis to avoid tau- dently of species traits [13], species may march through tology. A consensus was reached among 10 coral-reef time showing random episodes of extinction. Here, we scientists on the general principle underlying each trait and test an alternative to the concept of random episodes of the methodology of the scoring protocol (table 1)[16]. For regional extinctions, and propose that biological traits analysis, we selected 14 dominant (modern) coral genera could play a larger role than suggested by neutral theory for the Indo-Pacific Ocean and 15 for the Caribbean Sea. [13]. We test these ideas by comparing modern corals Two genera were subdivided based on morphology with with coral populations that lived on ancient Plio- Pavona classified as either foliose or encrusting/submassive Pleistocene reefs of the Caribbean that experienced a and Porites as branching or massive. Montastraea in the protracted period of complex environmental change and Caribbean were evaluated as either Montastraea annularis extinction [9,14,15]. Our objective was to evaluate whe- complex or Montastraea cavernosa. Although both genera ther regional extinction events of the Plio-Pleistocene and subgenera groups were examined, we refer to all corals Caribbean region lend insight into future events in the at the genus level. Each coral genus was then evaluated on Indo-Pacific. Our central hypothesis was that trends through their tolerance to a hypothetical two-month þ 38C thermal the Plio-Pleistocene will reflect contemporary trends on stress anomaly, during the solar insolation maximum. Simi- Indo-Pacific reefs. A mismatch between past and present larly, four key process variables were scored for a suite of trends would lend support to neutral theory, which suggests coral taxa, to address whether each process would affect that species extinctions are a random process. By contrast, recovery from the temperature anomaly (table 1). The a match between past and present trends would suggest a scores for the traits and processes were summed for each non-random, biological trait-based process. coral genus and classified as a resilience score. Although con- temporary species within each genus differs in terms of their geographical distribution—some are widespread and 2. MATERIAL AND METHODS others are restricted—classic taxonomic texts [17] and (a) Modern genera resilience scores recent molecular techniques show evidence that many We examined whether biological traits play a large role in the genera (e.g. Acropora, Porites, Stylophora,
Recommended publications
  • Reef Coralgal Assemblages As Recorders of Paleobathymetry and Sea Level Changes in the Indo-Pacific Province
    PERGAMON Quaternary Science Reviews 18 (1999) 1681-1695 QSR Reef coralgal assemblages as recorders of paleobathymetry and sea level changes in the Indo-Pacific province I' G. Cabioch">*,L.F. Montaggionib, G. Faurec, A. Ribaud-Lamentib "ORSTOM (L'Institut franqais de Recherche scientifique pour le Développement en Coopérationj, UMR 6526 'Géosciences Azur', B.P. A5, Noum& Cedex, New Caledonia '.:I bUPRESA CNRS 6019, Centre de Sédinientologie et Palhontologie, Université de Provence, 13331 Marseille Cedex 3, France 'UPRESA CNRS 6019, Laboratoire $Hydrobiologie A.larine et Continentale, Université des Sciences et Techniques du Languedoc, Place Eugène Bataillon, 34095 Montpellier Cedex 5, France æiP Abstract Science Ltd. All Eights reserved. - __ D l I Fonds Documentaire I R 1 I I 1 I O Il lull~Illi~~lÎ~~~~i~iipillill1002 1466 1. Introduction building coral communities, are regarded as- one of the most reliable sea-level markers (Liglity et al., 1978; During thellast few decades, our knowledge of psst- 1 Davies and Montaggioni, 1985; Hopley, 1986; Montag- glacial sea-level changes has been greatly enhanced gioni and Faure, 1997). through studies of reef sites (Fairbanks, 1989; Bard et al., Corals older than 6 ka BP are not generally directly 1990,1996; Chappell and Polach, 1991; Edwards et al., accessible from rapidly subsiding (e.g. intraplate volcanic 1993).The tropical zone offers the opportunity to exami- islands) or slowly uplifting coasts (e.g. hydro-isostasy- ne sea-level changes and the melting history of continen- experiencing areas). As a result, the only way to recover tal ice sheets far from the polar zones (Bard et al., 1996).
    [Show full text]
  • Checklist of Fish and Invertebrates Listed in the CITES Appendices
    JOINTS NATURE \=^ CONSERVATION COMMITTEE Checklist of fish and mvertebrates Usted in the CITES appendices JNCC REPORT (SSN0963-«OStl JOINT NATURE CONSERVATION COMMITTEE Report distribution Report Number: No. 238 Contract Number/JNCC project number: F7 1-12-332 Date received: 9 June 1995 Report tide: Checklist of fish and invertebrates listed in the CITES appendices Contract tide: Revised Checklists of CITES species database Contractor: World Conservation Monitoring Centre 219 Huntingdon Road, Cambridge, CB3 ODL Comments: A further fish and invertebrate edition in the Checklist series begun by NCC in 1979, revised and brought up to date with current CITES listings Restrictions: Distribution: JNCC report collection 2 copies Nature Conservancy Council for England, HQ, Library 1 copy Scottish Natural Heritage, HQ, Library 1 copy Countryside Council for Wales, HQ, Library 1 copy A T Smail, Copyright Libraries Agent, 100 Euston Road, London, NWl 2HQ 5 copies British Library, Legal Deposit Office, Boston Spa, Wetherby, West Yorkshire, LS23 7BQ 1 copy Chadwick-Healey Ltd, Cambridge Place, Cambridge, CB2 INR 1 copy BIOSIS UK, Garforth House, 54 Michlegate, York, YOl ILF 1 copy CITES Management and Scientific Authorities of EC Member States total 30 copies CITES Authorities, UK Dependencies total 13 copies CITES Secretariat 5 copies CITES Animals Committee chairman 1 copy European Commission DG Xl/D/2 1 copy World Conservation Monitoring Centre 20 copies TRAFFIC International 5 copies Animal Quarantine Station, Heathrow 1 copy Department of the Environment (GWD) 5 copies Foreign & Commonwealth Office (ESED) 1 copy HM Customs & Excise 3 copies M Bradley Taylor (ACPO) 1 copy ^\(\\ Joint Nature Conservation Committee Report No.
    [Show full text]
  • Taxonomic Checklist of CITES Listed Coral Species Part II
    CoP16 Doc. 43.1 (Rev. 1) Annex 5.2 (English only / Únicamente en inglés / Seulement en anglais) Taxonomic Checklist of CITES listed Coral Species Part II CORAL SPECIES AND SYNONYMS CURRENTLY RECOGNIZED IN THE UNEP‐WCMC DATABASE 1. Scleractinia families Family Name Accepted Name Species Author Nomenclature Reference Synonyms ACROPORIDAE Acropora abrolhosensis Veron, 1985 Veron (2000) Madrepora crassa Milne Edwards & Haime, 1860; ACROPORIDAE Acropora abrotanoides (Lamarck, 1816) Veron (2000) Madrepora abrotanoides Lamarck, 1816; Acropora mangarevensis Vaughan, 1906 ACROPORIDAE Acropora aculeus (Dana, 1846) Veron (2000) Madrepora aculeus Dana, 1846 Madrepora acuminata Verrill, 1864; Madrepora diffusa ACROPORIDAE Acropora acuminata (Verrill, 1864) Veron (2000) Verrill, 1864; Acropora diffusa (Verrill, 1864); Madrepora nigra Brook, 1892 ACROPORIDAE Acropora akajimensis Veron, 1990 Veron (2000) Madrepora coronata Brook, 1892; Madrepora ACROPORIDAE Acropora anthocercis (Brook, 1893) Veron (2000) anthocercis Brook, 1893 ACROPORIDAE Acropora arabensis Hodgson & Carpenter, 1995 Veron (2000) Madrepora aspera Dana, 1846; Acropora cribripora (Dana, 1846); Madrepora cribripora Dana, 1846; Acropora manni (Quelch, 1886); Madrepora manni ACROPORIDAE Acropora aspera (Dana, 1846) Veron (2000) Quelch, 1886; Acropora hebes (Dana, 1846); Madrepora hebes Dana, 1846; Acropora yaeyamaensis Eguchi & Shirai, 1977 ACROPORIDAE Acropora austera (Dana, 1846) Veron (2000) Madrepora austera Dana, 1846 ACROPORIDAE Acropora awi Wallace & Wolstenholme, 1998 Veron (2000) ACROPORIDAE Acropora azurea Veron & Wallace, 1984 Veron (2000) ACROPORIDAE Acropora batunai Wallace, 1997 Veron (2000) ACROPORIDAE Acropora bifurcata Nemenzo, 1971 Veron (2000) ACROPORIDAE Acropora branchi Riegl, 1995 Veron (2000) Madrepora brueggemanni Brook, 1891; Isopora ACROPORIDAE Acropora brueggemanni (Brook, 1891) Veron (2000) brueggemanni (Brook, 1891) ACROPORIDAE Acropora bushyensis Veron & Wallace, 1984 Veron (2000) Acropora fasciculare Latypov, 1992 ACROPORIDAE Acropora cardenae Wells, 1985 Veron (2000) CoP16 Doc.
    [Show full text]
  • Florida Keys…
    What Do We Know? • Florida Keys… − Stony coral benthic cover declined by 40% from 1996 – 2009 (Ruzicka et al. 2013). − Potential Driving Factor? Stress due to extreme cold & warm water temperatures − Stony coral communities in patch reefs remained relatively constant after the 1998 El Niño (Ruzicka et al. 2013). − Patch reefs exposed to moderate SST Carysfort Reef - Images from Gene Shinn - USGS Photo Gallery variability exhibited the highest % live coral cover (Soto et al. 2011). Objective To test if the differences in stony coral diversity on Florida Keys reefs were correlated with habitats or SST variability from 1996 - 2010. Methods: Coral Reef Evaluation & Monitoring Program (CREMP) % coral cover 43 species DRY TORTUGAS UPPER KEYS MIDDLE KEYS LOWER KEYS 36 CREMP STATIONS (Patch Reefs (11), Offshore Shallow (12), Offshore Deep (13)) Methods: Sea Surface Temperature (SST) • Annual SST variance were derived from weekly means. • Categories for SST variability (variance): • Low (<7.0°C2) • Intermediate (7.0 - 10.9°C2) • High (≥11.0°C2) Advanced Very High Resolution Radiometer (AVHRR) SST data Vega-Rodriguez M et al. (2015) Results 1 I 0.5 Acropora palmata I s i Millepora complanata x Multivariate Statistics A l a Acropora c i Agaricia agaricites n o Pseudodiploriarevealed clivosa cervicornisthat stonycomplex n a C 0 Porites astreoides Madracis auretenra h t i coral diversity varied w Diploria labyrinthiformis Agaricia lamarcki n o Siderastrea radians i t Porites porites a l e significantly with r r Orbicella annularis o C -0.5 Pseudodiploriahabitats strigosa Colpophyllia natansStephanocoenia intercepta Montastraea cavernosa Siderastrea siderea Canonical Analysis of Principal Coordinates (CAP) -1 0.6 -1 -0.5 0 0.5 1 Correlation with Canonical Axis I ) % 0.4 7 6 .
    [Show full text]
  • Impact of the 2005 Coral Bleaching Event on Porites Porites and Colpophyllia Natans at Tektite Reef, US Virgin Islands
    View metadata, citation and similar papers at core.ac.uk brought to you by CORE provided by Springer - Publisher Connector Coral Reefs (2007) 26:689–693 DOI 10.1007/s00338-007-0241-y NOTE Impact of the 2005 coral bleaching event on Porites porites and Colpophyllia natans at Tektite Reef, US Virgin Islands K. R. T. Whelan · J. Miller · O. Sanchez · M. Patterson Received: 7 August 2006 / Accepted: 19 April 2007 / Published online: 6 June 2007 © Springer-Verlag 2007 Abstract A thermal stress anomaly in 2005 caused mass Introduction coral bleaching at a number of north-east Caribbean reefs. The impact of the thermal stress event and subsequent Coral bleaching occurs when coral polyps loose pigment or White-plague disease type II on Porites porites and Colpo- expel zooxanthellae due to physiological stress, which phyllia natans was monitored using a time series of photo- recently has been most-often related to high water tempera- graphs from Tektite Reef, Virgin Islands National Park, tures and high solar radiation (Brown 1997; Winter et al. St. John. Over 92% of the P. porites and 96% of the 1998; Santavy et al. 2005). Since the 1980s, reports of coral C. natans experienced extensive bleaching (>30% of col- bleaching in the Caribbean have increased, with major ony bleached). During the study, 56% of P. porites and Caribbean-wide bleaching occurring in 1997–1998 (Hoegh- 42% of C. natans experienced whole-colony mortality Guldberg 1999; Aronson et al. 2000; Gardner et al. 2003). within the sample plots. While all whole-colony mortality Approximately 43–47% of coral tissue bleached at two St of P.
    [Show full text]
  • Review on Hard Coral Recruitment (Cnidaria: Scleractinia) in Colombia
    Universitas Scientiarum, 2011, Vol. 16 N° 3: 200-218 Disponible en línea en: www.javeriana.edu.co/universitas_scientiarum 2011, Vol. 16 N° 3: 200-218 SICI: 2027-1352(201109/12)16:3<200:RHCRCSIC>2.0.TS;2-W Invited review Review on hard coral recruitment (Cnidaria: Scleractinia) in Colombia Alberto Acosta1, Luisa F. Dueñas2, Valeria Pizarro3 1 Unidad de Ecología y Sistemática, Departamento de Biología, Facultad de Ciencias, Pontificia Universidad Javeriana, Bogotá, D.C., Colombia. 2 Laboratorio de Biología Molecular Marina - BIOMMAR, Departamento de Ciencias Biológicas, Facultad de Ciencias, Universidad de los Andes, Bogotá, D.C., Colombia. 3 Programa de Biología Marina, Facultad de Ciencias Naturales, Universidad Jorge Tadeo Lozano. Santa Marta. Colombia. * [email protected] Recibido: 28-02-2011; Aceptado: 11-05-2011 Abstract Recruitment, defined and measured as the incorporation of new individuals (i.e. coral juveniles) into a population, is a fundamental process for ecologists, evolutionists and conservationists due to its direct effect on population structure and function. Because most coral populations are self-feeding, a breakdown in recruitment would lead to local extinction. Recruitment indirectly affects both renewal and maintenance of existing and future coral communities, coral reef biodiversity (bottom-up effect) and therefore coral reef resilience. This process has been used as an indirect measure of individual reproductive success (fitness) and is the final stage of larval dispersal leading to population connectivity. As a result, recruitment has been proposed as an indicator of coral-reef health in marine protected areas, as well as a central aspect of the decision-making process concerning management and conservation.
    [Show full text]
  • Biological Environmental Survey in Cat Ba Island
    Biodiversity International Journal Research Article Open Access Biological environmental survey in Cat Ba Island Abstract Volume 2 Issue 2 - 2018 Cat Ba Island has a significant biodiversity value as it is home to a number of rare and endangered species of plants and animals, with the world’s rarest primates the Golden- Doan Quang Tri,1,2 Tran Hong Thai2 headed Langur. According to the study results, Cat Ba place have listed 2,380 species of 1Ton Duc Thang University, Vietnam animals and plants including: terrestrial plants 741 species; living animals in the forest area 2 Vietnam Meteorological and Hydrological Administration, 282 species; mangrove plants 30 species; seaweeds 79 species; phytoplankton 287 species; Vietnam plank tonic animals 98 species; sea-fish 196 species; corals 154 species. It is identified as one of the areas of highest biodiversity importance in Vietnam and is recognized as a high Correspondence: Doan Quang Tri, Sustainable Management of priority for global conservation. Natural Resources and Environment Research Group, Faculty of Environment and Labour Safety, Ton Duc Thang University, Ho Keywords: mangrove, seagrass, coral reef, phytoplankton, cat ba island Chi Minh City, Vietnam, Email [email protected] Received: December 04, 2017 | Published: March 28, 2018 Introduction the richest marine biological system because of its diversity in the North of Vietnam.3‒7 Biosphere reserves Cat Ba Island has been recognized as a UNESCO World on December 02nd, 2004. It is the 4th world’s biosphere reserve in Vietnam. Biosphere reserves Cat Ba archipelago including great majority of Cat Ba Island in Cat Hai district, Hai Phong city, Vietnam.
    [Show full text]
  • Patterns of Septal Biomineralization in Scleractinia Compared with Their 28S Rrna Phylogeny
    PBlackwell Publishingatterns Ltd. of septal biomineralization in Scleractinia compared with their 28S rRNA phylogeny: a dual approach for a new taxonomic framework JEAN-PIERRE CUIF, GUILLAUME LECOINTRE, CHRISTINE PERRIN, ANNIE TILLIER & SIMON TILLIER Accepted: 2 December 2002 Cuif, J.-P., Lecointre, G., Perrin, C., Tillier, A. & Tillier, S. (2003). Patterns of septal bio- mineralization in Scleractinia compared with their 28S rRNA phylogeny: a dual approach for a new taxonomic framework. — Zoologica Scripta, 32, 459–473. A molecular phylogeny of the Scleractinia is reconstructed from approximately 700 nucleo- tides of the 5′end of the 28S rDNA obtained from 40 species. A comparison of molecular phylogenic trees with biomineralization patterns of coral septa suggests that at least five clades are corroborated by both types of data. Agaricidae and Dendrophylliidae are found to be monophyletic, that is supported by microstructural data. Conversely, Faviidae and Caryophyl- liidae are found to be paraphyletic: Cladocora should be excluded from the faviids, whereas Eusmilia should be excluded from the caryophylliids. The conclusion is also supported by the positions, sizes and shapes of centres of calcification. The traditional Guyniidae are diphyletic, corroborating Stolarski’s hypothesis ‘A’. Some results from our most parsimonious trees are not strongly statistically supported but corroborated by other molecular studies and micro- structural observations. For example, in the scleractinian phylogenetic tree, there are several lines of evidence (including those from our data) to distinguish a Faviidae–Mussidae lineage and a Dendrophylliidae–Agaricidae–Poritidae–Siderastreidae lineage. From a methodological standpoint, our results suggest that co-ordinated studies creating links between biomineralization patterns and molecular phylogeny may provide an efficient working approach for a re- examination of scleractinian classification.
    [Show full text]
  • The Genetic Identity of Dinoflagellate Symbionts in Caribbean Octocorals
    Coral Reefs (2004) 23: 465-472 DOI 10.1007/S00338-004-0408-8 REPORT Tamar L. Goulet • Mary Alice CofFroth The genetic identity of dinoflagellate symbionts in Caribbean octocorals Received: 2 September 2002 / Accepted: 20 December 2003 / Published online: 29 July 2004 © Springer-Verlag 2004 Abstract Many cnidarians (e.g., corals, octocorals, sea Introduction anemones) maintain a symbiosis with dinoflagellates (zooxanthellae). Zooxanthellae are grouped into The cornerstone of the coral reef ecosystem is the sym- clades, with studies focusing on scleractinian corals. biosis between cnidarians (e.g., corals, octocorals, sea We characterized zooxanthellae in 35 species of Caribbean octocorals. Most Caribbean octocoral spe- anemones) and unicellular dinoñagellates commonly called zooxanthellae. Studies of zooxanthella symbioses cies (88.6%) hosted clade B zooxanthellae, 8.6% have previously been hampered by the difficulty of hosted clade C, and one species (2.9%) hosted clades B and C. Erythropodium caribaeorum harbored clade identifying the algae. Past techniques relied on culturing and/or identifying zooxanthellae based on their free- C and a unique RFLP pattern, which, when se- swimming form (Trench 1997), antigenic features quenced, fell within clade C. Five octocoral species (Kinzie and Chee 1982), and cell architecture (Blank displayed no zooxanthella cladal variation with depth. 1987), among others. These techniques were time-con- Nine of the ten octocoral species sampled throughout suming, required a great deal of expertise, and resulted the Caribbean exhibited no regional zooxanthella cla- in the differentiation of only a small number of zoo- dal differences. The exception, Briareum asbestinum, xanthella species. Molecular techniques amplifying had some colonies from the Dry Tortugas exhibiting zooxanthella DNA encoding for the small and large the E.
    [Show full text]
  • Volume 2. Animals
    AC20 Doc. 8.5 Annex (English only/Seulement en anglais/Únicamente en inglés) REVIEW OF SIGNIFICANT TRADE ANALYSIS OF TRADE TRENDS WITH NOTES ON THE CONSERVATION STATUS OF SELECTED SPECIES Volume 2. Animals Prepared for the CITES Animals Committee, CITES Secretariat by the United Nations Environment Programme World Conservation Monitoring Centre JANUARY 2004 AC20 Doc. 8.5 – p. 3 Prepared and produced by: UNEP World Conservation Monitoring Centre, Cambridge, UK UNEP WORLD CONSERVATION MONITORING CENTRE (UNEP-WCMC) www.unep-wcmc.org The UNEP World Conservation Monitoring Centre is the biodiversity assessment and policy implementation arm of the United Nations Environment Programme, the world’s foremost intergovernmental environmental organisation. UNEP-WCMC aims to help decision-makers recognise the value of biodiversity to people everywhere, and to apply this knowledge to all that they do. The Centre’s challenge is to transform complex data into policy-relevant information, to build tools and systems for analysis and integration, and to support the needs of nations and the international community as they engage in joint programmes of action. UNEP-WCMC provides objective, scientifically rigorous products and services that include ecosystem assessments, support for implementation of environmental agreements, regional and global biodiversity information, research on threats and impacts, and development of future scenarios for the living world. Prepared for: The CITES Secretariat, Geneva A contribution to UNEP - The United Nations Environment Programme Printed by: UNEP World Conservation Monitoring Centre 219 Huntingdon Road, Cambridge CB3 0DL, UK © Copyright: UNEP World Conservation Monitoring Centre/CITES Secretariat The contents of this report do not necessarily reflect the views or policies of UNEP or contributory organisations.
    [Show full text]
  • (Anthozoa) from the Lower Oligocene (Rupelian) of the Eastern Alps, Austria
    TO L O N O G E I L C A A P I ' T A A T L E I I A Bollettino della Società Paleontologica Italiana, 59 (3), 2020, 319-336. Modena C N O A S S. P. I. Scleractinian corals (Anthozoa) from the lower Oligocene (Rupelian) of the Eastern Alps, Austria Rosemarie Christine Baron-Szabo* & Diethard Sanders R.C. Baron-Szabo, Department of Invertebrate Zoology, Smithsonian Institution, NMNH, W-205, MRC 163, P.O. Box 37012, Washington DC, 20013- 7012 USA; Forschungsinstitut Senckenberg, Senckenberganlage 25, D-60325 Frankfurt/Main, Germany; [email protected]; Rosemarie.Baron- [email protected] *corresponding author D. Sanders, Institut für Geologie, Universität of Innsbruck, Innrain 52, A-6020 Innsbruck, Austria; [email protected] KEY WORDS - Scleractinia, taxonomy, paleoecology, paleobiogeography. ABSTRACT - In the Werlberg Member (Rupelian pro parte) of the Paisslberg Formation (Eastern Alps), an assemblage of colonial corals of eleven species pertaining to eleven genera and eleven families was identified:Stylocoenia carryensis, Acropora lavandulina, ?Colpophyllia sp., Dendrogyra intermedia, Caulastraea pseudoflabellum, Hydnophyllia costata, Pindosmilia cf. brunni, Actinacis rollei, Pavona profunda, Agathiphyllia gregaria, and Faksephyllia faxoensis. This is the first Oligocene coral assemblage reported from the Paisslberg Formation (Werlberg Member) of the Eastern Alps, consisting exclusively of colonial forms. The assemblage represents the northernmost fauna of reefal corals reported to date for Rupelian time. The Werlberg Member accumulated during marine transgression onto a truncated succession of older carbonate rocks. The corals grew as isolated colonies and in carpets in a protected shoreface setting punctuated by high-energy events. Coral growth forms comprise massive to sublamellar forms, and branched (dendroid, ramose) forms.
    [Show full text]
  • Final Corals Supplemental Information Report
    Supplemental Information Report on Status Review Report And Draft Management Report For 82 Coral Candidate Species November 2012 Southeast and Pacific Islands Regional Offices National Marine Fisheries Service National Oceanic and Atmospheric Administration Department of Commerce Table of Contents INTRODUCTION ............................................................................................................................................. 1 Background ............................................................................................................................................... 1 Methods .................................................................................................................................................... 1 Purpose ..................................................................................................................................................... 2 MISCELLANEOUS COMMENTS RECEIVED ...................................................................................................... 3 SRR EXECUTIVE SUMMARY ........................................................................................................................... 4 1. Introduction ........................................................................................................................................... 4 2. General Background on Corals and Coral Reefs .................................................................................... 4 2.1 Taxonomy & Distribution .............................................................................................................
    [Show full text]