Folliculinid Ciliates: a New Threat to Caribbean Corals?
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Coral Bleaching Early Warning Network Current Conditions Report #20090910
Mote Marine Laboratory / Florida Keys National Marine Sanctuary Coral Bleaching Early Warning Network Current Conditions Report #20090910 Updated September 10, 2009 Summary: Based on climate predictions, current conditions, and field observations, the threat for mass coral bleaching within the FKNMS remains MODERATE. Figure 2. NOAA’s Coral Bleaching HotSpot Map for September 10, 2009. Figure 1. NOAA’s Coral Bleaching Thermal Stress Outlook for Sept. – Dec., 2009. www.osdpd.noaa.gov/PSB/EPS/SST/climohot.html http://coralreefwatch.noaa.gov/satellite/index.html Weather and Sea Temperatures According to the latest NOAA Coral Reef Watch Coral Bleaching Thermal Stress Outlook (updated Sept. 10, 2009) there continues to be significant potential for coral bleaching throughout the Caribbean in 2009, especially in the Lesser Antilles; however, it now appears that the likelihood of significant bleaching in the Florida Keys has been reduced compared to the rest of the greater Caribbean (Fig. 1). Current remote sensing analysis by NOAA’s Coral Reef Watch program Figure 3. NOAA’s Degree Heating Weeks Map for September 10, 2009. indicates that the Florida Keys region continues to experience elevated levels www.osdpd.noaa.gov/PSB/EPS/SST/dhw_retro.html of thermal stress and moderate potential for coral bleaching. NOAA’s recent Water Temperatures (August 27 - September 10, 2009) Coral Bleaching HotSpot Map (Fig. 2), which provides current sea surface 35 temperature (SST) compared to the historically expected SST’s for the region, shows that temperature anomalies for the Florida Keys National Marine 30 Sanctuary and surrounding waters continue to remain above-average and have increased slightly since the end of August. -
The Coral Trait Database, a Curated Database of Trait Information for Coral Species from the Global Oceans
www.nature.com/scientificdata OPEN The Coral Trait Database, a curated SUBJECT CATEGORIES » Community ecology database of trait information for » Marine biology » Biodiversity coral species from the global oceans » Biogeography 1 2 3 2 4 Joshua S. Madin , Kristen D. Anderson , Magnus Heide Andreasen , Tom C.L. Bridge , , » Coral reefs 5 2 6 7 1 1 Stephen D. Cairns , Sean R. Connolly , , Emily S. Darling , Marcela Diaz , Daniel S. Falster , 8 8 2 6 9 3 Erik C. Franklin , Ruth D. Gates , Mia O. Hoogenboom , , Danwei Huang , Sally A. Keith , 1 2 2 4 10 Matthew A. Kosnik , Chao-Yang Kuo , Janice M. Lough , , Catherine E. Lovelock , 1 1 1 11 12 13 Osmar Luiz , Julieta Martinelli , Toni Mizerek , John M. Pandolfi , Xavier Pochon , , 2 8 2 14 Morgan S. Pratchett , Hollie M. Putnam , T. Edward Roberts , Michael Stat , 15 16 2 Carden C. Wallace , Elizabeth Widman & Andrew H. Baird Received: 06 October 2015 28 2016 Accepted: January Trait-based approaches advance ecological and evolutionary research because traits provide a strong link to Published: 29 March 2016 an organism’s function and fitness. Trait-based research might lead to a deeper understanding of the functions of, and services provided by, ecosystems, thereby improving management, which is vital in the current era of rapid environmental change. Coral reef scientists have long collected trait data for corals; however, these are difficult to access and often under-utilized in addressing large-scale questions. We present the Coral Trait Database initiative that aims to bring together physiological, morphological, ecological, phylogenetic and biogeographic trait information into a single repository. -
MARINE FAUNA and FLORA of BERMUDA a Systematic Guide to the Identification of Marine Organisms
MARINE FAUNA AND FLORA OF BERMUDA A Systematic Guide to the Identification of Marine Organisms Edited by WOLFGANG STERRER Bermuda Biological Station St. George's, Bermuda in cooperation with Christiane Schoepfer-Sterrer and 63 text contributors A Wiley-Interscience Publication JOHN WILEY & SONS New York Chichester Brisbane Toronto Singapore ANTHOZOA 159 sucker) on the exumbrella. Color vari many Actiniaria and Ceriantharia can able, mostly greenish gray-blue, the move if exposed to unfavorable condi greenish color due to zooxanthellae tions. Actiniaria can creep along on their embedded in the mesoglea. Polyp pedal discs at 8-10 cm/hr, pull themselves slender; strobilation of the monodisc by their tentacles, move by peristalsis type. Medusae are found, upside through loose sediment, float in currents, down and usually in large congrega and even swim by coordinated tentacular tions, on the muddy bottoms of in motion. shore bays and ponds. Both subclasses are represented in Ber W. STERRER muda. Because the orders are so diverse morphologically, they are often discussed separately. In some classifications the an Class Anthozoa (Corals, anemones) thozoan orders are grouped into 3 (not the 2 considered here) subclasses, splitting off CHARACTERISTICS: Exclusively polypoid, sol the Ceriantharia and Antipatharia into a itary or colonial eNIDARIA. Oral end ex separate subclass, the Ceriantipatharia. panded into oral disc which bears the mouth and Corallimorpharia are sometimes consid one or more rings of hollow tentacles. ered a suborder of Scleractinia. Approxi Stomodeum well developed, often with 1 or 2 mately 6,500 species of Anthozoa are siphonoglyphs. Gastrovascular cavity compart known. Of 93 species reported from Ber mentalized by radially arranged mesenteries. -
Microbiomes of Gall-Inducing Copepod Crustaceans from the Corals Stylophora Pistillata (Scleractinia) and Gorgonia Ventalina
www.nature.com/scientificreports OPEN Microbiomes of gall-inducing copepod crustaceans from the corals Stylophora pistillata Received: 26 February 2018 Accepted: 18 July 2018 (Scleractinia) and Gorgonia Published: xx xx xxxx ventalina (Alcyonacea) Pavel V. Shelyakin1,2, Sofya K. Garushyants1,3, Mikhail A. Nikitin4, Sofya V. Mudrova5, Michael Berumen 5, Arjen G. C. L. Speksnijder6, Bert W. Hoeksema6, Diego Fontaneto7, Mikhail S. Gelfand1,3,4,8 & Viatcheslav N. Ivanenko 6,9 Corals harbor complex and diverse microbial communities that strongly impact host ftness and resistance to diseases, but these microbes themselves can be infuenced by stresses, like those caused by the presence of macroscopic symbionts. In addition to directly infuencing the host, symbionts may transmit pathogenic microbial communities. We analyzed two coral gall-forming copepod systems by using 16S rRNA gene metagenomic sequencing: (1) the sea fan Gorgonia ventalina with copepods of the genus Sphaerippe from the Caribbean and (2) the scleractinian coral Stylophora pistillata with copepods of the genus Spaniomolgus from the Saudi Arabian part of the Red Sea. We show that bacterial communities in these two systems were substantially diferent with Actinobacteria, Alphaproteobacteria, and Betaproteobacteria more prevalent in samples from Gorgonia ventalina, and Gammaproteobacteria in Stylophora pistillata. In Stylophora pistillata, normal coral microbiomes were enriched with the common coral symbiont Endozoicomonas and some unclassifed bacteria, while copepod and gall-tissue microbiomes were highly enriched with the family ME2 (Oceanospirillales) or Rhodobacteraceae. In Gorgonia ventalina, no bacterial group had signifcantly diferent prevalence in the normal coral tissues, copepods, and injured tissues. The total microbiome composition of polyps injured by copepods was diferent. -
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. -
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. -
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 . -
Analysis of Polycyclic Aromatic Hydrocarbons (Pah) in Soil Of
Rev. Int. Contam. Ambie. 36 (3) 677-687, 2020 https://doi.org/10.20937/RICA.53573 ANALYSIS OF POLYCYCLIC AROMATIC HYDROCARBONS (PAH) IN SOIL OF MANGROVE FOREST OF THE VENEZUELAN CARIBBEAN COAST Análisis de hidrocarburos aromáticos policíclicos (HAP) en suelos de bosques de manglares de las costas del Caribe venezolano Liliana LÓPEZ1*, María Beatriz BARRETO2, Maria do Carmo RUARO PERALBA3, Eduardo BARRETO-PITTOL1,2, Salvador LO MÓNACO1 and Rut DÍAZ1,4 1 Laboratorio de Geoquímica Orgánica, Instituto de Ciencias de la Tierra (ICT), Facultad de Ciencias, Univer- sidad Central de Venezuela, Caracas, Venezuela. Caracas 1053 2 Laboratorio de Ecología de la Vegetación. Instituto de Zoología y Ecología Tropical (IZET) Facultad de Ciencias Universidad Central de Venezuela, Caracas, Venezuela. Caracas 1053 3 Instituto de Química, Universidade Federal do Rio Grande do Sul, Brazil. 474 CEP 96201-900 4 Departamento de Geoquímica, Instituto de Química, Universidade Federal Fluminense, Niterói, Brazil (present address) 16 Niterói, Río de Janeiro 1151 * Author for correspondence: [email protected] (Received: March 2019; accepted: October 2019) Key words: Morrocoy National Park, Cuare Inlet, mangroves, soluble organic matter, GC-MS, PAHs diagnostic ratios ABSTRACT In order to identify the levels of contamination of mangrove soils by polycyclic aro- matic hydrocarbons (PAH), their concentration was determined by gas chromatogra- phy coupled to mass spectrometry in the fraction of aromatic hydrocarbons obtained from soluble organic matter (SOM). Soils are located in Cuare Inlet and Morrocoy National Park from Venezuela, and samples were collected in Punta La Matica (PLM) and Tucacas Bay (ETU) respectively. Naphthalene, acenaphthene, acenaphthalene, benzo(ghi)perylene, dibenzo(ah)anthracene and indene have concentrations lower than the detection threshold for the technique employed (≤ 20 ng/g). -
Surface Waters of the Atlantic and Was Ascribed to Continuous Inputs of HCH from Africa and South America (Loganathan & Kannan, 1994)
See discussions, stats, and author profiles for this publication at: https://www.researchgate.net/publication/252353401 POPs IN LATIN AMERICA Article CITATIONS READS 0 22 2 authors, including: Michelle anne Allsopp University of Exeter 22 PUBLICATIONS 240 CITATIONS SEE PROFILE All content following this page was uploaded by Michelle anne Allsopp on 19 August 2014. The user has requested enhancement of the downloaded file. 1 POPs IN LATIN AMERICA A review of persistent organic pollutant levels in Latin America Authors: Michelle Allsopp* and Bea Erry *Greenpeace Research Laboratories, Department of Biological Sciences, University of Exeter, Prince of Wales Road Exeter EX4 4PS UK www.greenpeace.org October 2000 Special thanks are due to Marcelo Furtado and Wytze van der Naald of Greenpeace International, David Santillo of Greenpeace Research Laboratories, UK, and Karen Suassuna and Cristina Bonfiglioli of Greenpeace Brazil for reviewing the draft text of the report. 2 TABLE OF CONTENTS EXECUTIVE SUMMARY 1 INTRODUCTION.................................................................................................14 1.1 The Chemicals of Concern..................................................................................15 2 GLOBAL POLLUTION AND TRANSPORT OF POPS .................................18 2.1 Fate of POPs in Tropical Ecosystems.................................................................19 2.2 Time Trends of POPs Levels in the Global Environment ..................................19 3 POPS IN LATIN AMERICA...............................................................................22 -
White-Band Disease in <I>Acropora Palmata</I>
NOTES 639 BULLETIN OF MARINE SCIENCE. 32(2): 639-643. 1982 WHITE-BAND DISEASE IN ACROPORA PALMATA: IMPLICATIONS FOR THE STRUCTURE AND GROWTH OF SHALLOW REEFS W. B. Gladfelter In the last two decades a wide variety of organisms has been implicated in the destruction of reef-building corals (Glynn, 1973; Endean, 1976; Antonius, 1977). These fall generally into three categories: predators (Endean, 1973; Bak and van Eys, 1975; Reese, 1977), competitors for substrate (Glynn, 1973; Lang, 1973; Gladfelter et al., 1978) and disease-causing organisms (Garrett and DuckIow, 1975; Mitchell and Chet, 1975). In most instances the known impact of such organisms is restricted to portions of, or at most, single coral colonies. The impact of such organisms on whole reefs or systems has been documented only for the predatory starfish Acanthaster planci (Endean, 1973). In the present study we document the impact of another agent on a reef-wide scale. In much of the Caribbean Sea shallow windward reefs are dominated at depths of 1 to 5 m or more by the large branched coral Acropora palmata (Adey and Burke, 1976; Adey, 1978). In some such reefs >99% of living coral surface be- longs to this species (pers. obs.). In addition to quantitative dominance on such reefs this coral has one of the greatest rates of deposition of CaC03 per unit tissue surface (Gladfelter et al., 1978; Gladfelter and Gladfelter, unpublished) as well as high linear growth rates (5-10 cm/yr, Gladfelter et al., 1978) and consequently healthy A. palmata reefs exhibit some of the greatest measured reef growth rates (Adey and Burke, 1976 and unpublished calculations by Gladfelter and Gladfelter 2 of 10.3 kg CaC03/m /yr). -
SEDIMENTARY FRAMEWORK of Lmainland FRINGING REEF DEVELOPMENT, CAPE TRIBULATION AREA
GREAT BARRIER REEF MARINE PARK AUTHORITY TECHNICAL MEMORANDUM GBRMPA-TM-14 SEDIMENTARY FRAMEWORK OF lMAINLAND FRINGING REEF DEVELOPMENT, CAPE TRIBULATION AREA D.P. JOHNSON and RM.CARTER Department of Geology James Cook University of North Queensland Townsville, Q 4811, Australia DATE November, 1987 SUMMARY Mainland fringing reefs with a diverse coral fauna have developed in the Cape Tribulation area primarily upon coastal sedi- ment bodies such as beach shoals and creek mouth bars. Growth on steep rocky headlands is minor. The reefs have exten- sive sandy beaches to landward, and an irregular outer margin. Typically there is a raised platform of dead nef along the outer edge of the reef, and dead coral columns lie buried under the reef flat. Live coral growth is restricted to the outer reef slope. Seaward of the reefs is a narrow wedge of muddy, terrigenous sediment, which thins offshore. Beach, reef and inner shelf sediments all contain 50% terrigenous material, indicating the reefs have always grown under conditions of heavy terrigenous influx. The relatively shallow lower limit of coral growth (ca 6m below ADD) is typical of reef growth in turbid waters, where decreased light levels inhibit coral growth. Radiocarbon dating of material from surveyed sites confirms the age of the fossil coral columns as 33304110 ybp, indicating that they grew during the late postglacial sea-level high (ca 5500-6500 ybp). The former thriving reef-flat was killed by a post-5500 ybp sea-level fall of ca 1 m. Although this study has not assessed the community structure of the fringing reefs, nor whether changes are presently occur- ring, it is clear the corals present today on the fore-reef slope have always lived under heavy terrigenous influence, and that the fossil reef-flat can be explained as due to the mid-Holocene fall in sea-level. -
Coral Disease Fact Sheet
Florida Department of Environmental Protection Coral Reef Conservation Program SEAFAN BleachWatch Program Coral Disease Fact Sheet About Coral Disease Like all other animals, corals can be affected by disease. Coral disease was first recognized in the Florida Keys and the Caribbean in the 1970s, and since that time disease reports have emerged from reefs worldwide. Naturally, there are background levels of coral disease but reports of elevated disease levels – often called disease outbreaks – have been increasing in both frequency and severity over the past few decades. Today, coral disease is recognized as a major driver of coral mortality and reef degradation. Coral disease can result from infection by microscopic organisms (such as bacteria or fungi) or can be caused by abnormal growth (akin to tumors). The origins or causes of most coral diseases are not known and difficult to determine. There is increasing evidence that environmental stressors, including increasing water temperatures, elevated nutrient levels, sewage input, sedimentation, overfishing, plastic pollution, and even recreational diving, are increasing the prevalence and Disease affecting Great Star Coral (Montastraea severity of coral diseases. There is also strong evidence cavernosa). Photo credit: Nikole Ordway-Heath (Broward County; 2016). that a combination of coral bleaching and disease can be particularly devastating to coral populations. This is likely due to corals losing a major source of energy during a bleaching event, reducing their ability to fight off or control disease agents. Coral disease is often identifiable by a change in tissue color or skeletal structure as well as progressive tissue loss. Tissue loss may originate from a single discrete spot, multiple discrete areas, or appear scattered throughout the colony.