Coral Diseases: What Is Really Known? Laurie L
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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. -
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. -
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 . -
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. -
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. -
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). -
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. -
High Density of Diploria Strigosa Increases
HIGH DENSITY OF DIPLORIA STRIGOSA INCREASES PREVALENCE OF BLACK BAND DISEASE IN CORAL REEFS OF NORTHERN BERMUDA Sarah Carpenter Department of Biology, Clark University, Worcester, MA 01610 ([email protected]) Abstract Black Band Disease (BBD) is one of the most widespread and destructive coral infectious diseases. The disease moves down the infected coral leaving complete coral tissue degradation in its wake. This coral disease is caused by a group of coexisting bacteria; however, the main causative agent is Phormidium corallyticum. The objective of this study was to determine how BBD prominence is affected by the density of D. strigosa, a common reef building coral found along Bermuda coasts. Quadrats were randomly placed on the reefs at Whalebone Bay and Tobacco Bay and then density and percent infection were recorded and calculated. The results from the observations showed a significant, positive correlation between coral density and percent infection by BBD. This provides evidence that BBD is a water borne infection and that transmission can occur at distances up to 1m. Information about BBD is still scant, but in order to prevent future damage, details pertaining to transmission methods and patterns will be necessary. Key Words: Black Band Disease, Diploria strigosa, density Introduction Coral pathogens are a relatively new area of study, with the first reports and descriptions made in the 1970’s. Today, more than thirty coral diseases have been reported, each threatening the resilience of coral communities (Green and Bruckner 2000). The earliest identified infection was characterized by a dark band, which separated the healthy coral from the dead coral. -
Atoll Research Bulletin No. 481 First Protozoan Coral
ATOLL RESEARCH BULLETIN NO. 481 FIRST PROTOZOAN CORAL-KILLER IDENTIFIED IN THE INDO-PACIFIC BY ARNFRIED A. ANTONIUS AND DIANA LIPSCOMB ISSUED BY NATIONAL MUSEUM OF NATURAL HISTORY SMITHSONIAN INSTITUTION WASHINGTON, D.C., U.S.A. JUNE 2000 Great Barrier Reef 0 M Mauritius 6 0 120 Figure 1. Chart of Indo-Pacific region showing the three SEB observation sites where corals infected with Halofollict~lina corallcuia were investigated: the coral reefs along the coast of Sinai, Red Sea; around the island of Mauritius, Indian Ocean; and in the area of Lizard Island, Great Barrier Reef, Pacific. Motupore Island on the SE coast of Papua New Guinea is not marked on the chart. Sites that were investigated with negative result (no SEB found) are: B: Bali; W: Wakatobi Islands; G: Guam; and M: Moorea. FIRST PROTOZOAN CORAL-KILLER IDENTIFIED IN THE INDO-PACIFIC ARNFRIED ANTONIUS' and DIANA LIPS COMB^ ABSTRACT A unique coral disease has appeared on several Indo-Pacific reefs. Unlike most known coral diseases, this one is caused by an eukaryote, specifically Halofolliculina covallasia, a heterotrich, folliculinid ciliate. This protist is sessile inside of a secreted black test or lorica. It kills the coral and damages the skeleton when it settles on the living coral tissue and secretes the lorica. Thus, the disease was termed Skeleton Eroding Band (SEB). The ciliate population forms an advancing black line on the coral leaving behind it the denuded white coral skeleton, often sprinkled with a multitude of empty black loricae. This disease was first noted in 1988 and since has been observed infecting both branching and massive corals at several locations in the Indo-Pacific. -
Assessing the Effectiveness of Two Intervention Methods for Stony Coral
www.nature.com/scientificreports OPEN Assessing the efectiveness of two intervention methods for stony coral tissue loss disease on Montastraea cavernosa Erin N. Shilling 1*, Ian R. Combs 1,2 & Joshua D. Voss 1* Stony coral tissue loss disease (SCTLD) was frst observed in Florida in 2014 and has since spread to multiple coral reefs across the wider Caribbean. The northern section of Florida’s Coral Reef has been heavily impacted by this outbreak, with some reefs experiencing as much as a 60% loss of living coral tissue area. We experimentally assessed the efectiveness of two intervention treatments on SCTLD-afected Montastraea cavernosa colonies in situ. Colonies were tagged and divided into three treatment groups: (1) chlorinated epoxy, (2) amoxicillin combined with CoreRx/Ocean Alchemists Base 2B, and (3) untreated controls. The experimental colonies were monitored periodically over 11 months to assess treatment efectiveness by tracking lesion development and overall disease status. The Base 2B plus amoxicillin treatment had a 95% success rate at healing individual disease lesions but did not necessarily prevent treated colonies from developing new lesions over time. Chlorinated epoxy treatments were not signifcantly diferent from untreated control colonies, suggesting that chlorinated epoxy treatments are an inefective intervention technique for SCTLD. The results of this experiment expand management options during coral disease outbreaks and contribute to overall knowledge regarding coral health and disease. Coral reefs face many threats, including, but not limited to, warming ocean temperatures, overfshing, increased nutrient and plastic pollution, hurricanes, ocean acidifcation, and disease outbreaks 1–6. Coral diseases are com- plex, involving both pathogenic agents and coral immune responses. -
Disease in Tropical Coral Reef Ecosystems
DISEASE IN TROPICAL CORAL REEF ECOSYSTEMS Key Messages on Coral Disease Coral Disease An introductory guide for policy advisors and decision makers Disease in Tropical Coral Reef Ecosystems ICRI Key Messages on Coral Disease There is a clear consensus from the growing scientific literature that large-scale coral disease outbreaks represent a significant threat to the productivity and diversity of coral reef ecosystems. Global climate change has the potential to greatly increase the prevalence of coral disease worldwide, leading to a rise in associated coral mortality. This introductory guide aims to inform policy and decision-makers worldwide about the alarming emergence and progression of disease throughout coral reef ecosystems, the possible interactions of disease with other environmental influences causing stress to reef ecosystems, as well as appropriate management responses promoted by the international community. CITATION ICRI/UNEP-WCMC (2010). Disease in Tropical Coral Reef Ecosystems: ICRI Key Messages on Coral Disease. 11pp. ONLINE GUIDE AND FURTHER INFORMATION A copy of this guide, as well as further information on coral disease, can be found on the website of the Global Coral Disease Database (GCDD): www.coraldisease.org CONTRIBUTORS Produced by UNEP-WCMC, Cambridge, United Kingdom Prepared by Nicola Barnard and Christel Scheske, with generous support from the members of the ICRI Ad Hoc Committee on Coral Disease: Jan-Willem von Bochove, Angelique Brathwaite, Dave Gulko, Anthony Hooten, and Michael Schleyer. Additional inputs were provided by members of the GEF Coral Reef Targeted Research Disease Working Group: Laurie Raymundo and Ernesto Weil. Design and layout by Dan Shurey Quality Assurance This guide has been produced with financial support from the US Department of State.