Atoll Research Bulletin No. 481 First Protozoan Coral
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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. -
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. -
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. -
Zooxanthellae Regulation in Yellow Blotch/Band and Other Coral Diseases Contrasted with Temperature Related Bleaching: in Situ Destruction Vs Expulsion
Symbiosis, 37 (2004) 63–85 63 Balaban, Philadelphia/Rehovot Zooxanthellae Regulation in Yellow Blotch/Band and Other Coral Diseases Contrasted with Temperature Related Bleaching: In Situ Destruction vs Expulsion JAMES M. CERVINO1*, RAYMOND HAYES2, THOMAS J. GOREAU3, and GARRIET W. SMITH4 1University of South Carolina, Marine Sciences Department, Columbia, SC 29208, Email. [email protected]; 2College of Medicine, Howard University, Washington, DC; 3Global Coral Reef Alliance, Cambridge, MA; 4University of South Carolina, Aiken, SC, USA Received November 3, 2003; Accepted March 1, 2004 Abstract Impairment and breakdown in the symbiotic relationship between the coral host and its zooxanthellae has been documented in the major Caribbean reef building coral, Montastraea spp., when it is infected with yellow band/blotch disease (YBD) pathogens and/or exposed to unusually high seawater temperatures. Progressive degradation of zooxanthellar cellular integrity occurs, leading to the deterioration of coral tissue. Cytoplasmic organelles were displaced and chloroplasts are reduced and marginalized which is accompanied by internal swelling, vacuolization, fragmentation, and loss of cell wall structural integrity. Changes in algae that occur in YBD-infected corals differ from changes seen in corals undergoing solely temperature-induced coral bleaching, however. In many disease-infected corals, there is no evidence of zooxanthella in the mucus, unlike in thermal bleaching, where zooxanthellae was evident in the coral surface layer. Isolated zooxanthellae Presented at the 4th International Symbiosis Congress, August 17–23, 2003, Halifax, Canada *The author to whom correspondence should be sent. 0334-5114/2004/$05.50 ©2004 Balaban 64 J.M. CERVINO ET AL. inoculated with YBD pathogens showed a 96% decrease in chlorophyll a pigments compared to controls, and a 90% decrease in mitotic cell division over 96 hours of YBD bacterial inoculation (<p=0.0016). -
The Epizootiology of Coral Diseases in South Florida
The Epizootiology of Coral Diseases in South Florida Research and Development EPA/600/R-05/146 May 2006 The Epizootiology of Coral Diseases in South Florida by Deborah L. Santavy1, Jed Campbell1, Robert L. Quarles1, James M. Patrick1, Linda M. Harwell1, Mel Parsons2 , Lauri MacLaughlin3 , John Halas3, Erich Mueller4, 5, Esther C. Peters4, 6, Jane Hawkridge4, 7 1United States Environmental Protection Agency National Health and Environmental Effects Research Laboratory Gulf Ecology Division 1 Sabine Island Drive Gulf Breeze, FL 32561 2United States Environmental Protection Agency, Region 4 Science and Ecosystems Support Division 980 College Station Road Athens, GA 30605 3NOAA, Florida Keys National Marine Sanctuary Upper Region, MM 95 Overseas Highway Key Largo, FL 33037 4Mote Marine Laboratory Center for Tropical Research 24244 Overseas Highway (US 1) Summerland Key, FL 33042 5Perry Institute for Marine Science 100 N. U.S. Highway 1, Suite 202 Jupiter, FL 33477 6Tetra Tech, Inc. 10306 Eaton Place, Suite 340 Fairfax, VA 22030 7Joint Nature Conservation Committee, Monkstone House, City Road Peterborough, United Kingdom PE1 1JY Notice The U.S. Environmental Protection Agency (U.S. EPA), Office of Research and Development (ORD), National Health and Environmental Effect Research Laboratory (NHEERL), Gulf Ecology Division (GED), the U.S. Department of Commerce (U.S. DOC) National Oceanographic and Atmospheric Association (NOAA) National Marine Sanctuary Program Florida Keys National Marine Sanctuary (FKNMS), and the U.S. Department of Interior (DOI) National Park Service (NPS) Dry Tortugas National Park (DTNP) jointly conducted this program. The report has undergone U.S. EPA’s peer and administrative reviews and has received approval for publication as a U.S. -
Changes in the Bacterial Community Associated with Black Band Disease in a Red Sea Coral, Favia Sp., in Relation to Disease Phases
Vol. 116: 47–58, 2015 DISEASES OF AQUATIC ORGANISMS Published September 17 doi: 10.3354/dao02911 Dis Aquat Org Changes in the bacterial community associated with black band disease in a Red Sea coral, Favia sp., in relation to disease phases Luba Arotsker1, Esti Kramarsky-Winter1, Eitan Ben-Dov2,3, Nachshon Siboni1, Ariel Kushmaro1,2,4,* 1Avram and Stella Goldstein-Goren Department of Biotechnology Engineering, Ben-Gurion University of the Negev, PO Box 653, Be’er-Sheva 84105, Israel 2National Institute for Biotechnology in the Negev, Ben-Gurion University of the Negev, Be’er-Sheva 84105, Israel 3Department of Life Sciences, Achva Academic College, MP Shikmim 79800, Israel 4School of Materials Science and Engineering, Nanyang Technological University, Singapore ABSTRACT: Changes of the black band disease (BBD)-associated microbial consortium on the surface of a Favia sp. coral colony were assessed in relation to the different disease phases. A number of highly active bacterial groups changed in numbers as the BBD disease signs changed. These included Gamma- and Epsilonproteobacteria, Bacteroidetes and Firmicutes groups. One cyanobacterium strain, BGP10_4ST (FJ210722), was constantly present in the disease interface and adjacent tissues of the affected corals, regardless of disease phase. The dynamics of the oper- ational taxonomic units (OTUs) of this BBD-specific strain provide a marker regarding the disease phase. The disease’s active phase is characterized by a wide dark band progressing along the tis- sue-skeleton interface and by numerous bacterial OTUs. Cyanobacterial OTUs decreased in num- bers as the disease signs waned, perhaps opening a niche for additional microorganisms. Even when black band signs disappeared there was a consistent though low abundance of the BBD- specific cyanobacteria (BGP10_4ST), and the microbial community of the disease-skeleton inter- face remained surprisingly similar to the original band community. -
Coral Diseases: What Is Really Known? Laurie L
REVIEWS Coral diseases: what is really known? Laurie L. Richardson uring the International Reports of new and emerging coral Research in the late 1970s and Year of the Reef (1997) and diseases have proliferated in recent years. early 1980s followed the same de- continuing into the Inter- Such coral diseases are often cited as scriptive approach. New results, Dnational Year of the Ocean contributing to coral reef decline. Many of however, included the first quan- (1998), much attention and activity these diseases, however, have been titative study of disease preva- have been focused on evaluating described solely on the basis of field lence, and it was determined that the current status of coral reefs1–6. characteristics, and in some instances white band disease was relent- The uniform conclusion of these there is disagreement as to whether an lessly eliminating the important multiple assessments is that coral observed coral condition is actually a reef-forming acroporid corals of reef ecosystems are degrading, disease. A disease pathogen has been shallow Caribbean waters13. This and that this is most likely a com- identified for only three coral diseases, was the first case in which the po- bined result of global warming, and for only two of these has the pathogen tential severity of coral diseases ozone depletion, overfishing, eutro- been shown (in the laboratory) to be the was verified. phication, poor land-use practices disease agent. In one case, the same Further efforts were made and other manifestations of human disease name has been used for several to identify pathogens associated activities. All of these reports have widely varying coral syndromes, with specific diseases, and ad- emphasized that an increase in whereas in another multiple disease ditional causative agents were coral disease is contributing to reef names have been applied to symptoms proposed14–16. -
Coral Reefs of Japan -3 Coral Diseases 2 Hideyuki Yamashiro 1 Introduction 2 Malignant Coral Diseases
0201_03(英) 04.9.3 3:04 PM ページ 56 02 Coral Reefs of Japan -3 Coral diseases 2 Hideyuki Yamashiro 1 Introduction 2 Malignant coral diseases Many of the coral communities around the world may dis- Coral disease transmission processes are poorly under- appear within a few decades as a result of influences such stood. They can be caused by infection with pathogenic as global warming (Hughes et al. 2003). In Japan, elevat- bacteria, viruses, fungi, or protozoans, as well as by ed seawater temperatures during the 1997/1998 El Niño- helminthes and arthropods. Coral diseases can also be Southern Oscillation (ENSO) event caused the most triggered by abiotic factors such as temperature, soil par- severe coral bleaching and mortality ever observed. This ticles, ultraviolet rays, heavy metals, and agricultural phenomenon has continued to occur intermittently dur- chemicals. However, in reality, both biotic and abiotic fac- ing subsequent years. In addition to bleaching, corals tors are likely to be intricately intertwined in many cases, have been threatened with predation by the crown-of- and specifying a single causative factor is not easy. thorns starfish (Acanthaster planci), smothering by ter- rigenous sediments, and poisoning by agricultural chemi- Many coral diseases have been recognized, but compara- cals in runoff. Since the 1970s, there have been reports of tively little is known about the causative agents bacterial diseases among hard corals (scleractinians), and (Richardson 1998). Research is further complicated by the number of such reports increased throughout the the assignment of more than one descriptive name to a 1990s. In some locations, the damage caused by coral dis- single disease.