Intensification of Climate Change Impacts on Ecosystem Components
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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. -
SA Wioresearchcompendium.Pdf
Compiling authors Dr Angus Paterson Prof. Juliet Hermes Dr Tommy Bornman Tracy Klarenbeek Dr Gilbert Siko Rose Palmer Report design: Rose Palmer Contributing authors Prof. Janine Adams Ms Maryke Musson Prof. Isabelle Ansorge Mr Mduduzi Mzimela Dr Björn Backeberg Mr Ashley Naidoo Prof. Paulette Bloomer Dr Larry Oellermann Dr Thomas Bornman Ryan Palmer Dr Hayley Cawthra Dr Angus Paterson Geremy Cliff Dr Brilliant Petja Prof. Rosemary Dorrington Nicole du Plessis Dr Thembinkosi Steven Dlaza Dr Anthony Ribbink Prof. Ken Findlay Prof. Chris Reason Prof. William Froneman Prof. Michael Roberts Dr Enrico Gennari Prof. Mathieu Rouault Dr Issufo Halo Prof. Ursula Scharler Dr. Jean Harris Dr Gilbert Siko Prof. Juliet Hermes Dr Kerry Sink Dr Jenny Huggett Dr Gavin Snow Tracy Klarenbeek Johan Stander Prof. Mandy Lombard Dr Neville Sweijd Neil Malan Prof. Peter Teske Benita Maritz Dr Niall Vine Meaghen McCord Prof. Sophie von der Heydem Tammy Morris SA RESEARCH IN THE WIO ContEnts INDEX of rEsEarCh topiCs ‑ 2 introDuCtion ‑ 3 thE WEstErn inDian oCEan ‑ 4 rEsEarCh ActivitiEs ‑ 6 govErnmEnt DEpartmEnts ‑ 7 Department of Science & Technology (DST) Department of Environmental Affairs (DEA) Department of Agriculture, Forestry & Fisheries (DAFF) sCiEnCE CounCils & rEsEarCh institutions ‑ 13 National Research Foundation (NRF) Council for Geoscience (CGS) Council for Scientific & Industrial Research (CSIR) Institute for Maritime Technology (IMT) KwaZulu-Natal Sharks Board (KZNSB) South African Environmental Observation Network (SAEON) Egagasini node South African -
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. -
Molasses Reef Sanctuary Preservation Area
Molasses Reef Sanctuary Preservation Area SANCTUARY AREAS Wellwood Restoration Research Sand Only Ecological Reserve Existing Management Area Sanctuary Preservation Area Sand (SPAs) Wildlife Lighted Management Area Marker 10 Shallow Sea Grass Rubble Shallow Coral Sand 25' 35' Very Shallow Island 5' 18” Mooring Buoy 3 - 5ft. 40'-50' Spar Buoy 30” Yellow Sanctuary Buoy FKNMS Shipwreck Trail A Boating and Angling Guide to the Molasses Reef Sanctuary Preservation Area With certain exceptions, the following activities are prohibited Sanctuary-Wide: • Moving, removing, taking, injuring, touching, breaking, • Operating a vessel at more than 4 knots/no wake cutting or possessing coral or live rock. within 100 yards of a “divers down” flag. • Discharging or depositing treated or untreated sewage • Diving or snorkeling without a dive flag. from marine sanitation devices, trash and other • Operating a vessel in such a manner which endangers materials life, limb, marine resources, or property. • Dredging, drilling, prop dredging or otherwise altering • Releasing exotic species. the seabed, or placing or abandoning any structure on • Damaging or removing markers, mooring buoys, the seabed. scientific equipment, boundary buoys, and trap buoys. • Operating a vessel in such a manner as to strike or • Moving, removing, injuring, or possessing historical otherwise injure coral, seagrass, or other immobile resources. organisms attached to the seabed, or cause prop • Taking or possessing protected wildlife. scarring. • Using or possessing explosives or electrical charges. • Having a vessel anchored on living coral in water less • Harvesting, possessing or landing any marine life than 40 feet deep when the bottom can be seen. species except as allowed by the Florida Fish and Anchoring on hardbottom is allowed. -
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. -
FAU Institutional Repository
FAU Institutional Repository http://purl.fcla.edu/fau/fauir This paper was submitted by the faculty of FAU’s Harbor Branch Oceanographic Institute Notice: ©2002 Elsevier Science Ltd. This is the author’s version of a work accepted for publication by Elsevier. Changes resulting from the publishing process, including peer review, editing, corrections, structural formatting and other quality control mechanisms, may not be reflected in this document. Changes may have been made to this work since it was submitted for publication. The definitive version has been published at http://www.elsevier.com/locate/csr and may be cited as Lee, Thomas N., Ned Smith (2002) Volume transport variability through the Florida Keys tidal Channels, Continental Shelf Research 22(9):1361–1377 doi:10.1016/S0278‐4343(02)00003‐1 Continental Shelf Research 22 (2002) 1361–1377 Volume transport variability through the Florida Keys tidal channels Thomas N. Leea,*, Ned Smithb a Rosenstiel School of Marine and Atmospheric Science, University of Miami, 4600 Rickenbacker Causeway, Miami, FL 33149, USA b Harbor Branch Oceanographic Institution, 5600 US Highway 1, North, Ft. Pierce, FL 34946, USA Received 28 February 2001; received in revised form 13 July 2001; accepted 18 September 2001 Abstract Shipboard measurements of volume transports through the passages of the middle Florida Keys are used together with time series of moored transports, cross-Key sea level slopes and local wind records to investigate the mechanisms controllingtransport variability. Predicted tidal transport amplitudes rangedfrom 76000 m3/s in LongKey Channel to 71500 m3/s in Channel 2. Subtidal transport variations are primarily due to local wind driven cross-Key sea level slopes. -
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. -
Adm Issue 10 Finnished
4x4x4x4 Four times a year Four times the copy Four times the quality Four times the dive experience Advanced Diver Magazine might just be a quarterly magazine, printing four issues a year. Still, compared to all other U.S. monthly dive maga- zines, Advanced Diver provides four times the copy, four times the quality and four times the dive experience. The staff and contribu- tors at ADM are all about diving, diving more than should be legally allowed. We are constantly out in the field "doing it," exploring, photographing and gathering the latest information about what we love to do. In this issue, you might notice that ADM is once again expanding by 16 pages to bring you, our readers, even more information and contin- ued high-quality photography. Our goal is to be the best dive magazine in the history of diving! I think we are on the right track. Tell us what you think and read about what others have to say in the new "letters to bubba" section found on page 17. Curt Bowen Publisher Issue 10 • • Pg 3 Advanced Diver Magazine, Inc. © 2001, All Rights Reserved Editor & Publisher Curt Bowen General Manager Linda Bowen Staff Writers / Photographers Jeff Barris • Jon Bojar Brett Hemphill • Tom Isgar Leroy McNeal • Bill Mercadante John Rawlings • Jim Rozzi Deco-Modeling Dr. Bruce Wienke Text Editor Heidi Spencer Assistants Rusty Farst • Tim O’Leary • David Rhea Jason Richards • Joe Rojas • Wes Skiles Contributors (alphabetical listing) Mike Ball•Philip Beckner•Vern Benke Dan Block•Bart Bjorkman•Jack & Karen Bowen Steve Cantu•Rich & Doris Chupak•Bob Halstead Jitka Hyniova•Steve Keene•Dan Malone Tim Morgan•Jeff Parnell•Duncan Price Jakub Rehacek•Adam Rose•Carl Saieva Susan Sharples•Charley Tulip•David Walker Guy Wittig•Mark Zurl Advanced Diver Magazine is published quarterly in Bradenton, Florida. -
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 ............................................................................................................. -
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).