The Epizootiology of Coral Diseases in South Florida
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Reef Fish Biodiversity in the Florida Keys National Marine Sanctuary Megan E
University of South Florida Scholar Commons Graduate Theses and Dissertations Graduate School November 2017 Reef Fish Biodiversity in the Florida Keys National Marine Sanctuary Megan E. Hepner University of South Florida, [email protected] Follow this and additional works at: https://scholarcommons.usf.edu/etd Part of the Biology Commons, Ecology and Evolutionary Biology Commons, and the Other Oceanography and Atmospheric Sciences and Meteorology Commons Scholar Commons Citation Hepner, Megan E., "Reef Fish Biodiversity in the Florida Keys National Marine Sanctuary" (2017). Graduate Theses and Dissertations. https://scholarcommons.usf.edu/etd/7408 This Thesis is brought to you for free and open access by the Graduate School at Scholar Commons. It has been accepted for inclusion in Graduate Theses and Dissertations by an authorized administrator of Scholar Commons. For more information, please contact [email protected]. Reef Fish Biodiversity in the Florida Keys National Marine Sanctuary by Megan E. Hepner A thesis submitted in partial fulfillment of the requirements for the degree of Master of Science Marine Science with a concentration in Marine Resource Assessment College of Marine Science University of South Florida Major Professor: Frank Muller-Karger, Ph.D. Christopher Stallings, Ph.D. Steve Gittings, Ph.D. Date of Approval: October 31st, 2017 Keywords: Species richness, biodiversity, functional diversity, species traits Copyright © 2017, Megan E. Hepner ACKNOWLEDGMENTS I am indebted to my major advisor, Dr. Frank Muller-Karger, who provided opportunities for me to strengthen my skills as a researcher on research cruises, dive surveys, and in the laboratory, and as a communicator through oral and presentations at conferences, and for encouraging my participation as a full team member in various meetings of the Marine Biodiversity Observation Network (MBON) and other science meetings. -
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. -
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. -
Appendix C - Monroe County
2016 Supplemental Summary Statewide Regional Evacuation Study APPENDIX C - MONROE COUNTY This document contains summaries (updated in 2016) of the following chapters of the 2010 Volume 1-11 Technical Data Report: Chapter 1: Regional Demographics Chapter 2: Regional Hazards Analysis Chapter 4: Regional Vulnerability and Population Analysis Funding provided by the Florida Work completed by the Division of Emergency Management South Florida Regional Council STATEWIDE REGIONAL EVACUATION STUDY – SOUTH FLORIDA APPENDIX C – MONROE COUNTY This page intentionally left blank. STATEWIDE REGIONAL EVACUATION STUDY – SOUTH FLORIDA APPENDIX C – MONROE COUNTY TABLE OF CONTENTS APPENDIX C – MONROE COUNTY Page A. Introduction ................................................................................................... 1 B. Small Area Data ............................................................................................. 1 C. Demographic Trends ...................................................................................... 4 D. Census Maps .................................................................................................. 9 E. Hazard Maps .................................................................................................15 F. Critical Facilities Vulnerability Analysis .............................................................23 List of Tables Table 1 Small Area Data ............................................................................................. 1 Table 2 Health Care Facilities Vulnerability -
Download the Meeting Program, Including Abstracts
PROGRAM: Overview of oral and poster presentations FINAL PROGRAM 37th AMLC SCIENTIFIC MEETING CURACAO (MAY 18-22, 2015) MAY 17 17:00 Registration (optional) and "ice breaker" on the beach at Carmabi END of DAY 0 (MAY 17) MAY 18 8:00 Registration at the Hilton Hotel 9:00 Official opening 37th AMLC Meeting The Eastern Caribbean: A laboratory for studying the resilience and 9:30 PLENARY: DR. B. STENECK management of coral reefs 10:30 Coffee break Time Authors Title Shifting baselines: three decades of nitrogen enrichment on two 11:00 * Lapointe B, Herren L, Tarnowski, M, Dustan P Caribbean coral reefs Finding a new path towards reef conservation: Antigua’s community- 11:15 S Camacho R, Steneck R based no-take reserves Lyons P, Arboleda E, Benkwitt C, Davis B, Gleason M, Howe 11:30 * C, Mathe J, Middleton J, Sikowitz N, Untersteggaber L, The effect of recreational scuba diving on the benthic community Villalobos S assemblage and structural complexity of Caribbean coral reefs Perspective on how fast and efficient sponge engines drive and 11:45 * De Goeij JM modulate the food web of reef ecosystems Lesion recovery of two scleractinian corals under low pH: 12:00 S Dungan A, Hall ER, DeGroot BC, Fine M implications for restoration efforts Session chair: Kristen Marhaver Kristen chair: Session The status of coral reefs and marine fisheries in Jamaica’s Portland 12:15 * Palmer SE, Lang JC Bight Protected Area to inform proposed development decisions 12:30 Lunch (can be obtained at the Hilton, Carmabi (next to Hilton) or nearby restaurants and bars Historical analysis of ciguatera incidence in the Caribbean islands 13:30 * Mancera-Pineda JE, Celis JS, Gavio B during 31 years: 1980-2010 Smith TB, Richlen ML, Robertson A, Liefer JD, Anderson DM, Ciguatera fish poisoning: long-term dynamics of Gambierdiscus spp. -
MSRP Appendix A
APPENDIX A: RECOVERY TEAM MEMBERS Multi-Species Recovery Plan for South Florida Appendix A. Names appearing in bold print denote those who authored or prepared Appointed Recovery various components of the recovery plan. Team Members Ralph Adams Geoffrey Babb Florida Atlantic University The Nature Conservancy Biological Sciences 222 South Westmonte Drive, Suite 300 Boca Raton, Florida 33431 Altimonte Springs, Florida 32714-4236 Ross Alliston Alice Bard Monroe County, Environmental Florida Department of Environmental Resource Director Protection 2798 Overseas Hwy Florida Park Service, District 3 Marathon , Florida 33050 1549 State Park Drive Clermont, Florida 34711 Ken Alvarez Florida Department of Enviromental Bob Barron Protection U.S. Army Corps of Engineers Florida Park Service, 1843 South Trail Regulatory Division Osprey, Florida 34229 P.O. Box 4970 Jacksonville, Florida 32232-0019 Loran Anderson Florida State University Oron L. “Sonny” Bass Department of Biological Science National Park Service Tallahassee, Florida 32306-2043 Everglades National Park 40001 State Road 9336 Tom Armentano Homestead, Florida 33034-6733 National Park Service Everglades National Park Steven Beissinger 40001 State Road 9336 Yale University - School of Homestead, Florida 33034-6733 Forestry & Environmental Studies Sage Hall, 205 Prospect Street David Arnold New Haven, Connecticut 06511 Florida Department of Environmental Protection Rob Bennetts 3900 Commonwealth Boulevard P.O. Box 502 Tallahassee, Florida 32399-3000 West Glacier, Montana 59936 Daniel F. Austin Michael Bentzien Florida Atlantic University U.S. Fish and Wildlife Service Biological Sciences Jacksonville Field Office 777 Glades Road 6620 Southpoint Drive South, Suite 310 Boca Raton, Florida 33431 Jacksonville, Florida 32216-0912 David Auth Nancy Bissett University of Florida The Natives Florida Museum of Natural History 2929 J.B. -
Campaign Treasurer's Report Summary
FLORIDA DEPARTMENT OF STATE, DIVISION OF ELECTIONS CAMPAIGN TREASURER’S REPORT SUMMARY (1)ERVIN HIGGS (2) ERVIN HIGGS Candidate, Committee or Party Name I.D. Number (3) 80 Key Haven Rd Key West FL 33040 Address (number and street) City State Zip Code Check box if address has changed since last report (4) Check appropriate box(es): PROPERTY APPRAISER ✔ Candidate (office sought): Political Committee Check if PC has DISBANDED Committee of Continuous Existence Check if CCE has DISBANDED Party Executive Committee (5) REPORT IDENTIFIERS Cover Period: From9/25/2004 To10/8/2004 Report Type: G3 ✔ Original Amendment Special Election Report Independent Expenditure Report (6) CONTRIBUTIONS THIS REPORT (7) EXPENDITURES THIS REPORT Monetary 1,700.00 1,416.98 Cash & Checks $ Expenditures $ Transfers to Office 0.00 0.00 Loans $ Account $ 1,700.00 1,416.98 Total Monetary $ Total Monetary $ 0.00 0.00 In-Kind $ (8) Other Distributions $ (9) TOTAL Monetary Contributions to Date (10) TOTAL Monetary Expenditures to Date 10,453.32 $ 17,675.00 $ (11) CERTIFICATION It is a first degree misdemeanor for any person to falsify a public record (ss. 839.13, F.S.) I certify that I have examined this report and it is I certify that I have examined this report and it is true, true, correct and complete correct and complete Name of Treasurer Deputy Treasurer Name of Candidate Chairman (PC/PTY only) XX Signature Signature DS-DE 12 (7/98) SEE REVERSE FOR INSTRUCTIONS AND CODE VALUES CAMPAIGN TREASURER’S REPORT – ITEMIZED CONTRIBUTIONS (1) Name ______________________________________________________ERVIN HIGGS (2) I.D. Number ____________________ERVIN HIGGS (3) Cover Period ___________________9/25/2004 through ___________________10/8/2004 (4) Page ____________1 of _____________1 (5) (7) (8) (9) (10) (11) (12) Date Full Name Contributor (6) (Last, Suffix, First, Middle) Sequence Street Address & Contribution In-kind Number City, State, Zip Code Type Occupation Type Description Amendment Amount Liermann Emily C I CHE 100.00 126 Indies Dr. -
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.