The State of Coral Reef Ecosystems of Florida
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Ecological Indicators for Assessing and Communicating Seagrass Status and Trends in Florida Bay§ Christopher J
Ecological Indicators 9S (2009) S68–S82 Contents lists available at ScienceDirect Ecological Indicators journal homepage: www.elsevier.com/locate/ecolind Ecological indicators for assessing and communicating seagrass status and trends in Florida Bay§ Christopher J. Madden a,*, David T. Rudnick a, Amanda A. McDonald a, Kevin M. Cunniff b, James W. Fourqurean c a Everglades Division, South Florida Water Management District, 8894 Belvedere Rd., West Palm Beach, FL 33411, USA b R.C.T. Engineering, Inc., 701 Northpoint Parkway, West Palm Beach, FL 33407, USA c Dept. of Biological Sciences and Southeast Environmental Research Center, Florida International University, Miami, FL 33199, USA ARTICLE INFO ABSTRACT Article history: A suite of seagrass indicator metrics is developed to evaluate four essential measures of seagrass Received 23 April 2008 community status for Florida Bay. The measures are based on several years of monitoring data using the Received in revised form 20 January 2009 Braun-Blanquet Cover Abundance (BBCA) scale to derive information about seagrass spatial extent, Accepted 11 February 2009 abundance, species diversity and presence of target species. As ecosystem restoration proceeds in south Florida, additional freshwater will be discharged to Florida Bay as a means to restore the bay’s hydrology Keywords: and salinity regime. Primary hypotheses about restoring ecological function of the keystone seagrass Florida Bay community are based on the premise that hydrologic restoration will increase environmental variability Seagrass and reduce hypersalinity. This will create greater niche space and permit multiple seagrass species to co- Status Indicators exist while maintaining good environmental conditions for Thalassia testudinum, the dominant climax Thalassia seagrass species. -
Federal Register/Vol. 63, No. 158/Monday, August 17, 1998
43870 Federal Register / Vol. 63, No. 158 / Monday, August 17, 1998 / Rules and Regulations U.S.C. 553) because: (1) The 1998±99 SUMMARY: The National Oceanic and effective July 1, 1997, and codified at 15 fiscal year began on July 1, 1998, and Atmospheric Administration amends CFR Part 922, Subpart P. the marketing order requires that the the regulations for the Florida Keys In September 1997, NOAA became rate of assessment for each fiscal year National Marine Sanctuary (FKNMS or aware that significant injury to, and apply to all assessable papayas handled Sanctuary) to reinstate and make destruction of, living coral on the during such fiscal year; (2) the permanent the temporary prohibition on Tortugas Bank, west of the Dry Tortugas Committee needs to have sufficient anchoring by vessels 50 meters or National Park, was being caused by the funds to pay its expenses which are greater in registered length on Tortugas anchoring of vessels 50 meters or greater incurred on a continuous basis; and (3) Bank. The preamble to this rule contains in registered length. handlers are aware of this action which an environmental assessment for this Section 922.165 of the Sanctuary was recommended by the Committee at action. The intent of this rule is to regulations provides that, where a public meeting and is similar to other protect the coral reef at Tortugas Bank. necessary to prevent or minimize the assessment rate actions issued in past The proposed rule was published on destruction of, loss of, or injury to a years. February 11, 1998 and the comment Sanctuary resources, any and all List of Subjects in 7 CFR Part 928 period ended on March 13, 1998. -
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. -
Dry Tortugas National Park Monroe County, Florida
APPENDIX A: ERRATA 1. Page 63, Commercial Services, second paragraph. Replace the second sentence with the following text: “The number of vessels used in the operation, and arrival and departure patterns at Fort Jefferson, will be determined in the concession contracting process.” Explanation: The number of vessels to be used by the ferry concessionaire, and appropriate arrival and departure patterns, will be determined during the concessions contracting process that will occur during implementation of the Final GMPA/EIS. 2. Page 64, Commercial Services, third paragraph. Change the last word of the fourth sentence from “six” to “twelve.” Explanation: Group size for snorkeling and diving with commercial guides in the research natural area zone will be limited to 12 passengers, rather than 6 passengers. 3. Page 64, Commercial Services, sixth paragraph. Change the fourth sentence to read: “CUA permits will be issued to boat operators for 12-passenger multi-day diving trips.” Explanation: Group size for guided multi-day diving trips by operators with Commercial Use Authorizations will be 12 passengers, rather than 6 passengers. 4. Page 40, Table 1. Ranges of Visitor Use At Specific Locations. Change the last sentence in the box on page 40 to read: “Group size for snorkeling and diving with commercial guides in waters in the research natural area shall be a maximum of 12 passengers, excluding the guide.” Explanation: Clarifies that maximum group size for guided multi-day diving trips in the RNA by operators with Commercial Use Authorizations will be 12 passengers, rather than six passengers. 5. Page 84, Table 4: Summary of Alternative Actions. -
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. -
Tortugas Ecological Reserve
Strategy for Stewardship Tortugas Ecological Reserve U.S. Department of Commerce DraftSupplemental National Oceanic and Atmospheric Administration Environmental National Ocean Service ImpactStatement/ Office of Ocean and Coastal Resource Management DraftSupplemental Marine Sanctuaries Division ManagementPlan EXECUTIVE SUMMARY The Florida Keys National Marine Sanctuary (FKNMS), working in cooperation with the State of Florida, the Gulf of Mexico Fishery Management Council, and the National Marine Fisheries Service, proposes to establish a 151 square nautical mile “no- take” ecological reserve to protect the critical coral reef ecosystem of the Tortugas, a remote area in the western part of the Florida Keys National Marine Sanctuary. The reserve would consist of two sections, Tortugas North and Tortugas South, and would require an expansion of Sanctuary boundaries to protect important coral reef resources in the areas of Sherwood Forest and Riley’s Hump. An ecological reserve in the Tortugas will preserve the richness of species and health of fish stocks in the Tortugas and throughout the Florida Keys, helping to ensure the stability of commercial and recreational fisheries. The reserve will protect important spawning areas for snapper and grouper, as well as valuable deepwater habitat for other commercial species. Restrictions on vessel discharge and anchoring will protect water quality and habitat complexity. The proposed reserve’s geographical isolation will help scientists distinguish between natural and human-caused changes to the coral reef environment. Protecting Ocean Wilderness Creating an ecological reserve in the Tortugas will protect some of the most productive and unique marine resources of the Sanctuary. Because of its remote location 70 miles west of Key West and more than 140 miles from mainland Florida, the Tortugas region has the best water quality in the Sanctuary. -
A Rapid Spread of the Stony Coral Tissue Loss Disease Outbreak in the Mexican Caribbean
A rapid spread of the stony coral tissue loss disease outbreak in the Mexican Caribbean Lorenzo Alvarez-Filip, Nuria Estrada-Saldívar, Esmeralda Pérez-Cervantes, Ana Molina-Hernández and Francisco J. González-Barrios Biodiversity and Reef Conservation Laboratory, Unidad Académica de Sistemas Arrecifales, Instituto de Ciencias del Mar y Limnología, Universidad Nacional Autónoma de México, Puerto Morelos, Quintana Roo, Mexico ABSTRACT Caribbean reef corals have experienced unprecedented declines from climate change, anthropogenic stressors and infectious diseases in recent decades. Since 2014, a highly lethal, new disease, called stony coral tissue loss disease, has impacted many reef-coral species in Florida. During the summer of 2018, we noticed an anomalously high disease prevalence affecting different coral species in the northern portion of the Mexican Caribbean. We assessed the severity of this outbreak in 2018/2019 using the AGRRA coral protocol to survey 82 reef sites across the Mexican Caribbean. Then, using a subset of 14 sites, we detailed information from before the outbreak (2016/2017) to explore the consequences of the disease on the condition and composition of coral communities. Our findings show that the disease outbreak has already spread across the entire region by affecting similar species (with similar disease patterns) to those previously described for Florida. However, we observed a great variability in prevalence and tissue mortality that was not attributable to any geographical gradient. Using long-term data, we determined that there is no evidence of such high coral disease prevalence anywhere in the region before 2018, which suggests that the entire Mexican Caribbean was afflicted by the disease within a few months. -
Colony Versus Population Variation in Susceptibility and Resistance to Dark Spot Syndrome in the Caribbean Coral Siderastrea Siderea
DISEASES OF AQUATIC ORGANISMS Vol. 69: 53–65, 2006 Published March 23 Dis Aquat Org Colony versus population variation in susceptibility and resistance to dark spot syndrome in the Caribbean coral Siderastrea siderea Deborah J. Gochfeld1,*, Julie B. Olson2, Marc Slattery1, 3 1National Center for Natural Products Research, PO Box 1848, University of Mississippi, University, Mississippi 38677, USA 2Department of Biological Sciences, PO Box 870344, University of Alabama, Tuscaloosa, Alabama 35487, USA 3Department of Pharmacognosy, PO Box 1848, University of Mississippi, University, Mississippi 38677, USA ABSTRACT: Scleractinian corals appear to be increasingly susceptible to pathogenic diseases, yet it is poorly understood why certain individuals, populations or species are more susceptible to diseases than others. Clearly an understanding of mechanisms of disease resistance in corals is essential to our understanding of patterns of disease incidence and virulence; this work must begin by examining the colony and population levels of organization. The Caribbean coral Siderastrea siderea exhibits vari- ability in susceptibility to dark spot syndrome (DSS), a disease of unknown origin that can result in tissue necrosis. On the reef scale, variability in DSS prevalence in S. siderea occurred through time, but was not correlated with site, seawater temperature or depth. We monitored colonies of S. siderea affected by DSS, as well as their nearest neighbor controls, for 2 years in the Bahamas and found a marked decline in extent of DSS infection in October of both years. A preliminary survey of antimi- crobial activity in S. siderea indicated selective activity against certain ecologically relevant bacteria. To assess whether changes in chemical defenses were responsible for the observed temporal vari- ability in DSS prevalence, we sampled S. -
Diseases in Coral Reef Organisms: Current Status and Information Gaps
DISEASES IN CORAL REEF ORGANISMS: CURRENT STATUS AND INFORMATION GAPS Ernesto Weil, Ph.D Department of Marine Sciences, University of Puerto Rico DISEASE • “Any impairment of an organism’s vital organ, system and/or body functions”. • Infectious diseases: caused by parasites / pathogens. • Non-Infectious diseases: caused by factors other than pathogens (genetic – environment- nutrition) Bleaching CURRENT STATUS WORLDWIDE • Over 30 diseases/syndromes reported worldwide - 22 of these in the Caribbean. • Only nine with pathogens identified (BBD-WBDII-ASP- WPII-WPX-RBD-Tumors-Bleaching-Pink Band). • Only five of these fulfilled Koch’s postulates. • Mechanisms of tissue mortality only known for BBD. • Reservoirs proposed for 2 diseases (BBD-ASP). • One natural vector identified (H.carunculata). CURRENT STATUS WORLDWIDE • Wide geographic distribution in the wider Caribbean. More restricted in the Indo-Pacific. • 112 coral spp, 10 octocorals, 11 sponges, 3 hydrocoral and 4 crustose algae species affected. • Wide host ranges for many diseases/syndromes • Contagion across colonies, species and different groups of organisms – big concern. • Proliferation of names without pathological confirmation – a problem for researchers and managers. Number of coral species affected by diseases/syndromes Caribbean 40 39 Indo-Pacific-RS 30 l species 25 a 21 20 18 of cor er b 14 14 14 12 10 Num 9 10 8 4 3 3 2 2 2 1 1 1 0 I -II D -I D M S -I D X E S R B ne e P B SS B U YB S B P PN R HE SE Li tod W B D R T DS W W T k a O in em P Tr Diseases/syndromes A Mfav B Ssid Mferox Mfr Mfr Mfav White plague contagion C D Dlab Ssid Paragonioithon sp S.siderea CURRENT STATUS WORLDWIDE • Significant losses in coral cover, habitat and biodiversity. -
Potential Role of Viruses in White Plague Coral Disease
The ISME Journal (2014) 8, 271–283 & 2014 International Society for Microbial Ecology All rights reserved 1751-7362/14 www.nature.com/ismej ORIGINAL ARTICLE Potential role of viruses in white plague coral disease Nitzan Soffer1,2, Marilyn E Brandt3, Adrienne MS Correa1,2,4, Tyler B Smith3 and Rebecca Vega Thurber1,2 1Department of Microbiology, Oregon State University, Corvallis, OR, USA; 2Department of Biological Sciences, Florida International University, North Miami, FL, USA; 3Center for Marine and Environmental Studies, University of the Virgin Islands, St Thomas, Virgin Islands, USA and 4Ecology and Evolutionary Biology Department, Rice University, Houston, TX, USA White plague (WP)-like diseases of tropical corals are implicated in reef decline worldwide, although their etiological cause is generally unknown. Studies thus far have focused on bacterial or eukaryotic pathogens as the source of these diseases; no studies have examined the role of viruses. Using a combination of transmission electron microscopy (TEM) and 454 pyrosequencing, we compared 24 viral metagenomes generated from Montastraea annularis corals showing signs of WP-like disease and/or bleaching, control conspecific corals, and adjacent seawater. TEM was used for visual inspection of diseased coral tissue. No bacteria were visually identified within diseased coral tissues, but viral particles and sequence similarities to eukaryotic circular Rep-encoding single-stranded DNA viruses and their associated satellites (SCSDVs) were abundant in WP diseased tissues. In contrast, sequence similarities to SCSDVs were not found in any healthy coral tissues, suggesting SCSDVs might have a role in WP disease. Furthermore, Herpesviridae gene signatures dominated healthy tissues, corroborating reports that herpes-like viruses infect all corals. -
Necrotic Patches Affect Acropora Palmata (Scleractinia: Acroporidae) in the Mexican Caribbean
DISEASES OF AQUATIC ORGANISMS Vol. 47: 229–234, 2001 Published December 5 Dis Aquat Org Necrotic patches affect Acropora palmata (Scleractinia: Acroporidae) in the Mexican Caribbean R. E. Rodríguez-Martínez*, A. T. Banaszak, E. Jordán-Dahlgren Instituto de Ciencias del Mar y Limnología, UNAM Apartado Postal 1152, 77500 Cancún, Q Roo, México ABSTRACT: An outbreak of necrotic patches was observed affecting Acropora palmata in the Mexi- can Caribbean in the summer of 1999. This study documents the tissue loss produced by these patches. Following a marked initial increase in the number of patches, there was a decrease in the appearance of new patches but the size of the patches increased throughout the study. In some cases patches expanded but in most cases they enlarged due to fusion of 2 or more patches. Patches recov- ered but not sufficiently to overcome damage in most colonies surveyed. Percentage tissue loss does not appear to be directly related to temperature but may be related to a combination of factors asso- ciated with prolonged summer doldrum-like conditions. The necrotic patch syndrome can have a substantial impact in tissue loss in affected A. palmata colonies. KEY WORDS: Coral diseases · Patchy necrosis · Acropora palmata · Mexican Caribbean Resale or republication not permitted without written consent of the publisher INTRODUCTION satisfying Koch’s postulates (Richardson 1998). Richard- son (1998) has suggested that in the absence of formal Acropora palmata (Lamarck, 1816) is the dominant identification of a causative agent a ‘disease’ should be reef-building coral in many Caribbean reefs at depths called a syndrome or potential disease state. -
Coral Bleaching Examples
Mote Marine Laboratory / Florida Keys National Marine Sanctuary Florida Keys BleachWatch Program EXAMPLES OF BLEACHING Common Name: Common Name: Knobby Cactus Coral Staghorn Coral Coral Type: Coral Type: Fleshy Branching Bleaching Severity: Bleaching Severity: No Bleaching No Bleaching Mycetophyllia ferox NO BLEACHING Acropora cervicornis Common Name: Common Name: Flower Coral Lettuce Coral Coral Type: Coral Type: Flower / Cup Leaf / Plate / Sheet Bleaching Severity: Bleaching Severity: No Bleaching No Bleaching Eusmilia fastigiana Undaria agaricites PALING BLEACHED Common Name: Common Name: Massive Starlet Coral Finger Coral Coral Type: Coral Type: Mound and Boulder Branching Bleaching Severity: Bleaching Severity: Paling Bleached Siderastrea siderea Porites porites Common Name: Common Name: Boulder Brain Coral Mountainous Star Coral Coral Type: Coral Type: Mound and Boulder Mound and Boulder Bleaching Severity: Bleaching Severity: Paling Bleached Colpophyllia natans Orbicella faveolata Common Name: Common Name: Boulder Star Coral Boulder Brain Coral Coral Type: Coral Type: Mound and Boulder Mound and Boulder Bleaching Severity: Bleaching Severity: Upper Surface / Paling Bleached Orbicella annularis Colpophyllia natans Progression of coral bleaching…… Photo 1 Photo 2 Photo 3 TIME AND STRESS The above photos illustrate a time line of bleaching for Elkhorn Coral Acropora palmata. Photo 1 is a healthy colony with a brown tint provided by the zooxanthellae. Photo 2 the entire colony has expelled their zooxanthellae causing a “bleached” white appearance. Photo 3 the colony was not able to regain the zooxanthellae and mortality and algae growth has occurred. Helpful tips on IDENTIFICATION…. Photo: CRogers Black-Band Disease White Pox Disease Yellow-Band Disease Forms a dark ring usually starting on Forms small white patches of Circular yellow tissue with the outer edges of the coral.