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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. -
Coral Reef Protection in Quintana Roo, Mexico. Intercoast #34 ______
_____________________________________________________________________________ Coral Reef Protection in Quintana Roo, Mexico. Intercoast #34 _____________________________________________________________________________ Bezaury, Juan and Jennifer McCann 1999 Citation: Narragansett, Rhode Island USA: Coastal Resources Center.InterCoast Network Newsletter, Spring 1999 For more information contact: Pamela Rubinoff, Coastal Resources Center, Graduate School of Oceanography, University of Rhode Island. 220 South Ferry Road, Narragansett, RI 02882 Telephone: 401.874.6224 Fax: 401.789.4670 Email: [email protected] This five year project aims to conserve critical coastal resources in Mexico by building capacity of NGOs, Universities, communities and other key public and private stakeholders to promote an integrated approach to participatory coastal management and enhanced decision-making. This publication was made possible through support provided by the U.S. Agency for International Development’s Office of Environment and Natural Resources Bureau for Economic Growth, Agriculture and Trade under the terms of Cooperative Agreement No. PCE-A-00-95-0030-05. INTERNATIONAL NEWSLETTER OF COASTAL MANAGEMENT Narragansett, Rhode Island, U.S.A. • #31 • Spring, 1998 Protecting the Maya Reef Intercoast Through Multi-National Survey Results Cooperation Show Diverse manage their coastal resources region- Readership By Juan Bezaury and ally. The overall goal is to take advan- Jennifer McCann tage of growing opportunities for sus- ore than 200 people tainable development, -
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. -
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 -
Marine Protected Areas (Mpas) in Management 1 of Coral Reefs
ISRS BRIEFING PAPER 1 MARINE PROTECTED AREAS (MPAS) IN MANAGEMENT 1 OF CORAL REEFS SYNOPSIS Marine protected areas (MPAs) may stop all extractive uses, protect particular species or locally prohibit specific kinds of fishing. These areas may be established for reasons of conservation, tourism or fisheries management. This briefing paper discusses the potential uses of MPAs, factors that have affected their success and the conditions under which they are likely to be effective. ¾ MPAs are often established as a conservation tool, allowing protection of species sensitive to fishing and thus preserving intact ecosystems, their processes and biodiversity and ultimately their resilience to perturbations. ¾ Increases in charismatic species such as large groupers in MPAs combined with the perception that the reefs there are relatively pristine mean that MPAs can play a significant role in tourism. ¾ By reducing fishing mortality, effective MPAs have positive effects locally on abundances, biomass, sizes and reproductive outputs of many exploitable site- attached reef species. ¾ Because high biomass of focal species is sought but this is quickly depleted and is slow to recover, poaching is a problem in most reef MPAs. ¾ Target-species ‘spillover’ into fishing areas is likely occurring close to the MPA boundaries and benefits will often be related to MPA size. Evidence for MPAs acting as a source of larval export remains weak. ¾ The science of MPAs is at an early stage of its development and MPAs will rarely suffice alone to address the main objectives of fisheries management; concomitant control of effort and other measures are needed to reduce fishery impacts, sustain yields or help stocks to recover. -
Florida Keys National Marine Sanctuary
Florida Keys National Marine Sanctuary Review and Discussion February 19, 2020 IJ Florida Fish and Wildlife Conservation Commission This is a review and discussion of the Florida Keys National Marine Sanctuary’s (FKNMS) Restoration Blueprint, the FWC’s role in managing the fisheries resources within the FKNMS, proposed regulatory actions, and next steps. Division: Marine Fisheries Management Authors: Jessica McCawley, John Hunt, Martha Guyas, and CJ Sweetman Contact Phone Number: 850-487-0554 Report date: February 17, 2020 Unless otherwise noted, images throughout the presentation are by FWC or Florida Keys National Marine Sanctuary. FKNMS Process Reminder • Oct. and Dec. - FKNMS discussions • Jan. - FWC staff meetings with diverse stakeholder organizations • Today - Look at all relevant aspects of plan and consider FWC's proposed response • April - FWC comments due • Summer 2020 - FWC begin rulemaking process for state waters As a management partner in the Florida Keys National Marine Sanctuary (FKNMS), FWC has been engaged in review of the Restoration Blueprint (Draft Environmental Impact Statement, DEIS) over the past several months. In October and December, the Commission discussed the FKNMS Restoration Blueprint. In January, FWC staff met with a variety of stakeholders to better understand their comments on particular issues addressed within the DEIS. Today, the presentation will cover all relevant aspects of the plan and staff recommendations based on a review of the science and stakeholder comments, which will be outlined in the next two slides. FWC requested and has been granted an extension for submitting agency comments to the FKNMS until April. Following the Commission’s response to the FKNMS, FWC will consider rulemaking for fisheries management items state waters. -
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. -
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. -
Coral Reef Biological Criteria: Using the Clean Water Act to Protect a National Treasure
EPA/600/R-10/054 | July 2010 | www.epa.gov/ord Coral Reef Biological Criteria: Using the Clean Water Act to Protect a National Treasure Offi ce of Research and Development | National Health and Environmental Effects Research Laboratory EPA/600/R-10/054 July 2010 www.epa.gov/ord Coral Reef Biological Criteria Using the Clean Water Act to Protect a National Treasure by Patricia Bradley Leska S. Fore Atlantic Ecology Division Statistical Design NHEERL, ORD 136 NW 40th St. 33 East Quay Road Seattle, WA 98107 Key West, FL 33040 William Fisher Wayne Davis Gulf Ecology Division Environmental Analysis Division NHEERL, ORD Offi ce of Environmental Information 1 Sabine Island Drive 701 Mapes Road Gulf Breeze, FL 32561 Fort Meade, MD 20755 Contract No. EP-C-06-033 Work Assignment 3-11 Great Lakes Environmental Center, Inc Project Officer: Work Assignment Manager: Susan K. Jackson Wayne Davis Offi ce of Water Offi ce of Environmental Information Washington, DC 20460 Fort Meade, MD 20755 National Health and Environmental Effects Research Laboratory Offi ce of Research and Development Washington, DC 20460 Printed on chlorine free 100% recycled paper with 100% post-consumer fiber using vegetable-based ink. Notice and Disclaimer The U.S. Environmental Protection Agency through its Offi ce of Research and Development, Offi ce of Environmental Information, and Offi ce of Water funded and collaborated in the research described here under Contract EP-C-06-033, Work Assignment 3-11, to Great Lakes Environmental Center, Inc. It has been subject to the Agency’s peer and administrative review and has been approved for publication as an EPA document. -
An Environmental Assessment of the John Pennekamp Coral Reef State Park and the Key Largo Coral Reef Marine Sanctuary (Unpublished 1983 Report)
An environmental assessment of the John Pennekamp Coral Reef State Park and the Key Largo Coral Reef Marine Sanctuary (Unpublished 1983 Report) Item Type monograph Authors Voss, Gilbert L.; Voss, Nancy A.; Cantillo, Andriana Y.; Bello, Maria J. Publisher NOAA/National Ocean Service/National Centers for Coastal Ocean Science Download date 07/10/2021 01:47:07 Link to Item http://hdl.handle.net/1834/19992 NOAA/University of Miami Joint Publication NOAA Technical Memorandum NOS NCCOS CCMA 161 NOAA LISD Current References 2002-6 University of Miami RSMAS TR 2002-03 Coastal and Estuarine Data Archaeology and Rescue Program AN ENVIRONMENTAL ASSESSMENT OF THE JOHN PENNEKAMP CORAL REEF STATE PARK AND THE KEY LARGO CORAL REEF MARINE SANCTUARY (Unpublished 1983 Report) November 2002 US Department of Commerce University of Miami National Oceanic and Atmospheric Rosenstiel School of Marine and Administration Atmospheric Science Silver Spring, MD Miami, FL a NOAA/University of Miami Joint Publication NOAA Technical Memorandum NOS NCCOS CCMA 161 NOAA LISD Current References 2002-6 University of Miami RSMAS TR 2002-03 AN ENVIRONMENTAL ASSESSMENT OF THE JOHN PENNEKAMP CORAL REEF STATE PARK AND THE KEY LARGO CORAL REEF MARINE SANCTUARY (Unpublished 1983 Report) Gilbert L. Voss Rosenstiel School of Marine and Atmospheric Science University of Miami Nancy A. Voss Rosenstiel School of Marine and Atmospheric Science University of Miami Adriana Y. Cantillo NOAA National Ocean Service Maria J. Bello NOAA Miami Regional Library (Editors, 2002) November 2002 United States National Oceanic and Department of Commerce Atmospheric Administration National Ocean Service Donald L. Evans Conrad C. Lautenbacher, Jr. -
Coral Reefs Are Deteriorating Worldwide at Alarming Rates
U.S. CORAL REEF TASK FORC FY2000 ACCOMPLISHMENTS AND FUTURE ACTIVITIES oral reefs are among the most diverse and biologically complex ecosystems on earth. C These rainforests of the sea provide economic and environmental services to millions of people as areas of natural beauty and recreation, sources of food, jobs, chemicals, pharmaceuticals, and shoreline protection. Now under threat from multiple stresses that are overwhelming their natural resilience, coral reefs are deteriorating worldwide at alarming rates. An estimated 25% of the world’s reefs have already been lost and 60% are threatened by bleaching, disease, and a variety of human activities including shoreline development, polluted runoff from agricultural and land-use practices, ship groundings, over-harvesting, destructive fishing, and global climate change, http://coral.aoml.noaa.gov/gcrmn/status_2000.pdf. The trend in coral reef health is downward, and these ancient ecosystems are in peril. In response to this growing global environmental crisis, the Coral Reef Protection Executive Order 13089 was issued on June 11, 1998. The Executive Order established the United States Coral Reef Task Force (CRTF), which includes the major federal agencies responsible for aspects of coral reef conservation, plus our state and territorial partners. Through the policies set forth in the Executive Order, the federal government was directed to strengthen its steward- ship of the nation’s reef eco- systems and coral reefs around the world. 2 The Coral Reef Task Force identified two fundamental themes Working with government and non-government partners, for immediate and sustained national action: the CRTF has made a number of significant advances to implement the National Action Plan and conserve coral reef ecosystems in — Understand coral reef ecosystems and the natural and anthro- pogenic processes that determine their health and viability; the United States and globally. -
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.