I. Coral Reef (CR) Formation & Development
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Field Guide to the Nonindigenous Marine Fishes of Florida
Field Guide to the Nonindigenous Marine Fishes of Florida Schofield, P. J., J. A. Morris, Jr. and L. Akins Mention of trade names or commercial products does not constitute endorsement or recommendation for their use by the United States goverment. Pamela J. Schofield, Ph.D. U.S. Geological Survey Florida Integrated Science Center 7920 NW 71st Street Gainesville, FL 32653 [email protected] James A. Morris, Jr., Ph.D. National Oceanic and Atmospheric Administration National Ocean Service National Centers for Coastal Ocean Science Center for Coastal Fisheries and Habitat Research 101 Pivers Island Road Beaufort, NC 28516 [email protected] Lad Akins Reef Environmental Education Foundation (REEF) 98300 Overseas Highway Key Largo, FL 33037 [email protected] Suggested Citation: Schofield, P. J., J. A. Morris, Jr. and L. Akins. 2009. Field Guide to Nonindigenous Marine Fishes of Florida. NOAA Technical Memorandum NOS NCCOS 92. Field Guide to Nonindigenous Marine Fishes of Florida Pamela J. Schofield, Ph.D. James A. Morris, Jr., Ph.D. Lad Akins NOAA, National Ocean Service National Centers for Coastal Ocean Science NOAA Technical Memorandum NOS NCCOS 92. September 2009 United States Department of National Oceanic and National Ocean Service Commerce Atmospheric Administration Gary F. Locke Jane Lubchenco John H. Dunnigan Secretary Administrator Assistant Administrator Table of Contents Introduction ................................................................................................ i Methods .....................................................................................................ii -
Fisheries Benefits of Marine Managed Areas in Hawaii
Fisheries benefits of Marine Managed Areas in Hawaii Alan Friedlander Herman Cesar 30 April 2004 Alan M. Friedlander NOAA, National Ocean Service, National Centers for Coastal Ocean Science - Biogeography Program & Oceanic Institute Makapu‘u Point/41-202 Kalanianaole Hwy, Waimanalo, Hawai‘i 96795. E-mail: [email protected] Herman Cesar Cesar Environmental Economics Consulting Kastanjelaan 9 6828 GH Arnhem The Netherlands E-mail: [email protected] Web: www.ceec.nl 2 Fisheries Benefits of MMAs Contents 1. Introduction 3 2. Marine Protected Area Theory and Empirical Evidence 5 3. Description of Study Sites 12 4. Empirical Information On Fish Assemblage Characteristics 17 5. Empirical Information on MPAs in Hawaii – Overall Comparison of Protected Areas 22 6. Recommendations for Modifications to Existing MPAS and for the Design and Siting of Future Protected Areas 25 7. References 31 Appendix I. Top ten species observed on transects for the Six Study Sites 37 Colophon This study is part of a larger report with the title “Assessment of Economic Benefits and Costs of Marine Managed Areas in Hawaii" by Herman Cesar, Pieter van Beukering and Alan Friedlander. This publication is a result of research carried out by Cesar Environmental Economics Consulting (CEEC) and funded by the National Oceanic and Atmospheric Administration, Coastal Ocean Program, under awards NA 160A2412 to the University of Hawaii for the Hawaii Coral Reef Initiative Research Program. Co- funding was obtained from the Division of Aquatic Resources (DAR) and the Department of Business, Economic Development & Tourism (DBEDT). This specific study was compiled by Alan M. Friedlander, under a subcontract with CEEC. -
Hawai'i Institute of Marine Biology Northwestern Hawaiian Islands
Hawai‘i Institute of Marine Biology Northwestern Hawaiian Islands Coral Reef Research Partnership Quarterly Progress Reports II-III August, 2005-March, 2006 Report submitted by Malia Rivera and Jo-Ann Leong April 21, 2006 Photo credits: Front cover and back cover-reef at French Frigate Shoals. Upper left, reef at Pearl and Hermes. Photos by James Watt. Hawai‘i Institute of Marine Biology Northwestern Hawaiian Islands Coral Reef Research Partnership Quarterly Progress Reports II-III August, 2005-March, 2006 Report submitted by Malia Rivera and Jo-Ann Leong April 21, 2006 Acknowledgments. Hawaii Institute of Marine Biology (HIMB) acknowledges the support of Senator Daniel K. Inouye’s Office, the National Marine Sanctuary Program (NMSP), the Northwestern Hawaiian Islands Coral Reef Ecosystem Reserve (NWHICRER), State of Hawaii Department of Land and Natural Resources (DLNR) Division of Aquatic Resources, US Fish and Wildlife Service, NOAA Fisheries, and the numerous University of Hawaii partners involved in this project. Funding provided by NMSP MOA 2005-008/66832. Photos provided by NOAA NWHICRER and HIMB. Aerial photo of Moku o Lo‘e (Coconut Island) by Brent Daniel. Background The Hawai‘i Institute of Marine Biology (School of Ocean and Earth Science and Technology, University of Hawai‘i at Mānoa) signed a memorandum of agreement with National Marine Sanctuary Program (NOS, NOAA) on March 28, 2005, to assist the Northwestern Hawaiian Islands Coral Reef Ecosystem Reserve (NWHICRER) with scientific research required for the development of a science-based ecosystem management plan. With this overriding objective, a scope of work was developed to: 1. Understand the population structures of bottomfish, lobsters, reef fish, endemic coral species, and adult predator species in the NWHI. -
Most Impaired" Coral Reef Areas in the State of Hawai'i
Final Report: EPA Grant CD97918401-0 P. L. Jokiel, K S. Rodgers and Eric K. Brown Page 1 Assessment, Mapping and Monitoring of Selected "Most Impaired" Coral Reef Areas in the State of Hawai'i. Paul L. Jokiel Ku'ulei Rodgers and Eric K. Brown Hawaii Coral Reef Assessment and Monitoring Program (CRAMP) Hawai‘i Institute of Marine Biology P.O.Box 1346 Kāne'ohe, HI 96744 Phone: 808 236 7440 e-mail: [email protected] Final Report: EPA Grant CD97918401-0 April 1, 2004. Final Report: EPA Grant CD97918401-0 P. L. Jokiel, K S. Rodgers and Eric K. Brown Page 2 Table of Contents 0.0 Overview of project in relation to main Hawaiian Islands ................................................3 0.1 Introduction...................................................................................................................3 0.2 Overview of coral reefs – Main Hawaiian Islands........................................................4 1.0 Ka¯ne‘ohe Bay .................................................................................................................12 1.1 South Ka¯ne‘ohe Bay Segment ...................................................................................62 1.2 Central Ka¯ne‘ohe Bay Segment..................................................................................86 1.3 North Ka¯ne‘ohe Bay Segment ....................................................................................94 2.0 South Moloka‘i ................................................................................................................96 2.1 Kamalō -
2.02 Rajasuriya 2008
ARJAN RAJASURIYA National Aquatic Resources Research and Development Agency, Crow Island, Colombo 15, Sri Lanka [email protected]; [email protected] fringing and patch reefs (Swan, 1983; Rajasuriya et al., 1995; Rajasuriya & White, 1995). Fringing coral reef Selected coral reefs were monitored in the northern, areas occur in a narrow band along the coast except in western and southern coastal waters of Sri Lanka to the southeast and northeast of the island where sand assess their current status and to understand the movement inhibits their formation. The shallow recovery processes after the 1998 coral bleaching event continental shelf of Gulf of Mannar contains extensive and the 2004 tsunami. The highest rate of recovery coral patch reefs from the Bar Reef to Mannar Island was observed at the Bar Reef Marine Sanctuary where (Rajasuriya, 1991; Rajasuriya, et al. 1998a; Rajasuriya rapid growth of Acropora cytherea and Pocillopora & Premaratne, 2000). In addition to these coral reefs, damicornis has contributed to reef recovery. which are limited to a depth of about 10m, there are Pocillopora damicornis has shown a high level of offshore coral patches in the west and east of the recruitment and growth on most reef habitats island at varying distances (15 -20 km) from the including reefs in the south. An increase in the growth coastline at an average depth of 20m (Rajasuriya, of the calcareous alga Halimeda and high levels of 2005). Sandstone and limestone reefs occur as sedimentation has negatively affected some fringing discontinuous bands parallel to the shore from inshore reefs especially in the south. Reef surveys carried out areas to the edge of the continental shelf (Swan, 1983; for the first time in the northern coastal waters around Rajasuriya et al., 1995). -
Cleaner Wrasse Influence Habitat Selection of Young Damselfish
1 Cleaner wrasse influence habitat selection of young damselfish 2 3 4 D. Sun*1, K. L. Cheney1, J. Werminghausen1, E. C. McClure1, 2, M. G. Meekan3, M. I. 5 McCormick2, T. H. Cribb1, A. S. Grutter1 6 7 1 School of Biological Sciences, The University of Queensland, St Lucia, QLD 4072, 8 Australia 9 2 ARC Centre of Excellence for Coral Reef Studies and College of Marine and 10 Environmental Sciences, James Cook University, Townsville, QLD 4811, Australia 11 3 Australian Institute of Marine Science, The UWA Oceans Institute (M096), Crawley, WA 12 6009, Australia 13 14 *Author for correspondence: Derek Sun 15 Email: [email protected] 16 Phone: +61 7 3365 1398 17 Fax: +61 7 3365 1655 18 19 Keywords: Recruitment, Ectoparasites, Cleaning behaviour, Damselfish, Mutualism 20 21 1 22 Abstract 23 The presence of bluestreak cleaner wrasse, Labroides dimidiatus, on coral reefs increases 24 total abundance and biodiversity of reef fishes. The mechanism(s) that cause such shifts in 25 population structure are unclear, but it is possible that young fish preferentially settle into 26 microhabitats where cleaner wrasse are present. As a first step to investigate this possibility, 27 we conducted aquarium experiments to examine whether settlement-stage and young 28 juveniles of ambon damselfish, Pomacentrus amboinensis, selected a microhabitat near a 29 cleaner wrasse (adult or juvenile). Both settlement-stage (0 d post-settlement) and juvenile (~ 30 5 weeks post-settlement) fish spent a greater proportion of time in a microhabitat adjacent to 31 L. dimidiatus than in one next to a control fish (a non-cleaner wrasse, Halichoeres 32 melanurus) or one where no fish was present. -
Coral Health and Disease in the Pacific: Vision for Action
IV. STATE OF KNOWLEDGE IN THE PACIFIC—WHAT DO WE KNOW AND WHAT HAVE WE LEARNED? OVERVIEW OF ISSUES UNIQUE TO THE PACIFIC: BIOLOGICAL & SOCIAL PERSPECTIVES Michael J. Gawel Guam EPA 120 Bengbing St. Y-Papao Dededo, GU 96929 [email protected] Pacific Islands The term “Pacific Islands” in the context of this paper arbitrarily refers to those tropical islands of the central and western Pacific Ocean which support shallow hermatypic coral reefs, but excluding the Hawaiian Archipelago, which is covered in other papers. The tropical Pacific Island nations and territories all support coral reefs and, no doubt, harbor coral diseases, although these have not been scientifically documented in many of the islands. In fact, as part of the U.S. National Action Plan to Conserve Coral Reefs, surveys in 2002 and 2004 of coral reef academic scientists, resource managers, government agencies and NGOs recorded that in the U.S. Pacific islands they perceived “no threat” from coral disease, although American Samoa registered an increase to perception of “moderate threat” in the 2004 survey (Waddell, 2005). This lack of concern partially reflects a lack of information on the status of diseases in many islands. Wilkinson (2004, p. 405) notes that in American Samoa and Micronesia “Coral bleaching and disease were either rare or undocumented in 1994, but are now clearly evident and considered a serious threat to many reefs in the region.” The Pacific island coral reefs range from veneers on newly emergent volcanic islands, to platform-like fringing reefs, to barrier reefs with lagoons, to atolls, and include non- emergent isolated banks. -
Unique Quantitative Symbiodiniaceae Signature of Coral Colonies Revealed
www.nature.com/scientificreports OPEN Unique quantitative Symbiodiniaceae signature of coral colonies revealed through spatio- Received: 14 November 2018 Accepted: 25 April 2019 temporal survey in Moorea Published: xx xx xxxx Héloïse Rouzé1, Gaël Lecellier 2,3, Xavier Pochon4,5, Gergely Torda6 & Véronique Berteaux-Lecellier 1,2 One of the mechanisms of rapid adaptation or acclimatization to environmental changes in corals is through the dynamics of the composition of their associated endosymbiotic Symbiodiniaceae community. The various species of these dinofagellates are characterized by diferent biological properties, some of which can confer stress tolerance to the coral host. Compelling evidence indicates that the corals’ Symbiodiniaceae community can change via shufing and/or switching but the ecological relevance and the governance of these processes remain elusive. Using a qPCR approach to follow the dynamics of Symbiodiniaceae genera in tagged colonies of three coral species over a 10–18 month period, we detected putative genus-level switching of algal symbionts, with coral species-specifc rates of occurrence. However, the dynamics of the corals’ Symbiodiniaceae community composition was not driven by environmental parameters. On the contrary, putative shufing event were observed in two coral species during anomalous seawater temperatures and nutrient concentrations. Most notably, our results reveal that a suit of permanent Symbiodiniaceae genera is maintained in each colony in a specifc range of quantities, giving a unique ‘Symbiodiniaceae signature’ to the host. This individual signature, together with sporadic symbiont switching may account for the intra-specifc diferences in resistance and resilience observed during environmental anomalies. Dinofagellate algae from the family Symbiodiniaceae are one of the keystone taxa for coral reef ecosystems. -
Observations on the Reproduction of Acropora Corals Along the Tuticorin Coast of the Gulf of Mannar, Southeastern India
Indian Journal of Marine Sciences Vol. 39(2), June 2010, pp. 219-226 Observations on the reproduction of Acropora corals along the Tuticorin coast of the Gulf of Mannar, Southeastern India K Diraviya Raj & J K Patterson Edward Suganthi Devadason Marine Research Institute, 44-Beach Road, Tuticorin–628 001, Tamil Nadu, India [E-mail: [email protected]] Received 5 February 2009; revised 22 June 2009 Pattern of reproduction was studied in Acropora species along Tuticorin coast in the Gulf of Mannar from 2006-2008. Extensive surveys were conducted to monitor reproductive maturity and the timing of spawning. Gametes were observed from January with colonies releasing gametes by the end of March. Acropora cytherea showed immature colonies in January (48-79%) and February (56-76%) and mature colonies in March (36-86%). Likewise, the other species of Acropora examined showed 50-75% of immature colonies in January and an increase of 10-20% of immature colonies in February, and matured in March. The average percentage of mature colonies in March was as follows, A. formosa 47-76%, A. valenciennesi 50-81%, A. intermedia 50-81%, A. nobilis 25-82%, A. micropthalma 56-83%, A. hemprichi 39-83%, A. hyacinthus 33-100%, A. corymbosa 59-65%. Spawning was observed in A. cytherea on 24 March 2006, 10 days after full moon; 28 March in 2007, 5 days prior to full moon; and 8 March 2008, 1 day after new moon. Approximately 30,000 egg and sperm bundles were observed in 1 litre of water and each bundle had 20-25 eggs in A. -
The Global Trade in Marine Ornamental Species
From Ocean to Aquarium The global trade in marine ornamental species Colette Wabnitz, Michelle Taylor, Edmund Green and Tries Razak From Ocean to Aquarium The global trade in marine ornamental species Colette Wabnitz, Michelle Taylor, Edmund Green and Tries Razak ACKNOWLEDGEMENTS UNEP World Conservation This report would not have been The authors would like to thank Helen Monitoring Centre possible without the participation of Corrigan for her help with the analyses 219 Huntingdon Road many colleagues from the Marine of CITES data, and Sarah Ferriss for Cambridge CB3 0DL, UK Aquarium Council, particularly assisting in assembling information Tel: +44 (0) 1223 277314 Aquilino A. Alvarez, Paul Holthus and and analysing Annex D and GMAD data Fax: +44 (0) 1223 277136 Peter Scott, and all trading companies on Hippocampus spp. We are grateful E-mail: [email protected] who made data available to us for to Neville Ash for reviewing and editing Website: www.unep-wcmc.org inclusion into GMAD. The kind earlier versions of the manuscript. Director: Mark Collins assistance of Akbar, John Brandt, Thanks also for additional John Caldwell, Lucy Conway, Emily comments to Katharina Fabricius, THE UNEP WORLD CONSERVATION Corcoran, Keith Davenport, John Daphné Fautin, Bert Hoeksema, Caroline MONITORING CENTRE is the biodiversity Dawes, MM Faugère et Gavand, Cédric Raymakers and Charles Veron; for assessment and policy implemen- Genevois, Thomas Jung, Peter Karn, providing reprints, to Alan Friedlander, tation arm of the United Nations Firoze Nathani, Manfred Menzel, Julie Hawkins, Sherry Larkin and Tom Environment Programme (UNEP), the Davide di Mohtarami, Edward Molou, Ogawa; and for providing the picture on world’s foremost intergovernmental environmental organization. -
Inventory of Marine Vertebrate Species and Fish-Habitat Utilization Patterns in Coastal Waters Off Four National Parks in Hawai‘I
PACIFIC COOPERATIVE STUDIES UNIT UNIVERSITY OF HAWAI`I AT MĀNOA Dr. David C. Duffy, Unit Leader Department of Botany 3190 Maile Way, St. John #408 Honolulu, Hawai’i 96822 Technical Report 168 Inventory of marine vertebrate species and fish-habitat utilization patterns in coastal waters off four national parks in Hawai‘i February 2010 Jim Beets, Ph.D.1, Eric Brown, Ph.D.2, and Alan Friedlander, Ph.D.3 1University of Hawaii at Hilo, 200 W. Kawili St., Hilo, Hawai‘i 96720 2Kalaupapa National Historical Park, P.O. Box 2222, Kalaupapa, HI 96742 3NOAA/NOS/NCCOS/CCMA/Biogeography Team, Makapu‘u Point, Waimānalo, Hawai‘i 96795 PCSU is a cooperative program between the University of Hawai`i and U.S. National Park Service, Cooperative Ecological Studies Unit. Organization Contact Information: National Park Service, Inventory and Monitoring Program, Pacific Island Network, P.O. Box 52, Hawai‘i National Park, HI 96718, phone: 808-985-6180, fax: 808-985-6111 http://science.nature.nps.gov/im/units/pacn/ Recommended Citation: Beets, J., E. Brown, and A. Friedlander. 2010. Inventory of marine vertebrate species and fish-habitat utilization patterns in coastal waters off four national parks in Hawai‘i. Pacific Cooperative Studies Unit Technical Report 168. University of Hawai‘i at Mānoa, Department of Botany. Honolulu, HI. 55 pg. Key words: Inventory, marine vertebrates, marine fishes, marine mammals, marine turtles Place key words: Hawai‘i, Pacific Island Network, Molokai, island of Hawai‘i, Kaloko-Honokōhau National Historical Park, Kalaupapa National -
An Updated Assessment of Symbiodinium Spp. That
An updated assessment of Symbiodinium spp. that associate with common scleractinian corals from Moorea (French Polynesia) reveals high diversity among background symbionts and a novel finding of clade B Héloïse Rouzé1, Gaël J. Lecellier1,2,6, Denis Saulnier3, Serge Planes1, Yannick Gueguen4, Herman H. Wirshing5 and Véronique Berteaux-Lecellier1,6 1 PSL CRIOBE USR3278 CNRS-EPHE-UPVD, Labex CORAIL, Papetoai, Moorea, French Polynesia 2 Université de Paris Saclay, Departement de Biologie, Versailles-Saint Quentin, Paris, Versailles Cedex, France 3 UMR241 EIO Ifremer-ILM-IRD-UPF, Labex CORAIL, Taravao, French Polynesia 4 UMR5244 IHPE, CNRS-Ifremer-UM-UPVD, Université de Montpellier, Montpellier, France 5 Department of Invertebrate Zoology, Smithsonian National Museum of Natural History, Washington, D.C., USA 6 Current affiliation: UMR250/9220 ENTROPIE IRD-CNRS-UR, Labex CORAIL, Promenade Roger-Laroque, Noumea cedex, New Caledonia, France ABSTRACT The adaptative bleaching hypothesis (ABH) states that, depending on the symbiotic flexibility of coral hosts (i.e., the ability of corals to ``switch'' or ``shuffle'' their algal symbionts), coral bleaching can lead to a change in the composition of their associated Symbiodinium community and, thus, contribute to the coral's overall survival. In order to determine the flexibility of corals, molecular tools are required to provide accurate species delineations and to detect low levels of coral-associated Symbiodinium. Here, we used highly sensitive quantitative (real-time) PCR (qPCR) technology to analyse Submitted 20 April 2016 five common coral species from Moorea (French Polynesia), previously screened Accepted 2 December 2016 using only traditional molecular methods, to assess the presence of low-abundance Published 5 January 2017 (background) Symbiodinium spp.