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Couturier LIE, Marshall AD, Jaine FRA, Kashiwagi T, Pierce SJ, Townsend KA, Weeks SJ, Bennett MB, Richardson AJ. Biology, ecology and conservation of the Mobulidae. JOURNAL OF FISH BIOLOGY 2012; 80:1075-1119. [PMID: 22497374 DOI: 10.1111/j.1095-8649.2012.03264.x] [Citation(s) in RCA: 98] [Impact Index Per Article: 7.5] [Reference Citation Analysis] [Abstract] [MESH Headings] [Track Full Text] [Subscribe] [Scholar Register] [Indexed: 05/26/2023]
Abstract
The Mobulidae are zooplanktivorous elasmobranchs comprising two recognized species of manta rays (Manta spp.) and nine recognized species of devil rays (Mobula spp.). They are found circumglobally in tropical, subtropical and temperate coastal waters. Although mobulids have been recorded for over 400 years, critical knowledge gaps still compromise the ability to assess the status of these species. On the basis of a review of 263 publications, a comparative synthesis of the biology and ecology of mobulids was conducted to examine their evolution, taxonomy, distribution, population trends, movements and aggregation, reproduction, growth and longevity, feeding, natural mortality and direct and indirect anthropogenic threats. There has been a marked increase in the number of published studies on mobulids since c. 1990, particularly for the genus Manta, although the genus Mobula remains poorly understood. Mobulid species have many common biological characteristics although their ecologies appear to be species-specific, and sometimes region-specific. Movement studies suggest that mobulids are highly mobile and have the potential to rapidly travel large distances. Fishing pressure is the major threat to many mobulid populations, with current levels of exploitation in target fisheries unlikely to be sustainable. Advances in the fields of population genetics, acoustic and satellite tracking, and stable-isotope and fatty-acid analyses will provide new insights into the biology and ecology of these species. Future research should focus on the uncertain taxonomy of mobulid species, the degree of overlap between their large-scale movement and human activities such as fisheries and pollution, and the need for management of inter-jurisdictional fisheries in developing nations to ensure their long-term sustainability. Closer collaboration among researchers worldwide is necessary to ensure standardized sampling and modelling methodologies to underpin global population estimates and status.
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Affiliation(s)
- L I E Couturier
- School of Biomedical Sciences, The University of Queensland, St Lucia, Qld 4072, Australia.
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SHEPPARD CRC, ATEWEBERHAN M, BOWEN BW, CARR P, CHEN CA, CLUBBE C, CRAIG MT, EBINGHAUS R, EBLE J, FITZSIMMONS N, GAITHER MR, GAN CH, GOLLOCK M, GUZMAN N, GRAHAM NAJ, HARRIS A, JONES R, KESHAVMURTHY S, KOLDEWEY H, LUNDIN CG, MORTIMER JA, OBURA D, PFEIFFER M, PRICE ARG, PURKIS S, RAINES P, READMAN JW, RIEGL B, ROGERS A, SCHLEYER M, SEAWARD MRD, SHEPPARD ALS, TAMELANDER J, TURNER JR, VISRAM S, VOGLER C, VOGT S, WOLSCHKE H, YANG JMC, YANG SY, YESSON C. Reefs and islands of the Chagos Archipelago, Indian Ocean: why it is the world's largest no-take marine protected area. AQUATIC CONSERVATION : MARINE AND FRESHWATER ECOSYSTEMS 2012; 22:232-261. [PMID: 25505830 PMCID: PMC4260629 DOI: 10.1002/aqc.1248] [Citation(s) in RCA: 69] [Impact Index Per Article: 5.3] [Reference Citation Analysis] [Abstract] [Key Words] [Grants] [Track Full Text] [Subscribe] [Scholar Register] [Indexed: 05/12/2023]
Abstract
The Chagos Archipelago was designated a no-take marine protected area (MPA) in 2010; it covers 550 000 km2, with more than 60 000 km2 shallow limestone platform and reefs. This has doubled the global cover of such MPAs.It contains 25-50% of the Indian Ocean reef area remaining in excellent condition, as well as the world's largest contiguous undamaged reef area. It has suffered from warming episodes, but after the most severe mortality event of 1998, coral cover was restored after 10 years.Coral reef fishes are orders of magnitude more abundant than in other Indian Ocean locations, regardless of whether the latter are fished or protected.Coral diseases are extremely low, and no invasive marine species are known.Genetically, Chagos marine species are part of the Western Indian Ocean, and Chagos serves as a 'stepping-stone' in the ocean.The no-take MPA extends to the 200 nm boundary, and. includes 86 unfished seamounts and 243 deep knolls as well as encompassing important pelagic species.On the larger islands, native plants, coconut crabs, bird and turtle colonies were largely destroyed in plantation times, but several smaller islands are in relatively undamaged state.There are now 10 'important bird areas', coconut crab density is high and numbers of green and hawksbill turtles are recovering.Diego Garcia atoll contains a military facility; this atoll contains one Ramsar site and several 'strict nature reserves'. Pollutant monitoring shows it to be the least polluted inhabited atoll in the world. Today, strict environmental regulations are enforced.Shoreline erosion is significant in many places. Its economic cost in the inhabited part of Diego Garcia is very high, but all islands are vulnerable.Chagos is ideally situated for several monitoring programmes, and use is increasingly being made of the archipelago for this purpose.
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Affiliation(s)
| | - M. ATEWEBERHAN
- School of Life Sciences, University of Warwick, CV4 7AL, UK
| | - B. W. BOWEN
- Hawai’i Institute of Marine Biology, P.O. Box 1346, Kane’ohe, Hawai’i. 96744, USA
| | - P. CARR
- BF BIOT, Diego Garcia, BIOT, BFPO 485, UK
| | - C. A. CHEN
- Biodiversity Research Centre, Academia Sinica, 128 Academia Road, Nankang, Taipei, 115, Taiwan
| | - C. CLUBBE
- Royal Botanic Gardens Kew, Richmond, Surrey TW9 3AB, UK
| | - M. T. CRAIG
- Department of Marine Sciences, University of Puerto Rico, Mayaguez, P.O. Box 9000, Mayaguez, PR 00681
| | - R. EBINGHAUS
- Department for Environmental Chemistry, Helmholtz-Zentrum Geesthacht, Zentrum für Material- und Küstenforschung GmbH, Max-Planck-Straße 1 I 21502, Geesthacht I, Germany
| | - J. EBLE
- Hawai’i Institute of Marine Biology, P.O. Box 1346, Kane’ohe, Hawai’i. 96744, USA
| | - N. FITZSIMMONS
- Institute for Applied Ecology, University of Canberra, ACT 2601, Australia
| | - M. R. GAITHER
- Hawai’i Institute of Marine Biology, P.O. Box 1346, Kane’ohe, Hawai’i. 96744, USA
| | - C-H. GAN
- Biodiversity Research Centre, Academia Sinica, 128 Academia Road, Nankang, Taipei, 115, Taiwan
| | - M. GOLLOCK
- Zoological Society of London, Regents Park, London, NW1 4RY, UK
| | - N. GUZMAN
- Nestor Guzman: NAVFACFE PWD DG Environmental, PSC 466 Box 5, FPO AP, 96595-0005
| | - N. A. J. GRAHAM
- ARC Centre of Excellence for Coral Reef Studies, James Cook University, Townsville, QLD 4811, Australia
| | - A. HARRIS
- School of Life Sciences, University of Warwick, CV4 7AL, UK
| | - R. JONES
- Zoological Society of London, Regents Park, London, NW1 4RY, UK
| | - S. KESHAVMURTHY
- Biodiversity Research Centre, Academia Sinica, 128 Academia Road, Nankang, Taipei, 115, Taiwan
| | - H. KOLDEWEY
- Zoological Society of London, Regents Park, London, NW1 4RY, UK
| | - C. G. LUNDIN
- IUCN Marine Programme, Rue Mauverney 28, Gland, 1196, Switzerland
| | - J. A. MORTIMER
- Department of Biology, University of Florida, Gainesville, Florida, USA
| | - D. OBURA
- CORDIO East Africa, #9 Kibaki Flats, Kenyatta Beach, Bamburi Beach, P.O.BOX 10135, Mombasa 80101, Kenya
| | - M. PFEIFFER
- RWTH Aachen University, Templergraben 55, 52056 Aachen, Germany
| | - A. R. G. PRICE
- School of Life Sciences, University of Warwick, CV4 7AL, UK
| | - S. PURKIS
- National Coral Reef Institute, Nova Southeastern University, Oceanographic Center, 8000 North Ocean Drive, Dania Beach, FL 33004, USA
| | - P. RAINES
- Coral Cay Conservation, Elizabeth House, 39 York Road, London SE1 7NQ, UK
| | - J. W. READMAN
- Plymouth Marine Laboratory, Prospect Place, The Hoe, Plymouth, PL1 3DH, UK
| | - B. RIEGL
- National Coral Reef Institute, Nova Southeastern University, Oceanographic Center, 8000 North Ocean Drive, Dania Beach, FL 33004, USA
| | - A. ROGERS
- Department of Zoology, University of Oxford, The Tinbergen Building, South Parks Road, Oxford, OX1 3PS, UK
| | - M. SCHLEYER
- Oceanographic Research Institute, PO Box 10712, Marine Parade, Durban, 4056, South Africa
| | - M. R. D SEAWARD
- Division of Archaeological, Geographical and Environmental Sciences, University of Bradford, Bradford, West Yorkshire BD7 1DP, UK
| | | | - J. TAMELANDER
- UNEP Division of Environmental Policy Implementation, UN, Rajdamnern Nok Av., Bangkok, 10200, Thailand
| | - J. R. TURNER
- School of Ocean Sciences, Bangor University, Menai Bridge, Anglesey, LL59 5AB, UK
| | - S. VISRAM
- Biodiversity Research Centre, Academia Sinica, 128 Academia Road, Nankang, Taipei, 115, Taiwan
| | - C. VOGLER
- Department für Geo- und Umweltwissenschaften Paläontologie & Geobiologie, Ludwig- Maximilians-Universität, Richard-Wagner-Str.10, 80333, München, Germany
| | - S. VOGT
- Naval Facilities Engineering Command Far East, PSC 473, Box 1, FPO AP 96349, USA
| | - H. WOLSCHKE
- Department for Environmental Chemistry, Helmholtz-Zentrum Geesthacht, Zentrum für Material- und Küstenforschung GmbH, Max-Planck-Straße 1 I 21502, Geesthacht I, Germany
| | - J. M-C. YANG
- Biodiversity Research Centre, Academia Sinica, 128 Academia Road, Nankang, Taipei, 115, Taiwan
| | - S-Y. YANG
- Biodiversity Research Centre, Academia Sinica, 128 Academia Road, Nankang, Taipei, 115, Taiwan
| | - C. YESSON
- Zoological Society of London, Regents Park, London, NW1 4RY, UK
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Nur N, Jahncke J, Herzog MP, Howar J, Hyrenbach KD, Zamon JE, Ainley DG, Wiens JA, Morgan K, Ballance LT, Stralberg D. Where the wild things are: predicting hotspots of seabird aggregations in the California Current System. ECOLOGICAL APPLICATIONS : A PUBLICATION OF THE ECOLOGICAL SOCIETY OF AMERICA 2011; 21:2241-57. [PMID: 21939058 DOI: 10.1890/10-1460.1] [Citation(s) in RCA: 27] [Impact Index Per Article: 1.9] [Reference Citation Analysis] [Abstract] [MESH Headings] [Track Full Text] [Subscribe] [Scholar Register] [Indexed: 05/26/2023]
Abstract
Marine protected areas (MPAs) provide an important tool for conservation of marine ecosystems. To be most effective, these areas should be strategically located in a manner that supports ecosystem function. To inform marine spatial planning and support strategic establishment of MPAs within the California Current System, we identified areas predicted to support multispecies aggregations of seabirds ("hotspots"). We developed habitat-association models for 16 species using information from at-sea observations collected over an 11-year period (1997-2008), bathymetric data, and remotely sensed oceanographic data for an area from north of Vancouver Island, Canada, to the USA/Mexico border and seaward 600 km from the coast. This approach enabled us to predict distribution and abundance of seabirds even in areas of few or no surveys. We developed single-species predictive models using a machine-learning algorithm: bagged decision trees. Single-species predictions were then combined to identify potential hotspots of seabird aggregation, using three criteria: (1) overall abundance among species, (2) importance of specific areas ("core areas") to individual species, and (3) predicted persistence of hotspots across years. Model predictions were applied to the entire California Current for four seasons (represented by February, May, July, and October) in each of 11 years. Overall, bathymetric variables were often important predictive variables, whereas oceanographic variables derived from remotely sensed data were generally less important. Predicted hotspots often aligned with currently protected areas (e.g., National Marine Sanctuaries), but we also identified potential hotspots in Northern California/Southern Oregon (from Cape Mendocino to Heceta Bank), Southern California (adjacent to the Channel Islands), and adjacent to Vancouver Island, British Columbia, that are not currently included in protected areas. Prioritization and identification of multispecies hotspots will depend on which group of species is of highest management priority. Modeling hotspots at a broad spatial scale can contribute to MPA site selection, particularly if complemented by fine-scale information for focal areas.
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Affiliation(s)
- Nadav Nur
- PRBO Conservation Science, 3820 Cypress Drive, #11, Petaluma, California 94954, USA
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