Vulnerabilities and fisheries impacts: the uncertain future of manta and devil rays

Manta and devil rays of the subfamily Mobulinae (mobulids) are rarely studied, large, pelagic elasmobranchs, with all eight of well‐evaluated species listed on the IUCN Red List as threatened or near threatened. Mobulids have life history characteristics (matrotrophic reproduction, extremely low fec...

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Published inAquatic conservation Vol. 26; no. 3; pp. 562 - 575
Main Authors Croll, Donald A., Dewar, Heidi, Dulvy, Nicholas K., Fernando, Daniel, Francis, Malcolm P., Galván-Magaña, Felipe, Hall, Martin, Heinrichs, Shawn, Marshall, Andrea, Mccauley, Douglas, Newton, Kelly M., Notarbartolo-Di-Sciara, Giuseppe, O'Malley, Mary, O'Sullivan, John, Poortvliet, Marloes, Roman, Marlon, Stevens, Guy, Tershy, Bernie R., White, William T.
Format Journal Article
LanguageEnglish
Published Oxford Blackwell Publishing Ltd 01.06.2016
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Abstract Manta and devil rays of the subfamily Mobulinae (mobulids) are rarely studied, large, pelagic elasmobranchs, with all eight of well‐evaluated species listed on the IUCN Red List as threatened or near threatened. Mobulids have life history characteristics (matrotrophic reproduction, extremely low fecundity, and delayed age of first reproduction) that make them exceptionally susceptible to overexploitation. Targeted and bycatch mortality from fisheries is a globally important and increasing threat, and targeted fisheries are incentivized by the high value of the global trade in mobulid gill plates. Fisheries bycatch of mobulids is substantial in tuna purse seine fisheries. Thirteen fisheries in 12 countries specifically targeting mobulids, and 30 fisheries in 23 countries with mobulid bycatch were identified. Aside from a few recently enacted national restrictions on capture, there is no comprehensive monitoring, assessment or control of mobulid fisheries or bycatch. Recent listing through the Convention on the International Trade in Endangered Species (CITES) may benefit mobulids of the genus Manta (manta rays), but none of the mobulids in the genus Mobula (devil rays) are protected. The relative economic costs of catch mitigation are minimal, particularly compared with a broad range of other, more complicated, marine conservation issues. Copyright © 2015 John Wiley & Sons, Ltd.
AbstractList Manta and devil rays of the subfamily Mobulinae (mobulids) are rarely studied, large, pelagic elasmobranchs, with all eight of well‐evaluated species listed on the IUCN Red List as threatened or near threatened. Mobulids have life history characteristics (matrotrophic reproduction, extremely low fecundity, and delayed age of first reproduction) that make them exceptionally susceptible to overexploitation. Targeted and bycatch mortality from fisheries is a globally important and increasing threat, and targeted fisheries are incentivized by the high value of the global trade in mobulid gill plates. Fisheries bycatch of mobulids is substantial in tuna purse seine fisheries. Thirteen fisheries in 12 countries specifically targeting mobulids, and 30 fisheries in 23 countries with mobulid bycatch were identified. Aside from a few recently enacted national restrictions on capture, there is no comprehensive monitoring, assessment or control of mobulid fisheries or bycatch. Recent listing through the Convention on the International Trade in Endangered Species (CITES) may benefit mobulids of the genus Manta (manta rays), but none of the mobulids in the genus Mobula (devil rays) are protected. The relative economic costs of catch mitigation are minimal, particularly compared with a broad range of other, more complicated, marine conservation issues. Copyright © 2015 John Wiley & Sons, Ltd.
Manta and devil rays of the subfamily Mobulinae (mobulids) are rarely studied, large, pelagic elasmobranchs, with all eight of well‐evaluated species listed on the IUCN Red List as threatened or near threatened. Mobulids have life history characteristics (matrotrophic reproduction, extremely low fecundity, and delayed age of first reproduction) that make them exceptionally susceptible to overexploitation. Targeted and bycatch mortality from fisheries is a globally important and increasing threat, and targeted fisheries are incentivized by the high value of the global trade in mobulid gill plates. Fisheries bycatch of mobulids is substantial in tuna purse seine fisheries. Thirteen fisheries in 12 countries specifically targeting mobulids, and 30 fisheries in 23 countries with mobulid bycatch were identified. Aside from a few recently enacted national restrictions on capture, there is no comprehensive monitoring, assessment or control of mobulid fisheries or bycatch. Recent listing through the Convention on the International Trade in Endangered Species (CITES) may benefit mobulids of the genus Manta (manta rays), but none of the mobulids in the genus Mobula (devil rays) are protected. The relative economic costs of catch mitigation are minimal, particularly compared with a broad range of other, more complicated, marine conservation issues. Copyright © 2015 John Wiley & Sons, Ltd.
1. Manta and devil rays of the subfamily Mobulinae (mobulids) are rarely studied, large, pelagic elasmobranchs, with all eight of well-evaluated species listed on the IUCN Red List as threatened or near threatened. 2. Mobulids have life history characteristics (matrotrophic reproduction, extremely low fecundity, and delayed age of first reproduction) that make them exceptionally susceptible to overexploitation. 3. Targeted and bycatch mortality from fisheries is a globally important and increasing threat, and targeted fisheries are incentivized by the high value of the global trade in mobulid gill plates. 4. Fisheries bycatch of mobulids is substantial in tuna purse seine fisheries. 5. Thirteen fisheries in 12 countries specifically targeting mobulids, and 30 fisheries in 23 countries with mobulid bycatch were identified. 6. Aside from a few recently enacted national restrictions on capture, there is no comprehensive monitoring, assessment or control of mobulid fisheries or bycatch. Recent listing through the Convention on the International Trade in Endangered Species (CITES) may benefit mobulids of the genus Manta (manta rays), but none of the mobulids in the genus Mobula (devil rays) are protected. 7. The relative economic costs of catch mitigation are minimal, particularly compared with a broad range of other, more complicated, marine conservation issues. Copyright copyright 2015 John Wiley & Sons, Ltd.
Manta and devil rays of the subfamily Mobulinae (mobulids) are rarely studied, large, pelagic elasmobranchs, with all eight of well‐evaluated species listed on the IUCN Red List as threatened or near threatened. Mobulids have life history characteristics (matrotrophic reproduction, extremely low fecundity, and delayed age of first reproduction) that make them exceptionally susceptible to overexploitation. Targeted and bycatch mortality from fisheries is a globally important and increasing threat, and targeted fisheries are incentivized by the high value of the global trade in mobulid gill plates. Fisheries bycatch of mobulids is substantial in tuna purse seine fisheries. Thirteen fisheries in 12 countries specifically targeting mobulids, and 30 fisheries in 23 countries with mobulid bycatch were identified. Aside from a few recently enacted national restrictions on capture, there is no comprehensive monitoring, assessment or control of mobulid fisheries or bycatch. Recent listing through the Convention on the International Trade in Endangered Species (CITES) may benefit mobulids of the genus Manta (manta rays), but none of the mobulids in the genus Mobula (devil rays) are protected. The relative economic costs of catch mitigation are minimal, particularly compared with a broad range of other, more complicated, marine conservation issues. Copyright © 2015 John Wiley & Sons, Ltd.
1. Manta and devil rays of the subfamily Mobulinae (mobulids) are rarely studied, large, pelagic elasmobranchs, with all eight of well-evaluated species listed on the IUCN Red List as threatened or near threatened. 2. Mobulids have life history characteristics (matrotrophic reproduction, extremely low fecundity, and delayed age of first reproduction) that make them exceptionally susceptible to overexploitation. 3. Targeted and bycatch mortality from fisheries is a globally important and increasing threat, and targeted fisheries are incentivized by the high value of the global trade in mobulid gill plates. 4. Fisheries bycatch of mobulids is substantial in tuna purse seine fisheries. 5. Thirteen fisheries in 12 countries specifically targeting mobulids, and 30 fisheries in 23 countries with mobulid bycatch were identified. 6. Aside from a few recently enacted national restrictions on capture, there is no comprehensive monitoring, assessment or control of mobulid fisheries or bycatch. Recent listing through the Convention on the International Trade in Endangered Species (CITES) may benefit mobulids of the genus Manta (manta rays), but none of the mobulids in the genus Mobula (devil rays) are protected. 7. The relative economic costs of catch mitigation are minimal, particularly compared with a broad range of other, more complicated, marine conservation issues. Copyright (C) 2015 John Wiley & Sons, Ltd.
Author Fernando, Daniel
Dewar, Heidi
Dulvy, Nicholas K.
Notarbartolo-Di-Sciara, Giuseppe
Poortvliet, Marloes
Stevens, Guy
Croll, Donald A.
Marshall, Andrea
Mccauley, Douglas
Hall, Martin
Tershy, Bernie R.
O'Malley, Mary
White, William T.
Heinrichs, Shawn
Galván-Magaña, Felipe
Roman, Marlon
Newton, Kelly M.
Francis, Malcolm P.
O'Sullivan, John
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  organization: Coastal Conservation Action Lab, University of California, Santa Cruz
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  organization: Biological Sciences, Simon Fraser University
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  organization: Department of Biology and Environmental Science, Linnaeus University
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  organization: Centro Interdisciplinario de Ciencias Marinas
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  fullname: Heinrichs, Shawn
  organization: Blue Sphere Media LLC
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  fullname: Marshall, Andrea
  organization: Marine Megafauna Foundation
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  surname: Mccauley
  fullname: Mccauley, Douglas
  organization: Department of Ecology, Evolution, and Marine Biology, University of California, Santa Barbara
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  surname: Newton
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  organization: Coastal Conservation Action Lab, University of California, Santa Cruz
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  givenname: Mary
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  organization: Manta Trust
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  organization: Monterey Bay Aquarium
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  organization: Coastal Conservation Action Lab, University of California, Santa Cruz
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  organization: Manta Trust
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  organization: Coastal Conservation Action Lab, University of California, Santa Cruz
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  givenname: William T.
  surname: White
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  organization: Marine and Atmospheric Research, Commonwealth Scientific and Industrial Research Organization
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References Hutchings J, Myers R. 2012. Life-history correlates of extinction risk and recovery potential. Ecological Applications 22: 1061-1067.
Dulvy NK, Baum JK, Clark S, Compagno LJV, Cortes E, Domingo A, Fordham S, Fowler S, Francis MP, Gibson C. 2008. You can swim but you can't hide: the global status and conservation of oceanic pelagic sharks and rays. Aquatic Conservation: Marine and Freshwater Ecosystems 18: 459-482.
Marshall AD, Bennett MB. 2010. Reproductive ecology of the reef manta ray Manta alfredi in southern Mozambique. Journal Fisheries Biology 77: 169-190.
Rohner C, Pierce S, Marshall A, Weeks S, Bennett M, Richardson A. 2013. Trends in sightings and environmental influences on a coastal aggregation of manta rays and whale sharks. Marine Ecology Progress Series 482: 153-168.
Poortvliet M, Hoarau G. 2013. The complete mitochondrial genome of the Spinetail Devilray, Mobula japanica. Mitochondrial DNA 24: 28-30.
Ward-Paige CA, Davis B, Worm B. 2013. Global population trends and human use patterns of Manta and Mobula rays. PLoS ONE 8:e74835.
Poortvliet M, Olsen JL, Croll DA, Bernardi G, Newton K, Kollias S, O'Sullivan J, Fernando D, Stevens G, Galván-Magaña F, et al. 2015. A dated molecular phylogeny of manta and devil rays (Mobulidae) based on mitogenome and nuclear sequences. Molecular Phylogenetics and Evolution 83: 72-85.
Amandè MJ, Ariz J, Chassot E, Chavance P, Delgado de Molina A, Gaertner D, Murua H, Pianet R, Ruiz J. 2011. By-catch and discards of the European purse seine tuna fishery in the Atlantic Ocean: estimation and characteristics for 2008 and 2009. Collective Volume Scientific Papers ICCAT 66: 2113-2120.
Poortvliet M, Galván-Magaña F, Bernardi G, Croll D, Olsen JL. 2011. Isolation and characterization of twelve microsatellite loci for the Japanese Devilray (Mobula japanica). Conservation Genetic Resources 3: 733-735.
Rajapackiam S, Mohan S, Rudramurthy N. 2007. Utilization of gill rakers of lesser devil ray Mobula diabolus - a new fish byproduct. Marine Fisheries Information Service Technical and Extension Series 191: 22-23.
Vaillant L, Diguet L. 1898. Sur le Cephaloptere du Golfe de Californie. Bulletin du Museum National d'Histoire Naturelle 4: 127-128.
Poisson F, Séret B, Vernet AL, Goujon M, Dagorn L. 2014. Collaborative research: Development of a manual on elasmobranch handling and release best practices in tropical tuna purse-seine fisheries. Marine Policy 44: 312-320.
Raje SG, Zacharia PU, Gopal-Raje S. 2009. Investigations on fishery and biology of nine species of rays in Mumbai waters. Indian Journal Fisheries 56: 95-101.
Adimey NM, Hudak CA, Powell JR, Bassos-Hull K, Foley A, Farmer NA, White L, Minch K. 2014. Fishery gear interactions from stranded bottlenose dolphins, Florida manatees and sea turtles in Florida, USA. Marine Pollution Bulletin 81: 103-115.
Anderson RC, Adam MS, Goes JI. 2011. From monsoons to mantas: seasonal distribution of Manta alfredi in the Maldives. Fisheries Oceanography 20: 104-113.
O'Malley MP, Lee-Brooks K, Medd HB. 2013. The global economic impact of manta ray watching tourism. PLoS ONE 8: e65051.
Roosevelt T. 1917. Harpooning Devilfish. Scribner's Magazine 62: 293-305.
Sumpton WD, Taylor SM, Gribble NA, McPherson G, Ham T. 2011. Gear selectivity of large-mesh nets and drumlines used to catch sharks in the Queensland Shark Control Program. African Journal of Marine Science 33: 37-43.
Dewar H, Mous P, Domeier M, Muljadi A, Pet J, Whitty J. 2008. Movements and site fidelity of the giant manta ray, Manta birostris, in the Komodo Marine Park, Indonesia. Marine Biology 155: 121-133.
Graham RT, Witt MJ, Castellanos DW, Remolina F, Maxwell S, Godley BJ, Hawkes LA. 2012. Satellite tracking of manta rays highlights challenges to their conservation. PLoS ONE 7: e36834.
Kashiwagi T, Broderick D, Lance SL, Bennett MB, Ovenden JR. 2012. Development and characterization of ten microsatellite loci for the reef manta ray Manta alfredi. Conservation Genetic Resources 4:1055-1058 .
Pianet R, Nordstrom V, Damiano A, Delgado de Molina A, Ariz J, Sabate I, Kouassi Y, Sow F. 2010. Statistiques de la pêcherie thonière Europeenne et assimilée dans l'Ocean Atlantique durant la période 1991-2008. Collective Volume Scientific Papers ICCAT 65: 561-591.
Stevens JD, Bonfil R, Dulvy NK, Walker PA. 2000. The effects of fishing on sharks, rays, and chimaeras (chondrichthyans), and the implications for marine ecosystems. ICES Journal Marine Science 57: 476-494.
Couturier LIE, Marshall AD, Jaine FR, Kashiwagi T, Pierce SJ, Townsend KA, Weeks SJ, Bennett MB, Richardson AJ. 2012. Biology, ecology and conservation of the Mobulidae. Journal of Fish Biology 80: 1075-1119.
Couturier LIE, Bennett MB, Richardson AJ. 2013. Mystery of giant rays off the Gaza strip solved. Oryx 47: 480.
McCauley DJ, DeSalles PA, Young HS, Papastamatiou YP, Caselle JE, Deakos MH, Gardner JPA, Garton DW, Collen JD, Micheli F. 2014. Reliance of mobile species on sensitive habitats: a case study of manta rays (Manta alfredi) and lagoons. Marine Biology 161: 1987-1998.
Hinojosa-Alvarez S, Díaz-Jaimes P, Marcet-Houben M, Gabaldón T. 2015. The complete mitochondrial genome of the Giant Manta Ray, Manta birostris. Mitochondrial DNA 26: 787-788.
Amandè MJ, Ariz J, Chassot E, Delgado de Molina A, Gaertner D, Murua H, Pianet R, Ruiz J, Chavance P. 2010. Bycatch of the European purse seine tuna fishery in the Atlantic Ocean for the 2003-2007 period. Aquatic Living Resources 23: 353-362.
Gill T. 1908. The Story of the Devil Fish. Smithsonian Miscellaneous Collections 52: 155-180.
Cuevas-Zimbrón E, Sosa-Nishizaki O, Pérez-Jiménez JC, O'Sullivan JB. 2012. An analysis of the feasibility of using caudal vertebrae for ageing the spinetail devilray, Mobula japanica (Müller and Henle, 1841). Environmental Biology of Fishes 96: 907-914.
White W, Giles J, Potter I. 2006a. Data on the bycatch fishery and reproductive biology of mobulid rays (Myliobatiformes) in Indonesia. Fisheries Research 82: 65-73.
Holcer D, Lazar B, Mackelworth P, Fortuna CM. 2013. Rare or just unknown? The occurrence of the giant devil ray (Mobula mobular) in the Adriatic Sea. Journal of Applied Ichthyology 29: 139-144.
Croll DA, Newton KM, Weng K, Galvan-Magana F, O'Sullivan J, Dewar H. 2012. Movement and habitat use by the spine-tail devil ray in the Eastern Pacific Ocean. Marine Ecology Progress Series 465: 193-200.
Dulvy NK, Pardo SA, Simpfendorfer CA, Carlson JK. 2014. Diagnosing the dangerous demography of manta rays using life history theory. Peer J 2: e400.
Paulin CD, Habib G, Carey CL, Swanson PM, Voss GJ. 1982. New records of Mobula japanica and Masturus lanceolatus, and further records of Luvaris imperialis. New Zealand Journal of Marine and Freshwater Research 16: 11-17.
Berman-Kowalewski M, Gulland FMD, Wilkin S, Calambokidis J, Mate B, Cordaro J, Rotstein D, St. Leger J, Collins P, Fahy K, Dover S. 2010. Association between blue whale (Balaenoptera musculus) mortality and ship strikes along the California coast. Aquatic Mammals 36: 59-66.
Dudley SFJ, Cliff G. 1993. Some effects of shark nets in the Natal nearshore environment. Environmental Biology of Fishes 36: 243-255.
Deakos M, Baker J, Bejder L. 2011. Characteristics of a manta ray Manta alfredi population off Maui, Hawaii, and implications for management. Marine Ecology Progress Series 429: 245-260.
Mohanraj G, Rajapackiam S, Mohan S, Batcha H, Gomathy S. 2009. Status of Elasmobranchs Fishery in Chennai, India. Asian Fisheries Science 22: 607-615.
Baker CS, Palumbi SR. 1994. Which whales are hunted? A molecular genetics approach to monitoring whaling. Science 265: 1538-1539.
Romanov EV. 2002. Bycatch in the tuna purse-seine fisheries of the western Indian Ocean. Fisheries Bulletin 100: 90-105.
Clarke SC, Manussen JE, Abercrombie DL, McAllister MK, Shivji MS. 2006. Identification of shark species composition and proportion in the Hong Kong shark fin market based on molecular genetics and trade records. Conservation Biology 20: 201-211.
Lewison RL, Crowder LB, Read AJ, Freeman SA. 2004. Understanding impacts of fisheries bycatch on marine megafauna. Trends Ecology Evolution 19: 598-604.
Marshall AD, Compagno LJV, Bennett MB. 2009. Redescription of the genus Manta with resurrection of Manta alfredi (Krefft, 1868)(Chondrichthyes; Myliobatoidei; Mobulidae). Zootaxa 2301: 1-28.
Gilman EL. 2011. Bycatch governance and best practice mitigation technology in global tuna fisheries. Marine Policy 35: 590-609.
Owens IPF, Bennett PM. 2000. Ecological basis of extinction risk in birds: habitat loss versus human persecution and introduced predators. Proceeding of the National Acadamy Science USA 97: 12144.
Elliott W. 1846. Carolina Sports: by Land and Water: Including Incidents of Devil-Fishing, Derby and Jackson: New York, NY.
Canese S, Cardinali A, Romeo T, Giusti M, Salvati E, Angiolillo M, Greco S. 2011. Diving behavior of the giant devil ray in the Mediterranean Sea. Endangered Species Research 14: 171-176.
García VB, Lucifor LO, Myers RA. 2008. The importance of habitat and life history to extinction risk in sharks, skates, rays and chimaeras. Proceeding of the Royal Society of London B 275: 83-89.
Notarbartolo-di-Sciara G. 1988. Natural history of the rays of the genus Mobula in the Gulf of California. Fisheries Bulletin 86: 45-66.
2013; 29
1982; 16
2013; 24
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2013; 482
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2015; 83
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2010; 36
2012; 465
2012
2011
2006b
2010
2008; 18
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2008
2007
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2011; 35
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2002
2011; 3
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2015; 26
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References_xml – reference: Graham RT, Witt MJ, Castellanos DW, Remolina F, Maxwell S, Godley BJ, Hawkes LA. 2012. Satellite tracking of manta rays highlights challenges to their conservation. PLoS ONE 7: e36834.
– reference: Stevens JD, Bonfil R, Dulvy NK, Walker PA. 2000. The effects of fishing on sharks, rays, and chimaeras (chondrichthyans), and the implications for marine ecosystems. ICES Journal Marine Science 57: 476-494.
– reference: Vaillant L, Diguet L. 1898. Sur le Cephaloptere du Golfe de Californie. Bulletin du Museum National d'Histoire Naturelle 4: 127-128.
– reference: Canese S, Cardinali A, Romeo T, Giusti M, Salvati E, Angiolillo M, Greco S. 2011. Diving behavior of the giant devil ray in the Mediterranean Sea. Endangered Species Research 14: 171-176.
– reference: Dudley SFJ, Cliff G. 1993. Some effects of shark nets in the Natal nearshore environment. Environmental Biology of Fishes 36: 243-255.
– reference: Deakos M, Baker J, Bejder L. 2011. Characteristics of a manta ray Manta alfredi population off Maui, Hawaii, and implications for management. Marine Ecology Progress Series 429: 245-260.
– reference: Sumpton WD, Taylor SM, Gribble NA, McPherson G, Ham T. 2011. Gear selectivity of large-mesh nets and drumlines used to catch sharks in the Queensland Shark Control Program. African Journal of Marine Science 33: 37-43.
– reference: Berman-Kowalewski M, Gulland FMD, Wilkin S, Calambokidis J, Mate B, Cordaro J, Rotstein D, St. Leger J, Collins P, Fahy K, Dover S. 2010. Association between blue whale (Balaenoptera musculus) mortality and ship strikes along the California coast. Aquatic Mammals 36: 59-66.
– reference: Kashiwagi T, Broderick D, Lance SL, Bennett MB, Ovenden JR. 2012. Development and characterization of ten microsatellite loci for the reef manta ray Manta alfredi. Conservation Genetic Resources 4:1055-1058 .
– reference: Gilman EL. 2011. Bycatch governance and best practice mitigation technology in global tuna fisheries. Marine Policy 35: 590-609.
– reference: Poortvliet M, Galván-Magaña F, Bernardi G, Croll D, Olsen JL. 2011. Isolation and characterization of twelve microsatellite loci for the Japanese Devilray (Mobula japanica). Conservation Genetic Resources 3: 733-735.
– reference: Owens IPF, Bennett PM. 2000. Ecological basis of extinction risk in birds: habitat loss versus human persecution and introduced predators. Proceeding of the National Acadamy Science USA 97: 12144.
– reference: Clarke SC, Manussen JE, Abercrombie DL, McAllister MK, Shivji MS. 2006. Identification of shark species composition and proportion in the Hong Kong shark fin market based on molecular genetics and trade records. Conservation Biology 20: 201-211.
– reference: Cuevas-Zimbrón E, Sosa-Nishizaki O, Pérez-Jiménez JC, O'Sullivan JB. 2012. An analysis of the feasibility of using caudal vertebrae for ageing the spinetail devilray, Mobula japanica (Müller and Henle, 1841). Environmental Biology of Fishes 96: 907-914.
– reference: Paulin CD, Habib G, Carey CL, Swanson PM, Voss GJ. 1982. New records of Mobula japanica and Masturus lanceolatus, and further records of Luvaris imperialis. New Zealand Journal of Marine and Freshwater Research 16: 11-17.
– reference: Pianet R, Nordstrom V, Damiano A, Delgado de Molina A, Ariz J, Sabate I, Kouassi Y, Sow F. 2010. Statistiques de la pêcherie thonière Europeenne et assimilée dans l'Ocean Atlantique durant la période 1991-2008. Collective Volume Scientific Papers ICCAT 65: 561-591.
– reference: Poortvliet M, Hoarau G. 2013. The complete mitochondrial genome of the Spinetail Devilray, Mobula japanica. Mitochondrial DNA 24: 28-30.
– reference: Dulvy NK, Pardo SA, Simpfendorfer CA, Carlson JK. 2014. Diagnosing the dangerous demography of manta rays using life history theory. Peer J 2: e400.
– reference: Croll DA, Newton KM, Weng K, Galvan-Magana F, O'Sullivan J, Dewar H. 2012. Movement and habitat use by the spine-tail devil ray in the Eastern Pacific Ocean. Marine Ecology Progress Series 465: 193-200.
– reference: Amandè MJ, Ariz J, Chassot E, Chavance P, Delgado de Molina A, Gaertner D, Murua H, Pianet R, Ruiz J. 2011. By-catch and discards of the European purse seine tuna fishery in the Atlantic Ocean: estimation and characteristics for 2008 and 2009. Collective Volume Scientific Papers ICCAT 66: 2113-2120.
– reference: Rohner C, Pierce S, Marshall A, Weeks S, Bennett M, Richardson A. 2013. Trends in sightings and environmental influences on a coastal aggregation of manta rays and whale sharks. Marine Ecology Progress Series 482: 153-168.
– reference: Romanov EV. 2002. Bycatch in the tuna purse-seine fisheries of the western Indian Ocean. Fisheries Bulletin 100: 90-105.
– reference: Lewison RL, Crowder LB, Read AJ, Freeman SA. 2004. Understanding impacts of fisheries bycatch on marine megafauna. Trends Ecology Evolution 19: 598-604.
– reference: Mohanraj G, Rajapackiam S, Mohan S, Batcha H, Gomathy S. 2009. Status of Elasmobranchs Fishery in Chennai, India. Asian Fisheries Science 22: 607-615.
– reference: White W, Giles J, Potter I. 2006a. Data on the bycatch fishery and reproductive biology of mobulid rays (Myliobatiformes) in Indonesia. Fisheries Research 82: 65-73.
– reference: Gill T. 1908. The Story of the Devil Fish. Smithsonian Miscellaneous Collections 52: 155-180.
– reference: Poortvliet M, Olsen JL, Croll DA, Bernardi G, Newton K, Kollias S, O'Sullivan J, Fernando D, Stevens G, Galván-Magaña F, et al. 2015. A dated molecular phylogeny of manta and devil rays (Mobulidae) based on mitogenome and nuclear sequences. Molecular Phylogenetics and Evolution 83: 72-85.
– reference: Amandè MJ, Ariz J, Chassot E, Delgado de Molina A, Gaertner D, Murua H, Pianet R, Ruiz J, Chavance P. 2010. Bycatch of the European purse seine tuna fishery in the Atlantic Ocean for the 2003-2007 period. Aquatic Living Resources 23: 353-362.
– reference: Baker CS, Palumbi SR. 1994. Which whales are hunted? A molecular genetics approach to monitoring whaling. Science 265: 1538-1539.
– reference: Elliott W. 1846. Carolina Sports: by Land and Water: Including Incidents of Devil-Fishing, Derby and Jackson: New York, NY.
– reference: Dulvy NK, Baum JK, Clark S, Compagno LJV, Cortes E, Domingo A, Fordham S, Fowler S, Francis MP, Gibson C. 2008. You can swim but you can't hide: the global status and conservation of oceanic pelagic sharks and rays. Aquatic Conservation: Marine and Freshwater Ecosystems 18: 459-482.
– reference: Ward-Paige CA, Davis B, Worm B. 2013. Global population trends and human use patterns of Manta and Mobula rays. PLoS ONE 8:e74835.
– reference: Hutchings J, Myers R. 2012. Life-history correlates of extinction risk and recovery potential. Ecological Applications 22: 1061-1067.
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Snippet Manta and devil rays of the subfamily Mobulinae (mobulids) are rarely studied, large, pelagic elasmobranchs, with all eight of well‐evaluated species listed on...
Manta and devil rays of the subfamily Mobulinae (mobulids) are rarely studied, large, pelagic elasmobranchs, with all eight of well-evaluated species listed on...
1. Manta and devil rays of the subfamily Mobulinae (mobulids) are rarely studied, large, pelagic elasmobranchs, with all eight of well-evaluated species listed...
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proquest
crossref
wiley
istex
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StartPage 562
SubjectTerms Akvatisk ekologi
Aquatic Ecology
bycatch
coastal
conservation evaluation
Convention on International Trade in Endangered Species
economic costs
Elasmobranchii
endangered species
fecundity
fish
fishing
Freshwater
life history
Manta
Marine
Mobula
monitoring
mortality
ocean
Thunnus
trade
tuna
Title Vulnerabilities and fisheries impacts: the uncertain future of manta and devil rays
URI https://api.istex.fr/ark:/67375/WNG-L7LNXRW7-Z/fulltext.pdf
https://onlinelibrary.wiley.com/doi/abs/10.1002%2Faqc.2591
https://www.proquest.com/docview/1797270911
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Volume 26
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