|Scientific Name:||Lamna nasus (Northwest Atlantic subpopulation)|
|Species Authority:||(Bonnaterre, 1788)|
See Lamna nasus
|Red List Category & Criteria:||Endangered A1abd ver 3.1|
|Assessor(s):||Stevens, J., Fowler, S.L., Soldo, A., McCord, M., Baum, J., Acuña, E. & Domingo, A.|
|Reviewer(s):||Cavanagh, R.D., Heupel, M. & Simpfendorfer, C. (Shark Red List Authority)|
The porbeagle is a wide-ranging, coastal and oceanic shark, but with apparently little exchange between adjacent populations. Low reproductive capacity and high commercial value (in target and incidental fisheries) of mature and immature age classes makes this species highly vulnerable to over-exploitation and population depletion. This depletion, despite variations in availability of data and degree of depletion between the northern and southern hemispheres, is considered to meet Vulnerable criteria globally. The eastern and western North Atlantic populations have both been seriously over-exploited by directed longline fisheries. Collapse of the Northeast Atlantic population led to intensive target fishing in the well-documented Northwest Atlantic fishery in the 1960s, with most of the virgin biomass removed in just six years. Renewed target fishing in the 1990s led to a further population decline to ~11–17% of virgin biomass within the three generation period for this species. Recently improved management in the Northwest Atlantic should now help stocks to recover, however the Northeast Atlantic population has been subject to unrestricted fishing pressure ever since its earlier crash. Data are lacking, but stock depletion is considered to be much greater than in the Northwest Atlantic. Longline tuna and swordfish fleets in the southern hemisphere take a significant partially-utilised bycatch. Only limited trend data are available, including over 90% declines in landings by the Uruguayan longline fleet in the southwest Atlantic.
|Range Description:||The porbeagle shark is a wide-ranging coastal and oceanic species found in temperate and cold-temperate waters worldwide (1 to 18°C, 0 to 370 m), more common on continental shelves. Coastal and oceanic, amphitemperate, with centres of distribution in the North Atlantic and in a circumglobal band of temperate water of the southern Atlantic, southern Indian Ocean, southern Pacific and Antarctic Ocean (Compagno 2001). In the Southwest Atlantic Ocean it is found below 26°S (A. Domingo, pers.comm.), in the Southeastern Pacific, between 23 and 37°S (E. Acuña, pers. comm). Tagging studies in the Northwest Atlantic have shown mainly short to moderate distances of up to 1,500 km along continental shelves (Francis et al. in press). Distances travelled by 143 porbeagle tagged in a US study ranged 4 to 1,005 nautical miles (nm), with a mean distance of 234 nm, with over 90% moving less than 500 nm from their original tagging location (Kohler et al. 2002). Porbeagles tagged off southern England have been recaptured off Spain, Denmark and Norway (2,370 km away), and a porbeagle tagged in Ireland travelled 4,260 km Kohler and Turner 2001), suggesting mixing throughout their range in the Northeast Atlantic (Stevens 1976, 1990). According to the Canadian Department of Fisheries and Oceans (DFO 2001a), mature porbeagle sharks are rarely seen in winter and spring, with monthly catches exhibiting a seasonal and sex-specific migration of mature sharks towards the southern Newfoundland mating grounds in spring. The birthing grounds for the porbeagle shark in the Northwest Atlantic remain unknown (DFO 2001a). There is little known about the porbeagle shark in subequatorial Africa. No information on mating or nursery grounds is available. Porbeagles in the Northwest Atlantic make annual migrations along the coast between the Gulf of Maine and Newfoundland (Campana et al. 1999, Campana and Joyce 2004).|
Native:Bermuda; Canada (Newfoundland I, Nova Scotia); Greenland; United States (Maine, Massachusetts, New Jersey, New York, Rhode Island)
|FAO Marine Fishing Areas:||
Atlantic – northwest; Atlantic – western central
|Range Map:||Click here to open the map viewer and explore range.|
North Atlantic tagging studies (DFO 1999, Kohler et al. 2002, Stevens 1990) indicate only one trans-Atlantic movement (Kohler and Turner 2001), implying that the two north Atlantic populations are distinct. There is no evidence of genetic exchange between the North Atlantic and the Southern Hemisphere population(s), which are separated by warm water. The number of subpopulations in the southern oceans is unknown.
Biomass of the Northwest Atlantic porbeagle population was estimated at 4,409 t (11% of virgin biomass) and female spawners estimated at 6,075 (10% of the virgin abundance) (Campana et al. 2001).
Populations studied in the North Atlantic and Mediterranean segregate by size and sex. Although adults are very rare in the Mediterranean, it appears to be a nursery ground.
|Habitat and Ecology:||
This section is taken mainly from Stevens (in press) species assessment for Lamna nasus (in Fowler et al. in press).
The porbeagle reaches a maximum reported size of 355 cm TL (Francis et al. in press). Males mature at about 165 cm TL in the South Pacific and 195 cm TL in the North Atlantic. Females mature at about 195 cm TL in the South Pacific and 245 cm TL in the North Atlantic (Jensen et al. 2002, Francis and Duffy 2005, Francis et al. in press).
Reproduction is oophagous with litters of 1 to 5 pups (average four) produced, which are 68 to 78 cm TL at birth (Compagno 1984a, Gauld 1989, DFO 2001a, Francis and Stevens 2000, Francis et al. in press). Aasen (1963) estimated that the gestation period was about eight months in the North Atlantic and that individual females breed each year. However, Shann (1923) found two distinct size groups of embryos present in the December to February period and suggested that gestation may last 18 to 24 months. Gauld (1989) noted that a resting period may be present between parturition and fertilisation. Francis and Stevens (2000), Jensen et al. (2002) and Francis et al. (in press) estimate an 8–9 month gestation period. Birth occurs in spring off Europe, spring-summer off North America and winter in Australasia (Aasen 1963, Francis and Stevens 2000, Jensen et al. 2002) and the Eastern Pacific off Chile (Acuña et al. unpublished data).
Natanson et al. (2002) and Campana et al. (2002) examined age and growth in the North West Atlantic population and reported a maximum age of 26 years. However they estimated longevity might be as high as 46 years in an unfished population. Ages at 50% maturity for North Atlantic males and females are 8 and 13 years respectively (Jensen et al. 2002).
Porbeagles feed mostly on teleost fish, both pelagic and demersal species, and on cephalopods (Compagno 1984a). In the North West Atlantic, pelagic fish and squid are the main diet in deep water, and pelagic and demersal fish are important in their diet in shallow water (Joyce et al. 2002).
Like other mackerel sharks, the porbeagle is endothermic, maintaining its muscle and visceral temperatures above that of the surrounding seawater. It prefers temperatures below 18°C and has been caught in water temperatures as low as 2°C on the bottom (3°C on the surface) at high latitudes (Svetlov 1978). The preferred temperature range in the Northwest Atlantic is 5 to 10°C (Campana and Joyce 2004).
Porbeagle fishing in the Northwest Atlantic started in 1961, when the fleet of Norwegian shark longliners began operating off the coast of New England and Newfoundland after the Northeast Atlantic stocks had been depleted. Catches increased rapidly from about 1,900 t in 1961 to more than 9,000 t in 1964. By 1965 many of the vessels had switched to other species or moved to other grounds because of the population decline. The fishery collapsed after only six years, landing less than 1,000 t in 1970. Smaller landings were also reported by Faeroese fishing vessels from around the same time and throughout the 1970s and 1980s. Norwegian and Faeroese fleets have been excluded from Canadian waters since the establishment of Canada’s EEZ in 1995. Canadian and US authorities reported all landings after 1995. Porbeagle sharks are now taken almost exclusively by a Canadian directed longline fishery. Bycatch in swordfish longline fisheries and various inshore fisheries are minimal, rarely exceeding 40 t in recent years (DFO 2001a).
Following the collapse of the fishery in the 1960s, it took ~25 years for recovery to ~30% of virgin biomass to take place. Three Canadian vessels entered the targeted Northwest Atlantic fishery in 1994. Catches of 1,000 to 2,000 t/year throughout much of the 1990s reduced population levels to a new low in under ten years: the average size of sharks and catch rates (number/hook) were the smallest on record in 1999 and 2000. By 2000, catch rates of mature sharks were reduced to 10% of the 1992 peak, and immature catch rates to 30% of the 1991 peak. The biomass in 2000 was estimated as 11 to 17% of virgin biomass and fully recruited F estimated as 0.26 (DFO 2001a). The current porbeagle population is seriously depleted and will require a greatly reduced fishing mortality if recovery is to occur (DFO 2001). The 2001 stock assessment by the Canadian Department of Fisheries states: ‘An annual catch of 200 to 250 t would correspond to fishing at about MSY and would allow population growth.’ Following this advice, the Canadian quota was reduced to 250 t for the period 2002 to 2007 to allow population growth and recovery. There is a small quota (92 t) for porbeagle in the US EEZ.
The 1995 Fisheries Management Plan for pelagic sharks in Atlantic Canada established precautionary catch levels of 1,500 t for porbeagle in the target shark fishery. License limitation, a ban on finning, restrictions on gear, area and seasons, bycatch limits and restrictions to recreational fishers permitting hook and release only were also implemented (Hurley 1998). The porbeagle TAC was reduced to 1,000 t in 1997 (O’Boyle et al. 1998), then to 1,700 t during the two years 2000–2001 while additional scientific information was collected (DFO 2001b). As a result of these studies, it was concluded that the population was seriously depleted (to 10–20% of virgin biomass) and would require a greatly decreased fishing mortality if recovery is to occur. An annual catch of 200 to 250 t would correspond to fishing at about MSY and would allow population growth. However, annual catch levels of about 1,000 t would be sustainable over the long term once the population has recovered. These DFO analyses, which are the basis for the regional assessment, are contested by COSEWIC (2004), who notes that the quota for 2002 to 2007 of 200 to 250 t represents a substantial reduction from catches in the mid-1990s, but even this amount now corresponds to a high exploitation rate because of the low population abundance. It is highly uncertain if this quota reduction will be sufficient to halt the porbeagle decline, and if so, to what extent the population will recover, given that there is uncertainty in estimating FMSY and the quota, the low number of mature animals remaining in the population, that at its current low abundance the population may experience depensation (Allee effects), and that reduction in fishing pressure is not always sufficient for population recovery (Hutchings 2001). COSEWIC (Committee on the status of endangered wildlife in Canada) designated porbeagle as Endangered in 2004 (COSEWIC 2004).
Since 1993, shark fisheries in Atlantic and Gulf of Mexico waters in the US have been managed under the Fishery Management Plan for Sharks of the Atlantic Ocean. The plan set commercial quotas in the US EEZ for 10 species of pelagic sharks at 580 t dressed weight annually, with recreational bag limits also applied. There is a small quota (92 t) for porbeagle. Commercial fishers require an annual shark permit, and finning is prohibited.
Aasen, O. 1963. Length and growth of the porbeagle (Lamna nasus, Bonaterre) in the North West Atlantic. FiskDir. Skr. Serie Havundersokelser 13(6): 20-37.
Acuña, E., Cid, L., Pérez, E., Kong, I., Araya, M., Lamilla, J. and Peñailillo, J. 2001. Estudio biológico de tiburones (marrajo dentudo, azulejo y tiburón sardinero) en la zona norte y central de Chile. Informes Técnicos FIP, FIP/IT Nº 2000-23
Acuña, E., Villarroel, J.C. and Grau, R. 2002. Fauna Ictica Asociada a la Pesquería de Pez Espada (Xiphias gladius Linnaeus). Gayana (Concepc.) 66(2): 263–267.
Anonymous. 2002. Report of the meeting of experts for the elaboration of an Action Plan for the conservation of Mediterranean species of cartilaginous fish. UNEP, RAC/SPA, Tunis.
Anonymous. 2004. Draft proposal to include Porbeagle (Lamna nasus) in Appendix II of CITES. Submitted by the Federal Republic of Germany to the member states of the European Community. SRG 28/10/1.
Bello, G. 1999. The Chondrichthyans of the Adriatic Sea. Acta Adriatica 40(1): 65–76
Bini, G. 1967. Atlante dei pesci delle coste Italiane, vol. I. Leptocardi, Ciclostomi, Selaci. Mondo Sommerso Editrice.
Binot, M., Bless, R., Boye, P., Gruttke, H. and Pretscher, P. (eds) 1998. Rote Liste gefährdeter Tiere Deutschlands. Schriftenreihe für Landschaftspflege und Naturschutz. vol. 55. Bonn-Bad Godesberg (Bundesamt für Naturschutz).
Bonfil, R. 1994. Overview of world elasmobranch fisheries. FAO Fisheries Technical Paper 341. FAO, Rome.
Buencuerpo, V., Rios, S. and Moron, J. 1998. Pelagic sharks associated with the swordfish, Xiphias gladius, fishery in the eastern North Atlantic Ocean and the Strait of Gibraltar. Fishery Bulletin 96: 667–685.
Campana, S.E. and Joyce, W.N. 2004. Temperature and depth associations of porbeagle shark (Lamna nasus) in the northwest Atlantic. Fish. Oceanogr. 13: 52–64.
Campana, S.E., Joyce, W., Marks, L., Natanson, L.J., Kohler, N.E., Jensen, C.F., Mello, J.J., Pratt Jr., H.L. and Myklevoll, S. 2002. Population dynamics of the porbeagle in the Northwest Atlantic Ocean. North. Am. J. Fish. Management 22: 106–121.
Campana, S.E., Natanson, L.J. and Myklevoll, S. 2002. Bomb dating and age determination of large pelagic sharks. Can. J. Fish. Aquat. Sci. 59: 450–455.
Campana, S., Joyce, W. and L. Marks. 2003. Status of the Porbeagle Shark (Lamna nasus) population in the Northwest Atlantic in the context of species at risk. Canadian Science Advisory Secretariat. Res. Doc. 2003/007.
Campana, S., Marks, L., Joyce, W. and Harley, S. 2001. Analytical assessment of the porbeagle (Lamna nasus) population in the Northwest Atlantic, with estimates of long-term sustainable yield. Canadian Science Advisory Secretariat (CSAS) Res. Doc. 2001/067.
Campana, S., Marks, L., Joyce, W., Hurley, P., Showell, M. and Kulka, D. 1999. An analytical assessment of the porbeagle shark (Lamna nasus) population in the northwest Atlantic. CSAS. Res Doc.99/158.
Compagno, L.J.V. 1984. FAO species catalogue. Vol. 4. Sharks of the world. An annotated and illustrated catalogue of shark species known to date. FAO Fish. Synop. No. 125, vol. 4.
COSEWIC. 2004. COSEWIC assessment and status report on the porbeagle shark Lamna nasus in Canada. Committee on the Status of Endangered Wildlife in Canada. Ottawa. (Species at Risk Public Registry).
De la Serna, J.M., Valeiras, J., Ortiz, J.M. and Macias D. 2002. Large Pelagic sharks as by-catch in the Mediterranean Swordfish Longline Fishery: some biological aspects. NAFO SCR Doc.02/137 Serial No. N4759.
Department of Fisheries and Oceans (DFO). 1999. Porbeagle shark in NAFO subareas 3-6. DFO Science Stock Status Report B3-09 (1999).
Department of Fisheries and Oceans (DFO). 2001a. Porbeagle Shark in NAFO Subareas 3-6. DFO Science Stock Status Report B3-09(2001). DFO, Maritimes Region, Canada.
Department of Fisheries and Oceans (DFO). 2001b. Canadian Atlantic Pelagic Shark Integrated Fishery Management Plan, 2000-2001.
Domingo, A. 2000. Los Elasmobranquios Pelágicos Capturados por la flota de longline Uruguaya. In: M. Rey (ed.). Consideraciones Sobre la Pesca Incidental Producida por la Actividad de la Flota Atunera Dirigida a Grandes Pelágicos. “Plan De Investigación Pesquera”. Inape – Pnud Uru/92/003.
Domingo, A., Mora, O. and Cornes, M. 2001. Evolución de las capturas de elasmobranquios pelágicos en la pesquería de atunes de Uruguay, con énfasis en los tiburones azul (prionace glauca), moro (Isurus oxyrinchus) y porbeagle (Lamna nasus). Col. Vol. Sci. Pap. ICCAT 54(4): 1406–1420.
Ellis, J.R. and Shacklee, S.E. 1995. Notes on porbeagle sharks, Lamna nasus, from the Bristol Channel. Journal of Fish Biology 46: 368–370.
Filanti, T., Megalofonou, P., Petrosino, G. and De Metrio, G. 1986. Incidence of Selachii in longline swordfish fishery in the Gulf of Taranto. Nova Thalassia 8(3): 667–669.
Fischer, W., Bauchot, M.-L. and Schneider, M. 1987. Fiches FAO d'identification des espèces pour les besoins de la pêche. Méditerranée et mer Noire. Zone de Pêche 37. FAO, Rome, Italy.
Fleming, E.H. and Papageorgiou, P.A. 1997. Shark fisheries and trade in Europe. TRAFFIC Europe.
Food and Agriculture Organization of the United Nations. 2003. Lamna nasus. Rome, Italy Available at: http://www.fao.org/fishery/species/2798/en.
Francis, M.P. and Duffy, C. 2005. Length at maturity in three pelagic sharks (Lamna nasus, Isurus oxyrinchus and Prionace glauca) from New Zealand. Fishery Bulletin 103: 489–500.
Francis, M.P. and Stevens, J.D. 2000. Reproduction, embryonic development and growth of the porbeagle shark, Lamna nasus, in the South-west Pacific Ocean. Fishery Bulletin 98: 41–63.
Francis, M.P., Natanson, L.J. and Campana, S.E. In press. Porbeagle (Lamna nasus). In: E.K. Pikitch, & M. Camhi (eds). Sharks of the open ocean. Blackwell Scientific Publications.
Gauld, J.A. 1989. Records of porbeagles landed in Scotland, with observations on the biology, distribution and exploitation of the species. Scottish Fisheries Research Report 45, ISSN 0308 8022.
Hazin, F.M., Broadhurst, A. and Amorim, C. (in press). Catch of pelagic sharks by subsurface longline fisheries in the South Atlantic Ocean: A review of available data with emphasis on Uruguay and Brazil In: M. Camhi & E. Pikitch (eds). Sharks of the open Ocean. Blackwell Scientific, New York
Heessen, H.J.L. (ed.). 2003. Development of Elasmobranch Assessments DELASS. European Commission DG Fish Study Contract 99/055, Final Report, January 2003
Hilton-Taylor, C. 2000. 2000 IUCN Red List of Threatened Species. IUCN, Gland, Switzerland and Cambridge, UK.
Hurley, P.C.F. 1998. A review of the fishery for pelagic sharks in Atlantic Canada. Special issue science and management of shark fisheries. In: R.E. Hueter (ed.) Proceedings of an international symposium held at the 125th annual meeting of the American Fisheries Society, Tampa, Florida, USA August 30, 1995. Fisheries Research 39: 105–228.
Hutchings, J.A. 2001. Influence of population decline, fishing, and spawner variability on the recovery of marine fishes. Journal of Fish Biology 59(A): 306–322.
IUCN. 2006. 2006 IUCN Red List of Threatened Species. www.iucnredlist.org. Downloaded on 04 May 2006.
IUCN SSC Shark Specialist Group. Specialist Group website. Available at: http://www.iucnssg.org/.
Jardas, I. 1996. Jadranska ihtiofauna. Školska knjiga, Zagreb.
Jensen, C.F., Natanson, L.J., Pratt, H.L., Kohler, N.E. and Campana, S.E. 2002. The reproductive biology of the porbeagle shark, Lamna nasus, in the western North Atlantic Ocean. Fish. Bull. 100: 727–738.
Joyce, W., Campana, S.E., Natanson, L.J., Kohler, N.E., Pratt, H.L. and Jensen, C.F. 2002. Analysis of stomach contents of the porbeagle shark (Lamna nasus) in the northwest Atlantic. ICES J. Mar. Sci. 59: 1263–1269.
Kabasakal, H. 2002. Elasmobranch species of the Seas of Turkey. Annales, Ser. Hist. Nat. 12(1): 15–22.
Kohler N.E. and Turner P.A. 2001. Shark tagging: A review of conventional methods and studies. Environmental Biology of Fishes 60(1–3): 191–223.
Kohler, N.E., Turner, P.A., Hoey, J.J., Natanson, L.J. and Briggs, R. 2002. Tag and recapture data for three pelagic shark species, blue shark (Prionace glauca), shortfin mako (Isurus oxyrinchus), and porbeagle (Lamna nasus) in the North Atlantic Ocean. ICCAT Collective Volume of Scientific Papers SCRS/2001/064 1231–1260.
Lallemand-Lemoine, L. 1991. Analysis of the French fishery for porbeagle Lamna nasus (Bonnaterre, 1788). ICES-CM-1991/G:71.
Last, P.R. and Stevens, J.D. 1994. Sharks and Rays of Australia. CSIRO, Australia.
Macias, D. and De La Serna, J.M. 2002. By-catch composition in the Spanish Mediterranean longline fishery. In: M. Vacchi, G. La Mesa, F. Serena & B. Seret (eds) Proceedings of the 4th Elasmobranch Association Meeting, Livorno (Italy) 2000. ICRAM, ARPAT & SFI: 198
Marconi, M. and De Maddalena, A. 2001. On the capture of a young porbeagle, Lamna nasus (Bonnaterre, 1788), in the western Adriatic Sea. Annales, Ser. Hist. Nat. 11, 2(25): 179–184.
McCoy, M.A. and Ishihara, H. 1999. The Socio-economic Importance of Sharks in the U.S. Flag Areas of the Western and Central Pacific (Admininstrative Report AR-SWR-99-01), prepared for U.S. Department of Commerce, National Marine Fisheries Service, Southwest Region, Long Beach, California, United States.
Megalofonou, P., Damalas, D., Yannopoulos, C., De Metrio, G., Deflorio, M., De La Serna, J.M. and Macias, D. 2000. By catches and discards of sharks in the large pelagic fisheries in the Mediterranean Sea. Final report of the Project No 97/50 DG XIV/C1, Comm. Of the EU Communities.
Mejuto, J. 1985. Associated catches of sharks, Prionace glauca, Isurus oxyrinchus and Lamna nasus, with NW and N Spanish swordfish fishery in 1984. ICES C.M. 1985/H:42
Natanson, L.J., Mello, J.J. and Campana, S.E. 2002. Validated age and growth of the porbeagle shark, Lamna nasus, in the western North Atlantic Ocean. Fish. Bull. 100: 266–278.
O’Boyle, R.N., Fowler, G.M., Hurley, P.C.F., Joyce, W. and Showell, M.A. 1998. Update on the status of NAFO SA 3-6 porbeagle shark (Lamna nasus). Canadian Stock Assessment Secretariat Research Document 98/41: 2–58.
Orsi Relini, L. and Garibaldi, F. 2002. Pups of Lamnid sharks from the Ligurian Sea: morphological and biometrical characteristics of taxonomic value. In: M. Vacchi, G. La Mesa, F. Serena & B. Seret (eds). Proceedings of the 4th Elasmobranch Association Meeting, Livorno (Italy) 2000. ICRAM, ARPAT & SFI: 199
Rae, B.B. 1962. Porbeagle sharks. Dept. Ag. Fish., Scot. Fish. Bull. 18: 17–18.
Rose, D.A. 1996. An overview of world trade in sharks and other cartilaginous fishes. TRAFFIC International, Cambridge
Serena, F. and Vacchi, M. 1997. Attivita di studio sui grandi pesci cartilaginei dell’alto Tirreneo e Mar Ligure nell’ambito del programma L.E.M. (Large elasmobranchs monitoring). Quad. Civ. Staz. Idrobiol. N. 22: 17–21.
SGRST. 2002. Commission of the European Communities. Report of the Subgroup on Resource Status (SGRST) of the Scientific, Technical and Economic Committee for Fisheries (STECF): Elasmobranch Fisheries. Brussels, 23-26 September 2002.
Shann, E.W. 1923. The embryonic development of the porbeagle shark, Lamna cornubica. Proceedings of the Zoological Society of London 11: 161–171.
Shivji, M., Clarke, S., Pank, M., Natanson, L., Kohler, N. and Stanhope, M. 2002. Rapid molecular genetic identification of pelagic shark body-parts conservation and trade-monitoring. Conservation Biology 16(4): 1036–1047.
Soldo, A. and Jardas, I. 2002. Large sharks in the Eastern Adriatic. In: M. Vacchi, G. La Mesa, F. Serena & B. Seret (eds) Proceedings of the 4th Elasmobranch Association Meeting, Livorno (Italy) 2000. ICRAM, ARPAT & SFI: 141-155.
Sonu, S.C. 1998. Shark fisheries, trade, and market of Japan. NOAA Technical Memorandum NMFS.
Stevens, J. 2005. Porbeagle shark Lamna nasus. In: S.L. Fowler, R.D. Cavanagh, M. Camhi, G.H. Burgess, G. Cailliet, S.V. Fordham, C.A. Simpfendorfer J.A. Musick (eds). Sharks, rays and chimaeras: the status of the chondrichthyan fishes. IUCN SSC Shark Specialist Group. IUCN, Gland, Switzerland and Cambridge, UK.
Stevens, J.D. 1976. Preliminary results of shark tagging in the north-east Atlantic, 1972–1975. Journal of the Marine Biological Association of the United Kingdom 56: 929–937.
Stevens, J.D. 1990. Further results from a tagging study of pelagic sharks in the north-east Atlantic. Journal of the Marine Biological Association of the UK. 70:707–720.
Stevens, J.D. and Wayte, S.E. In press. The bycatch of pelagic sharks in Australia’s tuna longline fisheries. In: E. Pikitch & M. Camhi (eds). Sharks of the open ocean. Proceedings of the Monterey pelagic shark meeting Feb 1999. Blackwell Scientific Press, UK.
Sullivan, K.J., Mace, P.M., Smith, N.W.M., Griffiths, M.H., Todd, P.R., Livingston, M.E., Harley, S., Key, J.M. and Connell, A.M. (eds). 2005. Report from the Fishery Assessment Plenary, May 2005: stock assessments and yield estimates. Ministry of Fisheries, Wellington.
Svetlov, M.F. 1978. The porbeagle, Lamna nasus, in Antarctic waters. Journal of Ichthyology 18(5): 850–851.
Tortonese, E. 1956. Leptocardia, Ciclostomata, Selachii, Fauna d’Italia. Vol. II. Ed. Calderini, Bologna.
Vacchi M., Biagi V., Pajetta R., Fiordiponti R., Serena F. and G. Notarbartolo Di Sciara. 2002. Elasmobranch catches by tuna trap of Baratti (Northern Tyrrhenian Sea) from 1898 to 1922. In: Proceedings of the 4th European Elasmobranch Association Meeting, Livorno (Italy), 2000. M. Vacchi, G. La Mesa, F. Serena and B. Séret (eds.). pp:177–183. ICRAM, ARPAT & SFI.
Vannuccini, S. 1999. Shark utilization, marketing and trade. FAO Fisheries Technical Paper. No. 389. Rome, FAO.
Vas, P. and Thorpe, T. 1998. Commercial landings of sharks in South-Western England. Shark News 12: November 1998.
|Citation:||Stevens, J., Fowler, S.L., Soldo, A., McCord, M., Baum, J., Acuña, E. & Domingo, A. 2006. Lamna nasus (Northwest Atlantic subpopulation). The IUCN Red List of Threatened Species. Version 2014.2. <www.iucnredlist.org>. Downloaded on 21 October 2014.|