|Scientific Name:||Sphyrna zygaena|
|Species Authority:||(Linnaeus, 1758)|
|Red List Category & Criteria:||Vulnerable A2bd+3bd+4bd ver 3.1|
|Assessor/s:||Casper, B.M., Domingo, A., Gaibor, N., Heupel, M.R., Kotas, E., Lamónaca, A.F., Pérez-Jimenez, J.C., Simpfendorfer, C., Smith, W.D., Stevens, J.D., Soldo, A. & Vooren, C.M.|
|Reviewer/s:||Valenti, S.V. & Fowler, S.L. (Shark Red List Authority)|
This assessment is based on the information published in the 2005 shark status survey (Fowler et al. 2005).
The Smooth Hammerhead (Sphyrna zygaena) is one of the larger hammerhead sharks, found world-wide in temperate and tropical seas, with a wider range than other members of its family. It is semipelagic and occurs on the continental shelf. Although few data are available on the Smooth Hammerhead?s life-history characteristics, it is a large hammerhead shark and presumably at least as biologically vulnerable as S. lewini. This species is caught with a wide variety of gears in both coastal and oceanic fisheries, as bycatch and a target. Therefore in some areas, all size classes and reproductive stages are susceptible to capture. The Smooth Hammerhead?s large fins are highly valued for their high fin ray count and they are being increasingly targeted in some areas in response to increasing demand for the fin trade. Few species-specific data are available to assess population trends because catches of hammerhead sharks are often grouped together under a single category. Very often these sharks are finned and the carcasses discarded. This species has sometimes been confused with S. lewini in the tropics and these two species are probably misidentified with each other in some areas. Time series data on population trends in hammerhead sharks, including S. zygaena, are available from the Northwest and Western Central Atlantic and the Mediterranean Sea. In the Northwest and Western Central Atlantic, where S. zygaena is outnumbered by S. lewini by about ten to one, analysis of U.S. pelagic longline logbook data estimated that Sphrynidae (including S. lewini, S. mokarran and S. zygaena) declined in abundance by 89% since 1986. In the Mediterranean Sea, where S. zygaena outnumbers S. lewini, compilation and meta-analysis of time series abundance indices estimated that Sphrynidae (including S. lewini, S. mokarran and S. zygaena) declined by >99% in abundance and biomass since the early 19th century. While very steep declines have been recorded in these areas, the species is afforded some refuge in other areas of its range, such as southern Australia, where it is abundant and fishing pressure is low. The species is currently assessed as Vulnerable globally and further investigation into threats, population trends, catches and life-history parameters throughout its range is required to determine whether it may warrant a higher category in the future.
|Range Description:||This shark is found in coastal and open ocean (Domingo in prep) temperate and tropical waters, with a wider range than other members of its family (Compagno in prep). The full extent of this species? range in tropical waters may be incompletely known at present, due to probably confusion with the more abundant Scalloped Hammerhead (S. lewini) (Compagno in prep).
Western Atlantic: From Nova Scotia to Florida, USA and Virgin Islands to southern Argentina (Compagno in prep, Domingo in prep, Last and Stevens 1994).
Eastern Atlantic: From the UK and as a vagrant in the North Sea, southwards, including the Mediterranean Sea, where has been reported as more common in the western basin (Buencuerpo et al. 1998), to Mauritania, Senegal, Cape Verde Islands, Guinea, Ivory Coast, and Angola (Compagno in prep, Last and Stevens 1994).
Indian Ocean: South Africa and southern Mozambique, Comoros Islands, southern India, Sri Lanka, and Australia (Western Australia, South Australia, Victoria, Tasmania) (Compagno in prep, Last and Stevens 1994).
Western Pacific: From Viet Nam (Gulf of Tonkin) to Japan and southern Russia in the Northwest Pacific. Australia (New South Wales), New Zealand, Lord Howe and Kermadec Islands in the Southwest Pacific (Compagno in prep, Last and Stevens 1994).
Eastern Pacific: From northern California, USA, to Gulf of California, Mexico, Panama, and from Ecuador to Chile, including Galapagos Islands (Compagno in prep, Last and Stevens 1994).
Also occurs off the Hawaiian Islands, USA and possibly off Samoa (Compagno in prep, Last and Stevens 1994).
Native:Albania; Algeria; Argentina; Australia; Bahrain; Belgium; Bosnia and Herzegovina; Brazil; Canada; Chile; China; Croatia; Cyprus; Denmark; Egypt; Estonia; Finland; Germany; Greece; Greenland; Iceland; India; Iran, Islamic Republic of; Iraq; Ireland; Israel; Italy; Japan; Korea, Democratic People's Republic of; Korea, Republic of; Kuwait; Latvia; Lebanon; Libya; Lithuania; Madagascar; Mexico; Montenegro; Morocco; Mozambique; Namibia; Netherlands; New Zealand; Norway; Oman; Pakistan; Peru; Poland; Portugal; Qatar; Russian Federation; Saudi Arabia; Slovenia; South Africa; Spain; Sweden; Syrian Arab Republic; Tunisia; Turkey; United Arab Emirates; United Kingdom; United States (Alabama, Alaska, Aleutian Is., California, Connecticut, Delaware, Florida, Georgia, Louisiana, Maine, Maryland, Massachusetts, Mississippi, New Hampshire, New Jersey, North Carolina, Oregon, Rhode Island, South Carolina, Texas, Virginia, Washington); Uruguay; Western Sahara
|FAO Marine Fishing Areas:||
Atlantic – southeast; Atlantic – northwest; Atlantic – northeast; Atlantic – western central; Atlantic – eastern central; Atlantic – southwest; Indian Ocean – western; Indian Ocean – eastern; Mediterranean and Black Sea; Pacific – southwest; Pacific – northwest; Pacific – eastern central; Pacific – southeast
|Range Map:||Click here to open the map viewer and explore range.|
|Population:||Specific data on populations of this species are generally unavailable in many areas because hammerhead shark catches are often grouped to include several Sphyrna species. Furthermore, this species has sometimes been confused with the Scalloped Hammerhead (S. lewini) in the tropics and these two species are probably misidentified with each other.|
|Habitat and Ecology:||
The large majority of the information for this section is taken from Simpfendorfer (2005).
The Smooth Hammerhead is a coastal-pelagic and semi-oceanic and occurs on the continental shelf, to 200 m depth (Ebert 2003). Smale (1991) reported that large individuals were commonly found over deep reefs on the edge of the continental shelf. The species has also been observed in freshwater in Indian River, Florida, USA (G. Burgess pers. comm.) and in the Rio de la Plata estuary in Uruguay (Doño 2008, Domingo in prep.). In the demersal gillnet fishery in southern Western Australia, juvenile S. zygaena are caught on the bottom in depths from the shore to at least 60 m (C. Simpfendorfer pers. comm.). Compagno (in prep.) reports that this species occurs at or near the surface in the East China Sea, whereas S. mokarran and S. lewini range into deeper water in this area. The nursery habitat of this species is smooth sandy substrate in shallow waters, down to depths of 10m. Large schools of juvenile S. zygaena have been reported from off South Africa (Bass et al. 1975). Off southern Brazil in South America, S. zygaena occurs at depths of 10?100 m (Kotas 2004, Vooren et al. 2005). Nursery areas and juveniles have been reported in coastal waters off Uruguay from mid-Rio de la Plata to the Atlantic Ocean bordering with Brazilian waters from November to March at temperatures of 16?23°C and salinities of 12?27 ups (Doño 2008, Domingo in prep.).
There are only limited published biological data on S. zygaena, despite its widespread occurrence. Compagno (1984, in prep.) reported that the species reaches a maximum size of 370?400 cm total length (TL). Stevens (1984) reported that off the east coast of Australia males mature at about 250?260 cm TL and females at about 265 cm TL. Castro and Mejuto (1995) reported gravid females between 220 and 255 cm fork length (FL), but gave no relationship between fork and total length. Bass et al. (1975) reported a female S. zygaena from South Africa that appeared to have recently mated in February and another female caught in November that contained full-term embryos. Stevens (1984) reported that off the east coast of Australia parturition occurs between January and March, with ovulation at about the same time. The gestation period off eastern Australia would appear to be 10?11 months. Castro and Mejuto (1995) reported 21 gravid females with a mean litter size of 33.5 from the waters of western Africa. Off eastern Australia Stevens (1975) reported litter sizes between 20?49 (mean 32). The sex ratio of embryos is 1:1 (Stevens 1984, Castro and Mejuto 1995). Compagno (1984, in prep) gave the size at birth as 50?61 cm. Smale (1991) and Doño (2008) reported juveniles with open umbilical scars from South Africa at sizes between 59 and 63 cm, and from Uruguay between 49 and 55 cm TL, respectively. Possible pupping grounds and nursery areas for this species include the northern Gulf of California and shallow coastal waters off southern Brazil and Uruguay (Vooren 1997, 1999, Vooren and Klippel 2005, Doño et al. in prep). In Uruguay pupping grounds and nursery areas were reported in coastal waters by Doño (2008).
Although maximum age has yet to be determined for this species, it is thought that the lifespan of the smooth hammerhead may be 20 years or longer (FLMNH 2008). Further information is required on the biology and life-history parameters of this species.
Squid and teleosts are the most common prey. Based on specimens caught by recreational anglers off New South Wales, Australia, Stevens (1984) reported that 76% of specimens with food in their stomachs contained squid and 54% teleosts. For S. zygaena less than 2 m in length from the waters off South Africa, Smale (1991) reported that the diet was dominated by inshore squid (mostly Loligo v. reynaudii), with teleosts such as Hake, Horse Mackerel and Ribbonfish also important. Crustaceans and elasmobranchs have also been reported from stomach analyses (Bass et al. 1975, Compagno 1984, Smale 1991, Last and Stevens 1994). Compagno (1984) reported that sharks and rays were a favoured food, presumably of larger specimens. However, of 145 S. zygaena from South Africa examined by Dudley and Cliff (1993) only 0.7% contained elasmobranch prey.
Smooth Hammerhead is caught with a variety of gears, including with pelagic longlines, handlines, gillnets, purse-seines and pelagic and bottom trawls (Bonfil 1994, Compagno in prep, Maguire et al. 2006). In a review of world elasmobranch fisheries Bonfil (1994) listed S. zygaena as being reported in catches from directed shark fisheries off the east and west coasts of the USA, Brazil, Spain, Taiwan and Philippines. It also is taken in the shark fishery off south-western Australia (Heald 1987) and western Africa (Castro and Mejuto 1995). This shark is undoubtedly caught in shark fisheries in other parts of its range, but has not been reported separately from other hammerhead species. Very often these sharks are finned and the carcasses discarded. Bonfil (1994) also reported that this species is caught as bycatch in a number of non-shark fisheries, particularly pelagic longline and gillnet fisheries that operate close to temperate and subtropical continental shelves (e.g., South Pacific driftnet fishery, Mediterranean drift net fishery, Spanish longline fishery operating in the Mediterranean Sea and eastern Atlantic Ocean, and Indian Ocean tuna longline fishery). The capture of S. zygaena in many of these fisheries is infrequent (Bonfil 1994). Although size data are limited, catches in pelagic fisheries appear to be dominated by larger individuals, while juveniles are common in inshore shelf fisheries.
This species? fins are highly valued and they are being increasingly targeted in some areas in response to increasing demand for shark fins. Hammerhead shark species S. zygaena and S. lewini were found to represent at least 4?5% of the fins auctioned in Hong Kong, the world?s largest shark fin trading center (Clarke et al. 2006a). Hammerhead shark fins are generally high value compared to other species because of their high fin ray count (S. Clarke unpubl. data). It is estimated that between 1.3 and 2.7 million S. zygaena and/or S. lewini are represented in the shark fin trade each year or, in biomass, 49,000 to 90,000 mt (Clarke et al. 2006b).
Catches of Sphyrnidae have been reported only from the Atlantic Ocean since 1991 and these landings are undoubtedly under-reported. The catch was near 2,200 tonnes in 2004 (Maguire et al. 2006). Only S. zygaena and S. lewini are reported as individual species in the Food and Agriculture Organisation (FAO) fisheries statistics, but hammerhead catches are often grouped in one category as, Sphyrna species, which makes identification of actual catches of S. zygaena difficult.
Northeast Atlantic and Mediterranean Sea
The Smooth Hammerhead appears to be less common in the central Mediterranean, in comparison to the western regions of this sea. Buencuerpo et al. (1998) reported that 757 specimens were captured during their pelagic longline and gillnet survey from July 1991-July 1992 off southern Spain. Most of these specimens were presumed to be part of the Atlantic population. In the Northeast Atlantic and Mediterranean Sea this species is mainly caught by longlines and gillnets, particularly as bycatch in tuna and swordfish fisheries. Despite a ban on driftnetting in Mediterranean waters, this practice continues illegally (WWF 2005). A recent study of the Moroccan driftnet fleet operating in the Alboran Sea (southwest Mediterranean) and around the Strait of Gibraltar by Tudela et al. (2005) indicates that pelagic fishing pressure in this area is beyond the reproductive capacity of several other semi-oceanic shark species that were previously caught with S. zygaena (such as Alopias vulpinus). Some of these vessels appear to be increasingly targeting sharks by deploying driftnets closer to shore (Tudela et al. 2005). Sphyrna zygaena is not mentioned in this study. However, this species was reported in Buencuerpo et al.?s (1998) survey of longline and gillnet landings from the same area in 1992. Buencuerpo et al. (1998) report the highest catches of Sphyrna zygaena in the Spanish swordfish fishery from the western African coasts and near the Strait of Gibraltar.
Ferretti et al. (2008) compiled nine time series of abundance indices from commercial and recreational fishery landings, scientific surveys and sighting records, to reconstruct long-term population trends of large sharks in the northwestern Mediterranean Sea. Of the taxa for which there were enough data to investigate, hammerhead sharks (Sphyrna spp) declined the fastest; they appeared to disappear from coastal waters after 1963 and catches declines consistently in pelagic waters in the early 1980s in all sectors. Meta-analysis showed an average instantaneous rate of decline of -0.17 (CI 95%: ?0.34, ?0.003; time range 178 years) in abundance and -0.36 (CI 95%: -0.56, -0.1?6; time range: 107 years) in biomass, which translated into an estimated species decline of >99.99% in both cases. Walker et al. (2005) also report that the species has virtually disappeared from the central-southern Mediterranean Sea since 1986.
Mejuto et al. (2002) estimate landings of 240 tons of Sphyrna spp. And 1.1 ton of Sphyrna zygaena in the North Atlantic for the Spanish Surface longline fleet in 1999. De la Serna et al. (2002) reported only eight specimens of S. zyagaena (0.05%) in a total 17,759 sharks caught during a survey of the Spanish Mediterranean Fisheries from 1997?1999. This is significantly lower when compared to results of the same fishery along the west African coast and Iberian peninsula (where 757 specimens in period July 1991?July 1992 were caught). Megalofonou et al. (2000) only recorded four specimens during their survey of shark bycatches and discards in Mediterranean large pelagic fisheries in 1998?1999 (one in the Adriatic, two in the Ionian Sea and one in Spanish Mediterranean waters). There are few recent records of Sphyrna species in the eastern Mediterranean Sea. A total of 16 records of S. zygaena were collected in the eastern Adriatic from the 19th century to the 1950s, including reported catches were distributed throughout whole of the eastern coast. A higher number of records were reported during the 19th century in comparison to the 20th century (10 vs. 6, respectively) and the species has not been reported in this area since 1956 (Soldo and Jardas 2002). Although it occurs in open waters of southern Adriatic, it is only caught very rarely (Bello 1999). There were only 13 records of S. zygaena in the Northern Tyrrhenian and Ligurian Seas from the 1960s-1995 and there are no reports of this species during the last five years (F. Serena pers. comm.).
Longline fleets exert intense fishing pressure throughout the Northwest Atlantic (Baum et al. 2003). Baum et al. (2003) estimated that hammerhead sharks (grouped data for S. lewini, S. mokarran and S. zygaena) have declined in abundance by 89% since 1986 (95% confidence interval (CI): 86 to 91%) in their analysis of U.S. pelagic longline logbook data. This group is primarily composed of S. lewini; in Virginia Institute of Marine Science sampling programmes since 1973, S. lewini outnumbered S. zygaena by more than ten to one (Ha 2006).
In the Southwest Atlantic S. zygaena faces two main threats related to fisheries: catches of juveniles and pups along the continental shelf by different fishing gears (mainly bottom gillnets and trawlers (Vooren and Lamónaca 2003, Kotas and Petrere 2002, Doño 2008); and adult and juvenile catches by gillnets and longlines throughout the continental shelf and oceanic environments for the international fin market (Kotas et al. 2001, Kotas and Petrere 2002ab, Kotas and Petrere 2003, Zerbini and Kotas 1998, Domingo in prep). The species therefore faces intensive fishing pressure at all points in its life-cycle in this area. Off southern Brazil; from 1983?2005, indices of abundance of neonates of S. zygaena varied from 1?5% of the abundance of those of S. lewini in the same area (Vooren et al. 2005). Catches of neonates, juveniles and adults are taken by longline fleets based in Itajaí, which operate along the coast of southern Brazil (Kotas and Petrere 2002). The species is also a known bycatch of domestic, as well as Taiwanese, Japanese and other international longline fishing fleets operating throughout the South Atlantic Ocean (Joung et al. 2005, Matsushita and Matsunaga 2002). Juveniles and adults are also taken as bycatch by longline fleets operating in shelf and oceanic waters off Uruguay and Brazil (200-3000m). Given the declining trends apparent in other areas of the species? range where it is heavily fished, for example the Mediterranean Sea, the population in the Southwest Atlantic may be unable to withstand continued fishing pressure.
Sphyrna zygaena is taken as both target and bycatch in artisanal and industrial fisheries along the eastern Pacific coast of the Americas. Landings of this species in Guatemala, Costa Rica, Panama and Mexico have been reported as 1% of the total chondrichthyan catch. Seasonal surveys of fisheries on the eastern coast of Mexico, conducted during 1998?1999, showed that S. zygaena was a common component of the landings of directed shark fisheries. The majority of those landed were juveniles in many areas (Bizzaro et al. 2007). This study reports that large sharks, such as S. zygaena were usually targeted in directed drift gillnet, or to a lesser extent, surface longline fisheries. Márquez-Farías (2000) report an overall decline in catch rates for all shark species in the Gulf of California. This species has also been reported as bycatch in longline, bottom trawl and gillnets in the landings of other Central and South American countries, down to Peru. In Ecuador, S. zygaena represents 11% of the total chondrichthyan landings. There is a high proportion of juveniles in these Ecuadorian landings; 91% of female (measuring S. zygaena represented 12.5% of total chondrichthyan landings over the period 1996-2005 (Romero, M. PANtiburones).
An artisanal fishing fleet targeting sharks south of Tres Marias Islands in the Central Mexican Pacific operated out of La Cruz Huanacaxtle from the early 1990s to 1997, after which they moved to Yavaros in the Central Gulf of California, apparently following the migratory movements of some of the shark species (Pérez-Jiménez et al. 2005). Pérez-Jiménez et al. (2005) monitored the shark landings of this fleet from 1995?1996. Sphyrna zygaena was the most important of 10 species recorded in 607 sets taken south of the Tres Marias Islands, composing 35% of 2,004 sharks recorded. This artisanal fleet has not caught sharks south of the Tres Marias Islands or in the Central Gulf of California since the late-1990s (Pérez-Jiménez et al. 2005).
Illegal fisheries target sharks for their fins around the Galapagos Islands. There are no specific data for these fisheries, but given the high value of its fins, it is very likely that it is targeted in illegal finning activities. Illegal fishing in this area is not only practiced by fishermen from the Galapagos, but also by the industrial and artisanal fleets from continental Ecuador and international fleets (Coello 2005). Divers and dive guides in the Galapagos have noted a severe decrease in shark number and schools of hammerhead sharks (P. Zarate pers comm.). The Ecuadorian Government issued a decree in 2004 prohibiting fin export from Ecuador, in an attempt to help stop illegal finning in the Galapagos. Unfortunately the Decree had the reverse effect of establishing illegal trade routes with fins now being exported mainly via adjacent Peru and Colombia, where there is no regulation banning finning. Interviews within fishermen and traders in both Ecuador and Peru suggest that there are illegal trade routes for fins transported both from continental Ecuador and directly from the Galapagos to Peru, and illegal finning activity is ongoing (Sáenz 2005, WildAid 2005).
Hammerhead sharks, including S. zygaena, are also caught by international purse seine fleets targeting tunas in the high seas of the Eastern Pacific, particularly those associated with Fish Aggregating Devices (FADs) (Román-Verdesoto and Orozco-Zöller 2005). IATTC conducted a one year species sampling programme to determine the accuracy of identification by fisheries observers on these vessels. Sphyrna zygaena was found to represent 1.7% and S. lewini, 3.6% of the sharks recorded during this programme, respectively.
In the West Australian demersal gillnet fishery Sphyrna zygaena is an important bycatch species, but appears not to be impacted by this low fishing pressure. The species is reasonably abundant around the northern North Island of New Zealand, and the most abundant shark species recorded in aerial surveys along the northwest coast. In New Zealand, neonates and small juveniles are a common bycatch in commercial gillnet fisheries for flatfish, and are also commonly taken by trawlers and Danish seiners. They are usually discarded, although juveniles discarded from gillnets are usually dead. Adults are mainly taken by gamefishers as bycatch when targeting marlin with live baits, and consequently the annual catch is small. Many of the sharks taken by game fishers are released alive (C. Duffy, pers. comm.). S. zygaena is abundant in the region, and significant numbers of adults do not appear to be taken in commercial fisheries.
Sphyrna zygaena, along with S. lewini and S. mokarran, are exploited by the commercial line fishery and recreational game fishery off New South Wales. The majority of the hammerhead catch in commercial and recreational fisheries is composed of S. zygaena and S. lewini (Scandol et al. 2008). Total commercial hammerhead landings peaked in 1993/94 at 15/7 t. Annual commercial catches have averaged ~3 t in the last five years. Most hammerhead landings come from the Ocean Trap and Line Fishery (74%), but they are also taken in the Estuary General and Ocean Trawl Fisheries.
Information on catches of S. zygaena by recreational anglers is very limited due to the lack of species identification. Total catch of hammerhead sharks by recreational gamefishing and protective beach meshing remained at about 250 sharks per year between the 1970s and 2001, with >95% of recreational gamefishing catches being tagged and released. It is likely that S. zygaena is caught in recreational fisheries off temperate and subtropical coasts. This species has also been reported from nets set in the New South Wales beach protection programme (Krough 1994). This employs large mesh gillnets to catch large sharks as a measure to protect beach users from shark attack. In the New South Wales programme, hammerheads (mostly S. zygaena) made up nearly 50% of the catch of 4,715 sharks in the period from 1972?73 to 1989?90 (Reid and Krough 1992). The large mesh nets used by shark control programmes appear to be very efficient at catching hammerhead sharks, including S. zygaena, while catches are very low on the large baited lines used in some programmes (Simpfendorfer 1993).
Hammerhead sharks, including S. zygaena, are taken in a variety of artisanal and commercial fisheries in this region as both target and bycatch, however, no reliable species specific data are available because catches tend to be grouped into ?Sphyrna spp.?, if recorded at all. Pelagic fisheries have operated in the Indian Ocean for more than 50 years; Japanese long-liners in the eastern Indian Ocean since 1952 and in the western region since 1956. Russian, Taiwanese and South Korean vessels have fished there since 1954?1966 (Gubanov and Paramonov 1993). The Spanish swordfish longline fishery, which also targets sharks, is also active across the Indian Ocean (ICCAT 2005). Large hook and line and in mesh gillnet fisheries are known to target sharks off India, where this species occurs (Anderson and Simpfendorfer 2005). Finning and discarding of carcasses has also been reported, especially in offshore and high seas fisheries (Anderson and Simpfendorfer 2005). A recent review of fisheries in the Indian Ocean (Young et al. 2006) reported that sharks in this area are considered fully to over-exploited. Large numbers of longline vessels have also been reported to be operating illegally in coastal waters of the western Indian Ocean, primarily targeting hammerhead sharks and giant guitarfish (IOTC 2005, Dudley and Simpfendorfer 2006).
Japanese data on hammerhead species are limited, but reported landings in Japan?s coastal ports totaled 11-34 mt annually between 2000 and 2004 with an average of 24 mt per annum. No CPUE trends are available (Japan Fisheries Agency 2006).
Smooth hammerhead is a member of the family Sphyrnidae, which is listed on Annex I, Highly Migratory Species, of the UN Convention on the Law of the Sea. States are urged to cooperate over the management of these species. No such management yet exists. Precautionary adaptive collaborative management of target and bycatch fisheries is urgently needed for this highly migratory species. It is also essential to improve and sustain data collection and develop stock assessments for this species. Listing on international resource management agreements, such as the Convention on Migratory Species (CMS) could help to drive improvements in national and regional management and facilitate collaboration between states, for this species and other migratory sharks.
The adoption of shark finning bans by fishing states (e.g., USA, Australia, Brazil), regional entities (EU) and regional fisheries organisations (e.g. ICCAT, IOTC, IATTC, WCPFC) is accelerating and should increasingly prevent the capture of oceanic sharks for their fins alone. Strict enforcement of these bans is required if they are to be effective.
Management plans, fishing regulation, and monitoring programs are needed throughout this species? range. Estimates of acceptable catch rates should be viewed with precaution until there is more certainty in age and growth parameters and further research on the species? life-history characteristics is required. Protection of known adult aggregation sites and coastal nursery areas is also recommended.
In the USA, this species is included in the Large Coastal Shark complex management unit on the US Highly Migratory Species Fishery Management Plan, however there are no management measures specific to this species and no stock assessments have been undertaken for it. Enforcement of Brazilian laws restricting the length of pelagic gillnets and banning trawl fishing at a distance of less than 3 nm from shore has been difficult and therefore trawling in inshore nursery grounds has persisted.
Anderson, R.C. and Simpfendorfer, C. 2005. Indian Ocean. In: S.L. Fowler, R.D. Cavanagh, M. Camhi, G.H. Burgess, G.M. Cailliet, S.V. Fordham, C.A. Simpfendorfer and J.A. Musick (eds), Sharks, Rays and Chimaeras: The Status of the Chondrichthyan Fishes. Status Survey, pp. 140-149. IUCN/ SSC Shark Specialist Group, IUCN, Gland, Switzerland and Cambridge, UK.
Arzi, J., Delgado de Molina, A., Ramos, M.L. and Santana, J.C. 2006. Check list and catch rate data by hook type and bait for bycatch species caught by Spanish experimental longline cruises in the South-western Indian Ocean during 2005. IOTC.
Bass, A.J., D'Aubrey, J.D. and Kistnasamy, N. 1975. Sharks of the east coast of southern Africa. III. The families Carcharhinidae (excluding Mustelus and Carcharhinus) and Sphyrnidae. South African Association for Marine Biological Research. Oceanographic Research Institute. Investigational Reports.
Baum, J.K., Myers, R.A., Kehler, D.G., Worm, B., Harley, S.J. and Doherty, P.A. 2003. Collapse and conservation of shark populations in the Northwest Atlantic. Science 299: 389-392.
Bello, G. 1999. The Chondrichthyans of the Adriatic Sea. Acta Adriatica 40(1): 65-76.
Bonfil, R. 1994. Overview of world elasmobranch fisheries. FAO Fisheries Technical Paper. 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.
Castro, J.A. and Mejuto, J. 1995. Reproductive parameters of blue shark, Prionace glauca, and other sharks in the Gulf of Guinea. Marine and Freshwater Research 46: 967?73.
Clarke, S.C., Magnussen, J.E., Abercrombie, D.L., McAllister, M.K. and Shivji, M.S. 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(1): 201-211.
Clarke, S.C.,McAllister, M.K., Milner-Gulland, E.J., Kirkwood, G.P., Michielsens, C.G.J., Agnew, D.J., Pikitch, E.K., Nakano, H. and Shivji, M.S. 2006. Global Estimates of Shark Catches using Trade Records from Commercial Markets. Ecology Letters 9: 1115-1126.
Cliff, G. and Dudley, S.F.J. 1992. Protection against shark attack in South Africa, 1952 to 1990. Australian Journal of Marine and Freshwater Research 43(1): 263? 272.
Coello, S. 2005. La Administración de los Chondrichthyes en Ecuador. Aportes para el Plan Nacional de Tiburones. UICN, Quito, Ecuador.
Compagno, L.J.V. 1984. Sharks of the World. An annotated and illustrated catalogue of shark species to date. Part II (Carcharhiniformes). FAO Fisheries Synopsis, FAO, Rome.
Compagno, L.J.V., Dando, M. and Fowler, S.L. 2005. Sharks of the World. Harper Collins.
Compagno, L.J.V. in prep.. Sharks of the World. An annotated and illustrated catalogue of the shark species known to date. Volume 3: Carcharhiniformes. FAO, Rome.
Doño, F. 2008. Identificación y caracterización de áreas de cría del tiburón Martillo (Sphyrna spp.) en las costas de Uruguay. Tesis de Licenciatura, Facultad de Ciencias, Universidad de la República de Uruguay.
Dudley, S. and Simpfendorfer, C. 2006. Population status of 14 shark species caught in the protective gillnets off KwaZulu-Natal beaches, South Africa, 1978-2003. Marine and Freshwater Research 57: 225-240.
Dudley, S.F.J. and Cliff, G. 1993. Some effects of shark nets in the Natal nearshore environment. Environmental Biology of Fishes 36: 243?255.
Ebert, D.A. 2003. The sharks, rays and chimaeras of California. University of California Press.
Ferretti, F., Myers, R.A., Serena, F. and Lotze, H.K. 2008. Loss of Large Predatory Sharks from the Mediterranean Sea. Conservation Biology 22: 952-964.
FLMNH (Florida Museum of Natural History). 2008. Biological Profile: smooth hammerhead Sphyrna zygaena,/i>, FLMNH website. Available at: Available at: http://www.flmnh.ufl.edu/fish/gallery/descript/smhammer/smoothhammerhead.html..
Fowler, S.L., Cavanagh, R.D., Camhi, M., Burgess, G.H., Cailliet, G.M., Fordham, S.V., Simpfendorfer, C.A. and Musick, J.A. (comps and eds). 2005. Sharks, Rays and Chimaeras: The Status of the Chondrichthyan Fishes. Status Survey. pp. x + 461. IUCN/SSC Shark Specialist Group, IUCN, Gland, Switzerland and Cambridge, UK.
Gubanov, E.P. and Paramonov, V.V. 1993. Syr'-evye-resursy-tuntsov-i-soputstvuyushchikh-ob"ektov-promysla-mirovogookeana-i-problemy-ikh-ratsyonal'-nogo-ispol'-zovanniya.In: V.N. Yakovlev, E.V. Romanov, N.A. Lebedeva, Yu.K. Trushyn, I.G. Timokhin, B.G. Trotsenko and V.V Korkosh (eds), pp. 69-71. KERCH-UKRAINE YUGNIRO.
Ha, D.S. 2006. Ecology and Conservation of Virginia Shark Species: Analysis of 30 Years of Virginia Long-Line Census Data, 1974-2004. Ph.D. dissertation, Virginia Institute of Marine Science, College of William and Mary.
Haimovici M. and Mendonça J.T. 1996. Descartes da fauna acompanhante na pesca de arrasto de tangones dirigida a linguados e camarões na plataforma continental do sul do Brasil. Atlântica, Rio Grande.
Heald, D.I. 1987. The commercial shark fishery in temperate waters of Western Australia. Fisheries Report (WA Fisheries Department) 75: 71.
ICCAT. 2005. Report of the 2004 Inter-sessional meeting of the ICCAT Subcommittee on bycatches: shark stock assessment. Col. Vol. Sci. Pap. ICCAT. ICCAT.
IOTC (Indian Ocean Tuna Commission). 2005. Information on shark finning fisheries. IOTC-2005-S9-08[EN]. IOTC, Victoria, Seychelles.
Japan Fisheries Agency. 2006. The current status of international fisheries resources ? 2004 edition, Fisheries Agency/Fisheries Integration Research Center [in Japanese].
Joung, S.J., Liu, K.M., Liao, Y.Y. and Hsu, H.H. 2005. Observed by-catch of Taiwanese tuna longline fishery in the South Atlantic Ocean. Journal of the Fisheries Society of Taiwan 32(1): 69-77.
Kotas, J.E. 2004. Dinâmica de populações e pesca do tubarão-martelo Sphyrna lewini capturado no mar territorial e zona econômica exclusiva do sudeste-sul do Brasil. Ciênciias da engenharia ambienta. Escola de Engenharia de São Carlos. CRHEA ? USP.
Kotas, J.E. and Petrere, M. 2002. Estatísticas dos desembarques de tubarão martelo (Sphyrna spp) no sudeste e sul do Brasil. Capítulo da tese de doutoramento. Escola de Engenharia de São Carlos. CRHEA ? USP.
Kotas, J.E. and Petrere, M. 2002. Análise da distribuição e abundância relativa dos tubarões-martelo (Sphyrna lewini e Sphyrna zygaena) através do modelo linear generalizado (GLM). Capítulo da tese de doutoramento. Escola de Engenharia de São Carlos. CRHEA ? USP.
Krough, M. 1994. Spatial, seasonal and biological analysis of sharks caught in the New South Wales protective beach meshing programme. Australian Journal of Marine and Freshwater Research 45: 1087? 1106.
Last, P.R. and Stevens, J.D. 1994. Sharks and Rays of Australia. CSIRO, Melbourne, Australia.
Maguire, J.-J., Sissenwine, M., Csirke, J., Grainger, R. and Garcia, S. 2006. The state of world highly migratory, straddling and other high seas fishery resources and associated species. FAO Fisheries Technical Paper. FAO, Rome, Italy.
Marquez-Farias, F. 2000. Tiburones del Golfo de California. In: SEMARNAP Sustentabilidad y Pesca Responsable en México: Evaluación y Manejo 1999?2000. INP, SEMARNAP, México.
Matsushita, Y. and Matsunaga, H. 2002. Species composition and CPUE of pelagic sharks observed by Japanese observers for tuna longline fisheries in the Atlantic Ocean. Col.Vol.Sci.Pap. ICCAT.
Megalofonou, P., Damalas, D., Yannopoulos, C., De Metrio, G., Deflorio, M., De La Serna, J.M. and Macias, D. 2000. Bycatches and discards of sharks in the large pelagic fisheries in the Mediterranean Sea. Commission of the European Communities.
Megalofonou, P., Yannopoulos, C., Damalas, D., De Metrio, G., Deflorio, M., De La Serna, J.M. and Macias, D. 2005. Incidental catch and estimated discards of pelagic sharks from the swordfish and tuna fisheries in the Mediterranean Sea. Fishery Bulletin 103: 620-634.
Mejuto, J., Garcia-Cortes, B and De La Serna, J.M. 2002. Preliminary scientific estimations of by-catches landed by the spanish surface longline fleet in 1999 in the Atlantic ocean and Mediterranean sea. Col. Vol. Sci. Pap. ICCAT.
Pérez-Jiménez, J.C., Sosa-Nishizaki, O., Furlong-Estrada, E., Corro-Espinosa, D., Venegas-Herrera, A. and Barragán-Cuencas, O.V. 2005. Artisanal Shark Fishery at "Tres Marias" Islands and Isabel Island in the Central Mexican Pacific. Journal of Northwest Atlantic Fishery Science 35: 333?343.
Reid, D.D. and Krough, M. 1992. Assessment of catches from protective shark meshing off New South Wales beaches between 1950 and 1990. Australian Journal of Marine and Freshwater Research 43: 283?296.
Román-Verdesoto, M. and Orozco-Zöller, M. 2005. Inter-American Tropical Tuna Commission: Bycatches of Sharks in the tuna purse-seine fishery of the Eastern Pacific Ocean reported by observes of the IATTC, 1993-2004. Data Report 11. IATTC, La Jolla, California, USA.
Sáenz, C. 2005. Comercialización del pepino de mar, langosta y aletas de tiburón. Consultant report for TRAFFIC South America.
Scandol, J., Rowling, K. and Graham, K. 2008. Hammerhead sharks. Status of Fisheries Resources in NSW 2006/07. NSW Department of Primary Industries, Cronulla.
Simpfendorfer, C. 1993. The Queensland shark meshing program: analysis of the results from Townsville, North Queensland. In: J. Pepperell, J. West and P. Wood (eds), Shark Conservation. Proceedings of an International Workshop on the Conservation of Elasmobranchs held at Taronga Zoo, pp. 71?85. Sydney, Australia, February 24, 1991.
Simpfendorfer, C.A. 2005. Smooth hammerhead: Sphyrna zygaena. In: S.L. Fowler, R.D. Cavanagh, M. Camhi, G.H. Burgess, G.M. Cailliet, S.V. Fordham, C.A. Simpfendorfer and J.A. Musick (eds), Sharks, Rays and Chimaeras: The Status of the Chondrichthyan Fishes. Status Survey, pp. x + 461. IUCN SSC Shark Specialist Group, IUCN, Gland, Switzerland and Cambridge, UK.
Smale, M.J. 1991. Occurrence and feeding of three shark species, Carcharhinus brachyurus, C. obscurus and Sphyrna zygaena, on the eastern cape coast of South Africa. South African Journal of Marine Science 11: 31?42.
Soldo, A. and Jardas, I. 2002. Large sharks in the Eastern Adriatic. In: M. Vacchi, G. La Mesa, F. Serena and B. Seret (eds), Proceedings of the 4th European Elamobranch Association Meeting, pp. 141-155. Livorno, Italy.
Stevens, J.D. 1975. Vertebral rings as a means of age determination in the blue shark (Prionace glauca L.). Journal of the Marine Biological Association of the United Kingdom 55: 657?665.
Stevens, J.D. 1984. Biological observations on sharks caught by sports fishermen off New South Wales. Australian Journal of Marine and Freshwater Research 35: 573?590.
Tudela, S., Kai Kai, A., Maynou, F., El Andalossi, M. and Guglielmi, P. 2005. Driftnet fishing and biodiversity conservation: the case study of the large-scale Moroccan driftnet fleet operating in the Alboran Sea (SW Mediterranean). Biological Conservation 121: 65?78.
Vooren, C.M. 1997. Demersal elasmobranchs. In: U. Seeliger, C. Odebrecht and J.P. Castello (eds), Subtropical Convergence Environments, The Coast and Sea in the Southwestern Atlantic, pp. 141?145. Springer Verlag, Berlin, Germany.
Vooren, C.M., Klippel, S. and Galina, A.B. 2005. Biologia e status conservação dos tubarão-martelo Sphyrna lewini e S. zygaena. In: C.M. Vooren and S. Klippel (eds), Ações para a conservação de tubarões e raias no sul do Brasil, pp. 97-112. Igaré, Porto Alegre.
Walker, P., Cavanagh, R.D., Ducrocq, M. and Fowler, S.L. 2005. Northeast Atlantic (Including Mediterranean and Black Sea). In: S.L. Fowler, R.D. Cavanagh, M. Camhi, G.H. Burgess, G.M. Cailliet, S.V. Fordham, C.A. Simpfendorfer and J.A. Musick (eds), Sharks, Rays and Chimaeras: The Status of the Chondrichthyan Fishes, pp. 71-94. IUCN SSC Shark Specialist Group. IUCN, Gland, Switzerland and Cambridge, UK.
WildAid. 2005. Tocando fondo: La desaparición de los tiburones en el Pacífico Tropical Oriental.
WWF. 2005. EU bid to evade driftnet ban. Available at: At: http://photos.panda.org/about_wwf/where_we_work/africa/where/tunisia/index.cfm?uNewsID=21291.
Young, C. de. 2006. Review of the state of world marine capture fisheries management: Indian Ocean. FAO Fisheries Technical Paper. FAO, Rome, Italy.
Zerbini, A.N. and Kotas, J.E. 1998. A Note on Cetacean Bycatch in Pelagic Dritnetting off Southern Brazil. Report Of The International Whaling Commission. Cambridge, U.K.
|Citation:||Casper, B.M., Domingo, A., Gaibor, N., Heupel, M.R., Kotas, E., Lamónaca, A.F., Pérez-Jimenez, J.C., Simpfendorfer, C., Smith, W.D., Stevens, J.D., Soldo, A. & Vooren, C.M. 2005. Sphyrna zygaena. In: IUCN 2013. IUCN Red List of Threatened Species. Version 2013.2. <www.iucnredlist.org>. Downloaded on 23 April 2014.|
|Feedback:||If you see any errors or have any questions or suggestions on what is shown on this page, please fill in the feedback form so that we can correct or extend the information provided|