First documented presence of Galeocerdo cuvier (Péron & Lesueur, 1822) (ELASMOBRANCHII, CARCHARHINIDAE) in the Mediterranean basin (Libyan waters)
© The Author(s) 2016
Received: 9 September 2016
Accepted: 9 September 2016
Published: 17 October 2016
One male and one female specimen of tiger shark, Galeocerdo cuvier (Péron & Lesueur, 1822), were accidentally caught by a drifting longline for swordfish in the south Mediterranean (Libyan waters). This finding confirms beyond any doubt that the tiger shark may be encountered in the waters of the Mediterranean Sea. Although records of this species has previously been reported, the information is partial or dubious, due to the lack of a description of the individuals found or the uncertain provenance of preserved material. Our finding confirms the record of this species in the southern part of the Mediterranean basin. Images, as well as morphometrics and information on stomach contents are given. Based on the size of the individuals, it is considered that the two specimens were born recently, presumably inside the Mediterranean Sea and likely close to the area where the individuals were found.
Our report is the first tiger shark record documented by photographic evidence, in the Mediterranean Sea. The new findings, in this particular case of two recently born individuals, may contribute to addressing the question of whether the presence of the tiger shark can be considered occasional (as vagrant or isolated), or proof of its stable occurrence in the region.
Tiger sharks belong to the Family of CARCHARHINIDAE Jordan & Evermann, 1896. This species can be considered circumglobal, found at all latitudes excluding Polar Regions. They generally live in warm, temperate and tropical seas and are considered vagrant in the Eastern North Atlantic (Ebert & Stehmann, 2013) including the Mediterranean Sea (Golani et al. 2002). Tiger shark normally resides further south; including the Azores, Morocco and Canary Islands as far as the Ghana coasts, but it is probable that the species has a wider distribution range in the area. It is also present from the coast of the U.S.A. stretching to Uruguay, including the Gulf of Mexico and Caribbean islands and in the Pacific and Indian oceans and Red Sea (Compagno, 1984; Randall, 1992; Bonfil & Abdallah, 2004; Ebert & Stehmann, 2013).
The maximum reported size of the tiger shark is 740 cm in total length (TL) and 3110 kg (Fourmanoir, 1961). However, tiger sharks are generally not longer than 500 cm in TL. The tiger shark is the only viviparous carcharhinid shark to exhibit internal incubator that does not develop a yolk-sac placenta (Bram et al., 2005); it is able to produce one of the larger litter sizes with 10–82 young per litter (Tester, 1969; Bass et al., 1975; Simpfendorfer, 1992) with a gestation period between 12 to 16 months in the Northern Hemisphere (Clark & von Schmidt, 1965). Mating normally occurs in the spring and pupping takes place throughout spring and early summer, usually from April to June. Size at birth ranges between 46 and 90 cm TL (Compagno, 1984; Randall, 1992; Simpfendorfer, 1992).
Materials and methods
The tiger shark specimens were caught by Tripoli fishers using artisanal drifting longlines baited with sardines in order to target swordfish. This kind of gear, locally named “bringali sayeb”, fish between 10–500 m in the water column, and is especially utilized by “mator” boats. These vessels have an average power of 214,86 kW and range in length from 5 to over 18 m (12 m on average). In the early 2000s, mator boats constituted the 28 % of the 1800 artisanal fishing boats operating in Libya. Only few mator boats target swordfish (Lamboeuf, 2000). The longline gear is made of a main monofilament (Ø 2–3 mm) of about 14 km long. One double line snood, consisting of a monofilament (Ø 1.3 mm) of 1.5 m with hooks (size number 01), is connected to the main line every 50 m. Every 5 hooks a float is connected the main line by a monofilament 3.5 m long.
Morphometric measurements for tiger Shark Galeocerdo cuvier caught in the Libyan coasts
Presecond dorsal length
Prefirst dorsal length
1st dorsal anterior margin
1st dorsal base length
1st dorsal height
Dorsal caudal margin
Preventral caudal margin
Stomach contents of tiger sharks, female and male, caught along the coasts of Libya
• Cephalopod beak
• Semi digested cephalopod
• Semi digested fish (9 cm) probably Clupeiformes
• Semi digested fish (14 cm) probably Mackerel
• Pair of cephalopod beaks
• Semi digested cephalopod
Other morphometric measurements are reported in Table 1. The stomach contents of both the female and male specimens were not significant regarding to the possibility of recognizing any organisms present. Indeed, in both cases, the contents of the stomachs, cephalopods and fishes, were almost completely digested and difficult to determine at the species level (Table 2).
The Mediterranean Sea has a long and complex history, which left traces in the actual status of its fauna and flora. After the opening of the Suez Canal and climate changes occurring at global and Mediterranean levels resulting in increased mean sea and surface temperatures, immigrant fauna and flora species, called lessepsian, moved into the Mediterranean from the Red Sea through the Suez Canal (Por, 1978). This phenomenon is still on-going. Continuous and important exchanges of marine organisms also occur at the Strait of Gibraltar between the Mediterranean Sea and the Atlantic Ocean. The Libyan coasts, positioned in the south of the Mediterranean, may be affected by immigration from both origins. This wide area is characterised by different habitats and topography.
In the Mediterranean, many elasmobranch populations are now rare due to intense fishing activity, in which they are target or by-catch. Such fishing pressure has produced local extinctions or stock reductions of some elasmobranchs making certain fishing activities no longer economically viable (Ferretti et al., 2008). Such phenomena are less intense in the southern part of the basin, especially along the Libyan coasts. In fact, in this area, some artisanal fisheries using fixed gillnets, bottom set nets and drifting longlines still target cartilaginous fish such as Carcharhinidae, Lamnidae, Rhinobathos spp. and Squatina squatina (Lamboeuf, 2000). For this reason, the catch of some top predators such as the tiger shark near the coast is likely. Tiger sharks, especially juveniles, are taken as by-catch in many fisheries around the world, including those using longlines targeting swordfish and tuna, particularly those operating close to the continental shelves (Anderson, 1985; Berkeley & Campos, 1988).
Our finding can be considered the first well-documented occurrence of G. cuvier in the southern Mediterranean. It confirms the sporadic occurrence of the species in the Mediterranean Sea. However this record cannot be taken as a proof of the stable occurrence of the species in the region or of a geographic extension of the species in to the Mediterranean Sea, even if, recently, 5 nm north of the Gorgona Island (North West Mediterranean), one of us has personally observed another specimen of about 2 m long, during a sportfishing on 29th of September 2015, unfortunately no photo was taken. As noted, the previous records led to doubts about the occurrence of tiger sharks in the Mediterranean basin (Serena, 2005) one from Malaga, Spain (Pinto de la Rosa, 1994) and the second from Sicily, Italy (Celona, 2000) were based only on the description of the jaws with no certified evidence of their provenance. The information in both publications is not accompanied by any photographic documentation of the whole individual and in one case (Pinto de la Rosa, 1994) the description was very limited.
Tiger sharks give birth generally along coastal areas at depths lower than 100 m. The growth of young tiger sharks is quite rapid and they nearly double their size over the first year of life (Branstetter et al., 1987; Randall, 1992; Smith et al., 1998). Therefore, the specimens described here (male 95.8 cm and female 97.4 cm) are likely to have been born recently in that area probably in the second part of 2014 and hence are assumed to be only a few months old. Juvenile tiger sharks are very slender with flexible bodies, swim with an inefficient motion and are very vulnerable to predators (Branstetter et al., 1987). It is unlikely that they were able to swim for very long distances as those needed to reach Libyan waters from either the Red Sea or the Atlantic. As a consequence, there are two possible alternative explanations for the finding of those two juvenile specimens. The first one is to hypothesize that the two pups were delivered from a resident female. Alternatively, these pups could have been delivered by a pregnant vagrant female. It has been reported that tiger sharks undertake trips of thousands of kilometres (8,000 km in 99 days (Heithaus et al., 2007), or 1,800 km in 48 days (Holmes et al., 2014) and gestation periods of 12–16 months have been estimated (Clark & von Schmidt, 1965). Therefore it is possible that mating could have happened outside the Mediterranean. Indeed, more compelling arguments are needed to support an enlargement of the distribution range and stable presence of the tiger shark in the Mediterranean waters.
Increased tropical influx through the Gibraltar Strait and the Suez Canal has resulted in the so-called “tropicalization” of the Mediterranean Sea (Bianchi & Morri, 2003). Until the mid 20th century, alien species introduction, establishment, and expansion rates were low (Zenetos et al., 2008), mainly as a result of the water temperature and salinity barriers between the Red Sea and the Mediterranean Sea (Galil, 2006). The dispersal success and expansion of an invasive species depends upon many aspects after the suitability of the abiotic environment. The occasional specimens of tiger sharks recorded up to now are unable to support any real dispersal process linked to climate change.
The data used for the present short note were obtained thanks to the collaboration of artisanal fishery fishermen of the Tripoli harbour. We are very grateful to the fishermen of the Tripoli harbour for their collaboration. Thanks also to Alvaro Juan Abella and Cecilia Mancusi (ARPAT, Italy) for the invaluable suggestions and for the revision of the text. Special thanks to the National Authority for Scientific Research of Libya for funding the project of invasive marine species in the Libyan coasts. Thanks also to Anassuya Ramachandran (Francis Crick Institute Limited, London, UK) and Ronan Russell (UCSF School of Medicine, San Francisco, USA) for reviewing the English language used in the text. Finally we want to thank the anonymous referees for suggesting appropriate changes which made the text more comprehensive.
All authors read and approved the final manuscript.
The authors declare that they have no competing interests.
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