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Research Article
Additional records of the little sleeper shark, Somniosus rostratus (Elasmobranchii: Squaliformes: Somniosidae), in Mediterranean Sea
expand article infoGianni Insacco, Bruno Zava§, Filippo Spadola|, Danilo Scannella, Alan Deidun#, Franco Cigala-Fulgosi¤, Massimiliano Valastro«, Antonio Di Natale«, Corrado Piccinetti», Maria Corsini-Foka˄
‡ Museo Civico di Storia Naturale, Comiso, Italy
§ Wilderness Studi Ambientali, Palermo, Italy
| Università degli Studi di Messina, Messina, Italy
¶ Italian Institute for Environmental Protection and Research, Palermo, Italy
# University of Malta, Msida, Malta
¤ Unaffiliated, Parma, Italy
« Aquastudio, Messina, Italy
» Laboratorio di Biologia Marina e Pesca dell’Università di Bologna in Fano, Fano, Italy
˄ Hellenic Centre for Marine Research, Institute of Oceanography, Hydrobiological Station of Rhodes, Rhodes, Greece
Open Access

Abstract

This study investigates the distribution and morphometrics of the little sleeper shark, Somniosus rostratus (Risso, 1827), in the Mediterranean Sea. Ten sharks caught as bycatch between 2009 and 2019 in the northern sectors of the Strait of Sicily, the south Tyrrhenian Sea, the northwestern Ionian Sea, and the south Adriatic Sea using drifting longlines, as well as five retrieved from the Tripoli (Libya) marketplace, were morphologically confirmed to represent S. rostratus. The sharks exhibited typical characteristics for this species and were all caught from deep waters, indicating a potential mesopelagic habit. The study also utilized literature reviews and global databases for a comprehensive mapping of S. rostratus distribution in the Mediterranean Sea, which revealed sporadic occurrences in the eastern Mediterranean and an absence in the north Adriatic Sea. Morphometric data provided insights into the reproductive characteristics of S. rostratus. The study highlights the ecological significance of the Strait of Sicily (Central Mediterranean Sea) for the species, indicating it as a likely spawning area, and underscores the impact of the interactions between sharks and pelagic drifting swordfish fisheries in the Mediterranean, which result in increased mortality rates for threatened shark and ray species. Prioritizing conservation measures for endangered elasmobranch populations is crucial for maintaining marine ecosystem balance and ensuring fishery resource sustainability.

Keywords

biodiversity, distribution, elasmobranch Mediterranean Sea, Somniosus rostratus

Introduction

The deep-water little sleeper shark, Somniosus rostratus (Risso, 1827), is a rare or apparently rare chondrichthyan (Garibaldi et al. 2012; Guallart et al. 2013), currently assessed at the global level as Least Concern by the IUCN Red List (Finucci et al. 2020).

The little sleeper shark is found at depths from 180 m to 2734 m, reaches a maximum total length of 1314 mm (Weigmann 2016), and apparently feeds mainly on cephalopods, but also benthic invertebrates and fishes (Golani 1986; Garibaldi et al. 2012; Guallart et al. 2013; Barría et al. 2015a; Capapé et al. 2020; Ebert and Dando 2022). The apparent rarity of this shark may be due to several reasons, including a naturally low population density (Garibaldi et al. 2012; Guallart et al. 2013), the inadequacy of the fishing gears deployed in catching this species, and the non-exploitation of deep bottom-dwelling habitats throughout its range.

The general distribution of S. rostratus includes the Eastern Atlantic, extending from areas off the United Kingdom and Ireland, to France, Portugal, the Madeira Islands, Canary Islands and Western Sahara, as well as the Western Central Atlantic, possibly from areas located off Cuba, up to the Mediterranean Sea (Compagno 1984; Yano et al. 2004; Ebert and Stehmann 2013; Ebert et al. 2013; Meléndez et al. 2017; Finucci et al. 2020; Ebert and Dando 2022). In the Mediterranean, S. rostratus is prevalent in the western sector, albeit not very abundant, and appears sporadically in the eastern sector; to date, it is absent in the north Adriatic and the Black Sea (Goren and Galil 2015; Serena et al. 2020; Damalas et al. 2022; Ebert and Dando 2022).

In this study, the capture of S. rostratus from the Strait of Sicily in the central Mediterranean, plus additional records from the Tyrrhenian, Ionian, Adriatic, and Libyan waters is described, and the distribution records of this species in the basin, recently reviewed by Capapé et al. (2020), is updated.

Material and methods

Three specimens of Somniosus rostratus were captured in the northern sectors of the Strait of Sicily, by a commercial fishing vessel as swordfish bycatch, two specimens (S1 and S2) on 13 September 2015 off Licata (Fig. 1: map ID 36; Fig. 2A), the third (S3) on 15 September 2015 off Gela (Fig. 1: Map ID 37; Fig. 2A) (Table 1). Mesopelagic drifting longlines (Kirby Sea; fishing hook No. 2) baited with mackerel and squids were used. Catches were carried out during the night. The fishermen declared that they had never landed those sharks before. Between August and September 2016, two additional specimens (S4 and S5) were fished by the same boat and with the same gear reported above, off Scoglitti (Fig. 1: map ID 38; Fig. 2B) (Table 1).

Figure 1. 

Geographical distribution of Somniosus rostratus based on the previous records and presently reported study within the Mediterranean Basin. The red star shows occurrence records for this study; the green circle represents occurrence records with geographic coordinates, from the literature; the pink represents occurrence records without geographic coordinates; and the black triangles are GBIF occurrence records (GIBF 2024). The numbers refer to the “Map ID” in the Table 1 to identify the reference of the record.

Figure 2. 

Somniosus rostratus from the Strait of Sicily. A. females S1 (MSNC 4885), S2 (WSASr1), and S3 (MSNC 4886) captured in 2015 (Fig. 1) Map ID 36 [S1–S2], 37 [S3]. B: female S4 (MSNC 4887), and male S5 (MSNC 4888) captured in 2016 (Fig. 1) Map ID 38 [S4–S5].

Table 1.

Summary of Somniosus rostratus records in the Mediterranean (The majority of records cited after Capapé et al. 2020).

Marine region Locality Map ID Year Latitude (N), Longitude (E) Depth [m] Fishing gear N W [g] TL [mm] FL [mm] Reference
Adriatic Sea South sector 19 [1]
Off Apulia 34 2012? 427–788 MEMO [2] [3]
South sector 41 2019 41°17′38.92′′N, 17°43′31.09′′E 1140 MD-LL 1♂ 3121 890 This study (S10)
South sector 42 2019 41°45′00.00′′N, 17°22'00.12''E 1100 LL 4 Bueloni personal communication
Aegean Sea North of Crete 10 [4] [5] [6] [7]
North sector 18 1990–1992 100–500 BT [8] [7]
Algerian Sea 9 [9]
100 km off Algiers (Dellys, Cap Djenet, Bou Haroun, Cherchell) 28 2009–2015 36°55′N, 3°53′E 19 [10]
36°43′N, 3°36′E
36°40′N, 4°40′E
36°37′N, 2°11′E
Catalan Sea Off Barcelona 16 1987 41°02′N, 3°04′E 1975 LL 1♂ 680 [11]
Off Barcelona 22 1994 40°42′N, 1°32′E 180 LL 1♂ 650 [11]
Off Barcelona 23 1999 41°01′N, 2°16′E 534 BT 1♀ pr. 1000 [12]
Ibiza Channel 35 2013–2014 550–670 BT 20 (8♀ pr.) 874–1042 [13] [14]
Catalan Sea Gulf of Lions 33 2011–2013 40–2200 BT 5 715–980 [15] [16]
Gulf of Lions Off Nice 1 1826 Very deep 1♀ 310 [17]
Off Nice 1 1874 1♀ pr. [18]
Off Nice 1 1880? [19]
Off Nice 1 1880 1♂ 705 [20]
Off Nice 1 1900 1♂ 282 [20]
Off Nice 1 1882? 1♀ 490 [20]
Ionian Sea East of Sicily 4 1892 1 [21]
East of Sicily, off Simeto River estuary 5 1893 1000 1♀ pr. [21]
Northwestern 15 1985–1988? >200 [22]C
Eastern sector 21 Questionable in [23]
Northwestern sector 27 2009 37°48′42.01′′N, 16°56'08.99''E MD-LL 1♀ ~5000 This study (S6)
Northwestern sector 30 2010 38°45′15.01′′N, 17°51′24.01′′E MD-LL 1 ~8000 This study (S7)
Northwestern sector 30 2010 38°53′32.39′′N, 17°35′46.79′′E MD-LL 1 ~6000 This study (S8)
Levantine Sea Off Haifa 13 1985 32°58′44′′N, 34°35′46′′E 1330 LL 1♂ 775 [24]
Off Haifa 14 1985–1991 32°31′00′′N, 34°02′00′′E 1280–1500 LL 8 (2♀ pr.) [25]
33°02′00′′N, 34°37′00′′E
Off Israel coasts 17 1988–1999 734–1558 BT [26]
Syrian waters 24 2001 35°36′N, 35°39′E 450 LL 76 1020 (largest) [27] [28] [29] [30] [31]
Off Fethiye 25 2008 36°25′00′′N, 28°47′00′′E 2500 LL 1♀ 810 [32]
Libyan Sea Libyan waters, west 12 [33] [34] [35] [36]
Tripoli market NM 2006 5 This study, ADN personal observation (S11-S15)
Off South of Crete 26 2009 34°32′37.68′′N, 25°46′30.00′′E 1200 OT 1 [37]
Ligurian Sea 2 820 [38 [39]
2 1♀pr. [40] [1]
2 [41] [40] [42] [1]
2 2010? >1500 LL 25♂ >655 [43] [44]
2 2010? >1500 LL 30♀ Some ♀ > 800 [43] [44]
2 2015 [45]
Genova 6 1899 1♀ 955 [20]
Ligurian Sea Sestri Levante 7 1899 1♀ 937 [20]
Sestri Levante 7 1979 44°10′N, 9°25′E 1♀ pr. 822 [20]
Bonassola 8 1909 [40]
Ventimiglia 11 1♀ 953 [20]
Strait of Gibraltar and Alboran Sea 39 [46]
Strait of Sicily Malta Island 32 2011 LL 2♀ 935 1036 [47]
Malta Island 32 2015 1 [48]
Malta Island 32 2016 1 [48]
Off Licata 36 2015 36°45′59.93′′N, 13°51′36.67′′E ~700 MD-LL 2♀ pr. 6850 6650 992 985 This study (S1, S2)
Off Gela 37 2015 36°42′12.00′′N, 14°08′09.00′′E ~700 MD-LL 1♀ pr. 7480 990 This study (S3)
Off Scoglitti 38 2016 36°45′29.04′′N, 14°05′03.40′′E MD-LL 1♀ 1♂ 5950 1140 925 618 This study (S4, S5)
Off Ras Jebel, northeastern Tunisian coast 40 2019 37°31′28′′N, 10°17′10′′E 120 BT 990 [49]
Tyrrhenian Sea Off Palermo 3 1874 1♀ 880 [50]
20
Off Anzio 29 2010 LL 1♀ 800 [51]
Aeolian Islands 31 2011 38°43′31.20′′N, 14°59′29.40′′E MD-LL 1 5000 This study (S9)
Western Mediterranean NM 2009–2013 36–44°N, 2–5°E LL 24 715–980 [52] [16]

The specimens S1, S3, S4, and S5 were deposited at the Museo Civico di Storia Naturale, Comiso, Italy (MSNC) and S2 was deposited at the Wilderness Studi Ambientali, Palermo, Italy (WSA). At these institutions, selected morphometric measurements were taken to the nearest 1 mm using a digital caliper, following Compagno (1984); weight was determined to the nearest 0.1 g (Table 2). Females were dissected, the uterine contents examined and, in case of pregnancy, eggs and embryos were counted and measured. The following catalog numbers were assigned to the above five sharks: S1, MSNC 4885; S2, WSASr1; S3, MSNC 4886; S4, MSNC 4887; and S5, MSNC 4888.

Table 2.

Selected biometric characters of specimens S1–S5 of Somniosus rostratus captured on the Strait of Sicily (specimens defined and illustrated in Fig. 2).

Character Specimen reference number
S1 S2 S3 S4 S5
Date of capture 13 Sep. 2015 13 Sep.2015 15 Sep. 2015 26 Aug. 2016 14 Sep. 2016
Sex
Total weight (g) 6850 6650 7480 5950 1140
Morphometric characters mm [% of TL] mm [% of TL] mm [% of TL] mm [% of TL] mm [% of TL]
Total length (TL) 992 985 990 925 618 91.3
Fork length 903 91.0 903 91.7 906 91.5 873 94.4 564 81.6
Precaudal length 812 81.9 806 81.8 805 81.3 772 83.5 504 35.9
Pre-first dorsal length 347 35.0 352 35.7 347 35.1 327 35.4 222 67.0
Pre-second dorsal length 678 68.3 650 66.0 684 69.1 647 69.9 414 20.1
Head length 203 20.5 202 20.5 194 19.6 183 19.8 124 1.6
Eye length 16 1.6 16 1.6 15 1.5 14 1.5 10 1.5
Eye height 13 1.3 13 1.3 12 1.2 11 1.2 9 17.3
Prebranchial length 147 14.8 138 14.0 135 13.6 146 15.8 107 20.7
Prepectoral length 205 20.7 204 20.7 197 19.9 188 20.3 128 61.2
Prepelvic length 609 61.4 612 62.1 626 63.2 594 64.2 378 7.8
Premouth length 63 6.4 65 6.6 65 6.6 55 5.9 48 6.0
Pectoral base 62 6.3 66 6.7 66 6.7 59 6.4 37 12.1
Pectoral anterior margin 123 12.4 122 12.4 113 11.4 118 12.8 75 5.3
Pectoral inner margin 35 3.5 43 4.4 43 4.3 46 5.0 33 9.1
Pectoral posterior margin 75 7.6 80 8.1 94 9.5 98 10.6 56 12.3
Pectoral height 94 9.5 97 9.8 96 9.7 118 12.8 76 8.9
First dorsal base 78 7.9 84 8.5 84 8.5 83 9.0 55 10.5
First dorsal anterior margin 106 10.7 105 10.7 113 11.4 112 12.1 65 6.1
First dorsal inner margin 49 4.9 59 6.0 55 5.6 53 5.7 38 6.6
First dorsal posterior margin 64 6.5 74 7.5 68 6.9 56 6.1 41 18.4
Dorsal margin of caudal 180 18.1 184 18.7 162 16.4 183 19.8 114 7.1
Lower postventral margin of caudal 83 8.4 80 8.1 80 8.1 88 9.5 44 14.4
Preventral margin of caudal 138 13.9 140 14.2 130 13.1 142 15.4 89 91.3

Other records of S. rostratus collected through experimental fishing surveys are furthermore presented (Table 1):

  • On 22 July 2009, in the northwestern Ionian Sea, a specimen (S6) (Fig. 1: map ID 27) (Fig. 3) was caught using a drifting longline set with 1100 hooks (soaking time 24 h 30 min), targeting swordfish (six swordfish were captured, with a total weight of 233 kg), along with a specimen of Pteroplatytrygon violacea (Bonaparte, 1832) (≈7 kg).
  • On 21 and 22 July 2010, two specimens of S. rostratus (S7 and S8) were captured in the northwestern Ionian Sea (Fig. 1: map ID 30), using a drifting longline equipped with 1100 hooks (soaking time ≈ 14 h). The longline was targeting swordfish, resulting in the capture of 11 specimens weighing (in total) 395 kg and 8 specimens weighing 411 kg, respectively. Furthermore, on 21 July 2010, a specimen of Zu cristatus (Bonelli, 1819) (≈4 kg), along with four specimens of Ruvettus pretiosus Cocco, 1833 (total weight ≈ 44 kg), were unintentionally caught and subsequently discarded. On 22 July 2010, only three specimens of R. pretiosus (total weight ≈ 44 kg) were caught and discarded.
  • On 14 July 2011, a specimen (S9) was captured in the southern Tyrrhenian Sea around the Aeolian Islands (Fig. 1: map ID 31), using a drifting longline (1100 hooks; soaking time 6 h 30 min) targeting swordfish (8 swordfish specimens weighing 167 kg) along with a specimen of Z. cristatus (≈4 kg).
  • On 4 September 2019, in the southern Adriatic (Fig. 1: map ID 41), a specimen (S10) was caught using a drifting longline. The fishing operation occurred between 03:45 and 09:39 hours.
  • In 2006, one of us (ADN) observed the presence of five specimens of S. rostratus (S11 to S15) in the Tripoli fish market. After interviewing the fishers, it was ascertained that the five specimens were caught with pelagic longlines, together with other sharks, off the central-western Libyan coast.

For S6–S9 only an approximate weight was obtained, while TL and weight were measured for S10; S6–S10 were discarded. No data were collected for S11–S15.

The geographical distribution of the little sleeper shark was mapped gathering all existing scientific literature concerning previous records of the species in the Mediterranean Sea (Table 1). In addition, any missing data was added using the Global Biodiversity Information Facility (GBIF 2024), excluding all non-georeferenced data. The map was created using Quantum GIS software (QGIS 2020), following the methodology outlined by Sardo et al. (2022).

The records of S. rostratus in the Mediterranean Sea provided by Capapé et al. (2020) have been updated, with the addition of information on shark capture and size, when available (Table 1).

Results

All of the fifteen sharks recorded in the presently reported study were identified as Somniosus rostratus following the keys and descriptions given by Cigala-Fulgosi and Gandolfi (1983), Compagno (1984), Serena (2005), Ebert et al. (2013), and Capapé et al. (2020) (Table 1).

The four specimens S1–S4 were females with a total length (TL) ranging from 925 mm to 992 mm (973 ± 32 mm) and a weight ranging from 5950 to 7480 g (6732 ± 630 g); the males S5 and S10 were 618 mm and 890 mm TL and 1140 g and 3121 in weight, respectively (Tables 1, 2) (Fig. 2).

The brief description of the specimens is the following: short snout, pointed in its profile, rounded underside, dorsal fins without spines, equal-sized dorsal fins, anal fin absent, long ventral caudal lobe, first dorsal fin on back closer to pectorals than pelvic fins, short keels on base of caudal fin (Figs 2, 3, 4A, 4B). Color: body brown, fins darker, snout black. The dental formula obtained from S3 was: 31–31 teeth in the upper jaw and 18–18 teeth in the lower jaw (Fig. 4C).

Figure 3. 

Somniosus rostratus (female S6) captured in the northwestern Ionian Sea in 2009 (Fig. 1: map ID 27).

Figure 4. 

Somniosus rostratus. (A) Lateral view of head (specimen S2). (B) Ventral view of head (specimen S2). (C) Anterior view of dissected jaw with full dental armament (specimen S3).

The selected morphometric measurements of S1–S5, expressed as % of TL (Table 2) as well as the dental formula obtained from S3, were included in the ranges retrieved from the literature (Cigala-Fulgosi and Gandolfi 1983; Golani 1986; Herman et al. 1989; Capapé et al. 2020; Hsu et al. 2020).

Females S1–S3 were pregnant. The number of embryos ranged from 9 to 14 and they were very small, from 2 to 50 mm in length (Table 3) (Fig. 5).

Figure 5. 

Somniosus rostratus embryo, approximately 50 mm in length, of the S3 caught in the Strait of Sicily in 2015 (MSNC 4886; Fig. 1: map ID 35; see Table 2).

Table 3.

Additional biometric characters of three females of Somniosus rostratus captured in the Strait of Sicily in 2015 (specimens defined and illustrated in Fig. 2).

Character Specimen reference number
S1 S2 S3
Gonad weight [g] 422 R/788 L 596 R/470 L 416 R/813 L
Liver weight [g] 671 595 429
Intestine weight [g] 281 370 448
Number of embryos in oviducts 4 R/5 L 7 R/7 L
Length of embryos [mm] 2 40–50
Number of ova in oviducts 5 R/4 L

Discussion

The TL of three of the four females of Somniosus rostratus caught from the Strait of Sicily corresponded to the values expected for adult specimens (Barrull and Mate 2001; Guallart et al. 2013) and approached the maximum size observed in Mediterranean waters (Table 1) (Barría et al. 2015b; De Lojola Fernández et al. 2017).

The little sleeper shark is an ovoviviparous species, that gives birth to a litter of 8–17 young whose length ranges between 210 and 280 mm (Compagno 1984; Golani et al. 2006; Froese and Pauly 2022). After evisceration, different developmental stages of gonads in our females of similar size were observed and the low number of ova and embryos counted supported the hypothesis that the species is not very prolific (Capapé et al. 2020).

Somniosus rostratus is generally captured as bycatch by bottom trawlers and mesopelagic longlines at various depths, frequently in deep waters, and it is generally discarded (Séret et al. 2009; FAO 2016; Finucci et al. 2020; Carpentieri et al. 2021). Similarly, specimens in the presently reported study were incidentally caught in the relatively deep waters of the central Mediterranean Sea and of the south Adriatic Sea through drifting mesopelagic longlines used in swordfish fishery. Although generally described as a bathydemersal shark, the wide range of depths at which it has been captured in the Mediterranean (Table 3) and the remains of the mesopelagic cephalopod Histioteuthis sp. in its stomach could suggest a mesopelagic habit for S. rostratus, able to actively move in the water column (Guallart et al. 2013; Guallart and García-Salinas 2015; Barría et al. 2015a). Generally, pregnant females are caught near the bottom (Guallart et al. 2013).

Some of the specimens reported in Table 1, as well as embryos, fetuses and/or anatomical parts of this species of shark caught in the basin are deposited in the collections of various Museums of Natural History; for example in Spain (Barrull et al. 1999; Barrull and Mate 2001), France (Yano et al. 2004; Chagnoux 2022), Czech Republic (Šanda and De Maddalena 2003), Italy (Doderlein 1878–1879; Tortonese 1938, 1956; Di Palma 1979; Sarà and Sarà 1990; Vanni 1992; Mizzan 1994; Mancusi et al. 2002; Carnevale et al. 2007), and the United Kingdom (Gray 1851; Ridewood 1921; Yano et al. 2004). Additionally, a number of Mediterranean basin findings are documented in GBIF (2024), covering areas off Valencia and Alicante, Spain, and the southern Adriatic Sea (Fig. 1).

As already observed (Irmak and Özden 2021; Ebert and Dando 2022), the density of records of S. rostratus appears highest in the western sector of the Mediterranean Sea, prevalently in the Ligurian and Catalan seas (Fig. 1; Table 3). Abundant bycatches were observed between the Balearic Islands and the Spanish coast (De Loyola Fernández et al. 2017) and off the Ligurian coast (Garibaldi et al. 2012, Garibaldi 2015), while nursery grounds were identified in the eastern and northeastern waters of Spain as well as in the Ligurian Sea (Capapé et al. 2020).

The occurrence of S. rostratus is known from the eastern sector of the basin (Goren and Galil 2015; Golani 2021; Damalas et al. 2022), but to date, it appears to be more sporadic in eastern areas than in the western sector (Fig. 1; Table 1). Until recently, the occurrence of S. rostratus in the Turkish waters required confirmation (Kabasakal 2019, 2020); the presence of the species was ascertained for the southwestern waters of the country by Irmak and Özden (2021) and S. rostratus was therefore added to the shark fauna of the Turkish waters (Kabasakal 2021). In the Aegean waters, the little sleeper shark was rarely observed (Papaconstantinou 2014) and it was not detected during the experimental bottom trawl surveys performed from 2005 to 2014 in the southern sectors of these waters (Peristeraki et al. 2017). In Syrian waters, S. rostratus has been reported as frequent by Ali (2018), but it has not been observed in recent surveys (Alkusairy and Saad 2018).

In the central Mediterranean and in the Adriatic Sea, which include the areas of interest of the presently reported note, S. rostratus has been found in the Strait of Sicily, the western Ionian, and the South Adriatic Sea (Table 1). Although based on literature (Compagno 1984; Séret et al. 2009; Finucci et al. 2020; Ebert and Dando 2022), the distribution range of S. rostratus also comprises the western Libyan waters, the species has not been listed in a recent inventory of the Chondrichthyes of Libyan coasts (Shakman et al. 2023); the occurrence in this region was confirmed by one of us (ADN) in 2006 after the observation of specimens at the fish market of Tripoli. In the Strait of Sicily, the little sleeper shark has been recorded for the first time in Maltese waters, in 2011 (Vella et al. 2013) and, more recently, in 2019, the species was detected for the first time in northeastern Tunisian waters (Capapé et al. 2020).

Additional reasons for the diverse distribution of S. rostratus in the various areas of the Mediterranean Sea might be the different degree of coverage of on-board observers on fishing vessels or of landing controls or even the different density or distribution of scientific surveys conducted in the various parts of the basin. Any of these factors is potentially able to bias our perception and knowledge of the geographical distribution of this species.

Although the occurrence of S. rostratus is generally known off Sicilian coasts (Tortonese 1956; Ragonese et al. 2013), the species was never reported in various experimental bottom trawl surveys performed in the Sicily Channel during the period 1994–2020 (Scacco et al. 2002; Relini et al. 2010; Ragonese et al. 2013; Geraci et al. 2017; Fernandez-Arcaya et al. 2019; Ragonese 2022; Farrugio and Soldo unpublished * ).

Consequently, the findings of S. rostratus documented here are of huge importance, not only because they determine the presence of this uncommon shark in the northern sectors of the Strait of Sicily, but also because they could indicate the presence of a likely spawning area for the species.

The whole Strait of Sicily is recognized as an Ecologically or Biologically Significant Area (EBSA) (Consoli et al. 2016; UNEP 2016; Di Lorenzo et al. 2018) and the presence of important nurseries and spawning areas for many fishery resources (Consoli et al. 2016), as well as for threatened and endangered species of elasmobranchs, heavily impacted by human pressures such as fishery activities, have been underlined numerous times (Zava et al. 2016, 2020, 2022; Colloca et al. 2019; Geraci et al. 2019; Scannella et al. 2020).

The interaction between sharks and pelagic or mesopelagic drifting swordfish fisheries, which unintentionally catch sharks and other species as bycatch, leading to detrimental impacts on shark populations, is another significant issue raised by this note. These interactions can result in increased mortality rates for sharks and rays, further exacerbating the decline of already threatened and endangered species, many of which are not properly assessed in the Mediterranean Sea, due to the insufficient availability of data. The International Commission for the Conservation of Atlantic Tunas (ICCAT) has the mandate to assess the pelagic species that might be impacted by the fisheries targeting tunas and billfish species and on-board observers have been imposed on a defined percentage of some fleets, but the available data is still insufficient for any reliable assessment of the shark species concerned in the Mediterranean Sea. Understanding the dynamics of this interaction and its ecological consequences is crucial for effective conservation and management efforts concerning this species. Conservation measures that prioritize the protection of endangered elasmobranch populations are crucial for maintaining the balance of marine ecosystems and for ensuring the sustainability of fishery resources.

Conclusions

The presently reported study provides valuable insights into the distribution and morphological characteristics of the deep-water little sleeper shark, Somniosus rostratus, in the Mediterranean Sea. It underscores the challenges associated with studying deep-water species, particularly those with low-population densities or elusive behaviors, and sheds light on the potential reasons for the perceived rarity of S. rostratus.

The findings suggest a mesopelagic habit for the little sleeper shark, supported by the range of depths at which it has been captured and the presence of mesopelagic cephalopods in its stomach. Additionally, morphometric data offer insights into the reproductive characteristics of the species, emphasizing the ecological significance of the Strait of Sicily (central Mediterranean Sea) as a potential spawning area. Given the relevance of the Strait of Sicily as an Ecologically or Biologically Significant Area (EBSA), the study underscores the need for effective conservation measures in this region. It encourages further research and monitoring efforts to better understand and protect essential habitats for marine life.

The study reveals that S. rostratus, along with other elasmobranchs, is captured as bycatch in pelagic swordfish longline fisheries. The resulting interactions lead to increased mortality rates for vulnerable shark and ray species, highlighting the importance of considering the ecological consequences of bycatch interactions, especially for threatened and endangered elasmobranch populations. The International Commission for the Conservation of Atlantic Tunas (ICCAT) and other relevant bodies are urged to address data gaps and assess the impact of fisheries on the conservation status of deep-water shark species in the Mediterranean.

In conclusion, this research contributes valuable data on the distribution and characteristics of S. rostratus and underscores broader conservation challenges related to bycatch interactions. It emphasizes the need for proactive measures to ensure the sustainability of Mediterranean marine ecosystems. The study serves as a call to action for enhanced collaboration between scientific communities, fisheries management organizations, and conservation bodies to address the complexities surrounding the conservation of deep-water shark species in the region.

Acknowledgments

The authors warmly thank Captain Vincenzo Belgiorno of the FV Santa Barbara (IPE 956), and its crew, Salvatore Belgiorno, Angelo Cellura, Giuseppe Moncada, and Paolo De Marco for sharing information on the captures of Somniosus rostratus and depositing the specimens at the Museo Civico di Storia Naturale di Comiso, Ragusa, Italy. The authors also thank the crews of the MP Ariete (04CT01061) and MP Arcadia (14ME00571), as well as Dr Elia Bueloni, Centro Sperimentale per la Tutela Degli Habitat (CESTHA), Ravenna; Prof Luca Sineo, Dipartimento Scienze e Tecnologie Biologiche, Chimiche e Farmaceutiche, University of Palermo; and Attia Mohamed, Rhodes, Greece, for technical support; Giovanna Polizzi and Claudia Manno, Wilderness studi ambientali, Palermo, Prof Gianluca Sarà for allowing us to consult the library of the father Dr Raimondo Sarà. Authors are further grateful to anonymous reviewers for helpful and constructive suggestions on the first version of the manuscript.

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