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Mediterranean and Black Sea Cetacean Red List Assessment<br />

Tursiops truncatus<br />

Israeli<br />

Mediterranean<br />

coast (Israel)<br />

Ionian Sea<br />

(Greece)<br />

Amvrakikos Gulf<br />

(Greece)<br />

Central Adriatic Sea<br />

(Kornati & Murtar<br />

Sea, Croatia)<br />

North-eastern<br />

Adriatic Sea<br />

(Kvarneric, Croatia)<br />

North-eastern<br />

Adriatic Sea<br />

(Kvarneric, Croatia)<br />

North-eastern<br />

Adriatic Sea<br />

(Kvarneric, Croatia)<br />

North Adriatic Sea<br />

(Gulf of Trieste,<br />

Slovenia)<br />

- inshore<br />

1999-<br />

2004<br />

-<br />

85<br />

-<br />

480 inshore<br />

1993-<br />

2003<br />

2001-<br />

2005<br />

- 48<br />

400 inshore<br />

0.38 152 -<br />

136-<br />

186<br />

300 inshore 2002 - 14<br />

800 inshore<br />

1990-<br />

2004<br />

- 120<br />

1,000 inshore 1997<br />

113<br />

0.06<br />

2,000 inshore 2003<br />

102<br />

0.05<br />

600 inshore<br />

2002-<br />

2004<br />

0.08 47<br />

Information on status and trends of the subpopulation is fragmentary because of the evident substructure<br />

and the diversity of the monitoring efforts and the fisheries with dolphin bycatch. The only Mediterranean<br />

area with quantitative historical information that can be used for direct calculation of trend and present<br />

status is the northern Adriatic Sea. There, bottlenose dolphin numbers likely declined by at least 50%<br />

over the past 50 years, largely as a consequence of historical killing, followed by habitat degradation<br />

and overfishing (Bearzi et al. 2004). For other parts of the northern Mediterranean, e.g. Spain, Italy and<br />

southern France, the available information on removals and trends in abundance is less precise and<br />

clear but suggests similar trends (Silvani et al. 1992; reports by workshop participants). A decline in<br />

abundance of about 39% was observed in a limited area of the north-eastern Adriatic between 1995 and<br />

2003 (Fortuna submitted). The nature and extent of by-catch and other threats vary with region, but the<br />

overall pattern leads to the suspicion that the basin population has been reduced by at least 30% over<br />

the last 60 years. In recent years, as suggested by sightings and strandings, gaps have appeared in a<br />

formerly continuous distribution along the Mediterranean coast of Spain, indicating a reduction in the area<br />

of occupancy (reported by workshop participants).<br />

Habitat and Ecology<br />

Bottlenose dolphins in the Mediterranean are commonly regarded as coastal/inshore animals (Notarbartolo<br />

di Sciara and Demma 1997; Gannier 2005). However, they are regularly found in deep waters near the<br />

continental slope in the Alborán and Balearic seas (Forcada et al. 2004; Cañadas and Hammond in press)<br />

and in continental-shelf offshore waters of the Adriatic Sea and Tunisian plateau (Bearzi et al. 2004; Ben<br />

Naceur et al. 2004).<br />

The mean size of bottlenose dolphin groups varies according to location, from typically small numbers in<br />

coastal waters (Bearzi et al. 1997; Ben Naceur et al. 2004) to larger numbers in pelagic waters (Forcada<br />

et al. 2004; Cañadas and Hammond in press). Coastal bottlenose dolphin groups average 7 individuals,<br />

whereas the mean size of offshore groups is about 35. Association with other cetacean species is<br />

uncommon, except in the Alborán Sea (Cañadas et al. 2002).<br />

Mediterranean bottlenose dolphins are catholic feeders with a preference for demersal prey (Blanco et al.<br />

2001). In coastal waters they can spend up to 5% of their time following trawlers (Bearzi et al. 1999). They<br />

also sometimes forage around fish-farm cages or take fish from gillnets (Lauriano et al. 2004; Diaz et al.<br />

2006).<br />

Threats<br />

Owing to their occurrence in coastal waters, bottlenose dolphins are regularly exposed to a wide variety<br />

of human activities. Those in the Mediterranean were subjected to hunting until the 1960s (Bearzi et al.<br />

2004). The main threats in recent times include: 1) reduced availability of prey caused by overfishing<br />

and environmental degradation; 2) incidental mortality in fishing gear; and 3) toxic effects of xenobiotic<br />

Annex 3: Regular Species<br />

68

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