Size in Square Kilometres
11 697 km2
Qualifying Species and Criteria
Black Sea bottlenose dolphin – Tursiops truncatus ponticus
Criterion A, B(1, 2), C(2, 3)
Black Sea common dolphin – Delphinus delphis ponticus
Criterion A, B(2), C(2, 3)
Black Sea harbour porpoise – Phocoena phocoena relicta
Criterion A, B(1, 2), C(2, 3)
Marine Mammal Diversity
Tursiops truncatus ponticus, Delphinus delphis ponticus, Phocoena phocoena relicta, Stenella coeruleoalba, Tursiops truncatus truncatus, Delphinus delphis delphis, Monachus monachus
Download fact sheet
The Turkish Strait System, including the Istanbul Strait (Bosphorus), Marmara Sea and Çanakkale Strait (Dardanelles), connects the Black Sea with the Mediterranean. The Preboshoric area is the extension of the Turkish Straits System into the Black Sea, still under the influence of the Mediterranean waters. The IMMA holds important habitats both for the Mediterranean subpopulations and Black Sea subspecies of cetaceans (Endangered harbour porpoise – Phocoena phocoena relicta, Endangered bottlenose dolphin – Tursiops truncatus ponticus, Vulnerable common dolphin – Delphinus delphis ponticus). This IMMA is important as a foraging area and migration corridor, connecting the Black Sea and the Mediterranean Sea. It acts as a biological corridor and holds important habitats for foraging. Three cetacean species are present year-round and the bottlenose dolphins show some residency especially in the Istanbul Strait. The IMMA contains multiple cetacean subpopulations and subspecies that do not interact anywhere else.
Description of Qualifying Criteria
Criterion A – Species or Population Vulnerability
In the Turkish Straits System and Prebosphoric IMMA, both Mediterranean and Black Sea subspecies of bottlenose dolphins, common dolphins and harbour porpoises are found. The Black Sea subspecies of harbour porpoise and bottlenose dolphin are listed as Endangered (EN), and Black Sea common dolphins as Vulnerable (VU) on the IUCN Red list (Birkun 2008; Birkun and Frantzis 2008; Birkun 2012). Common dolphins and bottlenose dolphins in the Mediterranean Sea are listed as Endangered (EN) and Vulnerable (VU) respectively (Bearzi 2003; Bearzi et al. 2012). Further, the Turkish Straits System also holds the northern extent of Mediterranean Monk Seals, a species which has shown critical decline in its population, although with a recent rise in their sightings. Mediterranean Monk Seals were recently downgraded from Critically Endangered (CR) to Endangered (EN) on the IUCN Red list (Karamanlidis et al. 2019). The Turkish Straits System acts as the only connecting corridor between the Mediterranean and Black Sea populations of cetaceans, all of which hold threatened population status. Moreover, this is the only location in which the Black Sea subspecies of delphinids mix with the Mediterranean subpopulations.
Criterion B: Distribution and Abundance
Sub-criterion B1: Small and Resident Populations
Bottlenose dolphins are commonly observed within the Istanbul Strait and its neighbouring waters, with high site fidelity between and within years and seasons (Tezel 1958; Dede et al. 2016; Akkaya Baş et al. 2019). Among 87 bottlenose dolphin individuals photo-identified within the Istanbul Strait, 40 show regular presence within and between years, indicating a resident population with a likely home range that extends beyond the boundaries of the strait (Akkaya Baş et al. 2019). Additionally, common dolphins and harbour porpoises are frequently reported within the Istanbul Strait with year-round presence. While bottlenose dolphins represent the species most frequently encountered in the strait composing over 50% of sightings, harbour porpoises followed by common dolphins form 29% and 20% of the sightings, respectively (Bas et al. 2014). Although each species was present year-round in the strait, bottlenose dolphins were recorded most frequently in spring months, while it was winter for harbour porpoises and summer for common dolphins (Bas et al. 2014). Due to the lack of individual identification of common dolphins or harbour porpoises in the Strait, it is unclear if the year-round sightings belong to the same individuals, thus indicating a resident population, or that the species use the area as a corridor between the Black Sea and Mediterranean Sea or a combination of both.
Regarding Marmara Sea, all the cetacean species were frequently sighted throughout the year with highest encounters recorded in autumn followed by spring, with 0.8 and 0.5 sightings per 10nm, respectively (Dede and Öztürk 2007, Öztürk et al. 2009; Altuğ et al. 2011). However, due to the lack of photo-identification study in the Marmara Sea, their residency pattern still needs to be assessed.
Regarding their population genetics, a recent study revealed that common dolphins showed no significant genetic differences between the Turkish Straits System and the Mediterranean Sea (Tonay et al. 2020) and the existence of an isolated subpopulation of the harbour porpoise in the Turkish Straits System has been proposed based on mtDNA and ddRAD-seq analyses (Tonay et al. 2017; Uzun et al. 2018). Whilst anthropogenic disturbances mean that the Istanbul Strait itself is unlikely to be a reproductive area, the high presence of calves and juveniles of bottlenose dolphin and harbour porpoises suggest that TSS may hold breeding grounds.
Sub-criterion B2: Aggregations
Bottlenose dolphins, common dolphins and harbour porpoises show year-round presence in the Istanbul Strait and are regularly sighted in Marmara and Çanakkale Strait (Dede et al. 2016; Akkaya et al. 2017). Each species shows spatial-temporal aggregations within the Turkish Straits System IMMA. In general, common dolphins are sighted in spring and autumn, harbour porpoises mostly between March and July, while bottlenose dolphins are sighted throughout the year in the Istanbul Strait (Dede et al. 2016). Bottlenose dolphins aggregate year-round within the southern and northern entries of the Strait, with increased group size in winter seasons. Harbour porpoises and common dolphins aggregate in the northern entry of the Istanbul Strait, with group sizes reaching on average 9 and 12 individuals, respectively (Dede et al. 2016, Akkaya Bas et al. 2014; 2019). In general, cetacean sightings peaked in between May-June and October- November during the pelagic fish migration (Dede et al. 2016).
The Istanbul Strait is relatively well studied regarding the encounter rate of species. The average encounter rate of cetaceans was reported as 0.76 sightings per 10 km in the Istanbul Strait in 2009 (Öztürk et al. 2009). Another study estimated an average encounter rate of bottlenose dolphins of 4 groups (22 individuals) per 10 km, with a peak encounter rate of 11 groups (75 individuals) per 10 km during spring during surveys conducted between 2010 and 2014 (Akkaya et al. 2019). A year-round encounter rate of 0.33 groups (2.39 individuals) per 10km was estimated for common dolphins which peaked in summer with an encounter rate of 0.73 groups (4.97 individuals) per 10km (DMAD, unpublished data). In summary, during the pelagic fish migration, in spring and autumn, delphinid aggregation in the Istanbul Strait increases. It is predicted that the majority of these are Black Sea subspecies, but it should also be considered that they are Mediterranean subpopulations (for Tursiops and Delphinus) that arrived at this time.
Seasonal line transect surveys on cetacean populations in the Turkish Straits System estimated 669 bottlenose dolphin individuals (189-2372 95% CI) and 1192 (468-2592 95 %CI) common dolphins in April 1999 (Dede et al 2016). In a more recent study the abundance of bottlenose dolphins was estimated as 1978 individuals (95% CI: 781 – 5011), common dolphins as 702 individuals (95% CI: 245 – 2012) and harbour porpoise as 1940 individuals (95% CI: 632 – 5960) in July 2019 (TUDAV 2020 unpublished data).
Criterion C: Key Life Cycle Activities
Sub-criterion C2: Feeding Areas
The Istanbul Strait and its neighbouring waters to the Black Sea holds one of the most important and intensive fishing grounds in Turkey as a result of seasonal fish migration between the Mediterranean and Black Sea. It is in fact one of the top three fishing grounds of Turkey. Each of the three cetacean species show regular foraging behaviour within the Istanbul Strait. During the season of pelagic fish migration in spring and autumn, cetaceans use the Straits as a natural trap for feeding on migratory pelagic fishes. Passive acoustic monitoring also suggests that delphinids were mainly feeding or socializing in spring seasons in the Istanbul Strait (Dede et al. 2014; Kameyama et al. 2014). A behavioural study revealed that bottlenose dolphins and common dolphins, engage in foraging behaviour in spring and summer seasons at the northern entry, while bottlenose dolphins also forage throughout the year in the southern entry of the Strait and its neighbouring Marmara Sea. By contrast, in winter and summer seasons porpoises were concentrated in relatively smaller locations than bottlenose dolphins at the northern and southern entry of the strait (Akkaya Bas 2014).
Sub-criterion C3: Migration Routes
The Turkish Straits System IMMA is the only migration route for cetaceans between the Mediterranean and the Black Seas (Öztürk and Öztürk 1996). Recent studies on population genetics revealed that common dolphins are genetically similar in the Black Sea and Mediterranean Sea, which indicates the importance of the Turkish Straits System to their connectivity. Further, Black Sea harbour porpoises are sighted within the Northern Aegean Sea which is a species that is absent in the rest of the eastern Mediterranean Sea. Genetic evidence suggests that the Northern Aegean Sea populations of harbour porpoises are highly likely to be dispersed from the Black Sea through the Turkish Straits System (Tonay et al. 2017). A comparison between photo-identification catalogues revealed the presence of the same individual bottlenose dolphins both in the Istanbul Strait and Black Sea (unpublished data). Especially for common dolphins, which have high dispersal potential, the protection of narrow seaways like the Turkish Straits System to enhance connectivity may be crucial (Tonay et al. 2020).
Akkaya Bas, A. 2014. Investigation on the Interactions Between Cetaceans and Marine Traffic in the Istanbul Strait (PhD thesis). Istanbul University (in Turkish).
Akkaya Baş, A., Öztürk, A.A. and Öztürk, B. 2014. Selection of critical habitats for bottlenose dolphins (Tursiops truncatus) based on behavioural data, in relation to marine traffic in the Istanbul Strait, Turkey. Marine Mammal Science 31: 979–997.
Akkaya Bas, A., Christiansen, F., Amaha Öztürk, A., Öztürk, B. and McIntosh, C. 2017. The effects of marine traffic on the behaviour of Black Sea harbour porpoises (Phocoena phocoena relicta) within the Istanbul Strait, Turkey. PLoS ONE 12(3): e0172970.
Akkaya Baş, A., Öztürk, B., and Amaha Öztürk, A. 2019. Encounter rate, residency pattern and site fidelity of bottlenose dolphins (Tursiops truncatus) within the Istanbul Strait, Turkey. Journal of the Marine Biological Association of the United Kingdom, 99(4): 1009-1016.
ACCOBAMS-MOP 2010. ACCOBAMS-MOP4/2010/Res.4.15.
Bearzi, G. 2003. Delphinus delphis (Mediterranean subpopulation). The IUCN Red List of Threatened Species 2003: e.T41762A10557372. https://dx.doi.org/10.2305/IUCN.UK.2003.RLTS.T41762A10557372.en. Downloaded on 26 February 2021.
Bearzi, G., Fortuna, C. and Reeves, R. 2012. Tursiops truncatus (Mediterranean subpopulation). The IUCN Red List of Threatened Species 2012: e.T16369383A16369386. https://dx.doi.org/10.2305/IUCN.UK.2012-1.RLTS.T16369383A16369386.en. Downloaded on 26 February 2021.
Birkun Jr., A.A. 2008. Delphinus delphis ssp. ponticus. The IUCN Red List of Threatened Species 2008: e.T133729A3875256. https://dx.doi.org/10.2305/IUCN.UK.2008.RLTS.T133729A3875256.en. Downloaded on 25 February 2021.
Birkun, A. 2012. Tursiops truncatus ssp. ponticus. The IUCN Red List of Threatened Species 2012: e.T133714A17771698. https://dx.doi.org/10.2305/IUCN.UK.2012.RLTS.T133714A17771698.en. Downloaded on 25 February 2021.
Birkun Jr., A.A. and Frantzis, A. 2008. Phocoena phocoena ssp. relicta. The IUCN Red List of Threatened Species 2008: e.T17030A6737111. https://dx.doi.org/10.2305/IUCN.UK.2008.RLTS.T17030A6737111.en. Downloaded on 25 February 2021.
Birpınar, M.E., Talu, G.F. and Gönençgil, B. 2009. Environmental effects of maritime traffic on the İstanbul Strait. Environ Monit Assess 152: 13.
Dede, A., 1999. Investigations on the marine mammals population living in the Turkish Straits System (Doctoral dissertation, PhD thesis. Istanbul University, Istanbul, Turkey (in Turkish).
Dede, A., Öztürk, A.A., Akamatsu, T., Tonay, A.M., and Öztürk, B. 2014. Longterm passive acoustic monitoring revealed seasonal and diel patterns of cetacean presence in the Istanbul Strait. Journal of the Marine Biological Association of the United Kingdom. 94 (6): 1195-1202
Dede, A., Tonay, A.M., Öztürk, A.A., and Öztürk, B. 2016. Status of the marine mammals population of the Sea of Marmara. In: M.N. Çağatay, E.Özsoy, Ne. Balkıs, Nu. Balkıs, B. Öztürk, (Eds). The Sea of Marmara Marine Biodiversity, Fisheries, Conservation and Governance, pp. 863-879. Istanbul: Turkish Marine Research Foundation Publication no: 42.
Kameyama, S., Akamatsu, T., Dede, A., Öztürk A.A., and Nobuaki, A. 2014. Acoustic discrimination between harbour porpoises and delphinids by using a simple twoband comparison. J. Acoust. Soc. Am. 136 (2): 922-929.
Karamanlidis, A.A., Adamantopoulou, S., Tounta, E. and Dendrinos, P. 2019. Monachus monachus (Eastern Mediterranean subpopulation). The IUCN Red List of Threatened Species 2019: e.T120868935A120869697. https://dx.doi.org/10.2305/IUCN.UK.2019-1.RLTS.T120868935A120869697.en. Downloaded on 25 February 2021.
Öztürk, B. 1994. Evaluation of the present status and trend of monk seal populations in Turkey. In: Present Status and Trend of the Mediterranean Monk Seal (Monachus monachus) Populations. RAC/SPA (UNEP), Tunis, UNEP (OCA)) /MED WG.87/4, p.33.
Öztürk, B. and Öztürk, A.A. 1996. On the biology of the Turkish straits system. Bulletin de l’Institut Océanographique 17: 205–221.
Öztürk, A.A., Dede, A., Tonay, A.M., and Öztürk, B. 2009. Cetacean surveys in the Istanbul (Bosphorus) Strait in 2007-2008. 23rd Annual Conf. European Cetacean Society, Istanbul, Turkey.
Tezel, R. 1958. Dolphins that cannot be seen in the Strait, Fish and Fisheries. Publication of EBK, Vol 6, No 1 (in Turkish).
Tonay, A.M., Yazıcı, Ö., Dede, A., Bilgin, S., Danyer, E., Aytemiz, I., Maracı, Ö., Öztürk, A.A., Öztürk, B., and Bilgin, R. 2017. Is there a distinct harbor porpoise subpopulation in the Marmara Sea? Mitochondrial DNA Part A 28(4): 558-564.
Tonay, A.M., Uzun, B., Dede, A., Öztürk A.A., Danyer E., Danyer Aytemiz, I., Bilgin, S., Öztürk, B., and Bilgin, R. 2020. Population genetic structure of the short-beaked common dolphin from the Black Sea and the Turkish Straits System. Mitochondrial DNA Part A. 31 (6): 257–264.
TUDAV 2020. The Marmara Sea Cetacean Survey MarCet 2019. Turkish Marine Research Foundation Report.
Uzun, B., Tonay, A.M., Dede, A., Danyer, E., Danyer Aytemiz, I., Öztürk, Amaha A., Öztürk, B., Bilgin, R. 2018. Genetic investigation on the population structure of the harbour porpoises living
in Turkish waters by double digest restriction associated DNA (ddRAD) sequencing. 32. Conference of European Cetacean Society, 6-10 April 2018, La Spezia, Italy. 79pp.
Yüce, H. 1990. Investigation of the Mediterranean water in the Strait of Istanbul (Bosphorus) and the Black Sea. Oceanologica Acta 13 (2): 177-186.
Zaitsev. Y. 2008. An Introduction to the Black Sea Ecology. 228 p. Odessa: Smil Edition and Publishing Agency ltd.