ArticlePDF Available

Exploring a possible nursery ground of white shark (Carcharodon carcharias) in Edremit Bay (northeastern Aegean Sea, Turkey)

Authors:

Abstract and Figures

Between 1 July 2008 and 14 April 2018, five young-of-the-year (YOY) (TL range 85-175 cm) and six juvenile (TL range 180-300 cm) white sharks (Carcharodon carcharias) were caught off the Turkish coast of the Aegean Sea. The mean length + standard deviation of YOY and juvenile white sharks were 138.1+34 cm and 206.6+46 cm, respectively. The YOY white sharks were caught only in Edremit Bay and juveniles were captured in several localities outside of the mentioned region. Based on the findings of previous studies, it is suggested that Edremit Bay may serve as a nursery ground for C. carcharias in the northern Aegean Sea and the surrounding insular marine area outside of the bay waters, may serve as a growing and feeding ground for juveniles until maturity. The white shark population in the Mediterranean may be considered at greater risk of local extirpations than previously thought, and effective management of Edremit Bay as a nursery ground is crucial regarding the overall survival of white sharks in the Mediterranean.
Content may be subject to copyright.
176
J. Black Sea/Mediterranean Environment
Vol. 26, No. 2: 176-189 (2020)
RESEARCH ARTICLE
Exploring a possible nursery ground of white shark
(Carcharodon carcharias) in Edremit Bay (northeastern
Aegean Sea, Turkey)
Hakan Kabasakal
ORCID ID: 0000-0001-8189-9748
Ichthyological Research Society, Tantavi Mah., Menteşoğlu Cad., İdil apt., 30/4, 34764
Ümraniye, İstanbul, TURKEY
Corresponding author: kabasakal.hakan@gmail.com
Abstract
Between 1 July 2008 and 14 April 2018, five young-of-the-year (YOY) (TL range 85-175
cm) and six juvenile (TL range 180-300 cm) white sharks (Carcharodon carcharias) were
caught off the Turkish coast of the Aegean Sea. The mean length + standard deviation of
YOY and juvenile white sharks were 138.1+34 cm and 206.6+46 cm, respectively. The
YOY white sharks were caught only in Edremit Bay and juveniles were captured in several
localities outside of the mentioned region. Based on the findings of previous studies, it is
suggested that Edremit Bay may serve as a nursery ground for C. carcharias in the northern
Aegean Sea and the surrounding insular marine area outside of the bay waters, may serve
as a growing and feeding ground for juveniles until maturity. The white shark population
in the Mediterranean may be considered at greater risk of local extirpations than previously
thought, and effective management of Edremit Bay as a nursery ground is crucial regarding
the overall survival of white sharks in the Mediterranean.
Keywords: Nursery ground, white shark, Carcharodon carcharias, Aegean, conservation,
survival
Received: 25.05.2020, Accepted: 14.08.2020
Introduction
Nursery areas, which have been recognized as a concept in the scientific literature
for nearly a century, are widely considered to be essential habitats for sharks
(Heithaus 2007; Heupel et al. 2007). Since shark nurseries have been defined as
essential habitats for breeding of a given shark species (Heithaus 2007), the
development of appropriate management for nursery areas relies on the ability to
177
accurately identify those areas that are of greatest importance (Heupel et al.
2007).
White shark, Carcharodon carcharias (Linnaeus, 1758), is one of the four species
of the family Lamnidae, occurring in the Mediterranean Sea. It is an epipelagic
shark, inhabiting coastal and off shore waters, from surface down to a depth of
1300 m (Serena 2005). Its distribution range includes the whole Mediterranean,
but currently absent in the Marmara and Black Seas (De Maddalena and Heim
2012; Kabasakal 2014). Global distribution of C. carcharias extends in temperate
oceans of both hemispheres, and rarely found in tropical waters (Serena 2005).
White sharks can be defined as ‘nomads’ of the oceans, because of their two-year
long-distance migrations between widely separated nursery areas (Domeier and
Nasby-Lucas 2013). Male and female white sharks are known to have site fidelity,
which is termed as ‘philopatry’ (Domeier and Nasby-Lucas 2013; Gubili et al.
2010), which means that adults will return to the areas for breeding, where they
were born.
In the recent Red List assessment by Rigby et al. (2019), global conservation
status of C. carcharias was evaluated as vulnerable; however, according to Dulvy
et al. (2016) and Otero et al. (2019), C. carcharias is critically endangered in the
Mediterranean Sea. Therefore, effective management of its nursery grounds is
crucial for the survival of the species in the Mediterranean, where it has little or
no contemporary immigration from the Atlantic (Gubili et al. 2010). Due to the
occurrence of young-of-the-year (YOY) and pregnant female white sharks,
Tunisian and Sicilian neritic waters have been historically and contemporarily
considered as the main nursery area of C. carcharias in the Mediterranean Sea
(Boldrocchi et al. 2017; Bradai et al. 2012; De Maddalena and Heim 2012;
Fergusson 1996; Saidi et al. 2005). According to Boldrocchi et al. (2017),
between the second half of the 19th and the begining of the 20th century, Sibenik
Bay and the nearby Kvarner Gulf area might also serve as a nursery ground for
C. carcharias.
Following the incidental captures of two newborn specimens in Edremit Bay
(Figure 1), in early July 2008 (Kabasakal and Gedikoğlu 2008), three more YOY
white sharks were also incidentally captured in the same area (Kabasakal 2014;
Kabasakal et al. 2018). Occurrence of five YOY specimens in a close vicinity in
different years suggests that Edremit Bay may serve as a nursery area for C.
carcharias in the northern Aegean Sea. Since appropriate management of nursery
areas relies on accurate identification and mapping of these essential habitats
(Heupel et al. 2007), it is crucial to determine the approximate boundaries of this
possible nursery ground in Edremit Bay. In the present study, based on available
data, attempts to draw a preliminary map of this nursery ground are made, and
the implications of commercial fisheries, continuing in the same region are
discussed.
178
Materials and Methods
Study Area
The Aegean Sea is topographically divided into two basins by (approximately)
the 38° parallel, i.e. into the north and south Aegean (Papaconstantinou 1992).
Mean monthly sea surface temparatures vary from 8°C in the north during winter,
up to 26°C in the south during summer (Poulos et al. 1997). The Aegean
archipelago is a typical archipelago of continental islands, which are forming
groups of minor islands in wide marine space (Türküstün 2015).
Figure 1. Map showing the capture localities of YOY and juvenile white sharks, off
Turkish coast of Aegean Sea. Numbers are same with those in Table 1.
179
Data Collection
Since the white shark is a critically endangered species and protected in certain
parts of the Mediterranean (Otero et al. 2019; Serena 2005), the selection of an
appropriate sampling method for the present study was an instance of typical
opportunistic research, consisting in dead animal sampling (Jessup 2003). A
regular screening of scientific literature, social media, local newspaper - both
printed and online - provided information on the YOY and juvenile white sharks,
incidentally captured off Turkish coast of Aegean Sea (Figure 1). Nine out of 11
white sharks were previously published and relevant information of these
specimens were exctracted from Kabasakal (2014), Kabasakal and Gedikoğlu
(2008), Kabasakal and Kabasakal (2015), and Kabasakal et al. (2009, 2018). Two
specimens are new records (Table 1). Capture data (type of fishing gears, date
and locality of captures, total length (TL) in cm and weight (W) in kg) were
recorded for new specimens. Age distribution of YOY and juvenile white sharks
was assessed using the following length categories (Boldrocchi et al. 2017): YOY
(<1.75 m TL) and juvenile (>1.75-3.0 m TL).
Results and Discussion
Between 1 July 2008 and 14 April 2018, five YOY (TL 85-175 cm) and six
juvenile (TL 180-300 cm) white sharks were caught off Turkish coast of Aegean
Sea (Figure 1). These specimens are depicted on Figures 2 and 3, and relevant
information are presented in Table 1. The mean length + standard deviation of
YOY and juvenile white sharks were 138.1+34 cm and 206.6+46 cm,
respectively. YOY white sharks (specimens 1, 2, 5, 7 and 9) were caught only in
Edremit Bay and juveniles were captured in several localities outside of the bay
(Gökçeada, specimens 3 and 8; Çanakkale, specimen 4; Yeni Foça, specimen 6;
Karaburun, specimen 11; and Didim, specimen 10; Table 1; Figure 1). One of the
YOY white sharks (specimen 5) was released alive (Figure 3). Two specimens
(18.1%) were captured in purse-seining fishery, and eight specimens (72.7%)
were incidentally captured by artisanal fishermen deploying coastal stationary-,
gill- or trammel-nets, and one specimen (9.09%) was captured by means of a
bottom-trawler. Thus, nearly 82 % (n=9) of the YOY and juvenile white sharks
were captured in demersal fisheries.
Umbilical scars were seen in three newborns (specimens 1, 2 and 5; Figure 4),
which were captured in early July (Table 1), and other two YOY white sharks
were captured in January and April. Juvenile white sharks were captured in April
(n=2), June (n=1), September (n=1), January (n=1) and February (n=1) (Table 1).
Most of the young white sharks were recorded in spring and summer months.
180
Figure 2. YOY and juvenile white sharks examined in the present study. (A) specimen 7;
(B) specimen 4; (C) specimen 6; (D) specimen 10; (E) specimen 9; (F) specimen 8;
(G) specimen 11; (H) specimen 1; (I) specimen 3; and (J) specimen 2. Specimen
numbers are same with the numbers accompanying the bold dots () seen on Figure 1.
Capture details of the specimens are presented on Table 1.
Figure 3. Captured images from the video of releasing a YOY white shark
(specimen 5 in Table 1, Figure 1), off the coast of Altınoluk
(Video footage: Cenk Balkan).
181
Table 1. Capture data and relevant references of YOY and juvenile white sharks
examined in the present study
No*
Date
Locality
W
(kg)
Gear
References
1
1 July 2008
Altınoluk
-
Gill-net
Kabasakal and Gedikoğlu
(2008)
2
4 July 2008
Altınoluk
-
Gill-net
Kabasakal and Gedikoğlu
(2008)
3
21 Feb. 2009
Gökçeada
47.5
Bottom-trawl
Kabasakal et al. (2009)
4
15 April 2009
Çanakkale
102
Purse-seine
Kabasakal et al. (2009)
5
6 July 2011
Altınoluk
-
Trammel-net
Kabasakal (2014)
6
19 Sept. 2014
Yeni Foça
40
Stationary-
net
Kabasakal and Kabasakal
(2015)
7
2 January 2016
Altınoluk
-
Stationary-
net
Kabasakal et al. (2018)
8
January 2017
Gökçeada
-
Stationary-
net
This study
9
April 2017
Altınoluk
-
Gill-net
This study
10
4 June 2017
Didim
60
Purse-seiner
Kabasakal et al. (2018)
11
14 April 2018
Karaburun
-
Stationary-
net
Kabasakal et al. (2018)
*Numbers seen in ‘No’ column are same with the numbers in Figure 1.
In a recent study on distribution, ecology and status of the white shark in the
Mediterranean Sea, Boldrocchi et al. (2017) reported on the captures of 29 YOYs
in several locations, including the Aegean Sea where six out of 29 Mediterranean
YOYs were captured. Furthermore, Boldrocchi et al. (2017) stated that juvenile
white sharks have been recorded in all regions of the Mediterranean, except in the
Marmara Sea. Available data on the occurrence of C. carcharias in Turkish
waters reveal that YOY or juvenile white sharks have not been historically or
contemporarily occurred in the Marmara Sea (Kabasakal 2003, 2014).
Movements of white sharks in the Mediterranean Sea is closely associated with
the migrations of the bluefin tuna, Thunnus thynnus (Linnaeus, 1758) (De
Maddalena and Heim 2012). Majority of the historical catch records of C.
carcharias in the Marmara Sea consisted of adult specimens (>450 cm TL),
which have been the bycatch of tuna handliners (Kabasakal 2003, 2016).
Presently it can only be speculated that the Marmara Sea might have served as a
historical feeding ground for adult white sharks. The mean length of YOYs
recorded in several parts of the Mediterranean Sea ranged from 104+24.9 cm
(Aegean Sea) to 151+14.1 cm (Sicilian Channel) (Boldrocchi et al. 2017). With
the addition of recent captures of specimens with TL 160 and 175 cm (specimens
7 and 9), however, mean TL of YOYs in the Aegean Sea should be updated as
138.1+34 cm.
182
Figure 4. Umbilical scars (birth marks) on the ventral surfaces of neonates; (A)
specimen 1, and (B) specimen 2 in Table 1.
The seasonality of occurrence of YOYs and juveniles in the Turkish Aegean Sea
well coincides with the seasonality data presented by Boldrocchi et al. (2017),
Santana-Morales et al. (2012), De Maddalena and Heim (2012), and White et al.
(2019), who reported a close affinity of the high numbers of occurrences with the
warmer months of the year. According to Boldrocchi et al. (2017) and De
Maddalane and Heim (2012), YOYs were captured in spring and summer months
in the Mediterranean. In the present study, four out of five YOYs were captured
in summer (early July, specimens 1, 2 and 5) and mid-spring (April, specimen 9),
and one YOY was captured in winter (January, specimen 7) (Table 1). Total
length of the specimen 7 YOY was 175 cm, when it was captured in January, and
at that time no birth mark (umbilical scar) was seen. Thus, it can be supposed that,
183
the specimen 7 was born in the preceeding summer, and remained in Edremit Bay
nursery ground for further growing. According to Santana-Morales et al. (2012),
the umbilical scar was still visible in the white shark specimens of 150 and 163
cm TL.
Although juvenile white sharks are known to frequent inshore water (Harasti et
al. 2017), they are also known to travel for relatively long distances beyond the
perimeters of their nurseries (see eg. Bruce et al. 2019; Weng et al. 2007). Weng
et al. (2007) reported on a YOY, which moved 700 km away from its nursery
between late September and mid October. In a recent survey dealing with the
broad-scale movements of juvenile white sharks in eastern Australia, Bruce et al.
(2019) found that juveniles can travel for 1800 km, crossing from Bass Strait to
New Zealand. Soutward and northward occurrences of juveniles in remote
regions outside of Edremit Bay nursery were also observed (Figure 1). In the
northward of Edremit Bay, three juveniles were captured off Çanakkale and
Gökçeada coasts (specimens 3, 4 and 8), and in the southward, two juveniles
(specimens 6 and 11) were captured off İzmir coast, and one juvenile (specimen
10) was captured off Didim coast. As it is clearly seen on Figure 1, Aegean
seabord of Turkey has a peninsular coastline and assuming that specimen 11 was
born in Edremit Bay, then it should have been travelled more than 500 km before
it was captured off Didim. For the moment, on the basis of available data, it is not
possible to answer the question, whether specimen 11 was born in Edremit Bay
or in another unidentified nursery in the southern Aegean Sea. Despite the
uncertainties about the provenance of specimen 11, it had enough potential for
travelling from Edremit Bay to Didim, as suggested by the movement data of
juveniles given by Bruce et al. (2019) and Weng et al. (2007).
Offshore and coastal islands appear to offer several advantages to YOYs and
juveniles, as revealed, for example, by the studies of Curtis et al. (2018), Hoyos-
Padilla et al. (2016) and Klimley (1985). The preference for coastal and insular
water of the YOY and juvenile white sharks is reflected by the relatively shallow
depths at which these sharks were captured in the present study. Depth of the
bottom where the juvenile white sharks were captured was less than 150 m and
YOYs were captured in water as shallow as 10 m. As suggested by Hoyos-Padilla
et al. (2016), insular marine areas provides juvenile white sharks with an
opportunity to start their first offshore migrations, probably for feeding on
demersal prey and then coming back to their nursery grounds to avoid predators.
From this perspective, Edremit Bay nursery ground, which is surrounded by
offshore and coastal islands, provides a habitat for growing juveniles to gain
experience of movement between offshore islands and nearshore before departing
for long-distance migrations. Hoyos-Padilla et al. (2016) found that tagged
juvenile white sharks remained near Guadalupe Island for 12 to 14 months before
departing distant regions.
184
Throughout its global distribution range, survival of young white sharks is
threatened by the pressure of coastal artisanal fisheries with stationary nets, such
as gill-net or trammel-net fishery (Klimley 1985; Santana-Morales et al. 2012).
According to Santana-Morales et al. (2012), highest incidental captures of
juvenile white sharks were recorded in the artisanal bottom-set gill-nets, with
nearly 75% of sharks caught using this fishing gear in western Baja California
(Mexico). Curtis et al. (2018) also stated that bycatch of juvenile and YOY white
sharks in the New York Bight (western north Atlantic) occurs in gill-net fishery.
In an extensive research on the interactions of juvenile white sharks with gill-net
fishery, Lyons et al. (2013) reported that gill-net fishery is significantly and
positively correlated with the incidence of white shark captures. In the present
study, nearly 73% (8 out of 11) of white sharks were incidentally captured by
bottom-set nets, including stationary- (36.3%), gill- (27.2%) and trammel-nets
(9.09%). The addition of one specimen (9.09%), which was captured by a bottom-
trawler, reveals that nearly 82% (9 out of 11) of juveniles and YOYs of the present
study were captured in demersal fisheries (Table 1).
Previous studies revealed that, juvenile white sharks feed primarily on bottom
dwelling fishes (White et al. 2019), and nursery grounds in their coastal habitats
may overlap with areas highly impacted by fisheries (Boldrocchi et al. 2017).
According to Domeier and Nasby-Lucas (2013), YOY and juvenile white sharks
do not have the mass and strength for breaking through most commercial fishing
gear, thus they represent the most vulnerable stage of C. carcharias.
In conclusion, based on incidental captures of YOY white sharks between 2008
and 2018, it is suggested that Edremit Bay may serve as a nursery ground for C.
carcharias, in the northern Aegean Sea, and the surrounding insular marine area
from northward to southward outside of bay waters, may serve as a growing and
feeding ground for juveniles until maturity. Since juvenile fish abundance in
nursery areas, including YOYs, may provide an estimate of recruitment trends
(Harasti et al. 2016), an extensive in situ survey with nondestructive methods is
required to investigate the habitat use, site fidelity, relative abundance, seasonal
occurence and movements of YOY and juvenile white sharks, occurred in the
Edremit Bay and surrounding marine area. Since the white shark is critically
endangered in the Mediterranean Sea (Otero et al. 2019), the use of stereo-
BRUVs (Baited Remote Underwater Video) may provide a viable and
nondestructive method to obtain estimates of the size and presence of white
sharks, as proposed by Harasti et al. (2016). Based on available genetic data
(Gubili et al. 2010), Mediterranean white shark population may be considered at
greater risk of local extirpations than previously thought, and effective
management of Edremit Bay as a possible nursery ground is crucial regarding the
overall survival of Mediterranean white sharks.
185
Acknowledgments
Author thanks to fishermen for their friendly contributions during the white shark
investigation in Turkish waters which has been continuing since 2003. A special thank
goes to Mr. Cenk Balkan, for generously sharing the video of specimen 5. Author also
thanks to anonymous referees for their comments.
Edremit Körfezi’nde (kuzeydoğu Ege Denizi) büyük
beyaz köpekbalığının (Carcharodon carcharias) olası
üreme alanı
Öz
1 Temmuz 2008 ve 14 Nisan 2018 tarihleri arasında, Ege Denizi’nin Türkiye kıyılarında
5 tane yenidoğan (TB aralığı 85-175 cm) ve 6 tane juvenil (TB aralığı 180-300 cm) büyük
beyaz köpekbalığı yakalanmıştır. Yenidoğan ve juvenil büyük beyaz köpekbalıklarının
ortalama tam boyları (TB), sırasıyla, 138.1+34 cm ve 206.6+46 cm’dir. Yenidoğanlar
sadece Edremit Körfezi’nde yakalandıkları halde, juveniller körfez dışında kalan farklı ve
körfeze uzak bölgelerde yakalanmışlardır. Eldeki veriler, Edremit Körfezi’nin kuzey Ege
Denizi’nde C. carcharias’ın üreme alanı olduğunu akla getirmektedir. Ayrıca, körfezin
yakın ve uzak çevresindeki adaları kuşatan deniz alanları, görünüşe göre juvenil büyük
beyaz köpekbalıklarına olgunluğa erişinciye kadar beslenme ve gelişme alanı
sağlamaktadır. Akdeniz’de büyük beyaz köpekbalığı popülasyonunun karşı karşıya olduğu
yok olma riski düşünüldüğünden daha fazla olabilir. Bu bakımdan, Edremit Körfezi’ndeki
üreme alanında etkin bir yönetim planı uygulanması, Akdeniz’de büyük beyaz
köpekbalıklarının genel sağkalımları açısından kritik önemdedir.
Anahtar kelimeler: Üreme alanı, büyük beyaz köpekbalığı, Carcharodon carcharias,
Ege Denizi, koruma, sağkalım
References
Boldrocchi, G., Kiszka, J., Purkis, S., Storai, T., Zinzula, L., Burkholder, D.
(2017) Distribution, ecology, and status of the white shark, Carcharodon
carcharias, in the Mediterranean Sea. Reviews in Fish Biology and Fisheries 27:
515-534.
Bradai, M.N., Saidi, B., Enajjar, S. (2012) Elasmobranchs of the Mediterranean
and Black Sea: Status, Ecology and Biology. Bibliographic Analysis. Studies and
Reviews, No. 91. General Fisheries Commission for the Mediterranean, FAO,
Rome. 103 pp.
Bruce, B. D., Harasti, D., Lee, K., Gallen, C., Bradford, R. (2019) Broad-scale
movements of juvenile white sharks Carcharodon carcharias in eastern Australia
from acoustic and satellite telemetry. Marine Ecology Progress Series 619: 1-15.
186
Curtis, T.H., Metzger, G., Fischer, C., McBride, B., McCallister, M., Winn, L.J.,
Quinlan, J., Ajemian, M.J. (2018) First insights into the movements of young-of-
the-year white sharks (Carcharodon carcharias) in the western North Atlantic
Ocean. Scientific Reports 8: 10794.
De Maddalena, A., Heim, W. (2012) Mediterranean Great White Sharks. A
Comprehensive Study Including All Recorded Sightings. McFarland &
Company, Inc. Publishers, Jefferson, North Carolina & London.
Domeier, M. L., Nasby-Lucas, N. (2013) Two-year migration of adult female
white sharks (Carcharodon carcharias) reveals widely separated nursery areas
and conservation concerns. Animal Biotelemetry 1: 2. doi: 10.1186/2050-3385-
1-2.
Dulvy, N.K., Allen, D.J., Ralph, G.M. Walls, R.H.L. (2016) The Conservation
Status of Sharks, Rays and Chimaeras in the Mediterranean Sea (Brochure).
IUCN, Malaga, Spain.
Fergusson, I. K. (1996) Distribution and Autoecology of the White Shark in the
Eastern North Atlantic Ocean and the Mediterranean Sea. In: Great White Sharks.
The Biology of Carcharodon carcharias (eds., Klimley, A.P. D., Ainley, G.).
Academic Press. pp. 321-345.
Gubili, C., Bilgin, R., Kalkan, E., Karhan, S. Ü., Jones, C. S., Sims, D. W.,
Kabasakal, H., Martin, A. P., Noble, L. R. (2010) Antipodean white sharks on a
Mediterranean walkabout? Historical dispersal leads to genetic discontinuity and
an endangered anomalous population. Proceedings of the Royal Society B.
278: 1679-1686.
Harasti, D., Lee, K., Bruce, B., Gallen, C., Bradford, R. (2017) Juvenile white
sharks Carcharodon carcharias use estuarine environments in south-eastern
Australia. Marine Biology 164: 58.
Harasti, D., Lee, K. A., Laird, R., Bradford, R., Bruce, B. (2016) Use of stereo
baited remote underwater video systems to estimate the presence and size of white
sharks (Carcharodon carcharias). Marine and Freshwater Research 68 (7):
1391-1396.
Heithaus, M. R. (2007) Nursery areas as essential shark habitats: a theoretical
perspective. American Fisheries Society Symposium 50: 3-13.
Heupel, M. R., Carlson, J. K., Simpfendorfer, C. A. (2007) Shark nursery areas:
concepts, definition, characterization and assumptions. Marine Ecology Progress
Series 337: 287-297.
187
Hoyos-Padilla, E. M., Klimley, A. P., Galvan-Magana, F., Antoniou, A. (2016)
Contrasts in the movements and habitat use of juvenile and adult white sharks
(Carcharodon carcharias) at Guadalupe Island, Mexico. Animal Biotelemetry 4:
14
Jessup, D.A. (2003) Opportunistic research and sampling combined with fish and
wildlife management actions or crisis response. ILAR Journal 44: 277-285.
Kabasakal, H. (2003) Historical records of the great white shark, Carcharodon
carcharias (Linnaeus, 1758) (Lamniformes: Lamnidae), from the Sea of
Marmara. ANNALES - Series historia naturalis 13: 173-180.
Kabasakal, H. (2014) The status of the great white shark (Carcharodon
carcharias) in Turkey’s waters. Marine Biodiversity Records 7; eo: 1-8
doi:10.1017/S1755267214000980.
Kabasakal, H. (2016) Historical dispersal of the great white shark, Carcharodon
carcharias, and bluefin tuna, Thunnus thynnus, in Turkish waters: decline of a
predator in response to the loss of its prey. ANNALES - Series historia naturalis
26: 213-220.
Kabasakal, H., Bayrı, E., Ataç, E. (2018) Recent records of the great white shark,
Carcharodon carcharias (Linnaeus, 1758) (Chondrichthyes: Lamnidae), in
Turkish waters (Eastern Mediterranean). ANNALES Series historia naturalis
28: 93-98.
Kabasakal, H., Gedikoğlu, S.Ö. (2008) Two new-born great white sharks,
Carcharodon carcharias (Linnaeus, 1758) (Lamniformes; Lamnidae) from
Turkish waters of north Aegean Sea. Acta Adriatica 49: 125-135.
Kabasakal, H., Kabasakal, Ö. (2015) Recent record of the great white shark,
Carcharodon carcharias (Linnaeus, 1758), from central Aegean Sea off Turkey’s
coast. ANNALES Series historia naturalis 25: 11-14.
Kabasakal, H., Yarmaz, A., Gedikoğlu, S.Ö. (2009) Two juvenile great white
sharks, Carcharodon carcharias (Linnaeus, 1758) (Chondrichthyes; Lamnidae),
caught in the northeastern Aegean Sea. ANNALES Series historia naturalis 19:
127-134.
Klimley, A.P. (1985) The areal distribution and autoecology of the white shark,
Carcharodon carcharias, off the west coast of North America. Biology of the
White Shark A symposium. In: Sibley, G., Seigel, J.A., Swift, C.C. (Eds.).
Memoirs of the Southern California Academy of Sciences 9, pp. 15-40.
188
Lyons, K., Jarvis, E.T., Jorgensen, S.J., Weng, K., O’Sullivan, J., Winkler, C.,
Lowe, C.G. (2013) The degree and result of gillnet fishery interactions with
juvenile white sharks in southern California assessed by fishery-independent and
dependent-methods. Fisheries Research 147: 370-380.
Otero, M., Serena F., Gerovasileiou, V., Barone, M., Bo, M., Arcos, J.M.,
Vulcano A., Xavier, J. (2019) Identifcation guide of vulnerable species
incidentally caught in Mediterranean fsheries. IUCN, Malaga, Spain, 204 pp.
Papaconstantinou, C. (1992) General remarks on the Greek seas fish fauna.
Doriana 6: 8 pp.
Poulos, S.E., Drakopoulos, P.G., Collins, M.B. (1997) Seasonal variability in sea
surface oceanographic conditions in the Aegean Sea (Eastern Mediterranean): an
overview. Journal of Marine Systems 13: 225-244.
Rigby, C.L., Barreto, R., Carlson, J., Fernando, D., Fordham, S., Francis, M.P.,
Herman, K., Jabado, R.W., Liu, K.M., Lowe, C.G, Marshall, A., Pacoureau, N.,
Romanov, E., Sherley, R.B., Winker, H. (2019) Carcharodon carcharias. The
IUCN Red List of Threatened Species 2019: e.T3855A2878674.
http://dx.doi.org/10.2305/IUCN.UK.2019-3.RLTS.T3855A2878674.en
Saïdi, B., Bradaï, M.N., Bouaïn, A., Guélorget, O., Capapé, C. (2005) Capture of
a pregnant female white shark, Carcharodon carcharias (Lamnidae) in the Gulf
of Gabès (southern Tunisia, central Mediterranean) with comments on oophagy
in sharks. Cybium 29: 303-307.
Santana-Morales, O., Sosa-Nishizaki, O., Escobedo-Olvera, M.A., Onate-
Gonzalez, E.C., O’Sullivan, J.B., Cartamill, D. (2012) Incidental Catch and
Ecological Observations of Juvenile White Sharks, Carcharodon carcharias, in
Western Baja California, Mexico: Conservation Implications. In: Global
Perspectives on the Biology and Life History of the White Shark (ed., Domeier,
M.L.). CRC Press, Taylor & Francis Group, Boca Raton, pp.187-198.
Serena, F. (2005) Field identification guide to the sharks and rays of the
Mediterranean and Black Sea. FAO Species Identification Guide for Fishery
Purposes, FAO, Rome, 97 pp.
Türküstün, F.A. (2015) Aegean Islands by the Vision of Piri Reis. In: The Aegean
Sea Marine Biodiversity, Fisheries, Conservation and Governance. (eds.,
Katağan, T., Tokaç, A., Beşiktepe, Ş., Öztürk, B.) Turkish Marine Research
Foundation (TUDAV), Publication No: 41, Istanbul, Turkey, pp. 5-15.
Weng, K.C., O’Sullivan, J. B., Lowe, C.G., Winkler, C.E., Dewar, H., Block, B.
A. (2007) Movements, behavior and habitat preferences of juvenile white sharks
189
Carcharodon carcharias in the eastern Pacific. Marine Ecology Progress Series
338: 211-224.
White, C.F., Lyons, K., Jorgenson, S.J., O’Sullivan, J., Winkler, C., Weng, K.C.,
Lowe, C.G. (2019) Quantifying habitat selection and variability in habitat
suitability for juvenile white sharks. PLoS ONE 14: e0214642.
... A census of the Mediterranean's observations and catches has been published (De Maddalena & Heim, 2012). The distribution and ecology of the species have also been studied (Boldrocchi et al., 2017), and the hypothesis of the presence of several nurseries in the Mediterranean has been developed: the Sicily Channel (Fergusson, 1996;Fergusson et al., 2000;Boldrocchi et al., 2017), the Adriatic Sea and the Aegean Sea (Kabasakal, 2014(Kabasakal, , 2020. These studies pointed out a decline in the Mediterranean population, where the species is considered as critically endangered (Dulvy et al., 2016). ...
... The numerous observations in the south-central Mediterranean is, therefore, not in opposition to the presence of hotspots in the northwestern Mediterranean (Moro et al., 2020), due to the thermal amplitude of the two areas. In addition, the northwest sector could instead be a seasonal feeding sector for adults, while the central-south (Fergusson, 2002;Saïdi et al., 2005) and Turkish waters (Kabasakal, 2020) could be considered as nurseries sectors. Site fidelity and seasonality are reported for white sharks in the northeast Pacific (Jorgensen et al., 2009). ...
Article
Full-text available
We put into perspective the knowledge about white sharks (Carcharodon carcharias) in the Mediterranean Sea to identify if the northwestern part is an area of interest and the most efficient methodologies to highlight the presence of the species. We have compiled the main peer-reviewed works, officials' reports and theses, both worldwide and more specifically in the Mediterranean. We focused on studies that allow us to define a more precise framework to search the species. In the Mediterranean, a particular link has been highlighted with bluefin tuna (Thunnus thynnus). The northwestern Mediterranean Sea has unique characteristics compared to other parts of the sea regarding primary productivity, surface temperature, presence of tuna, and is bordered by two white sharks' hotspots. We list methodologies for detecting the species worldwide, including BRUVS and environmental DNA. We also make recommendations for field studies.
... Carcharodon carcharias is rare in the present-day Mediterranean Basin [14], being relatively more common in the Adriatic Sea, Sicilian Channel and Tyrrhenian Sea [7,15]. Some marine Life 2023, 13, 2085 2 of 16 areas along the Tunisian and Sicilian coasts [16][17][18], as well as in the Aegean Sea [19,20], have been proposed to serve as nursery grounds for the Mediterranean white sharks. ...
... being relatively more common in the Adriatic Sea, Sicilian Channel and Tyrrhenian S [7,15]. Some marine areas along the Tunisian and Sicilian coasts [16][17][18], as well as in Aegean Sea [19,20], have been proposed to serve as nursery grounds for the Mediter nean white sharks. ...
Article
Full-text available
The white shark, Carcharodon carcharias, is the main top predator of the present-day Mediterranean Sea. The deep past of C. carcharias in the Mediterranean is witnessed by a rather conspicuous, mostly Pliocene fossil record. Here, we provide a synthesis of the palaeobiology and palaeoecology of the Mediterranean white sharks. Phenetically modern white shark teeth first appeared around the Miocene–Pliocene transition in the Pacific, and soon after in the Mediterranean. Molecular phylogenetic analyses support an origin of the Mediterranean white shark population from the dispersal of Australian/Pacific palaeopopulations, which may have occurred through the Central American Seaway. Tooth dimensions suggest that the Mediterranean white sharks could have grown up to about 7 m total length during the Pliocene. A richer-than-today marine mammal fauna was likely pivotal in supporting the Mediterranean white sharks through the Pliocene and most of the Quaternary. White sharks have seemingly become more common as other macropredators declined and disappeared, notwithstanding the concurrent demise of many potential prey items in the context of the latest Pliocene and Quaternary climatic and environmental perturbations of the Mediterranean region. The overall generalist trophic habits of C. carcharias were likely crucial for securing ecological success in the highly variable Mediterranean scenario by allowing the transition to a mostly piscivorous diet as the regional marine mammal fauna shrank.
... This is further supported by a historical record of a gravid female caught near Rijeka [20]. Similarly, several other areas in the Mediterranean Sea have been proposed as potential nursery areas for white sharks, i.e., the Sicilian Channel, Italy [14]; the Gulf of Gabes, Tunisia [14,43,44]; and Edremit Bay, Turkey [45], based on increased juvenile occurrences. However, no discrete nursery areas have been definitively identified in the Mediterranean Sea yet [25]. ...
Article
Full-text available
The presence of the white shark (Carcharodon carcharias) in the Mediterranean Sea is well documented, but mainly through historical and opportunistic records. Historically, the Adriatic Sea, particularly its eastern coastline, was considered a hotspot for white sharks, with relatively frequent reports of juvenile specimens suggesting a potential nursery area. However, since the second half of the 20th century, the abundance of white sharks in the Adriatic has experienced a dramatic decline, with the last confirmed sighting recorded in 2011. In this study, we report the recent capture of a young-of-the-year (YOY) white shark off the Croatian coast, previously misidentified as a porbeagle shark (Lamna nasus). In addition, we revisit historical records of white sharks in the Adriatic Sea to assess whether this region can be considered a nursery area. Our findings highlight significant gaps in the understanding of white shark spatial ecology and reproductive biology in the Mediterranean Sea. Furthermore, this study emphasizes the critical role citizen science and public engagement can play in documenting occurrences of these elusive and endangered predators, offering valuable insights for future conservation efforts.
... This minimized the influence of tuna trap catches, which, historically, almost exclusively caught adult white sharks , and between the 1960s and 1980s were gradually discontinued due to the development of offshore industrial fisheries (Fromentin & Powers, 2005). The two major abundance hot spots highlighted by our results are hypothesized white shark nurseries and breeding grounds: the Sicilian Channel (De Maddalena & Heim, 2012;Fergusson, 2002) and the north-east Aegean Sea (Kabasakal, 2020). Although the coastal distribution of records can be associated with most human activities being concentrated close to the shores, we attempted to control this factor with the estimated index of observation effort. ...
Article
Conserving oceanic apex predators, such as sharks, is of utmost importance. However, scant abundance and distribution data often challenge understanding the population status of many threatened species. Occurrence records are often scarce and opportunistic, and fieldwork aimed to retrieve additional data is expensive and prone to failure. Integrating various data sources becomes crucial to developing species distribution models for informed sampling and conservation purposes. The white shark, for example, is a rare but persistent inhabitant of the Mediterranean Sea. Here, it is considered Critically Endangered by the IUCN, while population abundance, distribution patterns, and habitat use are still poorly known. This study uses available occurrence records from 1985 to 2021 from diverse sources to construct a spatial log-Gaussian Cox process, with data-source specific detection functions and thinning, and accounting for physical barriers. This model estimates white shark presence intensity alongside uncertainty through a Bayesian approach with Integrated Nested Laplace Approximation (INLA) and the inlabru R package. For the first time, we projected species occurrence hot spots and landscapes of relative abundance (continuous measure of animal density in space) throughout the Mediterranean Sea. This approach can be used with other rare species for which presence-only data from different sources are available.
... In the NEP, multiple studies reported on the capture of numerous neonate C. carcharias (Oñate-González et al. 2017;Santana-Morales et al. 2012, 2020. More specifically, Oñate-González et al., (2017) utilized incidental catch records from Bahía Sebastián Vizcaíno, Mexico. ...
Article
Full-text available
The white shark (Carcharodon carcharias) is a globally distributed top predator. Due to its ecological importance and historical declining population trends, data contributing to conservation initiatives (e.g. habitat protections and resource management) pertaining to all life stages of this species are essential to facilitate population recovery. Of particular interest, the locations and discrete seasonality of C. carcharias parturition remain uncertain. Understanding C. carcharias parturition in relation to each population is relevant to population recovery since neonate to young-of-the-year (YOY) sharks are more vulnerable to predation and particularly threatened by and susceptible to commercial fishing pressure. Herein, this paper provides a synthesis from published literature across seven well-studied C. carcharias populations to identify common trends associated with parturition location, seasonality, and habitat characteristics. The data reviewed in this study are consistent with previous population-specific hypotheses, that C. carcharias parturition occurs during spring and summer for all populations. Further, this review also indicates that parturition likely occurs in insular shelf waters and water temperatures ranging from15.7 to 23.1 °C. Although discrete parturition sites were not identified, the compiled data are suggestive that C. carcharias parturition may occur over horizontal and vertical spatial scales that exceed the inshore, shallow water environments associated with nursery area habitat to perhaps minimize predation by conspecifics. Due to the vulnerability of C. carcharias, conducting non-lethal technological (e.g., baited remote underwater video systems—BRUVS), morphological (i.e., ontogenetic changes in dorsal fin shape), and reproductive (e.g., blood chemistry and ultrasonography) research that may help identify parturition location and seasonality are thus warranted.
... Surely, a further, greater, and more prolonged effort is needed to be able to spot, mark, and sample specimens of WS to evaluate their chances of survival in the Mediterranean Sea. Recently, Kabasakal (2020) reported the occurrence of another nursery ground of WSs in Bay of Edremit (northeastern Aegean Sea, Turkey), which should also be considered as a hotspot and protected, as well in the Gulf of Gabès (southern Tunisia, central Mediterranean Sea) (Bradai and Saidi, 2013). ...
Research
Full-text available
Described in the present report are documented attempts to tag and sample the white shark, Carcharodon carcharias (Linnaeus, 1758), along Italian coasts in the Mediterranean Sea, which took place near the Lampedusa Island in the lower Tyrrhenian Channel of Sicily, off the coast of Rimini in the Adriatic Sea, and of Civitavecchia in the central Tyrrhenian Sea. The project, activated in 2015, was aimed at tagging and sampling specimens of the white shark in order to collect data useful to implement conservation strategies in the Mediterranean Sea. Despite four tagging attempts made in 2017, 2018, 2021, and 2022 with 288 total hours of baiting activity and the use of 1030 kg of chum, no white sharks or any other shark species were sighted. Sažetak: POKUŠAJI LOCIRANJA I UZORKOVANJA VELIKE BIJELE PSINE, CARCHARODON CARCHARIAS (LAMNIFORMES: LAMNIDAE), UZ TALIJANSKU OBALU U SREDOZEMNOM MORU. U radu su dokumentirani pokušaji označavanja i uzorkovanja velike bijele psine Carcharodon carcharias (Linnaeus, 1758) uz talijansku obalu u Sredozemnom moru. Istraživanje je obavljeno na području oko otoka Lampeduze, u sicilijanskom kanalu u južnom Tirenskom moru, ispred Riminija u Jadranskom moru te kod Civitavecchije u centralnom Tirenskom moru. Projekt, koji je započeo 2015. godine, bio je usmjeren na označavanje i uzorkovanje primjeraka velike bijele psine s ciljem prikupljanja podataka važnih za implementaciju mjera za očuvanje populacije ove vrste u Sredozemnom moru. Unatoč četiri pokušaja označavanja obavljena 2017., 2018., 2021. i 2022. godine, u ukupnom trajanju od 288 sati primamljivanja uz pomoć mamca te 1030 kg mamca, ni jedan primjerak velike bijele psine, ni drugih vrsta morskih pasa, nije primijećen.
... Surely, a further, greater, and more prolonged effort is needed to be able to spot, mark, and sample specimens of WS to evaluate their chances of survival in the Mediterranean Sea. Recently, Kabasakal (2020) reported the occurrence of another nursery ground of WSs in Bay of Edremit (northeastern Aegean Sea, Turkey), which should also be considered as a hotspot and protected, as well in the Gulf of Gabès (southern Tunisia, central Mediterranean Sea) (Bradai and Saidi, 2013). ...
Article
Full-text available
Described in the present report are documented attempts to tag and sample the white shark, Carcharodon carcharias (Linnaeus, 1758), along Italian coasts in the Mediterranean Sea, which took place near the Lampedusa Island in the lower Tyrrhenian Channel of Sicily, off the coast of Rimini in the Adriatic Sea, and of Civitavecchia in the central Tyrrhenian Sea. The project, activated in 2015, was aimed at tagging and sampling specimens of the white shark in order to collect data useful to implement conservation strategies in the Mediterranean Sea. Despite four tagging attempts made in 2017, 2018, 2021, and 2022 with 288 total hours of baiting activity and the use of 1030 kg of chum, no white sharks or any other shark species were sighted.
... In light of Villafaña et al.'s (2020) suggestion that warm sea-surface temperatures could favour the establishment of white shark nurseries, C. carcharias may have exploited some portions of the Ligurian or upper Tyrrhenian seas as nursery areas during the overall warm Holocene Climate Optimum. This hypothesis is also supported by the likely occurrence of extant white shark parturition grounds in relatively warm waters along the Tunisian and Sicilian coasts (Bradaï & Saïdi 2013;Tiralongo et al. 2020) as well as in the Aegean Sea (Kabasakal 2020). That said, other mechanisms of habitat selection (e.g., the juveniles' preference for warm-temperate water temperatures, shallow depths, and short distance from the shore; White et al. 2019) may account for the abundance of immature white sharks in the Torre del Lago Northgrippian palaeobiotope. ...
Article
The white shark, Carcharodon carcharias (Linnaeus, 1758), is a fairly uncommon and somewhat enigmatic inhabitant of the present-day Mediterranean Basin. In this broad region, fossil teeth of C. carcharias are known from the lower Pliocene onwards, but definite Pleistocene records concentrate in a few southern Italian localities along the Ionian and Tyrrhenian coasts. Here, we report on new and historical specimens of C. carcharias from the Quaternary of Tuscany (central Italy), which provide valuable data on the post-Pliocene history of white sharks in the southern Ligurian Sea (a north-western Mediterranean quarter where white sharks are currently rare). Some of these finds come from mollusc-bearing sands that were quarried at Torre del Lago (Lucca Province). Originally regarded as “Versilian” (latest Pleistocene to Holocene) in age, these largely immature white shark teeth date back to the mid-Holocene (Northgrippian, roughly corresponding to the last phases of the Holocene Climate Optimum). A new dental specimen of C. carcharias originates from Lower Pleistocene (Calabrian, ?Emilian) sediments cropping out at Montalto, near Fauglia (Pisa Province). Among many other fossils, the Montalto locality has also yielded a monk seal calcaneum, thus hinting at a possible predator-prey relationship between the shark and the pinniped. An additional record comes from the Meloria Shoals, off Leghorn. It likely derives from the shallow-marine, Upper Pleistocene (Tyrrhenian) fossiliferous deposits that are locally exposed at the seafloor. Together with previous Pleistocene finds from southern Italy, these Tuscan fossils highlight the ecological plasticity of the Mediterranean white sharks, which persisted through the fairly massive climatic and environmental perturbations that characterised the Quaternary Period without obvious connections with their adjacent Atlantic conspecifics.
... For example, it has been proposed that the Mediterranean Sea may host important nursery areas for pelagic sharks (Costantini & Affronte 2003, Soldo 2005, Megalofonou et al. 2009, Jambura et al. 2021. Newborns, juveniles and immatures, and pregnant females of great white sharks Carcharodon carcharias (Saidi et al. 2005, Kabasakal & Gedikoğlu 2008, Kabasakal 2020, Leone et al. 2020, Scannella et al. 2020, blue sharks Prionace glauca (Megalofonou et al. 2009, Giovos et al. 2020, and shortfin makos Isurus oxyrinchus (Kabasakal 2015a, Udovičić et al. 2018, Giovos et al. 2020) have been repeatedly observed in multiple sectors of the Mediterranean Sea. However, no study has yet tested, under welldefined criteria (Heupel et al. 2007), whether these occurrences indicate the presence of nursery areas. ...
Article
The Mediterranean Sea, a biodiversity hotspot classified by the IUCN as critically threatened for sharks and rays, faces significant conservation challenges because of geopolitical complexities. Traditional, top‐down management strategies often fail, thus calling for alternative conservation approaches. This study documents the first recorded catch and release of a juvenile great white shark ( Carcharodon carcharias ) off Lampedusa Island (Central‐Southern Mediterranean Sea), facilitated by the EU‐cofunded LIFE ELIFE project. This successful release, achieved through collaboration between scientists and local fishers, underscores the importance of stakeholder involvement and cooperative strategies in conserving endangered elasmobranchs in the Mediterranean.
Article
Full-text available
In the late 1950s, a white shark, Carcharodon carcharias (Linnaeus, 1758), was incidentally captured by tuna handliners off the coast of Burgazada. Currently, 58 white sharks have been reported from Turkish waters, which represents some 7.5 percent of the total Mediterranean records (n=773). The decrease in white shark sightings from the Sea of Marmara over the years is most likely linked to a strong decline of tuna populations in the same region. The present study is one of the many examples of effective use of internet-based records in white shark research.
Book
Full-text available
This identification guide has been developed to support the monitoring of bycatch of vulnerable species in Mediterranean fisheries. The work has been produced within the context of the project “Understanding Mediterranean multi-taxa ‘bycatch’ of vulnerable species and testing mitigation– a collaborative approach” funded by MAVA Foundation through a partnership between the Agreement on the Conservation of Cetaceans of the Black Sea, Mediterranean Sea and contiguous Atlantic area (ACCOBAMS), the General Fisheries Commission for the Mediterranean (GFCM) of the Food and Agriculture Organization of the United Nations (FAO), the Regional Activity Centre for Specially Protected Areas of the United Nations Environment/Mediterranean Action Plan (SPA/RAC), International Union for Conservation of Nature – Centre for Mediterranean Cooperation (IUCN-Med), BirdLife Europe and Central Asia (BL ECA) and the Mediterranean Association to Save the Sea Turtles (MEDASSET). The compilation and final editing of the guide has been coordinated by IUCN with the support of all the involved partners and Mediterranean experts acknowledged in the document. Origin of text sources and materials used are described for each group taxa at the beginning of each chapter. The vulnerable species are grouped taxonomically into marine mammals, seabirds, sea turtles, chondrichthyans (sharks, rays and chimaeras), sponges and corals. The guide with the species descriptions has been developed to provide observers on board fishing vessels and fishers with identification assistance and general information about vulnerable species potentially caught as bycatch. Complementary to this, is the document Monitoring the incidental catch of vulnerable species in Mediterranean and Black Sea fisheries - methodology for data collection prepared by FAO/GFCM1 with the inputs provided by partner organizations. Each species description contains photographs, illustrations and narrative descriptions to highlight important anatomical structures and features of a particular species. Considering the difficulties of identification of some coral and sponge species living in the Mediterranean, these taxa groups have been grouped into morphological groups to allow easier identification, although it is recommended they are identified at species level when possible. For each species, there is a description of the main characteristics that can be used to identify the species (or for the case of sponges and corals, the morphological groups), together with its common name in several languages (English, Spanish, French and Arabic). Information is also provided if the species is protected under Appendix I (Endangered migratory species) and/or Appendix II (Migratory species conserved through Agreements) of the Convention on the Conservation of Migratory Species of Wild Animals (CMS); Appendix I (Species threatened with extinction) of the Convention on International Trade in Endangered Species of Wild Fauna and Flora (CITES); the Agreement on the Conservation of Cetaceans of the Black Sea, Mediterranean Sea and contiguous Atlantic area (ACCOBAMS); or under Annex II (List of Endangered or Threatened Species) or III (List of Species Whose Exploitation is Regulated) of the SPA/ BD Protocol (Specially Protected Areas and Biological Diversity in the Mediterranean) of the Barcelona Convention. Additionally, it is provided if the species is included at any GFCM (General Fisheries Commission for the Mediterranean) recommendations on fisheries management measures for conservation of the species in the GFCM area as well as the management recommendations and resolutions adopted by ICCAT (International Commission for the Conservation of Atlantic Tunas) on bycatch in tuna and tuna-like fisheries. Finally is given the conservation status following IUCN conservation categories in 2019.
Article
Full-text available
While adult white sharks (Carcharodon carcharias) are apex predators with a circumglobal distribution, juvenile white sharks (JWS) feed primarily on bottom dwelling fishes and tend to be coastally associated. Despite the assumedly easier access to juveniles compared to large, migratory adults, limited information is available on the movements, environments, and distributions of individuals during this life stage. To quantify movement and understand their distribution in the southern California Bight, JWS were captured and fitted with dorsal fin-mounted satellite transmitters (SPOT tags; n = 18). Nine individuals crossed the U.S. border into Baja California, Mexico. Individuals used shallow habitats (134.96 ± 191.1 m) close to shore (7.16 ± 5.65 km). A generalized linear model with a binomial distribution was used to predict the presence of individuals based on several environmental predictors from these areas. Juveniles were found to select shallow habitats (< 1000 m deep) close to land (< 30 km of the shoreline) in waters ranging from 14 to 24°C. Southern California was found to be suitable eight months of the year, while coastal habitats in Baja California were suitable year-round. The model predicted seasonal movement with sharks moving from southern California to Baja California during winter. Additionally, habitat distribution changed inter-annually with sharks having a more northerly distribution during years with a higher Pacific Decadal Oscillation index, suggesting sharks may forego their annual fall migrations to Baja California, Mexico, during El Niño years. Model predictions aligned with fishery-dependent catch data, with a greater number of sharks being captured during periods and/or areas of increased habitat suitability. Thus, habitat models could be useful for predicting the presence of JWS in other areas, and can be used as a tool for potentially reducing fishery interactions during seasons and locations where there is increased susceptibility of incidental catch.
Article
Full-text available
Between January 2016 and April 2018, 3 juvenile great white sharks, Carcharodon carcharias (Linnaeus, 1758), were incidentally captured in the coastal waters of the Turkish Aegean Sea. Journeys of young-of-the-year (YOY) and juvenile specimens can increase the risk of their encountering fshing gears if the specimens head for regions where the fshery of the great whites is not banned. An understanding of the geographic range and knowledge of the vertical distribution of the YOY and juvenile great whites are therefore necessary to implement a management plan for great white populations in Turkish waters and to reduce the incidental fshing mortality of this vulnerable top predator.
Article
Full-text available
In recent years, white sharks (Carcharodon carcharias) have become more accessible to researchers off the northeastern U.S. as feeding aggregation sites have emerged and the population has increased. However, there has been limited research on young-of-the-year (YOY) sharks relative to older age classes in this region. Previous research indicated that YOY white sharks were most frequently observed in the New York Bight, suggesting the region serves a nursery role. To further examine the species' use of this area, we deployed satellite and acoustic tags on ten YOY white sharks (138-166 cm total length) off Long Island, New York. The sharks remained resident in New York Bight waters through summer (August through October), further supporting the notion that the region is a nursery area. Southward movements were observed during fall, with overwintering habitat identified off North and South Carolina shelf waters. Return migrations toward the New York Bight were observed in some individuals the following spring. YOY white sharks in this heavily-populated region are exposed to anthropogenic impacts such as fisheries bycatch and coastal habitat degradation. As juvenile survival rates are important for long-term population sustainability, further research is necessary to assess the potential impacts of these activities on the western North Atlantic white shark population.
Article
Full-text available
The occurrence of the white shark, Carcharodon carcharias, in the Mediterranean Sea has been reported since the Middle Ages (476–1453). Several studies have documented its presence in various areas of the basin, but no comprehensive review of the distribution and status of this species is available for the area. We compiled a total of 628 white shark records from 476 to 2015. Data suggests that the white shark is more common in the western Mediterranean Sea, especially in the Adriatic Sea and in the Sicilian Channel and is more frequently observed during summer months. However, analysis using night-time satellite imagery showed the existence of an anthropogenic bias in the distribution of white sharks. All size classes have been recorded in the region. However, the highest occurrence of young of the year has been recorded in the Sicilian Channel, in the Adriatic Sea and in the Aegean Sea, in summer, suggesting these areas might serve as nursery grounds. In the Mediterranean Sea, the white shark exhibits a broad diet. The most common prey found include small cetaceans (Tursiops truncatus, Stenella coeruleoalba), tuna (Thunnus spp.), swordfish (Xiphias gladius) and loggerhead sea turtle (Caretta caretta). A total of 53 white shark records refer to interactions between sharks and humans that resulted in a detrimental impact on humans, which include 42 bites and 11 reports of the presence of human remains in the stomach of captured animals. Analysis of the temporal variation in mean total lengths of white sharks found a decreasing trend from 1913 to 2012. The decreasing length of white sharks suggests this species might be declining in the Mediterranean Sea.
Article
Full-text available
Estuarine environments are known to provide important feeding, breeding, resting and nursery areas for a range of shark species, including some which are considered dangerous to humans. Juvenile white sharks (<3 m) are known to frequent inshore environments, particularly ocean beaches, but their presence in and use of estuaries and coastal embayments is unclear. Given that estuarine environments are often surrounded by highly populated areas, understanding how white sharks use these environments will not only assist with their conservation management, but also inform public safety policies. The use of estuarine environments by acoustic-tagged white sharks was investigated from 2009 to 2015 at Port Stephens, New South Wales and Corner Inlet, Victoria, both of which adjoin known nursery areas for the species. Juvenile white sharks were detected within both estuaries, with 20 individuals recorded within the Port Stephens estuary, including four on one day. Only one tagged shark was detected within Corner Inlet; however, monitoring effort and local tagging in the area was more restricted. Detections in Port Stephens were predominantly from October to January and peaked in November. This study demonstrates that the footprint of known nursery areas for white sharks in eastern Australia should be expanded to include their adjacent estuarine environments. Consequently, there is clear potential for them to be exposed to a range of anthropogenic estuarine impacts, and that human interactions are more likely over warmer periods (summer), when human use of such waterways is more prevalent.