SciELO - Scientific Electronic Library Online

vol.15 issue3A new species of Bryconamericus (Characidae: Stevardiinae: Diapomini) from the upper rio Paraná basin, BrazilBiogeography of Amazonian fishes: deconstructing river basins as biogeographic units author indexsubject indexarticles search
Home Pagealphabetic serial listing  

Services on Demand




Related links


Neotropical Ichthyology

Print version ISSN 1679-6225On-line version ISSN 1982-0224

Neotrop. ichthyol. vol.15 no.3 Maringá  2017  Epub Sep 28, 2017 


Bioecology and movements of bull sharks, Carcharhinus leucas , caught in a long-term longline survey off northeastern Brazil

Yuri V. Niella1  2 

André S. Afonso2 

Fábio H. V. Hazin2 

1Departamento de Oceanografia, Universidade Federal de Pernambuco (UFPE), Av. Prof. Moraes Rego, 1235 - Cidade Universitária, 50670-901 Recife, PE, Brazil. (YVN) (corresponding author)

2Departamento de Pesca e Aquicultura, Universidade Federal Rural de Pernambuco (UFRPE), Rua Manoel de Medeiros, s/n - Dois Irmãos, 52171-900 Recife, PE, Brazil. (ASA), (FHVH)


A robust understanding of habitat usage by coastal shark species, and how it overlaps with human presence in densely-populated regions is needed to inform the development of efficient conservation strategies for these important top predators. An intensive longline survey conducted in nearshore waters off northeastern Brazil from 2004 through 2014 caught a total of 18 bull sharks (Carcharhinus leucas) (male-female ratio = 0.63:1), which can be dangerous to humans. Although most sharks were sexually mature, there was no evidence that this region could be used as a parturition or nursery area. Prey items identified in the guts of the sharks comprised teleosts, mollusks and elasmobranchs. Additionally, one satellite-tagged bull shark covered a great distance (> 3,000 km) in 75 days at liberty, making most use of shallow waters (< 20 m depth) and presumably also entering an estuarine area. Although bull sharks are not an important fishery resource in this region, such a reduced abundance coupled with its affinity for coastal and inshore habitats highlights the potential vulnerability of C. leucas to deleterious anthropic interferences off northeastern Brazil.

Keywords: Drumline; Longline; Maturity status; Pop-up satellite archival tag; Recife


Um melhor entendimento sobre a utilização de hábitat das espécies de tubarões costeiros, e como ela se sobrepõe à presença humana em regiões altamente populosas, se faz necessário a fim de subsidiar o desenvolvimento de eficientes medidas de conservação para esses importantes predadores de topo. Um estudo intensivo utilizando espinhel, conduzido em águas costeiras do nordeste do Brasil entre os anos de 2004 e 2014, capturou um total de 18 tubarões cabeça-chata (Carcharhinus leucas) (proporção macho-fêmea = 0,63:1), os quais podem ser perigosos para humanos. Apesar da maioria dos tubarões estarem sexualmente maduros, não houve evidências de que essa região esteja sendo utilizada como uma área de parto ou berçário. Entre os itens alimentares identificados foram encontrados teleósteos, moluscos e elasmobrânquios. Além disso, um tubarão cabeça-chata marcado com um transmissor satélite percorreu uma grande distância (> 3.000 km) em 75 dias em liberdade, fazendo o uso de águas superficiais (< 20 m profundidade) e presumivelmente entrando em uma área estuarina. Apesar de os tubarões cabeça-chata não corresponderem a um recurso pesqueiro importante nessa região, tal reduzida abundância juntamente com a sua afinidade por hábitats costeiros reforçam a potencial vulnerabilidade de C. leucas às interferências antrópicas deletérias ao longo da costa nordeste do Brasil.

Palavras-chave: Espinhel; Linhas de espera; Recife; Status de maturação; Transmissor satélite


Increasing human populations have generally been responsible for negative influences such as overfishing, water pollution and climate change on coastal ecosystems (Jackson et al., 2001), which correspond to important foraging and nursery grounds for several shark species (Heithaus et al., 2002; Simpfendorfer et al., 2005; Wiley, Simpfendorfer, 2007). Despite the high mobility of many sharks, some species exhibit considerable site fidelity in coastal regions (Simpfendorfer et al., 2005; Conrath, Musick, 2007; Wiley, Simpfendorfer, 2007), making them more susceptible to anthropogenic impacts. Indeed, some shark species may inclusively use artificial habitats created by large-scale urban development (Werry et al., 2012). Therefore, a better understanding of their bioecology, i.e. the interrelationships between biological and ecological features of species, their environments, and movement patterns is necessary to promote effective conservation.

The bull shark, Carcharhinus leucas (Müller & Henle, 1839), is a large carcharhinid, which can grow up to 4 m in total length (LT) (McCord, Lamberth, 2009). It is circumglobal in tropical and warm temperate coastal waters (Compagno, 2001; Hueter et al., 2005) and also in estuarine and freshwater habitats, which it tolerates due to an efficient osmoregulatory capability (Pillans et al., 2005; Reilly et al., 2011). Even though there is no evidence that this species copulates in freshwater, parturition likely occurs in warm-water estuaries and rivers (Montoya, Thorson, 1982; Compagno et al., 2005; Pillans et al., 2006). Adult C. leucas sharks make use of shallow nearshore habitats (Brunnschweiler et al., 2010; Hammerschlag et al., 2012; Heupel et al., 2015; Graham et al., 2016), particularly in areas of high freshwater inflow, associated with an elevated productivity, where they usually exhibit some level of site fidelity (Carlson et al., 2010; Daly et al., 2014). Nevertheless, this species also undertakes coastal migrations regulated by environmental, foraging and reproductive drivers (Daly et al., 2014; Espinoza et al., 2016). Open ocean migrations have also been observed, including one pregnant individual, which is known to have traversed the Indian Ocean from the Seychelles to Madagascar (Lea et al., 2015). The occurrence of bull sharks has also been reported from the insular shelves of the northeastern and southwestern Atlantic Ocean (Gadig et al., 2006; Bornatowski et al., 2012).

In Brazil, C. leucas have been found up to 3,000 km away from the Atlantic Ocean in the Amazon river (Thorson, 1972), and its occurrence has been reported in industrial and artisanal coastal fisheries from the northernmost state south to the Santa Catarina State, 27º in latitude (Amorim et al., 1998; Mazzoleni, Schwingel, 1999; Menezes et al., 2005; Rodrigues-Filho et al., 2009). Despite a considerable amount of published literature, little is yet known about the bioecology of C. leucas in the Southwestern Atlantic. The parturition period in Cananéia lagoon, in the São Paulo State, has been reported to occur from November to February (Sadowsky, 1971). Off Recife, in the Pernambuco State, the bull shark occurs occasionally but with much less frequency than other medium to large-bodied species such as the blacknose (Carcharhinus acronotus), the nurse (Ginglymostoma cirratum) and the tiger (Galeocerdo cuvier) sharks (Afonso et al., 2014). Also, bull sharks have been implicated in a local spate of shark bites in this region (Hazin et al., 2008), bringing additional concerns regarding the species.

This study aims at assessing the population structure of C. leucas off Recife and providing preliminary information on the bioecological traits of this species in a region poorly known to marine sciences, thus benefiting its conservation. Such information is also locally relevant for shark hazard mitigation purposes. Furthermore, the vertical and horizontal movements of one adult C. leucas assessed with a pop-up satellite archival tag are described for the first time in the western South Atlantic Ocean.

Material and Methods

Ethics statement. The capture and handling of C. leucas has been approved by the Instituto Chico Mendes de Conservação da Biodiversidade of the Brazilian Ministry of the Environment (permit no. 15083-8) and was carried out in full compliance with the recommendations of the regiment of the Commission of Ethics on the Usage of Animals from the Universidade Federal Rural de Pernambuco (license no. 041/2009; protocol no. 23082.009679/2009 D18).

Sampling procedure. Sharks were captured in nearshore waters off Recife, northeastern Brazil (8.17ºS, 34.88ºW). The fishing gear comprised two bottom longlines and 23 drumlines deployed in shallow water at mean (± SD) depths of 13.6 ± 1.0 m and 8.6 ± 2.2 m, respectively (Fig. 1). Both fishing gears were equipped with circle hooks (17/0) and baited with moray eel (Gymnothorax spp.). The longlines were deployed alongshore ca. 2-3 km from the coastline during the afternoon and retrieved early in the following morning (mean ± SD soak time = 15.55 ± 2.45 hours). Drumlines were deployed < 1 km from shore and were continuously in the water during each fishing trip, being retrieved in the morning for bait replacement.

Fig. 1 Map of the study area with the locations of Recife in South America, and fishing sites, i.e. Boa Viagem, Piedade and Paiva beaches. The deployment locations of the respective fishing gears, i.e. each drumline (x) and the two longlines, are also represented. 

The data were originated from a long-term shark survey in this region conducted from May 2004 to December 2014, and a thorough description of the fishing gear and fishing procedures can be found in Afonso et al. (2011) and Hazin, Afonso (2014). Further information regarding the abundance patterns of C. leucas in this region are detailed in Afonso et al. (2017).

Shark biology. Upon capture, bull sharks were sexed and measured for stretched LT to the nearest centimeter (cm). The specimens which did not survive the fishing gear were taken to the laboratory where they were weighed and dissected. Their stomach contents, when present, were identified to the lowest possible taxon and their reproductive tracts were analyzed to assess maturity status. In males, clasper calcification and rotation were inspected, as well as the presence of seminal fluid in the ampullae of the ductus deferens. Sexual maturity in females was determined based on the developmental stage of the reproductive organs, i.e. oviducal gland, ovary and uterus. The width of these organs was taken to the nearest millimeter (mm), and the presence of vitellogenic follicles, uterine eggs and ova still in the ovary was determined.

Because the data were not normally-distributed, non-parametric statistics were used to inspect for significant patterns in the C. leucas biological traits pooled by year. Possible shifts in shark sex ratio between the austral summer, i.e. from September to February, and winter, i.e. from March to August, were inspected with a Fisher’s test. Sex-related differences in shark size were analyzed with a Mann-Whitney test. Also, seasonality in bull shark LT was assessed using a Kruskal-Wallis test considering month as a factorial variable. Statistical significance was set at p < 0.05.

Vertical and horizontal movements. A mature male C. leucas (210 cm LT) was caught (8.14ºS, 34.54ºW) on 17 July 2012. The shark was tagged with a pop-up archival transmitter (mk-10; Wildlife Computers, USA) fitted to the first dorsal fin and set to detach after 75 days at liberty. Satellite-relayed data included maximum and minimum depths and temperatures and the proportion of time spent at 14 depth and temperature bins following a 3-hour time resolution. The 14 depth and temperature intervals were set at 0-1, 1-5, 5-10, 10-15, 15-20, 20-25, 25-30, 30-40, 40-50, 50-60, 60-80, 80-100, 100-150, and > 150 m, and at 12-15, 15-18, 18-20, 20-21, 21-22, 22-23, 23-24, 24-25, 25-26, 26-27, 27-28, 28-29, and > 29oC, respectively.

Luminosity data were used to generate raw geolocation estimates with proprietary software (WC-GPE v. 1.02.005; Wildlife Computers). The unscented Kalman-Filter state-space model was then applied to estimate the horizontal movements of the shark using the UKFSST R-library (Nielsen et al., 2012). An SST correction was carried out by comparing local SST recorded by the tag to satellite-measured SST data downloaded from the National Oceanic and Atmospheric Administration Earth System Research Laboratory (NOAA ESRL) database ( A bathymetric correction was also performed with the analyzepsat R-library (Galuardi, 2011) by screening the daily maximum depths achieved by the shark to avoid placing it either on land or in too shallow isobaths.

In order to inspect for possible behavioral shifts across the track, and considering the mostly latitudinal alignment of the movements performed, the movement rates were first calculated by dividing the latitude variation by the amount of time (number of days) elapsed between consecutive geolocations. The periods during which latitudinal movement rates were substantially lower than the overall mean movement rate were assigned to a resident mode, whereas movement rates higher than average were assigned to a transient mode. The distances between all locations were estimated to the nearest km with software GE-Path (v. 1.4.5) and used to calculate the corresponding swimming speeds between consecutive points, which were then averaged by movement mode, i.e. resident and transient.

The vertical movements were analyzed with generalized additive models (GAM) using the mgcv R-library (Wood, 2011). Models were built with the response variables i) time at surface (TAS), i.e. the percentage of time spent between the sea surface and the 5-m isobath, using a binomial distribution with logit link functions, and ii) maximum diving depth (MDD), using a Gaussian distribution with identity link functions, following Afonso, Hazin (2015). Candidate predictor variables included the diel cycle, i.e. day (from 6:00 a.m. to 5:59 p.m.) or night (from 6:00 p.m. to 5:59 a.m.), lunar phase, SST and movement mode. Additionally, a modified version of the split moving window gradient analysis (SMWGA) (Cornelius, Reynolds, 1991) was applied to the time at depth (TAD) and time at temperature (TAT) histograms to assess for shifts in shark vertical behavior as it adequately deals with ARGOS-relayed data with gaps in the dataset (Queiroz et al., 2010).

Finally, a paired t-test was used to inspect for possible estuarine habitat usage in a specific period following a rapid decrease in SST in the last few days of the track. For such a purpose, the temperatures on the sea surface and at the 8-m isobath measured by the tag were compared during this particular event.


Bioecology. A total of 18 C. leucas (male-female ratio = 0.63:1) were caught during the 11-year study span and no significant shifts in sex-ratio between austral summer and winter were observed (Fisher’s test; odds ratio = 4.58; p-value = 0.315). Shark LT ranged from 144 to 266 cm (mean = 206.44 ± 34.81 cm) and did not significantly differ between sexes (Mann-Whitney; W = 41.5; p-value = 0.820) neither throughout the year (Kruskal-Wallis; Chi-squared = 9.41; p-value = 0.308).

Mature C. leucas were more represented in the catch (61.1%) and were mostly caught during the austral summer (81.8%), when a higher abundance of bull sharks has been reported in this region (Afonso et al., 2017). Among male sharks, 57.1% were mature with sizes ranging from 213 to 251 cm LT (weight = 74.2-121.0 kg), whereas juvenile males measured between 157 and 186 cm LT (30.6-50.5 kg). In addition, two mature specimens measuring 213 (77.8 kg) and 249 (108.3 kg) cm LT had a considerable amount of seminal volume. The great majority of females (72.7%) was also mature and measured between 205 and 266 cm LT (72.0-148.5 kg), whereas immature females measured between 144 and 190 cm LT (24.2-68.0 kg). Among females smaller than 201 cm LT, the width of reproductive organs ranged from 1.3-2.5 cm (ovaries), 0.6-1.4 cm (oviducal glands) and 0.3-0.5 cm (uterus). In females larger than 206 cm LT, the same measurements varied from 5.3-14.9 (ovaries), 3.0-7.7 cm (oviducal glands) and 2.2-11.3 cm (uterus). No pregnant females were sampled.

Among 16 dissected stomachs, nine (56.2%) were completely empty and one was everted (Tab. 1). The prey items identified in the stomachs of three juvenile sharks (< 190 cm LT) comprised the vertebral columns of teleosts and a squid beak (Tab. 1). The stomachs of three mature individuals, measuring between 238-266 cm LT, contained fragments of an unidentified species of crab, a squid beak, the head of a crucifix sea catfish (Sciades proops Valenciennes, 1840) and the remains of an unidentified species of stingray (Tab. 1).

Tab. 1 Stomach contents (Stomach) of the Carcharhinus leucas captured and their respective total length (LT) and sexual development (Development). It was not possible to identify the stomach contents of the sharks typed in bold, i.e. S14 and S17, because they were tagged and released. (*) The tracking data from the recovered transmitter revealed that this shark has died a few hours after being released. 

Year Shark Sex L T Development Stomach
2004 S1 Male 215 Mature Empty
2004 S2 Female 207 Mature Empty
2005 S3 Male 186 Imature Empty
2006 S4 Female 212 Mature Empty
2006 S5 Female 250 Mature Everted
2006 S6 Female 190 Imature Empty
2007 S7 Male 213 Mature Empty
2008 S8 Female 170 Imature Teleost vertebral column
2008 S9 Female 144 Imature Teleost vertebral column
2011 S10 Male 157 Imature Empty
2012 S11 Female 200 Imature Empty
2012 S12 Male 150 Imature Squid beak
2012 S13 Male 249 Mature Crab and Squid beak
2012 S14 Male 210 Mature
2013 S15 Female 266 Mature Head of Sciades proops
2014 S16 Female 210 Mature Empty
2014 S17 * Female 248 Mature
2014 S18 Female 238 Mature Stingray

Movement patterns. The tagged shark (S14; Tab. 1) spent 97.4% of the time between the sea surface and the 20-m isobath, and reached a maximum depth of 64 (± 4) m (Fig. 2a). Accordingly, it was exposed only to a small thermal gradient and spent 96.9% of the time in temperatures warmer than 24ºC (Fig. 2b), which correspond to the typical temperatures from the mixed surface layer in this region (Afonso, Hazin, 2015). The SMWGA output indicated two significant shifts in its vertical distribution. The first occurred on 22 July 2012, when the shark moved through relatively shallower waters (Fig. 2a) although experiencing lower temperatures (Fig. 2b). The second, more pronounced shift occurred on 29 August 2012, when the shark once again moved to shallower habitats (Fig. 2a) but with warmer waters (Fig. 2b). In the beginning of the track the shark experienced a progressive decrease in SST, whereas a second marked decrease occurred much faster in the end of the track and lasted for at least 3 days (Fig. 2c). During this period, the shark maintained a consistently shallow distribution (maximum depth = 8 ± 4 m) and the temperature at the 8-m isobath was significantly warmer than the temperatures at the surface (T-test; mean of the differences = 0.52ºC; t = -5.099; df = 4; p-value = 0.006), which is typical of salt-wedge estuaries (Newton, 1996). During September, the Maraú Estuary (ca. 30 km away from pop-off location) exhibits similar temperatures to those registered by the tag, and its maximum depth of 12 m (Santana, 2012) is compatible with the maximum depths reached by the shark. All these evidences indicate that the shark probably accessed this particular estuary on 26 September 2012.

Fig. 2 Representative tracks depicting vertical usage by the Carcharhinus leucas during the track. The color scale in the upper panel inform the proportion of time spent at each depth/temperature stratum, whereas in the lower panel it represents the water temperature (°C). Above the plots, the first graduated horizontal bars with small divisions represents the diel cycle, i.e. daytime (white squares) and night time (black squares). The second graduated horizontal bar with wider divisions depicts the lunar cycle, where the all-black and allwhite rectangles depict the new and full moon phases, respectively. On the top of (a) and (b) a panel depicts the SMWGA output, and the vertical dotted lines represent statistically significant shifts in vertical behavior. Bellow (a) and (b) plots, the black and white rectangles represent transiency and residency behavior, respectively. The horizontal dashed line and shaded area in (c) represent the 60-m isobaths of the shelf break and the period when the temperatures rapidly decreased. a. depth; b. temperature; and c. temperature at depth. 

This C. leucas traveled 3,389 km during the 75 days of the monitoring period. Although the geolocations estimated with the Kalman-filter algorithm suggested an extensive use of oceanic waters during most of the track, the Brazilian continental platform was included in nearly all the respective error ellipses (Fig. 3). The shark initially moved southwards through a minimum distance of 2,116 km away from the release location, reaching the coast of the Rio de Janeiro State (24.58ºS, 37.50ºW) after 38 days at-liberty. Then the shark traveled 1,273 km northwards until the tag detached in coastal waters off Bahia State (14.15ºS, 38.94ºW) (Fig. 3).

Fig. 3 UKFSST model of the Carcharhinus leucas movements along the Brazilian coast. The blue and pink points represent deployment and pop-up locations, respectively. The bathymetric profile and corresponding months of each geolocation are represented by the color scales. The dashed orange line represents the most probable track of the shark. The red shaded areas depict the confidence intervals of the model positions. 

Although only 13 geolocations were used to classify the shark movement mode as transient or resident, this method is considered to be adequate because there is no evidence of movement rates being influenced by the amount of time elapsed (S1), which could translate into a sampling artifact rather than its actual movement rate. Three residency periods were identified, with minimum residency time varying from 5 to 17 days (Figs. 2a-b). In these periods the shark moved at a considerably lower mean rate (0.08 ± 0.04º latitude variation·day-1) in comparison with transient periods (0.65 ± 0.26º latitude variation·day-1). The overall mean swimming speed equaled 0.52 ± 0.31 m·s-1. During transiency periods the shark moved at a mean speed of 0.77 ± 0.08 m·s-1, whereas considerably slower swimming speeds were observed during residency periods (0.18 ± 0.09 m·s-1).

The TAS model included the variables lunar phase and diel cycle (Tab. 2; S2). The shark spent a significantly lower proportion of time at depths shallower than 5 m during the new moon (Tab. 2). Regarding the diel cycle, a greater proportion of time was spent at depths < 5 m during the nighttime (Tab. 2). The MDD model included the variables SST and movement mode as the best predictors (Tab. 3; S3). The shark tended to dive to greater depths (around the 30-m isobath) when the SST ranged from 23.5ºC to 24.5ºC (Fig. 4; Tab. 2, S4), corresponding to the region between the Rio de Janeiro and the Espírito Santo States (20ºS-19ºS). In addition, it also moved through deeper isobaths when exhibiting transient behavior (Tab. 2).

Fig. 4 Significant effect of the continuous variable sea surface temperature upon the maximum diving depth of the Carcharhinus leucas tagged, assessed with a generalized additive model (GAM). The horizontal dashed line and shaded area depict null effect and 95% confidence intervals, respectively. 

Tab. 2 Generalized additive model of the time spent at the sea surface. Included are the predictor variables lunar phase (LunPha) and diel cycle (Diel), the coefficient estimate (Est.), standard errors (SE), z-statistics (z) and corresponding p-values (p). 

Model Variable Est. SE z p
LunPha + Diel Intercept -0.08 0.25 -0.33 < 0.001
(LunPha) full 0.43 0.33 1.31 0.189
(LunPha) last 0.50 0.38 1.32 0.184
(LunPha) new -0.75 0.30 -2.46 0.013
(Diel) night 0.51 0.24 2.12 0.033

Tab. 3 Generalized additive model of the maximum diving depth. Included are the predictor variables sea surface temperature (SST) and movement mode (MovMod), the coefficient estimate (Est.), standard errors (SE), z-statistics (z) of the categorical variable, effective (Edf.) and reference (Ref.df) degrees of freedom, and χ 2-statistics (Chi.sq) of the continuous variable, and corresponding p-values (p). (*) Variable modeled with a continuous smooth function. 

Model Variable Est. SE z Edf. Ref.df Chi.sq p
SST + MovMod Intercept 13.07 0.71 18.32 < 0.001
SST* 5.15 6.24 10.35 < 0.001
(MovMod) transient 3.31 0.87 3.76 < 0.001


Despite the low number of sharks sampled (N = 18), this study provides important information about C. leucas from the western South Atlantic, where the demography of the species is uncertain and the few studies available suggest intense fishing exploitation (Karl et al., 2010). Given the current Near Threatened status of C. leucas (Simpfendorfer, Burgess, 2009), the collection of bioecological data is essential for implementing future efficient conservation strategies in the Brazilian northeastern coast.

The low numbers of C. leucas caught off Recife, coupled with a substantial sampling effort (ca. 500,000 hooks) and time length (132 months) being employed in this study, all suggest that this region does not hold a sustained population of this species. Hence, the bull sharks caught during this survey probably correspond to transient individuals from subpopulations distributed more densely elsewhere in this region. However, the lack of fisheries data precludes the assessment of C. leucas distribution at a regional scale. Although bull sharks are caught by industrial and artisanal fisheries operating in Brazilian waters, they usually occur at considerably lower abundances in comparison with other carcharhinids, such as C. porosus and C. acronotus in the northern region (Menezes et al., 2005; Rodrigues-Filho et al., 2009), and C. signatus and Prionace glauca in the southern region (Amorim et al., 1998; Mazzoleni, Schwingel, 1999). However, such a pattern could be related with the mostly offshore location of the longline fisheries in the southern region, consequently reducing the likelihood of capturing a bull shark. Such a combination of factors seems to be alarming for the conservation of C. leucas off the northeastern Brazilian coast, suggesting that management policies might be urgently needed. Considering that it is usually a non-targeted species, the prompt release of the bull sharks caught is strongly advised in this region, and further detailed studies on its demography should also be done.

Bull sharks have been implicated in hazardous shark-human interactions in South Africa (Cliff, Dudley, 1991), Australia (Dudley, 1997), Reunion Island (Lemahieu et al., 2017) and Brazil (Hazin et al., 2008). Although bull sharks are considerably less abundant than tiger sharks off Recife (Afonso et al., 2017), six incidents were reportedly inflicted by a C. leucas (Hazin et al., 2008) whereas only one incident was ascribed to G. cuvier (Gadig, Sazima, 2003). In addition, the generally large body sizes of the C. leucas caught in this study, together with a preferential use of shallow coastal waters including estuarine areas highlights the potential hazard that this species might pose to bathers off Recife, a densely-populated region encompassing several estuaries along its coast. The risk posed by C. leucas indicates that a better understanding of its spatial ecology should be achieved with such information being of utmost importance for eventual mitigation strategies of shark hazard.

The migratory patterns and drivers of C. leucas are yet to be thoroughly understood. Bull sharks have been reported to migrate towards warmer latitudes during the austral winter in the western Indian Ocean (Daly et al., 2014), and evidence of partial migrations in C. leucas tagged at the Great Barrier Reef, Australia, suggests a reproductive response (e.g. females migrating potentially to give birth) as the main driver (Espinoza et al., 2016). Although the shark tagged in this study has moved southwards during the austral winter, the temperature regime in this equatorial region might be sufficiently warm to inhibit a temperature-driven latitudinal migration. The tagged shark exhibited a clear preference for waters < 20 m in depth, similarly to conspecifics from the northern hemisphere (Carlson et al., 2010). It seems thus unlikely that the shark had moved at superficial waters from the oceanic province for such a protracted period, as proposed by the location estimates of the UKFSST algorithm. Considering that C. leucas exhibit a clear preference for coastal habitats (Carlson et al., 2010; Hammerschlag et al., 2012; Heupel et al., 2015; Graham et al., 2016), the fact that the maximum depth registered by the transmitter (64 ± 4 m) matches the minimum depth of the continental shelf break (Martins, Coutinho, 1981) suggests that this shark moved mostly within the neritic province. Previous tracking studies on C. leucas across the oceanic realm reported movements through greater depths (122-164 m) and lower temperatures (16-21ºC) (Carlson et al., 2010; Lea et al., 2015) than the shark tracked in this study, which sustain such a hypothesis. Since the error ellipses of geolocation estimates did comprise waters from the continental shelf, it is very plausible that the tagged shark remained closer to the coast than the track suggests. Notwithstanding, C. leucas have previously been reported to use oceanic regions (Gadig et al., 2006; Bornatowsky et al., 2012; Lea et al., 2015), and therefore it is possible that the shark moved off the continental shelf for some time. Despite the speed of movements observed by the tracked shark during the study, previous research on C. leucas suggest comparable migratory and residential movement rates to individuals in other water bodies (Carlson et al., 2010; Daly et al., 2014; Lea et al., 2015). Thus, the movement estimated, herein, was considered to be biologically plausible besides representing the most substantial movements ever reported for a male C. leucas.

The satellite track herein described suggest that C. leucas off Brazil might move through broad coastal areas, even though they tend to exhibit some level of residency in specific regions, as observed around highly productive areas from the North Atlantic (Carlson et al., 2010). In accordance, the longest residency period (17 days) measured in this study occurred in a region influenced by the Cabo Frio upwelling system (Valentin et al., 1985), suggesting that feeding responses might have influenced such a behavior. Besides, the shark dove to deeper isobaths of ca. 30-m while exhibiting transient behavior, similarly to that observed in an adult male C. leucas moving off the southeast coast of the United States (Carlson et al., 2010). The use of deeper isobaths while moving off the southeastern Brazilian coast could be explained by the considerably wider shelf (90,210 km) and deeper shelf break (150-185 m) in this region (Martins, Coutinho, 1981). The continuous use of inshore habitats by C. leucas throughout its lifecycle increases the species’ exposure to potentially harmful impacts resulting from anthropic interference, which is obviously higher in these habitats (Beatley et al., 2002). Indeed, skeletal deformities observed in the caudal fins of bull sharks caught at the Brazilian northeastern region suggest a negative influence posed by anthropogenic impacts in the coastal zone (Afonso et al., 2016).

The biological features of C. leucas herein reported generally agree with previously published studies on conspecifics from other regions, and contribute to the knowledge about this shark species in a region where little is yet known. The maturation size of the female C. leucas caught in this study agrees with the estimates of Cruz-Martínez et al. (2004), since all mature females were larger than 204 cm LT. Although mature specimens were largely represented in C. leucas catch and were mostly sampled during the austral summer, which reportedly corresponds to the parturition period of the species at the Brazilian southeastern coast (Sadowsky, 1971), no pregnant females were noted and no signs of recent mating activity were detected either (Clark, Schmidt, 1965; Pratt, Carrier, 2001). Further research comprising a greater number of specimens sampled, probably adopting a different fishing strategy, is required to better understand several important aspects of C. leucas bioecology in the southwestern Atlantic Ocean, including reproduction, age and growth, diet and habitat use.


The authors are deeply grateful to the crew of the R/V Sinuelo and the interns of the Laboratório de Tecnologia Pesqueira of the Universidade Federal Rural de Pernambuco for indispensable help with fishing procedures. We would also like to thank Nuno Queiroz for providing us with dedicated software to conduct the SMWGA analysis. A Master’s degree and a postdoctoral (contract no. BJT-A049/2013) fellowships granted by Coordenação de Aperfeiçoamento de Pessoal de Nível Superior to YVN and ASA, respectively, are acknowledged. Precious suggestions made by two anonymous referees who helped us to improve the quality of the manuscript are also acknowledged. We also thank Doug Beare for his contribution to the fluency of the manuscript.


Afonso AS, Andrade HA, Hazin FHV. Structure and dynamics of the shark assemblage off Recife, Northeastern Brazil. PLoS ONE. 2014; 9(7):e102369. [ Links ]

Afonso AS, Hazin FHV, Carvalho F, Pacheco JC, Hazin H, Kerstetter DW, Murie D, Burgess GH. Fishing gear modifications to reduce elasmobranch mortality in pelagic and bottom longline fisheries off Northeast Brazil. Fish Res. 2011; 108(2-3):336-43. [ Links ]

Afonso AS, Hazin FHV. Vertical movement patterns and ontogenetic niche expansion in the tiger shark, Galeocerdo cuvier. PLoS ONE . 2015; 10(1):e0116720. [ Links ]

Afonso AS, Niella YV, Cavalcanti E, Andrade MB, Afonso JS, Pinto PS, Hazin FHV. Spinal deformities in free-ranging bull sharks, Carcharhinus leucas (Müller and Henle, 1839), from the western South Atlantic Ocean. J Appl Ichthyol. 2016; 32(6):1217-220. [ Links ]

Afonso AS, Niella YV, Hazin FHV. Inferring trends and linkages between shark abundance and shark bites on humans for shark-hazard mitigation. Mar Freshwater Res. 2017; 68(7):1354-65. [ Links ]

Amorim AF, Arfelli CA, Fagundes L. Pelagic elasmobranchs caught by longliners off southern Brazil during 1974-97: an overview. Mar Freshwater Res . 1998; 49(7):621-32. [ Links ]

Beatley T, Brower D, Schwab AK. An introduction to coastal zone management. 2nd ed. Washington: Island Press; 2002. [ Links ]

Bornatowski H, Wedekin LL, Heithaus MR, Marcondes MCC, Rossi-Santos MR. Shark scavenging and predation on cetaceans at Abrolhos Bank, eastern Brazil. J Mar Biol Assoc UK. 2012; 92(8):1767-72. [ Links ]

Brunnschweiler JM, Queiroz N, Sims DW. Oceans apart? Short-term movements and behaviour of adult bull sharks Carcharhinus leucas in Atlantic and Pacific Oceans determined from pop-off satellite archival taggin. J Fish Biol. 2010; 77(6):1343-58. [ Links ]

Carlson JK, Ribera MM, Conrath CL, Heupel MR, Burgess GH. Habitat use and movement patterns of bull sharks Carcharhinus leucas determined using pop-up satellite archival tags. J Fish Biol . 2010; 77(3):661-75. [ Links ]

Clark E, Schmidt KV. Sharks of the central Gulf coast of Florida. Bull Mar Sci. 1965; 15(1):13-83. [ Links ]

Cliff G, Dudley SFJ. Sharks caught in the protective nets off Natal, South Africa. 4. The bull shark Carcharhinus leucas Valenciennes. S Afr J Marine Sci. 1991; 10(1):253-70. [ Links ]

Compagno LJV. Sharks of the world: an annotated and illustrated catalogue of shark species known to date. Bullhead, mackerel and carpet sharks (Heterodontiformes, Lamniformes and Orectolobiformes). Rome: FAO; 2001. (FAO species catalogue for fishery purposes; No. 1, vol 2). [ Links ]

Compagno LJV, Dando M, Fowler S. A field guide to the sharks of the world. London: Harper Collins; 2005. [ Links ]

Conrath CL, Musick JA. Investigations into depth and temperature habitat utilization of overwintering grounds of juvenile sandbar sharks, Carcharhinus plumbeus: the importance of nearshore North Carolina waters. Environ Biol Fish. 2007; 82(2):123-31. [ Links ]

Cornelius JM, Reynolds JF. On determining the statistical significance of discontinuities within ordered ecological data. Ecology. 1991; 72(6):2057-70. [ Links ]

Cruz-Martínez AC, Chiappa-Carrara X, Arenas-Fuentes V. Age and growth of the bull shark, Carcharhinus leucas, from Southern Gulf of Mexico. J Northwest Atl Fish Sci. 2004; 35(13):367-74. [ Links ]

Daly R, Smale MJ, Cowley PD, Froneman PW. Residency patterns and migration dynamics of adult bull sharks (Carcharhinus leucas) on the east coast of South Africa. PLoS ONE . 2014; 9(10):e109357. [ Links ]

Dudley SFJ. A comparison of the shark control programs of New South Wales and Queensland (Australia) and KwaZulu-Natal (South Africa). Ocean Coast Manage. 1997; 34(1):1-27. [ Links ]

Espinoza M, Heupel MR, Tobin AJ, Simpfendorfer CA. Evidence of partial migration in a large coastal predator: opportunistic foraging and reproduction as key drivers? PLoS ONE . 2016; 11(2):e0147608. [ Links ]

Gadig OBF, Juliano MF, Barreiros JP. Further notes on the capture of a Carcharhinus leucas in a northeastern Atlantic oceanic insular shelf, the Azores Archipelago, Portugal. Cybium. 2006; 30(4):31-33. [ Links ]

Gadig OBF, Sazima I. A non-fatal attack by the tiger shark, Galeocerdo cuvieri, on the northeast coast of Brazil (Chondrichthyes: Carcharhinidae). Arq Ciên Mar. 2003; 36(1-2):119-22. [ Links ]

Galuardi B. Analyzepsat: microwave telemetry PSAT analysis R package version 3.0. R Foundation for Statistical Computing. Vienna; 2011 [cited 2015 Mar 15]. Available from: Available from: ]

Graham F, Rynne P, Estevanez M, Luo J, Ault JS, Hammerschlag N. Use of marine protected areas and exclusive economic zones in the subtropical western North Atlantic Ocean by large highly mobile sharks. Diver Distrib. 2016; 22(5):534-46. [ Links ]

Hammerschlag N, Luo J, Irschick DJ, Ault JS. A comparison of spatial and movement patterns between sympatric predators: bull sharks (Carcharhinus leucas) and Atlantic tarpon (Megalops atlanticus). PLoS ONE . 2012; 7(9):e45958. [ Links ]

Hazin FHV, Afonso AS. A green strategy for shark attack mitigation off Recife, Brazil. Anim Conserv. 2014; 17(4):287-96. [ Links ]

Hazin FHV, Burgess GH, Carvalho FC. A shark attack outbreak off Recife, Pernambuco, Brazil: 1992-2006. B Mar Sci. 2008; 82(2):199-212. [ Links ]

Heithaus MR, Dill LM, Marshall GJ, Buhleier B. Habitat use and foraging behavior of tiger sharks (Galeocerdo cuvier) in a seagrass ecosystem. Mar Biol. 2002; 140(2):237-48. [ Links ]

Heupel MR, Simpfendorfer CA, Espinoza M, Smoothey AF, Tobin A, Peddemors V. Conservation challenges of shark with continental scale migrations. Front Mar Sci. 2015; 2:1-7. [ Links ]

Hueter RE, Heupel MR, Heist EJ, Keeney DB. Evidence of philopatry in sharks and implications for the management of shark fisheries. J Northw Atl Fish Sci. 2005; 35:239-47. [ Links ]

Jackson JBC, Kirby MX, Berger WH, Bjorndal KA, Botsford LW, Bourque BJ, Bradbury RH, Cooke R, Erlandson J, Estes JA, Hughes TP, Kidwell S, Lange CB, Lenihan HS, Pandolfi JM, Peterson CH, Steneck RS, Tegner MJ, Warner RR. Historical overfishing and the recent collapse of coastal ecosystems. Science. 2001; 293(5530):629-37. [ Links ]

Karl SA, Castro ALF, Lopez JA, Charvet P, Burgess GH. Phylogeography and conservation of the bull shark (Carcharhinus leucas) inferred from mitochondrial and microsatellite DNA. Conserv Genet. 2010; 12(2):371-82. [ Links ]

Lea JS, Humphries NE, Clarke CR, Sims DW. To Madagascar and back: long-distance, return migration across open ocean by a pregnant female bull shark Carcharhinus leucas. J Fish Biol . 2015; 87(6):1313-21. [ Links ]

Lemahieu A, Blaison A, Crochelet E, Bertrand G, Pennober G, Soria M. Human-shark interactions: the case study of Reunion island in the south-west Indian Ocean. Ocean Coast Manage . 2017; 136:73-82. [ Links ]

Martins LR, Coutinho PN. The Brazilian continental margin. Earth-Sci Rev. 1981; 17(1-2):87-107. [ Links ]

Mazzoleni RC, Schwingel PR. Elasmobranch species landed in Itajaí Harbor, Southern Brazil. Notas Téc FACIMAR. 1999; 3:111-18. [ Links ]

McCord ME, Lamberth SJ. Catching and tracking the world’s largest Zambezi (bull) shark Carcharhinus leucas in the Breede Estuary, South Africa: the first 43 hours. S Afr J Mar Sci. 2009; 31(1):107-11. [ Links ]

Menezes TS, Santos FN, Pereira CW. Elasmobranch fish fauna off Sergipe State, Brazil. Arq Ciên Mar . 2005; 38:79-83. [ Links ]

Montoya RV, Thorson TB. The bull shark (Carcharhinus leucas) and largetooth sash (Pristis perotteti) in Lake Bayano, a tropical man-made impoundment in Panama. Environ Biol Fishes. 1982; 7(4):341-47. [ Links ]

Newton GM. 1996. Estuarine ichthyoplankton ecology in relation to hydrology and zooplankton dynamics in a salt-wedge estuary. Mar Freshwater Res . 47(2):99-111. [ Links ]

Nielsen A, Sibert JR, Anchetta J, Galuardi B, Lam CH. Ukfsst: Kalman Filter tracking including Sea Surface Temperature R package version 0.3. R Foundation for Statistical Computing. Vienna; 2012 [cited 2015 Mar 22]. Available from: Available from: ]

Pillans RD, Anderson WG, Good JP, Hyodo S, Takei Y, Hazon N, Franklin CE. Plasma and erythrocyte solute properties of juvenile bull sharks, Carcharhinus leucas, acutely exposed to increasing environmental salinity. J Exp Mar Biol Ecol. 2006; 331(2):145-57. [ Links ]

Pillans RD, Good JP, Anderson WG, Hazon N, Franklin CE. Freshwater to seawater acclimation of juvenile bull sharks (Carcharhinus leucas): plasma osmolytes and Ka+/K+-ATPase activity gill, rectal gland, kidney and intestine. J Comp Physiol B. 2005; 175(1):37-44. [ Links ]

Pratt HL, Carrier JC. A review of elasmobranch reproductive behavior with a case study on the nurse shark, Ginglymostoma cirratum. Environ Biol Fishes. 2001; 60(1;3):157-88. [ Links ]

Queiroz N, Humphries NE, Noble LR, Santos AM, Sims DW. Short-term movements and diving behaviour of satellite-tracked blue shark Prionace glauca in the northeastern Atlantic Ocean. Mar Ecol Prog Ser. 2010; 406:265-79. [ Links ]

Reilly BD, Cramp RL, Wilson JM, Campbell HA, Franklin CE. Branchial osmoregulation in the euryhaline bull shark, Carcharhinus leucas: a molecular analysis of ion transporters. J Exp Biol. 2011; 214(17):2883-95. [ Links ]

Rodrigues-Filho LFS, Rocha TC, Rêgo PS, Schneider H, Sampaio I, Vallinoto M. Identification and phylogenetic inferences on stocks of sharks affected by the fishing industry off the Northern coast of Brazil. Genet Mol Biol. 2009; 32(2):405-13. [ Links ]

Sadowsky V. Notes on the bull shark Carcharhinus leucas in the lagoon region of Cananéia, Brazil. Bol Inst Oceanogr. 1971; 20(2):71-78. [ Links ]

Santana RMC. Composição e biomassa da comunidade fitoplanctônica no estuário do rio Maraú - Baía de Camamu (BA). [MSc Dissertation on the Internet]. Ilhéus, BA: Universidade Estadual de Santa Cruz; 2012 [cited 2015 Mar 24]. Available from: Available from: ]

Simpfendorfer CA, Burgess GH. The IUCN Red List of Threatened Species. Carcharhinus leucas. e.T39372A10187195 [Internet] 2009 [cited 2015 Mar 22]. Available from: Available from: ]

Simpfendorfer CA, Freitas GG, Wiley TR, Heupel MR. Distribution and habitat partitioning of immature bull sharks (Carcharhinus leucas) in a Southwest Florida Estuary. Estuaries. 2005; 28(1):78-85. [ Links ]

Thorson TB. Status of bull shark, Carcharhinus leucas, in Amazon River. Copeia. 1972; 1972(3); 601-05. [ Links ]

Valentin JL, Silva NML, Bastos CTBN. Les diatomées dans l’upwelling de Cabo Frio (Brésil): liste d’espècies et éstude écologique. J Plankton Res. 1985; 7(3):313-37. [ Links ]

Werry JM, Lee SY, Lemckert CJ, Otway NM. Natural of Artificial? Habitat-use by the bull shark, Carcharhinus leucas. PLoS ONE . 2012; 7(11):e49796. [ Links ]

Wiley TR, Simpfendorfer CA. The ecology of elasmobranchs occurring in the Everglades National Park, Florida: implications for conservation and management. Bull Mar Sci . 2007; 80(1):171-89. [ Links ]

Wood SN. Fast stable restricted maximum likelihood and marginal likelihood estimation of semiparametric generalized linear models. J Roy Stat Soc B. 2011; 73(1):3-36. [ Links ]

Received: July 18, 2016; Accepted: July 24, 2017

Creative Commons License This is an open-access article distributed under the terms of the Creative Commons Attribution License