Transoceanic dispersal and connectivity of a white shark (Carcharodon carcharias) between southern Africa and Southeast Asia
Dylan T. Irion





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Abstract
Population connectivity shapes dispersal, genetic structure, and responses to climate change. Understanding these patterns is vital for identifying threats and improving species management strategies. In May 2024, a fisher from Indonesia with a satellite tag in their possession contacted local conservationists from non-profit organisation Project Hiu. The Project Hiu staff contacted Wildlife Computers with the serial number and successfully located the tag owner. Remarkably, the tag was identified as having been attached to a 390 cm total-length (TL) subadult female white shark (Carcharodon carcharias) in May 2012 in South Africa. Through subsequent investigations, including email correspondence and interviews with the fishers, we have determined that in November 2016, a 473 cm TL female shark (misidentified at the time as a longfin mako shark, Isurus paucus) was captured in longline gear off the coast of Indonesia, Southeast Asia. This remarkable sequence of events marks the first documented movement and connectivity of a white shark between South Africa and Southeast Asia (Indonesia). Over the 4.5 years at liberty, the shark grew in length an estimated 83 cm (18.4 cm per year), supporting previous findings on growth rates for the species. This record of events highlighted both the potential for misidentification and trade of threatened and protected shark species and the increasing benefits of close collaboration with local fishers. This newly discovered link expands our understanding of their wide-ranging connectivity among remote regions, advances our knowledge of their biology and behavior, and underscores the importance of ongoing international research and conservation efforts to protect these apex predators and their habitats.
Keywords: high seas, international collaboration, longline, migration, protected species, satellite telemetry, species distribution, species management.
Introduction
Population connectivity, the degree of exchange of individuals among spatially separated populations, is essential for functioning marine ecosystems (Cowen et al. 2007). It influences dispersal and migration patterns, the formation of genetic population structure, source–sink population dynamics, and responses to climate change and other anthropogenic pressures (Kool et al. 2013; Beger et al. 2022). Furthermore, understanding marine connectivity and migration patterns is important to identify threats across a species’ range and opportunities for effective management (Queiroz et al. 2019; Sequeira et al. 2019).
Satellite-linked tags have transformed our understanding of animal movements, habitat use, and behaviors by providing unprecedented insights into their migrations across vast oceanic regions (Bonfil et al. 2005; Boyle et al. 2009; Orlov et al. 2020; Ramos et al. 2023). This knowledge has important applications for conservation and management, including identifying key foraging areas, migration corridors, and estimating overlap with fisheries to assess potential interactions and risks (Sequeira et al. 2019; Queiroz et al. 2019).
White sharks are well known for their transoceanic migrations (Bonfil et al. 2005; Blower et al. 2012; Duffy et al. 2012; Domeier and Nasby-Lucas 2013; Spaet et al. 2020). These border-crossing movements, along with their high vulnerability to overfishing, has supported their listing under CITES Appendix II and the Convention on Migratory Species (Rigby et al. 2022). However, they also show fidelity to coastal aggregation sites throughout their global range (Bonfil et al. 2005; Jorgensen et al. 2010; Domeier and Nasby-Lucas 2013; Skomal et al. 2017; Franks et al. 2021; Kock et al. 2022). Furthermore, in South Africa, many historically abundant coastal white shark aggregations have recently shown declines in sightings. The lack of a clear understanding of the population status, distribution in the region and drivers of movement continues to hinder effective management of the species (Bowlby et al. 2022, 2023, 2024; Kock et al. 2022; Gennari et al. 2024).
Our understanding of South African white shark distribution relies on telemetry, genetics, and catch-record data (Pardini et al. 2001; Bonfil et al. 2005; Andreotti et al. 2016; Kock et al. 2022). These sources indicate that the southern African coastline is an important area for juvenile and subadult sharks (<360 cm TL) of both sexes. Sharks in the south-western Indian Ocean pelagic realm are predominantly subadults and adults, and often females (Kock et al. 2022). Catches of large, mature individuals in Kenya, Tanzania, and Madagascar suggest potential shifts in habitat preference on reaching maturity. However, there is limited direct evidence linking these individuals to South Africa (Cliff et al. 2000; Zuffa et al. 2002), even though satellite tracking shows movement between cold-temperate South Africa and tropical Mozambique and Madagascar (Kock et al. 2022). Direct evidence of longitudinal dispersal from South Africa is currently documented by the movements of one individual from Dyer Island, Gansbaai to Ningaloo on the western coast of Australia, and supported by genetic data from six individuals with South African-like mtDNA haplotypes collected in eastern Australia and Tasmania (Pardini et al. 2001; Bonfil et al. 2005; Blower et al. 2012; Andreotti et al. 2016).
Pardini et al. (2001) found that maternally inherited mitochondrial genomes (mtDNA) were distinct between South African and Australasian white shark populations, but microsatellites in the nuclear genome were not significantly distinct. Bonfil et al. (2005) proposed that the genetic results from Pardini et al. (2001), which suggested that dispersal was limited to males, could be explained by philopatric female sharks from South Africa mating in Australia, but giving birth in South Africa. Further evidence of separate genetic clades between continents suggests that despite long-distance movements, genetic differences among shark populations in different regions remain distinct (Gubili et al. 2011; Blower et al. 2012; O’Leary et al. 2015; Andreotti et al. 2016). More recently, high-resolution genome-wide markers have shown that white sharks from South Africa, Australia and New Zealand form a distinct genetic clade from North Atlantic/Mediterranean, and North Pacific individuals (Wagner et al. 2024). These findings have highlighted the need for further research into the frequency of movement and connectivity of South African white sharks beyond their known ranges.
Through unexpected events, here we document the first recorded physical link and connectivity of a white shark between southern Africa and Southeast Asia. This discovery, facilitated by an incidental capture and a non-transmitting satellite tag, has highlighted collaboration among fishers, scientists and conservationists. It underscores the need for international cooperation and raises further questions about white shark dispersal and connectivity, especially considering changing ocean environments and shark distributions in South Africa.
Methods
On 9 May 2012, a SPOT-258 satellite transmitter (Wildlife Computers Inc., Redmond, WA, USA) was deployed on the first dorsal fin (Fig. 1a) of a 390 cm total-length (TL) female white shark. On the basis of her size, the female white shark was classified as a subadult (Malcolm et al. 2001; Márquez-Farías et al. 2024). Tagging took place aboard the M/V Ocearch and was part of a larger study investigating the movement of the species in southern Africa (Kock et al. 2022). Precise measurement and tagging of this individual occurred at Dyer Island, a productive Cape fur seal colony (Arctocephalus pusillus pusillus) situated in the temperate Atlantic Ocean, 8 km offshore of Gansbaai, South Africa (34°40′S, 019°25′E, Fig. 2, blue triangle). Data collection was conducted under the South African Department Forestry, Fisheries and the Environment: Oceans and Coasts permitting authority (Permit #RES2012/OCEARCH/umbrella-project) and adhered to the legal requirements of South Africa.
(a) Left-side dorsal photograph from the M/V Ocearch platform during tagging in May 2012 in Gansbaai, South Africa. (b) Left-side dorsal photograph from a shark cage diving charter in September 2012 in Gansbaai, South Africa (SharkWatchSA). (c) Left-side dorsal photograph taken at the landing site in Indonesia in 2016.

Top panel: SPOT satellite tag transmissions (black circles) for the white shark (Carcharodon carcharias) tagged at Gansbaai, South Africa, in May 2012. Dashed line in grey indicates the shortest straight-line distance between the last transmission and the capture location. Overviews corresponding to lower panels are indicated by lines and colour. Lower-left, blue border, shows inshore detections near the tagging site (tagging site indicated in blue triangle). Lower-right orange border depicts the region where the shark was captured in Indonesia in November 2016 (orange circle). Pink diamond indicates location of a previously documented catch (Fahmi and Dharmadi 2014). Purple square is an undocumented sighting of a large white shark filmed by recreational divers in Nusa Penida, Bali, and reported by popular media in 2019.

Results
Collaborative recovery of the SPOT tag
The recovery of the satellite tag was possible through the proactive efforts and investigation of several dedicated parties. In May 2024, Wildlife Computers received notice from Dr Chelsea Black, a member of the Scientific Team at Project Hiu, regarding a SPOT-258 tag recovered by a local fisher in Indonesia. The records of Wildlife Computers showed that this tag (SN 12SO155; PTT number 118863) was associated with a white shark tagged off the coast of South Africa in May 2012. Wildlife Computers subsequently contacted Ocearch and Mr Dylan Irion, whose names were associated with this tag in the Wildlife Computers data portal.
Following an investigation by using email threads, we deduced that on 29 November 2016, a fisher from Tanjung Luar captured a large shark that was misidentified as a 473 cm TL female longfin mako (Isurus paucus) in the waters of ‘Eastern Sumba or Tanjung Pamali’. The landing was reported to Mr Dharmadi of the Ministry of Marine Affairs and Fisheries of Indonesia, who relayed the information to Dr Simon Weigmann of Elasmo-Lab, Hamburg, and Chair of the Integrative Taxonomy Working Group of the IUCN SSC Shark Specialist Group. Dr Weigmann referred Mr Dharmadi to Dr David Ebert, who was then with Moss Landing Marine Laboratories, and they began an email correspondence with Wildlife Computers around December 2016. Wildlife Computers expected the tag to be returned for refurbishment, with an order number in place; however, it was never received. In an email thread between Wildlife Computers and Dr Ebert in December 2016, Dr Ebert confirmed that a fisher kept the tag at Tanjung Luar, East Lombok. Wildlife Computers and Mr Dharmadi contacted Ocearch, the owners listed on the tag purchase order, and plans were in place to recover the SPOT tag from the fisher and ship it to the USA for refurbishment. However, after the initial correspondence, there was no further communication, leading to the cancellation of the order and closing of the file. There was no follow-up until the team from Project Hiu in Lombok, Indonesia, was notified of the tag 8 years later, in May 2024, by a local fisher who had the tag in their possession.
Project Hiu works with local fishers in Indonesia to conserve sharks and has recently began deploying satellite tags and offering a monetary reward for observing or recovering any shark tags to promote the survival of individuals that might otherwise be targeted by fisheries. Through their diplomatic engagement with the fishing community, Project Hiu located the fishers who then detailed the 2016 catch of a large shark in East Sumba. The fishers kept the tag and contacted Project Hiu members after learning about the monetary reward.
The fishers recalled that the large shark was caught on a longline set at a depth of 50 m in cold water typical of the season, where upwelling can bring temperatures as low as 16°C (DeVantier et al. 2008). Tuna hooks were baited with mackerel fish and other fish products on branch lines spaced approximately 1.5 m apart. When retrieving the lines set the previous night, they found the large shark gut-hooked while scavenging on a bull shark (Carcharhinus leucas) caught on the same longline. The fishers hauled the large shark onboard the fishing vessel, cut it into sections, and immediately returned to Tanjung Luar to land the catch, where it was sold for 20 million Indonesian Rupiahs (USD~1400). The fishers then indicated the location of the capture on a map which they remembered due to its proximity to shore and a popular surfing location (Fig. 2, orange circle). They remember the capture well because of the large size of the shark, the tag on its dorsal fin and the amount of money they received.
Satellite track
Transmission data revealed that the white shark remained within approximately 150 km of the tagging location for at least 5 months, which was additionally confirmed via photographic records throughout the period (Fig. 1b). In 2013, following a brief window of no satellite transmissions, the shark transmitted a location from inside the uThukela Banks Marine Protected Area located between the cities of Durban and Richards Bay along the South African coast, marking the start of a journey covering ~38,000 km over 395 days, transmitting with a mean period of 8.55 h (s.d. = 37.3) between transmissions. During this journey, the shark spent most of its time in the open ocean, with notable visits near the subtropical front of the Indian Ocean, which is generally located between 30°S and 40°S, although its exact position varies seasonally and regionally. The journey included stops in the Exclusive Economic Zones of Mozambique and Madagascar, with its final transmitted location being approximately 1000 km south-east of Madagascar in April 2014 (Fig. 2). During this time, she encountered a wide range of sea-surface temperatures, ranging from 3.8°C to 29°C, swam at an average speed of 56 km per day and covered a cumulative distance of 37,178 km, measured as the straight-line distance between satellite transmissions (Pérez Mateu 2024). Photographic (Photo-ID) records indicate that the shark was known to researchers in South Africa as early as 2010, when it was encountered in Mossel Bay and estimated to be between 225 and 274 cm (size bin), and again in Mossel Bay in 2011, this time estimated to be between 275 and 324 cm (size bin). The last photographic record of this shark in South Africa was from September 2012, in Gansbaai, during a shark cage diving charter (Fig. 1b). The first tag transmission via satellite was received on 5 June 2012 (34°51′S, 020°2′E), and the last on 3 April 2014 (27°27′S, 056°3′E, Fig. 2), yielding a longer than expected transmitter lifetime of 22 months for the normally 1-year SPOT tags.
Growth rate
The shark was measured at 390 cm TL on 9 May 2012, during tag attachment, and then at 473 cm TL on 29 November 2016. All sharks landed in the fishery that processed this catch are measured by fisheries enumerators from the Ministry of Marine Affairs and Fisheries. Fishers typically process large sharks into sections on capture, owing to limited space onboard. Landings of large sharks are then measured by reconstructing the shark from its pieces and measuring the total length according to the number of floor tiles occupied by the shark. If landing measurements are reliable, this indicates that she grew by 83 cm to a size indicating sexual maturity (Malcolm et al. 2001; Márquez-Farías et al. 2024) over approximately 4.5 years, suggesting an average growth rate of about 18.4 cm per year.
Discussion
We have presented here the first documented physical link and connectivity between southern Africa and Southeast Asia, exhibiting the longest recorded one-way point-to-point dispersal of more than 10,000 km for a white shark. The tagging site in Gansbaai, South Africa, is renowned as a prime location for winter feeding on Cape fur seals from May to September, and provides a critical temperate, kelp-associated habitat for white sharks (Jewell et al. 2014; Towner et al. 2016). In contrast, the final capture location in Indonesia (10°20′S, 120°27′E; Fig. 2, orange circle) is dominated by reef building coral and tropical sea temperatures (Wilson et al. 2011). This striking transition highlights the species’ capacity for long-range dispersal between vastly different ecological niches. The movement between southern Africa and Southeast Asia surpasses the 9,000 km straight-line distance recorded for another subadult female white shark from Gansbaai, South Africa, to the west coast of Australia (Bonfil et al. 2005). This report marks only the second recorded transoceanic dispersal event for the species from South Africa, highlighting that despite extensive research, much remains to be learned about white sharks’ dispersal patterns in the southern hemisphere.
Transoceanic migrations and large-scale movements between cooler temperate and tropical waters have been well documented for white sharks across various regions (Boustany et al. 2002; Bonfil et al. 2005, 2010; Bruce et al. 2006; Domeier and Nasby-Lucas 2007, 2008; Weng et al. 2007; Guttridge et al. 2024). Whereas previous studies have reported movements between the temperate waters of South Africa and tropical regions such as Mozambique (Kock et al. 2022), the migration observed in this study spans a much greater distance, crossing a large ocean basin and providing new insights into the spatial dynamics of white shark movements.
In addition to the surprising connectivity between southern Africa and Southeast Asia, there are few documented occurrences of white sharks in Southeast Asia (Duffy 2016). The species is rarely reported in Indonesia, with the first confirmed record coming from Dompu, West Nusa Tenggara, where an estimated 6 m adult male white shark was harpooned by fishers onboard a demersal longliner (Fahmi and Dharmadi 2014; Fig. 2, pink diamond). However, given this discovery and the misidentification of the tagged shark from this study as a longfin mako, white shark presence in Indonesia may be more common than previously believed. Isurus oxyrinchus and I. paucus are documented in longline fisheries in Indonesia and can be mistaken for C. carcharias. In fact, misidentifications of mako species with C. carcharias are believed to occur in Indonesian fisheries statistics as exhibited in the present record (Oktaviyani et al. 2023). Shark catch recording programs conducted in several locations across Indonesia use an identification guidebook from White et al. (2006) that does not include an identification key for C. carcharias. This raises concerns about the trade of threatened species and underscores the need for improved species identification training, reporting, and when possible, access to DNA-based species identification/confirmation in markets.
Long-distance and transoceanic migrations expose white sharks to heightened mortality risks, such as capture in longline fisheries (Queiroz et al. 2019). Furthermore, shark fishing is widespread across Indonesian territorial waters, with diverse fish landing sites exhibiting varying facilities, characteristics, and conditions (Dewi et al. 2021). This record and the previous record from Indonesia provide evidence that some trade in white shark products is occurring, perhaps being complicated by species misidentification. The lack of sufficient information on catch data, potential yields, species diversity, biology, exploitation levels, and institutional socio-economic resources of sharks and rays in Indonesia hampers the development of a robust framework for sustainable fisheries management (Dharmadi et al. 2015; Dewi et al. 2021). However, contemporary trade in this species is not unique to Southeast Asia (Shivji et al. 2006). Nevertheless, as a signatory to CITES, Indonesia is obligated to regulate the utilization and trade of species listed in the CITES Appendices (Nurbani et al. 2021). Standardization and training in species identification, data recording and traceability is ongoing in the country and may be improved with updated species keys that reflect the discovery reported here (Oktaviyani et al. 2023). Simple educational resources and training has proven effective at improving the accuracy and reliability of species identification and reporting in similar fisheries (Macbeth et al. 2018).
The presence of South African sharks in the far eastern regions of the Indian Ocean aligns with our current understanding of genetic differentiation between populations of the species. Philopatric evidence, indicated by heterogeneity in mtDNA and uniformity in nuclear DNA based on microsatellite data, suggests that even though transoceanic movements may occasionally result in rare breeding or parturition, they are not expected to significantly contribute to gene flow (Pardini et al. 2001; Bonfil et al. 2005; Gubili et al. 2011; Blower et al. 2012; Andreotti et al. 2016; Wagner et al. 2024). The record offers some insight into white shark growth rates, although it is important to note that the reported length estimate may have a margin of error owing to measurement challenges during landing, because the shark was cut up and re-assembled for estimation. Over its 4.5 years at liberty, the shark grew an estimated 83 cm (18.4 cm per year), a growth rate faster than previously reported for subadults of this species (Christiansen et al. 2016). The discovery of such a widely displaced individual highlights the importance of gaining a clearer understanding of the distribution patterns of subadult and adult sharks in southern Africa and the mechanisms driving their dispersal. Given the increased pressure on this population, and a lack of data on white shark reproduction and fecundity, there is a critical need to satellite tag more large white sharks, particularly females. However, accessing adult sharks of both sexes has proven challenging, particularly after the displacement of white sharks from previous aggregation sites in the Western Cape, South Africa (Towner et al. 2022). Efforts might benefit from a focus on searching for white sharks off the southern coasts of Mozambique and Madagascar, and possibly Indonesia, where migratory females appear to be active. Furthermore, an overdue comparison of photo identification catalogues across countries would also complement telemetry and genetic datasets.
The South African white shark population size, trends, and the impact of killer whales (Orcinus orca), fisheries, and shark nets are currently the focus of extensive research and scientific debate (see Bowlby et al. 2022, 2023, 2024; Kock et al. 2022; Gennari et al. 2024). Recent studies have documented novel interactions between white sharks and killer whales (Towner et al. 2023, 2024), the displacement of white sharks by killer whales (Towner et al. 2022, 2023), and the vulnerability of white shark populations to human-induced mortality (Bowlby et al. 2022; Kock et al. 2022). These findings emphasize the need to fully understand the movements and connectivity between remote geographic areas and how frequently these occur. Increased redistribution may be expected if continued predatory displacement persists as an additional coastal threat to white sharks in South Africa.
The series of events documented here has highlighted the crucial role of the fishing industry and community engagement in scientific discovery, emphasizing the importance of multinational communication and collaboration. Simultaneously, the chronology of events also illustrates the importance of confirming information provided by fishers, questioning sources and following up on reports. Without the trusted working relationships built among conservation agencies, local fishers and the government, it is likely that this discovery would have remained unknown. Project Hiu has successfully recovered four tags through their relationships with the local fishing community, with two others highlighting the movements of tiger sharks from Australia to Indonesia. Establishing connections and building respect between conservationists and shark fishers forms a strong foundation for scientific advancement in the area. In a low socio-economic community that stands to benefit greatly from the indiscriminate capture of sharks, understanding how to navigate financial incentives to support scientific discovery and provide an alternative to fishing sharks is an ongoing challenge. The discovery made here may encourage continued communication and transparency regarding discovered tags and inspire fishers to have pride in their involvement with the conservation and research of sharks. The opportunity to also use this discovery to provide further training and materials for identifying sharks in these fisheries should be prioritised.
Our discovery has shown the previously unknown area of occurrence for white sharks from South Africa, expanding our understanding of their extensive range and connectivity among distant regions. It has also advanced our scientific understanding of white shark biology and behavior, emphasizing the importance of ongoing international research, collaboration and conservation efforts to protect these apex predators and their habitats. Most importantly, it has highlighted areas of focus for future improvements in understanding white shark ecology and conservation.
Data availability
Satellite telemetry data used in this study are available via the DOI:10.5281/zenodo.5575189.
Conflicts of interest
Alison Kock is a Guest Editor of the ‘White Sharks Global proceedings and recent advances in white shark ecology and conservation’ collection of Wildlife Research. To mitigate this potential conflict of interest she had no editor-level access to this manuscript during peer review. The authors have no further conflicts of interest to declare.
Declaration of funding
The study was made possible through generous funding by Fischer Productions for fieldwork and equipment costs.
Acknowledgements
We thank Dr Alan Boyd, Herman Oosthuizen, Darrell Anders and Michael Meÿer from the Department of Forestry, Fisheries and the Environmental: Oceans and Coasts Branch for operational support and permits to conduct this work. Additionally, Ryan Johnson, Dr Malcolm Smale, Dr Pieter Koen, Adrian Hewitt, Captain Brett McBride and the Ocearch crew were instrumental in the 2012 research expedition in South Africa. Ervin Indrayana Situmeang is also thanked for providing translation during the interview with fishers, and Dr Chelsea Black and the fishers working with Project Hiu for communicating the initial tag recovery. Our gratitude goes to Dr David Ebert and Mr Dharmadi for their original effort to notify the tag owners. Dr Alisa (Harley) Newton (Ocearch), Dr Robert Hueter (Ocearch), and Dr Sara Andreotti from Stellenbosch University provided useful comments that improved the paper. We also thank four anonymous reviewers whose comments further improved this work. We also thank Charlie Huveneers for generously covering the open access fees for this article.
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