Satellite telemetry is a widely used tool to define horizontal and vertical movements of elasmobranch species across a variety of environments [1, 2]. Studies have described critical habitats, redefined management strategies, and gathered important life-history data about these at-risk predators [3, 4]. However, very little information exists about pelagic sharks in the South Pacific despite the region’s exportation of substantial quantities of shark fins to the Hong Kong market. Fiji exported 76,634 kg of dried and frozen fins in 2011, though these estimates include fish not necessarily caught in Fijian waters [5]. Fijian communities and villages are generally not targeting sharks on nearshore reefs as no domestic market exists [6, 7]. Considering the gear types (longlines and gillnets) used by larger vessels to harvest sharks in large quantities, it is logical that fins harvested in Fijian waters are primarily from pelagic species.

The Republic of Fiji is home to several shark species that spend at least part of their life history associated with reef habitats. Whitetip reef (Triaenodon obesus), grey reef (Carcharhinus amblyrhyncos), blacktip reef (Carcharhinus melanopterus), bull (Carcharhinus leucas), and silvertip (Carcharhinus albimarginatus) sharks are commonly observed species on Fiji’s reefs [8, 9]. The former four species are also known to make nearshore slope or pelagic excursions [10, 11]. There are no current studies defining movements of pelagic sharks in the Fijian archipelago. Gathering fundamental ecological information, such as vertical and horizontal movement data obtained through satellite tagging, is the critical first step towards appropriate management of species in this area.

The silvertip shark is a slow-growing requiem shark, with a maximum recorded total length (TL) of 300 cm. Males and females reach maturity between 160–180 and 160–200 cm TL, respectively [11, 12]. Although widely distributed throughout the tropical Indian and Pacific Oceans, populations appear fragmented with minimal dispersion [10]. The silvertip shark inhabits coastal and offshore waters, and individuals are most commonly observed near coral reefs and nearshore reef slopes from the intertidal zone to depths of 600–800 m [10, 11, 14]. Juveniles inhabit shallow nearshore waters, such as lagoons. In contrast, adults occupy a larger range of habitats [10, 14]. Few studies have examined the horizontal movements of silvertip sharks. At Osprey Reef, Australia, silvertips demonstrated both year-round residency to this isolated seamount and unidirectional migrations, briefly being detected on neighboring reefs (~14 km away) [14].

Silvertip sharks are an active species with a diet consisting of benthic and pelagic teleosts, eagle rays, other sharks, and cephalopods [15]. A calculated trophic position of 4.2 traditionally classifies silvertip sharks as an apex predator [15].

The conservation status of silvertip sharks is undecided throughout most of its range, but based on available data, the species is currently Red-listed and classified as ‘Near Threatened’ by the International Union for Conservation of Nature (IUCN) [14]. Globally, silvertips are one of nine prominent shark species landed by high seas longlines and net fleets, either intentionally or as by-catch, and are identified in the Hong Kong fin trade [14, 16]. Reports of severe localized declines in Australia and Chagos, high catch rates in commercial and artisanal fisheries in South Africa, Indonesia, Thailand, Myanmar, Cambodia and the Philippines, coupled with its habitat-faithful nature suggest isolated populations are vulnerable to overexploitation [14, 17, 18]. A 1996 shark survey conducted in the Chagos Archipelago noted severe declines in sightings of silvertip sharks when compared to 1970 findings [18]. Given the species’ susceptibility to line capture, this decline was attributed to fishing pressure [18]. However, an increase in silvertip shark abundance was recorded during a 2006 survey, demonstrating the potential time-scales at which isolated populations can be reduced by over-fishing and show signs of recovery [19]. Though no current population data exist for silvertip sharks within the Fijian archipelago, the broader western Pacific tuna longline fishery reports high levels of silvertip by-catch [20]. Additional data may provide a basis for the reclassification of this species by the IUCN.

The cultural and governance structure of the Fijian islands offers unique protection to nearshore reefs and their associated species (including several shark species), which are locally managed by coastal villages that reside in the immediate area [7]. Community-based management or locally managed marine areas (LMMAs) have created de facto protection for certain reef-associated shark species, whereas offshore waters are, conversely, heavily fished by foreign longlining fleets [20]. It is unclear how much protection the silvertip shark obtains from Fijian LMMAs, as silvertips are suspected to inhabit shelf or pelagic waters during some life stages and/or routine movements [9, 10, 14]. A long-term assessment of shark relative abundance at an established Fijian provisioning site, observed seasonality to silvertip presence, being most abundant between September and December [8].

The lack of basic life-history data, the prevalence of silvertip sharks in the international fin trade [16], and recent discussions by the IUCN to relist the species as “vulnerable” [14] give merit to an ecology-focused satellite tagging study. Understanding water column use and the potential possibility to correlate such findings with fisheries-dependent data will be a vital step in protecting this species. The aim of this study was to describe the silvertip’s short-term depth and temperature use to obtain critical habitat data of this poorly understood species.

On April 7, 2014, one X-Tag was deployed on an immature female silvertip measuring 155 cm (TL) near Kadavu Island, Fiji (18.698S, 178.530E). The tag and tether prematurely detached from the shark on April 18, 2014, presumably due to attachment failure. After floating at the surface for 1 day, the tag released from the attached tether due to the constant pressure release mechanism and began transmitting on April 19, 2014. The first Argos location (18.556S, 178.442E) was 18.37 km NW from the deployment location (Figure 1). The tag was deployed at a location with bottom depth of approximately 48 m and the first Argos location had a bottom depth of approximately 1,950 m. All (100%) of the transmitted dataset was received through the Argos system providing a total of 2,182 combined depth and temperature records on 15-min intervals and 13 daily position estimates. Five delta limited depth records and seven delta limited temperature records were identified in the dataset.

The silvertip occupied depths between 0 and 381.9 m with a mean (±SD) of 59.9 ± 38.5 m. The silvertip spent the most time (97.0%) in the upper 150 m of the water column and over half of its time (52.9%) above 50 m. The animal spent minimal time near surface waters (3.1% of time in upper 10 m) (Figure 2). This individual recorded a mean temperature of 26.30 ± 1.71°C, and temperatures ranged from 14.16 to 28.57°C. Most temperature records (99.5%) fell between 22 and 29°C, and over half of the records (67.5%) fell between 26 and 29°C. The tag recorded deeper and colder records as the deployment progressed (maximum depth: r ² = 0.563, P = 0.004913; minimum temperature: r ² = 0.533, P = 0.006986) (Figure 2).

The daily daytime mean depths were significantly deeper than the daily nighttime mean depths (t _12.491 = 4.8537, P = 0.000353, Figure 3). Similarly, the daily daytime mean temperatures were significantly cooler than the daily nighttime mean temperatures (t _11.627 = 5.9908, P = 7.19 × 10⁻⁵, Figure 4). There was larger variation between consecutive depth records during the day period than the night period (t _17.554 = 4.8456, P = 0.0001389).

The three deepest 15-min records (215.2, 220.6, and 199 m) were recorded during the night and were delta limited descents. The daily maximum depth values from these 3 days extend to 263.6, 360.4, and 381.9 m, respectively (Figure 2). There were no consecutive depth records below 200 m, indicating that deep-water excursions were less than 30 min in duration.

Tracking a silvertip shark via PSAT provided previously unknown depth, temperature, and habitat information. Daytime and nighttime depth and temperature differences were identified. The shark inhabited deeper and cooler waters during the day. Consecutive daytime depth records exhibited greater variation compared to nighttime depth records, indicating expanded diurnal vertical habitat use. The silvertip’s diel vertical migration (DVM) to deeper daytime depths mimics that of multiple coastal, pelagic and reef-associated elasmobranchs [26–27]. In Palau, grey reef sharks exhibiting a crepuscular pattern of DVM by occupying shallowest depths (<30 m) at dawn and dusk was linked to foraging on shallow reefs [26]. Alternatively, grey reef sharks in Australia exhibited reverse DVM patterns (remaining shallower during the day, but not specifically dawn or dusk) to those tracked in Palau. In both studies, DVM patterns were attributed to foraging [28]. Grey reef sharks have shown to expand horizontal range at night; therefore, these intraspecific differences in DVM patterns may be explained by site-specific bathymetry and/or differences in prey behavior [14, 28]. Furthermore, juvenile white sharks (Carcharodon carcharias) demonstrated similar patterns of deeper daytime depths coupled with increased activity levels, suggesting daytime foraging behavior [27]. Silvertip diet has shown to contain ~13% cephalopods [15], therefore increased daytime vertical habitat use may reflect foraging on species which undergo DVM and seek daytime refuge at depth, such as cephalopods. Furthermore, the DVM pattern may be linked to temperature selection as well as foraging behavior. Small-spotted catsharks (Scyliorhinus canicula) exhibited nocturnal DVMs to warmer, shallower, and prey-rich depths with increased nighttime activity. Laboratory experiments determined this strategy of foraging in warm water and resting in colder water maximized bioenergetic efficiency [29].

Besides foraging behavior, the silvertip’s DVM may be attributed to predator avoidance, similar in function to those observed in juvenile Caribbean reef sharks in Belize. Large Caribbean reef sharks (>110 cm TL) perform DVM presumably for foraging on nocturnally vulnerable prey species (e.g., parrotfish) [26]. Meanwhile, at night, juvenile Caribbean reef sharks moved into shallow waters of the lagoon from the deeper fore-reef to reduce encounters with larger conspecifics [26]. In Fiji, larger conspecifics and other large-bodied shark species such as scalloped hammerhead (Sphyrna lewini), shortfin mako (Isurus oxyrinchus), tiger (Galeocerdo cuvier), and bull (C. leucas) sharks are potential predators of a juvenile silvertip shark.

The tagged animal spent most of its time in the epipelagic zone, although at least four deep-water excursions (>200 m) were identified in the daily maximum depth records. The maximum recorded depth was 381.9 m, but silvertip sharks have previously been recorded to maximum depths between 600 and 800 m [10]. The silvertip did not spend an extended duration (>30 min) at mesopelagic depths, suggesting that the deep dives were short excursions. Though the precise function is unknown, dives would likely be longer in duration if serving the purpose of predator avoidance [30]. The animal recorded increasing depth records as the deployment progressed, potentially corresponding to movement off the shelf and away from the tagging location. Although the tracked individual was tagged on the reef, the deep depth records corresponded to entering pelagic waters. Pelagic species are more likely to encounter commercial longline fishing than reef-associated species, particularly in regions with LMMAs such as Fiji. Commercial tuna longlines are frequently deployed at the surface overnight, increasing the likelihood silvertips will encounter longline gear. The species’ apparent inquisitive disposition (compared with other shark species) make it particularly susceptible to fishing mortality [18, 19].

The fine-scale movements of the silvertip could not be resolved by the tag’s light-based geolocations because the net displacement (<18 km) is considerably less than the best error rate of the X-Tag’s light-based geolocations. The tag detached from the shark due to attachment failure, and subsequently, the tag floated on the surface for 28 h before the first Argos location was estimated. Given that the tag drifted approximately 14 km during the first day of transmission, the tag may have drifted a comparable distance prior to transmission. Consequently, the first Argos location was not likely representative of the shark’s position. It was not expected that an animal this size would travel off the shelf to waters nearly 2,000 m deep given its size and presumed reef association. Site residency is common to many reef-associated shark species, especially in juveniles [14, 26, 31]. However, the deep dives recorded in situ support the use of deeper waters.

Residency to specific locales has been observed in silvertips [14]. Individuals have been repeatedly identified at shark provisioning sites even if not the targeted species of dive operators (B. Paige, pers comm.). Shark provisioning sites are increasing in Fiji as a result of a growing ecotourism sector. Provisioning sharks and the subsequent effect on their behavior is widely debated but must be considered when discussing a species’ movements. Our study area had one commercial dive operator which did not offer a shark feeding experience. Since there are no routine provisioning sites near the study site, the observed behaviors are considered connatural.

The habitat-faithful nature of silvertip shark, confined geographical populations, and life history suggest it is highly vulnerable to overexploitation [14]. Contemporary reports of localized extirpation throughout parts of its range highlight the need for further study of its geographically and genetically distinct populations. Though the data presented here describe a single individual, this pilot study can serve as a model for future silvertip tracking studies. Given the limited 12-day dataset, it is not appropriate to draw conclusions about this species. In retrospect, attaching the PSAT with a first dorsal bridal technique instead of an umbrella dart could have increased tag retention, as has been verified on reef-associated animals in the Caribbean (E. J. Brooks, pers comm.). However, the absence of fundamental data available for this species, especially in this region, gives the results merit. We identified diel differences, previously unreported, in the tracked individual’s vertical use of the water column and temperature use. The deeper depth distribution and increased vertical habitat observed during the day may suggest foraging behavior, but additional studies addressing diet are needed to identify prey composition. Of additional interest, the increased use of the upper water column at night could indicate predator avoidance or particular temperature selection. The silvertip shark’s apparent mix of reef-associated and pelagic behaviors, coupled with anecdotal reports that commercial longliners are increasingly deploying longlines in close proximity to reef systems during the night when local Fijians are less likely to observe or intervene, make silvertips especially vulnerable. Given high levels of intentional or unintentional landings from tuna longlines, specifically, within the Fijian archipelago, this species warrants additional movement studies and stock assessment surveys throughout its range.