- Open Access
Tracking sharks without teeth: a non-invasive rigid tag attachment for large predatory sharks
© Chapple et al. 2015
- Received: 1 January 2015
- Accepted: 9 May 2015
- Published: 1 June 2015
Many marine species are difficult to study because components of their lifecycles occur solely or partially outside of the observable realm of researchers. Advances in biologging tags have begun to give us glimpses into these unobservable states. However, many of these tags require rigid attachment to animals, which normally requires catching and restraining the animals. These methods become prohibitive with large, dangerous, or rare species, such as large predatory sharks, and can have significant consequences for individual survival and behavior. Therefore, there is a need for methods and hardware to non-invasively and rigidly attach biologging tags to large predatory sharks that presents limited effects on the animals and researchers. Here we test a clamp tag and methods to non-invasively and rigidly attach biologging tags to white sharks (Carcharodon carcharias) in Gansbaai, South Africa.
We developed stainless steel dorsal fin attachment clamps with abrasive pads for deployments of biologging devices on large marine organisms. We deployed 35 tags on 34 white sharks, which after modification, remained rigidly attached to the animals up to 93 h, even through significant dynamic motions, and released from the animals with little or no effect on the animals.
These tags and attachments present a technique and hardware to equip large predatory sharks with biologging tags without the need to catch or restrain them, and with some additional modification, these tags may remain on the animals for long periods with potentially reduced risk for both researcher and animal.
- White shark
- Dorsal fin
Initial studies of marine animals were dependent on direct observation of subject species, which required access to the animals in the wild or captive environments. However, the lifecycles of many marine species occur solely or partially outside of the observable realm of researchers, animals undertake movements or behaviors that cannot be studied in captive systems, or they cannot be appropriately maintained in captive facilities. The advent of animal-borne tags has provided an avenue to study some of these previously unobservable states. Initial acoustic and satellite tags provided information about the presence/absence, horizontal movements, vertical distribution, and temperature preferences of study animals [1, 2]. Advances in miniaturization of biologging tags (e.g., with accelerometers, magnetometers, heart-rate sensors, cameras, etc.) support increasingly complex studies of animals’ movements, behaviors, physiology, and/or their environment (see [3, 4]).
A combination of recent advances in biologging technologies has the potential to record previously unobservable states in the most secretive and difficult to study species. Especially large sharks, where capture is either not feasible or dangerous to animal or researcher, require methodological solutions since successful use of many biologging tags requires a rigid or predictable attachment on the animal. Traditional external shark tags (acoustic and pop-off satellite) are typically attached to animals via a flexible tether and a subcutaneous dart, which allows the tags to “wobble” as the animal swims. This action of the tags masks the changes in animal movement making them indistinguishable from tag movement. This wobble also presents significant challenges for frame stability and consistent focus on the area of interest when cameras are included. As a result, rigid mounts have typically required capture (i.e., with hook and line) and restraint of the animal either in the water or onboard a vessel , which can have significant physiological consequences for the animals [6, 7]. Additionally, though the tags often aim to continuously record the natural behaviors of the animal, the animals’ behaviors can be significantly influenced by the stress of capture/restraint [8, 9].
Gleiss et al.  introduced a clamp-tagging method on whale sharks (Rhincodon typus) that rigidly applied biologging tags via a specially designed tagging pole. Though this method works well for some large animals, characteristics of their methods preclude the use of these techniques with large predatory sharks. First, Gleiss et al.  swam with the whale sharks and applied the biologging tags underwater directly to the shark’s fin. As white sharks (Carcharodon carcharias) are the largest predatory fish in the oceans, free-swimming with them to deploy tags presents a significant risk to researchers. Secondly, Gleiss et al.  used clamps with 1.5-cm barbs to provide the anchoring of the units to the second dorsal fins. Though Gleiss et al.  found little effect from the tagging on the second dorsal fin of whale sharks, for white sharks, these biologging tags, which generally range in size from 100 to 500 g, must be placed on the first dorsal fin. These fins are biologically critical for stability while fast swimming  and are used scientifically as means to uniquely identify individuals across decades  and estimate abundance [13, 14]. Additionally, some communities are dependent on white sharks for ecotourism, so there are sensitivities to the risk (or perceived risk) of damage to dorsal fins from attaching data loggers . Therefore, attaching tags to the dorsal fin  could have significant biological and economic consequences that must be limited.
Therefore, it is advantageous to develop a method to attach biologging tags to large predatory sharks without catching or restraining the animals and with limited negative effects. To address this, we designed a modified rigid non-invasive fin clamp and attachment technique, based on Gleiss et al. , to deploy biologging tags on free-swimming white sharks. We attached these clamps, coupled with biologgers, at seasonal aggregation sites in Gansbaai, South Africa. This is the first time that this combination of sensors and attachment has been used on large white sharks. These methods do not require catching or restraining the animals, presenting an alternative method to rigidly attach biologging tags on large predatory marine animals while they free-swim with little risk to researchers, target species, and their recorded behaviors.
We conducted baiting and tagging efforts on a total of 12 days (6 days in August 2013 and 6 days May 2014) with a total effort of >88 h (45 h in August 2013 and 43 h in May 2014). During this ship time, we conducted 35 CATS tag deployment events (18 CATS Cams and 17 CATS Diaries) on 34 sharks (18 F:5 M). Following tagging, sharks typically continued to swim without an apparent change in behavior from the tagging. The estimated total length (TL) ranged from 2.1 to 4.3 m with an average size of 3.2 m. Average deployment duration (except for those physically removed) was 22 h with the shortest deployment of 1 h (first deployment) and the longest deployment was 93 h. All but two of the tags were retrieved as intended. The two tags not retrieved were observed on the animals but were not detected by radio signal during or after the expected deployment period. The failure of these two tags may have been a result of very high-frequency (VHF) pinger failure, tags releasing outside of the reception range or the flotation and/or VHFs being compromised by being bitten once released.
To the best of our knowledge, all tags were released from the clamps at the predicted times for the galvanic time releases (GTRs) (normally 12–72 h) leaving only the clamps on the fins. We were able to corroborate the duration of attachment with the data recorded on the tags by the loggers. The corrosion rates of the magnesium sleeves (and GTRs) are dependent on water temperature and animal speed; therefore, their release times varied depending upon the movements of the sharks through different water temperatures. In general, based on continued opportunistic observation of previously tagged animals by the authors and commercial cage-boat operators, we found that the clamps fell off between 7 and 10 days post-deployment.
Our results present a new attachment method for placing biologging tags that require rigidity for data collection on large predatory sharks. This method does not require animals to be caught or restrained, and researchers can remain in a boat (though free-swimming attachment could also be possible with less dangerous animals). After adjustment of the clamp strength, we successfully demonstrate that non-invasive clamps can remain rigidly fixed on the animals, even during significant dynamic motion (Fig. 1). The majority of tags and clamps remained on the sharks for the desired period and released from the animals with only discoloration markings or, in the rare case of the two units that remained on for 5 weeks, superficial wounds on the first dorsal fin. Observations of sharks and data indicate that the animals display typical swimming behavior post-tagging.
Clamp tags remained attached up to 93 h allowing high-quality recordings and data collection from tags that required stability (Fig. 1). Two clamps stayed on longer than anticipated (~5 weeks); however, the units were easily knocked off the animals revealing superficial abrasion wounds. White sharks have been observed to heal from wounds quickly , and in March 2015, one of these sharks was resighted with the fin fully healed and only dark spots indicating evidence of the injury (Additional file 1: Figure S1). However, the fact that the clamps did not fall off as expected was initially troubling. After reviewing the footage of the clamps on the animals, it became apparent that the remaining nub from where the clamp arm was cut during production provided enough friction on large animals (i.e., thicker fins) to hold the clamp on. We later remedied this by cutting the clamps closer to the spring and on both sides. Though unreleased clamps were a rare event, these modifications will ensure that the clamps come fully off the animals in the future.
The clamp system performed favorably in comparison to the early versions containing short spikes trialed on whale sharks by Gleiss et al. . Despite the lack of any piercing of tissue, clamps remained attached for desired durations and were easily deployed from a boat and in principal would perform equally well in species that can be attracted and tagged underwater. In comparison to the fin-clamping system developed by the National Geographic Imaging Unit (CritterCam), which relies on a large gas-pressure powered system capable of attaching tags to sharks from hours to days, our clamping system is small and light-weight (Chapple, Gleiss & Liebsch, pers. obs.), requires little equipment for deployment, and is easily constructed in most basic metal workshops. However, direct performance comparisons of the attachments have not been performed. The obvious drawback of these types of system is the need to study species bold enough to approach boats or researchers. Additionally, longer deployments are necessary to assess the use of these clamp systems with long-term tags.
We have further refined a new tool to equip sharks with the latest sensors available to animal biologists and as a result have opened the doors to studies on the ecology and physiology of some of the most difficult to study species. Our system is easy to implement in the field, for sharks that come within 1 m of the researcher and can be constructed without the need of a high-tech workshop. Importantly, this system does not require catching the animal on hook and line, effectively reducing the ill effects on the individual and any post-tagging trauma.
Fieldwork was conducted in the waters around Dyer Island, near Gansbaai, South Africa. Initial work, focused mainly at inshore aggregations sites, was conducted in August 2013. We conducted a second research expedition in May 2014 focused mainly in waters near Dyer Island and Geyser Rock.
The CATS tags were attached to a specially constructed stainless steel spring clamp via a docking pin and a corrodible GTR (Neptune Marine Products, USA; Fig. 3). Whereas Gleiss et al.  used 1.5-cm barbs to lock the clamp onto the fin, we used abrasive friction pads (~4 × 4 cm), which conformed to the dorsal fin and allowed the mount to stay on the fin at increased speeds without puncturing the skin. Because we only used friction pads and not barbs to attach to the fin, we increased the compression strength of the clamps. We increased the clamping strength to 118 N (~18 kPa or 1.8 N/cm2) and 196 N (~30 kPa or 3.1 N/cm2) to determine the appropriate amount of pressure.
A key component to non-invasive nature of the tag is the ability to passively release the unit from the animal after a given amount of time. To facilitate the predictable shedding of the clamp, one clamp arm was cut near the spring coil and was reconnected using a magnesium sleeve. Once in saltwater, after a relatively predictable period of time, the magnesium sleeve dissolved separating clamp from the arm, acting as a passive mechanism by which the complete spring system would release from the fin.
After a pre-set time, determined to increase probability of retrieving the tags, the GTR link corroded, and the tag unit floated free of the clamp and was found with a VHF receiver. This left only the clamp remaining on the animal until the magnesium sleeve corroded and released the entire clamp, leaving no hardware on the animal. This method aimed to ensure predictable passive release from the animal of the tag via the GTR and the clamp via the magnesium sleeve.
The authors would first like to thank N Liebsch and P Kraft at Customized Animal Tracking Solutions (CATS). We also thank W Chivell and D Chivell with Marine Dynamics and the Dyer Island Conservation Trust for logistical and vessel support for this project. We would also like to thank H Otto and K Baker for the use of their photos, A Boyd, J Cornelius, S Jorgensen, M Wcisel, A Towner, AB Casagrande IV, N Gormley, S Visagie, A Lynch, J Golbol, the Saxon Lodge, P du Toit, N Stelutto, E Gennari, and all the volunteers and staff at Marine Dynamics.
Funding was provided by Stanford University TAG A Giant fund and the National Geographic Society Expedition Councils Grant.
This research was conducted under DEA permit RES 2013/81 and RES2014/34.
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