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ANIMAL TELEMETRY (TAGGING) – A CRITICAL CONSERVATION TOOL

 

INTRO TO TELEMETRY

TAGGING AND TRACKING MOBULIDS

FREQUENTYLY ASKED QUESTIONS

TYPES OF TAGS

LEARN MORE ABOUT TAGGING

TAGGING IN SCIENTIFIC LITERATURE

Reef Manta Ray, Manta alfredi, CritterCam, Kottefaru Beyru, Raa Atoll, Maldives © Guy Stevens, Manta Trust 2016 (3).jpg
 

INTRODUCTION TO TELEMETRY

Animal telemetry is the science of gathering information on the movement and behaviour of organisms using animal-borne sensors, or tags, and is a critical tool for researchers and conservationists. Telemetry studies have been used on a vast range of species from tiny insects to mountain lions, to albatrosses, great white sharks, and many more in between. Although ocean based tracking brings with it new challenges, the methods have still been used on an extensive range of species, as seen in the figure below.

Satellite telemetry (tagging) has been used on dozens of marine species. This map highlights the diversity of species tagged in just one study; the Tagging of Pelagic Predators (TOPP) programme. Figure from Block et al., 2011.

Satellite telemetry (tagging) has been used on dozens of marine species. This map highlights the diversity of species tagged in just one study; the Tagging of Pelagic Predators (TOPP) programme. Figure from Block et al., 2011.

Telemetry studies have provided vital insight into the movement and behavioural ecology of manta and devil rays. This knowledge has been used to design effective conservation strategies for these vulnerable animals where these studies have taken place. On this webpage we explore some of the important research questions that these tools can help to answer, look at the types of tags and tracking methods widely used, examine how these activities affect mobulid rays, provide details of some fascinating tagging studies, and detail the conservation outcomes these studies have helped to achieve.

 
 

TAGGING AND TRACKING MOBULIDS

Oceanic manta ray (Mobula birostris) with a suction cup Crittercam in Mexico.

Oceanic manta ray (Mobula birostris) with a suction cup Crittercam in Mexico.

Manta and devil rays often undertake seasonal migrations, travelling tens, hundreds, and sometimes thousands of kilometres. This means that their habitat can encompass large areas, sometimes crossing national boundaries, where conservation management is often more challenging. Therefore, to effectively protect these animals, we must first understand what habitats they are using, when they are there, and what they are doing within it.

Photo identification (photo-ID) is one of the primary research methods favoured by Manta Trust scientists around the world and, over the last 15 years, it has provided great insight into the movements, size, and demographics of manta ray populations globally. It is a cheap and non-invasive data-collection technique that both trained researchers and members of the public can use. However, it alone cannot tell us everything that we need to know to adequately protect manta rays and their relatives around the world. Learn more about photo-ID and how you can contribute to our citizen science programme, IDtheManta.

A satellite tag deployed on an oceanic manta ray (Mobula birostris) in Mexico.

A satellite tag deployed on an oceanic manta ray (Mobula birostris) in Mexico.

One of the limitations of photo-ID research is that images can only be collected in locations (and at depths) that scuba divers and snorkellers can access; primarily restricting data collection to shallow reef systems. This means we have learnt a lot more about the spatial and behavioural ecology of the reef manta ray than their larger cousins, which live a more oceanic lifestyle. However, as this recent tagging study led by Initiative Manta En Nouvelle-Caledonie demonstrates, even with all the photo-ID data we have collected, there is still much we can learn about reef manta rays using other research methods. Photo-ID is further limited because most of the data is primarily collected from only a few aggregation sites where researchers know the rays regularly frequent to feed or clean, often for just a few minutes or hours at a time. Therefore, once the rays leave these sites, we have no idea where they are going, or what they are doing; knowledge which is critical if we are to effectively protect these species.

The Manta Trust utilises a wide range of research methods to gather knowledge on mobulid rays globally, which we then use to make informed management recommendations to governments and other stakeholders. These methods often include tagging studies. However, as tagging is an invasive technique, we only use it when it is required to fill vital knowledge gaps.

 
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 FREQUENTLY ASKED QUESTIONS

Click on the questions below to see our answers.

 

+ Does tagging harm the manta?

Due to the nature of the tag being an inserted dart, tagging is considered invasive. However, if done correctly, by a trained expert, tagging does not cause the manta ray any serious or long-term harm. A tag is inserted in the fold between a manta’s pectoral fin and its body cavity, where it will not damage any internal organs, and it will not get shaken about by the manta’s pectoral fins as they swim.

Watch this video of oceanic manta tagging from Mexico.

+ Does tagging hurt the manta?

It is impossible for us to really know what a manta feels when it is tagged, but we imagine it feels something like a bee sting, or an ear piercing; a short, sharp pain that passes quickly. Every manta reacts different when a tag is first attached, some barely flinch, whilst others dart off quickly. Reef manta rays tend to react more to tagging than oceanic manta rays, which often appear unfazed by the experience.

Watch this video of oceanic manta tagging from Mexico.

+ Does tagging scare manta rays away?

All our tagging studies data shows that manta rays are not deterred from returning to the location where they were tagged (see 'Learn More About Tagging' section below). In fact, researchers often see tagged manta rays return on the same day, reapproaching the same diver who tagged them minutes or hours after being tagged. Furthermore, long-term visitation patterns to the site where the individual was tagged do not change because of the tagging.

Watch this video of oceanic manta tagging from Mexico.

+ Can you track manta rays in real time with tags?

Currently, the only way to do this is from a boat immediately after tagging a manta with an active ‘pinger’ acoustic tag, using a directional hydrophone as described above in the ‘Types of Tags and Tracking’ section. This is a very labour-intensive tracking technique that can only be done for a short period of time. The technology does not exist to remotely track manta rays in real time. Read the section on 'Types of Tags and Trackers' below for more details on how they work.

+ How many manta rays do you need to tag?

This depends on the research question. However, most studies require at least half a dozen individuals to produce meaningful results, and ideally many more. As tagging equipment is very expensive, studies can often only afford 5-15 tags at a time.

+ Manta rays are protected in many countries, so why do they need to be tagged there?

There are several reasons why it is still critical to conduct tagging studies with manta rays in countries where they already have national protection. Some examples of these are:

  • To ensure that conservation measures in place are effective and sufficient. As Case Study Three (below) demonstrates, tagging data can help to direct management efforts to ensure that manta hunting does not continue under the radar. It is also important to assess whether other activities that are still permitted are unintentionally harming manta rays, and therefore need managing. For example, expanding tourism, coastal development or the incidental catch (bycatch) of manta rays by fisheries targeting other species.
  • To find out if manta rays are travelling into unprotected waters. We know that manta ray habitat can encompass large areas, sometimes crossing national boundaries. So, tagging manta rays within the safeguarded waters of one country can help us to find out if they are travelling into neighbouring waters where they may still be under threat from target fisheries. See Case Study 2 below for a specific example.
  • To provide information that can help to drive protective measures in other regions of the world. Gathering data on manta ray movement and behaviour in areas where they are well protected, can help us to learn more about these species at a baseline level (Case Studies 1 & 4 below).
  • To learn how anthropogenic threats unimpeded by protective legislation, such as rising sea temperatures or marine pollution, are impacting manta ray populations. Case Study Three (below) is also a great example of this.
 
 

Types of tags and trackers

Coded ‘Passive’ Acoustic Tags

A passive acoustic tag on the left and an acoustic receiver deployed on the reef on the right.

A passive acoustic tag on the left and an acoustic receiver deployed on the reef on the right.

These small tags emit a numerical ID signal (somewhat like Morse code) at regular intervals which can be picked up by special underwater “listening” receivers. Passive acoustic telemetry uses tags which signal on average once every 90 seconds. These signals are recorded by acoustic receivers placed in the marine environment. Each time a tagged manta passes within ~200 m of an acoustic receiver, the receiver will record the tags unique numerical ID. It is only possible to get data if an animal passes close to a receiver, so it is necessary to have lots of receivers positioned throughout the animal’s habitat if a clear understanding of the animal’s wider movements are to be recorded. Acoustic tags are therefore a great tool for studying fine-scale manta movements, studying social interactions, and the importance of specific sites over time. However, passive acoustic tracking does not provide any data on the tagged animal’s diving behaviour, the temperature of the water it is swimming through, or where the animal goes once it leaves the detection range of the receiver array. These tags have a long battery life, often lasting for many years. However, externally attached tags usually fall off the animals before the tag battery dies.

Active ‘Pinger’ Acoustic Tags

A researcher demonstrating how to deploy an acoustic tag on a manta ray.

A researcher demonstrating how to deploy an acoustic tag on a manta ray.

Active acoustic tagging uses ‘pinger’ tags which send out their “Morse code” continuously. Like the coded tags, these ID signals can be detected within a few hundred metres. However, instead of deploying passive listening stations, the pinger tags is tracked continuously from the surface using a directional hydrophone, usually attached to a small boat. This allows researchers to actively follow a tagged animal, like a manta ray. The pinger tag also sends its depth each time it pings, allowing the trackers to not only record the movement of the animal, but also its depth. The downside to this method is that it is very time and labour-intensive, and if the tracked animal is lost (i.e., it moves outside of the detection area), the track will end unless the animals can be found again before tag battery dies (which is usually within a few weeks). This method has been used very effectively to study manta rays within lagoons, but generally this method works better with slower moving animals with smaller home ranges.

Satellite Tags

Satellite tags have an internal computer that can be programmed to continuously record lots of environmental data, such as temperature, depth, light levels, and/or position. However, the more data you record, more often, the quicker tag’s memory space and battery is depleted. Furthermore, global positioning systems (GPS) do not work underwater. Therefore, a manta fitted with a satellite tag does NOT allow researchers to track its movements in real time because manta rays spend most of their time at depths below the surface. Instead, many satellite tags are designed to archive their data. These archival satellite tags store the information collected as the animal swims through its environment and then transmit this information at the end of the programmed deployment time (usually after a few months to a year), when the tag releases from the animals and floats to the surface.  Once at the surface, the tag attempt to transmit all its archived data in batches to satellites orbiting overhead (the ARGOS network) before its battery is drained.  This usually means researchers receive only partial datasets of the information collected by tags during attachment (unless a tag can be located - e.g., it washes onto a beach where is can be recovered), which they then piece together to build a picture of the animal’s movement and habitat use during the deployment period.

MiniPAT (Pop-up archival tag) with anchor, short tether and antenna.

MiniPAT (Pop-up archival tag) with anchor, short tether and antenna.

In these archival tags, positional information of the track is often inferred through geolocation (i.e., dusk/dawn light curves) because the only GPS location points are the tag deployment location and the location where the tag floated to the surface at the end of the track. However, geolocation comes with a degree of uncertainty because there can often be errors of 10s of kilometres in the estimated positions given. Nonetheless, geolocation provide critical information on general movement trends, especially if the tagged animals travel large geographical distances (i.e., hundreds or thousands of kilometres) as shown in figure above from the TOPP programme.

More recently, technological advances have allowed the integration of archival tags with SPOT transmitting tags. SPOT tags allow fast accurate GPS locations to be detected, even if a tag is at the surface for only a few seconds. SPOT tags are traditionally most frequently used on species like sea turtles, which regularly come to the surface to breathe. These GPS locations can be transmitted to orbiting satellite, relaying this information to the researcher. These advanced satellite tags are often attached to manta rays and other large megafauna using a tether system which tow the tag slightly above the animal so that when it is close to the surface the tag can send its position (and some other data also). A towed SPLASH satellite tag therefore has all the benefits of the traditional archival tag, and the SPOT tag combined.

To reiterate, satellite tags can only transmit data when their antenna breaks the surface of the water, so data is not received consistently or immediately. And even when location data is transmitted to the ARGOS satellites, there is usually a lag of 24 hours before this information is replayed to the researcher. Researchers therefore cannot use these tags to remotely track manta rays in real time. This is a myth often perpetuated through fictional TV shows.

Satellite tags provide much more data than acoustic tags, but they are also a lot more expensive. To learn more about the different types of satellite tag, watch Dr. Mark Erdmann’s webinar ‘The Truth About Tagging’.

Animal-Borne Video Cameras

Whilst acoustic and satellite tags deliver data on the movement ecology of manta rays, and the environmental conditions the tagged animals experience, they do not tell us what the animals was doing. I.e., was the manta ray feeding when it dived to 500 metres, or was it migrating, or thermoregulating, etc. Animal-borne video cameras are a new technology that is being used to provide, for the first time, direct observations of manta ray behaviour at depth. With a manta’s eye view, researchers can observe social interactions, feeding behaviour, inter-species interactions, and even identify prey species. In this recent collaboration between the Manta Trust, the National Geographic Society, and the Scripps Institution of Oceanography, ‘Crittercams’ were attached to manta rays to capture feeding behaviour at depth. The team also took the opportunity to trial various applications methods. The minimally invasive method of using an active suction attachment proved most successful when peanut butter was used as a sealant on oceanic manta rays. However, in reef manta rays, a modified mount system was required.

a) The Crittercam units used on manta rays are attached using a suction cup which only lasts a few hours. b) the Cittercam camera unit is attached to the manta ray to film from the manta’s perspective.

a) The Crittercam units used on manta rays are attached using a suction cup which only lasts a few hours. b) the Cittercam camera unit is attached to the manta ray to film from the manta’s perspective.

Tag Attachment

Due to the tough and rough texture of manta rays’ skin (which is comprised of dermal denticles), long term suction tags are not viable. Acoustic and satellite tags are therefore usually attached externally to manta rays using a metal dart and a short tether. The tethers corrode in saltwater over time releasing the tag. Depending on the tag type deployed, the corrosion time is adjusted accordingly (i.e., the use of steel vs. stainless steel or titanium darts, or plastic vs. steel line). In many species, passive acoustic tags are now routinely inserted inside the animal, much like your pet has a microchip inserted inside it in case it gets lost. These internal tags can give tracks of up to a decade whereas external tags usually last on average one year.

 
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Learn more about Tagging

 

Webinar with Dr. Mark Erdmann of Conservation International about tagging and its uses as a research tool.

Clip of researcher tagging oceanic manta rays (Mobula birostris) in Mexico.

 
 

Studies in the Maldives

In the Maldives between 2005 and 2019, 76 individuals (1.5% of the known population) were part of research studies involving either acoustic tags (n= 16 events), a biopsy (n=50 events), a crittercam deployment (n=10 events) or a combination of a biopsy and crittercam deployment on the same day (n=2). Two individuals were included in multiple studies on separate days; therefore, sightings data for these individuals was analysed before and after each of their research days (total of 76 individuals and 78 events).

Ninety-six per cent (n=73) of individuals researched (n=76) have been resighted since being included as part of a research group. In comparison, 76% (n=3,748) of the manta rays photographed in the Maldives (n=4,941) have been recorded more than once. See Figure 1 below for further information on the duration of time between re-sightings of individuals after research events.

 
Figure 1: Percentage of reef manta rays re-sighted in the Maldives, post-involvement in different research studies by duration of time between re-sightings (n= 50 biopsies, 16 acoustic tags, 10 crittercam deployments, 2 biopsies and crittercam deplo…

Figure 1: Percentage of reef manta rays re-sighted in the Maldives, post-involvement in different research studies by duration of time between re-sightings (n= 50 biopsies, 16 acoustic tags, 10 crittercam deployments, 2 biopsies and crittercam deployments, 4941 initial photo-ID captures). Ninety-six per cent of research events (n=75) resulted in a resighting post biopsy, tagging or crittercam deployment. Seventy-six percent (n=3748) of all individuals photographed (n=4941) in the Maldives have been re-sighted at least once.

 

Although there is variation between individuals, the vast majority have been resighted in similar frequency after (green dots in Figure 2) a research event as before (blue dots in Figure 2), clearly indicating no long term impact of such research techniques on sightings.

Figure 2: Sightings of individual reef manta rays in the Maldives pre- and post- inclusion in invasive research activities (biopsy, acoustic tag, crittercam, or crittercam and biopsy). Seventy-six individuals (labelled on the Y-axis) were targeted d…

Figure 2: Sightings of individual reef manta rays in the Maldives pre- and post- inclusion in invasive research activities (biopsy, acoustic tag, crittercam, or crittercam and biopsy). Seventy-six individuals (labelled on the Y-axis) were targeted during seventy-eight research events; the day of which has been designated by a pink dot on the timeline. *Note: the end date signifies the end of the 2019 study year. The year of research determined the possible time for sightings before and after the research event.

 
 

Laamu Atoll biopsies

A total of 10 biopsies were collected from reef manta rays (Mobula alfredi) at Hithadhoo Corner in Laamu Atoll, Maldives between the 10th of August 2016 and the 11th of September 2016. The average residency index (RI) for each manta biopsied was calculated before (0.0294, SD= 0.330) and after (0.0260, SD=0.330) the period where biopsies were collected. A paired t-test showed no significant difference in the residency of individuals included in the study before and after the biopsies [t(9) = 0.216, p = 0.8342]. The mean change in RI was -0.0025 (SD=0.04) for biopsied individuals, whereas the mean change for non-biopsied individuals was -0.0035 (SD=0.02). A Welch two samples t-test showed there was no statistically significant change [t(9.70) = -0.0859, p = 0.933] in residency between the biopsied and non-biopsied manta rays, pre-and post-sampling. Box plots were used to visually compare the differences between biopsied and non-biopsied individuals (Fig. 3). These residency indices were calculated for Hithadhoo Corner sightings between 1st July 2014 and 31st December 2018.

 
 
Table 1: Residency Index (RI) and change in RI of reef manta rays (Mobula alfredi) at Hithadhoo Corner, Laamu Atoll, Maldives before and after biopsy sampling. Individuals are grouped by whether a biopsy was conducted on the individual between the 1…

Table 1: Residency Index (RI) and change in RI of reef manta rays (Mobula alfredi) at Hithadhoo Corner, Laamu Atoll, Maldives before and after biopsy sampling. Individuals are grouped by whether a biopsy was conducted on the individual between the 10th of August 2016 and the 11th of September 2016.

Figure 3: A box plot shows the changes in the residency index for pre-and post-sampling periods of biopsied and non-biopsied populations of reef manta rays (Mobula alfredi) at Hithadhoo Corner, Laamu Atoll, Maldives. Plotted points represent individ…

Figure 3: A box plot shows the changes in the residency index for pre-and post-sampling periods of biopsied and non-biopsied populations of reef manta rays (Mobula alfredi) at Hithadhoo Corner, Laamu Atoll, Maldives. Plotted points represent individual manta rays identified at Hithadhoo Corner as of August 2016. A t-test revealed no statistically significant difference in the residency index change of biopsied and non-biopsied manta rays, t(9.70) = -0.0859, p = 0.933.

 
 

Hanifaru Bay acoustic tagging

Between the 12th of September 2009 and the 29th of September 2009, a total of eight reef manta rays (Mobula alfredi) were outfitted with acoustic tags in Hanifaru Bay, Baa Atoll, Maldives. The average residency index (RI) for each manta outfitted with an acoustic tag was calculated before (0.002, SD= 0.002) and after (0.005, SD=0.004) the period where tags were deployed. A paired two samples t-test showed no significant difference in residency between before and after the event [t(7) = -1.637, p = 0.1456]. The mean change in RI was 0.003 (SD=0.004) for tagged individuals, whereas the mean change for non-tagged individuals was 0.001 (SD=0.02). A Welch two samples t-test showed there was no statistically significant change [t(7.06) = -0.226, p = 0.828] in residency between the tagged and non-tagged manta rays, pre-and post-tagging. Box plots were used to visually compare the differences between tagged and non-tagged individuals (Fig. 4). Residency indices were calculated for all individuals identified in Hanifaru Bay prior to the tagging period through November 2011.

 
Table 2: Residency Index (RI) and change in RI of reef manta rays (Mobula alfredi) in Hanifaru Bay, Baa Atoll, Maldives pre-and-post-tagging.  Individuals are grouped by whether they were outfitted with a tag between the 12th of September 2009 …

Table 2: Residency Index (RI) and change in RI of reef manta rays (Mobula alfredi) in Hanifaru Bay, Baa Atoll, Maldives pre-and-post-tagging.  Individuals are grouped by whether they were outfitted with a tag between the 12th of September 2009 and the 29th of September 2009.

Figure 4: A box plot shows the changes in the residency index for tagged and non-tagged reef manta rays (Mobula alfredi) in Hanifaru Bay, Baa Atoll, Maldives after a tagging period in 2009. Plotted points represent individual manta rays identified i…

Figure 4: A box plot shows the changes in the residency index for tagged and non-tagged reef manta rays (Mobula alfredi) in Hanifaru Bay, Baa Atoll, Maldives after a tagging period in 2009. Plotted points represent individual manta rays identified in Hanifaru Bay as of the start of the tagging period in September 2009. A t-test revealed no statistically significant difference in the residency index change of tagged and non-tagged manta ray (7.06) = -0.226, p = 0.828.

 
 
Oceanic Manta Ray, Manta birostris, Southern Spur, Fuvahmulah Atoll, Maldives © Guy Stevens Manta Trust 2015 (14).jpg
 

TAGGING IN THE SCIENTIFIC LITERATURE

Interactive map of published scientific papers on manta and devil rays which utilised acoustic or satellite tracking (Click on the points to access the associated paper).

Within the map are links to papers published on mobulid tagging studies to date, with a few specific examples that demonstrate how well executed tagging research can have a positive impact for manta rays outlined below.

Case Study 1

A recent study in the Seychelles on the reef manta ray population using satellite telemetry identified high levels of site fidelity around D’Arros. The results of this tagging work directly helped inform the creation of the D'Arros Marine Protected Area. The tagging helped to show that the mantas spent a lot of their time around the shallow reef systems, which needed greater protections.

Case Study 2

Spatial ecology and conservation of Manta birostris in the Indo-Pacific: In the absence of ecological data, population declines in oceanic manta rays have been addressed primarily with international-scale management and conservation efforts. However, this recent study used satellite tagging in combination with genetic research to demonstrate that regional approaches to oceanic manta conservation could prove more effective. 

Case Study 3

Movement patterns and habitat use of juvenile reef manta rays in a nursery area of Raja Ampat’s Wayag Lagoon: In the six years prior to this project, conservation management of reef manta rays in Indonesia had shown considerable advances, but still little was known about new-born and juvenile manta rays in the region. This tagging study identified Wayag Lagoon in northwest Raja Ampat as a primary nursery and pupping ground for reef manta rays, highlighting the urgent need to limit potentially harmful boating activities inside the lagoon.

In 2014, Indonesia created the world’s largest manta sanctuary, but was only actively enforcing this protection in manta tourism areas. This satellite tagging study (and other unpublished studies in the region) showed conclusively that manta rays from tourism areas were moving through areas known to be manta hunting regions, which convinced the Indonesian government to pursue enforcement in these hunting regions too.

Case Study 4

Satellite tracking of reef manta rays in Sudan confirmed the importance of the Dungonab Bay and Mukkawar Island National Park as an important foraging habitat for this species. This additional weight for supporting the protection of the area is important when considering recent plans for a large-scale island development project including skyscrapers, international airport and extensive dredging activity.

 
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