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Electronic Tagging of Atlantic Bluefin Tuna (Thunnus thynnus, L.) Reveals Habitat Use and Behaviors in the Mediterranean Sea

  • Pablo Cermeño ,

    pcerme@gmail.com

    ‡ These authors contributed equally to this work.

    Affiliations Department of Biology, Stanford University, Hopkins Marine Station, Pacific Grove, California 93950, United States of America, WWF Mediterranean Programme, Barcelona 08002, Spain

  • Gemma Quílez-Badia ,

    ‡ These authors contributed equally to this work.

    Affiliation WWF Mediterranean Programme, Barcelona 08002, Spain

  • Andrés Ospina-Alvarez,

    Affiliations WWF Mediterranean Programme, Barcelona 08002, Spain, Center for Marine Conservation & Department of Ecology, Biological sciences Faculty, Pontificia Universidad Católica de Chile, Santiago de Chile 6513677, Chile

  • Susana Sainz-Trápaga,

    Affiliation WWF Mediterranean Programme, Barcelona 08002, Spain

  • Andre M. Boustany,

    Affiliations Department of Biology, Stanford University, Hopkins Marine Station, Pacific Grove, California 93950, United States of America, Nicholas School of the Environment, Duke University, Durham, North Carolina 27708, United States of America

  • Andy C. Seitz,

    Affiliations Tuna Research and Conservation Center, Monterey Bay Aquarium, Monterey, California 93940, United States of America, School of Fisheries and Ocean Sciences, University of Alaska Fairbanks, Fairbanks, Alaska 99775, United States of America

  • Sergi Tudela,

    Affiliation WWF Mediterranean Programme, Barcelona 08002, Spain

  • Barbara A. Block

    Affiliation Department of Biology, Stanford University, Hopkins Marine Station, Pacific Grove, California 93950, United States of America

Electronic Tagging of Atlantic Bluefin Tuna (Thunnus thynnus, L.) Reveals Habitat Use and Behaviors in the Mediterranean Sea

  • Pablo Cermeño, 
  • Gemma Quílez-Badia, 
  • Andrés Ospina-Alvarez, 
  • Susana Sainz-Trápaga, 
  • Andre M. Boustany, 
  • Andy C. Seitz, 
  • Sergi Tudela, 
  • Barbara A. Block
PLOS
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Abstract

We analyzed the movements of Atlantic tuna (Thunnus thynnus L.) in the Mediterranean Sea using data from 2 archival tags and 37 pop-up satellite archival tags (PAT). Bluefin tuna ranging in size from 12 to 248 kg were tagged on board recreational boats in the western Mediterranean and the Adriatic Sea between May and September during two different periods (2000 to 2001 and 2008 to 2012). Although tuna migrations between the Mediterranean Sea and the Atlantic Ocean have been well reported, our results indicate that part of the bluefin tuna population remains in the Mediterranean basin for much of the year, revealing a more complex population structure. In this study we demonstrate links between the western Mediterranean, the Adriatic and the Gulf of Sidra (Libya) using over 4336 recorded days of location and behavior data from tagged bluefin tuna with a maximum track length of 394 days. We described the oceanographic preferences and horizontal behaviors during the spawning season for 4 adult bluefin tuna. We also analyzed the time series data that reveals the vertical behavior of one pop-up satellite tag recovered, which was attached to a 43.9 kg tuna. This fish displayed a unique diving pattern within 16 days of the spawning season, suggesting a use of the thermocline as a thermoregulatory mechanism compatible with spawning. The results obtained hereby confirm that the Mediterranean is clearly an important habitat for this species, not only as spawning ground, but also as an overwintering foraging ground.

Introduction

Atlantic bluefin tuna are the largest members of the family Scombridae, with adult tuna reaching lengths of 3.31 m and a mass up to 725 kg [1]. The Atlantic bluefin tuna (Thunnus thynnus) has been a focus of marine fisheries research and a target of fishers since ancient times [2,3]. While sustainable fisheries for bluefin tuna have existed in the Mediterranean Sea for centuries, fishing mortality rates of this large predator escalated in recent decades [4]. This resulted in a sharp decline of the populations in the past four decades [5] and the risk of collapse of breeding populations both within the Gulf of Mexico and the Mediterranean Sea [6,7]. Improving fisheries models of Atlantic bluefin tuna population structure, migration patterns and habitat use is necessary, particularly on their spawning grounds where they are heavily exploited. Understanding habitat utilization is critical for the design of more effective management measures.

The Atlantic bluefin tuna have two known spawning grounds where reproductively active adults and larvae have been consistently found, i.e. the Gulf of Mexico/Caribbean/Straits of Florida (hereafter referred to as Gulf of Mexico) and the Mediterranean Sea [8]. Spawning may occur in other regions in the western Atlantic but to date, larval specimens are few and are recovered adjacent to known spawning regions [9]. The species has been managed by the International Commission for the Conservation of Atlantic Tuna (ICCAT) essentially as two populations, the western and the eastern populations with their respective breeding areas (Gulf of Mexico and the Mediterranean Sea), separated by the 45°W meridian [4]. Electronic tagging, otolith and genetic markers have shown that there is an extensive degree of mixing between distinct populations on the North Atlantic foraging grounds [1014]. Genetic studies suggest there are at least three distinct populations throughout its geographical range [1517] that most likely represents Gulf of Mexico, western Mediterranean and eastern Mediterranean populations.

Mature bluefin tuna of eastern origin undertake two types of migrations: movements into the Mediterranean Sea to spawn, which occurs during April and May [18], and a post-spawning foraging migration to the North Atlantic Ocean, around the end of July and August [1921]. Studies based on electronic archival and pop-up satellite archival tags in the past decade have been instrumental in identifying the details of bluefin tuna movement patterns, vertical distributions, temperature preferences and feeding habits. Most of these studies, however, have been carried out in the western Atlantic Ocean [1013,16, 2229] with over 2000 electronic tags having been deployed since the late 1990s. Interestingly, a significant number of Atlantic bluefin tuna archivally tagged in the western Atlantic, particularly in the coastal waters off North Carolina (eastern North America), displayed site directed fidelity to the western Mediterranean spawning grounds. This has been hypothesized to indicate eastern origin fish make trans-Atlantic migrations as juveniles but return to Mediterranean oceanic regions for spawning [13]. Only once has an Atlantic bluefin tuna tagged in the western Atlantic had a verified recapture to the east of the Adriatic Sea [12,13,26]. These fish presumably are spawned in the Mediterranean Sea, occupy the West Atlantic Ocean as juveniles presumably foraging on large schools of herring and menhaden, and then move back into the Mediterranean as they mature into spawners. Once spawning occurs electronic tagging has shown site directed fidelity to the western Mediterranean and western Atlantic [13].

Most of the Atlantic bluefin tuna tagging activity in the Mediterranean Sea has been based on conventional tags. These tags provide information on locations of release and recapture [3033], and to date make up 10% of the more than 57,000 conventional tags on Atlantic bluefin tuna released between 1940 and 2003 [33]. More recently, several studies involving electronic bluefin tuna tagging have been carried out in the Mediterranean Sea. De Metrio et al. [20,21,34] tagged mature bluefin tuna in fishing traps and tuna farms with single-point pop-up satellite tags (PST) providing limited results due to some early technical problems with the power output of the Argos satellite transmitters in these first generation tags. A study from juvenile Atlantic bluefin tuna tagged with archival tags in a tuna farm in Croatia [35] focused on vertical movements of the fish in the central Mediterranean Sea. A more recent study, using early models of the pop up satellite archival tags (PAT), has confirmed the rapid migration of post-spawning adults from the western Mediterranean to the Atlantic [36]. Other studies have also recently highlighted the importance of the Mediterranean Sea habitats not only for spawning but also as an ecological foraging area significant during overwintering periods [3742].

The spawning time for bluefin tuna occurs during June and July in the western and central Mediterranean Sea [18,30,4347]. Frontal structures and anticyclonic gyres are associated to the spawning strategy of the mature fish in the Catalan Sea [48] and in the Balearic Archipelago [49,50]. In the Balearic Sea, high numbers of bluefin tuna larvae have been collected in tows often associated with waters with an oceanographic signature of Atlantic origin (i.e. Sea Surface Salinity (SSS) up to 37.2) or with areas where Atlantic and Mediterranean waters mix (i.e. SSS between 37.2 and 38); with warm surface waters, mostly ranging from 23.5 to 25°C [49,51,52]; and with geostrophic velocities ranging from 0.0168 to 0.37 m/s [49]. Bluefin tuna showed a preference for deep waters surrounding the Balearic Islands [49], and for Chlorophyll-a (Chl-a) concentrations ranging from 0.08 to 0.15 mg/m3 in their Mediterranean spawning habitat [53]. A well-defined thermocline, preferably having a negative gradient of 3°C, has also been hypothesized to be important for spawning [54,55]. Consistent with this location is the arrival and recapture of western tagged bluefin tuna in the Mediterranean Sea in these regions [13].

In the western Atlantic, studies with electronic tags reveal bluefin tuna have a significant preference in the Gulf of Mexico during the spawning season for continental slope waters (i.e. 2800 to 3400 m), moderate sea surface temperatures (SST) around 24–25°C or 26–27°C, surface current speeds from 0.126 to 0.316 m/s, and low surface Chl-a concentrations (0.10 to 0.16 mg/m3) [56]. Aggregation behavior is also evident in the tracks (a linearity index of 0.56 SD ± 0.13), and unique oscillatory diving behaviors has been described during the putative breeding phases in the Gulf of Mexico [12,25,56] and more recently, in the Mediterranean [36].

Following the recent studies that suggest extended residential behaviors of Atlantic bluefin tuna in the Mediterranean, the main objective of the present study was to better characterize the pattern for those individuals who remain residential in the Mediterranean even after spawning. To date there has been very little description of the diving behaviors or oceanographic preferences of the tuna in the Mediterranean Sea during the spawning period. Data on the migratory behaviors and other ecological features of the eastern Atlantic bluefin tuna tagged in the western and central Mediterranean were thus collected to be able to increase our knowledge on the how bluefin tuna utilize these habitats and the ecology within the Mediterranean all year round.

Materials and Methods

Electronic Tagging

Atlantic bluefin tuna were tagged with electronic tags in expeditions that occurred between 2000 and 2012 in the western Mediterranean and the Adriatic Sea (Table 1). The first tagging expeditions were conducted in consecutive years of 2000 and 2001 in the Strait of Bonifacio (between Corsica and Sardinia), and the following expeditions in 5 consecutive tagging seasons from 2008 to 2012 in locations along the eastern Spanish coast—Roses and Llançà (NE Spain), Moraira (E Spain) and Algeciras (SE Spain)-, in the Balearic Islands—Port of Pollença (N Majorca, Spain)-, and in the Adriatic Sea—in San Benedetto del Tronto and Porto Barricata, E and NE Italy, respectively—(Fig. 1). Archival tags were only deployed in Roses (NE Spain). Tagging seasons started in the month of May (at the earliest) and ended by September. Tagging times depended on the accessibility of recreational fishers to bluefin tuna.

The research presented in this manuscript involved no endangered or protected species and no harm to the animals. The Stanford University Administrative Panel on Laboratory Animal Care research approved the protocol of the tagging operation in Corsica 2000 and 2001 (Protocol Number: 10786). No special permission was required for the other years in any of the locations as it was not required, however a special permit was granted by the Spanish Ministry "Agricultura, Alimentación y Medio Ambiente" for the 2011 tagging operations in Roses and Llançà (Table 1 and Fig. 1).

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Fig 1. Numbers represent the different tagging locations (1. Roses/Llançà, 2. Pollença, 3. Moraira, 4. Algeciras, 5. Strait of Bonifacio, 6. San Benedetto del Tronto, and 7. Porto Barricata).

Lines indicate the separation between the different Mediterranean basins based on FAO Fishing area criteria.

https://doi.org/10.1371/journal.pone.0116638.g001

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Table 1. Summary information on the deployments of electronic tags (>22 days on fish)—from 2000–2012 on western Mediterranean and Adriatic Sea bluefin tuna, analyzed in this study.

https://doi.org/10.1371/journal.pone.0116638.t001

Bluefin tuna were caught using recreational rod and reel fishing. Most bluefin tuna, under 30 kg, were captured by trolling lures, while adults were caught chunking the water with sardines to attract them. From 2000 to 2001 and from 2010 to 2012, adult bluefin tuna were brought on-board using a lip hook placed in the most rostral position of the lower jaw and pulled from the water to a wet vinyl mat. In some cases, a plastic landing net was used. In 2008 and 2009 adult bluefin tuna were tagged in the water using an aluminum tagging pole with only one insertion point and tag anchor. Two types of darts were used during the tagging expeditions, a titanium dart and an umbrella plastic dart.

Bluefin tuna that were brought on board the vessel and had a soft cloth soaked in a fish slime replacement (PolyAqua, Novalek) placed over their eyes while a seawater hose oxygenated their gills. A clip of the pectoral fin was kept for future genetic analyses, and curved fork length (CFL) was measured to the nearest 0.5 cm. CFL was transformed to fork length [57] and then to weight using the formula adopted by ICCAT for Mediterranean tuna (Arena unpublished cited in [58]). For those tuna tagged in the water a conservative estimation of the weight was made by the tagging team.

Electronic tagging was conducted with Pop-up Satellite Archival Transmitting tags (PAT MK10 and in the last three years MiniPAT tags built by Wildlife Computers, Redmond Washington). All satellite tags were placed on juveniles and adults in the base of the second dorsal fin. In addition, archival tags (MK9, Wildlife Computers), were surgically deployed in juvenile bluefin tunas considered too small for an external satellite tag.

A total of 92 electronic tags were deployed during the duration of this study: 62 pop-up satellite tags and 30 archival tags. From the 62 pop-up satellite tags deployed, 37 (25 tags from 33 total deployments of MK10 and 12 tags from 29 MiniPAT deployments) transmitted data and were at liberty for more than 22 days, which was the minimum time that we used to be included in this work (Table 1). Several dart types were used including titanium, umbrella and “Prince” nylon darts, All darts were attached to the tag using a similar tether constructed of 130 kg monofilament and shrink-wrap. When bluefin tuna were brought on board the deck, a second attachment loop was used to prevent excessive motion of the pop-up satellite tag (except in the early 2000 and 2001 expeditions where only 1 dart was used, see Table 1). This second anchor point was built with a titanium dart using 81.6 kg monofilament covered with a shrink wrap cover. Pop-up satellite archival tags were programmed to release from the tuna between 150 and 300 days post deployment.

Pop-up satellite tags recorded pressure, light and water temperature every 60 seconds interval. In 2000 and 2001, for Corsica pop-up satellite tags, temperature and depth data were grouped in 24-hour binned histograms. Temperature layers were set at 6, 10, 12, 14, 16, 18, 20, 22, 24, 26, 28 and 60°C and depth layers (calculated from pressure) were -1, 5, 10, 50, 100, 150, 200, 250, 300, 500, 700 and over 1000 m. The 2008–2012 pop-up satellite tags were grouped in 6-, 12- or 24-hour binned histograms (for 2012, 2008 to 2010, and 2011 tags, respectively), and temperature layers were set at 3, 6, 9, 12, 15, 18, 21, 24, 27, 30, 33 and 45°C. In 2008 and 2009 depth layers data were set at 0, 10, 20, 50, 100, 150, 200, 300, 400, 500, 600, 700, 800, and over 800 m. From 2010 depth layers were set at 0, 2, 10, 20, 50, 100, 150, 250, 300, 400, 500, 2000 and over 2000 m. Pop-up satellite tag number # 10P0648 was returned by a fisherman, getting access to the 5-second interval archival record.

The 30 MK9 archival tags (i.e. 21 in 2008, 2 in 2009, 2 in 2010 and 5 in 2011) were surgically implanted in the peritoneal cavity of juvenile tuna and programmed to record pressure, light, external temperature and internal temperature every 60 s. To implant the archival tags, a 3–4 cm incision with a sterile surgical blade was carefully made in the ventral musculature of the tuna following the surgery methodology described in Boustany et al. [59]. Tags were labeled in English, Spanish and Japanese to provide information on the reward for returning the tag. A conventional green external tag (Floy Tags) was also inserted close to the second dorsal fin to inform about the existence of an archival tag inside the tuna.

Bluefin tuna geolocations were estimated from light level and sea surface temperature data recorded by the tags. All tracks were processed by CLS using a tool based in state-space models (SSM). SSM’s constitute a robust statistical approach to refine satellite tracking data by accounting for observation errors and stochasticity in animal movement. The algorithm uses sea surface temperature and bottom topography data to better constrain the tracks. An ensemble Kalman filter is applied to solve for the trajectory, thus estimating the state vector and its covariance from a set of samples rather than the usual deterministic equations [6063]. The tags from the 2000–2001 expeditions were processed using a similar approach using custom algorithms as described in Teo et al. [64] and Block et al. [65].

FAO’s Major Fishing areas in the Mediterranean were adopted to separate the different basins [66] (Fig. 1).

Potential Spawning Behaviors Recorded by Electronic Tags

Geolocation, depth and temperature data were analyzed for four tuna during the spawning season. From the 39 analyzed tuna, only these four had their tags attached during the breeding season and potentially were exhibiting behaviors associated with spawning tuna. The maximum, minimum and mean for the estimated SST, and the maximum bathymetry from each calculated position were calculated using the data provided by CLS.

To determine the movements of the four tuna, we calculated the linearity index (LI) [67]. LI is the result of the linear distance between the endpoints divided by the path distance for each fish. The LI was calculated grouping the data every 5–6 days.

Time at Depth (TAD, i.e. daily average of the percentage of time spent at different depth bins set up) and Time at Temperature (TAT, i.e. daily average of the percentage of time spent at different temperature bins set up) during the spawning season were only calculated for the pop-up satellite archival tag # 10P0398, while # 10P0402 and # 10P0546 did not transmit this information.

The only pop-up satellite tag recovered from the four tuna showing potential spawning behavior was from a presumed mature tuna tagged in the Adriatic (# 10P0648). The record provided data in a time series every 5 seconds and was analyzed looking for unique behaviors potentially in association with spawning. Depth records < 0 m were assumed to be zero and 12 bins limits, focusing on the first depth layers, were defined by 0, 2, 5, 10, 15, 20, 30, 40, 50, 70, 100, 200 and > 200 m using Matlab (Mathwork, v 7.13.0.564). Following the methodology described in Jorgensen et al. [68], we calculated a distance matrix based on a hierarchical cluster tree using an un-weighted average distance (UPGMA) linkage algorithm (‘linkage’ function in Matlab) to differentiate dive behavior modes through the time at liberty based on the vertical distribution (‘pdist’ function). Distance calculations were obtained using the ‘City block’ measure, where bin values <0.1 were assigned as zero to avoid outliers or rare events. Then, the clusters were plotted along with a dendogram using the Matlab ‘dendogram’ function. Also IGOR Pro 6 (WaveMetrics) was used to show detailed behavior per day. Dive frequency was calculated identifying individual dives per day and grouped by season and cluster. A dive begins when the fish starts descending, and each dive includes a descent and an ascent. A dive ends when the fish starts to descent a second time, so every valley between two peaks is considered a dive.

Bluefin tuna fishing operations

To better understand habitat utilization of the bluefin tuna released in the Mediterranean Sea and for comparison with the electronic tagging data, the precise locations of the bluefin tuna fishing operations that had occurred inside the Mediterranean Sea from 1989 to 2012 were obtained (Fishspectrum company), for the period April to August. The dataset included purse seiners, longliners and bait boats from Algeria, Croatia, Egypt, France, Greece, Italy, Korea, Libya, Malta, Morocco, Spain, Tunisia and Turkey. In total, 6031 locations were established. Additionally, we added to these locations the spatial distribution of the Japanese longliners’ total bluefin tuna catches in Algerian waters from 2000 to 2007 [69].

Oceanographic Analyses

Bluefin tuna tracks were analyzed in combination with available satellite oceanographic data, which provided information on the main oceanographic features in the Mediterranean Sea areas. The movement paths of the Atlantic bluefin tuna were overlaid on ocean bathymetry to visualize the association of the movements with the continental shelf and slope using a Global Self-consistent, Hierarchical, High-resolution Shoreline (GSHHS) database version 2.2. (http://www.ngdc.noaa.gov/mgg/shorelines/data/gshhs) and ETOPO2 2-minute global bathymetry/topography high-resolution database (http://rda.ucar.edu/datasets/ds759.3/).

The moderate resolution imaging spectroradiometer MODIS AQUA L3 satellite data (incorporating standard atmospheric corrections) were acquired with a resolution of 1.2 km at high temporal frequency (http://oceancolor.gsfc.nasa.gov/DOCS/MODISA_processing.html). We used the global 8-day mean Nighttime Sea Surface Temperature (NSST) grids from MODIS that had been validated (ftp://podaac.jpl.nasa.gov, thermal IR SST, 4 km and 0.1°C resolution). Additionally, we obtained averaged weekly daytime measures of Chl-a concentration from MODIS databases. For each tag location, we extracted a Chl-a value. SSS and Geostrophic Velocity (UV) (zonal and meridional currents) data were downloaded from MyOcean [70]. The NSST, Chl-a, SSS and UV raw data were used as auxiliary environmental data.

Home range and habitat use

A utilization distribution (UD, [71]) was subsequently created from the satellite tracking using the ‘adehabitat’ package for R [72]. We used the default method for the estimation of the smoothing parameter, which supposes that the UD is bivariate normal. Under the utilization distribution model, we considered that the animals’ use of space can be described by a bivariate probability density function, the UD, which gives the probability density to relocate the animal at any place according to the coordinates (x, y) of this place. The home range deduced from the UD as the minimum area on which the probability to relocate the animal is equal to a specified value. For example, the 95% home range corresponds to the smallest area on which the probability to relocate the animal is equal to 0.95. Positions grouped by diving pattern (clusters) were represented using a Kernel density spatial analysis.

Statistical analyses for the oceanographic characteristics and the utilization areas were performed with the Statistics Toolbox in Matlab 8.0.0 (MATLAB 2011).

Results

The mean size of the Atlantic bluefin tuna released in the western Mediterranean Sea with pop-up satellite tags was 76.1 kg± 50.1 (SD). The bluefin tuna tagged in waters off eastern Spain and the Balearic Islands were on average 88 kg ± 58.7 (SD) and Corsica fish were 54.6 kg ± 14.4 (SD). In the Adriatic Sea, the size of tagged tuna was lower (49.1 kg ± 10.6 SD). Overall, the mean weight of the satellite tagged bluefin tuna was 69.5 kg ± 45.2 SD, and only 7 of the 37 tagged tuna analyzed during the study were over 100 kg (the average of these 7 large tuna was 146 kg, ± 49 SD).

The mean retention time of the pop-up satellite archival tags from fish that reported more than 22 days (Table 1) was 81.5 ± 45.4 (SD) days when using single point attachment methods (N = 20). Bluefin tuna tagged on deck with the addition of a second attachment loop (N = 17) averaged 136.2 ± 96.1 (SD) days. Even though the retention time increased by using a second loop, only two of the pop-up satellite tagged fish with a second loop, remained attached until their programmed release date recording 303 and 304 days of data respectively (Table 1). All of the satellite tagged bluefin tuna remained within the Mediterranean Sea post release and throughout the track duration (Fig. 2). These western and central Mediterranean tagged bluefin tuna primarily resided within the basin they were released in, and none moved into the eastern Mediterranean basin.

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Fig 2. Daily positions based on estimated geolocation of the 38 tuna analyzed in this study and tagged within the Mediterranean Sea with pop-up satellite and archival tags.

White circles represent the positions of the tuna tagged in the western Mediterranean basin (n = 28 pop-up tags + 1 internal tag), while yellow circles represent the positions of the tuna tagged in the Adriatic (n = 9 pop-up tags).

https://doi.org/10.1371/journal.pone.0116638.g002

Two bluefin tuna estimated at 13 kg (body size at tagging) have been recovered from the 30 surgically implanted internally tagged bluefin tuna in the Mediterranean Sea. Both of these fish were tagged and released in August 2008 in the waters off Roses, NE Spain (Table 2). The first internal tag recovered was from a bluefin tuna recaptured by a Spanish pelagic longliner after 391 days at liberty (ID # 0890138). The fish was 185 km from its deployment location when recaptured over a year (Fig. 3). The second internal tag (ID # 0890152) was recovered by a fishmonger in Venice, Italy from a tuna that had been caught at an unknown position around western Sicily (after 965 days at liberty). The first tag provided a complete archival time series record; however upon recalibration of the latter archival tag, the external temperature sensor showed a deviation from the original calibration and its thermal data could not be taken into account in the analyses. Although the complete archival tag geolocation track is not available, we were able to use the light level longitude record to establish the position and concluded this bluefin tuna did not leave the Mediterranean, nor did it visit the eastern Mediterranean. This bluefin inhabited waters between the 0 and the 18th meridian east (Fig. 4).

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Fig 3. Daily positions for the 38 tuna analyzed in this study.

Orange circles represent the internally tagged fish, while the white circles are the positions of the tunas tagged with pop-up satellite tags in both basins.

https://doi.org/10.1371/journal.pone.0116638.g003

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Table 2. Deployment data and recapture information of the implanted internal tags deployed in 2008 in Roses, NE Spain.

https://doi.org/10.1371/journal.pone.0116638.t002

In total, the 38 reporting electronic tags (including internal tag # 0890138) recorded 4336 days of location and behavior data on bluefin tuna behavior and habitat utilization within the Mediterranean Sea. Electronic tags deployed on Atlantic bluefin tuna in waters off eastern Spain (N = 18) recorded a total of 1669 days (average 92.7 ± 81.2 per track) and 391 days for the internally tagged juvenile released in eastern Spain. The Corsica deployments (N = 10, all MK10 pop-up satellite tags) generated 864 days of data (average 86.4 ± 57 days per track), while the tags deployed in the Adriatic Sea (N = 9) recorded 1412 days (average 156.9 ± 73.2 per track). Combining both the satellite and internal tagging data sets (including the internal tag # 0890152) revealed that none of the fish analyzed during the present study left the Mediterranean Sea during the 23 to 964 days that they carried an electronic tag. The tagged bluefin tuna released in western or central Mediterranean locations stayed within these two basins, in some cases crossing between them, and never ventured into the Alboran Sea (the southwestern most area of the Mediterranean Sea, just before the Strait of Gibraltar) or the eastern Mediterranean basin.

Habitat Use of Electronic Tagged Bluefin in the Mediterranean Sea

The seasonal analysis of the oceanic habitat use of the 38 tunas included in the analyses (Fig. 5) clearly showed the waters around the Balearic Islands and between the Ionian Sea and Libya are of high importance. The waters around the southern part of the Balearic archipelago were key waters occupied during the putative spawning period (Fig. 5A). Moreover, the main overwintering/feeding areas were identified as the waters south of the Gulf of Lions (Fig. 5B-5E) and the Adriatic Sea, primarily in this latter region the deeper waters of the Jabuka Pit (Fig. 5C-5E).

The trajectories of all the tagged tuna analyzed here, showed a distinct use of the basins within the Mediterranean (S1S3 Figs).

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Fig 5. Seasonal Utilization Distributions (UDs) of bluefin tuna.

The locations of the tuna were examined for the (A) spawning period (i.e. May 15 to July 15) and the seasonal periods of (B) spring, (C) summer, (D) autumn and (E) winter. UDs were computed using the Kernel method through the ad hoc method (h = Sigma*n^(-1/6), Sigma = 0.5*(sd(x)+sd(y))). The graphs show the UDs cumulative frequencies up to 95% (the color attributed to a given percentage p applies to areas comprised between p and p–1% isopleths).

https://doi.org/10.1371/journal.pone.0116638.g005

Adriatic

In total, 800 days of location and behavioral data (diving) were recorded inside the Adriatic Sea from the 9 pop-up satellite tags deployed there, 288 days in the western Mediterranean Sea basin (including the Tyrrhenian Sea), and 150 days in the Ionian Sea as well as in waters close to Libya. Geolocation position data demonstrated that tuna under 60 kg left the Adriatic Sea, while those over 60 kg (N = 2, Table 1) remained in the Adriatic Sea. The trajectories of these Adriatic Sea electronically tagged bluefin tuna show a distinct use of the regional basins within the Mediterranean Sea (S1 Fig.). Tuna tagged and released in the Adriatic Sea displayed an association with the waters over the bathymetrically deeper areas of this region, particularly the Jabuka Pit/Fossa di Pomo (i.e. mid-Adriatic) and the South Adriatic Pit, during all seasons. These fish showed a strong residency in these deeper bathymetry waters areas of the basin during all seasons except for spring—when most tags had already detached—(Figs. 2 and 5). Only two of these nine bluefin tuna left this central Mediterranean region towards the end of September to venture into the western portion of the Mediterranean Sea (ID # 10P0038 and 10P0401, S1.7 and S1.8 Figs.). These two fish, moved into the northwestern Mediterranean regions (in the vicinity of the Gulf of Lions), visiting the waters surrounding Corsica and Sardinia Islands on the way. After spending some time around Corsica and Sardinia and in the Tyrrhenian Sea, one of these individuals moved towards Libyan waters at the end of January where its satellite tag popped-off and reported on February 9—before the known spawning season. Two additional tuna tagged in the Adriatic Sea (ID #08A0394 and 08A0390, S1.2 and S1.3 Figs.) left the deployment area—although they remained within the central Mediterranean basin—and visited the Ionian Sea (between mid-March and beginning of May) and the Gulf of Sidra (from mid-January to the beginning of March) (Figs. 3, 5B and 5E).

From the nine Adriatic tuna, only one was tagged before the spawning season (i.e. # 10P0648, Table 1 and S1.9 Fig.). This fish left the Adriatic Sea towards the end of May, spent time in the Ionian Sea and in the waters south of Sicily, and came back to the Adriatic Sea around mid-August.

Western Mediterranean

Western Mediterranean electronic tagged adult tuna showed more fidelity to their deployment basin than the Adriatic ones (S2 Fig.). Even though the average of time at liberty of their deployments (i.e. 90.6 ± 72.4 (SD) days) limited the dispersion of the fish and could have biased the general view of their movements, overall, these tuna tended to concentrate in presumed feeding grounds (i.e. in the waters between the Gulf of Lions and the Balearic Islands) all year round (Figs. 5B to 5E), and only one individual went through the Strait of Sicily (i.e. # 10P0546, Table 1), reaching the Gulf of Sidra in June, during the known spawning season (Fig. 5A, S2.14 Fig.). A second tuna (i.e. # 10P0402, Table 1, S2.15 Fig.), was at the entrance of the Strait of Sicily when its tag released on its programmed day.

The two tuna with the longest duration of pop up satellite tag deployments (303 and 304 days, i.e. # 10P0546 and 10P0402, respectively), were deployed in Roses, NE Spain, and both occupied the aforementioned feeding area between the Gulf of Lions and the waters north of the Balearic Islands. This area is similar to that occupied by a bluefin tuna tagged in the Adriatic Sea (i.e. # 10P0038, Table 1 and S1.7 Fig.). This regional hot spot occurs from November until March (Figs. 2, 5 and S2.14 and S2.15 Figs.).

The juvenile Atlantic bluefin tuna tagged with an internal tag (# 0809138, Table 1) also displayed a different behavior from the larger sub-adult and adult tuna occupying the southern waters of the western Mediterranean basin. From the end of autumn to the beginning of spring this tuna visited the Tyrrhenian Sea and crossed the Strait of Sicily. From there it returned to the Balearic spawning ground and spent the rest of spring and summer in the waters around the Balearic Islands, until it was recaptured at the end of September, after 391 days at liberty (Fig. 3, S2.19 Fig).

Corsican individuals (N = 10), in particular, showed a high fidelity to the Strait of Bonifacio and around the northern area of Corsica (Fig. 5d, S3 Fig.).

Bluefin Tuna Fishing Operations

All the fishing operations (N = 6031) that occurred within the Mediterranean Sea, from 1989 to 2012, from purse seiners, longliners and bait boats were plotted together to examine potential aggregation sites of fish (Fig. 6).Altogether these catch data locations provide a proxy for the bluefin tuna distribution inside the Mediterranean during the past 23 years from April to August, as fishing vessels (mostly purse seiners coupled with spotting planes that were helping the fishery until recently) target mainly those areas where bluefin tuna aggregate.

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Fig 6. Locations of bluefin tuna fishing operations between April and August in the Mediterranean Sea from 1989 to 2012 (n = 6031) (different color dots), and spatial distribution of the Japanese longliners’ total bluefin tuna catches in Algeria from 2000 to 2007 (based on Abdelhadi et al.,[69]) (red dotted line).

PS = Purse seiners, LL = Longliners and BB = Bait boats.

https://doi.org/10.1371/journal.pone.0116638.g006

Comparing the fishing operations’ map with the trajectories and habitat use distributions of the 38 tags analyzed in the present study (Figs. 3, 5 and S1S3 Figs.), it can be observed that the fisheries data and the tagging data overlap almost completely; putting aside the Gulf of Naples (Tyrrhenian Sea) and the Levantine Sea, which were never visited by the electronic tagged tunas. Taken together the two data sets provide the likely geographical distribution of the species preferred habitats in the Mediterranean Sea and their potential foraging and reproductive hot spots.

Habitat Use and Behavior During the Spawning Season

Atlantic bluefin tuna are known to spawn in the Gulf of Mexico and Mediterranean, which provides the first indications of the locations, oceanographic parameters and behavioral patterns observed during the spawning period (see Introduction). Based on prior electronic tagging in the western Atlantic and the Mediterranean, specific patterns, including aggregation behavior in positional data, a period of shallower mean depths from diving records, coupled to a unique oscillatory diving pattern, and warm ambient temperature ranges have been observed during the spawning seasons of both, the Gulf of Mexico and the Mediterranean [25,36,49,56]. Only four of the bluefin tuna in this study, were at liberty with their tags attached during the known Mediterranean spawning season and considered at this time by size to be potentially mature adults (tags # 10P0648, 10P0398, 10P0402 and 10P0546) (Fig. 7). Variance statistics of the daily estimated positions for the trajectories of these four tunas can be found in S1 Table.

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Fig 7. Tagged bluefin tuna possibly engaging in spawning during the reproductive season.

Note: yellow squares indicate periods of time with low linearity values and possible spawning behavior.

https://doi.org/10.1371/journal.pone.0116638.g007

This bluefin tuna with tag # 10P0648 (43.9 kg and 135 cm CFL) that potentially could be classified as a Mediterranean spawner, was tagged in the Adriatic Sea on May 12, 2012 (Fig 7). The fish left the Adriatic on the 25th of May, returning to it on September 9 after 107 days at large outside the Adriatic. The pop-up satellite tag was recovered after 179 days close to the coast of Croatia in November 2012. A full archival data record (pressure, temperature and light time series) was obtained with an interval of 5 seconds providing a high resolution time series. The linearity index (LI) score showed residency periods along the track in different areas of the Ionian Sea (Fig. 8). The first period of residency occurred from the 26th to the 31st of May just after leaving the Adriatic (LI 0.48 and SST 19.79°C SD ± 0.38), a second period of aggregation occurred from the 11th to the 15th of June (between Zakynthos Island, Greece, and the southernmost point of continental Italy), with a Linearity index of 0.51 and SST of 23.63°C (SD ± 0.26), followed by 15 consecutive days of low LI (0.58, 0.36 and 0.41 for the periods 21st to 25th, 26th to 30th of June and 1st to 5th of July, respectively; while SST for the same periods was 25.64°C (SD ± 0.50), 26.19°C (SD ± 0.30) and 27.31°C (SD ± 0.19), respectively). The next resident behavior period occurred in Tunisian waters late in July (LI of 0.23 and SST of 25.44°C (SD ± 0.61) for the 21st to the 25th of July). Average bathymetry for the waters occupied for the period of the 26th to the 31st of May was 1091.29 m (SD ± 126.50), while for the June periods and the first period of July the average was 3511.41 m (SD ± 120.23). The bathymetry shoaled during the residential event of the 21st to the 25th of July (413.28 m, SD ± 425.90).

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Fig 8. Linearity index for the four tags at liberty from mid-May to October.

Green #10P0402, red #10P0398, black #10P0546 and blue #10P0648.

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To examine the diving behavior and depth distribution of this fish (# 10P0648) in more detail we performed a cluster analysis. This revealed 7 types of diving behavior modes (Figs. 9, 10A and Table 3). All 7 groups are described herein. The depth-bin histogram plot for cluster 2 (43.60% of the track) showed a higher preference of time in the surface waters, higher in use from the surface to 2 m and 5 to 10 m bins during the period from May to June (Fig. 10). Mean depth for cluster 2 for all days at liberty was 38.02 m (SD ± 41.47), while the average external temperature was 20.50°C (SD ± 1.86) and the dive frequency 2011 (SD ± 343). Maximum “U”-shaped dives down up to 300 m were observed in this cluster. The cluster 2 was predominant and mostly concentrated during June (14.53%) followed by May (8.72%), August (8.13%), September (6.39%) and October (4.06%). The mean depth varied during the months during the described spawning season. Values ranged from 14.58 m (SD ± 4.76) in May, 19.25 m (SD ± 17.10) in June and 30.51 m (SD ± 21.00) in July, while it continued increasing from August to September (Table 4), where there was no bathymetry limitation, and decreased again from September to October when moving through the North Adriatic basin where a shallower bathymetry was evident. External temperature means recorded by the tag were 17.85°C (SD ± 0.63), in May, 21.54°C (SD ± 1.65), 21.97°C (SD ± 2.38) and 21.28°C (SD ± 1.05) for June, July and August (Table 3), maximum external temperature (24.68°C) was reached in July.

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Fig 9. Dendrogram for tag #10P0648 determined from clustering analysis of differences in diving patterns Each column represents a 24-hours depth histogram (n = 175 days) and the color is the fraction of time.

The density variable is expressed as a fraction of each day spent in depth bins defined along the y-axis.

https://doi.org/10.1371/journal.pone.0116638.g009

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Fig 10. (A). Positions of the different clusters along the track of the tuna 10P0648 (in Black cluster #1, green cluster #2, red cluster #3, blue cluster #4, yellow cluster #5, violet #6 and in white cluster #7).

(B) Kernel distribution of cluster 2 and 3 during May, June and July. Number #1 compiled the period from 25th May to 5 th June, #2 from 7th to 14th June while #3 is for 17th to 30th of June.

https://doi.org/10.1371/journal.pone.0116638.g010

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Table 3. Mean values, maximums, minimums and standard deviation for the clusters obtained.

https://doi.org/10.1371/journal.pone.0116638.t003

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Table 4. Mean values, maximums, minimums and standard deviation for cluster 2 and 3 for all months when present.

https://doi.org/10.1371/journal.pone.0116638.t004

Cluster 3 pattern from this analyses corresponded to a high utilization of the water column comprised between 5 and 10 m with very few deep dives. Utilization of the surface waters (bins 0–2 m) was scarce. This behavior corresponded to the 16.20% of the entire track and was found in May (1.16%), June (2.9%), July (6.30%) and October (5.81%). Average depth of cluster 3 was 10.35 m (SD ± 3.15), external temperature 22.19°C (SD ± 2.49) and dive frequency 1765 (SD ± 190) (Table 3). June average depth was 7.70 m (SD ± 2.01), July 12.47 m (SD ± 3.79) and 9.70 m (SD ± 1.22) in October where the dive depths were bathymetrically constrained (Table 4). Cluster 4 (13.37%) showed a similar diving pattern on the first meters (0 to 15 m) as cluster 3 but showing increased residency between 100 and 200 m (Table 3). Cluster 5 (12.79%) corresponded to a surface behavior (bin 0 to 2 m) with occasional residency between 100–200 m. This behavior was found especially in the month of September around the South Adriatic Pit. Cluster 6 behavior (2.9%) was showed only during 5 days when visiting shallow waters (Table 3).

The last groups, cluster 1 (8.7%) and 7 (2.3%) mainly corresponded to the Adriatic basin (October) or other areas with a limited bathymetry, like the Tunisian basin (July). Here the shelf limits the diving of the tuna. The tuna exploited the entire water column in this region, but cluster 1 primarily used the upper layers (0–5 m). Maximum depth bins observed were 100 to 200 m for cluster 1 and 30 to 40 m for cluster 7. The mean depth was 16.77 m (SD ± 2.71) and 12.91 m (SD ± 1.00) for clusters 1 and 7, while external temperature and dive frequency were 20.42°C (SD ± 1.49), 20.61°C (SD ± 0.79) and 1694 dives (SD ± 321) and 1674 dives (SD ± 177), respectively.

Clusters 2 and 3 for May, June and July were analyzed using Kernel density distribution showing hot-spot areas overlapping with low LI scores (Fig. 10B). These two clusters showed a distinctive diving pattern associated with remarkable use of the thermocline (Fig. 11) that was found only in June. This high oscillation dive patterns, comprised vertical movements between 0 and 30 m, dive signatures crossing the mixed layer are unique to these clusters. Depth increased in the middle of the event period and, as a result of these dives, a thermal footprint in the external temperature profile was left (normally as an inverted triangle Figs. 11A and B). The thermal difference between the highest and the lowest temperature was between 2 and in some cases 6°C and these were detected only at night, from 11:15 pm to 2:30 am with duration between 60 to 120 min. This night diving behavior started on the 7th of June and lasted till the 3rd of July, but the thermocline was only used as described here in the period from the 11th to the 26th of June. For at least 3 days within this last mentioned period the tuna were not using the combination of high oscillation dives below the mixed layer (Fig. 11A).

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Fig 11. Depth and temperature profiles #10P0648.

Dot line corresponds to mixed layer while a dashed line is the thermocline. (A) Cluster 2, the high oscillatory dives are present but do not break the mixed layer (16 June). (B) Cluster 2, high oscillatory dives going below the thermocline, followed by a “U”-shape dive (21 June). (C) Cluster 3 (consecutive day), same pattern but only a few “V”-shape dives during the rest of the day (22 June).

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The limitation of the data received from the other 3 bluefin tuna forced us to use different approaches to assess their behaviors. The second tuna with tag # 10P0398, which was tagged in Moraira, E Spain on May 29, 2011(43.9 kg and 135 cm) moved to the oceanographic area well known as a region of spawning in the Balearic Islands (Fig. 7). This tuna showed the lowest LI score of all the 4 tuna, indicative of a residency pattern in these waters situated south of Majorca Island, Balearic Islands from the 16th to the 20th of June (LI 0.19). Then the tuna moved eastward and explored a small area between the Balearic Islands and Sardinia, Italy, from the 6th to the 10th of July (LI 0.59, Fig. 8). The mean SST estimated from the tag was 23.15°C (SD ± 0.47) during this June period, while the mean SST estimated in the July period was 24.92°C (SD ± 0.37). Time at temperature for the temperature range 21–24°C was 95.7% (SD ± 2.37) during the June period, and 85.95% (SD ± 14.93) for the temperature range 24–27°C during the July period. This indicates a clear preference for the temperature range 21–27°C, in accordance with what has previously been reported for preferences of tuna presumed spawning in the Balearic Sea [49,51,52]. The bathymetric depth estimated for those locations was 2351.91 m (SD ± 316.29) and 2862.92 m (SD ± 5.06), respectively. Time at depth for the depth range between surface and 20 m for those two periods was 80.16% (SD± 15.93) and 88.14% (SD ± 1.89), revealing a significant surface behavior pattern consistent with what is been reported previously for tunas in spawning areas in the Gulf of Mexico [25,56]. The satellite images for these periods show that the fish was in an area of mixing between Atlantic and Mediterranean waters (Fig. 12). Mean salinity for the first and second period was 37.38 ± 0.07 and 37.47 ± 0.03 respectively (Table 5).

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Fig 12. Trajectory of tuna with tag ID # 10P0398

(A) June 16 to June 20 (pink dot and triangle, respectively) and (B) July 6 to July 10 (pink dot and triangle, respectively) plotted with the mean Sea Surface Salinity (SSS) and the mean geostrophic velocity (UV) for those specific days.

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Table 5. Satellite oceanographic parameters for the 4 bluefin tuna (BFT) during the proposed spawning periods of tunas with tag ID # 10P0398, 10P0546, 10P0648 and 10P0402.

https://doi.org/10.1371/journal.pone.0116638.t005

Additional potential spawning fish were identified as tags numbered # 10P0402 and tag # 10P0546. Both bluefin tuna were tagged and released in Roses, NE Spain on August 31 and September 1 2011, respectively. They remained associated to the Gulf of Lions and N and NE Balearic Islands till early May and beginning of June 2012 when they migrated towards the central Mediterranean. For these tags the only data received was light levels and SST. Tuna with tag # 10P0402 started moving towards the central Mediterranean on the 2nd of June and popped-off on the programmed date. Towards the end of its trajectory (from the 26th to the 30th of June 2012), its LI score was 0.55 and at that time the fish was off the northern coast of Tunisia, at the entrance of the Strait of Sicily, after a track of c. 753 km in 28 days (Figs. 7 and 8). The mean SST estimated for this period was 24.02°C (SD ± 0.34), while the estimated mean bathymetry during those days was 369.26 m (SD ± 143.43).

Tag # 10P0546 left the western Mediterranean on the 9th of May and went straight toward the Gulf of Sidra, swimming c.1624 km in 29 days (LI 0.97, SD ± 0.02), where it remained from the 7th to the 20th of June, showing low LI scores from the 11th to 15th and from the 16th to the 20th of June (0.21 and 0.66, respectively (Fig. 8). The mean SST estimated from the tag was 23.35°C (SD ± 0.46) during the first period and 24.22°C (SD ± 0. 45) during the second, with an estimated mean bathymetry of 1048.04 m (SD ± 82.15) and 1199.72 m (SD ± 72.96), respectively. On the 21st of June the tuna left the area towards the W Mediterranean in a straight line (LI 0.99 (SD ± 0.00) till the 30th of June, when its tag popped-off, having swum about 610 km in 9 days (Figs. 7 and 8).

Satellite Analyses

Satellite oceanographic observations were obtained (i.e. Chl-a, NSST, SSS and UV) for the locations of the bluefin tunas (for tags # 10P0398, 10P0546, 10P0648 and10P0402) during the possible period for potential spawning activity (Table 5). We found that for bluefin tuna # 10P0398 and # 10P0402 all oceanographic parameters examined were within the range of criteria described previously for the Balearic [49,51,52] and Gulf of Mexico [56] spawning grounds. For bluefin tuna # 10P0546 and # 10P0648, whose tracks were in the central Mediterranean, satellite observed values were slightly higher than the theoretical spawning range for Chl-a, NSST and Salinity, described for the western Mediterranean and Gulf of Mexico.

Discussion

Atlantic bluefin tuna are hypothesized to migrate to the Mediterranean Sea from the Atlantic Ocean during the months of April to May [18] to reproduce, and after spawning in the Mediterranean they have been postulated to immediately initiate a migration out to the Atlantic Ocean to feed [1921]. Even though this is a well-documented movement pattern in the literature, the results herein reveal residency for long durations and are similar to the recent electronic tagging efforts reported [38,41]. Together the electronic tagging studies indicate that some bluefin tuna are residential within the Mediterranean for much of the year. Of the 39 electronic tags analyzed (including internal tag # 089152), all tagged bluefin tuna remained in the Mediterranean Sea for up to a year post release.

Recent Mediterranean Sea electronic tagging studies, which did not cover the Balearic Sea region, also concluded that after spawning, individuals below 100 kg do not exit the Mediterranean, remaining to forage in areas of high primary production in the Mediterranean Sea. To date, from tagging experiments only those individual tunas over 150 kg demonstrate a pattern of migration into the NE Atlantic Ocean, implying a size dependency to a North Atlantic migration [13,21,43,44]. In this study, although some of the tunas, which were tagged in the northern Balearic Islands, were over 150 kg in size these fish also displayed the residential behaviors typical of the smaller tagged fish. These large bluefin occupied the northern Balearic waters until the thermocline broke down, at which point they started moving away from this region. This residential behavior was also observed for tuna below 100 kg in this study. It has been hypothesized that dispersal movements away from the hot spot region of residency could be related to the drop of water temperatures and the disintegration of the thermocline with increased wind driven mixing around November [73]. Cooling of the water column and loss of the vertical structure may lead to less concentrated prey aggregations which may underlie the movements away from these areas as a reduction in prey availability may force bluefin tuna to move [74].

Two of the tagged tuna, deployed in waters off Roses (NE Spain), visited the Tyrrhenian Sea (bluefin tag # 08A0399 and 0809138). The first tagged fish had its tag pop off along the northern coast of Sicily at the beginning of December, while the second bluefin tuna spent November, December and January there before crossing the Strait of Sicily. Our data also revealed a connection between a tuna tagged in the Adriatic Sea and the western Mediterranean Sea. One individual tuna also showed a lesser known connection between the Adriatic Sea and Libyan waters in winter. In addition, a direct link due to movements between the western Mediterranean Sea population and the Gulf of Sidra waters (Libya) was observed during the spawning season (bluefin tag # 10P0546). Similar types of directed movements were also found by Fromentin & Lopuszanski [41].

Bluefin tunas tagged and released in Corsica, on the other hand, remained highly residential in a reduced area between the waters off Corsica and Sardinia for the entire period of the tracking time recorded (i.e. between 25 and 235 days), potentially suggestive of a forage aggregation for tunas. Moreover, the Algerian basin was also found to be an important foraging area for juvenile tuna. Like all bluefin tuna in the present study, these fish did not cross over to the eastern Mediterranean basin. Rodríguez-Roda [75] reported that a 45 kg tuna which was conventionally tagged in May in Sicily (Italy) appeared off the east Spanish coast in November. Similar results were recently obtained with electronic tagged fish in recently reported work by De la Serna et al. [38] who described results from 8 pop up satellite and 2 internal tags deployed in the same area and season as the present study. Moreover, Fromentin & Lopuszanski [41] also deployed 39 pop up satellite tags off Marseille (southern France) in autumn months and they reported an individual (> 150 kg) that visited the Sidra spawning ground at the end of June—in a similar fashion to the tuna with tag # 10P0546 in this study. Similarly, another tuna (approximately 50 kg) whose tag popped off in the Tyrrhenian Sea (north of Sicily) in late April displayed similar behaviors to bluefin tuna with tag # 08A0399 in this study. Aranda et al. [36] confirmed the migration of presumably post-spawning adult bluefin tuna from the southern Balearic waters to the Atlantic Ocean after having conducted satellite tagging during the spawning season. Similar to this finding, two individuals (> 150 kg) tagged with peritoneal implantedarchival tags off the eastern coast of USA, exhibited a multi-year site fidelity or homing behaviors to the western Mediterranean basin during the spawning season while overwintering in Atlantic waters [13]. These two archival tagged tunas did not enter the eastern Mediterranean Sea indicative of fidelity to the western Mediterranean known spawning areas. In fact to date, few bluefin tunas reported from the US electronic tagging studies have passed across the central Mediterranean indicative that these western Atlantic tagged bluefin are from populations that originate in the western Mediterranean. Taken together, the results from the previous studies and ours provide a view of the western Mediterranean as an area where bluefin of many year classes are mixing. These bluefin tuna exhibit behaviors suggesting that at least some bluefin adults and sub-adults are residential (current studies), while other fish return to spawn from the North Atlantic foraging grounds. Tagged bluefin show fidelity to the Balearic waters during the spawning season [13], and some post-spawners move out into the Atlantic Ocean after spawning [36] but return again the following spawning year. Although some residency is contributed to the short duration of tag attachments- the fact that longer retention tags also displayed the same behaviors provides further evidence that there are bluefin that are residential throughout the year in the western Mediterranean. Additionally, several recent studies using similar techniques indicate that foraging as well as spawning may be a key driver of retentive behaviors in the Mediterranean for bluefin tuna.

Juvenile bluefin tuna tagged with internal tags that were at large for long durations in the present study (391 and 965 days post release), remained in the western Mediterranean. One internally archival tagged fish displayed a short visit (bluefin tuna tag # 0809138, Fig. 3) to the central Mediterranean basin. Moreover, a long-term aggregation area associated with the Algerian Current system, between the Balearic Islands and the Algerian coast was found for at least one of the archival tagged juveniles (tag # 0809138, Fig. 3). Juvenile bluefin tuna tagged in November in the Adriatic Sea displayed a residential behavior in the central Mediterranean, although one fish moved to the waters south of France after 7 months at liberty and another one visited the Ionian Sea, the Aegean Sea and Libyan waters [35,76]. These results suggest significant residency of juvenile bluefin tuna within the central Mediterranean Sea, consistent with the movements observed for the young adult tuna tagged in the same area in the present study.

Electronic tagging, otolith and genetic results have also shown that significant numbers of juvenile bluefin tuna of Mediterranean origin are migrating into the western Atlantic Ocean to forage [3,13,17,77]. Taken together, the electronic tagging data from all studies indicates there are multiple demographic units of bluefin tuna, mixing in the Mediterranean with distinct behaviors, i.e. some migratory and some resident co- existing together, and mixing within these diverse oceanic regions. The hypothesis that there might be a co-occurrence of residential and migratory bluefin tunas in the Mediterranean has been proposed by many scientists previously (see review in Mather [8]), and even though the demographic relationships between tuna following each pattern at a given time remains unknown, it appears as though electronic tagging is validating the overlap of these behaviorally distinct fish. However, caution must be taken due to the short duration of tracks which do not allow significant time for dispersion and demonstrate the need for longer studies, only achievable with internal tags to garner 1–4 year tracks that may shed light on the population structure. Genetic studies have demonstrated population structuring within the Mediterranean Sea [77]. Combining genetics (identification of population structure with fin clips) and archival tagging would be a way to move forward with resolving the distinctive populations and their migratory trajectories.

Taking into account the weight distribution of bluefin tuna found (approximately 95% of large fish > 100 kg) in the Strait of Gibraltar and Moroccan tuna traps during the spawning migration [42,78,79], and the fact that most of the captures outside the spawning season in different areas of the Mediterranean Sea are small to medium tuna—i.e. eastern Mediterranean [80], Tyrrhenian and Messina Strait [81], South Balearic Islands [82], Strait of Gibraltar [19] and Tunisia [83]-, and the experimental tagging results from various authors [13,26,36,84], we can postulate that part of the Mediterranean highly migratory population comes in as others have suggested from foraging grounds in the north Atlantic. These bluefin tunas, spawned in the Mediterranean Sea, migrate to the North Atlantic to spend their juvenile life phase in the Atlantic Ocean, and after reaching a minimum size of at least 200 cm CFL (i.e. > 140 kg), migrate back into the Mediterranean Sea to spawn. In addition, as demonstrated by Block et al. [13], these North Atlantic foragers that spawn in the western Mediterranean, show multiple-year spawning fidelity after they return to the western Mediterranean, with multi-year entrances and exits for up to 4 consecutive years have been recorded on archival tags before their recapture. Block et al. [13] documented that, when entering the Mediterranean, these types of Atlantic bluefin tuna are large in body size in comparison to reports of early maturing population of eastern Mediterranean spawners, used in ICCAT assessments [4]. This hypothesis of a highly migratory later maturing bluefin entering the western Mediterranean for spawning is supported by the fact that the documented Mediterranean catches of larger tuna (> 150 kg) only increase during the spawning season [19,80,82,83,85]. Thus, the tagging, genetics and fisheries data taken together indicate that both, residential populations of bluefin, and migratory populations, overlap in the Mediterranean Sea. This should also be of importance to models of bluefin that only use a single age to maturity for Mediterranean bluefin given more than one population exists with distinctly different behaviors. Five of the 39 analyzed tunas in the present study were large fish (> 100 kg), which obviously raises the question about where do they fit in this Mediterranean Sea mosaic. Do these large residential tuna eventually become Atlantic migrants? Or do they always stay part of the resident population? Genetics and long duration tracks from archival or pop up satellite archival tags that are recovered will help establishing which population these particular tagged fish were from. Thus in the future, it is necessary to report a track with a genetic ID so that models incorporating such data know which population of fish they are assigning foraging locations and spawning areas to when modeling what these fish do [5].

Kernel density estimators were successfully used in several tracking studies to describe habitat use and to identify high use areas for marine animals [13,24,26,86,87]. The utilization distributions produced in the present study from the tracking data (Fig. 5) identified overwintering/feeding areas in the waters south of the Gulf of Lions and the Adriatic Sea, primarily the deeper waters of the Jabuka Pit. The Gulf of Lions is known as one of the most productive areas of the Mediterranean Sea due to hydrographic features such as a wide shelf, strong vertical mixing in winter, coastal upwelling and river runoff [88]. The latest sardine and anchovy biomass assessments performed by the General Fisheries Commission for the Mediterranean Sea (GFCM) found that their combined biomass was nearly 1 million tons in the northern Adriatic area [89], accounting as one of the most productive regions in the Mediterranean Sea [9092]. De la Serna et al. [93] analyzed the stomach contents of bluefin tuna in the western Mediterranean and found that the main ingested species were sardine and anchovy (apart from a number of unidentified fish species, i.e. Teleostei spp.). Additionally, and supporting our results, Druon et al. [53] detected the Gulf of Lions as potential feeding habitat in a model developed to map potential Atlantic bluefin tuna feeding and spawning habitats in the Mediterranean Sea; while recently, Fromentin & Lopuszanski [41] suggested an overwintering area for adult tuna south of Marseille (France).

Moreover, our results have been found to be in good agreement with the map presenting the overall bluefin tuna fishing operations in the Mediterranean Sea from 1989 to 2012 (Fig. 6). The map provides a comprehensive set of data for fishing locations for the species, thus, it can be considered a robust proxy for tuna aggregations in the Mediterranean, particularly from April to August. Important aggregation areas in the Tyrrhenian Sea and in the eastern Mediterranean, which are evident from the map with the bluefin tuna fishing operation locations (Fig. 6), and are well-known [81,9498] and references therein, for the Tyrrhenian Sea; and Karakulak and Oray [99] for the eastern Mediterranean—were not visited by the tuna tagged in this study during the spawning season (Fig. 2). No tags were deployed in these two regions, which could have led to these two gaps. Regarding the eastern Mediterranean, Karakulak and Oray [99] stated that a sub-population of bluefin tuna exists in the northern Levantine Sea, which is supported by tagging studies conducted in the eastern Mediterranean where tuna showed a tendency to remain in the Levantine Sea up to 36 days, the furthest one arriving to the Gulf of Laconia (Peloponnese, Greece) after 39 days, and the only fish in the study to visit the central Mediterranean [34].

Histological and larval studies also indicate that this region is a bluefin tuna spawning ground for the eastern Mediterranean basin [99101]. To date the mixing rates between the eastern, central and western Mediterranean basins have not been adequately resolved. Results from this study and prior works support existence of western Mediterranean bluefin population distinct from an eastern bluefin tuna population.

The Atlantic bluefin tuna population structure within the Mediterranean Sea appears to have a more complex structure than previously thought. Recent genetic studies employing a range of molecular markers have not reached a consensus on the stock structure of bluefin tuna in the Mediterranean [102110], although more recent genetic studies do agree on the fact that there is evidence of complex population differentiation within the Mediterranean [1517,111]. Riccioni et al. [77] have recently reported structure in relationship to oceanographic conditions providing one hypothesis for how bluefin may be diverging (e.g. preferences for oceanographic areas within the Mediterranean Sea). Advances will only occur when multidisciplinary studies are conducted using all available tools (genetics, tagging and isotopes).

The time series from the archival data of the bluefin tuna # 10P0648 recovered tag allowed us to perform a cluster analysis using custom depth bins to categorize the different diving behavior. Corriero et al. [112] found mature tuna of similar size than bluefin tuna # 10P0648 in early July in the north Ionian Sea. Their gonads showed late vitellogenesis with extensive atresia and no post-ovulatory follicles, suggesting that mature females inhabiting non-spawning areas, reabsorb their yolk reserve and do not spawn. These follicles can only be detected for a short time (< 24 h) following spawning in a number of tuna species [113115], so it can be also interpreted as a sign of cessation of spawning. From the cluster analyses on fish # 10P0648 we concluded that clusters 2 and 3 grouped behavior compatible with previously discussed spawning behaviors observed in the Gulf of Mexico. A high utilization of the surface waters occurred, from 5 to 10 m of the water column. These two clusters were concentrated in May, June and July and the Kernel density analysis for these clusters coincided with low aggregation as represented by LI scores for this tuna. Similar or lower LI were described in adult bluefin tuna spawning in the Gulf of Mexico by Teo et al.[56] (i.e LI 0.56 ± 0.1). SST in May registered by the tuna were on average 18.88± 0.83°C and these low temperatures are below the optimal temperature range identified as necessary for spawning, so we discarded this aggregation site and time of year and focused in those areas of low LI scores during June to interpret whether spawning may have occurred using some of the detailed observations of Teo et al. [56].

A detailed look at the depth and external temperature archival records of the June days showed that a high oscillation dive behavior appeared around midnight in the archival record. During this period, the fish moved below the mixed layer and we hypothesize that the bluefin tuna potentially uses these movements as a thermoregulatory cooling mechanism. At the thermocline, thermal rate of change is high with small changes of depth (Fig. 11). In most of the cases, after this behavior appeared, and coinciding with the dawn, the tuna made a deep “U”-shaped dive that other authors have interpreted as feeding [24]. The high oscillatory dives combined with the crossing of the mixed layer described above (Results section), occurred only during a 16 day period in June. This behavior was previously described for giant bluefin tuna in the Balearic Islands [36] and has been seen in the Gulf of Mexico (B. Block unpublished data). Moreover, they also found days during the spawning season where this behavior was not detected. Di Natale [54] and Piccinetti [55] suggested that a difference of at least 3°C between the upper and lower stratum of the thermocline is needed as physiological stimulus for spawning; this minimum difference was found in our data during the events described herein.

Bluefin tuna, like other temperate and tropical tunas, are a multiple batch spawner [116123], due to its asynchronous oocyte development [18,47]. Tuna spawning, therefore, can happen almost daily throughout the reproductive season [113115,124126]; in particular the spawning frequency or interval of bluefin tuna in the Mediterranean has been estimated at 1.2 days [18,127]. Bluefin tuna # 10P0648 showed a pattern of residency from the 11th to the 26th of June and simultaneously displayed repetitive vertical behavior during June in the Ionian Sea. The archival record also showed a thermoregulatory behavior that only occurred during this period and not in other areas or times. Potentially this is a behavior indicative of spawning, yet further data are required to confirm such a hypothesis. In both, the Mediterranean and the Gulf of Mexico, the location, size and intensity of spawning can be highly variable among years due to the spatial and temporal variability of the major oceanographic features (e.g. fronts) and environmental conditions (e.g. SST) [3,128]. Bluefin tuna are opportunistic spawners that follow environmental signals and adapt to year-to-year or longer-time variability [50].

The Balearic Sea, and more specifically the ocean area south of the Balearic Archipelago, has been identified as one of the key spawning grounds for Atlantic bluefin tuna within the Mediterranean Sea [3,13,49]. In this study, to investigate when tuna might be spawning in this region, we used both cluster and linearity analyses to discern periods of aggregation with unique behaviors. Considering the LI score, indicative of a sinuous behavior (suggestive of aggregation), bluefin tuna # 10P0398 showed two residential periods, from June 16 to June 20, 2011 (LI 0.19), and from July 6 to July 10, 2011 (LI 0.59). During these two periods the bluefin tuna were occupying the southern waters of the Balearic Islands and the waters between the Balearic Islands and Sardinia, respectively. At that time the fish experienced a period of residency as determined by the linearity index, similar to that observed by electronic tagged bluefin tuna in the Gulf of Mexico spawning season [25].

During both aggregation periods, bluefin tuna # 10P0398 was located in waters of lower salinity (i.e. 37.38 ± 0.07 and 37.47 ± 0.03), indicative of Atlantic and Mediterranean waters mixing, with moderate NSST (i.e. 22.7°C ± 0.2 and 23.4°C ± 0.04) and Chl-a concentrations (0.079 mg/m3 ± 0.012 and 0.083 mg/m3 ± 0.001) (Table 5). In addition, the timing of the aggregation is in agreement with previous studies where bluefin tuna were found in spawning condition to the south of the Balearic Islands from mid-June to mid-July [2,18,46,47,49,50,78,129]. Frontal structures with mesoscale eddies and anticyclonic gyres have been found to be associated to the presence of bluefin tuna at the time of spawning [49]. These two features, linked to egg and larvae retention, are hypothesized to be utilized by bluefin during the spawning period in the Balearic Archipelago [49,50]. In confirmation of this hypothesis, a high number of bluefin tuna larvae have been found associated with waters of Atlantic origin (i.e. SSS up to 37.2) or with areas where Atlantic and Mediterranean waters mix (i.e. SSS between 37.2 and 38) and with warm waters (over 20.5°C), mostly ranging from 23.5 to 25°C [49,51]. The trajectory from June 16th to June 20th and from July 6 to July 10 of tuna with tag # 10P0398 plotted against the satellite salinity, shows that the fish was in an area where waters of Atlantic origin were mixing with the waters from the Mediterranean Sea. (i.e. SSS of 37.38 ± 0.07 and 37.47 ± 0.03 for the first and second periods, respectively) (Fig. 12 and Table 5).

Larvae of Atlantic bluefin tuna have been found in the Balearic archipelago waters associated to geostrophic velocities ranging from 0.0168 to 0.37 m/s [49], and Chl-a concentrations ranging from 0.08 to 0.15 mg/m3 have been found to be preferred by spawning bluefin tuna in the Mediterranean Sea [53]. These values are comparable to the oceanographic conditions we found for tuna with tag # 10P0398 for both periods, i.e. an average UV of 0.139 ± 0.049 m/s and of 0.100 ± 0.037 m/s for the first and second period, respectively; and Chl-a concentrations ranging from 0.069 to 0.092 mg/m3 and from 0.082 to 0.084 mg/m3 for the first and second period, respectively (Table 5). Alemany et al. [49] also found that bluefin tuna showed a preference for deep waters in the Balearic Islands, similar to the deep bathymetric depths at which tuna with tag # 10P0398 was swimming, both, from June 16th to June 20th (i.e. between 2456 and 2588 m) and from July 6 to July 10 (i.e. between 2857 and 2870 m). Moreover, the vertical movements of this bluefin tuna were linked to the surface waters (> 80% of the time spent in the first 20 m), suggested by several authors as a spawning behavior [12,25,36,56]. Due to the lack of an archival record for this tag we cannot postulate that the tuna was spawning but the oceanographic parameters and residential behaviors could be compatible with spawning events at the locations this fish occurred in the region.

The bluefin tuna with tag # 10P0546, also showed behavioral indications of spawning, including a track with a low LI score from June 11th to June 15th, 2012. During this period the fish was in the Gulf of Sidra (Libya). The bluefin showed a preference for deep bathymetric depths (i.e. 1048.04 ± 82.15 m), NSST (i.e. mean of 22.74 ± 0.21°C), productivity (i.e. from 0.038 to 0.045 mg/m3) and geostrophic velocity (i.e. from 0.237 to 0.286 m/s) (Table 5). Moreover, the fast and long distant movement detected for this tuna between the northwestern Mediterranean and the central Mediterranean (i.e 1624 km in 29 days with high LI scores of 0.97 ± 0.07), with a short period of residency in the Gulf of Sidra, followed by a direct movement with high LI scores (0.99 ± 0.00), suggest a specific purpose compatible with spawning. Hence, this tuna displayed what could be a link between populations in the NW Mediterranean and the Libyan spawning sub-area 4, described by Di Natale [130] and also cited by Fromentin & Lopuszanski [41] in their study for a giant bluefin tuna. Similar results were also found for bluefin tuna with tag # 10P0402, which performed a similar migration towards the central Mediterranean. The pop up satellite archival tag released from this bluefin tuna on the programmed day, preventing us from knowing whether or not the tuna would have remained resident in this area. But the parameters transmitted met the criteria for spawning from June 26th to June 30th (i.e. mean of NSST 23.49 ± 0.18°C, mean of Chl-a 0.088 ± 0.003 mg/m3 and mean of SSS 37.93 ± 0.15), in an area off the northern coast of Tunisia, at the entrance of the Strait of Sicily (Fig. 7 and Table 5), which is not a known spawning Mediterranean area.

Conclusion

The results obtained during the present study provide new information on habitat use of the Mediterranean Sea by sub-adult and adult bluefin tuna. Electronic tagging results indicate extensive residency within the Mediterranean Sea by multiple year classes. The electronic tagging data sets provide the potential to observe residency and behavioral modes and oceanographic conditions associated with potential spawning in the Mediterranean. In this paper we have also identified in addition to known the spawning locations of the western Mediterranean, several potential new spawning areas that may be occurring outside these known areas. In these newly identified regions bluefin displayed behaviors that are consistent with potential spawning behaviors, and the oceanographic features and environmental conditions that bluefin tuna seek for spawning.

Currently used electronic tag technologies provide a choice between implantable archival tags and pop up satellite archival tags. This project occurred during phases of evolving technology. Most of the pop-up satellite tags used in this study were MK10s and large in size. These tags prematurely released, making it challenging to obtain a long duration track. However, the reduction in size of tags, the improved retention with the double attachment, has the potential to increase the days at liberty and length of the data sets acquired. To fully build a complete picture of the bluefin tuna habitat utilization of the Mediterranean and given the mixing evident of populations within the Mediterranean Sea, all future tagging should really be accompanied by other population identification technologies currently available (genetic ID of clip fins, otolith microchemistry and isotopes). Used in combination they offer the potential to finally unravel the mystery of bluefin tuna migrations and utilization of the Mediterranean Sea. The bluefin tuna patterns and population structure need to be understood in order to properly manage and conserve the species and the fishery.

Supporting Information

S1 Fig. Trajectories of all the Adriatic Sea tagged tuna analyzed in this study (Green triangle is deployment position and red triangle is the pop-off position)

https://doi.org/10.1371/journal.pone.0116638.s001

(PDF)

S2 Fig. Trajectories of all the western Mediterranean Sea tagged tuna analyzed in this study (Green triangle is deployment position and red triangle is the pop-off position).

https://doi.org/10.1371/journal.pone.0116638.s002

(PDF)

S3 Fig. Trajectories of all Corsica tagged tuna analyzed in this study (Green triangle is deployment position and red triangle is the pop-off position).

https://doi.org/10.1371/journal.pone.0116638.s003

(PDF)

S1 Table. Average, Standard Deviation, Minimum and Maximum of the daily estimated position variance for the trajectories of the four tunas that showed possible reproductive behavior in the present study.

https://doi.org/10.1371/journal.pone.0116638.s004

(DOCX)

Acknowledgments

The authors are also indebted to the many fishers and clubs that participated in the tagging effort. This includes “Confederación Española de Pesca Recreativa Responsable”, BigGame Italia, C.N. Sambenedettese and Barricata Fishing Club. We thank these owners and crew of the collaborative tagging vessels. The logistic support from the ports participating in the fishing and tagging events as well as to the collaboration of the WWF France vessel “Columbus” and its crew was appreciated. All mentioned partnerships were essential to make this tagging initiative “On the Med Tuna Trail” possible. We want also to thanks G. Urbani, D. Crepaldi, M. Castleton, E. Estess and J. Ganong, R. Kochevar, S. Wilson that provided assistance on preparing tags, data products and assistance with algorithms at different points during the project. We thank Tag A Giant, Stanford University for additional support. We would also like to thank the free availability of the altimeter products produced by Ssalto/Duacs and distributed by Aviso, with support from Cnes (http://www.aviso.oceanobs.com/duacs/).

Author Contributions

Conceived and designed the experiments: PC GQ AMB ACS SS ST BAB. Performed the experiments: PC GQ AMB ACS. Analyzed the data: PC GQ AO SS. Contributed reagents/materials/analysis tools: PC GQ AO. Wrote the paper: PC GQ AO SS AMB ACS ST BAB.

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