A strong behavioural plasticity is commonly evidenced in the movements of marine megafauna species, and it might be related to an adaptation to local conditions of the habitat. One way to investigate such behavioural plasticity is to satellite track a large number of individuals from contrasting foraging grounds, but despite recent advances in satellite telemetry techniques, such studies are still very limited in sea turtles.
From 2010 to 2018, 49 juvenile green turtles were satellite tracked from five contrasting feeding grounds located in the South-West Indian Ocean in order to (1) assess the diel patterns in their movements, (2) investigate the inter-individual and inter-site variability, and (3) explore the drivers of their daily movements using both static (habitat type and bathymetry) and dynamic variables (daily and tidal cycles).
Despite similarities observed in four feeding grounds (a diel pattern with a decreased distance to shore and smaller home ranges at night), contrasted habitats (e.g. mangrove, reef flat, fore-reef, terrace) associated with different resources (coral, seagrass, algae) were used in each island.
Juvenile green turtles in the South-West Indian Ocean show different responses to contrasting environmental conditions - both natural (habitat type and tidal cycle) and anthropogenic (urbanised vs. uninhabited island) demonstrating the ability to adapt to modification of habitat.
During their life, animals spend a considerable amount of time on the move . The purposes of movement can vary between species and the various stages of the life cycle, for example long-distance migration to daily foraging movements. Among the multiple causes of daily movements, the search for food and predator avoidance have been largely documented in terrestrial animals [2,3,4,5,6]. For instance, elk move to protective cover of wooded areas when wolves are present . Similarly, Courbin et al.  have shown that zebras exhibit a diel migration strategy associated with a particular habitat (vegetation cover at night) to adjust their behaviour to lions’ presence, and therefore reduce the encounter rate with their predator. Diel migrations in the marine realm have also been documented in a large range of marine species, from plankton [8, 9], seals [10, 11], cetaceans [12, 13], fish  to sea turtles [15,16,17,18,19].
Using satellite telemetry, such day-night differences have been recently observed in sea turtles. The tracking of loggerhead turtles suggested that these diel patterns might be driven by differences in resource availability (e.g. food vs. nocturnal refuges), competition or exploratory movements . Similarly, sub-adult hawksbill turtles tracked along Florida exhibited day-night patterns, using restricted home ranges at night, likely as refuges . Like their conspecific, a recent study showed a diel pattern in adult green turtles movements as they reduced their activity and home range size at night . Given that sea turtles rely on visual cues to forage and detect predators , this nocturnal behaviour is likely associated with resting and/or a predator avoidance strategy, whereas larger home ranges with higher activity levels during day-time may correspond to a foraging activity [15, 23, 24].
Although some behavioural similarities can be observed between individuals from the same species, a wide variation in plasticity responses is commonly evidenced in sea turtles [25,26,27,28,29,30,31,32], and is revealed by contrasting diet [33,34,35], diving behaviour [25, 26], spatial dynamics [20, 28, 31] or habitat used [25, 36]. For example, adult female green, loggerhead and leatherback turtles explore different habitats during their post-nesting migration, using both neritic and oceanic environments [27, 31, 37]. Similarly, juvenile green turtles from the Atlantic spread in different directions to reach distinct foraging grounds . The reasons for such a plasticity are still unclear, but may be related to the individual’s personality , a genetic diversity  or an adaptation to local conditions of the habitat .
To investigate the behavioural plasticity of sea turtles, this project satellite tracked a large number of juvenile green turtles (n = 49) from contrasting foraging grounds located in the South-West Indian Ocean (SWIO). The feeding grounds differed in terms of environmental conditions, e.g. bathymetry, bottom substrate, tidal cycle. The green turtle of the SWIO occupies a large geographical range, including important nesting sites on isolated French territories (Europa, Mayotte, Tromelin and Grande Glorieuse) [39,40,41,42,43,44], together with some foraging grounds used by both adults and juveniles [45, 46]. The present study aimed at (1) assessing the diel patterns in their movements in contrasting environments, (2) investigating the inter-individual and inter-site variability, and (3) exploring the drivers of their daily movements using both static (seafloor habitat and bathymetry) and dynamic variables (daily and tidal cycles). (i) It was expected that juvenile green turtles would exhibit day-night patterns, using restricted home ranges at night; (ii) individual variations in plasticity is also expected with turtles from the same island selecting different habitats; (iii) it was assumed that a strong inter-site variability would be found, with different habitat features used on each study site. It was felt that the fine-scale mapping of the seafloor habitats of each study site would help in understanding how this species may adapt its behaviour in response to a variety of local conditions, both natural (e.g. mangrove, lagoon) and anthropogenic (e.g. urbanised vs. uninhabited island).
The large study region spreads from 40 to 55°E and from 11 to 22°S, and is located in scattered French overseas territories of the South-West Indian Ocean, including three French Scattered Islands (Europa, Glorieuses and Juan de Nova), and two Departments (Mayotte and La Reunion) – See Fig. 1. The five study sites differ in terms of anthropogenic pressure as Mayotte and La Reunion are inhabited islands with a developed tourist activity, whereas the three remaining islands (Europa, Glorieuses and Juan de Nova) are uninhabited areas being only a temporary home to French military personnel and scientists.
Between 2010 and 2018, 49 juvenile green turtles were caught and satellite tagged in Europa (n = 11), Glorieuses (n = 10), Juan de Nova (n = 9), Mayotte (n = 9) and La Reunion (n = 10) – See Fig. 1. In-water turtles were captured in shallow waters by rodeo from a boat or by hand (when animals were resting in pools) , or scuba diving in deep waters. Once captured, standard morphometric data were recorded for each individual. The curved carapace length (CCL) was measured from the anterior point at midline (nuchal scute) to the posterior notch at midline between the supracaudals , and body mass was taken using an electronic dynamometer. Each turtle was photo-identified according to the method developed by Jean et al. (2010) . Argos-Fastloc GPS tags (Wildlife Computers Redmond, WA, USA) that provide Fastloc-GPS data relayed via the Argos satellite system (http://www.argos-system.org/) were then fixed on each juvenile green turtle. In order to increase the number of positions recorded, the Fastloc GPS tags were programmed to record GPS locations at a sampling interval set at 30 min.
Due to the restricted dispersal pattern commonly observed in juvenile green turtles in their coastal habitats and the large uncertainties associated with Argos locations, only Fastloc locations were retained for the analysis to improve the quality of the results and provide reliable kernel estimates . The Fastloc-GPS data were filtered to reduce measurement errors by removing locations with residuals values above 35  and locations recorded by less than five satellites . We restricted our dataset to positions associated with a travel speed lower than 5 km.h− 1 . Finally, remaining positions located on land were discarded, representing between 2 and 17% of the dataset. To investigate diel movement patterns, locations were assigned as either day-time or night-time (using the suncalc package in R) that provides precise local time of sunrise and sunset.
Home range analysis
To investigate the residency pattern of the turtles, locate the high-use areas and estimate their home range size, a kernel utilisation density approach was used . The use of the reference bandwidth parameter href as smoothing parameter generally results in over-smoothing the data . Conversely, a bandwidth that minimises the least-square cross validation score (hlscv) often under-smoothes location data . To prevent over and under-smoothing, we therefore used a visual ad hoc approach previously applied to terrestrial animals [55, 56]. We first calculated the reference bandwidth parameter href for each turtle. Then, href was sequentially reduced in 0.10 increment (0.9 href, 0.8 href, 0.7 href, …) until 0.1 href, and the most appropriate smoothing parameter was chosen visually by comparing the kernel density to the original location data . Using this method, one kernel density was estimated for each individual and each day phase (day vs. night). The areas covered by the diurnal and nocturnal home ranges (50% contour, ) were then estimated for each individual using the adehabitatHR package. Individuals tracked for less than 10 days were discarded from the kernel analysis.
Kernel density estimates are known to be sensitive to sampling regime (i.e. tracking duration and number of locations recorded) . To address these potential bias and allow a comparison of kernel areas across individuals, we performed two sensitivity analyses to assess the potential influence of (i) the tracking duration and (ii) the number of locations on kernel estimates. Firstly, kernel areas (diurnal and nocturnal, separately) were calculated individually for different timeframes, i.e. every 30 d from 30 to 630 d. Secondly, kernel areas (diurnal and nocturnal, separately) were calculated individually for different numbers of locations selected randomly over the entire tracking length of each individual, i.e. every 10, 20, 50, 100, 150, 200, 350, 500, 700, 1000, 1500, 2000 and 2750 locations. The calculated areas were then compared using correlation matrices for each study site and each day phase.
Four environmental variables (both static and dynamic) were used to investigate the drivers of the turtles’ coastal movements:
Influence of depth: the fine-scale bathymetry (spatial resolution from 1 m to 5 m, up to a depth of 40 m) was first extracted at each turtle position using the Litto3D product provided by the SHOM (Service Hydrographique et Océanographique de la Marine, http://www.shom.fr/les-activites/projets/modele-numerique-terre-mer/couverture/ocean-indien/).
Influence of the distance to shore: using maps of each island shoreline, the shortest distance between each turtle location and the coastline was also calculated.
Influence of the seafloor habitats: maps of the seafloor habitats available (characterised by their geomorphology, dominant benthic communities, roughness and exposition) were generated for all sites except Juan de Nova (data unavailable) . A total of 11 habitats was identified on the four sites (see Additional file 6: Figure S6):
Lagoonal terrace (hereafter called “Terrace”),
Unexposed fore-reef (“Fore-reef”),
Exposed fore-reef (“E. fore-reef”),
Exposed fore-reef with high complexity (“C. fore-reef”),
Unexposed reef flat (“Reef flat”),
Exposed reef flat (“E. reef flat”),
Fore-reef and reef patch of terrace (“Reef patch”),
Blind pass (“Pass”),
Influence of the tides: tidal cycles (e.g. tidal height) were calculated for every 10 min at the location of each study site from the SHOM database. Then a sea height value was attributed to each turtle’s location according to the corresponding tidal time previously extracted at the study site.
Habitat selection analysis
Habitat use and habitat selection were assessed by compositional analysis using the adehabitatHS package . To take into account the potential diel pattern, the analysis was conducted separately for the diurnal and nocturnal habitats. The habitat available was defined as the habitat located within the Maximum Convex Polygon (95% MCP) of all turtles of each study site, and it was calculated for day and night positions using the adehabitatHR package. The habitat used corresponded to the individual 50% kernel contours calculated during day and night for each turtle (the individuals kept for the kernel analysis, n = 48). By quantifying the ratio of the used against the available habitat , selection ratios were computed for each site and each time of the day to assess the habitat affinities according to day-time and night-time (e.g. feeding during the day vs. resting at night).
To investigate the inter-site and inter-individual variabilities, several Multiple Analysis of Variance (MANOVA) were tested using R by taking different dependent (DVs) and independent variables (IVs). (1) To test if turtles from the same island behaved differently, we tested for each site, the turtle ID as IV, and 5 DVs: bathymetry, sea height, habitat type, distance to shore and phase of the day. (2) To test if the turtles from different islands showed distinct behaviours, we performed a MANOVA with the site as IV and four DVs: bathymetry, sea height, distance to shore and phase of the day. (3) To test behavioural differences between day and night, we run MANOVA for each site, taking the phase of the day as IV and four DVs: bathymetry, sea height, habitat type and distance to shore. (4) Finally, to investigate which environmental predictor influenced the most the behaviour of the turtles, we performed MANOVAs for each site, taking alternatively the habitat type, bathymetry, sea height and distance to shore as IVs, and the geographical coordinates as DVs.
To investigate the diel pattern and the effect of tides on turtle movements, we constructed a series of Generalised Additive Mixed Models (GAMMs) using the mgcv package in R . The distance to shoreline was used as a response variable and a scat distribution was applied to the models to deal with the heavy tailed data. One model was run for each of the five study sites. Turtle ID was used as a random effect and therefore added as an explanatory variable. To reduce autocorrelation, the dataset was subsampled every 2 to 6 locations, and autocorrelation was then tested using the acf function in R. Two environmental predictors were used: time of the day and tidal height. Due to its circular distribution, a cyclic cubic regression spline (type “cc” in mgcv package) was used for the response variable. The predictors were first tested for collinearity using the Variance Inflation Factor (below three). Models with all possible combinations were then computed, and the models were compared based on the Akaike Information Criterion (AIC). The model residuals (QQ-plot and histogram) were then checked for normality to validate the most parsimonious model. When necessary, the response variable was log-transformed to make residuals homogeneous.
General tracking data
After filtering, a total of 49 juvenile green turtles were satellite tracked in Europa (n = 11), Glorieuses (n = 10), Juan de Nova (n = 9), Mayotte (n = 9) and La Reunion (n = 10), representing a large dataset of 20,277 GPS locations used in the analysis (Additional file 7: Table S1). The number of GPS locations per individual varied between 13 (#112120 in Europa) and 2723 (#32899c in La Reunion). The turtles measured on average (±SD) 59.8 ± 8.1 cm CCL and weighed 25.8 ± 10.8 kg. The tracking duration was on average 136 ± 104 days (range: 6–627 d). Among the 49 tracked individuals, only two turtles tagged in Europa (#32874b and # 32905b) left the island to reach the West coast of Madagascar whereas the 47 other turtles remained close to their release point (Additional file 1: Figure S1). The two turtles that departed remained in Europa waters for 92 (#32874b) and 68 days (# 32905b) respectively before leaving the island.
Among the 49 individuals tracked, 1 turtle was discarded from the kernel analysis due to a short tracking duration (< 20 d, #112120). The remaining turtles (n = 48) dispersed in shallow waters at all sites, rarely exceeding the 10 m isobaths (Fig. 2). Turtles dispersed much more in Glorieuses and Juan de Nova than in the three other sites. All the individuals except two, remained inside Europa’s mangrove. In Mayotte and La Reunion, the turtles also showed limited displacements. Both sensitivity analyses showed very limited influence on either the tracking length (Additional file 2: Figure S2), or the number of locations on the kernel estimation for all sites (Additional file 3: Figure S3). Indeed, the correlation matrices calculated for day and night indicated a strong correlation between the kernel areas of different tracking lengths (mean correlation coefficient ± SD: 0.96 ± 0.5) and number of locations (mean correlation coefficient ± SD: 0.93 ± 0.09).
Numerous high-use areas were identified showing a small proportion of overlap between individuals (Fig. 2). Except in Europa and in the East of Glorieuses (main island, Fig. 2a, b, c, d), where most of the high-use areas overlapped between day and night, a diel pattern was observed in the movements of the majority of the individuals in all study sites. In Mayotte, most of the turtles remained between the coastline and the 10 m isobaths, and in shallower waters during the day (Fig. 2g, h). The opposite pattern was observed in La Reunion, where the turtles concentrated their activity in deeper waters during the day, and remained in shallower waters (< 10 m deep) closer to shore at night (Fig. 2i, j).
The home ranges were relatively small for all sites (mean: 0.21 ± 0.27 km2, Fig. 3), but some differences were observed between sites and individuals. Except in Europa, the area covered by the 50% kernel contour was smaller at night. However, it was significant for Glorieuses (Wilcoxon test, p < 0.05) and Mayotte (Wilcoxon test, p < 0.01), whereas no significant difference was observed in Juan de Nova (Wilcoxon test, p = 0.0976), Europa (Wilcoxon test, p = 0.3750) and La Reunion (Wilcoxon test, p = 0.0839). A strong inter-individual plasticity was observed when looking at the areas used by the turtles during day and night (Fig. 3). For example, in Juan de Nova, the individual kernel areas ranged between 0.2 (#121820) and 1.3 km2 (#147154) – See Fig. 3d.
Distance to shore
For all sites, a diel pattern was observed in terms of distance to shore. Except for Mayotte, the distance to shore was shorter at night than during day-time (Fig. 4). This difference was significant for Mayotte (Wilcoxon test, V = 8, p < 0.05) and La Reunion (Wilcoxon test, V = 55, p < 0.005). A strong inter-individual plasticity was observed when looking at the average distance to shore (Additional file 4: Figure S4). For example, in Glorieuses, the average distance to shore calculated for each turtle ranged between 0.24 (#152022) and 4.31 km (#152026) – See Fig. 4b and Additional file 4: Figure S4.
The results from the GAMMs confirmed the strong relationship between the distance to shore and the time of the day for all sites (Fig. 5a, c, e, g, i). Except in Mayotte, the distance to shore increased during day-time, and decreased at night. Conversely, the turtles were closer to shore during day-time in Mayotte, being however further off the shoreline at noon (Fig. 5g). The explained deviances ranged from 18% in Mayotte to 57% in La Reunion, and the selected models contained both time of the day and tidal height as explanatory variables. For all sites, distance to shore decreased with increasing tidal height, in relation to tidal cycles. The GAMMs also showed a negative relationship between distance to shore and tidal height (Fig. 5b, d, f, h, j).
The bathymetry extracted at the turtles’ locations ranged from 0.5 to 37 m deep (Additional file 5: Figure S5). Turtles mainly used shallow habitats, with mean depths ranging from 1.5 m in Europa to a maximum of 7.5 m in La Reunion. Differences were observed between day and night, with shallower depths used at night for all sites but Mayotte. However, this diel pattern was only significant in Glorieuses (Wilcoxon test, V = 53, p < 0.05) and La Reunion (Wilcoxon test, V = 55, p < 0.005). Unlike the four other sites, the bathymetry used by the turtles decreased during the day in Mayotte and increased at night (Wilcoxon test, V = 3, p < 0.005). A strong inter-individual plasticity was observed when looking at the bathymetry associated with each individual’s location (Additional file 5: Figure S5). For example, in La Reunion, the average bathymetry extracted for each turtle ranged between 2.0 (#169516) and 13.6 m (#169513).
Regarding the seafloor habitat available, the habitats are illustrated in Additional file 6: Figure S6. Seagrass was common to Glorieuses, Mayotte and La Reunion, Exposed reef flat to Europa, Glorieuses and La Reunion, and Terrace to Europa, Glorieuses and Mayotte.
In Europa, the home ranges were mainly located on the Terrace, which was the most selected habitat, regardless the time of the day (Fig. 6a and Additional file 6: Figure S6a). Only two turtles used the Exposed reef flat and the Complex fore-reef.
In Glorieuses, individuals used three major habitats (Fore-reef, Reef flat and Seagrass), but no significant difference was observed between day and night (Fig. 6b and Additional file 6: Figure S6b, d). A large inter-individual variability was also observed based on large standard errors (Fig. 6b).
In Mayotte, the dominant habitat selected during day-time was Seagrass, whereas the Reef patch was preferred at night (Fig. 6c and Additional file 6: Figure S6c). Only two individuals also used the Seagrass at night.
In La Reunion, the habitat Pass was largely selected during both day and night (Fig. 6d and Additional file 6: Figure S6d). However, the turtles also used the Seagrass at night, located closer to shore.
The inter-individual and inter-site variabilities in terms of habitat used were confirmed by the MANOVA analysis. Individuals from the same island (turtle ID as IV) selected different habitats (DVs), i.e. bathymetry, sea height, seafloor substrate and distance to shore (MANOVA, p < 0.001). Similarly, turtles from different sites (site as IV) selected different habitats (DVs, MANOVA, p < 0.001). Also, the use of distinct diurnal and nocturnal habitats (phase of the day as IV) was evidenced for all sites (geographic coordinates as DVs, MANOVA, p < 0.001). Finally, except sea height, all environmental variables (IVs) had a significant effect on turtle distribution (geographic coordinates as DVs) at all sites (MANOVA, p < 0.001).
By compiling a large dataset of 49 juvenile green turtles satellite tracked in the South-West Indian Ocean from five contrasting feeding grounds, this study sheds light on the diel patterns movements and inter-individual and inter-site plasticity of this species. The analysis of the turtle locations (n = 20,277) in relation to their fine-scale habitat types (seafloor habitat, bathymetry and tidal height) enabled the characterisation of their (i) diurnal and (ii) nocturnal habitats, highlighting a pronounced behavioural plasticity.
The long tracking duration (mean ± SD: 136 ± 104 days) and the small home ranges (mean ± SD: 0.18 ± 0.25 km2) found in this study confirmed the strong site fidelity of juvenile green turtles to their developmental habitats, regardless of the foraging ground. Turtles limited their movements by remaining particularly close to their release positions. These results are in agreement with previous studies conducted in the Caribbean [24, 62,63,64,65,66], Atlantic [17, 67, 68], and to a lesser extent in the Mediterranean Sea  and Pacific . Kernel density estimates are known to be sensitive to sampling regime, via the number of locations and tracking duration that vary among individuals . The normal method to give the same weight to all individuals is to average the dataset to daily locations . Such procedure is inappropriate when looking at very fine scale movements (~tens of meters) in relation to habitat features, as it could have generated erroneous positions associated with wrong habitats. The sensitivity analysis performed in this study to test for a series of different tracking lengths confirmed that a nonhomogeneous sampling does not necessarily impact kernel estimations, making comparisons across turtles reliable. Similarly, the second sensitivity analysis conducted on different number of locations supported the comparison of the kernel areas across individuals. For these reasons, these kernel estimates provide a reliable indication of the core activity of diurnal and nocturnal sites used by this species and the associated habitat selected, and such a complete approach for tracking studies when using kernel densities is recommended.
The areas covered by the home ranges differed between day and night, with globally larger home ranges during day-time. Such diel patterns have also been documented in other sea turtle species, including the loggerhead and the hawksbill, and might be partly driven by differences in resource availability (food vs. nocturnal refuges) [20, 21]. In Mayotte, the strong overlap between the diurnal locations of the turtles and seagrass beds confirmed previous results , as the turtles exploited the seagrass meadow during the day. In Glorieuses, sparse seagrass patches (occur in some areas of the reef flat) and a large seagrass bed (located several kilometres away from the island) were used by only three individuals. If these individuals do feed on such seagrass species, it suggests a trade-off between the energy gain by consuming seagrass and the energy loss of travelling towards this specific habitat. Such inter-individual variability could also be due to intra-specific competition, as evidence by Dujon et al. . This large and dense seagrass bed is composed of only one species (Thalassodendron ciliatum [58, 70]), which is not usually consumed by green turtles , suggesting a generalist rather than a specialist behaviour and the use of alternative resources. Immature green turtles could therefore preferentially select seagrass beds when they are sufficiently abundant-accessible, and contain the preferred species; alternatively they would target substitute habitats.
The distance to shore also varied between diurnal and nocturnal habitats, with generally the use of deeper habitats farther from shore during the day. Although three different patterns were observed in Mediterranean loggerhead turtles, most of the tracked individuals in this study also used night-time sites closer to shore , likely as refuges from predators. In the foraging ground close to urbanised zones of La Reunion, the turtles favoured the slope located outside the lagoon during the day. Such diel pattern could be a strategy to avoid human disturbance during day-time , forcing the turtles to leave the lagoon in response to seaside tourism. While this human avoidance tactic could be reliable in La Reunion due to the intense leisure activity [72,73,74], this strategy is not adopted in Mayotte, despite significant human activities. The net energy gain induced by feeding on the large seagrass meadow located in the nearshore waters of Mayotte might counterbalance the disturbance caused by tourists. In contrast, the scarcity of such resources inside the lagoon of La Reunion (e.g. small patches of the monospecific seagrass beds Syringodium occur, but there is neither algae nor coral) may explain the aggregation of the turtles away from the shore during the day. During day-time, turtles from La Reunion select the habitat Pass, likely to transit easily between the outer core and the inner core of the lagoon from diurnal to nocturnal sites, and for cleaning, feeding on corals or resting in caves . A similar pattern was observed in loggerhead turtles tracked in the Mediterranean Sea , since some individuals used distinct day and night refuges with minimal overlap.
Unlike the four other foraging grounds, Europa was the only site where no difference in terms of home range size was observed between day and night. The particular geomorphology of the island (i.e. a semi-closed mangrove) providing simultaneously a shelter from predators and food resources might remove the necessity to shift between resting and foraging habitats. The use of overlapping day and night sites might increase feeding efficiency while minimising energy expenditure , and this strategy has already been observed in juvenile green turtles in Florida  and loggerhead turtles in the Mediterranean Sea .
Mangroves are complex ecosystems where juvenile green turtles have been observed feeding on leaves, propagules and fruit [33, 34, 47, 77,78,79]. Mangroves have been observed serving as nurseries for dolphins Southern of Brazil , as a result of an abundance in nutrients, fishes, crustaceans and algae [81, 82], while providing a refuge from predators. Despite mangroves in Europa serving as an alternative food supply, the resource might be less nutritiously and energetically less profitable than in the other sites, leading to slower growth rates , and making the turtles leave this feeding ground earlier than might be expected. The departure of two individuals that reached the west coast of Madagascar after spending only 2 to 3 months around the island lends some credence to this hypothesis. The smaller size of the individuals regularly measured in Europa (Bourjea, personal communications) compared to those of Glorieuses also suggests that the habitat found in Europa’s mangrove might be less profitable. The large size and diversity of habitats available in Glorieuses compared to Europa might also explain the strong inter-individual variability and the use of multiple habitats.
The turtles tracked in this study used smaller habitats at night in all study sites, which reinforces the hypothesis that sea turtles decrease their activity during night-time [15, 17, 84]. Such behaviour has also been observed in other species such as the loggerhead [20, 85] and the hawksbill [21, 86], suggesting a tactic to reduce predation risk , as turtles generally rest close to reef structures where they can find shelter in small caves and under reef ledges [17, 87]. This is probably the case in La Reunion , Glorieuses and Mayotte (Ballorain, personal communication), where many juvenile turtles are commonly observed resting in small caves. The question of the impact of predation has lately been addressed as one of the key questions in megafauna movement ecology , but remains poorly documented for sea turtles. To confirm if predation risk is a key factor in turtle movements in such islands, it will be necessary to conduct a dedicated study including direct observations of the relationship between sharks and green turtles, with some emphasis on corticosterone measurements (i.e. stress hormone).
In Mayotte, such a pattern was confirmed by the use of the Reef patch at night. The lengthy and deep resting dives recorded at night on coral and rocky habitats by adult green turtles in Mayotte  suggest a similar behaviour to that adopted by the juveniles in the same foraging ground. Although sea turtles rely mainly on visual cues to feed, some scattered records observed at night on the seagrass beds of La Reunion and Mayotte suggest that they could also feed during night-time, confirming strong behavioural plasticity. Unlike the stable and relatively static seafloor habitats (e.g. reefflat, slope), the dynamic seagrass beds might influence differently across years the habitat selected by the turtles. This is particularly true in La Reunion where the small patches of seagrass located on the reefflat are gradually disappearing over time, explaining why individuals tracked from 2018 (n = 4) selected less seagrass at night. Influenced by the moonlight, adult green turtles have already been observed feeding during full moon in Mayotte [19, 89], but no such relationship could be confirmed in this study. Both the spatial and temporal fine-scale behaviour of these individuals needs to be further investigated using time-depth recorders and cameras to develop a better understanding of the feeding activity in relation to the associated habitat.
As with similar studies on green turtles from Mexico and the Chagos Archipelago, nocturnal habitats were mostly located closer to land [15, 18]. The opposite behaviour observed in Mayotte (in deeper waters at night) might be driven by turtle’s buoyancy. Previous studies have demonstrated that long resting dives in sea turtles might be achieved by reaching neutral buoyancy at a certain depth (~ 19 m) both to reduce energy expenditure and perform longer dives [90, 91]. Such behaviour may be adopted by juvenile green turtles in Mayotte.
The tidal cycle might also explain turtle movements, forcing individuals to move away from the shoreline at low tides as some areas might become inaccessible. Given the negative relationship between distance to shore and tidal height, such hypothesis was supported in all sites. During periods of strong tidal coefficient in all islands (except La Reunion which has a small tidal range < 1 m), the area of the available habitat can be considerably reduced. Such occasional phenomena explains the erratic movements of some individuals from Europa that travelled outside the mangrove due to a lack of water in the inner core of the island. Similarly, movements away from shoreline were observed in Glorieuses, Juan de Nova and Mayotte, coinciding with the decreasing sea level induced by the tidal cycle. Remaining in close proximity to the tidal flow could also provide more opportunities to catch prey, especially those trapped due to water movements or benthic animals that emerge at rising tides. During flood tides, the water is generally more turbid, and using these turbid waters could be used by turtles as a tactic to avoid predators.
Although similarities in terms of movements were observed between the five foraging grounds, it is also worth mentioning the strong inter-site and inter-individual variability. The high degree of plasticity in sea turtles’ movements and home ranges has already been recorded in numerous studies [17, 89, 92,93,94], but this is the first time such plasticity has been demonstrated by a meta-analysis of juvenile green turtles’ movements tracked from five contrasted sites from the same Regional Management Unit . Inter-individual variability could be attributed to both intrinsic (e.g. level of experience, personality, metabolism rate, competition) and extrinsic factors (e.g. environmental perturbations, resource availability, predation). The contrasted habitats and associated resources observed at the five sites also contribute to this variability, and may reveal some dietary adaptations. The green turtle is known to have an omnivorous diet at this stage, feeding either on animal matter (e.g. cephalopods , gelatinous zooplankton [34, 35]), marine angiosperms (seagrass [96,97,98] or algae [33, 77, 99]). Stable isotope analysis should be conducted in the near future to investigate the diet of these juvenile green turtles at their foraging grounds, which may provide crucial information explaining the variability in their movements and habitat use. Investigating simultaneously the growth rate, the energy and nutrient content of the resources available and the quantities consumed in each habitat could provide an indication of the drivers of this behavioural plasticity.
Availability of data and materials
Data sharing not applicable to this article as no datasets were generated or analysed during the current study. If you do not wish to publicly share your data, please write: “Please contact author for data requests.
Akaike Information Criterion
Curved Carapace Length
Generalised Additive Model
Global Positioning System
- h lscv :
Least-square cross validation smoothing parameter
- h ref :
Reference bandwidth smoothing parameter
Maximum Convex Polygon
Service hydrographique et océanographique de la marine
Hansson L-A, Åkesson S. Animal movement across scales. UK: Oxford University Press; 2014.
Creel S, Winnie J, Maxwell B. Elk alter habitat selection as an antipredator response to wolves. Ecology. 2005;86:3387–97.
Davidson Z, Valeix M, Loveridge AJ, Hunt JE, Johnson PJ, Madzikanda H, et al. Environmental determinants of habitat and kill site selection in a large carnivore: scale matters. J Mammal. 2012;93:677–85.
Roberts C, Cain J, Cox R. Identifying ecologically relevant scales of habitat selection: diel habitat selection in elk. Ecosphere. 2017;8:e02013.
Vennen LMV, Patterson BR, Rodgers AR, Moffatt S, Anderson ML, Fryxell JM. Diel movement patterns influence daily variation in wolf kill rates on moose. Funct Ecol. 2016;30:1568–73.
Courbin N, Loveridge AJ, Macdonald DW, Fritz H, Valeix M, Makuwe ET, et al. Reactive responses of zebras to lion encounters shape their predator–prey space game at large scale. Oikos. 2016;125:829–38.
Courbin N, Loveridge AJ, Fritz H, Macdonald DW, Patin R, Valeix M, et al. Zebra diel migrations reduce encounter risk with lions at night. J Anim Ecol. 2019;88:92–101.
Benoit-Bird KJ, Au WWL. Extreme diel horizontal migrations by a tropical nearshore resident micronekton community. Mar Ecol Prog Ser. 2006;319:1–14.
Hays GC. A review of the adaptive significance and ecosystem consequences of zooplankton diel vertical migrations. In: Jones MB, Ingólfsson A, Ólafsson E, Helgason GV, Gunnarsson K, Svavarsson J, editors. Migrations and dispersal of marine organisms. Netherlands: Springer; 2003. p. 163–70.
Crawford JA, Frost KJ, Quakenbush LT, Whiting A. Seasonal and diel differences in dive and haul-out behavior of adult and subadult ringed seals (Pusa hispida) in the Bering and Chukchi seas. Polar Biol. 2019;42:65–80.
Horning M, Trillmich F. Lunar cycles in diel prey migrations exert a stronger effect on the diving of juveniles than adult Gal pagos fur seals. Proc R Soc Lond Ser B Biol Sci. 1999;266:1127–32.
Nuuttila HK, Bertelli CM, Mendzil A, Dearle N. Seasonal and diel patterns in cetacean use and foraging at a potential marine renewable energy site. Mar Pollut Bull. 2018;129:633–44.
Schaffeld T, Bräger S, Gallus A, Dähne M, Krügel K, Herrmann A, et al. Diel and seasonal patterns in acoustic presence and foraging behaviour of free-ranging harbour porpoises. Mar Ecol Prog Ser. 2016;547:257–72.
Clark CW, Levy DA. Diel vertical migrations by juvenile sockeye Salmon and the Antipredation window. Am Nat. 1988;131:271–90.
Christiansen F, Esteban N, Mortimer JA, Dujon AM, Hays GC. Diel and seasonal patterns in activity and home range size of green turtles on their foraging grounds revealed by extended Fastloc-GPS tracking. Mar Biol. 2016;164:10.
MacDonald BD, Madrak SV, Lewison RL, Seminoff JA, Eguchi T. Fine scale diel movement of the East Pacific green turtle, Chelonia mydas, in a highly urbanized foraging environment. J Exp Mar Biol Ecol. 2013;443:56–64.
Makowski C, Seminoff JA, Salmon M. Home range and habitat use of juvenile Atlantic green turtles (Chelonia mydas L.) on shallow reef habitats in Palm Beach, Florida, USA. Mar Biol. 2006;148:1167–79.
Seminoff JA, Jonnes T. Diel movements and activity ranges of green turtles (Chelonia mydas) at a temperate foraging area in the Gulf of California, Mexico. Herpetol Conserv Biol. 2006;1:81–6.
Ballorain K, Bourjea J, Ciccione S, Kato A, Hanuise N, Enstipp M, et al. Seasonal diving behaviour and feeding rhythms of green turtles at Mayotte Island. Mar Ecol Prog Ser. 2013;483:289–302.
Dujon AM, Schofield G, Lester RE, Papafitsoros K, Hays GC. Complex movement patterns by foraging loggerhead sea turtles outside the breeding season identified using Argos-linked Fastloc-global positioning system. Mar Ecol. 2018;39:e12489.
Wood LD, Brunnick B, Milton SL. Home range and movement patterns of subadult Hawksbill Sea turtles in Southeast Florida. J Herpetol. 2016;51:58–67.
Heithaus M, Frid A, Dill L. Shark-inflicted injury frequencies, escape ability, and habitat use of green and loggerhead turtles. Mar Biol. 2002;140:229–36.
Bjorndal KA. Nutrition and grazing behavior of the green turtle Chelonia mydas. Mar Biol. 1980;56:147–54.
Ogden JC, Robinson L, Whitlock K, Daganhardt H, Cebula R. Diel foraging patterns in juvenile green turtles (Chelonia mydas L.) in St. Croix United States virgin islands. J Exp Mar Biol Ecol. 1983;66:199–205.
Hays GC, Glen F, Broderick AC, Godley BJ, Metcalfe JD. Behavioural plasticity in a large marine herbivore: contrasting patterns of depth utilisation between two green turtle (Chelonia mydas) populations. Mar Biol. 2002;141:985–90.
Hays GC, Houghton JDR, Isaacs C, King RS, Lloyd C, Lovell P. First records of oceanic dive profiles for leatherback turtles, Dermochelys coriacea, indicate behavioural plasticity associated with long-distance migration. Anim Behav. 2004;67:733–43.
Richardson PB, Broderick AC, Coyne MS, Ekanayake L, Kapurusinghe T, Premakumara C, et al. Satellite telemetry reveals behavioural plasticity in a green turtle population nesting in Sri Lanka. Mar Biol. 2013;160:1415–26.
Schofield G, Katselidis KA, Dimopoulos P, Pantis JD, Hays GC. Behaviour analysis of the loggerhead sea turtle Caretta caretta from direct in-water observation. Endanger Species Res. 2006;2:71–9.
Schofield G, Hobson VJ, Lilley MKS, Katselidis KA, Bishop CM, Brown P, et al. Inter-annual variability in the home range of breeding turtles: implications for current and future conservation management. Biol Conserv. 2010;143:722–30.
Rees AF, Al-Kiyumi A, Broderick AC, Papathanasopoulou N, Godley BJ. Conservation related insights into the behaviour of the olive ridley sea turtle Lepidochelys olivacea nesting in Oman. Mar Ecol Prog Ser. 2012;450:195–205.
Luschi P, Mencacci R, Cerritelli G, Papetti L, Hochscheid S. Large-scale movements in the oceanic environment identify important foraging areas for loggerheads in Central Mediterranean Sea. Mar Biol. 2017;165:4.
Chambault P, de Thoisy B, Huguin M, Martin J, Bonola M, Etienne D, et al. Connecting paths between juvenile and adult habitats in the Atlantic green turtle using genetics and satellite tracking. Ecol Evol. 2018;8:12790–802.
Carrión-Cortez JA, Zárate P, Seminoff JA. Feeding ecology of the green sea turtle (Chelonia mydas) in the Galapagos Islands. J Mar Biol Assoc U K. 2010;90:1005–13.
Amorocho DF, Reina RD. Feeding ecology of the East Pacific green sea turtle Chelonia mydas agassizii at Gorgona National Park, Colombia. Endanger Species Res. 2007;3:43–51.
González Carman V, Botto F, Gaitán E, Albareda D, Campagna C, Mianzan H. A jellyfish diet for the herbivorous green turtle Chelonia mydas in the temperate SW Atlantic. Mar Biol. 2014;161:339–49.
Dalleau M, Benhamou S, Sudre J, Ciccione S, Bourjea J. The spatial ecology of juvenile loggerhead turtles (Caretta caretta) in the Indian Ocean sheds light on the “lost years” mystery. Mar Biol. 2014;161:1835–49.
Chambault P, Roquet F, Benhamou S, Baudena A, Pauthenet E, de Thoisy B, et al. The Gulf stream frontal system: a key oceanographic feature in the habitat selection of the leatherback turtle? Deep-Sea Res I Oceanogr Res Pap. 2017;123:35–47.
Griffin LP, Brownscombe JW, Gagné TO, Wilson ADM, Cooke SJ, Danylchuk AJ. Individual-level behavioral responses of immature green turtles to snorkeler disturbance. Oecologia. 2017;183:909–17.
Bourjea J, Lapègue S, Gagnevin L, Broderick D, Mortimer JA, Ciccione S, et al. Phylogeography of the green turtle, Chelonia mydas, in the Southwest Indian Ocean. Mol Ecol. 2007;16:175–86.
Dalleau M, Ciccione S, Mortimer JA, Garnier J, Benhamou S, Bourjea J. Nesting phenology of marine turtles: insights from a regional comparative analysis on green turtle (Chelonia mydas). PLoS One. 2012;7:e46920.
Lauret-Stepler M, Bourjea J, Roos D, Pelletier D, Ryan PG, Ciccione S, et al. Reproductive seasonality and trend of Chelonia mydas in the SW Indian Ocean: a 20 yr study based on track counts. Endanger Species Res. 2007;3:217–27.
Le Gall JY, Taquet M, Cluet D, Biais G. Caractéristiques topographiques et thermiques d’un site de ponte majeur de la tortue verte Chelonia mydas dans l’ocean indien Sud-ouest: Europa. Mésogée. 1988;48:43–9.
Ballorain K. Ecologie trophique de la tortue verte Chelonia mydas dans les herbiers marins et algueraies du sud-ouest de l’océan Indien [Internet]: CNRS-IPHC, Kélonia, Ifremer, Université de La Réunion; 2010. Available from: https://tel.archives-ouvertes.fr/tel-00576264/. [cited 2019 Jul 19]
Roos D, Pelletier D, Ciccione S, Taquet M, Hughes G. Aerial and snorkelling census techniques for estimating green turtle abundance on foraging areas: a pilot study in Mayotte Island (Indian Ocean). Aquat Living Resour. 2005;18:193–8.
Bourjea J, Ciccione S, Lauret-Stepler M, Marmoex C, Jean C. Les îles Éparses : vingt-cinq ans de recherche sur les tortues marines. Bull Soc Herp Fr. 2011;139:95–111.
Ballorain K, Ciccione S, Bourjea J, Grizel H, Enstipp M, Georges J-Y. Habitat use of a multispecific seagrass meadow by green turtles Chelonia mydas at Mayotte Island. Mar Biol. 2010;157:2581–90.
Limpus C. Mangroves in the diet of Chelonia mydas in Queensland, Australia. Mar Turt Newsl. 2000;89:13–5 Available from: http://www.seaturtle.org/mtn/archives/mtn89/mtn89p13.shtml?nocount. [cited 2019 May 13].
Eckert KL, Bjorndal K, Abreu-Grobois FA, Donnelly M. Factors to consider in the tagging of sea turtles. Research and management techniques for the conservation of sea turtles; 1999.
Jean C, Ciccione S, Talma S, Ballorain K, Bourjea J. Photo-identification method for green and hawksbill turtles-first results from Reunion. Indian Ocean Turtle Newsl. 2010;11:8–13.
Thomson JA, Börger L, Christianen MJA, Esteban N, Laloë J-O, Hays GC. Implications of location accuracy and data volume for home range estimation and fine-scale movement analysis: comparing Argos and Fastloc-GPS tracking data. Mar Biol. 2017;164:204.
Dujon AM, Lindstrom RT, Hays GC. The accuracy of Fastloc-GPS locations and implications for animal tracking. Methods Ecol Evol. 2014;5:1162–9.
Worton BJ. Kernel methods for estimating the utilization distribution in home-range studies. Ecology. 1989;70:164–8.
Kie JG. A rule-based ad hoc method for selecting a bandwidth in kernel home-range analyses. Anim Biotelem. 2013;1:13.
Kie JG, Matthiopoulos J, Fieberg J, Powell RA, Cagnacci, Mitchell MS, et al. The home-range concept: are traditional estimators still relevant with modern telemetry technology? Philos Trans R Soc B Biol Sci. 2010;365:2221–31.
Berger KM, Gese EM. Does interference competition with wolves limit the distribution and abundance of coyotes? J Anim Ecol. 2007;76:1075–85.
Jacques CN, Jenks JA, Klaver RW. Seasonal movements and home-range use by female pronghorns in sagebrush-steppe communities of Western South Dakota. J Mammal. 2009;90:433–41.
Börger L, Franconi N, Michele GD, Gantz A, Meschi F, Manica A, et al. Effects of sampling regime on the mean and variance of home range size estimates. J Anim Ecol. 2006;75(6):1393-1405.
Chabanet P. Suivi et inventaire des récifs coralliens des îles Eparses et de Mayotte. Programme SIREME, Coordination IRD, Rapport pour le compte des TAAF, du department de Mayotte. La Réunion: Agence Française pour le Développement et l’Union européenne; 2017.
Calenge C. The package “adehabitat” for the R software: a tool for the analysis of space and habitat use by animals. Ecol Model. 2006;197:516–9.
Manly BF, McDonald L, Thomas DL, McDonald TL, Erickson WP. Resource selection by animals: statistical design and analysis for field studies: Springer Science & Business Media; 2007.
Manly BFJ, McDonald LL, and Thomas DL. Resource selection by animals: statistical design and analysisfor field studies. New York: Chapman and Hall;1993.
Brill RW, Balazs GH, Holland KN, Chang RKC, Sullivan S, George JC. Daily movements, habitat use, and submergence intervals of normal and tumor-bearing juvenile green turtles (Chelonia mydas L.) within a foraging area in the Hawaiian islands. J Exp Mar Biol Ecol. 1995;185:203–18.
Fuentes MMPB, Gillis AJ, Ceriani SA, Guttridge TL, Van Zinnicq Bergmann MPM, Smukall M, et al. Informing marine protected areas in Bimini, Bahamas by considering hotspots for green turtles (Chelonia mydas). Biodivers Conserv. 2019;28:197–211.
Meylan PA, Meylan AB, Gray JA. The ecology and migrations of sea turtles 8. Tests of the developmental habitat hypothesis. Bull Am Mus Nat Hist. 2011;2011:1–70.
Wildermann NE, Sasso CR, Stokes LW, Snodgrass D, Fuentes MMPB. Habitat use and behavior of multiple species of marine turtles at a foraging area in the Northeastern Gulf of Mexico. Front Mar Sci. 2019;6 Available from: https://www.frontiersin.org/articles/10.3389/fmars.2019.00155/full. [cited 2019 Apr 26].
Lamont MM, Fujisaki I, Stephens BS, Hackett C. Home range and habitat use of juvenile green turtles (Chelonia mydas) in the northern Gulf of Mexico. Anim Biotelem. 2015;3:53.
Godley BJ, Lima EHSM, Åkesson S, Broderick AC, Glen F, Godfrey MH, et al. Movement patterns of green turtles in Brazilian coastal waters described by satellite tracking and flipper tagging. Mar Ecol Prog Ser. 2003;253:279–88.
Hart KM, Fujisaki I. Satellite tracking reveals habitat use by juvenile green sea turtles Chelonia mydas in the Everglades, Florida, USA. Endanger Species Res. 2010;11:221–32.
Naro-Maciel E, Arengo F, Galante P, Vintinner E, Holmes KE, Balazs G, et al. Marine protected areas and migratory species: residency of green turtles at Palmyra Atoll, Central Pacific. Endanger Species Res. 2018;37:165–82.
Ballorain K, Dedeken M. Rapport de mission PANAMAG 1 – Volet Herbiers marins du Parc naturel marin des Glorieuses: PNMG/AAMP/TAAF; 2016.
Balazs GH, Forsyth R, Kam A. Preliminary assessment of habitat utilization by Hawaiian green turtles in their resident foraging pastures. Washington, DC: NOAA Tech Memo NMFS-SWFC-71. US Dep Comm; 1987.
David G, Antona M, Botta A, Daré W, Denis J, Durieux L, et al. La gestion intégrée du littoral récifal de la Réunion : de la connaissance scientifique à l’action publique, jeux d’échelles et jeux d’acteurs. Agir ensemble pour le littoral : mobilisations scientifiques pour le renouvellement des politiques publiques. 2009. Available from: http://agritrop.cirad.fr/544039/. [cited 2019 Jun 27].
Lemahieu A. Fréquentation et usages littoraux dans la Réserve Naturelle Marine de la Réunion : élaboration d’un suivi pour l’analyse des dynamiques spatio-temporelles et apports de l’outil à la gestion et la recherche interdisciplinaire. 2015. Available from: http://www.theses.fr/s90296. [cited 2019 Jun 27].
Mirault E, David G. Estimation des valeurs socio-économiques des récifs coralliens de l’île de la Réunion. St Denis de la Réunion: IRD/DIREN/IFRECOR/UE; 2006.
IRD La Réunion. Rapport scientifique final du programme CHARC: Etude du comportement des requins bouledogue (Carcharhinus leucas) et tigre (Galeocerdo cuvier) à La Réunion: La Réunion; 2015. p. 1–132.
Jadot C, Donnay A, Acolas ML, Cornet Y, Bégout Anras ML. Activity patterns, home-range size, and habitat utilization of Sarpa salpa (Teleostei: Sparidae) in the Mediterranean Sea. ICES J Mar Sci. 2006;63:128–39.
López-Mendilaharsu M, Gardner SC, Seminoff JA, Riosmena-Rodriguez R. Identifying critical foraging habitats of the green turtle (Chelonia mydas) along the Pacific coast of the Baja California peninsula, Mexico. Aquat Conserv Mar Freshwat Ecosyst. 2005;15:259–69.
Nagaoka SM, Martins AS, dos Santos RG, Tognella MMP, de Oliveira Filho EC, Seminoff JA. Diet of juvenile green turtles (Chelonia mydas) associating with artisanal fishing traps in a subtropical estuary in Brazil. Mar Biol. 2012;159:573–81.
Pendoley K, Fitzpatrick J. Browsing of mangroves by green turtles in Western Australia. Mar Turt Newsl. 1999;84:10 Available from: http://www.seaturtle.org/mtn/archives/mtn84/mtn84p10.shtml. [cited 2019 May 13].
Flores P a C, Bazzalo M. Home ranges and movement patterns of the marine tucuxi dolphin, Sotalia fluviatilis, in Baía Norte, southern Brazil. Lat Am J Aquat Mamm. 2004;3:37–52.
Cannicci S, Burrows D, Fratini S, Smith TJ, Offenberg J, Dahdouh-Guebas F. Faunal impact on vegetation structure and ecosystem function in mangrove forests: a review. Aquat Bot. 2008;89:186–200.
Nagelkerken I, Blaber SJM, Bouillon S, Green P, Haywood M, Kirton LG, et al. The habitat function of mangroves for terrestrial and marine fauna: a review. Aquat Bot. 2008;89:155–85.
Derville S. Ecology and reproductive behaviour of the Green turtle, Chelonia mydas, in the South Western Indian Ocean: Ecole Normale Supérieure de Lyon; 2013.
Crear DP, Lawson DD, Seminoff JA, Eguchi T, LeRoux RA, Lowe CG. Habitat use and behavior of the East Pacific Green Turtle, Chelonia mydas, in an Urbanized System. SOCA. 2017;116:17–32.
Snape RTE, Bradshaw PJ, Broderick AC, Fuller WJ, Stokes KL, Godley BJ. Off-the-shelf GPS technology to inform marine protected areas for marine turtles. Biol Conserv. 2018;227:301–9.
Chevis MG, Godley BJ, Lewis JP, Lewis JJ, Scales KL, Graham RT. Movement patterns of juvenile hawksbill turtles Eretmochelys imbricata at a Caribbean coral atoll: long-term tracking using passive acoustic telemetry. Endanger Species Res. 2017;32:309–19.
Hazel J, Lawler IR, Hamann M. Diving at the shallow end: Green turtle behaviour in near-shore foraging habitat. J Exp Mar Biol Ecol. 2009;371:84–92.
Hays GC, Ferreira LC, Sequeira AMM, Meekan MG, Duarte CM, Bailey H, et al. Key questions in marine megafauna movement ecology. Trends Ecol Evol. 2016;31:463–75.
Taquet C, Taquet M, Dempster T, Soria M, Ciccione S, Roos D, et al. Foraging of the green sea turtle Chelonia mydas on seagrass beds at Mayotte Island (Indian Ocean), determined by acoustic transmitters. Mar Ecol Prog Ser. 2006;306:295–302.
Hays GC, Adams CR, Broderick AC, Godley BJ, Lucas DJ, Metcalfe JD, et al. The diving behaviour of green turtles at Ascension Island. Anim Behav. 2000;59:577–86.
Minamikawa S, Naito Y, Sato K, Matsuzawa Y, Bando T, Sakamoto W. Maintenance of neutral buoyancy by depth selection in the loggerhead turtle Caretta caretta. J Exp Biol. 2000;203:2967–75.
Bjorndal KA, Bolten AB, Chaloupka M, Saba VS, Bellini C, Marcovaldi MAG, et al. Ecological regime shift drives declining growth rates of sea turtles throughout the West Atlantic. Glob Chang Biol. 2017;23:4556–68.
Hazel J, Hamann M, Lawler IR. Home range of immature green turtles tracked at an offshore tropical reef using automated passive acoustic technology. Mar Biol. 2013;160:617–27.
Seminoff JA, Resendiz A, Nichols WJ. Home range of green turtles Chelonia mydas at a coastal foraging area in the Gulf of California, Mexico. Mar Ecol Prog Ser. 2002;242:253–65.
Wallace BP, DiMatteo AD, Hurley BJ, Finkbeiner EM, Bolten AB, Chaloupka MY, et al. Regional management units for marine turtles: a novel framework for prioritizing conservation and research across multiple scales. PLoS One. 2010;5:e15465.
Gama LR, Domit C, Broadhurst MK, Fuentes MMPB, Millar RB. Green turtle Chelonia mydas foraging ecology at 25°S in the western Atlantic: evidence to support a feeding model driven by intrinsic and extrinsic variability. Mar Ecol Prog Ser. 2016;542:209–19.
Fuentes MMPB, Lawler IR, Gyuris E. Dietary preferences of juvenile green turtles (Chelonia mydas) on a tropical reef flat. Wildl Res. 2007;33:671–8.
Guebert-Bartholo FM, Barletta M, Costa MF, Monteiro-Filho ELA. Using gut contents to assess foraging patterns of juvenile green turtles Chelonia mydas in the Paranaguá Estuary, Brazil. Endanger Species Res. 2011;13:131–43.
Reisser J, Proietti M, Sazima I, Kinas P, Horta P, Secchi E. Feeding ecology of the green turtle (Chelonia mydas) at rocky reefs in western South Atlantic. Mar Biol. 2013;160:3169–79.
The analyses were carried out within the framework of the NEXT project with the support of IFREMER, CNRS-IPHC, Institut Océanographique de Monaco, Fondation Albert Ier and the Prince of Monaco. The study was also part of the following projects: DYMITILE, DYMATURE, PANAMAG, HATOCAM, EFEHMAR-ECOTOM, and CHARC carried out by IFREMER, Kelonia, AFB/PNMG-PNMM, CEDTM, and IRD. This study was also carried out within the framework of the « National Action Plan for Sea Turtles in the French territories of the south-west Indian Ocean ». Figure 2 was produced using Sentinel 2 imagery from ESA remote sensing data. The authors also thank the logistical support of Escale, Jardin Maore, OceanObs, Antsiva, and to the staff of the Délégation Océan Indien of IFREMER. We are also grateful to the French Southern and Antarctic Lands (TAAF) for the logistical support and permits to conduct the fieldwork on the Eparses Islands, to Simon Benhamou, Pascal Lazure and Annie Fiandrino for their help on the analyses. We finally thank Georges Hughes for his valuable help on the English proofreading.
The study was financed by IFREMER, DEAL La Réunion, DEAL Mayotte, Institut Océanographique de Monaco, French Biodiversity Agency (Mayotte Marine Nature Park, Glorieuses Marine Nature Park), CEDTM, Kelonia, Conseil Régional de La Réunion, IFRECOR, BNOI/ONCFS, Fondation Crédit Agricole, IRD and the French Ministry. PC was funded by IFREMER and Institut Océanographique de Monaco.
Ethics approval and consent to participate
This study meets the legal requirements of the French territories where this work was carried out, and follows all institutional guidelines. The protocol was approved by the “Conseil National de la Protection de la Nature” (CNPN, http://www.conservation-nature.com) and the French Ministry of Ecology acting as an ethics committee in French territories. The committee reference numbers were the following: the project DYMITILE in Europa (n°2010–83 du 03/09/2010), the project DYMATURE in Juan de Nova (n°2015–24), the project PANAMAG in Glorieuses (n°2015–98), the projects CHARC (n°19/12/2012) and HATOCAM (n° 2017–01) in La Reunion, and the project EFEHMAR-ECOTOM in Mayotte (n°199/DEAL/SEPR/2012, 01/DEAL/SEPR/2015 and 049/DEAL/SEPR/2016).
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The authors declare that they have no competing interests.
Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.
GPS locations on (a) Europa, (b) Glorieuses, (c) Juan de Nova, (d) Mayotte and (e) La Reunion. Red dots refer to release locations. (f) Migratory movements of two individuals that left Europa.
Correlation matrices of the kernel areas tested for different tracking durations during day (left) and night (right) in (a, b) Europa, (c, d) Glorieuses, (e, f) Juan de Nova, (g, h) Mayotte and (i, j) La Reunion. Tracking durations are numbers in red.
Correlation matrices of the kernel areas tested for different number of locations during day (left) and night (right) in (a, b) Europa, (c, d) Glorieuses, (e, f) Juan de Nova, (g, h) Mayotte and (i, j) La Reunion. Locations numbers are numbers in red.
Box plots of the distance to shore extracted at each turtle location showing the inter-individual variability.
Box plots of the bathymetry extracted at each turtle location showing the inter-individual variability.
Maps of the seafloor habitats in (a) Europa, (b) Glorieuses, (c) Mayotte and (d) La Reunion. Habitat available are illustrated by the MCP (dotted black lines) and the individual habitat used by the red (diurnal) and blue (nocturnal) contours.
Summary of the data collected from the 49 juvenile green turtles satellite tracked. N refers to the total number of GPS locations retained for the analysis.
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Chambault, P., Dalleau, M., Nicet, JB. et al. Contrasted habitats and individual plasticity drive the fine scale movements of juvenile green turtles in coastal ecosystems. Mov Ecol 8, 1 (2020). https://doi.org/10.1186/s40462-019-0184-2