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Figure 5 in Distribution patterns of ocellated eagle rays, Aetobatus ocellatus, along two sites in Moorea Island, French Polynesia

Figure 5. – Percentage of observations for the ten different behaviours according to the study site: swimming, foraging, chafing, cruising, escape, pre-mating, jumping, conspecific interaction, heterospecific interaction, come-close. See Table II for details on each behaviour.

Figure 2 in Distribution patterns of ocellated eagle rays, Aetobatus ocellatus, along two sites in Moorea Island, French Polynesia

Figure 2. – Multiple Correspondence Analysis factor map (2 first components, 34.5% and 19.4%, respectively) representing the relationship between the study sites (ClubMed/Mareto), ontogenetic stage of the eagle rays (male/female/juvenile), seasons (wet/dry), and the time of the day (am/pm).

Figure 1 in Distribution patterns of ocellated eagle rays, Aetobatus ocellatus, along two sites in Moorea Island, French Polynesia

Figure 1. – Map highlighting the two study sites on Moorea Island, French Polynesia: Mareto and ClubMed.

Figure 3 in Temporal dynamics of the recruitment of glass eels in two valleys of French Polynesia (Tahiti and Moorea Islands)

Figure 3. – Annual monitoring of glass eels recruitment for each of the three species in: A: Moorea; B: Tahiti; C: Moorea and Tahiti, given in number of specimens per month.

Figure 4 in Temporal dynamics of the recruitment of glass eels in two valleys of French Polynesia (Tahiti and Moorea Islands)

Figure 4. – Composition of the recruitment of Anguilla species from Moorea and Tahiti Islands given in percent; * test chiº, p-value <0.001.

Figure 5 in Temporal dynamics of the recruitment of glass eels in two valleys of French Polynesia (Tahiti and Moorea Islands)

Figure 5. – Mean length (in mm) of the glass eel specimens at recruitment, for the three species in Moorea and Tahiti islands; * test chiº, p-value <0.001.

Figure 4 in Distribution patterns of ocellated eagle rays, Aetobatus ocellatus, along two sites in Moorea Island, French Polynesia

Figure 4. – Abundance (number of macroinvertebrate individuals) and biomass (grams) for the two study sites. The boxes represent the first and third quartiles, black lines are the medians (second quartiles), and whiskers cor- respond to the range (min-max) of the distributions. An asterisk indicates sta- tistically significant differences.

Figure 3 in Distribution patterns of ocellated eagle rays, Aetobatus ocellatus, along two sites in Moorea Island, French Polynesia

Figure 3. – Multiple Factor Analysis scatter plots (2 first components, 18% and 13%, respectively) representing the relationship between sex (male/ female/ juvenile), the site (ClubMed/Mareto) and the environmental factors: wave and wind direction (east/north/south/ west), wind speed (high/medium/low) and current strength (no/light/medium/ strong).

Figure 2 in Temporal dynamics of the recruitment of glass eels in two valleys of French Polynesia (Tahiti and Moorea Islands)

Figure 2. – Annual monitoring of glass eels recruitment in the Opunohu River on the Moorea Island and in the Vaituoru River on the Tahiti Island per year, given in number of specimens caught per day.

Figure 1 in Temporal dynamics of the recruitment of glass eels in two valleys of French Polynesia (Tahiti and Moorea Islands)

Figure 1. – Location of Opunohu's mouth in Moorea Island and Papenoo's mouth in Tahiti Island.

Acoustic recording: Pihaena (Moorea Island) January 2021

Dataset "Highlighting the resilience potential of marine protected areas in the face of coral bleaching with passive acoustic monitoring" Status: Marine Protected Area, coast: North, site: Pihaena, island: Moorea Island, depth:  10 m, position: external slope of the barrier reef, latitude: -17.4765, longitude: -149.8291, year: 2021, month: January, format: wav. The files are named DDHHMMSS (DD = day, HH = hour, MM = minutes, SS = seconds).  Sampling frequency: 44.1 kHz, type of recorder: SNAP, type of hydrophone: HTI-96, sensitivity: between -170.1 and -169.6 dB re 1 V µPa^-1, gain: between 2 and 2.05 dB, acquisition: continuously. This research is funded by two grants attributed to Xavier Raick. The first one is from the King Leopold III Fund for Nature Exploration and Conservation and the second one is from the University of Liège “financement mission scientifique”. This research is part of the project “Acoustics to Assess the Health Status of Reefs” hosted by the Ocean Decade Research Programme on the Maritime Acoustic Environment (OD-MAE) endorsed by the 2021-2030 United Nations Decade of Ocean Science for Sustainable Development (UNESCO). More information can be found in the main text and in the Supplementary Materials of the related article by Raick et al. ""Highlighting the resilience potential of marine protected areas in the face of coral bleaching with passive acoustic monitoring".

Acoustic recording: Nuarei (Moorea Island) January 2021

Dataset "Highlighting the resilience potential of marine protected areas in the face of coral bleaching with passive acoustic monitoring" Status: Marine Protected Area, coast: East, site: Nuarei, island: Moorea Island, depth:  10 m, position: external slope of the barrier reef, latitude: -17.5006, longitude: -149.7546, year: 2021, month: January, format: wav. The files are named DDHHMMSS (DD = day, HH = hour, MM = minutes, SS = seconds).  Sampling frequency: 44.1 kHz, type of recorder: SNAP, type of hydrophone: HTI-96, sensitivity: between -170.1 and -169.6 dB re 1 V µPa^-1, gain: between 2 and 2.05 dB, acquisition: continuously. This research is funded by two grants attributed to Xavier Raick. The first one is from the King Leopold III Fund for Nature Exploration and Conservation and the second one is from the University of Liège “financement mission scientifique”. This research is part of the project “Acoustics to Assess the Health Status of Reefs” hosted by the Ocean Decade Research Programme on the Maritime Acoustic Environment (OD-MAE) endorsed by the 2021-2030 United Nations Decade of Ocean Science for Sustainable Development (UNESCO). More information can be found in the main text and in the Supplementary Materials of the related article by Raick et al. ""Highlighting the resilience potential of marine protected areas in the face of coral bleaching with passive acoustic monitoring".

Acoustic recording: Temae (Moorea Island) January 2021

Dataset "Highlighting the resilience potential of marine protected areas in the face of coral bleaching with passive acoustic monitoring" Status: non Marine Protected Area, coast: East, site: Temae, island: Moorea Island, depth:  10 m, position: external slope of the barrier reef, latitude: -17.5067, longitude: -149.7600, year: 2021, month: January, format: wav. The files are named DDHHMMSS (DD = day, HH = hour, MM = minutes, SS = seconds).  Sampling frequency: 44.1 kHz, type of recorder: SNAP, type of hydrophone: HTI-96, sensitivity: between -170.1 and -169.6 dB re 1 V µPa^-1, gain: between 2 and 2.05 dB, acquisition: continuously. This research is funded by two grants attributed to Xavier Raick. The first one is from the King Leopold III Fund for Nature Exploration and Conservation and the second one is from the University of Liège “financement mission scientifique”. This research is part of the project “Acoustics to Assess the Health Status of Reefs” hosted by the Ocean Decade Research Programme on the Maritime Acoustic Environment (OD-MAE) endorsed by the 2021-2030 United Nations Decade of Ocean Science for Sustainable Development (UNESCO). More information can be found in the main text and in the Supplementary Materials of the related article by Raick et al. ""Highlighting the resilience potential of marine protected areas in the face of coral bleaching with passive acoustic monitoring".

Acoustic recording: E2B (Moorea Island) January 2021

Dataset "Highlighting the resilience potential of marine protected areas in the face of coral bleaching with passive acoustic monitoring" Status: non Marine Protected Area, coast: North, site: Entre deux baies (E2B), island: Moorea Island, depth:  10 m, position: external slope of the barrier reef, latitude: -17.4751, longitude: -149.8372 , year: 2021, month: January, format: wav. The files are named DDHHMMSS (DD = day, HH = hour, MM = minutes, SS = seconds).  Sampling frequency: 44.1 kHz, type of recorder: SNAP, type of hydrophone: HTI-96, sensitivity: between -170.1 and -169.6 dB re 1 V µPa^-1, gain: between 2 and 2.05 dB, acquisition: continuously. This research is funded by two grants attributed to Xavier Raick. The first one is from the King Leopold III Fund for Nature Exploration and Conservation and the second one is from the University of Liège “financement mission scientifique”. This research is part of the project “Acoustics to Assess the Health Status of Reefs” hosted by the Ocean Decade Research Programme on the Maritime Acoustic Environment (OD-MAE) endorsed by the 2021-2030 United Nations Decade of Ocean Science for Sustainable Development (UNESCO). More information can be found in the main text and in the Supplementary Materials of the related article by Raick et al. ""Highlighting the resilience potential of marine protected areas in the face of coral bleaching with passive acoustic monitoring".

FIGURE 11. Axianassa heardi n in Four new infaunal decapod crustaceans (Caridea: Alpheidae and Gebiidea: Axianassidae) from Lizard Island, Australia, one of them also occurring in Moorea, French Polynesia

FIGURE 11. Axianassa heardi n. sp., holotype, male from Lizard Island, Australia (QM W29049): A, third maxilliped, lateral; B, same, detail of crista dentata, mesial; C, major cheliped, mesial; D, same, lateral; E, same, fingers of chela (setae omitted); F, minor cheliped, lateral; G, second pereiopod, lateral; H, third pereiopod, lateral; I, fifth pereiopod, lateral.

FIGURE 7. Athanopsis saurus n in Four new infaunal decapod crustaceans (Caridea: Alpheidae and Gebiidea: Axianassidae) from Lizard Island, Australia, one of them also occurring in Moorea, French Polynesia

FIGURE 7. Athanopsis saurus n. sp., holotype, male from Lizard Island, Australia (QM W29048): A, second pereiopod, lateral; B, third pereiopod, lateral; C, same, distal merus, carpus, propodus and dactylus; D, fourth pereiopod, lateral; E, fifth pereiopod, lateral; F, same, distal carpus, propodus and dactylus, mesial.

FIGURE 4. Athanas daviei n in Four new infaunal decapod crustaceans (Caridea: Alpheidae and Gebiidea: Axianassidae) from Lizard Island, Australia, one of them also occurring in Moorea, French Polynesia

FIGURE 4. Athanas daviei n. sp., holotype, male from Lizard Island, Australia (QM W29047): A, major cheliped, mesial; B, same, lateral; C, same, carpus and chela, mesial (extensor view); D, minor cheliped, mesial; E, same, lateral; F, second pereiopod, lateral; G, third pereiopod, lateral; H, same, distal propodus and dactylus; I, fifth pereiopod, lateral.

FIGURE 10. Axianassa heardi n in Four new infaunal decapod crustaceans (Caridea: Alpheidae and Gebiidea: Axianassidae) from Lizard Island, Australia, one of them also occurring in Moorea, French Polynesia

FIGURE 10. Axianassa heardi n. sp., holotype, male from Lizard Island, Australia (QM W29049): A, mandible, lateral; B, same, mesial; C, maxillule, lateral; D, maxilla, lateral; E, same, endopod, mesial view; F, first maxilliped, lateral; G, same, mesial; H, second maxilliped, lateral.

FIGURE 9. Axianassa heardi n in Four new infaunal decapod crustaceans (Caridea: Alpheidae and Gebiidea: Axianassidae) from Lizard Island, Australia, one of them also occurring in Moorea, French Polynesia

FIGURE 9. Axianassa heardi n. sp., holotype, male from Lizard Island, Australia (QM W29049): A, general lateral view of carapace and abdomen; B, frontal region, dorsal (left antennule regenerating); C, same, lateral; D, rostrum and eyestalks, lateral; E, same, dorsal; F, antennal acicle, dorsal; G, uropod, dorsal; H, same, detail of posterior portion of exopod (setae omitted); I, telson, dorsal.