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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.

FIG. 1. — Michelopagurus tangaloa n in A new species of the hermit crab genus Michelopagurus McLaughlin, 1997 (Crustacea: Decapoda: Paguridae) from Moorea, French Polynesia

FIG. 1. — Michelopagurus tangaloa n. sp., holotype ♂ 2.7 mm, Moorea, French Polynesia (MNHN IU-2013-5647 ex UF23537): A, shield and cephalic appendages, dorsal view; B, left antennal peduncle, lateral view; C, basis and ischium with crista dentata of left third maxilliped, inner view; D, sternite XII (of third pereopods), ventral view; E, sternite XIV and coxae of fifth pereopods with sexual tubes, ventral view; F, telson, dorsal view. Scale bars: A, 1 mm; B-F, 0.5 mm.

FIG. 3. — Michelopagurus tangaloa n in A new species of the hermit crab genus Michelopagurus McLaughlin, 1997 (Crustacea: Decapoda: Paguridae) from Moorea, French Polynesia

FIG. 3. — Michelopagurus tangaloa n. sp., holotype ♂ 2.7 mm, Moorea, French Polynesia (MNHN IU–2013–5647 ex UF23537): A, right second pereopod, lateral view; B, dactyl of same, mesial view; C, right third pereopod, lateral view; D, dactyl of same, mesial view; E, propodus and dactyl of left fourth pereopod, lateral view. Scale bars: A-D, 1 mm; E, 0.5 mm.

FIG. 4. — Michelopagurus tangaloa n in A new species of the hermit crab genus Michelopagurus McLaughlin, 1997 (Crustacea: Decapoda: Paguridae) from Moorea, French Polynesia

FIG. 4. — Michelopagurus tangaloa n. sp., 1 ♀ 3.1 mm, Moorea, French Polynesia (USNM 1253315 ex UF 23526), freshly collected specimen removed from housing, dorsal view.

FIG. 2. — Michelopagurus tangaloa n in A new species of the hermit crab genus Michelopagurus McLaughlin, 1997 (Crustacea: Decapoda: Paguridae) from Moorea, French Polynesia

FIG. 2. — Michelopagurus tangaloa n. sp., holotype ♂ 2.7 mm, Moorea, French Polynesia (MNHN IU–2013–5647 ex UF23537), chelipeds: A, right, dorsal view; B, left, dorsal view; C, D, carpus and chela of same in lateral (C) and mesial (D) views. Scale bar: 1 mm.

Figure 10. - Different fish abundance dynamic profiles between 1983 and 2014 in Long term monitoring of coral and fish assemblages (1983-2014) in Tiahura reefs, Moorea, French Polynesia

Figure 10. - Different fish abundance dynamic profiles between 1983 and 2014 on the outer slope at Tiahura sector in Moorea.

Figure 6 in Long term monitoring of coral and fish assemblages (1983-2014) in Tiahura reefs, Moorea, French Polynesia

Figure 6. - Commercial fish abundance at Tiahura sector in Moorea for the barrier reef and outer slope. Second-degree polynomial models were fitted to data (*: 0.01 <p ≤ 0.05, **: 0.001 <p≤ 0.01).

Figure 4 in Long term monitoring of coral and fish assemblages (1983-2014) in Tiahura reefs, Moorea, French Polynesia

Figure 4. - Total fish abundance at Tiahura sector in Moorea for the fringing reef. Second degree polynomial models were fitted to data (*: 0.01 <p ≤ 0.05, **: 0.001 <p ≤ 0.01).

Figure 9 in Long term monitoring of coral and fish assemblages (1983-2014) in Tiahura reefs, Moorea, French Polynesia

Figure 9. - Herbivorous fish species richness at Tiahura sector in Moorea for the three habitats. Linear models were fitted to data (**: 0.001 <p ≤ 0.01; ***: p ≤ 0.001).

Figure 5 in Long term monitoring of coral and fish assemblages (1983-2014) in Tiahura reefs, Moorea, French Polynesia

Figure 5. - Total fish species richness at Tiahura sector in Moorea for the fringing reef. Linear models were fitted to data (***: p ≤ 0.001).

Figure 8 in Long term monitoring of coral and fish assemblages (1983-2014) in Tiahura reefs, Moorea, French Polynesia

Figure 8. - Herbivorous fish abundance at Tiahura sector in Moorea for the barrier reef and outer slope. Linear models were fitted to data (**: 0.001 <p ≤ 0.01).

Figure 3 in Long term monitoring of coral and fish assemblages (1983-2014) in Tiahura reefs, Moorea, French Polynesia

Figure 3. - Temporal dynamics in coral percentage cover on the outer slope of Tiahura sector from 1979 to 2011. Stars denote the five main disturbances that affected the reef over the study period (COTS: Acanthaster planci outbreak). Dotted lines correspond to linear interpolation of coral percentage cover.

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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.