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Fig. 3 in A new species of Quadrivisio (Amphipoda, Maeridae) from coastal tropical lagoons (Benin, West Africa)

Fig. 3. Quadrivisio laleyei sp. nov. A., C. Holotype, ♂, 7.5 mm, MNHN IU-2017-209, gnathopod. B., D. Paratype, ♀, 7.0 mm, MNHN IU-2017-211, gnathopod.

Fig. 2 in A new species of Quadrivisio (Amphipoda, Maeridae) from coastal tropical lagoons (Benin, West Africa)

Fig. 2. Quadrivisio laleyei sp. nov., ♂, holotype, 7.5 mm, MNHN IU-2017-209. A. Habitus (scale 1). B. Lower lip (scale 3). C. First antenna (scale 2). D. Second antenna (scale 2). E. Left mandible (scale 4). F. Maxilliped palp (scale 3).

Fig. 5 in A new species of Quadrivisio (Amphipoda, Maeridae) from coastal tropical lagoons (Benin, West Africa)

Fig. 5. Quadrivisio laleyi sp. nov. A–D., F. Holotype, ♂, 7.5 mm, MNHN IU-2017-209. E. Paratype, ♀, 7.0 mm, MNHN IU-2017-211. A. Male uropod 1 (scale 1). B. Male uropod 2 (scale 1). C. Male urosome (scale 1). D. Male uropod 3 (scale 1). E. Female uropod 3 (scale 1). F. Male telson (scale 2).

Fig. 4 in A new species of Quadrivisio (Amphipoda, Maeridae) from coastal tropical lagoons (Benin, West Africa)

Fig. 4. Quadrivisio laleyi sp. nov. A–B., D–E. Holotype, ♂, 7.5 mm, MNHN IU-2017-209. C. Paratype, ♂, 7.6 mm, MNHN IU-2017-210. A. Pereopod 3. B. Pereopod 4. C. Pereopod 5. D. Pereopod 6. E. Pereopod 7.

opencc-by-4.0May 2016View details →

Figure 2 in Carbon primary sources and estuarine habitat use by two congeneric ariid catfishes in a subtropical coastal lagoon

Figure 2. Carbon isotope ratios (d13C) and total length (TL, mm) of individuals of Genidens genidens (closed circles) and Genidens barbus (open circles) collected in the interface between the estuarine and freshwater zones of Patos Lagoon in present study. DISCUSSION According to the model of the life cycle suggested by ARAúJO (1988), G. barbus move between freshwater to the estuary during their first year of life. After reaching sexual maturity, adults migrate to the ocean, returning to freshwater to spawn. Our work with stable isotopes corroborates the general movement pattern proposed in this model by providing evidence that the primary producers at the estuary are an important source of carbon for juveniles of G. barbus during the initial phase of their development. There is no current model describing the life cycle of G. genidens at the Patos Lagoon. ARAúJO (1988) mentioned that this species remains in the upper limit of the estuarine zone or in the limnetic portion of the lagoon and that its juveniles are occasionally found in the estuary. Based on fish sampling restricted to the mixohaline zone of the Patos Lagoon, some authors classified this species as estuarine resident (CHAO et al. 1985, ARAúJO 1988). However, VIEIRA et al. (2010) demonstrated that G. genidens occurs from the estuary to the uppermost northern portion of the lagoon, which is located ~180 km from the lagoon's connection with the sea, and can remain year round at freshwater. Our work provides new evidence that this catfish species derives energy from the estuarine and freshwater zones of

opencc-by-4.0Sep 2017View details →

Figure 2 in Impacts of environmental factors on zooplankton taxonomic diversity in coastal lagoons in Turkey

Figure 2. Venn diagram showing identified zooplankton taxa distribution and number of taxa (in parentheses) in the lagoons.

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Figure 1 in Assessment of the zooplankton community structure of the coastal Uzungöl Lagoon (Kızılırmak Delta, Turkey) based on community indices and physicochemical parameters

Figure 1. Geographical location of study area, coordinates of sampling points. Station 1: 41°32'33.85"N - 36°04'56.80"E; Station 2: 41°33'36.66"N - 36°05'22.24"E; Station 3: 41°34'11.10"N - 36°05'40.67"E; Station 4: 41°34'44.82"N - 36°06'0.14"E; Station 5: 41°35'7.57"N - 36° 06'20.14"E.

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Figure 6 in Assessment of the zooplankton community structure of the coastal Uzungöl Lagoon (Kızılırmak Delta, Turkey) based on community indices and physicochemical parameters

Figure 6. Zooplankton community indices (Shannon Diversity, Pielou evenness and Species richness) during the study period.

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Figure 3 in Assessment of the zooplankton community structure of the coastal Uzungöl Lagoon (Kızılırmak Delta, Turkey) based on community indices and physicochemical parameters

Figure 3. Seasonal density (ind. m -3) changes of nauplii larvae and copepodit individuals in Uzungöl Lagoon.

Fig. 2 in Temporal dynamics of species associations in the parasite community of European eels, Anguilla anguilla, from a coastal lagoon

Fig. 2. Intensity of infection (mean ± SE number of parasites per host, including infected hosts only) of the six most common helminth parasites of eels, Anguilla anguilla, in Comacchio Lagoons, during three sampling periods. Graphs on the right-hand side do not include the 2015–2017 period, as these species were not found during that period. See Table 1 for full species names.

Fig. 4 in Temporal dynamics of species associations in the parasite community of European eels, Anguilla anguilla, from a coastal lagoon

Fig. 4. Pairwise relationships between numbers of parasites per host for the three most common digenean parasites of eels, Anguilla anguilla, in Comacchio Lagoons, across all three sampling periods combined. The line represents the relationship (with 95% confidence intervals) predicted by the generalized linear model; see text. Tick marks indicate partial residuals with either positive (top) or negative values (bottom). See Table 1 for full species names.

Fig. 3 in Temporal dynamics of species associations in the parasite community of European eels, Anguilla anguilla, from a coastal lagoon

Fig. 3. Scatterplots of pairwise relationships between numbers of parasites per host for the three most common digenean parasites of eels, Anguilla anguilla, in Comacchio Lagoons, across all three sampling periods combined. See Table 1 for full species names.

Fig. 1 in Temporal dynamics of species associations in the parasite community of European eels, Anguilla anguilla, from a coastal lagoon

Fig. 1. Abundance (mean number of parasites per host, including non-infected hosts) of the six most common helminth parasites of eels, Anguilla anguilla, in Comacchio Lagoons, during three sampling periods: 2005–2006 (N = 140 eels), 2010–2013 (N = 131), and 2015–2017 (N = 30). Note that some values for the time period 2015–2017 are based on very few fish; see Table 1 for actual numbers and for full species names.

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Fig. 3 in Effect of vegetation and abiotic factors on the abundance and population structure of Crocodylus acutus (Cuvier, 1806) in coastal lagoons of Colima, Mexico

Fig. 3. Dendrogram considering the crocodiles observed, water salinity, temperature, depth, and the four vegetation types present. Acronym definitions and characteristics of the sites are given in Table 1.

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Fig. 1 in Effect of vegetation and abiotic factors on the abundance and population structure of Crocodylus acutus (Cuvier, 1806) in coastal lagoons of Colima, Mexico

Fig. 1. Selected sites in the study area. Acronym definitions and characteristics of the sites are given in Table 1.

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Fig. 2 in Effect of vegetation and abiotic factors on the abundance and population structure of Crocodylus acutus (Cuvier, 1806) in coastal lagoons of Colima, Mexico

Fig. 2. Non-metric Multidimensional Scaling (NMDS) analysis showing the formation of two groups, by taking into account the crocodiles observed, water salinity, temperature, depth, and the four vegetation types present. Acronym definitions and characteristics of the sites are given in Table 1.

Fig. 7. A and B in Reproduction of Brevoortia aurea (Spix & Agassiz, 1829) (Actinopterygii: Clupeidae) in the Mar Chiquita Coastal Lagoon, Buenos Aires, Argentina

Fig. 7. A and B: Batch fecundity as a function of total weight (without ovary) and total length, respectively. C and D: Relative fecundity as a function of total weight (without ovary) and total length respectively.

Fig. 4 in Reproduction of Brevoortia aurea (Spix & Agassiz, 1829) (Actinopterygii: Clupeidae) in the Mar Chiquita Coastal Lagoon, Buenos Aires, Argentina

Fig. 4. Monthly relative frequency of the different gonadal development stages observed in females of Brevoortia aurea on the annual cycle, and the added samples of October and November for the Mar Chiquita coastal lagoon.

Fig. 8 in Reproduction of Brevoortia aurea (Spix & Agassiz, 1829) (Actinopterygii: Clupeidae) in the Mar Chiquita Coastal Lagoon, Buenos Aires, Argentina

Fig. 8. Proportion of mature individuals observed for each length classes of Brevoortia aurea. Females (black circles, dotted line) L 50 = 27.77 cm, N = 588. Males (white circles, solid line) L 50 = 26.59 cm, N = 293.

Fig. 2 in Reproduction of Brevoortia aurea (Spix & Agassiz, 1829) (Actinopterygii: Clupeidae) in the Mar Chiquita Coastal Lagoon, Buenos Aires, Argentina

Fig. 2. Captures per unite effort (CPUE kg/h), temperature (°C) and salinity (psu) obtained for Brevoortia aurea during sampled period in Mar Chiquita Coastal Lagoon.