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Fig. 4 in The role of vegetated areas on fish assemblage of the Paraná River floodplain: effects of different hydrological conditions

Fig. 4. NMDS ordination of dominant fish for different hydrologic condition (HW = high water, FW receding water, IS isolation) and sites (S). Ope = Odontostilbe pequira, Cvo = Cyphocharax voga, Spi = Serrapinnus calliurus, Abi = Astyanax bimaculatus, Pli = Prochilodus lineatus, Mdi = Moenkhausia dichroura, Gba = Gymnogeophagus balzanii, Rbo = Roeboides microlepis, Opa = Odontostilbe paraguayensis, Dte = Diapoma terofali.

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Fig. 2 in The role of vegetated areas on fish assemblage of the Paraná River floodplain: effects of different hydrological conditions

Fig. 2. Water level fluctuations of the Paraná River at Corrientes between 1997 and 2001. The Sites were connected with the Paraná River above the hydrological level indicated by the horizontal lines. The number of flooding days (in parentheses) indicates the connectivity between the floodplain and the river channel.

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Fig. 3 in The role of vegetated areas on fish assemblage of the Paraná River floodplain: effects of different hydrological conditions

Fig. 3. Cluster analysis based on Jaccard distance (UPGMA method) of fish assemblages in the seven floodplain lakes. A. March 1999 (after a long lasting inundation phase of the Paraná River), B-September 1999 (at receding water) and C- February 2000 (during isolation).

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Figure 1 in Species richness of urban and rural fish assemblages in the Grijalva Basin floodplain, southern Gulf of Mexico

Figure 1. – Map of the study area in the floodplain of the Grijalva Basin. Sampling sites (ID), 1 = Gordiano, 2 = La Pólvora, 3 = Ilusiones, 4 = Costeñito and 5 = Loma de Caballo urban lagoons (circles); 6 = Campo, 7 = Manguito, 8 = Pucté, 9 = Maluco and 10 = Playa de Poza rural lagoons (stars); and 11 = González, 12 = Carrizal, 13 = Grijalva, 14 = Pichucalco and 15 = Samaria rivers (triangles) in rural sites. MR = Mezcalapa River; MvR = Mezcalapa Viejo River. Map modified of http:// antares.inegi.org.mx/analisis/red_ hidro/SIATL/#

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Figure 2 in On the occurrence of Spirogyra maxima (Zygnematophyceae) in the Upper PArAná River floodplAin

Figure 2. Spirogyra maxima (Hassall) Wittrock. A. Vegetative filament; B. Vegetative cell with detail for the terminal walls; C. Detail showing the conjugation tube formed by both gametangia; D. Filaments with scaraliform conjugation. Bars = 50µm.

Fig. 10 in Pools and rapids as spawning and nursery areas for fish in a river stretch without floodplains

Fig. 10. Canonical correlation analysis relating the abundance of the different larval stages from October 2011 to March 2012. Eggs: eggs; LY: larval yolk; PF: preflexion; F: flexion; PosF: postflexion.

Fig. 9 in Pools and rapids as spawning and nursery areas for fish in a river stretch without floodplains

Fig. 9. Average density ± standard error of the different larval stages captured in the rapids and pool environments of the Peixe River. Period from October 2011 to March 2012. Larval stages: Preflexion (a), Flexion (b) and Postflexion (c).

Fig. 7 in Pools and rapids as spawning and nursery areas for fish in a river stretch without floodplains

Fig. 7. Average density ± standard deviation of the spatiotemporal distribution of benthic organisms captured in the rapids and pool environments in the Peixe River, between the months of October 2011 and March 2012.

Fig. 3 in Pools and rapids as spawning and nursery areas for fish in a river stretch without floodplains

Fig. 3. Some species of fish larvae found in the upper Uruguay River: (A) Leporinus amae, (B) Bryconamericus stramineus, (C) Hoplias spp., (D) Leporinus obtusidens, (E) Schizodon aff. nasutus, (F) Rhamdia quelen, (G) Odontesthes aff. perugiae, (H) Serrasalmus maculatus, (I) Astyanax jacuhiensis, (J) Steindachnerina spp. egg and (K) Apareiodon affinis egg (Scale = 1mm).

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Рис. 2. Типичные местообитания чернобровой камышевки: a — поΛынники в пос. Гайворон; b — тростниковые пΛавни в с. Сосновка Fig. 2. Typical habitats of the black-browed warbler: a — wormwood in the Gaivoron village; b — reed floodplains in the Sosnovka village in in the Ussuri region

Рис. 2. Типичные местообитания чернобровой камышевки: a — поΛынники в пос. Гайворон; b — тростниковые пΛавни в с. Сосновка Fig. 2. Typical habitats of the black-browed warbler: a — wormwood in the Gaivoron village; b — reed floodplains in the Sosnovka village

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Text-fig. 3 Pollen diagram from the locality of Bohutín. 0-0.01 m – sandy soil mixed with humus, slightly clayey, sample B11; 0.05 m – grey-blue strongly sandy clay, sample B10; 0.10-0.25 m – brown-grey sandy clay with plant remains and mixed with a small amount of peat, sample B9, sample B8 (0.15 m), sample B7 (0.20 m), sample B6 (0.25 m); 0.30-0.35 m – dark sandy clay mixed with peat and plant remains, sample B5, sample B4 (0.35 m); 0.40 m – grey strongly sandy clay mixed with peat, sample B3; 0.45-0.50 m – grey-blue strongly sandy clay, sample B2, sample B1 (0.50 m). in Reconstruction Of Vegetation Development On The Floodplain Of The Litavka River In The Holocene (Central Bohemia, Brdy Mts.)

Text-fig. 3 Pollen diagram from the locality of Bohutín. 0-0.01 m – sandy soil mixed with humus, slightly clayey, sample B11; 0.05 m – grey-blue strongly sandy clay, sample B10; 0.10-0.25 m – brown-grey sandy clay with plant remains and mixed with a small amount of peat, sample B9, sample B8 (0.15 m), sample B7 (0.20 m), sample B6 (0.25 m); 0.30-0.35 m – dark sandy clay mixed with peat and plant remains, sample B5, sample B4 (0.35 m); 0.40 m – grey strongly sandy clay mixed with peat, sample B3; 0.45-0.50 m – grey-blue strongly sandy clay, sample B2, sample B1 (0.50 m).

Fig. 2 in Trophic relationships in fish assemblages of Neotropical floodplain lakes: selectivity and feeding overlap mediated by food availability

Fig. 2. Ordination by principal coordinate analysis (PCoA) of the food resource availability for six floodplain lakes along the Upper Paraná River, Paraná-Mato Grosso do Sul. AQI = aquatic insects; OAI = other aquatic invertebrates; OTI = other terrestrial invertebrates; PLA = plants; TRI = terrestrial insects.

Fig.5 in Trophic relationships in fish assemblages of Neotropical floodplain lakes: selectivity and feeding overlap mediated by food availability

Fig.5. Relationship between the mean of the proportional overlap Index (IS) and the scores of the first PCoA axis of resource availability in isolated floodplain lakes along the upper Paraná River.Values of IS closer to 1 indicates greater diet overlap. The mean IS was calculated based on individuals of 3 (ZÉ = ZÉ Marinho), 7 (Carioca = Car), 4 (TiÃo = Tia), 5 (Genipapo = Gen), 2 (CidÃo = Cid) and 5 species (Canal = Can).AQI = aquatic insects; PLA = plants.

Fig. 1 in Trophic relationships in fish assemblages of Neotropical floodplain lakes: selectivity and feeding overlap mediated by food availability

Fig. 1. Locations of the lakes on the upper Paraná River floodplain, Brazil: 1, Canal do Meio; 2, Carioca; 3, ZÉ Marinho; 4, CidÃo; 5, Genipapo; 6, TiÃo.

Fig. 4 in Trophic relationships in fish assemblages of Neotropical floodplain lakes: selectivity and feeding overlap mediated by food availability

Fig. 4. Relationship of the mean the Schoener's Index (O) between pairs of species and the scores of the first PCoA axis of resource availability in isolated floodplain lakes along the upper Paraná River. The mean O was calculated based on 10 (ZÉ = ZÉ Marinho), 28 (Carioca = Car), 6 (TiÃo = Tia), 21 (Genipapo = Gen), 3 (CidÃo = Cid) and 10 (Canal = Can) pairs of species. AQI = aquatic insects; PLA = plants.

Fig. 3 in Trophic relationships in fish assemblages of Neotropical floodplain lakes: selectivity and feeding overlap mediated by food availability

Fig. 3. Relationships between feeding selectivity by fish and the availability of food resources for six floodplain lakes along the Upper Paraná River, ParanáMato Grosso do Sul. Shape of data distribution (envelope effect) was significant.

Fig. 7 in Biometry of neotropical invertebrates inhabiting floodplain rivers: unraveling bionomy

Fig. 7. Differences in slopes obtained for lineal regressions of mollusks with and without shells. Invertebrates were collected in the Paraná River floodplain from 2005 through 2014.

Fig. 1 in Biometry of neotropical invertebrates inhabiting floodplain rivers: unraveling bionomy

Fig. 1. Lower to higher fit level (R2) for the lineal models on metric-DW variation of invertebrates. The pie-chart shows the proportion (%) of values that fall within each R2 category. Invertebrates were collected in the Paraná River floodplain from 2005 through 2014.

Fig. 2-5 in Biometry of neotropical invertebrates inhabiting floodplain rivers: unraveling bionomy

Fig. 2-5. Dispersion plots and lineal curves on L-DW regressions for (2) oligochaetes, (3) mollusks, (4) insects and (5) all invertebrates together. For Planorbidae L=D and for Ampullariidae L= H. In Fig. 5 only apple snails H-DW were considered within "Gastropoda" and only Corbiculidae and Hyriidae (and not Sphaeriidae) were considered within "Bivalvia". Invertebrates were collected in the Paraná River floodplain from 2005 through 2014.

Fig. 6 in Biometry of neotropical invertebrates inhabiting floodplain rivers: unraveling bionomy

Fig. 6. Fit levels obtained from freshwater invertebrates metric-DW lineal regressions. L= length, W= width and other metrics= "W" for clams, "D2" for apple snails and "Tibia" for mayflies. Invertebrates were collected in the Paraná River floodplain from 2005 through 2014.