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517 results for “Floodplain”
Distribution. Restricted to the Kafue Flats floodplain of the Kafue River, S Zambia. in Bovidae
Distribution. Restricted to the Kafue Flats floodplain of the Kafue River, S Zambia.
Onshore Methane Seeps in West Siberian Floodplains
<p>Recently numerous methane seeps were found in West Siberian middle taiga river floodplains. Seepage occurs in unvegetated spots and areas of saturated quicksand deposits and in the bottom of river stream beds. Despite the origin of CH<sub>4</sub> in these seeps is not fully understood, they can make substantial contribution in regional greenhouse gas emission. Possibly, seeps are a unique phenomenon of the studied region.</p> <p>These videos were produced to supplement our researches on gas origin, emission rates and seeps area.</p>
Fig. 5 in A new species of copepod (Copepoda: Calanoida) from the floodplain of the lower Mekong River Basin in Thailand and Cambodia, with an amended diagnosis of the genus Dentodiaptomus Shen & Tai, 1964
Fig. 5. Dentodiaptomus orientalis, new species, male: A, P1; B, P2; C, P3; D, P4; E, P5, posterior view; F, a part of the right P5 Exp-2, lateral view; G, left P5 Exp-2, posterior view; H, left P5 Exp-2, frontal view.
Fig. 3 in Effects of the interannual variations in the flood pulse mediated by hypoxia tolerance: the case of the fish assemblages in the upper Paraná River floodplain
Fig. 3. Interannual variation of the absolute and mean ± s.e. values of dissolved oxygen (a, c) and water transparency (b, d) in lakes (circle) and river channels (square) of the upper Paraná River floodplain, in years of short (2000 and 2001) and moderate (2002 and 2003) floods. Numbers 1-6 are codes of the sampling stations (see Fig. 1).
Figure 4 in Species richness of urban and rural fish assemblages in the Grijalva Basin floodplain, southern Gulf of Mexico
Figure 4. – Fish distributed in the Villahermosa city and rural areas in the Grijalva floodplain. 1 – Dorosoma anale, 2 – D. petenense, 3 – Astyanax finitimus, 4 – Pterygoplichthys spp., 5 – Cathorops aguadulce, 6 – Rhamdia guatemalensis, 7 – Cincelichthys pearsei, 8 – Cribroheros robertsoni, 9 – Mayaheros urophthalmus, 10 – Oreochromis niloticus. 11 – Oscura heterospila, 12 – Parachromis friedrichsthalii, 13 – Parachromis managuensis, 14 – Vieja bifasciata, 15 – V. melanurus, 16 – Hyporhamphus mexicanus, 17 – Strongylura hubbsi, 18 – Ophisternon aenigmaticum, 19 – Centropomus undecimalis, 20 – Diapterus auratus, and 21 – Eugerres mexicanus.
Figure 2 in Species richness of urban and rural fish assemblages in the Grijalva Basin floodplain, southern Gulf of Mexico
Figure 2. – Fish distributed in the Villahermosa city and rural areas in the Grijalva floodplain. 1 – Atractosteus tropicus, 2 – Megalops atlanticus, 3 – Ctenopharyngodon idella, 4 – Cyprinus carpio, 5 – Brycon guatemalensis, and 6 – Petenia splendida.
Figure 3 in Species richness of urban and rural fish assemblages in the Grijalva Basin floodplain, southern Gulf of Mexico
Figure 3. – Fish distributed in the Villahermosa city and rural areas in the Grijalva floodplain. 1 – Anchoa mitchilli, 2 – Brevoortia gunteri, 3 – Hyphessobrycon compressus, 4 – Batrachoides goldmani, 5 – Dormitator maculatus, 6 – Eleotris amblyopsis, 7 – Gobiomorus dormitor, 8 – Oreochromis aureus, 9 – Rocio octofasciata, 10 – Thorichthys helleri, 11 – T. meeki, 12 – T. pasionis, 13 – Trichromis salvini, 14 – Atherinella alvarezi, 15 – Cynodonichthys tenuis, 16 – Belonesox belizanus, 17 – Carlhubbsia kidderi, 18 – Gambusia sexradiata, 19 – G. yucatana, 20 – Pseudoxiphophorus bimaculatus, 21 – Heterophallus echeagarayi, 22 – Phallichthys fairweatheri, 23 – Poecilia kykesis, 24 – P. mexicana. 25 – Xiphophorus maculatus, 26 – Achirus lineatus, and 27 – Microphis lineatus.
Figure 3 in On the occurrence of Spirogyra maxima (Zygnematophyceae) in the Upper PArAná River floodplAin
Figure 3. Reproductive stages of Spirogyra maxima (Hassall) Wittrock. A. Filaments with scalariform conjugation and mature zygospores; B-C. Detail of immature zygospores; D-E. Details of mature zygospores. Bars = 50µm.
Figure 1 in On the occurrence of Spirogyra maxima (Zygnematophyceae) in the Upper PArAná River floodplAin
Figure 1. Partial view of collection site where the Spirogyra filaments were sampled intermingled in banks of aquatic macrophytes in the Rio Baía, Upper Paraná River floodplain, Brazil. A. General view of the habitat; B. Close view of Spirogyra massive growth; C. Spirogyra filaments collected from the bank.
Fig. 11 in Pools and rapids as spawning and nursery areas for fish in a river stretch without floodplains
Fig. 11. Conceptual model of the distribution patterns of eggs and larvae in the early stages of two environments in the Peixe River (upper Uruguay River), from October 2011 to March 2012.
Fig. 6 in Pools and rapids as spawning and nursery areas for fish in a river stretch without floodplains
Fig. 6. Average density ± standard deviation of the macrozooplankton organisms captured in both environments (rapids and pool) of the Peixe River, between October 2011 and March 2012.
Fig. 4 in Pools and rapids as spawning and nursery areas for fish in a river stretch without floodplains
Fig. 4. Average repletion degree (%) of the captured larvae digestive tract from both environments of the Peixe River, from October 2011 to March 2012. Number of larvae examined is shown in brackets. Repletion degree: E - empty; PE - partially empty; PF - partially full; F - full.
Fig. 8 in Pools and rapids as spawning and nursery areas for fish in a river stretch without floodplains
Fig. 8. Average density ± standard error of the larvae captured in the Peixe River with light traps in different environments and months from October 2011 to March 2012.
Fig. 5 in Pools and rapids as spawning and nursery areas for fish in a river stretch without floodplains
Fig. 5. Average flow and precipitation ratings registered in the Peixe River, from October 2011 to March 2012. Source: Consórcio de Itá.
Figures 1-3 from: Santos-Silva L, Gimenez Pinheiro T, Isaac Marques M, Dênis Battirola L (2018) Phenology of Promestosoma boggianii (Diplopoda: Polydesmida: Paradoxosomatidae) in a Neotropical floodplain. Zoologia 35: 1-8. https://doi.org/10.3897/zoologia.35.e14764
Figures 1-3 (1) The Pantanal and its 11 sub-regions, with emphasis on the Pantanal of Poconé, Mato Grosso, Brazil. (2) Study area with the location of the three sample units (A1, A2 and A3), along the Porto Cercado Road, between the Bento Gomes and Cuiabá rivers, within the floodplain of the Poconé Pantanal, Mato Grosso. (3) Illustration indicating the floodable (I) and non-floodable (NI) habitats, with the three quadrats (P1, P2, P3) and layouts for the pitfall traps and mini-Winkler extractors. (Source: Silva et al. 2000, Meurer 2015, modified).
Figure 4 from: Santos-Silva L, Gimenez Pinheiro T, Isaac Marques M, Dênis Battirola L (2018) Phenology of Promestosoma boggianii (Diplopoda: Polydesmida: Paradoxosomatidae) in a Neotropical floodplain. Zoologia 35: 1-8. https://doi.org/10.3897/zoologia.35.e14764
Figure 4 Distribution of Promestosoma boggianii according to stages of development (juvenile stages III, IV, V, VI, VII and adult) throughout the seasonal periods (dry season, rising water, high water and receding water) in a floodplain of Mato Grosso's northern Pantanal region, Brazil.
Figure 6 from: Ferreira GS, Almeida dos Santos DA, Lopes EV (2019) Richness, abundance and microhabitat use by Ardeidae (Aves: Pelecaniformes) during one seasonal cycle in the floodplain lakesof the lower Amazon River. Zoologia 36: 1-10. https://doi.org/10.3897/zoologia.36.e30475
Figure 6 Factorial diagram of the Canonical Correspondence Analysis, including environmental variables (wave height, wave period, swash time, organic matter%, rainfall and frequency of storm wave events) and macrofauna species on Grussaí and Manguinhos beaches. Ab: Atlantorchestoideabrasiliensis; Dh: Donaxhanleyanus; Eb: Emeritabrasiliensis; Exb: Excirolanabraziliensis; Hc: Hemipodiacaliforniensis; Mys: Mysida sp.; Nem: Nemertea; Olig: Oligochaeta; Ov: Olivancillariavesica; Pen: Peneidae; Pue: Puelche sp.; Sco: Scolelepis sp.; Tt: Talorchestiatucurauna.
Figure 4 from: Ferreira GS, Almeida dos Santos DA, Lopes EV (2019) Richness, abundance and microhabitat use by Ardeidae (Aves: Pelecaniformes) during one seasonal cycle in the floodplain lakesof the lower Amazon River. Zoologia 36: 1-10. https://doi.org/10.3897/zoologia.36.e30475
Figure 4 Number of species (richness) and density (individuals/m2) for the dissipative (Manguinhos Beach) and intermediate (Grussaí Beach) beaches in the dry (July/2012, August/2012, July/2013 and September/2013) and rainy (January/2013, February/2013, March/2014 and April/2014) seasons.
Figure 3 from: Ferreira GS, Almeida dos Santos DA, Lopes EV (2019) Richness, abundance and microhabitat use by Ardeidae (Aves: Pelecaniformes) during one seasonal cycle in the floodplain lakesof the lower Amazon River. Zoologia 36: 1-10. https://doi.org/10.3897/zoologia.36.e30475
Figure 3 Monthly discharge of Paraíba do Sul River and rainfall. River discharge and rainfall are correlated variables (R> 0.5). Rainfall data refer to Campos dos Goytacazes municipality (40–50 km from Grussaí and Manguinhos beaches) and was obtained from National Institute for Meteorology (INMET: http://www.inmet.gov.br).
Figure 5 from: Ferreira GS, Almeida dos Santos DA, Lopes EV (2019) Richness, abundance and microhabitat use by Ardeidae (Aves: Pelecaniformes) during one seasonal cycle in the floodplain lakesof the lower Amazon River. Zoologia 36: 1-10. https://doi.org/10.3897/zoologia.36.e30475
Figure 5 Regression analysis of the macrofauna richness and density as function of the number of storm wave events (SWE) and wave height, respectively. The pink dots represent each dependent (marine debris on ghost crab burrow) and independent variables (distance from urban settlements). Blue shaded area indicates 95% confidence intervals and pink line is the distribution of residuals. Blue line is the regression straight. Only significant (p < 0.05) predictors were considered in the effects plot.
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