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FIGURE 3 in Taxonomic and phylogenetic beta diversity in headwater stream fish communities of the Paraná and Paraguai River basins
FIGURE 3 | Turnover and nestedness components of taxonomic and phylogenetic beta diversity in streams of the Paraná and Paraguai River basins. Clockwise from top left: total, turnover and nestedness components of taxonomic beta diversity; at the bottom, total, turnover and nestedness components of phylogenetic beta diversity. Filled circles correspond to Paraná streams and triangles to Paraguai streams.
FIGURE 2 in Taxonomic and phylogenetic beta diversity in headwater stream fish communities of the Paraná and Paraguai River basins
FIGURE 2 | Phylogenetic hypothesis for fish collected in headwater streams of the Paraná and Paraguai River basins.
FIGURE 1 in Taxonomic and phylogenetic beta diversity in headwater stream fish communities of the Paraná and Paraguai River basins
FIGURE 1 | Headwater streams sampled in the Paraná and Paraguai River basins. Blue circles represent streams of the Paraguai basin, and black triangles represent streams of the Paraná basin. The stars represent waterfalls. The color indicates the variation in altitude.
Time series of electrical conductivity, temperature and relative stream stage recorded in surface water and streambed sediments of River Erpe and River Gruendlach, Germany
<p><span><a href="../api/records/13336325/draft/files/temp_EC_timeseries.csv/content" target="_blank" rel="noopener noreferrer">temp_EC_timeseries.csv</a></span>: Time series of electrical conductivity (mS cm<sup>-1</sup>), temperature (degC) and relative stream stage (cm) recorded in the surface water and in streambed sediments (depth in cm) of River Erpe and River Gruendlach, Germany.</p> <p> </p> <p><span><a href="../api/records/13336325/draft/files/porewater_ec_timeseries.csv/content" target="_blank" rel="noopener noreferrer">porewater_ec_timeseries.csv</a></span>: Time series of electrical conductivity (mS cm<sup>-1</sup>), temperature (degC), relative stream stage (cm) and total pressure (hPa) recorded in the surface water and in streambed sediments (depth in cm) of River Erpe and River Ammer, Germany, and the Sturt River, South Australia.</p>
FIGURE 3 in Fish functional trophic groups in headwater karst streams from the Upper Paraguay River basin
FIGURE 3 | Representative images of the fish assemblage from Serra da Bodoquena streams. A. Farlowella paraguayensis among twigs and leaf litter in the substrate; B. Hypostomus froehlichi between boulders; C. Creagrutus meridionalis foraging near a sandy substrate; D. Pimelodella taenioptera and Astyanax lacustris foraging among leaf litter in the substrate; E. Hyphessobrycon eques and Jupiaba acanthogaster using marginal vegetation; F. Characidium zebra using the sit-and-wait tactics on the sandy substrate; G. Psalidodon marionae foraging near the rocky substrate; H. Salminus brasiliensis swimming in the water column; I. Prochilodus lineatus foraging near patches of vegetation. Photos: Renato M. Romero and Fabrício B. Teresa.
FIGURE 4 in Fish functional trophic groups in headwater karst streams from the Upper Paraguay River basin
FIGURE 4 | Compilation of number of families on each Functional Trophic Group among different biomes in Brazil. Bar colors represent the shared FTGs among biomes considering Sazima (1986), Sabino, Zuanon (1998), Casatti et al. (2001), Brejão et al. (2013), Freitas et al. (2021), and this work. Blue bar: FTGs registered in Pantanal+Amazon+Atlantic Forest; Red bar: FTGs registered in Pantanal+Amazon; Green bar: FTG registered only in Amazon. Silhouettes represent the families with more records on each FTG.
FIGURE 1 in Fish functional trophic groups in headwater karst streams from the Upper Paraguay River basin
FIGURE 1 | Main drainages of Serra da Bodoquena. The Miranda River watershed (blue) and the Perdido River watershed (red). Highlighted lines represent Salobra River in the North and Perdido River in the South. In green, the Formoso River watershed, a tributary of Miranda drainage. Black dots represent the points of underwater observations of the fish species.
FIGURE 2 in Fish functional trophic groups in headwater karst streams from the Upper Paraguay River basin
FIGURE 2 | Distribution of sizes classes of fish from Serra da Bodoquena stream according to instream horizontal occupation.
FIGURE 5 in Fish functional trophic groups in headwater karst streams from the Upper Paraguay River basin
FIGURE 5 | Number of accumulated Functional Trophic Groups by fish families considering Brazilian inland freshwaters works from Sazima (1986), Sabino, Zuanon (1998), Casatti et al. (2001), Brejão et al. (2013), Freitas et al. (2021), and this work.
Data underlying submission "Tracing stream flow in confluent rivers – a journey from chaos to order"
<p>These data underly the analysis presented in the manuscript "Tracing stream flow in confluent rivers – a journey from chaos to order" by Erwin Zehe, Samuel Schroers and Hubert Savenije.</p> <p>The data used for this analysis are available were taken from the globally available the HydroSHEDS data base <em>at https://www.hydrosheds.org created by Lehner et al. (2008)</em>. The extracted data for analyzing the 18 of the largest Rivers are stored as csv files sorted by river names. The metadata are provided in "HydroSHEDS_TechDoc_v1_4.pdf" and "BasinATLAS_Catalog_v10.pdf".</p> <p>The matal codes for data analysis and simulations were tested and should be self-explaining.</p> <p> Lehner, B., Verdin, K. & Jarvis, A. New Global Hydrography Derived From Spaceborne Elevation Data. <em>Eos, Transactions American Geophysical Union</em> <strong>89</strong>, 93-94, doi:<a href="https://doi.org/10.1029/2008EO100001">https://doi.org/10.1029/2008EO100001</a> (2008).</p>
Fig. 3 in Evidence of the color pattern variation in populations of Gymnotus pantanal (Gymnotiformes) from three streams in the upper Paraná River basin, Brazil
Fig. 3. Color pattern variation in Gymnotus pantanal from Pinheirinho and Jacutinga streams. (a) 209.8 mm TL (NUP 9311); (b) 181.0 mm TL (NUP 9311); (c) 150.0 mm TL (NUP 9312); (d) 125.0 mm TL (NUP 9312).
Fig. 4 in Evidence of the color pattern variation in populations of Gymnotus pantanal (Gymnotiformes) from three streams in the upper Paraná River basin, Brazil
Fig. 4. Principal Component Analysis (PCA) ordination (a) and average values (± standard error) of the axes scores 1 (b) and 2 (c) from PCA ordination of morphometric characters for Gymnotus pantanal atypical color pattern (G. 1) and Gymnotus pantanal sensu stricto (G. 2).
Fig. 5 in Changes in the structure of fish assemblages in streams along an undisturbed-impacted gradient, upper Paraná River basin, Central Brazil
Fig. 5. ABC curves per year of fish assemblages from stream stretches located in impacted areas. NP1 = Palmito; NP2 = Onça; NP3 = Unnamed Stream 3. W = statistical value for each stream.
Fig. 2 in Changes in the structure of fish assemblages in streams along an undisturbed-impacted gradient, upper Paraná River basin, Central Brazil
Fig. 2. Fish assemblage rarefaction plot by stream stretches. P1 = Macaúba; P2 = Carapina; P3 = Barreiro; P4 = Cana Brava; NP1 = Palmito; NP2 = Onça; NP3 = Unnamed Stream 3; NP4= Bandeira; NP5 = Pedreira; NP6 = Unnamed Stream 2.
Fig. 1 in Changes in the structure of fish assemblages in streams along an undisturbed-impacted gradient, upper Paraná River basin, Central Brazil
Fig. 1. Location of the streams sampled in the João Leite River basin, Goiás, Central Brazil. The broken line represents the limits of the basin. Clear grey area = Altamiro de Moura Pacheco State Park; Goiânia and Anápolis are the main cities in the basin. P1 = Macaúba; P2 = Carapina; P3 = Barreiro; P4 = Cana Brava; NP1 = Palmito; NP2 = Onça; NP3 = Unnamed Stream 3; NP4 = Bandeira; NP5 = Pedreira; NP6 = Unnamed Stream 2.
Fig. 3 in Changes in the structure of fish assemblages in streams along an undisturbed-impacted gradient, upper Paraná River basin, Central Brazil
Fig. 3. Fish assemblage dendogram resulting from the Morisita-Horns analysis. Roman numerals indicate the groups and the small box the scale of variance. P1 = Macaúba; P2 = Carapina; P3 = Barreiro; P4 = Cana Brava; NP1 = Palmito; NP2 = Onça; NP3 = Unnamed Stream 3; NP4 = Bandeira; NP5 = Pedreira; NP6 = Unnamed Stream 2.
Fig. 4 in Changes in the structure of fish assemblages in streams along an undisturbed-impacted gradient, upper Paraná River basin, Central Brazil
Fig. 4. ABC curves per year of fish assemblages from stream stretches located in preserved areas. P1 = Macaúba; P2 = Carapina; P3 = Barreiro; P4 = Cana Brava. W = statistical value for each stream.
Fig. 6 in Changes in the structure of fish assemblages in streams along an undisturbed-impacted gradient, upper Paraná River basin, Central Brazil
Fig. 6. ABC curves per year of fish assemblages from stream stretches located in impacted areas. NP4 = Bandeira; NP5 = Pedreira; NP6 = Unnamed Stream 2. W = statistical value for each stream.
Fig. 1 in Influence of environmental variables and anthropogenic perturbations on stream fish assemblages, Upper Paraná River, Central Brazil
Fig. 1. Locations of the sampled sites (dots) in the streams of the Ouvidor River, Goiás State, Brazil. Squares indicate the main cities.
Data-set of the partial pressure of CO2, dissolved concentrations of CH4, N2O, NO3-, NO2- and NH4+, specific conductivity and water temperature in the rivers and streams of the Napo River basin in Ecuador (2018, 2019, 2020, 2021)
<p>Data-set consists of two files:</p> <p>- data_ghgs.xlsx : Time-stamped and georeferenced data-set of the partial pressure of CO2 (pCO2 in ppm), dissolved CH4 concentration (CH4 in nmol/L), dissolved N2O concentration (N2O in nmol/L), specific (Sp.) conductivity (in µS/cm), water temperature (in °C), dissolved nitrate concentration (NO3- in µmol/L), dissolved nitrite concentration (NO2- in µmol/L), and dissolved ammonia concentration (NH4+ in µmol/L) in the rivers and streams of the Napo River basin in Ecuador (October 2018 and 2019, January 2019 and 2020, April 2019 and 2021, July 2019 and 2020). Gas measurements were made by headspace equilibration directly in the field with a infra-red gas analyser for CO2 and in the lab with a gas chromatograph for CH4 and N2O. NO3-, NO2- and NH4+ were measured with standard colometric procedures. Sampling and analytical protocols are provided here <a href="https://doi.org/10.5194/bg-16-3801-2019">https://doi.org/10.5194/bg-16-3801-2019</a></p> <p>- RiverATLAS.xlsx: hydro-environmental data for the sampled streams extracted from RiverATLAS (https://www.nature.com/articles/s41597-019-0300-6). Data codes and units are available here: https://data.hydrosheds.org/file/technical-documentation/HydroATLAS_TechDoc_v10_1.pdf</p> <p>First column of each of the two files provides station ID allowing to merge both data-sets.</p>
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