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407 results for “riparian”
Linked collectors and determiners for: Deer Creek Riparian Restoration Ecological Monitoring.
Natural history specimen data linked to collectors and determiners held within, "Deer Creek Riparian Restoration Ecological Monitoring". Claims or attributions were made on Bionomia by volunteer Scribes, <a href="https://bionomia.net/dataset/f61e69d1-e79f-4ccb-bd92-56a7cefcf1e4">https://bionomia.net/dataset/f61e69d1-e79f-4ccb-bd92-56a7cefcf1e4</a> using specimen data from the dataset aggregated by the Global Biodiversity Information Facility, <a href="https://gbif.org/dataset/f61e69d1-e79f-4ccb-bd92-56a7cefcf1e4">https://gbif.org/dataset/f61e69d1-e79f-4ccb-bd92-56a7cefcf1e4</a>. Formatted as a Frictionless Data package.
Linked collectors and determiners for: A distinct new species of riparian rock-dwelling gecko (genus: Hemidactylus) from the southern Western Ghats.
Natural history specimen data linked to collectors and determiners held within, "A distinct new species of riparian rock-dwelling gecko (genus: Hemidactylus) from the southern Western Ghats". Claims or attributions were made on Bionomia by volunteer Scribes, <a href="https://bionomia.net/dataset/bfc6faaf-9085-47f4-b80f-0cf69eb717d1">https://bionomia.net/dataset/bfc6faaf-9085-47f4-b80f-0cf69eb717d1</a> using specimen data from the dataset aggregated by the Global Biodiversity Information Facility, <a href="https://gbif.org/dataset/bfc6faaf-9085-47f4-b80f-0cf69eb717d1">https://gbif.org/dataset/bfc6faaf-9085-47f4-b80f-0cf69eb717d1</a>. Formatted as a Frictionless Data package.
Fig. 3 in A new riparian Andean Potamites (Reptilia, Squamata, Gymnophtalmidae) from El Sira Mountains, central Peru, with comments on P. ecpleopus Cope 1875, and on the taxonomy and biogeography of Potamites
Fig. 3. Variation of the type series showing the dorsal (left column) and ventral (right column) views of paratypes. A–B. ♂, CORBIDI 14468 (SVL = 54.5). C–D. ♂, CORBIDI 14469 (SVL = 59.6). E–F. ♀, CORBIDI 14470 (SVL = 51.6).
Fig. 8 in A new riparian Andean Potamites (Reptilia, Squamata, Gymnophtalmidae) from El Sira Mountains, central Peru, with comments on P. ecpleopus Cope 1875, and on the taxonomy and biogeography of Potamites
Fig. 8. Lateral views comparing the condition of tubercles on flanks and sides of the neck (red arrows) and anterodorsal scales on limbs (green arrows). A. Potamites hydroimperator sp. nov. (paratype ♂, CORBIDI 14468). B. P. ecpleopus Cope, 1875 (uncollected ♂) from Yurimaguas. C. P. ecpleopus Cope, 1875, ♂ (CORBIDI 9516) from Cerros de Kampankis. Photographs by Germán Chávez (A), Angel Chujutalli (B) and Alessandro Catenazzi (C).
Fig. 4 in A new riparian Andean Potamites (Reptilia, Squamata, Gymnophtalmidae) from El Sira Mountains, central Peru, with comments on P. ecpleopus Cope 1875, and on the taxonomy and biogeography of Potamites
Fig. 4. Lateral (left columns) and dorsal (right columns) views of the head of all species of Potamites Doan & Castoe, 2005, showing condition of superciliars (turquoise), loreal (purple), frontonasals (yellow), parietals and interparietal (blue), postparietals (red), and azygous scales (green). A–B. P. hydroimperator sp. nov. (CORBIDI 13915, holotype). C–D. P. ecpleopus Cope, 1875 (CORBIDI 9059). E–F. P. erythrocularis Chávez & Catenazzi, 2014 (MUSM 28056, holotype). G–H. P.juruazensis Avila-Pires & Vitt, 2001 (CORBIDI 15504). I–J. P. montanicola Chávez & Vasquez, 2012 (CORBIDI 8322, holotype). K–L. P. ocellatus Sinitsin, 1930 (AMNH 22512, holotype). M–N. P. strangulatus Cope, 1868 (CORBIDI 11415). O–P. P. trachodus Uzzell, 1966 (CORBIDI 15515).
Fig. 7 in A new riparian Andean Potamites (Reptilia, Squamata, Gymnophtalmidae) from El Sira Mountains, central Peru, with comments on P. ecpleopus Cope 1875, and on the taxonomy and biogeography of Potamites
Fig. 7. Keeled dorsum in species of Potamites Doan & Castoe, 2005 showing the pattern of the dorsolateral keeled rows (blue) and paravertebral keeled rows (red). A. P. hydroimperator sp. nov. (CORBIDI 13915, holotype). B. P. ecpleopus Cope, 1875 (CORBIDI 11338). C. P. erythrocularis Chávez & Catenazzi, 2014 (CORBIDI 21841). D. P.juruazensis Avila-Pires & Vitt, 2001 (MPEG 17775, holotype). E. P. montanicola Chávez & Vasquez, 2012 (CORBIDI 8322, holotype). F. P. ocellatus Sinitsin, 1930 (AMNH 22512, holotype). G. P. trachodus Uzzell, 1966 (CORBIDI 15515).
Fig. 2 in A new riparian Andean Potamites (Reptilia, Squamata, Gymnophtalmidae) from El Sira Mountains, central Peru, with comments on P. ecpleopus Cope 1875, and on the taxonomy and biogeography of Potamites
Fig. 2. Holotype in life of Potamites hydroimperator sp. nov., CORBIDI 13915 (SVL = 59.4 mm). A. Dorsal view. B. Ventral view. C. Dorsolateral view of the head.
Fig. 6 in A new riparian Andean Potamites (Reptilia, Squamata, Gymnophtalmidae) from El Sira Mountains, central Peru, with comments on P. ecpleopus Cope 1875, and on the taxonomy and biogeography of Potamites
Fig. 6. Panoramic view of the primary forest on the mountains of the type locality of Potamites hydroimperator sp. nov. in El Sira Communal Reserve.
Fig. 5 in A new riparian Andean Potamites (Reptilia, Squamata, Gymnophtalmidae) from El Sira Mountains, central Peru, with comments on P. ecpleopus Cope 1875, and on the taxonomy and biogeography of Potamites
Fig. 5. Coloration in life of males of all species of Potamites Doan & Castoe, 2005 ocurrying in Peru. A–B. P. hydroimperator sp. nov. (CORBIDI 14468). C–D. P. ecpleopus Cope, 1875 (CORBIDI 9516). E–F. P. erythrocularis Chávez & Catenazzi, 2014 (MUSM 30260). G–H. P.juruazensis Avila-Pires & Vitt, 2001 (CORBIDI 15504). I–J. P. montanicola Chávez & Vasquez, 2012 (CORBIDI 10596). K–L. P. strangulatus Cope, 1868 (CORBIDI 11415). M–N. P. trachodus Uzzell, 1966 (CORBIDI 15515). Photographs by Germán Chávez (A–B, G–J, M–N) and Alessandro Catenazzi (C–F, K–L).
Text-fig. 18. Landscape reconstruction of the Late Miocene localities of the North Caucasus studied. a – general view of the reconstructed riparian biotope; b – periaquatic fauna. Drawings by S. Kruskop. in Late Miocene (Early Turolian) Vertebrate Faunas And Associated Biotic Record Of The Northern Caucasus: Geology, Taxonomy, Palaeoenvironment, Biochronology
Text-fig. 18. Landscape reconstruction of the Late Miocene localities of the North Caucasus studied. a – general view of the reconstructed riparian biotope; b – periaquatic fauna. Drawings by S. Kruskop.
Fig. 5 in Feeding ecology of Auchenipterichthys longimanus (Siluriformes: Auchenipteridae) in a riparian flooded forest of Eastern Amazonia, Brazil
Fig. 5. Repletion index (RI%) of Auchenipterichthys longimanus from rivers of National Forest of Caxiuanã (PA, Brazil) related to hydrological periods.
Fig. 2 in Feeding ecology of Auchenipterichthys longimanus (Siluriformes: Auchenipteridae) in a riparian flooded forest of Eastern Amazonia, Brazil
Fig. 2. Fluviometry from the rivers of the Caxiuanã National Forest in the period between July 2008 and July 2009. Data obtained from the fluviometric station of Caiçara of the National Water Agency (ANA).
Fig. 3 in Feeding ecology of Auchenipterichthys longimanus (Siluriformes: Auchenipteridae) in a riparian flooded forest of Eastern Amazonia, Brazil
Fig. 3. (a) Graphic representation of the non-metric multidimensional scaling analysis (NMDS) of the diet of Auchenipterichthys
Fig. 1 in Feeding ecology of Auchenipterichthys longimanus (Siluriformes: Auchenipteridae) in a riparian flooded forest of Eastern Amazonia, Brazil
Fig. 1. Location of the Caxiuanã National Forest, showing the rivers where the fish were collected. Curuá River - Ferreira Penna Research Station (ECFPn), Caxiuanã River, Puraquequara River and Caquajó River. Some black spots represent more than one collection site.
Fig. 4 in Feeding ecology of Auchenipterichthys longimanus (Siluriformes: Auchenipteridae) in a riparian flooded forest of Eastern Amazonia, Brazil
Fig. 4. Trophic niche breadth (Levins index; B) of the a midnight catfish Auchenipterichthys longimanus from rivers of the Caxiuanã National Forest of (PA, Brazil) related to hydrological periods.
Fig. 2 in Influence of the riparian zone phytophysiognomies on the longitudinal distribution of fishes: evidence from a Brazilian savanna stream
Fig. 2. Two-dimension ordinations based on Jaccard similarity coefficient (a) and on Bray-Curtis (b), considering the ten samples from the wet and dry seasons from the Correntes stream, central west Brazil.
Fig. 1 in Influence of the riparian zone phytophysiognomies on the longitudinal distribution of fishes: evidence from a Brazilian savanna stream
Fig. 1. Map showing localization of the sampled reaches of Correntes stream in the plateau region of the Paraguay basin, Mato Grosso do Sul State, Brazil.
HeadwaterstreamSNevada: data on riparian vegetation and water parameters of headwater streams in Sierra Nevada, Spain
<p>Providing historical data on riparian plant biodiversity and physico-chemical parameters of stream water in Mediterranean mountains helps to assess the effects of climate change and other human stressors on these sensitive and critical ecosystems. This database collects data from the main natural headwater streams of the Sierra Nevada (southeastern Spain), a high mountain (up to 3,479 meters above sea level, m.a.s.l.) recognized as a biodiversity super hotspot (Arroyo et al., 2022) in the Mediterranean Basin. On this mountain, rivers and landscapes depend on snowmelt water, representing an excellent scenario for evaluating global change's impacts. This dataset covers first- to third-order headwater streams at 41 sites from 832 to 1,997 m.a.s.l., collected from December 2006 to July 2007. Our goal is to supply information on the vegetation associated with streambanks, the essential physico-chemical parameters of stream water, and the physiographic features of the subwatersheds. Riparian vegetation data correspond to six plots sampled at each site, including total canopy, individual number, height and DBH (diameter at breast height) in woody species, and cover percentage for herbs. Physico-chemical parameters were measured in situ (electric conductivity, pH, dissolved O2 concentration, stream discharge) and determined in the laboratory [alkalinity, soluble reactive phosphate-phosphorus (SRP), total phosphorus (TP), nitrate-nitrogen (NO3-–N), ammonium-nitrogen (NH4+–N), total nitrogen (TN)]. Watershed physiographic variables comprise drainage area, minimum altitude, maximum altitude, mean slope, orientation, stream order, stream length, and land cover surface percentage. We recorded 197 plant taxa (67 species, 28 subspecies and 2 hybrids), representing 8.4% of the Sierra Nevada vascular flora. Due to the botanical nomenclature used, the database can be linked to FloraSNevada database (Lorite et al., 2020), contributing to Sierra Nevada (Spain) as a laboratory of global processes.</p> <p>For more information about the data, see the metadata document (Metadata_HeadwaterstreamSNevada.docx).</p>
Removing invasive giant reed reshapes desert riparian butterfly and bird communities
<p>Giant reed (Arundo donax) is a prevalent invasive plant in desert riparian ecosystems that threatens wildlife habitat. From 2008 to 2018, under a United States–Mexico partnership, prescribed burns and herbicide applications were used to remove giant reed and promote native revegetation along the Rio Grande – Río Bravo floodplain in west Texas, USA, and Mexico. Our goal was to explore the effects of the removal efforts on butterfly and bird communities and their habitat along the United States portion of the Rio Grande – Río Bravo floodplain in Big Bend National Park, Texas. During spring and summer, 2016–2017, we surveyed butterflies, birds, and their habitat using ground-collected and remotely sensed data. Using a variety of generalized linear and N-mixture modeling routines and multivariate analyses, we found that the initial giant reed removal efforts removed key components of riparian habitat leading to reduced butterfly and bird communities. Within several years following management, giant reed levels remained low, while riparian habitat conditions and butterfly and bird communities largely rebounded, including many disturbance-sensitive butterfly species and riparian-associated bird species. Butterflies were most consistently associated with forb and grass cover, and birds with a remotely sensed index of greenness (the normalized difference vegetation index), several vegetation cover types, and habitat heterogeneity, habitat elements that were most common in locations that had the longest time to recover following management actions. Our results suggest that prescribed burns and herbicide applications, when used following protocols to minimize risk to wildlife, can limit the spread of giant reed in desert riparian systems and introduce habitat conditions that support diverse and abundant butterfly and bird communities. </p>
Data from: Broad-scale meta-analysis of drivers mediating adverse impacts of flow regulation on riparian vegetation
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Allen Brain Atlas
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DANDI Archive for NWB datasets
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International Brain Laboratory public data
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OpenNeuro
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