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17 results for “fishing risk assessment”
Figure 3 in America's Most Wanted Fishes: cataloging risk assessments to prioritize invasive species for management action
Figure 3. The proportion of risk statuses of fish families with four or more species assessed at the extent of Florida. Panel (A) shows the proportion of species with high, moderate, low, multiple, and undetermined risk statuses of assessed species (total number of species evaluated in a family). Panel (B) shows the ratio of assessed to unassessed species in a given family (total species in a family). Total species in a family were obtained from FishBase (Froese and Pauly 2023).
Figure 1 in America's Most Wanted Fishes: cataloging risk assessments to prioritize invasive species for management action
Figure 1. The proportion of risk statuses of fish families with four or more species assessed at the extent of the conterminous U.S. Panel (A) shows the proportion of species with high, moderate, low, multiple, and undetermined risk statuses of assessed species (total number of species evaluated in a family). Panel (B) shows the ratio of assessed to unassessed species in a given family (total species in a family). Total species in a family were obtained from FishBase (Froese and Pauly 2023).
Figure 2 in America's Most Wanted Fishes: cataloging risk assessments to prioritize invasive species for management action
Figure 2. The proportion of risk statuses of fish families with four or more species assessed at the extent of the Great Lakes region. Panel (A) shows the proportion of species with high, moderate, low, multiple, and undetermined risk statuses of assessed species (total number of species evaluated in a family). Panel (B) shows the ratio of assessed to unassessed species in a given family (total species in a family). Total species in a family were obtained from FishBase (Froese and Pauly 2023).
FIGURE 5 in Assessing extinction risk from geographic distribution data in Neotropical freshwater fishes
FIGURE 5 | Collection points for 442 threatened Neotropical freshwater fishes (NFF) colored by elevation and sized by species' description year. Threatened NFF species are often those described decades ago, with range-restricted distributions in the upland rivers of the Brazilian Shield and the Colombian Andes, and coastal Atlantic and Caribbean drainages. CR: Critically Endangered; EN: Endangered; VU: Vulnerable; DD: Data Deficient (gray). Data for 4,412 localities with geographic coordinates.
FIGURE 6 in Assessing extinction risk from geographic distribution data in Neotropical freshwater fishes
FIGURE 6 | Collection points for 671 potentially threatened Neotropical Freshwater Fishes (NFF). Potentially threatened NFF species predicted by the ConR package using EOO estimates are usually distributed outside protected areas (e.g., national parks, indigenous lands: green) and more often located in the upland rivers of the northern, central and southern Andes, and Eastern Guiana Shield. CR: Critically Endangered; EN: Endangered; VU: Vulnerable; LC or NT: Least Concern or Near Threatened; DD: Data Deficient. Data for 4,412 localities with geographic coordinates. Protected areas (green) from: https://www.protectedplanet.net.
FIGURE 2 in Assessing extinction risk from geographic distribution data in Neotropical freshwater fishes
FIGURE 2 | Extinction risks in 3,001 Neotropical freshwater fishes (NFF). On average, 14% (422 of 3,001) NFF species are classified by the IUCN Red List (RL) as Vulnerable (VU), Endangered (EN) or Critically Endangered (CR). Extinction risks are relatively similar among the orders Characiformes (8.2%), Siluriformes (10.8%), Cichliformes (10.0%), and Gymnotiformes (14.9%). An exception is the clade Cyprinodontiformes, where about 48% of species are classified as either VU, EN, or CR. LC or NT: Least Concern or Near Threatened; DD: Data Deficient.
FIGURE 4 in Assessing extinction risk from geographic distribution data in Neotropical freshwater fishes
FIGURE 4 | Collection points for 442 threatened Neotropical freshwater fishes (NFF). Threatened NFF species classified by the IUCN Red List (RL) are often distributed in the upland rivers of the Brazilian Shield and the Colombian Andes, and coastal Atlantic and Caribbean drainages. CR: Critically Endangered; EN: Endangered; VU: Vulnerable; DD: Data Deficient. Data for 4,412 localities with geographic coordinates.
FIGURE 3 in Assessing extinction risk from geographic distribution data in Neotropical freshwater fishes
FIGURE 3 | Association among three variables and extinction risks in 3,001 Neotropical freshwater fishes (NFF). A. IUCN-Red List (RL) threat categories by species description dates. B. Species description dates by taxonomic orders. C. IUCN-RL categories by geographic ranges. D. Geographic ranges by taxonomic orders. E. IUCN-RL categories by elevation ranges. F. Elevational ranges by taxonomic orders. Threatened status are usually higher for recently described NFF species, those inhabiting narrow geographic ranges, and those confined to upland river drainages. CR: Critically Endangered; EN: Endangered; VU: Vulnerable; DD: Data Deficient.
FIGURE 1 in Assessing extinction risk from geographic distribution data in Neotropical freshwater fishes
FIGURE 1 | Sample of the phenotypic diversity of Neotropical freshwater fishes. Upper left to lower right: Lycengraulis grossidens (Spix & Agassiz, 1829); Hyphessobrycon hexastichos Bertaco & Carvalho, 2005; Geophagus neambi Lucinda, Lucena & Assis, 2010; Crenicichla lepidota Heckel, 1840; Trachelyopterus galeatus (Linnaeus, 1766); Anablepsoides xinguensis (Costa, 2010); Abramites hypselonotus (Günther 1868); Pituna xinguensis Costa & Nielsen, 2007; Gymnotus cuia Craig, Malabarba, Crampton & Albert, 2018; Apteronotus caudimaculosus de Santana, 2003; Colomesus tocantinensis Amaral, Brito, Silva & Carvalho, 2013; Corydoras britskii (Nijssen & Isbrücker, 1983). Species not shown in scale.
Assessing patterns and risk to Chilean freshwater fish distributions using multi-species occupancy models
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Table 1 in America's Most Wanted Fishes: cataloging risk assessments to prioritize invasive species for management action
<p><b>Table 1.</b> List of fish species with high-risk statuses in the conterminous U.S., in the Great Lakes region, and in the state of Florida. Horizontal lines separate families and species for clarity.</p><table><tbody><tr><th>Family Name</th><th>Fish species name</th><th>Conterminous U.S.</th><th>Great Lakes</th><th>Florida</th></tr></tbody><tbody><tr><th>Atherinidae</th><td><i>Atherina boyeri</i> (Risso, 1810)</td><td>X</td><td>X</td><td></td></tr><tr><th>Atherinopsidae</th><td><i>Menidia beryllina</i> (Cope, 1867)</td><td>X</td><td></td><td></td></tr><tr><td><i>Odontesthes bonariensis</i> (Valenciennes, 1835)</td><td>X</td><td></td><td></td></tr><tr><th>Callichthyidae</th><td><i>Hoplosternum littorale</i> (Hancock, 1828)</td><td></td><td></td><td>X</td></tr><tr><th>Centrarchidae</th><td><i>Lepomis microlophus</i> (Günther, 1859)</td><td>X</td><td>X</td><td></td></tr><tr><td><i>Micropterus dolomieu</i> (Lacepède, 1802)</td><td>X</td><td></td><td></td></tr><tr><td><i>Micropterus salmoides</i> (Lacepède, 1802)</td><td>X</td><td></td><td></td></tr><tr><th>Centropomidae</th><td><i>Lates niloticus</i> (Linnaeus, 1758)</td><td>X</td><td></td><td></td></tr><tr><th>Channidae</th><td><i>Channa argus</i> (Cantor, 1842)</td><td>X</td><td></td><td>X</td></tr><tr><td><i>Channa marulius</i> (Hamilton, 1822)</td><td></td><td></td><td>X</td></tr><tr><th>Characidae</th><td><i>Pygocentrus nattereri</i> (Kner, 1858)</td><td>X</td><td></td><td></td></tr><tr><th>Cichlidae</th><td><i>Amatitlania nigrofasciata</i> (Günther, 1867)</td><td>X</td><td></td><td>X</td></tr><tr><td><i>Astronotus ocellatus</i> (Agassiz, 1831)</td><td>X</td><td></td><td></td></tr><tr><td><i>Cichla kelberi</i> (Kullander & Ferreira, 2006)</td><td>X</td><td></td><td></td></tr><tr><td><i>Cichla ocellaris</i> (Bloch & Schneider, 1801)</td><td>X</td><td></td><td>X</td></tr><tr><td><i>Cichlasoma uropthalma</i> (Günther, 1862)</td><td>X</td><td></td><td>X</td></tr><tr><td><i>Coptodon rendalli</i> (Boulenger, 1897)</td><td>X</td><td></td><td></td></tr><tr><td><i>Coptodon zilli</i> (Gervais, 1848)</td><td>X</td><td></td><td>X</td></tr><tr><td><i>Hemichromis letourneuxi</i> (Sauvage, 1880)</td><td>X</td><td></td><td></td></tr><tr><td><i>Herichthys cyanoguttatus</i> (Baird & Girard, 1854)</td><td>X</td><td></td><td></td></tr><tr><td><i>Oreochromis aureus</i> (Steindachner, 1864)</td><td>X</td><td></td><td>X</td></tr><tr><td><i>Oreochromis mossambicus</i> (Peters, 1852)</td><td>X</td><td></td><td>X</td></tr><tr><td><i>Oreochromis niloticus</i> (Linnaeus, 1758)</td><td>X</td><td></td><td>X</td></tr><tr><td><i>Parachromis managuensis</i> (Günther, 1862)</td><td>X</td><td></td><td>X</td></tr><tr><td><i>Pelmatotilapia mariae</i> (Boulenger, 1899)</td><td>X</td><td></td><td></td></tr><tr><td><i>Sarotherodon melanotheron</i> (Rüppell, 1852)</td><td>X</td><td></td><td></td></tr><tr><td><i>Serranochromis robustus</i> (Günther, 1864)</td><td>X</td><td></td><td></td></tr><tr><th>Clariidae</th><td><i>Clarias batrachus</i> (Linnaeus, 1758)</td><td>X</td><td></td><td>X</td></tr><tr><td><i>Clarias fuscus</i> (Lacepède, 1803)</td><td>X</td><td></td><td></td></tr><tr><td><i>Clarias gariepinus</i> (Burchell, 1822)</td><td>X</td><td></td><td></td></tr><tr><th>Clupeidae</th><td><i>Alosa aestivalis</i> (Mitchell, 1814)</td><td>X</td><td></td><td></td></tr><tr><td><i>Alosa pseudoharengus</i> (Wilson, 1811)</td><td>X</td><td>X</td><td></td></tr><tr><th>Cobitidae</th><td><i>Misgurnus anguillicaudatus</i> (Cantor, 1842)</td><td>X</td><td></td><td>X</td></tr><tr><th>Cyprinidae</th><td><i>Abramis brama</i> (Linnaeus, 1758)</td><td>X</td><td></td><td></td></tr><tr><td><i>Alburnus alburnus</i> (Linnaeus, 1758)</td><td>X</td><td></td><td></td></tr><tr><td><i>Barbus barbus</i> (Linnaeus, 1758)</td><td>X</td><td></td><td></td></tr><tr><td><i>Carassius auratus</i> (Linnaeus, 1758)</td><td></td><td></td><td>X</td></tr><tr><td><i>Carassius gibelio</i> (Bloch, 1782)</td><td>X</td><td></td><td></td></tr><tr><td><i>Ctenopharyngodon idella</i> (Valenciennes, 1844)</td><td>X</td><td>X</td><td>X</td></tr><tr><td><i>Culter alburnus</i> (Basilewsky, 1855)</td><td>X</td><td></td><td></td></tr><tr><td><i>Cyprinella lutrensis</i> (Baird & Girard, 1853)</td><td>X</td><td></td><td></td></tr><tr><td><i>Cyprinus carpio</i> (Linnaeus, 1758)</td><td>X</td><td>X</td><td>X</td></tr><tr><td><i>Gobio gobio</i> (Linnaeus, 1758)</td><td>X</td><td></td><td></td></tr><tr><td><i>Hypophthalmichthys molitrix</i> (Valenciennes, 1844)</td><td>X</td><td></td><td></td></tr><tr><td><i>Hypophthalmichthys nobilis</i> (Richardson, 1845)</td><td>X</td><td></td><td>X</td></tr><tr><td><i>Leuciscus idus</i> (Linnaeus, 1758)</td><td>X</td><td></td><td></td></tr><tr><td><i>Mylopharyngodon piceus</i> (Richardson, 1846)</td><td>X</td><td></td><td></td></tr><tr><td><i>Opsariichthys uncirostris</i> (Temminck & Schlegel, 1846)</td><td>X</td><td></td><td></td></tr><tr><td><i>Pimephales promelas</i> (Rafinsque, 1820)</td><td></td><td></td><td>X</td></tr><tr><td><i>Phoxinus phoxinus</i> (Linnaeus, 1758)</td><td>X</td><td></td><td></td></tr><tr><td><i>Protochondrostoma genei</i> (Bonaparte, 1839)</td><td>X</td><td></td><td></td></tr><tr><td><i>Pseudorasbora parva</i> (Temminck & Schlegel, 1846)</td><td>X</td><td></td><td></td></tr><tr><td><i>Rhodeus amarus</i> (Bloch, 1782)</td><td>X</td><td></td><td></td></tr><tr><td><i>Rutilus aula</i> (Bonparte,1841)</td><td>X</td><td></td><td></td></tr><tr><td><i>Rutilus rutilus</i> (Linnaeus, 1758)</td><td>X</td><td>X</td><td></td></tr><tr><td><i>Scardinius erythrophthalmus</i> (Linnaeus, 1758)</td><td>X</td><td>X</td><td></td></tr><tr><td><i>Tinca tinca</i> (Linnaeus, 1758)</td><td>X</td><td>X</td><td></td></tr><tr><th>Esocidae</th><td><i>Esox lucius</i> (Linnaeus, 1758)</td><td>X</td><td></td><td></td></tr><tr><td><i>Esox masquinongy</i> (Mitchill, 1824)</td><td>X</td><td></td><td></td></tr><tr><th>Gasterosteidae</th><td><i>Gasterosteus aculeatus</i> (Linnaeus, 1758)</td><td>X</td><td>X</td><td></td></tr><tr><th>Gobiidae</th><td><i>Neogobius melanostomus</i> (Pallas, 1814)</td><td>X</td><td>X</td><td></td></tr><tr><td><i>Ponticola platyrostris</i> (Pallas, 1814)</td><td>X</td><td></td><td></td></tr><tr><td><i>Proterorhinus semilunaris</i> (Heckel, 1837)</td><td>X</td><td></td><td></td></tr><tr><th>Heteropneustidae</th><td><i>Heteropneustes fossilis</i> (Bloch, 1794)</td><td>X</td><td></td><td></td></tr><tr><th>Ictaluridae</th><td><i>Ictalurus furcatus</i> (Valenciennes, 1840)</td><td>X</td><td></td><td></td></tr><tr><td><i>Pylodictis olivaris</i> (Rafinesque, 1818)</td><td>X</td><td></td><td></td></tr><tr><th>Loricariidae</th><td><i>Hypostomus plecostomus</i> (Linnaeus, 1758)</td><td>X</td><td></td><td>X</td></tr><tr><td><i>Pterygoplichthys anisitsi</i> (Eigenmann & Kennedy, 1903)</td><td></td><td></td><td>X</td></tr><tr><td><i>Pterygoplichthys disjunctivus</i> (Weber, 1991)</td><td>X</td><td></td><td>X</td></tr><tr><td><i>Pterygoplichthys multiradiatus</i> (Hancock, 1828)</td><td>X</td><td></td><td>X</td></tr><tr><td><i>Pterygoplichthys pardalis</i> (Castelnau, 1855)</td><td>X</td><td></td><td></td></tr><tr><th>Moronidae</th><td><i>Morone americana</i> (Gmelin, 1789)</td><td>X</td><td>X</td><td></td></tr><tr><th>Notopteridae</th><td><i>Chitala ornata</i> (Gray, 1831)</td><td>X</td><td></td><td></td></tr><tr><th>Odontobutidae</th><td><i>Perccottus glenii</i> (Dybowski, 1877)</td><td>X</td><td></td><td></td></tr><tr><th>Osmeridae</th><td><i>Hypomesus nipponensis</i> (McAllister, 1963)</td><td>X</td><td></td><td></td></tr><tr><td><i>Osmerus eperlanus</i> (Linnaeus, 1758)</td><td>X</td><td>X</td><td></td></tr><tr><td><i>Osmerus mordax</i> (Mitchill, 1814)</td><td>X</td><td></td><td></td></tr><tr><th>Osphronemidae</th><td><i>Trichogaster lalius</i> (Hamilton, 1822)</td><td>X</td><td></td><td></td></tr><tr><td><i>Trichopodus trichopterus</i> (Pallas, 1770)</td><td>X</td><td></td><td></td></tr><tr><th>Percidae</th><td><i>Gymnocephalus cernua</i> (Linnaeus, 1758)</td><td>X</td><td>X</td><td></td></tr><tr><td><i>Perca flavescens</i> (Mitchill, 1814)</td><td>X</td><td></td><td></td></tr><tr><td><i>Perca fluviatilis</i> (Linnaeus, 1758)</td><td>X</td><td>X</td><td></td></tr><tr><td><i>Sander lucioperca</i> (Linnaeus, 1758)</td><td>X</td><td></td><td></td></tr><tr><td><i>Sander vitreus</i> (Mitchill, 1818)</td><td>X</td><td></td><td></td></tr><tr><th>Petromyzontidae</th><td><i>Petromyzon marinus</i> (Linnaeus, 1758)</td><td></td><td>X</td><td></td></tr><tr><th>Poeciliidae</th><td><i>Belonesox belizanus</i> (Kner, 1860)</td><td>X</td><td></td><td></td></tr><tr><td><i>Gambusia affinis</i> (Baird & Girard, 1853)</td><td>X</td><td></td><td>X</td></tr><tr><td><i>Gambusia holbrooki</i> (Girard, 1859)</td><td>X</td><td></td><td></td></tr><tr><td><i>Poecilia latipinna</i> (Lesueur, 1821)</td><td>X</td><td></td><td></td></tr><tr><td><i>Poecilia reticulata</i> (Peters, 1859)</td><td>X</td><td></td><td>X</td></tr><tr><td><i>Poecilia sphenops</i> (Valciennes, 1846)</td><td>X</td><td></td><td>X</td></tr><tr><td><i>Xiphophorus helleri</i> (Heckel, 1848)</td><td>X</td><td></td><td></td></tr><tr><td><i>Xiphophorus variatus</i> (Meek, 1904)</td><td>X</td><td></td><td></td></tr><tr><th>Polypteridae</th><td><i>Polypterus delhezi</i> (Boulenger, 1899)</td><td></td><td></td><td>X</td></tr><tr><th>Pomacentridae</th><td><i>Neopomacentrus cyanomos</i> (Bleeker, 1856)</td><td>X</td><td></td><td></td></tr><tr><th>Potamotrygonidae</th><td><i>Potamotrygon falkneri</i> (Castex & Maciel, 1963)</td><td>X</td><td></td><td></td></tr><tr><td><i>Potamotrygon motoro</i> (Müller & Henle, 1841)</td><td>X</td><td></td><td></td></tr><tr><td><i>Potamotrygon schuhmacheri</i> (Castex, 1964)</td><td>X</td><td></td><td></td></tr><tr><th>Salmonidae</th><td><i>Coregonus albula</i> (Linnaeus, 1758)</td><td>X</td><td></td><td></td></tr><tr><td><i>Coregonus lavaretus</i> (Linnaeus, 1758)</td><td>X</td><td></td><td></td></tr><tr><td><i>Coregonus maraena</i> (Bloch, 1779)</td><td>X</td><td></td><td></td></tr><tr><td><i>Coregonus peled</i> (Gmelin, 1789)</td><td>X</td><td></td><td></td></tr><tr><td><i>Hucho hucho</i> (Linnaeus, 1758)</td><td>X</td><td></td><td></td></tr><tr><td><i>Oncorhynchus kisutch</i> (Walbaum, 1792)</td><td></td><td>X</td><td></td></tr><tr><td><i>Oncorhynchus mykiss</i> (Walbaum, 1792)</td><td></td><td>X</td><td></td></tr><tr><td><i>Oncorhynchus tshawytscha</i> (Walbaum, 1792)</td><td></td><td>X</td><td></td></tr><tr><td><i>Salmo trutta</i> (Linnaeus, 1758)</td><td></td><td>X</td><td></td></tr><tr><th>Scorpaenidae</th><td><i>Pterois miles</i> (Bennett, 1828)</td><td>X</td><td></td><td></td></tr><tr><td><i>Pterois volitans</i> (Linnaeus, 1758)</td><td>X</td><td></td><td></td></tr><tr><th>Siluridae</th><td><i>Silurus glanis</i> (Linnaeus, 1758)</td><td>X</td><td></td><td></td></tr></tbody></table>
Fig. 2 in Assessment of mercury contamination in Brycon falcatus (Characiformes: Bryconidae) and human health risk by consumption of this fish from the Teles Pires River, Southern Amazonia
Fig. 2. Relationship between weight and standard length of Brycon falcatus collected from rivers of the Teles Pires River basin from November 2014 to October 2016.
Fig. 1. a in Assessment of mercury contamination in Brycon falcatus (Characiformes: Bryconidae) and human health risk by consumption of this fish from the Teles Pires River, Southern Amazonia
Fig. 1. a. Brazil, with the state of Mato Grosso marked as stripes. b. The state of Mato Grosso with the Teles Pires River shown in bold. b. Brycon falcatus sample collection sites (black circles), accompanied by pictographs of the main human activities found at each site. The black arrow indicates the flow direction of rivers. The specimens were collected from November 2014 to October 2016.
Supplementary material 1 from: Dickey JWE, Arnott G, McGlade CLO, Moore A, Riddell GE, Dick JTA (2022) Threats at home? Assessing the potential ecological impacts and risks of commonly traded pet fishes. NeoBiota 73: 109-136. https://doi.org/10.3897/neobiota.73.80542
Table S1
Supplementary material 3 from: Dickey JWE, Arnott G, McGlade CLO, Moore A, Riddell GE, Dick JTA (2022) Threats at home? Assessing the potential ecological impacts and risks of commonly traded pet fishes. NeoBiota 73: 109-136. https://doi.org/10.3897/neobiota.73.80542
Figure S2
Supplementary material 2 from: Dickey JWE, Arnott G, McGlade CLO, Moore A, Riddell GE, Dick JTA (2022) Threats at home? Assessing the potential ecological impacts and risks of commonly traded pet fishes. NeoBiota 73: 109-136. https://doi.org/10.3897/neobiota.73.80542
Figure S1
Clinical Study to Assess High-DHA Fish Oil on Biomarkers of Cardiovascular Disease Risk in Adults on Statin Therapy
ClinicalTrials.gov study NCT01690312. IPD Sharing: Not stated. Countries: 1. Publications: 0.
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Allen Brain Atlas
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Annotated Behaviour and Observability Dataset (ABODe)
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DANDI Archive for NWB datasets
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The International Brain Laboratory public data releases expose standardized mouse decision-making experiments, including Neuropixels recordings, widefield calcium imaging, behavior, and session metadata accessed through the ONE API.
OpenNeuro
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