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zenodo36/100

Figure 5 in Microplastics in commercial fish digestive tracts from freshwater habitats in Northern Thailand

Figure 5. Composition of microplastic found in freshwater fish; a) size b) morphotype c) color.

opencc-by-4.0Nov 2023View details →

zenodo36/100

Arctic Biodiversity: Arctic Freshwater Fishes

Biogeography and other attributes for Arctic organisms, various sources.Meltofte, H. (ed.) 2013. Arctic Biodiversity Assessment. Status and trends in Arctic biodiversity. Conservation of Arctic Flora and Fauna, Akureyri. https://arcticbiodiversity.is/index.php/the-report/chapters/fishes

opennotspecifiedAug 2024View details →

zenodo36/100

FIGURE 4 in Freshwater fishes of the Río de la Plata: current assemblage structure

FIGURE 4 | Figure caption on next page.

opencc-by-4.0Oct 2022View details →

zenodo36/100

The influence of food web structure and foraging behaviour on visual system traits in a predatory freshwater fish

Dataset used in the manuscript titled "The influence of food web structure and foraging behaviour on visual system traits in a predatory freshwater fish" Dataset includes lake trout visual system traits, body size, and food web structural attributes sampled from four different lakes in Algonquin, ON, Canada.

opencc-by-4.0May 2024View details →

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Table 1 in Risk screening of non-native freshwater fishes in Yunnan Province, China

Table 1. Non-native freshwater fish (with taxonomy) screened for their risk of invasiveness in Yunnan Province with the Aquatic Species Invasiveness Screening Kit (AS-ISK)<table><tbody><tr><th>Order</th><th>Family</th><th>Taxon name</th><th>Common name</th><th>A priori categorisation</th><th>Native region</th></tr></tbody><tbody><tr><th>Anguilliformes</th><td>Anguillidae</td><td>Anguilla anguilla</td><td>European eel</td><td>Non-invasive</td><td>Europe</td></tr><tr><td>Anguilla japonica</td><td>Japanese eel</td><td>Non-invasive</td><td>Asia</td></tr><tr><th>Acipenseriformes</th><td>Acipenseridae</td><td>Acipenser baerii</td><td>Siberian sturgeon</td><td>Invasive</td><td>Europe, Asia</td></tr><tr><th>Beloniformes</th><td>Hemiramphidae</td><td>Hyporhamphus intermedius</td><td>Asian pencil halfbeak</td><td>Non-invasive</td><td>China, Japan</td></tr><tr><th>Centrarchiformes</th><td>Centrarchidae</td><td>Micropterus salmoides</td><td>Largemouth bass</td><td>Invasive</td><td>North America</td></tr><tr><th>Characiformes</th><td>Serrasalmidae</td><td>Piaractus brachypomus</td><td>Pirapitinga</td><td>Invasive</td><td>Brazil, Colombia</td></tr><tr><td>Prochilo-dontidae</td><td>Prochilodus lineatus</td><td>Streaked prochilod</td><td>Non-invasive</td><td>Brazil, Chile</td></tr><tr><td>Cyprinidae</td><td>Acheilognathus chankaensis</td><td>Xingkai bitterling</td><td>Non-invasive</td><td>China</td></tr><tr><td>Acheilognathus macropterus</td><td>Largefin bitterling</td><td>Non-invasive</td><td>China</td></tr><tr><td>Carassius cuvieri</td><td>Japanese white crucian carp</td><td>Invasive</td><td>Japan</td></tr><tr><td>Ctenopharyngodon idella</td><td>Grass carp</td><td>Invasive</td><td>China</td></tr><tr><td>Cultrichthys erythropterus</td><td>Redfin culter</td><td>Non-invasive</td><td>China</td></tr><tr><td>Hypophthalmichthys molitrix</td><td>Silver carp</td><td>Invasive</td><td>China</td></tr><tr><td>Hypophthalmichthys nobilis</td><td>Bighead carp</td><td>Invasive</td><td>China</td></tr><tr><td>Labeo rohita</td><td>Roho labeo</td><td>Non-invasive</td><td>India, Myanmar</td></tr><tr><td>Megalobrama amblycephala</td><td>Wuchang bream</td><td>Non-invasive</td><td>China</td></tr><tr><td>Mylopharyngodon piceus</td><td>Black carp</td><td>Invasive</td><td>China</td></tr><tr><td>Parabramis pekinensis</td><td>White Amur bream</td><td>Non-invasive</td><td>China</td></tr><tr><td>Cobitidae</td><td>Paramisgurnus dabryanus</td><td>Taiwaninmutakala</td><td>Non-invasive</td><td>China</td></tr><tr><td>Cyprinidae</td><td>Sarcocheilichthys nigripinnis</td><td>Rainbow gudgeon</td><td>Non-invasive</td><td>China</td></tr><tr><td>Tinca tinca</td><td>Tench</td><td>Invasive</td><td>Europe</td></tr><tr><td>Toxabramis swinhonis</td><td>Thin sharpbelly</td><td>Non-invasive</td><td>China</td></tr><tr><th>Cyprinodontiformes</th><td>Poeciliidae</td><td>Gambusia affinis</td><td>Western mosquitofish</td><td>Invasive</td><td>America</td></tr><tr><th>Osmeriformes</th><td>Osmeridae</td><td>Hypomesus olidus</td><td>Pond smelt</td><td>Non-invasive</td><td>China, Japan</td></tr><tr><td>Salangidae</td><td>Neosalanx taihuensis</td><td>Taihu icefish</td><td>Invasive</td><td>China</td></tr><tr><td>Protosalanx hyalocranius</td><td>Clearhead icefish</td><td>Non-invasive</td><td>China</td></tr><tr><th>Perciformes</th><td>Cichlidae</td><td>Oreochromis aureus</td><td>Blue tilapia</td><td>Invasive</td><td>Africa</td></tr><tr><td>Oreochromis mossambicus</td><td>Mozambique tilapia</td><td>Invasive</td><td>Africa</td></tr><tr><td>Oreochromis niloticus</td><td>Nile tilapia</td><td>Invasive</td><td>Africa</td></tr><tr><td>Gobiidae</td><td>Rhinogobius cliffordpopei</td><td>Goby</td><td>Invasive</td><td>China</td></tr><tr><td>Sinipercidae</td><td>Siniperca chuatsi</td><td>Chinese perch</td><td>Non-invasive</td><td>China</td></tr><tr><th>Salmoniformes</th><td>Salmonidae</td><td>Oncorhynchus mykiss</td><td>Rainbow trout</td><td>Invasive</td><td>North America</td></tr><tr><td>Salmo trutta</td><td>Brown trout</td><td>Invasive</td><td>Europe</td></tr><tr><th>Siluriformes</th><td>Ictaluridae</td><td>Ameiurus nebulosus</td><td>Brown bullhead</td><td>Invasive</td><td>Canada, America</td></tr><tr><td>Clariidae</td><td>Clarias gariepinus</td><td>North African catfish</td><td>Invasive</td><td>Africa</td></tr><tr><td>Loricariidae</td><td>Hypostomus plecostomus</td><td>Suckermouth catfish</td><td>Invasive</td><td>South America</td></tr><tr><td>Ictaluridae</td><td>Ictalurus punctatus</td><td>Channel catfish</td><td>Invasive</td><td>North American</td></tr></tbody></table>

opencc-by-4.0Jan 2024View details →

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Table 2 in Risk screening of non-native freshwater fishes in Yunnan Province, China

Table 2. Non-native freshwater fish species assessed with the Aquatic Species Invasiveness Screening Kit (AS-ISK) for Yunnan Province<table><tbody><tr><th>Species name</th><th>A priori categorisation</th><th>Screening component</th><th></th><th>Confidence</th></tr><tr><th>BRA</th><th>BRA+CCA</th><th></th><th>CL</th><th>CF</th></tr><tr><th>Score</th><th>Outcome</th><th>Score</th><th>Outcome</th><th>Delta</th><th>Total</th><th>BRA</th><th>CCA</th><th>Total</th><th>BRA</th><th>CCA</th></tr></tbody><tbody><tr><th>Acheilognathus chankaensis</th><td>N</td><td>10</td><td>Medium</td><td>8</td><td>Medium</td><td>−2</td><td>3.4</td><td>3.4</td><td>3.5</td><td>0.85</td><td>0.85</td><td>0.88</td></tr><tr><th>Acheilognathus macropterus</th><td>N</td><td>−2</td><td>Low</td><td>−4</td><td>Low</td><td>−2</td><td>3.3</td><td>3.3</td><td>3.2</td><td>0.81</td><td>0.82</td><td>0.79</td></tr><tr><th>Acipenser baerii</th><td>Y</td><td>26</td><td>High</td><td>32</td><td>High</td><td>6</td><td>3.0</td><td>3.0</td><td>2.8</td><td>0.74</td><td>0.74</td><td>0.71</td></tr><tr><th>Ameiurus nebulosus</th><td>Y</td><td>29</td><td>High</td><td>35</td><td>High</td><td>6</td><td>3.0</td><td>3.0</td><td>2.8</td><td>0.75</td><td>0.76</td><td>0.71</td></tr><tr><th>Anguilla anguilla</th><td>N</td><td>0</td><td>Low</td><td>−2</td><td>Low</td><td>−2</td><td>3.0</td><td>3.0</td><td>3.0</td><td>0.77</td><td>0.77</td><td>0.75</td></tr><tr><th>Anguilla japonica</th><td>N</td><td>−2</td><td>Low</td><td>−4</td><td>Low</td><td>−2</td><td>3.1</td><td>3.2</td><td>3.0</td><td>0.79</td><td>0.80</td><td>0.75</td></tr><tr><th>Carassius cuvieri</th><td>Y</td><td>24</td><td>High</td><td>28</td><td>High</td><td>4</td><td>3.1</td><td>3.1</td><td>2.8</td><td>0.78</td><td>0.79</td><td>0.71</td></tr><tr><th>Clarias gariepinus</th><td>Y</td><td>39.5</td><td>High</td><td>47.5</td><td>High</td><td>8</td><td>3.1</td><td>3.1</td><td>2.8</td><td>0.77</td><td>0.78</td><td>0.71</td></tr><tr><th>Ctenopharyngodon idella</th><td>Y</td><td>29.5</td><td>High</td><td>33.5</td><td>High</td><td>4</td><td>3.3</td><td>3.3</td><td>3.2</td><td>0.83</td><td>0.84</td><td>0.79</td></tr><tr><th>Cultrichthys erythropterus</th><td>N</td><td>22.5</td><td>High</td><td>24.5</td><td>High</td><td>2</td><td>3.2</td><td>3.3</td><td>3.0</td><td>0.81</td><td>0.82</td><td>0.75</td></tr><tr><th>Gambusia affinis</th><td>Y</td><td>39</td><td>High</td><td>41</td><td>High</td><td>2</td><td>3.1</td><td>3.1</td><td>3.0</td><td>0.78</td><td>0.78</td><td>0.75</td></tr><tr><th>Hypomesus olidus</th><td>N</td><td>16</td><td>Medium</td><td>16</td><td>Medium</td><td>0</td><td>3.2</td><td>3.2</td><td>3.0</td><td>0.79</td><td>0.80</td><td>0.75</td></tr><tr><th>Hypophthalmichthys molitrix</th><td>Y</td><td>24</td><td>High</td><td>30</td><td>High</td><td>6</td><td>3.3</td><td>3.3</td><td>3.0</td><td>0.83</td><td>0.84</td><td>0.75</td></tr><tr><th>Hypophthalmichthys nobilis</th><td>Y</td><td>26</td><td>High</td><td>32</td><td>High</td><td>6</td><td>3.3</td><td>3.4</td><td>3.0</td><td>0.84</td><td>0.85</td><td>0.75</td></tr><tr><th>Hyporhamphus intermedius</th><td>N</td><td>7</td><td>Medium</td><td>7</td><td>Medium</td><td>0</td><td>3.2</td><td>3.2</td><td>3.0</td><td>0.80</td><td>0.80</td><td>0.75</td></tr><tr><th>Hypostomus plecostomus</th><td>Y</td><td>51</td><td>High</td><td>59</td><td>High</td><td>8</td><td>3.0</td><td>3.0</td><td>3.0</td><td>0.75</td><td>0.74</td><td>0.75</td></tr><tr><th>Ictalurus punctatus</th><td>Y</td><td>36.5</td><td>High</td><td>42.5</td><td>High</td><td>6</td><td>3.0</td><td>3.0</td><td>2.7</td><td>0.75</td><td>0.76</td><td>0.67</td></tr><tr><th>Labeo rohita</th><td>N</td><td>10</td><td>Medium</td><td>14</td><td>Medium</td><td>4</td><td>3.1</td><td>3.2</td><td>3.0</td><td>0.79</td><td>0.79</td><td>0.75</td></tr><tr><th>Megalobrama amblycephala</th><td>N</td><td>10</td><td>Medium</td><td>10</td><td>Medium</td><td>0</td><td>3.4</td><td>3.4</td><td>3.3</td><td>0.84</td><td>0.84</td><td>0.83</td></tr><tr><th>Micropterus salmoides</th><td>Y</td><td>35</td><td>High</td><td>43</td><td>High</td><td>8</td><td>3.1</td><td>3.2</td><td>2.5</td><td>0.79</td><td>0.81</td><td>0.63</td></tr><tr><th>Mylopharyngodon piceus</th><td>Y</td><td>29</td><td>High</td><td>35</td><td>High</td><td>6</td><td>3.3</td><td>3.3</td><td>3.0</td><td>0.82</td><td>0.83</td><td>0.75</td></tr><tr><th>Neosalanx taihuensis</th><td>N</td><td>24.5</td><td>High</td><td>22.5</td><td>High</td><td>−2</td><td>3.4</td><td>3.4</td><td>3.0</td><td>0.85</td><td>0.86</td><td>0.75</td></tr><tr><th>Oncorhynchus mykiss</th><td>Y</td><td>29</td><td>High</td><td>37</td><td>High</td><td>8</td><td>3.0</td><td>3.0</td><td>2.8</td><td>0.75</td><td>0.75</td><td>0.71</td></tr><tr><th>Oreochromis aureus</th><td>Y</td><td>49</td><td>High</td><td>61</td><td>High</td><td>12</td><td>3.1</td><td>3.1</td><td>2.7</td><td>0.77</td><td>0.78</td><td>0.67</td></tr><tr><th>Oreochromis mossambicus</th><td>Y</td><td>44.5</td><td>High</td><td>56.5</td><td>High</td><td>12</td><td>2.9</td><td>3.0</td><td>2.8</td><td>0.75</td><td>0.75</td><td>0.71</td></tr><tr><th>Oreochromis niloticus</th><td>Y</td><td>47</td><td>High</td><td>59</td><td>High</td><td>12</td><td>2.9</td><td>3.0</td><td>2.5</td><td>0.74</td><td>0.75</td><td>0.63</td></tr><tr><th>Parabramis pekinensis</th><td>N</td><td>5.5</td><td>Medium</td><td>3.5</td><td>Medium</td><td>−2</td><td>3.3</td><td>3.3</td><td>3.0</td><td>0.81</td><td>0.82</td><td>0.75</td></tr><tr><th>Paramisgurnus dabryanus</th><td>N</td><td>13.5</td><td>Medium</td><td>17.5</td><td>High</td><td>4</td><td>3.2</td><td>3.2</td><td>3.0</td><td>0.80</td><td>0.80</td><td>0.75</td></tr><tr><th>Piaractus brachypomus</th><td>Y</td><td>8</td><td>Medium</td><td>12</td><td>Medium</td><td>4</td><td>3.1</td><td>3.1</td><td>3.0</td><td>0.77</td><td>0.77</td><td>0.75</td></tr><tr><th>Prochilodus lineatus</th><td>N</td><td>11</td><td>Medium</td><td>17</td><td>Medium</td><td>6</td><td>3.1</td><td>3.1</td><td>3.0</td><td>0.76</td><td>0.77</td><td>0.75</td></tr><tr><th>Protosalanx hyalocranius</th><td>N</td><td>14.5</td><td>Medium</td><td>12.5</td><td>Medium</td><td>−2</td><td>3.1</td><td>3.1</td><td>2.8</td><td>0.76</td><td>0.77</td><td>0.71</td></tr><tr><th>Rhinogobius cliffordpopei</th><td>Y</td><td>37</td><td>High</td><td>43</td><td>High</td><td>6</td><td>3.1</td><td>3.1</td><td>2.8</td><td>0.76</td><td>0.77</td><td>0.71</td></tr><tr><th>Salmo trutta</th><td>Y</td><td>18</td><td>High</td><td>12</td><td>Medium</td><td>−6</td><td>2.9</td><td>2.9</td><td>3.0</td><td>0.73</td><td>0.72</td><td>0.75</td></tr><tr><th>Sarcocheilichthys nigripinnis</th><td>N</td><td>3</td><td>Medium</td><td>3</td><td>Medium</td><td>0</td><td>3.5</td><td>3.5</td><td>3.2</td><td>0.86</td><td>0.87</td><td>0.79</td></tr><tr><th>Siniperca chuatsi</th><td>N</td><td>14.5</td><td>Medium</td><td>18.5</td><td>High</td><td>4</td><td>3.0</td><td>3.0</td><td>2.8</td><td>0.74</td><td>0.74</td><td>0.71</td></tr><tr><th>Tinca tinca</th><td>Y</td><td>21</td><td>High</td><td>27</td><td>High</td><td>6</td><td>3.1</td><td>3.1</td><td>3.0</td><td>0.77</td><td>0.77</td><td>0.75</td></tr><tr><th>Toxabramis swinhonis</th><td>N</td><td>16.5</td><td>Medium</td><td>16.5</td><td>Medium</td><td>0</td><td>3.3</td><td>3.4</td><td>3.2</td><td>0.84</td><td>0.84</td><td>0.79</td></tr><tr><th>A priori categorisation (N: non-invasive; Y: invasive); Screening component (BRA: Basic Risk Assessment, BRA+CCA: BRA+ Climate Change Assessment, Delta: BRA+CCA score minus BRA score); Confidence (CL: confidence level, CF: confidence factor); Outcome (Low: score <1, Medium: 1 ≤ score <17.25, High: score ≥ 17.25)</th></tr></tbody></table>

opencc-by-4.0Jan 2024View details →

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A global dataset of freshwater fish trophic interactions

Dataset associated with Ridgway and Wesner. 2024. A global dataset of freshwater fish trophic interactions. Scientific Data.

opencc-by-4.0Sep 2024View details →

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Data from: Genomic signatures of paleodrainages in a freshwater fish along the southeastern coast of Brazil: genetic structure reflects past riverine properties

Past shifts in connectivity in riverine environments (for example, sea-level changes) and the properties of current drainages can act as drivers of genetic structure and demographic processes in riverine population of fishes. However, it is unclear whether the same river properties that structure variation on recent timescales will also leave similar genomic signatures that reflect paleodrainage properties. By characterizing genetic structure in a freshwater fish species (Hollandichthys multifasciatus) from a system of basins along the Atlantic coast of Brazil we test for the effects of paleodrainages caused by sea-level changes during the Pleistocene. Given that the paleodrainage properties differ along the Brazilian coast, we also evaluate whether estimated genetic diversity within paleodrainages can be explained by past riverine properties (i.e., area and number of rivers in a paleodrainage). Our results demonstrate that genetic structure between populations is not just highly concordant with paleodrainages, but that differences in the genetic diversity among paleodrainages correspond to the joint effect of differences in the area encompassed by, and the number of rivers, within a paleodrainage. Our findings extend the influence of current riverine properties on genetic diversity to those associated with past paleodrainage properties. We discuss how these findings may explain the inconsistent support for paleodrainages in structuring divergence from different global regions and the importance of taking into account past conditions for understanding the high species diversity of freshwater fish that we currently observe in the world, and especially in the Neotropics.

opencc-zeroDec 2016View details →

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Fig. 124. Chrysichthys auratus, 242.0 in The non-native freshwater fishes of Singapore: an annotated compilation

Fig. 124. Chrysichthys auratus, 242.0 mm SL, Bishan (Lim RHB).

opencc-by-4.0Apr 2020View details →

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Fig. 123 in The non-native freshwater fishes of Singapore: an annotated compilation

Fig. 123. Horabagrus brachysoma, length not recorded, 700 g, Kranji Reservoir (Looh CW).

opencc-by-4.0Apr 2020View details →

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Fig. 125. Leporinus fasciatus, 67.0 in The non-native freshwater fishes of Singapore: an annotated compilation

Fig. 125. Leporinus fasciatus, 67.0 mm SL, trade material.

opencc-by-4.0Apr 2020View details →

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Fig. 117. Trichopodus pectoralis, 96.6 in The non-native freshwater fishes of Singapore: an annotated compilation

Fig. 117. Trichopodus pectoralis, 96.6 mm SL, Sungei Buloh.

opencc-by-4.0Apr 2020View details →

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Fig. 120 in The non-native freshwater fishes of Singapore: an annotated compilation

Fig. 120. Number of first records of non-native fish species from 1849 to 2016.

opencc-by-4.0Apr 2020View details →

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Fig. 118 in The non-native freshwater fishes of Singapore: an annotated compilation

Fig. 118. Trichopsis schalleri, ca. 35.0 mm SL, Thailand.

opencc-by-4.0Apr 2020View details →

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Fig. 114. Sphaerichthys osphromenoides, 32.0 in The non-native freshwater fishes of Singapore: an annotated compilation

Fig. 114. Sphaerichthys osphromenoides, 32.0 mm SL, Malaysia.

opencc-by-4.0Apr 2020View details →

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Fig. 111. Macropodus opercularis, 45.5 in The non-native freshwater fishes of Singapore: an annotated compilation

Fig. 111. Macropodus opercularis, 45.5 mm SL male, trade material.

opencc-by-4.0Apr 2020View details →

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Fig. 106. Red Tilapia, 132.0 in The non-native freshwater fishes of Singapore: an annotated compilation

Fig. 106. Red Tilapia, 132.0 mm SL, Pangsua Pond.

opencc-by-4.0Apr 2020View details →

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Fig. 110 in The non-native freshwater fishes of Singapore: an annotated compilation

Fig. 110. Betta splendens, ca. 30 mm SL male, trade material.

opencc-by-4.0Apr 2020View details →

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Fig. 112. Osphronemus goramy, 142 in The non-native freshwater fishes of Singapore: an annotated compilation

Fig. 112. Osphronemus goramy, 142 mm SL, Serangoon Reservoir.

opencc-by-4.0Apr 2020View details →

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Fig. 126 in The non-native freshwater fishes of Singapore: an annotated compilation

Fig. 126. Veija × Mayaheros (?) hybrid, 115.9 mm SL, Jurong Lake.

opencc-by-4.0Apr 2020View details →

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Allen Brain Atlas

Allen Brain Atlas is an Allen Institute collection of brain map atlases, datasets, APIs, and analysis tools covering mouse, human, and non-human primate brain resources.

allen-brain-atlas

neuroscienceopenDocumentation, web resources, and API references are available online.

Last verified 2026-04-30Open record

Annotated Behaviour and Observability Dataset (ABODe)

ABODe is a University of Edinburgh DataShare dataset for behavior classification in group-housed mice using home-cage video, identities, bounding boxes, ground-plate positions, and annotator labels.

abode-home-cage

behavioral-neuroscienceopenThe DataShare record exposes download links for annotations, documentation, license text, and the zipped per-snippet data directory.

Last verified 2026-04-30Open record

DANDI Archive for NWB datasets

DANDI is a BRAIN Initiative archive for publishing and sharing neurophysiology data, including electrophysiology, optophysiology, and behavioral data packaged as NWB and related standards.

dandi-nwb

electrophysiologyopenPublished Dandiset metadata and archive endpoints are available through the production DANDI API.

Last verified 2026-04-30Open record

International Brain Laboratory public data

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.

ibl

behavioral-neuroscienceopenPublic sessions can be searched and loaded from the IBL public data server through ONE.

Last verified 2026-04-29Open record

OpenNeuro

OpenNeuro is a free, open platform for sharing neuroimaging datasets, with public search, dataset pages, and download paths for web, S3, DataLad, and the OpenNeuro CLI.

openneuro

neuroscienceopenPublished datasets are available on demand over the internet.

Last verified 2026-04-29Open record