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Comprehensive List of Non-Native Species Established in Three Major Regions of the U.S: Simpson et al, 2019
Simpson, Annie; Eyler, Meghan C.; Sikes, Derek; Bowser, Matt; and Sellers, Elizabeth A. (2020) A comprehensive list of non-native species established in three major regions of the United States: Version 3.0, (ver. 3.0, 2020): U.S. Geological Survey data release, <p></p>https://doi.org/10.5066/P9E5K160.<p></p>Simpson, A., Eyler, M.C., Sikes, D., Bowser, M., Sellers, E., Guala, G.F., Cannister, M., Libby, R., and Kozlowski, N., 2019, A comprehensive list of non-native species established in three major regions of the United States: Version 2.0, (ver. 2.0, 2019): U.S. Geological Survey data release, <p></p>https://doi.org/10.5066/P9E5K160.
Covsel output summary of 141 native - non-native plant species pairs in Switzerland
<p>The covariates as selected by the covsel R package (Adde et al. 2023) for 141 native - non-native congeneric plant species pairs in Switzerland.</p> <p>Publication of covsel R package:</p> <p>Adde, A., Rey, P.-L., Fopp, F., Petitpierre, B., Schweiger, A. K., Broennimann, O., Lehmann, A., Zimmermann, N. E., Altermatt, F., Pellissier, L., & Guisan, A. (2023). Too many candidates: Embedded covariate selection procedure for species distribution modelling with the covsel R package. Ecological Informatics, 75, 102080. https://doi.org/10.1016/j.ecoinf.2023.102080</p>
Table 1 in Risk screening of non-native freshwater fishes in Yunnan Province, China
<p><b>Table 1.</b> Non-native freshwater fish (with taxonomy) screened for their risk of invasiveness in Yunnan Province with the Aquatic Species Invasiveness Screening Kit (AS-ISK)</p><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><i>Anguilla anguilla</i></td><td>European eel</td><td>Non-invasive</td><td>Europe</td></tr><tr><td><i>Anguilla japonica</i></td><td>Japanese eel</td><td>Non-invasive</td><td>Asia</td></tr><tr><th>Acipenseriformes</th><td>Acipenseridae</td><td><i>Acipenser baerii</i></td><td>Siberian sturgeon</td><td>Invasive</td><td>Europe, Asia</td></tr><tr><th>Beloniformes</th><td>Hemiramphidae</td><td><i>Hyporhamphus intermedius</i></td><td>Asian pencil halfbeak</td><td>Non-invasive</td><td>China, Japan</td></tr><tr><th>Centrarchiformes</th><td>Centrarchidae</td><td><i>Micropterus salmoides</i></td><td>Largemouth bass</td><td>Invasive</td><td>North America</td></tr><tr><th>Characiformes</th><td>Serrasalmidae</td><td><i>Piaractus brachypomus</i></td><td>Pirapitinga</td><td>Invasive</td><td>Brazil, Colombia</td></tr><tr><td>Prochilo-dontidae</td><td><i>Prochilodus lineatus</i></td><td>Streaked prochilod</td><td>Non-invasive</td><td>Brazil, Chile</td></tr><tr><td>Cyprinidae</td><td><i>Acheilognathus chankaensis</i></td><td>Xingkai bitterling</td><td>Non-invasive</td><td>China</td></tr><tr><td><i>Acheilognathus macropterus</i></td><td>Largefin bitterling</td><td>Non-invasive</td><td>China</td></tr><tr><td><i>Carassius cuvieri</i></td><td>Japanese white crucian carp</td><td>Invasive</td><td>Japan</td></tr><tr><td><i>Ctenopharyngodon idella</i></td><td>Grass carp</td><td>Invasive</td><td>China</td></tr><tr><td><i>Cultrichthys erythropterus</i></td><td>Redfin culter</td><td>Non-invasive</td><td>China</td></tr><tr><td><i>Hypophthalmichthys molitrix</i></td><td>Silver carp</td><td>Invasive</td><td>China</td></tr><tr><td><i>Hypophthalmichthys nobilis</i></td><td>Bighead carp</td><td>Invasive</td><td>China</td></tr><tr><td><i>Labeo rohita</i></td><td>Roho labeo</td><td>Non-invasive</td><td>India, Myanmar</td></tr><tr><td><i>Megalobrama amblycephala</i></td><td>Wuchang bream</td><td>Non-invasive</td><td>China</td></tr><tr><td><i>Mylopharyngodon piceus</i></td><td>Black carp</td><td>Invasive</td><td>China</td></tr><tr><td><i>Parabramis pekinensis</i></td><td>White Amur bream</td><td>Non-invasive</td><td>China</td></tr><tr><td>Cobitidae</td><td><i>Paramisgurnus dabryanus</i></td><td>Taiwaninmutakala</td><td>Non-invasive</td><td>China</td></tr><tr><td>Cyprinidae</td><td><i>Sarcocheilichthys nigripinnis</i></td><td>Rainbow gudgeon</td><td>Non-invasive</td><td>China</td></tr><tr><td><i>Tinca tinca</i></td><td>Tench</td><td>Invasive</td><td>Europe</td></tr><tr><td><i>Toxabramis swinhonis</i></td><td>Thin sharpbelly</td><td>Non-invasive</td><td>China</td></tr><tr><th>Cyprinodontiformes</th><td>Poeciliidae</td><td><i>Gambusia affinis</i></td><td>Western mosquitofish</td><td>Invasive</td><td>America</td></tr><tr><th>Osmeriformes</th><td>Osmeridae</td><td><i>Hypomesus olidus</i></td><td>Pond smelt</td><td>Non-invasive</td><td>China, Japan</td></tr><tr><td>Salangidae</td><td><i>Neosalanx taihuensis</i></td><td>Taihu icefish</td><td>Invasive</td><td>China</td></tr><tr><td><i>Protosalanx hyalocranius</i></td><td>Clearhead icefish</td><td>Non-invasive</td><td>China</td></tr><tr><th>Perciformes</th><td>Cichlidae</td><td><i>Oreochromis aureus</i></td><td>Blue tilapia</td><td>Invasive</td><td>Africa</td></tr><tr><td><i>Oreochromis mossambicus</i></td><td>Mozambique tilapia</td><td>Invasive</td><td>Africa</td></tr><tr><td><i>Oreochromis niloticus</i></td><td>Nile tilapia</td><td>Invasive</td><td>Africa</td></tr><tr><td>Gobiidae</td><td><i>Rhinogobius cliffordpopei</i></td><td>Goby</td><td>Invasive</td><td>China</td></tr><tr><td>Sinipercidae</td><td><i>Siniperca chuatsi</i></td><td>Chinese perch</td><td>Non-invasive</td><td>China</td></tr><tr><th>Salmoniformes</th><td>Salmonidae</td><td><i>Oncorhynchus mykiss</i></td><td>Rainbow trout</td><td>Invasive</td><td>North America</td></tr><tr><td><i>Salmo trutta</i></td><td>Brown trout</td><td>Invasive</td><td>Europe</td></tr><tr><th>Siluriformes</th><td>Ictaluridae</td><td><i>Ameiurus nebulosus</i></td><td>Brown bullhead</td><td>Invasive</td><td>Canada, America</td></tr><tr><td>Clariidae</td><td><i>Clarias gariepinus</i></td><td>North African catfish</td><td>Invasive</td><td>Africa</td></tr><tr><td>Loricariidae</td><td><i>Hypostomus plecostomus</i></td><td>Suckermouth catfish</td><td>Invasive</td><td>South America</td></tr><tr><td>Ictaluridae</td><td><i>Ictalurus punctatus</i></td><td>Channel catfish</td><td>Invasive</td><td>North American</td></tr></tbody></table>
Table 2 in Risk screening of non-native freshwater fishes in Yunnan Province, China
<p><b>Table 2.</b> Non-native freshwater fish species assessed with the Aquatic Species Invasiveness Screening Kit (AS-ISK) for Yunnan Province</p><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><i>Acheilognathus chankaensis</i></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><i>Acheilognathus macropterus</i></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><i>Acipenser baerii</i></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><i>Ameiurus nebulosus</i></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><i>Anguilla anguilla</i></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><i>Anguilla japonica</i></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><i>Carassius cuvieri</i></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><i>Clarias gariepinus</i></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><i>Ctenopharyngodon idella</i></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><i>Cultrichthys erythropterus</i></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><i>Gambusia affinis</i></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><i>Hypomesus olidus</i></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><i>Hypophthalmichthys molitrix</i></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><i>Hypophthalmichthys nobilis</i></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><i>Hyporhamphus intermedius</i></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><i>Hypostomus plecostomus</i></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><i>Ictalurus punctatus</i></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><i>Labeo rohita</i></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><i>Megalobrama amblycephala</i></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><i>Micropterus salmoides</i></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><i>Mylopharyngodon piceus</i></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><i>Neosalanx taihuensis</i></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><i>Oncorhynchus mykiss</i></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><i>Oreochromis aureus</i></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><i>Oreochromis mossambicus</i></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><i>Oreochromis niloticus</i></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><i>Parabramis pekinensis</i></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><i>Paramisgurnus dabryanus</i></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><i>Piaractus brachypomus</i></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><i>Prochilodus lineatus</i></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><i>Protosalanx hyalocranius</i></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><i>Rhinogobius cliffordpopei</i></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><i>Salmo trutta</i></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><i>Sarcocheilichthys nigripinnis</i></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><i>Siniperca chuatsi</i></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><i>Tinca tinca</i></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><i>Toxabramis swinhonis</i></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>
Non-native vegetation encroachment drives functional turnover in island nematodes
<p>This community data matrix accompanies the manuscript "<span>Non-native vegetation encroachment drives functional turnover in island nematodes" by Adam Sharp, <span>Margarida Correia, Alan Gray, Rebecca Lawson, Martha Ledger, Noel Tawatao & Thomas Prior.</span></span></p>
The known unknowns in international border interceptions of non-native insects datasets
<p>Set of datasets for analysis in Turner et al. (2024).</p> <p>Turner, R.M., Liebhold, A.M., Nahrung, H.F. <em>et al.</em> The known unknowns in international border interceptions of non-native insects. <em>Biol Invasions</em> <strong>27</strong>, 50 (2025). https://doi.org/10.1007/s10530-024-03502-3</p>
Ancestral sperm ecotypes reveal multiple invasions of a non-native fish in northern Europe
For externally fertilising organisms in the aquatic environment, the abiotic fertilisation medium can be a strong selecting force. Among bony fishes, sperm are adapted to function in a narrow salinity range. A notable exception is the family Gobiidae, where several species reproduce across a wide salinity range. The family also contains several wide-spread invasive species. To better understand how these fishes tolerate such varying conditions, we measured sperm performance in relation to salinity from a freshwater and a brackish population within their ancestral Ponto-Caspian region of the round goby, Neogobius melanostomus. These two ancestral populations were then compared to nine additional invaded sites across northern Europe, both in terms of their sperm traits and by using genomic SNP markers. Our results show clear patterns of ancestral adaptations to freshwater and brackish salinities in their sperm performance. Population genomic analyses show that the ancestral ecotypes have generally established themselves in environments that fit their sperm adaptations. Sites close to ports with intense shipping show that both outbreeding and admixture can affect the sperm performance of a population in a given salinity. Rapid adaptation to local conditions is also supported at some sites. Historical and contemporary evolution in the traits of the round goby sperm cells is tightly linked to the population and seascape genomics as well as biogeographic processes in these invasive fishes. Since the risk of a population establishing in an area is related to the genotype by environment match, port connectivity and the ancestry of the round goby population can likely be useful for predicting the species spread.
Clustering of Catalytic Nanocompartments for Enhancing an Extracellular Non-Native Cascade Reaction
<p>Data underlying the figures in the publication “Clustering of Catalytic Nanocompartments for Enhancing an Extracellular Non-Native Cascade Reaction”, published in <em>Chemical Science</em> <strong>2021</strong>.</p> <p>Table of contents:</p> <p><strong>1. Figure 2</strong>; Zip. archive containing the experimental data of the graphs in <em>Figure 2</em>.</p> <p><strong>2. Figure 3</strong>; Zip. archive containing the experimental data of the graphs in <em>Figure 3</em>.</p> <p><strong>3. Figure 4</strong>; Zip. archive containing the experimental data of the graphs in <em>Figure 4</em>.</p> <p><strong>4. Figure 5</strong>; Zip. archive containing the experimental data of the graphs in <em>Figure 5</em>.</p> <p><strong>5. Figure 7</strong>; Zip. archive containing the experimental data of the graphs in <em>Figure 7</em>.</p>
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).
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).
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.
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.
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.
Fig. 118 in The non-native freshwater fishes of Singapore: an annotated compilation
Fig. 118. Trichopsis schalleri, ca. 35.0 mm SL, Thailand.
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.
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.
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.
Fig. 110 in The non-native freshwater fishes of Singapore: an annotated compilation
Fig. 110. Betta splendens, ca. 30 mm SL male, trade material.
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.
Fig. 126 in The non-native freshwater fishes of Singapore: an annotated compilation
Fig. 126. Veija × Mayaheros (?) hybrid, 115.9 mm SL, Jurong Lake.
ScienceDex guides
Understand access before you commit
These curated guides explain access requirements, typical timelines, costs, and reuse considerations for widely used research datasets.
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.
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.
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.
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.
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.