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Fig. 2 in Analysis of propagule pressure and genetic diversity in the invasibility of a freshwater apex predator: the peacock bass (genus Cichla)
Fig. 2. Structure bar plots of probabilities of assignment of each individual from populations of CP in green (1 - TOC, 2 - ITU, 3 - ML and 4 - FU) and CK in red (5 - TOC, 6 - ITU, 7 - TRM, 8 - RD). Probabilities of assignment (q) of each individual to each cluster are shown along the x-axis.
Figure 2 in Pets or predators? climate change and invasion risk of red-eared slider (Trachemys scripta elgans)
Figure 2. PCA-env for native and Indian climate for Trachemys scripta elegans. A) The green polygon represents nice unfilling, the blue polygon represents niche overlap, and the red polygon denotes nice expansion. The arrow indicates the niche centroid change. B) The correlation circle shows the relative contribution of different variables. C) and D) represent niche similarity and equivalency.
Figure 1 in Pets or predators? climate change and invasion risk of red-eared slider (Trachemys scripta elgans)
Figure 1. Predicted potential distribution of Trachemys scripta elegans under current and two future climate change scenarios.
Figure 3 in Pets or predators? climate change and invasion risk of red-eared slider (Trachemys scripta elgans)
Figure 3. Map showing species richness of native freshwater turtles at the sub-basin level in India.
Fig. 3 in Native anuran species as prey of invasive American Bullfrog, Lithobates catesbeianus, in Brazil: a review with new predation records
Fig. 3. Spatial distribution of Lithobates catesbeianus invasive populations and predation reports of native anurans in Brazil. White circles: American Bullfrog populations in Brazil (Both et al. 2011; Instituto Horus 2016); yellow stars: predation reports of adult Boana raniceps and adult Phyllomedusa distincta in southern and southeastern Brazil; light green circles: locations of 41 published predation records.
Fig. 2 in Native anuran species as prey of invasive American Bullfrog, Lithobates catesbeianus, in Brazil: a review with new predation records
Fig. 2. (A) Predation of an adult Phyllomedusa distincta by Lithobates catesbeianus, (B) Adult P. distincta partially digested, removed from the oral cavity of L. catesbeianus.
Fig. 1 in Native anuran species as prey of invasive American Bullfrog, Lithobates catesbeianus, in Brazil: a review with new predation records
Fig. 1. Adult Lithobates catesbeianus swallowing an adult Boana raniceps in an artificial permanent pond within pasture area in southern Brazil.
Invasive predators affect community-wide pollinator visitation
<p>Disruption of plant-pollinator interactions by invasive predators is poorly understood but may pose a critical threat for native ecosystems. In a multi-year field experiment in Hawaiʻi, we suppressed abundances of globally invasive predators and then observed insect visitation to flowers of six native plant species. Three plant species are federally endangered (<i>Haplostachys haplostachya</i>, <i>Silene lanceolata</i>, <i>Tetramolopium arenarium</i>) and three are common throughout their range (<i>Bidens menziesii</i>, <i>Dubautia linearis</i>, <i>Sida fallax</i>). Insect visitors were primarily generalist pollinators, including taxa that occur worldwide such as solitary bees (e.g., <i>Lasioglossum impavidum</i>), social bees (e.g., <i>Apis mellifera</i>), and syrphid flies (e.g., <i>Allograpta exotica</i>). We found that suppressing invasive rats (<i>Rattus rattus</i>), mice (<i>Mus musculus</i>), ants (<i>Linepithema humile</i>, <i>Tapinoma melanocephalum</i>), and yellowjacket wasps (<i>Vespula pensylvanica</i>) had positive effects on pollinator visitation to plants in 16 of 19 significant predator-pollinator-plant interactions. We found only positive effects of suppressing rats and ants, and both positive and negative effects of suppressing mice and yellowjacket wasps, on frequency of interactions between pollinators and plants. Model results predicted that predator eradication could increase frequency of insect visitation to flowering species, in some cases by >90%. Previous results from the system showed that these flowering species produced significantly more seed when flowers were allowed to outcross than when flowers were bagged to exclude pollinators, indicating limited autogamy. Our findings highlight the potential benefits of suppression or eradication of invasive rodents, ants, and yellowjackets in order to reverse pollination disruption, particularly in locations with high numbers of at-risk plant species or already imperiled pollinator populations.</p>
Dataset for: Native versus invasive nest predators in Iceland
<p>Common eider <em>(Somateria mollissima)</em> nest counts in Breiðafjörður Bay in West Iceland in the two archipelagos Brokey (95 islands over 123 years) and Purkey (39 islands over 27 years) along with size information on islands and their distance from mainland. Information on presence/absence of invasive American mink <em>(Neogale vison)</em> and native arctic fox <em>(Vulpes lagopus)</em> as well as the Atlantic Multidecadal Oscillation index (AMO) is provided, too.</p>
Invasive predators affect community-wide pollinator visitation
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Dataset for: Native versus invasive nest predators in Iceland
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Data and code from: Invasive grass indirectly alters seasonal patterns in seed predation
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Limited migration from physiological refugia constrains the rescue of native gastropods facing an invasive predator
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Data from: Fox control and fire influence the occurrence of invasive predators and threatened native prey
<p>It can be challenging to distinguish management impacts from other population drivers, including 'natural' processes and co-occurring threats. However, disentangling processes is important, particularly when management may have unintended consequences, such as mesopredator release. We explored the effects of long-term, broadscale poison-baiting programs on the distribution of red foxes <em>Vulpes vulpes</em> (targeted invasive predator), feral cats <em>Felis catus</em> (unmanaged invasive competitor) and two of their threatened native prey in two fire-affected regions of south-eastern Australia. We synthesised data from 3,667 camera-trap deployments at 1,232 sites (172,052 trap-nights), combining experimental manipulation of foxes and fire with space-for-time approaches. Fox control effectiveness––in terms of decreased probability of fox occurrence and increased probability of prey occurrence––depended on the duration and intensity of the poison-baiting program. The effects of fox control on prey occurrence also varied between the two native prey species: fox control was strongly beneficial to the long-nosed potoroo <em>Potorous tridactylus</em> but had no measurable effect on southern brown bandicoot <em>Isoodon obesulus</em> occurrence. Feral cat occupancy tended to be higher in landscapes with long-term fox control, although we found no effect of fox-bait density on fine-scale cat occurrence. Time since fire (0–80 years) was associated with the occurrence of each study species, but its association with invasive predators also differed among vegetation types. Invasive predators and altered fire regimes are key, often overlapping, biodiversity threats. Our work highlights the importance of fine-scale monitoring and consideration of multiple drivers in distribution models to develop effective, tailored conservation strategies.</p>
Fig. 6 in Reciprocal Predation Between Preserved And Invasive Species: Adult Bombina Bombina Predate Young Whitebaits Of Alien Fish Perccottus Glenii
Fig. 6. Plot for fitted model of initial number of live and predated P. glenii.
Fig. 2. Experimental box with P in Reciprocal Predation Between Preserved And Invasive Species: Adult Bombina Bombina Predate Young Whitebaits Of Alien Fish Perccottus Glenii
Fig. 2. Experimental box with P. glenii and pair of B. bombina.
Fig.11 in First Records Of New Aquatic Predator Pelodiscus Sinensis (Wiegmann 1835) In Latvia And Preliminary Ecological Risk Assessment Of The Invasion For Autochthonic Emys Orbicularis (Linnaeus 1758)
Fig.11. Peculiarities of P.sinensis findings waterbodies water connectivity in Latvia.
Fig.1 in First Records Of New Aquatic Predator Pelodiscus Sinensis (Wiegmann 1835) In Latvia And Preliminary Ecological Risk Assessment Of The Invasion For Autochthonic Emys Orbicularis (Linnaeus 1758)
Fig.1. Placement of the findings of Pelodiscus sinensis in Latvia.
Fig. 2 in Behavioral Responses Of Salmonid Fingerlings To New Invasive Fish Predator Perccottus Glenii
Fig. 2. Large adult Perccottus glenii male used in the experiment.
Fig. 4 in First Records Of New Aquatic Predator Pelodiscus Sinensis (Wiegmann 1835) In Latvia And Preliminary Ecological Risk Assessment Of The Invasion For Autochthonic Emys Orbicularis (Linnaeus 1758)
Fig. 4. Ventral side of the first P.sinensis #PeSi0001 found in Latvia.
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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.
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.