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Spread of the non-native anemone Anemonia alicemartinae Häussermann & Försterra, 2001 along the Humboldt-current large marine ecosystem: an ecological niche model approach
<p>Environmental variables and script</p>
Figure 1. Chama pacifica Broderip, 1835. a in The alien spreading of Chama pacifica Broderip, 1835 (Mollusca: Bivalvia: Chamidae) in the Mediterranean Sea
Figure 1. Chama pacifica Broderip, 1835. a) and b) Specimens from Fokià Bay (Kàrpathos Island, Greece): 52.0 × 31.9 and 49.5 × 50.6. c) Mediterranean spreading and first record dates.
Figure 1 in The History of Little Fire Ant Wasmannia auropunctata Roger in the Hawaiian Islands: Spread, Control, and Local Eradication
Figure 1. Number of known locations infested with Wasmannia auropunctata on Hawaii island between 1999 and 2007. Data sourced from Conant and Hirayama (2000); Motoki et al. (Motoki et al. 2013), P. Conant (pers. com.) and informal reports from Hawaii Department of Agriculture.
Figure 4 in The History of Little Fire Ant Wasmannia auropunctata Roger in the Hawaiian Islands: Spread, Control, and Local Eradication
Figure 4. Map of Kauai showing location infested by Wasmannia auropuntata (2012). Currently this site is putatively ant free.
Figure 2 in The History of Little Fire Ant Wasmannia auropunctata Roger in the Hawaiian Islands: Spread, Control, and Local Eradication
Figure 2. Location of properties infested with Wasmannia auropunctata in January 2007 prepared by Hawaii Department of Agriculture.
Figure 6 in The History of Little Fire Ant Wasmannia auropunctata Roger in the Hawaiian Islands: Spread, Control, and Local Eradication
Figure 6. Locations of known sites on Oahu infested with Wasmannia auropunctata. (currently the infestation in Mililani and the original infestation in Waimanalo are putatively ant-free)
Fig. 4 in Global and temporal spread of a taxonomically challenging invasive ant, Brachyponera chinensis (Hymenoptera: Formicidae)
Fig. 4. Temporal distribution of reproductive individuals (female and male alates) and brood presence within Brachyponera chinensis nests (dark gray) with overall sampling period shown in light gray. Numbers indicated when sampling occurred during the yr.
Fig. 3 in Global and temporal spread of a taxonomically challenging invasive ant, Brachyponera chinensis (Hymenoptera: Formicidae)
Fig. 3. Elevation distribution of Brachyponera chinensis in its native range. Shaded areas correspond to the elevation at which B. chinensis has been collected for each specific reference. Light gray areas were sites at a given altitude that were sampled, but no B. chinensis were found. References used are presented in
Fig. 2 in Global and temporal spread of a taxonomically challenging invasive ant, Brachyponera chinensis (Hymenoptera: Formicidae)
Fig. 2. Introduced range distributions. (A-E) Spread over time of Brachyponera chinensis from the earliest record in 1932 to 2018 in the US presented by 20-yr periods, with 1 record from Washington State not displayed; (F) and along the east coast of the Black Sea in south Russia and Georgia (with color code for temporal periods similar to Figs. D, E).
Fig. 1 in Global and temporal spread of a taxonomically challenging invasive ant, Brachyponera chinensis (Hymenoptera: Formicidae)
Fig. 1. Distribution of Brachyponera chinensis in Asia presenting records identified as part of the B. chinensis species complex (light gray) and confirmed records of B. chinensis s.s. (dark gray).
Fig. 1 in Spread of two invasive flies (Diptera: Drosophilidae) infesting commercial fruits in southeastern Brazil
Fig. 1. Brazilian states previously invaded by Drosophila suzukii and its new dispersion area in Espírito Santo State, Brazil.
Fig. 1 in Maconellicoccus hirsutus (Hemiptera: Pseudococcidae) in Brazil: recent spread, natural enemies, and new hosts
Fig. 1. Geographic distribution of Maconellicoccus hirsutus (Green) (Hemiptera: Pseudococcidae) in Brazil, and M. hirsutus collection locations in the state of Espírito Santo, Brazil.
Fig. 2 in Spread and distribution of the naturalized orchid bee Euglossa dilemma in Florida
Fig. 2. Spread of Euglossa dilemma in Florida from the first detection in Broward County in 2003 to much of central Florida by 2022. County names appear on the map illustrating the first occurrence of the bee in the county during that time period. Locality data are from collection and identification records the Florida State Collection of Arthropods in Gainesville from 2003 to 2022, and iNaturalist observations 2015 to 2022.
Fig. 1 in Spread and distribution of the naturalized orchid bee Euglossa dilemma in Florida
Fig. 1. Current distribution of Euglossa dilemma in Florida. Red dots are collection and identification record localities from the Florida State Collection of Arthropods from 2003 to 2022. Blue dots are iNaturalist observations from 2015 to 2022. Gray shading is the predicted potential distribution by the Maxent model (Hinojosa-Díaz et al. 2009).
Fig. 2. Sarcocyst and bradyzoite morphology. A. Isolated S in Sarcocystis rileyi (Apicomplexa) in Anas platyrhynchos in Europe with a potential for spread
Fig. 2. Sarcocyst and bradyzoite morphology. A. Isolated S. rileyi sarcocysts (mean length 5.25 mm) mounted in Aquatex, B. Wet smear of liberated bradyzoites (mean length 13.48 μm) from a sarcocyst of S. rileyi, C. Histological section of a sarcocyst in the musculature of the mallard (scale bar 100 μm), D. Histological section of a S. rileyi sarcocyst in pectoral musculature of male mallard showing densely packed bradyzoites with strongly stained nuclei. Haematoxylin staining. DePeX mounting, (scale bar 100 μm).
Fig. 3 in Sarcocystis rileyi (Apicomplexa) in Anas platyrhynchos in Europe with a potential for spread
Fig. 3. Alignment of PCR products. The shading on the scale at the top indicates a part of sequences, which resulted in no proper similarity towards any sequence at GenBank. Arrows indicate the features of the combined sequence (MZ151434). The grey bars indicate GenBank sequences with 100% similarity to the obtained sequences. The black bars indicate obtained PCR products, which notations at the left are "Forward primer vs Reverse primer".
Fig. 1 in Sarcocystis rileyi (Apicomplexa) in Anas platyrhynchos in Europe with a potential for spread
Fig. 1. Sarcocystis rileyi sarcocysts in mallard musculature. A. Pectoral musculature, B. Dorsal musculature, C. Hand and arm musculature, D. Leg musculature.
FIGURE 3 in Ichthyofauna on the move: fish colonization and spread through the São Francisco Interbasin Water Transfer Project
FIGURE 3 | Canonical analysis of principal coordinates (CAP) for the species and sites that contributed to the differences between basins and reservoirs (SF = São Francisco River basin, PB = Paraíba do Norte River basin, EAR = East Axis Reservoirs). Fitted site scores are colored and shaped according to the basin or EAR designation. A subset of species that explain at least 70% of the variation among sites is represented by species name abbreviation (two first letters of genus and the two first of the epithet). The only predictor significant for the linear model was richness.
FIGURE 2 in Ichthyofauna on the move: fish colonization and spread through the São Francisco Interbasin Water Transfer Project
FIGURE 2 | Seriated ordination of the species presence/ absence at the sampling sites of the East Axis of the São Francisco River Integration Project (SF-IWT). Black cells represent the presence of the species at a particular location. The species written in bold represents the new occurrence record in the receiving basin. In the upper right corner, Venn diagram showing species richness interactions between groups of sites. SF = São Francisco River basin, PB = Paraíba do Norte River basin, EAR = East Axis Reservoirs.
FIGURE 5 in Ichthyofauna on the move: fish colonization and spread through the São Francisco Interbasin Water Transfer Project
FIGURE 5 | Spatial distribution of Anchoviella vaillanti. The size of the circles represents juveniles/adults' abundance at each sampling site. The species went from the Sao Francisco donor basin through the SF-IWT East Axis artificial canals and reservoirs, reaching the receiving Paraíba do Norte basin sites, in the states of Pernambuco (PE) and Paraíba (PB), Brazil. DB = Donor basin, EAR = East Axis Reservoirs, RB = Receiving basin. Detailed location list of the sampling sites in Tab. S1.
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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.