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Figure 1 in Novel tools and best practices for education about invasive alien species
Figure 1. On the right: Franz Josef Glacier School student recording a European alder (Alnus glutinosa) sapling using the iNat app, New Zealand (Photo: Murray Dawson). On the left: High school students measuring tree diameter in an urban park, Portugal (Photo: Hélia Marchante) and the excavation of Bohemian knotweed (Fallopia bohemica) during a KORINA science camp, Germany (Photo: Katrin Schneider).
Figure 2 in Risk screening and management of alien terrestrial planarians in The Netherlands
Figure 2. Cumulative number of introduced species based on the years of first records of alien terrestrial planarians in the United Kingdom, France, and The Netherlands.
Figure 1 in Mowing inhibits the invasion of the alien species Solidago altissima and is an effective management strategy
Figure 1. (a) Coverage of S. altissima and (b) the average number of species per quadrat in the S. altissima-dominant areas or uninvaded areas. Data are presented as means ± standard errors of 14 replicates. Bars with different letters are significantly different at p <0.05 (Student's t-test).
Figure 2 in Mowing inhibits the invasion of the alien species Solidago altissima and is an effective management strategy
Figure 2. Number of shoots of S. altissima in March 2018 and April 2019. Mowing 1: mowed once in July; Mowing 2: mowed twice in May and September; Mowing 3: mowed three times in May, July, and September; Eco 200: 30% of shoots in the quadrats were cut near the ground, and the cut surfaces were covered with Eco 200 block. Data are presented as means ± standard errors of 14 replicates. Bars with different letters are significantly different at p <0.05 (ANOVA with post hoc Tukey's test).
Figure 1 in Early detection of alien fern species through the consultation of horticultural catalogues
Figure 1. Prevalence of different (a, c) scales and (b, d) modes of trade expressed as proportions of the total number of traders and total number of species recorded per trade country. Treatment of species that were traded both on-ground and via e-commerce is detailed in the methods. Countries of trade: Canada (CA), United States of America (US), the United Kingdom and the Republic of Ireland (UKI), South Africa (ZA), Australia (AU), New Zealand (NZ).
FIG. 2 in Epiphytic bryophytes on alien host-tree species in Wrocław (SW Poland)
FIG. 2. — Comparison of the percentage of incidence of individual bryophyte species on trunks of alien host trees situated in complexes of urban greenery and urban buildings. Key: Species for which statistical significance (p<0.05) was found in preferences to occur more frequently in one of the land-use complexes are marked with an asterisk. Tests were not performed in cases in which one of the components (population in greenery or built-up space) was equal to zero.
FIG. 4 in Epiphytic bryophytes on alien host-tree species in Wrocław (SW Poland)
FIG. 4. — UPGMA phenogramme of the bryofloristic similarity of the phorophytes based on the species total coverage in the plots on the individual tree species. Key: I, II, IIa… groups and subgroups of the bryofloristic similarity; dashed lines show borders among the latter; alien tree species were marked in bold.
FIG. 3 in Epiphytic bryophytes on alien host-tree species in Wrocław (SW Poland)
FIG. 3. — Comparison of the percentage of incidence of the individual bryophyte species on trunks of alien host trees situated in the inner vs. outer city. Key: symbols as in Fig. 2. Tests were not performed in cases in which one of the components (population in inner or outer city) was equal to zero.
FIG. 1 in Epiphytic bryophytes on alien host-tree species in Wrocław (SW Poland)
FIG. 1. — Location of the plots in relation to the spatial structure of Wrocław (based on Urban Atlas 2012, Copernicus Land Monitoring System). Legend: 1, Continuous urban fabric (sealing level> 80%); 2, Discontinuous dense urban fabric (S.L.: 50%-80%); 3, Discontinuous medium and low urban fabric (S.L.: 10%-50%); 4, Industrial and commercial areas; 5, Transport and communication areas; 6, Forests; 7, Green urban areas; 8, Sports and leisure facilities; 9, Agricultural and semi-natural areas; 10, Water bodies; 11, Field measurements; 12, City inner zone (description in text).
Fig. 5 in Review of marine alien isopods in Türkiye with two new records: of Paracerceis sculpta and Paranthura japonica Abstract
Fig. 5: Body parts of Paranthura japonica (A, first antenna; B, second antenna; C, telson; D, uropodal exopod; E, uropodal endopod; F, fourth pereiopod; G, second pereiopod; H, first pereiopod. Scale bar: 80 µm).
Figure 4 in Alien turtles in Spain: Modeling a growing problem
Figure 4. Mobility-Oriented Parity estimation of the environmental similarity between donor and recipient regions. Lighter colors indicate greater similarity and higher model transferability. Clockwise, modeled similarity with North America (A), South America (B), eastern Mediterranean (C), and eastern Asia (D).
Figure 3 in Alien turtles in Spain: Modeling a growing problem
Figure 3. Map of Spain representing the sum of the projections of the alien species of tortoises. A) projections without bias correction; B) bias-corrected projections. The inset shows the Canary Islands.
Figure 2 in Alien turtles in Spain: Modeling a growing problem
Figure 2. Map of Spain representing the sum of the projections of the alien species of aquatic turtles. A) projections without bias correction; B) bias-corrected projections. The inset shows the Canary Islands.
Figure 1 in Alien turtles in Spain: Modeling a growing problem
Figure 1. Map of Spain representing the modeled niche overlap (projections without bias corrections) between native (blue) and alien (red) species of the alien species of turtles (A) and tortoises (B). The inset shows the Canary Islands.
Figure 3 in The effectiveness of hot water pressurized spray in field conditions to slow the spread of invasive alien species
Figure 3. (A) Average maximum temperature, (B) Average thermal exposure (area under the curve), of hot water spray applied to Dreissena polymorpha, Dikerogammarus villosus and Crassula helmsii from three distances (10, 20, 30 cm) and for three durations (5, 10, 15 seconds). Error bars show standard error (n = 36).
Figure 4 in Modelling hot spot areas for the invasive alien plant Elodea nuttallii in the EU
Figure 4. The occurrence with data thinned by extraction from subset 1 (A) and subset 2 (B) of occurrence data. The combined output of both is also presented (C). Areas with low uncertainty and above the habitat suitability threshold (i.e. priority areas) are marked in red while areas with high uncertainty are marked in yellow. The grid size of all 3 maps is 1 km2.
Figure 2 in Modelling hot spot areas for the invasive alien plant Elodea nuttallii in the EU
Figure 2. The model performance (regularized training gain) of the MaxEnt model generated using subset 2 of the occurrence data when the variable in question is omitted or used in isolation, compared to the performance of the model when all variables are used.
Figure 6. The occurrence with data from subset 1 in Modelling hot spot areas for the invasive alien plant Elodea nuttallii in the EU
Figure 6. The occurrence with data from subset 1 (A) and subset 3 (B). The combined output of both is also presented (C). Areas with low uncertainty and above the habitat suitability threshold (i.e. priority areas) are marked in red while areas with high uncertainty are marked in yellow. The grid size of all 3 maps is 1 km2.
Figure 2 in The effectiveness of hot water pressurized spray in field conditions to slow the spread of invasive alien species
Figure 2. Average temperature of hot water spray treatment applied to Dreissena polymorpha, Dikerogammarus villosus and Crassula helmsii from three distances (10, 20, 30 cm) and for three durations (5, 10, 15 seconds) and control cold water treatment (from 10 cm for 15 seconds). Grey shading shows standard error of average (n = 36).
Figure 1 in The effectiveness of hot water pressurized spray in field conditions to slow the spread of invasive alien species
Figure 1. Photographs of four invasive alien species utilised in hot water spray effectiveness experiments; a. Dikerogammarus villosus, b. Dreissena polymorpha, c. Crassula helmsii, d. Hydrocotyle ranunculoides. Photographs by Chris Pollock (a, b, c) and Stephanie Bradbeer (d).
ScienceDex guides
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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)
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DANDI Archive for NWB datasets
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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.