Find research datasets worth reusing

Fig. 4 in Native Bugseed Species Corispermum Intermedium Schweigg And Alien Corispermum Pallasii Steven In Coastal Habitats Of Latvia - New Knowledges Of Distribution And Invasions

Fig. 4. Annual pioneer vegetation with Corispermum pallasii on dune habitats in Mērsrags, Latvia (Photo: P. Evarts-Bunders).

Fig. 1 in Native Bugseed Species Corispermum Intermedium Schweigg And Alien Corispermum Pallasii Steven In Coastal Habitats Of Latvia - New Knowledges Of Distribution And Invasions

Fig. 1. Locations of transects in coastal habitats in the whole seashore of Latvia (Explanation of transects numbers see Table 1).

Fig. 3 in Native Bugseed Species Corispermum Intermedium Schweigg And Alien Corispermum Pallasii Steven In Coastal Habitats Of Latvia - New Knowledges Of Distribution And Invasions

Fig. 3. Distribution of Corispermum intermedium Schweigg (left) and C. pallasiii Steven (right) in Latvia (1st row – localities known till 1940; 2nd row – localities known 1940 – 1990; 3rd row - localities known or verified since 1990).

opencc-by-4.0Feb 2021View details →

FIGURE 6 in Adjustments in population and reproductive dynamics of native and non-native congeneric species during 26 years after invasion

FIGURE 6 | Stages of gonadal maturation at each age class for individuals of Serrasalmus marginatus (non-native; left) and S. maculatus (native; right) piranha species in the upper Paraná River floodplain, at each sampled time-period. The classification was based on Brown-Peterson et al. (2011). A. and B. 1986–1988: first time-period; C. and D. 2000–2002: second time-period; E. and F. 2010–2012: third timeperiod. CPUE values are fewer when compared to total CPUE values since individuals without standard length, sex and maturation stage were not considered in the estimation of age.

opencc-by-4.0Feb 2021View details →

FIGURE 3 in Adjustments in population and reproductive dynamics of native and non-native congeneric species during 26 years after invasion

FIGURE 3 | Age frequencies of both non-native (left) and native species (right) for each sex and each sampled time-period in the upper Paraná River floodplain. A. and B. 1986–1988: first time-period; C. and D. 2000–2002: second time-period; E. and F. 2010–2012: third time-period. CPUE values are fewer when compared to total CPUE values since individuals without standard length and sex were not considered in the estimation of age.

opencc-by-4.0Feb 2021View details →

FIGURE 1 in Adjustments in population and reproductive dynamics of native and non-native congeneric species during 26 years after invasion

FIGURE 1 | Map of the upper Paraná River floodplain showing its main tributaries. Sampling sites are marked: rivers and channels (circles), connected (squares), and isolated (triangles) floodplain lakes. Color of symbols are for Paraná (black), Ivinheima (white), and Baía (grey) rivers.

Figure 6 in New records of alien and potentially invasive grass (Poaceae) species for southern Africa

Figure 6. Jarava plumosa global distribution map, with country- or regional-level shading, taken and modified from POWO (2020).

Figure 2 in New records of alien and potentially invasive grass (Poaceae) species for southern Africa

Figure 2. Agrostis capillaris global distribution map, with country- or regional-level shading, taken and modified from POWO (2020).

Figure 5 in New records of alien and potentially invasive grass (Poaceae) species for southern Africa

Figure 5. Jarava plumosa; A, whole plant; B, inflorescence close-up; C, floret. Image A of R.J. Soreng et al. ZA-30 (US), B and C of R.J. Soreng et al. ZA-30 (PRE).

Figure 4 in New records of alien and potentially invasive grass (Poaceae) species for southern Africa

Figure 4. Festuca rubra global distribution map, with country- or regional-level shading, taken and modified from POWO (2020).

Figure 3 in New records of alien and potentially invasive grass (Poaceae) species for southern Africa

Figure 3. Festuca rubra; A, whole plant; B, lateral-tending rhizome covered in cataphylls; C, leaf sheath and junction with blade of a tiller showing strigose hairs; D, spikelet; E, base of palea with lemma removed to reveal the ovary and stamens; F, close-up of glabrous ovary apex. Images A and B of S.P. Sylvester et al. 3455 (US), C–F of S.P. Sylvester et al. 3455 (PRE).

opencc-by-4.0Feb 2019View details →

Fig. 1 in The Eurasian Collared Dove (Streptopelia decaocto Frivaldszky, 1838) - a subrecent invasive species of the avifauna of Bulgaria (subfossil records)

Fig. 1. Late Holocene subfossil record of the Eurasian Collared Dove (Streptopelia decaocto) in Bulgaria: Topchii (1); Madara - 1 (2); Madara - 2 (3); Shirokovo (4); Isperih (5).

opencc-by-4.0Jun 2016View details →

Fig. 3 in Establishment and spread of two invasive subterranean termite species (Coptotermes formosanus and C. gestroi; Isoptera: Rhinotermitidae) in metropolitan southeastern Florida (1990-2015)

Fig. 3. Cumulative area within metropolitan southeastern Florida that is at risk of infestation by Coptotermes species over time. An area at risk was determined by the zone within a 500 m radius from a termite record (at scale on the figure).

opencc-by-4.0Jun 2016View details →

Fig. 1 in Establishment and spread of two invasive subterranean termite species (Coptotermes formosanus and C. gestroi; Isoptera: Rhinotermitidae) in metropolitan southeastern Florida (1990-2015)

Fig. 1. Putative distribution of Coptotermes formosanus and Coptotermes gestroi in the southeastern United States. Both species have a distribution overlap in metropolitan southeastern Florida.

opencc-by-4.0Jun 2016View details →

Fig. 2 in Establishment and spread of two invasive subterranean termite species (Coptotermes formosanus and C. gestroi; Isoptera: Rhinotermitidae) in metropolitan southeastern Florida (1990-2015)

Fig. 2. Distribution of Coptotermes formosanus and Coptotermes gestroi in metropolitan southeastern Florida 2000–2015.

Fig. 3 in Novel aspects of Drosophila suzukii (Diptera: Drosophilidae) biology and an improved method for culturing this invasive species with a modified D. melanogaster diet

Fig. 3. Effect of triethylamine anesthetic exposure on the recovery of Drosophila adults: D. melanogaster (white circles, n = 181 adults), D. suzukii (black circles, n = 175 adults).

Fig. 2 in Novel aspects of Drosophila suzukii (Diptera: Drosophilidae) biology and an improved method for culturing this invasive species with a modified D. melanogaster diet

Fig. 2. Effects of dietary ethanol (normal environmental ethanol range ≈ 0– 9% ethanol) on Drosophila suzukii survival when compared with D. melanogaster tolerance to ethanol (top graph) and sex-specific sensitivities of D. suzukii adults to ethanol (bottom graph). Summary of probit analyses are provided and statistics with bo = intercept estimate, b1 = estimated slope estimate for each fly species, with b1 = 0 for the baseline control in each graph (D. suzukii [top graph], D. suzukii males [bottom graph]).

Fig. 1 in Novel aspects of Drosophila suzukii (Diptera: Drosophilidae) biology and an improved method for culturing this invasive species with a modified D. melanogaster diet

Fig. 1. Dietary manipulation of Drosophila suzukii cultures based on the use of 5 berry species (blackberry, strawberry, black cherry, blueberry, and grape) with a no-fruit (No Fruit) control (grey bars), and cultures to which yeast was added (+Y) or omitted (−Y) from 4-24® drosophila media (white bars). Asterisks indicate mean differences from 2 respective baseline controls (B), i.e., Blackberry−Y (14 d) and Blackberry+Y (21 d), according to multiple Wilcoxon 2-sample tests.

opencc-by-4.0Sep 2016View details →

Fig. 3 in Interspecific competition between two exotic parasitoids (Hymenoptera: Aphelinidae) of an invasive Bemisia tabaci species (Hemiptera: Aleyrodidae)

Fig. 3. Mean (± SE) number of progeny produced by Eretmocerus sp. nr. emiratus under all parasitoid release combinations and host plants. Treatment types are abbreviated as follows: Ee, Er. sp. nr. emiratus only; Eb/Ee, Encarsia bimaculata followed by Er. sp. nr. emiratus; Ee/Eb, Er. sp. nr. emiratus followed by En. bimaculata; Ee+Eb, Er. sp. nr. emiratus and En. bimaculata together. Columns with the same lower case letter within each host plant are not significantly different (difflsmeans, P> 0.05).