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183 results for “exotic species”
Figure 5 from: Mesibov R, Car CA (2015) A new genus and species of native exotic millipede in Australia (Diplopoda, Polydesmida, Paradoxosomatidae). ZooKeys 498: 7-16. https://doi.org/10.3897/zookeys.498.9716
Figure 5 - Known localities for Taxidiotisoma portabile sp. n. as of 30 March 2015 (filled and open circles). The eight numbered localities are discussed in the text. Geographic projection; inset shows location of main map.
Figure 4 from: Mesibov R, Car CA (2015) A new genus and species of native exotic millipede in Australia (Diplopoda, Polydesmida, Paradoxosomatidae). ZooKeys 498: 7-16. https://doi.org/10.3897/zookeys.498.9716
Figure 4 - Taxidiotisoma portabile sp. n., holotype male (AM KS. 94041), detail of left gonopod tip, anterior view. Abbreviations: F femorite, NSB non-seminiferous branch, S solenomere, s1 process with prostatic groove, s2 cowl-shaped process, pg prostatic groove, t tooth. Dotted line denotes path of prostatic groove. Scale bar: 0.2 mm.
Figure 2 from: Mesibov R, Car CA (2015) A new genus and species of native exotic millipede in Australia (Diplopoda, Polydesmida, Paradoxosomatidae). ZooKeys 498: 7-16. https://doi.org/10.3897/zookeys.498.9716
Figure 2 - Taxidiotisoma portabile sp. n., male ex NMV K-12071. A Leg 1 B Sternal lamella on ring 5, posterior view. Scale bars: 0.2 mm.
Figure 3 from: Mesibov R, Car CA (2015) A new genus and species of native exotic millipede in Australia (Diplopoda, Polydesmida, Paradoxosomatidae). ZooKeys 498: 7-16. https://doi.org/10.3897/zookeys.498.9716
Figure 3 - Taxidiotisoma portabile sp. n., holotype male (AM KS. 94041), left gonopod. A posterior B anterior C medial and D lateral views. Abbreviations: C coxa, F femorite, NSB non-seminiferous branch, PF prefemur, S solenomere, s1 process with prostatic groove, s2 cowl-shaped process. Scale bars: 0.5 mm.
Figure 1 from: Mesibov R, Car CA (2015) A new genus and species of native exotic millipede in Australia (Diplopoda, Polydesmida, Paradoxosomatidae). ZooKeys 498: 7-16. https://doi.org/10.3897/zookeys.498.9716
Figure 1 - Taxidiotisoma portabile sp. n., male ex NMV K-12071. A Habitus B dorsal views of midbody rings C lateral views of midbody rings; anterior to right D Lateral views of head E oblique views of head. Scale bars: 2.5 mm (A); 1 mm (B, C); 0.5 mm (D, E).
Data from: Enhancing gardens as habitats for flower-visiting aerial insects (pollinators): should we plant native or exotic species?
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Data from: The relationship between native species richness and exotic species richness or occurrence will always be negative when the total number of species is accounted for in statistical models: A response to Beaury et al.
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Data from: Exotic or not, leaf trait dissimilarity modulates the effect of dominant species on mixed litter decomposition
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Figure 3 from: Żurawlew P, Desutter-Grandcolas L, Szymański P, Herman DB (2020) New records of exotic crickets in Europe: Homoeogryllus species (Orthoptera: Gryllidea: Phalangopsidae). Journal of Orthoptera Research 29(2): 121-125. https://doi.org/10.3897/jor.29.50387
Figure 3 Homoeogryllus tessellatus (Serville, 1838) male observed in Warsaw (Poland).
Data from: Exotic species enhance response diversity to land-use change but modify functional composition
Two main mechanisms may buffer ecosystem functions despite biodiversity loss. First, multiple species could share similar ecological roles, thus providing functional redundancy. Second, species may respond differently to environmental change (response diversity). However, ecosystem function would be best protected when functionally redundant species also show response diversity. This linkage has not been studied directly, so we investigated whether native and exotic pollinator species with similar traits (functional redundancy) differed in abundance (response diversity) across an agricultural intensification gradient. Exotic pollinator species contributed most positive responses, which partially stabilized overall abundance of the pollinator community. However, although some functionally redundant species exhibited response diversity, this was not consistent across functional groups and aggregate abundances within each functional group were rarely stabilized. This shows functional redundancy and response diversity do not always operate in concert. Hence, despite exotic species becoming increasingly dominant in human-modified systems, they cannot replace the functional composition of native species.
Figure 1 in A preliminary report on freshwater mollusca of Arunachal Pradesh, Northeast India and first report of an exotic invasive species Physella acuta (Draparnaud, 1805) from the state
Figure 1. Physella acuta (Draparnaud, 1805).
Data from: Exotic plant species are locally adapted but not to high UV‐B radiation: a reciprocal multi‐species experiment
Ultraviolet (UV) radiation intensities differ among global regions, with significantly higher levels in the southern hemisphere. UV-B may act as an environmental filter during plant invasions, which might particularly apply to plant species from Europe introduced to New Zealand. Just like for any other abiotic or biotic filter, successful invaders can cope with novel environmental conditions via plastic responses and/or through rapid adaptation by natural selection in the exotic range. We conducted a multi-species experiment with herbaceous plants in two common gardens located in the species' 'native' and exotic ranges, in Germany and New Zealand, respectively. We used plants of German and New Zealand origin of eight species to test for adaptation to higher UV-B radiation in their new range. In each common garden, all plants were exposed to three radiation treatments: (i) ambient sunlight, (ii) exclusion of UV-B while transmitting ambient UV-A, and (iii) combined exclusion of UV-B and UV-A. Linear mixed-effect models revealed significant effects of UV-B on growth and leaf traits and an indication for UV-B-induced biomass reduction in both common gardens pointing to an impact of natural, ambient UV radiation intensities experienced by plants in the northern and in the southern hemisphere. In both common gardens, the respective local plants (i.e. German origins in Germany, New Zealand origins in New Zealand) displayed enhanced productivity and aboveground biomass allocation, thus providing evidence for recent evolutionary processes in the exotic range. Genetic differentiation between different origins in consequence of divergent local selection pressures was found for specific leaf area. This differentiation particularly hints at different selective forces in both ranges while only little evidence was found for an immediate selective effect of high UV-B intensities in the exotic range. However, reaction norm slopes across ranges revealed higher plasticity of exotic individuals in functional leaf traits that might allow for a more sensitive regulation of photoprotection measures in response to UV-B. During the colonization, New Zealand populations might have been selected for the observed higher phenotypic plasticity and a consequently increased ability to successfully spread in the exotic range.
Data from: Exotic species enhance response diversity to land-use change but modify functional composition
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Data from: Additive genetic variation in resistance traits of an exotic pine species: little evidence for constraints on evolution of resistance against native herbivores
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Data from: A theory of island biogeography for exotic species
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Data from: Exotic plant species are locally adapted but not to high UV‐B radiation: a reciprocal multi‐species experiment
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FIGURE 27 in Identification of exotic pest and Australian native and naturalised species of Tetranychus (Acari: Tetranychidae)
FIGURE 27. Tetranychus pacificus McGregor, female. (a) Pretarsus I, IV; (b) Transverse pattern of dorsal striae between setae e and f; (c) Pregenital striae; (d) Pregenital striae, different specimen. Male. (e) Pretarsi I and II; (f) Aedeagus, different specimens.
FIGURE 23 in Identification of exotic pest and Australian native and naturalised species of Tetranychus (Acari: Tetranychidae)
FIGURE 23. Tetranychus marianae McGregor, female. (a) Pretarsus III; (b) Tarsi I, dorsal and ventral view, dashed line indicates level of proximal duplex setae; (c) Diamond-shaped pattern of dorsal striae between setae e and f; (d) Ventral striae between setae 3a. Male. (e) Pretarsus I; (f) Pretarsus II; (g) Aedeagus.
FIGURE 12 in Identification of exotic pest and Australian native and naturalised species of Tetranychus (Acari: Tetranychidae)
FIGURE 12. Tetranychus desertorum Banks, female. (a) Pretarsus I; (b) Weak diamond-shaped pattern of dorsal striae between setae e and f; (c) Pregenital striae. Male: (d) Aedeagus; (e) Pretarsus I; (f) Pretarsus II.
Data from: Nutrient enhancement of allelopathic effects of exotic on native plant species
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