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112 results for “introduced population”

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zenodo32/100

Figure 1 in The conservation paradox of an introduced population of a threatened species: spadefoot toads in the coastal dunes of the Netherlands

Figure 1. Sampling sites of the common spadefoot toad (Pelobates fuscus). The main map shows localities sampled outside and the inset localities sampled inside the Netherlands (see main text for details). A rough outline of the natural distribution range in the Netherlands is shaded grey. Localities that contain haplotypes found in the Netherlands are colour coded; otherwise they are left grey (FUS stands for P. fuscus). Sampling details are in supplementary table S1.

opennotspecifiedNov 2022View details →
zenodo32/100

Figure 3 in The conservation paradox of an introduced population of a threatened species: spadefoot toads in the coastal dunes of the Netherlands

Figure 3. Haplotype network for the common spadefoot toad (Pelobates fuscus) Haplotypes relevant to the current study are colour coded; the remainder is left grey (details in supplementary table S1). The prefix 'FUS' is not shown for the haplotype codes.

opennotspecifiedNov 2022View details →
zenodo32/100

Figure 2 in An extended mtDNA phylogeography for the alpine newt illuminates the provenance of introduced populations

Figure 2. Majority rule consensus Bayesian phylogeny for the alpine newt (Ichthyosaura alpestris) based on 651 bp of the mtDNA gene ND4. The outgroup is not shown. Spanish haplotypes are highlighted with an asterisk. Haplotype details can Downloaded from Brill.com 08/07/2024 04:58:17PM be found in supplementary table S1 and a moreviadetailed Open Access version. of Thisthisis an phylogenyopen is access availablearticlein supplementary distributed fig. underS1. the terms

opennotspecifiedJul 2023View details →
zenodo32/100

Figure 2 in The conservation paradox of an introduced population of a threatened species: spadefoot toads in the coastal dunes of the Netherlands

Figure 2. Phylogenetic tree for common spadefoot toad (Pelobates fuscus) and Pallas's spadefoot toad (P. vespertinus). Haplotypes relevant to the current study are colour coded; the remainder is left grey (details in Table S1). Haplotype abbreviations are: FUS = P. fuscus, VES = P. vespertinus, BAL = P. balcanicus, SYR = P. syriacus, CUL = P. cultripes, and VAR = P. varaldii.

opennotspecifiedNov 2022View details →
dryad32/100

Data from: Linking genetic diversity and temporal fluctuations in population abundance of the introduced feral cat (Felis silvestris catus) on the Kerguelen Archipelago.

Linking temporal variations of genetic diversity, including allelic richness and heterozygosity, and spatio-temporal fluctuations in population abundance has emerged as an important tool for understanding demographic and evolutionary processes in natural populations. This so-called 'genetic monitoring' was conducted across 12 consecutive years (1996-2007) at three sites for the feral cat, introduced onto the Kerguelen Archipelago fifty years ago. Temporal changes in allelic richness and heterozygosity at 18 microsatellite DNA loci were compared to temporal changes in the adult population abundance index, obtained by typical demographic monitoring. No association was found at the island spatial scale but we observed an association between genetic diversity and adult population indices from year to year within each study site. More particularly, the magnitude of successive increases or decreases in the adult population abundance index appeared to be the major factor linking the trajectories of genetic diversity and adult population abundance indices. Natal dispersal and/or local recruitment, both facilitated by high juvenile survival when the adult population size is small, are proposed as the major demographic processes contributing to such an observed pattern. Finally, we suggested avoiding the use of the harmonic mean as an estimator of long-term population size to study the relationships between demographic fluctuations and heterozygosity in populations characterized by strong multi-annual density fluctuations.

opencc-zeroDec 2010View details →
dryad32/100

Data from: Population genomics of the introduced and cultivated Pacific kelp Undaria pinnatifida: marinas — not farms — drive regional connectivity and establishment in natural rocky reefs

Ports and farms are well-known primary introduction hotspots for marine non-indigenous species (NIS). The extent to which these anthropogenic habitats are sustainable sources of propagules and influence the evolution of NIS in natural habitats was examined in the edible seaweed Undaria pinnatifida, native to Asia and introduced to Europe in the 1970s. Following its deliberate introduction 40 years ago along the French coast of the English Channel, this kelp is found in three contrasting habitat types: farms, marinas, and natural rocky reefs. In light of the continuous spread of this NIS, it is imperative to better understand the processes behind its sustainable establishment in the wild. In addition, developing effective management plans to curtail the spread of U. pinnatifida requires determining how the three types of populations interact with one another. In addition to an analysis using microsatellites, we developed, for the first time in a kelp, a ddRAD-sequencing technique to genotype 738 individuals sampled in 11 rocky reefs, 12 marinas, and 2 farms located along ca. 1000 km of coastline. As expected, the RAD-seq panel showed more power than the microsatellite panel for identifying fine-grained patterns. However, both panels demonstrated habitat-specific properties of the study populations. In particular, farms displayed very low genetic diversity and no inbreeding conversely to populations in marinas and natural rocky reefs. In addition, strong, but chaotic regional genetic structure, was revealed, consistent with human-mediated dispersal (e.g., leisure boating). We also uncovered a tight relationship between populations in rocky reefs and those in nearby marinas, but not with nearby farms, suggesting spill-over from marinas into the wild. Finally, a temporal survey (20 generations) showed that wild populations are self-sustaining, without local adaptation to any of the three habitats. These findings highlight that limiting the spread of U. pinnatifida requires management policies that also target marinas.

opencc-zeroDec 2017View details →
dryad32/100

Data from: Introduced Scotch broom (Cytisus scoparius) invades the genome of native populations in vulnerable heathland habitats

Cytisus scoparius is a global invasive species that affects local flora and fauna at the intercontinental level. Its natural distribution spans across Europe, but seeds have also been moved among countries, mixing plants of native and non-native genetic origins. Hybridization between the introduced and native gene pool is likely to threaten both the native gene pool and the local flora. In this study, we address the potential threat of invasive C. scoparius to local gene pools in vulnerable heathlands. We used nuclear single nucleotide polymorphic (SNP) and simple sequence repeat (SSR) markers together with plastid SSR and indel markers to investigate the level and direction of gene flow between invasive and native heathland C. scoparius. Analyses of population structures confirmed the presence of two gene pools: one native and the other invasive. The nuclear genome of the native types was highly introgressed with the invasive genome, and we observed advanced-generation hybrids, suggesting that hybridization has been occurring for several generations. There is asymmetrical gene flow from the invasive to the native gene pool, which can be attributed to higher fecundity in the invasive individuals, measured by the number of flowers and seed pods. Strong spatial genetic structure in plastid markers and weaker structure in nuclear markers suggest that seeds spread over relatively short distances and that gene flow over longer distances is mainly facilitated by pollen dispersal. We further show that the growth habits of heathland plants become more vigorous with increased introgression from the invaders. Implications of the findings are discussed in relation to future management of invading C. scoparius.

opencc-zeroDec 2015View details →
dryad32/100

Introduced populations of the garden lupine are adapted to local generalist snails but have lost alkaloid diversity

<p>Intraspecific variation in growth and defence among plant populations can be driven by differences in (a)biotic conditions, such as herbivory and resources. Introduction of species to novel environments affects simultaneously herbivory encountered by a plant and resource availability both directly and via altered competitive environment. Here, we address the question of how growth (leaf mass per area (LMA), plant size) and resistance traits (leaf alkaloids, leaf trichomes, resistance to a generalist snail) vary and covary between native and introduced populations of the garden lupine, Lupinus polyphyllus. We focused specifically on evolved differences among populations by measuring traits from plants grown from seed in a common environment. Plants from the introduced populations were more resistant against the generalist snail, Arianta arbustorum, and they had more leaf trichomes and higher LMA than plants from the native populations. The composition of alkaloids differed between native and introduced populations, with the native populations having more diversity in alkaloids among them. Resistance was positively associated with plant size and LMA across all populations. Other trait associations differed between native and introduced areas, implying that certain trade-offs may be fundamentally different between native and introduced populations. Our results suggest that, for the introduced populations, the loss of native herbivores and the alterations in resource availability have led to a lower diversity in leaf alkaloids among populations and may facilitate the evolution of novel trait optima without compensatory trade-offs. Such phytochemical similarity among introduced populations provides novel insights into mechanisms promoting successful plant invasions.</p>

opencc-zeroSep 2021View details →
zenodo32/100

Supplementary material 1 from: Craves JA, Anich NM (2023) Status and distribution of an introduced population of European Goldfinches (Carduelis carduelis) in the western Great Lakes region of North America. NeoBiota 81: 129-155. https://doi.org/10.3897/neobiota.81.97736

Records of European Goldfinches in North America, 2001–2021, by state/province with county totals. Records represent observations, not individual birds. Regions included in the western Great Lakes region are in bold

opencc-zeroJan 2023View details →
zenodo32/100

Supplementary material 2 from: Craves JA, Anich NM (2023) Status and distribution of an introduced population of European Goldfinches (Carduelis carduelis) in the western Great Lakes region of North America. NeoBiota 81: 129-155. https://doi.org/10.3897/neobiota.81.97736

Mapped locations of confirmed breeding European Goldfinches in the western Great Lakes region, 2001–2021

opencc-zeroJan 2023View details →
dryad32/100

Data: Phenotypic trait differences between Iris pseudacorus in native and introduced ranges support greater capacity of invasive populations to withstand sea level rise

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publicMar 2023View details →
dryad32/100

Data from: Maintenance of genetic diversity in an introduced island population of Guanacos after seven decades and two severe demographic bottlenecks: implications for camelid conservation

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publicApr 2014View details →
dryad32/100

Assessing the population genetic structure of introduced rainbow trout (Oncorhynchus mykiss) in the Lake Tahoe basin: A case for understanding hybridization potential during the reintroduction of the native Endangered Species Act listed Lahontan cutthroat trout (O. clarkii henshawi)

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publicApr 2022View details →
dryad32/100

Data from: Water availability as an agent of selection in introduced populations of Arabidopsis thaliana: impacts on flowering time evolution

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publicMar 2016View details →
dryad32/100

Data from: Population genetic structure and reproductive strategy of the introduced grass Centotheca lappacea in tropical land-use systems in Sumatra

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publicJan 2017View details →
dryad32/100

Data from: Genomics of invasion: diversity and selection in introduced populations of monkeyflowers (Mimulus guttatus)

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publicJul 2014View details →
dryad32/100

Data from: Linking genetic diversity and temporal fluctuations in population abundance of the introduced feral cat (Felis silvestris catus) on the Kerguelen Archipelago.

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publicSep 2011View details →
dryad32/100

Data from: Genetic variation and evolution of secondary compounds in native and introduced populations of the invasive plant Melaleuca quinquenervia

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publicNov 2011View details →
dryad32/100

Data from: Plant toxin levels in nectar vary spatially across native and introduced populations

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publicMar 2017View details →
dryad32/100

Data from: Genetic variation and clonal diversity in introduced populations of Mimulus guttatus assessed by genotyping at 62 single nucleotide polymorphism loci

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publicJan 2018View details →

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International Brain Laboratory public data

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OpenNeuro

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Last verified 2026-04-29Open record