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981 results for “Alienates”

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dryad32/100

Dataset for: Differential responses to fertilization and competition among invasive, non-invasive alien and native Bidens species

<p class="manuscript">Comparative studies of invasive, non-invasive alien, and native congenic plant species can identify plant traits that drive invasiveness. In particular, functional traits associated with rapid growth rate and high fecundity likely facilitate invasive success. As such traits often exhibit high phenotypic plasticity, characterizing plastic responses to anthropogenic environmental changes such as eutrophication and disturbance is important for predicting the invasive success of alien plant species in the future. Here, we compared trait expression and phenotypic plasticity at the species level among invasive, non-invasive alien, and native <i>Bidens</i> species. Plants were grown under nutrient addition and competition treatments, and their functional, morphological, and seed traits were examined. Invasive <i>B. frondosa</i> exhibited higher phenotypic plasticity in most measured traits than did the alien non-invasive <i>B. pilosa</i> or native <i>B. bipinnata</i>. However, differential plastic responses to environmental treatments rarely altered the rank of trait values among the three <i>Bidens</i> species, except for the number of inflorescences. The achene size of <i>B. frondosa</i> was larger, but its pappus length was shorter than that of <i>B. pilosa</i>. Two species demonstrated opposite plastic responses of pappus length to fertilization. These results suggest that the plasticity of functional traits does not significantly contribute to the invasive success of <i>B. frondosa</i>. The dispersal efficiency of <i>B. frondosa</i> is expected to be lower than that of <i>B. pilosa</i>, suggesting that long-distance dispersal is likely not a critical factor in determining invasive success.</p>

opencc-zeroNov 2021View details →
zenodo32/100

Supplementary material 1 from: Di Gristina E, Domina G, Barone G (2021) The alien vascular flora of Stromboli and Vulcano (Aeolian Islands, Italy). Italian Botanist 12: 63-75. https://doi.org/10.3897/italianbotanist.12.74033

Table with the species and subspecies of alien vascular plants present in the islands of Stromboli and Vulcano

opencc-zeroNov 2021View details →
zenodo32/100

Supplementary material 2 from: Muñoz-Mas R, Carrete M, Castro-Díez P, Delibes-Mateos M, Jaques JA, López-Darias M, Nogales M, Pino J, Traveset A, Turon X, Vilà M, García-Berthou E (2021) Management of invasive alien species in Spain: a bibliometric review. NeoBiota 70: 123-150. https://doi.org/10.3897/neobiota.70.68202

Table S1. Table of features, categories and definitions used to characterise the compiled literature

opencc-zeroDec 2021View details →
dryad32/100

Prioritizing terrestrial invasive alien plant species for management in urban ecosystems

<p>1. Invasive alien plant species (IAPs) in urban areas can have detrimental effects on biodiversity, ecosystem services and human well-being. Urban areas are complex social management mosaics with high land-use diversity, complex land tenure patterns, and many different stakeholder groups, some of which derive benefits from invading species. Urban conservation practitioners face complex decisions about which IAPs require management. Yet most IAPs prioritization frameworks have been designed for and implemented in natural or rural areas and are generally inadequate for guiding effective and sustainable interventions in urbanized areas.</p> <p>2. We modified an existing prioritization scheme to develop a framework for prioritizing terrestrial IAPs in urban areas which applies evidence-based (data-driven) and stakeholder-based (local knowledge) assessments to score and rank alien plant species in terms of their priority for management using an objective set of criteria.</p> <p>3. The framework consists of forty-six criteria, grouped into eight modules which assess invasion status, habitat requirements, biological characteristics, dispersal ability, distribution, impact (positive and negative), and potential for control for each alien plant species under consideration.</p> <p>4. We use the city of Toronto, Canada as a case study to test our framework – a list of 50 IAPs were effectively scored and ranked in order of high to low priority for control. Species with the highest <i>total prioritization scores</i> were <i>Vincetoxicum</i> <i>rossicum</i> (Dog Strangling Vine), <i>Convolvulus</i> <i>arvensis</i> (Field Bindweed) and <i>Taraxacum</i> <i>officinale</i> (Common Dandelion) (ranked 1, 2 and 3, respectively).</p> <p>5. Many of the identified high priority species align with the those previously flagged as of management concern by conservation practitioners, but also include those that are not actively managed due to their perceived lower ecological impacts. These species still require high resource investment for other objectives such as aesthetics. This highlights the complexity of alien plant species management in urban areas.</p> <p>6.<i> Synthesis and applications. </i>Prioritizing invasive alien plants for management in urban areas is particularly challenging due to often conflicting ecological, economic, and social objectives. We use available evidence and local stakeholder knowledge to develop an objective and systematic prioritization tool which can assist conservation practitioners in selecting priority species for management action in complex urban landscapes.</p>

opencc-zeroJan 2022View details →
dryad32/100

Data from: Herbivory may mediate the effects of nutrients on the dominance of alien plants

<p>1. Numerous studies have highlighted the role of nutrient availability and fluctuations therein for invasion success of alien plants. Others also highlighted the role of herbivores in invasion success. However, how herbivory and the level and fluctuations in nutrient availability interact in driving alien plant invasion into native communities remains largely unexplored.</p> <p>2. We grew eight invasive alien species as target species in pot-mesocosms with five different synthetic native communities in a three-factorial design with two levels of nutrient availability (low <i>vs</i> high), two levels of nutrient fluctuation (constant <i>vs</i> pulsed) and two levels of herbivory (with <i>vs</i> without).</p> <p>3. The relative biomass production of the alien target plants decreased in response to an increase in nutrient availability, and increased in response to the presence of herbivores. Furthermore, herbivory could interact with changes in nutrient availability and nutrient fluctuations to affect the dominance of the alien target species (a marginally significant interaction; 90% CIs: [0.005, 0.176]).</p> <p>4. Synthesis: Our multispecies experiment indicates that herbivory could mediate the interactive effect of nutrient enrichment and variability in nutrient supply on invasion of alien plants into native communities. Therefore, we recommend that studies testing the fluctuating resources hypothesis should also consider interactive effect of other trophic levels.</p>

opencc-zeroFeb 2022View details →
zenodo32/100

Alien species checklists - occurrence tables

<p>Tables representing species-regions occurrences based on alien species databases. The tables were modified from the original sources to standardise the for the workflow, and to incorporate the taxonomic harmosation.</p> <p>1- Final_checklist_amphibians - created based on the information available in &quot;Capinha, C. <em>et al.</em> Diversity, biogeography and the global flows of alien amphibians and reptiles. <em>Divers Distrib</em> <strong>23</strong>, 1313&ndash;1322 (2017).&quot;</p> <p>2- Final_checklist_ants - created based on the information available in &quot;Gu&eacute;nard, B., Weiser, M. D., G&oacute;mez, K., Narula, N. &amp; Economo, E. P. The Global Ant Biodiversity Informatics (GABI) database: synthesizing data on the geographic distribution of ant species (Hymenoptera: Formicidae). <em>Myrmecological News</em> <strong>24</strong>, 83&ndash;89 (2017).&quot;</p> <p>3- Final_checklist_birds - created based on the information available in &quot;Dyer, E. E., Redding, D. W. &amp; Blackburn, T. M. The global avian invasions atlas, a database of alien bird distributions worldwide. <em>Sci Data</em> <strong>4</strong>, 170041 (2017).&quot;</p> <p>4- Final_checklist_freshwaterfish - created based on the information available in &quot;Tedesco, P. A. <em>et al.</em> A global database on freshwater fish species occurrence in drainage basins. <em>Sci Data</em> <strong>4</strong>, 170141 (2017).&quot;</p> <p>5- Final_checklist_macrofungi - created based on the information available in &quot;Monteiro, M. <em>et al.</em> A database of the global distribution of alien macrofungi. <em>Biodiversity Data Journal </em><strong>8</strong>, e51459 (2020).&quot;</p> <p>6- Final_checklist_mammals- created based on the information available in &quot;Biancolini, D. <em>et al</em>. DAMA: the global Distribution of Alien Mammals database. <em>Ecology</em> <strong>102</strong>, (2021).&quot;</p> <p>7- Final_checklist_plants- created based on the information available in &quot;Kleunen, M. <em>et al.</em> The Global Naturalised Alien Flora (GloNAF) database. <em>Ecology</em> <strong>100</strong>, (2019).&quot;</p> <p>8- Final_checklist_reptiles- created based on the information available in &quot;Capinha, C. <em>et al.</em> Diversity, biogeography and the global flows of alien amphibians and reptiles. <em>Divers Distrib</em> <strong>23</strong>, 1313&ndash;1322 (2017).&quot;</p> <p>9- Final_checklist_spiders- created based on the information shared by co-author Wolfgang Nentwig.</p>

opencc-by-4.0Apr 2022View details →
zenodo32/100

Supplementary material 3 from: Anđelković AA, Lawson Handley L, Marchante E, Adriaens T, Brown PMJ, Tricarico E, Verbrugge LNH (2022) A review of volunteers' motivations to monitor and control invasive alien species. NeoBiota 73: 153-175. https://doi.org/10.3897/neobiota.73.79636

List of recommendations for designing projects to ensure maximum recruitment and volunteer retention extracted from the studies used in the analysis (for their full references, please see Suppl. material 1) and their link to our recommendations

opencc-zeroMay 2022View details →
zenodo32/100

Supplementary material 2 from: Cerri J, Lioy S, Porporato M, Bertolino S (2022) Combining surveys and on-line searching volumes to analyze public awareness about invasive alien species: a case study with the invasive Asian yellow-legged hornet (Vespa velutina) in Italy. NeoBiota 73: 177-192. https://doi.org/10.3897/neobiota.73.80359

Distribution of scores to the questions on the perceived impacts of V. velutina and its severity in relation to various threats for beekeeping

opencc-zeroMay 2022View details →
dryad32/100

The adaptive capacity of alien and endangered plants in China

<p>The datasets used in the article includes of "Endangered plants.csv" and "Alien plants.csv". The dataset of "Endangered plants" contains data from the list of the National Key Protected Wild Plants (the first and second batches) officially approved by the State Council, 1898 plants were recorded in the information system of the Chinese Rare and Endangered Plants. The dataset of "Alien plants" contains data from The Checklist of the Chinese Invasive Plants and 562 alien plants were recorded.</p> <p>Diaspore morphological traits were collected from database of the Flora of China (<a href="http://www.iplant.cn/foc/">http://www.iplant.cn/foc/</a>). Diaspore Information Database from Royal Botanic Gardens (<a href="http://data.kew.org/sid/">http://data.kew.org/sid/</a>), and the PLANTS Database of the United States (https://plants.usda.gov/java/).</p> <p>Each dataset includes 29 columns: ID, Species, Family, Dispersal strategy, The number of dispersal strategies of a plant, Reproductive mode, The number of reproductive modes of a plant, Life form, Habitat type, The number of habitats of a plant, Distribution scale, Score 1-16, Adaptive capacity to stressful environments, and Adaptive capacity to disturbed environments.</p> <p>Dispersal strategy includes: autochory (barochory, ballistic dispersal, and blastochory); anemochory (macrogeochory, meteor-anemochory, trichometeorochory, and pterometeorochory); hydrochory (bythisochory, zoohydrochory, and nautohydrochory); zoochory (endozoochory, epizoochory, frugivory, graminivory, granivory, and myrmecochory); and anthropochory (agochory, ethelochory, speirochory, and anthropochory). The number of dispersal strategies of a plant includes: one or two modes, three modes, four modes, and more than four modes. The reproductive mode includes: 1) spores or seeds; 2) ramets; 3) cutting, layering, or grafting; 4) rhizome; and 5) budding. The number of reproductive modes of a plant includes: one mode, two modes, three modes, and more than three modes. Life form includes:<span> </span>annual and biennial, perennial, vine, shrub, and arbor. Habitat type includes: 1) deserts or desert steppes; 2) steppes or dry hillsides; 3) waysides, near villages or wastelands; 4) farm lands; 5) meadow steppes or grasslands; 6) exposed rocks and crevices or tree tops; 7) forest edges, shrublands, or jungles; 8) rivers, lake banks, or benches; 9) marshes, wet meadows, or paddy fields and 10) in water. The number of plant habitats includes: one type, two types, three types, and more than three types. Distribution scale county scale (&lt; 5 × 10<sup>4</sup> km<sup>2</sup>), municipal scale (5–35 × 10<sup>4</sup> km<sup>2</sup>), provincial scale or autonomous regions (35–150 × 10<sup>4</sup> km<sup>2</sup>), and national scale (&gt;150 × 104 km<sup>2</sup>). Score 1-16 are scores of in corresponding indicator assessed in stressful and disturbed environment, respectively. Adaptive capacity to stressful and disturbed environments are total scores of plants assessed to stressful and disturbed environments.</p>

opencc-zeroMay 2022View details →
zenodo32/100

Disentangling the role of environmental filtering and biotic resistance on alien invasions in a reservoir area

<p>Data from: Disentangling the role of environmental filtering and biotic resistance on alien invasions in a reservoir area</p>

opencc-by-4.0May 2022View details →
zenodo32/100

Supplementary material 1 from: Demetriou J, Koutsoukos E, Davranoglou L, Roy HE, Spodek M, Martinou AF (2022) First records of the alien Eucalyptus psyllids Blastopsylla occidentalis (Hemiptera, Aphalaridae) from Cyprus and Platyobria biemani (Hemiptera, Aphalaridae) from Cyprus and continental Greece. Travaux du Muséum National d'Histoire Naturelle "Grigore Antipa" 65(1): 25-36. https://doi.org/10.3897/travaux.65.e82873

Supplementary material 1 from: Demetriou J, Koutsoukos E, Davranoglou L, Roy HE, Spodek M, Martinou AF (2022) First records of the alien Eucalyptus psyllids Blastopsylla occidentalis (Hemiptera, Aphalaridae) from Cyprus and Platyobria biemani (Hemiptera, Aphalaridae) from Cyprus and continental Greece. Travaux du Muséum National d'Histoire Naturelle "Grigore Antipa" 65(1): 25-36. https://doi.org/10.3897/travaux.65.e82873

opencc-by-4.0Jun 2022View details →
zenodo32/100

Subspecies and Distribution. P. v. vampyrus Linnaeus, 1758 — Java. P.v. edulis E. Geoffroy Saint-Hilaire, 1810 — Lesser Sunda Is (Timor). P. v. lanensis Mearns, 1905 — Philippines. P.v. natunae K. Andersen, 1908 — Borneo and Natuna Is. P. v. pluton Temminck, 1853 — W Lesser Sunda Is. P. v. sumatrensis Ludeking, 1862 — S mainland SE Asia and Malay Peninsula, Sumatra, Lingga Archipelago, Bangka, and S Mentawai Is (Sipora, North Pagai, and South Pagai). Chinese record from Shaanxi Province likely alien. in Pteropodidae

Subspecies and Distribution. P. v. vampyrus Linnaeus, 1758 — Java. P.v. edulis E. Geoffroy Saint-Hilaire, 1810 — Lesser Sunda Is (Timor). P. v. lanensis Mearns, 1905 — Philippines. P.v. natunae K. Andersen, 1908 — Borneo and Natuna Is. P. v. pluton Temminck, 1853 — W Lesser Sunda Is. P. v. sumatrensis Ludeking, 1862 — S mainland SE Asia and Malay Peninsula, Sumatra, Lingga Archipelago, Bangka, and S Mentawai Is (Sipora, North Pagai, and South Pagai). Chinese record from Shaanxi Province likely alien.

opennotspecifiedOct 2019View details →
zenodo32/100

FIGURE 4 in Morphological diversification of alien and native aquatic snails of the genus Physa and Aplexa (Gastropoda: Physidae) of Western and Central European range

FIGURE 4. Ranges of occurrence of species of the family Physidae. 1—P. acuta, 2—A. hypnorum, 3—P. gyrina, 4—P. fontinalis (Feliksiak 1939; Adam 1960; Backhuys 1975, Vidal Abarca &amp; Suarez 1986; Lisický 1991; Anderson 1996, 1997;Turner et al. 1998; Cossignani &amp; Cossignani 1995; Kerney 1999; Anderson 2003; Beran 2004; Bank 2006; Yildirim et al. 2006; Son 2007; Horsȃk et al. 2010; Glöer &amp; Diercking 2010; CABI Data Mining 2011; Bódis et al. 2012; Laenko 2012; Van Damme et al. 2012; Welter-Schultes 2012; Glöer 2015; Vinarski et al. 2015; Raković et al. 2016; Piechocki &amp; Wawrzyniak-Wydrowska 2016; Moroz et al. 2017; Cieplok &amp; Spyra 2020; www.faunaeuropea.org; http://www.animalbase.uni-goettingen.de).

opennotspecifiedJul 2022View details →
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FIGURE 7 in Morphological diversification of alien and native aquatic snails of the genus Physa and Aplexa (Gastropoda: Physidae) of Western and Central European range

FIGURE 7. Characteristic features of P. gyrina with special emphasis on the white lip (10.18150/WOIHYB) (Phot. M. Gawlak).

opennotspecifiedJul 2022View details →
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FIGURE 3 in Morphological diversification of alien and native aquatic snails of the genus Physa and Aplexa (Gastropoda: Physidae) of Western and Central European range

FIGURE 3. Scanning electron microscopy image of A. hypnorum shell (10.18150/UFOMHM) A, B—front (with visible lip) and back side of the shell, C—projecting lamellar crystals on the lip (Phot. A—C M. Gawlak).

opennotspecifiedJul 2022View details →
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FIGURE 2 in Morphological diversification of alien and native aquatic snails of the genus Physa and Aplexa (Gastropoda: Physidae) of Western and Central European range

FIGURE 2. Scanning electron micrographs of the shell apex of Physidae (10.18150/FIZSWX) Horizontally: A—P. acuta (subsidence ponds); B—A. hypnorum (anthropogenic ponds, Poland); C—P. fontinalis (Nida River, Poland); D—P. gyrina (Ireland, The Argory- ditch and Sandy Bay L Neagh; Wales, Gwent Levels in pond in flood plain (l. Killen); E- Apex of the small (young) specimens—1—P. acuta, 2—A. hyponorum, 3—P. fontinalis, 4—P. gyrina (Phot. A–E M. Gawlak).

opennotspecifiedJul 2022View details →
zenodo32/100

FIGURE 1 in Morphological diversification of alien and native aquatic snails of the genus Physa and Aplexa (Gastropoda: Physidae) of Western and Central European range

FIGURE 1. Physidae of Western and Central Europe (10.18150/YPDFJU)—general shell morphology A—Physa acuta (Phot. M. Kanturski), B—Aplexa hypnorum, C—Physa fontinalis, D—Physa gyrina; 1—front side of the shell, 2—shell from the side view, 3—back side of the shell (Phot. B–D A. Cieplok, A. Spyra).

opennotspecifiedJul 2022View details →
zenodo32/100

FIGURE 6. P in Morphological diversification of alien and native aquatic snails of the genus Physa and Aplexa (Gastropoda: Physidae) of Western and Central European range

FIGURE 6. P. acuta shell features (SEM) (10.18150/G6UWMN); in which the sutural belts are visible (A), the structure of a white lip (B) with characteristic projecting lamellar crystals (C) is indicated by an arrow (Phot. A–C M. Gawlak), (D) a view of the lip visible under the stereoscopic microscope (Phot. M. Kanturski).

opennotspecifiedJul 2022View details →
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FIGURE 8 in Morphological diversification of alien and native aquatic snails of the genus Physa and Aplexa (Gastropoda: Physidae) of Western and Central European range

FIGURE 8. Correspondence Analysis (CA) diagram for the Physidae species; 1—Whorl convexity, 2—Spire, 3—Shell thickness, 4—Thickened appendages, 5—Shell shine, 6—Shell width and height ratio, 7—Aperture height, 8—Shell height, 9—Lip, 10—Apex, 11—Shell width, 12—Aperture width, 13—Spire height.

opennotspecifiedJul 2022View details →
zenodo32/100

Supplementary material 2 from: Sirbu C, Miu IV, Gavrilidis AA, Gradinaru SR, Niculae IM, Preda C, Oprea A, Urziceanu M, Camen-Comanescu P, Nagoda E, Sirbu IM, Memedemin D, Anastasiu P (2022) Distribution and pathways of introduction of invasive alien plant species in Romania. NeoBiota 75: 1-21. https://doi.org/10.3897/neobiota.75.84684

Appendix S2. Altitudinal range of invasive and potentially invasive alien plant species recorded in Romania

opencc-zeroAug 2022View details →

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