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The cladoceran Daphnia lumholtzi is a subtropical and tropical zooplankter, and an invasive species in North America. Thus far, D. lumholtzi has not been detected in Europe. Here we investigated whether a hypothetical introduction to Europe could result in a successful invasion, either now or in the near future when facilitated by climate change. In laboratory experiments, we tested whether different clones of D. lumholtzi can invade a resident community consisting of native Daphnia from lake Klostersee, Germany, and how invasion success depends on temperature and the presence or absence of planktivorous fish. In some treatments, invasion success was consistently high, and D. lumholtzi reached densities similar to the native competitors by the end of the experiment. The presence of a planktivorous fish reduced the invasion success of D. lumholtzi, and a clone with an inducible defense against fish predation was a more successful invader than a permanently defended clone. Of the three temperatures tested in this study (15, 20, and 24 °C), invasion success was highest at 20 °C. To understand the competitive interaction between native and introduced Daphnia, we fit a Lotka-Volterra-type competition model to the population dynamics. Our experimental and modeling results suggest that D. lumholtzi can invade European lakes and can cause substantial declines in the population size of native Daphnia, with potential consequences for higher trophic levels.
Hemidactylus frenatus is an Asian gecko species that has invaded many tropical regions to become one of the most widespread lizards worldwide. This species has dispersed across the Pacific Ocean to reach Hawaii and subsequently Mexico and other Central American countries. More recently, it has been reported from northwestern South America. Using 12S and cytb mitochondrial DNA sequences I found that South American and Galápagos haplotypes are identical to those from Hawaii and Papua New Guinea, suggesting a common Melanesian origin for both Hawaii and South America. Literature records suggest that H. frenatus arrived in Colombia around the mid-‘90s, dispersed south into Ecuador in less than five years, and arrived in the Galápagos about one decade later.
The recruitment processes and resulting distribution pattern of bird-dispersed Canary Island Date Palm, Phoenix canariensis (family Arecaceae) in a riverine forest setting are described. All palms on a near-urban peninsula of the Murrumbidgee River near Hay, New South Wales were GPS mapped and classified into height-dependent age categories. The distribution of the plants was examined spatially in relation to possible source palms and in relation to elevation with regard to flooding levels. Successful recruitment is subject to a range of environmental parameters, primarily palatability to vectors and seedling mortality due to lack of moisture, frost or grazing by herbivores. If a seedling survives that critical period of the first 18 months, long-term success is (almost) guaranteed, unless catastrophic events (bushfires, prolonged flooding) intervene. Based on the findings, a conceptual model for the recruitment of Phoenix canariensis palms is provided. Even though the palms produce fruit for much of the year (March–December), the time window for successful recruitment is restricted to a period from August to mid-September with short shoulder periods on either side.
Dog-strangling vine (Vincetoxicum rossicum) is an exotic plant originating from Central and Eastern Europe that is becoming increasingly invasive in southern Ontario, Canada. Once established, it successfully displaces local native plant species but mechanisms behind this plant’s high competitive ability are not fully understood. It is unknown whether cooler temperatures will limit the range expansion of V. rossicum, which has demonstrated high tolerance for other environmental variables such as light and soil moisture. Furthermore, if V. rossicum can establish outside its current climatic limit it is unknown whether competition with native species can significantly contribute to reduce fitness and slow down invasion. We conducted an experiment to test the potential of V. rossicum to spread into northern areas of Ontario using a set of growth chambers to simulate southern and northern Ontario climatic temperature regimes. We also tested plant-plant competition by growing V. rossicum in pots with a highly abundant native species, Solidago canadensis, and comparing growth responses to plants grown alone. We found that the fitness of V. rossicum was not affected by the cooler climate despite a delay in reproductive phenology. Growing V. rossicum with S. canadensis caused a significant reduction in seedpod biomass of V. rossicum. However, we did not detect a temperature x competition interaction in spite of evidence for adaptation of S. canadensis to cooler temperature conditions. We conclude that the spread of V. rossicum north within the tested range is unlikely to be limited by climatic temperature but competition with an abundant native species may contribute to slow it down.
Biosecurity measures are commonly used to prevent the introduction of non-native species to natural environments globally, yet the efficacy of practices is rarely tested under operational conditions. A voluntary biosecurity measure was trialled in the Norwegian high Arctic following concern that non-native species might be transferred to the region on the footwear of travellers. Passengers aboard an expedition cruise ship disinfected their footwear with the broad spectrum disinfectant Virkon S prior to and in-between landing at sites around the remote Svalbard archipelago. The authors evaluated the efficacy of simply stepping through a disinfectant foot bath, which is the most common practice of footwear disinfection aboard expedition cruise ships in the Arctic. This was compared to a more time consuming and little-used method involving drying disinfected footwear, as proposed by other studies. The two practices were evaluated by measuring microbial growth on paired footwear samples before and after disinfection under both conditions. Step-through disinfection did not substantially reduce microbial growth on the footwear. Allowing disinfected footwear to dry, however, reduced the microbial burden significantly to lower levels. Thus, the currently adopted procedures used aboard ships are ineffective at removing microbial burden and are only effective when footwear is given more time to dry than currently granted under operational conditions. These findings underscore results from empirical research performed elsewhere and suggest the need to better relay this information to practitioners. It is suggested that footwear should minimally be wiped dry after step-through disinfection as a reasonable compromise between biosecurity and practicability.
The impacts of invasive alien species are greatest when they become dominant members of a community, introduce novel traits, and displace native species. Invasions by alien mollusks represent a novel context by which to compare trait differences between generalist native and introduced herbivores in terrestrial ecosystems. Here, we determined the abundance, habitat, feeding preferences, as well as the metabolic rate of the native Pacific banana slug (Ariolimax columbianus) and the alien black slug (Arion rufus) in the coastal forests of British Columbia, Canada. Through a series of observational and experimental studies, we found that alien slugs are more abundant, differ in their habitat preferences, and consumed more fungi (mushrooms) than native banana slugs. Conversely, in an enclosures experiment we found that herbivory damage by native slugs was higher compared to enclosures with alien only and control enclosures. Finally, metabolic rates were similar for both slug species. These results suggest that alien black slugs possess a suite of traits that make them functionally different from native banana slugs.
Seit 1890 wird die aus dem westlichen Nordamerika stammende Fabacee Lupinus polyphyllus Lindl. (Stauden-Lupine) in Deutschland beobachtet. Ihre großflächigsten Vorkommen in Deutschland finden sich derzeit in der Hohen Rhön im Gebiet Leitgraben/Elsgellen (407 ha: 1998 10,6 % Lupinus-Bedeckung). Dort werden fast alle Wiesen mit Auflagen des Bayerischen Vertragsnaturschutzprogramms bewirtschaftet. Dies bedeutet, zeitlich gestaffelte Pflegetermine zwischen 10. Juli und 31. Oktober (Abschluss der Pflegearbeiten), die den Zeitraum der Samenbildung von Lupinus vollständig erschließen. Nachweisbar ist, dass dort, wo innerhalb der Vertragsnaturschutzflächen Heugewinnung die primäre Motivation für die Nutzung ist - dies bedeutet Nutzung zum frühest möglichen Zeitpunkt - keine Lupinus-Etablierung nachweisbar ist! Neben rechtzeitiger Mahd ist Beweidung mit (Rhön-)Schafen geeignet, die Ver- und Ausbreitung von Lupinus einzudämmen. Auch dafür gilt, dass sie vor der Samenreife (ab Anfang Juli) von Lupinus durchzuführen ist, da reife Lupinus-Samen durch Schafe endozooisch ausgebreitet werden. Vegetationsaufnahmen von Kleinseggenrieden (Caricetum fuscae), Borstgrasrasen (Polygalu-Nardetum) und Goldhaferwiesen (Geranio-Trisetetum), in denen Lupinus polyphyllus mit höheren Deckungsgraden (> 25 %) vorkommt, belegen, dass die niedrigwüchsigen Arten der Krautschicht zurückgedrängt werden. Parallel dazu nehmen die kräftige Horste ausbildenden Gräser Poa chaixii und Deschampsia cespitosa zu. Eine Trennartengruppe mit den Ruderalarten Cerastium glomeratum, Galium aparine agg., Galeopsis tetrahit, Cirsium arvense und Urtica dioica charakterisiert die Lupinus-Fazies. Die Konkurrenzkraft der Dominanzbestände mit Lupinus erklärt sich über die Biomasseverteilung in Form einer umgekehrten Pyramide, die über Bestandeshöhe (zwischen 70 und 110 cm) und dichte Belaubung stark beschattend auf tiefere Vegetationsschichten (< 30 cm) wirkt, so dass deren Arten ausdünnen, wenn sie nicht die ausreichende Plastizität im Höhenwachstum besitzen, um mit Lupinus mitzuhalten. Auch andere Dominanzbestände-aufbauende Arten wie Impatiens glandulifera, Heracleum mantegazzianum und Reynoutria ssp. besitzen diese Eigenschaft und können aufgrund ihrer Wuchshöhe sogar die Funktion einer fehlenden Strauchschicht übernehmen.
In the summers of 2006 and 2007 presumed bites of Cheiracanthium spiders triggered mass hysteria in Austria and some regions of Germany, including northern Saxonia. Here we report the first records of Cheiracanthium mildei L. Koch, 1864 from Saxony and new records of C. punctorium (Villers, 1789) from Saxony and Brandenburg. C. punctorium is probably a native species in southern Germany. It shows a moderate area expansion that could be driven by global warming. Further records in north-western Saxony are to be expected. By contrast, C. mildei has to be regarded an invasive alien species that has rapidly spread into Central Europe from the Mediterranean. Leipzig is the north-easternmost locality in Europe reached so far, a further 230 km away from Nuremberg, the leading edge in 2006. A number of records in different districts of Leipzig suggest that the species is already established in the town. We also report verified bites of both species. The mild to moderate symptoms are in accordance with recent literature reviews.
Current globalization and technological progress has facilitated and increased the international trade of plant products worldwide and has promoted the long-distance movement of immobile sucking pests such as whiteflies attached on plants. Therefore, being able to compile and update information on intercepted insect pests will help to improve the inspection procedures, to detect, identify and mitigate the damage caused by exotic invasive pests. Records of whiteflies (Hemiptera: Aleyrodidae) intercepted on import plants from 2013 to 2021 in the Pest Information System (PIS) database of South Korea were analyzed. A total of 32 species belonging to 19 genera were intercepted on plants imported into South Korea from 20 countries, mostly located in the Oriental region including China. Brief diagnoses, an identification key and photographs of the 32 species intercepted on agricultural commodities and the countries from which they were detected on plants are given to assist in their identification. In addition, this information provides background data and scientific rationale for decisions regarding the management of whiteflies intercepted at the South Korean ports on imported plant products to prevent the introduction and establishment of exotic whiteflies into South Korea.
ZooBank registration. urn:lsid:zoobank.org:pub:D0889D43-F905-4CCD-A6A2-D4E376E5FC79
Duchesnea indica, die Indische Scheinerdbeere, stammt aus mild-humiden Bergregionen Asiens und wird in Mitteleuropa seit Beginn des 19. Jahrhunderts als Zierpflanze kultiviert. In den letzten Jahrzehnten breitet sich die Art in Deutschland insbesondere in milden Regionen zunehmend spontan aus. Im stärker kontinental getönten Klima Nordostbayerns ist Duchesnea bislang noch nicht außerhalb gärtnerischer Anpflanzungen anzutreffen, wenngleich sie sich beispielsweise auf dem Areal des Ökologisch-Botanischen Gartens der Universität Bayreuth seit vielen Jahren stark vegetativ ausbreitet. In der vorliegenden Studie wurde daher das Potenzial der generativen Ausbreitung von Duchesnea indica im Vergleich zur morphologisch ähnlichen einheimischen Fragaria vesca untersucht und die Hypothese zugrunde gelegt, dass die Produktion keimfähiger Samen und/oder deren Ausbreitung limitierend für die Etablierung von Duchesnea indica an neuen Standorten ist. Duchesnea produziert in einer Vegetationsperiode mehr Samen (einsamige Nussfrüchte) als die heimische Fragaria. Sie hat zudem eine deutlich längere Phase der Fruktifikation, die vom Frühsommer bis zum ersten Frost im Herbst reicht. Die Samen von Duchesnea sind zu über 90% keimfähig, selbst wenn sie zwei Wochen vor der Keimung bei -18°C gelagert wurden. Ihre Früchte werden in gleichem Maße wie diejenigen der Walderdbeere sowohl von Vögeln wie auch von Kleinsäugern verschleppt. Limitierend für die Besiedlung neuer Standorte über Samen könnte das Keimverhalten von Duchesnea sein. Die Samenkeimung beginnt erst 21 Tage nach der Aussaat (bei Fragaria nach 8 Tagen) und endet nach bis zu 56 Tagen (bei Fragaria nach 13 Tagen). In weiteren Unteruchungen ist zu klären, ob die Bedingungen der Keimlingsetablierung begrenzend für die weitere Ausbreitung von Duchesnea indica wirken.