scholarly journals Fatal attraction: sexually cannibalistic invaders attract naive native mantids

2013 ◽  
Vol 9 (6) ◽  
pp. 20130746 ◽  
Author(s):  
Murray P. Fea ◽  
Margaret C. Stanley ◽  
Gregory I. Holwell

Overlap in the form of sexual signals such as pheromones raises the possibility of reproductive interference by invasive species on similar, yet naive native species. Here, we test the potential for reproductive interference through heterospecific mate attraction and subsequent predation of males by females of a sexually cannibalistic invasive praying mantis. Miomantis caffra is invasive in New Zealand, where it is widely considered to be displacing the only native mantis species, Orthodera novaezealandiae , and yet mechanisms behind this displacement are unknown. We demonstrate that native males are more attracted to the chemical cues of introduced females than those of conspecific females. Heterospecific pairings also resulted in a high degree of mortality for native males. This provides evidence for a mechanism behind displacement that has until now been undetected and highlights the potential for reproductive interference to greatly influence the impact of an invasive species.

Author(s):  
Amy Krist ◽  
Mark Dybdahl

Invasive species are one of the greatest threats to global biodiversity. Hence, understanding the role of invasive species is of grave importance to managing and minimizing the impact of biological invasions. To date, the ecological impacts of biological invasions have received significant attention, but little effort has been made to address the evolutionary impact (Sakai et al. 2001, Cox 2004). This is despite the fact that evolutionary impacts are likely to be widespread; invasive species have been shown to alter patterns of natural selection or gene flow within native populations (Parker et al. 1999), and many of the best examples of rapid evolution involve invasive species interacting with native species (Reznick and Ghalambor 2001, Strauss et al. 2006). We have begun to address some of the evolutionary consequences of the invasion of the New Zealand mud snail, (Potamopyrgus antipodarum) on a species of native snail in the Greater Yellowstone Area (GYA).


2010 ◽  
Vol 26 (3) ◽  
pp. 347-350 ◽  
Author(s):  
Jannie Fries Linnebjerg ◽  
Dennis M. Hansen ◽  
Nancy Bunbury ◽  
Jens M. Olesen

Disruption of ecosystems is one of the biggest threats posed by invasive species (Mack et al. 2000). Thus, one of the most important challenges is to understand the impact of exotic species on native species and habitats (e.g. Jones 2008). The probability that entire ‘invasive communities’ will develop increases as more species establish in new areas (Bourgeois et al. 2005). For example, introduced species may act in concert, facilitating one another's invasion, and increasing the likelihood of successful establishment, spread and impact. Simberloff & Von Holle (1999) introduced the term ‘invasional meltdown’ for this process, which has received widespread attention since (e.g. O'Dowd 2003, Richardson et al. 2000, Simberloff 2006). Positive interactions among introduced species are relatively common, but few have been studied in detail (Traveset & Richardson 2006). Examples include introduced insects and birds that pollinate and disperse exotic plants, thereby facilitating the spread of these species into non-invaded habitats (Goulson 2003, Mandon-Dalger et al. 2004, Simberloff & Von Holle 1999). From a more general ecological perspective, the study of interactions involving introduced and invasive species can contribute to our knowledge of ecological processes – for example, community assembly and indirect interactions.


Author(s):  
Heather Thon ◽  
Amy Krist

Understanding invasive species impacts is critical to determining how an ecosystem may function after an introduction. Invasive species can alter the structure and function of ecosystems, reduce biological diversity, and alter communities through predation, facilitation and competition. In the past 30 years, the invasive New Zealand mud snail (Potamopyrgus antipodarum) has established in areas of conservation concern in the American West including Yellowstone National Park. To develop a greater understanding of the impact of P. antipodarum on the native co-occurring snail, Fossaria (Bakerilymnaea) bulimoides group, we conducted two experiments to assess the interactions occurring between these snails. We found that F. bulimoides growth was reduced by all interactors, but especially by P. antipodarum. In addition, growth of F. bulimoides was much more affected by high biomass of snails than P. antipodarum. P. antipodarum grew more in the presence of interactors and their growth was facilitated by the presence of the native snail F. bulimoides.


2021 ◽  
Author(s):  
◽  
Evan Brenton-Rule

<p>Biological invasions are one of the major causes of biodiversity decline on the planet. The key driver of the global movement of invasive species is international trade. As a response to trade driven invasive species risk, international and domestic regulations have been promulgated with the goal of managing the spread and impact of non-native species. My aims in this thesis were twofold. First, my goal was to review a subset of international and domestic regulations with a view to commenting on their fitness for purpose and suggesting potential improvements. Second, I used the example of non-native and invasive Hymenoptera, as well as their pathogens, to illustrate the risks posed by invasive species and gaps in their management.   In order to assess international and domestic regulations, I reviewed the World Trade Organization’s (WTO) Agreement on Sanitary and Phytosanitary Measures, as well as associated disputes. I argue that the WTO’s regulatory system does, for the most part, allow domestic regulators to manage invasive species risk as they see fit. Subsequently, the focus of the thesis narrows to investigate New Zealand’s pre- and post-border regime managing invasive species. I argue that New Zealand’s pre-border approach represents international best practice, but the post-border management of species is fragmented. The power to manage invasive species has been delegated to sub-national and regional bodies, which typically approach invasive species management in different ways. This variation has led to regulatory inconsistencies in pests managed and funding allocated. There appears to be a substantial lack of planning in some spaces, such as the risk of aquatic invasions. I make recommendations to ameliorate these inconsistencies.   My second aim involved the study of non-native and invasive Hymenoptera in New Zealand, as well as the pathogens they carry, in order to illustrate the risks posed by invasive species and gaps in their management. I show that the globally widespread invasive Argentine ant (Linepithema humile) may play a role in the pathogen dynamics and mortality of honey bee hives where the species occur sympatrically. Hives in the presence of Argentine ants suffered significantly higher mortality rates relative to hives without ants and always had higher levels of a honey bee pathogen Deformed wing virus. I demonstrate that honey bee pathogens are found in a range of invasive Hymenoptera in New Zealand. I amplify entire genomes of the honey bee virus Kashmir bee virus (KBV) from three species of non-native or invasive Hymenoptera (Argentine ants, common wasps and honey bees). I show that there is KBV strain variability within and between regions, but more between regions. Further, I demonstrate the result that as sampled KBV sequence length increases, so too does sampled diversity. These results highlight how ‘an’ invasive species is typically not alone: they carry a range of diseases that are almost always not considered in international and regional management plans.   Patterns of non-native Hymenoptera carrying honey bee diseases were not restricted to New Zealand. I used mitochondrial DNA to find the likely origin of invasive populations of the globally distributed invasive German wasp. I demonstrate that German wasps show reduced genetic diversity in the invaded range compared to the native range. Populations in the introduced range are likely to have arrived from different source populations. In some regions there were likely multiple introductions. Other regions are genetically homogenous and represent potential areas for use of gene drive technologies. All four different honey bee pathogens assayed for were found in German wasp populations worldwide. These results highlight how the introduction of one exotic species likely brings a range of pathogens. This example of pathogens in Hymenoptera is likely to be true for nearly all non-native introductions.  Many of the impacts of biological invasions, such as predation and competition, are relatively obvious and are frequently studied. However some, such as the impact of pathogens, are unseen and poorly understood. Legal regulation is often a post-hoc response implemented once a problem has already arisen. At a global level regulatory regimes operate relatively effectively. As the focus becomes more granular, such as the case of pathogens of Hymenoptera, fewer controls exists. This thesis helps to reduce uncertainty in this area as well as makes recommendations as to how these risks may be managed.</p>


2012 ◽  
Vol 18 (2) ◽  
pp. 77 ◽  
Author(s):  
Heather Parks ◽  
Kyle Clifton ◽  
Lauren Best ◽  
Bridget Johnson

PEST-PROOF (exclusion) fences are designed to prevent non-native, predatory and pest species from repopulating an area set aside to protect vulnerable native plant and animal species. Pest-proof fencing provides security from invasive species, but can isolate the native species enclosed within. On one hand, some rare native species exist on the mainland due to the pest-free status achieved through the use of exclusion fences. On the other hand, these reintroduced populations are now isolated a situation where they would not be found naturally (Jamieson et al. 2006). Exclusion fences must be constantly maintained or the sanctuary risks reinvasion. An important question for conservation biologists and managers to answer is therefore — when is exclusion fencing the best option for protecting native species from introduced pests? We have drawn our examples from New Zealand and Australia where progress has been made with regard to the design and utilization of exclusion fences.


Author(s):  
Maria Balazova ◽  
Dana Blahutova ◽  
Terezia Valaskova

Biological invasions are recognised as a potentially major threat to biodiversity and may have considerable economic and social effects. Public, including pupils, attitudes may have large implications for invasive species management in terms of prevention, early warning and eradication success, but significant is the relations between the lay public’s visions of nature, their knowledge about non-native species and their perceptions of invasive species management. The more direct experience people have with the impact of invasive species, the more likely they will be able to understand the potential benefits of management programmes. The aim of our work was to prepare educational materials about invasive organisms for elementary schools. Some of them were subsequently applied directly in practice as part of an excursion in a schoolyard in west Slovakia, where up to six species of invasive plants were identified in the close proximity to the school. Keywords: Biological invasions, prevention, education, excursion.


2006 ◽  
Vol 11 (4) ◽  
pp. 429-452 ◽  
Author(s):  
HEIDI J. ALBERS ◽  
MICHAEL J. GOLDBACH ◽  
DANIEL T. KAFFINE

Policies to influence land use decisions in agriculture or grazing can increase the ability of invasive species to out-compete native species and thereby disrupt seemingly stable ecological-economic systems. Building off of models of interdependent resources, invasive species and soil fertility, this paper develops a model of shifting cultivation decisions for two types of farmers, one who sees the threat of invasive grasses and one who does not. The paper uses numerical solutions to this dynamic decision problem to examine the impact of various policies on farmer welfare and on the stability of the economic-ecological system. Some policies undermine the resilience of the system, while other policies augment the system's ability to withstand species invasions.


Author(s):  
Taylor Alexander Hughson

AbstractThis article seeks to explain how Aotearoa New Zealand moved from a consensus that the New Zealand Curriculum (NZC) should grant a high degree of autonomy to teachers, to an emerging view that it ought to be more prescriptive about content. To do this, it takes an assemblage approach to policy analysis, understanding policies as constantly evolving ‘bundles’ of divergent components temporarily woven together. The article first explores the complex intermingling of Third Way priorities, knowledge economy discourses, educational progressivism and narratives of ‘harmonious’ biculturalism which constitute the 2007 NZC. It then explores the sustained critique of the NZC from the 2015 parliamentary petition calling for compulsory teaching of the New Zealand Wars, up to the government’s 2021 ‘curriculum refresh’ announcement. It is argued that this ‘refresh’ moves to reassemble the NZC so that it accommodates a series of demands made of it in recent years, including demands the curriculum take a more active role in redressing the impact of colonisation, and demands from both business-aligned groups and academics that the curriculum become more ‘knowledge-led’.


2021 ◽  
Author(s):  
◽  
Kerri Lukis

<p>Karori Sanctuary (252 ha) is a fenced restoration site in Wellington, New Zealand from which all species of introduced mammals have been eradicated except house mice (Mus musculus). In 2006, the endemic New Zealand frog Leiopelma pakeka was transferred to Karori Sanctuary as part of a long term plan to restore the site's original biota. This was a significant event in that it was the first re-introduction of a New Zealand frog to a mainland site, the first New Zealand amphibian translocation for the purpose of restoration and the first time L. pakeka were released into habitat also occupied by an introduced mammal. An adaptive management regime facilitated research within the constraints of a community restoration project for which only a small population (n=60) was made available for release. Two groups (n = 30) were released into mouse-proof enclosures in February and October, 2006. Survival was high (97%) and frogs maintained a healthy body condition. Breeding was not detected during the first year and this was attributed to an inappropriate sex ratios that were restructured in April 2007 when half of the frogs (n= 29) were removed from the enclosures and released into forest habitat. The survival, condition and recruitment of frogs living inside and outside of the mouse-proof enclosures were compared. Both groups initially had a similar recapture rate, but after one year, just one frog (3%) was recaptured outside the enclosure compared with 27 adults (93%) and fourteen juveniles captured within the enclosure. In March 2009, 26 of the 29 individuals originally released into the enclosure were recaptured and a further ten juveniles were captured for the first time. No individuals have been sighted outside the enclosure since March 2008. Post-release movements did not explain the apparent decline of the population living outside of the enclosure. The mean distance dispersed during the first month after release (3.4 +/- 0.05 m) did not significantly increase after eight months (4.2 +/- 0.05 m) and the maximum-recorded dispersal distance was 7.0 m. The centre of activity of the nine frogs captured > 5 occasions were all within 3 m of the release site and kernel estimates of high habitat usage clustered around artificially constructed rock piles. Predation by house mice and/or native species such as little spotted kiwi (Apteryx owenii) were considered the most likely explanation for the failure to recapture frogs outside of the enclosure, especially those frogs that appeared to have settled at the release site. The extremely low number of individuals released outside of the enclosure exacerbated the impact of processes acting on the founding population. Recommendations are provided for the next adaptive management stage and include transferring an additional 100 frogs from Maud Island for release into forest habitat outside of the mouse-proof enclosure. Post-release movements should be restricted and all potential predators except house mice excluded. The population within the enclosures should be retained as is. Finally, the viability including L. pakeka in attempts to reconstruct mainland communities is examined.</p>


2021 ◽  
Author(s):  
◽  
Kerri Lukis

<p>Karori Sanctuary (252 ha) is a fenced restoration site in Wellington, New Zealand from which all species of introduced mammals have been eradicated except house mice (Mus musculus). In 2006, the endemic New Zealand frog Leiopelma pakeka was transferred to Karori Sanctuary as part of a long term plan to restore the site's original biota. This was a significant event in that it was the first re-introduction of a New Zealand frog to a mainland site, the first New Zealand amphibian translocation for the purpose of restoration and the first time L. pakeka were released into habitat also occupied by an introduced mammal. An adaptive management regime facilitated research within the constraints of a community restoration project for which only a small population (n=60) was made available for release. Two groups (n = 30) were released into mouse-proof enclosures in February and October, 2006. Survival was high (97%) and frogs maintained a healthy body condition. Breeding was not detected during the first year and this was attributed to an inappropriate sex ratios that were restructured in April 2007 when half of the frogs (n= 29) were removed from the enclosures and released into forest habitat. The survival, condition and recruitment of frogs living inside and outside of the mouse-proof enclosures were compared. Both groups initially had a similar recapture rate, but after one year, just one frog (3%) was recaptured outside the enclosure compared with 27 adults (93%) and fourteen juveniles captured within the enclosure. In March 2009, 26 of the 29 individuals originally released into the enclosure were recaptured and a further ten juveniles were captured for the first time. No individuals have been sighted outside the enclosure since March 2008. Post-release movements did not explain the apparent decline of the population living outside of the enclosure. The mean distance dispersed during the first month after release (3.4 +/- 0.05 m) did not significantly increase after eight months (4.2 +/- 0.05 m) and the maximum-recorded dispersal distance was 7.0 m. The centre of activity of the nine frogs captured > 5 occasions were all within 3 m of the release site and kernel estimates of high habitat usage clustered around artificially constructed rock piles. Predation by house mice and/or native species such as little spotted kiwi (Apteryx owenii) were considered the most likely explanation for the failure to recapture frogs outside of the enclosure, especially those frogs that appeared to have settled at the release site. The extremely low number of individuals released outside of the enclosure exacerbated the impact of processes acting on the founding population. Recommendations are provided for the next adaptive management stage and include transferring an additional 100 frogs from Maud Island for release into forest habitat outside of the mouse-proof enclosure. Post-release movements should be restricted and all potential predators except house mice excluded. The population within the enclosures should be retained as is. Finally, the viability including L. pakeka in attempts to reconstruct mainland communities is examined.</p>


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