scholarly journals Ulva,UmbraulvaandGemina: genetic survey of New Zealand taxa reveals diversity and introduced species

2009 ◽  
Vol 44 (2) ◽  
pp. 143-154 ◽  
Author(s):  
Svenja Heesch ◽  
Judy E.S. Broom ◽  
Kate F. Neill ◽  
Tracy J. Farr ◽  
Jennifer L. Dalen ◽  
...  
2010 ◽  
Vol 14 ◽  
pp. 5-11
Author(s):  
W.M. Williams

The New Zealand flora is a mixture of indigenous and introduced species. The indigenous species have a high intrinsic value while the introduced species include all of the crop and pasture plants upon which the export-led economy depends. New Zealand must maintain both of these important sources of biodiversity in balance. Seed banks are useful tools for biodiversity management. In New Zealand, a seed bank for indigenous species has been a very recent initiative. By contrast, seed banks for introduced species have been established for over 70 years. The reasons for this discrepancy are discussed. For the economic species, conserved genetic diversity is used to enhance productivity and the environment. Large advances can be gained from species that are not used as economic plants. The gene-pool of white clover has been expanded by the use of minor species conserved as seeds in the Margot Forde Germplasm Centre. Keywords: Seed banks, biodiversity conservation, New Zealand flora


2010 ◽  
Vol 16 (4) ◽  
pp. 230 ◽  
Author(s):  
Mark N. H. Seabrook-Davision ◽  
Dianne H. Brunton

The issue of naturalization of introduced species to New Zealand was raised in an article in Nature (Ritchie 1922a Thompson 1922) 88 years ago. Here, we take the opportunity to assess the impacts of introduced species to the islands of New Zealand, one of the only entire countries, such as Madagascar, Japan, Philippines and New Caledonia to be described as a biodiversity hotspot (Reid 1998; Abbitt et al. 2000; Smith et al. 2001; Mittermeier et al. 2004). Between 1769 and 1919, 1170 species were recorded as being introduced to New Zealand (Thompson 1922) (Table 1). Ritchie (1922) reviewed the publication of Thompson?s inventory and warned against the introduction of exotic species without proper planning and assessment of the impacts on the existing biota. The warning was given because of New Zealand?s biodiversity had evolved in the absence of mammalian predators. Many bird, reptile and invertebrate species had limited defences against mammal species such as rats Rattus spp, mustelids (Stoat Mustela erminea, Ferret Mustela furo and Weasel Mustela nivalis vulgari), Brushtail Possum Trichosurus vulpectula and Cat Felis cattus. At the beginning of the 20th century, most of New Zealand?s large land vertebrates were extinct or threatened with extinction. The rapid expansion of mustelids, rats and Cat had caused considerable contractions in the distribution of large ground birds such as Kakapo Strigops habroptilus, South Island Takahe Porphyrio mantelli hochstetteri and species of waterfowl.


2021 ◽  
Author(s):  
Priscilla M. Wehi ◽  
Deborah J. Wilson ◽  
Clive Stone ◽  
Hayley Ricardo ◽  
Chris Jones ◽  
...  

2021 ◽  
Author(s):  
◽  
Charles Daniel Clark

<p>Recent biological invasions provide a unique opportunity to examine how species may adapt to novel conditions over relatively short time frames. Introduced species may respond to novel environmental conditions in the new range via rapid evolution, phenotypic plasticity, or the rapid evolution of phenotypic plasticity. However, the prevalence of these different mechanisms in introduced species remains unclear. In this thesis, I explore how introduced plant species may adjust their phenotype when introduced to a new range.  First, I tested for evidence of phenotypic change through time in key morphological traits (plant height, leaf area, leaf shape, and leaf mass per unit area), using historic herbarium records for 34 plants introduced to Australia and New Zealand. Thirty-two out of 94 trait-species combinations showed evidence for change through time. The rate and direction of trait change was variable across species and the local climate. One possibility is that species introduced to a new range exhibit different trait responses depending on the relative difference in environment between the native and introduced range. To investigate this, I quantified climatic niche shifts in introduced species relative to their native range. I then predicted trait change through time from the magnitude and direction of climate niche shift in a meta-regression. This is the first study to simultaneously assess trait change in multiple introduced species in relation to a shift in their realised niche. Overall, climate niche shifts did not predict trait change through time, suggesting that climate may not be the predominant driver of trait change in plants introduced to Australia and New Zealand. Alternatively, the combined uncertainty and the mismatch in spatial scales that may arise when combining these two methods could mask any underlying patterns in plant trait responses to the new environment.  It has been hypothesised that introduced species may respond to a sudden change in environment, by rapidly selecting for an increase in phenotypic plasticity. I tested for a difference in phenotypic plasticity between the native and introduced ranges of a beach daisy, Arctotheca populifolia. Contrary to my expectations, A. populifolia has shown a loss of phenotypic plasticity in as little as 80 years since its introduction to Australia. When using a meta-analysis to test for an overall difference in plasticity across multiple traits, I found that the current practice of calculating an effect size of an effect size (Hedges’ d) can lead to misleading results. I demonstrate how this issue arises when calculating a difference in Hedges’ d between two populations with different standard deviations. I propose an alternative way to calculate Hedges’ d to give a more accurate reflection of the difference in plasticity between ranges.  Finally, I combine different lines of evidence from the previous chapters in a case study to explore how A. populifolia has changed since its introduction to Australia, and examine any discrepancies between the results. A glasshouse experiment revealed distinct trait differences between native and introduced populations of A. populifolia, which were not reflected in trait change through time inferred from herbarium specimens. Additionally, measured trait differences between ranges in the glasshouse experiment better reflected a niche shift into wetter climate, than the predicted trait change through time from herbarium specimens. This suggests that trait differences determined in glasshouse or common garden experiments, may be a more suitable approach to assess trait change in relation to a realised niche shift than using herbarium specimens.</p>


Zootaxa ◽  
2010 ◽  
Vol 2484 (1) ◽  
pp. 45 ◽  
Author(s):  
A. C. EYLES ◽  
M. B. MALIPATIL

Nysius caledoniae Distant, 1920 is recorded for the first time as an alien introduced species in New Zealand. Collection with young stages indicates that it may already have established itself in Auckland. Characters of the species enabling its identification are presented. The pest-status of N. caledoniae, N. vinitor Bergroth, 1891, and N. huttoni White, 1878, is reviewed. A key to the genera of Orsillidae in New Zealand is provided, along with a revised key to the species of Nysius in that country.


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