Trilepidea Adamsii
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Explosive New Zealand Mistletoe Example, 4 of 7 Flowers on Sheet AK103910)
SCIENTIFIC CORRESPONDENCE pattern, as do herbarium sheets (for Explosive New Zealand mistletoe example, 4 of 7 flowers on sheet AK103910). Trilepidea almost certainly SIR- Many flowers of the mistletoe arium sheets show an even more special had more complex explosive flowers than Peraxilla tetrapetala (Loranthaceae) in New ized explosive mechanism than in Peraxilla. Peraxilla. Such specialization may have Zealand open from the bottom (f in the We discovered explosive flower opening rendered Trilepidea more sensitive to figure) rather than the top (d); Kuijtl called in both endemic New Zealand Peraxilla reduced bird densities due to introduced this an "unsolved mystery ... we cannot species when we noted that flower buds mammalian predators, contributing to its even guess at the meaning of this bizarre bagged for hand pollination almost never rapid and puzzling5 decline. performance." Here we report that flower opened (3/394 for P. tetrapetala, 1/82 for P. Explosive flower opening is well known buds of P. tetrapetala and P. colensoi open colensoi). The petals remained fused at the in other mistletoes6, including many of from the top only when twisted by top, while eventually undergoing abscis the 230 species in Africa3, and a few a bird, a form of 'explosive' flower open sion from their base (fin the figure). Field species in India7, Java, New Guinea and ing common in Africa but previously observations of unbagged flowers revealed South America1•6. However, this is the unknown in Australasia. Kuijt's "bizarre that they were opened by two native first report from Australasia. The New performance" is simply the consequence of honeyeaters (Meliphagidae ): tuis (Pros Zealand flora generally displays few flowers not being visited by birds. -
Malaysia's Unique Biological Diversity: New Insights from Molecular Evolutionary Studies of Parasitic Flowering Plants
Malaysia's Unique Biological Diversity: New Insights from Molecular Evolutionary Studies of Parasitic Flowering Plants Daniel L. Nickrent Department of Plant Biology Southern Illinois University Carbondale, IL 62901-6509 e-mail: [email protected] October 2, 1995 ABSTRACT Malaysia is home to a rich assemblage of parasitic flowering plants representing seven families, 46 genera and approximately 100 species. These plants are seldom considered candidates for conservation efforts, however, many species are important components of the tropical ecosystem that show complex associations with other organisms and unique biochemical features. Results of a phylogenetic analysis of 29 members of Santalales using a combined dataset of nuclear-encoded 18S rDNA and plastid-encoded rbcL sequences are presented. Sequences from representatives of three nonphotosynthetic, holoparasitic families often allied with Santalales, Balanophoraceae, Hydnoraceae and Rafflesiaceae, have been obtained from nuclear-encoded 18S rDNA and plastid- encoded 16S rDNA. As with 18S rDNA, the 16S rDNA sequences from all three holoparasite families showed an increase in the number of substitutions. The greatest increases were seen in Mitrastema and Hydnora, greater than values obtained from pairwise comparisons involving taxa as phylogenetically distant as angiosperms and liverworts. A case is made that these plants represent unique natural genetic experiments that offer a wealth of opportunity for molecular genetic and phylogenetic analyses. 2 “We do not know enough about any gene, species, or ecosystem to be able to calculate its ecological and economic worth in the large scheme of things” (Ehrenfeld 1988) Why conserve parasitic plants? When considering the reasons for conservation of biodiversity, one inevitably concludes that all involve value judgments that are, in essence, anthropocentric. -
Spatial Variation in Impacts of Brushtail Possums on Two Loranthaceous Mistletoe Species
SWEETAPPLE:Available on-line at:POSSUM http://www.newzealandecology.org/nzje/ IMPACTS ON MISTLETOE 177 Spatial variation in impacts of brushtail possums on two Loranthaceous mistletoe species Peter J. Sweetapple Landcare Research, PO Box 40, Lincoln 7640, New Zealand (Email: [email protected]) Published on-line: 8 October 2008 ___________________________________________________________________________________________________________________________________ Abstract: Browsing by introduced brushtail possums is linked to major declines in mistletoe abundance in New Zealand, yet in some areas mistletoes persist, apparently unaffected by the presence of possums. To determine the cause of this spatial variation in impact I investigated the abundance and condition (crown dieback and extent of possum browse cover) of two mistletoes (Alepis flavida, Peraxilla tetrapetala) and abundance and diet of possums in two mountain beech (Nothofagus solandri var. cliffortioides) forests in the central-eastern South Island of New Zealand. Mistletoe is common and there are long-established uncontrolled possum populations in both forests. Mistletoes were abundant (216–1359 per hectare) and important in possum diet (41–59% of total diet), but possum density was low (c. 2 per hectare) in both areas. Possum impacts were slight with low browse frequencies and intensities over much of the study sites. However, impacts were significantly greater at a forest margin, where possum abundance was highest, and at a high-altitude site where mistletoe density was lowest. Mistletoe crown dieback was inversely proportional to intensity of possum browsing. These results suggest that the persistence of abundant mistletoe populations at these sites is due to mistletoe productivity matching or exceeding consumption by possums in these forests of low possum-carrying _______________________________________________________________________________________________________________________________capacity, rather than low possum preference for the local mistletoe populations. -
2008 • Te Papa Tongarewa, Wellington, New Zealand
New Zealand Plant Conservation Network CELEBRATING OUR NATIVE PLANT LIFE Conference Proceedings 8-10 August 2008 • Te Papa Tongarewa, Wellington, New Zealand Sponsored by Wellington and Hutt City Councils and the Department of Conservation and supported by Enviroschools and Te Papa Tongarewa www.nzpcn.org.nz This publication is the proceedings of the NZ Plant Conservation Network conference held at the Museum of New Zealand Te Papa Tongarewa, Wellington, New Zealand from 6-7th August 2008. The workshop was organised by the New Zealand Plant Conservation Network, with sponsorship from Wellington and Hutt City Councils, the Department of Conservation and with support from Enviroschools and Te papa Tongarewa. Cover photos (clockwise from bottom left): Celmisia mackaui, Hinewai 2007; Anaphalioides bellidioides; Cobden Beach, West Coast; basic outcrop on Mt. Herbert, Banks Peninsula, Canterbury; Leptinella sp. New Zealand Plant Conservation Network CELEBRATING OUR NATIVE PLANT LIFE Conference Proceedings 8-10 August 2008 • Te Papa Tongarewa, Wellington, New Zealand Sponsored by Wellington and Hutt City Councils and the Department of Conservation and supported by Enviroschools and Te Papa Tongarewa www.nzpcn.org.nz © 2009, New Zealand Plant Conservation Network ISBN 978-0-473-14950-5 Publication designed by Cerulean • www.cerulean.co.nz TABLE OF CONTENTS Executive summary. 6 Introduction and background . 7 Purpose of this report . 7 Global Strategy for Plant Conservation. 7 Enviroschools native plant forum. 7 Tane Ngahere Lecture. 8 2008 Conference introduction by the President. 9 Conference papers Investigations into the food value of bracken fern rhizomes . 11 A Plant on the Edge - The Trials of Coastal Peppercress Recovery. -
List of Current Names for Trees & Shrubs of New Zealand by Poole
List of current names for Trees & Shrubs of New Zealand by Poole and Adams Extracted from the Plant Names Database on 31 January 2012 Alectryon grandis ............................................... Alectryon excelsus subsp. grandis (Cheeseman) de Lange & E.K.Cameron Alseuosmia ×quercifolia ..................................... Alseuosmia quercifolia A.Cunn. Avicennia marina var. resinifera ......................... Avicennia marina subsp. australasica (Walp.) J.Everett Brachyglottis repanda ........................................ Brachyglottis repanda var. fragrans D.G.Drury Carmichaelia aligera .......................................... Carmichaelia australis R.Br. Carmichaelia angustata ..................................... Carmichaelia odorata Benth. Carmichaelia angustata var. pubescens ............ Carmichaelia odorata Benth. Carmichaelia arenaria ........................................ Carmichaelia australis R.Br. Carmichaelia compacta var. procumbens .......... Carmichaelia compacta Petrie Carmichaelia cunninghamii ................................ Carmichaelia australis R.Br. Carmichaelia egmontiana .................................. Carmichaelia australis R.Br. Carmichaelia enysii ............................................ Carmichaelia nana (Hook.f.) Hook.f. Carmichaelia enysii var. ambigua ...................... Carmichaelia nana (Hook.f.) Hook.f. Carmichaelia fieldii ............................................. Carmichaelia juncea Hook.f. Carmichaelia flagelliformis ................................. Carmichaelia australis -
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66 AvailableNew on-lineZealand at: Journal http://www.newzealandecology.org/nzje/ of Ecology, Vol. 34, No. 1, 2010 special issue: Feathers to Fur The ecological transformation of Aotearoa/New Zealand Mutualisms with the wreckage of an avifauna: the status of bird pollination and fruit- dispersal in New Zealand Dave Kelly1*, Jenny J. Ladley1, Alastair W. Robertson2, Sandra H. Anderson3, Debra M. Wotton1, and Susan K. Wiser4 1School of Biological Sciences, University of Canterbury, Private Bag 4800, Christchurch 8140, New Zealand 2Ecology, Institute of Natural Resources, Massey University, Private Bag 11222, Palmerston North 4474, New Zealand 3School of Environment, University of Auckland, Private Bag 92019, Auckland 1010, New Zealand 4Landcare Research, PO Box 40, Lincoln 7640, New Zealand *Author for correspondence (Email: [email protected]) Published on-line: 9 November 2009 Abstract: Worldwide declines in bird numbers have recently renewed interest in how well bird–plant mutualisms are functioning. In New Zealand, it has been argued that bird pollination was relatively unimportant and bird- pollination failure was unlikely to threaten any New Zealand plants, whereas dispersal mutualisms were widespread and in some cases potentially at risk because of reliance on a single large frugivore, the kereru (Hemiphaga novaeseelandiae). Work since 1989, however, has changed that assessment. Smaller individual fruits of most plant species can be dispersed by mid-sized birds such as tui (Prosthemadera novaezelandiae) because both fruits and birds vary in size within a species. Only one species (Beilschmiedia tarairi) has no individual fruits small enough for this to occur. Germination of 19 fleshy-fruited species, including most species with fruits >8 mm diameter, does not depend on birds removing the fruit pulp. -
Threatened Plants of Waikato Conservancy Threatened Plants of Waikato Conservancy
Threatened plants of Waikato Conservancy Threatened plants of Waikato Conservancy Andrea Brandon, Peter de Lange and Andrew Townsend Published by: Department of Conservation P.O. Box 10-420 Wellington, New Zealand This publication was prepared by DOC Science Publishing, Science & Research Unit: editing by Jaap Jasperse and layout by Jeremy Rolfe. Publication was approved by the Manager, Biodiversity Recovery Unit, Science Technology and Information Services, Department of Conservation, Wellington. © April 2004, Department of Conservation ISBN 0-478-22095-2 CONTENTS Acknowledgements 5 Introduction 6 Species profiles 9 Amphibromus fluitans 10 Anzybas carsei 12 Asplenium cimmeriorum 14 Austrofestuca littoralis 15 Brachyglottis kirkii var. kirkii 17 Carex litorosa 18 Carmichaelia williamsii 19 Centipeda minima subsp. minima 21 Cyclosorus interruptus 23 Dactylanthus taylorii 24 Deschampsia cespitosa 26 Desmoschoenus spiralis 28 Epacris sinclairii 30 Euphorbia glauca 31 Gratiola nana 33 Hebe scopulorum 34 Hebe speciosa 35 Lepidium flexicaule 37 Lepidium oleraceum 39 Libertia peregrinans 41 Linguella puberula 42 Lycopodiella serpentina 44 Marattia salicina 45 Mazus novaezeelandiae 47 Melicytus flexuosus 49 Myosotis petiolata var. pansa 51 Olearia pachyphylla 52 Ophioglossum petiolatum 54 Picris burbidgei 55 Pimelea tomentosa 57 Pittosporum kirkii 58 Pittosporum turneri 60 Plumatochilos tasmanicum 62 Pomaderris apetala subsp. maritima 63 Pomaderris phylicifolia 65 Prasophyllum aff. patens 67 Pseudopanax laetus 68 Pterostylis micromega 69 Pterostylis -
New Zealand's Loranthaceous Mistletoes Has Only Recently Been Documented, with Many Facets Still to Be Fully Explored
Part 3 Threats to New Zealand mistletoes 139 Evidence for the impacts of possums on mistletoes Colin C. Ogle Department of Conservation, Private Bag 3016, Wanganui SUMMARY The evidence is updated on the impacts of introduced brushtail possums (Trichosurus vulpecula) on New Zealand’s loranthaceous mistletoes. It is concluded that possums eat mistletoes and they probably kill both individual plants and populations of mistletoes. Management practices that prevent possums reaching mistletoe plants have produced improvements in mistletoe growth and abundance. Because it is desirable to obtain further evidence of the impacts of possums, managers of mistletoe habitats should endeavour to incorporate a research component into their work to enhance mistletoe populations. 1. INTRODUCTION The work of Wilson (1984) was the first published study on the impacts of the introduced brushtail possum (Trichosurus vulpecula) on a population of New Zealand mistletoes. Ogle & Wilson (1985) extended this to a national review, collating published and unpublished sources on the distribution and abundance of loranthaceous mistletoes and related these to the occurrence and impacts of possums. Much of the evidence was anecdotal and the case pointing to possums as the cause of mistletoe decline was based more on indirect evidence than on experiments or direct observations of possums destroying mistletoe plants. Nevertheless, widespread mistletoe decline was demonstrated and possums were identified as the main (but not the only) cause. Ten years on from Ogle & Wilson's (1985) review, the case against possums has been widely accepted, especially in “popular” articles and books (Barlow 1987, James 1990, Webb et al. 1990, Clark 1993). However, some of the key questions posed by Ogle & Wilson (1985) remain largely unanswered. -
Monitoring Leaf Loss and Possum Impact on New Zealand Beech
Monitoring leaf loss and possum impact on New Zealand beech mistletoes A thesis submitted in partial fulfilment of the requirements for the . Degree of Master of Science in Botany at the University of Canterbury by Laura A. Sessions "",,;:f University of Canterbury 1999 THESIS v. 11 TABLE OF CONTENTS Table of Contents .............................................................................................................. ii List of Tables ................................................................................................................. viii List of Figures ................................................................................................................ xiii List of Plates ................................................................................................................... xv ABSTRACT ................................................................................................................... xvi CHAPTER 1: INTRODUCTION .................................................................................... 1 1.1. IMPORTANCE OF HERBIVORY TO PLANT DEMOGRAPHY AND PERFORMANCE ........... 1 1.2. HERBIVORY IN NEW ZEALAND ............................................................................... 2 1.2.1. The rata example ............................................................................................. 4 1.2.2. The importance o/herbivory to native mistletoes ........................................... 5 1.3. PROJECT GOALS ..................................................................................................... -
Mistletoe Reproductive Mutualisms in a West African
MISTLETOE REPRODUCTIVE MUTUALISMS IN A WEST AFRICAN MONTANE FOREST A thesis submitted in partial fulfilment of the requirements for the Degree of Master of Science in Ecology in the School of Biological Sciences Department. by Kerry Anne Weston University of Canterbury 2009 i Acknowledgements Firstly, I would like to thank my supervisor Hazel Chapman for providing me with the opportunity to conduct research in such a special place. My five months in Africa have made a lasting impression on me and for that I am forever grateful.Thank you for all your help and support during my study Hazel, and for presenting me with the challenge of a lifetime. I hugely respect all that you have accomplished at Ngel Nyaki. To my co-supervisor, Dave Kelly, under whose guidance I found my way. Endless thanks for all your technical input and support, I hope in return I’ve contributed something valuable to the mistletoe collective. To my lovely friend and field assistant Usman Usuf, who accompanied me tirelessly with such patience and humour. We had the best time and I always felt safe knowing you were alongside. Usman, your skills and contribution were invaluable to my study; you taught me so much about the forest, your land and language. Thank you. To all the field assistants at Ngel Nyaki, thank you all for your help and encouragement during my time at Ngel Nyaki. Special thanks to Bobo Zubairu and all the villagers who helped sew mesh bags for me, I am so grateful for your contribution. Thank you also Jenny Brown, for giving up your time to guide me through the intricacies of statistical modeling in R. -
Recent Anthropogenic Plant Extinctions Differ in Biodiversity Hotspots and Coldspots Johannes J
Recent Anthropogenic Plant Extinctions Differ in Biodiversity Hotspots and Coldspots Johannes J. Le Roux, Cang Hui, Maria L. Castillo, José M. Iriondo, Jan-Hendrik Keet, Anatoliy A. Khapugin, Frédéric Médail, Marcel Rejmánek, Genevieve Theron, Florencia A. Yannelli, et al. To cite this version: Johannes J. Le Roux, Cang Hui, Maria L. Castillo, José M. Iriondo, Jan-Hendrik Keet, et al.. Recent Anthropogenic Plant Extinctions Differ in Biodiversity Hotspots and Coldspots. Current Biology - CB, Elsevier, 2019, 29 (17), pp.2912-2918. 10.1016/j.cub.2019.07.063. hal-02272311 HAL Id: hal-02272311 https://hal-amu.archives-ouvertes.fr/hal-02272311 Submitted on 27 Aug 2019 HAL is a multi-disciplinary open access L’archive ouverte pluridisciplinaire HAL, est archive for the deposit and dissemination of sci- destinée au dépôt et à la diffusion de documents entific research documents, whether they are pub- scientifiques de niveau recherche, publiés ou non, lished or not. The documents may come from émanant des établissements d’enseignement et de teaching and research institutions in France or recherche français ou étrangers, des laboratoires abroad, or from public or private research centers. publics ou privés. Recent Anthropogenic Plant Extinctions Differ in Biodiversity Hotspots and Coldspots Johannes J. Le Roux,1,11,12,* Cang Hui,2,3,4 Maria L. Castillo,2 Jose M. Iriondo,5 Jan-Hendrik Keet,6 Anatoliy A. Khapugin,7,8 Fred eric Medail, 9 Marcel Rejma´ nek,10 Genevieve Theron,6 Florencia A. Yannelli,2 and Heidi Hirsch2,11,* 1Department of Biological -
Korthalsella: Viscaceae)
Copyright is owned by the Author of the thesis. Permission is given for a copy to be downloaded by an individual for the purpose of research and private study only. The thesis may not be reproduced elsewhere without the permission of the Author. Systematics, Biology and Ecology of New Zealand’s Pygmy Mistletoes (Korthalsella: Viscaceae) A thesis presented in partial fulfilment of the requirements for the degree of Doctor of Philosophy in Ecology at Massey University, Manawatu, New Zealand Amir Sultan 2014 ii Abstract New Zealand’s pygmy mistletoes belong to the genus Korthalsella Tieghem, which comprises about 30 species ranging from Malesia to Hawaii, the Marquesas and Henderson Islands in the east, Japan in the north, Australia, New Zealand in the south, and Ethiopia and Madagascar to the west. Mainland Australia, Hawaii, Malesia and Madagascar all have high levels of species richness. This thesis shows that Korthalsella has high levels of regional endemism and has widespread parallelism and supports the biogeographic model of speciation, whereas, the traditional sections based on morphology are not supported. Korthalsella is represented in New Zealand by a monophyletic clade of three species K. clavata (Kirk) Cheeseman, K. lindsayi (Oliver ex J. D. Hooker) Engl., and K. salicornioides (A. Cunningham) Tiegh. Korthalsella clavata and K. lindsayi are both generalists with relatively broad host ranges whereas K. salicornioides is a specialist species with most host records from two myrtaceous genera Kunzea Rchb. (kanuka) and Leptospermum J. R. Forst & G. Forst (manuka). Cross-infection experiments in Korthalsella salicornioides indicate the presence of putative Kunzea- and Leptospermum-specific races with better success rates of seedling survival when maternal and recipient hosts were the same.