Mistletoes and Thionins
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"Santalales (Including Mistletoes)"
Santalales (Including Introductory article Mistletoes) Article Contents . Introduction Daniel L Nickrent, Southern Illinois University, Carbondale, Illinois, USA . Taxonomy and Phylogenetics . Morphology, Life Cycle and Ecology . Biogeography of Mistletoes . Importance of Mistletoes Online posting date: 15th March 2011 Mistletoes are flowering plants in the sandalwood order that produce some of their own sugars via photosynthesis (Santalales) that parasitise tree branches. They evolved to holoparasites that do not photosynthesise. Holopar- five separate times in the order and are today represented asites are thus totally dependent on their host plant for by 88 genera and nearly 1600 species. Loranthaceae nutrients. Up until recently, all members of Santalales were considered hemiparasites. Molecular phylogenetic ana- (c. 1000 species) and Viscaceae (550 species) have the lyses have shown that the holoparasite family Balano- highest species diversity. In South America Misodendrum phoraceae is part of this order (Nickrent et al., 2005; (a parasite of Nothofagus) is the first to have evolved Barkman et al., 2007), however, its relationship to other the mistletoe habit ca. 80 million years ago. The family families is yet to be determined. See also: Nutrient Amphorogynaceae is of interest because some of its Acquisition, Assimilation and Utilization; Parasitism: the members are transitional between root and stem para- Variety of Parasites sites. Many mistletoes have developed mutualistic rela- The sandalwood order is of interest from the standpoint tionships with birds that act as both pollinators and seed of the evolution of parasitism because three early diverging dispersers. Although some mistletoes are serious patho- families (comprising 12 genera and 58 species) are auto- gens of forest and commercial trees (e.g. -
2020 Majura Ainslie Plant List.Xlsx
Plant Species List for Mount Majura and Mount Ainslie, Canberra Base data from Ingwerson, F; O. Evans & B. Griffiths. (1974). Vegetation of the Ainslie-Majura Reserve . Conservation Series No. 2. AGPS Canberra. Re-organised, revised and updated by Michael Doherty, CSIRO Ecosystem Sciences and Waltraud Pix, Friends of Mt. Majura With advice from Isobel Crawford, Australian Botanical Surveys Current version of 01.10.2020 Names: Census of Plants of the Australian Capital Territory, Version 4.1, 2019 Enquiries:Version 3.0 [email protected] (8th June 2012) subsp. = subspecies Form ? = questionable status or identity f = herb, forb sp. aff. = having close affinities with i.e. similar but not quite the sameo = herb, orchid syn. = synonymous with i.e. most recent previous name, or alternativeg = nameherb, grass sens. lat. = in the broad sense of the species concept gl = herb, grass- or sedge-like var. = variety s = shrub (including creeper and climber) sp. = species i.e. identity yet to be finalised st = shrub / small tree spp. = species in the plural i.e. more than one species t = tree MM Mount Majura. Notionally north of “Blue Metal” Road; MA Mount Ainslie. Notionally south of “Blue Metal” Road (VVV) Species occurrence checking; currently focused on Mt. Majura rather than Mt. Ainslie. No ticks next to name = species reported but not yet confirmed for Mt Majura and Mt Ainslie. Status is locally native except for: PE = Planted Exotic PN = Planted Non-local Native WE = Weed Exotic WN = Weed Non-local Native ‘Planted’ status refers to individuals which are planted but not spreading ‘Weed’ status refers to species reproducing in the wild Scientific name Common name MM MA Status Form Family Isolepis sp . -
Synthesizing Ecosystem Implications of Mistletoe Infection
Environmental Research Letters LETTER • OPEN ACCESS Related content - Networks on Networks: Water transport in Mistletoe, friend and foe: synthesizing ecosystem plants A G Hunt and S Manzoni implications of mistletoe infection - Networks on Networks: Edaphic constraints: the role of the soil in vegetation growth To cite this article: Anne Griebel et al 2017 Environ. Res. Lett. 12 115012 A G Hunt and S Manzoni - Impact of mountain pine beetle induced mortality on forest carbon and water fluxes David E Reed, Brent E Ewers and Elise Pendall View the article online for updates and enhancements. This content was downloaded from IP address 137.154.212.215 on 17/12/2017 at 21:57 Environ. Res. Lett. 12 (2017) 115012 https://doi.org/10.1088/1748-9326/aa8fff LETTER Mistletoe, friend and foe: synthesizing ecosystem OPEN ACCESS implications of mistletoe infection RECEIVED 28 June 2017 Anne Griebel1,3 ,DavidWatson2 and Elise Pendall1 REVISED 1 Hawkesbury Institute for the Environment, Western Sydney University, Locked Bag 1797, Penrith, NSW, Australia 12 September 2017 2 Institute for Land, Water and Society, Charles Sturt University, PO box 789, Albury, NSW, Australia ACCEPTED FOR PUBLICATION 3 Author to whom any correspondence should be addressed. 29 September 2017 PUBLISHED E-mail: [email protected] 16 November 2017 Keywords: mistletoe, climate change, biodiversity, parasitic plants, tree mortality, forest disturbance Original content from this work may be used Abstract under the terms of the Creative Commons Biotic disturbances are affecting a wide range of tree species in all climates, and their occurrence is Attribution 3.0 licence. contributing to increasing rates of tree mortality globally. -
Bruxner Park Flora Reserve Working Plan
Bruxner Park Flora Reserve Working Plan Working Plan for Bruxner Park Flora Reserve No 3 Upper North East Forest Agreement Region North East Region Contents Page 1. DETAILS OF THE RESERVE 2 1.1 Introduction 2 1.2 Location 2 1.3 Key Attributes of the Reserve 2 1.4 General Description 2 1.5 History 6 1.6 Current Usage 8 2. SYSTEM OF MANAGEMENT 9 2.1 Objectives of Management 9 2.2 Management Strategies 9 2.3 Management Responsibility 11 2.4 Monitoring, Reporting and Review 11 3. LIST OF APPENDICES 11 Appendix 1 Map 1 Locality Appendix 1 Map 2 Cadastral Boundaries, Forest Types and Streams Appendix 1 Map 3 Vegetation Growth Stages Appendix 1 Map 4 Existing Occupation Permits and Recreation Facilities Appendix 2 Flora Species known to occur in the Reserve Appendix 3 Fauna records within the Reserve Y:\Tourism and Partnerships\Recreation Areas\Orara East SF\Bruxner Flora Reserve\FlRWP_Bruxner.docx 1 Bruxner Park Flora Reserve Working Plan 1. Details of the Reserve 1.1 Introduction This plan has been prepared as a supplementary plan under the Nature Conservation Strategy of the Upper North East Ecologically Sustainable Forest Management (ESFM) Plan. It is prepared in accordance with the terms of section 25A (5) of the Forestry Act 1916 with the objective to provide for the future management of that part of Orara East State Forest No 536 set aside as Bruxner Park Flora Reserve No 3. The plan was approved by the Minister for Forests on 16.5.2011 and will be reviewed in 2021. -
Loranthaceae1
Flora of South Australia 5th Edition | Edited by Jürgen Kellermann LORANTHACEAE1 P.J. Lang2 & B.A. Barlow3 Aerial hemi-parasitic shrubs on branches of woody plants attached by haustoria; leaves mostly opposite, entire. Inflorescence terminal or lateral; flowers bisexual; calyx reduced to an entire, lobed or toothed limb at the apex of the ovary, without vascular bundles; corolla free or fused, regular or slightly zygomorphic, 4–6-merous, valvate; stamens as many as and opposite the petals, epipetalous, anthers 2- or 4-locular, mostly basifixed, immobile, introrse and continuous with the filament but sometimes dorsifixed and then usually versatile, opening by longitudinal slits; pollen trilobate; ovary inferior, without differentiated locules or ovules. Fruit berry-like; seed single, surrounded by a copious viscous layer. Mistletoes. 73 genera and around 950 species widely distributed in the tropics and south temperate regions with a few species in temperate Asia and Europe. Australia has 12 genera (6 endemic) and 75 species. Reference: Barlow (1966, 1984, 1996), Nickrent et al. (2010), Watson (2011). 1. Petals free 2. Anthers basifixed, immobile, introrse; inflorescence axillary 3. Inflorescence not subtended by enlarged bracts more than 20 mm long ....................................... 1. Amyema 3: Inflorescence subtended by enlarged bracts more than 20 mm long which enclose the buds prior to anthesis ......................................................................................................................... 2. Diplatia 2: Anthers dorsifixed, versatile; inflorescence terminal ........................................................................... 4. Muellerina 1: Petals united into a curved tube, more deeply divided on the concave side ................................................ 3. Lysiana 1. AMYEMA Tiegh. Bull. Soc. Bot. France 41: 499 (1894). (Greek a-, negative; myeo, I instruct, initiate; referring to the genus being not previously recognised; cf. -
Lodgepole Pine Dwarf Mistletoe in Taylor Park, Colorado Report for the Taylor Park Environmental Assessment
Lodgepole Pine Dwarf Mistletoe in Taylor Park, Colorado Report for the Taylor Park Environmental Assessment Jim Worrall, Ph.D. Gunnison Service Center Forest Health Protection Rocky Mountain Region USDA Forest Service 1. INTRODUCTION ............................................................................................................................... 2 2. DESCRIPTION, DISTRIBUTION, HOSTS ..................................................................................... 2 3. LIFE CYCLE....................................................................................................................................... 3 4. SCOPE OF TREATMENTS RELATIVE TO INFESTED AREA ................................................. 4 5. IMPACTS ON TREES AND FORESTS ........................................................................................... 4 5.1 TREE GROWTH AND LONGEVITY .................................................................................................... 4 5.2 EFFECTS OF DWARF MISTLETOE ON FOREST DYNAMICS ............................................................... 6 5.3 RATE OF SPREAD AND INTENSIFICATION ........................................................................................ 6 6. IMPACTS OF DWARF MISTLETOES ON ANIMALS ................................................................ 6 6.1 DIVERSITY AND ABUNDANCE OF VERTEBRATES ............................................................................ 7 6.2 EFFECT OF MISTLETOE-CAUSED SNAGS ON VERTEBRATES ............................................................12 -
Dwarf Mistletoes: Biology, Pathology, and Systematics
This file was created by scanning the printed publication. Errors identified by the software have been corrected; however, some errors may remain. CHAPTER 10 Anatomy of the Dwarf Mistletoe Shoot System Carol A. Wilson and Clyde L. Calvin * In this chapter, we present an overview of the Morphology of Shoots structure of the Arceuthobium shoot system. Anatomical examination reveals that dwarf mistletoes Arceuthobium does not produce shoots immedi are indeed well adapted to a parasitic habit. An exten ately after germination. The endophytic system first sive endophytic system (see chapter 11) interacts develops within the host branch. Oftentimes, the only physiologically with the host to obtain needed evidence of infection is swelling of the tissues near the resources (water, minerals, and photosynthates); and infection site (Scharpf 1967). After 1 to 3 years, the first the shoots provide regulatory and reproductive func shoots are produced (table 2.1). All shoots arise from tions. Beyond specialization of their morphology (Le., the endophytic system and thus are root-borne shoots their leaves are reduced to scales), the dwarf mistle (Groff and Kaplan 1988). In emerging shoots, the toes also show peculiarities of their structure that leaves of adjacent nodes overlap and conceal the stem. reflect their phylogenetic relationships with other As the internodes elongate, stem segments become mistletoes and illustrate a high degree of specialization visible; but the shoot apex remains tightly enclosed by for the parasitic habit. From Arceuthobium globosum, newly developing leaf primordia (fig. 10.lA). Two the largest described species with shoots 70 cm tall oppositely arranged leaves, joined at their bases, occur and 5 cm in diameter, toA. -
Researchcommons.Waikato.Ac.Nz
View metadata, citation and similar papers at core.ac.uk brought to you by CORE provided by Research Commons@Waikato http://researchcommons.waikato.ac.nz/ Research Commons at the University of Waikato Copyright Statement: The digital copy of this thesis is protected by the Copyright Act 1994 (New Zealand). The thesis may be consulted by you, provided you comply with the provisions of the Act and the following conditions of use: Any use you make of these documents or images must be for research or private study purposes only, and you may not make them available to any other person. Authors control the copyright of their thesis. You will recognise the author’s right to be identified as the author of the thesis, and due acknowledgement will be made to the author where appropriate. You will obtain the author’s permission before publishing any material from the thesis. Identifying Host Species of Dactylanthus taylorii using DNA Barcoding A thesis submitted in partial fulfilment of the requirements for the degree of Masters of Science in Biological Sciences at The University of Waikato by Cassarndra Marie Parker _________ The University of Waikato 2015 Acknowledgements: This thesis wouldn't have been possible without the support of many people. Firstly, my supervisors Dr Chrissen Gemmill and Dr Avi Holzapfel - your professional expertise, advice, and patience were invaluable. From pitching the idea in 2012 to reading through drafts in the final fortnight, I've been humbled to work with such dedicated and accomplished scientists. Special mention also goes to Thomas Emmitt, David Mudge, Steven Miller, the Auckland Zoo horticulture team and Kevin. -
Epiparasitism in Phoradendron Durangense and P. Falcatum (Viscaceae) Clyde L
Aliso: A Journal of Systematic and Evolutionary Botany Volume 27 | Issue 1 Article 2 2009 Epiparasitism in Phoradendron durangense and P. falcatum (Viscaceae) Clyde L. Calvin Rancho Santa Ana Botanic Garden, Claremont, California Carol A. Wilson Rancho Santa Ana Botanic Garden, Claremont, California Follow this and additional works at: http://scholarship.claremont.edu/aliso Part of the Botany Commons Recommended Citation Calvin, Clyde L. and Wilson, Carol A. (2009) "Epiparasitism in Phoradendron durangense and P. falcatum (Viscaceae)," Aliso: A Journal of Systematic and Evolutionary Botany: Vol. 27: Iss. 1, Article 2. Available at: http://scholarship.claremont.edu/aliso/vol27/iss1/2 Aliso, 27, pp. 1–12 ’ 2009, Rancho Santa Ana Botanic Garden EPIPARASITISM IN PHORADENDRON DURANGENSE AND P. FALCATUM (VISCACEAE) CLYDE L. CALVIN1 AND CAROL A. WILSON1,2 1Rancho Santa Ana Botanic Garden, 1500 North College Avenue, Claremont, California 91711-3157, USA 2Corresponding author ([email protected]) ABSTRACT Phoradendron, the largest mistletoe genus in the New World, extends from temperate North America to temperate South America. Most species are parasitic on terrestrial hosts, but a few occur only, or primarily, on other species of Phoradendron. We examined relationships among two obligate epiparasites, P. durangense and P. falcatum, and their parasitic hosts. Fruit and seed of both epiparasites were small compared to those of their parasitic hosts. Seed of epiparasites was established on parasitic-host stems, leaves, and inflorescences. Shoots developed from the plumular region or from buds on the holdfast or subjacent tissue. The developing endophytic system initially consisted of multiple separate strands that widened, merged, and often entirely displaced its parasitic host from the cambial cylinder. -
Pdf Clickbook Booklet
Grand Canyon Flora: Upper Bright Angel Trail # Famil ID Scientific Name (*)Common Name #iN Mile #Pl/Loc Lycopods 1 Selag Selaginella mutica spike-moss 1 1.81 1/1 Gymnosperms 2 Cupre Juniperus osteosperma Utah juniper 5 0.00 20/9 3 Ephed Ephedra viridis green ephedra 9 0.34 50/9 4 Pinac Pinus edulis two-needle pinyon pine 9 0.00 50/9 5 Pinac Pinus ponderosa ponderosa pine 3 0.13 / 6 Pinac Pseudotsuga menziesii var. glauca Rocky Mountain Douglas fir 7 0.38 10/3 Eudicots 7 Amara Amaranthus albus *tumble pigweed 0.02 5/2 8 Amara Amaranthus powellii Powell's amaranth 0.00 20/2 9 Amara Atriplex canescens fourwing saltbush 3.73 1/1 10 Amara Atriplex rosea *tumbling oracle 0.02 40/2 11 Amara Chenopodium fremontii Fremont's goosefoot 0.08 20/5 12 Amara Salsola tragus *Russian thistle 1 0.01 20/3 13 Anaca Rhus aromatica skunkbush 2 1.17 20/6 14 Apiac Yabea microcarpa California hedge-parsley 3.46 2/1 15 Apocy Asclepias subverticillata poison milkweed 3.61 1/1 16 Aster Acourtia wrightii brownfoot 3 3.46 2/2 17 Aster Ageratina herbacea fragrant snakeroot 3 0.20 30/5 18 Aster Artemisia bigelovii Bigelow sagebrush 1 1.77 iN/1 19 Aster Artemisia ludoviciana silver wormwood 1 0.05 99/9 20 Aster Artemisia nova black sagebrush 0.23 x/1 21 Aster Artemisia tridentata big sagebrush 0.15 30/9 22 Aster Baccharis salicifolia mule fat 2 IG iN/1 23 Aster Baccharis sarothroides broom baccharis 1 4.60 iN/1 24 Aster Brickellia californica California brickellbush 6 0.04 99/9 25 Aster Brickellia longifolia longleaf brickellbush 2 1.71 99/9 26 Aster Chaetopappa ericoides rose heath 0.44 20/6 27 Aster Cirsium arizonicum Arizona thistle 9 0.05 30/9 28 Aster Dieteria canescens hoary-aster 7 0.00 50/9 29 Aster Encelia resinifera resin brittlebush 3.28 30/7 30 Aster Ericameria arizonica Grand Canyon Goldenweed 1 0.12 20/8 31 Aster Ericameria nauseosa var. -
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. -
Mt Mabu, Mozambique: Biodiversity and Conservation
Darwin Initiative Award 15/036: Monitoring and Managing Biodiversity Loss in South-East Africa's Montane Ecosystems MT MABU, MOZAMBIQUE: BIODIVERSITY AND CONSERVATION November 2012 Jonathan Timberlake, Julian Bayliss, Françoise Dowsett-Lemaire, Colin Congdon, Bill Branch, Steve Collins, Michael Curran, Robert J. Dowsett, Lincoln Fishpool, Jorge Francisco, Tim Harris, Mirjam Kopp & Camila de Sousa ABRI african butterfly research in Forestry Research Institute of Malawi Biodiversity of Mt Mabu, Mozambique, page 2 Front cover: Main camp in lower forest area on Mt Mabu (JB). Frontispiece: View over Mabu forest to north (TT, top); Hermenegildo Matimele plant collecting (TT, middle L); view of Mt Mabu from abandoned tea estate (JT, middle R); butterflies (Lachnoptera ayresii) mating (JB, bottom L); Atheris mabuensis (JB, bottom R). Photo credits: JB – Julian Bayliss CS ‒ Camila de Sousa JT – Jonathan Timberlake TT – Tom Timberlake TH – Tim Harris Suggested citation: Timberlake, J.R., Bayliss, J., Dowsett-Lemaire, F., Congdon, C., Branch, W.R., Collins, S., Curran, M., Dowsett, R.J., Fishpool, L., Francisco, J., Harris, T., Kopp, M. & de Sousa, C. (2012). Mt Mabu, Mozambique: Biodiversity and Conservation. Report produced under the Darwin Initiative Award 15/036. Royal Botanic Gardens, Kew, London. 94 pp. Biodiversity of Mt Mabu, Mozambique, page 3 LIST OF CONTENTS List of Contents .......................................................................................................................... 3 List of Tables .............................................................................................................................