Threatened Plants Tasmania Newsletter July 2016
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Recovery Plan for the Tallong Midge Orchid (Genoplesium Plumosum)
Approved Recovery Plan Recovery Plan for the Tallong Midge Orchid (Genoplesium plumosum) NSW NATIONAL PARKS AND May 2002 WILDLIFE SERVICE © NSW National Parks and Wildlife Service, 2002. This work is copyright, however material presented in this Plan may be copied for personal use or published for educational purposes, providing that any extracts are fully acknowledged. Apart from this and any other use as permitted under the Copyright Act 1968, no part may be reproduced without prior written permission from NPWS. NSW National Parks and Wildlife Service, 43 Bridge Street, (PO Box 1967) Hurstville NSW 2220 Tel: 02 9585 6444 www.npws.nsw.gov.au Requests for information or comments regarding the recovery program for the Tallong Midge Orchid are best directed to: The Tallong Midge Orchid Recovery Team Coordinator, Threatened Species Unit, NPWS Southern Directorate, PO Box 2115, Queanbeyan NSW 2620 Ph: (02) 6298 9700 Or The Director, Regional Wildlife Programs, Wildlife Australia Branch, Environment Australia, PO Box 636, Canberra ACT 2601 Ph: (02) 6274 1111 Cover illustration: Tallong Midge Orchid. Photographer: John Briggs This Plan should be cited as following: NSW National Parks and Wildlife Service (2002). Approved Recovery Plan for the Tallong Midge Orchid (Genoplesium plumosum). NSW National Parks and Wildlife Service, Hurstville NSW. ISBN 07 313 6457 0 Approved Recovery Plan The Tallong Midge Orchid Recovery Plan for the Tallong Midge Orchid (Genoplesium plumosum) Executive Summary This document constitutes the formal National and New South Wales State Recovery Plan for the Tallong Midge Orchid Genoplesium plumosum. It considers the conservation requirements of the species across its known range, identifies the future actions to be taken to ensure its long-term viability and the parties who will carry these out. -
Complete Chloroplast Genomes Shed Light on Phylogenetic
www.nature.com/scientificreports OPEN Complete chloroplast genomes shed light on phylogenetic relationships, divergence time, and biogeography of Allioideae (Amaryllidaceae) Ju Namgung1,4, Hoang Dang Khoa Do1,2,4, Changkyun Kim1, Hyeok Jae Choi3 & Joo‑Hwan Kim1* Allioideae includes economically important bulb crops such as garlic, onion, leeks, and some ornamental plants in Amaryllidaceae. Here, we reported the complete chloroplast genome (cpDNA) sequences of 17 species of Allioideae, fve of Amaryllidoideae, and one of Agapanthoideae. These cpDNA sequences represent 80 protein‑coding, 30 tRNA, and four rRNA genes, and range from 151,808 to 159,998 bp in length. Loss and pseudogenization of multiple genes (i.e., rps2, infA, and rpl22) appear to have occurred multiple times during the evolution of Alloideae. Additionally, eight mutation hotspots, including rps15-ycf1, rps16-trnQ-UUG, petG-trnW-CCA , psbA upstream, rpl32- trnL-UAG , ycf1, rpl22, matK, and ndhF, were identifed in the studied Allium species. Additionally, we present the frst phylogenomic analysis among the four tribes of Allioideae based on 74 cpDNA coding regions of 21 species of Allioideae, fve species of Amaryllidoideae, one species of Agapanthoideae, and fve species representing selected members of Asparagales. Our molecular phylogenomic results strongly support the monophyly of Allioideae, which is sister to Amaryllioideae. Within Allioideae, Tulbaghieae was sister to Gilliesieae‑Leucocoryneae whereas Allieae was sister to the clade of Tulbaghieae‑ Gilliesieae‑Leucocoryneae. Molecular dating analyses revealed the crown age of Allioideae in the Eocene (40.1 mya) followed by diferentiation of Allieae in the early Miocene (21.3 mya). The split of Gilliesieae from Leucocoryneae was estimated at 16.5 mya. -
Prasophyllum Stellatum Stellatum (Ben Lomond Leek-Orchid)
Listing Statement for Prasophyllum stellatum (ben lomond leek-orchid) Prasophyllum stellatum ben lomond leek-orchid T A S M A N I A N T H R E A T E N E D S P E C I E S L I S T I N G S T A T E M E N T Image by Mark Wapstra Scientific name: Prasophyllum stellatum D.L.Jones, Austral. Orchid Res . 3: 115 (1998) Common name: ben lomond leek-orchid (Wapstra et al. 2005) Group: vascular plant, dicotyledon, family Orchidaceae Status: Threatened Species Protection Act 1995 : endangered Environment Protection and Biodiversity Conservation Act 1999 : Critically Endangered Distribution: Endemic status: Endemic to Tasmania Tasmanian NRM Region: North Figure 1 . The distribution of Prasophyllum stellatum Plate 1. Prasophyllum stellatum from the Storys Creek type location (image by Mark Wapstra) 1 Threatened Species Section – Department of Primary Industries, Parks, Water and Environment Listing Statement for Prasophyllum stellatum (ben lomond leek-orchid) IDENTIFICATION AND ECOLOGY withered fertilised flowers) when seen. The Prasophyllum species, commonly known as leek- species may not flower or emerge in dry years. orchids, are deciduous terrestrials with small, fleshy, round or oval tubers and a few fleshy, Description irregular roots. Most species are dormant over The following description for the published summer and autumn and begin growth in early concept of Prasophyllum stellatum is adapted from winter. The single, erect, hollow leaf is reddish Jones (1998), Jones et al. (1999) and Jones at the base as opposed to green as in onion- (2006). However, recent field studies (Wapstra orchids ( Microtis ). -
Flora and Fauna Guarantee Act 1988 Protected Flora List November 2019
Department of Environment, Land, Water & Planning Flora and Fauna Guarantee Act 1988 Protected Flora List November 2019 What is Protected Flora? Protected flora are native plants or communities of native plants that have legal protection under the Flora and Fauna Guarantee Act 1988. The Protected Flora List includes plants from three sources: plant taxa (species, subspecies or varieties) listed as threatened under the Flora and Fauna Guarantee Act 1988 plant taxa belonging to communities listed as threatened under the Flora and Fauna Guarantee Act 1988 plant taxa which are not threatened but require protection for other reasons. For example, some species which are attractive or highly sought after, such as orchids and grass trees, are protected so that the removal of these species from the wild can be controlled. For all listed species protection includes living (eg flowers, seeds, shoots and roots) and non-living (eg bark, leaves and other litter) plant material. Do I need a permit or licence? The handling of protected flora is regulated by the Department of Environment, Land, Water & Planning (DELWP) to ensure that any harvesting or loss is ecologically sustainable. You must obtain a ‘Protected Flora Licence’ or Permit from one of the Regional Offices of DELWP if you want to collect protected native plants or if you are planning to do works or other activities on public land which might kill, injure or disturb protected native plants. In most cases, you do not require a Licence or Permit for works or activities on private land, although you may require a planning permit from your local council. -
The Consequences of a Management Strategy for the Endangered Karner Blue Butterfly
THE CONSEQUENCES OF A MANAGEMENT STRATEGY FOR THE ENDANGERED KARNER BLUE BUTTERFLY Bradley A. Pickens A Thesis Submitted to the Graduate College of Bowling Green State University in partial fulfillment of the requirements for the degree of MASTER OF SCIENCE August 2006 Committee: Karen V. Root, Advisor Helen J. Michaels Juan L. Bouzat © 2006 Bradley A. Pickens All Rights Reserved iii ABSTRACT Karen V. Root, Advisor The effects of management on threatened and endangered species are difficult to discern, and yet, are vitally important for implementing adaptive management. The federally endangered Karner blue butterfly (Karner blue), Lycaeides melissa samuelis inhabits oak savanna or pine barrens, is a specialist on its host-plant, wild blue lupine, Lupinus perennis, and has two broods per year. The Karner blue was reintroduced into the globally rare black oak/lupine savannas of Ohio, USA in 1998. Current management practices involve burning 1/3, mowing 1/3, and leaving 1/3 of the lupine stems unmanaged at each site. Prescribed burning generally kills any Karner blue eggs present, so a trade-off exists between burning to maintain the habitat and Karner blue mortality. The objective of my research was to quantify the effects of this management strategy on the Karner blue. In the first part of my study, I examined several environmental factors, which influenced the nutritional quality (nitrogen and water content) of lupine to the Karner blue. My results showed management did not affect lupine nutrition for either brood. For the second brood, I found that vegetation density best predicted lupine nutritional quality, but canopy cover and aspect had an impact as well. -
Redalyc.ARE OUR ORCHIDS SAFE DOWN UNDER?
Lankesteriana International Journal on Orchidology ISSN: 1409-3871 [email protected] Universidad de Costa Rica Costa Rica BACKHOUSE, GARY N. ARE OUR ORCHIDS SAFE DOWN UNDER? A NATIONAL ASSESSMENT OF THREATENED ORCHIDS IN AUSTRALIA Lankesteriana International Journal on Orchidology, vol. 7, núm. 1-2, marzo, 2007, pp. 28- 43 Universidad de Costa Rica Cartago, Costa Rica Available in: http://www.redalyc.org/articulo.oa?id=44339813005 How to cite Complete issue Scientific Information System More information about this article Network of Scientific Journals from Latin America, the Caribbean, Spain and Portugal Journal's homepage in redalyc.org Non-profit academic project, developed under the open access initiative LANKESTERIANA 7(1-2): 28-43. 2007. ARE OUR ORCHIDS SAFE DOWN UNDER? A NATIONAL ASSESSMENT OF THREATENED ORCHIDS IN AUSTRALIA GARY N. BACKHOUSE Biodiversity and Ecosystem Services Division, Department of Sustainability and Environment 8 Nicholson Street, East Melbourne, Victoria 3002 Australia [email protected] KEY WORDS:threatened orchids Australia conservation status Introduction Many orchid species are included in this list. This paper examines the listing process for threatened Australia has about 1700 species of orchids, com- orchids in Australia, compares regional and national prising about 1300 named species in about 190 gen- lists of threatened orchids, and provides recommen- era, plus at least 400 undescribed species (Jones dations for improving the process of listing regionally 2006, pers. comm.). About 1400 species (82%) are and nationally threatened orchids. geophytes, almost all deciduous, seasonal species, while 300 species (18%) are evergreen epiphytes Methods and/or lithophytes. At least 95% of this orchid flora is endemic to Australia. -
ACT, Australian Capital Territory
Biodiversity Summary for NRM Regions Species List What is the summary for and where does it come from? This list has been produced by the Department of Sustainability, Environment, Water, Population and Communities (SEWPC) for the Natural Resource Management Spatial Information System. The list was produced using the AustralianAustralian Natural Natural Heritage Heritage Assessment Assessment Tool Tool (ANHAT), which analyses data from a range of plant and animal surveys and collections from across Australia to automatically generate a report for each NRM region. Data sources (Appendix 2) include national and state herbaria, museums, state governments, CSIRO, Birds Australia and a range of surveys conducted by or for DEWHA. For each family of plant and animal covered by ANHAT (Appendix 1), this document gives the number of species in the country and how many of them are found in the region. It also identifies species listed as Vulnerable, Critically Endangered, Endangered or Conservation Dependent under the EPBC Act. A biodiversity summary for this region is also available. For more information please see: www.environment.gov.au/heritage/anhat/index.html Limitations • ANHAT currently contains information on the distribution of over 30,000 Australian taxa. This includes all mammals, birds, reptiles, frogs and fish, 137 families of vascular plants (over 15,000 species) and a range of invertebrate groups. Groups notnot yet yet covered covered in inANHAT ANHAT are notnot included included in in the the list. list. • The data used come from authoritative sources, but they are not perfect. All species names have been confirmed as valid species names, but it is not possible to confirm all species locations. -
Chromosome Numbers in Lomandra (Dasypogonaceae)
Telopea 2(6): 741-744 (1986) 741 CHROMOSOME NUMBERS IN LOMANDRA (DASYPOGONACEAE) BARBARA G. BRIGGS (Accepted for publication 22.3 .1985) ABSTRACT Briggs, Barbara G. (National Herbarium of New South Wales, Royal Botanic Gardens, Sydney, Australia 2000) 1986. Chromosome numbers in Lomandra (Dasypogonaceae). Telopea 2(6): 741-744 - Chromosome numbers for Sections Lomandra (13 species studied) and Typhopsis (one species) are based on x = 8, but three species of Sect. Cephalogyne have x = 7. Eight species are reported as diploid and five as tetraploid, while four show infraspecific polyploidy. The chromosome numbers of 17 species have been determined (Table 1). Several of these counts were previously reported (in Lee 1966) but without citation of voucher specimens. Preparations were of root-tips or pre-meiotic floral buds, pre-treated with saturated aqueous p-dichlorobenzene for about 2 Y4 hours, fixed in 1:3 acetic-alcohol and stained with aceta-orcein or alcoholic carmine. The sex of many vouchers could not be determined, since they were collected out of the flowering season. One of the counts of L. preissii (Waterhouse NSW 75454), a diploid, was cultivated for nine months in Sydney and there produced female and herma phrodite flowers and set fruit in isolation from other flowering plants of Lomandra. This genus is normally dioecious but hermaphrodite flowers occur sporadically in other species (A. T. Lee pers. comm.). Two base numbers are represented: x = 8 in the 13 counted species of Sect. Lomandra and x = 7 in three species of Sect. Cephalogyne, following the classi fication of Stevens (1978). A count of 2n = 16 has been obtained on L. -
Xanthorrhoea Preissii Woodlands and Shrublands (Swan Coastal Plain Community Type 3C - Gibson Et Al
INTERIM RECOVERY PLAN NO. 60 Corymbia calophylla - Xanthorrhoea preissii woodlands and shrublands (Swan Coastal Plain Community type 3c - Gibson et al. 1994) INTERIM RECOVERY PLAN 2000-2003 by Val English and John Blyth January 2000 Department of Conservation and Land Management Western Australian Threatened Species and Communities Unit PO Box 51, Wanneroo, WA 6946 Department of Conservation and Land Management FOREWORD Interim Recovery Plans (IRPs) are developed within the framework laid down in Department of Conservation and Land Management (CALM) Policy Statements Nos 44 and 50 IRPs outline the recovery actions that are required to urgently address those threatening processes most affecting the ongoing survival of threatened taxa or ecological communities, and begin the recovery process. CALM is committed to ensuring that Critically Endangered ecological communities are conserved through the preparation and implementation of Recovery Plans or Interim Recovery Plans and by ensuring that conservation action commences as soon as possible and always within one year of endorsement of that rank by CALM's Director of Nature Conservation. This Interim Recovery Plan will operate from 31January 2000 but will remain in force until withdrawn or replaced. It is intended that, if the ecological community is still ranked Critically Endangered, this IRP will be replaced by a full Recovery Plan after three years. The provision of funds identified in this Interim Recovery Plan is dependent on budgetary and other constraints affecting CALM, as well as the need to address other priorities. Information in this IRP was accurate at January 2000. 2 SUMMARY Name: Corymbia calophylla - Xanthorrhoea preissii woodlands and shrublands Description: Plant community located on heavy soils of the eastern side of the Swan Coastal Plain between Bullsbrook, and Waterloo near Bunbury. -
WRA Species Report
Family: Xanthorrhoeaceae Taxon: Xanthorrhoea preissii Synonym: Xanthorrhoea reflexa D.A.Herb. Common Name: Balga Xanthorrhoea pecoris F.Muell. Grass Tree Questionaire : current 20090513 Assessor: Chuck Chimera Designation: L Status: Assessor Approved Data Entry Person: Chuck Chimera WRA Score -5 101 Is the species highly domesticated? y=-3, n=0 n 102 Has the species become naturalized where grown? y=1, n=-1 103 Does the species have weedy races? y=1, n=-1 201 Species suited to tropical or subtropical climate(s) - If island is primarily wet habitat, then (0-low; 1-intermediate; 2- Intermediate substitute "wet tropical" for "tropical or subtropical" high) (See Appendix 2) 202 Quality of climate match data (0-low; 1-intermediate; 2- High high) (See Appendix 2) 203 Broad climate suitability (environmental versatility) y=1, n=0 n 204 Native or naturalized in regions with tropical or subtropical climates y=1, n=0 n 205 Does the species have a history of repeated introductions outside its natural range? y=-2, ?=-1, n=0 y 301 Naturalized beyond native range y = 1*multiplier (see n Appendix 2), n= question 205 302 Garden/amenity/disturbance weed n=0, y = 1*multiplier (see Appendix 2) 303 Agricultural/forestry/horticultural weed n=0, y = 2*multiplier (see n Appendix 2) 304 Environmental weed n=0, y = 2*multiplier (see n Appendix 2) 305 Congeneric weed n=0, y = 1*multiplier (see n Appendix 2) 401 Produces spines, thorns or burrs y=1, n=0 n 402 Allelopathic y=1, n=0 n 403 Parasitic y=1, n=0 n 404 Unpalatable to grazing animals y=1, n=-1 n 405 Toxic -
Prasophyllum Murfetii
PLANT Prasophyllum murfetii AUS SA AMLR Endemism Life History Distribution and Population Very restricted distribution, known only from Fleurieu CE E E AMLR Perennial Peninsula.2 Occurs in two locations, Mount Compass and Parawa areas, which are separated by the broad Family ORCHIDACEAE Inman Valley that does not contain any suitable habitat.6 Surveys in 2008 only re-recorded one sub-population in Stipiturus CP, containing 15 - 20 plants (J. Quarmby pers. comm. 2009). Many of the formerly recorded sub- populations have not been re-recorded for the past two to three decades and may be extinct. Most formerly recorded populations were on private land that is now degraded (J. Quarmby pers. comm. 2009). Area of occupancy estimated at less than 1% of the swamp habitat that remains in good condition on Fleurieu Peninsula (Duffield and Hill 2002). Distribution is highly fragmented.6 Pre-1983 AMLR filtered records from Mount Compass and Parawa, with additional records around Mount Compass, and a single record near Finniss.4 There are also records from the shores of Lake Alexandrina.6 Habitat Photo: © Rosemary Taplin Found in a variety of swampy habitats, in low-lying areas around the margins of permanent swamps or Conservation Significance lakes (Bates and Weber 1990). Grows on brown to Endemic to the AMLR where the species’ relative black, wet, loam soils (Jones 2000).2,6 area of occupancy is classified as ‘Very Restricted’.4 Recorded with Leptospermum sp. growing on damp Future survival is precarious given its very restricted peaty soil.5 geographic distribution, fragmented sub-populations (mostly unprotected sites) and ongoing threats.6 Within the AMLR the preferred broad vegetation group is Wetland.4 Description Robust leek-orchid to 80 cm tall. -
The Genus Microtis R. Br. (Orchidaceae): a Taxonomic Revision with Notes on Biology
J. Adelaide Bot. Gard. 7(1): 45-89 (1984) THE GENUS MICROTIS R. BR. (ORCHIDACEAE): A TAXONOMIC REVISION WITH NOTES ON BIOLOGY R. Bates 38 Portmamock Street, Fairview Park, South Australia 5126 Abstract A taxonomic revision of Micro lis is presented in which nine species are recognised; M. globula is described as new. M. brownii, M. magnadenia and M. truncata are placed in synonymy with M. rara. M. media is treatéd as a synonym of M. unifolia. The biology, taxonomic affinities and distribution are considered for each species, a key is provided and a detailed description of each species is supplemented with illustrations. Introduction Since Robert Brown (1810) described Microtis there have been numerous taxa added but no complete revision has appeared, nor has any flora dealt with all species. Bentham (1873, p. 269) when discussing the difficulty of determining many Australian orchids, including Microtis, from dried material wrote, "It is to be hoped that the revision of these ... vvill be taken on byresident botanists who have the opportunity of studying them in the fresh state". With this in mind the present author has observed, photographed and collected all species of Microtis in the process of completing this revision. Plants were obtained from as many locations as possible and cultivated in Adelaide and populations of all Australian species studied in the field. Endophytic soil fungi on Microtis were isolated and identified by Dr J. Warcup (Waite Agricultural Research Institute). Chromosome counts were attempted but results were inconclusive. Loans were obtained from numerous herbaria (see acknowledgements). Types of all taxa were examined unless otherwise indicated in the text.