Towards Understanding the Fossil Record Better: Insights from Recently Deposited Plant Macrofossils in a Sclerophyll-Dominated Subalpine Environment

Total Page:16

File Type:pdf, Size:1020Kb

Towards Understanding the Fossil Record Better: Insights from Recently Deposited Plant Macrofossils in a Sclerophyll-Dominated Subalpine Environment Review of Palaeobotany and Palynology 233 (2016) 1–11 Contents lists available at ScienceDirect Review of Palaeobotany and Palynology journal homepage: www.elsevier.com/locate/revpalbo Towards understanding the fossil record better: Insights from recently deposited plant macrofossils in a sclerophyll-dominated subalpine environment Giselle A. Astorga ⁎, Gregory J. Jordan, Timothy Brodribb School of Biological Sciences, University of Tasmania, Private bag 55, Hobart, Tasmania 7001, Australia article info abstract Article history: Accumulations of plant macrofossils in lake sediments and other sedimentary deposits are increasingly being Received 27 January 2014 used to refine our understanding of past vegetation history, ecological processes and related climate conditions. Received in revised form 20 June 2016 However, past vegetation studies based on the use of disarticulated plant structures need to consider the specific Accepted 23 June 2016 potential for fossilisation of different species and different plant organs. Such knowledge is available for many Available online 28 June 2016 systems, but the taphonomy of sclerophyll floras is very poorly known. Keywords: To provide understanding of the taphonomic processes affecting the representation of sclerophyllous plant Plant taphonomy species in fossil assemblages this study investigated the potential source vegetation of plant remains extracted Surface sediments from modern sediments of a subalpine lake in Tasmania, southernmost Australia. It was found that the vast Plant macrofossils majority of the leaf types represented in the sediments belong to broadleaf sclerophyllous species living in Plant megafossils close proximity to the lake, although the representation of species was not related to their values of leaf mass Megaflora per unit area. Leaf assemblages Additionally, a bias between the abundance of species in the standing vegetation and the number of leaves of the Sclerophyll vegetation same species in sediments was observed. Thus, small-leaved shrub species, such as many members of Ericaceae, Representation produce comparatively many more leaves and tend to be over-represented in sediments. In contrast, even though, large-leaved tree species such as Eucalyptus and Nothofagus are dominant in the standing vegetation, they produce substantially fewer foliar organs per ground area of vegetation. Accounting for these discrepancies, we developed an intrinsic representativity index that provides a more accurate picture of the relationship between the leaf assemblages incorporated in the sediments and the abundance of these species in the source vegetation. © 2016 Elsevier B.V. All rights reserved. 1. Introduction implications for the interpretation of plant macrofossil records. However, there have been very few such studies. Evergreen sclerophyll floras are widely distributed around the Accumulations of plant macrofossils (also known as megafossils) in world, especially in Mediterranean-type climates, where they represent different depositional environments, such as lakes or streambeds are the most diverse floras outside the tropics (Cowling et al., 1996). used to refine our understanding of past vegetation history, ecological However, plant macrofossil evidence indicates that diverse sclerophyll processes and related climate conditions (e.g. Allen and Huntley, floras existed under wet non-Mediterranean climates in the Cenozoic, 1999; Birks, 2001; Huntley, 2001; Collinson et al., 2010; Gee, 2005). and even as recently as the early Pleistocene, leading to questions about However, plant macrofossil assemblages can only be validly interpreted the link between sclerophylly and dry climates (e.g. Axelrod, 1975; in the light of the potential biases resulting from the differential preser- Chen et al., 2014; Hill, 2004; Palamarev, 1989; Schnitzler et al., vation of different organs and species. The analysis of plant macrofossils 2011; Sniderman et al., 2013). Plant taphonomic studies investigating from surface sediment samples, the recently deposited sediments in the potential for fossilisation of different plant organs and species in depositional environments such as lakes, can enhance the understand- sclerophyll-dominated environments may, therefore, have important ing of processes that determine the differential potential for fossilisation (Dieffenbacher-Krall and Halteman, 2000; Dieffenbacher-Krall, 2007; Spicer and Wolfe, 1987). ⁎ Corresponding author at: School of Biological Sciences (Life Science Building), The potential for fossilisation in plants may vary depending on both University of Tasmania, Private Bag 55, Hobart, TAS 7001, Australia. E-mail addresses: [email protected] (G.A. Astorga), intrinsic and extrinsic factors (Martin, 1999; Spicer, 1991). In particular, [email protected] (G.J. Jordan), [email protected] (T. Brodribb). intrinsic factors or individual characteristics of plant organs (e.g. the http://dx.doi.org/10.1016/j.revpalbo.2016.06.004 0034-6667/© 2016 Elsevier B.V. All rights reserved. 2 G.A. Astorga et al. / Review of Palaeobotany and Palynology 233 (2016) 1–11 degree of sclerophylly, number, weight, size and chemical composition macroremains collected by Hill and Gibson (1986), and information of leaves and reproductive structures) can be major determinants of the of present day vegetation within the catchment of the lake. Although likelihood of a species becoming fossilised. This is mainly because these Hill and Gibson (1986) made extensive macrofossil collections, they factors can affect the capacity of plant organs to be transported and made no analyses of reproductive structures or detailed consideration preserved in sediments (Ferguson, 1985, 2005; Gastaldo and Demko, of the potential source vegetation. Thus, this study aims to elucidate 2011; Spicer, 1989, 1991). Additionally, the potential for fossilisation is the modern representation of plant macrofossils within the sediments also affected by extrinsic factors (i.e. the natural characteristics of an of Lake Dobson, the identification of key taphonomic factors likely area). For instance, topographic features of the depositional environ- affecting the final representation of plant species within sediments, ment, the geographic distance of plant communities to the site of and to resolve whether the observed patterns are similar to those deposition, and the presence and ability of wind and/or flowing water found in other systems and geographic areas. to transport plant material (Ferguson, 2005; Gastaldo and Demko, 2011; Greenwood, 1992; Spicer, 1989; Spicer and Wolfe, 1987). Thus, 2. Materials and methods complex interactions of intrinsic and extrinsic factors may determine the final representation of plant parts within sediments resulting in fossil 2.1. Study site assemblages that rarely reflect their source vegetation in simple one to one relationships of abundance (Allen and Huntley, 1999; Birks, 2001, Lake Dobson (42°41′ S, 146° 35′ E) is located in the sub-alpine area 2013; Birks and Birks, 1980; Spicer, 1991; Spicer and Wolfe, 1987). of Mt. Field National Park, south-central Tasmania, Australia at an Plant taphonomic studies can usually provide insights into the altitude of 1034 m. The lake covers c. 5.7 ha, and occupies a glacial cirque relationship between the abundance of organs from a specific taxon bounded on the eastern side by a lateral moraine and on the west part present in the sediments, and the frequency of the same taxon in the by a headwall 250 m high rising at a slope of ~30° (Fig. 1). The lake is source vegetation (Birks, 2013; Birks and Birks, 1980; Spicer and Wolfe, irrigated mainly by two incoming streams: The Golden Stairs Creek 1987). However, in these studies the representativity (i.e. the proportion flowing from the Mawson Plateau down to the east, and Eagle Tarn of organs of a species in terms of the total number of organs preserved in Creek connecting Lake Dobson with Eagle Tarn to the north (Fig. 1). sediments) of any given species may vary markedly depending on the Prevailing winds in Lake Dobson area blow predominantly from west system in which it is measured. Partly because the representativity of a to east (Hill and Gibson, 1986). species is measured relative to the abundance of other represented Most of Tasmania has a temperate climate with mild summers or species, and is therefore non-independent of these other species. Thus, a cool summer in higher plateau areas (Stern et al., 2000). The park is more powerful approach is to use taphonomic studies to develop an located in a transitional area between a perhumid region of wet vegeta- understanding of the potential for fossilisation of different plant organs tion types, including extensive wet sedgeland/heaths and cool temperate and species in depositional settings. closed forests, extending to the west, and a subhumid region of Eucalyptus Taphonomic studies to date, including terrestrial and aquatic open forests and grasslands extending to the east (Harris and Kitchener, systems, especially in Europe (Allen and Huntley, 1999; Birks and 2005; Macphail, 1979; Read, 1999). Annual mean temperature at Lake Birks, 1980; Collinson, 1983; Greatrex, 1983; Spicer, 1981) and North Dobson is 6.2 °C with mean temperature of the warmest and coldest America (Demko et al., 1998; Dieffenbacher-Krall and Halteman, quarter 10.3 °C and 2.3 °C, and annual mean precipitation of 1454 mm. 2000; Dunwiddie, 1987; Spicer and Wolfe, 1987) have identified some Snowfalls are common between July and September. Climatic parameters general
Recommended publications
  • Wild Mersey Mountain Bike Development
    Wild Mersey Mountain Bike Development Natural Values Report Warrawee Conservation Area through to Railton Prepared for : Kentish Council and Latrobe Council Report prepared by: Matt Rose Natural State PO Box 139, Ulverstone, TAS, 7315 www.naturalstate.com.au 1 | NATURAL STATE – PO Box 139, Ulverstone TAS 7315. Mobile: 0437 971 144 www.naturalstate.com.au Table of contents Executive Summary ......................................................................................................................................... 5 1 Introduction ................................................................................................................................................ 6 1.1 Background ........................................................................................................................................... 6 1.2 Description of the proposed development activities ...................................................................... 6 1.3 Description of the study areas ............................................................................................................ 8 1.4 The Warrawee Conservation Area ..................................................................................................... 8 1.5 Warrawee to Railton trail ..................................................................................................................... 8 2 Methodology ..............................................................................................................................................
    [Show full text]
  • Vegetation Benchmarks Rainforest and Related Scrub
    Vegetation Benchmarks Rainforest and related scrub Eucryphia lucida Vegetation Condition Benchmarks version 1 Rainforest and Related Scrub RPW Athrotaxis cupressoides open woodland: Sphagnum peatland facies Community Description: Athrotaxis cupressoides (5–8 m) forms small woodland patches or appears as copses and scattered small trees. On the Central Plateau (and other dolerite areas such as Mount Field), broad poorly– drained valleys and small glacial depressions may contain scattered A. cupressoides trees and copses over Sphagnum cristatum bogs. In the treeless gaps, Sphagnum cristatum is usually overgrown by a combination of any of Richea scoparia, R. gunnii, Baloskion australe, Epacris gunnii and Gleichenia alpina. This is one of three benchmarks available for assessing the condition of RPW. This is the appropriate benchmark to use in assessing the condition of the Sphagnum facies of the listed Athrotaxis cupressoides open woodland community (Schedule 3A, Nature Conservation Act 2002). Benchmarks: Length Component Cover % Height (m) DBH (cm) #/ha (m)/0.1 ha Canopy 10% - - - Large Trees - 6 20 5 Organic Litter 10% - Logs ≥ 10 - 2 Large Logs ≥ 10 Recruitment Continuous Understorey Life Forms LF code # Spp Cover % Immature tree IT 1 1 Medium shrub/small shrub S 3 30 Medium sedge/rush/sagg/lily MSR 2 10 Ground fern GF 1 1 Mosses and Lichens ML 1 70 Total 5 8 Last reviewed – 2 November 2016 Tasmanian Vegetation Monitoring and Mapping Program Department of Primary Industries, Parks, Water and Environment http://www.dpipwe.tas.gov.au/tasveg RPW Athrotaxis cupressoides open woodland: Sphagnum facies Species lists: Canopy Tree Species Common Name Notes Athrotaxis cupressoides pencil pine Present as a sparse canopy Typical Understorey Species * Common Name LF Code Epacris gunnii coral heath S Richea scoparia scoparia S Richea gunnii bog candleheath S Astelia alpina pineapple grass MSR Baloskion australe southern cordrush MSR Gleichenia alpina dwarf coralfern GF Sphagnum cristatum sphagnum ML *This list is provided as a guide only.
    [Show full text]
  • Edition 2 from Forest to Fjaeldmark the Vegetation Communities Highland Treeless Vegetation
    Edition 2 From Forest to Fjaeldmark The Vegetation Communities Highland treeless vegetation Richea scoparia Edition 2 From Forest to Fjaeldmark 1 Highland treeless vegetation Community (Code) Page Alpine coniferous heathland (HCH) 4 Cushion moorland (HCM) 6 Eastern alpine heathland (HHE) 8 Eastern alpine sedgeland (HSE) 10 Eastern alpine vegetation (undifferentiated) (HUE) 12 Western alpine heathland (HHW) 13 Western alpine sedgeland/herbland (HSW) 15 General description Rainforest and related scrub, Dry eucalypt forest and woodland, Scrub, heathland and coastal complexes. Highland treeless vegetation communities occur Likewise, some non-forest communities with wide within the alpine zone where the growth of trees is environmental amplitudes, such as wetlands, may be impeded by climatic factors. The altitude above found in alpine areas. which trees cannot survive varies between approximately 700 m in the south-west to over The boundaries between alpine vegetation communities are usually well defined, but 1 400 m in the north-east highlands; its exact location depends on a number of factors. In many communities may occur in a tight mosaic. In these parts of Tasmania the boundary is not well defined. situations, mapping community boundaries at Sometimes tree lines are inverted due to exposure 1:25 000 may not be feasible. This is particularly the or frost hollows. problem in the eastern highlands; the class Eastern alpine vegetation (undifferentiated) (HUE) is used in There are seven specific highland heathland, those areas where remote sensing does not provide sedgeland and moorland mapping communities, sufficient resolution. including one undifferentiated class. Other highland treeless vegetation such as grasslands, herbfields, A minor revision in 2017 added information on the grassy sedgelands and wetlands are described in occurrence of peatland pool complexes, and other sections.
    [Show full text]
  • Jervis Bay Territory Page 1 of 50 21-Jan-11 Species List for NRM Region (Blank), Jervis Bay 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.
    [Show full text]
  • Pollination Ecology and Evolution of Epacrids
    Pollination Ecology and Evolution of Epacrids by Karen A. Johnson BSc (Hons) Submitted in fulfilment of the requirements for the Degree of Doctor of Philosophy University of Tasmania February 2012 ii Declaration of originality This thesis contains no material which has been accepted for the award of any other degree or diploma by the University or any other institution, except by way of background information and duly acknowledged in the thesis, and to the best of my knowledge and belief no material previously published or written by another person except where due acknowledgement is made in the text of the thesis, nor does the thesis contain any material that infringes copyright. Karen A. Johnson Statement of authority of access This thesis may be made available for copying. Copying of any part of this thesis is prohibited for two years from the date this statement was signed; after that time limited copying is permitted in accordance with the Copyright Act 1968. Karen A. Johnson iii iv Abstract Relationships between plants and their pollinators are thought to have played a major role in the morphological diversification of angiosperms. The epacrids (subfamily Styphelioideae) comprise more than 550 species of woody plants ranging from small prostrate shrubs to temperate rainforest emergents. Their range extends from SE Asia through Oceania to Tierra del Fuego with their highest diversity in Australia. The overall aim of the thesis is to determine the relationships between epacrid floral features and potential pollinators, and assess the evolutionary status of any pollination syndromes. The main hypotheses were that flower characteristics relate to pollinators in predictable ways; and that there is convergent evolution in the development of pollination syndromes.
    [Show full text]
  • Introduction Methods Results
    Papers and Proceedings Royal Society ofTasmania, Volume 1999 103 THE CHARACTERISTICS AND MANAGEMENT PROBLEMS OF THE VEGETATION AND FLORA OF THE HUNTINGFIELD AREA, SOUTHERN TASMANIA by J.B. Kirkpatrick (with two tables, four text-figures and one appendix) KIRKPATRICK, J.B., 1999 (31:x): The characteristics and management problems of the vegetation and flora of the Huntingfield area, southern Tasmania. Pap. Proc. R. Soc. Tasm. 133(1): 103-113. ISSN 0080-4703. School of Geography and Environmental Studies, University ofTasmania, GPO Box 252-78, Hobart, Tasmania, Australia 7001. The Huntingfield area has a varied vegetation, including substantial areas ofEucalyptus amygdalina heathy woodland, heath, buttongrass moorland and E. amygdalina shrubbyforest, with smaller areas ofwetland, grassland and E. ovata shrubbyforest. Six floristic communities are described for the area. Two hundred and one native vascular plant taxa, 26 moss species and ten liverworts are known from the area, which is particularly rich in orchids, two ofwhich are rare in Tasmania. Four other plant species are known to be rare and/or unreserved inTasmania. Sixty-four exotic plantspecies have been observed in the area, most ofwhich do not threaten the native biodiversity. However, a group offire-adapted shrubs are potentially serious invaders. Management problems in the area include the maintenance ofopen areas, weed invasion, pathogen invasion, introduced animals, fire, mechanised recreation, drainage from houses and roads, rubbish dumping and the gathering offirewood, sand and plants. Key Words: flora, forest, heath, Huntingfield, management, Tasmania, vegetation, wetland, woodland. INTRODUCTION species with the most cover in the shrub stratum (dominant species) was noted. If another species had more than half The Huntingfield Estate, approximately 400 ha of forest, the cover ofthe dominant one it was noted as a codominant.
    [Show full text]
  • Kosipe Revisited
    Peat in the mountains of New Guinea G.S. Hope Department of Archaeology and Natural History, Australian National University, Canberra, Australia _______________________________________________________________________________________ SUMMARY Peatlands are common in montane areas above 1,000 m in New Guinea and become extensive above 3,000 m in the subalpine zone. In the montane mires, swamp forests and grass or sedge fens predominate on swampy valley bottoms. These mires may be 4–8 m in depth and up to 30,000 years in age. In Papua New Guinea (PNG) there is about 2,250 km2 of montane peatland, and Papua Province (the Indonesian western half of the island) probably contains much more. Above 3,000 m, peat soils form under blanket bog on slopes as well as on valley floors. Vegetation types include cushion bog, grass bog and sedge fen. Typical peat depths are 0.5‒1 m on slopes, but valley floors and hollows contain up to 10 m of peat. The estimated total extent of mountain peatland is 14,800 km2 with 5,965 km2 in PNG and about 8,800 km2 in Papua Province. The stratigraphy, age structure and vegetation histories of 45 peatland or organic limnic sites above 750 m have been investigated since 1965. These record major vegetation shifts at 28,000, 17,000‒14,000 and 9,000 years ago and a variable history of human disturbance from 14,000 years ago with extensive clearance by the mid- Holocene at some sites. While montane peatlands were important agricultural centres in the Holocene, the introduction of new dryland crops has resulted in the abandonment of some peatlands in the last few centuries.
    [Show full text]
  • Ficha Catalográfica Online
    UNIVERSIDADE ESTADUAL DE CAMPINAS INSTITUTO DE BIOLOGIA – IB SUZANA MARIA DOS SANTOS COSTA SYSTEMATIC STUDIES IN CRYPTANGIEAE (CYPERACEAE) ESTUDOS FILOGENÉTICOS E SISTEMÁTICOS EM CRYPTANGIEAE CAMPINAS, SÃO PAULO 2018 SUZANA MARIA DOS SANTOS COSTA SYSTEMATIC STUDIES IN CRYPTANGIEAE (CYPERACEAE) ESTUDOS FILOGENÉTICOS E SISTEMÁTICOS EM CRYPTANGIEAE Thesis presented to the Institute of Biology of the University of Campinas in partial fulfillment of the requirements for the degree of PhD in Plant Biology Tese apresentada ao Instituto de Biologia da Universidade Estadual de Campinas como parte dos requisitos exigidos para a obtenção do Título de Doutora em Biologia Vegetal ESTE ARQUIVO DIGITAL CORRESPONDE À VERSÃO FINAL DA TESE DEFENDIDA PELA ALUNA Suzana Maria dos Santos Costa E ORIENTADA PELA Profa. Maria do Carmo Estanislau do Amaral (UNICAMP) E CO- ORIENTADA pelo Prof. William Wayt Thomas (NYBG). Orientadora: Maria do Carmo Estanislau do Amaral Co-Orientador: William Wayt Thomas CAMPINAS, SÃO PAULO 2018 Agência(s) de fomento e nº(s) de processo(s): CNPq, 142322/2015-6; CAPES Ficha catalográfica Universidade Estadual de Campinas Biblioteca do Instituto de Biologia Mara Janaina de Oliveira - CRB 8/6972 Costa, Suzana Maria dos Santos, 1987- C823s CosSystematic studies in Cryptangieae (Cyperaceae) / Suzana Maria dos Santos Costa. – Campinas, SP : [s.n.], 2018. CosOrientador: Maria do Carmo Estanislau do Amaral. CosCoorientador: William Wayt Thomas. CosTese (doutorado) – Universidade Estadual de Campinas, Instituto de Biologia. Cos1. Savanas. 2. Campinarana. 3. Campos rupestres. 4. Filogenia - Aspectos moleculares. 5. Cyperaceae. I. Amaral, Maria do Carmo Estanislau do, 1958-. II. Thomas, William Wayt, 1951-. III. Universidade Estadual de Campinas. Instituto de Biologia. IV. Título.
    [Show full text]
  • TASMANIAN HIGH MOUNTAIN VEGETATION II - ROCKY HILL and PYRAMID MOUNTAIN by J.B
    Papers and Proceedings of the Royal Society of Tasmania, Volume 118, 1984 (ms. received 10.VI.1983) TASMANIAN HIGH MOUNTAIN VEGETATION II - ROCKY HILL AND PYRAMID MOUNTAIN by J.B. Kirkpatrick Department of Geography, University of Tasmania (with two tables, three text-figures and four plates) ABSTRACT KIRKPATRICK, J.B., 1984 (31 viii): Tasmanian high mountain vegetation II - Rocky Hill and Pyramid Mountain. Pap. Proc. R. Soc. Tasm., ll8: 5-20, pls 1-4. https://doi.org/10.26749/rstpp.118.5 ISSN 0080-4703. Department of Geography, University of Tasmania, Hobart, Tasmania, Australia. Rocky Hill and Pyramid Mountain are composed of horizontally bedded Permian to Upper Carboniferous sedimentary rocks, the nature of which has encouraged the development of fjaeldmark and nonsorted stone steps and stripes. Buried A throtax1:s logs in the present alpine zone, the patterns of distribution of fire-susceptible species and other evidence suggest that the area has been subject to at least two severe and extensive fires, which have resulted in landscape instability. Nevertheless, the present vegetation of the area is varied, lacking only deciduous heath and tussock grassland of the alpine subformations and having a full range from sedgeland to closed-forest in the subalpine vegetation. The species composition of the vegetation of the two mountains is most similar to that of Cradle Mountain. INTRODUCTION The Tasmanian high mountains possess varied floras and vegetation complexes, these variations most strongly relating to precipitation and soil characteristics (Kirkpatrick 1980, 1982, 1983). Most of the mountains with alpine vegetation (sensu Kirkpatrick 1982) consist of dolerite or highly siliceous quartzites and quartzitic conglomerates.
    [Show full text]
  • Eucalyptus That Are Ideal for British Gardens
    Barks, shoots and leaves Grafton Nursery grows hardy forms of Antipodean Eucalyptus that are ideal for British gardens WORDS JOHN HOYLAND PHOTOGRAPHS JASON INGRAM Gower Hilary Collins checks the growth on a selection of the hardy eucalyptus grown at Grafton Nursery. Nearby assistant grower Adam Barnes keeps the more mature trees in check with some careful pruning. 68 FOR CUTTING 1 Eucalyptus ‘Shannon Blue’ VERY FEW TREES ARE AS FASCINATING A hybrid bred for the floristry trade, this vigorous plant has stems of rounded, glaucous, silver AS EUCALYPTS: THEY ARE HIGHLY leaves. It can be grown as a hedge and retains EVOLVED AND EXTREMELY VARIED its colour through the winter. Unpruned height 10m. RHS H5†. 2 Eucalyptus nicholii An airy tree with narrow, almost feathery, sage- green leaves. Its common name – narrow-leaved black peppermint – references its strongly aromatic foliage. Unpruned height 12m. RHS H5. 3 Eucalyptus pulverulenta ‘Baby Blue’ ardeners can be blinkered, disregarding a whole A compact, bushy cultivar that can be grown in a pot. The silvery-grey stems are long-lasting genus because of the faults of a few members. when cut for flower arrangements. Unpruned Eucalyptus has suffered this fate, largely because of height 5m. RHS H5. the thuggish behaviour of Eucalyptus gunnii, the most widely available species, which will grow to huge 4 Eucalyptus gunnii proportions in a very short time. “There are far better The most widely grown species in the UK. It has peeling cream and brown bark, rounded, species,” says grower Hilary Collins. “Beautiful glaucous-blue juvenile leaves and elliptic or eucalypts for small terraces or large pots, those for sickle-shaped, grey-green adult leaves.
    [Show full text]
  • World Heritage Values and to Identify New Values
    FLORISTIC VALUES OF THE TASMANIAN WILDERNESS WORLD HERITAGE AREA J. Balmer, J. Whinam, J. Kelman, J.B. Kirkpatrick & E. Lazarus Nature Conservation Branch Report October 2004 This report was prepared under the direction of the Department of Primary Industries, Water and Environment (World Heritage Area Vegetation Program). Commonwealth Government funds were contributed to the project through the World Heritage Area program. The views and opinions expressed in this report are those of the authors and do not necessarily reflect those of the Department of Primary Industries, Water and Environment or those of the Department of the Environment and Heritage. ISSN 1441–0680 Copyright 2003 Crown in right of State of Tasmania Apart from fair dealing for the purposes of private study, research, criticism or review, as permitted under the Copyright Act, no part may be reproduced by any means without permission from the Department of Primary Industries, Water and Environment. Published by Nature Conservation Branch Department of Primary Industries, Water and Environment GPO Box 44 Hobart Tasmania, 7001 Front Cover Photograph: Alpine bolster heath (1050 metres) at Mt Anne. Stunted Nothofagus cunninghamii is shrouded in mist with Richea pandanifolia scattered throughout and Astelia alpina in the foreground. Photograph taken by Grant Dixon Back Cover Photograph: Nothofagus gunnii leaf with fossil imprint in deposits dating from 35-40 million years ago: Photograph taken by Greg Jordan Cite as: Balmer J., Whinam J., Kelman J., Kirkpatrick J.B. & Lazarus E. (2004) A review of the floristic values of the Tasmanian Wilderness World Heritage Area. Nature Conservation Report 2004/3. Department of Primary Industries Water and Environment, Tasmania, Australia T ABLE OF C ONTENTS ACKNOWLEDGMENTS .................................................................................................................................................................................1 1.
    [Show full text]
  • Plant Communities of Mt Barrow & Mt Barrow Falls
    PLANT COMMUNITIES OF MT BARROW & MT BARROW FALLS John B. Davies Margaret J. Davies Consultant Queen Victoria and Art and Plomley Foundation II Mt Barrow J.B. & M.J. (1990) of Mt Barrow and Mt Barrow No.2 © Queen Victoria and Art Wellington St., Launceston,Tasmania 1990 CONTENTS ACKNOWLEDGEMENTS 3 BACKGROUND 4 SURVEY MT BARROW 11 OF MT BARROW PLANT COMMUNITIES 14 AND THEIR RESERVATION COMPARISON THE VEGETATION AT 30 BARROW AND LOMOND BOTANICAL OF MT BARROW RESERVE 31 DESCRIPTION THE COMMUNITIES BARROW FALLS THEIR APPENDIX 1 36 APPENDIX 2­ MAP 3 39 APPENDIX 4 APPENDIX 5 APPENDIX 6­ SPECIES 49 ACKNOWLEDGEMENTS Thanks are due to a number of people for assistance with this project. Firstly administrative assistance was by the Director of the Victoria Museum and Art Gallery, Mr Chris TasselL assistance was Michael Body, Kath Craig Reid and Mary Cameron. crt>''Y'it>,nt" are also due to Telecom for providing a key to the on the plateau, the Department of Lands, Parks and for providing a transparency base map of the area, and to Mr Mike Brouder and Mr John Harris Commission), for the use of 1 :20,000 colour aerial photographs of the area. Taxonomic was provided by Cameron (Honorary Research Associate, Queen Victoria Museum and Art Gallery) who also mounted all the plant collected, and various staff of the Tasmanian Herbarium particularly Mr Alex Dr Tony Orchard, Mr D. 1. Morris and Dr Winifred Curtis. thanks are due to Dr Brad Potts (Botany Department, of Tasmania) for assistance with data and table production and to Prof Kirkpatrick and Environmental ..J'U'U'~;'" of Tasmania) for the use and word-processing.
    [Show full text]