Scrub, Heathland and Coastal Complexes

Total Page:16

File Type:pdf, Size:1020Kb

Scrub, Heathland and Coastal Complexes Edition 2 From Forest to Fjaeldmark The Vegetation Communities Scrub, heathland and coastal complexes Correa alba Edition 2 From Forest to Fjaeldmark 1 Scrub, heathland and coastal complexes Community (Code) Page Acacia longifolia coastal scrub (SAL) 12 Banksia marginata wet scrub (SBM) 14 Broad-leaf scrub (SBR) 16 Coastal heathland (SCH) 18 Coastal scrub (SSC) 21 Coastal scrub on alkaline sands (SCA) 23 Eastern riparian scrub (SRE) 25 Eastern scrub on dolerite (SED) 28 Heathland on calcareous substrates (SCL) 30 Kunzea ambigua regrowth scrub (SKA) 32 Leptospermum glaucescens heathland and scrub (SLG) 34 Leptospermum lanigerum scrub (SLL) 37 Leptospermum scoparium heathland and scrub (SLS) 39 Leptospermum with rainforest scrub (SRF) 41 Melaleuca pustulata scrub (SMP) 43 Melaleuca squamea heathland (SMM) 45 Melaleuca squarrosa scrub (SMR) 47 Rookery halophytic herbland (SRH) 49 Scrub complex on King Island (SSK) 51 Spray zone coastal complex (SSZ) 53 Subalpine heathland (SHS) 55 Western regrowth complex (SWR) 57 Western subalpine scrub (SSW) 59 Western wet scrub (SWW) 61 Wet heathland (SHW) 63 Edition 2 From Forest to Fjaeldmark 1 General description The communities in this section are structurally and floristically variable and are divided into mapping Scrubs, heathlands and the diverse complexes that units on the basis of the nature or identity of the they may form are, with a few notable exceptions, dominant or most common species, and to a lesser dominated by scleromorphic species. The canopy extent on structure and habitat. structure of the woody plants in these communities varies from 30 to 100% solid crown cover and is usually 5 m or less in height. While this height is the Ecological theory arbitrary divide between forest (including woodland) Scrub and heathland communities may represent and scrub (Specht 1970), taller vegetation is included either biotic climax or a particular stage in vegetation in these mapping units when it maintains a dense development within a sere, depending on where scrubby structure and/or a floristic composition they occur. Climax vegetation is capable of indistinguishable from communities typically 5 m or remaining floristically and structurally stable for long less in height. periods in the absence of disturbance. Vegetation representing stages in a sere change floristically and Scrub and heathland communities typically have only structurally over time in the absence of disturbance. two strata; a dominant layer of shrubs comprising Where vegetation changes rapidly in its structural one to many species; and a ground layer of herbs, and/or floristic form, it will present a challenge for orchids, prostrate shrubs, ferns and occasionally mapping due to its temporal instability. grasses and/or sedges. Some heath and scrub vegetation also includes emergent trees, but where Trees are excluded from areas of biotic climax present, these never form more than 5% solid vegetation by the presence of climatic, hydrologic, or crown cover. soil factors that prevent tree growth or survival. Examples of habitats where heathland and scrub The ground layer is often sparse in vegetation cover may form stable biotic climax communities include and species richness, although it may be diverse mature vegetation in coastal habitats subject to salt- and/or dense in the more open-canopy spray and wind-pruning, where shrub species are communities. If shrubs form less than a 30% solid rarely able to reach heights in excess of 5 m. crown cover over a ground layer dominated by grasses, sedges or rushes, then the vegetation is not Large areas of heathland and scrub occur in areas considered part of Scrub, heathland and coastal where natural successional processes which would complexes. normally lead to the development of forest have been deflected by disturbance. Fire frequency is the Areas mapped in TASVEG by units described in most common driver of vegetation succession in Scrub, heathland and coastal complexes occur from Tasmania. Fire in combination with other factors sea level to about 1200 m and on a range of rock such as infertile substrates, frequent water-logging or types in all climates. desiccation, and/or frost leads to the development Not all heath and scrub vegetation is mapped in of scrub and heathland by excluding trees. Areas units described in this section. Heathland and scrub with frequent fire are most commonly occupied by in alpine areas are dealt with in the section Highland sedgeland or grassland while forests occur where treeless vegetation. Scrub forming vegetation with a fires are relatively infrequent (Jackson 1968, Brown prominent component of rainforest species (sensu and Podger 1982, Ellis 1985). Scrub is common in Jarman et al. 1984) is classified in the section areas with an intermediate fire frequency. Rainforest and related scrub. Also excluded from Vegetation characteristics, climate, topographic this section are floristic communities which in factors and human behaviour all affect the restricted situations have a mature height of less disturbance regimes. Different combinations of than 5 m but elsewhere commonly develop into disturbance regimes, climate and edaphic situations forest. For example, Melaleuca ericifolia dominated result in the development of different vegetation vegetation is always mapped as Melaleuca ericifolia communities. Thus there are complex feedbacks swamp forest (NME) within the Non-eucalypt forest between vegetation, micro-climate, soil and and woodland section even when it forms a low disturbance regimes, which reinforce the presence of dense shrubbery in coastal areas. The Intersectional particular vegetation stages and prevent succession Key and keys to each section will redirect users to to climax vegetation communities. the appropriate section and mapping unit. Edition 2 From Forest to Fjaeldmark 2 The vegetation community resulting from a leaf scrub (SBR). The description for SBR was particular and persistent disturbance regime is broadened to include forest forms of the assemblage referred to as ‘meta-stable’, since it usually re- previously described by NNP. establishes quickly after disturbance and is disturbed Three of the five complexes described previously again before later-stage succession can take place. were discontinued and have been replaced by finer- scale mapping of areas previously covered by these Mapping scrub and heathlands units. The units Heathland scrub mosaic on Flinders In general, TASVEG mapping attempts to represent Island (SHF) and Heathland scrub complex at the vegetation as it appears from the most current Wingaroo (SCW) have been differentiated into their source imagery. However in some instances it is component communities which include Freshwater obvious that a recent disturbance has given rise to a aquatic sedgeland and rushland (ASF) and Wet pioneer community likely to persist for a short heathland (SHW). The unit Seabird rookery duration only. Where there is evidence that the complex (SRC) has also been differentiated into its pioneering vegetation will be replaced quickly by a major component communities by fine-scale meta-stable vegetation community, then it is the mapping. Where tussock grasses dominated rookery meta-stable vegetation type (usually the pre- vegetation, these are now mapped (where of disturbance community) that is mapped. This can be sufficient size) to the most appropriate grassland achieved using information from earlier imagery or unit, while the taller heathy vegetation is likely to deduced from undisturbed remnants. have become Coastal heathland (SCH). However a new unit has been erected to distinguish the Classification review herbaceous-halophytic shrubland component of A recent review of the mapping units in the Scrub, rookery vegetation. The new unit, Rookery heathland and coastal complexes section led to halophytic herbland (SRH), has only the superficial changes in the TASVEG classification at the end of resemblance to any of the other heathlands and 2012. The unit descriptions, the key for the section scrubs, but it is included here because of its and the Intersectional Key were all revised to proximity to coastal heathlands and scrub with describe more accurately the vegetation that is which it has at least some species in common. The included in each unit and how they are distinguished new unit will not be confined to mapping of seabird in the new classification. Several units were rookery areas but will be used to map any areas of discontinued. These units will continue to appear in vegetation with this floristic composition. TASVEG only until the mapping of these areas can Coastal complex on King Island (SCK) has been be revised and reallocated to other units. For revised and renamed Spray zone coastal complex descriptions to these discontinued units consult the (SSZ). The redefined unit excludes coastal scrub and first edition of Forest to Fjaeldmark (Harris and heathland although inevitably some will be Kitchener 2005). Several new units have been incorporated unintentionally due to the constraints erected and will map at least part of the extent of of mapping scale. SSZ still includes a complex of these communities for the first time in version 3.0 of vegetation formations, but will no longer be the TASVEG data set. More accurate and complete restricted to mapping King Island vegetation. SSZ has coverage of new units will be provided in later been broadened to map spray zone vegetation in versions of TASVEG as the mapping is revised. exposed coastal areas of Tasmanian and its off-shore As part of the change in classification two units were islands. Vegetation not matching the description for removed from other sections and placed into the this new unit on King Island will be placed in the best Scrub, heathlands and coastal complexes section. matching coastal unit available, most commonly One of these was Leptospermum with rainforest Coastal heathland (SCH). scrub (RLS) which was moved into this section from The other two complexes were retained—Scrub the Rainforest and related scrub section because complex on King Island (SSK) and the Queenstown rainforest species do not dominate the community. regrowth mosaic (SQR), although the latter has The new code is for this unit is SRF.
Recommended publications
  • Toward a Resolution of Campanulid Phylogeny, with Special Reference to the Placement of Dipsacales
    TAXON 57 (1) • February 2008: 53–65 Winkworth & al. • Campanulid phylogeny MOLECULAR PHYLOGENETICS Toward a resolution of Campanulid phylogeny, with special reference to the placement of Dipsacales Richard C. Winkworth1,2, Johannes Lundberg3 & Michael J. Donoghue4 1 Departamento de Botânica, Instituto de Biociências, Universidade de São Paulo, Caixa Postal 11461–CEP 05422-970, São Paulo, SP, Brazil. [email protected] (author for correspondence) 2 Current address: School of Biology, Chemistry, and Environmental Sciences, University of the South Pacific, Private Bag, Laucala Campus, Suva, Fiji 3 Department of Phanerogamic Botany, The Swedish Museum of Natural History, Box 50007, 104 05 Stockholm, Sweden 4 Department of Ecology & Evolutionary Biology and Peabody Museum of Natural History, Yale University, P.O. Box 208106, New Haven, Connecticut 06520-8106, U.S.A. Broad-scale phylogenetic analyses of the angiosperms and of the Asteridae have failed to confidently resolve relationships among the major lineages of the campanulid Asteridae (i.e., the euasterid II of APG II, 2003). To address this problem we assembled presently available sequences for a core set of 50 taxa, representing the diver- sity of the four largest lineages (Apiales, Aquifoliales, Asterales, Dipsacales) as well as the smaller “unplaced” groups (e.g., Bruniaceae, Paracryphiaceae, Columelliaceae). We constructed four data matrices for phylogenetic analysis: a chloroplast coding matrix (atpB, matK, ndhF, rbcL), a chloroplast non-coding matrix (rps16 intron, trnT-F region, trnV-atpE IGS), a combined chloroplast dataset (all seven chloroplast regions), and a combined genome matrix (seven chloroplast regions plus 18S and 26S rDNA). Bayesian analyses of these datasets using mixed substitution models produced often well-resolved and supported trees.
    [Show full text]
  • Border Rivers Maranoa - Balonne QLD Page 1 of 125 21-Jan-11 Species List for NRM Region Border Rivers Maranoa - Balonne, Queensland
    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]
  • Tasmanian Wilderness World Heritage Area
    Appendix 4 1 World Heritage Values of the Tasmanian Wilderness 1.1 Note that the Department of the Environment's website states that: A draft Statement of Outstanding Universal Value which will take into account the new areas added in 2013 is expected to be considered by the World Heritage Committee in 2014. Outstanding Universal Value 1.2 The Tasmanian Wilderness is an extensive, wild, beautiful temperate land where cultural heritage of the Tasmanian Aboriginal people is preserved. 1.3 It is one of the three largest temperate wilderness areas remaining in the Southern Hemisphere. The region is home to some of the deepest and longest caves in Australia. It is renowned for its diversity of flora, and some of the longest lived trees and tallest flowering plants in the world grow in the area. The Tasmanian Wilderness is a stronghold for several animals that are either extinct or threatened on mainland Australia. 1.4 In the southwest Aboriginal people developed a unique cultural tradition based on a specialized stone and bone toolkit that enabled the hunting and processing of a single prey species (Bennett's wallaby) that provided nearly all of their dietary protein and fat. Extensive limestone cave systems contain rock art sites that have been dated to the end of the Pleistocene period. Southwest Tasmanian Aboriginal artistic expression during the last Ice Age is only known from the dark recesses of limestone caves. 1.5 The Tasmanian Wilderness was inscribed on the World Heritage List in 1982 and extended in 1989, 2010, 2012 and again in 2013.
    [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]
  • 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]
  • The Smut Fungi (Ustilaginomycetes) of Restionaceae S. Lat
    MYCOLOGIA BALCANICA 3: 19–46 (2006) 19 Th e smut fungi (Ustilaginomycetes) of Restionaceae s. lat. Kálmán Vánky Herbarium Ustilaginales Vánky (H.U.V.), Gabriel-Biel-Str. 5, D-72076 Tübingen, Germany (e-mail: [email protected]) Received 2 October 2005 / Accepted 25 October 2005 Abstract. Smut fungi of Restionaceae s. lat. were studied. Th ey are classifi ed into two genera, Restiosporium and Websdanea. Problems of species delimitation in these smuts are discussed. In addition to the nine known smut fungi, thirteen new species are described and illustrated: Restiosporium anarthriae, R. apodasmiae, R. chaetanthi, R. desmocladii, R. eurychordae, R. fl exuosum, R. hypolaenae, R. lepyrodiae, R. pallentis, R. patei, R. proliferum, R. spathacei, and R. sphacelatum. Key words: new species, Restionaceae s. lat., Restiosporium, smut fungi, taxonomy, Websdanea Introduction and stained in 1 % aqueous uranyl acetate for 1 h in the dark. After fi ve washes in distilled water, the material was Th e monocotyledonous Restionaceae is a remarkable family dehydrated in acetone series, embedded in Spurr’s plastic, of Southern Hemisphere, evergreen, rush-like plants. Th ey and sectioned with a diamond knife. Semi-thin sections are concentrated mainly in SW Africa and in SW Australia. were stained with new fuchsin and crystal violet, mounted Th e c. 320 species of African Restionaceae, in 19 genera, were in ‘Entellan’ and studied in a light microscope. revised by Linder (1985, 1991). Th e 170 species of Australian Spore ball and spore morphology was studied using Restionaceae s. lat. were published by Meney & Pate (1999) a light microscope (LM) with an oil immersion lens at a in a beautifully illustrated monograph.
    [Show full text]
  • Low Risk Aquarium and Pond Plants
    Plant Identification Guide Low-risk aquarium and pond plants Planting these in your pond or aquarium is environmentally-friendly. Glossostigma elatinoides, image © Sonia Frimmel. One of the biggest threats to New Zealand’s waterbodies is the establishment and proliferation of weeds. The majority of New Zealand’s current aquatic weeds started out as aquarium and pond plants. To reduce the occurrence of new weeds becoming established in waterbodies this guide has been prepared to encourage the use of aquarium and pond plants that pose minimal risk to waterbodies. Guide prepared by Dr John Clayton, Paula Reeves, Paul Champion and Tracey Edwards, National Centre of Aquatic Biodiversity and Biosecurity, NIWA with funding from the Department of Conservation. The guides will be updated on a regular basis and will be available on the NIWA website: www.niwa.co.nz/ncabb/tools. Key to plant life-forms Sprawling marginal plants. Grow across the ground and out over water. Pond plants Short turf-like plants. Grow in shallow water on the edges of ponds and foreground of aquariums. Includes very small plants (up to 2-3 cm in height). Most species can grow both submerged (usually more erect) and emergent. Pond and aquarium plants Tall emergent plants. Can grow in water depths up to 2 m deep depending on the species. Usually tall reed-like plants but sometimes with broad leaves. Ideal for deeper ponds. Pond plants Free floating plants. These plants grow on the water surface and are not anchored to banks or bottom substrates. Pond and aquarium plants Floating-leaved plants. Water lily-type plants.
    [Show full text]
  • Plant Life of Western Australia
    INTRODUCTION The characteristic features of the vegetation of Australia I. General Physiography At present the animals and plants of Australia are isolated from the rest of the world, except by way of the Torres Straits to New Guinea and southeast Asia. Even here adverse climatic conditions restrict or make it impossible for migration. Over a long period this isolation has meant that even what was common to the floras of the southern Asiatic Archipelago and Australia has become restricted to small areas. This resulted in an ever increasing divergence. As a consequence, Australia is a true island continent, with its own peculiar flora and fauna. As in southern Africa, Australia is largely an extensive plateau, although at a lower elevation. As in Africa too, the plateau increases gradually in height towards the east, culminating in a high ridge from which the land then drops steeply to a narrow coastal plain crossed by short rivers. On the west coast the plateau is only 00-00 m in height but there is usually an abrupt descent to the narrow coastal region. The plateau drops towards the center, and the major rivers flow into this depression. Fed from the high eastern margin of the plateau, these rivers run through low rainfall areas to the sea. While the tropical northern region is characterized by a wet summer and dry win- ter, the actual amount of rain is determined by additional factors. On the mountainous east coast the rainfall is high, while it diminishes with surprising rapidity towards the interior. Thus in New South Wales, the yearly rainfall at the edge of the plateau and the adjacent coast often reaches over 100 cm.
    [Show full text]
  • Phytophthora Resistance and Susceptibility Stock List
    Currently known status of the following plants to Phytophthora species - pathogenic water moulds from the Agricultural Pathology & Kingdom Protista. Biological Farming Service C ompiled by Dr Mary Cole, Agpath P/L. Agricultural Consultants since 1980 S=susceptible; MS=moderately susceptible; T= tolerant; MT=moderately tolerant; ?=no information available. Phytophthora status Life Form Botanical Name Family Common Name Susceptible (S) Tolerant (T) Unknown (UnK) Shrub Acacia brownii Mimosaceae Heath Wattle MS Tree Acacia dealbata Mimosaceae Silver Wattle T Shrub Acacia genistifolia Mimosaceae Spreading Wattle MS Tree Acacia implexa Mimosaceae Lightwood MT Tree Acacia leprosa Mimosaceae Cinnamon Wattle ? Tree Acacia mearnsii Mimosaceae Black Wattle MS Tree Acacia melanoxylon Mimosaceae Blackwood MT Tree Acacia mucronata Mimosaceae Narrow Leaf Wattle S Tree Acacia myrtifolia Mimosaceae Myrtle Wattle S Shrub Acacia myrtifolia Mimosaceae Myrtle Wattle S Tree Acacia obliquinervia Mimosaceae Mountain Hickory Wattle ? Shrub Acacia oxycedrus Mimosaceae Spike Wattle S Shrub Acacia paradoxa Mimosaceae Hedge Wattle MT Tree Acacia pycnantha Mimosaceae Golden Wattle S Shrub Acacia sophorae Mimosaceae Coast Wattle S Shrub Acacia stricta Mimosaceae Hop Wattle ? Shrubs Acacia suaveolens Mimosaceae Sweet Wattle S Tree Acacia ulicifolia Mimosaceae Juniper Wattle S Shrub Acacia verniciflua Mimosaceae Varnish wattle S Shrub Acacia verticillata Mimosaceae Prickly Moses ? Groundcover Acaena novae-zelandiae Rosaceae Bidgee-Widgee T Tree Allocasuarina littoralis Casuarinaceae Black Sheoke S Tree Allocasuarina paludosa Casuarinaceae Swamp Sheoke S Tree Allocasuarina verticillata Casuarinaceae Drooping Sheoak S Sedge Amperea xipchoclada Euphorbaceae Broom Spurge S Grass Amphibromus neesii Poaceae Swamp Wallaby Grass ? Shrub Aotus ericoides Papillionaceae Common Aotus S Groundcover Apium prostratum Apiaceae Sea Celery MS Herb Arthropodium milleflorum Asparagaceae Pale Vanilla Lily S? Herb Arthropodium strictum Asparagaceae Chocolate Lily S? Shrub Atriplex paludosa ssp.
    [Show full text]
  • Structural and Floristic Variation in the Forest Communities of the West Tamar, Tasmania
    Papers and Proceedings of the Royal Society of Tasmania, Volume 117, 1983. [ms. received 3.9.1982) STRUCTURAL AND FLORISTIC VARIATION IN THE FOREST COMMUNITIES OF THE WEST TAMAR, TASMANIA. by M.J. Brown and R.T. Buckney N.P.W.S., P.O. Box 210, Sandy Bay, Tas. 7005 and School of Life Sciences, N.S.W. Inst. Tech., P.O. Box 123, Broadway, N.S.W. 2007. (with three tables and five text-figures) ABSTRACT BROWN, M.J. & BUCKNEY, R.T., 1983 (31 viii): Structural and floristic variation in the forest communities of the West Tamar, Tasmania. Pap. Proc. R. Soc. Tasm., 117: 135- 152. https://doi.org/10.26749/rstpp.117.135 ISSN 0080-4703. National Parks & Wildlife Service, P.O. Box 210, Sandy Bay, Tasmania and School of Life Sciences, N.S.W. Institute of Technology, P.O. Box 123, Broadway, New South Wales. The forest communities in the West Tamar were sampled by a stratified random process using 55 plots selected after preliminary analy sis of 243 Forestry Commission continuous forest inventory plots, which occur in the area. A total of 13 floristic units were recognised and described. The relationship of the floristic units to changing water availability, drainage, soil fertility and fire frequency are assessed and the problems of structural versus floristic classifications of forest types are discussed. INTRODUCTION The dry forests of Tasmania occupy some of the most heavily utilised areas of the state. Clearing for agriculture and urban development, sawlog extraction, firewood getting and burning combined with stock grazing have all made their mark on this vegeta­ tion.
    [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]
  • RHS the Garden 2012 Index Volume 137, Parts 1-12
    Index 2012: Volume 137, Parts 112 Index 2012 The The The The The The GardenJanuary 2012 | www.rhs.org.uk | £4.25 GardenFebruary 2012 | www.rhs.org.uk | £4.25 GardenMarch 2012 | www.rhs.org.uk | £4.25 GardenApril 2012 | www.rhs.org.uk | £4.25 GardenMay 2012 | www.rhs.org.uk | £4.25 GardenJune 2012 | www.rhs.org.uk | £4.25 RHS TRIAL: LIVING Succeed with SIMPLE WINTER GARDENS GROWING BUSY LIZZIE RHS GUIDANCE Helleborus niger PLANTING IDEAS WHICH LOBELIA Why your DOWNY FOR GARDENING taken from the GARDEN GROW THE BEST TO CHOOSE On home garden is vital MILDEW WITHOUT A Winter Walk at ORCHIDS SHALLOTS for wildlife How to spot it Anglesey Abbey and what to HOSEPIPE Vegetables to Radishes to grow instead get growing ground pep up this Growing chard this month rough the seasons summer's and leaf beet at Tom Stuart-Smith's salads private garden 19522012: GROW YOUR OWN CELEBRATING Small vegetables OUR ROYAL for limited spaces PATRON SOLOMON’S SEALS: SHADE LOVERS TO Iris for Welcome Dahlias in containers CHERISH wınter to the headline for fi ne summer displays Enjoy a SUCCEED WITH The HIPPEASTRUM Heavenly summer colour How to succeed ALL IN THE MIX snowdrop with auriculas 25 best Witch hazels for seasonal scent Ensuring a successful magnolias of roses peat-free start for your PLANTS ON CANVAS: REDUCING PEAT USE IN GARDENING seeds and cuttings season CELEBRATING BOTANICAL ART STRAWBERRY GROWING DIVIDING PERENNIALS bearded iris PLUS YORKSHIRE NURSERY VISIT WITH ROY LANCASTER May12 Cover.indd 1 05/04/2012 11:31 Jan12 Cover.indd 1 01/12/2011 10:03 Feb12 Cover.indd 1 05/01/2012 15:43 Mar12 Cover.indd 1 08/02/2012 16:17 Apr12 Cover.indd 1 08/03/2012 16:08 Jun12 OFC.indd 1 14/05/2012 15:46 1 January 2012 2 February 2012 3 March 2012 4 April 2012 5 May 2012 6 June 2012 Numbers in bold before ‘Moonshine’ 9: 55 gardens, by David inaequalis) 10: 25, 25 gracile ‘Chelsea Girl’ 7: the page number(s) sibirica subsp.
    [Show full text]