Native Plants As Environmental Weeds on the Mornington Peninsula
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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. -
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. -
Inquiry Into the Utilisation of Victorian Native Flora and Fauna
ENVIRONMENT AND NATURAL RESOURCES COMMITTEE INQUIRY INTO THE UTILISATION OF VICTORIAN NATIVE FLORA AND FAUNA REPORT June 2000 ___________________________________ Ordered to be printed ___________________________________ VICTORIAN GOVERNMENT PRINTER 2000 No 30 Session 1999/2000 The Committee records its appreciation to all those who have contributed to the Inquiry and the preparation of this report. A large number of individuals and organisations made their expertise and experience available through the submission process, the Committee’s inspection program and the public hearing process; they are listed in the Appendices. Specialist consultancies were undertaken by Mr Quentin Farmar-Bowers of Star Eight Consulting, Dr Graham Steed of G.R. Steed and Associates Pty Ltd and Mrs Tannetje Bryant and Mr Keith Akers of the Faculty of Law, Monash University. Technical review and advice was provided by Dr Robert Begg and Mr Spencer Field of the Department of Natural Resources and Environment and their associates. Additional technical advice was provided by Mr Tony Charters, Director of Planning and Destination Development, Tourism Queensland, Dr Graham Hall and associates of the Tasmanian Department of Parks and Wildlife, Professor Hundle of the National Ecotourism Accreditation Program, and Dr Ray Wills, Senior Ecologist at Kings Park and Botanic Gardens, Western Australia. The cover photograph is of Grampians Thryptomene (Thryptomene calycina) taken by Dr David Beardsell. Cover design by Luke Flood of Actual Size, with printing by Acuprint. Editing services were provided by Ms Heather Kelly. The report was drafted by the staff of the Environment and Natural Resources Committee: Ms Julie Currey, Dr Andrea Lindsay, and Mr Brad Miles. -
Construction of an Environmentally Sustainable Development on a Modified Coastal Sand Mined and Landfill Site—Part 2
Sustainability 2010, 2, 717-741; doi:10.3390/su2030717 OPEN ACCESS sustainability ISSN 2071-1050 www.mdpi.com/journal/sustainability Article Construction of an Environmentally Sustainable Development on a Modified Coastal Sand Mined and Landfill Site—Part 2. Re-Establishing the Natural Ecosystems on the Reconstructed Beach Dunes AnneMarie Clements 1, *, Appollonia Simmonds 1, Pamela Hazelton 2, Catherine Inwood 3, Christy Woolcock 4, Anne-Laure Markovina 5 and Pamela O’Sullivan 6 1 Anne Clements and Associates Pty Ltd, P.O. Box 1623, North Sydney 2059, Australia 2 Faculty of Engineering and IT, University of Technology, Sydney, P.O. Box 123, Broadway, NSW 2007, Australia; E-Mail: [email protected] 3 17 Canton Parade, Noraville, NSW 2263, Australia; E-Mail: [email protected] 4 Tentacle Inc., 2 Henderson Street, Norah Head, NSW 2263, Australia; E-Mail: [email protected] 5 School of Biological Sciences, University of Sydney, Building A10, Science Road, NSW 2006, Australia; E-Mail: [email protected] 6 Australasian Mycological Society, P.O. Box 154, Ourimbah, NSW 2258, Australia; E-Mail: [email protected] * Author to whom correspondence should be addressed; E-Mail: [email protected]; Tel.: +61-2-9955-9733; Fax: +61-2-9957-4343. Received: 1 February 2010; in revised form: 25 February 2010 / Accepted: 1 March 2010 / Published: 9 March 2010 __________________________________________________________________________________ Abstract: Mimicking natural processes lead to progressive colonization and stabilization of the reconstructed beach dune ecosystem, as part of the ecologically sustainable development of Magenta Shores, on the central coast of New South Wales, Australia. -
Acacia Pendula (Weeping Myall)
Cunninghamia Date of Publication: 17 December 2014 A journal of plant ecology for eastern Australia ISSN 0727- 9620 (print) • ISSN 2200 - 405X (Online) Acacia pendula (Weeping Myall) in the Hunter Valley of New South Wales: early explorers’ journals, database records and habitat assessments raise doubts over naturally occurring populations Stephen Bell1,3 & Colin Driscoll2 1 Eastcoast Flora Survey, PO Box 216 Kotara Fair NSW 2289, [email protected] 2 Hunter Eco, PO Box 1047 Toronto NSW 2283, [email protected] 3 School of Environmental and Life Sciences, University of Newcastle, Callaghan NSW 2308 Abstract: Acacia pendula, Weeping Myall, (family Fabaceae) is the most legislatively protected plant species in the New South Wales Hunter Valley. Under the NSW Threatened Species Conservation Act 1995 it is listed as an Endangered Population (in the Hunter Valley) and as a component of two Endangered Ecological Communities (one in the Hunter, one elsewhere in NSW); it is also listed as a Critically Endangered Ecological Community (in the Hunter Valley) on the Commonwealth Environment Protection and Biodiversity Conservation Act 1999 and listed as threatened in three other eastern Australian States. To ascertain the likely original distribution of stands of Acacia pendula in the Hunter Valley, this paper examines the writings of early Australian explorers, herbarium and database records, and the species habitat attributes across NSW. None of the journals examined, including those of botanist/explorer Allan Cunningham (who originally collected Acacia pendula from the Lachlan River in 1817), Thomas Mitchell or Ludwig Leichhardt, make note of the species for the Hunter Valley. Several explorers do, however, record Acacia pendula regularly (>100 times) across other parts of NSW, Queensland, and South Australia. -
COAST WATTLE at Nine Mile Beach
Glamorgan Spring Bay BIODIVERSITY FACT SHEET No 1 COAST WATTLE at Nine Mile Beach The aim of this fact sheet is to clarify issues with regard to COAST WATTLE at Nine Mile Beach in relation to its: Common and scientific name Origin Recognition and Potential fire hazard Recognition Many plants can exhibit a degree of variation between individuals of the same species and this can sometimes be confusing when attempting to identify a species. Some such variation is present in COAST WATTLE at Nine Mile Beach. Typical COAST WATTLE can be recognised by the following characteristics: Seed pods Commonly coiled or contorted Leaf (or phyllode*3): Shape Broadest part of the leaf is in the upper half Length 5 – 12 cm Width 10 – 30 mm COAST WATTLE (Acacia longifolia subsp. sophorae) - Photo 4: Leaves (phyllodes); Veins 2 - 4 prominent primary veins Photo 5 (inset): Seed pods Notes *1 There are two subspecies of Acacia longifolia. These are Acacia longifolia subsp. sophorae and Acacia longifolia subsp. longifolia. However, some authorities consider these subspecies to be two distinct species. Furthermore some plant nurseries sell COAST WATTLE as Acacia sophorae. *2 Biodiversity, or biological diversity, is the variety of all life forms. It includes genetic diversity, species diversity and ecosystem diversity. *3 The ‘leaves’ of many wattles are not true leaves but ‘phyllodes’ which are technically defined as ‘an expanded, leaf-like petiole (or leaf stalk) lacking a true leaf blade’. References and Further Information: • Australian Native Plants Society: http://anpsa.org.au • Flora of Australia. Volume 11b. Mimosaceae, Acacia Pt 2. Melbourne: ABRS/CSIRO Publishing (2001). -
Scientific Opinion 1
EFSA Journal 2015;13(4):4079 SCIENTIFIC OPINION 1 Risk to plant health in the EU territory of the intentional release 2 of the bud-galling wasp Trichilogaster acaciaelongifoliae 3 1 for the control of the invasive alien plant Acacia longifolia 4 EFSA Panel on Plant Health (PLH)2,3 5 European Food Safety Authority (EFSA), Parma, Italy 6 ABSTRACT 7 The EFSA Panel on Plant Health was requested by the European Commission to assess the risk to plant health in 8 the European Union if the Australian bud-galling wasp Trichilogaster acaciaelongifoliae was released for the 9 control of the invasive alien plant Acacia longifolia in Portugal. T. acaciaelongifoliae feeds on A. longifolia and 10 A. floribunda. In South Africa, following its intentional introduction in 1982 and 1983, the wasp is now present 11 throughout the range of A. longifolia in that country, with most plants showing galls and seed set reductions of, 12 initially, up to 95 %. Climatic conditions in the EU are largely suitable for establishment wherever A. longifolia 13 and A. floribunda are present. T. acaciaelongifoliae is moderately likely to establish and spread in the EU, by 14 natural means, but particularly if it is intentionally moved to control populations of A. longifolia other than those 15 present in Portugal. The effects on native biodiversity and ecosystems resulting from invasive populations of 16 A. longifolia are likely to be reduced by the wasp. A. longifolia is grown as an ornamental plant in some EU 17 countries. A. floribunda is not an invasive plant in the EU and is cultivated as an ornamental plant on a small 18 scale in France, Greece and Italy. -
Investigating the Distribution of Acacia Longifolia Ssp. Sophorae in South
30 Plant Protection Quarterly Vol.21(1) 2006 and Paull 2000, Mitchell and Wilson 2005). Yet despite the probable impacts, relative- Investigating the distribution of Acacia longifolia ssp. ly little is known about the inland inva- sion of coast wattle in south-west Victoria, sophorae in south-west Victoria using satellite remote including the current extent of invasion and factors involved in the invasion proc- sensing and GIS ess. It is diffi cult to assess the threat of the species and develop appropriate manage- A B C A Jennifer Emeny , Gordon Duff , Dianne Simmons and Anne Wallis ment strategies without such information. A School of Ecology and Environment, Deakin University, PO Box 423, Field assessment of coast wattle in south- Warrnambool, Victoria 3280, Australia. west Victoria has been made diffi cult by B CRC for Tropical Savannas Management, Charles Darwin University, the extent and remoteness of vegetation in Darwin, Northern Territory 0909, Australia. the region (Baldock et al. 1995 b). C School of Ecology and Environment, Deakin University, 221 Burwood There has been considerable interest in Highway, Burwood, Victoria 3125, Australia. the use of geospatial technologies in envi- ronmental weed management. Of particu- lar interest is the potential use of remote sensing for mapping weed distribution (e.g. Everitt et al. 1991, 1992, 1999, 2001, Pitt and Miller 1988, Ullah et al. 1989a,b, Summary 1997, Costello et al. 2000, Mullet 2001). In Everitt and Escobar 1996, Frazier 1998, Mapping and analysis of the distribution Victoria, most coastal and near-coastal re- Bulman 2000, Crossman and Kochergen of environmental weeds is an important serves now contain at least one Australian 2002, Underwood et al. -
Structural Development of Vegetation On
Audet et al. Ecological Processes 2013, 2:20 http://www.ecologicalprocesses.com/content/2/1/20 RESEARCH Open Access Structural development of vegetation on rehabilitated North Stradbroke Island: Above/belowground feedback may facilitate alternative ecological outcomes Patrick Audet*, Amanda Gravina, Vanessa Glenn, Phill McKenna, Helen Vickers, Melina Gillespie and David Mulligan Abstract Introduction: This study depicts broad-scale revegetation patterns following sand mining on North Stradbroke Island, south-eastern Queensland, Australia. Methods: Based on an ecological timeline spanning 4–20 years post-rehabilitation, the structure of these ecosystems (n = 146) was assessed by distinguishing between periods of ‘older’ (pre-1995) and ‘younger’ (post-1995) rehabilitation practices. Results: The general rehabilitation outlook appeared promising, whereby an adequate forest composition and suitable levels of native biodiversity (consisting of mixed-eucalypt communities) were achieved across the majority of rehabilitated sites over a relatively short time. Still, older sites (n = 36) appeared to deviate relative to natural analogues as indicated by their lack of under-storey heath and simplified canopy composition now characterised by mono-dominant black sheoak (Allocasuarina littoralis) reaching up to 60% of the total tree density. These changes coincided with lower soil fertility parameters (e.g., total carbon, total nitrogen, and nutrient holding capacity) leading us to believe that altered growth conditions associated with the initial mining disturbance could have facilitated an opportunistic colonisation by this species. Once established, it is suspected that the black sheoak’s above/belowground ecological behaviour (i.e., relating to its leaf-litter allelopathy and potential for soil-nitrogen fixation) further exacerbated its mono-dominant distribution by inhibiting the development of other native species. -
The Role of Pollinators, Seed Dispersers and Belowground Symbionts in the Invasion Success of Acacia
Lincoln University Digital Thesis Copyright Statement The digital copy of this thesis is protected by the Copyright Act 1994 (New Zealand). This thesis may be consulted by you, provided you comply with the provisions of the Act and the following conditions of use: you will use the copy only for the purposes of research or private study 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. Do mutualists matter? The role of pollinators, seed dispersers and belowground symbionts in the invasion success of Acacia __________________________________ A thesis submitted in partial fulfilment of the requirements for the Degree of Doctor of Philosophy at Lincoln University by Elizabeth M. Wandrag _______________________________ Lincoln University, New Zealand 2012 Abstract Plant species introduced to new locations may lose their natural enemies but can also leave behind important mutualists. Here, I take a novel comparative approach to identify the potential role of mutualistic interactions in determining invasion outcomes. I examine the strength of pollination, seed dispersal and belowground symbioses with nitrogen-fixing bacteria (rhizobia) across three species that vary in invasion success in both their introduced and native range. I used species of Australian Acacia introduced to New Zealand. I hypothesised that if interactions with mutualists are important for plant invasion then species would vary in the strength of interactions with one or more of the groups of mutualists I examined, and that the pattern of variation would correlate with the degree to which they have established and spread in New Zealand. -
Coastal Mycology: Boundary Conditions for Arbuscular Mycorrhizal (AM) Fungi in Incipient Sand Dunes
Coastal mycology: Boundary conditions for arbuscular mycorrhizal (AM) fungi in incipient sand dunes Lynda Michelle Lever ORCID 0000‐0003‐3857‐8556 Submitted in total fulfilment of the requirements of the degree of Doctor of Philosophy June 2018 Faculty of Science, School of Geography The University of Melbourne Abstract Little is known about the relationship between the colonization by arbuscular mycorrhizal (AM) fungi in grasses in the ephemeral environment of incipient sand dunes. Yet, consideration of dune vegetation without including the soil biota in the substrate, means that a significant biological component of the dune system is ignored. Ephemeral incipient dunes are an extreme and environmentally stressful ecosystem, encountering strong and salt-laden winds, sea water overwash, and low nutrients and these dunes are subject to a frequency and magnitude of storm action that foredunes are not. Incipient dunes represent a challenging opportunity in which to add to our understanding of coastal AM fungal tolerances, species richness and biogeography, in association with their equally resilient symbionts. Arbuscular mycorrhizal fungi are ubiquitous in soil, and have an association with approximately 90% of terrestrial vascular plants, exchanging mineral nutrients and water for carbon compounds. These fungi are the most common mycorrhizal fungi in the sand dune ecosystem, and play a significant role in the establishment and proliferation of pioneer plants such as Thinopyrum junceiforme (Sea Wheatgrass), an exotic C3 dune grass, and the native C4 dune grass, Spinifex sericeus (Hairy Spinifex). The unifying hypothesis was that AM fungi in incipient dunes have life history strategies that equip them for disturbance and sodium chloride levels not found in other contexts. -
Invasion of Portuguese Dunes by Acacia Longifolia
Invasion of Portuguese dunes by Acacia longifolia : present status and perspectives for the future Hélia Marchante Dissertação de Doutoramento na área científica de Biologia, especialidade Ecologia, apresentada à Faculdade de Ciências e Tecnologia da Universidade de Coimbra. Coimbra, Fevereiro 2011 i ii Supervisors : Professora Doutora Helena Maria de Oliveira Freitas Centro de Ecologia Funcional, Departamento de Ciências da Vida Faculdade de Ciências e Tecnologia Universidade de Coimbra Professor Doutor John Hugh Hoffmann Department of Zoology University of Cape Town, South Africa The present work was financially supported by Fundação para a Ciência e a Tecnologia, Ministério da Ciência, Tecnologia e Ensino Superior through projects INVADER (POCTI/BSE/42335/2001) and INVADER II (POCI/AMB/61387/2004) and grant SFRH/BD/24987/2005 to Hélia Marchante. iii iv ABSTRACT Invasive species are one of the main threats to biodiversity worldwide, with serious impacts for the environment, economy and ecosystems services. Invasion ecology is a relatively recent field of increasing importance in environmental research and management, with a growing number of publications and new wide-reaching initiatives. Even so, many questions still need to be answered and more research is clearly needed. This work investigated several aspects of the invasion of a Mediterranean dune ecosystem by a Leguminosae tree, Acacia longifolia (Andrews) Willd. , aiming to contribute to filling some specific gaps in invasion Ecology, and providing practical and useful management options for managers. The effects of A. longifolia at vegetation level, in areas with different invasion durations (stands invaded for more than 20 years, hereafter “long-invaded”, compared to stands invaded after a summer fire in 1995 – hereafter “recently invaded”) were compared, over a five-year period, with non-invaded situations, using multiple parameters.