A. PPRWS Referral
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Their Botany, Essential Oils and Uses 6.86 MB
MELALEUCAS THEIR BOTANY, ESSENTIAL OILS AND USES Joseph J. Brophy, Lyndley A. Craven and John C. Doran MELALEUCAS THEIR BOTANY, ESSENTIAL OILS AND USES Joseph J. Brophy School of Chemistry, University of New South Wales Lyndley A. Craven Australian National Herbarium, CSIRO Plant Industry John C. Doran Australian Tree Seed Centre, CSIRO Plant Industry 2013 The Australian Centre for International Agricultural Research (ACIAR) was established in June 1982 by an Act of the Australian Parliament. ACIAR operates as part of Australia's international development cooperation program, with a mission to achieve more productive and sustainable agricultural systems, for the benefit of developing countries and Australia. It commissions collaborative research between Australian and developing-country researchers in areas where Australia has special research competence. It also administers Australia's contribution to the International Agricultural Research Centres. Where trade names are used this constitutes neither endorsement of nor discrimination against any product by ACIAR. ACIAR MONOGRAPH SERIES This series contains the results of original research supported by ACIAR, or material deemed relevant to ACIAR’s research and development objectives. The series is distributed internationally, with an emphasis on developing countries. © Australian Centre for International Agricultural Research (ACIAR) 2013 This work is copyright. Apart from any use as permitted under the Copyright Act 1968, no part may be reproduced by any process without prior written permission from ACIAR, GPO Box 1571, Canberra ACT 2601, Australia, [email protected] Brophy J.J., Craven L.A. and Doran J.C. 2013. Melaleucas: their botany, essential oils and uses. ACIAR Monograph No. 156. Australian Centre for International Agricultural Research: Canberra. -
Post-Fire Recovery of Woody Plants in the New England Tableland Bioregion
Post-fire recovery of woody plants in the New England Tableland Bioregion Peter J. ClarkeA, Kirsten J. E. Knox, Monica L. Campbell and Lachlan M. Copeland Botany, School of Environmental and Rural Sciences, University of New England, Armidale, NSW 2351, AUSTRALIA. ACorresponding author; email: [email protected] Abstract: The resprouting response of plant species to fire is a key life history trait that has profound effects on post-fire population dynamics and community composition. This study documents the post-fire response (resprouting and maturation times) of woody species in six contrasting formations in the New England Tableland Bioregion of eastern Australia. Rainforest had the highest proportion of resprouting woody taxa and rocky outcrops had the lowest. Surprisingly, no significant difference in the median maturation length was found among habitats, but the communities varied in the range of maturation times. Within these communities, seedlings of species killed by fire, mature faster than seedlings of species that resprout. The slowest maturing species were those that have canopy held seed banks and were killed by fire, and these were used as indicator species to examine fire immaturity risk. Finally, we examine whether current fire management immaturity thresholds appear to be appropriate for these communities and find they need to be amended. Cunninghamia (2009) 11(2): 221–239 Introduction Maturation times of new recruits for those plants killed by fire is also a critical biological variable in the context of fire Fire is a pervasive ecological factor that influences the regimes because this time sets the lower limit for fire intervals evolution, distribution and abundance of woody plants that can cause local population decline or extirpation (Keith (Whelan 1995; Bond & van Wilgen 1996; Bradstock et al. -
Springbrook Rescue Restoration Project
Springbrook Rescue Restoration Project Progress Report Australian Rainforest Conservation Society Inc. September 2011 This Report was prepared by Aila Keto and Keith Scott Contents Introduction 1 Progress Report 2 1. Foundational activities Program logic defined using INFFER and SER guidelines 2 Potential threats and barriers to ecological restoration described; risk factors identified; mitigation options evaluated 2 Resources requirements identified and costed: feasibility determined 2 Monitoring, evaluation and reporting processes defined 3 Conceptual and growth models of ecological restoration selected 5 Conceptual models for social systems relevant to a social- ecological systems approach to restoration selected 5 Assets defined and described: significant species selected and life history attributes completed 5 Community support strategy defined 8 Policy deficiencies that allow continuing threatening processes identified 8 2. Initial activities and outcomes (0–3 years) Conceptual and growth models of ecological restoration evaluated 11 Conceptual models of social learning evaluated 11 Threats and barriers to ecological restoration under active control based on observation and monitoring 11 Extent of invasion by Aristea ecklonii and other priority weeds identified; control options assessed and measures underway 13 Sensor system installed for recording environmental parameters 15 Long-term monitoring plots set up; growth rate, soil moisture and other measurements initiated; restoration trials started 16 Natural regeneration identified, -
Climate Change and Queensland Biodiversity
Climate Change and Queensland Biodiversity An independent report commissioned by the Department of Environment and Resource Management (Qld) Tim Low © Author: Tim Low Date: March 2011 Citation: Low T. (2011) Climate Change and Terrestrial Biodiversity in Queensland. Department of Environment and Resource Management, Queensland Government, Brisbane. On the Cover: The purple-necked rock wallaby (Petrogale purpureicollis) inhabits a very rocky region – the North-West Highlands – where survival during heatwaves and droughts depends on access to shady rock shelters. Rising temperatures will render many of their smaller shade refuges unusuable. Photo: Brett Taylor Paperbarks (Melaleuca leucadendra) are the trees at most risk from sea level rise, because they are habitat dominants on recently formed plains near the sea where freshwater settles. They were probably scarce when the sea fell during glacials, and tend to support less biodiversity than older forest types. Photo: Jeanette Kemp, DERM Contents 1. Introduction and summary 1 5. Ecological framework 52 1.1 Introduction 1 5.1 The evidence base 53 1.2 Summary 4 5.1.1 Climatically incoherent distributions 53 1.3 Acknowledgements 5 5.1.2 Introduced species distributions 56 5.1.3 Experimental evidence 58 2. Climate change past and future 7 5.1.4 Genetic evidence 58 5.1.5 Fossil evidence 58 2.1 Temperature 8 5.2 Why distributions might not reflect climate 59 2.1.1 Past temperatures 9 5.2.1 Physical constraints 60 2.2 Rainfall 10 5.2.2 Fire 62 2.2.1 Past rainfall 11 5.2.3 Limited dispersal 63 2.3 Drought 12 5.2.4 Evolutionary history 65 2.3.1 Past drought 12 5.2.5 Lack of facilitation 65 2.4 Cyclones 12 5.2.6 Competition 66 2.4.1 Past cyclones 12 5.2.7 Predators and pathogens 70 2.5 Fire 13 5.3 Discussion 71 2.5.1 Past fire 13 5.3.1 High altitude species 71 2.6 Sea level rise 14 5.3.2 Other species 73 2.6.1 Past sea level rise 14 5.4 Management consequences 74 3. -
Springbrook Rescue Restoration Project
Springbrook Rescue Restoration Project Progress Report Australian Rainforest Conservation Society Inc. September 2011 This Report was prepared by Aila Keto and Keith Scott Contents Introduction 1 Progress Report 2 1. Foundational activities Program logic defined using INFFER and SER guidelines 2 Potential threats and barriers to ecological restoration described; risk factors identified; mitigation options evaluated 2 Resources requirements identified and costed: feasibility determined 2 Monitoring, evaluation and reporting processes defined 3 Conceptual and growth models of ecological restoration selected 5 Conceptual models for social systems relevant to a social- ecological systems approach to restoration selected 5 Assets defined and described: significant species selected and life history attributes completed 5 Community support strategy defined 8 Policy deficiencies that allow continuing threatening processes identified 8 2. Initial activities and outcomes (0–3 years) Conceptual and growth models of ecological restoration evaluated 11 Conceptual models of social learning evaluated 11 Threats and barriers to ecological restoration under active control based on observation and monitoring 11 Extent of invasion by Aristea ecklonii and other priority weeds identified; control options assessed and measures underway 13 Sensor system installed for recording environmental parameters 15 Long-term monitoring plots set up; growth rate, soil moisture and other measurements initiated; restoration trials started 16 Natural regeneration identified, -
Eucryphia Volume 23 No.5 March 2019 Journal of the Australian Plants Society Tasmania Inc
Eucryphia Volume 23 No.5 March 2019 Journal of the Australian Plants Society Tasmania Inc. ISSN 1324-3888 Online ISSN 2209-0452 J. Cullen© D. Burns $2.20 PRINT POST APPROVAL No. 100004305 Eucryphia March 2019 02 © M. Killen 1 APST’s Big Day Out: 1 Members at the edible precinct with Emma Hope answering questions. 2 Floral bouquet for her Excellency the Governor brought by Rosemary Verbeeten. 3 Planter boxes in the edible precinct. 2 3 © M. Killen © M. Killen Front Cover: Dick’s Alyogyne huegelii, see article page 20. Left: A low-growing Alyogyne huegelii also in Dick’s garden. PRINTER: THE XEROX SHOP, 118 BATHURST STREET HOBART TASMANIA 7000 © D. Burns Eucryphia March 2019 01 EUCRYPHIA Contents ISSN 1324-3888 Published quarterly in Membership subs. & renewals 2 March, June, September and December by Australian Plants Society Tasmania Inc Membership 3 ABN 64 482 394 473 Editor 3 Patron: Her Excellency, Professor the Honourable Kate Warner, AC, President’s Plot 4 Governor of Tasmania Society postal address: Constitutional Review 5 PO Box 3035, Ulverstone MDC Ulverstone Tas 7315 Report from Council 5 Editor: Mary Slattery AGM Agenda 6 [email protected] Contributions and letters to the editor Study Group Highlights 7 are welcome. If possible they should be forwarded by email to the editor at Calendar 2019 8 [email protected] or typed using one side of the paper only. If Publications 9 handwritten, please print botanical names and the names of people. ANPSA News 10 Original text may be reprinted, unless otherwise indicated, provided an Blooming Biodiversity 11 acknowledgment of the source is given. -
The Vegetation Communities 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. -
TAS003 PPRWS Pipeline 20170515
Glamorgan Spring Bay Council Prosser Plains Raw Water Scheme (PPRWS) Water Distribution pipeline Botanical Survey and Fauna Habitat Assessment 15th May 2017 Andrew North [email protected] Philip Barker [email protected] 163 Campbell Street Hobart TAS 7000 Telephone 03. 6231 9788 Facsimile 03. 6231 9877 Flora and Fauna Habitat Assessment – Prosser Plains Raw Water Scheme Title: Glamorgan Spring Bay Council Prosser Plains Raw Water Scheme (PPRWS) Botanical Survey and Fauna Habitat Assessment Document Dr Philip Barker 1 February 2017 Prepared NBES By: 2 February 2017 Document David Burt Reviewed by By: CHANGE RECORD Issue Date Changed By Description of Change 1.1 7/2/17 P Barker Minor edits provided by David Burt 1.2 13/4/17 P. Barker Take account of route modification 1.3 11/5/17 P. Barker Adjustments to comply with DoE requests for information. i North Barker Ecosystem Services TAS003 Flora and Fauna Habitat Assessment – Prosser Plains Raw Water Scheme SUMMARY AND RECOMMENDATIONS Glamorgan Spring Bay Council is investigating the potential to construct the Prosser Plains Raw Water Scheme (PPRWS). This scheme includes a dam on the Tea Tree Rivulet and a pipeline from below the weir on Prosser River to Louisville Point. Between the dam wall and the weir the water will be transferred down the Tea Tree Rivulet and then via the Prosser River. This report considers the natural values and potential impacts and ,mitigation related to the location and construction of the pipeline. Toward that end this report documents the vegetation and the flora and fauna values of the footprint of the development. -
Genetic Basis of Pathogenicity in Uredo Rangelii
Plant Health AUSTRALIA National Myrtle Rust Transition to Management (T2M) Program Final Report Genetic basis of pathogenicity in Uredo rangelii Authors: Dr. Karanjeet S. Sandhu and Prof. Robert F. Park The University of Sydney Plant Breeding Institute Cobbitty NSW 2570 September 2013 PHA Project Number: P218 Name of Research Provider: The University of Sydney Project Title: Project 4.1: Genetic basis of pathogenicity in Uredo rangelii Principal Investigators: Dr. Karanjeet Sandhu and Prof. Robert Park Faculty of Agriculture and Environment, the University of Sydney, Plant Breeding Institute Private Bag 4011, Narellan NSW 2567, Australia Correspondence: [email protected], T +61 2 9351 8806, F +61 2 9351 8875 or [email protected], T +61 2 9351 8821, F +61 2 9351 8875 Disclaimer: This report has been created by the University of Sydney solely for the use by Plant Health Australia Limited, its authorised contractors and agents and specifically for the purposes of Plant Health Australia Limited. The University of Sydney does not warrant that the report, when used by persons other than Plant Health Australia Limited or its unauthorised contractors or agents, will be accurate, reliable, complete, up to date or fit for any purpose and disclaims all liability for any loss, damage, cost or expense incurred in or arising from such use to the extent permitted by law. Final Report PHA_P218_4.1 Page 1 Summary: Myrtle rust was first time detected in Australia on the central coast of NSW in April 2010, from Agonis flexuosa, Callistemon viminalis and Syncarpia glomulifera plants. Based on the tonsured urediniospores, initially this pathogen was described as Uredo rangelii but later on with the detection of teliospores and studying the sequence of the rDNA ITS region, it was considered to be a strain of Puccinia psidii sensu lato, a guava rust causing fungal pathogen that was first detected in Brazil in 1884. -
Newsletter No.33
Dear members, Firstly, I must apologise for the lateness of this newsletter but I have been awaiting receipt of details of the report on " New combinations in MelaIezrca for Australian smcies ofCalllis~ernon ( Myrtaceae. ) ". A copy of the current changes is attached. A number of specific epithets have been changed but some species have had only the genus name changed. Callistemon viminalis has been oflcially recognisedpreviously as Melaluuca viminalis. Callistemon citrinus has likewise been previously recognised and is now M. citrina. Lyn Craven is currently working on apaper describing a few new species of callistemons in Melaleuca. Lyn suggeste that horticulturalists continue to use " callistemon" as the common name. Have fun getting used to the new names!! It is still very dry here but we don't have that all on our own. There appears to be many parts of Australia in more dire straits than we are. We have only lost a couple ofplants so far. It has been amazing how most have hung on with virtually no additional water. Callistemons , or Melaleucas as they will be known in future, appear to be one of the toughest as they are stillflowering happily along despite the lack of moisture. We have had more flowers on the Callistemons this year than I can recall in previous years. Callistemonplants are still lookingfiesh and green and have lost very few leaves when compared to some species fiom other genera - Eucalyptus, Lophostemon, Backhousia and Syzygiium to name a few. We have been able to keep our fern garden going so far with use of washing machine water etc. -
Puccinia Psidii (Myrtle Rust) – AUSTRALIAN HOST LIST Version Current at 24 Sept
Puccinia psidii (Myrtle Rust) – AUSTRALIAN HOST LIST version current at 24 Sept. 2014 This is PDF of a Word Table version; see also separate PDF of Excel version (same data), as separate file on this website. This list records all host taxa (all of family Myrtaceae) for Puccinia psidii recorded within Australia. See separate Global host-list on this website for world-wide records. Suggested citation: Giblin F & Carnegie AJ (2014) Puccinia psidii (Myrtle Rust) – Australian host list. Version current at 24 Sept. 2014. http://www.anpc.asn.au/resources/Myrtle_Rust.html Contribution acknowledgments: Pegg G, Guymer G, Bean T, McKenna S, Lidbetter J, Entwistle P, Smith D, Morin L, Sandu K, Makinson RO LEGEND Natural occurrence of host species within Australia (by jurisdiction) – excludes non-naturalised occurrences. Queensland (Qld), New South Wales (NSW - excludes ACT and Lord Howe Island), Australian Capital Territory (ACT), Lord Howe Island (LHI), Victoria (Vic), Tasmania (Tas), South Australia (SA), Western Australia (WA), Northern Territory (NTerr), Christmas Island (ChI). [LHI is listed separately from mainland NSW, of which it is administratively part, because of its World Heritage Area status. ChI is listed separately from mainland Australia because of its Commonwealth Territory status.] Ex-risk status = Extinction-risk status (source-lists below are legislative unless otherwise stated): Queensland: Nature Conservation (Wildlife) Regulation 2006, current as at 9 May 2014. https://www.legislation.qld.gov.au/LEGISLTN/CURRENT/N/NatureConWiR06.pdf, accessed 15 Aug. 2014. Available categories: ExW = Extinct in the Wild [in Qld]; E = Endangered; V = Vulnerable; NearThr = Near Threatened; LC = Least Concern [all native taxa not otherwise categorised – LC taxa are not shown on this host-list document]. -
Species of City-Wide Significance for Conservation (2016 Update)
Species of City-wide Significance for Conservation (2016 Update) Final Report June 2016 CITY OF GOLD COAST Speciesecology of City-wide Significance/ vegetation for Conservation / wildlife (2016 Update) / aquatic ecologyecosure / GIS.com.au | i Executive summary The City of Gold Coast engaged Ecosure Pty Ltd to undertake a review of the 2012 species of city-wide significance for conservation list and develop a decision-framework for prioritising species for future conservation management actions. Through a review of the existing criteria, updating the legislative status and scoring the base list of species for the Gold Coast local government area against the revised criteria, a draft list of city-wide significant species was established. An expert panel review of the draft species list resulted in a final city-wide significant species list containing 572 flora and 160 fauna species, from a base species list containing 1,952 vascular and legislatively significant non-vascular flora and 609 vertebrate and legislatively significant invertebrate fauna species. This species list will be used by the City to create a priority species list as part of a priority species management program. Part of the scope of this present project has been to review various frameworks to assess priorities. After an in-depth literature review and consultative process, Ecosure recommended the Back on Track Phase II methods as a suitable decision- support framework for the City. Customisation of the Back on Track Phase II methods to suit the City’s requirements are summarised in Section 3.6 of this report. Section 4 provides recommendations which have arisen during the course of this project and include for example, the timeframe for future reviews of the city-wide significant species list and decision-support framework criteria, items for consideration in future reviews and suggestions for the subsequent application of the species list.