March Meeting and Excursion What’S Inside: Page for Our First Excursion This Year We Will Meet at 9.30Am
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Conospermum Hookeri Hookeri (Tasmanian Smokebush)
Listing Statement for Conospermum hookeri (tasmanian smokebush) Conospermum hookeri tasmanian smokebush FAMILY: Proteaceae T A S M A N I A N T H R E A T E N E D S P E C I E S L I S T I N G S T A T E M E N T GROUP: Dicotyledon Photos: Naomi Lawrence Scientific name: Conospermum hookeri (Meisn.) E.M.Benn., Fl. Australia 16: 485 (1995) (Meisn.) Common name: tasmanian smokebush Name history: previously known in Tasmania as Conospermum taxifolium. Group: vascular plant, dicotyledon, family Proteaceae Status: Threatened Species Protection Act 1995: vulnerable Environment Protection and Biodiversity Conservation Act 1999: Vulnerable Distribution: Biogeographic origin: endemic to Tasmania Tasmanian NRM regions: North, South Tasmanian IBRA Bioregions (V6): South East, Northern Midlands, Ben Lomond, Flinders Figure 1. Distribution of Conospermum hookeri Plate 1. Conospermum hookeri in flower. showing IBRA (V6) bioregions 1 Threatened Species Section – Department of Primary Industries, Parks, Water and Environment Listing Statement for Conospermum hookeri (tasmanian smokebush) Conospermum hookeri may be limited by low seed SUMMARY: Conospermum hookeri (tasmanian production rates. Other species of Conospermum smokebush) is a small shrub in the Proteaceae are known to have low reproductive outputs. family. It is endemic to Tasmania, occurring Approximately 50% of flowers of Conospermum along the East Coast from Bruny Island to species form fruit though only a small Cape Barren Island in 10 locations, two proportion of these produce viable seed presumed locally extinct and another of (Morrison et al. 1994). uncertain status. The number of subpopulations is estimated to be 40, with five Conospermum hookeri makes a highly significant presumed locally extinct or of uncertain status. -
Flying-Fox Dispersal Feasibility Study Cassia Wildlife Corridor, Coolum Beach and Tepequar Drive Roost, Maroochydore
Sunshine Coast Council Flying-Fox Dispersal Feasibility Study Cassia Wildlife Corridor, Coolum Beach and Tepequar Drive Roost, Maroochydore. Environmental Operations May 2013 0 | Page Table of Contents Introduction ................................................................................................................................ 2 Purpose ............................................................................................................................................... 2 Flying-fox Mitigation Strategies .......................................................................................................... 2 State and Federal Permits ................................................................................................................... 4 Roost Management Plan .................................................................................................................... 4 Risk ...................................................................................................................................................... 5 Flying-fox Dispersal Success in Australia ............................................................................................. 6 References .......................................................................................................................................... 7 Cassia Wildlife Corridor ................................................................................................................ 8 Background ........................................................................................................................................ -
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. -
Brisbane Native Plants by Suburb
INDEX - BRISBANE SUBURBS SPECIES LIST Acacia Ridge. ...........15 Chelmer ...................14 Hamilton. .................10 Mayne. .................25 Pullenvale............... 22 Toowong ....................46 Albion .......................25 Chermside West .11 Hawthorne................. 7 McDowall. ..............6 Torwood .....................47 Alderley ....................45 Clayfield ..................14 Heathwood.... 34. Meeandah.............. 2 Queensport ............32 Trinder Park ...............32 Algester.................... 15 Coopers Plains........32 Hemmant. .................32 Merthyr .................7 Annerley ...................32 Coorparoo ................3 Hendra. .................10 Middle Park .........19 Rainworth. ..............47 Underwood. ................41 Anstead ....................17 Corinda. ..................14 Herston ....................5 Milton ...................46 Ransome. ................32 Upper Brookfield .......23 Archerfield ...............32 Highgate Hill. ........43 Mitchelton ...........45 Red Hill.................... 43 Upper Mt gravatt. .......15 Ascot. .......................36 Darra .......................33 Hill End ..................45 Moggill. .................20 Richlands ................34 Ashgrove. ................26 Deagon ....................2 Holland Park........... 3 Moorooka. ............32 River Hills................ 19 Virginia ........................31 Aspley ......................31 Doboy ......................2 Morningside. .........3 Robertson ................42 Auchenflower -
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. -
North Head Winter Flowers
North Head Winter Flowers Cryptandra amara Cryptandra Actinotus helianthi ESBS Flannel Flower Epacris microphylla ESBS Coral Heath Pandorea pandorana Epacris longiflora ESBS Epacris obtusifolia ESBS Wonga Vine Fuchsia Heath Blunt-leaf Heath Helichrysum elatum White Paper Daisy Actinotus minor ESBS Lesser Flannel Flower Patersonia sericea ESBS Silky Purple Flag Melaleuca quinquinervia Correa reflexa Broad-leaved Paper-bark Common Correa Correa alba White Correa Boronia ledifolia Boronia parviflora ESBS Swamp Boronia Sydney Boronia Brachyloma daphnoides ESBS Rulingia hermanniifolia Ricinocarpus pinifolius ESBS Daphne Heath Rulingia Wedding Bush Westringia fructosa Coast Rosemary Leucopogon ericoides ESBS Pink Beard Heath Philotheca buxifolia ESBS Box-leaved Wax Flower Philotheca salsolifolia ESBS Philotheca Conospermum taxifolium ESBS Coneseeds Conospermum longifolium Long-leaf Coneseeds Grevillea sericea Pink Spider Flower Sprengelia incarnata Pink Swamp Heath Leucopogon microphyllus ESBS Small-leaved White Beard Plectranthus parviflorus Synoum glandulosum Cockspur Flower Scented Rosewood Leptospermum laevigatum ESBS Coast Tea Tree Calytrix tetragona Fringe Myrtle Dampiera stricta Blue Dampiera Leucopogon setiger Beard Heath Bauera rubioides ESBS Leptospermum trinervium River Rose, Dog Rose Flakey Bark Tea Tree Styphelia triflora Five Corners Styphelia tubiflora Red Five-Corners Monotoca elliptica ESBS Cyanicula caerulea Pittosporum undulatum Tree Broom-Heath ESBS Blue Caladenia, Blue Fairy Sweet Pittosporum Stylidium lineare Narrow-leaf -
Boronia Granitica (Granite Boronia)
Approved NSW and National Recovery Plan Recovery Plan for Boronia granitica (Granite Boronia) July 2002 © NSW National Parks and Wildlife Service, 2002. This work is copyright. However, material presented in this plan may be copied for personal use or published for educational purposes, providing that any extracts are fully acknowledged. Apart from this and any other use as permitted under the Copyright Act 1968, no part may be reproduced without prior written permission from the NPWS. NSW National Parks and Wildlife Service 43 Bridge Street (PO Box 1967) Hurstville NSW 2220 Tel: 02 9585 6444 www.npws.nsw.gov.au For further information contact: Granite Boronia Recovery Coordinator Threatened Species Unit, Northern Directorate NSW National Parks and Wildlife Service Locked Bag 914 Coffs Harbour NSW 2450 Tel: 02 6651 5946 Cover illustration: Boronia granitica (Granite Boronia) Cover illustrator: Ann Sheppard This plan should be cited as follows: NSW National Parks and Wildlife Service (2002). Recovery Plan for Boronia granitica (Granite Boronia). NSW National Parks and Wildlife Service, Hurstville. ISBN 0 7313 68894 Approved Recovery Plan Boronia granitica Executive Summary Introduction Boronia granitica (Granite Boronia) is a medium-sized, open shrub with pinnate foliage and pink flowers. It grows in heathy vegetation amongst granite boulders of the New England Batholith, where it is restricted to a limited number of mostly small populations. This recovery plan describes our current understanding of B. granitica, documents the research undertaken to date and identifies management actions required and parties responsible in addressing the conservation of B. granitica. Legislative context The Threatened Species Conservation Act 1995 (TSC Act) is NSW’s most comprehensive legislative framework to protect and encourage the recovery of threatened species, populations and communities. -
Vegetation and Floristics of Ironbark Nature Reserve & Bornhardtia
Vegetation and Floristics of Ironbark Nature Reserve & Bornhardtia Voluntary Conservation Area Dr John T. Hunter (aka Thomas D. McGann) August 2002 © J.T.Hunter 2002 75 Kendall Rd, Invergowrie NSW, 2350 Ph. & Fax: (02) 6775 2452 Email: [email protected] A Report to the New South Wales National Parks and Wildlife Service i Vegetation of Ironbark & Bornhardtia Summary The vegetation of Ironbark Nature Reserve and the Bornhardtia Voluntary Conservation Area is described and mapped (scale 1:25 000). Eleven communities are defined based on classification (Kulczynski association) with further sub-assemblages described. These eleven communities were mapped based on ground truthing, air photo interpretation and landform. One community is listed as Endangered on state and federal acts (TSC & EPB&C Acts), three are considered here to be vulnerable and all others are considered to be poorly or inadequately reserved across their range. Most communities are of woodland and open forest structure. The communities show considerable variation and intergrade along common boundaries and in particular on intermediate soil types. Drainage, Easting, Soil Depth, Physiography and protection from the North were the major correlative influences on community distribution, however Northing and Rock Type were also strongly correlated. A total of 477 vascular plant taxa were found from 93 families and 269 genera. At least 39 species are considered of significance, 30 are of regional significance and a further nine are of state or national significance. Two species are listed on the TSC Act, one as Endangered and one as Vulnerable nine are RoTAP listed species or are listed under this criteria in other publications. -
Vegetation and Floristics of Butterleaf National Park, Butterleaf State Conservation Area and the Bezzants Lease
Vegetation and Floristics of Butterleaf National Park, Butterleaf State Conservation Area and the Bezzants Lease Dr John T. Hunter May 2011 23 Kendall Rd, Invergowrie NSW, 2350 Ph. & Fax: (02) 6775 2452 Email: [email protected] A Report to the New South Wales National Parks and Wildlife Service & the Nature Conservation Trust of NSW i Vegetation of Butterleaf & Bezzants Lease Summary The vegetation of the Butterleaf National Park and State Conservation Area and Bezzant’s Lease is described and mapped (scale 1:25 000). Nine communities and three sub-associations are defined based on classification (Kulczynski association). These eight communities and three sub-associations were mapped based on ground truthing, air photo interpretation and landform. The communities described and their status is: Floristic Community Area Reservation Status C1a: Eucalyptus radiata – E. Not listed as a community of concern though 1,875 ha campanulata – E. obliqua likely a unique association within the area. C1b: Eucalyptus obliqua – E. Not listed as a community of concern. 263 ha brunnea – E. saligna C1c: Eucalyptus campanulata Not listed as a community of concern. 250 ha – E. obliqua – E. saligna C2: Eucalyptus acaciiformis – Likely to be included as an Endangered Angophora floribunda Ecological Community within the Montane 8.7 ha Peatlands and Swamps determination of the TSC Act. C3: Eucalyptus caliginosa – Not listed as a community of concern though E. bridgesiana – E. 433 ha likely a unique association within the area. laevopinea C4: Eucalyptus nova-anglica Would fall within the Endangered Ecological – E. acaciiformis – E. 39.8 ha Community New England Peppermint subtilior Woodland on the TSC and EPBC Acts. -
Australian Plants Suitable for Tamworth Regional Council Areas
Australian Plants Suitable for Tamworth Regional Council Areas Eucalyptus blakelyi Photo Tony Croft Tamworth Group of Australian Plants Society As at July 2007 Eucalyptus blakelyi II TAMWORTH REGIONAL COUNCIL RAINFALL DATA Most of the Tamworth Regional Council area receives an average annual rainfall of 600 to 800mm except for the north- west corner on the Mount Kaputar plateau and the tablelands country from Bendemeer through Woolbrook to Hanging Rock above Nundle which often receives between 800 to 1000mm. Similarly temperatures vary across the region with average annual minimums on the tablelands and nearby areas between 6 and 9 degrees Celsius. A series of frosts are received across the entire region each winter. Average annual maximums are between 18 and 21 degrees on the tablelands, 21 to 24 degrees across most of the region and 24 to 27 degrees in the west of the region. 1. Barraba 2. Manilla 250 180 160 200 140 120 150 2004/2005 100 2004-2005 80 100 Average Average 60 50 40 20 0 0 il il ec Jan eb ay ec Jan eb ay July Aug Sept Oct Nov D F Apr M June July Aug Sept Oct Nov D F Apr M June March March 3. Nundle 4.Tamworth 250 200 250 200 m 150 2004-2005 2003-2004 150 2003-2004 Average 100 100 2004-2005 m in Rainfall 50 50 0 y t l e 0 ct an h J rc Jul gust Sep O Nov Dec Feb Apri May Jun n b y Ma uly Oct e rch pril une Au J Aug Sept Nov Dec Ja F a A Ma J M Recent and Average Rainfall for Barraba, Manilla, Nundle, Tamworth and Woolbrook Location Rainfall Rainfall Average 2004-2005 2003-2004 Rainfall in mm in mm in mm Barraba 780.9 689 Manilla 627.9 498.1 651.4 Not Nundle 793.7 868 Available Tamworth 629.6 759.2 673 Woolbrook 686.8 784.5 783 More detailed weather information can be found on the Bureau of Meteorology website. -
The Effects of Fire-Related Germination Cues, Time-Since-Fire and Habitats on the Germinable Soil-Borne Seed Banks at the Torrington State Conservation Area (NSW)
The effects of fire-related germination cues, time-since-fire and habitats on the germinable soil-borne seed banks at the Torrington State Conservation Area (NSW). Kinzang Dorji November 2004 A thesis submitted for the degree of Master of Scientific Studies at the University of New England, Armidale, Australia. ABSTRACT To determine the effects of fire-related germination cues, time-since-fire and habitats, soil-borne seed bank samples of rocky outcrops and forest habitats of Torrington State Conservation Area were examined under glasshouse conditions. A total of 1766 seedlings were recorded from the 128 sample trays over the trial duration of 9 weeks. After 9 weeks, no more seedlings emerged. The seedlings were identified as belonging to 44 species from 38 genera and 23 plant families; comprising 21 woody species, 17 forb species, 3 graminoid species and 3 grass species. The most prominent plant families were Fabaceae (8 woody species) followed by Myrtaceae (4 woody species), Apiaceae (4 forb species) and Epacridaceae, Poaceae and Asteraceae with 3 species each. Both seedling emergence and species richness was greater for heat and combinatorial effect of heat and smoke induced treatments than for control and smoke treatments. However, only the species richness was significant for treatments. Time-since-fire significantly affected the community composition. There were a total of 1351 seedlings germinated from the sites with long time-since-fire (>10 yrs.) and 415 seedlings were emerged from the sites with short time-since-fire (18 months). Germinants were mostly shown from the long-burnt rocky outcrops. There was a habitats effect with rocky outcrop samples having significantly more germinable seeds (1522 seedlings) than soil samples collected from forest habitats (144 seedlings). -
Vegetation Management Plan
8 November 2017 Document Version Control Project Title: Habitat Rehabilitation Management Plan - Yarrabilba Authors: Kieran Richardt, Dr Sarah Butler and Mark Ballantyne File reference: NCO11-0011_Yarrabilba Project leader: Kieran Richardt Phone: +(61) 7 5576 5568, +(61) 4 1541 3408 Email: [email protected] Client: Lend Lease Client contact: Rob Ball Revision History Version: Purpose: Issued by: Date Reviewer: Date: Draft Peer review Sarah Butler 25/02/15 Dionne Coburn 26/02/15 V1 Assessment Sarah Butler 26/02/15 Rob Ball 26/02/15 V2 Assessment Sarah Butler 26/02/15 Kieran Richardt 23/03/15 V3 Amendment Rob Ball 07/11/17 M.N. Runkowski 08/11/17 Declaration of Accuracy In making this declaration, I am aware that section 491 of the Environment Protection and Biodiversity Conservation Act 1999 (Cth) (EPBC Act) makes it an offence in certain circumstances to knowingly provide false or misleading information or documents to specified persons who are known to be performing a duty or carrying out a function under the EPBC Act or the Environment Protection and Biodiversity Conservation Regulations 2000 (Cth). The offence is punishable on conviction by imprisonment or a fine, or both. I am authorised to bind the approval holder to this declaration and that I have no knowledge of that authorisation being revoked at the time of making this declaration. Date 8 November 2017 This report and any files associated with it contain information which is confidential and may also be legally privileged. This document is and shall remain the property of Natura Pacific Pty Ltd (t/a Natura Consulting).