Department of Health Shenton Park Site Flora and Fauna Assessment

Total Page:16

File Type:pdf, Size:1020Kb

Department of Health Shenton Park Site Flora and Fauna Assessment Appendix C Environmental Reports (GHD 2015 and PGV Environmental 2015) URBIS 20152707 - PA1149 - SHENTON PARK DRAFT SCHEME REPORT - FINAL FOR LODGEMENT APPENDICES LandCorp Department of Health Shenton Park Site Flora and Fauna Assessment April 2015 This document is in draft form. The contents, including any opinions, conclusions or recommendations contained in, or which may be implied from, Executive summary LandCorp is undertaking preliminary investigations at Shenton Park Rehabilitation Hospital (Shenton Park) to determine its potential for future redevelopment. LandCorp commissioned GHD Pty Ltd (GHD) to undertake Level 1 flora and Level 1 fauna surveys at Shenton Park (The Study area) to investigate and report on the presence of any significant flora and fauna. The scope of works to complete the flora and fauna survey of the Study area aimed to satisfy all scoping requirements documented by LandCorp. The survey was undertaken in accordance with relevant legislation and guidelines. The results of the flora and fauna surveys are summarised below. The Shenton Park site includes a section of Jarrah Banksia woodland in the western part of the property that is in good condition and has relatively high environmental value. The area is adjacent to Bush Forever site 218. The remainder of the site includes parkland cleared areas and a man-made sump with a number of introduced species. The survey resulted in the recording of 109 flora species (41 of these are introduced). One Priority 4 species, Jacksonia sericea, was recorded in the western section of the site. Approximately 100 plants are present. One Threatened species, the orchid Caladenia huegelii, could potentially occur at the site. The timing of the survey was not suitable for determining the presence of this species. There are no recorded Threatened Ecological Communities (TECs) listed under the Environment Protection and Biodiversity Conservation Act 1999 (EPBC Act) or by the Department of Parks and Wildlife (DPaW) within 5 km of the Shenton Park site. Some of the site vegetation may align with a Priority Ecological Community, PEC 27 – Banksia dominated woodlands of the Swan Coastal Plain. Eleven conservation significant fauna species were considered to possibly occur or be likely to occur on the Shenton Park site, based on habitat suitability and records. No conservation significant species were recorded during the site survey. Three EPBC listed species are considered likely to occur at the site, and eight species may possibly utilize the site opportunistically. The three likely species are: x Calyptorhynchus latirostris (Carnaby's Black Cockatoo); x Calyptorhynchus banksia naso (Forest Red-tailed Black Cockatoo); and x Calyptorhynchus baudinii (Baudin’s Black Cockatoo) The Shenton Park site has potential nesting trees spread across the site. Based on DSEWPaC (2012) guidelines, approximately 1.88 hectares of feeding habitat and 2.4 hectares of potential breeding habitat is present. Potential for referrals under State or Commonwealth environmental acts DSEWPaC (2012) provides a risk table that gives guidance on what the Department views as risks\impacts to Black Cockatoos that will trigger referral. Based on an assessment of the risks, clearing of bushland at sites and subsequent impacts to Black Cockatoos would trigger referral based on: y Clearing of 2.4 hectares of potential breeding habitat at Shenton Park. y Clearing of 1.88 hectares of feeding habitat at Shenton Park. y Potential hydrological changes to feeding habitat at Shenton Park. GHD | Report for LandCorp - Department of Health Shenton Park Site, 61/276230/0 | i y Degradation of habitat through land changes; in particular, further edging effect of feeding habitat at Shenton Park. y Increased competition of breeding habitat by other species by removing hollows. y And potential movement or establishment of Phytophthora spp. (dieback) into Black Cockatoo habitat. Recommendations Further survey of the bushland section of the Shenton Park hospital site may be required if that area is to be cleared in the future. There is potential for the presence of the King Spider Orchid, Caladenia huegelii, which must be surveyed for in late September to mid-October. This report is subject to, and must be read in conjunction with, the limitations set out in sections 1.3 and 1.4 and the assumptions and qualifications contained throughout the Report. ii | GHD | Report for LandCorp - Department of Health Shenton Park Site, 61/276230/0 Table of contents 1. Introduction ............................................................................................................................... 1 1.1 Background ..................................................................................................................... 1 1.2 Study area....................................................................................................................... 1 1.3 Scope and limitations ...................................................................................................... 1 1.4 Assumptions.................................................................................................................... 2 2. Methodology ............................................................................................................................. 2 2.1 Desktop assessment ....................................................................................................... 2 2.2 Flora field assessment ..................................................................................................... 2 2.3 Fauna field assessment ................................................................................................... 3 2.4 Survey limitations ............................................................................................................ 4 3. Results ...................................................................................................................................... 5 3.1 Broad vegetation classification ........................................................................................ 5 3.2 Vegetation association .................................................................................................... 5 3.3 Threatened and Priority Ecological Communities ............................................................. 6 3.4 Site vegetation types ....................................................................................................... 6 3.5 Vegetation condition ........................................................................................................ 8 3.6 Flora diversity .................................................................................................................. 8 3.7 Conservation significant flora ........................................................................................... 9 3.8 Fauna habitat .................................................................................................................. 9 3.9 Fauna diversity .............................................................................................................. 10 3.10 Conservation significant fauna ....................................................................................... 11 3.11 Black cockatoos ............................................................................................................ 13 3.12 Risk referral table .......................................................................................................... 14 4. Conclusion and recommendations ........................................................................................... 15 4.1 Recommendations ........................................................................................................ 15 5. References ............................................................................................................................. 16 Table index Table 1 Extent remaining of vegetation type in the State, Bioregion and relevant Local Government Area ............................................................................................................ 6 Table 2 Vegetation types.............................................................................................................. 7 Table 3 Vegetation condition rating scale ..................................................................................... 8 Table 4 Fauna species recorded during field survey ................................................................... 10 Table 5 Likelihood of occurrence of conservation significant fauna ............................................. 11 Table 6 Black cockatoo risk referral assessment ........................................................................ 14 GHD | Report for LandCorp - Department of Health Shenton Park Site, 61/276230/0 | iii Figure index Figure 1 Locality.......................................................................................................................... 19 Figure 2 Vegetation Types .......................................................................................................... 19 Figure 3 Vegetation Condition ..................................................................................................... 19 Figure 4 Potential Nesting Trees for Black Cockatoos ................................................................. 19 Appendices Appendix A - Figures Appendix B – Desktop Search Results Appendix C - Field Survey Results Appendix D - Relevant
Recommended publications
  • Flora and Vegetation Survey of the Proposed Kwinana to Australind Gas
    __________________________________________________________________________________ FLORA AND VEGETATION SURVEY OF THE PROPOSED KWINANA TO AUSTRALIND GAS PIPELINE INFRASTRUCTURE CORRIDOR Prepared for: Bowman Bishaw Gorham and Department of Mineral and Petroleum Resources Prepared by: Mattiske Consulting Pty Ltd November 2003 MATTISKE CONSULTING PTY LTD DRD0301/039/03 __________________________________________________________________________________ TABLE OF CONTENTS Page 1. SUMMARY............................................................................................................................................... 1 2. INTRODUCTION ..................................................................................................................................... 2 2.1 Location................................................................................................................................................. 2 2.2 Climate .................................................................................................................................................. 2 2.3 Vegetation.............................................................................................................................................. 3 2.4 Declared Rare and Priority Flora......................................................................................................... 3 2.5 Local and Regional Significance........................................................................................................... 5 2.6 Threatened
    [Show full text]
  • ALINTA DBNGP LOOPING 10 Rehabilitation Management Plan
    DBNGP (WA) Nominees Pty Ltd DBNGP LOOPING 10 Rehabilitation Management Plan ALINTA DBNGP LOOPING 10 Rehabilitation Management Plan November 2005 Ecos Consulting (Aust) Pty Ltd CONTENTS 1 INTRODUCTION ................................................................................ 1 2 REHABILITATION REVIEW............................................................ 1 2.1 REHABILITATION OBJECTIVES ............................................................... 2 3 EXISTING VEGETATION ................................................................. 2 3.1 FLORA AND VEGETATION...................................................................... 2 3.2 VEGETATION STUDIES ........................................................................... 4 3.2.1 Study Method ............................................................................... 4 3.2.2 Study Results ................................................................................ 7 3.3 OTHER ENVIRONMENTAL VALUES ...................................................... 10 4 REHABILITATION STRATEGY..................................................... 11 5 REHABILITATION METHODS ..................................................... 11 5.1 WEED MANAGEMENT.......................................................................... 11 5.2 DIEBACK (PHYTOPHTHORA CINNAMOMI) MANAGEMENT .................... 11 5.3 PRIORITY AND RARE FLORA MANAGEMENT ........................................ 12 5.4 RESOURCE MANAGEMENT ................................................................... 13 5.5
    [Show full text]
  • 10 Seed Release and Dispersal Mechanisms
    10 Seed Release and Dispersal Mechanisms For seedling recruitment to occur seeds need to be dispersed into an environment that promotes germination and seedling survival. Dispersal consists of two phases. Primary dispersal is defined as the initial transport of seeds or seed-bearing fruits (collectively seeds and fruits are called diaspores) to the ground or water body, or for aerial parasites, a host branch. Secondary dispersal relates to any subsequent movement to the seed’s final resting place. Primary dispersal may be active (e.g. seeds released explosively from the fruit, e.g. dehiscence (opening) of Hardenbergia pods), passive (e.g. seeds fall out when the capsules of Eucalyptus open), or require a vector to aid in seed removal (e.g. wind uplift of winged seeds of Hakea or winged fruits of Nuytsia; Amyema berries consumed by mistletoe birds). Secondary dispersal involves either a biotic (e.g. ants) or environmental (e.g. wind, water) vector, and it is usually a different mechanism than that involved in primary dispersal. While primary dispersal is usually only for a few metres, secondary dispersal may cover several kilometres, and sometimes thousands for tiny seeds. This chapter covers some of the dispersal mechanisms exhibited by the SouthWest flora following their release. Terminology used to describe seed dispersal mechanisms is provided in Table 10.1. Table 10.1: Seed dispersal terminology. Term Definition Anemochory Wind dispersed Chamaechory Dispersal by rolling along the ground (wind assisted) Zoochory Animal dispersed (general) Myrmecochory Ant dispersed Ornithochory Bird dispersed Mammalochory Mammal dispersed Hydrochory Water dispersed Barochory Unassisted (gravity causes seeds to drop to the ground) Autochory Dispersal assisted by the actions of the parent plant (e.g.
    [Show full text]
  • Integrated Approach to Nitrogen Fixing Tree Germplasm Development
    INTEGRATED APPROACH TO NITROGEN FIXING TREE GERMPLASM DEVELOPMENT JAKE HALLIDAY' ABSTRACT - The performance of nitrogen fixing trees introduced to new environments depends on proper reconstitution of the symbiotic associatioi on which the trees rely for their nutrition. Thus selection strategies employed to identify adapted g.rmplasm for particular sites must provide for three-way selection of seed, rhiobia and mycorrhizae. Selected lines must then be multiplied before they can be deployed in varying types of development programs. Speciai problems are faced in accomplishing these ends with virtually all nitrogen fixing tr-es. Results and experiences are described which emphasize the importance of parallel selection of plant germplasm and Rhizobiurn strains. '.n the case of VA mycorrhizae, effective symbioses can occur without specific inoculation. Methods for selecting and multiplying trees and their microsymbionts on a large scale are described and discussed. Index terms: mycorrhiza technology, Rhizobium technology, nitrogen fixing trees, plant selection, seed technology. AqAO INTEGRADA PARA DESENVOLVER GERMOPLASMAS FIXADORES DE NITROGtNIO RESUMO - 0 comportamento de Arvores fixadoras denitrogdniodcpoisde serem introdu­ zidas em novas ambientes depende da reconstituiiSo plena das associaq6es simbi6ticas, as quais contribuem para a nutripo drs plantas. No entanto, as estrat~gias de selecio em­ pregadas para identificar germoplasmas adaptados para certos locais precisam levar em conta a seleno conjunta das sementes, do riz6bio e das micorrizas. As linhas selecionadao tim de multiplicar-se em grande escala arites de serem utilizadas em vdrios tipos de progra­ mas. Encontram-se grades problemas para alcancar estes fins em quase todoi os casos de Arvores fixadaras de nitrogdnio. Descrevem-se experidncias e resultados que enfatizam a importhncia da seleqio paralela de germoplasma de plantas e cepas de Rhizobium.
    [Show full text]
  • Fruits and Seeds of Genera in the Subfamily Faboideae (Fabaceae)
    Fruits and Seeds of United States Department of Genera in the Subfamily Agriculture Agricultural Faboideae (Fabaceae) Research Service Technical Bulletin Number 1890 Volume I December 2003 United States Department of Agriculture Fruits and Seeds of Agricultural Research Genera in the Subfamily Service Technical Bulletin Faboideae (Fabaceae) Number 1890 Volume I Joseph H. Kirkbride, Jr., Charles R. Gunn, and Anna L. Weitzman Fruits of A, Centrolobium paraense E.L.R. Tulasne. B, Laburnum anagyroides F.K. Medikus. C, Adesmia boronoides J.D. Hooker. D, Hippocrepis comosa, C. Linnaeus. E, Campylotropis macrocarpa (A.A. von Bunge) A. Rehder. F, Mucuna urens (C. Linnaeus) F.K. Medikus. G, Phaseolus polystachios (C. Linnaeus) N.L. Britton, E.E. Stern, & F. Poggenburg. H, Medicago orbicularis (C. Linnaeus) B. Bartalini. I, Riedeliella graciliflora H.A.T. Harms. J, Medicago arabica (C. Linnaeus) W. Hudson. Kirkbride is a research botanist, U.S. Department of Agriculture, Agricultural Research Service, Systematic Botany and Mycology Laboratory, BARC West Room 304, Building 011A, Beltsville, MD, 20705-2350 (email = [email protected]). Gunn is a botanist (retired) from Brevard, NC (email = [email protected]). Weitzman is a botanist with the Smithsonian Institution, Department of Botany, Washington, DC. Abstract Kirkbride, Joseph H., Jr., Charles R. Gunn, and Anna L radicle junction, Crotalarieae, cuticle, Cytiseae, Weitzman. 2003. Fruits and seeds of genera in the subfamily Dalbergieae, Daleeae, dehiscence, DELTA, Desmodieae, Faboideae (Fabaceae). U. S. Department of Agriculture, Dipteryxeae, distribution, embryo, embryonic axis, en- Technical Bulletin No. 1890, 1,212 pp. docarp, endosperm, epicarp, epicotyl, Euchresteae, Fabeae, fracture line, follicle, funiculus, Galegeae, Genisteae, Technical identification of fruits and seeds of the economi- gynophore, halo, Hedysareae, hilar groove, hilar groove cally important legume plant family (Fabaceae or lips, hilum, Hypocalypteae, hypocotyl, indehiscent, Leguminosae) is often required of U.S.
    [Show full text]
  • Digital 4 Pty Ltd Lot 802 and Part 803 Erindale Road, Hamersley Section 38 Referral Supporting Document
    Digital 4 Pty Ltd Lot 802 and Part 803 Erindale Road, Hamersley Section 38 referral Supporting Document 25 May 2020 57707-125649 (Rev 3) JBS&G Australia Pty Ltd T/A Strategen-JBS&G Table of Contents Executive Summary .................................................................................................................. v 1. Introduction ................................................................................................................... 1 1.1 Purpose and scope .............................................................................................. 1 1.2 Proponent ............................................................................................................ 1 1.3 Environmental impact assessment process ........................................................ 1 1.4 Other approvals and regulation .......................................................................... 2 1.4.1 Environment Protection and Biodiversity Conservation Act 1999 ...... 2 2. The proposal .................................................................................................................. 7 2.1 Background and justification ............................................................................... 7 2.2 Proposal description ............................................................................................ 7 2.2.1 Key proposal characteristics ................................................................ 7 2.3 Local and regional context .................................................................................
    [Show full text]
  • 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.
    [Show full text]
  • Version 2 Targeted Threatened Flora Search Proposed Demonstration Trail Mount Clarence Albany
    Unit 5A 209 Chester Pass Road Albany WA 6330 9842 1575 [email protected] ABN 48 138 824 272 Job Ref: COA011 7th December 2016 Sandra Maciejewski Reserves Officer City of Albany PO Box 484 Albany WA 6331 Updated Report – Version 2 Targeted Threatened Flora Search Proposed Demonstration Trail Mount Clarence Albany Dear Sandra, On the 26th October 2016 Botanists/Ecologist, Karlene Bain and Bianca Theyer (Bio Diverse Solutions) undertook a targeted linear threatened flora search of 840m for a proposed mountain bike alignment at Mount Clarence, City of Albany (refer to Attachment A for the survey area). This survey was required as there was potential for threatened flora to be present within the subject area and there is proposed clearing of native vegetation as part of the proposed bike trail. The scope of work included: Undertake Targeted Flora Survey across subject site through linear sampling (10m buffer) in vegetation types present and mapping of boundaries of vegetation; Undertake any identification of any flora species, including herbarium identification if required; GPS and map any populations of Threatened Species (if applicable); and Prepare brief report on findings as per appropriate government agency legislation and guidelines. It is noted this survey was undertaken during the spring flowering period. The threatened flora search of the linear bike trail found that the Mount Clarence reserve is a diverse habitat with four vegetation types mapped, being: 1. Granite outcrop and fringing Taxandria shrub land; 2. Tall Gastrolobium shrub land; 3. Open Jarrah/ Marri woodland; and 4. Coastal heath. In November 2016 an occurrence of Stylidium falcatum (P1) was found (5 plants) on laterite soils associated with a cleared alignment for a powerline, on the edge of the jarrah/ marri ecotype.
    [Show full text]
  • Low Flammability Local Native Species (Complete List)
    Indicative List of Low Flammability Plants – All local native species – Shire of Serpentine Jarrahdale – May 2010 Low flammability local native species (complete list) Location key – preferred soil types for local native species Location Soil type Comments P Pinjarra Plain Beermullah, Guildford and Serpentine River soils Alluvial soils, fertile clays and loams; usually flat deposits carried down from the scarp Natural vegetation is typical of wetlands, with sheoaks and paperbarks, or marri and flooded gum woodlands, or shrublands, herblands or sedgelands B Bassendean Dunes Bassendean sands, Southern River and Bassendean swamps Pale grey-yellow sand, infertile, often acidic, lacking in organic matter Natural vegetation is banksia woodland with woollybush, or woodlands of paperbarks, flooded gum, marri and banksia in swamps F Foothills Forrestfield soils (Ridge Hill Shelf) Sand and gravel Natural vegetation is woodland of jarrah and marri on gravel, with banksias, sheoaks and woody pear on sand S Darling Scarp Clay-gravels, compacted hard in summer, moist in winter, prone to erosion on steep slopes Natural vegetation on shallow soils is shrublands, on deeper soils is woodland of jarrah, marri, wandoo and flooded gum D Darling Plateau Clay-gravels, compacted hard in summer, moist in winter Natural vegetation on laterite (gravel) is woodland or forest of jarrah and marri with banksia and snottygobble, on granite outcrops is woodland, shrubland or herbs, in valleys is forests of jarrah, marri, yarri and flooded gum with banksia Flammability
    [Show full text]
  • Terminal Differentiation of Symbiotic Rhizobia in Certain Legume Species And
    Terminal differentiation of symbiotic rhizobia in certain legume species and its implications for legume-rhizobia coevolution A DISSERTATION SUBMITTED TO THE FACULTY OF THE GRADUATE SCHOOL OF THE UNIVERSITY OF MINNESOTA BY Ryoko Oono IN PARTIAL FULFILLMENT OF THE REQUIREMENTS FOR THE DEGREE OF DOCTOR OF PHILOSOPHY R. Ford Denison Advisor August, 2010 © Ryoko Oono 2010 Acknowledgements I would like to give special thanks to Bruce A. Sorrie, Alan Weakley, Carol A. McCormick, Will Cook, Mark T. Buntaine and Troy Mielke for helping me find legume species in North Carolina and Minnesota. This thesis would also not be possible without the mentorship of my committee members, Ruth G. Shaw, George D. Weiblen, Peter Tiffin, and Imke Schmitt as well as the patience and guidance from my thesis advisor, R. Ford Denison, and senior lab graduate student, Will C. Ratcliff. Many thanks for supporting me these last five years and taking the time in fostering my research skills. Additional thanks to many of the undergraduate students working in our lab, including Carolyn G. Anderson, who contributed to Chapter 4 and Justin Bower, whose work will build upon this dissertation. I would also like to thank Toby E. Kiers for giving me the opportunity to write a Tansley Review with her for New Phytologist. Thank you to Janet I. Sprent for collaborating with me on the publication of Chapter 2 and Mike Sadowsky for many interesting discussions on rhizobia. Thank you to the University of Minnesota Plant Biological Sciences Program for supporting me as a graduate student for these past five years with teaching assistantships and summer fellowships.
    [Show full text]
  • PLANTS Figure 3
    Legend Site Boundary 383 000mE N Not Included in Study Cadastral Boundary 02040 60 80 100m GRAND BOULEVARD SCALE 1 : 3 000 at A4 (MGA) Easement Boundary Location of Jacksonia sericea (P4) 2 Number of Plants Vegetation Condition Boundary VG Vegetation Condition 2 PICCADILLY 6 4886 488 250mN 250mN D 1 1 CIRCLE DRIVE CD 999 10 G-D 9000 1 7 D 1 6 488 000mN CD JOONDALUP D Mc LARTY AVENUE 1001 VG G-D G-D CD 2016-255-f03.dgn SHENTON AVENUE 6 487 750mN CADASTRAL SOURCE: Landgate, March 2016. AERIAL PHOTOGRAPH SOURCE: NearMap, flown March 2016. Housing Authority ENVIRONMENTAL ASSESSMENT REPORT ENVIRONMENTAL CONNECT JOONDALUP Drawn: J. Cabot Date: 23 Mar 2016 VEGETATION CONDITION AND LOCATION Figure 3 Job: 10253 Rpt: 2016-255 Revision: A OF Jacksonia sericea (P4) PLANTS Figure 4 PINPOINT CARTOGRAPHICS (08) 9562 7136 Legend Site Boundary 383 000mE N Not Included in Study Cadastral Boundary 02040 60 80 100m GRAND BOULEVARD SCALE 1 : 3 000 at A4 (MGA) Easement Boundary Significant Trees Jarrah (Eucalyptus marginata) Tuart (Eucalyptus gomphocephala) Standing Dead Tree Hollow Observed PICCADILLY 6 488 250mN CIRCLE DRIVE 999 9000 6 488 000mN JOONDALUP Mc LARTY AVENUE Mc LARTY AVENUE 1001 2016-255-f04.dgn SHENTON AVENUE 6 487 750mN CADASTRAL SOURCE: Landgate, March 2016. AERIAL PHOTOGRAPH SOURCE: NearMap, flown March 2016. Housing Authority ENVIRONMENTAL ASSESSMENT REPORT ENVIRONMENTAL CONNECT JOONDALUP Drawn: J. Cabot Date: 23 Mar 2016 BLACK COCKATOO HABITAT Figure 4 Job: 10253 Rpt: 2016-255 Revision: A PINPOINT CARTOGRAPHICS (08) 9562 7136 APPENDIX 1 Naturemap Report NatureMap Species Report Created By Jackalyn Hams on 10/03/2016 Current Names Only Yes Core Datasets Only Yes Method 'By Circle' Centre 115°45' 56'' E,31°44' 12'' S Buffer 4km Group By Kingdom Kingdom Species Records Animalia 328 11155 Bacteria 2 6 Fungi 40 83 Plantae 460 878 Protozoa 13 19 TOTAL 843 12141 Name ID Species Name Naturalised Conservation Code 1Endemic To Query Area Animalia 1.
    [Show full text]
  • Roadside Vegetation and Conservation Values in the Shire Of
    RRooaaddssiiddee VVeeggeettaattiioonn aanndd CCoonnsseerrvvaattiioonn VVaalluueess iinn tthhee SShhiirree ooff SSeerrppeennttiinnee--JJaarrrraahhddaallee Photo by P. Haro December 2006 CONTENTS EXECUTIVE SUMMARY 1 PART A: OVERVIEW OF ROADSIDE CONSERVATION 2 1.0 Why is Roadside Vegetation Important? 3 2.0 What are the Threats? 4 2.1 Lack of Awareness 4 2.2 Roadside Clearing 4 2.3 Fire 5 2.4 Weeds 6 2.5 Salinity 7 3.0 Legislative Requirements 8 4.0 Environmentally Sensitive Areas 9 5.0 Flora Roads 10 PART B: THE NATURAL ENVIRONMENT IN SERPENTINE-JARRAHDALE 11 1.0 Flora 12 2.0 Declared Rare Flora (DRF) 12 3.0 Fauna 14 4.0 Remnant Vegetation Cover 17 PART C: ROADSIDE SURVEYS IN THE SHIRE OF SERPENTINE-JARRAHDALE 18 1.0 Introduction 19 1.1 Methods 19 1.2 Mapping Roadside Conservation Values 20 1.3 Roadside Conservation Value Categories 20 2.0 Using the Roadside Conservation Value Map (RCV) Map 22 3.0 Results 24 PART D: ROADSIDE MANAGEMENT RECOMMENDATIONS 31 1.0 Management Recommendations 32 2.0 Minimising Disturbance 33 3.0 Planning for Roadsides 34 4.0 Setting Objectives 34 REFERENCES 35 FIGURES Figure 1. Native vegetation on roadsides in the Shire of Serpentine-Jarrahdale. Figure 2. Number of native plant species in roadsides in the Shire of Serpentine-Jarrahdale. Figure 3. Extent of native vegetation in roadsides in the Shire of Serpentine-Jarrahdale. Figure 4. Roadside vegetation value as a biological corridor in the Shire of Serpentine- Jarrahdale. Figure 5. Weed infestation along roadsides in the Shire of Serpentine-Jarrahdale. Figure 6.
    [Show full text]