EIS 1395 ABO2O1 83 Flora and Rehabilitation

Total Page:16

File Type:pdf, Size:1020Kb

EIS 1395 ABO2O1 83 Flora and Rehabilitation EIS 1395 ABO2O1 83 Flora and rehabilitation assessment report: proposed further clay/shale extraction and waste disposal operation - Kemp Creek Quarry NSW D EPT PRHARy IDUSTR1ES 1hlh1'lif AB0201 83 .EMENTS & ASSOCIATES PTY. LIMITED (A.C.N. 002 564 436) cal Consultants Environmental and Botani Box 1623, North Sydney 2059 Phone: (02) 9955 3362, Facsimile: (02) 9957 4343 October 1995 Flora and rehabilitation assessment report: Proposed further clay/shale extraction and waste disposal operation - Kemp Creek Quarry prepared by: Dr AnneMarie Clements and A.N. Rodd prepared for: Rob Corkery R.W. Corkery & Co. Pty Limited P0 Box 80, ORANGE 2800 '1 Contents - 1 .0 Existing environment - the biological setting 1.1 Climate 1.2 Geology and topography 1.3 Land use 2.0 Flora 2.1 Survey findings 2.2 Status of native vegetation 2.2.1 Species 2.2.2 Plant communities 3.0 Flora conclusions 4.0 Precautions 5.0 Rehabilitation 5.1 Recommendations 5.1.1 Adjoining the electricity easement 5.1.2 Additional planting areas 6.0 Stockpiles References Acknowledgments Tables 1 Full species names as given in Harden (1990, 1991, 1992, 1993 in press) 2 Transect statistics of tree species, classification of areas 3 Structural form classification Appendices 1 Vegetation species present in the transects The flora of the proposed further clay/shale extraction and waste disposal operation at Kemps Creek was surveyed on 23 September 1993 by Dr AnneMarie Clements and A.N. Rodd, and rehabilitation potential assessed on 9 May 1995 by Dr AnneMarie Clements. 1.0 Existing environment - the biological setting 1.1 Climate The study area is located on the Cumberland Plain of Sydney approximately 40 km inland. The climatic condition in Sydney vary according to distance from the sea and topographic features. Rainfall shows a decreasing gradient from the coast to Liverpool with the study area receive an average rainfall of approximately 700 mm. Liverpool's annual average rainfall is about 70% of the Sydney rainfall. There is also differences in seasonal terms, with the Cumberland Plain experiencing its wettest period during summer, near the coast most of the rain falls in autumn. The sequence of wet and dry days tens to be longer on the Cumberland Plain than on the coast. Temperature extremes are also more pronounced with mean summer daily maximum at Badgerys Creek (1936->) of 29° C (Jan), Bringelly (1970->) of 29° C (Jan), Liverpool (1962->) of 28° C (Jan), Prospect Dam (1887->) of 28° C (Jan) and Campbelltown (1959-1984) of 28° C (Jan) and mean winter daily minimum at Badgerys Creek (1936->) of 4° C (July), Bringelly (1970->) of 5° C (July), Liverpool (1962->) of 4, C (July), Prospect Dam (1887->) of 6.0° C and Campbelltown (1959- 1 984) of 3° C (July) (Commonwealth of Australia 1 988) than Sydney (mean month daily maximum in January of 25 C and mean monthly minimum in July of 8° C). 1.2 Geology and topography The original land surface is gentle (about 1:50 slope, NSW Dept of Lands 1988), western sloping flood plain, east of Kemps Creek in Western Sydney. The 50 m AHD contour passes through the south-western corner of the site. On the soil landscape series sheet (Bannerman and Hazelton 1989), the site is classified as disturbed, adjoining on southern boundary South Creek soil landscape group and on the east, north and western boundaries by Blacktown soil landscape group. The South Creek soil landscape group is the present active flood plain of many drainage networks of the Cumberland Plain, including the South, Eastern, Kemps and Prospect Creeks system. The Blacktown soil landscape group consists of gentle undulating rises on Wianamatta Group Shales. This soil landscape cover at least 50% of the Liverpool municipality. It has a high urban and rural capacity and is capable of sustaining regular cultivation and grazing (Bannerman and Hazelton 1989). 1 The soils of both these landscape groups are derived from Wianamatta Group Shales. 1 13 Land use The land to east has been cleared for grazing with some market gardening. To the west, there has been land clearing for past grazing activities. In the south and the west, there are regrowth forest of Cumberland vegetation. The extent of natural flooding was probably the main determinant of the land use and extent of clearing. The site has been extensively quarried for clays for roofing tiles at Lion Tile at Enfield. Since 1989, Brandown Pty Ltd have been backfilling a number of the pits with non-putrescible waste. There are number of artificial wetlands in south-west section of the site. 2.0 Flora Native Western Sydney plants now survive only in small patches of remnant bush along creek lines and in a few inadequate reserves. There are about 475 I native plant species of which 147 are vulnerable to extinction in Western Sydney (Benson and McDonald 1991). In this survey, 78 native species and 17 exotic species were recorded (Table 1, locations given in Appendix 1 and Figure I 1). The Blacktown soil landscape group has undergone major clearing, the regrowth I areas to the west of the site represents one of the few remaining stands. The native vegetation of the active flood plain of the South Creek soil landscape is not well represented in Liverpool Municipality. The only major patch is along Kemps Creek (Clements and Taylor 1992). Benson (1985) classified the plant community along Kemps Creek "9f", an open forest with the main canopy species being Angophora subve/utina (Broad-leaved Apple), Eucalyptus I amplifolia (Cabbage Gum) and E. tereticornis (Forest Red Gum). On these deep alluvial soils and poorly drained alluvial flats of Western Sydney, such as South, Kemps and Orphan School Creeks, are tall patches of E. ampilfolia (Cabbage I Gum), sometime with patches of Casuarina glauca (Swamp Oak). C. glauca is commonly found near estuarine swamps and lakes. Brackish subsoil water is I characteristic of the Wianamatta Shales. Manynative species are listed as rare in Western Sydney (Benson and McDougall 1991). Few of these species are listed as rare or threatened Australian plants (Briggs and Leigh 1988). 2.1 Survey findings This survey collected detailed vegetation data mainly from areas of remnant I native vegetation. 1 2 TABLE I - Species recorded for site NOTES: 1. Bot. name code is used in Appendix I 2. Asterisk preceding Bot. name code signifies exotic species Bot. name code Botanical name Common name TPteridophytes Marsileaceae MARSI MUTI Marsilea mutica Striped Nardoo Sinopteridaceae CHEILA SIEB Cheilanthes sieberi subsp. sieberi Rock Fern * PELLAVIRI Pellaea viridis 3. Dicotyledons Acanthaceae BRUNONIE AUST Brunoniella australis Blue Trumpet, Blue Yam Apiaceae CENTE CORD Centella cordifolia Heart-leaved Pennywort * CICL LEPT Ciclospermum leptophyllum Slender Celery Apocynaceae PARS STRA Parsonsia straminea Common Silkpod, Monkey Rope Asclepiadaceae * ARAUJHORT Araujia hortorum Moth Vine, Cruel Plant Asteraceae * ASTER SUBU Aster subulatus Bushy Starwort, Wild Aster * HYPOCH RADI Hypochoeris radicata Flatweed, Cat's-ears, False Dandelion LAGENGRAC Lagenifera gracilis OLEAR MICR Olearia microphylla OZOT DIOS Ozothamnus diosmifolius Pill Flower, White Dogwood * SENE MADA Seneclo madagascariensis Fireweed, Madagascar Ragwort * SONC OLER Sonchus oleraceus Common Sow-thistle. Milk-thistle VERN CINE Vernonia cinerea Casuarinaceae ALLO LITT Allocasuarina littoralis Black She-Oak CASU GLAU Casuarina clauca Swamp Oak, Swamp She-oak Chenopodiaceae EINA HAST Einadia hastata Berry Saltbush EINA NUTA Einadia nutans Climbing Saltbush Convolvulaceae CONVO ERUB Convolvulus erubescens Native Bindweed, Blushing Bindweed, Pink Bind DICHON MICR Dichondra micrantha Kidney-weed Crassulaceae * BRYO DELA Bryophyllum delago Mother-of-Millions CRASS SIEB Crassula sieberiana Australian Stonecrop Epacridaceae ASTROL HUMI Astroloma hurnifusum Cranberry_Heath LEUCOP JUNI Leucopogon juniperinus Long-flowered Beard-heath Fabaceae Faboideae CHORIZE PARV Chorizema parviflorum Eastern Flame Pea DAVIE ACIC Daviesia acicularis Sandplain Bitter-pea DESM VARI Desmodium varians Slender Tick-trefoil DILL JUNI Dillwynia juniperina Eggs-and-bacon HARD VIOL Hardenbergia violacea False Sarsaparilla JACK SCOP Jacksonia scoparia Dogwood PLATYL FORM PARV Platylobium formosum su Handsome Flat-pea I I Bot. name code Botanical name Common name PULT VILL Pultenaea villosa Fabaceae Mimosoideae ACAC DECU Acacia decurrens Black Wattle ACAC ULIC Acacia ulicifolia Pricldy Moses, Prickly Wattle Haloragaceae * MYRIOP AQUA Myriophyllum aquaticum Parrots Feather, Brazilian Water-milfoil Lamiaceae AJUGAUST Aivaaaustralis Nabve Bugle,_Austrahan Bugle Lobeliaceae PRAT PURP Pratia purpurascens WNteroot Loranthaceae AMYE GAUD Amyema gaudichaudU Paperbark Mistletoe Malvaceae * SIDA RHOM Sida rhombifolia Paddy's Lucerne, Common Sida Myoporaceae - EREMOP DEBI - Eremophila debilis Winter Apple, Amulla Myrtaceae ANGO FLOR Angophora floribunda Rough-barked Apple - EUCA AMPL Eucalyptus amplifolia Cabbage Gum EUCA GLOBO Eucalyptus globoidea White_Stringybark EUCA MOLU Eucalyptus moluccana Coast Grey Box EUCA TERE Eucalyptus tereticornis Forest Red Gum, Queensland Blue Gum MELA DECO Melaleuca decora White Cloud Tree MELA LINA Melaleuca linartfolia Flax-leaved Paperbark, Snow-in-summer Oleaceae * LIGUSTR SINE Ligustrum sinense Small-Leaved Privet, Chinese Privet Oxalidaceae O)(AL EXIL Oxalis exilis Creeping Oxalis Pittosporaceae BURS SPIN Bursaria spinosa var. spinosa Australian Boxthorn Plantaginaceae PLANT DEBI Plantago debilis * PLANT LANC Plantago lanceolata Plantain, Ribwort Polygonaceae * RUME
Recommended publications
  • 2020 Majura Ainslie Plant List.Xlsx
    Plant Species List for Mount Majura and Mount Ainslie, Canberra Base data from Ingwerson, F; O. Evans & B. Griffiths. (1974). Vegetation of the Ainslie-Majura Reserve . Conservation Series No. 2. AGPS Canberra. Re-organised, revised and updated by Michael Doherty, CSIRO Ecosystem Sciences and Waltraud Pix, Friends of Mt. Majura With advice from Isobel Crawford, Australian Botanical Surveys Current version of 01.10.2020 Names: Census of Plants of the Australian Capital Territory, Version 4.1, 2019 Enquiries:Version 3.0 [email protected] (8th June 2012) subsp. = subspecies Form ? = questionable status or identity f = herb, forb sp. aff. = having close affinities with i.e. similar but not quite the sameo = herb, orchid syn. = synonymous with i.e. most recent previous name, or alternativeg = nameherb, grass sens. lat. = in the broad sense of the species concept gl = herb, grass- or sedge-like var. = variety s = shrub (including creeper and climber) sp. = species i.e. identity yet to be finalised st = shrub / small tree spp. = species in the plural i.e. more than one species t = tree MM Mount Majura. Notionally north of “Blue Metal” Road; MA Mount Ainslie. Notionally south of “Blue Metal” Road (VVV) Species occurrence checking; currently focused on Mt. Majura rather than Mt. Ainslie. No ticks next to name = species reported but not yet confirmed for Mt Majura and Mt Ainslie. Status is locally native except for: PE = Planted Exotic PN = Planted Non-local Native WE = Weed Exotic WN = Weed Non-local Native ‘Planted’ status refers to individuals which are planted but not spreading ‘Weed’ status refers to species reproducing in the wild Scientific name Common name MM MA Status Form Family Isolepis sp .
    [Show full text]
  • 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.
    [Show full text]
  • Appendix 3 Section 5A Assessments “Seven Part Tests”
    APPENDIX 3 SECTION 5A ASSESSMENTS “SEVEN PART TESTS” Appendix 3: Seven Part Tests Swamp Sclerophyll Forest Swamp Sclerophyll Forest on Coastal Floodplains of the NSW North Coast, Sydney Basin and South East Corner bioregions is listed as an Endangered Ecological Community under the NSW Threatened Species Conservation Act (1995). It is not listed under the schedules of the Commonwealth Environmental Protection and Biodiversity Conservation Act (1999). Swamp Sclerophyll Forest on Coastal Floodplains of the NSW North Coast, Sydney Basin and South East Corner bioregions includes and replaces Sydney Coastal Estuary Swamp Forest in the Sydney Basin bioregion Endangered Ecological Community. This community is associated with humic clay loams and sandy loams, on waterlogged or periodically inundated alluvial flats and drainage lines associated with coastal floodplains (NSW Scientific Committee 2011). It occurs typically as open forests to woodlands, although partial clearing may have reduced the canopy to scattered trees or scrub. The understorey may contain areas of fernland and tall reedland or sedgeland which in turn may also form mosaics with other floodplain communities and often fringe wetlands with semi-permanent standing water (NSW Scientific Committee 2011). Swamp Sclerophyll Forest on Coastal Floodplains generally occurs below 20 metres ASL, often on small floodplains or where the larger floodplains adjoin lithic substrates or coastal sand plains (NSW Scientific Committee 2011). The species composition of Swamp Sclerophyll Forest is primarily determined by the frequency and duration of waterlogging and the texture, salinity nutrient and moisture content of the soil. The species composition of the trees varies considerably, but the most widespread and abundant dominant trees include Eucalyptus robusta Swamp Mahogany, Melaleuca quinquenervia and, south from Sydney, Eucalyptus botryoides Bangalay and Eucalyptus longifolia Woollybutt (OEH 2015a).
    [Show full text]
  • Southern Gulf, Queensland
    Biodiversity Summary for NRM Regions Species List What is the summary for and where does it come from? This list has been produced by the Department of Sustainability, Environment, Water, Population and Communities (SEWPC) for the Natural Resource Management Spatial Information System. The list was produced using the AustralianAustralian Natural Natural Heritage Heritage Assessment Assessment Tool Tool (ANHAT), which analyses data from a range of plant and animal surveys and collections from across Australia to automatically generate a report for each NRM region. Data sources (Appendix 2) include national and state herbaria, museums, state governments, CSIRO, Birds Australia and a range of surveys conducted by or for DEWHA. For each family of plant and animal covered by ANHAT (Appendix 1), this document gives the number of species in the country and how many of them are found in the region. It also identifies species listed as Vulnerable, Critically Endangered, Endangered or Conservation Dependent under the EPBC Act. A biodiversity summary for this region is also available. For more information please see: www.environment.gov.au/heritage/anhat/index.html Limitations • ANHAT currently contains information on the distribution of over 30,000 Australian taxa. This includes all mammals, birds, reptiles, frogs and fish, 137 families of vascular plants (over 15,000 species) and a range of invertebrate groups. Groups notnot yet yet covered covered in inANHAT ANHAT are notnot included included in in the the list. list. • The data used come from authoritative sources, but they are not perfect. All species names have been confirmed as valid species names, but it is not possible to confirm all species locations.
    [Show full text]
  • Native Trees and Shrubs for Seaside Areas
    NATIVE TREES & SHRUBS RECOMMENDED FOR SEASIDE AREAS NOOSA & DISTRICT LANDCARE GROUP STATION STREET, POMONA PH: 5485 2468 PLANTS SUITABLE FOR SEASIDE AREAS This list has been prepared as a guide to the selection of trees and shrubs suitable for planting on the coastal areas of Queensland. Most species are available from Noosa Landcare’s nurseries. Others listed are generally available from nurseries specializing in native plants. The problems of seaside plantings are mainly concerned with salt-laden winds which burn the foliage of tender plants. For such exposed sites the following plants will provide a resistant windbreak. SPECIES COMMON NAME (SHRUBS – Up to 5 metres) Acacia podalryiifolia Queensland silver wattle Acacia spectabilis Glory or Mudgee wattle Acacia suaveolens Sweet wattle Alectryon coriaceous Beach bird’s eye Baeckea frutescens Weeping baeckea Banksia ericiifolia Heath-leaved banksia Banksia oblingifolia Dwarf banksia Banksia spinulosa var. spinulosa Spiny-leaved honeysuckle Banksia spinulosa var. collina Hair-pin banksia Callistemon citrinus Crimson bottlebrush Callistemon pachyphyllus Wallum bottlebrush Callistemon rigidus Stiff bottlebrush Grevillea banksii Bank’s grevillea Hakea sericea White hakea Leptospermum brachyandrum Weeping tea-tree Leptospermum laevigatum Coast tea-tree Leptospermum petersonii Lemon-scented tea-tree Leptospermum polygalyfolium Wild may Melaleuca armillaris Bracelet honey myrtle Melaleuca alternifolia Paperbark Melaleauca bracteata River tea-tree Melaleuca nodosa Prickly-leaved paperbark Petalostigma
    [Show full text]
  • Swamp Sclerophyll Forest on Coastal Floodplains
    Where fire has been excluded for long periods in Swamp Sclerophyll Forest, it may contain many species typical of the EEC, Littoral Rainforest, and on the NSW North Coast where substrates are volcanically derived it may adjoin with the EEC, Swamp Sclerophyll Forest Lowland Rainforest on Floodplains. Lucas McKinnon Determining the on Coastal Floodplains conservation value of remnants Introduction The degree of disturbance (i.e. the site condition) These guidelines provide background information of any remnant of Swamp Sclerophyll Forest may to assist land managers and approval authorities vary dependant on past land use, management Swamp Sclerophyll Forest in Wollongong LGA, showing the to identify remnants of Swamp Sclerophyll Forest practices and/or natural disturbance and this Lucas McKinnon transition between 3 components of the community, reedland, on Coastal Floodplains (hereafter referred to should be considered at the time of assessment. shrubland and sclerophyll forest. as Swamp Sclerophyll Forest), an Endangered Whilst not exhaustive, the following are a Ecological Community (EEC). For more detailed number of variations of Swamp Sclerophyll Forest information refer to the Swamp Sclerophyll Forest you may encounter: Profile and the NSW Scientific Committee Final It is important to take these factors into account Determination at: 1. Tree canopy intact with limited native when determining the conservation significance threatenedspecies.environment.nsw.gov.au vegetation in the understorey due to of remnants. underscrubbing, stock grazing pressure or too What is an Endangered Paperbark Forest on the NSW North Coast, a component frequent fire; For further assistance Ecological Community? of Swamp Sclerophyll Forest 2. Tree canopy intact (+/– reduced cover) with This and other EEC guidelines are available limited native vegetation in the understorey on DECC Threatened Species website: An ecological community is an assemblage dense and the community takes on the structure due to lack of fire or weed infestation (e.g.
    [Show full text]
  • Native Plants of Sydney Harbour National Park: Historical Records and Species Lists, and Their Value for Conservation Monitoring
    Native plants of Sydney Harbour National Park: historical records and species lists, and their value for conservation monitoring Doug Benson National Herbarium of New South Wales, Royal Botanic Gardens, Mrs Macquaries Rd, Sydney 2000 AUSTRALIA [email protected] Abstract: Sydney Harbour National Park (lat 33° 53’S; long 151° 13’E), protects significant vegetation on the harbour foreshores close to Sydney City CBD; its floristic abundance and landscape beauty has been acknowledged since the writings of the First Fleet in 1788. Surprisingly, although historical plant collections were made as early as1802, and localised surveys have listed species for parts of the Park since the 1960s, a detailed survey of the flora of whole Park is still needed. This paper provides the first definitive list of the c.400 native flora species for Sydney Harbour National Park (total area 390 ha) showing occurrence on the seven terrestrial sub-regions or precincts (North Head, South Head, Dobroyd Head, Middle Head, Chowder Head, Bradleys Head and Nielsen Park). The list is based on historical species lists, records from the NSW Office of Environment and Heritage (formerly Dept of Environment, Climate Change and Water) Atlas, National Herbarium of New South Wales specimen details, and some additional fieldwork. 131 species have only been recorded from a single precinct site and many are not substantiated with a recent herbarium specimen (though there are historical specimens from the general area for many). Species reported in the sources but for which no current or historic specimen exists are listed separately as being of questionable/non-local status.
    [Show full text]
  • Sydenham to Bankstown Environmental Impact Statement
    SYDENHAM TO BANKSTOWN ENVIRONMENTAL IMPACT STATEMENT > Technical Paper 9 - Biodiversity assessment report Transport for NSW Sydney Metro City & Southwest Sydenham to Bankstown upgrade Environmental Impact Statement Technical Paper 9 – Biodiversity Assessment Report August 2017 Table of contents 1. Introduction..................................................................................................................................... 1 1.1 Overview .............................................................................................................................. 1 1.2 The project ........................................................................................................................... 2 1.3 Purpose and scope of this report ....................................................................................... 12 1.4 Secretary’s environmental assessment requirements ....................................................... 13 1.5 Legislation and policy......................................................................................................... 14 2. Methodology ................................................................................................................................. 17 2.1 Approach ............................................................................................................................ 17 2.2 Desktop research ............................................................................................................... 17 2.3 Field survey .......................................................................................................................
    [Show full text]
  • EA App. K Veg Management
    DRAFT VEGETATION MANAGEMENT PLAN EXTENSION OF SAND QUARRY CLEARY BROS (BOMBO) GERROA A report prepared by KEVIN MILLS & ASSOCIATES PTY LIMITED SEPTEMBER 2006 06/04/2 DRAFT VEGETATION MANAGEMENT PLAN EXTENSION OF SAND QUARRY CLEARY BROS (BOMBO) GERROA a report prepared by KEVIN MILLS & ASSOCIATES ECOLOGICAL AND ENVIRONMENTAL CONSULTANTS 114 NORTH CURRAMORE ROAD JAMBEROO NSW 2533 ABN 346 816 238 93 for CLEARY BROS (BOMBO) PTY LIMITED PO BOX 210 PORT KEMBLA NSW 2505 September 2006 06/04/2 Kevin Mills & Associates Pty Limited ACN 003 441 610 as trustee for Kevin Mills & Associates Trust COPYRIGHT © Kevin Mills & Associates 2006 All intellectual property and copyright reserved. Apart from any fair dealing for the purpose of private study, research, criticism or review, as permitted under the Copyright Act, 1968, no part of this report may be reproduced, transmitted, stored in a retrieval system or updated in any form or by any means (electronic, mechanical, photocopying, recording or otherwise) without written permission. Enquiries should be addressed to Kevin Mills & Associates. Kevin Mills & Associates Draft Vegetation Management Plan i Cleary Bros (Bombo) Quarry, Gerroa VEGETATION MANAGEMENT PLAN EXTENSION OF SAND QUARRY CLEARY BROS (BOMBO) GERROA CONTENTS 1 INTRODUCTION ................................................................................................... 1 2 THE PROJECT AREA .......................................................................................... 1 3 EXISTING VEGETATION AND HABITATS.........................................................
    [Show full text]
  • Vegetation of Imbota and Yina Nature Reserves, Armidale, New South Wales
    Vegetation of Imbota and Yina Nature Reserves, Armidale, New South Wales John T. Hunter School of Behavioural, Cognative and Social Sciences, University of New England, Armidale, NSW 2351 AUSTRALIA Email: [email protected] Abstract: The vegetation of Imbota Nature Reserve (30° 35’S, 151° 45’E) (218 ha in area), 10 km south-east of Armidale, and Yina Nature Reserve (30° 29’S, 151° 45’E), (101 ha in area), 10 km east of Armidale, on the Northern Tablelands, NSW, is described. Based on classification analyses, air photo interpretation and ground-truthing, seven vegetation communities are described and mapped : 1. Eucalyptus caliginosa (Broad-leaved Stringybark) Grassy Forest and Woodland on deep soils at Imbota 2. Eucalyptus viminalis (Manna Gum) Grassy Forest and Woodland, Community 3. Eucalyptus caliginosa (Broad-leaved Stringybark) Grassy Forest and Woodland on shallow soils at Imbota 4. Eucalyptus caliginosa (Broad-leaved Stringybark) Grassy Forest and Woodland at Yina 5. Eucalyptus blakelyi (Blakely’s Red Gum) – Eucalyptus melliodora (Yellow Box) Woodland 6. Eucalyptus viminalis (Manna Gum) – Eucalyptus nova-anglica (New England Peppermint) Grassy Forest and Woodland 7. Riparian Herbfields 252 vascular plant taxa (from 59 families) were recorded from the two reserves, 179 species in Imbota NR, the larger reserve and 209 in Yina NR. The lower species richness at Imbota is likely to have resulted human disturbance rather than from overall habitat heterogeneity. Cunninghamia (2007) 10(2): 215–224 Introduction 1030 m. The eastern boundary is marked by Burying Ground Creek, a minor tributary of the Commissioners Waters, Imbota Nature Reserve (30° 35’S, 151° 45’E) and Yina that eventually flows into the Gara River and the eastern Nature Reserve (30° 29’S, 151° 45E’) lie 10 km to the fall of the Divide.
    [Show full text]
  • Cunninghamia : a Journal of Plant Ecology for Eastern Australia
    Benson & Howell, Cumberland Plain Woodland ecology then and now 631 Cumberland Plain Woodland ecology then and now: interpretations and implications from the work of Robert Brown and others Doug Benson and Jocelyn Howell Benson, Doug & Howell, Jocelyn (Plant Sciences Branch, Royal Botanic Gardens and Domain Trust, Mrs Macquaries Road, Sydney NSW 2000, Australia) 2002. Cumberland Plain Woodland ecology then and now: Interpretations and implications from the work of Robert Brown and others. Cunninghamia 7 (4): 631–650. (Paper presented at Robert Brown 200 conference.) By the time Robert Brown visited western Sydney (1802–1805), its vegetation was already beginning to be affected by settlers’ activities. The Cumberland Plain Woodland that occurred on the clay soils has now been extensively cleared and long-term management of remnants for species conservation is of high priority. Robert Brown’s collections in the area, together with descriptions by Atkinson, Cunningham and other writers, provide us with valuable information on the vegetation and its floristic composition. Supported by recent site monitoring at Mount Annan Botanic Garden at Campbelltown, we interpret this information in the light of current ecological knowledge and conclude that: • Woodland structure is variable in the short term; therefore seeking to conserve structure exactly as described in the historical literature is not necessarily appropriate. • While the historical literature provides evidence of the broad floristic composition of the Cumberland Plain area overall, it does not provide sufficient detail on individual sites; future management of specific sites must therefore be based on current data. • The evidence suggests relatively few species have become extinct overall, possibly because many species appear to be relatively long-lived, and have mechanisms to survive drought, fire and grazing, though not soil alteration.
    [Show full text]
  • TAXON:Melaleuca Alternifolia (Maiden & Betche) Cheel SCORE
    TAXON: Melaleuca alternifolia SCORE: 7.0 RATING: High Risk (Maiden & Betche) Cheel Taxon: Melaleuca alternifolia (Maiden & Betche) Cheel Family: Myrtaceae Common Name(s): narrow leaf paperbark Synonym(s): Melaleuca linariifolia var. alternifolia Maiden & Betche narrow leaf teatree teatree Assessor: Chuck Chimera Status: Assessor Approved End Date: 4 Apr 2019 WRA Score: 7.0 Designation: H(HPWRA) Rating: High Risk Keywords: Subtropical Tree, Essential Oil, Dense Stands, Wind-Dispersed, Coppices Qsn # Question Answer Option Answer 101 Is the species highly domesticated? y=-3, n=0 n 102 Has the species become naturalized where grown? 103 Does the species have weedy races? Species suited to tropical or subtropical climate(s) - If 201 island is primarily wet habitat, then substitute "wet (0-low; 1-intermediate; 2-high) (See Appendix 2) High tropical" for "tropical or subtropical" 202 Quality of climate match data (0-low; 1-intermediate; 2-high) (See Appendix 2) High 203 Broad climate suitability (environmental versatility) y=1, n=0 n Native or naturalized in regions with tropical or 204 y=1, n=0 y subtropical climates Does the species have a history of repeated introductions 205 y=-2, ?=-1, n=0 n outside its natural range? 301 Naturalized beyond native range y = 1*multiplier (see Appendix 2), n= question 205 n 302 Garden/amenity/disturbance weed n=0, y = 1*multiplier (see Appendix 2) n 303 Agricultural/forestry/horticultural weed n=0, y = 2*multiplier (see Appendix 2) n 304 Environmental weed n=0, y = 2*multiplier (see Appendix 2) n 305 Congeneric
    [Show full text]