MAY 2010
OAKAJEE PORT AND RAIL OAKAJEE TERRESTRIAL PORT DEVELOPMENT FLORA AND VEGETATION ASSESSMENT
This page has been left blank intentionally
OAKAJEE PORT AND RAIL OAKAJEE TERRESTRIAL PORT DEVELOPMENT FLORA AND VEGETATION ASSESSMENT
May 2010
Oakajee Port and Rail Oakajee Terrestrial Port Development: Flora and Vegetation Assessment
Document Status Approved for Issue Rev. Author Reviewer Date Name Distributed To Date R. Graham, C. Tauss, C. Slee, 1 J. Gilovitz, C. Cox 23 Feb 2009 C. Cox C. Miller 23 Feb 2009 C. Winton, M. Fulton, C. Cox C. Winton, 2 C. Cox 30 June 2009 T. Souster C. Miller 2 July 2009 C. Slee C. Winton, 3 C. Cox 30 June 2009 C. Cox C. Miller 3 August 2009 C. Cox 22 January 22 January 4 C. Macpherson C. Macpherson C. Miller 2010 2010 5 C. Macpherson T. Souster 19 February C. Macpherson C. Miller 19 February 6 M. Hay M. Hay 25 February T. Souster C. Miller 25 February 7 C. Macpherson T. Souster 20 April C. Macpherson C. Miller 20 April 2010 8 C. Macpherson T. Souster 18 May 2010 C. Macpherson Damien McAlinten 19 May 2010
ecologia Environment (2010). Reproduction of this report in whole or in part by electronic, mechanical or chemical means including photocopying, recording or by any information storage and retrieval system, in any language, is strictly prohibited without the express approval of Oakajee Port and Rail and/or ecologia Environment.
Restrictions on Use
This report has been prepared specifically for Oakajee Port and Rail. Neither the report nor its contents may be referred to or quoted in any statement, study, report, application, prospectus, loan, or other agreement document, without the express approval of Oakajee Port and Rail and/or ecologia Environment.
ecologia Environment 1025 Wellington Street WEST PERTH WA 6005 Phone: 08 9322 1944 Fax: 08 9322 1599 Email: [email protected]
May 2010 i
Oakajee Port and Rail Oakajee Terrestrial Port Development: Flora and Vegetation Assessment
TABLE OF CONTENTS
EXECUTIVE SUMMARY...... VIII 1 INTRODUCTION ...... 1 1.1 STUDY BACKGROUND ...... 1 1.2 LEGISLATIVE FRAMEWORK ...... 1 1.3 SURVEY OBJECTIVES...... 4 2 REGIONAL SETTING...... 5 2.1 CLIMATE ...... 5 2.2 GEOLOGY...... 7 2.3 GERALDTON SANDPLAINS BIOGEOGRAPHIC REGION...... 7 2.4 LANDFORMS...... 12 2.5 BEARD VEGETATION MAPPING...... 13 2.6 DISTRIBUTION OF NATIVE VEGETATION WITHIN THE AREAS SURVEYED ...... 15 2.7 PREVIOUS BIOLOGICAL SURVEYS IN THE STUDY AREA ...... 15 2.8 LAND USES IN THE SUBREGION ...... 16 2.9 LAND USE HISTORY ...... 16 3 SURVEY METHODS...... 19 3.1 DETERMINATION OF SURVEY SAMPLING DESIGN AND INTENSITY...... 19 3.2 VEGETATION AND FLORA SURVEY ...... 20 3.2.1 Flora Survey Sites...... 20 3.2.2 Vegetation Mapping...... 23 3.3 THREATENED FLORA SURVEY...... 23 4 VEGETATION...... 27 4.1 VEGETATION UNITS OF THE SURVEY AREA...... 27 4.2 VEGETATION CONDITION...... 39 5 FLORA...... 41 5.1 SAMPLING ADEQUACY...... 41 5.2 FLORA OF CONSERVATION SIGNIFICANCE...... 42 5.2.1 Statutory Framework...... 42 5.2.2 Priority Flora Previously Recorded Near the Study Area...... 42 5.2.3 DRF and Priority Flora Recorded During the Current Survey ...... 43
May 2010 ii
Oakajee Port and Rail Oakajee Terrestrial Port Development: Flora and Vegetation Assessment
5.3 SPECIES OF INTEREST ...... 53 5.4 INTRODUCED FLORA ...... 53 5.4.1 Weeds of National Significance ...... 53 5.4.2 Declared Plants...... 53 5.4.3 Introduced Flora within the Study Area ...... 54 5.5 SURVEY LIMITATIONS AND CONSTRAINTS...... 59 6 CONSERVATION SIGNIFICANCE ...... 61 6.1 FLORA...... 61 6.1.1 Flora of National Significance ...... 61 6.1.2 Flora of State Significance ...... 61 6.1.3 Flora of Regional Significance...... 65 6.1.4 Flora of Local Significance ...... 66 6.2 VEGETATION ...... 66 6.2.1 Vegetation of National Significance ...... 66 6.2.2 Vegetation of State Significance...... 66 6.2.3 Vegetation of Regional Significance ...... 70 6.2.4 Vegetation of Local Significance...... 74 7 STUDY TEAM...... 75 8 REFERENCES...... 77 FIGURES Figure 1.1 – Location of the Port Study Area ...... 3 Figure 2.1 – Summary of Climatic Data for Geraldton Port (Source BoM, 2009)...... 5 Figure 2.2 – Location of Geraldton Hills Subregion on the West Coast of Western Australia ...... 8 Figure 2.3 – Land Systems of the Study Area ...... 9 Figure 2.4 – Map of Landforms of the Geraldton Area from Playford et al. (1970)...... 13 Figure 2.5 – Vegetation of the Study Area (Beard and Burns 1976) ...... 14 Figure 2.6 – Conservation Reserves and Remnant Vegetation of the Study Area ...... 17 Figure 3.1 – Locations of Quadrats within the Study Area...... 22 Figure 3.2 – Location of Transects walked in the Study Area...... 25 Figure 4.1 – Distribution of Vegetation Units within the Study Area...... 37 Figure 5.1 – Species Accumulation Curve for Bounded Quadrats within the Study Area...... 42 Figure 5.2 – Location of Species of Conservation Significance recorded during ecologia surveys ...... 51
May 2010 iii
Oakajee Port and Rail Oakajee Terrestrial Port Development: Flora and Vegetation Assessment
Figure 5.3 – Distribution of Declared Weed Species Recorded within the Study Area...... 55 Figure 5.4 – Distribution of Non‐Declared Weed Species Recorded within the Study Area...... 57 TABLES
Table 2.1 – Climatic Averages for Geraldton Port Weather Station (008050) ...... 6
Table 2.2 – Rainfall Preceeding Surveys – Geraldton Airport Weather Station (008051)...... 6
Table 2.3 – Descriptions of Land Systems and Map Subunits Found within the Study Area (Dye et al, 1990)...... 10
Table 2.4 – Remnant Bushland within Surveyed Areas...... 15
Table 3.1 – Factors Likely to Influence Survey Design (EPA, 2004) ...... 19
Table 3.2 – Vegetation Structure Classification (adapted from Keighery, 1994) ...... 20
Table 3.3 – Proportion of the Total Area Surveyed for Threatened Flora ...... 23
Table 4.1 – Vegetation Units Mapped at the Sub‐association Level within the Study Area ...... 28
Table 4.2 – Vegetation Condition Scale (Keighery, 1994 cited in BushForever, 2000) ...... 39
Table 4.3 – Vegetation Condition at Each Bounded Quadrat Site...... 39
Table 5.1 – General Flora Statisitcs of the Study Area ...... 41
Table 5.2 – Conservation Significant Flora Recorded during the ecologia Survey ...... 43
Table 5.3 – Priority Flora Recorded During ecologia Surveys...... 44
Table 5.4 – Declared Weeds Recorded in the Study Area...... 54
Table 5.5 – Flora and Vegetation Survey Limitations...... 59
Table 6.1 – Priority Flora Recorded in the Study Area (All data sources)...... 62
Table 6.2 – Number of Plants Assumed for Records Where Only Descriptions or % Cover Available...63
Table 6.3 – Conservation Significant Flora Recorded Within the Study Area (All Data Sources)...... 64
Table 6.4 – Flora of Conservation Significance Recorded in the Study Area Which Are At Least 85% Endemic to the Bioregion ...... 65
Table 6.5 – Species Recorded within the Study Area which are Range Extensions of Previously Known Range ...... 65
Table 6.6 – Distribution of Locally Restricted Conservation Signifcant Species in Local Reserves ...... 66
Table 6.7 – Representation of Beard Vegetation Units Within the State, Conservation Reserves, Geraldton Sandplains Region and the Study Area...... 68
Table 6.8 – Comparison of Vegetation Units mapped in the Oakajee Study AreaDuring the Current Study and the GRFVS ...... 72
May 2010 iv
Oakajee Port and Rail Oakajee Terrestrial Port Development: Flora and Vegetation Assessment
APPENDICES
Appendix A SUMMARY OF PREVIOUS STUDIES...... 81
Appendix B FLORISTIC QUADRAT DATA...... 87
Appendix C VASCULAR PLANT SPECIES INVENTORY ...... 111
Appendix D DEFINITIONS OF CONSERVATION CODES ...... 123
Appendix E RARE AND PRIORITY FLORA SEARCH RESULTS...... 127
Appendix F LOCATIONS OF FLORA OF CONSERVATION SIGNIFICANCE RECORDED DURING ECOLOGIA SURVEYS...... 133
Appendix G WEEDS RECORDED WITHIN THE OAKAJEE STUDY AREA...... 161
Appendix H WESTERN AUSTRALIA DECLARED WEED CATEGORIES & WEEDS KNOWN TO OCCUR IN GERALDTON REGION ...... 169
Appendix I SPECIES RECORDED IN THE OAKAJEE STUDY AREA WHICH ARE ENDEMIC OR MORE THEN 85% ENDEMIC TO GERALDTON SANDPLAINS ...... 175
May 2010 v
Oakajee Port and Rail Oakajee Terrestrial Port Development: Flora and Vegetation Assessment
ACRONYMS
List all acronyms used in the report here. Format alphabetically as follows:
BOM Bureau of Meteorology
DEC Department of Environmental Conservation
DAFWA Department of Agriculture and Food Western Australia
DEWHA Department of the Environment, Water, Heritage and the Arts
EPA Environmental Protection Authority
EPBC Act Environment Protection and Biodiversity Conservation Act 1950
IBRA Interim Biogeographic Regionalisation for Australia
OPR Oakajee Port and Rail
PEC Priority Ecological Community
TEC Threatened Ecological Communities
WC Act Wildlife Conservation Act 1950
May 2010 vi
Oakajee Port and Rail Oakajee Terrestrial Port Development: Flora and Vegetation Assessment
GLOSSARY
Approved Port:
The deepwater port facility at Oakajee for which the Department of State Development is the proponent. This Proposal was approved by the WA Government in 1998, with the release of Ministerial Statement 469 (Approved Port), and more recently updated with an approved Section 46.
Conservation Significant:
This term is applied to species which are protected under the Environment Protection and Biodiversity Conservation Act 1999, the Wildlife Conservation Act 1950, or are listed by the Department of Environment and Conservation as priority fauna.
Oakajee Port and Rail Development:
The larger OPR proposal comprising the marine port, terrestrial port and rail components, each the subject of a separate approvals process.
The Proposal Area:
The Proposal refers to the footprint of this development as outlined in the PER.
Study Area:
An area larger than the proposal area, surveyed for the purpose of biological studies. The area may generally be described as extending approximately 12 km along the coast (between the Oakajee and Buller Rivers) and approximately 7 km inland at its widest point.
Priority Ecological Community (PEC):
Possible threatened ecological communities that do not meet survey criteria are added to DEC’s Priority Ecological Community Lists under Priorities 1, 2 and 3. Ecological Communities that are adequately known, are rare but not threatened, or meet criteria for Near Threatened, or that have been recently removed from the threatened list, are placed in Priority 4. These ecological communities require regular monitoring. Conservation Dependent ecological communities are placed in Priority 5.
Threatened ecological community (TEC):
A TEC is one which is found to fit into one of the following categories; “presumed totally destroyed”, “critically endangered”, “endangered” or “vulnerable”.
May 2010 vii
Oakajee Port and Rail Oakajee Terrestrial Port Development: Flora and Vegetation Assessment
EXECUTIVE SUMMARY
OPR proposes to construct a deepwater port and terrestrial iron‐ore handling facilities at Oakajee. The site is located 24 km north of Geraldton, within the proposed Oakajee Industrial Estate, between the Oakajee and Buller Rivers. The terrestrial facilities proposed include the port rail system, access and service corridors, a car dumper, stockpiles, ore in‐loading and out‐ loading infrastructure, and supporting facilities.
OPR commissioned ecologia Environment (ecologia) to undertake a single phase Level 2 survey of the vegetation and flora of the Oakajee study area and surrounds. The surveyed area of 4,743 ha (hereafter referred to as the Study Area) extends for approximately 12 km along the coast and approximately 7 km inland at its widest point.
Following the single phase survey a follow‐up threatened flora survey, targeting conservation significant flora taxa located during the initial survey, was carried out over the Study Area and an additional area of 267 ha directly to the south of the Study Area.
The primary objective of these surveys was to provide sufficient information to the Environmental Protection Authority (EPA) to assess the impact of the development on the vegetation and flora of the area. The EPA’s objectives with regards to management of native flora and vegetation are to: • Avoid adverse impacts on biological diversity comprising the different plants and the ecosystems they form at the levels of genetic, species and ecosystem diversity.
• Maintain the abundance, species diversity, geographic distribution and productivity of vegetation communities.
• Protect Declared Rare Flora (DRF) consistent with the provisions of the Wildlife Conservation Act 1950.
• Protect other flora species of conservation significance.
The single phase Level 2 survey was carried out in August 2006 and the threatened flora survey was carried out in March 2009. Systematic and opportunistic sampling methods were used during the vegetation and flora survey and 21 quadrats were assessed over the Study Area. Relevees were also walked through some areas and 14 vegetation units at the sub association level were described and mapped over the Study Area.
The Study Area lies in the Geraldton Sandplains Biogeographic Region of the Interim Biogeographic Regionalisation for Australia (IBRA). The Geraldton Sandplains IBRA region is further subdivided into the Edel, Geraldton Hills and Lesueur Sandplain subregions. The Oakajee Study Area occurs in the Geraldton Hills subregion.
The Oakajee Port Study Area lies within an area of coastal vegetation mapped by Beard and Burns as the Greenough System. The Greenough vegetation system is characterised by a coastal limestone belt extending from Kalbarri to Dongara. Beard and Burns mapped five vegetation types within the Study Area: sparsely vegetated drift sand; Banksia woodland and Acacia scrub; Acacia ligulata open scrub; mixed (Melaleuca, Hakea) thicket; and Jam scrub with York Gum.
May 2010 viii
Oakajee Port and Rail Oakajee Terrestrial Port Development: Flora and Vegetation Assessment
Vegetation
Fourteen vegetation sub‐associations were mapped within the Study Area by ecologia.
1. Olearia axillaris low open shrubs, Spinifex longifolius hummock grasses. 2. Juncus kraussii closed sedgeland. 3. Acacia rostellifera – Stylobasium spathulatum – Tetragonia implexicoma – Acanthocarpus preissii open to closed medium to low scrub. 4. Acacia xanthina – Melaleuca cardiophylla (+/‐ Grevillea argyrophylla) closed scrub. 5. Melaleuca cardiophylla – Grevillea argyrophylla scrub or heath (sometimes with Eucalyptus dolichocera mallee and Diplolaena grandiflora scrub). 6. Banksia prionotes (+/‐ Banksia menziesii) open scrub. 7. Eucalyptus camaldulensis ‐ Casuarina obesa low closed forest. 8. Grevillea ‐ Melaleuca and other low shrubs over Borya sphaerocephala mats on laterite/sandstone. 9. Acacia acuminata sparse low trees over A. tetragonophylla shrubs. 10. Tall shrubs of Grevillea – Melaleuca ‐ Acacia spp. over species rich open heath. 11. Melaleuca cardiophylla – Grevillea argyrophylla dense tall heath. 12. Acacia xanthina mid to tall dense scrub. 13. Acacia rostellifera tall dense scrub. 14. Eucalyptus spp. mixed revegetation on previously disturbed land. Areas of bare sand and disturbed agricultural land were also mapped.
The majority of the Study Area comprises areas of disturbed grazing and farmland, as well as large areas of remnant and regrown native vegetation. Most of the intact native vegetation at Oakajee occurs adjacent to the coastline and alongside the Oakajee and Buller Rivers. Smaller areas of fragmented native vegetation also occur within larger areas of cleared farmland. The majority of the sand plain area has been cleared in the past and is now used for pastoral purposes.
Database searches indicate that no threatened ecological communities (TEC) or priority ecological communities (PEC) occur in the area.
Flora
A total of 372 vascular flora taxa (including 43 naturalised alien taxa or weeds), from 74 families, was recorded during the two surveys carried out by ecologia at the Oakajee Study Area.
Eleven priority flora taxa were recorded during the two surveys carried by ecologia. One additional Priority 1 taxon, Leucopogon psammophilus, was recorded outside the Study Area immediately adjacent to the eastern boundary and is not discussed further in this document. An additional four taxa have previously been recorded within the Study Area by other surveys. Hence the total number of Priority Flora that has been recorded within the Study Area is 15.
May 2010 ix
Oakajee Port and Rail Oakajee Terrestrial Port Development: Flora and Vegetation Assessment
Forty three weed species were recorded during the surveys by ecologia. A further 18 species were recorded in previous surveys, bringing the total number of weeds to 61. One species, Tamarix aphylla, is identified as a weed of national significance (WONS). Four species (Carthamus lanatus, Datura wrightii, Echium plantagineum and Tamarix aphylla) are listed as Declared Weeds in Western Australia. Conservation Significance
The significance of the vegetation and flora of the Study Area has been assessed at four spatial scales: national, state, regional and local.
At a national level, there are no vegetation units of conservation significance. The mallee tree Eucalyptus blaxellii, which is known from three locations within the Study Area, is currently listed as “Vulnerable” under the Environment Protection and Biodiversity Conservation Act 1950 (EPBC Act) and is therefore of national significance. Recent surveys have considerably expanded the number of populations of this species such that its status under state legislation has been revised from DRF to Priority 4. It is likely that its status under the EPBC Act will also be revised.
At a state level the 14 Priority Flora recorded within the Study Area are of significance. There are no TEC or PEC within the Study Area and hence no vegetation of state significance.
At a regional level vegetation types are considered significant if endemic to the Geraldton Sandplains Bioregion or if the distributions are limited or unknown. The mapping by Beard at 1:1,000,000 is the only source of mapping available for the whole of the bioregion and hence is the only means of quantifying the regional representation. Units 440 (Acacia ligulata open shrub), 359 (Banksia woodland and Acacia scrub), Unit 35 (Acacia acuminata with Eucalyptus loxophleba) and 675 (Mixed Melaleuca, Hakea thicket), constituting 21.0%, 49.0%, 11.8% and 0.4% of the native vegetation within the Study Area respectively, are all highly or entirely confined to the Geraldton Sandplains bioregion and indeed the Geraldton Hills (GS2) subregion.
Of the units present, only Unit 129, sparsely vegetated drift sand, is well represented in conservation reserves (53.3%). Unit 35, Jam scrub with York Gum, is the most heavily cleared unit (only 17% of pre‐European extent remaining) and has only 2.4% of its remaining areas within reserves. Units 359 and 675, with 25% and 27% respectively of pre‐European extent and <0.01% and 2.5% respectively within reserves are also regionally vulnerable and inadequately reserved.
A total of 18 taxa recorded within the survey area have distributions entirely within the bioregion, and a further 20 taxa have distributions that are at least 85% within the bioregion, equating to 11% of the total species inventory. Twelve of the fifteen flora of conservation status recorded within the study are currently known entirely or almost entirely from the Geraldton Sandplains Bioregion. Current records at the WA Herbarium indicate that four species have distributions less than 100 km in breadth. The taxon Lepidosperma sp. Moresby Range (P1) appears to be highly restricted, with a distribution confined to approximately 20 km. As the area has been relatively well surveyed over the years, it is highly likely to be locally endemic.
Vegetation and flora species are of local significance when their presence is confined to a specialised habitat type that is not common in the local area and whose disturbance or removal may lead to local extinction.
The Oakajee coastal vegetation is considered significant at a local level by virtue of its size and condition. No coastal conservation reserves and virtually no intact coastal vegetation exist in the vicinity of Geraldton. Hence the Study Area is one of only a few large areas of vegetation f(o any
May 2010 x
Oakajee Port and Rail Oakajee Terrestrial Port Development: Flora and Vegetation Assessment type) in good to excellent condition remaining. The locally‐uncommon and dense coastal limestone ridge and sand dune vegetation provides significant refuge and habitat for fauna. The vegetation of the Moresby Ranges (to the east of the Study Area) is highly fragmented but includes species‐rich mallee, heath and scrub assemblages. The Oakajee River forms a corridor between the intact coastal habitats and the diverse habitats of the Moresby Range to the east.
May 2010 xi
Oakajee Port and Rail Oakajee Terrestrial Port Development: Flora and Vegetation Assessment
1 INTRODUCTION
1.1 STUDY BACKGROUND
OPR proposes to construct a deepwater port and terrestrial iron‐ore handling facilities at Oakajee. The site is located 24 km north of Geraldton, within the proposed Oakajee Industrial Estate, between the Oakajee and Buller Rivers (Figure 1.1). The terrestrial facilities proposed include the port rail system, access and service corridors, a car dumper, stockpiles, ore in‐loading and out‐loading infrastructure, and supporting facilities.
OPR commissioned ecologia Environment (ecologia) to undertake a single phase Level 2 survey of the vegetation and flora of the Oakajee Study Area and surrounds. The surveyed area of 4,743 ha (hereafter referred to as the Study Area) extends for approximately 12 km along the coast and approximately 7 km inland at its widest point.
Following the single phase survey a follow‐up threatened flora survey, targeting conservation significant flora taxa located during the initial survey, was carried out over the Study Area and an additional area of 267 ha directly to the south of the Study Area.
1.2 LEGISLATIVE FRAMEWORK
Federal and state legislation applicable to the conservation of native flora and fauna includes, but is not limited to, the Environment Protection and Biodiversity Conservation Act 1999 (EPBC Act), the Wildlife Conservation Act 1950 (WC Act) and the Environmental Protection Act 1986 (EP Act).
Section 4a of the EP Act requires that developments take into account the following principles applicable to native flora: • The Precautionary Principle Where there are threats of serious or irreversible damage, lack of full scientific certainty should not be used as a reason for postponing measures to prevent environmental degradation. • The Principles of Intergenerational Equity The present generation should ensure that the health, diversity and productivity of the environment is maintained or enhanced for the benefit of future generations. • The Principle of the Conservation of Biological Diversity and Ecological Integrity Conservation of biological diversity and ecological integrity should be a fundamental consideration.
Furthermore, biological surveys undertaken as part of the Environmental Impact Assessment (EIA) process are required to address the following: • Environmental Protection Authority’s (EPA’s) Position Statement No. 3: Terrestrial Biological Surveys as an Element of Biodiversity Protection (EPA, 2002), and • Guidance Statement No. 51: Terrestrial Flora and Vegetation Surveys for Environmental Impact Assessment in Western Australia (EPA, 2004a).
Native flora in Western Australia is protected at a Federal level under the EPBC Act and at a State level under the WC Act.
May 2010 1
Oakajee Port and Rail Oakajee Terrestrial Port Development: Flora and Vegetation Assessment
The EPBC Act was developed to provide for the protection of the environment, especially those aspects of the environment that are matters of national environmental significance, to promote ecologically sustainable development through the conservation and ecologically sustainable use of natural resources; and to promote the conservation of biodiversity. The EPBC Act includes provisions to protect native species (and in particular, to prevent the extinction and promote the recovery of threatened species). In addition to the principles outlined in Section 4a of the EP Act, Section 3a of the EPBC Act includes the principle of ecologically sustainable development, dictating that decision‐ making processes should effectively integrate both long‐term and short‐term economic, environmental, social and equitable considerations.
The WC Act was developed to provide for the conservation and protection of wildlife in Western Australia. Under Section 14 of this Act, all fauna and flora within Western Australia are protected; however, the Minister may, via a notice published in the Government Gazette, declare a list of flora taxa identified as likely to become extinct, or as rare, or otherwise in need of special protection. The current listing was gazetted on the 5 August 2008 (Wildlife Conservation, 2008(2)).
May 2010 2
Oakajee Port and Rail Oakajee Terrestrial Port Development: Flora and Vegetation Assessment
Figure 1.1 – Location of the Port Study Area
May 2010 3
Oakajee Port and Rail Oakajee Terrestrial Port Development: Flora and Vegetation Assessment
1.3 SURVEY OBJECTIVES
OPR commissioned ecologia Environment (ecologia) to undertake a baseline biological survey of the vegetation and flora of the Oakajee area as part of the EIA for the Port development.
The EPA’s objectives with regards to management of native flora and vegetation are to: • Avoid adverse impacts on biological diversity comprising the different plants and animals and the ecosystems they form, at the levels of genetic, species and ecosystem diversity;
• Maintain the abundance, species diversity, geographic distribution and productivity of vegetation communities;
• Protect Declared Rare Flora (DRF) consistent with the provisions of the WC Act 1950; and
• Protect other flora species of conservation significance.
Therefore, the primary objective of this study was to provide sufficient information to the EPA to assess the impact of the Port development on the vegetation and flora of the area, to allow these objectives to be upheld.
The survey was designed to satisfy the requirements documented in EPA’s Guidance Statement 51 (2004a) and Position Statement No. 3 (2002), thus providing: • A review of background information (including literature and database searches).
• An inventory of vegetation types and flora species occurring in the Study Area, incorporating recent published and unpublished records.
• An inventory of species of biological and conservation significance recorded or likely to occur within the development footprint and surrounds.
• A map and detailed description of vegetation types and vegetation condition of the Study Area.
• A description of the characteristics of the vegetation types.
• An appraisal of the current knowledge base for the area, including a review of previous surveys relevant to the current study.
• A review of regional and biogeographical significance, including the conservation status of species recorded in the Study Area.
May 2010 4
Oakajee Port and Rail Oakajee Terrestrial Port Development: Flora and Vegetation Assessment
2 REGIONAL SETTING
2.1 CLIMATE
Climate data for the Oakajee Study Area is based on records from the weather station located at Geraldton Port (Figure 2.1). The Geraldton region experiences a Mediterranean‐type climate, characterised by hot, dry summers and mild, wet winters. The mean annual rainfall is 448.7 mm, three quarters of which falls in winter between May and August. This is a result of the northward movement of the sub‐tropical ridge. Rain falls on an average 40.8 days annually and the wettest month is July. The summer months are characteristically dry, with December and January receiving an average of approximately 9.6 mm of rain. These months are also influenced by the tropical cyclone period which occasionally brings heavy localised rainfall to the area. Geraldton is affected by cyclones approximately once every six to eight years.
Figure 2.1 – Summary of Climatic Data for Geraldton Port (Source BoM, 2009)
Mean maximum temperatures range from 29.7°C in summer to 19.8°C in winter, and mean minimum temperatures range from 10.5°C in winter to 18.8°C in summer (Table 2.1). Seasonal extremes can occur from north‐easterly winds moving across the arid‐interior of the state bringing very hot summer days and cold fronts moving across the Southern Ocean bringing windy, winter days. The highest maximum temperatures can reach 46.4°C in summer and 35.8°C in winter, while the lowest minimum temperatures are approximately 10.6°C in summer and 0.8°C in winter.
May 2010 5
Oakajee Port and Rail Oakajee Terrestrial Port Development: Flora and Vegetation Assessment
Table 2.1 – Climatic Averages for Geraldton Port Weather Station (008050) J F M A M J J A S O N D Annual Mean Rainfall (mm) 5.9 8.5 13.1 23.8 69.4 114.3 91.0 65.1 30.5 17.7 7.7 3.7 448.7 Mean daily max. temp (°C) 29.1 29.7 28.8 26.6 23.2 20.8 19.8 20.4 21.7 23.0 25.5 27.5 24.7 Mean daily min. temp (°C) 18.4 18.8 17.8 15.7 13.3 11.8 10.5 10.8 11.4 12.6 15.1 16.9 14.4 Mean 9 am relative humidity (%) 59 60 60 60 67 71 72 69 64 60 58 59 63 Mean 3 pm relative humidity (%) 64 63 62 61 60 62 62 61 61 61 62 64 62 Mean 9 am wind speed (km/hr) 14.4 13.9 13.5 12.5 12.6 14.1 13.9 13.5 13.3 13.7 15.4 15.2 13.8 Mean 3 pm wind speed (km/hr) 18.9 18.3 16.5 14.5 13.6 14.3 14.7 14.9 15.6 17.7 19.6 20.4 16.6 Mean no. of rain days 0.6 0.8 1.2 2.5 5.3 7.6 7.7 6.4 4.1 2.7 1.3 0.6 40.8 Highest monthly rainfall (mm) 96.3 116.6 169.1 116.1 328.2 328.2 205.3 241.7 104.9 85.2 49.7 32.0 Source: Bureau of Meteorology, 2009 (Lat 28.78° S, Long 114.16° E; Data from 1877 until (last record 2009); Elevation 3.0 m) Note: numbers in red font indicate highest records and numbers in blue font lowest records. Total rainfall in the three months preceding the August 2006 vegetation and flora survey was 75.0 mm (Table 2.2), which is much lower than the long‐term mean total for the same three months (275.6 mm). Total rainfall in the three months preceding the threatened flora mapping survey was 4.4 mm, which is less than the long‐term mean total for the same three months (26.1 mm).
Table 2.2 – Rainfall Preceeding Surveys – Geraldton Airport Weather Station (008051) Year J F M A M J J A S O N D Total Monthly Rainfall (mm) 2006 26 3.8 0 6.4 9.6 5.8 59.6 50.4 18.8 7.4 3.2 6.4 2007 3 1.2 0.6 7.2 20 25.4 65.6 49.6 22.8 20.2 0.8 14.6 2008 0 34.6 6.6 53.2 14.2 63.4 108.4 7.6 38.4 14 3.6 3.4 2009 0.4 0.6 0.4 1.2 40.4 117.4 91.4 65.2 43.8 10.4 16.8 0.4 Average Monthly Rainfall (mm) (1961 to 2009) 7.0 14.3 18.5 25.0 75.3 111.9 88.4 66.5 31.7 20.0 12.0 4.8 Source: Bureau of Meteorology, 2010 (Lat 28°48'43"S, Long 114°42'51"E; Data from 1877 until (last record 2009); Elevation 3.0 m) Note: Data in bold denotes months when surveys were conducted. As rainfall data for the Geraldton Port is incomplete for the period of interest, data from the Geraldton Airport approximately 9.2 km from the Geraldton Port has been utilised.
May 2010 6
Oakajee Port and Rail Oakajee Terrestrial Port Development: Flora and Vegetation Assessment
2.2 GEOLOGY
The Geraldton region incorporates the southern end of the Carnarvon Basin and the northern end of the Perth Basin, with exposed areas of Permian/Silurian siltstone and Jurassic sandstones, mostly overlain by sand plains, alluvial plains and coastal limestone (Desmond and Chant, 2001). Sandy earths of an extensive, undulating, lateritic sandplain mantling Permian to Cretaceous strata, underlain by Phanerozoic sediments also occur in the region (Desmond and Chant, 2001).
The geology of the Oakajee area has been described by Playford et al. (1970). Oakajee lies on the coastal belt of limestone and sand dunes which have developed along the coast north and south of Geraldton. The coastal limestone belt forms hills up to 130 m high, and extends up to 8 km inland.
The main formations in the Oakajee area are: • dune and beach sands of white calcareous and quartzose sands; and
• coastal limestone and overlying podsolic sand of eolianite and leached quartz sands.
Smaller areas of laterite and associated sand and underlying highly weathered rocks also occur. The sand represents the eluvial soil horizon of the laterite profile.
Large areas of granulite, a unit of the Northampton Block which has the oldest rocks, are found in the area and the granulites are predominantly metasedimentary.
Jurassic sediments occur widely throughout the eastern side of the Study Area and form the Champion Bay Group, comprising Kojarena Sandstone, Newmarracarra Limestone, Bringo Shale and Colalura Sandstone.
2.3 GERALDTON SANDPLAINS BIOGEOGRAPHIC REGION
The Study Area lies in the Geraldton Sandplains Biogeographic Region of the Interim Biogeographic Regionalisation for Australia (IBRA) (Environment Australia, 2007). The Geraldton Sandplains IBRA region is further subdivided into the Edel, Geraldton Hills and Lesueur Sandplain Subregions (Figure 2.2). The Oakajee Study Area occurs in the Geraldton Hills subregion (GS2).
The Geraldton Hills subregion incorporates the southern end of the Carnarvon Basin and the northern end of the Perth Basin. This subregion is described by Desmond and Chant (2001) as Permian/Silurian siltstone and Jurassic sandstones, mostly overlain by sandplains, alluvial plains, and coastal limestone. Typical vegetation of the area includes sand heaths with emergent Banksia and Actinostrobus, York Gum woodlands on alluvial plains, proteaceous heath and Acacia scrubs on limestone, depending on the depth of the coastal‐sand mantle (Desmond and Chant, 2001). This subregion also includes the Pinjarra Orogen which is an area of hill country with a Proterozoic basement, and comprises extensive, undulating, lateritic uplands mantled in sandplain supporting proteaceous shrublands and mallees while valleys support York Gum.
Currently, 515 Priority Flora taxa are listed on FloraBase as occurring in the Geraldton Sandplains Bioregion (Western Australian Herbarium, June 2009).
May 2010 7
Oakajee Port and Rail Oakajee Terrestrial Port Development: Flora and Vegetation Assessment
Figure 2.2 – Location of Geraldton Hills Subregion on the West Coast of Western Australia
Dye et al. (1990) conducted a soil and landform inventory of the area immediately around Geraldton, south from Coronation Beach to Cape Burney along the coast, 13.7 km inland in the north and 7.6 km inland to the south. Eight land systems were described with each further divided into map units based on landform, soil type and drainage.
Figure 2.3 shows the land systems mapped within the Study Area (Dye et al,. 1990). Descriptions of the land system units and the map unit subdivisions are provided in Table 2.3. The Quindalup and Tamala Limestone Land Systems have been mapped over most of the Study Area.
May 2010 8
262000 264000 266000 268000 270000 221Ta_2 225No_2 225No_1 225Mo_2 225Mo_1Mss
225Mo_2Mf1
Ñ Ñ Ñ Ñ Ñ 6840000 225Mo_2Mf2 221Qu_1Qs1
221Qu_1Qp1 221Ta_2Tst
Ñ Ñ Ñ Ñ Ñ
6838000 221Ta_5Tb
225No_1R 225No_1GrR
225No_2An1 225No_1GrD 225No_2Af
221Qu_1Qp2 Ñ Ñ Ñ Ñ 225No_1GrSÑ 6836000
221Ta_5Tr
221QuX_BEACH 225No_1Dr Ñ Ñ 221Qu_1Qm Ñ Ñ Ñ 6834000 221Ta_3Ysp
221Ta_5Ts Ñ Ñ 221Qu_1Qf221Qu_1Qs2Ñ Ñ Ñ 6832000
225NoX_MINE
Ñ Ñ Ñ Ñ Ñ 6830000 K 0 0.8 1.6 Legend OPR Rail Alignment Kilometres Study Area Absolute Scale - 1:50,000
Figure: 2.3 Drawn: SG Project ID: 721 Date: 15/06/09 Land Systems of Coordinate System Unique Map ID: S090 Name: GDA 1994 MGA Zone 50 the Study Area Projection: Transverse Mercator Datum: GDA 1994 A4
Oakajee Port and Rail Oakajee Terrestrial Port Development: Flora and Vegetation Assessment
Table 2.3 – Descriptions of Land Systems and Map Subunits Found within the Study Area (Dye et al, 1990)
Land Systems Description ID on Figure 2.3
Frontal Areas – low lying plain adjoining foredune or beach 221Qu_1Qs1
Swale areas – gently undulating plains surrounded by parabolic dunes. 221Qu_1Qs2
Low dunes – smaller scale parabolic dunes with slopes ranging from 10 – 55%. Relief 5‐15 m 221Qu_1Qp1 Quindalup System: This land system consists of Safety Bay sand, Holocene shoreline deposits and dunes. Steep dunes ‐ large scale parabolic dunes with slopes ranging from 45‐65%. Relief 20‐40 m. 221Qu_1Qp2
Active parabolic dunes and blowouts ‐ large scale un vegetated or sparsely vegetated transgressive dune ridges. Rates of advance vary between 1 – 10 m per year. Active parabolic dunes are associated with the 221Qu_1Qm heading/leeward edge of the transgressive dune ridges. Foredune ‐ a narrow frontal dune with slopes ranging from 45‐65% and relief from 5‐10 m. Some areas are 221Qu_1Qf un vegetated and eroded.
Bare sand of the beach areas. 221QuX_BEACH
Tamala System: This land system consists of lines of dune limestone Steep Rocky Slopes: steep dune slopes on the western side of the Tamala Limestone land system with very parallel to the coast, immediately 221Ta_2Tst common limestone out‐crop and shallow, siliceous brown sands. east of the Quindalup Land System. The coastal area of this unit consists of relict dune swale topography. Yellow Sandplain ‐ Level to undulating sandplain. The remnant of the relict dune swale system of the Limestone outcrops occur in the 221Ta_3Ysp higher areas. Tamala Limestone association. Deep Red Soils ‐ lower lying and swale areas of the Tamala Limestone land system. Slopes 1‐3%. 221Ta_5Tr
May 2010 10
Oakajee Port and Rail Oakajee Terrestrial Port Development: Flora and Vegetation Assessment
Land Systems Description ID on Figure 2.3
Rock Outcrop and Shallow Sand ‐ gently undulating to undulating cemented relict dune crests of Tamala Limestone with shallow red and brown siliceous sands, and common limestone outcrop. Limestone 221Ta_5Ts outcrop is irregular because of solution weathering.
Grey Brown Sands ‐ mid to lower slopes of Tamala Limestone ridges and some isolated rises to the north of 221Ta_5Tb the Greenough alluvial plain. Generally occurs on the western side of the Tamala Limestone land system. Northampton System: ‐ Granulite Country – gently rolling but Dissected Country – moderately inclined to steep rocky slopes (10 – 20%) often strongly dissected. Shallow sometimes undulating to hilly terrain 225No_1GrD (3‐10% slope) on granulite rock. The sandy soils and common to very common rock outcrop. lower slopes of the rolling hills form a convergent drainage pattern. Sandstone remnants of the Moresby Range are steeper areas within the Rolling Country. 225No_1GrR unit.
Northampton System: Recent Recent Alluvium Subject to Flooding – lower terraces of the major rivers, subject to regular flooding, 0‐1% 225No_2Af Alluvium – recent alluvial deposits on slope. the terraces of the major rivers and along minor tributaries. Soil types are variable. Recent Alluvium not Subject to Regular Flooding – well‐drained massive soils with sandy fabric. Commonly 225No_2An1 with a heavier textured alluvial deposit overlying a buried profile of loamy sand.
Northampton System: Rock outcrop. Rock Outcrop 225No_1R
May 2010 11
Oakajee Port and Rail Oakajee Terrestrial Port Development: Flora and Vegetation Assessment
2.4 LANDFORMS
The Geraldton region primarily consists of coastal heath vegetation and semi‐arid woodlands overlying sandy or gravelly soils on sandplains or low hills. Playford et al. (1970) identified four main landform types on the mainland. These are the Victoria Plateau, River Drainage Systems, Greenough Flats, and the Coastal Belt (Figure 2.4).
The Victoria Plateau is the most inland formation, consisting of gently undulating sandplain over laterite with some flat topped mesas and sand dunes.
The River Drainage Systems are associated with riparian areas of the Greenough, Chapman, Hutt, Bowes and several minor rivers. These formations extend from the coast to the eastern areas of the Victoria Plateau. They are characterised by rounded hills of Precambrian rocks and flat‐topped hills of Jurassic and Triassic sediments, which are often capped by laterite and represent eroded remnants of the Victoria Plateau.
The Greenough Flats are in the south of the region and form the floodplain surrounding the mouth of the Greenough River. This system consists of fertile soil and has been used intensively for agriculture since the 1850s. A ridge of coastal limestone runs parallel to the coast, dividing the flats in two.
The Coastal Belt System consists of sand dunes, often mobile, and some very tall (60 m high) ridges of limestone up to 130 m high, with cliffs around the Hutt River. Hutt Lagoon, a large salt lake, is also in this area.
The main landforms of the Study Area itself are the narrow coastal strip of Quindalup sand dunes, the Spearwood sand dune system further inland, the Northampton system (consisting of low hills and rises underlain by Proterozoic rocks), and the Moresby plateau and footslopes underlain by Jurassic rocks (Langford, 2001).
May 2010 12
Oakajee Port and Rail Oakajee Terrestrial Port Development: Flora and Vegetation Assessment
Figure 2.4 – Map of Landforms of the Geraldton Area from Playford et al. (1970)
2.5 BEARD VEGETATION MAPPING
Beard and Burns (1976) mapped the vegetation of the Geraldton region and grouped similar areas according to vegetation (Figure 2.5). The Study Area lies within an area of coastal vegetation known as the Greenough System.
The Greenough vegetation system is characterised by a coastal limestone belt extending from Kalbarri to Dongara. The limestone belt varies in width, elevation and in topography. The limestone belt forms several extensive, shore‐parallel ridges along the entire length of the coast in the region and outcrops at the coast as tall sea cliffs north of Oakajee near Horrocks Beach. It includes abrupt rocky ridges, more gentle soil‐covered areas, alluvial flats and lagoons. On the seaward side, the limestone is covered with a mantle of recent, poorly consolidated or still mobile dune sands (Beard and Burns, 1976).
Six vegetation types were mapped (Figure 2.5) within the Study Area (Beard and Burns, 1976):
1. Sparsely vegetated drift sand (map notation: ds) (129); 2. Banksia woodland and Acacia scrub (map notation abSi) (359);
3. Acacia ligulata open shrub(map notation a21Sr); (440) 4. Mixed (Melaleuca, Hakea) thicket (map notation mhSc) (675): 5. Jam scrub with York Gum (map notation e6Mr.a19Si) (35) ; and
6. Shrublands, Acacia neurophylla thicket (map notation a33Sc) (413).
May 2010 13
262000 264000 266000 268000 270000 6840000
e6Mr a19Si
mhSc 6838000
a21Sr
abSi 6836000 mhSc
ds 6834000
a33Sc 6832000
ds K
a21Sr 0 0.75 1.5 6830000 Kilometres Legend Absolute Scale - 1:35,000 OPR Rail Alignment ds mhSc a21Sr abSi Oakajee Study Area
Figure: 2-5 Drawn: SG Vegetation of the Project ID: 721 Date: 30/06/09 Unique Map ID: M141 Coordinate System study area Name: GDA 1994 MGA Zone 50 Projection: Transverse Mercator A3 Datum: GDA 1994
Oakajee Port and Rail Oakajee Terrestrial Port Development: Flora and Vegetation Assessment
2.6 DISTRIBUTION OF NATIVE VEGETATION WITHIN THE AREAS SURVEYED
The Study Area comprises areas of disturbed grazing and farmland, as well as large areas of remnant and regrown native vegetation, as summarised in Table 2.4. Most of the intact native vegetation at Oakajee occurs adjacent to the coastline and alongside the Oakajee and Buller Rivers. Smaller areas of fragmented native vegetation also occur among larger areas of cleared farmland. The majority of the sand plain area has been cleared in the past and is now used for pastoral purposes. The remaining areas with vegetation cover provide important habitats for vertebrate and invertebrate fauna.
Table 2.4 – Remnant Bushland within Surveyed Areas
Proportion of Total Area Total Area of All Areas of Remnant Area Surveyed which is Remnant Bushland Vegetation (ha) Bushland (ha) (%) Flora and vegetation 4,743 1,647 35 survey Additional area to south incorporated into rare flora 267 230 86 survey
2.7 PREVIOUS BIOLOGICAL SURVEYS IN THE STUDY AREA
The coastal flora and vegetation of the calcareous sands and Tamala Limestone is relatively well known (Tauss, 2002 & 2005). One detailed floristic study has been conducted of the flora and vegetation of the lateritic sandstone settings of the nearby Moresby Ranges (Keating, 2002), and this vegetation extends into the eastern section of the Study Area.
A list of previous studies carried out in the Study Area is included in Appendix A. The findings of surveys previously carried out within the Study Area by Dames & Moore (1993) and Muir Environmental (1997) are detailed below. The Dames & Moore Study Area did not extend further north than the Oakajee River, whereas the Muir Study Area extended approximately 1 km north of the Oakajee River and approximately 2 km to the south of the current survey’s northern boundary. A map of the Dames and Moore survey boundary is included as Figure A.1 in Appendix A.
Dames and Moore (1993) mapped the Study Area as six major plant associations at the 1:25,000 scale and recorded 165 vascular plant species (including 27 weeds). No DRF species were recorded during this survey. One Priority Flora species, Grevillea triloba (P3), was located in Reserve 16200 on the North West Coastal Highway.
Muir Environmental (1997) mapped six “terrain types” and recorded 217 species of vascular flora (including 37 weed species). One DRF, two Priority Flora species and one orchid of potential conservation significance were recorded as listed below: • Eucalyptus blaxellii (DRF at the time of survey) was found on a breakaway near the southern branch of the Oakajee River. This species was recorded as a single plant in very poor condition. • Grevillea triloba (P3) was located on both sides of the Oakajee River valley, in Reserve 16200, and along roadsides. • Verticordia penicillaris (P4) was located on Reserve 16200. A single plant of a hybrid between Caladenia hoffmanii (DRF) and Caladenia longicauda was also reported on the Banksia sandplain. This suggested that Caladenia hoffmanii (DRF) also may have been present nearby at some stage.
May 2010 15
Oakajee Port and Rail Oakajee Terrestrial Port Development: Flora and Vegetation Assessment
The six “terrain types” and a summary of the dominant floristic components and vegetation structure (where given) that were mapped by Muir Environmental (1997) are listed below.
A: Mobile Dunes Olearia axillaris ‐ Acacia rostellifera.
B: Stable Sand Dunes Olearia axillaris ‐ Acacia rostellifera ‐ Anthocercis littorea ‐ Spinifex longifolia.
C: Limestone Ridge Acacia xanthina to 4 m in height, Grevillea argyrophylla and Melaleuca cardiophylla. Also Eucalyptus eudesmioides, Hakea obliqua, Acacia rostellifera, Conostylis stylidioides and Loxocarya myrioclada.
D: Sandplains Banksia prionotes, Acacia rostellifera, Acacia cyclops, Banksia sessilis, Hakea lissocarpha, Allocasuarina campestris, Hibbertia spp., Acanthocarpus preissii, Conostylis stylidioides and Loxocarya myrioclada.
E: River Margins Eucalyptus camaldulensis, Casuarina obesa, Melaleuca rhaphiophylla, Acacia acuminata and Acacia cyclops. In upper valley margins Hakea recurva, Hakea obliqua and Banksia fraseri var. ashbyi.
F: Valley Slope Complexes Acacia acuminata, Acacia tetragonophylla, Allocasuarina campestris, Grevillea triloba and Hakea recurva. Understory of Banksia fraseri var. ashbyi, Lepidosperma tenue and Borya sphaerocephala.
2.8 LAND USES IN THE SUBREGION
The dominant land use in the Geraldton Hills subregion is dry‐land agriculture (65.8%) together with grazing native pastures (13.2%). Smaller areas consist of conservation land (13.2%) and unallocated Crown land (UCL) and Crown reserves (6.47%). Over 68% of the area in conservation estate in the subregion is contained in Kalbarri National Park (approximately 100 km north of Study Area) at the far north‐western periphery of the subregion. A further 20% of the subregion’s conservation estate is contained in a single reserve, Wandana Nature Reserve (80 km NE of Study Area), at the north‐ eastern periphery of the subregion. The remainder of the subregion has very few conservation reserves, the majority of which are small, threatened by salinity and on agriculturally unproductive land (Desmond and Chant, 2001).
Reserves in the surrounding area south to Geraldton are shown in Figure 2.6.
2.9 LAND USE HISTORY
Much of the area around Geraldton is occupied by wheat and sheep farms. Lupins, canola, and barley are also major crops, and fruit, vegetable and dairy farms are present. Grazing occurs on native and modified pastures (Stuart‐Street and Clarke, 2005) and farming in the area dates from 1856 (Beard and Burns, 1976).
May 2010 16
265000 270000 275000
200000 250000 300000 350000 Western Murchison Legend Tallering 6848236 6950000 Edel OPR Proposed Rail Alignment Oakabella Nature Reserve
Environmentally Sensitive Areas Kalbarri Nature Reserve National Parks and Reserves
Remnant Vegetation 6900000 Wandana Nature Reserve Nilligarri Nature Reserve
Geraldton Hills East Yuna Avon Wh e National Park
Study Area 6850000
6843236 K Indarra Spring Nature Reserve 02040 Geraldton ! Kilometres Absolute Scale - 1:1,400,000
Bella Vista Nature Reserve
Howatharra Nature Reserve 6838236
Oakajee Nature Reserve
Nature Reserve 16200 6833236 Moresby Range Nature Reserve
Wokatherra Nature Reserve K
024 6828236 Kilometres Absolute Scale - 1:60,000
Figure: 2.6 Drawn: SG Conservation Reserves Project ID: 721 Date: 14/01/10 and Remnant Vegetation Coordinate System Unique Map ID: S091 within and Surrounding Name: GDA 1994 MGA Zone 50 the Study Area Projection: Transverse Mercator Datum: GDA 1994 A3
Oakajee Port and Rail Oakajee Terrestrial Port Development: Flora and Vegetation Assessment
This page has been left blank intentionally
May 2010 18
Oakajee Port and Rail Oakajee Terrestrial Port Development: Flora and Vegetation Assessment
3 SURVEY METHODS
The survey methods adopted by ecologia are aligned with Environmental Protection Authority Guidance Statement No. 51 (EPA 2004) and Position Statement No. 3 (EPA 2002). The 2006 survey conforms to a single phase Level 2 survey, comprising a reconnaissance survey, single phase flora and vegetation survey and mapping of the vegetation of the area, as per Statement 51. A single phase Level 2 survey was considered appropriate for the area given the previous survey work already undertaken in the area. A subsequent survey, which targeted flora of conservation significance that had been previously recorded within the Study Area or its surrounds, was conducted.
3.1 DETERMINATION OF SURVEY SAMPLING DESIGN AND INTENSITY
Prior to conducting the surveys, a review was undertaken of factors likely to influence survey design. These factors and the methodological actions taken in response are presented in Table 3.1.
Table 3.1 – Factors Likely to Influence Survey Design (EPA, 2004)
Factor Relevance Comment Regional data from other surveys undertaken in the area was reviewed. Sampling design Guidance Data was collected at an area‐specific level. Twenty one quadrats (and and intensity at two Statement No. additional opportunistic relevees) were initially assessed within the Study levels – regional 51 Area. A follow‐up threatened flora survey was also conducted within the and area specific Study Area. Sites were selected from aerial photography prior to the survey. While in Landform – scale, Guidance the field, vegetation types occurring in the different landforms were rarity, Statement No. ground‐truthed. Sites were located to sample the variety of land forms heterogeneity 51 present. Sites were selected from aerial photography prior to the survey. While in the field, vegetation types occurring in the different habitats were ground‐ Habitat – scale, Guidance truthed. Sites were located to sample the variety of habitats present. rarity, Statement No. heterogeneity 51 Opportunistic relevees were used to supplement the quadrat‐based data to ensure that all vegetation units present were surveyed and to maximise coverage of the area within the time available. Lists of conservation significant taxa recorded in the vicinity of the Study Area were obtained by DEC database searches prior to August 2006 and again in 2010. Vegetation and Flora survey (see Section 5.2.2). Habitats where conservation significant taxa could potentially occur were targeted during the field surveys. Potential for A threatened flora survey was conducted in March 2009. The search conservation Guidance concentrated specifically on the conservation significant flora located significant flora to Statement No. during the initial (2006) survey, but also on other conservation significant occur, based on 51 flora that had been located during previous surveys of the area. As the habitat analysis Priority Flora taxa were located in diverse habitats, all habitats of the Study Area were sampled during this survey. The results from the threatened flora survey were used to estimate numbers of conservation significant flora occurring in the Study Area and the development footprint. Information on adjacent areas – Guidance Information was requested from relevant government databases (Section previous surveys Statement No. 5.2.2) and was collated from reports undertaken in the vicinity of the Study and herbarium 51 Area prior to the August 2006 survey (Section 2.7). records
May 2010 19
Oakajee Port and Rail Oakajee Terrestrial Port Development: Flora and Vegetation Assessment
Factor Relevance Comment The survey design combined data collection from bounded quadrats with Vegetation Guidance opportunistic collections from relevees. The use of bounded quadrats structure, diversity Statement No. allowed the vegetation to be analysed to assess the degree of diversity. and seasonality 51 The use of relevees increased the area which could be searched for flora of significance and significantly supplemented the total inventory of plants. Results including Details on the flora of the Study Area are included in this report. A species/area Guidance vegetation map and detailed vegetation descriptions are provided for the curves, species and Statement No. Study Area. A species accumulation analysis was conducted using data ecosystem diversity 51 from the 2006 survey (Section 5.1). and heterogeneity
3.2 VEGETATION AND FLORA SURVEY
3.2.1 Flora Survey Sites
Prior to the 2006 survey, a search of the Department of Environment and Conservation (DEC) Threatened Flora Database was undertaken to determine species of conservation significance previously recorded in the vicinity of the Oakajee Study Area.
The vegetation and flora survey was conducted in August 2006. Twenty one sampling locations were chosen by means of aerial photography, topographical features and field observations to ensure that all vegetation types present within the footprint were sampled. Nested quadrats of 100 m2 and 400 m2 were sampled at each location.
Within each quadrat the vegetation description, life‐form strata, percentage cover of individual species, surface soil type, litter cover, vegetation condition and sources of disturbance were recorded. Vegetation was described using the canopy cover rankings and terminology adapted from Keighery (1994) as summarized in Table 3.2.
Table 3.2 – Vegetation Structure Classification (adapted from Keighery, 1994)
Canopy Cover Life form / Height Class Dense 70 ‐ 100% Mid‐dense 30‐ 70% Sparse 10 ‐ 30% Very Sparse 2 ‐ 10%
Trees > 30 m Tall Closed Forest Open Forest Tall Woodland Open Tall woodland Trees 10 – 30 m Closed Forest Open Forest Woodland Open Woodland Trees < 10 m Low Closed Forest Low Open Forest Low Woodland Low Open woodland
*Mallee Closed Mallee Mallee Open Mallee Very Open mallee
Shrubs > 2 m Closed scrub Scrub Open Scrub Tall Open shrubs Shrubs <2 m Closed heath Heath Open Heath Low open shrubs Grasses Closed Grasses Grasses Open Grasses Sparse gasses Herbs Closed Herbs Herbs Open Herbs Sparse herbs
Rushes/ sedges > 0.5 m Closed Tall Sedges Tall Sedges Open Tall Sedges Sparse tall sedges < 0.5 m Closed Sedges Sedges Open Sedges Sparse sedges
*Note: In agreement with current usage by Eucalyptus specialists (Brooker et al., 2002), in this study “mallee” is defined as Eucalyptus spp. that are multi‐stemmed from the ground level and usually less than 10 m in height, whilst “tree” is defined as being single‐stemmed at ground level and greater than 5m in height.
May 2010 20
Oakajee Port and Rail Oakajee Terrestrial Port Development: Flora and Vegetation Assessment
In degraded areas where vegetation was very sparse and/or species poor, bounded quadrats were replaced by transects in which the flora present was opportunistically recorded. Degraded vegetation in which this method was employed was located within a damp land adjacent to the beach (Opportunistic Site 22), the riparian vegetation of the Oakajee River (Opportunistic Site 23), a lateritic area adjacent to Coronation Beach Rd (Opportunistic Site 24), a lateritic plateau west of Reserve No 16200 near the southern branch of the Oakajee River (Opportunistic Site 25) and the adjacent lateritic valleys (Opportunistic Site 26).
Three additional locations were surveyed using opportunistic collection from transects: • Melaleuca cardiophylla – Grevillea argyrophylla dense tall heath (Opportunistic Site 27);
• Acacia xanthina tall dense scrub (Opportunistic Site 28); and
• A strip of re‐vegetation running through the eastern section of the farmed land (Opportunistic Site 29).
The locations of bounded quadrats and the opportunistic collection transects are shown on Figure 3.1.
Additional transects were conducted through all areas of remnant vegetation, with a greater intensity of searching in those areas of vegetation in good to excellent condition. Taxa of potential conservation significance were photographed and their locations were recorded with a GPS. These traverses enabled confirmation of plant community boundaries and supplemented the floristic inventory of the Study Area with species not recorded within bounded quadrats.
Plant species were either identified in the field or specimens were collected for later identification. Vegetation structure was classified by a system adapted from Keighery (1994). Nomenclature and taxonomy follow that of the Western Australian Herbarium (FloraBase, 2010).
May 2010 21
Oakajee Port and Rail Oakajee Terrestrial Port Development: Flora and Vegetation Assessment
3.2.2 Vegetation Mapping
Colour aerial photography at 1:40,000 was used to interpret the vegetation patterns of the Study Area and verified using linked ground traverses and observations of dominant species and vegetation structure. Sampling sites were selected to be representative of the vegetation types as interpreted from the photographs and field observations. The boundaries of the major vegetation units derived from the field observations and subsequent analysis of data collected from bounded quadrats were mapped onto the aerial photograph to provide a visual summary of the extent of vegetation units over the entire site.
The boundaries of the vegetation units mapped from information collected during the 2006 survey were ground truthed and further refined during the threatened flora survey.
3.3 THREATENED FLORA SURVEY
A threatened flora survey was conducted in March 2009, to determine the extent of populations of conservation significant flora within the Study Area and an adjacent area (267 ha) of largely native vegetation to the immediate south. The search concentrated on the conservation significant taxa located during the vegetation and flora survey; however other conservation significant taxa recorded during earlier surveys of the Oakajee area were also targeted.
Due to the large size of the Study Area and the dense vegetation in some locations, the whole area could not be systematically grid searched during the threatened flora survey. Therefore a sub‐set of the vegetation was surveyed by transects over 18 person days as detailed by Figure 3.2. Transects were distributed such that each vegetation type was represented. The total area surveyed for threatened flora is detailed in Table 3.3.
Table 3.3 – Proportion of the Total Area Surveyed for Threatened Flora
Area of Remnant Area of Transects Proportion of Remnant Surveyed Area Bushland (ha) Surveyed (ha) Bushland Surveyed (%)
Study Area and additional area included 2,097.1 77.6 3.70 in rare flora survey
The survey included east‐west transects through the coastal vegetation from Coronation Beach Road (northern extent) to approximately 2 km south of Buller River (southern extent) and transects through other significant patches of remnant vegetation including; roadside vegetation (Coronation Beach Road and North West Coastal Highway), roadside reserves (Crown Reserve 16200) and large areas of remnant vegetation in the pastoral areas.
Transects were walked through remnant bushland occurring within the following proposed infrastructure development areas: • onshore storage area;
• stockyard;
• rail maintenance yard and workshops;
• port access road; and
• potential haul road alignment options.
May 2010 23
Oakajee Port and Rail Oakajee Terrestrial Port Development: Flora and Vegetation Assessment
The length of transects walked varied depending on the vegetation being surveyed however the width of each transect was approximately 10 meters. The east‐west running transects were spaced approximately 200 m apart and ran the width of the vegetation unit. Transects within the North West Coastal Highway ran parallel to the Highway on each side of the road. The majority of transects were 200 m in length and spaced approximately 400 m apart. Transects through significant patches of remnant vegetation ran east‐west and were spaced 100 m or 200 m apart. Transects within the areas of proposed disturbance were more closely spaced to ensure the habitat was well covered.
An additional survey, targeting Melaleuca huttensis was conducted in April 2009. This survey opportunistically searched a subset of the locations listed by the DEC databases in the vicinity of the Study Area, with the primary focus on publicly accessible landholdings (ecologia, 2010). Individual plants were counted at all locations which could be accessed. The numbers of plants present at some private landholdings was estimated by surveying the numbers present at the boundaries.
May 2010 24
Oakajee Port and Rail Oakajee Terrestrial Port Development: Flora and Vegetation Assessment
This page has been left blank intentionally
May 2010 26
Oakajee Port and Rail Oakajee Terrestrial Port Development: Flora and Vegetation Assessment
4 VEGETATION
4.1 VEGETATION UNITS OF THE SURVEY AREA
Fourteen vegetation units at the sub association level were described (Table 4.1) and mapped at the scale of 1:40,000 (Figure 4.1). This total excludes two areas mapped as bare sand and disturbed agricultural land. Much of the vegetation in the Study Area, particularly the sandplain, laterite vegetation and riparian units has either been cleared for agriculture or is degraded from weed invasion, or from grazing by livestock and feral animals. However, there are significant areas (representative of all the vegetation types other than riparian vegetation) present in the Study Area that are still species‐rich and in very good to excellent condition. Individual site data is presented in Appendix B.
May 2010 27
Oakajee Port and Rail Oakajee Terrestrial Port Development: Flora and Vegetation Assessment Table 4.1 – Vegetation Units Mapped at the Sub‐association Level within the Study Area
Site Number Vegetation Unit and Typical Habitat Photograph
Sub Association 1: Olearia axillaris low open shrubs, Spinifex longifolius hummock grasses (+/‐ Scaevola crassifolia). Foredunes.
Olearia axillaris – Scaevola crassifolia low open shrubs over Spinifex longifolius sparse grass. 7 Calcareous sand on low Holocene foredune.
Olearia axillaris ‐ Acacia rostellifera low shrubs over Spinifex longifolius sparse grass. 16 Calcareous sand on low Holocene foredune.
Olearia axillaris open heath over Spinifex longifolius mid dense grass. Calcareous sand on 17 low Holocene foredune.
Sub Association 2: Juncus kraussii closed sedgeland. Swale
Opportunistic Site Juncus kraussii closed sedgeland with low open shrubs of Olearia axillaris. Seasonally 22 waterlogged swale in Holocene dunes.
May 2010 28
Oakajee Port and Rail Oakajee Terrestrial Port Development: Flora and Vegetation Assessment Site Number Vegetation Unit and Typical Habitat Photograph
Sub Association 3: Acacia rostellifera – Stylobasium spathulatum – Tetragonia implexicoma – Acanthocarpus preissii open to closed medium to low scrub. Deep sands on secondary dune crests and slopes.
Acacia rostellifera ‐ Scaevola tomentosa ‐ Tetragonia implexicoma open scrub over Poa 18 poiformis ‐ Austrostipa elegantissima ‐ Lomandra maritima open grasses and sparse herbs. Deep calcareous sand on Holocene secondary dune.
Sub Association 4: Acacia xanthina – Melaleuca cardiophylla (+/‐ Grevillea argyrophylla) closed scrub. Tamala limestone slopes and hill crests.
Acacia xanthina closed scrub over low open shrubs including Pimelea microcephala subsp. 21 microcephala and Melaleuca cardiophylla and naturalized alien grasses. Shallow calcareous sand over Pleistocene Tamala Limestone in deflated interdunal swales.
Patchy closed scrub of Acacia xanthina over low open shrubs of Melaleuca cardiophylla – 3 Grevillea argyrophylla. Shallow calcareous sand over Tamala Limestone on ridges.
Acacia xanthina open scrub over Grevillea argyrophylla – Melaleuca cardiophylla low 4 shrubs over sparse Desmocladus asper twine rush. Shallow calcareous sand over Tamala Limestone on ridges.
May 2010 29
Oakajee Port and Rail Oakajee Terrestrial Port Development: Flora and Vegetation Assessment Site Number Vegetation Unit and Typical Habitat Photograph
Acacia xanthina open scrub over low shrubs Melaleuca cardiophylla – Thryptomene 10 baeckeacea ‐ Templetonia retusa over sparse twine rush Desmocladus asper. Shallow calcareous sand over Pleistocene Tamala Limestone on ridges and slopes.
Sub Association 5: Melaleuca cardiophylla– Grevillea argyrophylla scrub or heath (+/‐ Eucalyptus dolichocera mallee and Diplolaena grandiflora scrub). Tamala limestone slopes and ridges
Melaleuca cardiophylla – Grevillea argyrophylla patchy open heath over Gahnia lanigera – 15 Desmocladus asper open sedges and twine rushes. Skeletal calcareous sand over limestone on cliff slope.
Grevillea argyrophylla – Melaleuca cardiophylla closed scrub over low open shrubs of Pimelea microcephala subsp. microcephala – Olearia dampieri subsp. dampieri ‐ Rhagodia 20 preissii subsp. obovata over sparse Desmocladus asper twine rush. Shallow calcareous sand over limestone on low ridge.
Low open shrubs of Melaleuca cardiophylla – Diplolaena grandiflora over open grasses of 9 Poa poiformis and Desmocladus asper twine rushes. Shallow calcareous sand over rocky limestone slope.
Eucalyptus dolichocera low open mallee (less than 2.5 m in height) over Melaleuca 8 cardiophylla tall shrubs over Diplolaena grandiflora – Templetonia retusa – Grevillea argyrophylla low shrubs. Gullies on the slopes of Tamala Limestone outcrops.
Eucalyptus dolichocera low open mallee (less than 3 m in height) over Melaleuca 14 cardiophylla – Enchylaena tomentosa ‐ Diplopeltis petiolaris low shrubs. Gullies on the slopes of Tamala Limestone outcrops.
Eucalyptus dolichocera low, mid‐dense mallee (less than 4 m in height) over open heath of 19 Melaleuca cardiophylla – Melaleuca campanae – Templetonia retusa ‐ Acacia xanthina over sparse annual herbs and grasses. Gullies on the slopes of Tamala Limestone outcrops.
Grevillea argyrophylla closed patchy scrub over sparse low shrubs and mid‐dense 5 naturalized alien grasses and herbs. Shallow calcareous sand over Tamala Limestone on limestone ridges.
May 2010 30
Oakajee Port and Rail Oakajee Terrestrial Port Development: Flora and Vegetation Assessment
Site Number Vegetation Unit and Typical Habitat Photograph
Sub Association 6: Banksia prionotes (+/‐ Banksia menziesii) open scrub. Sandplains
Banksia prionotes open scrub over low shrubs including Keraudrenia hermanniifolia and mid‐dense sedgeland of Mesomelaena pseudostygia. Banksia menziesii and Acacia 1 rostellifera occasionally occur in this sub association. Pale orange‐ brown quartz sand on plain.
Sub Association 7: Eucalyptus camaldulensis ‐ Casuarina obesa low closed forest (+/‐ Melaleuca rhaphiophylla and Cyperus gymnocaulos). River drainage systems.
Low closed forest of Eucalyptus camaldulensis over sparse Juncus kraussii rushes and weedy shrubs, annuals and grasses including *Ricinus communis, *Lycium ferocissimum, *Ehrharta longiflora, Fumaria sp. and *Tropaeolum majus. This unit is best developed at Opportunistic site the lower Oakajee River, west of the shore parallel limestone ridge that is dissected by the 23 river. Inland from the above, Casuarina obesa low closed forest dominates the riparian vegetation, although Eucalyptus camaldulensis is still common. In addition, the tree species Melaleuca rhaphiophylla and the sedge species Cyperus gymnocaulos are common along sections of the river systems in this sub association.
May 2010 31
Oakajee Port and Rail Oakajee Terrestrial Port Development: Flora and Vegetation Assessment Site Number Vegetation Unit and Typical Habitat Photograph
Sub Association 8: Grevillea ‐ Melaleuca and other low shrubs over Borya sphaerocephala mats. Laterite/sandstone Patchy low shrubs of Grevillea eriostachya – Grevillea triloba (P3) – Melaleuca fulgens subsp. steedmanii over open mats of Borya sphaerocephala ‐Stylidium elongatum ‐ 13 Conostylis prolifera over sparse sedges of Lepidosperma tenue and sparse annual herbs. Low lateritic/sandstone outcrop on undulating plain. Very sparse, very low shrubs, herbs and sedges including Acacia tetragonophylla, Hakea sp., Blackallia nudiflora (P3), Cryptandra sp., and Thryptomene baeckeacea over patchy Opportunistic site mats of Borya sphaerocephala with Schoenus clandestinus, Cyanicula gemmata, Caladenia 24 footeana, Thelymitra antennifera, Leporella fimbriata, Wurmbea dioica subsp. alba, Lomandra micrantha subsp. micrantha, Acanthocarpus parviflorus (P3), Scaevola sp.,
Lepidosperma sp. Moresby Range (P1) and Dampiera altissima. Low lateritic/sandstone outcrop. Very sparse, very low shrubs, herbs and sedges including Acacia tetragonophylla, Blackallia Opportunistic site nudiflora (P3), Cryptandra spp., and Verticordia picta over sparse patchy mats of Borya 25 sphaerocephala with Cheilanthes adiantoides, Acanthocarpus parviflorus (P3), Lepidosperma tenue, Stylidium elongatum, Neurachne alopecuroidea, Schoenus clandestinus and Rhodanthe spicata. On lateritic/sandstone plateau near southern branch of Oakajee River.
Sub Association 9: Acacia acuminata sparse low trees over Acacia tetragonophylla shrubs (+/‐ Eucalyptus spp. mallees, grasses and weedy herbs). Low gentle to moderate hill slopes.
Mid‐dense Eucalyptus spp. mallees (such as Eucalyptus loxophleba subsp. loxophleba) over sparse low shrubs of Acacia tetragonophylla, Acacia acuminata, pasture grasses and herbs. Canopy intact but understorey degraded due to intensive grazing. On rocky lateritic Opportunistic site undulating plain to lower hill slope. This sub association is typically dominated by trees of 26 Acacia acuminata and occasionally Hakea preissii or Hakea recurva. Eucalyptus spp. mallee is locally common in some areas. Grevillea triloba (P3) occasionally occurs in this sub association on sandstone/laterite.
May 2010 32
Oakajee Port and Rail Oakajee Terrestrial Port Development: Flora and Vegetation Assessment Site Number Vegetation Unit and Typical Habitat Photograph
Sub Association 10: Tall shrubs of Grevillea – Melaleuca ‐ Acacia spp. over species rich open heath. Sand over laterite on undulating plains.
Tall shrubs of Grevillea eriostachya ‐ Melaleuca fulgens subsp. steedmanii over open heath of Conospermum stoechadis – Melaleuca fulgens subsp. steedmanii over Triodia 11 danthonioides and open Mesomelaena pseudostygia – Desmocladus asper sedges and rushes. Shallow pale orange‐brown quartz muddy sand over laterite on undulating plain.
Site Number Vegetation Unit and Typical Habitat Photograph
Acacia rostellifera – Acacia dielsii – Allocasuarina campestris tall open shrubs over Conospermum stoechadis – Verticordia densiflora var. roseostella – Verticordia picta – 12 Acacia spathulifolia low shrubs over Mesomelaena pseudostygia – Desmocladus asper open No photo available sedges and rushes. Shallow pale orange‐brown quartz muddy sand over laterite on undulating plain.
May 2010 33
Oakajee Port and Rail Oakajee Terrestrial Port Development: Flora and Vegetation Assessment
Site Number Vegetation Unit and Typical Habitat Photograph
Sub Association 11: Melaleuca cardiophylla – Grevillea argyrophylla dense tall heath. Tamala limestone hill crests
Opportunistic site Melaleuca cardiophylla – Grevillea argyrophylla dense tall heath. Shallow calcareous sand 27 on rocky Tamala limestone hill crests.
Sub Association 12: Acacia xanthina mid to tall dense scrub. Calcareous sand on stony Tamala limestone hill crest.
This vegetation sub association forms a mosaic with sub association 4 and while these sub Opportunistic site associations have been mapped as discrete units there is some overlap between the two 28 that is not apparent on aerial imagery. This vegetation sub association and sub association 4 both occur on small sections of steep, stony limestone hill slopes.
May 2010 34
Oakajee Port and Rail Oakajee Terrestrial Port Development: Flora and Vegetation Assessment
Site Number Vegetation Unit and Typical Habitat Photograph
Sub Association 13: Acacia rostellifera tall dense scrub. Deep calcareous sand in Holocene secondary dune swales.
Acacia rostellifera patchy closed scrub over Stylobasium spathulatum open shrubs and mid‐ dense climbers Clematis linearifolia – Tetragonia implexicoma over sparse naturalized alien 2 grasses and herbs. Deep calcareous sand on Holocene secondary dune. This sub association often forms impenetrable tall dense scrub in broad sand dune swales.
Acacia rostellifera closed scrub (+/‐ Stylobasium spathulatum and Acanthocarpus preissii 6 low shrubs) over sparse naturalized alien grasses. Deep calcareous sand on Holocene secondary dune.
Sub Association 14: Eucalyptus spp. mixed revegetation on previously disturbed land.
This area is revegetated with introduced Eucalyptus species and is not represented by a Opportunistic site flora survey site. It occurs as windbreak/shelter belt plantings in paddock areas in addition 29 to very small areas along the North West Coastal Highway.
May 2010 35
Oakajee Port and Rail Oakajee Terrestrial Port Development: Flora and Vegetation Assessment This page has been left blank intentionally
May 2010 36
24 !(
01 !(
20 !(
18 !( 17 !(!(16
19 !(
23 !( 15 14!( !( 27 !(
25 26!( !(
05 !( 13 !( 02 12 Legend !( 03 !(11 !( !(
!( Survey Site
!( Opportunistic Site
29 04 !( OPR Rail Alignment !(
Olearia axillaris low open shrubs, 1 Spinifex longifolius hummock grasses (+/- Scaevola crassifolia).
22 2 Juncus kraussii closed sedgeland. !(
Acacia rostellifera – Stylobasium spathulatum 3 – Tetragonia implexicoma – Acanthocarpus preissii open to closed medium to low scrub.
Acacia xanthina – Melaleuca cardiophylla 06 07 !( 21 4 (+/- Grevillea argyrophylla) closed scrub. !( !(
Melaleuca cardiophylla – Grevillea argyrophylla 10 !( 5 scrub or heath (+/- Eucalyptus dolichocera mallee and 0809 Diplolaena grandiflora scrub). !(!(
Banksia prionotes (+/- Banksia menziesii) 6 28 open scrub. !( Eucalyptus camaldulensis - Casuarina obesa 7 low closed forest (+/- Melaleuca rhaphiophylla and Cyperus gymnocaulos).
Grevillea - Melaleuca and other 8 low shrubs over Borya sphaerocephala mats.
Acacia acuminata sparse low trees over 9 Acacia tetragonophylla shrubs (+/- Eucalyptus spp. mallees, pasture grasses and weedy herbs).
Tall shrubs of Grevillea – Melaleuca - Acacia 10 spp. over species rich open heath.
Melaleuca cardiophylla – Grevillea argyrophylla 11 dense tall heath.
12 Acacia xanthina mid to tall dense scrub. 13 Acacia rostellifera tall dense scrub. K Eucalyptus spp. mixed revegetation on 14 previously disturbed land. 0 1 2
15 Bare sand. Kilometres Absolute Scale - 1:40,000 16 Disturbed agricultural land.
Figure: 4-1 Drawn: SG Vegetation of Project ID: 721 Date: 30/06/09
the Oakajee Coordinate System Unique Map ID: M140 Name: GDA 1994 MGA Zone 50 study area Projection: Transverse Mercator Datum: GDA 1994 A3
Oakajee Port and Rail Oakajee Terrestrial Port Development: Flora and Vegetation Assessment
4.2 VEGETATION CONDITION Vegetation condition was assessed in the field using the vegetation condition scales detailed in Table 12 of Bush Forever, Volume 2 (Department of Environmental Protection, 2000) using criteria detailed in Table 4.2. Factors taken into consideration when determining these levels of disturbance are the presence of weeds, tracks and litter and any evidence of grazing and general ground disturbance. The proportion of quadrats ranked in each condition is listed in Table 4.3. The high number of quadrats located within excellent to good condition reflects the intentional bias of the survey towards intact native vegetation, particularly for the location of quadrats and does not reflect the range of vegetation condition present in the Study Area. As described in section 3.2.1, areas deemed in poor conditions were surveyed using opportunistic collections during foot traverses. Table 4.2 – Vegetation Condition Scale (Keighery, 1994 cited in BushForever, 2000)
Vegetation condition Criteria
Pristine No obvious sign of disturbance
Vegetation structure intact, disturbance affecting individual species and weeds are non‐ Excellent aggressive species Vegetation structure altered, obvious signs of disturbance e.g. repeated fires, presence of Very Good some more aggressive weed species, dieback, logging or grazing Vegetation structure significantly altered by very obvious signs of multiple disturbances. Retains basic vegetation structure or ability to regenerate it. Disturbance such as very Good frequent fires, presence of some very aggressive weeds at high density, partial clearing, dieback and grazing Basic vegetation structure severely impacted by disturbance. Scope for regeneration but not Degraded to a state approaching good condition without intensive management The structure of the vegetation is no longer intact and the area is completely or almost Completely Degraded completely without native species. Flora comprising weed or crop species with isolated native trees or shrubs.
Table 4.3 – Vegetation Condition at Each Bounded Quadrat Site
Condition Pristine Excellent Very good Good Degraded Completely Degraded
No. quadrats 0 9 3 9 0 0
May 2010 39
Oakajee Port and Rail Oakajee Terrestrial Port Development: Flora and Vegetation Assessment
This page has been left blank intentionally
May 2010 40
Oakajee Port and Rail Oakajee Terrestrial Port Development: Flora and Vegetation Assessment
5 FLORA
A total of 372 vascular flora taxa (including 43 naturalised alien taxa or weeds), from 74 families, was recorded during the two surveys carried out by ecologia at the Oakajee Study Area. Table 5.1 summarises the composition of the inventory, which is detailed in Appendix C. The high number of species from the family Poaceae reflects the relatively high number of weed grasses in the Study Area.
Table 5.1 – General Flora Statisitcs of the Study Area
Statistic Counts
Families 74 Species 372
Conservation Significant species 11
Weed species 43
Most speciose families Myrtaceae (36) Fabaceae (33) Poaceae (28) Asteraceae (no. of species) (23) Proteaceae (20) Most speciose genera Acacia (15) Eucalyptus (11) (no. of species) Melaleuca (9) Scaevola (8) Grevillea (6)