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LandCorp Report for Collie Shotts Industrial Park Vegetation Rehabilitation Plan November 2010
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November 2010 - Landcorp · 61/24064/101479 Collie Shotts Industrial Park 3 Vegetation Rehabilitation Plan 1. Introduction LandCorp referred the proposed development of the Shotts

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Page 1: November 2010 - Landcorp · 61/24064/101479 Collie Shotts Industrial Park 3 Vegetation Rehabilitation Plan 1. Introduction LandCorp referred the proposed development of the Shotts

LandCorp

Report for Collie ShottsIndustrial Park

Vegetation Rehabilitation Plan

November 2010

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161/24064/101479 Collie Shotts Industrial ParkVegetation Rehabilitation Plan

Contents

1. Introduction 3

1.1 Objective 3

1.2 Location 3

1.3 Overview of Rehabilitation Areas 3

2. Rehabilitation Protocol 5

2.1 Site Preparation 5

2.2 Topsoil Management 5

2.3 Mulching/Brushing 6

2.4 Species Mix 6

2.5 Planting Density 7

2.6 Timing of Planting of Tube Stock 7

2.7 Weed Control 7

2.8 Fuel Reduction Burning 8

2.9 Monitoring and Completion Criteria 8

2.10 Remediation Works 9

2.11 Time Frame 9

2.12 Responsibility 11

3. References 12

Table IndexTable 1 Time Frame for Rehabilitation and Monitoring Works 9Table 2 Rehabilitation Species and Numbers for the Jarrah- Banksia

Woodland Area at Shotts Industrial Park 17Table 3 Rehabilitation Species and Numbers for the Melaleuca preissiana –

Kunzea glabrescens Woodland Area at Shotts Industrial Park 19

Figure IndexFigure 1 Location 14Figure 2 Rehabilitation Areas Vegetation Types 15

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AppendicesA FiguresB Rehabilitation SpeciesC Dieback Working Group Western Australian Species Lists

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1. Introduction

LandCorp referred the proposed development of the Shotts Industrial Park (SIP) east of Collie, WesternAustralia, to the Department of Environment, Water, Heritage and the Arts (DEWHA) in September 2009.The referral related to potential impacts on matters of National Environmental Significance, specificallythreatened species, that are protected under the Environmental Protection and Biodiversity ConservationAct 1999 (EPBC Act). A decision on the referral was made by the Minister for the Environment and theproposed action was deemed to be a ‘Controlled Action’. In order to assess the proposal, DEWHA hasrequested additional information relating to the proposed offsets package, including a rehabilitation planfor areas identified within the SIP for rehabilitation.

This report addresses the requirement for a rehabilitation plan to be prepared for the areas identified inFigure 1. The entire Shotts Industrial Park was surveyed for flora and fauna in 2007 (GHD 2008). Theresults of the flora and vegetation survey have been used to inform this rehabilitation plan.

1.1 ObjectiveThe key objective of this plan is to “create a self-sustaining forest ecosystem by encouraging flora, faunaand soil characteristics similar to those present prior to clearing”.

1.2 LocationThe Shotts Industrial Park is located near the former Shotts townsite, approximately 7.5 km east of Colliein the south-west of WA. The SIP consists of approximately 235.6 ha of land to the south of CoalfieldsRoad (Figure 1).

1.3 Overview of Rehabilitation AreasLandCorp has identified areas of remnant vegetation within the SIP that will be retained as well as areasto be rehabilitated as part of an offset package for clearing remnant vegetation. The two areas to berehabilitated, designated as Area A and Area B are shown in Figure 2.

Area A comprises 6.22 ha and a portion of the area is a former sand quarry site with the balance madeup of a degraded regrowth (Figure 2). An existing infrastructure easement occurs immediately west ofArea A, within the SIP. There will be no rehabilitation within this easement. An additional 4 m accesstrack may also be required to the east of this existing infrastructure easement. In addition, a firebreakand emergency access track up to 8 m in width is likely to be required along the southern boundary ofArea A, 4 m either side of the SIP boundary. These access tracks and easements have been allowed forin determining the area of rehabilitation within Area A.

Area B is 0.23 ha in area and comprises a section of an existing haul road that will be diverted to makeroom for proposed industrial facilities (Figure 2).

The pre-clearing vegetation types of both rehabilitation areas have been extrapolated from the vegetationmapping undertaken by GHD in 2007, shown in Figure 2. Area A has two pre-clearing vegetation types;Jarrah – Banksia – Xylomelum – Sheoak Woodlands which covers approximately 5.25 ha and Melaleuca

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preissiana – Kunzea glabrescens Low Woodland which covers 0.67 ha. Area B has one pre-clearingvegetation type; Jarrah – Banksia – Xylomelum – Sheoak Woodlands which covers the entire 0.53 ha.

There is also potential for areas additional to those identified in this plan to require rehabilitation in thefuture. Any additional rehabilitation within the Shotts Industrial Park should be carried out following therehabilitation protocol outlined in this plan.

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2. Rehabilitation Protocol

2.1 Site PreparationSite preparation for the two rehabilitation areas will require different techniques. Area A is an old quarrysite that appears to have had some limited rehabilitation in the past. Area B is a section of an existinghaul road. This road will be closed and redirected.

2.1.1 Area A (old sand quarry site)

The old quarry site has some regrowth of native species. The site should be sprayed for weeds.Following weed control, weed free topsoil from the adjacent site proposed to be cleared for industrialfacilities should be spread evenly to a depth of 20 cm. Following topsoil return, tree stumps, logs androcks should be placed across the site and the ground ripped to a depth of 0.3 – 0.4 m. Any contouringor reshaping earthworks (if required) should be undertaken prior to ripping. Ripping should beundertaken along the existing ground contour lines to minimise the potential for erosion Ripping shouldbe carried out during dry conditions to maximise ground fracture.

The boundary of the two vegetation types within this area should be pegged out and flagged usingdifferent colour flagging tape, to ensure the correct species mix for each vegetation type is planted intothe correct area.

2.1.2 Area B (Haul Road)

The section of haul road to be rehabilitated has been very heavily compacted by laden haul trucks. Theroad should be ripped to a depth of 30 cm and any windrows evened out to the same level as the roadsurface. Weed free topsoil from the adjacent site proposed to be cleared for the industrial facility shouldbe spread to a depth of 20 cm. Following topsoil return, tree stumps, logs and rocks should be placedacross the site and the ground ripped along the ground contour to a depth of 1.0 m to break down thesubsoil and allow penetration by tree roots and water. Rip lines should be spaced at 3 m to 5 m intervals,resulting in furrows approximately 0.3 m high by 1.5 m wide. Any contouring or reshaping earthworks (ifrequired) should be undertaken prior to ripping. Ripping should be undertaken during dry conditions tomaximise ground fracture.

2.2 Topsoil ManagementA preliminary dieback assessment undertaken in 2008 indicated that dieback is present within the SIPsite, with spot infestations adjacent to roads and tracks. Numerous areas, including the sand quarry andwetland vegetation, were considered to be ‘uninterpretable’. The preliminary assessment determined thatany uninfested vegetation within or bounding the study area is likely to be at risk of dieback infestation, ifnot already infested.

Proponents in the SIP will be required to undertake comprehensive dieback interpretation anddemarcation prior to commencement of clearing within their development area. If dieback is present,individual proponents will be required to develop a dieback management plan prior to any land clearing

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being undertaken.

All topsoil to be used within rehabilitation areas will be sourced from areas of the same dieback category(e.g. if rehabilitation areas are found to be uninfested, all topsoil will be sourced from uninfested areas).Should areas proposed for rehabilitation be deemed to be uninterpretable, these areas will be treated asuninfected inline with the DEC’s strategy for the management of dieback. Additional information relatingto the management of dieback is available on the DEC website (www.dec.wa.gov.au/content/view/324/1789/).

Dieback management plans will include dieback hygiene measures to ensure all vehicles and equipmentare cleaned/washed down prior to mobilising to site, and when moving from dieback infected to diebackfree areas within the site.

All topsoil from the clearing of remnant vegetation within the proposed industrial site should be reusedwithin the SIP. It is preferable for the topsoil not to be stockpiled and to be directly returned onto therehabilitation sites. Topsoil stockpiles (if required) should be as low as possible (less than 2m) with alarge surface area for the preservation of seed stock and microbial activity. Stockpiles should be locatedin previously cleared areas, adjacent to the proposed rehabilitation areas. No stockpiles are to be locatedwithin the vicinity of the wetland to the south of Area A.

There are two different vegetation types being reinstated in the rehabilitation areas. The topsoil from thesimilar vegetation type being cleared should be respread in the rehabilitation areas identified to bereinstated with a similar vegetation type (i.e. topsoil from Jarrah – Banksia – Xylomelum – Sheoak areacleared should be respread on area to be revegetated with Jarrah – Banksia – Xylomelum – Sheoakspecies and topsoil from Melaleuca preissiana – Kunzea glabrescens area cleared should be respreadon area to be revegetated with Melaleuca preissiana – Kunzea glabrescens species).

2.3 Mulching/BrushingClearing of remnant vegetation within adjacent areas of the SIP creates the opportunity to collect seedrich mulch/brushing from areas to be cleared. Low growing vegetation slashed in the summer afterflowering should be collected and spread across the rehabilitation areas to provide additional seed, aid insoil moisture retention, erosion control and provide protection for germinants and newly planted tubestock.

As for the topsoil, the mulch/brushing collected should be separated by vegetation types and should bespread on the corresponding vegetation type being revegetated.

2.4 Species MixThe species list for the revegetation within the Shotts Industrial Park has been developed using previousflora and vegetation surveys undertaken for site. These are listed in Table 2, Appendix B. A typical ratioof the various strata for Jarrah forest is 1 tree : 2 shrubs : 3 herbs. Typically a dampland such as theMelaleuca preissiana – Kunzea glabrescens Low Woodland would have a dense overstorey withscattered low growing herbs. In this instance a ratio of 1 tree/tall shrub : 2 shrubs is considered to beappropriate.

It is not possible or practical to replace all of the species that were present pre-clearing as many planttaxa in WA are recalcitrant species that cannot be propagated using conventional methods. The species

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list for revegetation of Areas A and B are the same. With the exception of the Kingias andXanthorrhoeas, all of the species identified on the list can be propagated and it is proposed that thesespecies are reintroduced to the site as tube stock.

The species mix for revegetation provides a range of feed species used by Black Cockatoos includingProteaceous plants such as Banksia, Hakea and Grevillea; Marri and Jarrah (Myrtaceae family); andAllocasuarina species.

The presence of dieback has been identified as a potential constraint to the successful establishment ofthe preferred species mix as identified in Table 2 and Table 3, Appendix B. The Dieback Working Grouphas published a list of Western Australian native plants that are resistant to Phytophthora cinnamomi(dieback) and a list of Western Australian native plants that are susceptible to Phytophthora cinnamomi.These plant lists are included in Appendix C and can be used to identify replacement species should therehabilitation site be determined to be dieback infested.

2.4.1 Transplants

Kingia and Xanthorrhoea are very slow growing but transplant well. Both species are present in theremnant vegetation proposed for clearing. A number of these should be salvaged and transplanted intothe rehabilitation sites after site preparation and before tube stock is planted. Advice should be soughtfrom a specialist transplanting service regarding the ideal time to salvage and transplant these species.

2.5 Planting DensityA proposed planting density for the rehabilitation areas is one plant per m2. With correct site preparationand topsoil management, it is expected that the soil stored seed bank will germinate following substantialwinter rains resulting in a greater density.

The planting density of one plant per m2 allows room for some additional germination from the topsoil andmulching.

The total rehabilitation area is 6.45 ha. If a planting density of one plant per m2 is to be achieved then atotal of 64,500 tube stock will be required. Table 2 identifies local species that can be propagated andthe number of each species that should be planted as tube stock to achieve the ratio identified above.

2.6 Timing of Planting of Tube StockThere is no allowance in this plan for artificial watering of the rehabilitation areas. Where possible, tubestock should be planted following substantial winter rains. Ideal planting times are indicated in Table 1.The tubestock will establish quicker with warmer weather and longer daylight hours at the end of winter.This will also ensure survival through the first summer.

2.7 Weed ControlWeed control should be undertaken prior to any rehabilitation work on either of the rehabilitation sites.The rehabilitation sites should be inspected for weeds in the winter after significant rains. Appropriateweed control measures should be undertaken to reduce weed densities.

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2.8 Fuel Reduction BurningRehabilitation areas should not be burnt for a minimum of 7 years after planting, to allow species presentto reach reproductive maturity. Fuel reduction burning during this time is likely to reduce the success ofrehabilitation. This is not expected to cause a fire management issue as fuel loadings are unlikely toreach 8 tonnes per hectare in the first 7 years.

2.9 Monitoring and Completion CriteriaThe revegetation should be monitored on an annual basis after the summer which is when the mostattrition (death) of the planted tubestock and new germinants is likely to occur. The monitoring programshould be designed to inform a requirement for remediation works such as weed control and infillplanting. It is proposed that monitoring and remediation works be undertaken for a period of five yearsfollowing the rehabilitation to ensure the success of the revegetation program.

Monitoring of the rehabilitation areas should be undertaken annually in Autumn. One permanentlymarked 10 m x 10 m monitoring quadrat should be set up per hectare of revegetation. Informationrecorded for each quadrat should include:

Number of tubestock present;

Species of tubestock in quadrat;

Tubestock health;

Number of germinants;

Germinant species;

An estimate of the percentage canopy coverage of the native vegetation present within the quadrat;

Weed species present;

An estimate of the percentage coverage of the quadrat by weed species;

Any other observations such as erosion, fire or vandalism; and

Recommendations for remedial action.

It may not be possible to identify the species of some of the tubestock or germinant until they reachreproductive maturity. The most important thing here is to be able to identify the difference between localnative species and weed species.

Recommendations for remedial works should take into account the potential for dieback susceptiblespecies to die. These species should not be used in remedial plantings (check lists of resistant andsusceptible species in Appendix C).

2.9.1 Completion Criterion

The canopy cover of the tree layer across the site should be a minimum of 30% after five years. This willbe the equivalent of a “Low Woodland” (Vegetation Structural Classes Table 11; Bush Forever, 2000)and will have the potential to mature into a ’Woodland’ which is representative of the adjacent Jarrah-Banksia-Xylomelum-Sheoak Woodland and Melaleuca preissiana – Kunzea glabrescens Low Woodland.

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The completion criterion should also ensure a mix of trees, shrubs and herbs have established in therehabilitation areas. While the final density of plants per m2 may be lower than the original plantingdensity, it is expected that a minimum of 90% of the species planted as tube stock are established in therehabilitation areas after three years.

2.10 Remediation WorksRemediation works within the rehabilitation areas should be undertaken to ensure the completioncriterion as outline above is achieved. Remediation works may include:

Weed control;

Infill/extra planting; and

Erosion control e.g. brushing/mulching and/or topsoil replacement.

2.11 Time FrameA suggested time frame for the implementation of this rehabilitation plan has been provided in Table 1.This time frame provides a broad outline for a 5 year plan for the implementation of the revegetation, tobe commenced within 6 months following completion of construction.

Table 1 Time Frame for Rehabilitation and Monitoring Works

Activity Season Year Responsibility

Site inspection for weeds July/August 0 Proponent of DA4 /LandCorp

Order Tubestock for planting the followingwinter July/August 0 Proponent of DA4 /

LandCorp

Weed control August/September 0 Proponent of DA4 /LandCorp

Site preparation (as per Section 2.1) February/March 0 Proponent of DA4 /LandCorp

Mulch/Brush collection February/March 0 Proponent of DA4 /LandCorp

Weed control June/July 1 Proponent of DA4 /LandCorp

Plant Tubestock July/August 1 Proponent of DA4 /LandCorp

Revegetation Monitoring April/May 1 Proponent of DA4 /LandCorp

Order additional tubestock for plantingfollowing winter (year 2) July/August 1 Proponent of DA4 /

LandCorp

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Activity Season Year Responsibility

Weed control (if required) August/September 2 Proponent of DA4 /LandCorp

Weed control June/July 2 Proponent of DA4 /LandCorp

Plant Tubestock July/August 2 Proponent of DA4 /LandCorp

Revegetation Monitoring April/May 2 Proponent of DA4 /LandCorp

Order additional tubestock for plantingfollowing winter (year 3) July/August 2 Proponent of DA4 /

LandCorp

Weed control (if required) August/September 3 Proponent of DA4 /LandCorp

Weed control June/July 3 Proponent of DA4 /LandCorp

Plant Tubestock July/August 3 Proponent of DA4 /LandCorp

Revegetation Monitoring April/May 3 Proponent of DA4 /LandCorp

Order additional tubestock for plantingfollowing winter (year 4) July/August 3 Proponent of DA4 /

LandCorp

Weed control (if required) August/September 4 Proponent of DA4 /LandCorp

Weed control June/July 4 Proponent of DA4 /LandCorp

Plant Tubestock July/August 4 Proponent of DA4 /LandCorp

Revegetation Monitoring April/May 4 Proponent of DA4 /LandCorp

Order additional tubestock for plantingfollowing winter (year 5) July/August 4 Proponent of DA4 /

LandCorp

Weed control (if required) August/September 5 Proponent of DA4 /LandCorp

Weed control June/July 5 Proponent of DA4 /LandCorp

Plant Tubestock July/August 5 Proponent of DA4 /LandCorp

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Activity Season Year Responsibility

Revegetation Monitoring April/May 5 Proponent of DA4 /LandCorp

Order additional tubestock for plantingfollowing winter (year 6, if required) July/August 5 Proponent of DA4 /

LandCorp

2.12 ResponsibilityLandCorp proposes a lease arrangement with proponents of the SIP. The responsibility for rehabilitationand the ongoing management of rehabilitation areas within the SIP will be the responsibility of theproponent of DA4 and will form part of the formal lease agreements for the development area. LandCorpwill be responsible for rehabilitation and ongoing management of rehabilitation areas outside of theboundary of the SIP.

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3. References

Dieback Working Group website accessed 6 October 2010 http://www.dwg.org.au/go/publications-and-downloads/publications/index.cfm

GHD (2008) Collie Shotts Flora and Fauna Survey. Unpublished report for LandCorp.

Government of WA, 2000. Bush Forever Volume 1. Policies, Principles, Processes. Department ofEnvironmental Protection, Perth, Western Australia.

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Appendix A

Figures

Page 15: November 2010 - Landcorp · 61/24064/101479 Collie Shotts Industrial Park 3 Vegetation Rehabilitation Plan 1. Introduction LandCorp referred the proposed development of the Shotts

GHD House, 239 Adelaide Terrace Perth WA 6004 T 61 8 6222 8222 F 61 8 6222 8555 E [email protected] W www.ghd.com.au

E To Collie~7.5km

415,000

415,000

420,000

420,000

425,000

425,000

430,000

430,000

435,000

435,000

6,305,

000

6,305,

000

6,310,

000

6,310,

000

6,315,

000

6,315,

000

G:\61\2406409\GIS\Maps\MXD\612406409-G001_Fig01_Rev1.mxd© 2010. While GHD has taken care to ensure the accuracy of this product, GHD and LANDGATE, HARLEY SURVEY GROUP, GHD make no representations or warranties about its accuracy, completeness or suitability for any particular purpose. GHD and LANDGATE, HARLEY SURVEY GROUP, GHD cannot accept liability of any kind (whether in contract, tort or otherwise) for any expenses, losses, damages and/or costs (includingindirect or consequential damage) which are or may be incurred as a result of the product being inaccurate, incomplete or unsuitable in any way and for any reason.

LEGEND0 600 1,200 1,800 2,400 3,000

MetresMap Projection: Transverse Mercator

Horizontal Datum: Geocentric Datum of Australia (GDA)Grid: Map Grid of Australia 1994, Zone 50

LandCorpCollie Shotts Industrial Park

Vegetation Rehabilitation PlanFigure 1

Job NumberRevision 1

61-2406409

04 AUG 2010

Location Mapo Date

Data Source: Landgate: Cadastre - SLIP 20090320; Harley Survey Group: Proposed Shotts Industrial Park Boundary - 20090612; Landgate: Travellers Atlas - 2004; GHD: Rehabilitation Areas - 20100727. Created by: xntan, slee2, mjthompson, tgoad

1:60,000 (at A3)

! !

!

!

!

CAPEL

COLLIE

HARVEY

BUNBURY

DONNYBROOK

INDIAN OCEAN

Locality Map

Rehabilitation AreasProposed Industrial Park Boundaries

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GHD House, 239 Adelaide Terrace Perth WA 6004 T 61 8 6222 8222 F 61 8 6222 8555 E [email protected] W www.ghd.com.au

SHOT

TS R

IVER

RD

SOUT

H

1.77 Ha

SHOTTS RD

COALFIELDS RD

PREMIER RD

SHOTTS RIVER R D

COALFIELDS RD

2.88 Ha1.57 Ha

Area A6.22 Ha

Area B0.23 Ha

1b1b

1b

4e

4a

4b

2

1a

4c1b2

3b

1b

1b

1b

3b

1a

1b

3b

4d

3b

2

3a

3b3b

3b

5.27 ha

5.11 ha

4.22 ha

3.84 ha

2.59 ha

0.98 ha

2.59 ha

1.78 ha

1.54 ha

1.31 ha

1.13 ha

429,000

429,000

430,000

430,000

431,000

431,000

432,000

432,000

6,306,

000

6,306,

000

6,307,

000

6,307,

000

G:\61\24064\GIS\Maps\MXD\612406407-G001_Fig02_Rev7.mxd© 2010. While GHD has taken care to ensure the accuracy of this product, GHD and LANDGATE (SLIP) make no representations or warranties about its accuracy, completeness or suitability for any particular purpose. GHD and LANDGATE (SLIP) cannot accept liability of any kind (whether in contract, tort or otherwise) for any expenses, losses, damages and/or costs (including indirect or consequential damage) whichare or may be incurred as a result of the product being inaccurate, incomplete or unsuitable in any way and for any reason.

LEGEND0 100 200 300 400 50050

MetresMap Projection: Transverse Mercator

Horizontal Datum: Geocentric Datum of Australia (GDA)Grid: Map Grid of Australia 1994, Zone 50

LandCorpCollie Shotts Industrial Park

Figure 2

Job NumberRevision 7

61-2406407

20 Oct 2010

Rehabilitation Vegetation Typeso Date

Data Source: Landgate: Cadastre - 20100804; GHD: Proposed Industrial Park Boundary - 20090317; Landgate: Collie 2131 Feb 2008 Mosaic - 20091012; GA: Topo 250k Series 3 Topographic Data - 200607; GHD: Vegetation Retained, Rehabilitated - 20101020, Vegetation Types - 20080111, Emergency Access - 20100804; GHD: Possible Firebreak and Emergency Access - 20100812. Created by:kdiralu, tgoad,smhendrie,KDIRALU, sismail

1:10,000 (at A3)Vegetation Types

4a. Cleared Paddock

4b. Old Sand Quarry

4c. Old Shotts Townsite

4d. Plantation

4e. Infrastructure

Locality Map

1a. Jarrah-Marri - Sheoak Open Forest

1b. Jarrah-Banksia - Xylomelum - Sheoak Woodland

2. Banksia spp.- Sheoak - Muja Open Woodland3a. Melaleuca preissiana - Taxandria linearifolia - Kunzea glabrescens - Low Woodland3b. Melaleuca preissiana - Kunzea glabrescens - Low Woodland

!

!!

!

INDIANOCEAN

CAPEL

COLLIEBUNBURY

BINNINGUP

Locality Map

CadastrePossible Firebreak andEmergency Access

Proposed Boundary

Vegetation to be Retained

Area to be Rehabilitated

DA4

DA2DA3

DA5b

DA5a

DA1

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Appendix B

Rehabilitation Species

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Table 2 Rehabilitation Species and Numbers for the Jarrah- Banksia Woodland Area at Shotts Industrial Park

Family Genus Species Common Name Growth HabitHeight(m)

Numberrequiredfor Area A

Numberrequiredfor Area B Total

Fabaceae Kennedia coccinea Coral Vine climber 4062 166 4228Fabaceae Kennedia prostrata Scarlet Runner climber 4062 166 4228Ranunculaceae Clematis pubescens climber 4062 166 4228Haemodoraceae Anigozanthos manglesii herb 0.5 4062 166 4228Haemodoraceae Conostylis aculeata herb 0.3 4062 166 4228Hemerocallidaceae Dianella revoluta herb 0.3 4062 166 4228Juncaceae Juncus pallidus Pale Rush herb 1.5 4062 166 4228Dasypogonaceae Kingia australis Kingia shrub 3 824 33 857Fabaceae Jacksonia furcellata Grey Stinkwood shrub 3 824 33 857Fabaceae Mirbelia dilatata shrub 1.5 824 33 857Myrtaceae Callistemon glaucus Albany Bottlebrush shrub 3 824 33 857Myrtaceae Calothamnus quadrifidus One-sided Bottlebrush shrub 3 824 33 857Myrtaceae Darwinia citriodora Shrub 1 824 33 857Myrtaceae Hypocalymma angustifolium White Myrtle shrub 1 824 33 857Myrtaceae Kunzea glabrescens Spearwood shrub 3 824 33 857Myrtaceae Melaleuca incana subsp. incana shrub 3 824 33 857Myrtaceae Melaleuca thymoides shrub 1.5 824 33 857Proteaceae Grevillea manglesioides shrub 2 824 33 857Proteaceae Grevillea quercifolia Oak-leaf Grevillea shrub 0.7 824 33 857Proteaceae Hakea lissocarpha Honey Bush shrub 1.5 824 33 857Proteaceae Hakea prostrata Harsh Hakea shrub 3 824 33 857Proteaceae Hakea ruscifolia shrub 2 824 33 857Proteaceae Hakea trifurcata shrub 2 824 33 857Proteaceae Hakea varia Variable-leaved Hakea shrub 2 824 33 857

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Family Genus Species Common Name Growth HabitHeight(m)

Numberrequiredfor Area A

Numberrequiredfor Area B Total

Xanthorrhoeaceae Xanthorrhoea gracilis Graceful Grass Tree shrub 1.5 824 33 857Xanthorrhoeaceae Xanthorrhoea preissii Grass Tree shrub 1.5 824 33 857Fabaceae Acacia applanata small shrub 0.5 824 33 857Fabaceae Acacia nervosa Rib Wattle small shrub 0.5 824 33 857Fabaceae Acacia pulchella Prickly Moses small shrub 1.5 824 33 857Proteaceae Adenanthos obovatus Basket Flower small shrub 2 824 33 857Casuarinaceae Allocasuarina fraseriana Sheoak Tree 15 1353 54 1407Myrtaceae Corymbia calophylla Marri Tree 20 1353 54 1407Myrtaceae Eucalyptus decipiens Tree 15 1353 54 1407Myrtaceae Eucalyptus marginata Jarrah Tree 20 1353 54 1407Proteaceae Banksia attenuata Slender Banksia Tree 10 1353 54 1407Proteaceae Banksia grandis Bull Banksia Tree 10 1353 54 1407Proteaceae Xylomelum occidentale Woody Pear Tree 5 1353 54 1407

Total 56857 2299 59156

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61/24064/101479 Collie Shotts Industrial ParkVegetation Rehabilitation Plan

Table 3 Rehabilitation Species and Numbers for the Melaleuca preissiana – Kunzea glabrescens Woodland Area at ShottsIndustrial Park

Family Genus Species Common Name Growth HabitHeight(m)

Numberrequiredfor Area A

Total

Juncaceae Juncus pallidus Pale Rush Herb 2 274 274Fabaceae Acacia divergens shrub 2 274 274Fabaceae Acacia extensa Wiry wattle shrub 2 274 274Fabaceae Acacia pulchella Pickly Moses shrub 2 274 274Myrtaceae Callistemon glaucus Albany Bottlebrush shrub 3 274 274Myrtaceae Calothamnus lateralis shrub 1.5 274 274Myrtaceae Kunzea rostrata shrub 3 274 274Myrtaceae Pericalymma ellipticum Swamp Teatree shrub 3 274 274Fabaceae Acacia semitrullata small shrub 1 274 274Fabaceae Eutaxia virgata small shrub 1 274 274Fabaceae Euchilopsis linearis Swamp Pea small shrub 1 274 274Myrtaceae Darwinia oederoides small shrub 0.3 274 274Myrtaceae Hypocalymma angustifolium White Myrtle small shrub 1 274 274Myrtaceae Melaleuca incana subsp. incana small tree 3 445 445Myrtaceae Melaleuca preissiana Moonah small tree 6 445 445Myrtaceae Taxandria linearifolia Swamp peppermint small tree 5 445 445Myrtaceae Kunzea glabrescens Spearwood Tall shrub 4 445 445

Total 5342 5342

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61/24064/101479 Collie Shotts Industrial ParkVegetation Rehabilitation Plan

Appendix C

Dieback Working Group Western AustralianSpecies Lists

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Western Australian natives resistant toPhytophthora cinnamomi

Compiled by E. Groves, G. Hardy & J. McComb, Murdoch University

Information used to determine resistance to P. cinnamomi : 1a- field observations, 1b- field observation and recovery of P.cinnamomi; 2a- glasshouse inoculation of P. cinnamomi and recovery, 2b- field inoculation with P. cinnamomi and recovery.

Not Provided- no information was provided from the reference.

PLANT SPECIES NURSERYAVALABILITY

COMMON NAME ASSESSMENT REFERENCES

Acacia barbinervis Benth. 1b 12, 15Acacia baxteri Benth. Baxter's Wattle 1a 19Acacia browniana H.L.Wendl. 1b 15Acacia browniana var. intermedia 1a 20(E.Pritz)Maslin.Acacia cyclops G.Don. Coastal Wattle 1a A 20Acacia drummondii Lindl. Drummond's Wattle 1b A 15Acacia extensa Lindl. Wiry Wattle 1b 15Acacia huegelii Benth. 1b 16Acacia lateriticola Maslin Rib Wattle 1b 12, 15Acacia nervosa DC. 1b 12, 15Acacia preissiana (Meisn.) Maslin 1b 15Acacia pulchella R.Br. Prickly Moses 1a A 5Acacia saligna (Labill.) H.L.Wendl. Orange Wattle 1b A 16Acacia semitrullata Maslin. 1b 16Acacia urophylla Lindl. 1b A 12, 14, 15Agonis flexuosa (Willd.) Sweet. Peppermint 1b A 16Agonis juniperiana Schauer. Wattie NP 10Allocasuarina lehmanniana (Miq.) Dune Sheoak 1a 20L.A.S.JohnsonAllocasuarina humilis (Otto & F.Dietr.) Dwarf Sheoak 1a A 20L.A.S.JohnsonAllocasuarina microstachya (Miq.) 1a 20L.A.S.JohnsonAnarthria gracilis R.Br. 1a 20Anarthria prolifera R.Br. 1a 20Anarthria scabra R.Br. 1a 20Anigozanthos flavidus DC. Tall Kangaroo Paw 1b A 17Anigozanthos manglesii D.Don. Mangle's Kangaroo 1b A 16

Paw Anigozanthos rufus Labill. Red Kangaroo Paw 1b 17Asartea heteranthera 1a A 5, 10Astartea fascicularis (Labill.) DC. 1a A 20Astroloma pallidum R.Br. Kick Bush 1b 12, 15Baeckea pachyphylla (Benth.) 1a 20Baeckea camphorosmae Endl. Camphor Myrtle 1b A 5, 12, 15, 16Billardiera drummondiana (Putt.) E.M.Benn. 1b 15Billardiera variifolia DC. 1b 16Boronia crenulata (Sm.) Aniseed Boronia 1a A 20Boronia spathulata Lindl. Boronia 1b 15Bossiaea linophylla R.Br. 1a 20Bossiaea rufa R.Br. 1a 20Bossiaea webbii F.Muell. Water Bush 1a A 20Burchardia multiflora Lindl. Dwarf Burchardia 1a 20Burchardia umbellata R.Br. Milkmaids 1a 20Calothamnus affinis var longistamineus Turcz. 1a 20Calothamnus quadrifidus R.Br. One-sided Bottle 1a A 20

Brush Calothamnus sanguineus Labill. Silky-leaved Blood 1a A 20

Flower Calytix asperula (Schauer) Benth. Brush Starflower 1a 20Calytrix flavescens A.Cunn. Summer Starflower 1b 20Calytrix leschenaultii (Schauer) Benth. 1a 20Calytrix tenuiramea (Turcz.) Benth. 1a 20

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Western Australian natives resistant to Phytophthora cinnamomi (continued)

PLANT SPECIES NURSERYAVALABILITY

COMMON NAME ASSESSMENT REFERENCES

Cassytha flava Ness. Dodder Laurel 1b 16Cassytha glabella R.Br. Tangled Dodder 1b 16

Laurel Casuarina obesa Miq. Swamp Sheoak 1a A 5, 10Caustis dioica R.Br. 1a 20Chamaexeros serra (Endl.) Benth. Little Fringed Leaf 1a 20Chorizema aciculare (DC.) C.A.Gardner Needle-leafed 1a 20

Chorizema Clematis pubescens Endl. Common Clematis 1b 12, 15Comesperma calymega Labill. Blue-spiked Milkwort 1a 12Comesperma confertum Labill. 1a 20Comesperma virgatum Labill. Milkwort 1b 12, 15Conostylis aculeata R.Br. Prickly Conostylis 1b A 15, 16Conostylis pusilla Endl. 1b 15Conostylis serrulata R.Br. 1b 12, 15, 16Conostylis setigera R.Br. Bristly Cottonhead 1a 20Conostylis setosa Lindl. White Cottonhead 1b 12, 15Corymbia calophylla K.D.Hill & Marri 1a A 5, 12, 14, 15,16L.A.S.JohnsonCorymbia ficifolia (F. Muell.) K.D.Hill & 1a A 5L.A.S.JohnsonCryptostylis ovata R.Br. Slipper Orchid 1a 20Cyathochaeta avenacea (R.Br.) Benth. 1a 20Cyathochaeta clandestina (R.Br.) Benth. 1b 15Dampiera linearis R.Br. Common Dampiera 1b A 12, 16Darwinia citriodora (Endl.) Benth. Lemon-scented 1a A 5, 10

Darwinia Darwinia leiostyla (Turcz) Dorman 1a A 20Darwinia vestita (Endl.) Benth. Pom Pom Darwinia 1a 20Desmocladus fasciculatus (R.Br.) 1b 16B.G.Briggs & L.A.S.BriggsDesmocladus flexuosa (R. Br.) B.G.Briggs & 1b 16L.A.S.BriggsDodonaea viscosa Jacq. Sticky Hopbush 1a A 5, 10Drosera erthrorhiza Lindl. Red Ink Sundew 1a 20Drosera pallida Lindl. Pale Rainbow 1a 20Eriochilus dilatatus Lindl. White Bunny Orchid 1a 20Eriostemon spicatus A.Rich. Pepper and Salt 1b A 15, 16Eucalyptus accedens W.Fitzg. Powderpark Wandoo 1a A 5Eucalyptus angulosa Schauer Ridge-fruited Mallee 1a 20Eucalyptus astringens (Maiden) Maiden Brown Mallee NP 5Eucalyptus buprestium F.Muell. Apple Mallee 1a 20Eucalyptus camaldulensis Dehm. River Gum 1a A 5Eucalyptus conferruminata D.J.Carr & Bald Island Marlock 1a A 5S.G.M.CarrEucalyptus falcata Turcz Silver Mallet 1a 20Eucalyptus forrestiana Diels. Fuchsia Gum 1a A 5Eucalyptus gardneri Maiden Blue Mallet 1a 5Eucalyptus gomphocephala DC. Tuart 1a A 5Eucalyptus incrassata Labill. Lerp Mallee NP A 10Eucalyptus krusana F.Muell. Bookleaf Mallee 1a A 5, 10Eucalyptus laeliae Podger & Chippend Darling Range 1a A 5, 10

Ghost-Gum Eucalyptus lehmanniii (Schauer) Benth. Bushy Yate 1a A 19Eucalyptus megacarpa F.Muell. Bullich 1a A 5, 10Eucalyptus occidentalis Endl. Flat-topped Yate 1a A 5, 10Eucalyptus pachyloma Benth. Kalgan Plains Mallee 1a 20Eucalyptus patens Benth. Swan River Blackbutt 1a 5Eucalyptus preissiana Schauer Bell Fruited Mallee 1a A 20Eucalyptus rudis Endl. Flooded Gum 1a A 5Eucalyptus salmonophloia F.Muell. Salmon Gum NP A 10Eucalyptus spathulata Hook. Swamp Mallet 1a A 5

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Western Australian natives resistant to Phytophthora cinnamomi (continued)

PLANT SPECIES NURSERYAVALABILITY

COMMON NAME ASSESSMENT REFERENCES

Eucalyptus uncinata Turcz Hook-leafed Mallee 1a 20Eucalyptus wandoo Blakey. Wandoo 1a A 5, 10Gahnia trifida Labill. coast Saw-Sedge 1a 20Gompholobium capitatum A.Cunn. 1b 15Gompholobium tomentosum Labill. Hairy Yellow Pea 1b A 16Goodenia caerulea R.Br. 1a 20Goodenia scapigera R.Br. White Goodenia 1a 20Grevillea fasciculata var linearis R.Br. 1a 20Grevillea hookeriana Meisn. Red Toothbrushes 1a A 5, 10Grevillea synapheae R.Br. Catkin Grevillea 1b A 15Haemodorum paniculatum Lindl. Mardja 1b 16Hakea amplexicaulis R.Br. Prickly Hakea 1b 15Hakea corymbosa R.Br. Cauliflower hakea 1a 20Hakea lissocarpha R.Br. Honey Bush 1b A 12, 15, 16Hakea petiolaris Meisn. Sea Urchin Hakea 1a A 5, 10Hakea scoparia Meisn. NP A 10Hardenbergia comptoniana (Andrews) Native Wisteria 1b A 10, 16Benth.Hemiandra pungens R.Br. 1b A 16Hemigenia curvifolia F.Muell. Snakebush 1b 15Hibbertia silvestris Diels. 1b 15Hibbertia racemosa (Endl.) Gilg. Stalked Guinea 1b 16

FlowerHibbertia vaginata (Benth.) F.Muell. 1b 16Hovea chorizemifolia (Sweet) DC. Holly-leaved Hovea 1b 12, 15Hovea trisperma Benth. Common Hovea 1b A 16Hypocalymma angustifolium (Endl.) White Myrtle 1b 12, 15, 16SchauerHypocalymma myrtifolium Turcz. 1a 20Hypocalymma speciosum Turcz. 1a 20Isotoma hypocrateriformis (R.Br.) Druce. Woodbridge Poison 1a 12Johnsonia lupulina R.Br. Hooded Lily 1a 20Johnsonia teretifolia Endl. Hooded Lily 1a 20Kennedia coccinea Vent. Coral Vine 1b A 15Kennedia prostrata R.Br. Scarlet Runner 1b A 10, 15Kunzea preissiana Schauer 1a 20Lechenaultia biloba Lindl. Blue Lechenaultia 1b A 12, 15Lepidosperma scabrum Nees. 1b 15Lepidosperma squamatum Labill. 1a 12Lepidosperma tenue Benth. 1b 15Lepidosperma tetraquetrum Nees 1a 14Lepidosperma viscidum R.Br. Sticky Sword Sedge 1a 20Leporella fimbriata (Lindl.) A.S.George Hare Orchid 1a 20Leptocarpus tenax (Labill.) R.Br. Slender Twine Rush 1a 20Leptomeria cunninghamii Miq. 1b 15Leptomeria eriocoides Miq. 1a 20Leptospermum erubescens Schauer Roadside Teatree 1a 20Leucopogon glabellus R.Br. 1b 16Leucopogon pendulus R.Br. 1a 20Levenhookia pusilla R.Br Midget Stylewort 1a 12Lindsaea linearis SW. Screw Fern 1a 20Lobelia gibbosa Labill. Tall Lobelia 1a 20Lobelia rhytidosperma Benth. Wrinkled-Seeded 1a 12

LobeliaLogania serpyllifolia R.Br. 1a 20Lomandra integra T. Macfarlane 1b 16Lomandra nigricans T. Macfarlane 1b 16Lomandra pauciflora (R.Br.) Ewart. 1a 20Lomandra preissii (Endl.) Ewart. 1a 20Lomandra sonderi (F.Muell.) Ewart. 1b 16Lyginia barbata R.Br. 1b 16

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Western Australian natives resistant to Phytophthora cinnamomi (continued)

PLANT SPECIES NURSERYAVALABILITY

COMMON NAME ASSESSMENT REFERENCES

Macropidia fuliginosa (Hook.) Druce. Black Kangaroo Paw 2a A 17Meeboldina scariosa (R.Br) B.G.Briggs & 1b 16L.A.S.Briggs.Melalecua suberosa (Schauer) Corky Honeymyrtle 1a 20C.A.GardnerMelaleuca cuticularis Labill. Saltwater Paperbark 1a A 20Melaleuca diosmifolia Andrews. 1a A 5, 10Melaleuca holosericea Schauer 1a 19Melaleuca lanceolata Otto. Rottnest Teatree 1a A 5, 10Melaleuca laxiflora Turcz. 1a 14Melaleuca macronychia Turcz. 1a 5Melaleuca nesophila F.Muell. Mindiyed 1a A 5, 10Melaleuca pentagona Labill. 1a A 5, 10Melaleuca preissiana Schauer Moonash 1b A 16Melaleuca pulchella R.Br. Claw Flower 1a A 5, 10Melaleuca seriata Lindl. 1a A 20Melaleuca spathulata Schauer. 1a A 5, 10Melaleuca violacea Schauer. 1a A 5, 10Mesomelaena graciliceps (C.B.Clarke) 1a 12K.L.WilsonMesomelaena stygia (R.Br.) Nees 1a 20Mesomelaena tetragona (R.Br.) Benth. Semaphora Sedge 1b 15, 16Millotia tenuifolia Cass. Soft Millotia 1a 12Mirbelia dilatata R.Br. Holly-leaved Mirbelia 1b A 15Myoporum insulare R.Br. Blueberry Tree NP A 10Eucalyptus decurva F.Muell. Slender Mallee 1a 20Nuytsia floribunda (Labill.) Fenzl. Christmas Tree 1b A 16Olax phyllanthi (Labill.) R.Br. 1a 20Opercularia echinocephala Benth. Bristly Headed Stink 1b 12, 15

WeedOrthrosanthus laxus (Endl.) Benth. Morning Iris 1b A 16Paraserianthes lophantha (Willd). Benth. Albizia NP 10Patersonia pygmaea Lindl. Pygmy Patersonia 1b 12, 15Pentapeltis peltigera (Hook) Bunge. 1b 12, 15Persoonia aff. saccata R.Br. Snottygobble 1b 16Phlebocarya ciliata R.Br. 1b 16Phyllanthus calycinus Labill. False Boronia 1b A 12, 15Pimelea hispida R.Br. Bristly Pimelia 1a 20Pittosporum phylliraeoides DC. Weeping 1a A 5

PittosporumPlatysace tenuissima (Benth.) C.Norman 1b 15Poa poiformis (Labill.) Druce Coastal Poa 1a A 17Pteridium esculentum (G.Frost) Cockayne Bracken 1a 20Ptilotus manglesii (Lindl.) F.Muell. Pom Poms 1b 15Pultenea ericifolia Benth. 1a 20 Harpereria confertospicatus (Steud.) 1a 20B.G.Briggs & L.A.S.JohnsonScaevola striata R.Br. Royal Robe 1b 15Schoenus curvifolius (R.Br.) Roem. & Schult. 1b 16Schoenus pdicellatus (R.Br.) Benth. 1a 20Schoenus rigens S.T.Blake 1b 16Austrostipa compressa (R.Br.) S.W.L.Jacobs & 1a 20J.EverettStylidium brunonianum Benth. Pink Fountain 1a 20

TriggerplantStylidium imbricatum Benth. Tile leafed 1a 20

TriggerplantStylidium piliferum subsp minor (Mildbr.) 1a 20CarlquistStylidium scandens R.Br. Climbing Triggerplant 1a 12, 20

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Western Australian natives resistant to Phytophthora cinnamomi (continued)

PLANT SPECIES NURSERYAVALABILITY

COMMON NAME ASSESSMENT REFERENCES

Stylidium verticillatum F.Muell. Pink Mountain 1a 20Triggerplant

Synaphea petiolaris R.Br. 1b 15Taxandria floribunda (Turcz) J.R.Wheeler & 1a 20N.G.MarchantTaxandria parviceps Schauer. 1a 5Tetraria capillaris (F.Muell.) J.M.Black Hair Sedge 1a 20Tetraria octandra (Nees) Kuk. 1a 12Thysanotus dichotomus (Labill.) R.Br. Branching Fringed 1b 15

LilyThysanotus tenellus Endl. 1b 16Trichocline spathulata (DC.) J.H.Wills Native Gerbera 1b 12, 15Tricoryne elatior R.Br. Yellow Autumn Lily 1b 16Utricularia multifida R.Br. 1a 20Verticordia habrantha Schauer Hidden Featherflower 1a 20Xanthosia atkinsoniana F.Muell. 1b 12, 15Xanthosia candida (Benth.) Steud. 1b 12, 15Xanthosia huegelii (Benth.) Steud. 1b 16Xanthosia rotundifolia DC. Southern Cross 1a 20

W O R K I N G G R O U P

For more information please contact your local government authority or the Dieback Working GroupPhone: 0438 044 488Web: www.dwg.org.au

References used to Compile Lists of Western Australian Natives Susceptible and Resistant to Phytophthora cinnamomi.Compiled by E. Groves, G. Hardy & J. McComb, Murdoch University

REFERENCES:1. Alcoa of Australia (2002). Indicators of P. cinnamomi used by Interpreters. Environment Research Bulletin.2. Cho, J. J. (1983). Variability in susceptibility of some Banksia Species to Phytophthora cinnamomi and their distribution in Australia.

Plant Disease, 67; 869-871.3. Edmiston, R. J. (1989). Plants Resistant to Dieback. Department of Conservation and Land Management. 1-89.4. Environment Australia. (2001). Threat Abatement Plan for Dieback caused by the root-rot fungus Phytophthora cinnamomi.5. Gardner, J. H. & Rokich, P. A. (1987). Phytophthora cinnamomi in operational and rehabilitated bauxite mine area in South-western Australia. Alcoa of

Australia Environment Research Bulletin.13.6. Hart, R. (1983). Report on Dieback due to Phytophthora cinnamomi in Two People's Bay Nature Reserve.Department of Fisheries and Wildlife.7. Hill. (1990). Dieback Diseases and other Phytophthora spp. in the Northern Kwongon. In Nature,Conservation, Landscape and Recreational Values of

the Lesueur Area. A report to the Environmental Protection Authority from the Department of Conservation and Land Management. eds. A. Burbidge, S. D. Hopper & S. van Leeuwen, EPA. WA.8. Keighery, G. (1992). The impact of Phytophthora species on rare plants. In Dieback-What is the Future ?,

M. J. Freeman, R. Hart & M. Ryall, Northern Sandplains Dieback Working Group. Perth, pp. 29-36.9. Lee, T. C. & Wicks, T. J. (1977). Phytophthora cinnamomi in native vegetation in south Australia. Australasian Plant Pathology Newsletter, 6; 22-23.10. Marks, G. C. & Smith, I. W. (1991). The cinnamon fungus in Victorian forests. Victorian Government Publications, Melbourne11. McCredie, T. A., Dixon, K. W. & Sivasithamparam, K. (1985). Variability in the resistance of Banksia L.f. species to Phytophthora cinnamomi. Australian

Journal of Botany, 33; 629-637.12. McDougall, K. L., Hardy, G. E. S. J. & Hobbs, R. J. (2001). Additions to the host range of Phytophthora cinnamomi in the jarrah (Eucalyptus marginata)

forest of Western Australia. Australian Journal of Botany, 49; 193-19813. McDougall, K. L., Hobbs, R. J. & Hardy, G. E. S. J. (2002). Vegetation of Phytophthora cinnamomi-infested and adjoining uninfested sited in the northern

jarrah (Eucalyptus marginata) forest of Western Australia. Australian Journal of Botany, 50; 277-288.14. Podger, F. D. (1972). Phytophthora cinnamomi, a cause of lethal disease in indigenous plant communities in Western Australia.

Phytopathology, 62; 972-981.15. Shearer, B. L. & Dillon, M. (1996). Susceptibility of plant species in Banksia woodlands on the Swan Coastal Plain, Western Australia, to infection by

Phytophthora cinnamomi. Australian Journal of Botany, 44; 433-445.16. Shearer, B. L. & Dillon, M. (1995). Susceptibility of plant species in Eucalyptus marginata forest to infection by Phytophthora cinnamomi. Australian

Journal of Botany, 43; 113-134.17. Titze, J. F. & Palzer, C. R. (1969). Host list of Phytophthora cinnamomi Rands with special reference to Western Australia. Forestry and Timber Bureau,

Department of National Development. Technical Note No. 1.18. Tynan, K. M., Scott, E. S. & Sedgley, M. (1998). Evaluation of Banksia species for response to Phytophthora infection.

Plant Pathology, 47; 446-455.19. Tynan, K. M., Wilkinson, C. J., Holmes, J. M., Dell, B., Colquhoun, I. J., McComb, J. A. & Hardy, G. E. St. J. (2001). The long-term ability of phosphite to

control Phytophthora cinnamomi in two native plant communities of Western Australia. Australian Journal of Botany, 49; 761-770.20. Wills, R. T. (1993). Unpublished data.

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Western Australian natives susceptible toPhytophthora cinnamomi.

Compiled by E. Groves, G. Hardy & J. McComb, Murdoch University

Information used to determine resistance to P. cinnamomi : 1a- field observations, 1b- field observation and recovery of P.cinnamomi; 2a- glasshouse inoculation of P. cinnamomi and recovery, 2b- field inoculation with P. cinnamomi and recovery.

Not Provided- no information was provided from the reference.

PLANT SPECIES NURSERYAVALABILITY

COMMON NAME ASSESSMENT REFERENCES

Acacia campylophylla Benth. 1b 15Acacia myrtifolia (Sm.) Willd. 1b A 9Acacia stenoptera Benth. Narrow Winged 1b 16

Wattle Actinostrobus pyramidalis Miq. Swamp Cypress 2a 17Adenanthos barbiger Lindl. 1a A 1, 13, 16Adenanthos cumminghamii Meisn. Albany Woolly Bush NP A 4, 8Adenanthos cuneatus Labill. Coastal Jugflower 1a A 1, 6Adenanthos cygnorum Diels. Common Woolly Bush 2 1, 7Adenanthos detmoldii F. Muell. Scott River Jugflower 1a 1Adenanthos dobagii E.C. Nelson Fitzgerald Jugflower NP R 4,8Adenanthos ellipticus A.S. George Oval Leafed NP 8

AdenanthosAdenanthos filifolius Benth. 1a 19Adenanthos ileticos E.C. George Club Leafed NP 8

AdenanthosAdenanthos meisneri Lehm. 1a A 1Adenanthos obovatus Labill. Basket Flower 1b A 1, 7 14,16Adenanthos oreophilus E.C. Nelson 1a 19Adenanthos pungens ssp. effusus Spiky Adenanthos NP R 4Adenanthos pungens ssp. pungens NP R 4Adenanthos sericeus Labill. Woolly Bush 1a A 1Agonis linearifolia (DC.) Sweet Swamp Peppermint 1b 6Taxandria linearifolia (DC.) J.R Wheeler &N.G MerchantAgrostocrinum scabrum (R.Br) Baill. Bluegrass 1 12Allocasuarina fraseriana (Miq.) L.A.S. Sheoak 1b A 1, 6, 14JohnsonAllocasuarina humilis (Otto & F. Dietr.) Dwarf Sheoak 1a A 1, 7 14L.A.S. JohnsonAllocasuraina thuyoides (Miq.) L.A.S. Horned Sheoak 1a 19JohnsonAndersonia axilliflora (Stschegl) Druce Giant Andersonia NP R 4Andersonia caerulea R.Br. Foxtails 1a 1, 6Andersonia heterophylla Sond. 2 1, 7Andersonia lehmanniana Sond. 1a 1, 7Andersonia pinaster Lemson. 1a R 20Andersonia simplex (Stschegl.) Druce Spiked Andersonia 1b 6Aotus passerinoides Meisn. 1a 14, 17Astroloma cilatum (Lindl.) Druce Candle Cranberry 1b 3Astroloma xerophyllum (DC.) Sond. 2 1, 7, 18Banksia aculeata A.S George 1a 20Banksia ashbyi Baker. Ashby's Banksia 1b, 2a A 2Banksia attenuata R.Br Slender Banksia 1b, 2b A 1, 11, 14, 16Banksia audax C.A. Gardner 2a 11Banksia baueri R.Br Woolly Banksia 1b, 2a A 1, 2, 11Banksia baxteri R.Br Baxter's Banksia 1b A 1, 2, 11Banksia brownii R.Br Feather leaved 2a R 4, 2, 8, 11

BanksiaBanksia burdettii Baker f. Burdett's Banksia 2a A 2, 11Banksia caleyi R.Br. Cayley's Banksia 2a A 2, 11Banksia candolleana Meisn. Propeller Banksia 2a 2, 11Banksia coccinea R.Br. Scarlet Banksia 2a A 1, 2, 11Banksia cuneata A.S. George Quairading Banksia 2a R 8, 11

RARESPECIES

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Western Australian natives susceptible to Phytophthora cinnamomi (continued)

PLANT SPECIES NURSERYAVALABILITY

COMMON NAME ASSESSMENT REFERENCESRARESPECIES

Banksia dryandroides Sweet Dryandra-leaved 2a 11Banksia

Banksia elderiana F. Muell. & Tate Swordfish Banksia 2a 11Banksia gardneri A.S. George 2a 11Banksia gardneri var brevidentata A.S. 1a 20GeorgeBanksia gardneri var gardneri A.S. George 1a 20Banksia goodii R.Br Good's Banksia NP R 4, 8Banksia grandis Willd. Bull Banksia 2a A 1, 2, 11, 14, 15Banksia hookeriana Meisn. Hooker's Banskia 2a A 2, 11Banksia ilicifolia R.Br. Holly-leaved Banksia 1b 1, 14, 16Banksia laevigata Meisn. Tennisball Banksia 2a 11Banksia laricina C.A. Gardner Rose Banksia 2a 2, 11Banksia lemanniana Meisn. Lemann's Banksia 2a A 11Banksia lindleyana Meisn. Porcupine Banksia 2a 2, 11Banksia littoralis R.Br. Swamp Banksia 2a A 1, 11, 14Banksia lullfitzii C.A. Gardner 2a 11Banksia media R.Br. Southern Plains 2a A 1, 11

BanksiaBanksia menziesii R.Br. Firewood Banskia 1b, 2a A 1, 2, 11, 14, 16Banksia micrantha A.S George 1a 20Banksia nutans R.Br. Nodding Banksia 1a, 2a 1, 2, 11Banksia occidentalis R.Br. Red Swamp Banksia 1a, 2a A 1, 2, 11, 20Banksia oligantha A.S. George Wagin Banksia NP R 4, 8Banksia oreophila A.S George Mountain Banksia 1a 20Banksia petiolaris F. Muell. 2b A 11Banksia pilostylis C.A. Gardner 2b A 11Banksia praemorsa Andrews Cut-leaf Banksia 2a A 1, 11Banksia prionotes Lindl. Acorn Banksia 1b, 2a A 1, 2, 11Banksia pulchella R.Br. 2a 11Banksia quercifolia R.Br. Oak-leafed banksia 1a 1, 6Banksia repens Labill. Creeping Banksia 2b A 11Banksia seminuda (A.S. George) Rye River Banksia 1a A 1Banksia speciosa R.Br. Showy Banksia 1b, 2a A 1, 2, 11Banksia sphaerocarpa R.Br. Round- fruit Banksia 1b, 2a 1, 2, 11Banksia telmatiaea A.S. George Swamp fox Banksia 2 1, 7Banksia tricuspis Meisn. Pine Banksia NP 8Banksia verticillata R.Br. Albany Banksia 2a R 8, 11Banksia victoriae Meisn. Woolly Orange 2b A 11

Banksia Beaufortia anisandra Schauer 1b 6Beaufortia micrantha Schauer Little Bottlebrush 1a A 20Boronia fastigiata Bartl. Bushy Boronia 1 13Boronia revoluta Paul G. Wilson Ironcaps Boronia NP R 4Bossiaea eriocarpa Benth. Common Brown Pea 1b A 6, 16Bossiaea ornata (Lindl.) Benth. Broad leaf Brown Pea 1b 1, 3Brachysema papilio Crisp. NP R 4Calothamnus villosus R.Br. 1a 7Chamelaucium erythrochlora N.G. NP R 8Marchant & KeigheryChamelaucium griffinii N.G. Marchant & NP R 8KeigheryChamelaucium roycei N.G. Marchant & NP R 8KeigheryConospermum stoechadis Endl. Common Smokebush 1a A 1, 7Conospermum toddii F.Muell. Victorian Desert NP 8

SmokebushConospermum triplinervium R.Br. Tree Smokebush 2b A 7Conostephium pendulum Benth. Pearl flower 1b 1, 16Crowea angustifolia Sm. Crowea NP 1Dampiera alata Lindl. Winged-stem 1a 7

Dampiera

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PLANT SPECIES NURSERYAVALABILITY

COMMON NAME ASSESSMENT REFERENCESRARESPECIES

Darwinia collina C.A. Gardner Yellow NP R A 4, 8Mountain Bell

Darwinia macrostegia (Turcz) Benth. Mondorup Bell NP R A 4Darwinia meeboldii C.A. Gardner Cranbrook NP R 4, 8

BellDarwinia oxylepis N.G. Marchant & Gillam's Bell 1a R A 1, 8KeigheryDarwinia squarrosa (Turcz) Domin. Pink Mountain Bell 1a R 1, 9Darwinia wittwerorum N.G. Marchant & 1a R 1, 11KeigheryDasypogon bromeliifolius R.Br. Pineapple Bush 1b 1, 7, 16Daviesia decurrens Meisn. Prickly Bitter-Pea 1b A 15, 13Daviesia incrassata Sm. 1a 7Daviesia inflata Crisp. 1a 19Daviesia megacalyx Crisp. NP R 4Daviesia physodes G.Don. NP 19Daviesia preissii Meisn.Daviesia pseudaphylla Crisp. NP R 4Daviesia rhombifolia Meisn. 1b 15Dianella revoluta R.Br. Blueberry Lily 1b A 15Dryandra falcata R.Br. Prickly Dryandra 1a 20Dryandra plumosa R.Br. 1a 20Dryandra pteridifolia R.Br. Tangled Honeypot 1a 20Dryandra anatona A.S. George NP R 4Dryandra arctotidis R.Br. 1a 1, 20Dryandra armata R.Br. Prickly Dryandra 1a 1Dryandra bipinnatifida R.Br. 1a 1Dryandra cirsioides Meisn. 1a 20Dryandra formosa R.Br. Showy Dryandra 1b A 1, 6Dryandra ionthocarpa A.S. George 1a R 20Dryandra lindleyana Mesin. 1a A 1Dryandra mimica A.S. George Summer Honeypot NP 8Dryandra montana A.S. George NP R 4Dryandra mucronulata R.Br. Swordfish Dryandra 1a 20Dryandra nivea (Labill.) R.Br. Couch Honeypot 1a 1, 7, 14Dryandra pteridifolia R.Br. Tangled Honepot 1a 1Dryandra plumosa R.Br. 1a 20Dryandra quercifolia Meisn. Oakleafed Dryandra 1a 20Dryandra seneciifolia R.Br. 1a 1Dryandra serra R.Br. Serrate-leaved 1a 1

DryandraDryandra serratuloides Meisn. NP 4, 8Dryandra serratuloides Meisn. ssp. Perissa NP R 4, 11A.S GeorgeDryandra sessilis (Knight) Domin. Parrot Bush 1 A 1, 13Dryandra squarrosa R.Br. Pringle 1a 1Dryandra squarrosa R. Br. ssp. argillacea NP R 4A.S. GeorgeDryandra tenuifolia R.Br. 1a 20Eucalyptus marginata Sm. Jarrah 2b A 1, 14Eucalyptus todtiana F. Muell. Coastal Blackbutt 2a A 7, 14Evandra aristata R.Br 1a 1Gompholobium polymorphum R. Br. 2a 13Grevillea calliantha Makinson & Olde NP R 8Grevillea cirsiifolia Meisn. Varied-leaf Grevillea NP 8Grevillea crithmifolia R.Br. 1b A ShivasGrevillea saccata Benth. Pouched Grevillea NP A 8Grevillea tripartita Meisn. 1a 20Hakea ambigua Meisn. 1a 20Hakea baxteri R. Br Fan Hakea 1a 1Hakea cucullata R. Br. Hood leaved Hakea 1a 1

Western Australian natives susceptible to Phytophthora cinnamomi (continued)

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PLANT SPECIES NURSERYAVALABILITY

COMMON NAME ASSESSMENT REFERENCESRARESPECIES

Hakea flabellifolia Meisn. Fan-leaved Hakea NP 19Hakea lehmanniana Meisn. Blue Hakea 1a 20Hakea marginata R.Br. 1a 20Hakea oleifolia (Sm.) R. Br. 1a 1Hakea pandanicarpa ssp. crassifolia 1a 1, 20(Meisn.) R.M. BakerHakea prostrata R. Br. Harsh Hakea 1a A 1Hakea trifurcata (Sm.)R.Br Two-leaf Hakea 1a A 1Hakea undulata R.Br. Wavy-leafed Hakea 1a 1, 20Hibbbertia acerosa (DC.) Benth. Needle leaved Guinea 1b 3

FlowerHibbertia amplexicaulis Steud. 1b 15, 13, 3Hibbertia commutata Steud. 1 13Hibbertia desmophylla (Benth.) F. Muell. 1b 6Hibbertia furfuracea (DC.) Benth. NP 19Hibbertia huegelli (Endl.) F. Muell. 2a 13Hibbertia hypercoides (DC) Benth. 1b A 1, 7, 16Hibbertia inconspicua Steud. 1a 1Hibbertia lineata Steud. 1b 15Hibbertia montana Steud. 1b 3, 15Hibbertia montana var major Steud. 1b 3Hibbertia quadricolor Domin. 1b 13, 15Hibbertia rhadinopoda Domin. 2a 12Hibbertia stellaris Endl. 1b A 13Hovea elliptica (Sm.) D.C.. Tree Hovea 1b A 17Hovea pungens Benth. Devil's Pins 2a 14Hybanthus floribundus (Lindl.) F. Muell. 2a 12Hypocalymma robustum (Endl.) Lindl. Swan River Myrtle 1b A 1, 7, 15Hypocalymma strictum Schauer 1a A 20Isopogon attenuatus R.Br. 2b 17Isopogon axillaris R.Br. 1a 1Isopogon baxteri R.Br. Stirling Range 1a 20

ConeflowerIsopogon buxifolius R.Br. var obovatus 1a 20Benth.Isopogon formosus R.Br. Rose Coneflower 1b A 1Isopogon sphaerocephalus Lindl. Drumstick Isopogon 1b 1, 3, 15Isopogon teretifolius R.Br. var 1a 20petrophiloides.(R.Br) D. ForemanIsopogon trilobus R.Br. Barrel Coneflower 1a 20Isopogon uncinatus R. Br. NP R 4, 8Jacksonia floribunda Endl. Holly Pea 1a 1, 7, 17Jacksonia furcellata (Bonpl.) D.C. 1b A 16Jacksonia horrida D.C. 1a 1Jacksonia spinosa (Labill.) R.Br. 1b 6Jacksonia sternbergiana Huegl. Stinkwood 1b 16Kunzea ericifolia (Sm). Heynh. Spearwood 1b A 16Kunzea sulphurea Torey & P. Morris 1a 1Labichea punctata Benth. Lance-leaved Bassia 1a 12Lambertia ericifolia R.Br. Heath-leaved 1a 20

HoneysuckleLambertia echinata ssp. echinata R.Br. 1a R 4, 1, 8Lambertia echinata ssp. occidentalis NP R 4KeigheryLambertia fairallii Keighery Fairall's Honeysuckle NP R 4, 8Lambertia inermis R.Br. Chittick 1a 19Lambertia multiflora Lindl. Many-Flowered NP 19

HoneysuckleLambertia orbifolia CA Gardner Round-leaved NP R 4, 8

HoneysuckleLambertia uniflora R.Br. 1a 20

Western Australian natives susceptible to Phytophthora cinnamomi (continued)

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PLANT SPECIES NURSERYAVALABILITY

COMMON NAME ASSESSMENT REFERENCESRARESPECIES

Lasiopetalum floribundum Benth. Free FloweringLasiopetalum

Latrobea genistoides (Meisn.)Meisn. 1b 6Latrobea hirtella (Turcz) Benth. 1b 6Leucopogon australis R.Br. Spiked Beard-Heath 1a 1, 7, 14Leucopogon capitellatus D.C. 1b 1, 3, 7, 13, 15Leucopogon concinnus Benth. 1a 1Leucopogon conostephioides D.C. 1b 1, 16Leucopogon cymbiformis D.C. 1a 20Leucopogon distans R.Br. 1a 20Leucopogon distans R.Br. ssp. contractus 1a 20(Benth) J.M. PowellLeucopogon elegens Sond. 1b 6Leucopogon flavescens Sond. 1a 1, 6Leucopogon gibbosus Stschegl 1a 20Leucopogon gracillimus D.C. 1a 1Leucopogon nutans E. Pritzel. 1b 1, 15, 13Leucopogon obtectus Benth. Hidden Beard-Heath NP R 8Leucopogon oxycedrus Sond. 1b 3Leucopogon parviflorus Sond. 1a 1Leucopogon polymorphus Sond. 2b 7, 14Leucopogon propinquus R.Br. 1b 1, 3, 7, 15Leucopogon pulchellus Sond. 2b 17Leucopogon revolutus R.Br. 1a 1Leucopogon verticillatus R.Br. 1b 1, 3, 15Lomandra odora (Endl.) Ewart. Tiered Matrush 1a 1Lomandra sonderi (F. Muell.) Ewart. 1b 1, 3, 13, 13Loxocarya cinerea R.Br. 1 13Lysinema conspicuum R.Br. 1a 20Lysinema cillatum R.Br. Curry Flower 2b 7Macrozamia riedlei (Gaudich) C.A. Gardner Zamia 1b A 1, 14, 16Melaleuca scabra R.Br. Rough Honeymyrtle 2 A 1, 7Melaleuca subfalcata Turcz. 1a 20Melaleuca thymoides Labill. 1b A 16Monotoca tamariscina F. Muell. 1a 1Nemcia pulchella (Turcz) Crisp. 1a 1Opercularia vaginata Juss. Dogweed 1 13Patersonia babianoides Benth. 1 13Patersonia rudis Endl. Hairy Flag 1a 1Patersonia umbrosa Endl. Yellow Flags 1a 1Pattersonia occidentalis R.Br. Purple Flags 1b A 1, 7, 14, 15Pericalymma ellipticum (Endl.) Schauer Swamp Teatree 2a A 7, 14Persoonia elliptica R.Br. Spreading 1a 1

SnottygobblePersoonia longifolia R.Br. Snottygobble 1b 1, 13, 14, 17Petrophile biloba R.Br. Granite Petrophile 2a 14Petrophile divaricata R.Br. 1a 20Petrophile diversifolia R.Br. 1a 1Petrophile drummondii Meisn. 1a 7Petrophile ericifolia R.Br. 1a 20Petrophile linearis R.Br. Pixie Mops 1b 1, 7, 16Petrophile longifolia R.Br. Long Leaved 1a 20

ConebushPetrophile media R.Br. 1a 20Petrophile seminuda Lindl. 1a 20Petrophile serruriae R.Br. 1a 1Petrophile squamata R.Br. 1a 1Petrophile stricta Foreman 1a 7Pimelea suaveolens Meisn. Scented Banjine 1b 13, 15Platysace compressa (Labill.) Norman Tapeworn Plant 1a 13, 17Podocarpus drouynianus F. Muell. Wild Plum 1b A 1, 14

1b 3, 14, 15

Western Australian natives susceptible to Phytophthora cinnamomi (continued)

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PLANT SPECIES NURSERYAVALABILITY

COMMON NAME ASSESSMENT REFERENCESRARESPECIES

Scaevola calliptera Benth. Grey Scaevola 1 A 12Scholtzia involucrata (Endl.) Druce. Spiked Scholtzia 1a 1Sphenotoma dracophylloides Sond. 1a 20Sphenotoma gracile (R.Br.)Sweet Swamp Paper-heath 1a 20Sphenotoma squarrosum (Benth.) F. 2a 14Muell.Stirlingia latifolia (R.Br.) Steud. Blueboy 1a 1Stirlingia tenuifolia (R.Br.) Steud. 1a 20Stylidium amoenum R.Br. Lovely Triggerplant 2a 12Stylidium junceum R.Br. Reed Triggerplant 2a 12Stylidium schoenoides DC. Cow Kicks 1a 12Stylidium spathulatum R.Br. Creamy Triggerplant 1b 6Styphelia tenuiflora Lindl. Common Pinheath 1b 1, 13, 15Synaphea petiolaris R.Br. Synaphea 1a 1Synaphea polymorpha R.Br. Albany Synaphea 1a 20Tetrarrhena laevis R.Br. Forest Ricegrass 1a 13Tetratheca hirsuta Lindl. Blackeyed Susan 2b 12Tetratheca pilosa Labill. 1b 9Tetratheca setigera Endl. 1a 20Thomasia grandifolia Lindl. Large Flowered 2b 7

ThomasiaThyrptomene saxicola (Hook.) Schauer Rock Thryptomene 1a 7Thysanotus thyrsoideus Baker 1a 13Tremandra stelligera DC. 1a 1Trymalium ledifolium Fenzl. 1b 3, 14Verticordia densifolia Lindl. Compacted 1b A 4, 7, 14

FeatherflowerVerticordia huegelii Endl. Varigated 2b A 7, 14

FeatherflowerVerticordia nitens (Lindl.)Endl. Morrison 1a A 1, 7

Featherflower Xanthorrhoea nana D.A. Herb Dwarf Grasstree 1a 1Xanthorrhoea brevistyla D.A. Herb 1a 20Xanthorrhoea drummondii Harv. 1a 1Xanthorrhoea gracilis Endl. Graceful Grasstree 1b 1, 3, 7, 13, 14,

15Xanthorrhoea platyphylla D.J. Bedford 1a 20Xanthorrhoea preissii Endl. Grasstree 1b A 1, 3, 7, 13, 14,

16Xylomelum angustifolium Kippist & Meisn. Sandplain Woody Pear 1a 1Xylomelum occidentalis R. Br. Woody Pear 1a 1, 7

Western Australian natives susceptible to Phytophthora cinnamomi (continued)

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W O R K I N G G R O U P

For more information please contact your local government authority or the Dieback Working GroupPhone: 0438 044 488Web: www.dwg.org.au

Western Australian natives susceptible to Phytophthora cinnamomi (continued)

References used to Compile Lists of Western Australian Natives Susceptible and Resistant to Phytophthora cinnamomi.Compiled by E. Groves, G. Hardy & J. McComb, Murdoch University

REFERENCES:1. Alcoa of Australia (2002). Indicators of P. cinnamomi used by Interpreters. Environment Research Bulletin.2. Cho, J. J. (1983). Variability in susceptibility of some Banksia Species to Phytophthora cinnamomi and their distribution in Australia.

Plant Disease, 67; 869-871.3. Edmiston, R. J. (1989). Plants Resistant to Dieback. Department of Conservation and Land Management. 1-89.4. Environment Australia. (2001). Threat Abatement Plan for Dieback caused by the root-rot fungus Phytophthora cinnamomi.5. Gardner, J. H. & Rokich, P. A. (1987). Phytophthora cinnamomi in operational and rehabilitated bauxite mine area in South-western Australia. Alcoa of

Australia Environment Research Bulletin.13.6. Hart, R. (1983). Report on Dieback due to Phytophthora cinnamomi in Two People's Bay Nature Reserve.Department of Fisheries and Wildlife.7. Hill. (1990). Dieback Diseases and other Phytophthora spp. in the Northern Kwongon. In Nature,Conservation, Landscape and Recreational Values of

the Lesueur Area. A report to the Environmental Protection Authority from the Department of Conservation and Land Management. eds. A. Burbidge, S.D. Hopper & S. van Leeuwen, EPA. WA.

8. Keighery, G. (1992). The impact of Phytophthora species on rare plants. In Dieback-What is the Future ?, M. J. Freeman, R. Hart & M. Ryall, Northern Sandplains Dieback Working Group. Perth, pp. 29-36.

9. Lee, T. C. & Wicks, T. J. (1977). Phytophthora cinnamomi in native vegetation in south Australia. Australasian Plant Pathology Newsletter, 6; 22-23.10. Marks, G. C. & Smith, I. W. (1991). The cinnamon fungus in Victorian forests. Victorian Government Publications, Melbourne11. McCredie, T. A., Dixon, K. W. & Sivasithamparam, K. (1985). Variability in the resistance of Banksia L.f. species to Phytophthora cinnamomi. Australian

Journal of Botany, 33; 629-637.12. McDougall, K. L., Hardy, G. E. S. J. & Hobbs, R. J. (2001). Additions to the host range of Phytophthora cinnamomi in the jarrah (Eucalyptus marginata)

forest of Western Australia. Australian Journal of Botany, 49; 193-19813. McDougall, K. L., Hobbs, R. J. & Hardy, G. E. S. J. (2002). Vegetation of Phytophthora cinnamomi-infested and adjoining uninfested sited in the northern

jarrah (Eucalyptus marginata) forest of Western Australia. Australian Journal of Botany, 50; 277-288.14. Podger, F. D. (1972). Phytophthora cinnamomi, a cause of lethal disease in indigenous plant communities in Western Australia.

Phytopathology, 62; 972-981.15. Shearer, B. L. & Dillon, M. (1996). Susceptibility of plant species in Banksia woodlands on the Swan Coastal Plain, Western Australia, to infection by

Phytophthora cinnamomi. Australian Journal of Botany, 44; 433-445.16. Shearer, B. L. & Dillon, M. (1995). Susceptibility of plant species in Eucalyptus marginata forest to infection by Phytophthora cinnamomi. Australian

Journal of Botany, 43; 113-134.17. Titze, J. F. & Palzer, C. R. (1969). Host list of Phytophthora cinnamomi Rands with special reference to Western Australia. Forestry and Timber Bureau,

Department of National Development. Technical Note No. 1.18. Tynan, K. M., Scott, E. S. & Sedgley, M. (1998). Evaluation of Banksia species for response to Phytophthora infection.

Plant Pathology, 47; 446-455.19. Tynan, K. M., Wilkinson, C. J., Holmes, J. M., Dell, B., Colquhoun, I. J., McComb, J. A. & Hardy, G. E. St. J. (2001). The long-term ability of phosphite to

control Phytophthora cinnamomi in two native plant communities of Western Australia. Australian Journal of Botany, 49; 761-770.20. Wills, R. T. (1993). Unpublished data.

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