Attachment 3 - yassvalley.nsw.gov.au

www.5QS.com.au

Attachment 3 Flora and Fauna Assessment

L O DG E

E N VI R ON ME N T A L

D a t e : 2 6 A u g u s t 2 0 2 0

P r o j e c t C o d e : L E 1 1 1 8 b

FLORA AND FAUNA

ASSESSMENT

Y A S S R I VE R RO A D

I N T E RN A L R OA D S

P RE PA RE D F OR

5 QS C ON S U LT IN G G R O U P

Yass River Road

Flora and Fauna Assessment

LE1118b 1225 Yass River Road Internal Roads FFA.docx Page 1

LODGE ENVIRONMENTAL • www.lodgeenviro.com.au • ABN 85 631 988 148

Project Name:

Yass River Road Internal Roads– Flora and Fauna Assessment

Project Code:

LE1118b

Document Tracking:

Record of Distribution

Copies Report No. & File Name Status Date Prepared for:

1 x PDF LE1118b Yass River Road Leg 2 Flora and

Fauna Assessment.docx Rev.1 26 August 2020

5QS Consulting

Group

COMMERCIAL IN CONFIDENCE

This document has been prepared consistent with accepted scientific practice, supported by available data and resource conditions,

as determined by limited data acquisition during the assessment period, evident at Site at the time. The designated recipients of this

report accept all risks and responsibility for losses, damages, costs and other consequences resulting directly or indirectly from using

the results of the interpretation, the data, and any information or conclusions drawn from it, whether or not caused by any negligent

act or omission.

To the maximum permitted by law, Lodge Environmental excludes all liability to any person or identity, arising directly or indirectly

from using the information or material contained herein.

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Copyright in the material provided in this document is owned by Lodge Environmental Pty Ltd. Lodge Environmental reserves the

right to revoke this report, its content and results derived during the scope of work. Third parties may only use the information in

the ways described in this legal notice:

• Temporary copies may be generated, necessary to review the data.

• A single copy may be copied for research or personal use.

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• Request in writing is required for any variation to the above • An acknowledgement to the source of any data published from this document is mandatory

Prepared by:

Jack Talbert

Environmental Planner and Ecologist

Accredited Biodiversity Assessor BAAS18140

•

James Lidsey Ecologist

Sam Laming Junior Ecologist

Laura Lopresti Junior Ecologist

Lodge Environmental

ABN 85 631 988 148

Scientific License SL102041

Animal Research Authority – Flora and Fauna Survey

Mobile: 0423 296 045

Email: [email protected]

http://www.lodgeenviro.com.au/

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TABLE OF CONTENTS

1.0 Introduction ............................................................................................................................................. 4

1.1 Project Description ....................................................................................................................................... 4

1.2 Site Description ............................................................................................................................................ 4

1.3 Objectives .................................................................................................................................................... 4

2.0 Legislative Context ................................................................................................................................... 6

2.1 Environmental Planning and Assessment Act 1979 ..................................................................................... 6

2.2 Biodiversity Conservation Act 2016 ............................................................................................................. 6

2.3 Environment Protection and Biodiversity Conservation Act 1999 ............................................................... 7

2.4 Local Planning Instruments ......................................................................................................................... 7 2.4.1 Yass Valley Local Environment Plan 2013 ............................................................................................... 7

3.0 Methods ................................................................................................................................................... 8

3.1 Data and Literature Review ......................................................................................................................... 8

3.2 Field Survey .................................................................................................................................................. 8

3.3 Survey Weather ........................................................................................................................................... 9

3.4 Survey Limitations........................................................................................................................................ 9

4.0 Desktop Review ....................................................................................................................................... 10

4.1 Existing Vegetation and Biodiversity Values Mapping .............................................................................. 10

4.2 Threatened Flora Species ........................................................................................................................... 10

4.3 Threatened Fauna Species ......................................................................................................................... 10

5.0 Field survey Results ................................................................................................................................. 12

5.1 Existing Environment ................................................................................................................................. 12

5.1 Vegetation Communities ........................................................................................................................... 14

5.1 Flora ........................................................................................................................................................... 15 5.1.1 Threatened Flora Species ...................................................................................................................... 15

5.2 Fauna ......................................................................................................................................................... 15 5.2.1 Threatened Fauna Species .................................................................................................................... 15 5.2.2 Koala SEPP 44 ........................................................................................................................................ 16

6.0 Impact Assessment .................................................................................................................................. 17

6.1 Summary of Impacts .................................................................................................................................. 17

6.2 Yass Valley LEP ........................................................................................................................................... 17

6.3 Significance Assessments ........................................................................................................................... 18 6.3.1 Assessment of Significance under the EP&A Act and BC Act ................................................................ 18 6.3.2 EPBC Act Significant Impact Guidelines ................................................................................................. 20

6.4 BOS Trigger Assessment ............................................................................................................................ 20 6.4.1 Biodiversity Values Map ........................................................................................................................ 20 6.4.2 Native vegetation impacted .................................................................................................................. 20 6.4.3 Threatened species, populations or communities ................................................................................ 20

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6.4.4 Serious and Irreversible Impacts ........................................................................................................... 20 6.4.5 BOS Entry Determination ...................................................................................................................... 20

7.0 Recommendations ................................................................................................................................... 21

8.0 Conclusion ............................................................................................................................................... 22

9.0 References ............................................................................................................................................... 23

10.0 Limitations ............................................................................................................................................... 24

LIST OF TABLES, FIGURES & APPENDICES

TABLES

Table 1: Offset scheme thresholds - area criteria.................................................................................................................... 6

FIGURES

Figure 1: Subject Site ...................................................................................................................................................................... 5

Figure 2 Threatened species records within 10km of the site (BioNet 2020) ............................................................ 11

Figure 3 Validated vegetation communities mapped by Lodge Environmental (2020) ........................................ 13

Figure 4 Exotic and native Pastureland ..................................................................................................................................... 14

APPENDICES

Appendix A: Threatened flora and fauna likelihood table

Appendix B: Flora Species List

Appendix C: Fauna Species List

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1 .0 INTRODUCTION

Lodge Environmental were commissioned by 5QS Consulting Group to prepare this Flora and

Fauna Assessment (FFA) in anticipation of a proposed road and two associated construction areas

across Lot 2 and 5, DP1251902 - 1225 Yass River Road, Yass River 2582. This report describes the

native vegetation, threatened species, populations and communities and associated habitat

features which were recorded within the Subject Site in the context of an impact assessment. This

report is based on information obtained through data searches and field survey. The legislative

context, methods used, and recommendations are included within this report.

1.1 PROJECT DESCRIPTION

This report will assist in informing a development application associated with the proposed road

and construction areas proposed at the Subject Site. A small amount of vegetation clearance is

required for the proposed road and construction areas, however, they have largely been sited

over existing farm roads and pastoral lands.

1.2 SITE DESCRIPTION

The project address is 1225 Yass River Road, Yass River 2582 (Lot 2 and 5 DP1251902) located in

the Yass Valley Council (YVC) Local Government Area (LGA), with the YVC being the consenting

authority. The property is approximately 17.5 km south east of the Yass Town Centre. To the

north and east of the lot exists remnant areas of native vegetation, and to the south and west

exists the Yass River and the associated vegetation corridor.

The area proposed for the road and construction area (i.e. a strip within Lot 2 and 5 DP1251902)

is herein defined as the Subject Site. The impact assessment contained within this report is

conducted for all areas within the Subject Site (Figure 1).

1.3 OBJECTIVES

This report presents an assessment of possible impacts associated with the proposal at the Subject

Site and is based on a field investigation, a literature review of previous studies undertaken in the

region, the consultation of relevant databases and a consideration of the objectives of Section 4

of the EP&A Act, the State BC Act, the Commonwealth EPBC Act and any relevant State

Environmental Planning Policies (SEPP).

The environmental impacts of the development have been assessed via the Test of Significance

pursuant to Section 7.3 BC Act 2016, the Matters of National Environmental Significance (MNES)

under the EPBC Act, and the relevant clauses within the Yass Valley Local Environment Plan (LEP

2013). The direct and indirect ongoing impacts of the development are addressed in this FFA. If

necessary, Assessments of Significance have been undertaken.

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Figure 1: Subject Site

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2.0 LEGISLATIVE CONTEXT

2.1 ENVIRONMENTAL PLANNING AND ASSESSMENT ACT 1979

The NSW EP&A Act is the principal planning legislation for the state, providing a framework for

the overall environmental planning, and development assessment process. Various legislative

instruments, such as the BC Act, NSW Water Management Act 2000 (WM Act) and NSW Rural

Fires Act 2007 (RF Act) are integrated with the EP&A Act and have been reviewed below where

relevant.

2.2 BIODIVERSITY CONSERVATION ACT 2016

The NSW BC Act aims to slow the decline of threatened species, populations and communities

listed under the Act. The BC Act is integrated with the EP&A Act and requires consideration of

whether a development (Part 4 of the EP&A Act) is likely to significantly affect threatened species,

populations and ecological communities or their habitat.

The schedules of the BC Act lists species, populations and communities as endangered or

vulnerable. All developments, land use changes or activities need to be assessed to determine if

they will have an unacceptable impact on species, populations or communities listed on these

schedules.

The potential impact of the development on any threatened species, populations or communities

is assessed through application of an Assessment of Significance (AoS) under Section 7.3 of the

BC Act at the development application stage. If the impacts on the area are found to be

‘significant’, a Biodiversity Development Assessment Report (BDAR) would be required as

would concurrence from the Chief Executive of the NSW Office of Environment & Heritage (DPIE)

including application of the Biodiversity Assessment Methodology (BAM) and entering into the

Biodiversity Offset Scheme (BOS). A BDAR would also be deemed necessary if the proposed

subdivision were to involve clearance of vegetation mapped on the State Biodiversity Values Map

(BVM), or involve native vegetation clearance above the thresholds tables within the BC Act (Table

1).

Table 1: Offset scheme thresholds - area criteria

Minimum lot size associated with the property Threshold for clearing, above which the BAM

and offsets scheme applies

Less than 1 ha 0.25 ha or more

1 ha, and less than 40 ha 0.5 ha or more

40 ha, and less than 1,000 ha 1 ha or more

1,000 ha or greater 2 ha or more

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2.3 ENVIRONMENT PROTECTION AND BIODIVERSITY

CONSERVATION ACT 1999

The Commonwealth EPBC Act aims to protect and encourage the recovery of threatened species,

populations and communities listed under the Act. Under this Act an action will require approval

from the Minister for the Environment if the action has, will have, or is likely to have, a significant

impact on a MNES. MNES include listed threatened species and ecological communities,

migratory species and wetlands of international importance protected under international

agreements. Where applicable, the assessment criteria relevant to this Act must be drawn upon

to determine whether there would be a significant impact on these species and hence whether

referral to the Federal Environmental Minister is required.

2.4 LOCAL PLANNING INSTRUMENTS

2.4.1 Yass Valley Local Environment Plan 2013

The Yass Valley Local Environment Plan 2013 (LEP) is the principle planning instrument for the

YVC LGA. The LEP sets out the planning framework and establishes the requirements for the use

and development of land in the LGA. The LEP provides broad direction with regard to what types

of development are permitted within specific land use zones, as well as the principal development

standards for all land within the LGA.

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3.0 METHODS

3.1 DATA AND LITERATURE REVIEW

Data records and relevant literature pertaining to the ecology of the Subject Site and surrounding

areas were reviewed. The material reviewed included:

• NSW BioNet, Atlas of NSW Wildlife database search (10 km) (Accessed 20 January 2020)

• DPIE threatened species profile database (DPIE 2019)

• EPBC Act Protected Matter Search Tool (10 km) (Accessed 20 January 2020)

• Review of the State Biodiversity Values Map (Accessed 20 January 2020)

• Biometric Vegetation Type Mapping (DPIE 2013)

• Property Report (Accessed 20 January 2020)

• relevant legislative documents

• aerial photography

A review of the databases allowed for the production of a list of threatened species and

communities that may occur within the Subject Site (Appendix A). Likelihood of occurrences for

threatened species, endangered populations and communities in the Subject Site were then made

based on location of database records, the likely presence or absence of suitable habitat on the

site, and knowledge of the species’ ecology. The likelihood of occurrence was stratified using a

rating of “high”, “moderate” or “low” likelihood, with those species considered to have a

considerable likelihood of occurrence (following site validation) then identified as either

potentially “affected” by the proposal and therefore requiring a significance assessment or not.

3.2 FIELD SURVEY

To address the FFA the following survey methods were undertaken on the 21th January 2020 by

ecologists Jack Talbert, Samuel Laming and James Lidsey:

• Identification of plant species and vegetation communities present within the site

• search for signs of threatened species, observe and record significant flora and fauna –

threatened and migratory species, other incidental fauna observations

• observe and record current disturbance and threats (e.g. weeds, trampling, litter)

• identifying potential habitat for threatened fauna species/populations (e.g. hollow-

bearing trees (HBTs), creeks, boulders etc)

• recording presence of environmental weeds

• taking reference photographs of the entire site.

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3.3 SURVEY WEATHER

The weather during the field survey on 20 November 2019 is summarised below.

• Temperature on the day: 14.0 to 27.6°C

• Dominant NW wind of 44 km/hr

• 2.6mm rainfall

• 64% humidity

• 4/8 cloud cover

Observations were drawn from the Canberra Airport BOM Station {station 070351}.

3.4 SURVEY LIMITATIONS

Survey was conducted during Summer and may be outside of the optimal survey period for some

flora and fauna species. It is therefore possible that some species may not have been detected

due to their seasonal geographic variation. Cryptic species may not have been obvious. However,

habitat assessments were conducted to further predict the likelihood of species occurrence at the

site. A conservative approach was applied in the assumption of the presence of species that could

potentially occur within the site area. In this regard, the survey is considered adequate for the

purposes of this report.

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4.0 DESKTOP REVIEW

4.1 EXISTING VEGETATION AND BIODIVERSITY VALUES MAPPING

A review of the State Biodiversity Values Map was conducted on the 20th January 2020. The

Subject Site does not contain any areas of mapped biodiversity values (BV).

A review of vegetation mapping that covers the Subject Site (LLS 2014) identified no vegetation

types within the Subject Site.

4.2 THREATENED FLORA SPECIES

A review of the DPIE and Department of the Environment and Energy (DEE) databases identified

9 threatened plants listed under the BC Act and/or the EPBC Act that have been previously

recorded, or are considered to have habitat, within 10 km of the site (Figure 2). This initial

compilation of potentially occurring species informed the site survey, providing an indication of

which species required consideration within the site. An assessment of the likelihood of

occurrence of threatened flora species within the site is available in Appendix A and was used to

guide the field survey methodology. No threatened flora species were identified as having a

medium to high potential of occurrence in the Subject Site.

4.3 THREATENED FAUNA SPECIES

A review of the DPIE and DEE databases identified 28 threatened fauna listed under the BC Act

and/or the EPBC Act that have been previously recorded, or are considered to have habitat,

within 10 km of the site (Figure 2). An assessment of the likelihood of occurrence of threatened

fauna species within the site is available in Appendix A and was used to guide the field survey

methodology.

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Figure 2 Threatened species records within 10km of the site (BioNet 2020)

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5.0 FIELD SURVEY RESULTS

5.1 EXISTING ENVIRONMENT

The field inspection recorded the presence of one vegetation type as mapped in Figure 3, hereby

known as Exotic and Native Pastureland, however the Subject Site would have historically been

associated with two other vegetation communities which include:

• White Box-Yellow Box-Blakely’s Red Gum Grassy Woodland and Derived Native

Grassland

• Natural Temperate Grassland of the South Eastern Highlands

White Box Yellow Box Blakely’s Red Gum Woodland Threatened Ecological Community (TEC)

under both the State BC Act and Commonwealth EPBC Act which is regarded as an Endangered

Ecological Community and Critically Endangered respectively.

Following the introduction of agricultural activities in the area the site was subjected to grazing

in association with the introduction of exotic plant species. Continued agrarian management

regimes over numerous decades has replaced the natural vegetation with a high prevalence of

exotic species within the ground story. Occasional remnant paddock trees and small stands of

regrowth exist as all that remains of the previous natural vegetation.

The Subject Site lacked adequate diagnostic species for the justification of a potential plant

community type (PCT) or either of the afore-mentioned associated vegetation communities due

to the long history of clearing, farming and grazing practices within the area.

The Subject Site was entirely Exotic / cleared / pasturelandwhich consisted of various exotic and

native ground stratum plants, a small number of mid stratum species and an absence of any upper

stratum plant species.

The Subject Site did not contain any hollow-bearing trees, logs, creeks, large boulders or other

notable habitat features.

The Subject Site does not provide considerable habitat for threatened or non-threated fauna

beyond occasional foraging for common macropods and birds, and as flyover habitat for highly

mobile species.

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Figure 3 Validated vegetation communities mapped by Lodge Environmental (2020)

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5.1 VEGETATION COMMUNITIES

The field inspection recorded one vegetation type as mapped in Figure 3, which included:

• Exotic / cleared / pastureland(No PCT)

Exotic / cleared / pastureland

The ground stratum of Exotic / cleared / pastureland (Figure 4Error! Reference source not found.)

within the Subject Site was dominated by cleared ground. The dominant exotics were Hypochaeris

radicata (Catsear), Juncus usitatus (Soft Rush), Rumex brownie (Swamp Dock), Phalaris aquatica

(Canary Grass), Austrostipa verticillata (Slender Bamboo Grass) and Aristida benthamii var.

benthamii (Three-awned Spear Grass). The dominant natives were Rytidosperma racemosum

(Wallaby Grass) and Lomandra bracteate.

While the mid stratum was mostly absent there were a few scattered native and exotic species

including Acacia paradoxa (Kangaroo Thorn), Alhagi maurorum (Camel Thorn) and Rosa

rubiginosa (Sweet Briar). The upper stratum was entirely absent from the Subject Site.

No threatened flora species were recorded within the vegetation type.

Figure 4: Exotic / cleared / pastureland

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5.1 FLORA

A total of 26 species were recorded during the site inspection (14 natives and 12 exotic). A species

list is provided in Appendix A.

5.1.1 Threatened Flora Species

There were no threatened flora species identified within the Subject Site.

5.2 FAUNA

A total of 13 fauna species were identified within the Subject Site. A species list is included in

Appendix C. Targeted surveys were not conducted as part of this assessment.

5.2.1 Threatened Fauna Species

There were no threatened fauna species identified within the site.

In general, the habitat potential of the proposed development site has been reduced through

ecosystem simplification, historic clearing and the incursion of exotic groundcover species. This

has depleted natural resources such as food and shelter for native animals.

The following observations were noted:

• There is a low diversity of species and no structural diversity across the Subject Site to

provide a greater diversity and abundance of micro habitats.

• There are no Hollow Bearing Trees (HBTs).

• Introduced species have replaced native species thereby reducing food resources and

shelter sites.

• There are no rocks, caves, overhangs or crevices to provide habitat.

• There is no juvenile recruitment of trees or shrubs occurring.

In general, the habitat potential of the Subject Site for specialist native species, such as listed

threatened species, is very poor. However, the following threatened fauna species have been

recorded within 10 km of the Subject Site:

• Dusky Woodswallow (Artamus cyanopterus cyanopterus)

• Gang-gang Cockatoo (Callocephalon fimbriatum)

• Eastern Pygmy-possum (Cercartetus nanus)

• Speckled Warbler (Chthonicola sagittate)

• Brown Treecreeper (eastern subspecies) (Climacteris picumnus victoriae)

• Varied Sittella (Daphoenositta chrysoptera)

• Little Eagle (Hieraaetus morphnoides)

• Powerful Owl (Ninox strenua)

• Scarlet Robin (Petroica boodang)

• Flame Robin (Petroica phoenicea)

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• Koala (Phascolarctos cinereus)

• Superb Parrot (Polytelis swainsonii)

5.2.2 Koala SEPP 44

The Koala SEPP requires consideration within the YVC LGA. This SEPP aims to encourage the

conservation and management of natural vegetation that provides habitat for Koalas to ensure a

permanent, free living population over their present range and reverse the current trend of the

koala population decline. A development application affecting one hectare or more, in an

identified local government area, must be assessed under SEPP 44 (2.6). Given that the Subject

Site is greater than 1 ha in area, it must be determined whether the site is Potential Koala Habitat.

The following species are listed as Koala Feed Trees under the SEPP:

• Eucalyptus albens (White-top Box)

• Eucalyptus camaldulensis (River Red Gum)

• Eucalyptus haemastoma (Broad-leaved Scribbly Gum)

• Eucalyptus microcorys (Tallowwood)

• Eucalyptus populnea (Poplar Box)

• Eucalyptus punctata (Grey Gum)

• Eucalyptus robusta (Swamp Mahogany)

• Eucalyptus signata (Scribbly Gum)

• Eucalyptus tereticornis (Forest Red Gum)

• Eucalyptus viminalis (Ribbon Gum)

If Koala Feed Trees constitute 15% or more of the tree component in a site, the site is defined as

Potential Koala Habitat and must be further assessed to determine whether it is Core Koala

Habitat.

Given that none of the listed Koala Feed Trees were recorded within the Subject Site, it can be

concluded that it is not Potential Koala Habitat and the SEPP does not apply.

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6.0 IMPACT ASSESSMENT

6.1 SUMMARY OF IMPACTS

The proposed road and construction areas have been sited on almost entirely cleared land which

is dominated by cleared ground (much of which is already an access track), exotic groundcover

species and occasional native pasture grasses. No additional vegetation beyond the boundaries

of the site is required to be cleared.

Direct impacts

The Subject Site totals to 3.09 ha, of which all exists as a mix of exotic and native pastures

disbursed amongst cleared ground. The impacts will occur to:

• 3.09 ha of exotic / cleared / pastureland

The impact imposed by the proposed development on the mapped native vegetation is below

the Biodiversity Offset Scheme entrance impact threshold of 1 ha.

No threatened flora is to be impacted by the proposal.

The vegetation to be impacted is not considered to provide potential foraging habitat for

threatened fauna. However, the following species have been recorded within 10 km of the Subject

Site and will be further considered in this report:



Furthermore, upon review of the database searches and on-site habitat assessment, additional

species known to occur within the region are included will be further considered in this report

including;

• Pink-tailed Worm-lizard, Pink-tailed Legless Lizard (Aprasia parapulchella)

• Striped Legless Lizard (Delma impar)

• Golden Sun Moth (Synemon plana)

Indirect impacts

The subdivision of the land in the Subject Site is not considered to introduce any considerable

additional indirect impacts on important vegetation or fauna habitat, as the existing environment

has been degraded by its historical clearing and use for grazing.

There is no significant intact vegetation adjoining the Subject Site which could act as a habitat

corridor for mobile fauna.

The proposal is not considered to have any indirect impacts outside of the Subject Site.

6.2 YASS VALLEY LEP

The Subject Site is not covered by the Yass Valley LEP Biodiversity clause, nor is it covered by the

Riparian Lands and Watercourses clause.

The land is zoned RU1 – Primary Production, with the proposal being permissible with consent.

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6.3 SIGNIFICANCE ASSESSMENTS

6.3.1 Assessment of Significance under the EP&A Act and BC Act

Assessments using the criteria provided under the EP&A Act (i.e. Assessment of Significance (AoS))

must be taken into account by consent or determining authorities when considering a

development proposal or development application. This enables a decision to be made as to

whether there is likely to be a significant impact on the species and hence if entry into the

Biodiversity Offset Scheme (BOS) is required.

The results of the field survey have been used to inform whether significance assessments are

required and for which listed species and communities. The habitat in the Subject Site is not

considered to have the potential to be utilised by the majority of relevant threatened species,

even in a transient manner, for foraging, roosting or movement throughout the wider locality.


The Scarlet Robin inhabits dry eucalypt forests and woodlands. The understorey is usually open

and grassy with few scattered shrubs. During autumn and winter it moves to more open and

cleared areas. The Scarlet Robin forages amongst logs and woody debris for insects. The nest is

an open cup of plant fibres and cobwebs, sited in the fork of a tree.

Although the site has the potential for poor quality foraging habitat during the winter months this

is considered to have minimal significance when compared to the broader landscape. Areas

surrounding the Subject site have the potential to provide higher quality foraging habitat as they

consist of a more complex mosaic of woodlands and natural temperate grasslands.

In addition to this the Scarlet Robin often forages amongst logs and woody debris which was

absent across the Subject site.

Given the condition of the potential habitat, the Flame Robin is unlikely to be found within the

Subject site.


Flame Robins are found in a broad coastal band from southern Queensland to just west of the

South Australian border. The preferred habitat in summer includes moist eucalyptus forests and

open woodlands, in winter prefers open woodlands and farmlands. It is considered migratory. Diet

consists mainly of invertebrates.

Although the site has the potential for poor quality foraging habitat during the winter months this

is considered to have minimal significance when compared to the broader landscape. Areas

surrounding the Subject site have the potential to provide higher quality foraging habitat as they

consist of a more complex mosaic of woodlands and natural temperate grasslands.

Given the condition of the potential habitat, the Flame Robin is unlikely to be found within the

Subject Site.

• Pink-tailed Worm-lizard, Pink-tailed Legless Lizard (Aprasia parapulchella)

The Pink-tailed Worm-lizard is a fossorial species, which lives beneath surface rocks and occupies

ant burrows. It feed on ants, particularly their eggs and larvae. Thought to lay eggs within the ant

nests under rocks that it uses as a source of food and shelter. Key habitat features are a cover of

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native grasses, particularly Kangaroo Grass (Themeda australis), sparse or no tree cover, little or

no leaf litter, and scattered small rock with shallow embedment in the soil surface.

Although the site contained limited sheltering potential for the species, active searches were

undertaken for the species during appropriate timing (i.e. between September to May). Potential

refugia was targeted, with any displaced refugia placed back in the same position.

Although the site contained some scattered rocks that were embedded on occasion the Subject

Site overall presented poor quality habitat for the Pink-tailed Worm-lizard with minimal native

vegetation cover and low quality sheltering habitat.

There are no records within or adjoining the site, and given the limited dispersal ability of this

species, it is unlikely to be found within the Subject Site.

• Striped Legless Lizard (Delma impar)

The Striped Legless Lizard is found mainly in Natural Temperate Grassland but has also been

captured in grasslands that have a high exotic component. Its preferred habitat is where grassland

is dominated by perennial, tussock-forming grasses such as Kangaroo Grass (Themeda australis),

spear-grasses (Austrostipa spp.) and poa tussocks (Poa spp.), and occasionally wallaby grasses

(Austrodanthonia spp.). It is unlikely that this species would occur in the site given the low number

of tussock-forming grass species. Where the tussock forming species were present high levels of

grazing were noted. Suitable rocks were limited across the Subject Site, these are required as a

key form of sheltering habitat.

Although the site contained limited sheltering potential for the species, active searches were

undertaken for the species during appropriate timing (i.e. between September to May). Potential

refugia was targeted, with any displaced refugia placed back in the same position.

There are no records within or adjoining the site, and given the limited dispersal ability of this

species, it is unlikely to be found within the Subject Site.

• Golden Sun Moth (Synemon plana)

The Golden Sun Moth occurs in Natural Temperate Grasslands and grassy Box-Gum Woodlands

in which the ground layer is dominated by wallaby grasses (Austrodanthonia spp.). Grasslands

dominated by wallaby grasses are typically low and open. The bare ground between the tussocks

is thought to be an important microhabitat feature for the Golden Sun Moth, as it is typically these

areas on which the females are observed displaying to attract males. Its preferred habitat may

contain several wallaby grass species, which are typically associated with other grasses, particularly

spear-grasses (Austrostipa spp.) or Kangaroo Grass (Themeda australis). The site did contain

occasional preferred native grass species such as Wallaby Grass however it was found scattered

in low densities throughout the site, overgrown by out-competing weeds, and without bare

ground areas suitable for basking. Subsequently, the Subject Site is not considered to constitute

habitat for the Golden Sun Moth.

Given the above information, an AoS is not considered necessary for the above-listed threatened

species, and the proposal, under its current layout, is not considered to have any significant impact

on threatened species, ecological communities or populations such that a viable local population

will be placed at risk of extinction.

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6.3.2 EPBC Act Significant Impact Guidelines

The EPBC Act establishes a process for assessing the environmental impact of activities and

developments where MNES may be affected. The process includes the application of Significant

Impact Criteria for listed threatened species and ecological communities that represent a MNES

that will be impacted as a result of the proposed action. Significant impact guidelines that outline

a number of criteria have been developed by the Commonwealth, to provide assistance in

conducting the assessment and help decide whether or not a referral to the Commonwealth is

required.

No SICs were required for this assessment

6.4 BOS TRIGGER ASSESSMENT

6.4.1 Biodiversity Values Map

The Biodiversity Values Map does not affect any area for the proposed development.

6.4.2 Native vegetation impacted

The native vegetation impact threshold for the subject lot is 1 ha. The native vegetation to be

removed falls below the impact threshold and does not trigger BOS entry.

6.4.3 Threatened species, populations or communities

The proposal will not result in a significant impact upon any species, populations or communities

listed under State or Commonwealth legislation provided the proposal is approved as defined

within this assessment, and all recommendations and mitigation measures herein are adhered to.

6.4.4 Serious and Irreversible Impacts

The proposal does not trigger the BOS and as such, SAIIs do not apply.

6.4.5 BOS Entry Determination

Entry into the Biodiversity Offset Scheme is not required.

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7.0 RECOMMENDATIONS

This report assesses the removal of the exotic pastures within the Subject Site only. The following

recommendations are provided to minimise potential impacts to threatened and non-threatened

vegetation communities, flora and fauna that could result from the proposed action:

• Landscaping should aim to use species endemic to the area. Species listed in the South

East Regional Strategic Weed Management Plan 2017 – 2022 should not be planted.

• Adequate erosion and sediment control measures should be in place at all times during

construction in accordance with best practice guidelines (Landcom 2004), including:

o sediment fencing

o vehicle and machinery movement confined to designated work areas

o consideration given to weather, with works stopped if the onset of heavy rain is

deemed likely to cause soil erosion or soil structure damage.

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8.0 CONCLUSION

Through the completion of the survey conducted as part of this report, no threatened flora or

fauna were recorded within the Subject Site. Impacts are to occur to the exotic grassland which

comprises the entirety of the Subject Site.

Given the condition of the site, it was concluded that it contained no suitable habitat for specialist

species, including locally occurring threatened species.

This Flora and Fauna Assessment has adequately considered threatened species and communities

in the context of the proposed development at the subject site by:

• conducting field survey

• adopting the precautionary principle in the assessment of threatened species

• designating appropriate recommendations to minimise potential impacts to threatened

species that may transiently occur on the site as well as any other fauna

The assessments contained within this report have determined that the proposed road and

associated construction areas are unlikely to have a significant effect on the listed communities

or species or their habitat in accordance with the EP&A Act, BC Act and EPBC Act provided the

recommendations contained in this report are adhered to.

There will not be an impact on any mapped areas of Biodiversity Value, nor will there be an impact

on native vegetation above the relevant impact threshold.

Therefore, the preparation and submission of a BDAR or referral to the Commonwealth is not

required.

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9.0 REFERENCES

Cropper, S.C. (1993) Management of Endangered Plants. CSIRO Publications Victoria

Department of Primary Industries (DPI) (2014). Noxious and environmental weed control handbook – A

guide to weed control in non-crop, aquatic and bushland situations. 6th Edition. Department of Trade and

Investment, Regional Infrastructure and Services. Available at:

http://www.dpi.nsw.gov.au/content/agriculture/pests-weeds/weeds/publications/noxious-enviro-weed-

control

DEC (2004). Threatened Species Survey and Assessment: Guidelines for developments and activities

(working draft). NSW Department of Environment and Conservation, Hurstville NSW

DECC (2007). Threatened Species Assessment Guidelines: The Assessment of Significance. Department of

Environment and Climate Chance, Hurstville NSW

DotEE (2019). Protected Matters Report using coordinates -34.886191° 149.092588°

Fairley, A., & Moore, P. (2010). Native Plants of the Sydney Region. From Newcastle to Nowra and west to

the Dividing Range. Allen & Unwin

Keith, D. (2004). Ocean shores to desert dunes: the native vegetation of New South Wales and the ACT.

NSW Department of Environment and Conservation, Hurstville.

Landcom (2004). Soils and Construction Volume 1 Managing Urban Stormwater., 4th Edition, March 2004.

Leanord, G. (2007). Eucalypts of the Sydney Region. UNSW Press

Office of Environment and Heritage (DPIE) (2016). NSW Guide to Surveying Threatened Plants

Office of Environment and Heritage (DPIE) (2019a). Atlas of NSW Wildlife. Wildlife Data Unit, DPIE,

Parramatta NSW.

http://www.environment.nsw.gov.au/atlaspublicapp/UI_Modules/ATLAS_/AtlasSearch.aspx

Office of Environment and Heritage (DPIE) (2019b). Threatened species profiles. Accessed 25 November

2019. Available at http://www.threatenedspecies.environment.nsw.gov.au/index.aspx

Office of Environment and Heritage (DPIE) (2019c). NSW Scientific Committee Determinations. Accessed 5

August 2018. Available at http://www.environment.nsw.gov.au/determinations/

Robinson, L. (2003). Field Guide to the Native Plants of Sydney. Simon and Shuster Australia.

Tozer, M.G., Turner, K., Keith, D.A., Tindall, D., Pennay, C., Simpson, C., MacKenzie, B., Beukers, P. & Cox, S.

(2010). Native vegetation of southeast NSW: a revised classification and map for the coast and eastern

tablelands. Cunninghamia 11(3), 359-406.

http://www.environment.nsw.gov.au/determinations/

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10.0 LIMITATIONS

This report and the associated services performed by Lodge Environmental are in accordance with

the scope of services set out in the contract between Lodge Environmental and the Client. The

scope of services was defined by the requests of the Client, by the time and budgetary constraints

imposed by the Client, and by the availability of access to Site.

Lodge Environmental derived the data in this report primarily from visual inspections, and, limited

survey and analysis made on the dates indicated. In preparing this report, Lodge Environmental

has relied upon, and presumed accurate, certain information provided by government authorities,

the Client and others identified herein. The report has been prepared on the basis that while

Lodge Environmental believes all the information in it is deemed reliable and accurate at the time

of preparing the report, it does not warrant its accuracy or completeness and to the full extent

allowed by law excludes liability in contract, tort or otherwise, for any loss or damage sustained

by the Client arising from or in connection with the supply or use of the whole or any part of the

information in the report through any cause whatsoever.

The data, findings, observations, conclusions and recommendations in the report are based solely

upon the state of the Site at the time of the investigation. The passage of time, manifestation of

latent conditions or impacts of future events (e.g. changes in legislation, scientific knowledge, land

uses, etc) may render the report inaccurate. In those circumstances, Lodge Environmental shall

not be liable for any loss or damage that may be occasioned directly or indirectly through the use

of, or reliance on, the contents of the report.

This report has been prepared on behalf of and for the exclusive use of the Client, and is subject

to and issued in connection with the provisions of the agreement between Lodge Environmental

and the Client. Lodge Environmental accepts no liability or responsibility whatsoever and

expressly disclaims any responsibility for or in respect of any use of or reliance upon this report

by any third party or parties.

It is the responsibility of the Client to accept if the Client so chooses any recommendations

contained within and implement them in an appropriate, suitable and timely manner.

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Appendices

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Appendix A: Threatened flora and fauna likelihood table

Common Name Scientific Name

Legislation

Habitat Associations Likelihood of

Occurrence

Further

Significance

Assessment

Undertaken BC Act EPBC Act

Ecological Communities

Natural Temperate Grassland of the South Eastern

Highlands - CE

A natural grassland community dominated by a

range of perennial grass species and, in highly

intact sites, containing a large range of

herbaceous species. Often treeless, though trees

of a range of species may occur in low densities,

either as isolated individuals or in clumps. Many

of the flora species of the community are

threatened. Low No

White Box-Yellow Box-Blakely’s Red Gum Grassy

Woodland and Derived Native Grassland E CE

An open woodland community (sometimes

occurring as a forest formation), in which the

most obvious species are one or more of the

following: White Box Eucalyptus albens, Yellow

Box E. melliodora and Blakely's Red Gum E.

blakelyi. Intact sites contain a high diversity of

plant species, including additional tree species,

some shrub species, several climbing plant

species, many grasses and a very high diversity

of herbs. Low No

Plants

Yass Daisy Ammobium craspedioides V V

Found in moist or dry forest communities, Box-

Gum Woodland and secondary grassland

derived from clearing of these communities.

Grows in association with a large range of

eucalypts Found from near Crookwell on the

Southern Tablelands to near Wagga Wagga on

the South Western Slopes. Most populations are

in the Yass region Low No

Black Gum Eucalyptus aggregata V V Grows in the lowest parts of the landscape. Low No

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Legislation


Occurrence

Further

Significance

Assessment


Grows on alluvial soils, on cold, poorly-drained

flats and hollows adjacent to creeks and small

rivers.

River Swamp Wallaby-grass Amphibromus fluitans V V

Grows mostly in permanent swamps. The species

needs wetlands which are at least moderately

fertile and which have some bare ground,

conditions which are produced by seasonally-

fluctuating water levels. Low No

Hoary Sunray

Leucochrysum albicans var. tricolor - E

Occurs in a wide variety of grassland, woodland

and forest habitats, generally on relatively heavy

soils. Can occur in modified habitats such as

semi-urban areas and roadsides. Highly

dependent on the presence of bare ground for

germination. Low No

Pale Pomaderris Pomaderris pallida V

• This species usually grows in shrub communities

surrounded by Brittle Gum (Eucalyptus

mannifera) and Red Stringybark (E.

macrorhyncha) or Callitris spp. woodland. Low No

Tarengo Leek Orchid Prasophyllum petilum E E

• Natural populations are known from a total of

five sites in NSW. Grows in open sites within

Natural Temperate Grassland. Also grows in

grassy woodland in association with River

Tussock Poa labillardieri, Black Gum Eucalyptus

aggregata and tea-trees Leptospermum spp.

and within the grassy groundlayer dominated by

Kanagroo Grass under Box-Gum Woodland. Low No

Button Wrinklewort

Rutidosis leptorrhynchoides E E

Occurs in Box-Gum Woodland, secondary

grassland derived from Box-Gum Woodland or

in Natural Temperate Grassland; and often in the

ecotone between the two communities. Grows

on soils that are usually shallow; tends to occupy

areas where there is relatively less competition

from herbaceous species. Low No

Small Purple-pea Swainsona recta E E

Grows in association with understorey

dominants that include Kangaroo Grass Low No

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Legislation


Occurrence

Further

Significance

Assessment


Themeda australis, poa tussocks Poa spp. and

spear-grasses Austrostipa spp.

Austral Toadflax Thesium australe V V

Occurs in grassland on coastal headlands or

grassland and grassy woodland away from the

coast. Low No

Aves

Regent Honeyeater Anthochaera phrygia CE CE

Mainly inhabits temperate woodlands and open

forests of the inland slopes of south-east

Australia. These woodlands have significantly

large numbers of mature trees, high canopy

cover and abundance of

mistletoes. Low No

Dusky Woodswallow

Artamus cyanopterus cyanopterus V -

The species occurs throughout most of New

South Wales, but is sparsely scattered in, or

largely absent from, much of the upper western

region. Most breeding activity occurs on the

western slopes of the Great Dividing Range.

Primarily inhabit dry, open eucalypt forests and

woodlands, including mallee associations, with

an open or sparse understorey of eucalypt

saplings, acacias and other shrubs, and ground-

cover of grasses or sedges and fallen woody

debris. Low No

Gang-gang Cockatoo Callocephalon fimbriatum V -

Prefers tall montane forests and woodlands,

particularly in heavily timbered and mature wet

sclerophyll forests during summer, these being

at higher altitudes. In winter, occurs at lower

altitudes in drier, more open eucalypt forests

and woodlands, or in dry forest in coastal areas. Low No

Brown Treecreeper (eastern

subspecies)

Climacteris picumnus victoriae V -

The Brown Treecreeper, Australia’s largest

treecreeper, is a grey-brown bird with black

streaking on the lower breast and belly and

black bars on the undertail. Pale buff bands

across the flight feathers are obvious in flight.

Individuals are active, noisy and conspicuous, Low No

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Legislation


Occurrence

Further

Significance

Assessment


and give a loud ‘pink’ call, often repeated in

contact, and sometimes given in a series of 5 -

10 descending notes. Breeds from July to Feb

across its range.

Speckled Warbler Chthonicola sagittata V

Chthonicola sagittata occurs on the hills and

tablelands of the Great Dividing Range. Found in

eucalypt and cypress woodlands with a grassy

understorey, often on ridges or gullies. The

species nests on the ground in grass tussocks,

dense litter and fallen branches. They forage on

the ground for arthropods and seeds. Low No

Varied Sittella Daphoenositta chrysoptera V -

Inhabits eucalypt forests and woodlands,

especially those containing rough-barked

species and mature smooth-barked gums with

dead branches, mallee and Acacia woodland. Low No

Painted Honeyeater Grantiella picta V V

• The Painted Honeyeater is nomadic and occurs

at low densities throughout its range. Inhabits

Boree/ Weeping Myall (Acacia pendula),

Brigalow (A. harpophylla) and Box-Gum

Woodlands and Box-Ironbark Forests. A

specialist feeder on the fruits of mistletoes

growing on woodland eucalypts and acacias. Low No

Little Eagle Hieraaetus morphnoides V -

Occupies open eucalypt forest, woodland or

open woodland. Sheoak or Acacia woodlands

and riparian woodlands of interior NSW are also

used. Low No

White-throated Needletail Hirundapus caudacutus - M

Almost exclusively aerial. Takes insects on wing

over a range of habitat types. Recorded most

often above wooded areas, including open

forest and rainforest Low No

Swift Parrot Lathamus discolor E E

Eucalypt forests. When over-wintering on the

mainland, this species is dependent on winter-

flowering eucalypt species. Low No

Powerful Owl Ninox strenua V -

Large tracts of open or closed sclerophyll forest

or woodlands but can occur in fragmented Low No

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Legislation


Occurrence

Further

Significance

Assessment


landscapes as well. Gullies consisting of wet to

dry sclerophyll forest with a dense understorey.

Scarlet Robin Petroica boodang V -

Lives in dry eucalypt forests and woodlands. The

understorey is usually open and grassy with few

scattered shrubs. Its habitat usually contains

abundant logs and fallen timber: these are

important components of its habitat. Low No

Flame Robin Petroica phoenicea V -

Breeds in upland tall moist eucalypt forests and

woodlands, often on ridges and slopes.

Prefers clearings or areas with open

understoreys. The groundlayer of the breeding

habitat is dominated by native grasses and the

shrub layer may be either sparse or dense. Low No

Superb Parrot Polytelis swainsonii V V

Inhabit Box-Gum, Box-Cypress-pine and Boree

Woodlands and River Red Gum Forest. Nest in

the hollows of large trees (dead or alive) mainly

in tall riparian River Red Gum Forest or

Woodland. Trees can also be in open Box-Gum

Woodland or isolated paddock trees. Low No

Mammals

Eastern Pygmy-possum Cercartetus nanus V

Broad range of habitats from rainforest through

sclerophyll (including Box-Ironbark) forest and

woodland to heath, but in most areas woodlands

and heath appear to be preferred. Shelters in

tree hollows, rotten stumps, holes in the ground,

abandoned bird-nests, Ringtail Possum

(Pseudocheirus peregrinus) dreys or thickets of

vegetation

Low No

Large-eared Pied Bat Chalinolobus dwyeri V V Cave-roosting bat that forages in timbered

woodland and dry sclerophyll forest Low

No

Spotted-tailed Quoll Dasyurus maculatus V E

Recorded across a range of habitat types,

including rainforest, open forest, woodland,

coastal heath and inland riparian forest, from the

sub-alpine zone to the coastline.

Low No

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Legislation


Occurrence

Further

Significance

Assessment


Corben’s Long-eared Bat Nyctophilus corbeni V V

Inhabits a variety of vegetation types, including

mallee, bulloke Allocasuarina leuhmanni and box

eucalypt dominated communities, but it is

distinctly more common in ox/ironbark/cypress-

pine vegetation. Roosts in tree hollows, crevices,

and under loose bark. Low No

Greater Glider Petauroides volans - V

It is typically found in highest abundance in

taller, montane, moist eucalypt forests with

relatively old trees and abundant hollows. The

greater glider favours forests with a diversity of

eucalypt species, due to seasonal variation in its

preferred tree species. Low No

Koala Phascolarctos cinereus V V Open eucalypt forest and woodland, containing

a variety of ‘preferred’ feed trees Low No

Grey-headed Flying-fox Pteropus poliocephalus V V Occur in subtropical and temperate rainforests,

tall sclerophyll forests. Low No

Frogs

Green and Golden Bell Frog Litoria aurea E V

Most existing locations for the species occur as

small, coastal, or near coastal populations, with

records occurring between south of Grafton and

northern VIC. The species is found in marshes,

dams and stream sides, particularly those

containing bullrushes or spikerushes.

Low No

Booroolong Frog Litoria booroolongensis E E

Live along permanent streams with some

fringing vegetation cover such as ferns, sedges

or grasses. Adults occur on or near cobble banks

and other rock structures within stream margins.

Shelter under rocks or amongst vegetation near

the ground on the stream edge. Low No

Yellow-spotted Tree Frog Litoria castanea CE CE

Require large permanent ponds or slow flowing

'chain-of-ponds' streams with abundant

emergent vegetation such as bulrushes and

aquatic vegetation. Low No

Growling Grass Frog,

Southern Bell Frog Litoria raniformis E V

Usually found in or around permanent or

ephemeral Black Box/Lignum/Nitre Goosefoot Low No

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Legislation


Occurrence

Further

Significance

Assessment


swamps, Lignum/Typha swamps and River Red

Gum swamps or billabongs along floodplains

and river valleys. They are also found in irrigated

rice crops, particularly where there is no

available natural habitat.

Insects

Golden Sun Moth Synemon plana E CE

Occurs in Natural Temperate Grasslands and

grassy Box-Gum Woodlands in which

groundlayer is dominated by wallaby grasses

Austrodanthonia spp. Low No

Reptiles

Pink-tailed Worm-lizard Aprasia parapulchella V V

Inhabits sloping, open woodland areas with

predominantly native grassy groundlayers,

particularly those dominated by Kangaroo Grass

(Themeda australis). Sites are typically well-

drained, with rocky outcrops or scattered,

partially-buried rocks. Low No

Striped Legless Lizard Delma impar V V

Found mainly in Natural Temperate Grassland

but has also been captured in grasslands that

have a high exotic component. Also found in

secondary grassland near Natural Temperate

Grassland and occasionally in open Box-Gum

Woodland. Low No

Key. V=Vulnerable, E=Endangered, Ep=Endangered Population, CE=Critically Endangered, M=Migratory.

Species habitat associations have been informed predominantly from DPIE (2019) and DotEE (2019) species profiles.

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Appendix B: Flora Species List Scientific name Common name Native Exotic

Acacia paradoxa Kangaroo Thorn Yes

Alhagi maurorum Camel Thorn Yes

Argemone mexicana Mexican Poppy Yes

Aristida benthamii var.

benthamii

Three-awned Spear Grass Yes

Austrostipa verticillata Slender Bamboo Grass Yes

Avena fatua Wild Oats Yes

Cheilanthes sieberi Yes

Chondrilla juncea Skeleton weed Yes

Cynodon dactylon Couch Yes

Entolasia stricta Wiry Panic Yes

Eragrostis elongata Clustered Lovegrass Yes

Hypochaeris radicata Catsear, Flatweed Yes

Juncus usitatus Soft Rush Yes

Lolium perenne Perrenial Ryegrass Yes

Lomandra bracteata Yes

Modiola caroliniana Red-flowered Mallow Yes

Panicum effusum Hairy Panic Yes

Phalaris aquatica Canary Grass Yes

Plantago lanceolata Lamb’s Tongues, Plantain Yes

Poa labillardierei Tussock Yes

Polygonum arenastrum Wireweed Yes

Rosa rubiginosa Sweet Briar Yes

Rumex brownii Swamp Dock Yes

Rytidosperma racemosum Wallaby Grass Yes

Solanum nigrum Black Nightshade Yes

Themeda triandra Kangaroo Grass Yes

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Appendix C: Fauna Species List Class Name Scientific Name Common Name

Bird Acanthiza chrysorrhoa Yellow-rumped thornbill

Cacatua galerita Sulphur Crested Cockatoo

Eurystomus orientalis Oriental dollarbird

Gymnorhina tibicen Magpie

Platycercus eximius Eastern rosella

Psephotus haematonotus Red-rumped parrot

Merops ornatus Rainbow bee-eater

Microeca fascinans Jacky winter

Ocyphaps lophotes Crested pigeon

Pachycephala rufiventris Rufous Whistler

Rhipidura leucophrys Willie wagtail

Reptile Tiliqua rugosa Shingleback Lizard

Mammal Vulpes vulpes Fox

Attachment 3 - yassvalley.nsw.gov.au

Documents

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