20517 App M.pdf [As Published] · 132007.1259

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natural solutions

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Scanlon Property Group

 

Final Report

Ecological Assessment — 215-219
David Low Way, Peregian Beach

 

June 2007

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“IMPORTANT NOTE”

Apart from fair dealing for the purposes of private study, research, criticism, or review as permitted under the Copyright Act, no
part of this report, its attachments or appendices may be reproduced by any process without the written consent of Natural
Solutions Environmental Consultants Pty Ltd (“Natural Solutions"). All enquiries should be directed to Natural Solutions.

We have prepared this report for the sole purposes of Scanlon Property Group (“Client”) for the specific purpose only for which it
is supplied. This report is strictly limited to the Purpose and the facts and matters stated in it and does not apply directly or
indirectly and will not be used for any other application, purpose, use or matter.

In preparing this report we have made certain assumptions. We have assumed that all information and documents provided to
us by the Client or as a result of a specific request or enquiry were complete, accurate and up-to-date. Where we have obtained
information from a government register or database, we have assumed that the information is accurate. Where an assumption
has been made, we have not made any independent investigations with respect to the matters the subject of that assumption.
We are not aware of any reason why any of the assumptions are incorrect.

This report is presented without the assumption of a duty of care to any other person (other than the Client) (“Third Party”). The
report may not contain sufficient information for the purposes of a Third Party or for other uses. Without the prior written consent
of Natural Solutions:

a) this report may not be relied on by a Third Party; and

b) Natural Solutions will not be liable to a Third Party for any loss, damage, liability or claim arising out of or incidental to a
Third Party publishing, using or relying on the facts, content, opinions or subject matter contained in this report.

If a Third Party uses or relies on the facts, content, opinions or subject matter contained in this report with or without the consent
of Natural Solutions, Natural Solutions disclaims all risk and the Third Party assumes all risk and releases and indemnifies and
agrees to keep indemnified Natural Solutions from any loss, damage, claim or liability arising directly or indirectly from the use of
or reliance on this report.

In this note, a reference to loss and damage includes past and prospective economic loss, loss of profits, damage to property,
injury to any person (including death) costs and expenses incurred in taking measures to prevent, mitigate or rectify any harm,
loss of opportunity, legal costs, compensation, interest and any other direct, indirect, consequential or financial or other loss.

 

Quality Assurance Statement

 

 

 

Revision Author Reviewer Approved for Issue
No. Name Date
1 Jenni Garden Justin Watson Justin Watson 18 May 2007

Tyrone Lavery

 

 

 

 

 

 

NATURAL SOLUTIONS ENVIRONMENTAL CONSULTANTS PTY LTD

  

 

 

| Brisbane Office: f Cairns Office:

| Suite 16, Level 2 Central Brunswick, Level 2, 26 Florence Street

: Cnr Brunswick & Martin Streets i CAIRNS QLD 4870

' FORTITUDE VALLEY QLD 4006 : PO Box 6935, Cairns Qld 4870
PO Box 1156, Fortitude Valley Qld 4006 Tel: (07) 4041 3522

Tel: (07) 3124 9400 : Fax (07) 4051 4141

 

Fax: (07) 3124 9499
| Sunshine Coast Office - Steve Dudgeon | Townsville Office - Shayne Lowe

PO Box 1522 Level 4, Northtown Tower

» NOOSA HEADS QLD 4567 | 280 Flinders Mall (access via Ogden Street)
i i TOWNSVILLE QLD 4810

i | PO Box 279, Townsville Qld 4810

 

 

 

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Ecological Asse

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6.0
6.1
6.2
6.3

7.0
TA

TABLE OF CONTENTS

INTRODUCTION cesses tsssecsssnsnesexsnmncsoscssesnstenassurscucrevaunicanventsanivcsecnseederarenvens 1
Background

 

Scope of Work / Objectives

 
 

Site Description ,
Adjacent Land USe@.........cccccccccsseessecsecssccssecseecssecseceseesesessecsaceseseseeaessseseesseenseensee 2
STATUTORY CONSIDERATIONS. .......ccsscssssessesesssereseneesasenseseeseeseneeneneans 4

Federal Considerations ..........sscssssesessssssssssssesssessessnesseeeeeasens
Environment Protection and Biodiversity Conservation Act 1999

 
  
 
 
  
 
 
  
  

State Considerations. ..........
Integrated Planning Act 1997....
Vegetation Management Act 1999..
Environment Protection Act 1994....
Land Protection (Pest and Stock Route) Management Act 2002.
Nature Conservation Act 1992 and Regulations
Biodiversity Planning Assessment
South East Queensland Regional Plan 2005-2026 .
Biodiversity Assessment and Mapping Methodology (BAMM) .

 

Local Considerations
Noosa Shire Council Planning Scheme..

 

METHODOLOGV........ccscssesscsnseesensecensnssecensensesenseesensaseesessecseseusaraesersesaenense 17

Background Review
EPBC Protected Matters Database .
Wildlife Online Database..............
Regional Ecosystem (RE) Mapping.

 

 
 
 

Site Assessment.
Flora Assessment . ws
Falina ASSESSITIEN w...cevecsrnecrsnnsnrninisensansnemnsnnenaasnssennsaneonarnavennsnnnsaarisessenecsuerse 20

 

VEGETATION ASSESSMENT RESULTS .........csssesseseseeeeeeeeeeeeeeetenenenee 22
SIt@! SUPVOY ive. ereeneseraneersresecenscrenes cen unseen spreacencrmnecersnersm mn enineremrsen ees 22
SIQHHICANESPECISS ...0.-.ccecnsvecanenprnassvanvensuss nos nsrvensvereeunnseenussiecmecerenenuveneraenseereatess

 

FAUNA ASSESSMENT RESULTS..
Site Survey ...

 
 

Significant Species

BIODIVERSITY VALUES ........ccesesceeseseeeseeseeeeeneseseeseeseeneeseseesaeensneeesenenee 30
Caravan Park Areal.......csssessscesesenssessenenvaneuvatcsestsesctncnscunssns seseusversenssotecvesueensss 30
Vegetation Buffer 0.0... cccecessseesssessesesessesseseesesseeseesaneseeseseeseneseeeseneeaeaseeeeeeee 30
Remirianit Wet Heath Areal c..ncecssnsaviesscenevessnsnspeceincessesesessenererernenscananennesuceereenuneys 30

PROPOSED DEVELOPMENT

Environmental Considerations .

 

 

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12 Environini)ntal LiIMitatiOMs v.00. ..crssemreesseeceseserenssnenoonenennuvsnennreceemnnrnnesemnenncses 33
8.0 RECOMMENDATIONS AND MITIGATION MEASURES .........scseeeeeeee 36
9.0 CONCLUSION srisescsessessccsesetcsnssesnesesveseeserserenceseneeucecenmerersnercenrennuesemmneeeare 40
10.0 REFERENGES wisscescsscsccies sessnsevcevanvavanpanzveesweonseeunseveeveversetenapavivarsoraseseateecve 41
FIGURES

Figure 1

Figure 2

Figure 3. Noosa Heads Zone Map ZM4 +
Figure 4 _—_ Biodiversity Overlay Map OM4.1.............cecessessscseeeesesseeseescesseenseseeseeeneeaeens 15

Figure 5 Natural Hazards: Bushfire and Acid Sulfate Soils Overlay Map OM4.4.... 16
Figure 6
Figure 7 Broad Habitat Types ..
Figure 8 Proposed development layout

 

 
 

TABLES

 

Table 1 Relevant RE Descriptions
Table 2 Flora Species Identified on the Subject Site ....
Table 3 Likelihood of Significant Plant Species Occurring on Site...
Table 4 Likelihood of Significant Fauna Species Occurring on Site. a
Table 5 Habitat Types and Functional Value For Native Fauna .............::eeeeeee
Table 6 —_ Potential impacts on Site Ecological Values and Proposed Mitigation
INAS Ul es eee eeterene te entree erent er ere etree reteset entrees ttre reer enreen nett 36

 

 

APPENDICES

APPENDIX A _ Noosa Plan Local Law No. 10
APPENDIX B_ EPBC Protected Matters Report..
APPENDIX C_ Wildlife Online Report

 

 

 

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1.0 INTRODUCTION

1.1 BACKGROUND

Natural Solutions Environmental Consultants (Natural Solutions) has been requested by
Scanlon Property Group (the ‘client’) to undertake an Ecological Assessment of the properties
described as Lots 8, 9 and 10 on RP 9315 and Lot 56 on Crown Land MCH2969, Parish of
Weyba, County of March (the ‘site’). These properties are located at 215-219 David Low Way,
Peregian, within the local government area of Noosa Shire Council (NSC) (Figure 1).

Previous reporting and site assessments conducted in 2004 for the site by Natural Solution’s
staff (then C&B Group) have been consulted during the reporting of the Ecological Assessment
(Section 4.0 - Section 8.0).

1.2 Scope OF WorK / OBJECTIVES

The primary objective of the assessment was to investigate the site’s ecological values and
provide advice on the potential impacts on ecological values of the site and mitigation measures
required in relation to the proposed development. This Ecological Assessment report is to
accompany a Development Application for a material change of use for commercial buildings
(Visitor Hostel and Beach Shacks) on the existing caravan park area. The development will
also aim to protect and rehabilitate the ecological values of the wet heath habitat on the western
boundary. This report addresses local, state, and commonwealth requirements for the
assessment and protection of ecological values. In particular the report:

. Assesses the environmental values identified on the subject site;

. Identifies the occurrence, or likelihood of occurrence, of native fauna and flora species,
including significant species;

. Provides details of the potential environmental impacts and mitigation measures
associated with development of the subject site; and

. Provides recommendations for development and rehabilitation opportunities.

1.3 Site DESCRIPTION

The site is approximately 2 hectares in size and is located on a relatively flat (< 1%) landscape
located behind (west of) the Peregian Beach Hotel on the western side of David Low Way.
Roughly two-thirds of the site is used as a caravan park and camping grounds, and so has been
largely cleared of understorey, mid-storey, and ground cover vegetation. Several mature
canopy trees, primarily Broad-leaved Paperbark (Melaleuca quinquenervia) have been retained
on site. The ground cover within the caravan park area is currently maintained as mown grass.

The remaining third of the site (western portion) consists of remnant and regrowth vegetation.
Much of the regrowth vegetation occurs between the cleared caravan park area and the
remnant heath area, and is comprised of a dense mixture of native and exotic plant species.
The remnant vegetation occurring west of the regrowth vegetation, along the western boundary,
is dominated by native plants and is an extension of the Noosa National Park.

 

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1.3.1 Adjacent Land Use

The site is bounded to the north by a narrow strip of regrowth vegetation separating the site
from council owned playing fields, sporting complexes and associated infrastructure, and semi-
attached housing. To the east of the site is the Peregian Beach Hotel and David Low Way. A
narrow block of commercial buildings occur at the south-east site boundary, with the remainder
of the southern and the entire western site boundaries being bounded by remnant wet heath
vegetation communities of Noosa National Park.

The subject site has strategic environmental importance given its proximity to Noosa National
Park, which is identified and protected as a place of natural significance on the Register of the
National Estate (RNE) by the Environment Protection and Biodiversity Conservation (EPBC)
Act, and an Open Space Conservation Zone within the Noosa Plan (2006).

 

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Reregian,

Caravan

ite Boundary

IMPORTANT NOTE

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postion is approximate only.

 

   
  
  
    
 
  
     

 

 

 

(x). Scale shown is correct forthe original plan and any copies ofthis plan should be veriied
ly chacking against the bar scale

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‘consequential damage) and costs which you might incur as a result of the data being NATURAL SOLUTIONS ENVIR\ \L CONSULTANTS:

inacairate or ncomplete in any way and for any reason BRISBANE - CAIRNS - TOOWOOMBA - SUNSHINE COAST
ABN 38 103 132 716

Regional ecosystem mapping reproduced wih permission of Envronmental Protecion D B Project Mi Dio nabet aes

Agency 2004, Version 4, 2008-2005, rawn By roject Manager Purest aces

While every care is akon to ensure the accuracy ofthe Information Produc, the Envtonmental vw naturalsolutions.com.au

Protection Agency makes no representations or warranties about its accuracy, reliabilty, TLUIG Jw

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{including thou itaion, Faby negligence) for al expenses, losses, damages fncluding -

indirect or consequential damage) and cost which you might new as aresutolthe peas | PYOQTAM Checked Date Issue Drawing No.

being inaccurate or incomplete many way and for any reason

‘Atthis Scale the regional ecosystem linewotk should be used as a guide only. ArcGlS JW 17-05-2007 1 Figure 1_J07-049

RE data is mapped ata scala of 1:100,000 with a positonal accuracy of 100 metres.

 

 

 

 

 

 

 

 

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2.0 STATUTORY CONSIDERATIONS

The following sections outline the ecologically relevant federal, state, and local statutory
documents that are considered applicable to the proposed subject site, and the actions required
to address these requirements. The following legislation may require further detailed
consideration and possibly legal evaluation, where appropriate.

2.1 FEDERAL CONSIDERATIONS

2.1.1 Environment Protection and Biodiversity Conservation Act 1999

The Environment Protection & Biodiversity Conservation Act 1999 (EPBC Act) provides a
mechanism for assessing the environmental impact of activities and developments where
“Matters of National Environmental Significance” (MNES) may be significantly affected.

The Act identifies seven MNES, which require consideration and analysis, that is:

. RAMSAR wetland of international importance;

. World Heritage Properties;

. National Heritage Places;

. Commonwealth Marine Areas;

. Nationally listed threatened species and ecological communities;
. Nationally listed migratory species; and

. Nuclear actions (including uranium mining).

Under the Act, a referral is required if any future development on the site has or has the
potential to significantly impact directly or indirectly on any of these significant places or on any
listed threatened species.

A number of threatened and migratory species listed under this legislation potentially occur in
the site locality. In addition, the site also lies within 5km of two RAMSAR wetlands and two
natural places on the Register of the National Estate (RNE). Accordingly an EPBC referral will
be submitted, in due course, to the Department of Environment and Water Resources (DEWR),
outlining mitigation measures for protecting these significant species and areas. Section 3.1.1
provides further details of the MNES.

Section 4.0 outlines the significant species and their likelihood of occurrence on the subject
site, and Section 8.0 outlines the proposed mitigation measures to protect fauna and flora
species, and other environmental values of the site.

Register of National Estate (Australian Heritage Commission Act 1975)

The Register of the National Estate is a nation-wide heritage list for Australia that encompasses
natural, indigenous and historic places compiled by the Australian Heritage Council. There are
two natural heritage-listed places occurring within 5km of the subject site. Section 3.1.1
provides further details of these RNE places.

 

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2.2 STATE CONSIDERATIONS

224 Integrated Planning Act 1997
The Integrated Planning Act 1997 (IPA) seeks to achieve ecological sustainability by:

a) Coordinating and integrating planning at the local, regional, and State levels;

b) Managing the process by which development occurs; and

c) Managing the effects of development on the environment (including managing the use of
premises).

Compliance under this Act needs to be achieved. The Act identifies referral agencies and their
jurisdiction relevant to the assessment of development application.

The potential environmental impacts of the proposed development and the recommended
mitigation measures are outlined in Section 8.0. Other specific planning issues will be dealt
with by qualified town planners in other specialist reports.

2.2.2 Vegetation Management Act 1999

The purpose of the Vegetation Management Act 1999 (VMA) is to regulate clearing of remnant
vegetation on freehold and leasehold land by:

s Preserving remnant endangered, of concern, and not of concern Regional Ecosystems;
. Vegetation in areas of high nature conservation value; and
. Considering areas vulnerable to land degradation.

Analysis of the current mapping by the Department of Natural Resources and Water (DNRW)
indicates that the subject site contains two DNRW mapped Regional Ecosystems
(Section 3.1.3). The development works, within the site, will therefore need to adhere to the
regulations outlined in the VMA.

The Vegetation Management Act 1999 (VMA) is to be read in conjunction with the /ntegrated
Planning Act 1997 (IPA) with respect to the protection of remnant vegetation or category 1,
category 2, category 3, or category X vegetation.

The act restricts its reference to the removal of vegetation to section 22A: -
22A Particular vegetation clearing applications may be assessed
2) A vegetation clearing application is for a relevant purpose under this section if the applicant
satisfies the chief executive that the development applied for is —
(d) for establishing a necessary fence, firebreak, road or other built infrastructure, if there
is no suitable alternative site for the fence, firebreak, road or infrastructure;

The guidelines associated with the VMA 1999 provides for the removal of vegetation protected
under the VMA 1999 without a permit where that vegetation removal is for “Essential
Management”. Essential management is defined by the Act as: -

 

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Exemptions for clearing defined in Schedule, Part 1 of the Integrated Planning Act 1997
Exemptions on freehold land and indigenous land
(d) necessary for essential management

Essential management means clearing native vegetation:

(a) for establishing or maintaining a necessary fire break to protect infrastructure other
than a fence or road, if the maximum width of the fire break is equivalent to 1.5 times
the height of the tallest vegetation adjacent to the infrastructure, or 20 metres,
whichever is the greater or

(b) for establishing a necessary fire management line if the maximum width of the clearing
for the fire management line is 10 metres or

(c) _ by fire under the Fire and Rescue Service Act to reduce hazardous fuel load

It is also important to note the Vegetation Management Officers also use the 1.5 times the
height of the tallest vegetation adjacent to the infrastructure, or 20 metres whichever is the
greater as the setback rule for infrastructure from remnant vegetation. That is the closest wall of
a building (infrastructure) to remnant vegetation, protected under the VMA 1999 is to be located
no closer than 1.5 times the height of the tallest vegetation adjacent to the infrastructure or 20
metres which ever is the greater.

223 Environment Protection Act 1994

The object of the Environment Protection Act 1994 (EP Act) is to allow “...for development that
improves the quality of life, both now and in the future, in a way that maintains the ecological
processes on which life depends (‘ecologically sustainable development’)’.

The EP Act also has a number of policies that assist in promoting ecologically sustainable
development. These policies regulate:

. Air;

. Interim Waste;

" Noise;

. Waste Management; and
. Water.

It is understood that these issues will be addressed in the proposed development’s associated
management plans (e.g., Stormwater Management Plan) and / or conditions of approval.

2.2.4 Land Protection (Pest and Stock Route) Management Act 2002

The purpose of this Act is to provide for pest (flora and fauna) management for land and stock
route network management. Under this Act, there are procedures for declaring pest species
and obligations for landowners to keep land free of declared pest species.

This Act requires landholders to prevent the spread of declared pest species and control pests
within their land. Declared pest species observed on the subject site are detailed in Section 4.0

 

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(flora) and Section 5.0 (fauna). Mitigation measures to prevent the spread of declared pest
species are outlined in Section 8.0.

2.2.5 Nature Conservation Act 1992 and Regulations

The objectives of the Nature Conservation Act 1992 (NCA) are to protect native flora and fauna
and their habitat, and to use protected wildlife and areas in an ecologically sustainable manner.

A number of threatened species recorded as being within the locality of the subject site
(Section 4.0) are listed under the Schedules of the Nature Conservation (Wildlife) Regulation
(2006). The known, likely, or possible occurrences of these species within the subject site are
detailed in Section 4.0 (flora) and Section 5.0 (fauna).

The occurrence of these species within the subject site poses certain development constraints.
Section 8.0 outlines measures for mitigating the potential negative impacts on significant flora
and fauna species as a result of the proposed development works.

2.2.6 Biodiversity Planning Assessment

As a means to quantify biodiversity or conservation value of a site, the EPA Biodiversity
Assessment and Mapping methodology (EPA 2002) provides the framework for identifying the
site values through a process of “rating” various criteria.

The EPA has designated the subject site as of state significance (Figure 2) (EPA 2005b). The
designation relates to a number of criteria including: important habitat for EVR species,
remnants with a very high natural condition, and a high diversity of REs.

2.2.7 South East Queensland Regional Plan 2005-2026

The South East Queensland Regional Plan 2005-2026 (the ‘Regional Plan’) is a statutory and
planning instrument under the IPA (Qld Government, 2005). The primary purpose of the
Regional Plan is to provide a sustainable growth management strategy for South East
Queensland (SEQ) to the year 2026. The Regional Plan allocates land within SEQ into one of
five regional land use categories. Under this Regional Plan the subject site falls within the
‘Urban Footprint’ land use category which denotes it suitable for future urban development.

Included in the Regional Plan are policies to protect and enhance the region’s natural
environment, biodiversity, and future communities. The following policies are particularly
relevant to the Environmental Assessment for the site, and need to be considered during the
development application process:

1) Biodiversity (SEQ Regional Nature Conservation Strategy);
2) Koala Conservation (Nature Conservation (Koala) Conservation Plan 2006 and
Management Program 2006-2016); and

(1) The SEQ Regional Nature Conservation Strategy (RNCS) sets the regional framework for
nature conservation. The RNCS utilises the Biodiversity Planning Assessment (BPA) in order to

 

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identify areas of state, regional, and local biodiversity significance. According to the BPA, areas
of state significance were identified on the site (refer to Biodiversity Planning
Assessment) (Figure 2).

(2) The Nature Conservation (Koala) Conservation Plan 2006 and Management Program 2006-
2016 (Koala Plan) was adopted in October 2006, and is designed to protect and conserve
koalas (and their habitats) in Queensland through a statutory and policy framework. Under the
Koala Plan, the state is divided into three districts (A, B, and C). South East Queensland is
identified as ‘District A’, and within this district ‘Koala Habitat Areas’ have been mapped.
Certain new developments, occurring in ‘Koala Habitat Areas’, need to be assessed against
koala conservation criteria. Also, in Districts A & B clearing of koala habitat trees is to be done
in a sequential manner (to allow koalas to move off site of their own accord) and clearing of
koala habitat trees in a ‘Koala Habitat Area’ must be carried out in the presence of a spotter
catcher. The site is located within District A, and is mapped as an ‘Urban Koala Area’.
Any development in an ‘Urban Koala Area’ will be assessed against the Koala Conservation
Codes. In general, the codes applicable to the Urban Koala Area, requires koala sensitive
development and design to be applied. Recommendations regarding koala sensitive design are
outlined in Section 8.0.

 

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2.2.8 Biodiversity Assessment and Mapping Methodology (BAMM)

The BAMM classifies areas (areas based on RE mapping) into one of three levels of
Biodiversity significance: State, Regional, and Local or Other Values.

All areas within the site are rated as State significance. This means that the areas are
assessed as being significant for biodiversity at the bioregional or state scales. This rating also
includes areas assessed by other studies / processes as being significant at national or
international scales.

Seven diagnostic criteria are used to initially assess the Biodiversity Significance of areas:

1. Habitat for EVR Taxa (Criteria A) — this criterion brings together information on
Endangered, Vulnerable, and Rare (EVR) taxa using buffering of recorded sites in the
absence of Habitat Suitability Maps (HSM) for species. HSMs are gradually being
developed and will progressively replace point records of species.

2. Ecosystem Value (Criteria B) — this criterion combines a number of elements including
the Biodiversity Status of Regional Ecosystems (REs), the presence of poorly
conserved REs, the presence of significant wetlands, and areas of national importance
such as World Heritage Areas and RAMSAR sites (Note: B1=regional assessment;
B2=sub-regional assessment).

3. Tract Size (Criteria C) — this criterion is a measure of the relative size of tracts of
vegetation in the landscape.

4. Relative Size of REs (Criteria D) — this criterion classifies the relative size of each
examples of a RE. Patches are compared with all other occurrences of the same RE
(Note: D1=regional assessment; D2=sub-regional assessment).

5. Condition (Criteria E) — this criterion represents the quality of remnants judged by the
extent to which they resemble their natural condition.

6. Ecosystem Diversity (Criteria F) - this criterion reflects the degree to which REs are
‘packed’ within an area. That is, an area with high Ecosystem Diversity will have
relatively many REs and ecotones.

7. Context and Condition (Criteria G) - this criterion represents the extent to which
Remnant Unit incorporates, borders or buffers areas such as significant wetlands,
endangered ecosystems, and the degree to which a Remnant Unit is connected to other
vegetation.

For each area, each diagnostic criterion is allocated a standard rating of LOW, MEDIUM,
HIGH, or VERY HIGH.

The following table summarises the diagnostic criterion ratings for each of the areas within the
subject site, shown in Figure 2.

 

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CRITERIA
AREA
A B1 B2 Cc D1 D2 E F G
7 ' Very Mediu Very 7 '
1 Very High Very High | Low High Low Pi High High | Medium
i ; Very Mediu | Very 5 ;
2 Very High Very High | Low High Low i High High | Medium
7 7 Very Mediu Very 7 Very
3 Very High Medium Low High Low a High High High
A " Very Mediu | Very : Very
4 Very High Medium Low High Low a High High High
2.3 LOCAL CONSIDERATIONS
2.3.1 Noosa Shire Council Planning Scheme

Overlay Maps
The site and the proposed development works are influenced by three maps, and their relevant
codes, outlined in the Noosa Shire Council Planning Scheme (The Noosa Plan):

(1) Noosa Heads Zone Map ZM4 - this map shows that the site is zoned as ‘Open Space
Recreation’ (light green areas on map) (Figure 3). The planning intent of areas mapped
as open space recreation is intended to achieve the following:

“Areas of open space that contribute to the desired lifestyle of residents by offering
a variety of passive and active recreational experiences that are conducive to
community interaction and wellbeing”

(2) Biodiversity Overlay Map OM4.1 — this map shows that site does not have mapped on it
any environmental protection or enhancement areas, or riparian buffer areas. However,
the site is adjacent to Noosa National Park, which is mapped as an ‘Environmental
Protection Area’ (Figure 4). This classification warrants the highest level vegetation
protection in Noosa Shire, and the proposed development will need to provide mitigation
measures for protecting the adjacent environmental protection area.

(3) Natural Hazards: Bushfire and Acid Sulfate Soils Overlay Map OM4.4 — this map
shows that the site is identified as a combination of ‘High Potential Acid Sulfate Area’ and
‘Low Potential Acid Sulfate Area’ (Figure 5). An Acid Soils Management Plan will need to
be prepared, addressing the impacts of the development on areas of potential acid
sulfate soils and the proposed management of earthworks to minimise impacts on the
acid sulfate soils.

 

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An area along the southern site boundary is additionally mapped as a ‘High Bushfire
Hazard Area’ (Figure 5). Bushfire protection measures will need to be integrated into the
proposed development layout and it is considered that a long-term Bushfire Management
Plan will also need to be prepared for the proposed development.

Local Law No. 10 — Vegetation Management 2003

All vegetation in Noosa Shire is protected from vegetation interference under Council’s Local
Law No. 10 — Vegetation Management 2003 (Appendix A). Vegetation refers to all native
“...trees, plants and all other organisms of vegetable origin (whether dead or living) but does not
include declared plants within the meaning of the Rural Lands Protection Act 1985 or
undesirable species as described in a current landscaping guideline or pest management plan
adopted by Noosa Shire Council.” (Local Law No. 10 — Vegetation Management 2003, Part 1,
Section 4).

Accordingly, all vegetation management and rehabilitation activities proposed for within the
subject site must comply with the combined restrictions of Local Law No. 10 — Vegetation
Management 2003 for a Category C lot (i.e. freehold lot > 2 ha without an existing agreed
property vegetation management plan), and the relevant codes associated with the maps
outlined above. The following information outlines exempt and permitted vegetation
interference activities, as they relate to the proposed vegetation management and rehabilitation
of the subject site, and in accordance with the combined restrictions.

Exempt Vegetation Interference Activities
Vegetation interference activities relevant to the development and rehabilitation of the site and
which do not require Council approval (i.e. are exempt) are:

. The removal of undesirable vegetation;

. Pruning of native vegetation for the purpose of tree maintenance of hazard management,
where pruning results in no more than 20% loss of live canopy volume, per tree, per year.

(Note: Pruning does not include lopping or topping)

Permit Required Vegetation Interference Activities
Vegetation interference activities that do require Council approval (i.e. are not exempt) and so
will require an application under The Noosa Plan, are:

. Completely cutting down vegetation;

. Cutting or tearing branches, stems or roots, topping, pruning or lopping;

. Poisoning;

. Releasing oil, petroleum, paint, cement or any other deleterious substances to a root
zone;

7 Ringbarking;
. Scar barking;

 

. Fixing any object into the vegetation (e.g., into bark/trunk/branches) that may destroy or
seriously affect the vegetation;

. Using any tree climbing spikes that may destroy or seriously affect the vegetation;

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Damaging a root zone by compaction, excavation or filling in a way that may destroy or

seriously affect the vegetation;
Attaching a guy rope, cable or other contrivances that may destroy or seriously affect the

vegetation; and / or,
Uprooting or displacing that may destroy or seriously affect the vegetation.

 

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SCANLON PROPERTY GROUP a

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3.0 METHODOLOGY

3.1 BACKGROUND REVIEW

Relevant flora and fauna databases were reviewed in order to identify the suite of species
known to occur within the locale of the subject site. This section includes a summary of these
databases and their most relevant findings.

3.1.1 EPBC Protected Matters Database

A search of the Commonwealth Department of the Environment and Water Resources database
was conducted to produce a Protected Matters Report for a search area buffer of 5km around
the subject site. The report identifies the following Matters of National Environmental
Significance occurring within the search area (Appendix B):

. Two Wetlands of International Significance (Great Sandy Strait and Moreton Bay);

s 36 Threatened Species (11 birds, 2 frogs, 8 mammals, 2 ray-finned fishes, 5 reptiles, 2
sharks, and 6 plants); and

. 39 Migratory Species (23 birds, 9 mammals, 4 reptiles, and 1 shark).

Other matters protected by the EPBC Act, that were returned with the database search include:

. 2 Places on the RNE (Noosa-Maroochy Wallum Area, Peregian Environmental Park);

. 66 Listed Marine Species (23 birds, 1 mammal, 29 ray-finned fishes, and 13 reptiles);

. 14 Whales and Other Cetaceans;

. 2 State and Territory Reserves (Noosa National Park and Noosa River Fish Habitat); and
7 1 RFA (South East Queensland RFA).

3.1.2 Wildlife Online Database

The Queensland Government’s Environment Protection Agency (EPA) and Queensland Parks
and Wildlife Service (QPWS) Wildlife Online database was searched for flora and fauna records
within a search area buffer of 5km around the subject site. The search identified 1046 records,
(Appendix C) including:

- 18 fauna species and nine flora species listed by the Nature Conservation Act 1992
(NCA) as being regionally significant; and,

. Eight fauna species and two flora species listed by the EPBC Act as being nationally
significant.

3.1.3 Regional Ecosystem (RE) Mapping

RE mapping (Version 5.0) provided by the Department of Natural Resources and Water
(DNRW) were used to identify any REs occurring within the subject site. Three REs are
mapped as occurring within the subject site: 12.2.7 (not of concern), 12.2.12 (not of concern),
and 12.2.15 (not of concern) (Figure 6). Descriptions of these RE types are provided in
Table 1.

 

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TABLE 1

RELEVANT RE DESCRIPTIONS

 

RE

STATUS

DESCRIPTION

 

12.2.7

Not of Concern

Melaleuca quinquenervia open-forest to woodland. Other species include
Eucalyptus bancroftii, E. latisinensis, E. robusta, E. tereticornis, Corymbia
intermedia and Lophostemon suaveolens and Livistona decipiens. A shrub
layer may occur with frequent species including Melastoma affine or
Banksia robur. Dense stands of the exotic Baccharis halimifolia may occur
as a tall shrub understorey. The ground layer is sparse to dense and
comprised of species including the ferns Pteridium esculentum and
Blechnum indicum the sedges Schoenus brevifolius, Restio tetraphyllus,
Baumea rubiginosa and Gahnia sieberiana and the grass Imperata
cylindrica. Occurs on Quaternary coastal dunes and seasonally
waterlogged sand plains usually fringing drainage system behind beach
ridge plains or on old dunes, swales and sandy coastal creek levees.

 

12.2.12

Not of Concern

Closed or wet heath + stunted emergent shrubs/low trees. Characteristic
shrubs include Banksia spp. (especially B. robur) Boronia falcifolia,
Epacris spp., Baeckea frutescens, Schoenus brevifolius, Leptospermum
spp., Hakea actites, Melaleuca thymifolia, Xanthorrhoea fulva with
Baloskion spp. and Sporadanthus spp. in ground layer. Occurs on poorly
drained Quaternary coastal dunes and sand plains. Low part of sand mass
coastal landscapes where water collects from both overland flow and
infiltration from adjoining sand dunes.

 

12.2.15

 

 

Not of Concern

 

Coastal sedgeland with Baumea spp., Juncus spp. Lepironia articulata,
Gahnia spp. and Eleocharis spp. and associated water bodies. Occurs on
Quaternary coastal dunes and beaches. Low part of coastal landscape
where water collects from both overland flow and infiltration from adjoining
sand dunes.

 

 

 

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A

ee

 

 

 

   
  
   
   
  
 

IMPORTANT NOTE
Natural Sohitions Environmental Consultants accepts no responsiblity for any loss or

ay use or rely on this plan
tural Solutions:
suitable only forthe purpose ofthis plan. The accuracy ofthe
[contours have not been vatiied and no reliance should be placed upan such contours or any
purpose other than forthe criginal purpose ofthis plan.

 

i) Aerial photography and mapping has beon overlaid as a best fon the boundaries shown and]
postion is approximate only

iv) The dimensions, area, size and location of improvements shown on ths plan are

Jacproximate only and may vary

100
| Meters

 

Figure 6 - EPA Remnant RE Mapping

 

     
  

(v)_ Scale shown is correct fr the original plan and any copies ofthis plan should be veritiod
lby checking against the bar scale,

DIGITAL CADASTRAL DATA BASE
© The Siate of Queensiand (Department of Natural Resources) (1999

Based on Cadastral Data provided with the permission of the Depariment of Natural Resources
(Currant as at Aug/t999),

Scanlon Property Group

 

While evory care is taken to ensure the accuracy of this data, the Department of Natural
Resources makes no representations or warraniles about fs accuracy, reliably, completeness
fr suitably for any particular purpose and disclaims all responsibilty and al kabiy (including
without imation, labity in negigence) forall expenses, losses, damages (including inirect or
‘consequential damage) and costs which you might incur as a resuk of the data bsing
inaccurate or incomplete in any way and for any reason

Scale
1:1200

Size
A4

 

Regional ecosystem mapping reproduced with permission of Environmental Protection
‘Agency 2004. Version 4, 2003-2008.

While every care is taken to ensure the accuracy of he Information Product, the Envivonmental
Protection Agency makes no representations or warranties about its accuracy, reliability,
ccomploteness or suitability for any particular puroose and disclaims all ‘and ll ab

  

Drawn By
TLIG

Project Manager
JW

za

natural solutions

environmental cons
NATURAL SOLUTIONS ENVIRONMENTAL (

 

ants

 

BRISBANE - CAIRNS - TOOWOOMBA. SUNSHINE COAST

ABN 38 103 132716
Ph:07 4041 3522
Fax: 07 4051 3522
\wwewnaturalsolutions.com.au

 

 

 

{including without limitation, lability in negligance) for al expenses, losses, damages (including
Indirect or consequential damage) and costs which you might Incur as a result of the product
bboing inaccurate or incomplete in any way and for any reason.

[At this scale the regional ecosystem linwork should be used as a guide only,
RE data is mapped at a scale of 1:100,000 with a postional accuracy of 100 metros,

Program
ArcG|S

 

 

 

Checked
JW

 

Date
17-05-2007

Issue

 

Drawing No.
Figure 5_J07-049)

 

 

 

 

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3.2 Sit—E ASSESSMENT

A site inspection was conducted by Natural Solutions in May 2007. The primary objective of this
inspection was to conduct a rapid assessment of the flora and fauna present on the subject site,
and to identify development constraints in relation to flora and fauna. The assessment included:

. Identification of the broad vegetation communities and identification of incidental flora
species observation on site;

. Identification of incidental fauna species and fauna trace observations;

. Identification of any habitat resources located on, or surrounding, the site;

. Ground-truthing of EPA mapped RE type and extent;

Ls Consideration of ecological value of the subject site for the conservation of significant
species;

. Review of previous studies and reports conducted by C&B Group for the site.

The aim of the flora survey was to identify the broad vegetation communities that currently exist
on the site. Emphasis was placed on identifying significant flora species, and on analysing
vegetation communities to determine the likelinood of occurrence of any significant flora and
fauna species.

The aim of the fauna survey was to identify native and exotic species occurring on. site,
including significant fauna species, and potential key habitat and food resources that would
indicate the likelihood of significant species occurring within the subject site, even though they
may not have been detected during the fauna surveys.

3.2.1 Flora Assessment

The random meander technique was used to identify the flora species present on the site and
determine site vegetation communities. A broad sweep of individual vegetation communities
was undertaken to identify any significant flora species and assess the presence of habitat for
threatened plants and animals. Plant identifications were carried out by experienced ecologists
and using available flora and botanical reference material, where necessary.

It should be noted that the detectability of plants and the ability to accurately identify plants to
species level may vary greatly with the time of year, prevailing climate conditions, and the
presence of reproductive material (e.g. flowers, fruit, and seed capsules). Consequently, the
survey conducted for the subject site should not be regarded as conclusive evidence that
certain protected plants do not occur within the study site.

3.2.2 Fauna Assessment

An incidental fauna survey of the site was conducted concurrently with the flora assessment. All
species observed using or flying over the site were identified. In addition all scats, tracks, and
other fauna traces that were observed were identified. Scat samples were sent to Barbara
Triggs for expert analysis.

 

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All fauna surveys are subject to inherent limitations in the detection success of target species.
These limitations often result in a degree of false-absence records (i.e. a species is present, but
not detected). It is important, therefore, that the limitations to fauna surveys are identified and
the fauna survey results are viewed with these constraints in mind. The limitations to the fauna
surveys conducted at the subject site were:

. The survey period not coinciding with the period that some migratory or nomadic species
occur in the locality;

. Species with a large home ranges (e.g. owls and raptors) not present in this part of their
home range during the survey period;

. The difficulty in detecting certain species during the survey period (e.g. cryptic species,
species present in the study area at very low densities, and trap-shy species);

. Biological factors such as sex, age-class, and breeding biology, which may influence
species’ habitat use and detectability during different times of the year;

. The lack of suitable climatic conditions necessary for the presence and / or detectability of
certain species (e.g. amphibians following heavy rainfall);

. The current severe drought being experienced in the Southeast Queensland region will

influence the current detection success of various species for a number of reasons, for
example: population densities may have decreased leading to decreased detection
probability; certain species (e.g., amphibians) may enter a state of torpor during the
drought conditions; loss of favourable habitat conditions may force species to move
outside of the subject site; localised species extinctions (although species migrations into
suitable habitats may occur when the drought breaks) N.B. Previous site assessments,
by C&B Group, were conducted in more favourable weather conditions (i.e., during warm
rainy conditions), prior to the drought; and

. No detailed fauna trapping / transects were conducted, which substantially decreases the
likelihood of detecting fauna species occurring on site, particularly small ground-dwelling
species and cryptic / rare species.

 

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4.0 VEGETATION ASSESSMENT RESULTS

4.1 SITE SURVEY

For ease of discussion, the site has been divided into three broad habitat types (Figure 7):

(1) Caravan Park Area - The eastern two-thirds of the site has been historically cleared for
urban / commercial purposes, resulting in large areas of open, mown grass areas with
scattered canopy trees. This area is currently used and maintained as a caravan park.
The canopy trees in this area are predominantly Broad-leaved Paperbarks (Melaleuca
quinquenervia).

(2) Remnant Wet Heath Area - The western third of the site is an extension of the Noosa
National Park which adjoins the western site boundary. This area is largely undisturbed
and is comprised of remnant wet heath vegetation consistent with the EPA’s RE mapping.
Few exotic species were apparent in this area.

(3) Vegetation Buffer - The caravan park area is separated from the remnant wet heath
habitat by a strip of highly disturbed vegetation. This vegetation buffer is comprised of a
dense mixture of native and exotic vegetation. The abundance of exotic weed species in
this area is indicative of historical nutrient levels in storm water run-off.

The native and exotic flora species identified within the site during NSEC’s site visit are provided
in Table 2. It must be noted, however, that poor recordings were made of species in the
Poaceae, Restionaceae, Cyperaceae and Juncaceae families, all of which are well represented
at the site but require more time to produce an adequate identification. In addition, detection of
species in the remnant heath and. vegetation buffer areas was limited by the dense nature of
these areas.

 

 

It is our understanding, through communications with the Peregian Beach Caravan Park staff,
that the Noosa National Park conducted a prescribed management burn following NSEC’s site
visit. This management burn was expected to incorporate the remnant vegetation in the
western portion of the subject site. NSEC believes that an additional site visit within 6-12
months following this prescribed management burn may substantially increase the number of
native flora species able to be detected and identified within the remnant vegetation area.

 

 

 

 

 

TABLE 2 FLORA SPECIES IDENTIFIED ON THE SUBJECT SITE
FAMILY SCIENTIFIC NAME COMMON NAME
Native
Proteaceae Banksia robur Swamp Banksia

 

Blechnaceae

Blechnum indicum

Bungwall Fern

 

Rutaceae

Boronia parviflora

Swamp Boronia

 

Burmanniaceae

Burmannia disticha

Christmas Candles

 

 

 

 

 

 

 

 

Myrtaceae Callistemon pachyphyllus Wallum Bottlebrush
Lauraceae Cassytha glabella Slender dodder-laurel
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FAMILY SCIENTIFIC NAME COMMON NAME

Fabaceae Crotalaria montana Rattlepod

Cyperaceae Cyperus haspan -

Fabaceae Dillwynia floribunda =

Droseraceae Drosera binata ~

Droseraceae Drosera spatulata Spoon-leaved Sundew

Restionaceae Empodisma minus -

Ericaceae Epacris microphylla 7

Cyperaceae Gahnia sieberiana Sword Grass

Euphorbiaceae Glochidion ferdinandi Cheese Tree

 

Euphorbiaceae

Glochidion sumatranum

Large-leaved Cheese Tree

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

Bloodroot Haemodorum tenuifolium Haemodoraceae
Proteaceae Hakea actites =

Dilleniaceae Hibbertia salicifolia -

Malvaceae Hibiscus tiliaceus Cotton Tree

Juncaceae Juncus continuus Pithy Rush

Juncaceae Juncus usitatus Common Rush
Myrtaceae Leptospermum liversidgei Lemon-scented Leptospermum
Myrtaceae Leptospermum polygalifolium Wild May

Adiantaceae Lygodium microphyllum Climbing Maidenhair
Euphorbiaceae Macaranga tanarius Macaranga

Myrtaceae Melaleuca quinquenervia Broad-leaved Paperbark
Fabaceae Mirbelia rubiifolia i

Apocynaceae Parsonsia straminea Monkey Rope Vine
Polygonaceae Persicaria decipiens Smartweed
Proteaceae Persoonia virgata Geebung

 

Philydraceae

Philydrum lanuginosum

Woolly Frogmouth

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

Thymelaeaceae Pimelea linifolia Rice Flower
Dennstaedtiaceae Pteridium esculentum Common Bracken Fern
Fabaceae Pultenaea paleacea a Pea Bush
Epacridaceae Sprengelia sprengeliodes -
Sphagnaceae Sphagnum cuspidatum Sphagnum Moss
Typhaceae Typha orientalis Cumbungi
Xanthorrhoeaceae Xanthorrhoea fulva Wallum Grass Tree
Xyridaceae Xyris complanata Hat Pins
Exotic
Asteraceae Ageratum houstonianum Blue Billygoat Weed
Asteraceae Baccharis halimifolia Groundsel Bush?
Asteraceae Bidens pilosa Cobbler’s pegs

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FAMILY SCIENTIFIC NAME COMMON NAME

Cyperaceae Cyperus brevifolius Mullumbimby Couch

Cyperaceae Cyperus papyrus Papyrus

 

Caryophyllaceae

Drymaria cordata ssp. diandra

Tropical Chickweed

 

Fabaceae

Erythrina crista-galli

Cockscomb Coral Tree

 

Euphorbiaceae

Euphorbia cyathophora

Painted Spurge

 

Convolvulaceae

Ipomoea indica

Blue Morning Glory

 

 

 

 

 

Verbenaceae Lantana camara Lantana*®

Poaceae Melinis minutiflora Molasses Grass
Passifloraceae Passiflora subpeltata White Passionflower
Poaceae Pennisetum purpureum Elephant Grass
Araliaceae Schefflera actinophylla Umbrella Tree

 

Anacardiaceae

Schinus terebinthifolia

Broad-leaved Pepper Tree®

 

 

 

 

 

 

Poaceae Setaria sphacelata South African Pigeon Grass
Solanaceae Solanum seaforthianum Climbing Nightshade
Solanaceae Solanum torvum Devil's Fig

Arecaceae Syagrus romanzoffiana Cocos Palm

 

 

 

1, 2, 3: Weed species rating under the Land Protection (Pest and Stock Route Management) Act 2002.

4.2

SIGNIFICANT SPECIES

Fifteen significant (NCA and EPBC) flora species were identified during database searches as
potentially occurring within the subject site. Table 3 shows the likelihood of these species
occurring on the subject site, even if they may not have been identified during the field

assessments.

TABLE 3

LIKELIHOOD OF SIGNIFICANT PLANT SPECIES OCCURRING ON SITE

 

LIKELIHOOD

COMMON

SPECIES NAME

STATUS

HABITAT

OF
OCCURRENCE

 

Acacia baueri Tiny Wattle

Qv

Occurs in coastal heathland, particularly wet
heathlands & ecotone areas between wet
heathland & mid-open woodland communities
of low nutrient coastal plains. Occurs in
seasonally waterlogged sandy soils of the
coast & can stand a full sun exposure. Occurs
in shade in association with Banksia aemula
woodlands. In NSW, found in heathland and
adjacent plateaus, in Qld found mostly from
0-5m above sea level.

Likely

 

 

Allocasuarina Mt. Emu

emuina She-Oak

 

 

QE, CE

 

Open and closed heath on fine-grained
thyolite rocky slopes (Mt Peregian) and in
wallum heath on undulating coastal plain.
Occurs in coastal areas in low mixed species
mountain heath, low mixed species wet
heathland & in nearby Banksia _aemula

 

Possible

 

 

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environmental consultants
LIKELIHOOD
species | COMMON | status HABITAT OF
OCCURRENCE

ecotone areas where it grows as a middle

level plant. Colonises areas following fire or

major physical disturbance as long as

sufficient seed-bank is available.
Alyxia Chain Fruit QR Remnant Rainforest. Unlikely
magnifolia
Blandfordia Christmas QR Confined to coastal lowlands & requires the Possible
grandiflora Bells sandy, acidic soils found in the wet

heathlands and sedge lands. Occurs in low

wet closed heathlands with associated

species including Empodisma minor,

Lepyrodia interrupta, L.caudata, L.scariosa,

Gahnia sieberiana and Baumea articulata.
Bulbophyllum Miniature CV Only occurring on trunks and branches of Unlikely
globuliforme Moss-orchid (Hoop Pine) Araucacria cunninghamii. Tiny

epiphytic orchid which could be mistaken for

a moss or lichen because of its habit of

growing in extensive masses on trees.

Typically occurs in tall Aracarian rainforest

above 500m in altitude, but has been found in

rainforests of the coastal lowlands.
Cryptocarya Stinking Qv Woodlands and swamp-heath with intact leaf Unlikely
foetida cryptocarya litter with associated mycorrhizal fungi.
Durringtonia Durringtonia QR Grows in closed sedgeland communities in Possible
paludosa coastal swamps.
Eucalyptus Swamp QE, CE | Sandstone areas on sandy or stony soils. Possible
conglomerata | Stringybark Commonly cultivated.
Glycine QR A vine in Eucalypt forest. Known only from a Unlikely
argyrea small area on the Cooloola sand mass.
Gompholobium | Fabaceae QR Open or dry heath & wet heath. Possible
virgatum var.
emarginatum
Macarthuria QR Dry heath of Noosa region and Noosa River Possible
complanata Plain.
Phaius Lesser QE, CE | Swamps and islands in Moreton district. Possible
australis Swamp Grows in swamps & low-lying depressions in

Orchid forests of the coastal lowlands & ranges,

mostly at or near sea level. Often found in

association with Melaleuca quinquenervia &

wetlands. Requires full shade.
Prasophyllum QV, CV_ | low mountain heath and wallum areas of the Possible
wallum coastal lowlands. Also adjacent vegetation on

stabilised sand dunes and on shallow soils

over volcanic rhyolite.
Schoenus QR Swampy and wet heath coastal areas. Likely
scabripes
Symplocos QR Tall closed rainforests & in riparian rainforests Unlikely
harroldii on rich alluvial & basalt derived soils.

 

 

 

 

 

Status: C = Commonwealth (EPBC); Q = Queensland (NCA; LC = Least Concern; R = Rare; V = Vulnerable, E =

Endangered.

 

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SCANLON PROPERTY GROUP ——

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5.0 FAUNA ASSESSMENT RESULTS

 

5.1 SITE SURVEY

Nine bird species were identified during the site visit. Most of these birds were common species
such as Magpie Lark (Grallina cyanoleuca), Welcome Swallow (Hirundu neoxena), and
Lorikeets (Trichoglossus spp.). However, a Square-tailed Kite (Lophoictinia isura) was also
identified within the site. This species is listed as rare species within Queensland, according to
the Nature Conservation (Wildlife) Regulation 2006. A further three mammal species (red fox,
Vulpes vulpes, Swamp Wallaby, Wallabia bicolour, and Water Rat, Hydromys chrysogaster)
were identified from scat collected on site. The Red Fox is listed as a Class 2 pest species
under the Land Protection (Pest and Stock Route Management) Act 2002.

In addition, during the previous site inspection conducted by C&B Group, the exotic Cane Toad
(Bufo marinus) and native Wallum Froglet (Crinia tinnula) were both identified on site. The
Wallum Froglet is listed as a vulnerable species within Queensland, according to the Nature
Conservation (Wildlife) Regulation 2006.

These species identifications are not considered a comprehensive list of the species occurring
on site due to the limitations outlined in Section 3.2.2.

5.2 SIGNIFICANT SPECIES

Twenty-three significant fauna species (11 birds, 5 mammals, 2 reptiles, and 5 amphibians)
were identified during database searches as potentially occurring within 5km of the subject site.
Table 4 shows the likelihood of these species occurring on the subject site. Marine aquatic
species (i.e. exclusively marine mammals, birds, reptiles, fishes, and sharks) have been
excluded from Table 4.

 

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a

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

Ecological Assessment :
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TABLE 4 LIKELIHOOD OF SIGNIFICANT FAUNA SPECIES OCCURRING ON SITE
LIKELIHOOD
SPECIES coun. STATUS HABITAT OF
OCCURRENCE
Birds
Accipter Grey QR Rainforests, forests, forest gullies Unlikely
novaehollandiae Goshawk and valleys, tall woodlands and
timbered watercourses.
Anseranas Magpie Lo Large seasonal wetlands and well Transient
semipalmata Goose vegetated dams with rushes and
sedges.
Apus pacificus Fork-tailed M, LO Over open country, from semi Transient
Swift deserts to coasts.
Ardea alba Great Egret M, LO Wetlands, flooded pastures, dams, Occasional
estuarine mudflats, mangroves and
reefs.
Ardea ibis Cattle Egret M, LO Wide range of open habitats from Likely
grazing paddocks to wetlands and
tidal mudifats.
Calyptorhynchis Glossy Black Qv Allocasuarina species within Unlikely
lathami Cockatoo woodland, forests, timbered water
courses.
Cyclopsitta Coxen's Fig- | QE, CE, | Rainforests, adjacent eucalypt Unlikely
diophthalma coxeni_ | Parrot M woodlands and coastal scrubs with
fig and soft fruit trees.
Ephippiorhynchus Black- QR Coastal wetlands, mangroves, tidal Occasional
asiaticus necked Stork mudflats, and estuaries.
Erythrotriorchis Red QE, CV | Open forests, woodlands especially Possible
radiatus Goshawk near rivers, wetlands, rainforest Transient
fringes.
Gallinago hardwickii | Latham’s M, LO Soft wet ground or shallow tussocks Unlikely
Snipe and other green or dead growth.
Haliaeetus White-bellied M, LO Wide range of coastal habitats. Likely
leucogaster Sea Eagle
Hirundapus White- M, LO Airspace over forests, woodlands, Likely
caudactus throated farmlands, plains, lakes etc within
Needletail its range.
Lathamus discolor Swift Parrot CE,LO | Eucalypt forests and woodlands, Unlikely
plantations and banksias.
Merops ornatus Rainbow M,LO | Wide range of open habitats from Likely
Bee-eater grazing paddocks to wetlands and
tidal mudlfats.
Monarcha Black-faced M,LO | Rainforests, eucalypt woodlands, Unlikely
melanopsis Monarch coastal scrubs.
Monarcha Spectacled M,LO | Understorey of lowland and Unlikely
trivirgatus Monarch mountain rainforest.
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Draft Report environmental consultants
LIKELIHOOD
SPECIES Sener © |ISTATUS HABITAT OF
OCCURRENCE
Myiagra cyanoleuca | Satin M, LO Heavily vegetated gulllies in forests. Unlikely
Flycatcher
Nettapus Australian M, LO Deeper freshwater swamps, Unlikely
coromandelianus Cotton lagoons, dams.
albipennis Pygmy-
goose
Pezoporus wallicus | Ground Qv Heathlands of coasts, ranges, Likely
wallicus Parrot swampy heaths, drier ridges in
swamps, occasionally grasslands
near heathlands.
Rallus pectoralis Lewin's Rail QR Permanent to ephemeral, fresh to Likely
saline wetlands that have dense
emergent or fringing vegetation.
Rhipidura rufifrons | Rufous M,LO | Undergrowth of rainforests, wetter Unlikely
Fantail eucalypt forests, gullies.
Rostratula australis | Australian cv Well vegetated shallows and Likely
Painted margins of wetlands and other
Snipe water courses.
Rostratula Painted M, LO Well vegetated shallows and Likely
benghalensis Snipe margins of wetlands and other
water courses.
Sterna albifrons Little Tern M,LM_ | Coastal waters, bays, inlets, saline Unlikely
or brackish lakes, saltfields and
sewage ponds near coast.
Turnix Black- QV, CV Leaf litter in drier rainforests and Unlikely
melanogaster breasted scrubby woodlands.
Button-quail
Xanthomyza Regent QE, CE, | Dry open eucalypt forests and Unlikely
phrygia Honeyeater M woodlands particularly along creek
flats.
Mammals
Chalinolobus dwyeri | Large-eared QR, CV _ | Caves and mines in dry schlerophyll Unlikely
Pied Bat forests and woodlands as well as
higher altitude moist eucalypt forest
and edges of rainforest.
Dasyurus Spotted-tail QV,CE | Rainforest, open forest, woodland, Unlikely
maculatus Quoll coastal heathland and _ inland
maculatus riparian forest from sea-level to sub-
alps.
Potorous tridactylus | Long-nosed CV Subtropical and warm temperate Unlikely
tridactylus Potoroo rainforest, wet sclerophyll forest and
coastal healthy woodland with
dense understorey and light, sandy
soils.
Pteropus Grey-headed cv Rainforests, mangroves, Paperbark Transient
poliocephalus Flying-fox swamps, wet and dry sclerophyll
forest often in gullies and near
water.
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Draft Report environmental consultants
LIKELIHOOD
SPECIES COMMON | staTus HABITAT OF
OCCURRENCE
Xeromys myoides False Water} QV,CV | Saline grassland, mangroves, Unlikely
Rat margins of freshwater swamps and
lakes close to foredunes.
Reptiles
Coeranoscincus Three-toed QR, CV Rainforest and adjacent wet Unlikely
reticulatus Snake-tooth sclerophyll forests, where it is
Skink usually found in rotting logs or in
soil under fallen timber.
Ophioscincus Short QR Dry sclerophyll, coastal heathland, Unlikely
truncatus Limbed rainforest and associated wet
Snake Skink sclerophyll.
Amphibians
Adelotus brevis Tusked Frog Qv Near puddles, streams and water Unlikely
bodies in rainforest, wet
schlerophyll forest and open grazing
country. Usually found under logs or
stones or in cavities and crevices.
Crinia tinnula Wallum Qv Acid paperbark swamps of the Known
Froglet wallum country.
Litoria freycineti Wallum Qv A terrestrial frog found in a wide Likely
Rocketfrog variety of heath and forest habitats
usually on warm spring or summer
nights after rain.
Litoria Wallum QV, CV | Along creeks and in marshy or Likely
olongburensis Sedge Frog swampy lowland habitat amongst
emergent vegetation and reeds in
the wallum region.
Litoria cooloolensis_ | Cooloola QR Often associated with water in Likely
Sedge Frog wallum country, lowland rainforest

 

 

 

 

and vegetation surrounding
freshwater lakes.

 

 

Status: C = Commonwealth (EPBC); Q = Queensland (NCA); BCC = Brisbane City Council; LC = Least Concern; R =

Rare; V = Vulnerable; U-R = Uncommon to Rare; M = EPBC listed migratory species; LM = EPBC Listed marine

species; LO = EPBC listed over-fly marine species.

Habitat Description / Status References: Wildlife Online and EPBC Databases; Queensland Museum 1995.

 

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6.0 BIODIVERSITY VALUES

Within the subject site, historical use and disturbance of vegetation has resulted in a mosaic of
different habitat types occurring on site. The three broad habitat types occurring on site were
described in Section 4.1 (Figure 7). Each of these broad habitats offers elements that fulfil a
range of requirements for various native fauna species. In addition, elements such as fallen
logs, which are not necessarily associated with a particular habitat type, fulfil important foraging,
shelter, and nesting requirements for terrestrial reptiles and mammals. Reptiles may also use
such elements for thermoregulation (i.e., essential regulation of their body temperature). The
following sections outline the key habitat values / characteristics of each habitat type, and
Table 5 outlines broad fauna groups that may utilise each habitat type, and the functional value
provided for fauna by each habitat type.

6.1 CARAVAN PARK AREA

The grass ground cover in this area is regularly maintained (mown) and the area as a whole is
heavily utilised by people. As such this area affords little habitat value for ground-dwelling
native species, although a certain mammals such as macropods and bandicoots may potentially
forage in this area. The mature paperbark trees scattered through this area provide substantial
nesting, resting, and foraging habitat for various bird species. The trees may also provide
suitable nesting and foraging habitat for arboreal mammal and reptile species.

6.2 VEGETATION BUFFER

Although highly disturbed, this more densely vegetated area will provide habitat values similar to
those provided by the remnant wet heath area. However, the disturbed nature of this area is
likely to be unsuitable for certain species that are particularly sensitive to habitat condition and
external disturbances.

6.3 REMNANT WET HEATH AREA

The remnant vegetation in this area provides significant habitat values for native fauna species.
For instance, birds (including migratory species) may use the trees bordering the open wet
heath for resting, shelter, foraging, and / or nesting. Arboreal mammals such as gliders, koalas
and possums, require a series trees in order to disperse within and between home ranges.
These species, as well as bats, also utilise trees for resting, foraging, and shelter. Certain
reptiles (e.g. monitors, snakes, lizards, and geckos) may utilise trees for shelter and
thermoregulation.

The Gilgai formation (i.e. hummocky micro-relief of soils produced by expansion and contraction
caused by changes in moisture) of the wet heath also provides substantial habitat values for
various fauna species. For example, predatory birds and mammals may use the area for
foraging purposes. In addition, the area is particularly important for providing essential shelter,
nesting, refuge, and foraging values for amphibians and other small ground-dwelling species
(reptiles, mammals, and birds).

 

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TABLE 5 HABITAT TYPES AND FUNCTIONAL VALUE FOR NATIVE FAUNA

FUNCTIONAL ROLE
HABITAT

TYPE FAUNA GROUP

Thermo-
regulation

Foraging Dispersal Shelter Nesting

Arboreal
Terrestrial

Arboreal
Mammals

Caravan Terrestrial

Park Arboreal

Reptiles
Terrestrial

Arboreal
Amphibians
Terrestrial

Arboreal
Terrestrial

Arboreal
Mammals

Vegetation Terrestrial

Buffer Arboreal

Reptiles
Terrestrial

Arboreal
Amphibians
Terrestrial

Arboreal
Terrestrial

Arboreal
Mammals

Remnant Terrestrial

Wet'Heath Arboreal

Reptiles
Terrestrial

Arboreal
Amphibians
Terrestrial

 

Note, value of functional role for fauna groups: Hl High; H Moderate; EI) Low; [5] N/A.

 

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Es] Site Boundary

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SCANLON PROPERTY GROUP, &

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7.0 PROPOSED DEVELOPMENT

The proposed development is for a material change of use (MCU) for commercial and
accommodation buildings (Figure 8). A single commercial building is proposed for the east of
the site adjacent to David Low Way. The accommodation buildings are proposed for the
existing caravan park area as far west as the current vegetation buffer. These buildings will
consist of hostel accommodation comprising three buildings connected by raised walkways, and
30 beach shacks (one to become caretaker's residence).

In addition, a caretaker’s residence will occur at the entrance to the site, which will be via the
existing service road off David Low Way. Additional recreational infrastructure associated with
two communal areas (comprising cooking facilities, play areas, and pool) are also proposed to
be located centrally within the accommodation buildings.

The western portion of the site which is currently comprised of the vegetation buffer and
remnant wet heath habitat adjacent to Noosa National Park is retained within the proposed
development layout as a 35-80m vegetated buffer feature. In addition, the existing vegetation
buffer will be rehabilitated to remove and control weed species.

7.1 ENVIRONMENTAL CONSIDERATIONS

Ecological investigations suggest that the ecological constraints for further development of the
Peregian Beach Caravan Park will be associated with:

 

 

. Providing acceptable vegetated and rehabilitated buffers between the national park and
areas of development.

 

Further environmental considerations will need to include;

 

 

. Management of stormwater runoff into the buffer and National Park;
. Management of nutrient run off into the buffer and National Park;
. Bushfire management and mitigation measures (including set-backs, asset design, fire

breaks etc); and
. Acid sulphate soils management.

 

It is also our opinion that stormwater / nutrient runoff into the buffer / National Park will be a
major concern.

7.2 ENVIRONMENTAL LIMITATIONS

It is apparent, from previous Council correspondence (Noosa Shire Council, 2004), that areas of
remnant vegetation in the western portion of the subject site are unlikely to be approved for
development. These constraints are considered to also meet responsibilities in protecting
potential habitat for known threatened species listed under the Federal and State legislation.

 

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The remnant wet heath vegetation and currently disturbed vegetation buffer are retained in the
proposed development layout. In addition, rehabilitation of the vegetated buffer will act to
enhance habitat values for native fauna species, as well as acting to further protect the remnant
wet heath habitat and adjacent Noosa National Park from potential negative impacts associated
with the proposed development.

 

Large trees retained throughout the site and within the grassed area are also likely to be
ecological constraints, however such trees provide ecological and amenity value and their
retention could be used as a feature throughout the development layout.

 

 

Many of the mature paperbark trees currently existing in the caravan park area have been
retained in the proposed development layout. In addition, no clearing of native vegetation will
occur within the vegetated buffer or remnant wet heath areas.

 

 

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Page 40

 

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Page 41

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8.0 RECOMMENDATIONS AND MITIGATION MEASURES

The potential impacts associated with the proposed development, and the proposed measures
to mitigate these impacts, are identified in Table 6. The level or likelihood of the impact is
based on the ecological values identified for the site, proposed activity, and feasibility of
prevention and mitigation. A ‘high’ level of impact indicates it is highly likely that this impact will
occur and the ability to prevent the impact is minimal. In these instances, containment of the

 

Draft Report

impact and / or appropriate and acceptable mitigation measures would be considered. These
recommendations are to be considered in conjunction with other environmental management
measures, such as_ bushfire management, rehabilitation management, stormwater
management, and acid sulfate soils management.

In addition to the mitigation measures outlined below, NSEC advises that an EPBC referral
should be undertaken for the site, prior to development works.

TABLE 6 POTENTIAL IMPACTS ON SITE ECOLOGICAL VALUES AND PROPOSED
MITIGATION MEASURES

 

LEVEL OF

IMPACT IMPACT

PROPOSED MITIGATION MEASURES

 

Loss of Low

vegetation . Retention of vegetation within the buffer and remnant wet

heath areas, west of the current caravan park area.

. Rehabilitation of the existing vegetation buffer between the
caravan park area and the remnant wet heath area.

* Prepare and implement a Rehabilitation Management
Plan to direct the rehabilitation and replanting works to
occur within the vegetated buffer area.

. The rehabilitation of this area should consider bushfire
risks and protection of the remnant heath area from
pollutants and stormwater run-off. As such the
rehabilitation should occur in accordance with other
technical reports for the site

= Retention of many of the mature paperbark trees currently
existing within the caravan park area.

' Provision of temporary fencing (before and during
development works) to protect vegetation to be retained

x Fence along the boundary between the caravan park
area and the vegetation buffer; and

. Fence around mature trees to be retained within the
caravan park area.

. Minimise the likelihood of erosion and sedimentation through
the implementation of an Erosion and Sediment Control Plan.

. Avoid dispersal of pollutants / chemicals into retained
vegetation areas.

. Ensure all vehicles are cleaned (free of contaminants)
prior to entering the subject site.

= Prepare and implement a stormwater / run-off
management plan.

. Prepare a Landscaping Plan, which incorporates the use of

 

 

 

 

 

 

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IMPACT

LEVEL OF
IMPACT

PROPOSED MITIGATION MEASURES

 

Loss of
vegetation

(con't)

native and endemic plant species.

Regular monitoring, and repair if necessary, of temporary
fences (erected prior to and during construction phase)
bordering retained vegetation and areas of disturbance.

Suitable management of soil stripping and vegetation
mulching;

No dumping of refuse into retained vegetation areas.

Ongoing monitoring (and action if necessary) of all
rehabilitation areas in accordance with the Rehabilitation
Management Plan.

 

Loss of
significant
fauna / habitat

Low

Prepare an Environmental Management Plan for the pre-,
during, and post-construction phases, which will incorporate
detailed fauna management sections

Habitat for significant flora and fauna species will be retained
and enhanced within vegetated buffer and remnant wet heath
areas.

Site management plans / strategies to manage for significant
species during construction and operation are recommended.

Habitat and food resource trees are included in landscaping
and rehabilitation areas.

Any vegetation clearing on site will be conducted in a
sequential manner to allow koalas to move off the site at their
own accord.

Prior to tree felling activities, a spotter-catcher will be
employed to supervise clearing activities.

If a koala is spotted (by any person) in a tree on site during
vegetation clearing works, the tree containing the koala/s and
the surrounding trees must not be cleared on that day. These
trees may only be cleared on subsequent days if the koala/s
has moved out of them at their own will.

Fauna boxes will be erected in suitable trees to help offset the
potential necessary removal of hollow-bearing trees during the
construction phase.

Reduced speed limits (recommended maximum of 10 km) will
be implemented on the subject site’s internal road system.

Prohibition of domestic pets (e.g., dogs and cats) within the
site before, during, and after development works.

 

Water Quality /
Stormwater

 

 

High

 

Prepare a Stormwater Management and Water Quality Plan
for the site to appropriately manage the stormwater from the
proposed development (before, during, and after construction).

Appropriate barriers and fencing (along the boundary between
the existing caravan park area and the vegetated buffer)
during the construction phase to prevent contaminants
entering the wet heath area;

Appropriate stormwater infrastructure implemented (in
accordance with relevant stormwater plans for the subject
site);

Appropriate litter control measures across the site to prevent
litter and contaminants from the industrial area entering the
wet heath areas;

Appropriate _sediment__and__erosion control __measures

 

 

 

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IMPACT

LEVEL OF
IMPACT

PROPOSED MITIGATION MEASURES

 

Water Quality /
Stormwater

(con't)

implemented during the construction and operational phases;

Appropriate chemical storage implemented during construction
and operational phases (e.g., chemicals stored in designated
bunded areas).

Fertilisers and/or herbicides will be limited to frog-friendly
varieties.

Additional mitigation measures recommended in_ the
stormwater management and water quality plan will further
minimise this potential impact.

Regular monitoring of the water quality of, and quality and
quantity of stormwater run-off into, the wet heath and
vegetated buffer areas will occur during construction and
operational phases.

 

Weed invasion
/ edge effects

High

Prepare an Environmental Management Plan for the pre-,
during, and post-construction phases, which will incorporate
detailed flora management sections, including appropriate
pollutant / chemical management.

Currently the site supports a number of weed species that
have substantial potential as sources for weed invasions into
the remnant wet heath and adjacent Noosa National Park.

Avoid dispersal of weed species from both internal and
external sources by implementing control measures during the
construction phase, such as ensuring all vehicles are cleaned
(i.e., free of contaminants) prior to entering the subject site.

Ensure all removed weeds, weed-affected materials, and
rubbish are appropriately disposed of off-site.

Weed / vegetation disposal shall be undertaken in accordance
with appropriate guidelines outlined by Noosa Shire Council.

Weed removal management will be an integral part of the
site’s vegetation clearing, landscaping, and rehabilitation
works.

Only native and endemic plant species, consistent with
historical and surrounding RE communities, will be planted in
rehabilitation and landscaping works.

Retained vegetation shall be monitored to ensure weed levels
do not increase above an acceptable level.

 

Pest animals

Low

The proposed development is not expected to raise the
number of pest animals present on the site or within the
locality.

No disposal of food on-site during construction or operational
phases will be permitted.

No domestic animals will be allowed on site during
construction or operational phases.

 

Noise

 

 

Moderate

 

Avoid unnecessary noise, as it is a disturbance to fauna.

Minimise construction activities to reasonable daylight hours
(as per Council By-laws).

No night-works will be conducted during the construction
phase.

Prepare a noise report for the site, which makes
recommendations for reducing noise levels during the
construction & operational phases.

 

 

 

June 2007

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Page 44

SCANLON PROPERTY GROUP

 

=

 

 

 

 

 

 

 

 

Ecological Assessment .
a natural solutions
raft Report environmental consultants
LEVEL OF
IMPACT IMPACT PROPOSED MITIGATION MEASURES
Lighting Moderate Additional lighting of the area will result from the proposed
development. However, no night works are expected during
construction phases, which will thereby reduce the necessity
for additional lighting.
Light deflectors will be installed where necessary (e.g., along
the boundary between the development and the vegetated
buffer / Noosa National Park).
Prepare a lighting report, which details mitigation measures for
the impact of development lighting on native fauna.
June 2007

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Page 45

SCANLON PROPERTY GROUP SS

Ecological Assessment "
natural solutions

environmental consultants

Draft Report

9.0 CONCLUSION

The ecological assessment provides an indication of potential environmental constraints and
development opportunities (relating to vegetation and habitat).

It is anticipated that the proposed development within the current caravan park area is
sustainable with the use of certain provisions to protect the ecological and amenity value of the
remnant vegetation on the site and surrounds.

Measures that allow support for development and will protect and improve the ecological and
amenity condition of both the site and the adjacent Noosa National Park are considered
essential to a successful proposal for development of the site. These include:

. Storm-water / nutrient management;
. Rehabilitation;

a Erosion and sediment control; and

. Bushfire management.

It is considered that by incorporating the recommendations outlined in this report, the site’s
ecological values (and those of the adjacent Noosa National Park) will be appropriately
managed/protected.

 

June 2007 ( 40 )

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Page 46

SCANLON PROPERTY GROUP ———

Ecological Assessment Ff
natural solutions

environmental consultants

Draft Report

 

10.0 REFERENCES

C&B Group (2004) Clearing Constraints -— Peregian Beach Caravan Park. Letter to Scanlon
and Tozer Developments Pty Ltd.

C&B Group (2006) Preliminary Ecological Assessment. Report prepared for Scanlon
Developments Pty Ltd.

DEH (2006) EPBC Act Protected Matters Report (24 October 2006).Department of Environment
and Heritage, Canberra.

EPA (2002) Biodiversity Assessment and Mapping Methodology. Environmental Protection
Agency, Brisbane.

EPA (2005a) Southeast Queensland Biodiversity Planning Assessment Version 3.4.
Environmental Protection Agency, Brisbane.

EPA (2005b) Regional Ecosystem Extract: Digital Data, Zone 56 Version 5.0. Environmental
Protection Agency, Brisbane.

EPA (2005c) Wildlife Online Database Extract (24 October 2006). Environmental Protection
Agency, Brisbane.

McFarland, D. (1989) The Ground parrot Pezoporus wallicus wallicus (Kerr) in Queensland:
Habitat, Biology and Conservation. Report prepared for the Division of Conservation, Parks and
Wildlife. Department of Environment and Conservation, Queensland.

Menkhorst, P. & Knight, F. (2001) A Field Guide to the Mammals of Australia. Oxford University
Press, Oxford.

Morcombe, M. (2003) Field Guide to Australian Birds. Steve Parish Publishing Pty Ltd,
Archerfield, Queensland.

Noosa Shire Council (2006) The Noosa Plan. Noosa Shire Council. Available at:
http://www.noosa.qid.gov.au/PlanningDevelopment/PDPublications.shtml#TheNoosaPlan

Queensland Museum (1995) Wildlife of Greater Brisbane. Queensland Museum, Brisbane.
Queensland Museum (2003) Wild Plants of Greater Brisbane. Queensland Museum, Brisbane.

Queensland Parks & Wildlife Service (1999) Management Plan Noosa National Park. The State
of Queensland, Queensland Parks and Wildlife Service.

Wilson, S. (2005) A Field Guide to Reptiles of Queensland. Reed New Holland Publishers Pty
Ltd, Sydney.

 

June 2007 (41)

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Page 47

HATIA PROPERTY CORPORATION SS

Ecological Assessment :
natural solutions

Draft Report environmental consultants

 

APPENDIX A Noosa Plan Local Law No. 10

 

June 2007 (A)

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Page 48

NOOSA SHIRE COUNCIL
LOCAL LAW NO.10 - VEGETATION MANAGEMENT 2003

SUMMARY OF PROVISIONS

PART 1 - PRELIMINARY

AVP Y DY

Short title

Repeal of local law
Objects
Definitions
Application

Subordinate local laws

PART 2 - INTERFERENCE WITH VEGETATION

Division 1 - Prohibition of interference with vegetation

7.
8.

9.

Vegetation to which this local law applies
Requirement to hold permit

Exempt activities

Division 2 - Permits

10.

11.

12.

13.

14,
15.
16.
17.

Types of permits

Application for permit

Consideration of an application for a permit
Timeframe for decisions about permit applications

Refusal of permit
Term of permit
Conditions of permit

Compliance with conditions of a permit

Page 49

ey,

Division 3 - Property vegetation management plans
18. - About property vegetation management plans

19. Compliance with conditions of property vegetation management plan

PART 3- VEGETATION MANAGEMENT ORDERS AND NOTICES

20. Authorised persons

21. Stop order

22. Compliance notice

23. Reinstatement notice

24. The local government's power to have work carried out and recover costs

25. Formula for assessing the value of vegetation

26. Allocation of funds received through contravention of notices or forfeit of security
bonds

PART 4 - INVESTIGATION AND ENFORCEMENT
27. Inspection

28. Suspension or cancellation of a permit

29. No right to compensation

30. .Executive officer liability

31. Liability of third parties

32. Attempts to commit offences :

33. Property vegetation management plan notice provisions

34. Powers of court of conviction for an offence

PART 5 —- REVIEW

35. Reviewable decisions
36. Application for review
37. Carrying out areview _

38. Decision on review

Page 50

PART 6 - MISCELLANIOUS

39. Defence of reasonable excuse

Page 51

PART 1 - PRELIMINARY

Short title
1. This local law may be cited as Local Law No.10 - Vegetation Management 2003.

Repeal of local law
2, This local law repeals Local Law No. 20 Preservation of Trees and Vegetation.
Objects
3. The objects of this local law are to—
(a) _ conserve the shire’s natural resources, including—
(i) land which is of scenic, cultural, historic, educational, recreational, scientific,
environmental, economic, sociological or aesthetic value; and
(ii) soil or landforms such as natural drainage lines, watercourses and foreshores;
and
iii) the quality of the water, land and other natural resources; and
(iv) the extent and condition of bushland, wetlands and all other areas of remnant
vegetation and areas containing vegetation of local origin; and
(b) maintain the biological diversity of fauna and flora, including—
(i) plants and animals and their habitats; and
(ii) wildlife corridors and vegetation links; and
(c) manage activities that may impact upon vegetation so as to minimise the impact on
the shire's natural resources, including—
@) _ the ecological values of water catchment areas; and.
(ii) that part of the environment that may be harmed by vermin, pests, noxious
, plants or hazards: such as fire, development and inappropriate land
management; and
(iii) vistas and the visual identity of the landscape; and
(e) provide the necessary powers to enforce the provisions of this local law; and
(f) provide the necessary powers to require appropriate action to reinstate vegetation
interfered with in contravention of this local law; and

(g) inthe case of urban areas to preserve urban amenity and quality of life.

Page 52

Definitions
4, In this local law—

“authorised person” means a person appointed by the local government to be an authorised

person under this local law.
“category A lots” means freehold lots of 0.3 hectares or less.
“category B lots” means freehold lots of more than 0.3 hectares but less than 2 hectares.
“category C lots” means freehold lots of 2 hectares or more, other than category D lots.

“category D lots” means freehold lots of 2 hectares or more over which a current, agreed

property vegetation management plan exists.
“compliance notice” see section 22.
. “critical habitat” has the meaning used in the Nature Conservation Act 1992.
“development” has the meaning used in the Integrated Planning Act 1997.
“development approval” has the meaning used in the Integrated Planning Act 1997.
“executive officer” of a corporation, means a person who by law is considered to manage the

corporation whether or not that person is a director and regardless of what their position

is called.

“exempt activities” are activities defined in section 9 of this local law.

“exotic origin” means a species occurring in an area outside its historically known natural
range.

“exotic weeds” means a species of plant occurring in an areas outside its historical natural

range and which has negative impacts for the environment or people.

“fire management activities” means the controlled use of fire for pasture management, to
manage the risk of wild fire and to assist with the maintenance of ecological processes in

vegetation communities that are ecologically adapted to fire.

“foreshores” means the land in the shire lying between the high water mark and low water
mark at ordinary spring tides and controlled by the local government pursuant to the Local

Government Act 1993.

Page 53

“heathlands” means vegetation communities of local origin that are characterised by high

species diversity and a canopy height generally less than 1.5 metres, growing on sandy

soils and or soils subject to periodic inundation or waterlogging.

“interference with vegetation” includes destruction of the vegetation or interference with its

natural growth including, but not limited to—

{a)
(b)

(c)
(@

(e)
()
(g)

(h)

@

@)

®)
Y

cutting down; and

cutting or tearing branches, stems or roots, topping, pruning or lopping as per
Australian Standard AS 4373-1996; and

poisoning, including contamination; and

releasing oil, petroleum, paint, cement, mortar or other deleterious substances to a

root zone; and
ringbarking; and
scar barking; and

fixing any object into living tissue or surrounding trunk or branches that may

destroy or seriously affect the vegetation; and

using any tree-climbing spikes in healthy trees that may destroy or seriously affect

the vegetation, other than in accordance with AS 4373-1996; and

damaging a root zone by compaction, excavation or filling that may destroy or

seriously affect the vegetation; and

attaching a guy rope, cable or other contrivance that may destroy or seriously

affect the vegetation; and
uprooting or displacing that may destroy or seriously affect the vegetation; and

engaging in such other activity as may be specified in a subordinate local law that

may destroy or seriously affect the vegetation.

“local origin” means a species naturally occurring in Noosa Shire.

“lopping” has the meaning given in Australian Standard AS 4373-1996.

“Jot” has the meaning used in the Integrated Planning Act 1997.

Page 54

“material environmental harm” has the meaning used in the Environmental Protection Act
1994.

“native forests” means any locally indigenous community, the dominant species of which are
trees, containing throughout its growth—
(a) the complement of native species and habitats normally associated with a forest
type; or
(b) having the potential to develop the characteristics of a forest type; or
(c) forests that have been regenerated with human assistance following disturbance;
but excludes—

(d) plantations of native species; and

(e) previously logged native forest that has been regenerated with non-endemic

species.

“native vegetation” means vegetation of local origin occurring within its natural range.

“natural resources” has the meaning used in the Nature Conservation Act 1992.

“plantation forestry plot” means a forest of native or exotic species, planted or sown using
regular spacing, and managed for timber production and registered with the local
government as a plantation forestry plot and includes roads and other infrastructure

associated with plantation management.

“property maintenance activities” means interference with vegetation that is reasonably
necessary for property maintenance including construction and maintenance of farm
tracks and fences and sheds on site, maintenance of crops, slashing grass, harvesting of
crops, maintenance of pasture and cleared land areas, the pruning, felling and clearing of
orchard vegetation species, surveying purposes, collection of firewood for non
commercial purposes, removal of exotic weeds, and any other maintenance specified in a

property vegetation management plan.

“property vegetation management plan” means a plan that provides a specific program for a
specific lot that when approved, achieves compliance with this local law for the matters dealt

with by the program.

“pruning” has the meaning used in the Australian Standard AS 4373-1996.

Page 55

“rare, vulnerable or endangered wildlife” has the meaning used in the Nature Conservation
Act 1992.

“reasonably necessary” interference with vegetation is only regarded as reasonably
necessary for a particular purpose if there is no alternative way of achieving the purpose
that is prudent and feasible and would avoid the interference with vegetation or

significantly reduce the extent of the interference with vegetation.
“regional ecosystem” has the meaning used in the Vegetation Management Act 1999.
“regrowth” means any vegetation that is less than seven (7) years of age.
“reinstatement notice” see section 23.
“riparian vegetation” includes—

(a) vegetation along foreshores; and

(b) vegetation within:

(@) a permanent freshwater watercourse or existing within 50 metres from the

top of the bank of a permanent freshwater watercourse; or

(ii) a permanent tidal watercourse or existing within 250 metres from the top of

the bank of a permanent tidal watercourse; or

(iit) Lake Macdonald or within 400 metres of the full level of ponded water
within Lake Macdonald.

(iv) vegetation which is found in the riparian zone.

“riparian zone” means land which adjoins, directly influences, or is influenced by a body of

water.

“serious environmental harm” has the meaning used in the Environmental Protection Act

1994.

“subordinate local law” means a law made by a local government about a matter that a local

law expressly states that the local government may make about the matter.

_ “topping” has the meaning used in the Australian Standard AS 4347 - 1996.

Page 56

“vegetation” means trees, plants (including palms) and all other organisms of vegetable
origin (whether living or dead) but does not include declared plants within the meaning of
the Rural Lands Protection Act 1985 or undesirable species as described in a current

landscaping guideline or pest management plan adopted by Noosa Shire Council.
“vermin” has the meaning used in the Queensland Health Regulation 1996.

“watercourse” a river, creek, stream or channel which contains water under normal

conditions.

“wetlands” means an area of permanent or periodic inundation, whether natural or artificial,
static or flowing, fresh, brackish or saline, and includes an area of marine water the depth

of which at low tide is less that 6 metres.

Application

5. This local law applies to all frechold land within the Shire of Noosa.

Subordinate local laws

6.1) The local government may make subordinate local laws about any matters about

which this local law specifically provides for the making of subordinate local laws’.

(2) A subordinate local law must be consistent with the objectives of the local law.

1 See Section 9(2), section 11(1)(1), section 12(2) section 14(2), section 16(3), section 25, section 27(d) and
section 28(2) of this local law.

Page 57

PART 2 - INTERFERENCE WITH VEGETATION
Division 1 - Prohibition of interference with vegetation

Vegetation to which this local law applies
7. This local law applies to—
(a) in category A, B and C lots — all vegetation’.
(b) in category D lots — all vegetation as identified in an approved property

‘management plan’.

Requirement to hold a permit
8. A person must not interfere with vegetation unless—
(a) exempt by this local law’; or
(b) authorised by a permit or property vegetation management plan’.

Maximum penalty—850 penalty units.

Exempt activities
9.(1) Section 8 does not apply to the following exempt activities—
(a) property maintenance activities as defined in this local law®; and

(b) interference with vegetation that is reasonably necessary for emergency access or
works or where the interference with vegetation is immediately required in

response to an accident or emergency; and

g
(c) on category D lots — interference with vegetation in accordance with current,

approved property vegetation management plan’; and

? See section 4 of this local law.

3 See section 4, section 18 and section 19 of this local law.
* See section 9 of this local law.

5 See section 10, section 11 and section 18 of this local law.
® See section 4 of this local law.

7 See section 18 and section 19 of this local law.

Page 58

(d)

(©)

9)

(g)

(h)

interference with vegetation that is reasonably necessary for carrying out work

that is—
(i) authorised or required under an Act or Regulation or local law; or

(ii) specified in a notice served by the local government or another regulatory

authority; and

interference with vegetation in accordance with the conditions of a development

approval issued pursuant to the Integrated Planning Act 1997°; and

on category A lots— interference with vegetation within three (3) metres of an

existing building or structure where the interference is reasonably necessary for

access to the building or structure or has been approved in a landscape plan,

unless the vegetation is otherwise required to be retained in accordance with a

development approval’; and

on category B and C lots— interference with vegetation within ten (10) metres of -
an existing building or structure where the interference is reasonably necessary for

access to the building or structure or has been approved in a landscape plan*®,

unless the vegetation is otherwise required to be retained in accordance with a

development approval’*; and

not withstanding section 9(1)(g), on any category C or D lot greater than ten (10)
hectares in area, interference with vegetation within 30 metres of a building or
within 10 metres of a structure where the interference is reasonably necessary
control of fire risk to the building or structure unless the vegetation is otherwise

required to. be retained in accordance with a development approval; and

interference with vegetation within the path of a utility service; and

8 See section 4 of this local law.
° See section 4 of this local law.
1° See section 4 of this local law.
11 See section 4 of this local law.

Page 59

(Gj) on category A, B and C lots— pruning native vegetation for the purpose of tree
- maintenance or hazard management, where the pruning results in no more than
20% loss of the live canopy volume of a tree within a 12 month period and to

remove any doubt, lopping or topping is not pruning*?; and

(k) on category A, B and C lots— interference with vegetation that is regrowth as

defined by this local law other than—

G@) in areas defined as having significant land slip hazard potential by the Noosa
Shire Council Planning Scheme; and

(ii) rare and threatened flora as defined by the Nature Conservation Regulation
1994 or the Commonwealth Environment Protection and Biodiversity
Conservation Act 1999; and

‘

(iii) heathland and riparian vegetation communities’*; and
(iv) vegetation located in a critical habitat’; and

(v) vegetation that has been cleared in contravention of this local law

subsequent to its enactment; and

(interference with vegetation on those parts of lots designated as Agricultural Land
Conservation Area (ALCA) as defined in the Noosa Shire Planning Scheme; and
(m) fire management activities; and

(n) _ forest practices as defined in the Integrated Planning Act 1997.

(2) A subordinate local law may prescribe other exempt activities.

Division 2 - Permits

Types of permits
10. The local government may issue a permit upon such conditions as it considers appropriate

in the pursuance of this local law.

+? See section 4 of this local law regarding property maintenance activities.
*3 See section 4 of this local law.
4 See section 4 of this local law.

Page 60

Application for permit

11.4) An application for a permit to interfere with vegetation must include or be

accompanied by—

(a) particulars (including drawings) of the location of the land and of the subject
vegetation; and

(b) _ particulars of the type of vegetation; and

(c) particulars of the nature, time and place of the proposed interference; and

(d) _ the extent and duration of the proposed interference, and if the interference is to be
carried out in stages, the extent and duration of each stage; and —

(e) the method of disposal of the vegetation; and

(f) a statement of the reasons why the proposed interference with vegetation is
reasonably necessary; and

(g) in the case of category C lots where the interference is to enable a new agricultural,
pastoral use, or plantation forestry use, demonstration of the practical feasibility of
the proposed use; and

(h) whether the subject vegetation is within the area as defined as riparian vegetation;
and

(i) whether a permit has been issued within the 3 prior years; and

Gj) for category C lots, whether there has been interference with vegetation within the 3
prior years; and

(k) _ ifthe applicant is not the owner, the written consent of the owner; and

() any other information and material required by a subordinate local law.

(2) Within 14 days of receiving the application, the local government may, by written notice,

require the applicant to prepare a property vegetation management plan to support the

application’.

1 See section 18 and section 19 of this local law.

Page 61

Consideration of an application for a permit

12.(1) In making a decision on an application for a permit the local government must

consider the information supplied by the applicant and—

(a) with respect to applications regarding category A lots — whether the vegetation is of

local origin or exotic origin'®; and

(b) with respect to applications regarding any category of lots—

@

Gi)

(iii)

(iv)

()

(vi)

whether the area where interference with vegetation is proposed is within
400 metres of the full level of ponded water within Lake Macdonald;

the risk of erosion and the measures proposed to minimise it; and

whether the proposed interference would be consistent with the objects of
this local law and, if not, whether there would be a fundamental conflict

with the objects; and

the likely environmental impact of the proposed interference with

vegetation; and

documentation containing data about the environmental values of the
vegetation, including whether the vegetation is remnant vegetation of local
origin, classified as remnant ‘of concern’ regional ecosystem or remnant

‘endangered’ regional ecosystem or is vegetation located in a wetland*’; and

documentation containing data about the risk to public safety posed by the

vegetation; and

(vii) natural and cultural heritage values; and

(viii) the potential impacts of interference with the vegetation on water catchment

x)

areas or water quality; and

the environmental significance of the vegetation within its local and .

regional context; and

18 See section 4 of this local law.
17 Remnant ‘of concern’ and ‘endangered regional’ ecosystems are defined under the Vegetation Management

Act 1999.

Page 62

(x) _ the diversity of flora and fauna species supported, or likely to be supported _
by the vegetation; and

(xi) the conservation status of the flora and fauna communities supported by the

vegetation which is to be interfered with; and

(xii) the conservation status of any individual species of flora and fauna
supported or likely to be supported by the vegetation to be interfered with;

and

(xiii) the impacts on other persons or industries reliant on maintaining vegetation;

and

(xiv) if the clearing is to establish fire breaks between bushland and private
buildings, information available to the local government on the fire risk in

the area and any information supplied by the Queensland Fire Services; and
(xv) additional information given or received in relation to the application; and
(xvi) the local government planning scheme; and

(xvii)any proposed property vegetation management plan for the property where

the vegetation is located’®; and
(xviii) any effect of the proposed work on the neighbouring land.

(2)A subordinate local law may specify additional criteria that the local government must

- consider in making a decision.

Time frame for decisions about permit applications
13.(1) The local government's decision on an application for a permit with respect to a
category A lot, must be notified to the applicant in writing within 14 days of the receipt by the

local government of the application.

18 See section 18 and section 19 of this local law.

Page 63

(2) The local government must conduct a site visit within 21 days of the receipt of an
application with respect to a category B or category C lot and within a further 7 days must

either—

(a) provide the applicant with written notice of the local government's decision; or
(b) _ by written notice, request the applicant to submit a property vegetation management
plan to address any relevant matters reasonably required by the local government to

support the application and specified in the written notice.

(3) If the local government requires a property vegetation management plan to be

prepared—

(a) it is not required to consider the application further until a plan has been provided
or the landholder gives written notice of their refusal to submit the property
vegetation management plan;

(b) the landowner has a period of 6 months to prepare and present the plan to the local

government for approval; and

(c) upon receipt of the property vegetation management plan the local government
must provide the applicant with notification of approval or refusal of the

application within 14 days.

(4) The local government has the power to extend the time periods specified in sections
13(1), 13(2) or 13(3) in special circumstances, provided that it gives the applicant written
notice outlining the reason for the extension and the revised timeframe before the relevant

time period expires.

Refusal of permit

14.(1) The local government may refuse an application for a permit—
(a) if the local government considers that it is appropriate to refuse the permit in order to

advance the objectives of this local law’; or

1° See section 3 of this local law.

Page 64

(b) in the case of category B and C lots, if an applicant refuses to submit a property

vegetation management plan.?°

(2) A subordinate local law may specify other circumstances in which the local government

may refuse an application for a permit.

Term of permit

15.(1) A permit commences on the date specified in the permit.

(2) A permit is valid for 6 months for category A and B lots and 12 months for category C

lots.

(3) On category D lots a property vegetation management plan is valid for the period of time

specified in the property vegetation management plan”?.

(4) The local government has the power to extend the time periods specified in section 15(1),

15(2) and 15(3) in special circumstances.

Conditions of permit

16.(1) A permit may be granted subject to reasonable and relevant conditions.

. (2) The conditions of a permit may, for example—

@

(b)

()

(d)
©)

limit authorised operations relating to interference with vegetation to a specified
location or a specified area; and

require the holder to display the permit in a specified position or to produce the
permit for inspection on demand by an authorised person*?; and

require machinery or equipment operators to abide by a specific management plan or
Code of Practice as determined by the chief executive officer or authorised person;
and

require the applicant to comply with a property vegetation management plan**; and
require the applicant to reinstate or rehabilitate areas affected by the authorised

interference with vegetation.

20 See sections 13(2) and 13(3) of this local law.

21 See section 4, section 18 and section 19 of this local law.
22 See section 20 of this local law.

23 See section 19 of this local law.

Page 65

(3) The local government may, by subordinate local law, specify conditions that must be

imposed in a permit or that will ordinarily be imposed in a permit.

Compliance with conditions of a permit

17. The holder of a permit and the owner of land over which a permit has been issued must

ensure compliance with the conditions of a permit.

Maximum penalty—850 penalty units.

Division 3 - Property vegetation management plans

About property vegetation management plans

18.(1) The local government may approve a property vegetation management plan.

(2) A property vegetation management plan is a specific program for a specific lot that when

approved, achieves compliance with this local law for the matters dealt with by the program.

(3) Property vegetation management plans are plans that include—

(a) asite plan for the property which—

(i) _ is to scale, and including the whole lot; and

Gi) includes north point, address and real property description; and

(iii) displays—

(A)

®)
©
(D)
©)
®)

(G)
(H)

)

contours at 30 metre intervals or as available on the local government’s
geographic information system; and

catchment and sub catchment areas; and

watercourses; and

dams; and

areas of vegetation; and

the outline of the property boundaries and all structures on the property
including houses and sheds; and

the location of farm tracks and fences; and

the area of any plantation forestry plot registered with the local
government; and

areas designated for native forest harvesting; and

Page 66

(b)

(0)
(d)
()
(
(g)

(J) any areas where replanting or rehabilitation of native vegetation is to be
undertaken; and

the sequence, timing and pattern of work that will involve interference with
vegetation; and
procedures for interfering with vegetation and disposal of cut vegetation; and
management strategies for controlling declared plants or undesirable species; and
proposals for controlling erosion; and
proposals for protecting riparian zones; and

any other relevant matters reasonably required by the local government.

(4) The local government may also require a property vegetation management plan to display

wetlands.

(5) Property vegetation management plans may be—

(a)

(b)
()

proposed by an applicant for a permit before the local government has made its
decision; or
volunteered by the holder of a permit; or

required by the local government’*.

(6) Property vegetation management plans must be developed in consultation with—

(a)
(b)
©

@

the local government; and

the owner of the property; and

the appropriately qualified resource management agency/department approved by
the local government; and ,

where the local government considers it reasonably necessary, persons the local
government considers to be appropriately qualified to advise on particular issues

specified by the local government.

(7) Property vegetation management plans apply from any date approved by the local

government or other qualified authority and specified in a written notice.

(8) The holder of a property vegetation management plan must comply with the terms of the ©

property vegetation management plan.

(9) Where a property vegetation management plan is to be renewed and alterations are

contemplated, negotiation must be entered into three months before the plan expires.

24 See section 13 of this local law.

Page 67

(10) At the time of transfer of ownership of a property, the local government may agree to the
continuation of the property vegetation management plan.
(11) Where a property vegetation management plan is in existence, the local government will

maintain a record of the existence of the plan on the local government’s property record for the

property.

Compliance with conditions of a property vegetation management plan

19. The holder of a property vegetation management plan and the owner of land over which a
property vegetation management plan has been issued must ensure compliance with the
conditions of a property vegetation management plan.

Maximum-penalty—850 penalty units.

PART 3 —VEGETATION MANAGEMENT ORDERS AND NOTICES

Authorised persons

20.(1) The local government may appoint any of the following persons as authorised
persons for this local law—

(a) employees of the local government;

(b) _ other persons who are eligible for appointment as authorised persons under Chapter
15, part 5 of Local Government Act 1993°°.

(2) An appointment of a person as an authorised person under this part must state the
provisions for which the person is appointed as an authorised person.

(3) A local government may appoint a person as an authorised person under this part
only if the local government considers the person has the necessary expertise or experience
for the appointment.

Stop order
21.(1) An authorised person may verbally or in writing order the person to stop an activity (a
“stop order”) if the person unlawfully interferes with vegetation to which this local law applies.
(2) A person against whom a stop order is made must comply with the order.

Maximum Penalty—S0 penalty units.

28 Chapter 15, part 5 (Enforcement of local government acts) of Local Government Act 1993.

Page 68

Compliance notice

22.(1) An authorised person may give written notice in the form of a “compliance notice”
to any person and the owner of land if a person contravenes or is about to contravene a

provision of this local law or a condition of a permit.
(2) A compliance notice may—
(a) require the person to whom the notice is given to stop the contravention; and

(b) require the person to whom the notice is given to take specific action, within a
time specified in the notice, to remedy the contravention.
(3) A person to whom a compliance notice is given must comply with the compliance
notice.

Maximum Penalty—850 penalty units.

Reinstatement notice

23.(1) An authorised person may give written notice in the form of a “reinstatement
notice” to any person and or the owner of land who the authorised officer suspects on
reasonable grounds is responsible for interference with vegetation in contravention of this

local law.

(2) A reinstatement notice may require that the person to whom the notice is given,

either—

(a) _ take specified action to restore the vegetation or re-establish the vegetation; or
(b) compensate the community for the value of the vegetation as if the value of the

vegetation were a debt.
(3) A reinstatement notice may also require the person to whom the notice is given, to—

(a) make good any environmental damage directly or indirectly resulting from the

interference with the vegetation.

(4) If a reinstatement notice requires the planting of vegetation—
(a) _ the notice must specify the type of vegetation and where it is to be planted and the

period within which it is to be planted; and

Page 69

(b) _ the notice may require the person to undertake—
(@) specified action over a period stated in the notice to nurture the vegetation;
and
Gi) if the vegetation fails to germinate or thrive, further action as directed by an
authorised person; and
(iii) other measures including but not limited to crosion and sediment control.
(5) A person must comply with a reinstatement notice unless the person has a reasonable
excuse for not complying with it.

Maximum penalty—S0 penalty units.

The local government’s power to have work carried out and recover the costs

24. (1) If the person does not comply with a compliance notice or a reinstatement notice,
the local government may take action on any freehold land that the local government
considers reasonably necessary to ensure that the matters mentioned in the notice are
achieved.

(2) To enable action to be taken under subsection (1), the local government may authorise
persons, with or without vehicles, machinery, plant and equipment to enter and stay on any
freehold land.

(3) The local government’s costs of undertaking the work, as certified by the chief
executive officer and including the labour cost of the local government as the chief executive

: ») determines—

(a) are recoverable via the rates from the person to whom the notice was given; and
(b) if the notice was given to the owner or occupier of the land to which the notice
relates, are taken to be costs mentioned in section 1067 (Cost of work recoverable
as arate) of Local Government Act 1993.
(4) The procedure for recovery of costs in this section is in addition to and not in
derogation of any right to costs or compensation available under any other law.
(5) A certificate signed by the chief executive officer and stating any of the following
matters is evidence of—
(a) the carrying out of work by local government;
(b) _ the cost of the work;

Page 70

(c) the value of the lost vegetation calculated by reference to the formula set out in a
subordinate local law;
(d) _ the delivery of the account;

(ec) the amount of any costs and fees unpaid at the date of the certificate.

Formula for assessing the value of vegetation

25. A subordinate local law may prescribe a formula to be used in assessing the value of

vegetation for the purposes of this local law.

Allocation of funds received through contravention of notices or forfeit of security bonds
26. Lf the local government receives funds in accordance with section 24(2) of this local
law, the local government must allocate the money received to the Conservation Levy Fund or

appropriate Bushland Management Fund.

PART 4 - INVESTIGATION AND. ENFORCEMENT
Inspection
27. Ari authorised person may inspect any land”° to which this local law applies, to

determine whether the owner of the land or any permit holder has complied or is
complying with—

(a) the conditions of a permit or a property vegetation management plan; or

(b) astop order; or

(c) . acompliance notice; or

(d) _ the requirements of this local law and any relevant subordinate local laws”’.

Suspension or cancellation of permit
28.(1) The local government may suspend or cancel a permit if—
(a) _ the permit holder has failed to comply with the conditions of a compliance notice or

reinstatement notice; or

26 To enter the premises, the authorised person must comply with Chapter 15, part 5, division 6 of the Local
Government Act 1993.

27 The local government may also institute an approved inspection program under Chapter 15, part 5, division 7
of the Local Government Act 1993

Page 71

(b) the permit was issued because of a materially false or misleading representation or
declaration (made orally or in writing) by or on behalf of the applicant or in support
of the application; or

(c) rare, vulnerable or endangered vegetation or wildlife is discovered within an area to
which the permit applies; or

(d) the carrying out of the work associated with the interference with vegetation is
causing serious or material environmental harm;

(2) A subordinate local law can specify other grounds on which the local government may
suspend or cancel a permit.

(3) The local government may suspend a permit for a period of up to 2 months by giving the
permit holder written notice, in which case the permit is suspended from the time the notice is
received by the permit holder.

(4) Where the local government intends to extend the period of a permit suspension, or cancel
a permit following a period of suspension the local government must—

(a) give the permit holder written notice of the proposed suspension or cancellation and
invite the permit holder to make written representations about the proposed change
within 1 month; and

(b) take the written representations of the permit holder into account; and

(c) give the permit holder written notice of the decision regarding the suspension or
cancellation of the permit within 1 month of receipt of written representations by the

permit holder.

(5) If the permit holder is not notified as required by section 29(4), the proposed

suspension or cancellation will lapse.

No right to compensation
29. No person has the right to claim compensation if the local government or any authorised

person has exercised, in good faith, an authority conferred upon it or him or her by this local law.

Executive officer liability
30.(1) The executive officers of a corporation or company must ensure that the corporation

complies with this local law.

Page 72

(2) If a corporation commits an offence against a provision of this local law, each of the
executive officers of the corporation also commit an offence, namely, the offence of failing to
ensure that the corporation complies with this local law.

Maximum penalty—the penalty for the contravention of the provision by an individual.

(3) Evidence that the corporation has been convicted of an offence against a provision of
this local law is evidence that each of the executive officers committed the offence of failing
to ensure that the corporation complied with this local law.

(4) However, it is a defence for an executive officer to prove that—

(a) they were not in a position to influence the conduct of the corporation in relation

to the offence; and

(b) the executive officer took all reasonable steps to ensure that the corporation

complied with this local law.

Liability of third parties
31.(1) Any person who authorises, undertakes and benefits from a contravention of this
local law commits an offence.
Maximum penalty—the penalty for the contravention of the provision by an individual.
(2) A person is involved in a contravention of this local law if they—
(a) aid, abet, counsel or procure the contravention; or
(b) induce, whether by threats or promises or otherwise, the contravention;
(c) are in any way, directly or indirectly, knowingly concerned in, or party to, the
contravention; or
(d) conspire with others to effect the contravention; or
(e) knowingly benefit from or knowingly were capable of benefiting from the
contravention.
Attempts to commit offences
32.(1) A person who attempts to commit an offence under this local law commits an offence.

Maximum penalty—the maximum penalty for committing the offence

(2) The provisions of the Criminal Code (relevant to attempts to commit offences) apply to

the attempt.

Page 73

Property vegetation management plan notice provisions

33.(1) This section applies if the chief executive officer is of the opinion that—

(a)

(b)

)

@)

(e)

a person has committed an offence against this local law; and

there is sufficient evidence to support the allegation of the offence; and

as soon as reasonably practicable after the circumstances giving rise to the offence
occurred, the person notified particulars of the circumstances to the chief executive
officer; and

after the circumstances giving rise to the offence, the person took all reasonable and
practicable steps to minimise and remedy any adverse environmental effects; and
the person submitted a property vegetation management plan to the local

government for approval.

(2) The chief executive officer may by written notice issue a property vegetation management

plan notice, advising the person that no action will be taken with respect to the offence

provided that—

(a)
(b)

the property vegetation management plan is approved by the local government; and

the person complies with the approved property vegetation management plan.

Powers of court of conviction of an offence

34, If, in a proceeding for an offence against this local law the court finds the defendant

guilty, the court may order the defendant to pay to the local government—

(a)

(b)
(c)

(d)

the local government's reasonable costs and expenses in taking action to remedy
the damage or restore the vegetation; and

the value of the vegetation damaged; and

the fine; and

legal costs and the expenses of the prosecution.

PART 5—REVIEW

Reviewable decisions

35. A decision of the local government or an authorised person under this local law is

reviewable (a “reviewable decision”) unless it is—

(a)

a decision made by resolution of the local government; or

Page 74

(b) adecision made on an earlier application for review.
Application for review

36.(1) A person who is aggrieved by a reviewable decision may apply to the local

government for a review of the decision.
(2) An application for review of a reviewable decision must—
(a) be in writing; and
(b) _ state the reasons why the applicant considers the decision should be reviewed; and

(c) be lodged at the office of the local government within 21 days after the day on
which notice of the decision was given to the applicant or within a further period

allowed by the local government (before or after the end of that period).
Carrying out a review
37.(1) The local government must either—
(a) carry out a review at'a meeting of the local government; or
(b) have the review carried out by an authorised person.

(2) An authorised person who carries out a.review under subsection 38 (1)(b) must not be
the original decision maker and must be a person who is no less senior than the original

decision maker.
Decision on review

- 38.41) On completing a review, the local government may confirm, vary or reverse the

decision under review.

(2) The local government must give the applicant written notice of the result of the review -

within 40 days.

(3) The local government has the power to extend the time period specified in section
39(2) in special circumstances, provided that it gives the applicant a written notice outlining
the reason for the extension and the revised time frame before the relevant time period

expires.

Page 75

PART 6—MISCELLANEOUS
_ Defence of reasonable excuse

39. If a person is charged with an offence involving a contravention of a provision of this
local law, it is a defence to prove that the person had a reasonable and lawful excuse for the

contravention.

Page 76

HATIA PROPERTY CORPORATION S

Ecological Assessment .
natural solutions

environmental consultants

Draft Report

 

APPENDIX B EPBC Protected Matters Report

 

June 2007 (B)

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EPBC Act Protected Matters Report Page | of 14

 

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EPBC Act Protected Matters 2 May 2007 13:41
Report

This report provides general guidance on matters of national environmental significance and other
matters protected by the EPBC Act in the area you have selected. Information on the coverage of
this report and qualifications on data supporting this report are contained in the caveat at the end of
the report.

You may wish to print this report for reference before moving to other pages or websites.

The Australian Natural Resources Atlas at http://www.environment.gov.au/atlas may provide
further environmental information relevant to your selected area. Information about the EPBC Act
including significance guidelines, forms and application process details can be found at
http://www.environment.gov.au/epbc/assessmentsapprovals/index.html

 

 

 

 

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Report Contents: Summary
Details
e Matters of NES
e Other matters protected by the EPBC Act

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EPBC Act Protected Matters Report Page 2 of 14

e Extra Information
Caveat
Acknowledgments

 

Summary

Matters of National Environmental Significance

This part of the report summarises the matters of national environmental significance that may
occur in, or may relate to, the area you nominated. Further information is available in the detail part
of the report, which can be accessed by scrolling or following the links below. If you are proposing
to undertake an activity that may have a significant impact on one or more matters of national
environmental significance then you should consider the Administrative Guidelines on Significance
- see http://www.environment.gov.au/epbc/assessmentsapprovals/guidelines/index.html.

World Heritage Properties: None
National Heritage Places: None
Wetlands of International Significance: Z
(Ramsar Sites)

Commonwealth Marine Areas: Relevant
Threatened Ecological Communities: None
Threatened Species: 36
Migratory Species: 39

Other Matters Protected by the EPBC Act

This part of the report summarises other matters protected under the Act that may relate to the area
you nominated. Approval may be required for a proposed activity that significantly affects the
environment on Commonwealth land, when the action is outside the Commonwealth land, or the
environment anywhere when the action is taken on Commonwealth land. Approval may also be
required for the Commonwealth or Commonwealth agencies proposing to take an action that is
likely to have a significant impact on the environment anywhere.

The EPBC Act protects the environment on Commonwealth land, the environment from the actions
taken on Commonwealth land, and the environment from actions taken by Commonwealth
agencies. As heritage values of a place are part of the 'environment'’, these aspects of the EPBC Act
protect the Commonwealth Heritage values of a Commonwealth Heritage place and the heritage
values of a place on the Register of the National Estate. Information on the new heritage laws can
be found at http://www.environment.gov.au/heritage/index.html.

Please note that the current dataset on Commonwealth land is not complete. Further information on
Commonwealth land would need to be obtained from relevant sources including Commonwealth
agencies, local agencies, and land tenure maps.

A permit may be required for activities in or on a Commonwealth area that may affect a member of
a listed threatened species or ecological community, a member of a listed migratory species, whales

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EPBC Act Protected Matters Report Page 3 of 14

and other cetaceans, or a member of a listed marine species. Information on EPBC Act permit
requirements and application forms can be found at
http://www.environment.gov.au/epbc/permits/index.html.

Commonwealth Lands: None
Commonwealth Heritage Places: None
Places on the RNE: 2
Listed Marine Species: 66
Whales and Other Cetaceans: 14
Critical Habitats: None
Commonwealth Reserves: None

Extra Information

This part of the report provides information that may also be relevant to the area you have
nominated.

 

State and Territory Reserves: 2
Other Commonwealth Reserves: None
Regional Forest Agreements: 1
Details

Matters of National Environmental Significance

Wetlands of International Significance [| Dataset Information ]
(Ramsar Sites)

GREAT SANDY STRAIT Within same catchment as Ramsar site
MORETON BAY Within same catchment as Ramsar site
Commonwealth Marine Areas [ Dataset Information ]

Approval may be required for a proposed activity that is likely to have a significant impact on the
environment in a Commonwealth Marine Area, when the action is outside the Commonwealth
Marine Area, or the environment anywhere when the action is taken within the Commonwealth
Marine Area. Generally the Commonwealth Marine Area stretches from three nautical miles to two
hundred nautical miles from the coast.

Within 3 Nautical Mile Limit

Threatened Species [ Dataset Information ] Status Type of Presence

Birds

Cyclopsitta diophthalma coxeni* Endangered Species or species habitat likely to
Coxen's Fig-Parrot occur within area

Diomedea dabbenena * Endangered Foraging may occur within area

Tristan Albatross

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EPBC Act Protected Matters Report

Erythrotriorchis radiatus *
Red Goshawk

Lathamus discolor *
Swift Parrot

Macronectes giganteus *
Southern Giant-Petrel

Macronectes halli *
Northern Giant-Petrel

Pterodroma neglecta neglecta*
Kermadec Petrel (western)

Rostratula australis *
Australian Painted Snipe

Thalassarche impavida *
Campbell Albatross

Turnix melanogaster *
Black-breasted Button-quail

Xanthomyza phrygia *
Regent Honeyeater

Frogs

Litoria olongburensis *
Wallum Sedge Frog

Mixophyes iteratus *
Southern Barred Frog, Giant Barred Frog

Mammals

Balaenoptera musculus *
Blue Whale

Chalinolobus dwyeri *
Large-eared Pied Bat, Large Pied Bat

Dasyurus maculatus maculatus (SE mainland
population)*

Spot-tailed Quoll, Spotted-tail Quoll, Tiger
Quoll (southeastern mainland population)

Eubalaena australis *
Southern Right Whale

Megaptera novaeangliae *
Humpback Whale

Potorous tridactylus tridactylus*
Long-nosed Potoroo (SE mainland)

Pteropus poliocephalus *
Grey-headed Flying-fox

Xeromys myoides *
Water Mouse, False Water Rat

Ray-finned fishes

Nannoperca oxleyana *

Page 4 of 14

Vulnerable Species or species habitat likely to
occur within area

Endangered Species or species habitat may occur
within area

Endangered Species or species habitat may occur
within area

Vulnerable Species or species habitat may occur
within area

Vulnerable Species or species habitat may occur
within area

Vulnerable Species or species habitat may occur
within area

Vulnerable Species or species habitat may occur
within area

Vulnerable Species or species habitat likely to
occur within area

Endangered Species or species habitat may occur
within area

Vulnerable Species or species habitat likely to
occur within area

Endangered Species or species habitat likely to
occur within area

Endangered Species or species habitat may occur
within area

Vulnerable Species or species habitat may occur
within area

Endangered Species or species habitat may occur
within area

Endangered Species or species habitat likely to
occur within area

Vulnerable Breeding known to occur within area

Vulnerable Species or species habitat may occur
within area

Vulnerable Species or species habitat likely to
occur within area

Vulnerable Species or species habitat likely to
occur within area

Endangered Species or species habitat likely to

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EPBC Act Protected Matters Report

Oxleyan Pygmy Perch

Pseudomugil mellis *
Honey Blue-eye

Reptiles

Caretta caretta *
Loggerhead Turtle

Chelonia mydas *
Green Turtle

Coeranoscincus reticulatus *
Three-toed Snake-tooth Skink

Dermochelys coriacea *
Leathery Turtle, Leatherback Turtle, Luth

Lepidochelys olivacea *
Pacific Ridley, Olive Ridley

Sharks

Carcharias taurus (east coast population)*
Grey Nurse Shark (east coast population)

Rhincodon typus *
Whale Shark

Plants

Allocasuarina emuina *
Emu Mountain Sheoak

Bulbophyllum globuliforme *
Miniature Moss-orchid

Cryptocarya foetida *
Stinking Cryptocarya, Stinking Laurel

Eucalyptus conglomerata *
Swamp Stringybark

Phaius australis *
Lesser Swamp-orchid

Prasophyllum wallum *

Migratory Species [ Dataset Information ]
Migratory Terrestrial Species
Birds

Cyclopsitta diophthalma coxeni*
Coxen's Fig-Parrot

Haliaeetus leucogaster
White-bellied Sea-Eagle

Hirundapus caudacutus
White-throated Needletail

Merops ornatus *
Rainbow Bee-eater

file://Y:\JO7\JO7-049_215-219 David Low Way,Peregian\Project Data\Background\E...

Vulnerable

Endangered

Vulnerable

Vulnerable

Vulnerable

Endangered

Critically
Endangered

Vulnerable

Endangered
Vulnerable
Vulnerable
Endangered
Endangered
Vulnerable

Status

Migratory

Migratory

Migratory

Migratory

Page 5 of 14

occur within area

Species or species habitat likely to
occur within area

Breeding may occur within area

Species or species habitat may occur
within area

Species or species habitat may occur
within area

Species or species habitat may occur
within area

Species or species habitat may occur
within area

Species or species habitat may occur
within area

Species or species habitat may occur
within area

Species or species habitat likely to
occur within area

Species or species habitat likely to
occur within area

Species or species habitat likely to
occur within area

Species or species habitat likely to
occur within area

Species or species habitat likely to
occur within area

Species or species habitat likely to
occur within area

Type of Presence

Species or species habitat likely to
occur within area

Species or species habitat likely to
occur within area

Species or species habitat may occur
within area

Species or species habitat may occur
within area

17/05/2007

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EPBC Act Protected Matters Report

Monarcha melanopsis
Black-faced Monarch

Monarcha trivirgatus
Spectacled Monarch

Myiagra cyanoleuca
Satin Flycatcher

Rhipidura rufifrons
Rufous Fantail

Xanthomyza phrygia
Regent Honeyeater

Migratory Wetland Species
Birds

Ardea alba
Great Egret, White Egret

Ardea ibis
Cattle Egret

Gallinago hardwickii *
Latham's Snipe, Japanese Snipe

Nettapus coromandelianus albipennis
Australian Cotton Pygmy-goose

Rostratula benghalensis s. lat.
Painted Snipe

Migratory Marine Birds

Apus pacificus
Fork-tailed Swift

Ardea alba
Great Egret, White Egret

Ardea ibis
Cattle Egret

Calonectris leucomelas
Streaked Shearwater

Diomedea dabbenena
Tristan Albatross

Macronectes giganteus
Southern Giant-Petrel

Macronectes halli
Northern Giant-Petrel

Puffinus leucomelas
Streaked Shearwater

Sterna albifrons
Little Tern

Thalassarche chlororhynchos

Yellow-nosed Albatross, Atlantic Yellow-

nosed Albatross

Migratory
Migratory
Migratory
Migratory

Migratory

Migratory
Migratory
Migratory
Migratory

Migratory

Migratory
Migratory
Migratory
Migratory
Migratory
Migratory
Migratory
Migratory
Migratory

Migratory

Page 6 of 14

Breeding may occur within area
Breeding likely to occur within area
Breeding likely to occur within area
Breeding may occur within area

Species or species habitat may occur
within area

Species or species habitat may occur
within area

Species or species habitat may occur
within area

Species or species habitat may occur
within area

Species or species habitat may occur
within area

Species or species habitat may occur
within area

Species or species habitat may occur
within area

Species or species habitat may occur
within area

Species or species habitat may occur
within area

Species or species habitat may occur
within area

Foraging may occur within area

Species or species habitat may occur
within area

Species or species habitat may occur
within area
Species or species habitat may occur
within area
Species or species habitat may occur
within area

Species or species habitat may occur
within area

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EPBC Act Protected Matters Report

Thalassarche impavida
Campbell Albatross

Migratory Marine Species
Mammals

Balaenoptera edeni
Bryde's Whale

Balaenoptera musculus *
Blue Whale

Dugong dugon
Dugong

Eubalaena australis *
Southern Right Whale

Lagenorhynchus obscurus
Dusky Dolphin

Megaptera novaeangliae *
Humpback Whale

Orcaella brevirostris
Irrawaddy Dolphin

Orcinus orca
Killer Whale, Orca

Sousa chinensis
Indo-Pacific Humpback Dolphin

Reptiles

Caretta caretta *
Loggerhead Turtle

Chelonia mydas *
Green Turtle

Dermochelys coriacea *
Leathery Turtle, Leatherback Turtle, Luth

Lepidochelys olivacea *
Pacific Ridley, Olive Ridley

Sharks

Rhincodon typus
Whale Shark

Migratory

Migratory
Migratory
Migratory
Migratory
Migratory
Migratory
Migratory
Migratory

Migratory

Migratory
Migratory
Migratory

Migratory

Migratory

Page 7 of 14

Species or species habitat may occur
within area

Species or species habitat may occur
within area

Species or species habitat may occur
within area

Species or species habitat likely to
occur within area

Species or species habitat likely to
occur within area

Species or species habitat may occur
within area

Breeding known to occur within area

Species or species habitat may occur
within area

Species or species habitat may occur
within area

Species or species habitat may occur
within area

Breeding may occur within area

Species or species habitat may occur
within area

Species or species habitat may occur
within area

Species or species habitat may occur
within area

Species or species habitat may occur
within area

Other Matters Protected by the EPBC Act

Listed Marine Species [ Dataset Information ]

Birds

Anseranas semipalmata
Magpie Goose

Apus pacificus

file://Y:\JO7\JO7-049_215-219 David Low Way,Peregian\Project Data\Background\E...

Status

Listed -
overfly
marine
area

Listed -

Type of Presence

Species or species habitat may occur
within area

Species or species habitat may occur

17/05/2007

Page 84

EPBC Act Protected Matters Report

Fork-tailed Swift

Ardea alba
Great Egret, White Egret

Ardea ibis
Cattle Egret

Calonectris leacomelas
Streaked Shearwater

Catharacta skua
Great Skua

Diomedea dabbenena
Tristan Albatross

Gallinago hardwickii.*
Latham's Snipe, Japanese Snipe

Haliaeetus leucogaster
White-bellied Sea-Eagle

Hirundapus caudacutus
White-throated Needletail

Lathamus discolor *
Swift Parrot

Macronectes giganteus
Southern Giant-Petrel

Macronectes halli
Northern Giant-Petrel

Merops ornatus *
Rainbow Bee-eater

Monarcha melanopsis
Black-faced Monarch

Monarcha trivirgatus
Spectacled Monarch

overfly
marine
area

Listed -
overfly
marine
area

Listed -
overfly
marine
area

Listed
Listed
Listed

Listed -
overfly
marine
area

Listed

Listed -
overfly
marine
area

Listed -
overfly
marine
area

Listed
Listed

Listed -
overfly
marine
area

Listed -
overfly
marine
area

Listed -
overfly
marine
area

Page 8 of 14

within area

Species or species habitat may occur
within area

Species or species habitat may occur
within area

Species or species habitat may occur
within area

Species or species habitat may occur
within area

Foraging may occur within area

Species or species habitat may occur
within area

Species or species habitat likely to
occur within area

Species or species habitat may occur
within area

Species or species habitat may occur
within area

Species or species habitat may occur
within area

Species or species habitat may occur
within area

Species or species habitat may occur
within area

Breeding may occur within area

Breeding likely to occur within area

file://Y:\JO7\JO7-049_215-219 David Low Way,Peregian\Project Data\Background\E..._ 17/05/2007

Page 85

EPBC Act Protected Matters Report

Myiagra cyanoleuca
Satin Flycatcher

Nettapus coromandelianus albipennis
Australian Cotton Pygmy-goose

Rhipidura rufifrons
Rufous Fantail

Rostratula benghalensis s. lat.
Painted Snipe

Sterna albifrons
Little Tern

Thalassarche chlororhynchos
Yellow-nosed Albatross, Atlantic Yellow-nosed
Albatross

Thalassarche impavida
Campbell Albatross

Mammals

Dugong dugon

Dugong

Ray-finned fishes

Acentronura tentaculata

Hairy Pygmy Pipehorse

Campichthys tryoni

Tryon's Pipefish

Corythoichthys amplexus

Fijian Banded Pipefish, Brown-banded Pipefish

Corythoichthys ocellatus
Orange-spotted Pipefish, Ocellated Pipefish

Festucalex cinctus
Girdled Pipefish

Filicampus tigris

Tiger Pipefish

Halicampus grayi

Mud Pipefish, Gray's Pipefish

Hippichthys cyanospilos

Blue-speckled Pipefish, Blue-spotted Pipefish
Hippichthys heptagonus

Madura Pipefish, Reticulated Freshwater
Pipefish

Listed -
overfly
marine

area

Listed -
overfly
marine

area

Listed -
overfly
marine

area

Listed -
overfly
marine
area
Listed

Listed

Listed

Listed

Listed
Listed
Listed
Listed
Listed
Listed
Listed
Listed

Listed

Page 9 of 14

Breeding likely to occur within area

Species or species habitat may occur
within area

Breeding may occur within area

Species or species habitat may occur
within area

Species or species habitat may occur
within area

Species or species habitat may occur
within area

Species or species habitat may occur
within area

Species or species habitat likely to
occur within area

Species or species habitat may occur
within area

Species or species habitat may occur
within area
Species or species habitat may occur
within area

Species or species habitat may occur
within area

Species or species habitat may occur
within area

Species or species habitat may occur
within area

Species or species habitat may occur
within area

Species or species habitat may occur
within area

Species or species habitat may occur
within area

file://Y :\JO7\JO7-049_215-219 David Low Way,Peregian\Project Data\Background\E...__ 17/05/2007

Page 86

EPBC Act Protected Matters Report

Hippichthys penicillus
Beady Pipefish, Steep-nosed Pipefish

Hippocampus kelloggi
Kellogg's Seahorse

Hippocampus kuda
Spotted Seahorse, Yellow Seahorse

Hippocampus planifrons
Flat-face Seahorse

Hippocampus whitei
White's Seahorse, Crowned Seahorse, Sydney
Seahorse

Lissocampus runa
Javelin Pipefish

Maroubra perserrata
Sawtooth Pipefish

Micrognathus andersonii
Anderson's Pipefish, Shortnose Pipefish

Micrognathus brevirostris
Thorn-tailed Pipefish

Microphis manadensis
Manado River Pipefish, Manado Pipefish

Solegnathus dunckeri
Duncker's Pipehorse

Solegnathus hardwickii
Pipehorse

Solegnathus spinosissimus
Spiny Pipehorse, Australian Spiny Pipehorse

Solenostomus cyanopterus
Blue-finned Ghost Pipefish, Robust Ghost
Pipefish

Solenostomus paradoxus

Harlequin Ghost Pipefish, Ornate Ghost Pipefish

Stigmatopora nigra
Wide-bodied Pipefish, Black Pipefish

Syngnathoides biaculeatus
Double-ended Pipehorse, Alligator Pipefish

Trachyrhamphus bicoarctatus
Bend Stick Pipefish, Short-tailed Pipefish

Urocampus carinirostris
Hairy Pipefish

Vanacampus margaritifer
Mother-of-pearl Pipefish

Reptiles

Acalyptophis peronii
Horned Seasnake

Listed

Listed

Listed

Listed

Listed

Listed

Listed

Listed

Listed

Listed

Listed

Listed

Listed

Listed

Listed

Listed

Listed

Listed

Listed

Listed

Listed

Page 10 of 14

Species or species habitat may occur
within area

Species or species habitat may occur
within area

Species or species habitat may occur
within area

Species or species habitat may occur
within area

Species or species habitat may occur
within area

Species or species habitat may occur
within area

Species or species habitat may occur
within area

Species or species habitat may occur
within area

Species or species habitat may occur
within area

Species or species habitat may occur
within area

Species or species habitat may occur
within area

Species or species habitat may occur
within area

Species or species habitat may occur
within area

Species or species habitat may occur
within area

Species or species habitat may occur
within area

Species or species habitat may occur
within area

Species or species habitat may occur
within area

Species or species habitat may occur
within area

Species or species habitat may occur
within area

Species or species habitat may occur
within area

Species or species habitat may occur
within area

file://Y:\JO7\JO7-049_215-219 David Low Way,Peregian\Project Data\Background\E... 17/05/2007

Page 87

EPBC Act Protected Matters Report

Aipysurus laevis
Olive Seasnake

Astrotia stokesii
Stokes' Seasnake

Caretta caretta *
Loggerhead Turtle

Chelonia mydas *
Green Turtle

Dermochelys coriacea *

Leathery Turtle, Leatherback Turtle, Luth
Disteira kingii

Spectacled Seasnake

Disteira major
Olive-headed Seasnake

Emydocephalus annulatus
Turtle-headed Seasnake

Hydrophis elegans
Elegant Seasnake

Laticauda laticaudata
a sea krait

Lepidochelys olivacea *
Pacific Ridley, Olive Ridley

Pelamis platurus
Yellow-bellied Seasnake

Whales and Other Cetaceans [ Dataset
Information ]

Balaenoptera acutorostrata
Minke Whale

Balaenoptera edeni
Bryde's Whale

Balaenoptera musculus *
Blue Whale

Delphinus delphis
Common Dolphin

Eubalaena australis *
Southern Right Whale

Grampus griseus

Risso's Dolphin, Grampus
Lagenorhynchus obscurus
Dusky Dolphin

Megaptera novaeangliae *
Humpback Whale

Orcaella brevirostris
Irrawaddy Dolphin

file://Y :\JO7\JO7-049_ 215-219 David Low Way,Peregian\Project Data\Background\E...

Listed

Listed

Listed

Listed

Listed

Listed

Listed

Listed

Listed

Listed

Listed

Listed

Status

Cetacean

Cetacean

Cetacean

Cetacean

Cetacean

Cetacean

Cetacean

Cetacean

Cetacean

Page 11 of 14

Species or species habitat may occur
within area

Species or species habitat may occur
within area

Breeding may occur within area

Species or species habitat may occur
within area

Species or species habitat may occur
within area

Species or species habitat may occur
within area

Species or species habitat may occur
within area

Species or species habitat may occur
within area

Species or species habitat may occur
within area

Species or species habitat may occur
within area

Species or species habitat may occur
within area

Species or species habitat may occur
within area

Type of Presence

Species or species habitat may occur
within area

Species or species habitat may occur
within area

Species or species habitat may occur
within area

Species or species habitat may occur
within area

Species or species habitat likely to
occur within area

Species or species habitat may occur
within area

Species or species habitat may occur
within area

Breeding known to occur within area

Species or species habitat may occur
within area

17/05/2007

Page 88

EPBC Act Protected Matters Report Page 12 of 14

Orcinus orca Cetacean Species or species habitat may occur
Killer Whale, Orca within area

Sousa chinensis Cetacean Species or species habitat may occur
Indo-Pacific Humpback Dolphin within area

Stenella attenuata Cetacean Species or species habitat may occur
Spotted Dolphin, Pantropical Spotted Dolphin within area

Tursiops aduncus Cetacean Species or species habitat likely to
Spotted Bottlenose Dolphin occur within area

Tursiops truncatus Ss. str. Cetacean Species or species habitat may occur
Bottlenose Dolphin within area

Places on the RNE [ Dataset Information ]
Note that not all Indigenous sites may be listed.

Natural
Noosa - Maroochy Wallum Area QLD
Peregian Environmental Park QLD

Extra Information

State and Territory Reserves [ Dataset Information ]
Noosa National Park, QLD
Noosa River Fish Habitat Area, QLD

Regional Forest Agreements [ Dataset Information |
Note that all RFA areas including those still under consideration have been included.

South East Queensland RFA, Queensland

 

Caveat

The information presented in this report has been provided by a range of data sources as
acknowledged at the end of the report.

This report is designed to assist in identifying the locations of places which may be relevant in
determining obligations under the Environment Protection and Biodiversity Conservation Act 1999.
It holds mapped locations of World Heritage and Register of National Estate properties, Wetlands of
International Importance, Commonwealth and State/Territory reserves, listed threatened, migratory
and marine species and listed threatened ecological communities. Mapping of Commonwealth land
is not complete at this stage. Maps have been collated from a range of sources at various resolutions.

Not all species listed under the EPBC Act have been mapped (see below) and therefore a report is a
general guide only. Where available data supports mapping, the type of presence that can be
determined from the data is indicated in general terms. People using this information in making a
referral may need to consider the qualifications below and may need to seek and consider other
information sources.

For threatened ecological communities where the distribution is well known, maps are derived from
recovery plans, State vegetation maps, remote sensing imagery and other sources. Where threatened

file://Y:\JO7\JO7-049_215-219 David Low Way,Peregian\Project Data\Background\E... 17/05/2007

Page 89

EPBC Act Protected Matters Report Page 13 of 14

ecological community distributions are less well known, existing vegetation maps and point location
data are used to produce indicative distribution maps.

For species where the distributions are well known, maps are digitised from sources such as recovery
plans and detailed habitat studies. Where appropriate, core breeding, foraging and roosting areas are
indicated under "type of presence". For species whose distributions are less well known, point
locations are collated from government wildlife authorities, museums, and non-government
organisations; bioclimatic distribution models are generated and these validated by experts. In some
cases, the distribution maps are based solely on expert knowledge.

Only selected species covered by the migratory and marine provisions of the Act have been mapped.

The following species and ecological communities have not been mapped and do not appear in
reports produced from this database:

threatened species listed as extinct or considered as vagrants

some species and ecological communities that have only recently been listed

some terrestrial species that overfly the Commonwealth marine area

migratory species that are very widespread, vagrant, or only occur in small numbers.

The following groups have been mapped, but may not cover the complete distribution of the species:

e non-threatened seabirds which have only been mapped for recorded breeding sites;
e seals which have only been mapped for breeding sites near the Australian continent.

Such breeding sites may be important for the protection of the Commonwealth Marine environment.

Acknowledgments

This database has been compiled from a range of data sources. The Department acknowledges the
following custodians who have contributed valuable data and advice:

New South Wales National Parks and Wildlife Service

Department of Sustainability and Environment, Victoria

Department of Primary Industries, Water and Environment, Tasmania
Department of Environment and Heritage, South Australia Planning SA
Parks and Wildlife Commission of the Northern Territory
Environmental Protection Agency, Queensland

Birds Australia

Australian Bird and Bat Banding Scheme

Australian National Wildlife Collection

Natural history museums of Australia

Queensland Herbarium

National Herbarium of NSW

Royal Botanic Gardens and National Herbarium of Victoria
Tasmanian Herbarium

State Herbarium of South Australia

Northern Territory Herbarium

Western Australian Herbarium

Australian National Herbarium, Atherton and Canberra

University of New England

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EPBC Act Protected Matters Report Page 14 of 14

e Other groups and individuals
ANUCIIM Version 1.8, Centre for Resource and Environmental Studies, Australian National
University was used extensively for the production of draft maps of species distribution.
Environment Australia is extremely grateful to the many organisations and individuals who provided
expert advice and information on numerous draft distributions.

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© Commonwealth of Australia 2004

file://Y :\JO7\JO7-049_215-219 David Low Way,Peregian\Project Data\Background\E... 17/05/2007

Page 91

HATIA PROPERTY CORPORATION =a

Ecological Assessment 5
natural solutions

environmental consultants

Draft Report

 

APPENDIX C Wildlife Online Report

 

June 2007 (Cc)

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S 9 04096 J@AJ9A SuNeNse7 junanse einpaC eepluoyyey sojdes. = syewue
€ 9 oyoeb JeA/eA peyods Wetjnos luo] BINDaOQ aepluoy}ay, sjewlue
1 ‘ds einpeO eepluoyyeay soindel spewlue
6 5 eyeus poAe-ljewus Wiejseo suaosasbju snjeydacojdoulyy eepide|y sede:  — sjeujue
L 9 eyeus yoR|q porleq-pa. snoeuydiod siyoapnasg sander spewiue
€ 9 eyeus UMOIg We}sea sxe] efeuopnasd sayde. = syewjue
I 9 @BUS PBUMOO-3]YUM eeyauuey siydooe9 sede: = sjewue
Z 9 ayeus 88) UOWULUOD Beinjound sjydejespueq eepuqnjod sande sjewlue
z 9 ayeus Jeyemysey jujeut siydouopidoly eepuqnjoD soldei sjewjue
I 9 eyeUs 991] UMOIG suenbaiy eBlog eepuqnjog | spewue
L gq 3 atm, peeysebbo| Byereo Byaleg eeplluojEUD solide syewlue
L ao 9 Bsojnoew eIsalejuy eepiog sande syewlue
v 9 uoujAd yedseo Bjojids Byal0yy eepiog sojndes sfewlue
z 9 , syeasne e1oyduodiq eepiwueby solndes syeujue
I 9 iqqou !gqou iqqou sninjoqiyduiy eepiueby sejydes sjewiue
z 9 uoBelp sayem Useyse0 Junensa; snyyeubishyd eepilueby sender sjpewlue
s08y OGd4a VON WEN UO. .0D OWE, dIpUaIOS Ajjwe4 ssejg wophury

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v 9 soeshyeid yyeey sapiooue aoeshyed eeeoeldy — sjoolp seupiy sjue|d
z 9 BejosouE! eoeshleid eesoeldy — sjoalp 18yBIYy sjueid
L winjAydojde; wnuuedsojoh5 eeeovldy — sjoolp seusiy sjued
Zz 9 uwunjejsoid JeA wnjeysoid wnidy epeoridy s}ooip 194614 sjueid
Z 9 Bsjoul ‘dsqns esjoul auawAYyoes, eesoeidy = sjoolp seyBiy sjue|d
v 9 ByoeaUl, BOSAL} eeeoeldy — sjoalp zay6iy sjueid
I 9 esopnyjed afAjoa01pAH eeeoeldy — sjoalp ueybiy sjueid
© 9 BoneIse ea]UaD” eeeoridy — sjooip soupy sjueid
L 9 uwinjgejsoid winidy eeeoridy — sjoalp sey by sjuejd
© snyopiyjuigee] SNulYyos eeeoripieoeuy — sjoaip JeyBiy sjue|d
1 9 peemAo Jassa| Byejnojuap. e/ayjUBUIayYy eesoeyjuBeWY = sjoolp sayBIYy sjue|d
I euelyisesg BlayjueWayy eesoeyjuBeWY = soap sayBiy sjue|d
L 9 yoeuids puejesZz MeN sepiojuobeje}] euobeNe |, eeeoeoziy — s}oalp JeyBiy sjue|d
z 3 soes6id suaasaone|b snjoiqgodieg eeeoeoziy  — sjoolp JeyBiy sjued
L 3° Bioyoids Byeluourg eeeoeyjueoy — sjooip sayBiy sjuejd
v 9 snjdnuejul snosojoAg eesoepHaydAjous SUJO} sjueid
L 9 Way yaoI0 Bjejuap eyajsuyD = =—- eBaoepUA\dAjoUs Sule} sjueid
Z 9 Ula} oyeus winyjAydosojur winipoBAT aesoeeeziyoS SUJa} sjue|d
© 9 UJ8} QUOD peyouersq BWO}OYoIp BeeZIYOS aeaoeeezIyoS SUIa} sued
€ 9 Us2} QUOD payJo} epyig eaezIYaS aeeoeeRZIYOS SUJO} sjue|d
L Blulajes BISEjOW! BIUIAES aReoelUlAleS SUJO} sjuejd
k 3 usa} eaosBuew winsojvads wnyonsoiny BeBOePHA}q SUJO} sjuejd
z 9 uingeoingig winaohyeld aeooelpodsjog SUJO} sjue|d
L 9 : Binpi6u eueucsiq aesoeipodéjog SUJO} sjue|d
I 9 ue} Bury eleqieg BapoL eeeoepUuNUisc, SUJ9} sjue|d
L 2 BIBsayjgo sidejosydeyy §=— aeaoepidajoiyden SUJO} sjue|d
z 3 use} suOgysy Byoypioo sidajoiydayy = aeaoepidajoiydey SUI2} sjue|d
L 9 Bininsury sidajoiydayy = aeaoepidejosydeny SUJO} sjuejd
L 9 ule} Melos SUBAUI] BOCSPUIT eeeoreespur] SUIO} sjue|d
rd 9 BYOsISUE PERSPUIT eesoverspur] SUJO} sjue|d
I 9 BYydioulp eeespulT eesoreespur] SUl2} sjue|d
L 9 ue} eBpem Ade] eyAydosoiw BaespulT eesoverespur] SUJd} sjuejd
zZ 9 Byoyisua ‘dsqns eljojisue eaespulT eesoreespur] SUJ2} sjue|d
@ 9 esjoul BOBSPUIT eesoreespur] SUJ9}. sjue|d
z 3 SUROUI] eA sLeeul] Sue}doueIoiq eeeoR|uaYyoe|5, SUJO} sjue|d
€ 9 iijapuew Bjuayoe}5 aesoeR|UuaYola[5 SUJ9} sjue|d
v 5 Usa} fe109 peyonoed edieaip BIUaYIIE[D eeedeIUEYoIs!5 SUJO} syueid
€ 5 Biqnp BuaRYyoojeD aeeoRlUOSsyoIq SUUd} squeid
6 9 uayoesg UOLUWIOD winjugjnosa winipuajd  seeoejpee|suueq SUIO} sjue|d
‘ 9 usey Buim-syeq esjoul suejdoysi-L}  seeoenpeejsuueq SUJO} sjue|d
v 9 ueyoeig dwems Hojenul sidejodsLy = seeceypeejsuueq SUJO} sjue|d
1 5 wey ansub wineulbeypes winuyoe|g eeeoeUuyosiq Sue} syueid
OL 9 usay Joyem dems winolpul winuyoe|q eeeoeuyosiq SUL} syue|d
z 9 eljoze Aue} Bjyeuuld BOZy _ eeeoR||ozy SUI} sjue|d
I eueoaweojsne wen sourjawojes ewWUeBoIA td aeeoRjUBIpy SIO} sjue|d
S98H O8d4a WON awen uol._/o9 awe, -DYNUaINS Ajwie sse|Q wopbuly

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L asind s,piaydeys suojsedesing ejasdeg eeeorolsseig  — sjoalp seyBiy sued
L yeyo01 Bes Bynjuapa aflyeD eeeorolsseig = sJoalp JeuBiy sued
l poem mojjaA Bioyinsed eBosuyen eesorlsjsy  — sjoolp JeuBiy sjue}d
L 9 syjoes6 eroydouebeT eesoRlajsy — sjoolp JeuBiy sjue;d
v peem yeoBbAiIq eniq winuejuojsnoy winjeseby eesowlaisy  s}oolp JeyBiy sjue|d
6 ysnq jespunos6 Byoyuey sueyooeg eeeorlasy  — sjoolp soyuBiy sued
z 9 winasaujo winyyyjueAD aesoRlajisy  — sjoolp 19 yBiy sjue|d
L 9 Asyep am-ieddoo paseysnjo _Baplouyoese sidajopod eeeoRlsjsy  — sjoolp seuBiy sjued
L 9 Huosiyonul sisopyny eeeoRlajsy — sjoolp seyBiy sjueid
I 9 Astep Bunsepeas uepjob uinjeajoeig wnsAi1ys01exX eeeorleisy = sjooip JeuBiy sjuejd
I 9 Saplojulsseo snuUleYyjozO eeeorlajsy  — sjoolp seyBiy sjue|d
v Beqojiy ejoonaubeyds eeesoelajsy  —- soap seyBiy syueld
I 9 winueyejsne winieyjejqued eesoRlajsy  —_ sjoolp s8yBiy sued
I 9 suoyng mojjeA winejnoide winjeydasoshiyD eeeorleisy = sjoolp JeuBiy sjueld
€ 9 SNIOMUBLOICA SOPJYIOIZ aesorlajsy  — sjoolp Jeybiy sjuejd
Z peouyyolu} saploipideio winpeydac0ssel9 eveorleisy — sjooip JeyBiy sjueld
I 9 peampno Aesior wingjeoajn| winyeydeuBopnasd aeeorasy — s}oolp Jaybiy sjueid
z Byisnd “eA sisuapeued ezAu0D eeeoRajsy —- sjooip Jeybiy sjueid
I 9 essoj6Ayoriq “1eA eJOyjpUBIB BOW eeaoRajsy —sjooip JeyBiy sjuejd
€ @]}SIUJMOS UCLUWIOD snaoesejo snyouosg eeeoRlajsy  —_ sjoolp JauSiy syuejd
L sjsualieuog BZAUOD eeeoReisy —- sjoaip JeyBiy syuejd
I eueqeey |e} sisuedqeuins ezAuoD eesoRajsy —sjooip Jeybiy squejd
z BYO{YOUOS BIZ eeeoRajsy  —- sjooip Jeybiy sjuejd
z winjeyound ‘dsqns winjejound winseyje.4ued eeeoriajsy  —- sjoolp JeyBiy syueld
I 5 wintoouuey-wunsiojoseo ‘dsqns eyoyjsnBue sudi eeeoRlajsy —- sjoolp JayBiy sjueid
€ esojid suapig eesoRlajsy —- sjooip Jausiy syue|d
I 9 snjne] ojoeueg eeeozlelsy — sjoolp JeyBiy sued
I 49482 PIM snjejngns 1ajsy eesorajsy —- sjoolp Jaubiy syueid
I aysiu seeds aueBiNA WNISHD eeeorlejsy —- sjoolp seuBiy sjuejd
z 5 suenjony eipAuZ eesoRelsy —- sjoalp JeyBiy syue|d
I 9 BIdIJO9 SUM Byeqsoid eidyoz eesoeesy — sjoolp seyBiy syue|d
z 9 speeujnu Bulpeaids syejsne sayjedy eeeoRajsy — sjoop JeyBiy sjue|d
z seesyeo Pyeojpes suaeYOods}{ aeeoelsjsy  —- sJoolp seUBIYy sjue|d
I Byejoaoue sisdoasog aeeoelajsy  —- sjoolp seuBiy sjue|d
L 9 BIOYIG BIUOJSEYONA eeeoelajsy  —- sjooip seyuBiy syueid
L 9 sBed sejqqoo eayeu suapig Bipse2ossojH eeeoelejsy = sjoolp seuBiy sjue|d
L 5 winsouseo wnyoueusD eeeoepeidejsy  — sjooip JeyBiy syueid
I 9 B}eSO1 BIUePSIEYY eeeoepeidejosy — sjoolp JeyBiy sjuejd
zZ ysnquojjoo uoojeq sndresoshyd sndreooyduio5 eeooepeldajsy sjooip sauBiy sjueld
I ysnquoyjoo peey-pal eolaesseino seidajosy eeeoepeldejsy —sjooip sayBiy sjuejd
1 - quejd yjow Baoues eine. eeeoepeidejosy —sjoolp Jey6iy sjuejd
S 9 9a} Bjjauquin eyAydoujoe e1ayyjayos aeeorlesy  —- sjoolp seyblu sjue|d
‘€ 9 poom Alajao suebaja seloshjod eesorleiy  — sjoolp Jeubiy sjued
9 9 edoi Aeyuow BOUILUBIS BISUOSIEG eesoeuAcody _—sjoaip Jeybiy squejd
L epyumued yuid snasol snyjueseyjeg eeaoeufoody —sjoolp Jeybiy sjuejd
soe O8d4 WON SWeN UOL/05 BUE,, ONUBIOS Ajtwes ssejg wophury

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vz jo 01 eBeq

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v 9 Buopuenb yse snjejnojes sndieooae|z eeaoedieooee|y ~—s sjoaip seyBiy sued
I 9 yse Aueqeniq snjeaogo sndies0ee|z eeaoedieoose|y ~—s sjoolp seyBiy syueld
I 95 JUUBULING B1OSOIG eesoelesoiq — sjoolp JouBiy sjueid
9 9 Byeinjeds wiasoiq eeeorlesoiq —sjoolp JeyBiy sjueid
€ 9 MOPUNS PayJO} Belg BIBSOIG aesoRlasolq = sjoolp weuBiy sjue|d
S 9 moepuns aed Bjeyad esasoiq eeeoelesoiq = sjoolp JayBiy sjueid
€ 9 BoeulbAd e1asoiq eeeorlesoiq  —- sjoolp seyBiy sjueld
6 9 BUISOA BILAQQIH sesorlualid  — sjoolp seubiy sjue|d
@ 9 BPS BIMOQQIH a sqooip sey6iy sjue|d
S 9 SUBPUBDS BILAQqIH dq — sjooip seyBiy sued
9 5 ByOyONES PIVEQQIH id —- sjooip seybiy sjue|d
zg 3 BYOSNIQO “IEA SUBOUI] BIMOGGIH ad sjoorp sey6iy sjueld
€ 9 sueinaoe BlUegqiH id — sjoolp Jeybiy sjuejd
@ 9 SHBSUI] BIUEQQIH ad sjoorp seyByy sjuejd
L 9 BILeQIH seeor|ueliq — sjoorp seyBiy sjuejd
v 9 Bieneg paieysn|o Bjeydeo eieneg eesorjuouny ~— sjoorp seyBiy sjueld
L esueobeyep winjAydosig eeeorinsselg —s sjoolp seuBiy sjueld
L jue|d uojoeunsel winjeuujd winAydosig eesorinsselg — sJoolp seuBiy sjueld
@ 9 jooysyeob sisuajiseig ‘dsqns aeideo-sad eaowod eesoe|nAjOAUOD s}oolp 9yBiy sjuejd
z PoLeD BAOWOd} eeeoRiNA|OAUOD __sjoolp seybiy sjuejd
L oyejod joams sejejeg e@oulod) eeeoeinAjoAuog —_—sjooip seyBiy - sjueid
L Auo[6-Bujwiow enjq Bajpu} BeOWOd; eesoRinAjoAuoD —_sjoolp seyBiy sjueld
€ 9 - wineujwes6 wnouedsH eesorisnig = s}oolp souBiy sjueyd
L ee] UBOIXE/y seplolsoiquie winjpodousy) e@esoelpodoueyy _—sjoolp seyBiy sjueid
6h 9 sijesoyy] BULENSBIOIY eesoeuuenseg = sjooip Jeybiy sjueid
I 5 . eueou ‘dsqns eyoyjasinba euuensed egesoeuuenseg —sjooip seyBiy squejd
or. ga a yeo-eys nWwy IW euinwe euenseooly eesoeuuensey — sjoolp JeyBiy s}ueid
v . 5 yeo-eys dwems vone/6 euuensed eesoeuuensey) — sjoolp JeyBiy sjuejd
Z 9 Buyenseooly eesoeuuenseg — sjoollp JeyBiy sjueid
L Byepi0o ‘dsqns ejepioo euewsIq eeeoey|Aydofueg —sjoolp seybiy sjueid
1 winyjAydesja} uodieoXjog aeeoey|Aydofueg —_—sjoolp seyBiy sjuejd
1 paemyoiyo BIpAW BLE EIS eesouy|Aydofieg — sjoolp seusiy syueid
L 9 JOUIW “JeA BSOqUIAIOD PABdIEOA|Og eesoe|Aydoieg — syoolp seuBiy syue|d
I Boujpeb auayls eeooe|Aydofieg —sjooip saybiy sjue|d
9 9 Bljeqo| pejbue Bee BaqoT eesoginueduey —sjoalp JeyBiy syueid
€ 9 BaDPUBIQUIOU BAGO] eesorinuedwuen sjooip seyBiy sjue|d
z 9 ByAydouejs BI/aqo7 eeeorinuedueg —sjoolp JeuBiy sued
S 9 JOO. O}IYM sueoseindind elaqo7 eaeeoeinueduey — sjoalp uey6iy sjueid
Z 9 Hleqeniq Buyyweids syjoel6 eibsraquejyeM eeeorinuedueg  — sjooip JeyBiy sjue|d
L 9 eBiaquajyey, egeeoeinuedwey — sjooip seyuBiy sjuejd
1 Bjoujs eyundO aesorpeg = sjoaip seybiy sjue|d
L winutApip winipide7 eesoeolsselg ° sjoolp seybiy sjue|d
I USIPed PIM winasiueydes snueydey eeeoeolsselg  — sjoolp eyBiy syueid
1 ssaloiedded suqueiuy esuayeuog winipiday eesoeolsselg sjoolp .94yBiy sjue|d
L winso6n wnaysidey eveowolsseig = sjoolp seyBiy sjue|d
so9H Oda VON aWeN UO. 09 awed, dynuatos _. Alwe4 ssejo wopbury

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v 9 BulsapuRlO aujoA[D eeeoeqe4 sjoalp Jey6iy sued
L 9 ead auloA|6 Bujoege} auloA|D eesoeqe4  sjoolp ieyBiy sued
9 9 snjoe UOWWWOO soepiooue snjoy eesoeqe4  sjoolp seybiy sjuejd
\ 9 ueaq yor! je}seoo Basol BeABURD eeaoeqe4  sjoolp ieybiy sjueid
L Y ealhbie auroh}D eeeorqe4 sjoalp ueyBiy sjuejd
L 9 ueegq Auing eaquebib eunony eeeoeqe4  sjoolp seyBiy sjued
vy 9 Beelssog ssayjeo| Bjesua eeelssog eesoeqe4 sjoolp JeyBiy sjue|d
9 9 snjoe pejulod Bebiue snioy eeeoeqe4  sjoolp seubiy sjuejd
1 9 ueeq eunp eure eublA aeeoeqe —sjoalp seybiy syed
€ 9 Ipueuipsay uoIpiyooj[D eeeoriqioydny — sjoolp JeyBiy sued
Z 9 901] eseayo eyeiquin winuejewuns UoIpIYyoo{ey eeeoeiqioudng —sjoolp Jeu6iy sjueid
z 9 Saploouia WNAYAURIOIYY eeeoeiqioydny — sjoalp JeyBiy sjuejd
Y 9 994) auluinb suaosagnd ewibysojejad eeeoriqioudng —sjoolp JayBiy sjuejd
z 9 esayjuelod |jews BYAYdOJOIU BLOYJUBIOd eeeoriqioydnyg —sjoalp Jeybiy sjuejd
S 9 syejuauio snyjuepnasd eeeoriqioudnyg —sjoalp sey6iy sjueid
L Byoyidosshy aoAsaeweyo eeeoeriqioudny —sjoalp seyiy sjuejd
LL 9 ysng Bulppem snyjojiuid sodieoouloiy eeeoriqioydny —sjoolp Jeybiy s}uejd
€ 9 @uluInb \sas0y auejnoojuy PUIBYSOfe}ad eeeoeiqioydny — sjoolp sayBiy sued
L enjesuiod pemp Bioydoyjeho eiqioydny eeeoriqioudny sjoolp 4a4yBiy sjueid
v 9 eBuereoew snueue) ebueleoey eeeoriqioydnyg — soap seybiy sjueid
L peem onsneo pel Bjeysoid aokseeueyo eeeoeiqioydny — sjooip JeyBiy sued
L 9 eaosBuew Ayji Byooebe BL1BI@0IXF eeeoviqioydny —sjoolp JeyBiy sjueid
l snjjaueay snyjuel|AYd eeeoeiqioydny —sjooip seyBiy sjuejd
L 9 snyjueyAdd eeooeiqioydny — sjoaip s8ybiy sjue|d
6 9 yyeay woolg Ajyoud puedoos eo0j}OUOWy eesoepuoedy — sjoalp seysiy sjupid
Z 3 eyAydosoiu suoedy eeeoepwoedy — sjooip seyBiy sjueid
& 9 siuuojep uoGodooneT eeooepuoedy sjoolp 404yBiy sjueid
S 5 uyeey preeq UOWWLUOO snjyebija uoBodooneT eeeoepuoedy syooip s8ybiy sued
€ 5) yyeay Jeysnjo pel ejebaibhe ayoujoioy eeeoepuoedy s}ooip 4ey61y sjueid
L 9 Beyeoped eoiby eesoepuoedy — sjoolp seybiy sjueid
zZ ° saprouydep ewojAyorig eesoepuoedg — sjoolp seybiy sjueid
z 3 yyeay Apyoud snuuediun{ uoBodoone7 eeeoepuoedg = syoolp seyBiy sjueid
I 9 snioyiased uoBodoona7 eesoepwoedy — sjoolp seyBiy sjueid
8 9 sepioejauid uobodoone7 eesoepyoedy — sjoolp seusiy sjueid
z 95 ftulyoapioos ewiojAyoeig eeeoepuoedy — sjoaip saysiy sjueid
9 3 eyeBueids saployabueids eyabuaids eeeoepuoedy s}ooip 4eyB1y sjueid
Lb 9 saplouiedsojda; uoBodoone7 eeeoepyuoedy — sjoolp zeupiy sjueid
L 2 Bioyiaeig ‘dsqns sipuia eyeydAis eeeoepuoedy — sjoolp seyBiy sjue|d
z 9 eyAydosoju «rea ByAYydosoiul suioedz eeeoepuoedy = sjoolp sayBiy sjue|d
L 2 sepjouydep ‘dsqns sepiouydep ewojAyoeig seooepwoedy s}ooip sauBIy sjued
v 2 (LZ 4a)xeg'd pues] sasei-4) ‘ds eoojouoyy eeeoepuoedy —s syoalp seuBiy sjue|d
S 3 uyeey UOWWLUOO Byoysnyqo suoedy eeeoepuoedy — syooip saybiy sjuejd
z 29 SIPIA eyayds eeooepuoedy — sjoolp sauBiy sjuejd
8 9 yyeoy winyjem Byaygind suoedy eeeoepuoedy sjoolp seyBiy sjueid
L 9 sueBund eisyjooj\ seaoepuoedy sjoolp s94yB1y sjuejd
soey 9dd4a VON @WeN UO .0D awe, dyNUaINS Ajwwey sseig wopbuly

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z 5 BIOUs Braiduiegq eeeor|uepooy —sjooip JeyBiy sjueid
€ 9 saisued piim Bjeinyyeds eIAajo/ eesorluspooy sjoolp eyBiy sjue|d
z 9 Bjeingjued BIUapOOH eeeoR|uepoOy —sjoolp JeyBiy sued
Z 9 Biabije1s B1UePOOLE) eeeoe|uapoor sjooip seyBiy sjue|d
IL 5 Peoelepay BIUapOOy eeeoRluepoey — sjoolp seybiy sjueid
v 9 eioidweq eeeor|uspooy — soap seybly sjueid
I 9 Auneyueo yids uinjeoids winunejued eeeoeuequsy = sjoolp seubly sjueid
S 9 BONING BOAOH eesoeqe4  sjoolp seyBiy sued
L 9 BB/OBQUR] PAAOH eesoeqe4 sjooip JeyBiy sjue|d
z 9 esnjal eeeUalind eesoeqe4  sjoolp seybiy sjueid
z 9 BUCUIWIA Beoun! BURUIUILA eeeoeqe4  sjooip seyBiy sued
Zz 9 Buojas BIUAMIIIG eeeoeqe4 sjooip seyBiy sjuejd
z 9 BIsnqos eeeue}ynd eeeoeqe4  sjooip seyBiy sjuejd
v 9 ead ysng Aey BSOIIA PABUALNd eesoeqe4 sjoolp uaybiu sjueld
€ 9 BuBIUOU! BLe{B]01D oveoeqe4 s}oolp 4eyBiy syueld
8 9 Byequiw Ayyeey BYOJIQNU BOUIN eesoege4 — sjooip Jeybiy sjuejd
9 9 Byeinjjaquin eIseineq eeeoeqe4  sjooip Jaybiy sued
v 9 Bounquoy euAMiiG eeaoege- sjooip seybiy sjuejd
z 9 euuaqge|6 eluAmilig eeeoeqe4 sjoolp Jeybiy sjuejd
S 9 ead yey} WINSOULIO, WINIGO[AIBIq eeeoeqe4 sjooip Jeybiy sued
z 9 Beeissog a|qeueA ByAydosajay Baelssog eesoeqe4  sjoorp Jeybiy sued
1 BIBIOBOUR] PUBIE]OID eesoeqe4 sjoolp seyBiy sjueid
{ 9 onjiedsan euuyVZ eeeoeqe4 sjoorp seyBiy sjueld
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sey OGda WON awey uo b9 au, diUuaIog Awe ssejQ wopbury

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ZO: LE°6 1 18 2002/S0/Z0 e12q OBNXG - BUI|UC eyIPIIM AoUaby UONoS}O1g jeJUELWUOMAUZ

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S98yY Odd VON Swen uou 09 awe, . DyQuaiog Ayes Ssseio wop6uly

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L 9 saploiodoAw B2ayIO}IUd eeeoRiny — sjoaip seuBiy syueid
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Kingdom Class

protists
protists
protists
protists
protists
protists
protists
protists
protists
protists
protists

CODES

NCA - Indicates the conservation status of each taxon under the Nature Conservation Act 1992.

green algae
green algae
green algae
green algae
green algae
green algae
green algae
red algae
red algae
red algae
red algae

Family

Chlorophyceae
Chlorophyceae
Chlorophyceae
Chlorophyceae
Chlorophyceae
Chlorophyceae
Chlorophyceae
Rhodophyceae
Rhodophyceae
Rhodophyceae
Rhodophyceae

Scientific ‘ame

Gomontia
Phaeophila
Chaetomorpha
Cladophora
Caulerpa taxifolia
Cladophora prolifera
Chaetomorpha linum
Chondtia
Hydrolithon
Ceramium flaccidum
Spyridia filamentosa

Cao yon Name ' NCA EPBC Recs

QANQQ09NN0NN0NN
Bonanno won

The codes are Presumed Extinct (PE), Endangered (E), Vulnerable (V), Rare (R), Common (C) or Not Protected ( ).

EPBC - Indicates the conservation status of each taxon under the Environment Protection and Biodiversity Conservation Act 1999.
The codes are Conservation Dependent (CD), Critically Endangered (CE), Endangered (E), Extinct (EX), Extinct in the. Wild (XW) and Vulnerable (V).

Recs - Indicates the number of records of the species contained within the database for the area searched.

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Environmental Protection Agency Wildlife Online - Extract Date 02/05/2007 at 13:31:02