Original source · versioned page text
SUPERSEDED - Approved Plan - OPW23/0084
Plans and drawings: the text below has words only, no drawings.
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NOOSA COUNCIL SITE PLAN
APPROVED PLAN
OPW23/0084 5 SEPTEMBER 2023
DESIGNED BRISBANE SURVEYOR DATUM DRAWING STATUS
T 07 3852 4333
E [email protected]
PROJECT
DRAWN
GOLD COAST T 07 5571 1599
CHECKED
E [email protected] LOCATION DRAWING NUMBER
SUNSHINE COAST T 07 5391 3777 USE FIGURED DIMENSIONS ONLY. DO NOT SCALE, IF A DISCREPANCY ARISES
E [email protected] CHECK WITH THE PROJECT ENGINEER AND/OR SUPERVISING AUTHORITY. DO NOT
APPROVED J. HILL RPEQ 19891 WORK FROM REDUCED SCALE DRAWINGS (A1-A3 SIZE PAPER). COPYRIGHT OF ALL
For and on behalf of
NORTHERN NSW T 02 6674 8047
DRAWINGS & WORKS EXECUTED FROM THEM IS VESTED IN WESTERA PARTNERS
TITLE
DATE E [email protected] SHEET NUMBER REVISION
WESTERA PARTNERS PTY. LTD. AND USE OF THERE FORE WITHOUT PERMISSION IS STRICTLY PROHIBITED! IT IS
www.westerapartners.com.au ABN 52 097 417 975 CENTRAL VICTORIA T 03 5441 0922 THE BUILDERS RESPONSIBILITY TO ENSURE ALL WORKS ARE CARRIED OUT WITH
No. DATE REVISIONS DES DRN CHK APD DOCUMENT CONTROL APPROVED E [email protected] DUE CARE AND DILIGENCE TO COMPLY WITH THE CONTRACT DOCUMENTS. CLIENT
Document Set ID: 22439813
Version: 1, Version Date: 26/05/2023
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SECTION
TYPICAL A.C. PAVEMENT DETAIL
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CD < CD
< CD < CD < CD < CD <
CIVIL WORKS PLAN
NOOSA COUNCIL
APPROVED PLAN
OPW23/0084 5 SEPTEMBER 2023
DESIGNED BRISBANE SURVEYOR DATUM DRAWING STATUS
T 07 3852 4333
E [email protected]
PROJECT
DRAWN
GOLD COAST T 07 5571 1599
CHECKED
E [email protected] LOCATION DRAWING NUMBER
SUNSHINE COAST T 07 5391 3777 USE FIGURED DIMENSIONS ONLY. DO NOT SCALE, IF A DISCREPANCY ARISES
E [email protected] CHECK WITH THE PROJECT ENGINEER AND/OR SUPERVISING AUTHORITY. DO NOT
APPROVED J. HILL RPEQ 19891 WORK FROM REDUCED SCALE DRAWINGS (A1-A3 SIZE PAPER). COPYRIGHT OF ALL
For and on behalf of
NORTHERN NSW T 02 6674 8047
DRAWINGS & WORKS EXECUTED FROM THEM IS VESTED IN WESTERA PARTNERS
TITLE
DATE E [email protected] SHEET NUMBER REVISION
WESTERA PARTNERS PTY. LTD. AND USE OF THERE FORE WITHOUT PERMISSION IS STRICTLY PROHIBITED! IT IS
www.westerapartners.com.au ABN 52 097 417 975 CENTRAL VICTORIA T 03 5441 0922 THE BUILDERS RESPONSIBILITY TO ENSURE ALL WORKS ARE CARRIED OUT WITH
No. DATE REVISIONS DES DRN CHK APD DOCUMENT CONTROL APPROVED E [email protected] DUE CARE AND DILIGENCE TO COMPLY WITH THE CONTRACT DOCUMENTS. CLIENT
Document Set ID: 22439813
Version: 1, Version Date: 26/05/2023
Page 3
CIVIL WORKS PLAN
NOOSA COUNCIL
APPROVED PLAN
OPW23/0084 5 SEPTEMBER 2023
DESIGNED BRISBANE SURVEYOR DATUM DRAWING STATUS
T 07 3852 4333
E [email protected]
PROJECT
DRAWN
GOLD COAST T 07 5571 1599
CHECKED
E [email protected] LOCATION DRAWING NUMBER
SUNSHINE COAST T 07 5391 3777 USE FIGURED DIMENSIONS ONLY. DO NOT SCALE, IF A DISCREPANCY ARISES
E [email protected] CHECK WITH THE PROJECT ENGINEER AND/OR SUPERVISING AUTHORITY. DO NOT
APPROVED J. HILL RPEQ 19891 WORK FROM REDUCED SCALE DRAWINGS (A1-A3 SIZE PAPER). COPYRIGHT OF ALL
For and on behalf of
NORTHERN NSW T 02 6674 8047
DRAWINGS & WORKS EXECUTED FROM THEM IS VESTED IN WESTERA PARTNERS
TITLE
DATE E [email protected] SHEET NUMBER REVISION
WESTERA PARTNERS PTY. LTD. AND USE OF THERE FORE WITHOUT PERMISSION IS STRICTLY PROHIBITED! IT IS
www.westerapartners.com.au ABN 52 097 417 975 CENTRAL VICTORIA T 03 5441 0922 THE BUILDERS RESPONSIBILITY TO ENSURE ALL WORKS ARE CARRIED OUT WITH
No. DATE REVISIONS DES DRN CHK APD DOCUMENT CONTROL APPROVED E [email protected] DUE CARE AND DILIGENCE TO COMPLY WITH THE CONTRACT DOCUMENTS. CLIENT
Document Set ID: 22439813
Version: 1, Version Date: 26/05/2023
Page 4
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WATER PLAN
T T T T T T T T T T
W W W W W W W W W W W
E E E E E E E E E E E E E E E E E E E E E E E
NOOSA COUNCIL WATER INSET
APPROVED PLAN
OPW23/0084 5 SEPTEMBER 2023
DESIGNED BRISBANE SURVEYOR DATUM DRAWING STATUS
T 07 3852 4333
E [email protected]
PROJECT
DRAWN
GOLD COAST T 07 5571 1599
CHECKED
E [email protected] LOCATION DRAWING NUMBER
SUNSHINE COAST T 07 5391 3777 USE FIGURED DIMENSIONS ONLY. DO NOT SCALE, IF A DISCREPANCY ARISES
E [email protected] CHECK WITH THE PROJECT ENGINEER AND/OR SUPERVISING AUTHORITY. DO NOT
APPROVED J. HILL RPEQ 19891 WORK FROM REDUCED SCALE DRAWINGS (A1-A3 SIZE PAPER). COPYRIGHT OF ALL
For and on behalf of
NORTHERN NSW T 02 6674 8047
DRAWINGS & WORKS EXECUTED FROM THEM IS VESTED IN WESTERA PARTNERS
TITLE
DATE E [email protected] SHEET NUMBER REVISION
WESTERA PARTNERS PTY. LTD. AND USE OF THERE FORE WITHOUT PERMISSION IS STRICTLY PROHIBITED! IT IS
www.westerapartners.com.au ABN 52 097 417 975 CENTRAL VICTORIA T 03 5441 0922 THE BUILDERS RESPONSIBILITY TO ENSURE ALL WORKS ARE CARRIED OUT WITH
No. DATE REVISIONS DES DRN CHK APD DOCUMENT CONTROL APPROVED E [email protected] DUE CARE AND DILIGENCE TO COMPLY WITH THE CONTRACT DOCUMENTS. CLIENT
Document Set ID: 22439813
Version: 1, Version Date: 26/05/2023
Page 5
1
N
4C
Lot 21 U1324232
SP267225 Emt D Lot 22
4C (LV)
1-95 ABC
P191522
#59 SP267225 SP267225
33
P308979 #59
240LV
1-95 A
BC 4C Lot 1
RP212287
25
U1324233
#55
(LV)
P308980
Lot 1
SP186019
#47 DANGER
Lot 2 EXISTING LOT 3
SP186019 TELECOMS B LOT 4
Lot 2 EXISTING TREES, CONTACT #45 EXISTING TREES, CONTACT C
RP102636 DANGER
SU
ARBORIST REGARDING ARBORIST REGARDING
TREE PROTECTION ZONE TREE PROTECTION ZONE DAM
#2
MM
LIVE LV CABLE MARKER POST
TO BE INSTALLED DAM
CABLES
IT
EVERY 50m
RO
240LV
LARGE BUSHES ON
AD
BOUNDARY/FENCE
240LV
2 4.0 3B
P69053 BB
AA
AA
U1471289
4-7/3 0L
V D Emt A DAM 3C
.75 (L 24 3 EMT B
(LV) 58
V) SP186019 3A
3.75 T
4-7/
61
S T REE 1
CABLE MARKER POST TRENCH EXISTING CABLE MARKER POST
MI LL P69054
Lot 4 TO BE INSTALLED
CABLE MARKER POST
TO BE INSTALLED DRIVEWAY TO BE INSTALLED
RP160894 EVERY 50m EVERY 50m
EVERY 50m
2-7/3.00 (LV)
P97349 Lot 1 #39
P69052 32
RP64584
#1
ELECTRICAL CONTRACTOR
TRENCHING FROM STATION 2 -3, STATION
LEGEND
3A-3B AND STATION 3A-3C TO BE IN
CONSULTATION WITH AN ARBORIST TO
CONFIRM PROTECTED TREES/ROOTS AND TO EXISTING CONDUIT EXISTING OVERHEAD LINE
BE AWARE OF TREE PROTECTION ZONES.
PROPOSED CONDUIT PROPOSED OVERHEAD LINE
PROP. OH CONSUMERS LV CABLE TERMINATION
ELECTRICAL CONTRACTOR PROP. UG CONSUMERS 11kV CABLE TERMINATION
CONTRACTOR TO ARRANGE FOR TUNNEL
BORE FROM STN 3 - STN 3A (IN PROP. UG CONSUMERS BORE LV POLE
CONSULTATION WITH AN ARBORIST).
EXISTING PILLAR 11kV & LV POLE
ARBORIST TO BE ENGAGED BY THE
DEVELOPER DIRECTLY. PROPOSED PILLAR AIR BREAK SWITTH
PROPOSED C & I PILLAR RECLOSER
PROPOSED LINK PILLAR GROUND STAY
SURVEYOR
EXIST. CABLE IN CONDUIT LV LINKS
SURVEYOR TO PLACE A LINE PEG BEHIND THE
PROPOSED PILLAR LOCATION AT STN 3 TO
SATISFY ENERGEX'S REQUIREMENTS.
PROP. CABLE IN CONDUIT POLE TRANSFORMER
SPARE LV CONDUIT C PMT
SPARE HV CONDUIT R RMU
STREETLIGHT (LED) MEN EARTH
99 STATION NUMBER STAGE BOUNDARY
CABLE MARKER PLATE
NOTES
ELECTRICAL, TELECOMMUNICATIONS, 100mm MIN 1. CONSTRUCTION TO BE STRICTLY IN ACCORDANCE WITH THE RELEVANT
AND WATER SERVICES CAN BE INSTALLED ENERGEX CONSTRUCTION MANUALS.
IN THE SAME TRENCH SO LONG AS T
MINIMUM CLEARANCES ARE MET. 2. ALL MATERIALS TO BE SUPPLIED & INSTALLED BY THE CONTRACTOR.
MINIMUM CLEARANCE IS 100mm BETWEEN 100mm MIN T
3. LOCATE ALL EXISTING SERVICES PRIOR TO EXCAVATION. CONTACT BYDA
ALL SERVICES CONDUIT AND ALL OTHER (BEFORE YOU DIG). PHONE:1100, FAX:1300 652077. MINIMUM TWO WORKING
SERVICE CONDUITS. T E W
DAYS NOTICE REQUIRED.
100mm MIN 100mm MIN
E W E W 4. INSTALL PVC CABLE PROTECTION COVER STRIPS ABOVE INTERNAL CONDUITS
50mm MIN 50mm MIN
AND EXTERNAL CONDUITS WHERE NOT ON NORMAL ALIGNMENT.
50mm MIN 50mm MIN
DETAIL 'AA' DETAIL 'BB' 5. SUPPLY ALL LABELS TO ENERGEX SPECIFICATION.
NOT TO SCALE NOT TO SCALE
6. REFER TO NBN Co PIT & PIPE PLAN FOR THE TELECOMMUNICATIONS
INSTALLATION.
SOURCE DOCUMENTS
CREATOR DWG. NO. DATE
WESTERA PARTNERS S23-036-C_Civilwks - email 23.06.14.dwg 15/06/2023
NOOSA COUNCIL ORION SPATIAL SOLUTIONS S-2505-001-A Detail.dwg 15/06/2023
NOT FOR CONSTRUCTION APPROVED PLAN
OPW23/0084 5 SEPTEMBER 2023
ORION SPATIAL SOLUTIONS
ENERGEX
S-2505-002-B ROL.dwg
Drawing27.dwg
15/06/2023
14/06/2023
REVISION DESCRIPTION ALIGNMENTS DEVELOPER DRAWING TEMPLATE VERSION 1.00
CHECKED: S.LEFTWICH
Underground Power
- SCALE ENERGEX OH
ENERGEX UG
3.2m
0-900mm NEW LOTS DESIGNED: M.REMME DESCRIPTION
SCALE: 1:1000
PROJECT No.
3, 4 Electricity Reticulation
TELSTRA refer NBN layout PHONE: 0405 534 850
0 5 10 20
SCALE 1:1000
40 60
GAS refer APA layout RP DESCRIPTION ENGINEER: A.JEANNOTTE
Small Subdivision
22-079A
WATER refer Civil layout RPEQ No.: 12821 LOCATION
1:1000 @ A1 Lot 3 SP186019
STORMWATER refer Civil layout SIGNATURE: ENERGEX No.
1:2000 @ A3
SEWERAGE refer Civil layout COUNCIL NOOSA 43 Summit Road S6200123
A 04/08/2023 FOR APPROVALS MR AJ ALL UNITS ARE IN METERS UNLESS OTHER n/a COUNCIL REF. RAL22/0018
Copyright 2022 Jeannotte Engineering. All rights reserved. Pomona, QLD 4568 SHEET 1 of 2
REV DATE DESCRIPTION DD AP OTHERWISE SPECIFIED PEGGED? No UBD REF MAP: SC 4-G10 ISSUE DATE: 04/08/2023 A1
Document Set ID: 22571097
Version: 1, Version Date: 05/09/2023
Page 6
2
N
SU
M
2
MI
T
U1471289
RD
3.75 1
4-7/
P69054
P7919 SP11258 L ST
4-7/3.75 (100kVA) MIL
4-7/3.75
MILL ST P7925
1-95 ABC
AM
BU
LAN
CE
P272158
ST
EXISTING LV SCHEMATIC
ALL CABLES ARE 240mm² 4C Al UNLESS NOTED OTHERWISE
SCALE 1:2500
N
SU
MM
2 3
IT
U1471289
U12622694
RD
3.75 1
4-7/
P69054
T
P7919
4-7/3.75
SP11258
(100kVA) MILL S
4-7/3.75
MILL ST P7925
1-95 ABC
AM
BU
LAN
CE
P272158
ST
PROPOSED LV SCHEMATIC
ALL CABLES ARE 240mm² 4C Al UNLESS NOTED OTHERWISE
SCALE 1:2500
PROPOSED COMMISSIONING PLAN LV POLE LABEL STN 1
LABEL LABEL LETTER SITE LOCATION FOR
Tentative only & subject to amendment by ENERGEX' outage coordinator. SIZE COLOUR SIZE ATTACHING OF LABEL LABEL INFORMATION
POLE No.:
Live Line & LV switching x1 KOLANA AS PER P69054
300x100 BRONZE LABELING LV CABLE TO EASEMENT OFF OF SUMMIT RD U12622694 AND SERVICES
/ SILVER MANUAL LOCATION:
SWITCHING #1 6447-A4 SUMMIT RD
· INSTALL NEW LV CABLE FROM U1471289 WITHOUT CONNECTING
TO EXISTING NETWORK
· LIVE LINE TO BREAK BRIDGES AT LV UNDERGROUND
TERMINATION BRIDGING AT SUMMIT ROAD P69054.
· INSTALL NEW LV SWITCH AT P69054
· TERMINATE NEW LV CABLES TO U1471289
· TEST & COMMISSION NEW CABLE
Construction to be strictly in accordance with the relevant Energex construction
manuals. Customers to be notified of any outage as per Energex'
requirements.
NOOSA COUNCIL
NOT FOR CONSTRUCTION APPROVED PLAN
OPW23/0084 5 SEPTEMBER 2023
REVISION DESCRIPTION ALIGNMENTS DEVELOPER DRAWING TEMPLATE VERSION 1.00
CHECKED: S.LEFTWICH
Underground Power
- SCALE ENERGEX OH
ENERGEX UG
3.2m
0-900mm NEW LOTS DESIGNED: M.REMME DESCRIPTION
SCALE: 1:1000
PROJECT No.
3, 4 Electricity Reticulation
TELSTRA refer NBN layout PHONE: 0405 534 850
0 5 10 20 40
SCALE 1:1000
60
GAS refer APA layout RP DESCRIPTION ENGINEER: A.JEANNOTTE
Small Subdivision
22-079A
WATER refer Civil layout RPEQ No.: 12821 LOCATION
1:1000 @ A1 Lot 3 SP186019
STORMWATER refer Civil layout SIGNATURE: ENERGEX No.
1:2000 @ A3
SEWERAGE refer Civil layout COUNCIL NOOSA 43 Summit Road S6200123
A 04/08/2023 FOR APPROVALS MR AJ ALL UNITS ARE IN METERS UNLESS OTHER n/a COUNCIL REF. RAL22/0018
Copyright 2022 Jeannotte Engineering. All rights reserved. Pomona, QLD 4568 SHEET 2 of 2
REV DATE DESCRIPTION DD AP OTHERWISE SPECIFIED PEGGED? No UBD REF MAP: SC 4-G10 ISSUE DATE: 04/08/2023 A1
Document Set ID: 22571097
Version: 1, Version Date: 05/09/2023
Page 7
Fauna Management Plan
Summit Road, Pomona
Report Prepared for Base Architecture
Decision Notice RAL22/0018
Rev 0
NOOSA COUNCIL
APPROVED PLAN
OPW23/0084 5 SEPTEMBER 2023
Document Set ID: 22570982
Version: 1, Version Date: 05/09/2023
Page 8
DISCLAIMER
Information provided in this report is subject to copyright laws and is intended for the noted recipient(s)
only. This report remains the property of Biodiverse Environmental and may not be copied,
reproduced or submitted in whole or in part without the express permission of the author. Biodiverse
accepts no responsibility for any person or third party who may use or rely upon the concept of this
report, liabilities or cost incurred as a result of the information being inaccurate or incomplete in any
way for any reason. Parts of this report may contain information originally prepared by other parties –
in these cases these sources are cited. All advice is provided based upon information sources current
at time of report preparation. Biodiverse Environmental and the authors do not accept any form of
liability, be it contractual or otherwise, in respect of the data, errors, or omissions arising, through
misinterpretation of information, negligence or otherwise, however caused.
LEGISLATION
Under the Nature Conservation Act 1992 (NCA), Queensland's native wildlife is protected. A person
who intends to move, take, use or keep native fauna requires an appropriate permit to do so. Where
approved land clearing activities may result in displacement of native wildlife, Biodiverse is permitted
to observe or relocate animals under Rehabilitation Permit Number WA0043580.
STATEMENT OF QUALIFICATION
Biodiverse Environmental is a certified Fauna Spotter Catcher service provider under the NCA and
an independent environmental consultancy with appropriate experience to undertake fauna handling
and management, environmental and ecological surveying and reporting, and land management
activities.
Biodiverse Environmental holds a current Rehabilitation Permit and Damage Mitigation Permit under
the Nature Conservation (Administration) Regulation 2017 and Scientific Purposes Permit under the
relevant Nature Conservation (Animals) Regulation 2020.
Biodiverse Environmental and their endorsed employees can carry out:
- Spotter catcher activity under Rehabilitation Permit WA0043580 valid to 12 May 2025
- Removal and relocation of protected animals under Damage Mitigation Permit WA0015031
valid to 12 April 2025
- Taking a protected animal for scientific purposes under Scientific Purposes Permit
WA0026563 valid to 07 September 2025.
FAUNA MANAGEMENT PLAN | Summit Road, Pomona i
Document Set ID: 22570982
Version: 1, Version Date: 05/09/2023
Page 9
DOCUMENT CONTROL
Biodiverse Project
PR0704
Reference No.
Decision Notice
RAL22/0018
Application No.
Document Title PR0704-Base Architecture-Pomona-FMP-Rev0
Revision 0
Sina Kankaanpaa,
Prepared by 28/07/23
Ecologist
Jessica van Motman-Craig,
Reviewed by 28/07/23
Ecologist
Reviewed and Liam Pratt,
28/07/23
Approved by Director/Principal Ecologist
ACKNOWLEDGEMENTS
© All content including photos subject to Copyright
CONTACT DETAILS
Biodiverse Environmental
PO Box 320
Eudlo QLD 4554
0408 011 584
[email protected]
www.biodiverse-environmental.com.au
ABN: 18766198454
FAUNA MANAGEMENT PLAN | Summit Road, Pomona ii
Document Set ID: 22570982
Version: 1, Version Date: 05/09/2023
Page 10
CONTENTS
LIMITATIONS ................................................................................................................................... v
1. INTRODUCTION ....................................................................................................................... 1
1.1. Background ........................................................................................................................ 1
1.2. Purpose .............................................................................................................................. 1
1.3. Focus and Scope................................................................................................................ 1
1.4. Site Location ....................................................................................................................... 2
2. METHODS ................................................................................................................................ 5
2.1. Desktop Assessment .......................................................................................................... 5
2.2. Site Inspection .................................................................................................................... 5
3. RESULTS .................................................................................................................................. 6
3.1. Desktop Assessment .......................................................................................................... 6
3.1.1. Matters of National Environmental Significance ........................................................... 6
3.1.2. Matters of State Environmental Significance................................................................ 6
3.1.3. Matters of Local Environmental Significance ............................................................... 6
3.1.4. Fauna .......................................................................................................................... 8
3.2. Site Inspection .................................................................................................................. 10
3.2.2. Fauna ........................................................................................................................ 11
3.2.3. Habitat Features ........................................................................................................ 12
4. ISSUES AND MANAGEMENT STRATEGIES ......................................................................... 17
4.1. Presence of CREVNT Fauna ............................................................................................ 17
4.2. Vegetation Clearing .......................................................................................................... 19
4.3. Fauna Management During Clearing ................................................................................ 21
4.4. Animal Welfare ................................................................................................................. 25
4.5. Providing Safe Passage for Fauna ................................................................................... 27
4.6. Control of Feral, Domestic and Companion Animals ......................................................... 28
4.7. Habitat Rehabilitation and Protection ................................................................................ 29
5. DISCUSSION ............................................................................................................................. 31
APPENDIX I Protected Matters....................................................................................................... 32
APPENDIX II Plant Survey ............................................................................................................. 33
FAUNA MANAGEMENT PLAN | Summit Road, Pomona iii
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Page 11
LIST OF FIGURES
Figure 1. Site location ....................................................................................................................... 3
Figure 2. Development layout and tree retention plan, with rehabilitation area highlighted................ 4
Figure 3. Noosa Plan 2020 Planning Scheme Biodiversity, Waterways and Wetlands Overlay......... 7
Figure 4. Vegetation community i- Open landscaped lawns ............................................................ 10
Figure 5. Vegetation community ii- Slash pine plantation ................................................................ 10
Figure 6. Vegetation community iii- E. grandis open forest ............................................................. 11
Figure 7. Fauna release locations and clearing direction ................................................................ 24
LIST OF TABLES
Table 1. CREVNT fauna with a moderate to high likelihood of occurring on Site (DES Species Profile
and Threats Database and DES Conservation Advice). .................................................................... 9
Table 2. Habitat features identified during Site inspection ............................................................... 13
Table 3. Strategies to manage the presence of CREVNT fauna ..................................................... 17
Table 4. Strategies to manage the impacts of vegetation clearing .................................................. 19
Table 5. Strategies to manage fauna during clearing ...................................................................... 21
Table 6. Strategies to manage animal welfare ................................................................................ 25
Table 7. Strategies to provide safe passage for fauna .................................................................... 27
Table 8. Strategies to manage feral, domestic and companion animals .......................................... 29
Table 10. Strategies to rehabilitate and protect retained habitat...................................................... 29
FAUNA MANAGEMENT PLAN | Summit Road, Pomona iv
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Page 12
LIMITATIONS
• This report has been prepared by Biodiverse Environmental for Base Architecture.
• The services undertaken by Biodiverse Environmental in connection with preparing this report
were limited to those specifically detailed in the Fauna Management Plan and are subject to the
scope limitations set out in the report.
• The opinions, conclusions and any recommendations in this report are based on conditions
encountered and information reviewed at the date of preparation of the report. Biodiverse
Environmental has no responsibility or obligation to update this report to account for events or
changes occurring after the date that the report was prepared.
• The opinions, conclusions and any recommendations in this report are based on information
obtained from contemporary research and recommended best practice measures.
• Site conditions (including the presence of additional conservation significant species and/or their
habitat) may change after the date of this report. Biodiverse Environmental does not accept
responsibility arising from, or in connection with, any change to the Site conditions.
FAUNA MANAGEMENT PLAN | Summit Road, Pomona v
Document Set ID: 22570982
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Page 13
1. INTRODUCTION
1.1. Background
Biodiverse Environmental has been engaged by Base Architecture to prepare a Fauna Management
Plan (FMP) for works involving Reconfiguration of a Lot – 1 into 2 lots at 43 to 45 Summit Road,
Pomona (Lot 3 SP 186019/ Lot 2 on RP186019).
1.2. Purpose
The purpose of this report is to present information on the fauna and habitat features present within
the Site to assist the management of development and provide framework for the long-term
management of the Site. This report provides a consolidated management document to mitigate
impacts and protect native fauna during the approved clearing and construction activities, notably
conservation significant fauna (i.e., listed under the NC Act 1992 or EPBC Act 1999 as Critically
Endangered, Endangered, Vulnerable or Near threatened, henceforth CREVNT).
This report has been prepared to meet the requirements of Noosa Shire Council’s response to the
affiliated development application, with Clause 13 of approval conditions stating that “Vegetation must
only be removed or disturbed in accordance with a Fauna Management Plan (or part thereof) prepared
by a qualified person* and endorsed through an Operational Works approval”.
This report presents data collated from contemporary research, a review of previous studies in the
area and a Site inspection conducted on the 3rd of July 2023. Previous studies reviewed include:
• Bushfire Mitigation Report FM 5810-6 prepared by Eldon Bottcher Architect Pty Ltd.
• Ecological Assessment Report prepared by 28 South Environmental.
An associated Rehabilitation Management Plan has been prepared to address revegetation and
ecological enhancement outside of the clearing areas.
1.3. Focus and Scope
This FMP has been structured with a focus on the issues pertaining to management of fauna, and it
is envisaged that many activities will require the implementation of more than one component of the
FMP. This FMP refers to the statutory environmental and fauna management requirements as they
may apply, pursuant to all relevant policies, standards and regulation, along with end-user
consideration. In addition, this report seeks to ensure that fauna and fauna habitat in adjacent
conservation areas is not inadvertently adversely impacted.
This assessment report aims to mitigate the risk of injury, orphanage, or death of fauna prior to, during
and post-construction by providing management guidelines for the following:
• Presence of CREVNT Fauna
• Vegetation Clearing
FAUNA MANAGEMENT PLAN | Summit Road, Pomona 1
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Page 14
• Animal Welfare
• Fauna Management During Works
• Providing safe passage for fauna
• Control of feral, domestic and companion animals
• Habitat rehabilitation and enhancement
Compliance with this FMP is compulsory and incorporates the use of expert consultants, including a
registered and Department of Environment and Science (DES) approved Fauna Spotter Catcher
(FSC). Section 4. Issues and Management Strategies outlines statutory requirements, and management
guidelines and policies of the Management Plan.
1.4. Site Location
The project Site is located at 43 and 45 Summit Road, Pomona formally described as Lot 3 on
SP186019 and Lot 2 on RP186019. The Lot comprises approximately 3.4 hectares and is zoned as
Rural Residential. Surrounding land use includes Low Density Residential and Environmental
Management and Conservation Areas. A map showing the Site in context of surrounding land has
been provided as Figure 1 and the proposed development Site layout and tree retention plan in Figure
2.
The Site has been historically cleared, leaving approximately 20% of the Site as remnant vegetation.
A small pocket of Regional Ecosystem type 12.3.1a is present in the south-west corner. This RE is
described as gallery rainforest (notophyll vine forest) on alluvial plains and provides habitat for
Coxen's fig parrot (Cyclopsitta diophthalma coxeni) and Richmond birdwing butterfly (Ornithoptera
richmondia).
The far-eastern portion of the Site is mapped as RE 12.9-10.1, described as tall open forest often with
Eucalyptus resinifera, E. grandis, E. robusta and Corymbia intermedia on sedimentary rocks, usually
coastal. This ecosystem is known to provide suitable habitat for Koalas (Phascolarctos cinereus).
Two riverine drainage lines flow through the Site. Each is located within the mapped remnant
ecosystems, meeting north of the lot boundary and continuing to Six Mile Creek.
The proposed area of works and the vegetation management area addressed in this report do not
intercept any remnant ecosystem mapping. Vegetation within the development area contains a mix of
maintained native and exotic tree species and landscaped lawns. Dominant tree species include Slash
pine (Pinus elliottii), Mango (Mangifera indica) and Southern salwood (Acacia disparrima).
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SITE LOCATION
43-45 Summit Road, Pomona
Created by Sina Kankaanpaa
for Base Architecture on 05/07/2023
Legend
Highway
Main Road
Local Road
Site location
Figure 1. Site location
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Figure 2. Development layout and tree retention plan, with rehabilitation area highlighted.
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2. METHODS
2.1. Desktop Assessment
Prior to conducting the Site visit a comprehensive desktop analysis was undertaken. Species
information, including the collation of existing records for the survey area were obtained.
The Federal Government Department of Agriculture, Water and the Environment’s ‘Protected Matters
Search Tool’ (PMST) was used to generate a report that helped to determine whether Matters of
National Environmental Significance (MNES) or other matters protected by the Environment
Protection and Biodiversity Conservation Act 1999 (EPBC Act) are likely to occur on, or relate to, the
property.
The EPBC Act Protected Matters Report was used to identify listed threatened ecological
communities, and flora and fauna species, as well as their habitat that may occur or is likely to occur
within the property.
The Department of Environment and Science (DES) WildNet Database was consulted to identify
Matters of State Environmental Significance (MSES). The WildNet database supports Queensland’s
biodiversity and protected areas by providing important wildlife information that underpins
conservation policies, programs, and management responses.
Additionally, the local Noosa Shite Council Plan 2020 Planning Scheme was consulted to determine
Matters of Local Environmental Significance (MLES), specifically mapping overlays and development
codes pertaining to the project.
2.2. Site Inspection
The project area was assessed on the 3rd of July 2023 using a diurnal survey methodology following
a meander pattern, covering as much as possible of the Site. Arboreal, terrestrial, and aquatic features
were assessed.
This involved visually inspecting the project area for nests, hollows, burrows, arboreal termitarium,
waterbodies, anthropogenic (artificial) habitats, scratches, scats and tracks.
The ecologist also identified any fauna observed during the inspection. Detailed information about all
fauna and habitat features identified was recorded, and where possible, marked the habitat feature
with hi-visibility flagging tape for closer inspection during works.
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3. RESULTS
3.1. Desktop Assessment
3.1.1. Matters of National Environmental Significance
The following MNES were found to be applicable to the project area:
• Wetlands of International Importance (Ramsar Wetlands; approx. 40-50km downstream)
• Three [3] Listed Threatened Ecological Communities
• Fifty-four [54] Listed Threatened Species
• Fifteen [15] Listed Migratory Species.
Other matters protected under the EPBC Act relating to the Site includes twenty-two [22] Listed
Marine Species and the nearby Yurol Nature Refuge. The Site is not expected to support any Listed
Threatened Ecological Communities. The likelihood of occurrence of threatened species is detailed
in Table 1, where desktop records are ground-truthed against on-Site findings. The EPBC Act
Protected Matters Report is available in APPENDIX I Protected Matters.
3.1.2. Matters of State Environmental Significance
The following MSES were found to occur on, or relate to, the project area:
• 7a Threatened (endangered or vulnerable) wildlife (0.76ha or 21.7% of the subject lot)
• 7b Special least concern animals (0.76ha or 21.7% of the subject lot)
• 7c i Koala habitat area - core (SEQ) (0.72ha or 20.6% of the subject lot)
• 8a Regulated Vegetation - Endangered/Of concern in Category B (remnant) (0.76ha or 21.7%
of the subject lot)
• 8c Regulated Vegetation - Category R (GBR riverine regrowth) (0.28ha or 8.0% of the subject
lot)
• 8d Regulated Vegetation - Essential habitat (0.76ha or 21.7% of the subject lot)
• 8e Regulated Vegetation - intersecting a watercourse (0.3km)
All Regulated Vegetation and Koala habitat area applicable to the Site is located outside of the
proposed area of works. The MSES Environmental Report is available in APPENDIX I Protected
Matters.
3.1.3. Matters of Local Environmental Significance
The following MLES are mapped in the Noosa Plan 2020 Planning Scheme as pertaining to the Site:
• MSES Environmental Values and Area of Biodiversity Significance and a Stream Order 1-2
waterway, as per the Biodiversity, Waterways and Wetlands Overlay Map (i)
• Ecological Linkage, as per Strategic Framework Biodiversity and Environment Maps
• Riparian Buffer areas, as per the Riparian Buffer Overlay Map.
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Vegetation clearing boundaries do not overlap any mapped MLES (Figure 3) and building envelopes
have been positioned to comply with buffer zones outlined in overlay codes. Performance Outcomes
and Acceptable Outcomes of relevant Planning Scheme codes are available here: Noosa Planning
Scheme Biodiversity Overlay Code.
LEGEND
MSES Environmental Values
Biodiversity Significance
Connecting Habitat Area
Waterway
Riparian Buffer Area
Figure 3. Noosa Plan 2020 Planning Scheme Biodiversity, Waterways and Wetlands Overlay
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3.1.4. Fauna
A search of the PMST and WildNet databases was undertaken, identifying the species listed as
CREVNT under the NC Act and/or the EPBC Act that have potential to occur within 5 km of the project
area.
Searches returned a total of sixty-two [62] CREVNT fauna species. This included seven [7]
amphibians, nineteen [19] birds, thirteen [13] mammals, seven [7] reptiles, one [1] insect and fifteen
[15] migratory species. These search tools rate the likelihood of occurrence from ‘may occur’, ‘likely
to occur’ to ‘known to occur’ based on the presence of suitable habitat for foraging and/or breeding.
Due to the large list of species returned via this tool, an additional assessment was undertaken,
considering:
• whether the Site contained suitable breeding/roosting locations for the species; and
• whether the Site contained suitable foraging resources for the species.
Assessments determined that ten [10] species have a moderate to high likelihood of occurring within
the study area (Table 1). The clearing area is not expected to contain suitable habitat to support any
conservation significant species. Some species detailed in Table 1 may occur nearby, however are
unlikely to be found within the development area. Furthermore, the building envelopes have been
sited such that vegetation clearing and earthworks is not expected to impact on threatened ecological
communities or wildlife habitat as listed under national, state or local legislative frameworks.
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Table 1. CREVNT fauna with a moderate to high likelihood of occurring on Site (DES Species Profile and Threats Database and DES Conservation Advice).
Status
Fauna Name Habitat Requirements Likelihood of Occurrence
NCA / EPBC
Regent honeyeater Critically Primarily occurs in box-ironbark woodland, but also occurs in other E. robusta occurs on Site, and
(Anthochaera phrygia) Endangered forest types. Mainly feeds on nectar from eucalypts (e.g. Eucalyptus mistletoe may be present. Unlikely
robusta) and mistletoe, and prefers taller and larger diameter trees for to occur within development area.
foraging. Nests are usually placed in the canopy of mature trees with
rough bark.
South-eastern glossy black-cockatoo Vulnerable Feed almost exclusively on the seeds of sheoaks (Allocasuarina spp. No suitable nesting or feed trees are
(Calyptorhynchus lathami lathami) and Casuarina spp.). They nest in large hollows in both living and present within or adjacent to the
dead eucalypt trees. Eggs are laid from late January to early June. area of works. Unlikely to occur.
Red goshawk Endangered Occur in wooded and forested lands of tropical and warm-temperate May occur flying overhead, however
(Erythrotriorchis radiatus) conditions, and in riverine forests. Nests in large trees, frequently the suitable nesting trees do not occur
tallest and most massive in a tall stand. Habitat has to be open within area of works.
enough for fast attack and manoeuvring in flight, but provide cover for
ambushing of prey.
Australian painted-snipe Endangered Nest in a scrape in the ground near shallow wetlands, with areas of Site does not include suitable
(Rostratula australis) bare wet mud and both upper and canopy cover nearby. Thought to habitat. May occur flying overhead,
breed in response to wetland conditions. however will not be impacted.
Black-breasted buttonquail Vulnerable Nests consist of a scrape in the ground, lined with leaves, grass or Clearing area does not contain
(Turnix melanogaster) moss. Nests are well-concealed and placed in the buttress root of a suitable breeding habitat.
tree or sapling, the base of a fern or under a low bush or grass Rehabilitation area may contain
tussock. Breed from September to May. suitable nesting habitat.
Giant barred frog Endangered Found near larger streams in rainforest and moist hardwood forest, Site does not include suitable
(Mixophyes iteratus) under leaf litter or dense vegetation. May range up to 20m from habitat. Unlikely to occur.
streams on forest floor. Breeds in spring to autumn. Eggs are
depoSited under overhanging muddy banks.
Tusked frog Vulnerable Found in eucalypt forest close to ponds and slow-moving streams. Very likely to occur in rehabilitation
(Adelotus brevis) Breeds in spring to summer in leaf litter in a waterway. area. Unlikely to occur within area of
works.
Southern greater glider Endangered Most commonly occurs in tall, montane, moist eucalypt forests with Clearing area does not contain
(Petauroides volans) relatively old trees and abundant hollows. Breed between March and suitable breeding habitat.
June.
Koala Endangered Found in a range of forests containing Koala preferred food trees (e.g. Suitable habitat is available at the
(Phascolarctos cinereus) E. tereticornis). Breeds from September to February. eastern extent, however not within
the clearing area.
Grey-headed flying foxes Vulnerable Roosts are commonly found in gullies in vegetation with a dense May be present along waterways,
(Pteropus poliocephalus) canopy. Breeds in early autumn. however suitable roost trees are not
present within the clearing area.
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3.2. Site Inspection
3.2.1. Vegetation Communities
Vegetative structure identified on Site appeared consistent with desktop mapping of remnant regional
ecosystems. The Site can be separated into three [3] communities:
i. Open landscaped lawns with a mixture of scattered native and invasive species, including
Tuckeroo (Cupaniopsis anacardioides), Cocos palm (Syagrus romanzoffiana), Sweetgum
(Liquidambar styraciflua), White beech (Gmelina leichhardtii), Bunya pine (Araucaria Bidwillii),
Queensland maple (Flindersia brayleyan), Lemon-scented gum (Corymbia citriodora), Southern
salwood (Acacia disparrima) and Mango (Mangifera indica, Figure 4). A number of invasive
groundcover species are present in this area. Vegetation clearing works will occur predominantly
in this area.
Figure 4. Vegetation community i- Open landscaped lawns
ii. Slash Pine (Pinus elliottii) plantations at the northern and southern Site boundaries (Figure 5). As
per the approved development plan, these will be largely retained.
Figure 5. Vegetation community ii- Slash pine plantation
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iii. Open forest dominated by Flooded gum (Eucalyptus grandis) along both watercourses at the
eastern and western boundaries. Vegetation in these areas is generally mature with little mid-
storey cover. Additional species included Maidens wattle (Acacia maindenii), Pink bloodwood
(Corymbia intermedia), Brush box (Lophostemon confertus) and Tallowwood (Eucalyptus
microcorys, Figure 6). The community at the western waterway falls into the rehabilitation area.
See the RMP for details on rehabilitation and regeneration. The remnant vegetation at the eastern
boundary falls outside of the clearing area and will not be impacted by works.
Figure 6. Vegetation community iii- E. grandis open forest
No threatened flora was identified during the Site inspection. A full list of flora identified at the Site is
provided in APPENDIX II Plant Survey.
3.2.2. Fauna
While on Site, fauna species observed included Noisy miner (Manorina melanocephala), Laughing
kookaburra (Dacelo novaeguineae), Australian magpie (Gymnorhina tibicen) and Crested pigeon
(Ocyphaps lophotes).
Scats from a large macropod, most likely the Eastern Grey Kangaroo (Macropus giganteus) were
observed throughout the open landscaped areas. Fresh scratches were also found adjacent to the
western watercourse; however the species could not be confirmed. These are detailed along with
habitat features in Table 2.
The areas to be cleared provide only minimal habitat and resources, supporting fauna commonly
found in urban and peri-urban environments. Species such as Noisy miner are expected in these
areas with limited reliance on more complex forest ecosystems. Large hollow-bearing trees on the
clearing boundaries will be preferred by species such as Common brushtail possum (Trichosurus
vulpecula), as well as parrot species tolerant of urban disturbance.
There was no evidence of Koala occurrence on Site during the inspection, however they may still
occur during clearing works. Management actions in the event a Koala is located on Site during works
is detailed below in Section 4.1. Presence of CREVNT Fauna.
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3.2.3. Habitat Features
Eight [8] habitat features were recorded on Site during the inspection. Features within the clearing
area included multiple large woody debris piles, exfoliating bark, and man-made structures.
Vegetation clearing will not encroach on native flora communities on Site, however scattered
Eucalyptus trees, including Koala preferred food trees, are present in the clearing area. Connectivity
to remnant vegetation at the Site boundaries is only through species not generally utilised, herefore,
they are not expected to occur within the clearing area but may be present nearby.
Additional features which will not be affected by vegetation clearing works, however may be utilised
by fauna that can move into the clearing area, include waterbodies and termitaria. The arboreal
termitaria has a large hollow and can provide refuge for various reptile, bird, and mammal species.
Recorded habitat features are detailed in Table 2.
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Table 2. Habitat features identified during Site inspection
ID 01 Photograph
Description of habitat feature Waterbody
Status of habitat feature Active
-26.362242, 152.867513
Location of habitat feature
-26.361776, 152.864723
Two watercourses are present. These will not
Comments/Outcome
be impacted by vegetation clearing works.
ID 02 Photograph
Description of habitat feature Woody debris piles
Status of habitat feature Unknown
Location of habitat feature Throughout Site
Large woody debris piles are present
Comments/Outcome
throughout the clearing area.
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ID 03 Photograph
Description of habitat feature Large Eucalyptus with exfoliating bark
Status of habitat feature Unknown
Location of habitat feature -26.362316, 152.866256
Comments/Outcome Exfoliating bark on a Koala food tree.
ID 04 Photograph
Description of habitat feature Man-made structures
Status of habitat feature Unknown
-26.362019, 152.866682
Location of habitat feature
-26.362076, 152.866056
Comments/Outcome Multiple large structures are present.
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ID 05 Photograph
Description of habitat feature Kangaroo scat
Status of habitat feature Active
Location of habitat feature Throughout Site
Comments/Outcome Scats present throughout open grassed areas.
ID 06 Photograph
Description of habitat feature Scratches
Status of habitat feature Inactive
Location of habitat feature -26.362126, 152.865188
Fresh animal scratches. No habitat features in
Comments/Outcome
the tree.
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ID 07 Photograph
Description of habitat feature Arboreal termitarium with hollow
Status of habitat feature Unknown
Location of habitat feature -26.361709, 152.864652
Large termite mound with a large hollow.
Comments/Outcome
Adjacent to western waterway- to be retained.
ID 08 Photograph
Description of habitat feature Terrestrial termitarium
Status of habitat feature Inactive
Location of habitat feature -26.362007, 152.864847
Termite mound adjacent to western waterway-
Comments/Outcome
to be retained.
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4. ISSUES AND MANAGEMENT STRATEGIES
The vegetation which will be cleared is heavily disturbed and not representative of any prescribed
ecological community, and clearing will therefore not impact on any threatened ecological community,
threatened flora, terrestrial or arboreal fauna, or migratory fauna. Vegetation clearing and earthworks
is also not expected to impact on mapped regulated vegetation areas or wildlife habitat.
To reduce potential adverse impacts on fauna during vegetation clearing works, Pre-Clearance habitat
and fauna assessments should be conducted, as well as employing a trapping program to reduce
fauna load prior to works commencing. To limit on-going and long-term ecological impacts, Base
Architecture should consider installation of suitable nest boxes into retained habitat. This will attract
fauna species to the area and enhance ongoing ecological integrity of native vegetation at the Site
and in adjacent bushland.
The sections below outline strategies to manage the impacts of vegetation clearing and associated
works on native fauna and their habitat, as well as the responsibilities of personnel involved in the
works. The management issues and impact strategies are relevant to all fauna and threatened species
which are known to occur on the Site or have the possibility of occurring. All vegetation clearing,
mulching and grubbing must occur in the presence of a suitably qualified Fauna Spotter Catcher (FSC,
see Table 5 for details).
4.1. Presence of CREVNT Fauna
As detailed in Table 1, the clearing area does not contain suitable habitat to support any fauna
species of conservation significance. However, listed species such as the Tusked frog and Koala
are expected to occur in the surrounding vegetation and may be encountered during works.
Strategies to manage their presence and mitigate adverse impacts are outlined below.
Table 3. Strategies to manage the presence of CREVNT fauna
Issue Presence of CREVNT fauna within the development area
Management Reduce direct and indirect effects on Koala (Phascolarctos cinereus) and other CREVNT
objective fauna that may occur.
Requirements Before works:
to implement
• All personnel are to attend a pre-start meeting and be familiar with this FMP.
• Tree protection and no-go zones must be clearly delineated and communicated
to all personnel.
• A suitably qualified FSC must assess vegetation to be cleared and the
surrounding area for Koalas (and other CREVNT and Least Concern fauna) as
part of a pre-clearance assessment.
During works:
• A register of all fauna encountered is to be maintained and updated daily by the
FSC/Ecologist.
• A register of all breeding places encountered and tampered with is to be
maintained and updated daily by the FSC/Ecologist.
• The FSC must continually assess the Site for Koalas:
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o If a Koala is present within 100m, clearing must cease temporarily and a
safe buffer must be determined by the FSC.
o The FSC must continue to assess the Koala for signs of distress.
o If the Koala comes down from the tree, clearing must cease until the FSC
determines it can continue.
o Vegetation must be cleared such that a corridor of Koala preferred food
trees is retained to allow safe passage for the Koala out of the work zone.
o Clearing cannot resume within the buffer area until the Koala has self-
relocated to an adequate distance.
After works:
• All impact management strategies implemented and their relative success at
mitigating risks to fauna are to be reported on.
Performance 1. Zero disturbance must occur outside the permitted clearing area.
indicators 2. Mortality and disturbance of fauna should be prevented.
3. Suitable habitat within areas not scheduled for clearing remain functional and
stable ecosystems.
Personnel Base Architecture is held accountable for:
responsible
• Ensuring all relevant permits have been approved prior to commencing works.
• Ensuring all contractors are able to comply with this management plan.
• Ensuring habitat connectivity is maintained through corridors of retained
vegetation.
• Ensuring a suitably qualified FSC undertakes a Pre-Clearance survey to identify
habitat features and reduce fauna load prior to clearing within two [2] weeks of
clearing.
• Ensuring a suitably qualified FSC is present for all vegetation clearing.
The Clearing Contractor is responsible for conducting vegetation clearing in
accordance with this management plan.
The FSC / Ecologist is responsible for:
• Undertaking a thorough Pre-clearance survey, safely capturing fauna and
releasing fauna into suitable habitat and under suitable conditions.
• Maintaining detailed records of fauna interactions and fauna habitat cleared, as
well as preparing reports.
All personnel are responsible for upholding animal welfare by preventing and / or
minimizing the risk of distress, injury, illness, orphanage, predation, or death of fauna.
Reporting and The FSC / Ecologist is responsible for:
auditing
• Reporting on the number of hollows, hollow recruitment trees and arboreal
termitaries lost as a result of clearing works.
• Providing a Pre-Clearance Report, detailing all habitat features and/or breeding
places in the clearing area.
• Providing a Post-Clearance Report, detailing the clearing of any native
vegetation, including any fauna found and or relocated, and the details of all
habitat features removed during works.
• Maintaining fauna interactions and breeding place registers, to be submitted to
Base Architecture.
Base Architecture is responsible for providing the fauna interaction register, breeding
place register and Post-Clearance Report to DES within 6 months of works
commencing.
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Corrective In the event that practices are inconsistent with the strategies outlined in this FMP, the
action contractor should take the corrective steps and report non-compliance to the relevant
personnel.
The Tusked frog requires maintenance of suitable pond or stream conditions for its
continual successful breeding. If vegetation clearing impacts on the watercourses,
corrective actions must be taken immediately to minimize potential adverse impacts.
Timing The duration of the construction period.
4.2. Vegetation Clearing
Clearing of native vegetation can result in the direct injury or death of fauna. Clearing of the vegetation
on Site can also damage fauna habitat within retained vegetation. Grubbing can have additional soil
degradation impacts. Disturbing the soil by removing roots and ground cover will leave it exposed to
the elements and potentially increase erosion towards the watercourse. Exposed soil can also change
in structure, and sedimentation into the waterway can alter water quality. Further information regarding
soil disturbance, Site stabilisation, and erosion controls is provided in the RMP.
Table 4. Strategies to manage the impacts of vegetation clearing
Issue Fauna habitat and vegetation clearing
Management Reduce direct and indirect effects on fauna during the clearing processes.
objective
Requirements Clearing shall only occur once all approvals have been granted.
to implement
Before works:
• All personnel are to attend a pre-start meeting and be familiar with this FMP.
• Everyone involved in the construction will be instructed on their duties in relation
to vegetation clearing protocols and protecting native fauna. Areas intended for
vegetation clearing should be clearly defined and notified in detail.
• The Vegetation Protection Zone/s (VPZ) are to be clearly delineated.
• All erosion controls must be in place to reduce sedimentation into the
watercourses.
• A suitably qualified FSC is to undertake a Pre-Clearance survey prior to each
day of clearing works. The FSC is to record all data pertaining to wildlife
interactions and clearly indicate all habitat features (i.e., with use of spray paint
or high-visibility flagging tape).
During works:
• All clearing is to be carried out in the presence of a suitably qualified FSC who
has the primary role of safely capturing and relocating fauna impacted by works.
• Removal of understory and scrub trees is to be conducted first, followed by the
removal of non-habitat trees.
• Non-habitat trees and coarse woody debris should be stockpiled.
• Clearing of non-habitat trees will only occur where their removal will not impact
on identified habitat trees (e.g. canopies do not interconnect with habitat trees).
• Hollows within trees will be identified in the field before commencing clearing.
These will be marked for inspection and may require dismantling using a
qualified arborist and a cherry picker or elevated work platform (EWP).
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• The FSC will:
o inspect each of the potential habitat features (usually hollows, dreys and
arboreal termite nests) to determine the presence of arboreal fauna. This is
carried out by simply looking into hollows with the assistance of a small
torch, however, burrow and bore-scopes can also be useful for deep
hollows.
o If fauna is located within a hollow, a towel or rag will be firmly lodged into the
entrance to prevent wildlife from experiencing additional distress or
attempting to escape due to a perceived threat.
o If an occupied Ringtail possum drey is encountered, the FSC should quietly
approach (i.e., avoid contacting other branches) the drey in the EWP bucket
and physically capture the possum by placing the entire drey in a catch bag
or only the possum if it emerges from the drey.
o Once the hollow entrance has been secured the arborist or FSC will cut the
entire hollow limb off below the cavity where the branch remains solid. In
circumstances where a hollow continues into the main stem of the tree, a
small window will be carefully cut into the hollow, allowing the FSC to plug
the hollow above and below the window.
o When the fauna has been safely secured within its hollow, the entire limb
can then be placed in the EWP bucket or lowered to the ground using ropes.
o This limb will then be placed in a cool, quiet location until translocation to the
recipient habitat Site, when at dusk the hollow entrance is re-opened to
allow the fauna to emerge of its own accord.
• If there is more than one work zone undertaking clearing or earthworks, there is
the requirement for at least one FSC per work front.
• Undertake sequential clearing - the direction of sequential clearing should be
away from road infrastructure and threatening environments, and towards
habitat links to ensure fauna are not moving through disturbed areas (Figure 7).
• Trees to be cleared along the boundary of the VPZ are to be felled inwards to
avoid damaging surrounding retained vegetation.
• All trees to be removed will be rechecked by a FSC prior to and after felling, to
ensure there is no fauna present.
• All trees that are to be stockpiled overnight must be re-checked by the FSC prior
to mulching to ensure no fauna have relocated into the pile.
After works:
• Fauna should not be left in an isolated ‘island’ of habitat unless there is no other
option suitable.
• Cleared vegetation should be piled thoughtfully; kept away from waterways and
without causing damage to the surrounding habitat.
• Cleared vegetation must be piled in a way that will not disturb fauna movement.
• Large rocks and logs must be removed and placed in nearby vegetation to
provide shelter for fauna.
• Ongoing erosion controls must be in place to reduce erosion and sedimentation
into the watercourse.
Performance 1. Zero disturbance must occur outside the permitted clearing area.
indicators 2. Mortality and disturbance of fauna should be prevented.
Personnel Base Architecture is held accountable for:
responsible
• Ensuring all contractors have read and are able to comply with this
management plan.
• Ensuring a suitably qualified FSC undertakes a Pre-Clearance survey to identify
habitat features and reduce fauna load within two [2] weeks of clearing works.
• Ensuring a suitably qualified FSC is present for all vegetation clearing.
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The Clearing Contractor is responsible for:
• Conducting vegetation clearing in accordance with this management plan.
• Working with the FSC to relocate recovered hollows, logs and rocks.
The FSC / Ecologist is responsible for:
• Undertaking a Pre-Clearance survey, safely capturing fauna and releasing
fauna into suitable habitat and under suitable conditions.
• Maintaining detailed records of fauna interactions and fauna habitats cleared,
and preparing reports.
All personnel are responsible for upholding animal welfare by preventing and / or
minimizing the risk of distress, injury, illness, orphanage, predation, or death of fauna.
Reporting and The FSC / Ecologist is responsible for:
auditing
• Providing Base Architecture with a Pre-Clearance Report detailing how any
additional habitat features will be managed.
• Reporting on the number of hollows, hollow recruitment trees and arboreal
termitaria lost as a result of clearing works.
• Providing a Post-Clearance Report, detailing the clearing of any native
vegetation, including any fauna found and or relocated, and the details of all
habitat features removed during works.
Corrective In the event that practices are inconsistent with the strategies outlined in this FMP, the
action contractor should take the corrective steps and report non-compliance to the relevant
personnel.
Timing Pre-clearance survey to be completed no more than two [2] weeks prior to clearing.
An FSC/Ecologist is to be present for the duration of the vegetation clearing and
mulching works.
4.3. Fauna Management During Clearing
To manage fauna during works, a suitably qualified FSC must be engaged. The FSC bears sole
responsibility for handling and relocating fauna impacted by works.
Table 5. Strategies to manage fauna during clearing
Issue Fauna management during vegetation clearing works
Management Locate and safely release native fauna into suitable habitat.
objective
Requirements to A suitably qualified FSC is to be present on Site during all vegetation clearing,
implement mulching, and grubbing works. Essential qualifications and experience include:
o Venomous snake handling certificate
o Fauna Handling experience / fauna handling certificate
o First Aid and CPR
o Competent in Fauna ID and knowledge of habitat requirements
Before works:
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• Each day, the Site is to be thoroughly inspected by a suitably qualified FSC
to capture and relocate any fauna that has moved back into the impact area
overnight.
• All newly identified habitat features, and breeding Sites are to be marked with
flagging tape, and their planned mitigation measures are to be discussed with
the clearing crew.
• During this discussion, hazards to fauna dispersing away from the impact
Site should be discussed, such as predators, machinery, roads/traffic and
clearing operations.
• The FSC and clearing crew are to work collectively to determine the manner
and direction of clearing that best allowed fauna to safely self-relocate to
nearby suitable habitat.
During works:
• The FSC is to inspect habitat features and/or breeding places in cleared
vegetation for any fauna present.
• The FSC is to assess all fauna for injury, capture photographs if possible and
identify fauna to species level.
• Uninjured captured diurnal fauna are to be released into the closest suitable
habitat as soon as practicable. Suitable release locations are shown below in
Figure 7. Note: Aquatic fauna is not expected to occur, but frogs may be
present.
• Nocturnal fauna species are to be stored in a thermally suitable, quiet and
dark location and released at dusk into suitable habitat.
• The following environmental and ecological factors must be considered when
determining the timing and location of release:
o Habitat contains an adequate food supply and shelter.
o Weather, season, and time of day is appropriate for the species.
o Under circumstances which will not cause additional stress, such as
extreme weather conditions, the wrong time of day (i.e., nocturnal
species).
o In the appropriate social group. Some animals fare better if released into
social groups.
o Within 1km of the Site as per DES guidelines.
• Injured and orphaned fauna are to be secured in a thermally suitable, quiet
and dark location while assessments are made over the severity of injury.
• Viable fauna are to be transported swiftly to the closest vet or wildlife carer,
identified in Section 4.4 Animal welfare.
• Fauna suffering non-viable injuries are to be promptly euthanized, following
procedures outlined in the Code of Practice - Care of Sick, Injured or
Orphaned Protected Animals in Queensland (1992), or alternatively taken
immediately to a veterinary clinic for euthanasia.
• Hives of native bees (genus Tetragonula (syn Trigona) and/or Austroplebelia)
are to be salvaged during vegetation clearing works for relocation into the
retained vegetation.
After works:
• The FSC is to inspect habitat features and/or breeding places in cleared
vegetation for any fauna present.
Performance 1. Zero disturbance must occur outside the permitted clearing area.
indicators 2. Mortality and unnecessary disturbance of fauna should be prevented.
3. Suitable habitat within retained vegetation remain functional and stable
ecosystems, with safe passage for fauna.
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Personnel Base Architecture are responsible for:
responsible
• Ensuring the engaged FSC possesses all required qualifications.
• Ensuring that clearing works cease immediately if dictated by the FSC, e.g. if
a Koala is identified within 100m of works, or if injured fauna requires
immediate transportation to a veterinarian/carer.
The Clearing Contractor is responsible for:
• Communicating clearly with the FSC by use of radio, hand signals or other
agreed upon methods.
• Ceasing clearing and/or dewatering while the FSC is assessing fauna,
inspecting habitat features, transporting or relocating fauna, or is otherwise
engaged.
The FSC is responsible for:
• Managing all fauna during works.
• Maintaining detailed records of all fauna interactions and habitat features and
preparing reports.
Reporting and The FSC / Ecologist is responsible for:
auditing
• Providing Base Architecture with information pertaining to fauna
management during works, as part of the Post-Clearance Report.
• Maintaining a fauna register and submitting applicable returns to DES as per
permit requirements.
Corrective action In the event that practices are inconsistent with the strategies outlined in this FMP,
the Contractor should take the corrective steps and report non-compliance to the
relevant personnel.
Timing The duration of the clearing period.
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Figure 7. Fauna release locations and clearing direction
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4.4. Animal Welfare
The clearing of native vegetation has a high potential of negatively impacting fauna and may lead to
distress, injury, illness, orphanage, predation or death of fauna.
Table 6. Strategies to manage animal welfare
Issue Animal welfare
Management Prevent fauna deaths and reduce disturbance to fauna.
objective
Requirements to Before works:
implement
• Ensure that works are not undertaken under environmental conditions that
may result in additional impacts to fauna e.g. extreme weather.
• Ensure that works are timed to occur outside of key breeding seasons.
• A suitably qualified FSC is to undertake a Pre-Clearance survey within two
[2] weeks of works commencing, to identify any potential animal welfare
issues (e.g. active nests). Management strategies should be discussed,
including how clearing can be conducted to minimize the risk to fauna.
• As per Noosa council recommendation, a pre-clearing trapping program will
be implemented to target native ground-dwelling and arboreal fauna:
o Trapping must be undertaken for a minimum of four [4] nights prior to the
commencement of works.
o The following traps can be used:
i. Pitfall traps
ii. Small (Type A) Elliot traps- arboreal and terrestrial
iii. Large (Type B) Elliot traps- arboreal and terrestrial
iv. Cage traps
o Traps will be baited with a mixture of peanut butter, honey and oats.
During works:
• Ensure that the management strategies in 4.3. Fauna Management During
Works are implemented and followed by all personnel.
• Fauna handling and relocation must only be carried out by personnel with a
current Damage Mitigation Permit (DMP) and Animal Rehabilitation Permit
(ARP) from DES.
• FSCs are required to transport injured wildlife to the closest designated
veterinary clinic. Orphaned wildlife, for example unhatched bird eggs may be
relinquished to a suitably qualified wildlife carer. The clinics closest to the
Site are:
Sunshine Coast Vets
(8:30am – 5pm)
(07) 5485 0088
19 Reserve St, Pomona QLD 4568
Eumundi Wildlife Rehabilitation Centre
(6:30am – 5pm)
(07) 5442 8057
1411 Eumundi Noosa Rd, Eumundi QLD 4562
• Invasive and introduced fauna are to be managed ethically by the FSC. This
may include taking the animal to the nearest veterinary clinic for euthanasia.
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• A fauna incident register is to be updated daily throughout clearing
operations.
After works:
• The FSC must inspect all cleared vegetation and disturbed aquatic habitat for
fauna that may be present.
• Nest boxes can be placed in retained vegetation to offset lost habitat:
o Installation of nest boxes to compensate for the loss of hollows at a ratio
of 3:1 (i.e. three [3] nest boxes per hollow removed).
o Installation of nest boxes to compensate for the loss of hollow
recruitment trees at a ratio of 3:1 (i.e. three [3] nest boxes per hollow
recruitment tree removed).
o An FSC/Ecologist will determine suitable nest box types (target species)
to be commensurate of that identified on Site prior to and during clearing
works.
o Nest boxes should be selected to support a variety of fauna species, as
informed by the characteristics of hollows removed through clearing, and
observations of fauna made within the Site.
o An FSC/ Ecologist will identify suitable locations for nest box installation
with the following considerations:
i. Host tree species and health.
ii. Nest box height and aspect, for temperature regulation and fauna
entrance/exit behaviours.
iii. Availability of food and other resources.
iv. Away from predation or infestation by invasive species, e.g.
European bees.
o Nest boxes should be installed within two [2] months of clearing by a
qualified tree climbers.
o Nest boxes should be monitored at six-months [1], and one [1] and three
[3] year intervals to determine the effectiveness of the offset provided.
Summary reports should include information on occupancy and any
damage or maintenance required.
Performance 1. Zero disturbance must occur outside the permitted clearing area.
indicators 2. Mortality and unnecessary disturbance of fauna should be prevented.
3. Suitable habitat within retained vegetation remain functional and stable
ecosystems, with safe passage for fauna.
Personnel Base Architecture is held accountable for:
responsible
• Ensuring a suitably qualified FSC is present for all vegetation clearing.
• Working with the FSC to manage any animal welfare issues identified (for
example, active nests).
• Ensuring all personnel are reminded of their responsibility to uphold animal
welfare by preventing and / or minimizing the risk of distress, injury, illness,
orphanage, predation, or death of fauna.
• Ensuring all personnel understand that fauna is not to be handled by anyone
other than the licensed FSC.
• Ensuring that clearing works cease temporarily if an animal is injured, to
allow the FSC time to assess the level of injury and determine the next steps
required.
The Clearing Contractor is responsible for
• Communicating clearly and effectively with the FSC, by use of radio, hand
signals or other agreed upon methods.
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• Working carefully and under the impression that fauna may be concealed
within vegetation.
• Working with the FSC to manage any animal welfare issues identified.
• Not continuing to clear vegetation while the FSC is managing fauna.
The FSC / Ecologist is responsible for
• Undertaking trapping prior to vegetation clearing.
• Capturing and relocating fauna prior to and during works.
• Maintaining detailed records of fauna interactions and fauna habitats
cleared, and preparing reports.
• Determining suitable nest box numbers and types, and installation locations.
• Installation and monitoring of nest boxes.
Reporting and The FSC / Ecologist is responsible for:
auditing
• Maintaining a breeding place register.
• Maintaining a fauna register.
• Providing Base Architecture with completed registers for submission to DES.
• Providing Base Architecture with records of trapping as part of the Post-
Clearance Report, including:
i. Number and type of traps used, with GPS locations.
ii. Timing of trapping events.
iii. Captured fauna details and outcomes.
• If applicable, providing Base Architecture with a Nest Box Installation Report
and Nest Box Monitoring Reports, as necessary.
Corrective action Installation of nest boxes to offset lost habitat features.
Replacement or repair of nest boxes within two [2] months of receiving nest box
monitoring reports.
Timing Trapping will occur prior to the commencement of works.
Nest boxes should be installed within two [2] months of the completion of works.
Animal welfare must be managed for the duration of the development project.
4.5. Providing Safe Passage for Fauna
The following measures will be employed throughout the Site to reduce fauna habitat fragmentation
and facilitate movement.
Table 7. Strategies to provide safe passage for fauna
Issue Maintaining safe movement of fauna
Management Ensure safe movement of fauna within the retained habitat and decrease movement
objective opportunities through work areas.
Prevent fauna deaths and reduce disturbance to fauna.
Requirements to Fauna may attempt to relocate away from clearing operations and into neighbouring
implement lots.
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• Restrict or minimize vehicle and plant movement through Site while clearing
vegetation to reduce the chance of fauna-vehicle collision.
• Minimize vehicle movement through the Site pre-dawn and after dusk, which
are peak times of fauna movement.
• Ensure vegetation clearing is conducted in a manner that allows fauna to
relocate at their own volition, into areas that are not isolated islands of
vegetation (see Figure 7 and Table 5).
• Maintain and rehabilitate wildlife corridors to be retained through measures
including, but not limited to:
o Maintenance, rehabilitation, and protection of the waterbody at the eastern
boundary to facilitate movement of aquatic fauna.
o Nest box installation, as per Table 6.
Performance 1. Mortality and unnecessary disturbance of fauna should be prevented.
indicators 2. Fauna are not isolated on islands.
Personnel Base Architecture is required to:
responsible
• Inform all contractors, through means of a Site induction or pre-start meeting,
of their responsibility to abide by speed limits.
• Undertake rehabilitation measures as outlined above unless otherwise dictated
by Noosa Shire Council.
Reporting and Details of all fauna interactions, including injuries and/or deaths, are to be provided to
auditing the FSC/Ecologist for inclusion.
Corrective In the event that practices are inconsistent with the strategies outlined in the SMP and
action VDMP, the Contractor should take the corrective steps and report non-compliance to
the relevant personnel.
Timings The duration of vegetation clearing and construction works.
4.6. Control of Feral, Domestic and Companion Animals
Terrestrial vertebrate pest species that may be present within the Site include Cane toad (Rhinella
marina), Common myna (Acridotheres tristis), Red fox (Vulpes vulpes), House mouse (Mus
musculus), Black rat (Rattus rattus) and House gecko (Hemidactylus frenatus). Invasive fauna can
prey on and displace native fauna, degrade natural bushland and waterways, and spread invasive
plants, parasites, or diseases. Pest management is considered:
• During preparation for operational works.
• In on-going monitoring and management of retained and rehabilitated habitat.
The Biosecurity Act 2014 states that every person has a General Biosecurity Obligation to take all
reasonable and practical steps to minimise the risks associated with invasive animals under their
control.
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Table 8. Strategies to manage feral, domestic and companion animals
Issue Control of feral, domestic and companion animals
Management Minimize the impact of feral, domestic and companion animals on fauna within the Site
objective and adjacent areas.
Requirements to • Dogs and other companion animals are not permitted on Site.
implement • Discard waste in appropriate containers and reduce food sources available for
introduced rodents by:
o Promoting adequate housekeeping practices relating to food scrap
disposal.
o Provision of waste receptacles.
o Practice daily food waste removal.
o Provide communication with contractors to raise awareness of the impact
of invasive wildlife.
• All introduced fauna encountered by the FSC are to be euthanized ethically.
• Consult the Noosa Biosecurity Plan 2020 for specific legislative requirements.
Personnel Base Architecture is responsible for:
responsible
• Ensuring good housekeeping practices are enforced and adhered to on Site.
• Enforcing a ban on all dogs and companion animals on Site.
• Implementing reactive management if feral, domestic or companion animal
species are found to be adversely affecting local fauna.
The FSC is responsible for managing all invasive fauna humanely.
Corrective In the event that practices are inconsistent with the strategies outlined in the SMP and
action VDMP, the Contractor should take the corrective steps and report non-compliance to
the relevant personnel.
Timing The duration of the vegetation clearing works at a minimum.
4.7. Habitat Rehabilitation and Protection
Enhancement of retained habitat areas should be undertaken along with rehabilitation of the
western waterway. The following treatments and strategies in Table 10 will further benefit fauna within
retained habitat. See the RMP for detailed rehabilitation strategies.
Table 9. Strategies to rehabilitate and protect retained habitat
Issue Fauna habitat rehabilitation
Management Improve the habitat values for fauna within retained habitat.
objective
Requirements to • Consider installation of nest boxes to compensate loss of hollows and hollow
implement recruitment trees (Table 6).
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• Rehabilitate and maintain the western waterway. Ensure that any fences
erected in relation to this feature do not impede the movement of aquatic
fauna.
• Place any salvageable hollow tree limbs and other habitat features outside of
the clearing area to provide additional habitat:
o Suitable tree logs and root balls (above 400mm) that can be used as
habitat should be stockpiled and placed in covenant zone under the
direction of Site ecologist.
o Any Class 1 hardwood logs above 400mm diameter should be made
available to salvage for milling and used to build nest boxes. Biodiverse
Environmental can take suitable logs free of charge for this purpose.
• Contractors must adhere to all clearing boundaries and No-Go Zones.
Personnel Base Architecture are responsible for:
responsible
• Ensuring all contractors understand the expectations that hollow trees, coarse
woody debris and large rocks will be stockpiled for future placement within
retained habitat.
• Ensuring management of any erosion or sedimentation risks.
• Complying with all approval conditions of the Development Application
pertaining to habitat rehabilitation and landscaping.
The Clearing Contractor is responsible for:
• Working with the Fauna Spotter Catcher to relocate hollow trees, logs and
rocks.
The FSC / Ecologist is responsible for:
• Identifying habitat features for relocation.
• Communicating with other contractors to facilitate relocation of habitat.
• Determining the final quantity and type of nest boxes to be installed.
• Identifying suitable nest box host trees in retained habitat. The eastern extent
of the Site contains suitable host trees.
• Undertaking monitoring of nest boxes at the nominated time periods.
Reporting and If nest boxes are to be installed, the FSC / Ecologist is to provide a summary report
auditing detailing nest box installation, and subsequent reports detailing nest box monitoring
events.
Corrective Replacement or the repair of the nest boxes within 2 months of receiving the nest box
action monitoring reports.
Timings Nest boxes should be installed within 2 months of clearing works commencing.
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5. DISCUSSION
This FMP provides a consolidated management document to mitigate impacts and protect native
fauna during approved vegetation clearing works. It must be followed in conjunction with all other
approved plans, including the Rehabilitation Management Plan and the Bushfire Mitigation Report FM
5810-6.
Vegetation clearing shall only occur once all approvals have been granted and any necessary
environmental controls are in place. A FSC must be present for all vegetation clearing, mulching, and
grubbing works to mitigate adverse impacts and reduce disturbance to fauna.
The FSC, clearing contractors, and other on-site personnel must ensure works are undertaken in a
safe and professional manner with consideration for fauna management protocols at all times.
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APPENDIX I PROTECTED MATTERS
Protected Matters MNES
MSES Environmental Report
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APPENDIX II PLANT SURVEY
List sourced from Ecological Assessment Report prepared by 28 South Environmental – Attachment
6.
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Rehabilitation Management Plan
43 – 45 Summit Rd, Pomona
Report prepared for Base Architecture
Decision Notice RAL22/0018
Rev 0
NOOSA COUNCIL
APPROVED PLAN
OPW23/0084 5 SEPTEMBER 2023
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DISCLAIMER
Information provided in this report is subject to copyright laws and is intended for the noted recipient(s)
only. This report remains the property of Biodiverse Environmental and may not be copied,
reproduced or submitted in whole or in part without the express permission of the author. Biodiverse
accepts no responsibility for any person or third party who may use or rely upon the concept of this
report, liabilities or cost incurred as a result of the information being inaccurate or incomplete in any
way for any reason. Parts of this report may contain information originally prepared by other parties –
in these cases these sources are cited. All advice is provided based upon information sources current
at time of report preparation. Biodiverse Environmental and the authors do not accept any form of
liability, be it contractual or otherwise, in respect of the data, errors, or omissions arising, through
misinterpretation of information, negligence or otherwise, however caused.
LEGISLATION
Under the Biosecurity Act 2014 are biosecurity measures to safeguard our economy, agricultural
and tourism industries, environment and way of life, from:
• pests (e.g. wild dogs and weeds)
• diseases (e.g. foot-and-mouth disease)
• contaminants (e.g. lead on grazing land).
Under the Act, the Biosecurity Regulation 2016 sets out how the Act is implemented and applied.
Biosecurity is everyone’s responsibility, and we must all play a role to ensure we minimise biosecurity
risks to protect Queensland’s lifestyle, industries and environment from pests and diseases. All
Queenslanders have a general biosecurity obligation (GBO) under Queensland's Biosecurity Act
2014 to ensure you do not spread a pest, disease or a contaminant.
STATEMENT OF QUALIFICATION
Biodiverse Environmental is an independent environmental consultancy with appropriate experience
to undertake fauna spotter catching and fauna management, environmental and ecological surveying
and reporting, along with land, conservation, ecosystem and fire management activities in accordance
with federal, state and local laws and regulations.
The staff at Biodiverse Environmental are passionate about environmental management and are
respected leaders in their field. Our project managers and ecologists are experienced practitioners
in flora, fauna and environmental management projects and hold degrees in Science, Environmental
Science, Wildlife Biology, Animal Management, Horticulture whilst also possessing numerous industry
qualifications.
Biodiverse Environmental field staff possess the relevant qualifications and certifications to ensure
exceptional project delivery and adherence to safety on site to themselves and others including
Construction White Cards, 4x4 Driving, ACDC Licences, First Aid Certificates, current vaccination
status for Lyssa Virus, Venomous Snake Handling Certificates, Chainsaw Certificates, Working at
Heights and Confined Spaces Qualifications and various government, infrastructure certifications and
inductions.
LICENCES AND ACCREDITATIONS
Biodiverse Environmental holds a Ground Distribution Contractor Licence (Licence Number
GDC228935) granted to the company by the Department of Agriculture and Fisheries under the
Agricultural Chemicals Distribution Act 1966. This licence authorises Biodiverse Environmental to
carry out the business of ground distribution of herbicides.
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DOCUMENT CONTROL
Biodiverse Project
PR0704
Reference No.
Decision Notice
RAL22/0018
Application No.
Document Title PR0704-Base Architecture-Pomona-RMP-Rev0
Revision 0
Jessica van Motman-Craig,
Prepared by 28/07/23
Ecologist
Sina Kankaanpaa,
Reviewed by 28/07/23
Ecologist
Liam Pratt,
Approved by 28/07/23
Director/Principal Ecologist
ACKNOWLEDGEMENTS
© All content including photos subject to Copyright
CONTACT DETAILS
Biodiverse Environmental
PO Box 320
Eudlo QLD 4554
0408 011 584
[email protected]
www.biodiverse-environmental.com.au
ABN: 18766198454
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CONTENTS
LIMITATIONS ................................................................................................................................... 1
1. INTRODUCTION ....................................................................................................................... 2
1.1. Purpose .............................................................................................................................. 2
1.2. Background ........................................................................................................................ 2
1.3. Relevant Documents .......................................................................................................... 2
2. SITE DESCRIPTION ................................................................................................................. 3
2.1. Existing Vegetation ............................................................................................................. 4
2.2. Regional Ecosystems ......................................................................................................... 5
3. REHABILITATION.................................................................................................................. 6
3.1. Regeneration ...................................................................................................................... 6
3.1.1 Weed Species ............................................................................................................. 6
3.1.2. Weed Removal Technique .......................................................................................... 7
3.1.3. Weed Control Procedure ............................................................................................. 7
3.2. Revegetation ...................................................................................................................... 9
3.2.1. Planting Areas ............................................................................................................. 9
3.2.2. Species Selection ...................................................................................................... 12
3.2.2. Species Density......................................................................................................... 13
3.2.3. Revegetation Procedure ............................................................................................ 13
4. MONITORING ......................................................................................................................... 14
5. MAINTENANCE ...................................................................................................................... 14
5.1. Establishment and Maintenance Program ........................................................................ 15
5.2. Corrective Actions ............................................................................................................ 16
6. PERFORMANCE CRITERIA ................................................................................................... 17
7. RESPONSIBILITIES & REPORTING ...................................................................................... 18
LIST OF FIGURES
Figure 1. Site location map. .............................................................................................................. 3
Figure 2. Rehabilitation area (highlighted in yellow) – Site layout plan. ............................................. 4
Figure 3. Noosa Biosecurity Plan 2020 weed treatment guideline..................................................... 8
Figure 4. Viable planting area – western side of rehabilitation area................................................... 9
Figure 5. Viable planting area near entry gate - western side of rehabilitation area......................... 10
Figure 6. Potential planting area – eastern side of rehabilitation area. ............................................ 10
Figure 7. Rehabilitation area with viable planting areas highlighted. ............................................... 11
LIST OF TABLES
Table 1. Weed species observed in the rehabilitation area. .............................................................. 7
Table 2. Revegetation species selection ......................................................................................... 12
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Table 3. Establishment and maintenance program. ........................................................................ 15
Table 4. Corrective actions. ............................................................................................................ 16
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LIMITATIONS
• This report has been prepared by Biodiverse Environmental for Base Architecture.
• The services undertaken by Biodiverse Environmental in connection with preparing this report
were limited to those specifically detailed in the Rehabilitation Management Plan and are
subject to the purpose set out in the report.
• The opinions, conclusions and any recommendations in this report are based on conditions
encountered and information reviewed at the date of preparation of the report. Biodiverse
Environmental has no responsibility or obligation to update this report to account for events or
changes occurring after the date that the report was prepared.
• The opinions, conclusions and any recommendations in this report are based on information
obtained from contemporary research and recommended best practice measures.
• Site conditions may change after the date of this report. Biodiverse Environmental does not
accept responsibility arising from, or in connection with, any change to the Site conditions.
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1. INTRODUCTION
1.1. Purpose
Biodiverse Environmental has been engaged by Base Architecture to develop a Rehabilitation
Management Plan (RMP) for the works involving Reconfiguration of a Lot – 1 into 2 lots at 43 – 45
Summit Rd, Pomona (Lot 2 on RP186019 & Lot 3 on SP186019).
The RMP will fulfil Approval Condition 7 of Decision Notice RAL22/0018 stating “The land area
identified for rehabilitation on the approved plans must be rehabilitated and revegetated and removed
of all weed species listed in the following standards and legislation: a) declared plants under the Land
protection (Biosecurity Act 2014 and sub-ordinate Regulation 2016); b) Schedule 1, 2 and non-
scheduled invasive species listed in the Noosa Biosecurity Plan 2020”.
This report outlines the rehabilitation requirements for the environmental contractor undertaking the
works by providing details, procedures, and management requirements regarding rehabilitating,
revegetating, and removing weed species from the identified rehabilitation area.
1.2. Background
Biodiverse Environmental conducted a preliminary site inspection of the rehabilitation area on 3rd July
2023 at 43 – 45 Summit Rd, Pomona (henceforth referred to as the Site). This inspection was to
assess the condition of the Site, undertake a preliminary weed survey, and determine rehabilitation
works.
An associated Fauna Management Plan has been prepared to assist in the management of fauna
and habitat features during vegetation clearing and development at the Site.
1.3. Relevant Documents
Legislation pertaining to the proposed development Project include the Environment Protection and
Biodiversity Conservation Act 1999 (EPBC Act), which provides a framework for the protection of
biodiversity and matters of National Environmental Significance, and the Biosecurity Act 2014 as it
pertains to the management of biosecurity matters present on site.
Under Queensland’s Biosecurity Act 2014, all persons have an obligation to take reasonable and
practical measures to prevent or minimise the biosecurity risks associated with their activities or
dealings with the carriers of invasive plants.
The RMP contains data obtained from Noosa Council Approved Plans:
• Rehabilitation Management Plan prepared by 28 South Environmental.
• Ecological Assessment Report prepared by 28 South Environmental.
• Bushfire Mitigation Report FM 5810-6 prepared by Eldon Bottcher Architect Pty Ltd.
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2. SITE DESCRIPTION
The project Site is located at 43 – 45 Summit Road, Pomona formally described as Lot 3 on SP186019
and Lot 2 on RP186019. The Lot comprises approximately 3.4 hectares and is zoned as Rural
Residential. Surrounding land use includes Low Density Residential and Environmental Management
and Conservation Areas. A map showing the Site in context of surrounding land has been provided
as Figure 1.
The rehabilitation area is located at the western side of Lot 3, totalling 4,281m2 in area. An existing
waterway (dam) is present in the middle of the identified rehabilitation area. Figure 2 below shows
the proposed development Site layout map with the rehabilitation area outlined in yellow.
The site has been historically cleared, leaving approximately 20% of the Site as remnant vegetation.
This includes a small pocket of Regional Ecosystem 12.3.1a present in the south-west corner (in the
revegetation area) as well as the far eastern portion of the Site mapped as RE 12.9-10.1. Further
details regarding Regional Ecosystem vegetation are provided in 2.2. Regional Ecosystems.
Figure 1. Site location map.
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Figure 2. Rehabilitation area (highlighted in yellow) – Site layout plan.
2.1. Existing Vegetation
The existing vegetation at the rehabilitation area is predominantly sparse canopy and sub-canopy
trees dominated by Eucalyptus grandis (Flooded gum), Eucalyptus microcorys (Tallowwood), Acacia
maidenii (Maiden’s wattle), and Allocasuarina littoralis (Black she-oak) on the western side, with the
addition of Corymbia intermedia (Pink bloodwood) and Lophostemon confertus (Brush box) on the
eastern side. The existing vegetation in the rehabilitation area currently provides approximately 40%
canopy coverage of the area, varying where the native stands are located. The shrub and groundcover
layer consists of a combination of weed and native species.
An existing dam is located in the middle of the rehabilitation area with various native riparian
vegetation species also present along the banks. In some sections of the rehabilitation area,
approximately one third of the delineated area is observed to be riparian vegetation.
Figure 2. Vegetation present within the rehabilitation area.
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2.2. Regional Ecosystems
The rehabilitation area is primarily mapped as non-remnant vegetation. One small pocket of Regional
Ecosystem (RE) 12.3.1a is present in the south-western part of the rehabilitation area. Pre-clearance
RE mapping identifies the rehabilitation area as previously containing RE 12.3.11 and 12.3.2.
RE 12.3.1a:
Gallery rainforest (complex to simple notophyll vine forest) on alluvial plains; classed as endangered
under the Vegetation Management Act. Typical canopy species include Castanospermum australe,
Elaeocarpus grandis, Grevillea robusta, Cryptocarya obovata, Beilschmiedia obtusifolia, Dysoxylum
mollissimum subsp. molle, Pseudoweinmannia lachnocarpa, Argyrodendron trifoliolatum,
Planchonella australis, Ficus watkinsiana, F. macrophylla forma macrophylla, Aphananthe
philippinensis, Toona ciliata and Syzygium francisii. Emergent Eucalyptus grandis or Lophostemon
confertus may occur. Waterhousea floribunda and Tristaniopsis laurina may occur on banks of stream
channels. Typical sub canopy species include Cryptocarya triplinervis, Archontophoenix
cunninghamiana, Endiandra pubens, Arytera divaricata, Syzygium moorei and Macadamia spp.
Occurs on Quaternary alluvial plains and channels in areas of high rainfall (generally >1300mm).
Riverine. (BVG1M: 4b).
RE 12.3.11:
Eucalyptus tereticornis +/- Eucalyptus siderophloia, Corymbia intermedia open forest on alluvial plains
usually near coast; classed as of concern under the Vegetation Management Act. Corymbia
tessellaris, Lophostemon suaveolens and Melaleuca quinquenervia frequently occur and often form
a low tree layer. Other species present in scattered patches or low densities include Angophora
leiocarpa, E. exserta, E. grandis, E. latisinensis, E. tindaliae, E. racemosa and Melaleuca sieberi.
Corymbia trachyphloia and/or C. citriodora subsp. variegata may dominate on areas of Pleistocene
alluvia. Occurs on Quaternary alluvial plains and drainage lines along coastal lowlands. Rainfall
usually exceeds 1000mm/y. Contains Palustrine. (BVG1M: 16c).
RE 12.3.2:
Eucalyptus grandis tall open forest on alluvial plains; classed as of concern under the Vegetation
Management Act. Eucalyptus grandis +/- E. microcorys, Lophostemon confertus tall open forest often
with vine forest understorey ('wet sclerophyll'). Patches of Eucalyptus pilularis sometimes present
especially in vicinity of sedimentary rocks. Fringing streams and in narrow gullies in high rainfall areas.
Riverine. (BVG1M: 8a).
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3. REHABILITATION
The aim of this rehabilitation is to is to enhance the habitat value consistent with the Regional
Ecosystem and in a way that will encourage further ecosystem integrity. Works should be undertaken
in a manner which will minimise extensive light penetration and soil disturbance to reduce weed
germination/spread and soil erosion. Rehabilitation should not significantly reduce habitat quantity or
quality. Rehabilitation will assist in restoring, protecting, and enhancing the ecological values and
characteristics of the remaining regional ecosystem present on site.
A moderate amount of weed control is required before revegetation can occur. Conducting the weed
control required to fulfil Approval Condition 7 of Decision Notice RAL22/0018 will result in a slight
decrease of canopy coverage over the rehabilitation area and will require ongoing weed control works.
It is the responsibility of the engaged rehabilitation contractor to monitor the rehabilitation area for
erosion and sediment issues. Should vast areas become uncovered due to weed removal efforts, it
will be the responsibility of the contractor to ensure these areas are mulched and actively planted out
in a timely manner and monitored to ensure a proactive approach is taken for erosion and sediment
control requirements that may arise. If erosion and sedimentation occurs in the rehabilitation area,
further actions may be necessary and will be decided on by the rehabilitation contractor.
3.1. Regeneration
The initial regeneration works may be undertaken over a one-week period depending on the
environmental conditions, prior to going onto the maintenance program. Within this time frame weed
species are to be removed using appropriate removal techniques and in conjunction with
recommended methodologies outlined in the South East Queensland Ecological Restoration
Framework.
Works are to include:
• Identify native species
• Remove weeds away from native plants
• Undertake bush regeneration – to remove weed species
All vegetation areas to be rehabilitated will be swathed by appropriately qualified bush regenerators,
treating weed species with minimal disturbance to the ecosystem. At the end of these works the entire
site should be considered “clean”. This is defined as a point where all further works on the area is
only to maintain regenerating weed species.
3.1.1 Weed Species
In accordance with Approval Condition 7, the rehabilitation area must be removed of all weed species
listed as declared plants under the Biosecurity Act 2014 and schedule 1, 2 and non-scheduled
invasive species listed in the Noosa Biosecurity Plan 2020.
During the preliminary site inspection within the rehabilitation area, six [6] species of weeds listed
under the Biosecurity Act and Noosa Biosecurity Plan were observed and are listed in Table 1 below.
Different weeds may infiltrate the rehabilitation area during the development works and in the future
due to the surrounding disturbances. If additional weed species fitting the above requirements are
observed in the future, weed removal techniques and maintenance will be adjusted to include these
species.
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Table 1. Weed species observed in the rehabilitation area.
Weed species Biosecurity Act 2014 Noosa Biosecurity Weeds of National
Plan 2020 Significance (WoNS)
Senna pendula var. Non-scheduled
glabrata Invasive Species
(Easter cassia)
Schinus Category 3 Restricted Schedule 2 Invasive
terebinthefolius Invasive Biosecurity Matter
(Broad-leaved pepper
tree)
Lantana camara Category 5 Restricted Schedule 2 Invasive Yes
(Lantana) Invasive Biosecurity Matter
Ochna serrulata Non-scheduled
(Mickey mouse plant) Invasive Species
Cinnamomum Category 3 Restricted Schedule 2 Invasive
camphora Invasive Biosecurity Matter
(Camphor laurel)
Schefflera actinophylla Non-scheduled
(Umbrella tree) Invasive Species
3.1.2. Weed Removal Technique
A range of techniques may be employed to achieve the required results, such as, but not limited to
foliar spray, cut & paste, hand pull (manual removal), scrape & paste, frilling and mechanical removal.
Care should always be taken when completing these tasks including following operational, licensing,
and legislative requirements. All weed removal techniques utilized are to be in line with the South East
Queensland Ecological Restoration Framework.
Due to the proximity to the dam, the rehabilitation area is to be treated with a ‘frog friendly’ herbicide
such as Weed Master Duo or Roundup Biactive. Roundup Biactive has been specifically formulated
for use in environmentally sensitive areas by using surfactants that ensure a high level of safety to
aquatic organisms. Weedmaster Duo also contains aquatically approved surfactants that are frog
friendly and has full aquatic registration.
Herbicide application must be conducted by an appropriately qualified person in accordance with the
Agricultural Chemicals and Distribution Control Act. Application rates must follow the registered
product labels or applied in accordance with an Australian Pesticides and Veterinary Medicines
Authority (APVMA) permit where applicable.
3.1.3. Weed Control Procedure
Large patches of Lantana camara (Lantana) and Cinnamomum camphora (Camphor laurel) are
located throughout the whole rehabilitation area. Smaller scattered patches of Ochna serrulata
(Ochna), Senna pendula var. glabrata (Easter cassia), Schinus terebinthefolius (Broad-leaved
pepper tree), and Schefflera actinophylla (Umbrella tree) are also present throughout most of the
revegetation area.
A combination of foliar spray, cut & paste, and manual removal is recommended for the initial weed
control works on Site. To increase the viable planting space within the rehabilitation area, weed
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patches are to be treated with the cut & paste method with plant foliage and stems removed from the
area where possible. Manual removal technique is also be utilised for smaller weeds where possible.
To assist in the success of the revegetation planting, environmental weed grasses on site are to be
foliar sprayed before planting occurs. Additionally, mulching after the revegetation areas have been
sprayed will assist with revegetation, ongoing weed control, and maintenance.
Weed control works are to be conducted within an appropriate time of year for the species. The
rehabilitation works contractor is to consult the Department of Agriculture and Fisheries guidelines
(e.g DAF Lantana) as well as relevant local documents such as the Noosa Biosecurity Plan 2020
Calendar for Pest Plants in Figure 3 below.
After the initial weed control works are undertaken at the Site, signs of die-off should be evident within
3-4 weeks but may take longer due to the weed species being outside the optimal time for weed
control works. The main signs of die-off are significant yellowing of the leaves and plant.
Figure 3. Noosa Biosecurity Plan 2020 weed treatment guideline.
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3.2. Revegetation
Revegetation is required around the entirety of the rehabilitation area, focusing on a scattered planting
of small – medium trees to re-enhance the canopy coverage after weed control occurs in the area.
Ground covers and native grasses will be densely planted and utilized in areas where environmental
weed grasses are set to be removed. Revegetation of these areas will assist with long term prevention
of weed infiltration and improve existing vegetation health.
3.2.1. Planting Areas
Although reference documents state the rehabilitation area is 4,281m2, an existing dam is present in
the middle of the rehabilitation area, as well as current weed infestations reducing the viable planning
area. The section identified for rehabilitation on the eastern side of the rehabilitation area is also
currently unclear due to the lack of surveyor markings/pegs during the preliminary Site inspection and
GPS inaccuracies. After the initial weed control works are completed and all the viable planting space
can be accounted for, an accurate quantity of tube stock required for revegetation planting is to be
provided.
One of the viable planting areas along the dam at the western side of the rehabilitation area is shown
in Figure 4 below. Another viable planting area is the relatively clear section near the entry gate and
driveway also at the western side of the rehabilitation area (Figure 5). After initial weed control works
and mulching have been completed, infill planting can occur in these areas.
Figure 4. Viable planting area – western side of rehabilitation area.
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Figure 5. Viable planting area near entry gate - western side of rehabilitation area.
There is potential for a small amount of infill planting on the eastern side of the rehabilitation area
near the dam as seen in Figure 6 below. More potential planting areas on the eastern side of the
dam may be identified once weed control works occur and the eastern rehabilitation boundary is
defined on Site.
Figure 6. Potential planting area – eastern side of rehabilitation area.
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The following estimate of tube stock is for tendering purposes only and is not an accurate
representation of the quantity required. On Site ground-truthing after weed control works occur is
necessary to provide an accurate quantity. Final density required for rehabilitation areas is set out in
the criteria. Figure 7 below displays the viable planting area at the site, with the western side
highlighted in green and the eastern side highlighted in blue.
Figure 7. Rehabilitation area with viable planting areas highlighted.
Western side: Approximately 1000m2 Eastern side: Approximately 300m2
Estimated current plant coverage: 40% Estimated current plant coverage: 40%
Ground covers & grasses: over 20% of area Ground covers & grasses: over 60% of area
1 per 1m2 1 per 1m2
= 200 tube stock = 180 tube stock
Small trees: over 20% of area
1 per 3m2
= 66 tube stock
Medium trees: over 20% of area
1 per 5m2
= 40 tube stock
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3.2.2. Species Selection
Species are selected based on RE 12.3.1a and 12.3.11 with consideration for appropriate canopy
coverage and riparian buffer zone suitability. Planting on the western side of the rehabilitation area
will focus on small – medium tree species to re-enhance the canopy coverage and include ground
covers and native grasses. Planting on the eastern side of the rehabilitation area will focus on ground
covers.
It is crucial to select healthy stock and the appropriate species for the success of this project. The
following suggested list of plants is to be sourced in grow tubes from native nursery stocks such as
‘Coolum Community Native Nursery’, ‘Barung Landcare Native Plant Nursery’ or ‘Floribunda Bushcare
Nursery’. Care is to be taken to ensure purchased stock is healthy with vigorous growth, hardened off
and not overgrown or root bound.
Table 2. Revegetation species selection
Scientific Name Common Name
Elaeocarpus grandis White/blue quandong
Lophostemon confertus Brush box
Tristaniopsis laurina Water gum
Archontophoenix cunninghamiana Bangalow palm
Cryptocarya triplinervis Brown laurel
Waterhousea floribunda Weeping lilly pilly
Ficus coronata Sandpaper fig
Mallotus philippensis Red kamala
Dianella caerula Blue flax-lily
Lomandra longifolia Spiny-head mat-rush
Lomandra hystrix Green mat-rush
Hybanthus stellarioides Spade flower
Viola hederacea Ivy-leaved violet
Ottochloa gracillima Graceful grass
Oplismenus imbecillus Creeping beard grass
Themeda triandra Kangaroo grass
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3.2.2. Species Density
Species density is to be achieved through revegetation planting, natural recruitment, and retention of
native species.
• Grasses & ground covers – 0.5-1m centres
• Small trees – 2-3m centres
• Medium tree – 4-5m centres
Planting arrangement is to be consistent with plant abundance, spacing and groupings to mimic
natural conditions. Pioneer and fast-growing species are to be distributed throughout the planting to
produce a rapid canopy coverage to assist in the exclusion of weed species.
As outlined in section 3.2.1 Planting Areas above, a total of approximately 486 tube stock will be
required for the revegetation area. This includes 380 ground covers and grasses, 66 small trees, and
40 medium trees.
3.2.3. Revegetation Procedure
After initial weed control works are completed, Site preparation prior to revegetation will include
mulching the rehabilitation area with 100mm forest mulch or similar, taking care not to cover any
naturally recruiting natives.
Revegetation works should be undertaken as follows:
• Identify endemic species – clearly ID endemic plants and clear weeds away and where
required, mark individual plants or areas for easy recognition to minimise potential for off target
damage.
• Prepare the area for revegetation - Treat all existing weeds i.e., spot spray / wood weed
removal.
• Install tube stock
• Soak tube stock in NTS Nutri-Tech Black Gold (or similar product) prior to planting
• Using a mattock or similar tool dig a hole 20 – 30 mm greater than the height of the plant
container and twice as wide at the recommended densities
• Fertilise and hydrated water crystal each hole as per manufactures recommended rates
• Plant tube stock ensuring top of the planting medium is just below ground level
• Replace soil and firmly compacte around the tube stock
• Mound all excess soil around the individual to form a dam around the plant on the downhill
side
• Apply forest mulch (or similar) to aid in water retention
• Water thoroughly after planting- approximately 10 to 20L depending on site conditions
• Use an anti-transpirant product such as ‘Floraguard’ after watering
After all tube stock is planted, cardboard tree guards are to be installed around all tree species to
reduce the risk of plants being disturbed while establishing. Grasses and some ground covers do not
require tree guards. Tree guards are to be retrieved when plants reach waist height.
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4. MONITORING
Monitoring program begins upon completion of the revegetation and regeneration works. It is the
responsibility of the rehabilitation contractor to actively undertake monitoring and achieve the bi-
annual records. Data that should be collected includes:
• Average height of plants within the restoration area where planted (height in meters for tree,
shrub and groundcover species);
• Dominant species (qualitative description of the dominant species in each strata);
• Assessment of the health of vegetation within the restoration area;
• Percentage weed cover within the restoration area;
• Percentage of planted specimens survived;
• Notation of all natural deaths or illegal removal of any native plants; and
• Abundance of natural recruitment including native and exotic species.
Photographs shall be taken in cardinal directions at each monitoring site which is to consist of a 10 m
x 10 m plot. The plot should be marked with star pickets or flagging tape to allow for ease of
identification in the field. All works and chemicals used should be logged and documented as part of
the Monitoring Program. The restoration contractor should develop a pro-forma for the collection of
relevant monitoring information during all events to ensure consistency and comparability between
surveys.
5. MAINTENANCE
In addition to the monitoring, the maintenance program begins upon completion of the revegetation
and regeneration works. The aim of the maintenance schedule is to ensure bushland integrity is
achieved at the end of the program. Bushland integrity will be achieved by ensuring:
• High percent canopy cover
• High revegetation success rate
• Natural regeneration present
• Floristic and structural diversity consistent with the RE.
Subsequent weed control works will be required to remove any newly germinated weed species
before they become infestations. It is an essential aspect of any successful rehabilitation project and
if conducted in a timely manner can reduce on-going costs in the mid to long term.
The rehabilitation site is to be swathed by experienced bush regenerators, carefully hand weeding or
spot spraying weeds using knapsacks. All weed spraying is to be performed by ACDC licenced bush
regenerators as well as the company holding a Ground Distribution Licence.
All attempts must be made to reduce spray drift. Weed species seedlings, particularly grasses and
ground covers are not to be sprayed out and may require hand weeding to reduce the risk of applying
herbicide to non-target species. Weed Master Duo or a similar ‘frog friendly’ product when foliar
spaying should be used. Consideration must be taken when using Metsulfuron and application is only
to occur between September to April. An herbicide record sheet is to be completed when any herbicide
use occurs on site and is to be kept for 2 years.
The table below outlines the maintenance and monitoring schedule of the site and the required
actions.
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5.1. Establishment and Maintenance Program
Maintenance and monitoring works are to be undertaken on a regular basis. Table 3 below outlines
the maintenance and monitoring schedule of the site and the required actions.
Table 3. Establishment and maintenance program.
Works Year One Year Two Year Three
Watering If insufficient rainfall - watering Monthly monitoring: take Monthly monitoring:
is to be undertaken 3 times in action if required take action if required
the 1st week; 2 times in the 2nd
week after planting and once in
the 3rd week after planting. On-
going monitoring of soil
moisture depending on
weather conditions; take action
if required
Weed Control Monthly Bimonthly Quarterly
Application expected to vary Application expected to Application expected
according to season. vary according to to vary according to
season. season.
Mulching Initially during planting, then if If required Not required
required
Replacement Assess in 6 weeks, 3 months Replacement required if Replacement required
planting and 6 months; Replacement survival is < 95% if survival is < 95%
required if survival is < 90%
Additional Assess in 6 months; only Required if areas Not required
planting required in areas of insufficient insufficient in
establishment of canopy cover establishment of canopy
cover
Reporting Undertake bi-annually; provide Undertake bi-annually; Undertake bi-annually;
information to developer provide information to provide information to
developer developer
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5.2. Corrective Actions
Table 4 below outlines the corrective actions to be taken if an issue arises.
Table 4. Corrective actions.
Issue Monitoring Indicator Corrective Action
Low water Monthly; Plant wilting, die back, Implement an appropriate watering regime until
availability increase if in low soil moisture levels sufficient rain occurs
drought
Weed Monthly Large weed infestation Assess cause - off site sources, lack of mulch,
infestation out breaks; weeds existing seed bank etc., Implement appropriate
setting seed action - immediately undertake weed control,
increase maintenance schedule until under
control
Low growth Quarterly Height & canopy cover Assess cause - time of year, water availability,
rate projections below set high non endemic competition, low soil
criteria for each year nutrients, etc., Implement appropriate action –
increase watering schedule, weed control,
fertilise, etc; consider alternative species
Erosion, soil Monthly; after Loss of soil; formation of Assess cause – insufficient root systems, no
instability high rainfall rills ground cover, excessive runoff, etc.; Implement
events appropriate action - increase density of plants
with mat forming root systems; direct seed with
endemic grass species; install weed matting /
mulch etc.
Loss of Quarterly Die off or loss of Replace lost species at minimum 6 weeks prior
species individuals to end of maintenance period; consider
alternative species
Mulching Monthly Excessive weed growth Re-mulch where required
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6. PERFORMANCE CRITERIA
Year One
• Less than 10% weed and evidence of regular weed management
• Average tree height 1m with good health, vigour, and ground connection
• Less than 10% plant failure and evidence of supplementary planting
• Mulch to a minimum depth of 50-100mm in revegetation areas
• No rubbish present
Year Two
• Less than 5% weed and evidence of regular weed management
• Average tree height 1.8m with good health, vigour, and ground connection
• Less than 5% plant failure and evidence of supplementary planting
• Evidence of natural recruitment
• Mulch to a minimum depth of 100mm in revegetation area or adequate canopy cover to
suppress understorey weeds
• No rubbish present
Year Three
• Less than 5% weed and evidence of regular weed management
• Average tree height 3m with good health, vigour, and ground connection
• Less than 5% plant failure and evidence of supplementary planting
• The ground surface must not display any area devoid of vegetation coverage greater than
1.0 m² (within any 10.0 m² sample)
• Adequate canopy cover to suppress understorey weeds without additional mulch (except for
mulching to vegetation edge areas)
• No rubbish present
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7. RESPONSIBILITIES & REPORTING
All works outlined within this document are the responsibility of the developer to assign an appropriate
qualified bush regenerator, with a minimum of 5 years of experience in revegetation and regeneration,
certificate in Land and Conservation or equivalent, until the end of the maintenance period.
The quarterly monitoring and reports are to be undertaken by a suitably qualified bush regenerator
with a minimum of 5 years of experience. Reports are to be submitted to the developer containing
information on the maintenance, including watering, mulching, fertilising, weed control and other
necessary actions / rectification works completed during the “On Maintenance” period.
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