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BUSHFIRE HAZARD ASSESSMENT
AND MANAGEMENT PLAN
RESORT DRIVE, NOOSA SPRINGS,
NOOSA HEADS
PRECINCT F
LOT 7 SP178340
For
ALTUM CONSTRUCTIONS
AC1345BFIRE REV. 1
August 2016
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2
Document Control
Version Parenthood Authorised for Issue
No. Date Author Reviewer Name Document Status
0 03/08/2016 Julie Schubert Paula Duke Julie Schubert A
1 08/08/2016 Julie Schubert Paula Duke Julie Schubert V
A - Approval B – Building Approval C- Construction V – Version
T – For Tender X - Information P – Preliminary
The content of this document is provided in strict commercial confidence. The
content of this document shall not be disclosed to any third party, without the
express written authority of Duke Environmental. Copyright © Duke Environmental
2016.
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TABLE OF CONTENTS
1.0 INTRODUCTION ............................................................................................................................. 5
1.1 Preamble .................................................................................................................................. 5
1.2 Aims.......................................................................................................................................... 5
1.3 Site Location ........................................................................................................................... 5
1.4 Site Characteristics ................................................................................................................ 5
2.0 PROPOSAL DETAILS .................................................................................................................... 6
3.0 EXISTING GOVERNMENT INFORMATION................................................................................. 6
3.1 State Government .................................................................................................................. 6
3.2 Local Government.................................................................................................................. 6
4.0 DESKTOP BUSHFIRE HAZARD ASSESSMENT ....................................................................... 7
4.1 Methodology ........................................................................................................................... 7
4.2 Slope......................................................................................................................................... 7
4.3 Aspect ...................................................................................................................................... 7
4.4 Fire History .............................................................................................................................. 7
4.5 Vegetation................................................................................................................................ 8
4.6 Fuel Load ................................................................................................................................. 8
4.7 Predicted Fire Attack Routes and Sources........................................................................ 8
5.0 FIELD BUSHFIRE HAZARD ASSESSMENT............................................................................... 9
5.1 Methodology ........................................................................................................................... 9
5.2 Site Assessment..................................................................................................................... 9
5.2.1 Estimated Fuel Load (t/ha) .................................................................................... 9
5.2.2 Slope......................................................................................................................... 9
5.2.3 Aspect ...................................................................................................................... 9
5.2.4 Vegetation..............................................................................................................10
5.3 Additional Information – Nearest Fire Brigade ................................................................10
6.0 BUSHFIRE BEHAVIOUR ASSESSMENT ..................................................................................10
6.1 Potential Fireline Intensity (State Planning Policy 2014) ...............................................10
6.2 Asset Protection Zone .........................................................................................................10
7.0 RECOMMENDATIONS.................................................................................................................12
8.0 CONCLUSIONS ............................................................................................................................13
9.0 LIMITATIONS OF THIS STUDY ..................................................................................................13
10.0 CLOSURE ......................................................................................................................................14
11.0 REFERENCES ..............................................................................................................................15
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APPENDICES
APPENDIX A Drawings
Duke Environmental Drawing DE1345/02
Blackburne Jackson Design Drawing 7038-DA04-07
JFP Consultant Drawings M2652 VM01A-08A
APPENDIX B Site Photographs
APPENDIX C State Government Mapping
Regional Ecosystem Mapping
State Planning Policy Bushfire Hazard Areas Mapping
APPENDIX D Local Government Information
Noosa Plan Zoning Overlay
Noosa Plan Bushfire Hazard Overlay
Noosa Plan Biodiversity Overlay
Bushfire Hazard Overlay Code Response
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1.0 INTRODUCTION
1.1 Preamble
Duke Environmental was commissioned by Altum Constructions to undertake this
Bushfire Hazard Assessment and Management Plan. This document has been
prepared in response to Condition 12 of a Decision Notice issued by Council for a
Change to an Existing Approval (Ref: 132005.1133.4 (05/1133), dated 11 March
2016.
This Assessment and Management Plan has been compiled generally in accordance
with relevant aspects of the Natural Hazards Overlay Code of the Noosa Plan,
specifically Table 13.9 Bushfire hazard areas and the State Planning Policy (2014).
1.2 Aims
The aims of this study were to:
1) Provide assessment of the subject site with specific reference to Bushfire Hazard
Issues;
2) Provide discussion with regard to the Local and State Legislation.
Specific objectives involved the following:
- Site Assessment (vegetation communities/types);
- Desktop research (existing available government and other information); and
- State and Local Government agency consultation.
1.3 Site Location
The site is located at Resort Drive, Noosa Springs, Noosa Heads and is described as
Lot 7 SP178340 (Precinct F). The site is located approximately 2.5kms south of
Noosa Heads. Noosa Springs Golf and Spa resort is located to the west of the site on
Resort Drive. Residential units are located opposite the site to the west on Resort
Drive, with the golf fairways located behind these buildings. Precinct E2 (subject of a
separate development application) separates the site from Noosa National Park on
the southern boundary of the site. A Council Environmental Park adjoins the site to the
east.
Refer Duke Environmental Drawing DE1345/02 for Site Locality and Aerial
Photograph.
1.4 Site Characteristics
A large section of the site has been historically cleared, with remnant Allocasuarina
littoralis and Lophostemon confertus in the northern corner of the site. This lot has
been subject to historical sand mining and slopes from 12m to 15m (AHD) in the
centre of the site, before rising steeply to 30m. The site area of Lot 7 is approximately
4.262ha.
Refer Duke Environmental Drawing 1345/02 for Site Locality and Aerial Photograph
and Appendix B for Site Photographs.
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2.0 PROPOSAL DETAILS
The development will contain 151 units with associated infrastructure, car parking, and
communal resort facilities.
Refer Blackburne Jackson Drawing 7038-DA04-07 included in Appendix A for details.
3.0 EXISTING GOVERNMENT INFORMATION
A desktop survey was performed to collate existing government information relevant to the
proposal and this assessment. The following information was found to be applicable.
3.1 State Government
3.1.1 Regional Ecosystems
Regional Ecosystem mapping for the subject site indicates the presence of
R.E. 12.2.5 (Corymbia intermedia +/- Lophostemon confertus +/- Banksia spp.
+/- Callitris columellaris open forest on beach ridges usually on southern half
of bioregion) within the northern section of the site. The balance of the site is
mapped as Category X – vegetation not regulated under the VMA.
Refer Appendix C for Regional Ecosystems Mapping and details.
3.1.2 State Planning Policy
State Planning Policy interactive mapping indicates the northern section of the
lot contains an area of high potential bushfire intensity, which extends into the
conservation park to the east. This area on site generally correlates to the
mapped regional ecosystem. A small area of very high and high potential
bushfire intensity is mapped in the southern section of the site.
Refer Appendix C for copy of State Planning Policy bushfire hazard mapping.
3.2 Local Government
3.2.1 Local Authority Planning Scheme
The site is designated as “Semi-Attached Housing” under the Noosa Plan
zoning overlay.
Refer Appendix D for Local Authority Information.
3.2.2 Local Authority Bushfire Hazard Overlay
In accordance with the Noosa Plan Bushfire and Acid Sulfate Soils Overlay,
the site is mapped as Medium Bushfire Hazard area.
As the subject site is currently mapped under the Bushfire Hazard Overlay,
the Specific Outcomes under Table 13.9 of the overlay code are addressed in
Appendix D.
Also refer Appendix D for Local Authority Information, including excerpts from
relevant maps.
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3.2.3 Local Authority Biodiversity Overlay
Under the Noosa Plan Biodiversity overlay, a large area of the site is mapped
as Environmental Enhancement Area. Clearing of vegetation for the purposes
of an asset protection zone may require a response to the Biodiversity Code.
Refer Appendix D for Local Authority Information.
4.0 DESKTOP BUSHFIRE HAZARD ASSESSMENT
4.1 Methodology
Duke Environmental performed a Desktop Assessment of the site in terms of bushfire
hazard, relevant to the proposal. The site was assessed, generally against the
following criteria:
Slope;
Aspect;
Vegetation;
Fire History; and
Predicted fire attack sources.
Methodology was generally based on established best practice Bushfire Management
Guidelines and the requirements of the Noosa Plan Planning Scheme Policy 1 –
Information Council May Request. Additionally, calculations were undertaken in
accordance with State Planning Policy – state interest technical manual, Natural
Hazards, Risk and Resilience, A “fit for purpose” approach in undertaking natural
hazard studies and risk assessments.
4.2 Slope
Slope for various areas throughout the site was calculated using a generic “rise over
run” method, whereby vertical distance is calculated as a percentage of horizontal
distance, using a scaled plan with 1m contour intervals. The slope varies between 8%
and 14% (8 degrees max) for Precinct F. This includes the area of hazardous
vegetation in the conservation park to the east. The adjoining Lot 6 (Precinct E2) to
the south has a slope of 9 degrees.
Refer Blackburne Jackson Drawing 7038-DA04-07 included in Appendix A for details.
4.3 Aspect
The site aspect varies from south-west to west, whilst the adjoining Lot 6 has a
westerly aspect.
4.4 Fire History
Anecdotal evidence was obtained via telephone conversation on 21 October 2015
with Mr Brian Riley from Noosa Heads Fire Station.
Mr Riley advised that no fires have been recorded in the location of the site for the
past 6-7 years. He did advise however, the site has the potential for fire due to the
neighbouring National Park and Council Environmental Park. Mr Riley also advised
there was a fire in the National Park behind the sewage treatment plant approximately
2-3 years ago.
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Information was also obtained from Queensland Parks and Wildlife Service via email
dated 21 October 2015. Mr John McQueeney, Acting Ranger in Charge, advised the
last wildfire in the Noosa National Park was in 2014. Fires in the park have also
occurred in 1992, 1996 and 2008. Due to the vegetation type, fires in the area
experience very high intensity. There are no approved planned burns scheduled for
the section of Noosa National Park bordering the site.
4.5 Vegetation
The site is mapped as R.E. 12.2.5 (Corymbia intermedia +/- Lophostemon confertus
+/- Banksia spp. +/- Callitris columellaris open forest on beach ridges usually on
southern half of bioregion) within the northern section of the site. The balance of the
site is mapped as Category X – vegetation not regulated under the VMA.
Refer Regional Ecosystem Mapping in Appendix C for details.
4.6 Fuel Load
Fuel loads were estimated based on the vegetation communities mapped on the site.
Vegetation hazard classes and associated potential fuel loads have been determined
in accordance with Table 1 of the State Planning Policy – state interest technical
manual, Natural Hazards, Risk and Resilience, A “fit for purpose” approach in
undertaking natural hazard studies and risk assessments.
Table 4.1
Extract from Table 1 – Vegetation Hazard Classes (VHC) and associated
Potential Fuel Loads
VHC VHC Description Potential Fuel Load (t/ha)
2 Open forests/woodlands - 30
shrubby
6 Cypress and Casuarina 20
Also refer Section 5.2.1 for on-site assessment of fuel loads.
4.7 Predicted Fire Attack Routes and Sources
According to the Noosa Plan Bushfire Overlay, medium fire danger vegetation covers
the site and surrounding allotments, however these areas are mapped as High
potential hazard under the State Planning Policy.
Fire attack from the conservation park to the east is possible. The woody vegetation
on the ridge in this area is dominated by Lophostemon confertus and Callitris
columellaris with occasional emergent Eucalypt spp. The ridge area is bounded by
short heath/wetland vegetation to the east. Fire attack from the west is unlikely due to
current development and the golf fairways. Precinct E2 separates the site from the
national park to the south.
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5.0 FIELD BUSHFIRE HAZARD ASSESSMENT
5.1 Methodology
Methodology was generally based on established best practice Bushfire Management
Guidelines.
5.2 Site Assessment
Duke Environmental performed a Site Assessment on 19 October 2015 for
approximately two (2) hours over the site and adjoining Precinct E2 (Lot 6).
Methodology employed was aimed at providing a field based assessment of the site in
terms of bushfire hazard, relevant to the proposal. The site was assessed, generally
against the following criteria:
Estimated Fuel Load (t/ha);
Slope;
Aspect; and
Vegetation.
5.2.1 Estimated Fuel Load (t/ha)
Fuel loads were estimated for the various vegetation communities observed
on the site and the adjoining site to the east following site inspection. Potential
fuel loads have been determined in accordance with Table 1 of the State
Planning Policy – state interest technical manual, Natural Hazards, Risk and
Resilience, A “fit for purpose” approach in undertaking natural hazard studies
and risk assessments
Table 5.1
Estimated Fuel Loads
VHC VHC Description Potential Fuel Load (t/ha)
4 Heath communities 27
6 Cypress and Casuarina 20
7 Open forest/woodlands – 19
grassy
* Refer Section 6.1 for fuel hazard assessment details
5.2.2 Slope
The site assessment confirms the general details of the desktop assessment
regarding slope. The site was observed with topography generally analogous
with Undulating (>5% to 10%) to Rolling Hills (>10% to 20%), with the
exception of the steep sand slope central to the site which is devoid of
vegetation.
5.2.3 Aspect
Site assessment confirms that the building envelope is characterised by a
westerly aspect.
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5.2.4 Vegetation
The desktop assessment for vegetation has been generally confirmed by the
site assessment. However, we consider the understorey in the open forest
areas is dominated by heath, low grass and weed species, therefore VHC 7 is
considered more applicable than the mapped VHC 2.
Previously cleared areas of the site were dominated by weed species
including Sphagneticola trilobata (Singapore daisy), Pteridium esculentum
(bracken), Lycopersicon sp. (tomato plants), Lantana Camara (lantana) and
grass species. Vegetated areas were dominated by Callitris. columellaris and
Lophostemon. confertus with Allocasuarina littoralis and Banksia sp.
Evidence of historical burns was observed on the bark of several mature trees
within the Council Environmental Park bordering the access track on the
eastern boundary. The remnants of a small fire, less than 1m 2, were noted at
the junction of the Pubic Carpark on Resort Drive and the sand track
bordering the eastern boundary.
5.3 Additional Information – Nearest Fire Brigade
The nearest fire station is located at Noosa Heads, approximately 3km to the north of
the site.
6.0 BUSHFIRE BEHAVIOUR ASSESSMENT
6.1 Potential Fireline Intensity (State Planning Policy 2014)
As the current mapping within the Noosa Plan does not reflect the updated State
Planning Policy mapping, calculations to determine the Potential Fireline Intensity and
associated hazard score have been undertaken in accordance with State Planning
Policy – state interest technical manual, Natural Hazards, Risk and Resilience, A “fit
for purpose” approach in undertaking natural hazard studies and risk assessments.
This hazard score is calculated as follows:
Vegetation Hazard Class 4 – Heath communities – PFL = 27 t/ha
Note that the heath community has been selected as this community adjoins the site to the east
and has a higher hazard rating than the site vegetation.
FFDI = 40
Slope = 8 degrees
PFI = 0.62 x 272 x 40 x exp(0.069 x 8)
PFI = 31,398kW/m, High Hazard.
6.2 Asset Protection Zone
The Asset Protection Zone (APZ) or setback/safety buffer is land adjacent to the
hazardous vegetation that provides a firebreak to the development.
In accordance with the Noosa Plan Part 13 - Overlays, Table 13.9 Bushfire Hazard
Area, Section 13.34 Siting, design and construction; Probable Solution S7.1 states
that a setback distance from hazardous vegetation of 1.5 times the predominant
mature canopy tree height or 10m, whichever is the greater, is required.
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Based on statistical analysis of the tree survey data, the predominant canopy height is
10m. Therefore, a separation distance of 15m would be required between the
habitable structures and the hazardous vegetation, in accordance with the Code’s
Probable Solution. Refer to JFP Drawings M2652 VM01A-08A for building setback
distances.
We understand a minimum separation distance of 15m between the development and
the tree canopy on the eastern boundary is proposed. The buildings are separated
from the vegetation by a public walkway, the internal road linking to Precinct E and car
parking spaces. In accordance with the Australian Standard AS3959-2009
Construction of buildings in bushfire-prone areas, Table 2.4.5 (FDI 40), a separation
distance between 13m-<19m would require the elevations of buildings bordering the
Environmental Park (eastern boundary) to be constructed to a level to meet BAL-29.
Buildings with a separation distance of 19m-<28m would need to meet BAL-19
requirements on the eastern elevation. Required construction levels should be
confirmed with a Building Certifier prior to construction.
6.2.1 Bushfire Attack Discussion
The proposed minimum 15m setback distances for the proposed development
should provide adequate protection for buildings from potential fire attack. As
stated in the Australian Standard AS3959-2009 – Construction of buildings in
bushfire-prone areas, there is no guarantee that the building will survive every
bushfire event due to extreme weather conditions and the unpredictable
behaviour and nature of fire.
The proposed minimum 15m setback is considered appropriate for this site
based on the following:
The minimum setback distance of 15m is generally exceeded for most
buildings;
The buffer includes a non-vegetated area (the roadway and car
parking spaces) which separates the buildings from the vegetation;
Construction of buildings with a separation distance between13-<19m
will be in accordance with BAL-29 to minimise potential impact from
bushfire;
Construction of buildings with a separation distance between 19-<28m
will be in accordance with BAL-19 to minimise potential impact from
bushfire;
The proposed layout provides for a direct access route for evacuation
of the site to Resort Drive;
It is understood that the applicant is required to install eight (8) fire
hydrants as part of the development of this site and Precinct E2 (the
adjoining Lot 6). A bond of $189,000.00 is being held by Council for
this purpose;
Resort Drive will facilitate safe evacuation from the site if required, as
this road is bordered by the golf course to the west and leads away
from hazardous vegetation; and
A bushfire management and evacuation plan has been prepared for
the site by Altum Constructions.
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We consider bushfire prevention measures recommended in Section 7.0 of
this report to provide a level of protection to protect life and property on the
subject site.
7.0 RECOMMENDATIONS
We recommend the proposal be approved, in accordance with the proposed minimum 15m
separation distance. In addition, we provide the following recommendations for the proposal:
The minimum 15m separation distance (Asset Protection Zones) described in
Section 6.2 of this report to be provided between structures and the canopy of
adjoining vegetation.
Asset Protection Zones are to be maintained to reduce fuel loads and prevent
regrowth of woody vegetation. In this manner adequate access for firefighting
purposes can be achieved.
Construction of buildings with a separation distance between13-<19m to be in
accordance with BAL-29 to minimise potential impact from bushfire;
Construction of buildings with a separation distance between 19-<28m to be in
accordance with BAL-19 to minimise potential impact from bushfire;
Provision of fire hydrants on internal roads for access by firefighting services.
Landscaping is not to include plantings of eucalypt and other flammable species.
Plantings should generally involve local providence species with low fire risk. A
mowed grass buffer/setback between buildings and areas of vegetation is also
recommended.
Garden mulch applied in landscaped areas is to incorporate non-flammable material
such as pebbles or stone. Flammable mulch such as pine mulch or forest mulch is
not to be used, particularly within 5m of any structure.
Implementation of the Bushfire Management and Evacuation Plan prepared for the
site by Altum Constructions.
The following Body Corporate / Site Manager responsibilities be included in the
Community Management Statement for the development to further manage bushfire
risk:
a) Induction of staff to ensure awareness of Bushfire and Evacuation
Management Plan requirements;
b) Review the Bushfire and Evacuation Management Plan document
annually at the Body Corporate AGM with any changes to be made as
required;
c) Maintain all common landscape areas including:
Removal of combustible matter including leaves
Any new planting within the common areas must use fire retardant
species in accordance with the approved Vegetation Management
Plan.
d) Maintain a register of mobile phone numbers of owners and tenants and
provide an automated text message service to alert all residents and
tenants in the event of fire.
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e) Conduct tests and inspections of fire alarms in accordance with the
requirements of the Australian Standard 1851-2012 Routine service of
fire protection systems and equipment.
f) Conduct tests and maintenance on fire hydrants in accordance with
AS1851-2012.
8.0 CONCLUSIONS
Duke Environmental was commissioned by Altum Constructions to undertake this Bushfire
Hazard Assessment and Management Plan. The site is located at Resort Drive, Noosa Heads
and is described as Lot 7 SP178340.
The proposal consists of an application for a residential development comprising a total of 147
units with associated roads and infrastructure. The site was observed with topography
analogous with Undulating (>5% to 10%) to Rolling Hills (>10% to 20%).
Generally, based on the hazard scores we calculate the position of part of the development to
represent a high risk for bushfire attack, due to the site topography in this location and the
neighbouring Conservation Park.
The adopted predominant mature canopy tree height for the mapped hazardous vegetation
surrounding the proposed development is approximately 10m. The proposed building
envelopes allow a minimum 15m buffer to the canopy of this vegetation. The development on
site should include the removal of all hazardous vegetation and surface fuels on the site.
Based on the above assessment it is considered that the proposal be approved subject to the
recommendations in Section 7.0 of this report.
9.0 LIMITATIONS OF THIS STUDY
This study has been tailored to investigate issues at the area of interest, being Lot 7
SP178340, Resort Drive, Noosa Heads.
We consider that the study accurately reflects the status of environmental issues for the
proposed development at the time the study was undertaken. As stated in the Australian
Standard AS3959-2009:
“there is no guarantee that buildings will survive a bushfire event on every
occasion. This is substantially due to the unpredictable nature and behaviour
of fire and extreme weather conditions”
This report has been undertaken for the specific purposes of Altum Constructions, as detailed
in our correspondence to them, and is solely for the use of Altum Constructions.
This report is only to be used in full, and may not be used to support objectives other than
those set out herein, except where written approval, with comments, are provided by Duke
Environmental.
Duke Environmental accept no responsibility for the accuracy of information supplied to them
by second and third parties.
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- 14 - 10.0 CLOSURE Should further information be required please contact our office. Julie Schubert Paula Duke BEnvSc (in progress) MEngSc BAppSc(Chem) PGDipEd CEnv MEIANZ Environmental Technician Director For Duke Environmental For Duke Environmental AC1345BFIRE Rev. 1 August 2016 JS/js
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11.0 REFERENCES
1. Australian Standard, 2009. Construction of Buildings in Bushfire Prone Areas
AS3959-2009. SW Rural Fire Service, 2006. Planning for Bushfire Protection
2006.
2. State of Queensland (2014). State Planning Policy – state interest technical
manual, Natural Hazards, Risk and Resilience, A “fit for purpose” approach in
undertaking natural hazard studies and risk assessments.
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APPENDIX
A
DRAWINGS
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DRAWINGS
APPENDIX
A
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N
Subject Site
Lake Weyba
0 100 200 300 400 500m
SCALE 1:10, 000 A3
No Date Amendment ALTUM CONSTRUCTIONS
Design: J.S. APPROVED DOCUMENT STATUS CLIENT:
Drawn: J.S. FOR APPROVAL PROJECT: PROPOSED RESIDENTIAL DEVELOPMENT
.......................... (Not for Construction) Sheet of
Date: 21.06.2016 AT: RESORT DRIVE, NOOSA SPRINGS
Survey By: NOOSA HEADS DRAWING No:
Checked: P.M.D. DATE: ............. T/A Duke Environmental
DE1345/02
Datum: A.H.D. SIZE A3 ABN 53 111 368 944 TITLE: SITE LOCALITY
Page 18
PUBLIC WALKWAY RETAINING WALL
RETAINING WALL
PUBLIC WALKWAY CONNECTION TO PRECINCT E2
PUBLIC CARPARK
12650
16355
25600
16560
15895
COVERED LINK
COVERED LINK
BLOCK G BLOCK G BLOCK F
BLOCK D BLOCK E BLOCK F T17 T17 BLOCK K
T17 T18 T17
T16 T16 T16 T4 T5 T5 T4
T16
BLOCK B
BLOCK A T4 T5 T5 T5 T4 BLOCK C
DRIVE T4 T5 T5 T5 T4
T4 T5 T5 T5 T4
WAY
PATH WAY
PATH
13
18
16 BLOCK E
LANDSCAPING
PATHWAY
15 17
17 PRECINCT E2
18
06
BLOCK U BLOCK T 14
T8
T6 T5 T5 T6 T6 T5 T5 01
02 05 T7 D D
BLOCK
03 17 T5
10
07
09 BLOCK L
T8 04 09 T7
WAY
19 13
PATH
20 17 T8
12 11
T5
T5
T5 T8
BLOCK S T5
T8 T7 T7
T5 POOL
T5
T7 T8
BLOCK M
BLOCK O
PAT
T5 T5
HW
T8 T8
T8
BLOCK N
AY
T8
RETAINING WALLS
Y
WA
TH
PA
BLOCK C
T2 T2
RESORT COMPONENT T1 BLOCK P
P T2 T2 T2 T2
SPATIAL USE T1 BLOCK Q BLOCK B
T1
T1 BLOCK R AI
N
BUILDINGS G.F.A. T1
T1 AT
E RM
ER
BLOCK A
W E W
S
01 RECEPTION PARKING
0Ø Ø
15 150
G
IN
02 ARRIVAL
ST IN
G
E
I
EX X IST
I V
E
03 RECEPTION 45.0m2 IN
R R MA
04 CONVENIENCE 60.0m2 D 200
Ø
WA
TE
05 CAFE 115.0m2 T IST
ING
06 OUTDOOR DINING 95.0m2 R EX
O
07 MULTIPURPOSE ROOM 22.0m2 S
E
08 BOULEVARD R
09 AMENITIES 65.0m2
10 BACK OF HOUSE 16.0m2
11 GYMNASIUM 49.0m2
12 POOL EQUIPMENT 14.0m2
13 POOL
14 TREE LINED BOULEVARD
15 OPEN LANDSCAPING
16 PLAYGROUND
17 BBQ PAVILION
18 OPEN SPACE
19 REFUSE ROOM 17.0m2
20 MANAGERS OFFICE 73.0m2
TOTAL G.F.A. 571.0m2
PROPOSED PRECINCT F DEVELOPMENT, ALTUM CONSTRUCTIONS DEVELOPMENT APPROVAL north
scale: 1:1000 @ A3
issue: 07 date: 22-07-16
NOOSA SPRINGS, NOOSA HEADS GROUND FLOOR 7038-DA04
The designs, drawings and specification are copyright and always remain the property of Blackburne Jackson Design Pty Ltd.
Page 19
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RETAINED - SUBJECT TO
DETAILED ARBORIST
ASSESSMENT
A. PROJECT MANAGEMENT
A.1_ General
A copy of the VMP (Council approved copy) is to be provided to all involved project stakeholders.
A.2_ Roles and responsibilities
Superintendent
The Superintendent will fulfill the duties as described within AS4000 and will be a RPEQ Civil Supervisor
and will project manage the civil contractor including clearing works.
Superintendent's Representative (SR)
The superintendent's representative delegated to manage vegetation issues will be the Landscape
Architect. The Landscape Architect will liaise and seek approval from the Council ecologist/
environmental officer regarding any change to the tree retention strategies described on the approved
VMP. The SR will organise the project arborist as required when any works are to occur under trees
illustrated on the VMP. No works are to occur until this approval is received from Council.
Contractor
The contractor is to follow the requirements of this VMP as part of their WUC. Instructions are to be
given by the Superintendent and his/her representative on the responsibilities and restrictions placed on
works with regards to the revegetation and rehabilitation of the site. The contractor is to advise the
superintendent whenever works are programmed around trees to ensure the arborist can be present.
Pre-Start Meeting with Council
At the commencement of works, a pre-start meeting is to be held between the Council, contractor, the
Superintendent and the Superintendent's Representative. This meeting is to inform the contractor of the
intent of the VMP and to help locate areas or trees that have specific requirements, and to set up a
system of regular inspections by the SR to ensure the VMP is being adhered to. Any tree protection
fencing (construction barriers) required as per Note B2 should be installed at this time for approval by the
Council.
B.1 Clearing Procedures:
e Prior to commencement of clearing operations, the site is to be inspected and locations of fauna and
fauna habitat noted by a qualified wildlife officer (fauna spotter) capable of assessing, treating and
relocating fauna.
e Allcleared vegetation, with the exception of fertile weed material, is to be chipped and stockpiled for
reuse on site or taken offsite for lawful disposal.
e Large hollow trees and logs are to be retained as habitat for terrestrial species.
e Any detection of a Koala will require a mandatory stopworks.
B.2 Clearing methodology
The nature of the supervised clearing operation will be such that any Fauna will have the opportunity to
retreat into any protected or uncleared areas of the site or adjacent the site. Clearing is to be staged ina
way that directs fauna to adjacent habitat areas beyond the clearing works. Clearing shall begin at the
furthest point from the desired habitat vegetation and be cleared towards it. The fauna spotter shall be
present during these operations to ensure safe travel for any fauna spotted in trees or in the vicinity.
B.3. Storage And Stockpiling
e Stockpile areas are to be located, away from drainage lines, native bushland, vegetation to be retained,
or tree protection areas.
e Protect all stockpiles from erosion and erect erosion protection barriers to the perimeter of stockpiles -
refer to Civil Engineering drawings for sediment and erosion control program, control measures,
monitoring, and maintenance procedures.
e Trees mulched for reuse on the site must be stockpiled and turned regularly for at least 3 months.
B.4 Corrective actions and reporting reporting
If a contractor is found to be clearing vegetation indicated to be retained in the Vegetation Assessment
Schedule (VAS) found in this VMP then penalties may apply, as enforced through the Local By-Laws of
Council. Where trees to be protected are damaged, replacement of damaged vegetation shall be solely at
the contractor's expense. Costs will be determined using Australian Standard DR 99307 : Amenity trees -
Guide to valuation unless approved.
Fix barrier mesh
with at least two
wire ties to each
SINGLE TREE
Protective fence to be
installed. Refer Note 1. If —r
there is inadequate space .
cil for this fence, refer to PLAN VIEW
Z Drawing B in this detail. Wrap trunk with low- .
3| grade geotextile fabric. <
°
g €
s 3mm thickness €
wire ties. Fix to 8
DOK batten with 2 a
MULTIPLE TREES on heavy duty
SS anised staples
~ Bay a ScHafood
> battens.
Star pickets Maximum
at ° spacings 50mm.
maximum 3m 3
centres.
PLAN VIEW PICKET DETAIL ELEVATION
Tree Protection Using Mesh [B| Protection of Individual Tree
Barrier dd where creators ae smo ave eg used
nearby.
(-_\ TREE PROTECTION DETAILS
XK) Not to Scale
| APPROVAL ISSUE
LEGEND
TREES TO BE RETAINED
AND PROTECTED
TREES POSSIBLE FOR RETENTION
THE INTENT IS TO RETAIN THESE TREES SUBJECT TO
DETAILED DESIGN
A» 7s, TREES FOR REMOVAL
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‘ >
PFA TREE PROTECTION FENCE
FILL
Refer Civil Plans
CUT
Refer Civil Plans
TREE PROTECTION ZONE
IPZ | as PER AS4970-2009
A FOR APPROVAL 2016-08-01 RC AG
ISSUE: DETAILS: DATE: INIT: CHK'D:
S—==
JFOP
URBANCONSULTANTS
IRN ANNA
PROJECT TITLE:
PRECINCT F
AT
NOOSA SPRINGS, NOOSA HEADS
FOR:
ALTUM
eee
VEGETATION
MANAGEMENT PLAN /
COVER SHEET
COPYRIGHT © 2013 JFP URBAN CONSULTANTS PTY LTD. THIS DOCUMENT MAY NOT BE COPIED
OR TRANSMITTED IN ANY FORM OR BY ANY MEANS IN PART OR IN WHOLE WITHOUT THE
WRITTEN CONSENT OF JEP URBAN CONSULTANTS PTY LTD.
PROJECT: PLAN: ISSUE: NORTH:
M2652L VMO1 A
SCALE: 1:750 @ Al
DATE: 01/08/2016
FILE NAME: M2652_VMP_PLANS - PRECINCT F.DWG
Page 20
APPROVAL ISSUE LEGEND TREES TO BE RETAINED AND PROTECTED TREES POSSIBLE FOR RETENTION Ly THE INTENT IS TO RETAIN THESE TREES SUBJECT TO DETAILED DESIGN "7 < TREES FOR REMOVAL ° || REFER VEGETATION ASSESSMENT SCHEDULE ac - \ ai SY laa WEED SPECIES e | REFER VEGETATION ASSESSMENT SCHEDULE Ww va LS ysVy Z “DEAD TREES e \ REFER VEGETATION ASSESSMENT SCHEDULE ARS a Tpr1 | TREE PROTECTION FENCE FILL Refer Civil Plans CUT Refer Civil Plans TREE PROTECTION ZONE IPZ | as PER AS4970-2009 A FOR APPROVAL 2016-08-01 RC AG ISSUE: DETAILS: DATE: INIT: CHK'D: SSS VEGETATION TO BE ! ‘\. RETAINED - SUBJECT TO Di “9 , | URBANCONSULTANTS ‘ Tha ! FiawrS IRN ANNA DETAILED ARBORIST PLANNERS BRISBANE - SUNSHINE COAST - CENTRAL QLD ASS ESSM E NT URBAN DESIGNERS BRISBANE - JFP House SURVEYORS 76 Ernest Street, —_____— South Brisbane Qld 4101 ENGINEERS _— p07 3012 0100 W wwwjfp.com.au LANDSCAPE ARCHITECTS —jFp URBAN CONSULTANTS PTY. LTD. A.C.N. 050.414 04! PROJECT TITLE: PRECINCT F AT NOOSA SPRINGS, NOOSA HEADS FOR: ALTUM eA eee VEGETATION MANAGEMENT PLAN COPYRIGHT © 2013 JFP URBAN CONSULTANTS PTY LTD. THIS DOCUMENT MAY NOT BE COPIED OR TRANSMITTED IN ANY FORM OR BY ANY MEANS IN PART OR IN WHOLE WITHOUT THE WRITTEN CONSENT OF JEP URBAN CONSULTANTS PTY LTD. PROJECT: PLAN: ISSUE: _NORTH: M2652L VMO2 A C1) SCALE: 1:200 @ A1 DATE: 01/08/2016 FILE NAME: M2652_VMP_PLANS - PRECINCT F.DWG
Page 21
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ASSESSMENT
RC AG
2016-08-01
FOR APPROVAL
A
INIT: CHK'D:
DATE:
DETAILS:
ISSUE:
- CENTRAL QLD
BRISBANE - SUNSHINE COAST
BRISBANE - JFP House
PLANNERS
URBAN DESIGNERS
76 Ernest Street,
SURVEYORS
ENGINEERS.
South Brisbane Qld 4101
P07 3012 0100 W www. jfp.com.au
LANDSCAPE ARCHITECTS —JFP URBAN CONSULTANTS PTY. LTD. A.C.N. 050.414 045
PROJECT TITLE:
PRECINCT F
AT
NOOSA SPRINGS, NOOSA HEADS
eA eee
YO!
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SNK
SS 4 VEGETATION
COPYRIGHT © 2013 JFP URBAN CONSULTANTS PTY LTD. THIS DOCUMENT MAY NOT BE COPIED
OR TRANSMITTED IN ANY FORM OR BY ANY MEANS IN PART OR IN WHOLE WITHOUT THE
WRITTEN CONSENT OF JEP URBAN CONSULTANTS PTY LTD.
MANAGEMENT PLAN
Neyiwia
ISSUE:
M2652L VMO03 A
PLAN:
PROJECT:
M2652_VMP_PLANS - PRECINCT F.DWG
1:200 @ A1
01/08/2016
SCALE:
DATE:
FILE NAME:
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Page 22
— | APPROVAL ISSUE
LEGEND
TREES TO BE RETAINED
AND PROTECTED
TREES POSSIBLE FOR RETENTION
THE INTENT IS TO RETAIN THESE TREES SUBJECT TO
DETAILED DESIGN
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ISSUE: DETAILS: DATE: INIT: CHK'D:
WS
ATS
FRAN ANNA
URBANCONSULTANTS
PLANNERS BRISBANE - SUNSHINE COAST - CENTRAL QLD
URBAN DESIGNERS
SURVEYORS
ENGINEERS.
LANDSCAPE ARCHITECTS —JFp URBAN CONSULTANTS PTY. LTD. A.C.N. 050.414 04!
PROJECT TITLE:
PRECINCT F
AT
NOOSA SPRINGS, NOOSA HEADS
FOR:
ALTUM
eA eee
VEGETATION
MANAGEMENT PLAN
RETAINED - SUBIECT 9 N
DETAILED ARBORIST \ 2
COPYRIGHT © 2013 JFP URBAN CONSULTANTS PTY LTD. THIS DOCUMENT MAY NOT BE COPIED
OR TRANSMITTED IN ANY FORM OR BY ANY MEANS IN PART OR IN WHOLE WITHOUT THE
WRITTEN CONSENT OF JEP URBAN CONSULTANTS PTY LTD.
PROJECT: PLAN: ISSUE: NORTH:
M2652L VM0O4 A
SCALE: 1:200 @ A1
Cc DATE: 01/08/2016
: FILE NAME: M2652_VMP_PLANS - PRECINCT F.DWG
>
Page 23
APPROVAL ISSUE LEGEND TREES TO BE RETAINED AND PROTECTED TREES POSSIBLE FOR RETENTION THE INTENT IS TO RETAIN THESE TREES SUBJECT TO DETAILED DESIGN | 7s TREES FOR REMOVAL fr \ REFER VEGETATION ASSESSMENT SCHEDULE Sd S| vy aw > WEED SPECIES ) REFER VEGETATION ASSESSMENT SCHEDULE e ry VL. f > DEAD TREES e | REFER VEGETATION ASSESSMENT SCHEDULE € 5 we \ re PFA TREE PROTECTION FENCE FILL Refer Civil Plans CUT Refer Civil Plans TREE PROTECTION ZONE IPZ | as PER AS4970-2009 A FOR APPROVAL 2016-08-01 RC AG ISSUE: DETAILS: DATE: INIT: CHK'D: =A] eb mi URBANCONSULTANTS BRISBANE - SUNSHINE COAST - CENTRAL QLD RIS Jouse SIGNERS, PROJECT TITLE: PRECINCT F AT NOOSA SPRINGS, NOOSA HEADS FOR: ALTUM eA eee VEGETATION MANAGEMENT PLAN PYRIGHT © 2013 JFP URBAN CONSULTANTS PTY LTD. THIS DOCUMENT MAY NOT BE COPIED OR TRANSMITTED IN ANY FORM OR BY ANY MEANS IN PART OR IN WHOLE WITHOUT THE WRITTEN CONSENT OF JEP URBAN CONSULTANTS PTY LTD. PROJECT: PLAN: ISSUE: _NORTH: M2652L VMOS A C1) SCALE: 1:200 @ A1 DATE: 01/08/2016 FILE NAME: M2652_VMP_PLANS - PRECINCT F.DWG
Page 24
; | APPROVAL ISSUE LEGEND TREES TO BE RETAINED AND PROTECTED 5 TREES POSSIBLE FOR RETENTION THE INTENT IS TO RETAIN THESE TREES SUBJECT TO DETAILED DESIGN ~~’ 7 TREES FOR REMOVAL r || REFER VEGETATION ASSESSMENT SCHEDULE t } / KM v foe SO ‘ J > WEED SPECIES é e ) REFER VEGETATION ASSESSMENT SCHEDULE des L 2 DEAD TREES r REFER VEGETATION ASSESSMENT SCHEDULE z Ma we? Las Tpr1 | TREE PROTECTION FENCE FILL Refer Civil Plans CUT Refer Civil Plans TREE PROTECTION ZONE IPZ | as PER AS4970-2009 A FOR APPROVAL 2016-08-01 RC AG ; ISSUE: DETAILS: DATE: INIT: CHK'D: SESS (iE ig JFOP 1 ANNA URBANCONSULTANTS I 1 | | / | ; | : pid aaa | pry Jf y / pig lal Lo pid ee pp lg ley / | ! py PLANNERS BRISBANE - SUNSHINE COAST - CENTRAL QLD / URBAN DESIGNERS BRISBANE - JFP House / SURVEYORS 76 Ernest Street, / / / Sy id! , ‘ \ <> south Brisbane Qld 4101 yi! / / i / / / [ C \ R ENGINEERS P07 3012 0100 W www.jfp.com.au LANDSCAPE ARCHITECTS —JfP URBAN CONSULTANTS PTY. LTD. A.C.N. 050.414 045 PROJECT TITLE: PRECINCT F AT NOOSA SPRINGS, NOOSA HEADS yf 7 | | iC oN ' > : ALTUM VEGETATION TO BE / / RETAINED - SUBJECT TO , . VEGETATION DETAILED ARBORIST ‘O \ MANAGEMENT PLAN COPYRIGHT © 2013 JFP URBAN CONSULTANTS PTY LTD. THIS DOCUMENT MAY NOT BE COPIED OR TRANSMITTED IN ANY FORM OR BY ANY MEANS IN PART OR IN WHOLE WITHOUT THE | WRITTEN CONSENT OF JFP URBAN CONSULTANTS PTY LTD. PROJECT: PLAN: ISSUE: NORTH: M2652L VMO6 A C1) rA\\,° \ \\\ SCALE: 1:200 @ A1 JOINS SHEET VMO7 iW - yh VV NAN DATE: 01/08/2016 ? : ‘ \ \ \ 4 \ SST FILE NAME: M2652_VMP_PLANS - PRECINCT F.DWG T A
Page 25
ZA
7 |
A I
»S
VEGETATION ASSESSMENT SCHEDULE (VAS)
APPROVAL ISSUE
No. Species Common Name DBH(mm) | Height(m) | Spread(m) | Action Reason
504 |Allocasuarina littoralis Black Sheoak 100 7 3 Remove Retention not feasible
505 |Allocasuarina littoralis Black Sheoak 100 7 3 Remove Retention not feasible LEG END
506 |Allocasuarina littoralis Black Sheoak 100 7 3 Retain Outside of development footprint
507 |Callitris columellaris Bribie Island Pine 100 7 3 Retain Outside of development footprint ANG pROTECTED
508 |Allocasuarina littoralis Black Sheoak 100 7 3 Retain Outside of development footprint
509 |Allocasuarina littoralis Black Sheoak 100 9 3 Retain Outside of development footprint
510 | Corymbia intermedia Pink Bloodwood 4X0150 9 8 Retain | Outside of development footprint TREES POSSIBLE FOR RETENTION
511 |Lophostemon confertus Brushbox 400 7 8 Retain Outside of development footprint THE INTENT IS TO RETAIN THESE TREES SUBJECT TO
512 |Lophostemon confertus Brushbox 200 6 So Retain Outside of development footprint DETAILED DESIGN
513 |Lophostemon confertus Brushbox 3X200 10 6 Retain Outside of development footprint
514 |Lophostemon confertus Brushbox 3X150 10 6 Retain Outside of development footprint
515 |Lophostemon confertus Brushbox 200 7 oS Retain Outside of development footprint “ > TREES FOR REMOVAL SCHEDULE
516 |Lophostemon confertus Brushbox 2X200 10 6 Retain Outside of development footprint - |
517 |Lophostemon confertus Brushbox 200 8 4 Retain Outside of development footprint , v
518 | Corymbia intermedia Pink Bloodwood 100 8 3 Retain Outside of development footprint
519 |Lophostemon confertus Brushbox 4X0100 9 6 Retain | Outside of development footprint >\ WEED SPECIES
520 |Lophostemon confertus Brushbox 5X0150 10 7 Retain Outside of development footprint e REFER VEGETATION ASSESSMENT SCHEDULE
521 |Callitris columellaris Bribie Island Pine 300 11 4 Retain Outside of development footprint
522 | Callitris columellaris Bribie Island Pine 300 11 4 Retain Outside of development footprint .
523 |Allocasuarina littoralis Black Sheoak 150 7 4 Retain Outside of development footprint {~ = DEAD TREES
524 |Allocasuarina littoralis Black Sheoak 150 7 5 Remove Retention not feasible e | REFER VEGETATION ASSESSMENT SCHEDULE
525 |Allocasuarina littoralis Black Sheoak 100 7 5 Remove Retention not feasible >
526 |Allocasuarina littoralis Black Sheoak 100 6 4 Remove Retention not feasible
527 |Allocasuarina littoralis Black Sheoak 200 7 4 Retain Outside of development footprint pri | TREE PROTECTION FENCE
528 |Lophostemon confertus Brushbox 150 10 4 Retain Outside of development footprint
529 |Lophostemon confertus Brushbox 2X0200 9 8 Retain Outside of development footprint FILL
530 |Lophostemon confertus Brushbox 150 10 5 Retain Outside of development footprint Refer Civil Plans
531 |Allocasuarina littoralis Black Sheoak 100 5 3 Retain Outside of development footprint
532 |Allocasuarina littoralis Black Sheoak 150 10 5 Retain Outside of development footprint oo civ Plans
533 |Allocasuarina littoralis Black Sheoak 150 10 fo Remove Retention not feasible
537 |Allocasuarina littoralis Black Sheoak 150 9 4 Retain Outside of development footprint +P7 TREE PROTECTION ZONE
538 |Allocasuarina littoralis Black Sheoak 150 9 4 Retain | Outside of development footprint AS PER AS4970-2009
539 | Callitris columellaris Bribie Island Pine 200 10 6 Remove Retention not feasible
540 |Allocasuarina littoralis Black Sheoak 150 10 4 Retain Outside of development footprint
541 |Allocasuarina littoralis Black Sheoak 150 9 4 Remove Retention not feasible
542 |Allocasuarina littoralis Black Sheoak 150 9 4 Remove Retention not feasible
543 | Callitris columellaris Bribie Island Pine 300 11 6 TBA Impacted by earthworks
544 |Allocasuarina littoralis Black Sheoak 150 5 2 Retain Outside of development footprint
545 |Lophostemon confertus Brushbox 400 10 10 Retain Outside of development footprint
546 |Lophostemon confertus Brushbox 400 10 10 Retain Outside of development footprint
547 |Lophostemon confertus Brushbox 400 10 10 Retain Outside of development footprint
548 | 'Dead Tree’ 150 5 3 Retain Outside of development footprint
549 |Allocasuarina littoralis Black Sheoak 150 7 4 Retain Outside of development footprint
550 |Allocasuarina littoralis Black Sheoak 100 6 3 Retain Outside of development footprint
551 |Callitris columellaris Bribie Island Pine 100 9 4 Retain Outside of development footprint
552 | 'Dead Tree’ 100 6 4 Retain Outside of development footprint
553 |Lophostemon confertus Brushbox 600 11 10 Retain Outside of development footprint
554 |Lophostemon confertus Brushbox 300 9 7 Retain Outside of development footprint
555 | Callitris columellaris Bribie Island Pine 200 7 4 Retain Outside of development footprint
556 |Allocasuarina littoralis Black Sheoak 150 6 4 Retain Outside of development footprint
557 |Lophostemon confertus Brushbox 400 12 10 Retain Outside of development footprint
558 |Lophostemon confertus Brushbox 200 12 7 Retain Outside of development footprint
559 |Lophostemon confertus Brushbox 2X200 12 8 Retain Outside of development footprint
560 |Lophostemon confertus Brushbox 300 11 6 Retain Outside of development footprint
561 | 'Dead Tree’ 200 10 1 Retain Outside of development footprint
562 |Lophostemon confertus Brushbox 5xX0200 11 12 Retain Outside of development footprint
563 |Lophostemon confertus Brushbox 200 10 5 Retain Outside of development footprint
564 |Lophostemon confertus Brushbox 4X0200 8 10 Retain | Outside of development footprint A FOR APPROVAL 2016-08-01 RC_AG
565 | Callitris columellaris Bribie Island Pine 200 6 6 Retain | Outside of development footprint ISSUE: DETAILS: DATE: INIT: CHK'D:
566 |Callitris columellaris Bribie Island Pine 100 6 3 Remove Retention not feasible
567 |Allocasuarina littoralis Black Sheoak 150 7 4 Remove Retention not feasible
568 |Callitris columellaris Bribie Island Pine 150 7 4 Remove Retention not feasible
569 |Lophostemon confertus Brushbox 5X0250 10 12 TBA Impacted by earthworks
570 |Lophostemon confertus Brushbox 600 12 10 Retain Outside of development footprint =t | |
571 |Callitris columellaris Bribie Island Pine 400 8 6 Retain Outside of development footprint
572 |Lophostemon confertus Brushbox 300 12 7 Retain Outside of development footprint IRANANRIATATNY
573 |Lophostemon confertus Brushbox 150 9 5 Retain Outside of development footprint
574 |Lophostemon confertus Brushbox 100 9 So Retain Outside of development footprint URBANCONSULTANTS
575 |Lophostemon confertus Brushbox 4X0200 10 10 Retain Outside of development footprint
576 |Callitris columellaris Bribie Island Pine 400 10 7 Retain Outside of development footprint
577 |Lophostemon confertus Brushbox 5xX0200 12 10 Retain Outside of development footprint
578 |Lophostemon confertus Brushbox 100 8 3 Retain Outside of development footprint
579 |Lophostemon confertus Brushbox 100 8 3 Retain Outside of development footprint
580 |Lophostemon confertus Brushbox 100 8 3 Retain Outside of development footprint PROJECT TITLE:
581 |Lophostemon confertus Brushbox 3X0200 12 10 Retain Outside of development footprint
582 |Lophostemon confertus Brushbox 4x200 12 8 Retain Outside of development footprint PRECI N CT F
583 |Allocasuarina littoralis Black Sheoak 150 6 5 Retain Outside of development footprint AT
584 |Allocasuarina littoralis Black Sheoak 100 8 6 Retain Outside of development footprint NOOSA SPRI NGS, NOOSA HEADS
585 |Lophostemon confertus Brushbox 6X0100 10 7 Retain Outside of development footprint
586 |Lophostemon confertus Brushbox 300 10 7 Retain Outside of development footprint FOR:
587 |Lophostemon confertus Brushbox 100 7 3 Retain Outside of development footprint ALTUM
588 |Lophostemon confertus Brushbox 100 7 3 Retain Outside of development footprint ARTE
589 |Lophostemon confertus Brushbox 300 10 5 Retain Outside of development footprint .
590 |Lophostemon confertus Brushbox 200 10 4 Retain Outside of development footprint VEGETATION
591 |Lophostemon confertus Brushbox 3X0200 10 10 Retain Outside of development footprint
592 | 'Dead Tree’ 200 4 2 Retain Outside of development footprint MANAG EMENT PLAN
593 | Corymbia intermedia Pink Bloodwood 300 10 7 Retain Outside of development footprint VAS
594 | Corymbia intermedia Pink Bloodwood 300 10 7 Retain Outside of development footprint <prmgnn 6 dois NP UREA COMBULTANNS PIV LID” THE DOCUMENT WAY NOT BE COMED
595 |Lophostemon confertus Brushbox 3X0200 12 10 Retain Outside of development footprint OR TRANSMITTED IN ANY FORM OR BY ANY MEANS IN PART ORIN WHOLE WITHOUT THE
596 |Lophostemon confertus Brushbox 3X0200 12 10 Retain Outside of development footprint PTONSGn PE ISSUE: NORTH:
597 |Callitris columellaris Bribie Island Pine 600 12 10 Retain Outside of development footprint
598 |Corymbia intermedia Pink Bloodwood 200 10 7 Retain | Outside of development footprint | MI2652L VMOZ7 A
599 |Allocasuarina littoralis Black Sheoak 100 7 3 Remove Retention not feasible .
SCALE: 1:200 @ A1
DATE: 01/08/2016
M2652_VMP_PLANS - PRECINCT F.DWG
FILE NAME:
Page 26
VEGETATION ASSESSMENT SCHEDULE (VAS) No. Species Common Name DBH(mm) | Height(m) | Spread(m) | Action Reason 600 |Allocasuarina littoralis Black Sheoak 150 10 6 Retain Outside of development footprint 601 |Lophostemon confertus Brushbox 9X0100 10 10 Retain Outside of development footprint 602 | Callitris columellaris Bribie Island Pine 100 7 4 Retain Outside of development footprint 603 |Lophostemon confertus Brushbox 100 7 4 Retain Outside of development footprint 604 |Allocasuarina littoralis Black Sheoak 200 8 4 Remove Retention not feasible 605 | 'Dead Tree’ 200 8 4 Remove Retention not feasible 606 |Allocasuarina littoralis Black Sheoak 200 8 4 Retain Outside of development footprint 607 |Lophostemon confertus Brushbox 100 9 5 Retain Outside of development footprint 608 |Lophostemon confertus Brushbox 100 9 5 Retain Outside of development footprint 609 |Lophostemon confertus Brushbox 100 9 5 Retain Outside of development footprint 610 |Lophostemon confertus Brushbox 200 9 8 Retain Outside of development footprint 611 |Acacia disparrima Hickory Wattle 150 7 4 Retain Outside of development footprint 612 |Allocasuarina littoralis Black Sheoak 100 9 2 Retain Outside of development footprint 613 | Callitris columellaris Bribie Island Pine 300 11 7 Retain Outside of development footprint 614 |Allocasuarina littoralis Black Sheoak 100 6 4 Retain Outside of development footprint 615 |Banksia serrata Saw-tooth Banksia 100 5 5 Retain Outside of development footprint 616 |Acacia disparrima Hickory Wattle 150 7 5 Retain Outside of development footprint 617 | 'Dead Tree’ 150 7 4 Retain Outside of development footprint 618 |Acacia disparrima Hickory Wattle 300 9 7 Retain Outside of development footprint 619 |Allocasuarina littoralis Black Sheoak 100 9 5 Remove Retention not feasible 620 |Allocasuarina littoralis Black Sheoak 150 9 5 Remove Retention not feasible 621 | 'Dead Tree’ 150 5 5 Retain Outside of development footprint 622 |Allocasuarina littoralis Black Sheoak 150 6 4 Remove Retention not feasible 623 | Corymbia intermedia Pink Bloodwood 400 11 8 Retain Outside of development footprint 624 |Lophostemon confertus Brushbox 400 11 9 Retain Outside of development footprint 625 | Corymbia intermedia Pink Bloodwood 3X0200 12 10 Retain Outside of development footprint 626 | Corymbia intermedia Pink Bloodwood 150 10 6 Retain Outside of development footprint 627 |Allocasuarina littoralis Black Sheoak 200 10 6 Retain Outside of development footprint 628 | Corymbia intermedia Pink Bloodwood 150 9 7 Retain Outside of development footprint 629 |Allocasuarina littoralis Black Sheoak 200 12 6 Retain Outside of development footprint 630 |Allocasuarina littoralis Black Sheoak 150 11 6 Retain Outside of development footprint 631 |Allocasuarina littoralis Black Sheoak 300 12 7 Retain Outside of development footprint 632 |Allocasuarina littoralis Black Sheoak 150 9 5 Retain Outside of development footprint 633 |Allocasuarina littoralis Black Sheoak 100 7 4 Retain Outside of development footprint 634 |Lophostemon confertus Brushbox 300 12 7 Retain Outside of development footprint 635 |Lophostemon confertus Brushbox 500 12 12 Retain Outside of development footprint 636 |Lophostemon confertus Brushbox 200 12 6 Retain Outside of development footprint 637 |Lophostemon confertus Brushbox 3X0200 12 12 Retain Outside of development footprint 638 |Allocasuarina littoralis Black Sheoak 200 10 5 Retain Outside of development footprint 639 |Allocasuarina littoralis Black Sheoak 150 10 5 Retain Outside of development footprint 640 |Lophostemon confertus Brushbox 2X0100 10 8 Retain Outside of development footprint 641 |Banksia serrata Saw-tooth Banksia 100 4 2 Retain Outside of development footprint 642 |Lophostemon confertus Brushbox 2X0200 11 7 Retain Outside of development footprint 643 |Lophostemon confertus Brushbox 3X0200 10 10 Retain Outside of development footprint 644 |Lophostemon confertus Brushbox 150 10 4 Retain Outside of development footprint 645 |Lophostemon confertus Brushbox 150 12 5 Retain Outside of development footprint 646 | Corymbia intermedia Pink Bloodwood 100 4 3 Retain Outside of development footprint 647 |Corymbia intermedia Pink Bloodwood 200 6 7 Retain Outside of development footprint 648 |Lophostemon confertus Brushbox 2X0150 12 7 Retain Outside of development footprint 649 |Lophostemon confertus Brushbox 200 12 8 Retain Outside of development footprint 650 | Corymbia intermedia Pink Bloodwood 150 10 5 Retain Outside of development footprint 651 | Corymbia intermedia Pink Bloodwood 200 12 4 Retain Outside of development footprint 652 |Corymbia intermedia Pink Bloodwood 150 11 7 Retain Outside of development footprint 653 | Corymbia intermedia Pink Bloodwood 200 10 6 Retain Outside of development footprint 654 |Corymbia intermedia Pink Bloodwood 150 12 4 Retain Outside of development footprint 655 |Lophostemon confertus Brushbox 300 13 12 Retain Outside of development footprint 656 |Lophostemon confertus Brushbox 300 13 12 Retain Outside of development footprint 657 |Corymbia intermedia Pink Bloodwood 100 10 3 Retain Outside of development footprint 658 | Callitris columellaris Bribie Island Pine 200 11 7 Retain Outside of development footprint 659 | Corymbia intermedia Pink Bloodwood 150 11 4 Retain Outside of development footprint 660 |Lophostemon confertus Brushbox 2X0150 11 7 Retain Outside of development footprint 661 |Lophostemon confertus Brushbox 2X0150 11 7 Retain Outside of development footprint 662 |Lophostemon confertus Brushbox 2X0200 9 10 Retain Outside of development footprint 663 |Allocasuarina littoralis Black Sheoak 150 7 4 Retain Outside of development footprint 664 | Corymbia intermedia Pink Bloodwood 200 9 6 Remove Retention not feasible 665 |Lophostemon confertus Brushbox 200 9 6 Remove Retention not feasible 666 |Lophostemon confertus Brushbox 100 9 5 Retain Outside of development footprint 667 |Lophostemon confertus Brushbox 200 9 5 Retain Outside of development footprint 668 |Acacia disparrima Hickory Wattle 500 10 12 Retain Outside of development footprint 669 | Callitris columellaris Bribie Island Pine 200 12 4 Retain Outside of development footprint 670 |Callitris columellaris Bribie Island Pine 200 12 6 Retain Outside of development footprint 671 |Allocasuarina littoralis Black Sheoak 200 12 6 Retain Outside of development footprint 672 |Corymbia intermedia Pink Bloodwood 150 10 6 Retain Outside of development footprint 673 |Corymbia intermedia Pink Bloodwood 200 10 6 Retain Outside of development footprint 674 |Allocasuarina littoralis Black Sheoak 150 9 4 Retain Outside of development footprint 675 |Corymbia intermedia Pink Bloodwood 100 7 4 Retain Outside of development footprint 676 |Corymbia intermedia Pink Bloodwood 150 9 6 Retain Outside of development footprint 677 |Callitris columellaris Bribie Island Pine 100 12 4 Retain Outside of development footprint 678 |Callitris columellaris Bribie Island Pine 200 12 7 Retain Outside of development footprint 679 |Callitris columellaris Bribie Island Pine 250 12 7 Retain Outside of development footprint 680 |Callitris columellaris Bribie Island Pine 100 8 5 Retain Outside of development footprint 681 | Callitris columellaris Bribie Island Pine 150 10 5 Retain Outside of development footprint 682 |Lophostemon confertus Brushbox 150 9 6 Retain Outside of development footprint 683 |Lophostemon confertus Brushbox 500 11 12 Retain Outside of development footprint 684 | Corymbia intermedia Pink Bloodwood 100 5 4 Retain Outside of development footprint 685 | Corymbia intermedia Pink Bloodwood 150 7 6 Retain Outside of development footprint 686 |Banksia serrata Saw-tooth Banksia 200 4 4 Retain Outside of development footprint 687 |Banksia serrata Saw-tooth Banksia 300 6 6 Retain Outside of development footprint 688 |Lophostemon confertus Brushbox 200 10 6 Retain Outside of development footprint 689 |Lophostemon confertus Brushbox 100 7 4 Retain Outside of development footprint 690 |Acacia disparrima Hickory Wattle 200 6 6 Retain Outside of development footprint 691 |Callitris columellaris Bribie Island Pine 150 10 7 Retain Outside of development footprint 692 | Callitris columellaris Bribie Island Pine 500 10 6 Retain Outside of development footprint 693 | 'Dead Tree’ 150 6 3 Retain Outside of development footprint 694 |Allocasuarina littoralis Black Sheoak 150 7 4 Retain Outside of development footprint 695 |Banksia serrata Saw-tooth Banksia 2X0300 5 6 Retain Outside of development footprint 696 |Banksia serrata Saw-tooth Banksia 300 6 6 Retain Outside of development footprint 697 |Allocasuarina littoralis Black Sheoak 200 7 7 Remove Retention not feasible 698 | Callitris columellaris Bribie Island Pine 250 12 6 Retain Outside of development footprint 699 |Allocasuarina littoralis Black Sheoak 250 11 7 Retain Outside of development footprint No. Species Common Name DBH(mm) | Height(m) | Spread(m) | Action Reason 700 | ‘Dead Tree’ 200 9 4 Retain Outside of development footprint 701 |Callitris columellaris Bribie Island Pine 300 12 7 Remove Retention not feasible 702 |Callitris columellaris Bribie Island Pine 100 7 4 Remove Retention not feasible 703 |Lophostemon confertus Brushbox 300 12 10 TBA Impacted by earthworks 704 |Callitris columellaris Bribie Island Pine 300 10 7 TBA Impacted by earthworks 705 | Callitris columellaris Bribie Island Pine 100 9 5 Retain Outside of development footprint 706 |Corymbia intermedia Pink Bloodwood 200 11 7 Retain Outside of development footprint 707 |Callitris columellaris Bribie Island Pine 150 10 6 Retain Outside of development footprint 708 |Allocasuarina littoralis Black Sheoak 150 12 6 Retain Outside of development footprint 709 |Allocasuarina littoralis Black Sheoak 200 8 5 Retain | Outside of development footprint 710 |Callitris columellaris Bribie Island Pine 500 12 8 Retain Outside of development footprint 711 |Corymbia intermedia Pink Bloodwood 500 12 8 Retain Outside of development footprint 712 | 'Dead Tree’ 150 6 3 Retain Outside of development footprint 713 |Lophostemon confertus Brushbox 400 12 10 TBA Impacted by earthworks 714 |Lophostemon confertus Brushbox 150 9 4 Remove Retention not feasible 715 |Corymbia intermedia Pink Bloodwood 700 12 12 TBA Impacted by earthworks 716 | 'Dead Tree’ 250 9 7 Retain Outside of development footprint 717 |Lophostemon confertus Brushbox 400 12 12 Retain Outside of development footprint 718 |Allocasuarina littoralis Black Sheoak 250 6 7 Retain Outside of development footprint 719 |Lophostemon confertus Brushbox 200 12 6 TBA Impacted by earthworks 720 |Lophostemon confertus Brushbox 2X0200 12 10 Remove Retention not feasible 721 |Lophostemon confertus Brushbox 200 12 6 Remove Retention not feasible 722 |Allocasuarina littoralis Black Sheoak 100 7 4 Retain Outside of development footprint 723 |Lophostemon confertus Brushbox 4X0200 12 12 Remove Retention not feasible 724 |Macaranga tanarius Macaranga 200 SB 6 Remove Retention not feasible 725 |Macaranga tanarius Macaranga 200 5 6 Remove Retention not feasible 726 |Banksia serrata Saw-tooth Banksia 200 5 6 Remove Retention not feasible 727 |Allocasuarina littoralis Black Sheoak 100 5 3 Remove Retention not feasible 728 |Banksia serrata Saw-tooth Banksia 200 3 4 Remove Retention not feasible 729 |Banksia serrata Saw-tooth Banksia 200 So 4 Remove Retention not feasible 730 |Allocasuarina littoralis Black Sheoak 200 5 5 Remove Retention not feasible 731 |Allocasuarina littoralis Black Sheoak 100 6 4 Remove Retention not feasible 732 |Lophostemon confertus Brushbox 4X0300 10 10 Retain Outside of development footprint 733 |Lophostemon confertus Brushbox 3X0400 10 12 TBA Impacted by earthworks 734 |Allocasuarina littoralis Black Sheoak 100 7 3 Retain Outside of development footprint 735 |Corymbia intermedia Pink Bloodwood 150 8 4 Retain Outside of development footprint 736 | ‘Dead Tree’ 100 6 2 Retain Outside of development footprint 737 |Corymbia intermedia Pink Bloodwood 200 9 5 Retain Outside of development footprint 738 |Lophostemon confertus Brushbox 300 9 7 TBA Impacted by earthworks 739 |Acacia disparrima Hickory Wattle 100 So 4 Retain Outside of development footprint 740 |Allocasuarina littoralis Black Sheoak 150 6 4 Retain Outside of development footprint 741 |Allocasuarina littoralis Black Sheoak 250 6 5 Retain Outside of development footprint 742 |Lophostemon confertus Brushbox 150 8 5 Retain Outside of development footprint 743 | Corymbia intermedia Pink Bloodwood 250 8 7 Remove Retention not feasible 744 |Elaeocarpus obovatus Hard Quandong 200 6 5 Remove Retention not feasible 745 |Callitris columellaris Bribie Island Pine 100 5 2 Retain Outside of development footprint 746 |Eucalyptus tindaliae Tindale's Stringybark 300 9 6 Retain Outside of development footprint 747 |Allocasuarina littoralis Black Sheoak 100 So 4 Retain Outside of development footprint 748 |Eucalyptus tindaliae Tindale's Stringybark 250 10 7 Retain Outside of development footprint 749 |Lophostemon confertus Brushbox 400 8 8 Retain Outside of development footprint 750 |Lophostemon confertus Brushbox 300 10 9 Retain Outside of development footprint 751 |Corymbia intermedia Pink Bloodwood 5X0100 7 5 Retain Outside of development footprint 752 |Eucalyptus tereticornis Forest Red Gum 100 6 4 Remove Retention not feasible 753 |Eucalyptus propinqua Grey Gum 2X0150 8 5 Remove Retention not feasible 754 |Eucalyptus propinqua Grey Gum 200 10 6 Retain Outside of development footprint 755 | Syzygium luehmannii Small Leaved Lilly-Pilly 100 4 4 Retain Outside of development footprint 756 |Eucalyptus tereticornis Forest Red Gum 300 11 6 Retain | Outside of development footprint 757 |Eucalyptus propinqua Grey Gum 300 12 10 Retain Outside of development footprint 758 |Eucalyptus propinqua Grey Gum 300 12 10 Retain Outside of development footprint 759 | Melaleuca nodosa Prickly-Leaved Paperbark 100 5 4 Retain Outside of development footprint 760 | Melaleuca nodosa Prickly-Leaved Paperbark 100 5 4 Retain Outside of development footprint 761 |Randia fitzalanii Native Gardenia 100 5 5 Remove Retention not feasible 762 |Allocasuarina littoralis Black Sheoak 100 5 4 Remove Retention not feasible 763 |Corymbia intermedia Pink Bloodwood 800 10 13 Retain Outside of development footprint 764 |Lophostemon confertus Brushbox 3X0100 6 6 Retain | Outside of development footprint 765 | Callitris columellaris Bribie Island Pine 200 10 6 Retain Outside of development footprint 766 |Corymbia intermedia Pink Bloodwood 300 12 10 Retain Outside of development footprint 767 |Callitris columellaris Bribie Island Pine 250 12 7 Retain Outside of development footprint 768 |Corymbia intermedia Pink Bloodwood 200 7 6 Retain Outside of development footprint 769 | Callitris columellaris Bribie Island Pine 300 13 7 Retain Outside of development footprint 770 |Callitris columellaris Bribie Island Pine 150 6 6 Retain Outside of development footprint 771 |Lophostemon confertus Brushbox 400 12 8 Retain Outside of development footprint 772 |Callitris columellaris Bribie Island Pine 300 13 8 Remove Retention not feasible 773 |Lophostemon confertus Brushbox 100 7 5 Retain Outside of development footprint 774 |Callitris columellaris Bribie Island Pine 100 6 5 Retain Outside of development footprint 775 |Callitris columellaris Bribie Island Pine 250 12 6 Retain Outside of development footprint 776 |Randia fitzalanii Native Gardenia 200 6 6 Retain Outside of development footprint 777 |Banksia integrifolia Coastal Banksia 100 5 3 Retain Outside of development footprint 778 | Banksia integrifolia Coastal Banksia 150 6 3 Retain Outside of development footprint 779 |Corymbia intermedia Pink Bloodwood 150 10 5 Retain Outside of development footprint 780 | Callitris columellaris Bribie Island Pine 150 10 5 Retain Outside of development footprint 781 |Corymbia intermedia Pink Bloodwood 400 12 8 Retain Outside of development footprint 782 | Syzygium jambos Rose Apple 150 5 5 Retain Outside of development footprint 783 |Callitris columellaris Bribie Island Pine 150 7 3 Retain Outside of development footprint 784 | Syzygium jambos Rose Apple 150 5 6 Retain Outside of development footprint 785 |Eucalyptus propinqua Grey Gum 3xX0150 8 8 Retain Outside of development footprint 786 |Lophostemon confertus Brushbox 3X0300 10 10 TBA Impacted by earthworks 787 |Callitris columellaris Bribie Island Pine 200 7 6 Retain Outside of development footprint 788 | Melia azedarach White Cedar 250 7 7 Retain Outside of development footprint 789 |Lophostemon confertus Brushbox 200 11 6 Retain Outside of development footprint 790 | Callitris columellaris Bribie Island Pine 250 11 7 Retain Outside of development footprint 791 |Acacia disparrima Hickory Wattle 100 5 4 Remove Retention not feasible 792 | Callitris columellaris Bribie Island Pine 250 12 8 TBA Impacted by earthworks 793 |Callitris columellaris Bribie Island Pine 250 8 7 TBA Impacted by earthworks 794 |Lophostemon confertus Brushbox 400 12 9 TBA Impacted by earthworks 795 |Allocasuarina littoralis Black Sheoak 100 5 4 Remove Retention not feasible 796 |Callitris columellaris Bribie Island Pine 300 12 7 TBA Impacted by earthworks 797 |Allocasuarina littoralis Black Sheoak 100 5 3 TBA Impacted by earthworks 798 | Callitris columellaris Bribie Island Pine 500 12 10 Remove Retention not feasible 799 |Allocasuarina littoralis Black Sheoak 150 5 4 Retain Outside of development footprint 800 | Callitris columellaris Bribie Island Pine 300 12 7 Retain | Outside of development footprint 801 |Allocasuarina littoralis Black Sheoak 150 6 5 TBA Impacted by earthworks 802 |Allocasuarina littoralis Black Sheoak 150 6 5 TBA Impacted by earthworks 803 |Eucalyptus tereticornis Forest Red Gum 4X0150 8 6 TBA Impacted by earthworks 804 |Eucalyptus tereticornis Forest Red Gum 100 S 4 Retain Outside of development footprint 805 | Syzygium jambos Rose Apple 100 5 4 Retain Outside of development footprint 806 |Corymbia citriodora Spotted Gum 150 6 4 Retain Outside of development footprint | APPROVAL ISSUE | A FOR APPROVAL 2016-08-01 RC AG ISSUE: DETAILS: DATE: INIT: CHK'D: JFOP URBANCONSULTANTS IRN ANNA PROJECT TITLE: PRECINCT F AT NOOSA SPRINGS, NOOSA HEADS FOR: ALTUM eee VEGETATION MANAGEMENT PLAN VAS COPYRIGHT © 2013 JFP URBAN CONSULTANTS PTY LTD. THIS DOCUMENT MAY NOT BE COPIED OR TRANSMITTED IN ANY FORM OR BY ANY MEANS IN PART OR IN WHOLE WITHOUT THE WRITTEN CONSENT OF JEP URBAN CONSULTANTS PTY LTD. ane) Ol PLAN: ISSUE: NORTH: M2652L VM0O8 A SCALE: N/A DATE: 01/08/2016 FILE NAME: M2652_VMP_PLANS - PRECINCT F.DWG
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APPENDIX
B
SITE
PHOTOGRAPHS
AC1345BFIRE Rev. 1
August 2016
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APPENDIX
B
SITE
PHOTOGRAPHS
Page 28
Site Photographs
as at October 2015
P1 – Looking north across western section of site. P2 – Looking east from centre of site.
P3 – Looking south in centre of site. P4 – Looking north in centre of site.
AC1345BFIRE Page 1 of 2
August 2016
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Page 29
P5 – Looking south along eastern access track. P6 – Looking east across centre of site. P7 – Typical vegetation in east of site. P8 – Looking east across conservation park. AC1345BFIRE Page 2 of 2 August 2016 JS/js
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APPENDIX
C
STATE GOVERNMENT
MAPPING
AC1345BFIRE Rev. 1
August 2016
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APPENDIX
C
STATE GOVERNMENT
MAPPING
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19/10/2015 07:38:26
Lot: 7 Plan: SP178340
Page 1
[OCR of page images]
19/10/2015 07:38:26
Lot: 7 Plan: SP178340
507000 507250 507500 507750 508000 508250 508500 508750 509000 509250 509500 509750 510000 510250 510500 510750
160415 189°420° 150°4 18°50 180°515E 189°590°E 159°845°= 189°60°E 152°615°
Legend Disclaimer:
CI totana es While every care is taken to ensure the accuracy of this product, the
ee ae Department of Natural Resources and Mines makes no representations
Category A area (Vegetation offsets/compliance notices/VDecs) or warranties about its accuracy, reliability, completeness or suitability
for any particular purpose and disclaims all responsibility and all liability
|| Category B area (Remnant vegetation) {including without limitation, liability in negligence) for all expenses, losses,
[J category ¢ area (High-value regrowth vegetation) Government damages (including indirect or consequential damage) and costs which you
no a might incurr as a result of the product being inaccurate or incomplete in
ategory R area (Reef regrowth watercourse vegetation}
gory at 9 LocaLiTy o1GRAM any Way and for any reason
[_} category x area (Vegetation not regulated under the VMA)
Water
Area not categorised
Cadastral line
Property boundaries shown are
provided as a locational aid only
‘Additional information required for the assessment of vegetation values
is provided in the accompanying “Vegetation Management Supporting map’.
For further information go to the web site: wwnw.dnrm.qid.gov.au or contact
the Department of Natural Resources and Mines.
Digital data for the regulated vegetation management map is available from the
Queensland Spatial Portal at http:/vww.information.qld.gov.au/
This map is updated on a monthly basis to ensure new PMAVs are
included as they are approved
° 200 400 600 800 1,000 m
This product is projected into:
GDA 1994 MGA Zone 56
© The State of Queensland (Department of Natural Resources and Mines), 2015
Page 1
Page 32
19/10/2015 07:38:26 Lot: 7 Plan: SP178340 Page 2 [OCR of page images] 19/10/2015 07:38:26 Lot: 7 Plan: SP178340 507000 507250 507500 507750 508000 508250 508500 508750 509000 509250 1 1 509500 508750 510000 510250 510500 510750 1 1 1 1 7077750 ‘072000 7078250 7078500 7078750 7079000 7079250 7079800 7077500 1 7 6095 rx —— a 72228 S Z A2aisi2212 70130 S - N229 262418 2e-2430°S L per2eas's \ 1 2s-250°S fi 2515S 2: Sal 7077250 7077000 1625308 7076600 7076750 7076250 2845S 26260'S 153°415°E 152°4'30°E 159°445°E 1s2°50'E 160°S15E 159°50°E 152°545°E 15°60 150015 Vegetation Management Supporting Map Legend (NOU OG Y A Lot and Plan Category A or B area containing endangered regional ecosystems Category A or B area containing of concern regional ecosystems Category A or B area that is a least concern regional ecosystem Category A or B area containing remnant vegetation Category A or B area under Section 204H These areas are edged in yellow and filed with the remnant RE Status Category C area containing endangered regional ecosystems Category C area containing of concern regional ecosystems. Category C area that is a least concern regional ecosystem Category C area containing high value regrowth vegetation Category C area under Section 20AI ‘These areas are edged in purple and filed with the remnant RE Status Non Remnant Water Wetland on the vegetation management wetlands map Essential habitat on the essential habitat map Essential habitat species record Watercourse on the vegetation management watercourse and drainage feature map (Stream order shown as black number against stream where available) Roads National Parks, State Forest and other reserves Cadastral line Property boundaries shown are provided as a locational aid only Queensland Government LOCALITY DIAGRAM o 150300450600 750m This product is projected into: GDA 1994 MGA Zone 56 Labels for Essential Habitat are centred on the area of enquiry. Regional ecosystem linework has been compiled at a scale of 1:100 000. ‘except in designated areas where a compilation scale of 1:50 000 is, available. Linework should be used as a guide only. The positional accuracy of RE data mapped at a scale of 1:100 000 is +/- 100 metres. Disclaimer: While every care is taken to ensure the accuracy of this product, the Department of Natural Resources and Mines makes no representations or warranties about its accuracy, reliability, completeness or suitability for any particular purpose and disclaims all responsibility and all liability (including without limitation, liability in negligence) for all expenses, losses, damages (including indirect or consequential damage) and costs which you might incurr as a result of the product being inaccurate or incomplete in any way and for any reason Additional information may be required for the purposes of land clearing or assessment of a regional ecosystem map or PMAV applications. For further information go to the web site: www.dnrm.qid.gov.au or contact the Department of Natural Resources and Mines. Digital data for the vegetation management watercourse and drainage feature map, vegetation management wetlands map, essential habitat map and the vegetation management remnant and regional ecosystem map are available from the Queensland Spatial Portal at http:/;www.information. qld.gov.au! © The State of Queensland (Department of Natural Resources and Mines), 2015 Page 2
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19/10/2015 07:38:26
Lot: 7 Plan: SP178340
Vegetation Management Act 1999 - Extract from the essential habitat database
Essential habitat is required for assessment under the:
• State Development Assessment Provisions - Module 8: Native vegetation clearing which sets out the matters of interest to the state for development assessment under the Sustainable Planning
Act 2009; and
• Self-assessable vegetation clearing codes made under the Vegetation Management Act 1999
Essential habitat for one or more of the following species is found on and within 1.1 km of the identified subject lot/s or on and within 2.2 km of an identified coordinate on the accompanying essential habitat
map.
This report identifies essential habitat in Category A, B and Category C areas.
The numeric labels on the essential habitat map can be cross referenced with the database below to determine which essential habitat factors might exist for a particular species.
Essential habitat is compiled from a combination of species habitat models and buffered species records.
The Department of Natural Resources and Mines website (http://www.dnrm.qld.gov.au) has more information on how the layer is applied under the State Development Assessment Provisions - Module 8:
Native vegetation clearing and the Vegetation Management Act 1999.
Regional ecosystem is a mandatory essential habitat factor, unless otherwise stated.
Essential habitat, for protected wildlife, means a category A area, a category B area or category C area shown on the regulated vegetation management map-
1) (a) that has at least 3 essential habitat factors for the protected wildlife that must include any essential habitat factors that are stated as mandatory for the protected wildlife in the essential habitat
database; or
2) (b) in which the protected wildlife, at any stage of its life cycle, is located.
Essential habitat identifies endangered or vulnerable native wildlife prescribed under the Nature Conservation Act 1994.
Essential habitat in Category A and B (Remnant vegetation species record) areas:1100m Species Information
(no results)
Essential habitat in Category A and B (Remnant vegetation species record) areas:1100m Regional Ecosystems Information
(no results)
Essential habitat in Category A and B (Remnant vegetation) areas:1100m Species Information
Label Scientific Name Common Name NCA Status Vegetation Community Altitude Soils Position in
Landscape
609 Litoria freycineti Wallum Rocketfrog V Vegetation community is a mandatory essential habitat factor for Sea level to 200m. Sandy and alluvial None
this species. Freshwater acidic swamps/lagoons (permanent or substrates.
temporary still water) dominated by sedges (e.g. Baumea and
Eleocharis spp.) in heathland (e.g. Banksia/Xanthorrhoea), wallum
(Banksia aemula shrubland/woodland) or Melaleuca open forest
(e.g. M. quinquenervia), and adjacent Eucalyptus racemosa forest,
also found around acidic coastal lakes; on sand and sandstone;
can be found well away from water during non-breeding season.
1135 Pezoporus wallicus Ground Parrot V Lowland dry and wet heathland (0.25-1.5m high, diverse shrubs, Sea level to 200m. Sand and clay Plains and flats.
wallicus sedges & rushes), sedgeplain and sedgeland (excl. permanent substrates.
waterbodies); rarely in adjacent Banksia (wallum), Hakea or
Melaleuca shrubland/woodland with heath understorey.
686 Crinia tinnula Wallum Froglet V Vegetation community is a mandatory essential habitat factor for Sea level to 200m. Sandy and None
this species. Permanent to ephemeral acidic (pH 4.3 - 5.2), soft sandy-alluvial
freshwater in Melaleuca (e.g. M. quinquenervia) swamps, substrates.
sedgeland, wet and dry heathland (e.g. Banksia robur,
Xanthorrhoea) and wallum (Banksia aemula shrubland/woodland)
areas coastal lowlands on sand or sandstone, occasionally in
adjacent open forest/woodland (e.g. Eucalyptus racemosa,
Corymbia citriodora) with heathy understorey; known to persist in
small remnants (<10ha); may be found well away from water.
593 Litoria Wallum Sedgefrog V Vegetation community is a mandatory essential habitat factor for Sea level to 200m. Sandy substrates. Near/in
olongburensis this species. Well vegetated permanent to ephemeral freshwater waterbodies.
swamp, sedgeland, lake or creek, e.g. dense reed beds (including
Baumea, Restio spp.) occasionally with Melaleuca quinquenervia
or Callistemon pachyphyllus, acidic wallum swamps and wallum
creeks on coastal sand masses; most abundant in wallum (Banksia
aemula) swamps that seasonally flood where they are found
year-round; recorded in adjacent wet heath, dry heath, Gahnia
heath and Melaleuca swamp forest/open forest.
Essential habitat in Category A and B (Remnant vegetation) areas:1100m Regional Ecosystems Information
Label Regional Ecosystem (this is a mandatory essential habitat factor, unless otherwise stated)
609 12.2.2, 12.2.5, 12.2.7, 12.2.12, 12.2.13, 12.2.15, 12.3.4, 12.3.5, 12.3.6, 12.3.12, 12.3.13, 12.5.4, 12.5.9, 12.9-10.10,
12.9-10.22. These regional ecosystems are not a mandatory essential habitat factor for this species.
1135 12.2.12, 12.2.13, 12.2.15, 12.3.13, 12.5.9, 12.9-10.22
686 12.2.5, 12.2.7, 12.2.9, 12.2.10, 12.2.12, 12.2.15, 12.3.4, 12.3.5, 12.3.6, 12.3.12, 12.3.14, 12.5.10. These regional
ecosystems are not a mandatory essential habitat factor for this species.
593 12.2.5, 12.2.7, 12.2.12, 12.2.15. These regional ecosystems are not a mandatory essential habitat factor for this species.
Essential habitat in Category C (High value regrowth vegetation) areas:1100m Species Information
(no results)
Essential habitat in Category C (High value regrowth vegetation) areas:1100m Regional Ecosystems Information
Page 3
Page 34
State Planning Policy
Date: 28/09/2015
¢
Department of
Local government development assessment
Infrastructure, Local 0 70 140 210 280
Disclaimer:
This map has been prepared with due care based on the best available information at the time of publication. The State of
Government and Planning Metres
Queensland holds no responsibility for any errors, inconsistencies or omissions within this document. Any decisions made by
other parties based on this document are solely the responsibility of those parties.
© The State of Queensland 2015.
Page 35
Legend
Drawn Polygon Layer
Override 1
Cadastre (5k)
Cadastre (5k)
Bushfire hazard area (Bushfire prone area)
Very High Potential Bushfire Intensity
High Potential Bushfire Intensity
Medium Potential Bushfire Intensity
Potential Impact Buffer
Department of
State Planning Policy Date: 28/09/2015
Infrastructure, Local Local government development assessment
Disclaimer:
Government and Planning
This map has been prepared with due care based on the best available information at the time of publication. The State of
Queensland holds no responsibility for any errors, inconsistencies or omissions within this document. Any decisions made by
other parties based on this document are solely the responsibility of those parties.
© The State of Queensland 2015.
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APPENDIX
D
LOCAL GOVERNMENT
INFORMATION
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APPENDIX
D
LOCAL GOVERNMENT
INFORMATION
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Noosa Plan
Zone Map ZM6
Subject Site
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Noosa Plan
Zone Map ZM6
Noosa Heads
(Zone Map ZM6)
— — | Locality q=e=e=e Major Road Network [Detached Housing
|} — = Boundaries ~—;—~ Railway Line [DSemi-Attached Housing
Property N Shi Attached Housing
[ Boundaries — — - oosa shire Wvisitor Mixed Use
Major Water Boundary (Neighbourhood Centre
| | Bodies Streams Eibusiness Centre
. nd Rivers Community Services
Town/Village Hi Insef (_]Open Space Recreation
Boundaries sa ssasorzamant may be hare by be Cvetay| Hi Open Space Conservation
Gio, naz 3 scale of accuracy of 125 900, a Fe ar en
Sash dete on which 8s Doses was seteered apply fo development appicatens for urban activites, rural residential purposes
eee Plans of Development ——— Of a lot on land outside the Urban Footprint of me SEQ
Counei copyrant Reserved ce ao re
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Noosa Plan
Bushfire Hazard Overlay Map OM6.4
Subject Site
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Noosa Plan
Biodiversity Overlay Map OM6.1
Subject Site
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Extract from Noosa Plan
Section 13.31 Specific outcomes for the Natural Hazards Overlay Code
Table 13.9 Bushfire hazard areas
Column 1 Column 2 Column 3
Specific Outcomes Probable solutions Response
13.33 Effects of use and works
New Uses S4.1 The use is sited on The site is mapped under the
O4 The proposed use does land that is not in a Noosa Plan as Medium bushfire
not compromise the safety Medium or High Bushfire hazard area however the
or people or property from Hazard Area; majority of site vegetation will be
bushfire. OR cleared to facilitate the
S4.2 The use is sited on development.
land that is determined as
low bushfire risk by a site Proposed buildings which
specific bushfire hazard border the surrounding
assessment. vegetation to the east are
required to be set back 15m (1.5
times the predominant height of
the mature tree canopy of 10m).
We understand a minimum
setback distance of 15m to the
eastern boundary will be
available, with building
construction to comply with
BAL19 (for those buildings with
a setback distance of 19m-
<28m) and BAL29 (for those
buildings with a setback
distance of 13m-<19m), to
protect property. The majority of
building setbacks exceed 15m.
A Bushfire Management and
Evacuation Plan has been
prepared for the site to facilitate
safe evacuation in the event of
an emergency.
Protection of S5.1 Community Uses Not applicable – residential
Infrastructure and and Infrastructure Uses development
Community Uses are not located in a High
O5 Community uses and or Medium Bushfire
Infrastructure Uses, Hazard Area identified on
including that identified Overlay maps OM1.4 to
below, are able to function OM9.4;
effectively during and OR
immediately after bushfire S5.2 Building work will not
events- involve more than an
a) Emergency service additional 20m2 of gross
facilities; floor area to an existing
b) Hospitals; building;
c) Education Type 4 uses, OR
including stores for S5.3 Where located in a
valuable records or items of High or Medium Bushfire
historic or cultural Hazard Area identified on
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significance; and Overlay Maps OM1.4 to
d) Service and utility uses, OM9.4, uses are designed
including electricity to function effectively
substations, major electrical during and immediately
depots and water treatment after bushfire events.
plants.
Hazardous Materials S6.1 Hazardous material Not applicable – proposed
O6 Public safety and the are not manufactured and development is residential
environment are not stored on site.
adversely affected by the
detrimental impacts of
bushfire on hazardous
materials manufactured or
stored in bulk.
13.34 Siting, design and construction
O7 Uses and works S7.1 Uses and works Buildings which border the
including building works are including building works surrounding vegetation to the
site, designed and are sited- east are required to be set back
constructed to- a) on lots greater than 15m (1.5 times the predominant
a) minimise the number of 2500m2; height of the mature tree canopy
people ad property subject i) in locations of lowest of 10m).
to bushfire risk; and hazard within the lot;
b) maximise the protection and A minimum separation distance
of people and property ii) to achieve setbacks of 15m is considered
during the passage of a fire from hazardous appropriate for the buildings
front. vegetation of 1.5times along the eastern boundary
the predominant based on the following:
mature tree canopy
height or 10m Construction of buildings
whichever is the <19m from vegetation will be
greater: and in accordance with BAL-29 to
iii) 10m from any minimise potential impact from
retained vegetation bushfire;
strips or small areas of
vegetation; and Construction of buildings
iv) so that the elements 19m-<28m from vegetation will
of the development be in accordance with BAL-19;
least susceptible to fire
are sited closest to the The proposed layout
bushfire hazard; provides for a direct access
b) on lots 2500m2 or less route for evacuation of the site
– to maximise setbacks to Resort Drive;
from hazardous
vegetation. The road and car parking
areas provide a non-vegetated
area between the buildings
and the vegetation;
It is understood that the
applicant is required to install
eight (8) fire hydrants as part
of the development of this site
and Precinct E (the adjoining
Lot 6). A bond of $189,000.00
is being held by Council for
this purpose; and
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Resort Drive will facilitate
safe evacuation from the site if
required, as this road is
bordered by the golf course to
the west and leads away from
hazardous vegetation.
A Bushfire Management
and Evacuation Plan has been
prepared for the site.
13.35 Water supply for fire fighting
O8 An adequate and S8.1 For premises not in a The development will be
accessible water supply is water service area – each connected to a reticulated water
provided for fire fighting lot has an accessible da, supply.
purposes swimming pool or water
tank accessible by the fire
brigade tat contains at
least 5000 litres of water.
13.36 Vehicle access and fire trails
Firebreaks and fire S9.1 Firebreaks are Internal access roads within the
access tracks provided by – proposed development will
O9 Firebreaks or fire a) a cleared road reserve provide vehicle access to the
access tracks provide – not less than 20m wide majority of the perimeter
a) adequate access for located around the between buildings and
firefighting and other perimeter of the hazardous vegetation. The
emergency vehicles: and development; roads will be formed pavement
b) adequate width to OR and provide passing and
minimise the risk of fire b) fire access tracks turnaround areas.
crossover. between the development
and surrounding vegetated
lands that –
i) are a minimum cleared
width of 6m;
ii) have a maximum grade
of 1 in 8 (12.5%);
iii) have a formed
pavement;
iv) have access at each
end and in other locations
where necessary;
v) have passing areas and
turning areas;
vi) have clearly identified
access points for
emergency vehicles; and
vii) are located on public
land or within access
easements that are
granted in favour of the
Sunshine Coast Regional
Council (sic) and the
Queensland Fire and
Rescue Service.
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