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2014-01-28 Planning & Organisation Committee Item 4.4 Attachment 1
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ATTACHMENT 1
Planning & Organisation Committee
28 January 2014, Item 4.4
Temporary Local Planning Instrument
(Protected Vegetation Overlay) 2014
It is hereby certified that this is a true and correct copy of
Temporary Local Planning Instrument (Protected Vegetation Overlay) 2014
made in accordance with the Sustainable Planning Act 2009, by the Noosa Council.
Brett de Chastel
Chief Executive Officer
Date
1
Noosa Council
Temporary Local Planning Instrument
(Protected Vegetation Overlay) 2014
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Section 2
2
Noosa Council
Temporary Local Planning Instrument
(Protected Vegetation Overlay) 2014
2
Noosa Council
Temporary Local Planning Instrument
(Protected Vegetation Overlay) 2014Section 3
3
Noosa Council
Temporary Local Planning Instrument
(Protected Vegetation Overlay) 2014
Temporary Local Planning Instrument (Protected Vegetation Overlay) 2014
Page
Contents
Part 1 Preliminary ................................................................................................. 4
1 Short title ......................................................................................................................4
2 Object ..........................................................................................................................4
3 Commencement .........................................................................................................4
4 Expiry ..........................................................................................................................4
5 Interpretation ...............................................................................................................4
Part 2 Application of temporary local planning instrument .............................. 5
6 Application ..................................................................................................................5
7 Effect ...........................................................................................................................5
Part 3 Protected vegetation overlay .................................................................... 5
Division 1 General provisions ................................................................ 5
8 Structure .....................................................................................................................5
9 Protected vegetation overlay area ..............................................................................5
10 Protected vegetation ...................................................................................................5
11 Exempt clearing ..........................................................................................................6
Division 2 Assessment table .................................................................. 8
12 Assessment categories and relevant assessment criteria ...........................................8
13 Relationship with planning schemes ...........................................................................9
14 Protected vegetation overlay code ..............................................................................9
15 Compliance ..................................................................................................................9
16 Overall outcomes .........................................................................................................9
17 Specific outcomes and probable solutions ................................................................10
Schedule 1 Dictionary ................................................................................................. 12
Schedule 2 Property vegetation management plans for category 4 lots in the
prescribed Noosa Area ........................................................................... 17
Section 4
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Temporary Local Planning Instrument
(Protected Vegetation Overlay) 2014
Temporary Local Planning Instrument (Protected Vegetation Overlay) 2014
Part 1 Preliminary
1 Short title
This temporary local planning instrument may be cited as Temporary Local
Planning Instrument (Protected Vegetation Overlay) 2014.
2 Object
The object of this temporary local planning instrument is to ensure that
operational work for clearing protected vegetation within the local government
area, is appropriately managed through the application of provisions which
affect the operation of the planning schemes for the local government area.
3 Commencement
This temporary local planning instrument commences on 24 June 2014.
4 Expiry
This temporary local planning instrument expires on 24 June 2015.
5 Interpretation
(1) The dictionary in schedule 1 defines particular words used in this temporary
local planning instrument.
(2) In the interpretation of the following provisions of this temporary local planning
instrument, consideration may be given to the identified extrinsic material under
the Statutory Instruments Act 1992 —
(a) Schedule 2— a property vegetation management plan for a category 4
lot in the prescribed Noosa area under the former local law.
Section 5
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Temporary Local Planning Instrument
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Part 2 Application of temporary local planning
instrument
6 Application
(1) This temporary local planning instrument applies to the Noosa local government
area.
(2) This temporary local planning instrument applies to The Noosa Plan being
the planning scheme for the Noosa local government area.
7 Effect
This temporary local planning instrument affects the operation of the planning
scheme for the local government area by applying the provisions of Part 3
(Protected vegetation overlay) to the planning scheme.
Part 3 Protected vegetation overlay
Division 1 General provisions
8 Structure
Part 3 (Protected vegetation overlay) comprises the following—
(a) definitions;
(b) the protected vegetation overlay area;
(c) the assessment table for the protected vegetation overlay;
(d) the protected vegetation overlay code.
9 Protected vegetation overlay area
(1) The protected vegetation overlay applies to the planning scheme area of
The Noosa Plan prescribed Noosa Area.
10 Protected vegetation
The vegetation in the protected vegetation overlay area identified in Table 1
is protected from clearing (protected vegetation).
Section 6
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Table 1 Protected vegetation
Column 1 Column 2
Protected vegetation Protected vegetation
overlay area
Prescribed Noosa area 1. Category 1, 2 and 3 lots (refer to schedule 1) – all
vegetation
2. Category 4 lot – the vegetation identified as protected
vegetation for a property vegetation management plan in
schedule 2
11 Exempt clearing
(1) Protected vegetation in the protected vegetation overlay area may be cleared in the
circumstances stated in this section (exempt clearing).
(2) The following is exempt clearing in the prescribed Noosa area of the protected
vegetation overlay area—
(a) clearing which is a property maintenance activity;
(b) clearing which is reasonably necessary for emergency access or work or
is immediately required in response to an accident or emergency;
(c) clearing on a category 4 lot identified as exempt clearing for a property
vegetation management plan in schedule 3;
(d) clearing which is reasonably necessary for carrying out work that is—
(i) authorised or required under an Act, regulation or local law; or
(ii) specified in a notice given by the local government or another
regulatory authority;
(e) clearing in accordance with a development approval;
(f) clearing on a category 1 lot, where—
(i) the vegetation is within three (3) metres of an existing building
or structure; and
(ii) the clearing is reasonably necessary for access to the building or
structure or has been approved in a landscape plan; and
(iii) the vegetation is not otherwise required to be retained in
accordance with a development approval;
Section 7
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(g) clearing on a category 2 or 3 lot, where—
(i) the vegetation is within ten (10) metres of an existing building
or structure; and
(ii) the clearing is reasonably necessary for access to the building or
structure or has been approved in a landscape plan; and
(iii) the vegetation is not otherwise required to be retained in
accordance with a development approval;
(h) clearing on a category 3 or 4 lot greater than ten (10) hectares in area,
where—
(i) the vegetation is within 30 metres of a building or within ten
(10) metres of a structure; and
(ii) the clearing is reasonably necessary for the control of fire risk to
the building or structure; and
(iii) the vegetation is not otherwise required to be retained in
accordance with a development approval;
(i) clearing vegetation within the path of a utility service;
(j) clearing on a category 1, 2 or 3 lot, where the clearing —
(i) is pruning of native vegetation for the purpose of tree
maintenance or hazard management; and
(ii) results in no more than 20% loss of the live canopy volume of a
tree within a 12 month period; and
(iii) does not involve lopping or topping;
(k) the clearing is on a category 1, 2 or 3 lot, where the clearing is to
vegetation that is regrowth other than the following—
(i) vegetation in an area identified as a significant land slip hazard
potential in the local government’s planning scheme;
(ii) vegetation which is an endangered, vulnerable and near
threatened plant as defined by the Nature Conservation
(Wildlife) Regulation 2006;
(iii) vegetation which is critically endangered or vulnerable flora as
defined by the Commonwealth Environment Protection and
Biodiversity Conservation Act 1999;
(iv) heathland;
(v) riparian vegetation;
Section 8
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(vi) vegetation in a critical habitat;
(vii) vegetation in an area that has been cleared in
contravention of a local law including the former local
law;
(l) clearing on land in the Agricultural Land Conservation Area
(ALCA) identified in the local government’s planning scheme;
(m) clearing in the course of a fire management activity;
(n) clearing in the course of a forest practice;
(o) clearing in accordance with a permit under the former local law.
Division 2 Assessment table
12 Assessment categories and relevant assessment criteria
(1) The assessment category for operational work for clearing protected vegetation
in the protected vegetation overlay area is identified in column 2 of Table 2.
(2) The relevant assessment criteria for operational work for clearing protected
vegetation in the protected vegetation overlay area is identified in column 3
of Table 2.
Table 2 Assessment categories and relevant assessment criteria
Column 1 Column 2 Column 3
Type of development Assessment category Assessment criteria
Operational work for clearing Exempt if exempt clearing If code assessable—
protected vegetation in the Protected vegetation overlay
protected vegetation overlay Code assessable if not exempt code
area clearing
Editor's notes—
1. Operational work for clearing vegetation does not include clearing vegetation on—
a forest reserve under the Nature Conservation Act 1992; or
a protected area under the Nature Conservation Act 1992, section 28; or
an area declared as a state forest or timber reserve under the Forestry Act 1959; or
a forest entitlement area under the Land Act 1994. (Sustainable Planning Act 2009, section 10)
2. Clear, for vegetation—
(a) means remove, cut down, ringbark, push over, poison or destroy in any way including by burning,
flooding or draining; but
(b) does not include destroying standing vegetation by stock, or lopping a tree. (Sustainable Planning Act
2009, schedule 3)
3. Destroy, for vegetation, includes destroying it by burning, flooding or draining. (Sustainable Planning Act 2009,
schedule 3)
Section 9
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4. Lopping, a tree, means cutting or pruning its branches, but does not include—
(a) removing its trunk; and
(b) cutting or pruning its branches so severely that it dies. (Sustainable Planning Act 2009, schedule 3)
13 Relationship with planning schemes
If there is a difference between the assessment category for operational work
for clearing protected vegetation in the protected vegetation overlay area and
the assessment category for clearing vegetation in an assessment table of the
Noosa Plan, the higher assessment category is to prevail as follows—
(a) self-assessable development is a higher assessment category than
exempt development; and
(b) code assessable development is a higher assessment category than
exempt development and self-assessable development; and
(c) impact assessable development is a higher assessment category
than exempt development, self-assessable development and code
assessable development.
Division 3 Protected vegetation overlay code
14 Protected vegetation overlay code
The following provisions in this division comprise the protected vegetation
overlay code—
(a) compliance with the protected vegetation overlay code (section
15);
(b) overall outcomes for the protected vegetation overlay code
(section 16);
(c) specific outcomes and probable solutions for the protected
vegetation overlay code (section 17).
15 Compliance
Operational work for clearing protected vegetation in the protected vegetation
overlay area complies with the protected vegetation overlay code if there is
compliance with—
(a) the specific outcomes and overall outcomes of the protected
vegetation overlay code; or
(b) the overall outcomes of the protected vegetation overlay code if
the clearing of protected vegetation does not comply with the
specific outcomes.
16 Overall outcomes
(1) The overall outcomes are the purpose of the protected vegetation overlay code.
Section 10
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(2) The overall outcomes sought for the protected vegetation overlay code are the
following—
(a) to ensure that clearing protected vegetation, in particular significant
vegetation, only occurs where it is reasonably necessary;
(b) to ensure that where clearing protected vegetation is reasonably
necessary it occurs in an environmentally responsible manner.
17 Specific outcomes and probable solutions
(1) The specific outcomes sought for the protected vegetation overlay code are
identified in column 1 of Table 3.
(2) The probable solutions for assessable development are identified in column 2 of
Table 3.
Table 3 Specific outcomes and probable solutions
Column 1 Column 2
Specific outcomes Probable solutions
Clearing protected vegetation in the prescribed Noosa area of the protected
vegetation overlay area
O1 Clearing protected vegetation does not involve the No solution provided.
following—
(a) vegetation listed or referred to in the National Trust
of Queensland Heritage Register or in a Heritage
Register of the local government in a planning
scheme policy;
(b) vegetation identified or referred to in State or
Commonwealth legislation;
(c) habitat for an animal or plant identified in State or
Commonwealth legislation;
(d) vegetation located on a prominent hillside, slope or
ridgeline;
(e) vegetation the clearing of which may cause or
contribute to erosion or slippage;
(f) riparian vegetation;
(g) vegetation the clearing of which may have an
adverse impact on the hydrology of an area or upon
a hydrologically-sensitive plant community such as
heathland, sedgeland, melaleuca forest or mangrove
forest;
(h) vegetation which is or is capable of forming or
contributing to a buffer between different land uses;
(i) vegetation which is or is capable of forming or
contributing to a visual buffer or a buffer against
pollution, light spillage or noise;
(j) vegetation which contributes to visual amenity or
landscape quality
(k)
Section 11
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O2 Clearing protected vegetation does not involve the No solution provided.
following—
(a) vegetation within 400 metres of the full level of
ponded water within Lake Macdonald;
(b) vegetation the clearing of which is likely to
increase the risk of erosion;
(c) vegetation the clearing of which is likely to have
an adverse environmental impact;
(d) remnant vegetation of local origin, classified as
remnant of concern regional ecosystem or remnant
endangered regional ecosystem or is vegetation
located in a wetland;
(e) vegetation which has natural or cultural heritage
values;
(f) vegetation the clearing of which is likely to have an
adverse impact on a water catchment area or water
quality;
(g) vegetation the clearing of which is likely to have an
adverse impact on the diversity of flora and fauna
species supported or likely to be supported by the
vegetation;
(h) vegetation the clearing of which is likely to have an
adverse impact on a flora or fauna community
which has conservation status;
(i) vegetation the clearing of which is likely to have an
adverse impact on any individual species of flora
and fauna which has conservation status;
(j) vegetation the clearing of which is likely to have an
adverse impact on a person or industry reliant on
maintaining the vegetation;
(k) vegetation the clearing of which is likely to have an
adverse impact on the neighbouring land.
Section 12
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Schedule 1 Dictionary
section 5
building has the same meaning in the Sustainable Planning Act 2009.
category 1 lot means a freehold lot of 0.3 hectares or less in the prescribed Noosa area of
the protected vegetation overlay area.
category 2 lot means a freehold lot of more than 0.3 hectares but less than 2 hectares in the
prescribed Noosa area of the protected vegetation overlay area.
category 3 lot means a freehold lot of 2 hectares or more, other than a category 4 lot, in the
prescribed Noosa area of the protected vegetation overlay area.
category 4 lot means a freehold lot of 2 hectares or more which is subject to a property
vegetation management plan in the prescribed Noosa area of the protected vegetation
overlay area.
clearing has the same meaning in the Sustainable Planning Act 2009.
critical habitat has the same meaning in the Nature Conservation Act 1992.
destroy has the same meaning in the Sustainable Planning Act 2009.
development has the same meaning in the Sustainable Planning Act 2009.
development application has the same meaning in the Sustainable Planning Act 2009.
development approval has the same meaning in the Sustainable Planning Act 2009.
development permit has the same meaning in the Sustainable Planning Act 2009.
environment has the same meaning in the Sustainable Planning Act 2009.
exotic weeds means a species of plant occurring in an area outside its historical natural
range and which has a negative impact for the environment or people.
fire management activity means the controlled use of fire for pasture management, to
manage the risk of wild fire and to assist with the maintenance of ecological processes in
vegetation communities that are ecologically adapted to fire.
foreshore means the land in the local government area lying between the high water
mark and low water mark at ordinary spring tides and controlled by the local
government under the Local Government Act 2009.
forest practice has the same meaning in the Sustainable Planning Act 2009.
former local law means Interim Local Law No. 8 (Protection of Vegetation) 2011 and
includes Interim Subordinate Local Law No. 8 (Protection of Vegetation) 2011.
Section 13
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heathland means a vegetation community of local origin that is characterised by high
species diversity and a canopy height generally less than 1.5 metres, growing on sandy
soils and or soils subject to periodic inundation or waterlogging.
infrastructure has the same meaning in the Sustainable Planning Act 2009.
infrastructure agreement has the same meaning in the Sustainable Planning Act 2009.
land has the same meaning in the Sustainable Planning Act 2009.
land degradation means the following—
(a) soil erosion;
(b) a rising water table;
(c) the expression of salinity;
(d) mass movement by gravity of soil or rock;
(e) stream bank instability;
(f) a process that results in declining water quality in a river stream, creek or
watercourse or natural wetland.
local government area has the same meaning in the Sustainable Planning Act 2009.
local law has the same meaning in the Local Government Act 2009.
local origin means a species occurring in an area which is within its historical
natural range.
lopping has the same meaning in Sustainable Planning Act 2009.
lot has the same meaning in Sustainable Planning Act 2009.
native vegetation means vegetation of local origin occurring within its natural range.
natural heritage means any of the following—
(a) biodiversity and critical habitat as defined in the Nature Conservation Act
1992;
(b) an endangered, vulnerable, near threatened or presumed extinct species as
defined in the Nature Conservation (Wildlife) Regulation 2006;
(c) a matter of national environmental significance as defined in the
Environment Protection and Biodiversity Conservation Act 1999;
(d) an area included in the Commonwealth Government's Register of the
National Estate;
Section 14
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(e) an endangered and of concern regional ecosystem as defined in the
Vegetation Management Regulation 2000;
(f) vegetation required to support, protect and maintain biodiversity values within
the local government area, whether these be of local, regional, state or
national significance.
operational work has the same meaning in the Sustainable Planning Act 2009.
owner has the same meaning in the Sustainable Planning Act 2009.
exempt clearing see section 11.
planned burning means the burning of vegetation for the purpose of reducing the risk of
bushfire.
planning scheme area has the same meaning in the Sustainable Planning Act 2009.
planning scheme policy has the same meaning in the Sustainable Planning Act 2009.
prescribed Noosa area see section 9.
property maintenance activity means clearing protected vegetation which is
reasonably necessary for property maintenance including the following—
(a) the construction and maintenance of a farm track, fence and shed on a site;
(b) the maintenance of crops;
(c) the slashing of grass;
(d) the harvesting of crops;
(e) the maintenance of pasture and cleared land areas;
(f) the pruning, felling and clearing of orchard vegetation species;
(g) surveying purposes;
(h) the collection of firewood for non-commercial purposes;
(i) the removal of an exotic weed;
(j) any other maintenance activity specified in a property vegetation
management plan.
property vegetation management plan is a specific program of vegetation
management for a category 4 lot in the prescribed Noosa area of the protected
vegetation overlay area approved under the former local law which is included in
schedule 3.
protected vegetation see section 10.
Section 15
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protected vegetation overlay area means the parts of the local government area to which
the protected vegetation overlay applies as identified in section 9.
pruning has the same meaning in the Australian Standard AS 4373-2007.
reasonably necessary means clearing protected vegetation for a particular purpose where
there is no alternative way of achieving the purpose that is prudent and feasible and
would avoid clearing protected vegetation or significantly reduce the extent of clearing
protected vegetation.
regional ecosystem has the same meaning in the Vegetation Management Act 1999.
regrowth means any vegetation that is less than seven (7) years of age.
riparian vegetation includes the following—
(a) vegetation along a foreshore;
(b) vegetation in a permanent freshwater watercourse or existing within 50 metres
from the top of the bank of a permanent freshwater watercourse;
(c) vegetation in a permanent tidal watercourse or existing within 250 metres from
the top of the bank of a permanent tidal watercourse;
(d) vegetation in Lake Macdonald or within 400 metres of the full level of
ponded water within Lake Macdonald;
(e) vegetation in a riparian zone.
riparian zone means land which adjoins, directly influences or is influenced by a body
of water.
road has the same meaning in the Sustainable Planning Act 2009.
significant vegetation means the following—
(a) vegetation which is a valuable part of the historic, cultural, or natural
heritage of the local government area;
(b) vegetation which is important for protecting from land degradation;
(c) vegetation which is important for protecting, enhancing or contributing to local
and regional biodiversity values;
(d) vegetation which is important for protecting or enhancing a terrestrial or
aquatic waterway, water catchment or an ecosystem contained therein;
(e) vegetation which is important for its beneficial effect on the visual
amenity and landscape quality of the locality in which it is situated.
topping has the same meaning in the Australian Standard AS 4373-2007.
vegetation includes a tree, plant and an organism of vegetable origin, whether living
or dead, but does not include—
Section 16
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(a) a plant declared as a pest under the Land Protection (Pest and Stock Route
Management) Act 2002; or
(b) a weed or undesirable plant species as identified in a planning scheme
policy.
watercourse means a river, creek, stream or channel which contains water under
normal conditions.
waterway means a river, stream, creek, wetland, estuary, lake, lagoon and coastal
waters.
wetland means an area of permanent or periodic inundation, whether natural or
artificial, static or flowing, fresh, brackish or saline, and includes an area of
marine water the depth of which at low tide is less than 6 metres.
Section 17
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Schedule 2 Property vegetation and exempt clearing for property
vegetation management plans for category 4 lots in
the prescribed Noosa area
sections 10 and 11
Column 1 Column 2 Column 3 Column 4
Item Land Protected Exempt clearing for a property vegetation
vegetation for a management plan
property vegetation
management plan
1. Lot 183 on All vegetation Clearing for selected native forest harvesting in the
MCH947 areas identified on Plan 1 in accordance with the
126 Coveys following—
Road, 1. Ongoing management for sustainable timber
Tinbeerwah harvesting shall be carried out in areas of the land
indicated in Plan 1.
2. Timber harvesting shall be carried out in accordance
with the Department of Natural Resources Code of
Practice for Native Forest Timber Production.
2. Lot 2 on All vegetation Clearing for sustainable harvesting in the native
RP228124 vegetation area identified on Plan 2A and for farm
247 Eastern forestry in the plantation areas identified on Plan 2B in
Branch Road, Kin accordance with the following—
Kin 1. Timber harvesting is to be limited to—
the native vegetation area shown on Plan
2A; and
the farm forestry plantation area shown on
Plan 2B.
2. All timber harvesting shall be carried out in
accordance with the following codes of practice
nominated as amended—
Code of Practice for Native Forest Timber
Production (Department of Natural
Resources and Mines 1998);
Code of Practice for Plantation Forestry
(Department of Natural Resources and Mines
1997).
3. Lot 5 on All vegetation Clearing identified on Plan 3 in accordance with the
RP202431 following—
569 Black 1. Explore the beneficial use of any camphor laurel or
Mountain Road, wattle trees that are to be cleared either for timber or
Black Mountain firewood.
2. Notify the local government and the adjacent
neighbours when clearing works are to commence.
Section 18
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Column 1 Column 2 Column 3 Column 4
Item Land Protected Exempt clearing for a property vegetation
vegetation for a management plan
property vegetation
management plan
3. Cleared areas should be stabilised as soon as
possible by sowing grass seed at the recommended
rate to ensure rapid ground cover.
4. Obtain necessary permits from the fire warden
before any burning of cleared vegetation.
4. Lot 4 on All vegetation Clearing for thinning of native timber identified on
RP867319 Plan 4 in accordance with the following—
325 Top Forestry 1. Erosion from clearing works is to be minimised by
Road, Ridgewood windrowing cleared material along the contours and
sowing grass seed on cleared land.
2. Notify the local government and adjacent
neighbours when clearing is to take place.
3. Explore the beneficial re-use of any cleared timber
either for timber or firewood.
5. Lot 2 on All vegetation Clearing only for regeneration of the previously cleared
SP129577 area identified on Plan 5 in accordance with the
162 Ewarts Road, following—
Cooran 1. Areas that have recently been cleared, or excavated,
including the wall of the dam, shall be stabilised by
sowing grass seed.
2. The gully that had cleared vegetation pushed into it
should be allowed to regenerate with native species
to a width of 10 metres from each side of the gully.
6. Lot 10 on All vegetation Clearing for the thinning and regeneration of vegetation
RP802936 in the areas identified on Plan 6 in accordance with the
63 Hawk Road, following—
Pomona 1. All mature (greater than 300mm diameter at breast
height) Eucalypt trees (including trees which exhibit
nesting hollows) are to be retained in the area to be
cleared of regrowth vegetation.
2. Cleared trees shall be stabilised by sowing grass
seed at the recommended rate.
3. Explore the beneficial reuse of any cleared material,
such as firewood or poles as an alternative to
burning cleared material.
4. Appropriate sediment and erosion control devices
(such as temporary silt fences, and gully rock
stabilising spillways) shall be installed below
earthworks associated with construction of the two
dams to minimise potential sediment pollution of
any waterways.
5. Notify the local government and immediate
Section 19
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Column 1 Column 2 Column 3 Column 4
Item Land Protected Exempt clearing for a property vegetation
vegetation for a management plan
property vegetation
management plan
neighbours when works are to commence.
6. If burning off is required, obtain the necessary
permits from the fire warden and notify neighbours
when burning off is to occur.
7. Notify the local government when works are
finished to arrange a site inspection to ensure
compliance.
7. Lots 1 and 2 on All vegetation other Clearing for thinning regrowth for pasture and
RP102171 than in areas for harvesting spotted gum in the areas identified on Plan 7
228 Bunneys existing pasture in accordance with the following—
Lane and Kin Kin identified on Plan 7 1. All timber harvesting shall be in accordance with the
Road, Gympie Department of Natural Resources and Mines Code
of Practice for Native Timber Harvesting.
2. Following harvesting, ensure minimisation of
erosion by sowing grass seed on all bare areas.
3. Obtain a permit from the fire warden, and notify all
adjacent neighbours prior to burning off.
4. Notify the local government and all adjacent
neighbours prior to the harvesting work being
carried out.
5. Notify the local government when works are
finished to arrange a site inspection.
8. Lot 2 on All vegetation Clearing for farm forestry in the area identified on Plan
RP197576 8 in accordance with the following—
245 Middle Creek 1. Notify the farm forestry plot with the local
Road, Federal government once it is established.
9. Lot 1 on All vegetation Clearing for possible selective logging, existing farm
RP61270 forestry, regrowth areas for farm forestry, orchard,
94 Honeytree pasture and existing orchard in the areas identified on
Lane, Ridgewood Plan 9 in accordance with the following—
1. Notify the local government and adjacent
landholders when clearing is to take place.
2. The areas designated as ‘Nature Conservation and
Possible Selective Logging’ on the plan shall
undergo a site meeting and inspection from the local
government prior to any logging activity taking
place and until such time these areas should be set
aside for nature conservation.
3. Obtain a permit from the fire warden, and notify all
adjacent landholders prior to any burning off
activity.
10. Lot 5 on All vegetation Clearing for existing farm forestry, cleared and
Section 20
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Column 1 Column 2 Column 3 Column 4
Item Land Protected Exempt clearing for a property vegetation
vegetation for a management plan
property vegetation
management plan
RP867807 regrowth areas for farm forestry and selective logging
549 Middle Creek of remnant vegetation in the areas identified on Plan 10
Road, Black in accordance with the following—
Mountain 1. Comply with the ‘Native Forest Timber Production
Code of Practice’ for the Selective Logging area
indicated on Plan 10.
2. Notify the local government and adjacent
landholders when clearing and/or logging is to take
place.
3. No native vegetation shall be removed from gully
lines or steep sloping land.
4. All effort shall be made to retain and incorporate
native species in the proposed farm forestry plots.
5. Immediately after vegetation removal the cleared
area should be grassed and/or established for farm
forestry.
11. Lots 3, 4 and 5 on All vegetation Clearing for increased pasture area, small crops and
RP802272 and timber usage and the existing pine plantation in the
Lots 1 and 2 on areas identified on Plan 11 in accordance with the
RP192819 following—
314, 397, 403, 1. Notify the local government and adjacent
314, 292 Old landholders when clearing of vegetation is to occur.
Ceylon Road, 2. Vegetation removal to increase the pasture area
Ridgewood identified on Plan 11 is to be restricted to
environmental weeds and dying/dead wattles.
3. With the exception of item 2, no native vegetation is
to be interfered with.
4. Obtain a permit from the fire warden, and notify all
adjacent neighbours prior to burning off cleared
material.
12. Lots 6 and 7 on All vegetation Clearing for cattle and weed removal in the area
RP225964 identified on Plan 12 in accordance with the
782 and 806 following—
Black Mountain 1. No native species are to be interfered with apart
Road Black from the Acacia species.
Mountain, 2. No native vegetation clearing is to occur on steep
Cooroy sloping lands or within 30 metres from a waterway.
3. All environmental weeds are to be controlled and
removed from the property.
4. Prior to any significant vegetation clearing the
adjoining properties should be notified.
Section 21
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Column 1 Column 2 Column 3 Column 4
Item Land Protected Exempt clearing for a property vegetation
vegetation for a management plan
property vegetation
management plan
13. Lot 2 on All vegetation Clearing for environmental weeds for the whole of the
RP192071 land and selective clearing in the area identified on
72 Upper Plan 13 in accordance with the following—
Pinbarren Creek 1. Notify the local government and adjacent
Road, Pinbarren neighbours when clearing is to take place.
2. Only Acacia regrowth and environmental weeds are
to be cleared.
3. A minimum of 10 metre buffers are to be retained
for the gullies in the regrowth area.
4. No native vegetation is to be removed from steep
sloping land.
5. All environmental weeds are to be managed and
removed from the whole property.
14. Lot 11 on All vegetation Clearing for environmental weeds for the whole of the
RP814550 land and for selective clearing in the area identified on
132 Eastern Plan 14 in accordance with the following—
Branch Road, Kin 1. Notify the local government and adjacent
Kin neighbours when clearing is to take place.
2. Only Acacia regrowth and environmental weeds are
to be cleared.
3. No other native vegetation is to be removed from
steep sloping land.
4. All environmental weeds are to be managed and
removed from the whole property.
15. Lots 1 and 2 on The vegetation Clearing in accordance with the following—
SP 175064 identified for 1. Comply with the Vegetation Management Plan
1161 and 1145 protection in the dated 15 August 2006 included as Plan 15.
Cooroy Belli Vegetation
2. The five (5) large Crows Ash trees in Area G are to
Creek Road, Management Plan
be retained for aesthetic purposes and as potential
Ridgewood dated 15 August 2006
regenerators (seed dispersal).
and included as Plan
15 3. Where practically possible, rainforest species will be
retained for regeneration purposes.
16. Lot 3 on All vegetation Clearing in the approved clearing area and for removal
RP810775 of wattle regrowth in the areas identified on Plan 16 in
388 Coles Creek accordance with the following—
Road, Cooran 1. No vegetation within the Environmental Protection
zone under the Biodiversity Overlay of the Noosa
Plan 2006 may be cleared except for declared plants
and plans described as an undesirable plant species
in the Noosa Planning Scheme Policy 3 -
Landscaping Plants and Guidelines.
Section 22
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Column 1 Column 2 Column 3 Column 4
Item Land Protected Exempt clearing for a property vegetation
vegetation for a management plan
property vegetation
management plan
2. No vegetation may be cleared within a 20 metre
buffer zone either side of each waterway including
dams (refer to Plan 16), except for declared plants
and plants described as an undesirable plant species
in the Noosa Planning Scheme Policy 3 -
Landscaping Plants and Guidelines.
3. No regrowth vegetation may be cleared within the
area on the south western side of the property
entrance.
4. Revegetation with native species will be undertaken
in steep areas where the progressive removal of
Wattle regrowth (predominately Hickory and
Blackwood Wattle) has been permitted as generally
depicted on Plan 16. Species to be utilised in
revegetation may be selected from the species list
listed on Plan 16.
5. Declared plants and plants described as an
undesirable plant species in the Noosa Planning
Scheme Policy 3 - Landscaping Plants and
Guidelines may be progressively removed from the
property in a manner that causes minimal soil
disturbance.
6. Clearing widths for access roads and fences will be
no greater than 5 metres with passing lanes every 50
metres.
7. All clearing works will be undertaken manually and
cause minimum soil disturbance. All cleared
vegetation will be mulched and/or left to decompose
on site.
17. Lots 9 and 10 on All vegetation Clearing in accordance with the following—
RP885219 1. A vegetated buffer zone as identified on Plan 17 be
66 and 70 Forest maintained around the perimeter of the lower eastern
Acres Drive, boundary of the property, to a minimum width of 15
Cooroy metres. This 15 metre buffer will consist of native
vegetation (allowing native understorey to
regenerate) and be maintained weed free to ensure
natural regeneration. Due to the existence of
regenerative native species there is no need for
further planting.
2. No further clearing or thinning of vegetation be
carried out on the land for any purpose.
3. The existing native vegetation and buffer areas
identified on Plan 17 are to be maintained free of
Section 23
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Column 1 Column 2 Column 3 Column 4
Item Land Protected Exempt clearing for a property vegetation
vegetation for a management plan
property vegetation
management plan
Lantana and Cassia (and any other species listed as
an undesirable plant species in the Noosa Planning
Scheme Policy 3 – Landscaping Plans and
Guidelines to ensure natural regeneration and
succession.
18. Lot 3 on All vegetation Clearing for the conduct of forestry activities in the
RP860472 area identified as forestry on Plan 18 subject to the
471 Sister Tree following—
Creek Road, Kin 1. The forestry activities must not cause land
Kin degradation.
2. Adequate sediment and erosion controls must be in
place to prevent pollutants entering a water body
when conducting forestry activities.
3. A copy of the letter from the Sunshine Coast
Regional Council dated 4 March 2011 regarding the
property vegetation management plan must be
provided on request when conducting the planted
native forestry use.
19. Lots 2 and 3 on All vegetation Clearing in the fully cleared area and for selective
RP131369 thinning in the areas identified on Plan 19 subject to
96 and 108 Black the following—
Mountain Range 1. All cleared areas are to be sown with Japanese
Road, Cooroy Millet at the recommended rate of 25 kilograms per
hectare following clearing.
20. Lot 2 on The vegetation Clearing in accordance with the Property Vegetation
RP207968 identified for Management Plan dated 7 February 2011 included as
157 Moran Group protection in the Plan 20.
Road, Kin Kin Property Vegetation
Management Plan
dated 7 February 2011
and included as
Plan 20
Editor’s note—
In the interpretation of schedule 3, consideration may be given to a property vegetation management plan for a
category 4 lot in the prescribed Noosa area under the former local law as extrinsic material under the Statutory
Instruments Act 1992 (see section 4).
Section 24
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Plan 1 Lot 183 on MCH947 126 Coveys Road Tinbeerwah
Section 25
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(Protected Vegetation Overlay) 2014
Plan 2A Lot 2 on RP228124 247 Eastern Branch Road Kin Kin
Section 26
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Plan 2B Lot 2 on RP228124 247 Eastern Branch Road Kin Kin
Section 27
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Plan 3 Lot 5 on RP202431 569 Black Mountain Road Black Mountain
Section 28
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Plan 4 Lot 4 on RP867319 325 Top Forestry Road Ridgewood
Section 29
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Plan 5 Lot 2 on SP129577 162 Ewarts Road Cooran
Section 30
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Plan 6 Lot 10 on RP802936 63 Hawk Road Pomona
Section 31
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Plan 7 Lots 1 and 2 on RP102171 228 Bunneys Lane and Kin Kin Road Gympie
Section 32
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Plan 8 Lot 2 on RP197576 245 Middle Creek Road Federal
Section 33
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Plan 9 Lot 1 on RP61270 94 Honeytree Lane Ridgewood
Section 34
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Plan 10 Lot 5 on RP 867807 549 Middle Creek Road Black Mountain
Section 35
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Plan 11 Lots 3, 4 and 5 on RP802272 and Lots 1 and 2 on RP192819 314 397, 403, 314, 292 Old
Ceylon Road Ridgewood
Section 36
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Plan 12 Lots 6 and 7 on RP225964 782 and 806 Black Mountain Road Black Mountain
Section 37
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Plan 13 Lot 2 on RP192071 72 Upper Pinbarren Creek Road Pinbarren
Section 38
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Plan 14 Lot 11 on RP814550 132 Eastern Branch Road Kin Kin
Section 39
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Plan 15 Lots 1 and 2 on SP 175064 1161 and 1145 Cooroy Belli Creek Road Ridgewood
Section 40
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40
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Bach to the Brest
Intreduction
|
This report addresses a Noosa Shire Council request for a Property Vegetation Management |
Plan outlining forestry operations on Lots 1 and 2 SP 175064. ‘The proponent originally
purchased the land to utilise forest resources and provide a source of income. As tho land is
| not suitable for most other forms of primary production, the sustainable harvest of timber
products is a viable land use. The landholders offorts to date and in future aim to ereate a |
secure, productive and sustainable forest, while maintaining important ecological values.
| Several documents are attached including a Bushfire Management Report (Peter Turner), a
report on forestry practice methods to date (Dr G J Bacon) and the ‘code applying w native |
forest practice’. These documents are well compiled and | have avoided repetition of their
content.
| This document is divided into 4 sections: |
1) Background information — Page 2
2) Vegetation assessment — Page 3
3) Vegetation manugement — Page 5 |
4) summary - Page 9
|
Section 1 Background Information
1.1) Site History |
Much of the site was originally cleared for timber and to open up the land for grazing. Some
| areas are still open and dominated by exotic grusses, while others have been allowed to
regenerate naturally with forest averaging 30 — 50 yrs old,
| 1.2) Method
|
* Maps were derived by the current landowner using a Council supplied aerial photo with
DCDB and contours as a background and hand drawn overiays.
| * Reference material includes: SEQ Regional Ecosystems (EPA Qld Herbarium ~ Mapping )
Release SEQ 2004 Version 5) and the Code applying to native forest practice (NRM —
December 2005),
| ® Maro Russell carried out ground teuthing and vegetation surveys on 13/7/2006, |
The site was traversed along existing access tracks, along a major gully and parts of the |
creek to cover all represented RE's and one of the drainage lines to determine specics
| F
* Species scheduled under the Nature Conservation Act (1994) and EPBC Act (1992) were |
sought and recorded.
| 2
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| 7 = => = a — — —_ a
| Back to the Deh
* |
Section 2 Vegetation Assessment
ay Vegetation description !
Vegetation consists of some cleared land (mostly exotic grasses), but the majority is natural
| forest regrowth averaging 30-50 years old in better arcas, ‘The forest is in relatively bealthy
condition with good natural regeneration and, in general, little weed invasion that seriously
threatens biodiversity (Lantana does become u problem on lower slopes). |
| Diversity is high with over 200 native species recorded on the propesty during preliminary
flora surveys, Sucolyptus acmenoides (White Mahogany / Yellow Stringy-bark), & |
propingua (Grey Gum) and £siderophloia (Grey tonbark) dominate much of the canopy.
Also common are Lophostemon confertus (Brush Box), E. grandis (Flooded Gum), E
| microcorys (Tallowwood) and Corymbia intermedia (Pink Bloodwood). Understorey varies
from sparse to dense, with open forest or dry sclerophyll, on upper slopes merging into wet |
sclerophyll (myrtaceous cmergents with 3 rainforest understorey) in gullies. A Flora Survey
with species abundance is attached (Appendix 1).
Remnant vegetation in Queenstand is catcgorised into Regional Ecosystems (EPA Qid |
Herbarium — Mapping Release SEQ 2004 Version 5). This is the most accepted method of
identifying ecosystem types, taking both vegetation and geology into account. Two EPA
| maps showing ‘remnant’ vegetation are attached. One is a landscape scale and the other
zooms to the property scale. Lot | is highlighted with a bold black boundary for context. |
| The REs described are:
12.3.2
Wet scicrophyl! on alluvium including Excalyptus grandis +/- E microcorys with rainforest
understorey fringing streams (12.3.2).
| Conservation status — Of Concern
12.412
Wet sclerophy!l on metasediments znd interbedded volcanics including Eucalyptus grandis,
E. microcorys, E. acmenvides and Lophostemon confertus with a rainforest understorey.
| Conservation status — No concer at present
12.113
Open forest generally with Eucalyptus siderophioia an’ E propingua +\- E. microcorys, |
Lophosiemon confertus, Corymbia intermedia, E. acmenoides and E_ tereticornis. V ize forest
| species with E grandis often in gullies.
Conservation status — No concern at present |
12.11.10
Dry rainforest on metasediments - Notophyl! and notophy!l / microphyll vine forest +/-
_ Arowcaria cunninghamii,
Conservation status — No concer at present |
Field asscasment supports EPA classification of the first three REs and much of it is
Classified as remnant under the Vegetation Management Act (1999), 12.3.2 lines the creek,
merging into 12.11.2 up the gullies, merging into 12.11.3 up the slopes. While 12.11.10 is not |
well represented on the property, some elements of the ecosystem are present (eg abundance
of indicative species in understorey). Given long cnough with fire exclusion, the slow
| transition of vegetation would favour this forest type.
3|
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Back to the Tash
2.2) Weeds
While exotic weeds have not seriously impacted the forest system and naiural regeneration to
date, several weed species do pose a threat of further invasion. Lantana is the most prevalent
of the exotic species present and is abundant on the lower slopes. Other cnvironmental weeds
of concern include: Pinus sp. (Slash Pine), Schefflera actinophytia (Umbrella Tree), Melinus
minutiflora (Molasses Grass), Pennisetum purpurewn (Elephant Grass), Macroptilium
atropurpurium {Siratro) and other teguminous vines. A more comprehensive weed list and
relative abundances are attached at the end of the Flora Survey (Appendix 1).
2.3) Rare and threatened species
A single scheduled plant (Symplocos harroidii - Hairy Hazelwood) was recorded near the
southem boundary of Lot 2 while carrying out preliminary flora surveys. It was found
adjacent to the creek and is protected by the designated conservation zone (GPS — 56 J
0482386 / 7072877 - UTM). No forestry activities or disturbance will be carried out in the
40m buffer to the creck.
Although not scheduled, Diospyros ellipticifolia var. ebenus (Shiny-leaf Ebeny) occurs only
between the Tweed Vallcy and Gympie areas and is considered rare. The specimen observed
was in the gully on Lot 2 and has been clearly marked with surveyor’s tape. The landowner is
aware of its presence and aims to carry out very limited silviculture and only light harvesting
in this area.
Se ae
ee aK ae. aii
7. e t. 3 y eae Se ee ~ : ie _ — winnie =
ia Sg Saag \ ah Memes 1) 0 4 ors mee) WG nee ae
7 Lo giee 7 ff tie Sees rtd oh Ss. dae Nene ibs
eae. AR ED ee 3s
me fy yet Sean a” bites (5 S/R Bit a, -)8
P24 eS “ : See 8? Ara a / Leng arid,
as at a tee Oe Bees Ad), Biel yee fh
*y 5 ‘ 4 a ae Beth ‘ay oP & 7 Te 5 |
AY , ee . a a Boy 8A ESE OY o>
eg Be ae Om RS NE
te 7] SK pt RNS: a See (25 OY oe & able
* ‘rd a ho ox = - ebay << F Se ‘ ' ae *.> ' “7 ’
Re Sa et Eee imines PS Ne x 4
Above and right: Vegetailon varies from open iW i : . a €
F x * ‘
forest on the upper slopes {photo right) to wet 5 2 GEES
schlerophy!l in the gwilies (above). The density and ae. u 5 a
diversity of reinforest species increases as the tat aa ae oF anc: oy ew, 7"
altitude drops. The photo above is taken at the gully = > > UGp- fy My i
bottom the one on the right is near the top of a am om . Pe he gist ay
ridge. r * top ep. P 7 OF 6.:. , oF
sg me Bee ; et oa ain 4
4Section 43
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| Back to the Bush 2
‘Section 3 Vegetation Management |
| 31) Outline
The proponent aims to sustainably manage vegetation on both Lots 1 and 2 as a private
forestry operation. To achieve this goal a range of forestry practice techniques will need to be
undertaken, in particular —
Silviculture: Pruning — will be carried out routinely to increase timber quality, yield and |
value, while improving conditions for maintenance and fire contro},
| Thinning — will be carried out routinely to select best quality stock and
increase timber production and value. |
| Selective harvesting ~ will be carried out on approximately a 10-year cycle. Species with |
| potential for harvest are listed in Appendix 2 — attached,
| Access / salgging tracks / log landings — cxisting tracks will be maintained and new tracks |
are still to be built, including log landings and turn around areas, All existing tracks and those :
yet to be constructed are marked on the “Layer I’ map.
Fire management — Since the wildfire in 1993 seriously damaged buildings, forestry and the
ecology, the landowner has taken steps to cxclude fire, aiming to reduce damage to natural
and plantation timbers, improve fertility, reduce loss of stored carbon and to minimise |
| ecological impacts. Firebreaks and building envelopes will be maintained to reduce threat
from fires. While the landowner nims to keep fire off the property, occasional controlled |
| burns may be required if there is concern with excessive fuel loads or to trigger natural
regeneration (eg Eucalypt species). Peter Turner (11th June 2005) has compiled a bushfire |
| management plan and a copy is attached for reference.
| Weed contro! — will be carried out routinely to reduce competition for native regrowth. |
| Plantation forestry — Some planting and early establishment is already under way. These
areas will be extended and others will be planted with cabinet tinyber and hardwood specics.
Rehabilitation - An area (0.45 ha) has been designated for rehabilitation to compensate for |
the clearing of a building envelope of the same size in Lot }, |
Dams — All existing dams will be retained for fire control, stock water and for |
| reafforestation. Some dams may need cleaning out periodically or even enlargement in future. |
| 3.2) Code of practice |
The proponent states that all forestry management and harvesting activities will be carried out
in accordance with “the code applying to native forest practice on freehold land”, as
published by the Department of Natural Resources and Mines (1 December 2005). A copy
of this document has been attached as it forms # basis for all forestry activities on the
property. Also attached for reference is a report by Dr G J Bacon (8 March 2006), stating
that all works carried out to date have been compliant with the code.
a |Section 44
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| Back to the Bash
|
Weed control
| Declared weeds are now classified into 3 classes:
|
Class 1 - None recorded |
Class 2 - Saccharis halimifolia (Groundse| Bush)
| Class 3 - Cinnamomum camphora (Camphor Laurel), Lantana camara (Lantana) )
While occurrences were very rare, all Groundsc! must be completely cradicated to meet local
| and state government requirements. This can be done manually (cg. pulling small plants out
by the roots or digging out larger ones) or using a combination of manual work and herbicide
(cg. cut / swab large ones with 50 / 50 glyphosate / water. |
| Routine weed control on Lantana will be necessary as part of an on-going silviculture
program. Lantana (abundant) and Camphor Laurel (rare) will need to be controlled where
natural regeneration is threatened. Leaving Lantana unchecked has adverse effects for
biodiversity, timber production and sustainability. On the other hand Lantana has some
| positive attributes in a regenerating ecology, so a slow but regular approach will probably
work the best. Funding and / or assistance with labour arc available frum several levels of |
government to address the problem in the 4 ha conservation area along the creck. This area is
| certainly a priority from an ecological perspective.
|
Areas designated as open space and fircbreaks can be slashed / grazed to control weeds. The
idcal time to carry out weed control in difficult areas is soon after disturbance from logging
operations. Careful removal / treatment in and around netural regrowth can be done by
pulling out small plants by the roots or using a cane knife / brush hook and where necessary ,
treat stumps with glyphosate (2s above). Patches of Lantana with little or no native regrowth
evident could be sprayed with glyphosate solution. Care should be taken during ail weed
| control activities to avoid damage to establishing native seedlings and saplings.
Other weeds can be controlled on a routinely at the landholders discretion, as they do not fit |
the Class | — 3 categories. The exception to this is the revegetstion area, where weeds must to
| be controlled for at least 3 years to ensure successful re-establishment of native vegetation.
Specific information on weed treatments can be obtained through focal government weed |
officers or the Department of Natural Resources and Mines web site.
|
3.3) Site specific management |
Site specific management issucs and techniques are outlined below and relate to areas
| designated on ‘Layer 2’. The acrial photo (including contours and DCDB) provided by
council is used as a bese layer. Overlays were compiled and provided by the landholder st the |
same scale as the basc map.
| Conservation area ! (approx 3.4 ba) |
100m strip adjacent to Belli Creek Road. This arca is designated for minimal selective
harvesting only and will got be managed using silvicultural methods (ic no thinning and
| pruning). Some weed control will be carried out.
|
6
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| nv
Back to the Brush |
| Area A (approx 0.38 ha) |
| To be kept clear for safety as part of the Lot | building envelope. This will reduce risk of fire
near buildings, reduce !caf litter in gutters and avoid the threat of falling trees or branches |
| during storms, windy conditions, ete,
| Area B (approx 0,55ha)
Building envelope for Lot | to be kept clear or planted with fire retardant species in gardens,
Area C (approx 1.2 ha) |
| This area has been mostly cleared and will be kept this way to serve as a safety buffer for the
| house site, a fire break / access trail and also provides open space for two log landing areas.
Aves RE 1 (0.15 ha) and RE 2 (0.2 ha) |
These areas consist of dense regrowth of mostly immature trees. They will be subject to |
| Toutine silvicultural practice and some trees will be teft for harvest when mature.
| Areas Pi - P3 (approx 52 ha combined)
These areas represent most of the productive forestry on the two lots and as such will be |
managed using routine silviculture and harvest methods as specified in the code. Only
minimal silviculture and harvest will be carried out in gullies and on steeper slopes to reduce |
impacts on rainforest species in regrowth or potentially unstabic arcas.
| Areas ¥1 - ¥4 (approx 10.6 ha)
These areas are generally younger regrowth than those outlined above. Some enrichment |
| planting was carried out in Y1 and Y2, although the 1993 fire killed many young tees. As a
result some parts are open, while others have tree cover, Where there is a broken cancpy,
weeds proliferate, so their control is important if native forest is to be re-established here, In
particular leguminous vines and Lantana arc an issue.
Weed control, silviculture and harvesting will be carried out in these areas and if accessary |
some carichment planting will be undertaken in parts where natural regeneration is
inadequate or pianted trees were damaged by fire.
Area A2 (approx 1.8 ha) |
This area contains sheds, fruit trees and omamentals. With the exception of garden plants, it
| will be kept clear as a firebreak to protect infrastructure and utilised as a productive garden.
| Areas A3.1 — 3.4 (approx 3.6 ha)
These areas are mostly clear and will be kept that way to maintain an important firebreak and |
| to provide access for logging operations. Grazing will be carried out to keep it mostly open
and control weeds, |
Area MA (approx 0.2 ba) |
| ‘This area is a small Macadamia orchasd that is overgrown with Acacia, Lantana, etc. Wattles
and weeds will be controlled around nut trees. |
Area Z (epprox 0.45 ha) |
To compensate for clearing of a building envelope on Lot | the property owner plans to .
revegetate an area approximately the same size (sce ‘Layer | and 2”). Natural regencration is
profific in this area and will be retained and where necessary local hardwood species will be
7Section 46
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| Back to the Srrh
planted in gaps. Regular weed control for a period of 3 years will be necessary to ensure fast |
canopy establishment.
|
Area G (approx 5 ha) |
This ares is currcotly clear and will be kept that way as a firebreak and for grazing, Slashing
and or cattle will knock down and reduce the seed bank of the ciephant grass present, which
| can later be replaced with other species of pasture grasses.
|
Area LI (approx 2.2 ha)
This area of regenerating forest will be subject to light harvesting and limited silviculture to
| §nerease productivity, )
Area SIL (approx 2.5 ba)
| This area has been designated for farm forestry. {t wes planted with cabinet timber species
from 1989 - 1991, but many of these were destroyed in the 1993 fire, Remaining trees are
doing well and the area will be managed to improve growth of planted species and any
appropriate natural regeneration present. The canopy is dominated by senesccnt wattles,
| many of which will be removed to encourage growth of later phase trees (sce photo below).
a Oa
Pa
" \ * Per so, %
ELE ‘ v i |
: a Mee a iP ela . °
Right: (Area SIL) The senescent Acacias ee i ee 4% -
will be reduced and weeds controlled to i, 0 Ur " E> ~
| improve conditions for cabinet timbers. , pir iq’ te wn J te :
Silviculture will be carried out in this area to / } if We . |
maximise productivity. nl Samp i” ; he
} © PB i " 5. ay
Aas SAM HE ‘Pe |
ns fini ¥} fa *» ‘
ee + byt ° ws
oe «(fF eed or Oy vA ~
. >. 4 ’ * * 5
ye as % s + ae o 2 a) 4 4
Wt oes i, bE AA.»
| Dy ge Ss a
- . |
= <: oe FA
| . i v
ee _é * A |
6: ae ; Lah: (Arca G) Open space will be
id Vy f- 6 fyainiained as part of the fircbreas and
| oF SF, i: e st] Seeatinw perpones.
oe Shape nm |
r - ‘<j0" 1 : wr 2
ye a
| % oat One © 2 ‘ or |
‘ : *% - . * a ey
a
= = = = a = 1 7 |Section 47
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|
Back to the Basch
| Ceaservation area 2 (approx 4 ha)
A minimum 40m wide riparian buffer, along the leagth of the creek, has been designated as a |
conservation area. No forestry activities will be carried out here to ensure protection for the
area mapped ‘of concem’ Regional Ecosystem and the scheduled species — Symplocos harroldit
(Hairy Hazelwood) previously mentioned. |
The 2rea contains the greatest floral diversity oa the property and will provide a wildlife haven
free of disturbance. Such a buffer will help to maintain water quality and reduce any impact
from harvest operations. |
|
Section 4 Summary |
|
On investigating the vegetation on Lots | and 2 Belli Creck Road (SP175064) it was found to
comprise of a mixture of open land and forested areas of varying age. Better quality forest
| consists of 30 — $0 year old regrowth and is in good condition. Examples of several Regional
Ecosystems were present — onc is classified ‘of concem” along the creck and is protected !
within a designated conservation area. One scheduled species was recorded near the
boundary on the creek — Symplocos harroldii and also falls within the protected area. Weed
| invasion is not yet too serious, but several weeds of concem are listed in Section 2.2 that will
necd on-going control to reduce threats to the natural biodiversity and productivity.
| The landowner states that all forestry besed activities undertaken will comply with the “code
| applying to native forest practice on freehold !and”. This document forms the basis of
vegetation management on the property. |
|
|
|
|Section 48
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Appendix 1 - Flora Survey
[Appendix 1 Preliminary flora survey - Don Lawrie - Cooroy - Belli ChAT
Marc Russell 13/7/20 —— |
Form: Tree, $/T-amall O-orchid, F-4ern, P-paim
| Abundance: a - abundant, ¢ - common, u - uncommon, F - rare _ aoa
a
= — 7 ‘Memnosac a ,
| Ticociafoleaia lMimosacese | - | ‘
Acacia leiocaiyx —_ Mimosaceaa Carty flowering Black Waite ot _| |
Acacia ioraes! Menosac we leat Acac <
| [Acacia 'shonnesi ~~ |Mimosacese —JFemy-loat Watle foie
Acrnena smi Mya Tow teat Lily Pay
Acronycha isevts Rutac Gloss) - Si
cee ae — meres ieee ST eT =
| TAcronyc oblongifolia - R : By Pilly | Common Aspen |
- 29rec E: - - Red G Ren = ic
‘Actes indiey’ Euphortac ‘Actept ar
Adiantur /Adiantac rity Mardentair F
| eee a a ——p——_-§—_
pave hispida —jAdiartacese Rough Maiden Ha -——
chomes tee : Euphorbiscese [Native Hol p===s
| [Aieeesuerine tonics IG rest C = a
Aiphiioniaexcess = Rhamnac Rod Ash Te |
Aipinia cacndea—=S=Ss=~=~—~S~S«w I =) a:
An on ener Manosac iS
an nein - ee aa " ee > an iS
| [elon dete Sapndac nee Come sit
vo ra Giver icats a Sapndac Coog on ee , |
a — a
-— PAcatromyr hit (yn Gossiay yr Scaby My s
Blochnum c . Rlechnec iG Forr Fr
ma = . — — & ot = oa —
if ta! = 5 . lronbesi -
stems mocked ~~ —[Wrececese [UswyerC
‘Calochl Guba Cicksontec Bac t-
| (Cappars arborea Cap ate Capen fv
= cena i anmericter ahead oc, : : re
Cappar Sarmontosa 7 7 DP fac Carmd 0 Can fous
Carex sp (not flowering) Cyperac On creek t S|
ic crate = = ‘Apocynac: Curaniucsh S
Comonie mumeepatie ___ ___[Menlapermecese [Cewonte 000k
| i Dspermum austrate F abac Black Bean
| cami = mene - a
. chorrs ’ rn $ ; Giape a : |
a ——
iC : OwersSesssss
{Cissus antarctca aa vend ‘Kangaroo Vine, Native Grape _
Cessus hypogiauca Vita Water Vie
(Cissus opoc ———— Mitacose Water Vie SESE cj
| Page |
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|
|
eeeSection 49
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| 7 = = — — _ _ - | 7
| Appendix 1 - Flore Survey
Appendix 1 - Pretlimi flora survey - Don Lawrie - Cooroy - Belli Ck Rd |
Marc Russell 13/7/2008 a eames
_ [Form: T-tree, S/T email tree, v F-tem, P-paim
ndance: a - abundant, ¢-common,U-uncommMon,t-raro oe fe |
- Spec! | Famnih Common name
Cary austrais (Microctry R . lime 7 Ss
"| Gletenthes conringhanil ~~ euphoriscaso —|Cisistardues : |
ic 5 Glyonoxies Re oulac Traveller's Joy
| [Commersonia bartramia ss [Stercuecsas _ [Brown Kurrajong —_ 4 s
Cordyine petic —_—__fAgavaceso "| Brozd-leat Pam Lily” ¢ )
Condytine mbca — avecese Redrruited PaimLiy .
Corymbia intermedaa (Eucalyptus) Mytacese = |Pimk Bloodwood,
| cfoton ecronyenicies ‘Euphorbiacess | Thick-Leaved Croton ; Si
nee shorbrac. Silverteaf Croton iT
Croton veremad —~—=—=S*=*~*~C*«‘*dE pb laceme |NatveCroton i s |
Cryptocarye glaucesc Lauracese ceeood, Sives Sycamore J
| Cryptocarya | aeigats leureceze ss |Gicssylaureh = S
‘Cryptocarya medonaldii Lauraceae Cootoota Lauret
‘Cryptocarya microneura ; aC Murrog T
Cryptocerya schierophyia ___——‘(lmuracese | Thick-teaf Laurel s
Cryptocarya Inpinervis —_ (Laureceee _| These Veined Cryptocarya
[upanopsss parvioia | Sapindac Smell-Leaved Tuckeoo U
Cupaniopsis serrata Sapindac Smooth Yuckeroo i s |
Cyathea coopen iC 2 Rough Treefem -—-{— —,-+
a bid ane; ~ "TG rchidac Se Orchic = =
~~) mene ase - = eerie — eens
(Davicsiaumbelista — Fabecewe user Pe Bush . |
Dendrocnide monoides mbcac Gyms aianieiean e
| Denisiwoun | |Fabaceae Native Deis =
ic cofestroes Celastracese [Orr Boxwood
Dicscorea transvers3 Doscorsacsse [NatveYem
| [Dlospyros elliptictiotia (var ebenus) | Ebenacese Shiny-leal Ebony _ S
Diospyros fasoculos. Epenscese =-_-—s (Grey Ebomy |
‘Oxplogiotts austraks (syn. cunningham#ll) | Sapindac Natve Tamarind
_— [Doodia espera 2 ee Blechnaceee [Prickly Rasp Fem Perea a
Dood ppl . Biechnac oe aut seine |
Drypetes deplenche: (australesica) __ Euphorbigc owl
| pandas sereporeies Soisner Duboisia s
Dysox ferum ebac Rosewood on |
Dyeoxyum rufum tac ) Rosewood | oo
| a COC pusreticuiats ao | oc paceaa Biusbe AS oo { ‘Ss
Etattostachys nervosa | Sapindac BeetrootTree |
Embeke austratana co c Embelis v
Endiendra discolor _____ tauree RoseWalmt
| Eucalyptus acmencides Miyrtuce: White Mahogany, Yellow Stringy €
Eucatyp crebra oe _ 0 lronbark —_ |
Eucalys 4 8 5 Rose G “hod 4 Gum |
Page 2
a a a ~ ~ — = =e =< = |Section 50
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Appendix 1 - Flora Survey
- |Appendix 1 - Preliminary flora survey - Don Lawrie -Cooroy-BelliCk Ral )
Marc Russell 13/7/2006 | eee . = — —
orm: T-tree, S/T-smaill tree, S-ehrub, H-herb, Vv salsedge, O-orchid, Ffern, P-patm
| |Abundance: a - abundant, ¢ - common, u - uncommon, ¢ - rare a
Species emt —— [Common name Abundance | |
Eucalyptus microcorys Naynac allowwood . a
| essere pecpinase _—_—lNrtscese —"— KGroy Gare Seis Rice udi ice
Eucalyptus 6 nota Myrtac Grey tronbarc c ei
Cucatyg ——|Myntacese ~~ |Forest Rod Gum ———h—4 |
Eupomatia taurina Eupomatiacese | Bolwarra Ss
Euroschinus faicata Anacardiaceze —_Ribbonwood ay i)
| [Eustrephuslatfolus Philesiaceae —_ | Wombat Be eee —
cus coronata 7 Moracec Creek Sandpap ° C SY |
he et Moraceae [Sandpaper Fig T
| _—" a allanacese | Supplejac! —
| [Plindersie australis Rutaceae Crows
Fiindersia bennettiena Rutac Bennott’s A — |
| |Flindersia xanthoxyia Rutaceso =——i‘é{eellowwood
| |Gahnia aspera perac GRR G
Grewia latioia Ville Dog's Balls is |
| Byrne tac bie COUEe sae Settior's Flax ier G
iat violacea— Fabacese [False Sarspaiifia |
Harpulia hii Sapindac Biunt-leat Tulipwood
libisc ophyus =i ss sé ive alive Hibiscus S
_ [Hodgkinsonia ovatiltora tubiac Hodgkinsonia é
Hoves acutifolia Fabacese PointedteafHoves |
| ee ———— abaceae Motive tng : Ss
ane Saoindac ‘oarnb
Lastreopsis marginans __|Aspidiaceae (Oryd Glossy Shieid Fern |
Lepidosperma laterals (var. majus) _[Cyperaceaa | Variable Swordsedge G
| Litsemieefewna (Lauraceae Brown BollyGum
ee — — ees Ss — |
Lomendra confertifolia ianthorrhoeacead Forest Mat Rush :
amanda hystrix «= |Xanthorrhosacead Creek Mat Rush G
| |Lomandra longifolia anthoroeaceas Mat Rush G
Lomandre mubiiors Renihontwoesceed Meany fowered Wal Ruth |
Lomandra spiceta ____ [Xerithorhoeacead Rainforest MatRush G
Lophostemon confertus Myrtac BrushBox SS le
| lecarangatanarus = [Euphorbiac Mecaranga s
MacrozamiaWucida Zamna \Cycad 9 ioe
tu oxen |Euphorbiac GeenKemeis (| °#s-
(aioe dcobr Eghotlecess _Vekou Karas
ailotus philippens: epremeacees _ [Reg Kamae : |
Medico cunning 2utac Pink Heart s
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| _ = — — _
Appendix 1 - Fiora Survey
[Appendix 4 - Preliminary flora survey - Don Lawrie - C -BeliCkRd|
Marc Russell 13/7/2006 =| ae 3 —4 |
‘orm: T4ree, S/f-smail tree, S-ehrub, H-herb, V-vine, G-grass/sedge, O-orchid, F-torn, P-p
Abundance: a - abundent, c - common, u - uncommon, F - rare biel
| Snacle: SETTLES ¢ Commonname bund
Melia azedarach ia White Cedar iv |
= ene
| Meiodinus australis 8 =s_—s_—s__s | Apocynacese Belibird Vine
Mischoaryiera lautereriana ss |Sapindacese __|Corduroy Tamarind —
Mischocarpus pyiiormis ——|Sapindaceae [Yellow Pearfruit |
| enus semulus var undulatiiolus |Poaceae Beard Grass pI
Ottochioa gracifima Poaceae __ as a G |
Oxalis comiculata _______|Oxalidacoae _—[Yellow Wood Somel ou
Dxyiob cifollum (syn Podolobum) [Fabaceae Holyjeaf Bush Pea S
| [Ozot ___ Asteraceae |SagoBush s
Pandores inoides ~_|Bignoniaceae _|Native Jasmine
Pandorea pandorana__—_ Bignoniaceae —_ |Worga Ving
Parsonsia lanceolate AOC sceve (Rough Sitkpog
Pentacerus australis Rulaceee Bastard’s Crows Ash / ys
-—{Phylanthus gunn phorbiaceae oo ==
MA —_— a a :
Pilidiostigma rhytisperm’ acaue Smail-leaf Plum Myre
Pimeleatatfoia placaceae [Rice Flower
Piatycerium bitwcatum s/s = [Pelypodiaceae [Fikhorm 0
| Plstycerium superbum Polyoodiaceae |Staghom |
Plectranthus parviflorus fLamiscene : |
Potyscias eleg eas sce Celery Wood
iro o Archecese Pencil Cedar
| |pouteria australe (ayn Planchonalila austalSapotaceae |Back Apple —_ —
Pouteria o F landic 5 DO Icwae Blush nondoo |
Pseudoweinmannia lachnocerpa Cunoniaceae _—| Rose Marara |
jadephnicites = s—CsiCéC Ruin Smooth Psychovi: is
| Peau esculentum ________|Dennstaedtiacesc|Bracken
Pyrrosia confivens Polypodiaceae |RobberFem waeaia
apenea vanabiks sinaceas Muttonwood ic
Rhodamnia pubescens rtaceae BrownMalletwood =
Rhodomyrtu: ao = tacesa t
Rbogerum bowl urn Smilacaceae (Rip(Smai-ieat Suppiejack a
Ripogonum eiseyanum Smilacacese (Rip(Eisey's Suppiejack i
| Rubus moluccanus (syn. hii) Rosaceac lo
Rubus parviflorus (Rosaceae Small Raspberry __ .
Rubus rosffoius Rosaceae _—»_|Rose-ieaf Raspbemy a
Sarcomelicope s'mplcifol = Rutacese Saue Ss iS
Sarcopetaium harve ___|Meniapermaceae |Peart Vine |
| {Senecioamygdulifolius. = ==Ss—i(ité‘“‘;*C*C Nt Native Davy — —
Sida cordifolia Malvaceae Flannel Weed |
Sida rhombiiolia ~~ Maivacese [Common sida .
Sloanea australis Flaeocarpace Maiden'’s Blush Wy a
Page 4 |Section 52
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| 7 Appendix. 1 - Flora Survey 7 = a = |
pendix 1 - Preliminary flora - Don Lawrie -Cooroy-BeilliCkRd| |
Marc Russell 13/7/2006 aw =a
| |Fomn: Taree, 8/T small tree, 5: “ perchid, Paem, P-paimn |
, nce: » - abundent, ¢ - Common, u - uncommon, F- rare ail
_ Species : [Common name = [Form
: — Sat 3 =
__ fSimploces narrotda Symplocec . el
Teucrum argut _aegutam Lamuaces. _-_ |Natwe Germander
nda iencra = Poscese anemon Gress _ G
| [Toone ciliata (ayn. australe —__|Meioc Red Cedar 7 |
ree tomentose (Srt_eepers)_— BOS. ative Peach s
| scumingta NV etbenaceae [Vite —
Wikstroemia ndica Thymolneaceae | —
Witcies he piesiesnse Weer =
_ [Renthorhoea tatfola ssp. latfola | Xanthormoeacend Grasst Ps
iZehnertia c Ingham Cucurbitecess is der Cucumt A
Zieria miwstiors Rutnc [Smell Midge Bush |
Tiga robusta | Se a i ——— t 1+ — |
ome additional planted
aucona bidwili Argucatiaceaso |DunyaPine ' |
SS eee
8 oy ee ee
! |
| |
| |
Page 5 |Section 53
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| rn =. =s == — — _ a _ -
-' Appendix 1 - Flora Survey
{Appendix 7 - Preliminary flora eurvey - Don Lave - Coor - Belli Ck Rd
LOS aa V-vino, G-grasa/sedga, O-orehid, Fforn, P-paln
Marc Ruseell 13/7/2006 si sins aor a |
Abundance: a - abundant, c - common, tt - uncommon, F - rare a ;
| ecies —Sst~—<“‘~‘;‘;*~*~*~*dC ty = Common name Abundance [F |
eo | : —
Weed a .
eratum: nienum Asto ue Top
|i ssicaia' ~~ —Aacopladacono Nat Vin v—)
Baccharis halimAche Astorec pun u
| Sinnamomum camphora Lauraceae ; eae serne
| Ble 5 pilosa in ‘ 5 _ODD
cs vulgare alin A pawreress site of Spoar Thista |
Desmodium oncinatum — ——~(Fabeceae | Stver-teal Desmodium =
| Gomphocarpus physocarpus ———«lAaclepidaceae [Milkweed 0 a
janacamera | Merbvenaceoe flantane i |
Macropuium stropurpurtum ____[Fabacee ~ :
Macroot absceae Swao i |
| Neontonia wighti absceae (Glycine
Se —
Passifiona subpetala: Pasaifioraceae —_|Whie Flowered Passionirutt
| Passiflora suborosa Passificraceaa |Corky passionfruit
Pennisetum purpureum ss |Powcewe __—_—| Elephant Grass |
Prysates pe mana ______ {Solanaceae [Cap Goosebe
Phytolacca octandra Prjehecceens _liweed s
| Pinus sp oo = Pinagese Slash Ping
Scheifiera actnophylia —_—=SS—«(Araliaceae [Umbrella Tree |
Senne pendula var glabrata Carsaipinaceae [Winter Senna s
Setariasphacclala _—s_—s Poaceae ss |Staria Grass _ C
=
Solanum mauriianum == | SOC ben ng c
o ) seaforthianum LAM DING HIgh u — iil
Sporobolus ap _ —______|Paacees Paramatta Grass piaain, G
| Verbena bonariensa————~—__|\Vrbenacea | Purpletog = |
Vigna sp onl puceac OW f |
|
|
|
|
|
|
|
Page 6
E = 5 - 7 a 7 7 7 - |Section 54
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Appendix 2 - Species wiih harvest potental
Appendix 2 - Species with potentia! for harvest- Don Lawrie
Marc Russell 13/7/2006 oe
Species =e Family __ |Common name
Acacia baken - Mimosaceae Marblewood 6
Acacia disparrima (syn. aulacocarpa) cory Wattle
caciamelanoxyion [Mimosacese _——| Blackwood sac
Agathis robusta Asaucariaceae Kauri Pine 6
Allocasuarina torulosa [Casuarinaceae_ _ [Forest Oak
Aiphitonia excelsa Rhamnaceae Red Ash petite
Araucaria bidwillil 2 Araucanaceae Bunya Pine S
Araucanacunninghami Araucanacese Hoop Pine _
Bridelia exaliata : _____|Euphorbiaceae Scrub Ironbark
Castanospermum australe - sss Cs |Pabaceae ta
Corymbia intermedia (Eucalyptus) rtaceae Pink Bloadwood
Diospyrosfasciculosa 4." _—=»___—_-| Ebenaceae LO ee Se
Drypetes deplanchei (austrelasica) — = phorbiaceae Yellow Tulip 4
Dysoxylum fraserianum = ____jMeliaceae Rosewood _ & }
Dysoxylum moilissimum : ___. _|Meliaceae Red Bean a
Dysoxylum rufum . Meliacese Hairy Rosewood >
Elaeoca Sus grandis = aires Elaso CcCarmace2e Blue Quandong &
Elaeocarpus obovetus : Elzeocamacese | Hard Quandong a
Eucalyptus acmanoides ‘|Myrtaceae — _—| White Mahogany, Yellow Stringy Bark
———— ——
salvphis crebra Viyriaceae Narrow-leaftronbark ,
Eucalyptus grandis Mystaceae ss. [Rose Gum/Flooded Gum
Eucalyptus microcarys acese Fallowwood
Eucalyptus propinqua _ Myrtaceae |GreyGum
Eucalyptus siderophioia = |Myrtmcewe SS Greyironbar, 0
Eucalyptus tereticomis Myrtaceas _ ForestRedGum
Flindersia australis . Rutacezae (Crows ASN
Flindersia bennetfiana 0 Rutaceae | Bennett's Ash
Flindersia brayleana Rutaceae NG Matias Sr
Flindersia SICA VRC fp Sumpy Ash/Silver Ash .
Flindersia xanthoxyla = Rutaceae ——ss|Yellowwood aes -
Gmelina leichhardtii - Verbenacese While beech &
Grevillea robusta —— iiky Oak -
Herpullia hilt - oh Sapindacese _|Bluntleaf Tulipwood
Lophosteman confertus Myrtaceae —S-—_—«[ Brush Box eS =
Melia azedarach —______{Meliaceae___|While Cedar a
Rhodosphaera rhodantherma - Reece ~~
Meliaceao Red Cedar n
Page 1Section 56
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/ _ ccactasinii* Geecaagsadnanbillesidiaat he ee aceeenend eS |Section 57
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i tie Y RSL a
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q “s NAO Me ere aeSection 59
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| pws MAIN ACCESS
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7 et f
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: 91 yo oVaK nae ioe SN FESection 61
61
Noosa Council
Temporary Local Planning Instrument
(Protected Vegetation Overlay) 2014
Plan 16 Lot 3 on RP810775 388 Coles Creek Road Cooran
Section 62
62
Noosa Council
Temporary Local Planning Instrument
(Protected Vegetation Overlay) 2014
EEUU een
AA
:
ee eg
ecg
eg
|
a
igi
sc
Ue i eeeSection 63
63
Noosa Council
Temporary Local Planning Instrument
(Protected Vegetation Overlay) 2014
Plan 17 Lots 9 and 10 on RP885219 66 and 70 Forest Acres Drive Cooroy
Section 64
64
Noosa Council
Temporary Local Planning Instrument
(Protected Vegetation Overlay) 2014
Plan 18 Lot 3 on RP860472 471 Sister Tree Creek Road Kin Kin
Section 65
65
Noosa Council
Temporary Local Planning Instrument
(Protected Vegetation Overlay) 2014
Plan 19 Lots 2 and 3 on RP131369 96 and 108 Black Mountain Range Road Cooroy
Section 66
66
Noosa Council
Temporary Local Planning Instrument
(Protected Vegetation Overlay) 2014
Plan 20 Lot 2 on RP207968 157 Moran Group Road Kin Kin
Section 67
67
Noosa Council
Temporary Local Planning Instrument
(Protected Vegetation Overlay) 2014
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©Section 68
68
Noosa Council
Temporary Local Planning Instrument
(Protected Vegetation Overlay) 2014
68
Noosa Council
Temporary Local Planning Instrument
(Protected Vegetation Overlay) 2014
The Furm « Overview) Andrew Sreclair. Phease Web Albuns http: // pieasaweb qoogie.cent/ theandrewsinelin/ The tarniiver
Pimten . Heee Pectin: | alae ber (®t corn ‘ }
tad FP i tdy? . . E sje Joust | —
i" The Farm - Overview AsatrH ee Srnec tee
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Veto Propowed 470 track
Veue OY
i a me ar [Ais 6 carmen = =
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foe A timecectew Poset Cours ot |
left) 7/02/2011 122MSection 69
69
Noosa Council
Temporary Local Planning Instrument
(Protected Vegetation Overlay) 2014
69
Noosa Council
Temporary Local Planning Instrument
(Protected Vegetation Overlay) 2014
The Pann - Overview « Andrew Stocliir: Please Web Albuns http. /pleatawel:gougle com /abvinclaird 1/TheFarmtverview.
Mone ee Nene Features | tener iainl Teg mee cen .
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\ ' The Farm « Overview Arten Barun
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la View 24
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Th Cea teow oe often sé e on °
loll 7/02/2011 LAMSection 70
70
Noosa Council
Temporary Local Planning Instrument
(Protected Vegetation Overlay) 2014
70
Noosa Council
Temporary Local Planning Instrument
(Protected Vegetation Overlay) 2014
The Paes Overview Ardiew Sinclair- Please Web Allunes ett: / pleoawe lh woohoo n/t heulrewesteclae/ TheFarmOver
{hemes teem Fret | aha tee ) ert crm ’
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|
. faety reuse
Coste hep
Bx ; jae scoemment
P dentin Gee be
Lott W/O Pa PMSection 71
71
Noosa Council
Temporary Local Planning Instrument
(Protected Vegetation Overlay) 2014
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72
Noosa Council
Temporary Local Planning Instrument
(Protected Vegetation Overlay) 2014
72
Noosa Council
Temporary Local Planning Instrument
(Protected Vegetation Overlay) 2014
The Fann Cennviow « Andrew Simectur Uieesa Web Albuns http: / / pied meric com/abuinelart 1 / Theb arnitivervtiew
: Pliston § , . te. Festi aterene Lely 1 figrreit corm ’
tee PICUIEY My Tieies Peapte E2ptors Clash pact | Seoeeh |
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Yellow an possibte wirastrocture sdes, Blue ts for storage of phentation thinnings and Red is «lence, Stiows plantation Staqe
1. Gtage 0 yeas not planted at the tiene of thie photegrapt. Shed strowr irr batter centre. Mouse ste SOi Chern) ME of , ooe
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4 ices ree ane & cormneant
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(2 tsumvecait Post Comment |
OO Ht eeagee
tefl P0220) LoanSection 73
73
Noosa Council
Temporary Local Planning Instrument
(Protected Vegetation Overlay) 2014
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74
Noosa Council
Temporary Local Planning Instrument
(Protected Vegetation Overlay) 2014
tw . =
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75
Noosa Council
Temporary Local Planning Instrument
(Protected Vegetation Overlay) 2014
75
Noosa Council
Temporary Local Planning Instrument
(Protected Vegetation Overlay) 2014
Mowagenient Units ~ Andrew Sinclair - "ieawa Web Albuns http: /picasaweb.google.com/ absinchict 1/Mamngenmenttinita
rs” . — ~~
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rom fe Pal un St ee
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2010 Geoge | Leow et t ,
3of3 7/02/2011 Th55 AMSection 76
76
Noosa Council
Temporary Local Planning Instrument
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76
Noosa Council
Temporary Local Planning Instrument
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Management Strategies for Controlling
Species identified Control Method Status
Easter Cassia Cut and paint Almost eliminated. Follow up
al Easfer lime when flowers
make il readily visible.
Groundsel Cut and paint. Hand pull Almost eliminated, Follow
plants < 30 cm. up by slashing paddocks
regularly and re-inspection of
areas
Parramatta Grass Spray with Tussock Almost eliminated from work
areas. It only remains on the
driveway and around the ©
shed where i's controlled by
; respraying or hand pulling
Glycene Rernove stock, pull fram Slill requires work especially
trees, folar spray in back paddocks
Lantana Cut and paint. Removed from most of
front areas. Removal
planned in areas only where
revegetation will follow almost
immediately
Campher Laurel Chainsaw Progressive removal and
conversion into timber
processed on farm
Cobblers Pegs Slashing Regular slashing before
seeding suppresses further
seeding and growth.
Passifiora Hand removal Opportunistic removal
Asparagus fern Crowning and hand removal Opportunistic removal where
encountered.
Ipomea Alba Foliar spray, cut and paint, Large project in revegetation
hand pulling, fire atea Area of infestationSection 77
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Noosa Council
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| | contained to iust below |
second dam. Constant
monitoring, removal from
trees and hand pulling.
Experimenting with leaving
vines ta grown in 1/10
Glyphosate mix in sealed
containers.
Guava Chainsaw Opportunistic rernoval where
encounteredSection 78
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Noosa Council
Temporary Local Planning Instrument
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Proposals for Controlling Erosion and
for Protecting Riparian Zones
1. No clearing of native vegetation is to take place in watercourses of wilhin buffers
specified in the Australian Forest Standard.
* Allroads and infrastructure is to be placed in accordance with ihe ‘Code applying to a
native forest practice on freehold land’ and the Australian Forest Standard.
3. There are no wetlands on the propery
4. Proposals should see a the re-establishment of a vegetation buffer of at least Sri on all
watercourses and drainage lines
5. Some re-vegetation (planting) of native species may take place within the buffer zones
especially if weed control requires removal cf ground cover.
6. Some weed removal may take place within the buffer zones.
7. All work in buffers will only be part of a comprehensive re- vegetation program for that
management area,
8. All harvesting is to be in accordance with the Cocte, the Plantatian Code of Practice
and ihe Australian Fores! Standard and supervised by an accrediled body under that
Standard.
9. Any grazing will be excluded from riparian zones excepi to permit access to water,Section 79
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Noosa Council
Temporary Local Planning Instrument
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, * Ld
vegetation and disposal of cut
vegetation
Removal
Weeds - See detail on weed management plan (techniques includes foliar spray, cut and paint,
hand removal, slashing, chainsaw removal, and use of a mulching head positrack bobcat or
excavator as appropriate).
Plantation thinning and harvesting - hand removal using 3 chainsaw or in later years harvesting
head
Native forest harvesting ~ hand removal using a chainsaw /
Disposal
Weeds - See detail in weed management plan for each species (bag, burn, allow to rat, :
compost, use as timber, create mulch for replanting).
: Plantation thinning and harvest - sold where possible, residues used for on farm use (fencing).
timber, firewood
Native forest harvesting - as above plus regeneration burning where required including for top
disposal as regulated by the Australian Forest StandardSection 80
80
Noosa Council
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(Protected Vegetation Overlay) 2014
°
" Sequence
ote ‘ Man. ° ae Timing
Letter Name bj» Vegetation Slope Descriptivun Use . SQOMEM Ge Regime * ng Access
* Regime and
Pattern
Retain to 4wet iz
Maturity Exclusion . aD Wid
0-20 Gracual Contral fire Stst DOTLOM Carn
degrees harvest to oad by ey a
Cansiger
lower, Messmate encourage slasning and LOnsice
a » «» Plantation - 5 a £ ather
A Ar . PadGcockx Q.25 er one 20-30 Piantation native Forest Aruning and era. anotne a
Cloezians dan Stace 1 Fa ae Practice Wy 2035 crossing 3°
agrees Stace egeneration thinning 33
NW anc retention Grazing to be . unde s 8
: ra ve oeh pr
f q ais ite a i
comer of 3 few considered = ‘obrephoasee 38
stags as oneer tern .UTrens Foot access ae
habitat trees am B 78 =
- aan ~
ese
Exciusion — + > 39
- Start Qnu Qo
Retain Control fire So a2aOs
Area in front ain ipced 2005 g se
re ONE es amnte oad by Foot Access 25
Ba no o-20 «| farm in ae slashing and , ely Sad
See 0.2 Sampoo oat where een EERE. f pruningand Sno to. P tend.” S>
Pa |dock cegrees. sO} Farming ifotdah eee ES Grave! loca =3
Darypoo '= ~~ frenning 3 Q +
until @ use ts pltig sowt road Sa
Sorowi ta - — -ometne tn & cov. "lat c
= u Seine fe wrae NG tO OE . No
ound far It Hin Stats 83
consicered Piscrent BR g
longer term, TE" S53
Retain to
maturity Exclusion a
eg Gracua Contre! fire <=>
1-2 wey Se - Snes es
0-20 narvest to Seah 2005 Grave
Seqrees arves: (0 oad by
~ey! = Grivewa
= Messmate encourace sias — | orivyewsy
7 , ., Plantation. lower, o.--y 61, werege Forest SENOS BE. sens then 206m
L Ca ciac Hill Eo as Plantation native aine and ote then 2
Cloesiana 1-30 fo Practice RSW 2035 track 2WD
¢ a ‘ J . reaches aU3> cx Z
degrees 229" regendration thinning SrOGM: EVEL SH
Anan and retention Grazing to be .. iv
r ofa few considered sterus waters
pe Las afirc he
i_urrent
stags as ongerterm,.
nabitet treesSection 81
81
Noosa Council
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.
Plantation Exclusion.
area for : Contra: fire
varied load by Start:
Hidden area species of slashing and 2012/13
just ta the rainforest pruning and Fram gravel
> Hic den 0.2 Weeds 0-20 west of the engemics, Forest thinning. End: driveway,
Pa: idock , degrees main creek perhaps asa Practice Long term 2035 4WD or
and east of Nelder Fan return to tractor only
the road cemonstation néar natural Status:
site for loca: understory. Planned :
farm Too wet to zal
foresters. take a fire. 8 3
mani mir 0
00) wu nS Start: 4WD ar = 3
0-20 Leave as not i » Year 2004 tractor. aS
degrees Home | pasture for anty ; oa 5 8 S
~ Ho ne flower, addocks flrebreaks. netmintiua ranten — End: ZWD ali an Qa
. Pa idocks 1.5 Pasture 20-30 sound the Supress Infrastructure controled by 2035 weather g 2 OG Go
degrees shec weeds by sieshing. gravel g 5 S
uppe: siasiing. essentially oes oyenay to © as
r sadhy! “ t a i =
fuel free. ‘ : x5
Qn
Coo. burns <7
ae 5 Start: N
Reta’n as an on < 3 year Sa55;43 S 3
r a sock 5.5 Pasture Oe es on ane eae possidle tria: pmenty f controled by 5535 Greve oe
“ 5 creek planting of eee slashing. eves BONS Tae
wet feet Keep Status
natives, essentially Dammam
2g Prannec
fuei free,
Piantation &. 0-20 Retain to Exciusion. Start:
Cloeziana degrees Messmate maturity. Contra! fire 2010/11 Gravel
~ Go ina 'Ere _ , with some &, Sower, plantation Gradual Forest load by drivewe
Hit LL wicrocorys 20-30 6. marion “harvest to Practice slashing and Enc: rene va
and C. degrees >*9* - encourage oruning and 2035 through hill
Citradora upper native thinning. aSection 82
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Noosa Council
Temporary Local Planning Instrument
(Protected Vegetation Overlay) 2014
regeseration
and retention Grazing to be Status:
of & few considered - ‘
- - : Current
stags as ‘onger term.
. habitat trees.
Coo: burns .
on 3 ear Start:
0-26 Leave as on <7 2005 su ae
i - er racation. ZWD ati
degrees The area gasture for Main weather
, He Si 0.5 Pasture lower, immediately ‘irebreaks. Infrastructure “3 t Y ed) End: cravel
4 ise Site .5 Pastur . om. ene : controlied by 2 .cL q
ARE ONS ° 20-30 aroundithe Suoress / Farming sjashin ¥ 2035 driveway to : ~ 4
degrees house site weeds by sasning. mveway t ys
upper slashing Kees Status: Snee, 9g Ss
woe essentially eee @ 9
fuel free Current 9
1 ! . Q 2
Preferred > g =
opticn ta ‘8 Q 9
minimise Exclusion g 2 OG &
erosion after S $
tentiat is tati 3
potentiai is to plantation. oF 3
remove only Flre may be 52>
smail areas used ta =o
Predominatty at a time and control Start: <7
weeds (Pine, repiant a few weeds and 2012/13 S 3
mohor rows each dispose of 5
i Pine eons. 0-20 Pine vear Forest vacey End: awd via a
v ne 9 : . POPost ark . EA, . .
{ 0 ver E 0.75 ov decrees Plantation 40 ee ~ ae bottom cam
Pie atation Groundsel, an i Alternative = Pract-ce 2035 ,
igwei iower slopes oer Peet bee Wall,
same young option is Cantrai fire
natives, same mecasnica! road ov Status:
wattle) remava! af ali siasning and Piannec
weeds anc pruning anc
smmediate tainsing.
replanting. Grazing to ae ‘
This wauid consicered
raquire some longer term,
natives to be
removedSection 83
83
Noosa Council
Temporary Local Planning Instrument
(Protected Vegetation Overlay) 2014
where it is
not possigle
to effectively F
dear and
plant around
them, :
exclusion
after
plantation.
Fire may be
Retain all used to z a
Predominate'y vegetation contrai Start: 9 3
weeds (Pine, for site weeds and 2007 4WD or a 8
Camphor, 20-20 Pine stanility. disonse of tractar via &§
5 Ue 2er Pine 0.5 Lantana, dearees Plantation Over time Native Forest them. End: ~ northern soz
Fle station ? Groundsel, ° - “remove Practice 2035 ridgeline sss
o - * . Ga ' L . - . :
upper upper siopes rc e: = : 7 Qa
some young weecs Control fire from Ark Spl an
natives, some species and load by Status: Paddock. = g 9 &
wattle} manage for slashing and Current : S35 §
timber. oruning and 9s
thinning. g >
tae kn ke Qy
Grazing to be <= 3
cansiderec N53
onger term, eS
A +
Grave!
Hand clear sewvewav
weeds and Exclusion. a
Some ant bee - ee Start: then either
on 5 replant under Control fire = 3 AID) teaek
pasture, O-20 Seat : 2011 4wD track
some E degrees existing large jy ative Forest (089 OY alone top ar
oes eg Area arounc Kauri and&. vis POPS’ slashing anc 3 * p
. oes Grandis, iewer, oy Crandic ar Practice anc oe End: anotner
K Ka unt Hill 3.8 2 snag le Gg Grancis at a . pruning and Sas :
Some A. 20-30 fo inn wea pis Forest nen 2035 along the
> _ Kauite igh STOCKING ee snNnning. ~
Robusta, degrees a Practice ee , bottom,
much upper rate. Grazing to be Status: Cansider :
Camphor rps intensive considered undenwa im rovin to
B hand longer term, ¥ np veg
maintenance all weather
4awD access
Vi 4 ,Section 84
84
Noosa Council
Temporary Local Planning Instrument
(Protected Vegetation Overlay) 2014
along
sertam.
. Consider
extending
{brusheutter} anc
> a amoraving
for 2-3 years. PPFOW NG
4wD access
aang Lop to
cive all
weather
access. >a
Start: vig . 3 3
AWD vig S
3008 batter Gam @ 9
Remove “ wall, Consider oO g
weed . Coo, burns reinstating 2s
iL Gry Gums 0.18 E. Popingua Yo otees SIV Gus species. Narve Fores: on < 10 year soos creek oo S
6 « ; 0-20 . ; ative Fores ©O™ can. reinstating
e Anne . ractic eet 13 . Q
Manace for “ rotation. cus crossing o 2 8
Fenceposts, . when creek 22ek
Status: oe 2 Qo
; - dry for Sse
Underway Jo . 25
tractor an'y. os54
sat
Foat only at 85
this stage. : 23
Existing very Cansicer N 5
iarae Start: tracter path 8 &
0-20 Messmate is 2OLO/14 na the : ™
degrees Messmates seeding Coal burns ottom to
. Me ssmate - . lower, onthe Norzh uphill. Retain Native Forest 00! BUMS Ena: within
M . 0.5 & Cloeziana = : , : . an < 10 year - winching
Ric ge 20-30 of drainage and enhance Practice .: © 2035 eee
decrees ilne these trees otenion. eistanice.
: : r ov cistance
upper by removing Status: hab tesc .
weed species Dianned WEBCO!
in the area access TOac
to be
constructec
: on the top.Section 85
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Noosa Council
Temporary Local Planning Instrument
(Protected Vegetation Overlay) 2014
_ p-2g ‘Native Fence, Soro/t 1
E. Cloeziana, degrees Forest on firebreak, oui
Ne thern Corymbia u or the northern access to be Native Forest Cool burns End: 4WD for
N . : 2.5 citriodora ,C, PPT? Fenceline maintained ae “on < 10 year <0" most from
Ricge . 20-30 oe . Practice . 2035
intermedia, L. degrees which is on the edge rotation, Ark Paddock. .
Confertus lower eocessinie of this forest Status:
/ by 4WD ractice area. :
¥ P Planned
Start. > Foot only
- , , 6-20 Largely 2015 nee
nexpiored degrees Op an impenetrapie a Very dense i
WaT en is : f JE
dueto dense , regrowsly en far ih been Cool burns lantana. 83
A - lower, ; so far. When Native Forest + End: : + Oo
Q Th: Bowl 5 iantana. 39-30 2fG8 SDOVE Fe permits, Practice on < 10 year 3035 Consider 2 9
Same watiles “~~~ the Too nen us rotation. ow access over s 3
vg degrees remave some , ac
visible Dam a top dam a
upper ‘antana. Status: sb =
wall. E88
Fianned Ra 8
+ ->qQ
Cooi burns S208
on < 3 year g = 2
rotation, Start: 9 > 5.
Contro| 2005 8 > =
mainly by go
Area under : . <¢
. . * Leave slashing, : WD grass =
p Po varlines 0.3 Pasture 0-20 _ Energex s * Infrastructure Hash g To ENG: awd grass N 5
aegrees oan cleared. bethe main 20235 Gaddocks. Sa
powerlines eons Kk
Prebreak for KS
fires coming Status:
West outof Startec
the Stete
Forest.
Predaminately Supress Start: Foot only at
weeds (Pine, 0-20 weeds. 2042/13 nie sta i"
. aA = 4 u
Campnher, degrees Pine Perhaps bia stage. i
: . . . : . a , ool burns Consider
> Western Pine 07 Lantana, lower, plantation plantation to Native Forest on < 10 vear End: tractor patn
a Pia itation “" Groundsel, 20-30 western be placed in Practice -otation yee! 2035 from nb ‘
some young degrees area this area but oe pottorn to
natives, some upper more likety Status: within .
4 t 4 Ni q
wattle}. only passive PignnedSection 86
86
Noosa Council
Temporary Local Planning Instrument
(Protected Vegetation Overlay) 2014
management ,
or
encicament
planting. wincning
i Grandse: distance.
removed,
dlennai
follow-up
Start: Foot only at
Unexalo ed : 20 Area of 2008 as stage. >a
ir re: ~? 200 the rane
R a ee se oner heavy Manage 2S ye coregt COULDUTE — Eng seta ath 3 3
a o en * Crees . - p wer
rowih <t . OWE! = aly ores ERG: reactor Os Pad
. Ri : ° some wattles 20 30 regrowth on forest Practice on < 10 year 5935 from the ital s 8
ge a ow ** _ northern practice _ rotation. . rom te top oo 8
visible also E&. degrees _, to within Qe
: : "ae §»=©6HOPES . meee: a mh <rea
Cioeziana uape: Status: winching oo 8
Started distance. 8 a
ISvew
Hand S. eQooa
maintained SS5§
for 2 © 3 2.
: Qe
erevious 85
summers. 243
. t . ~
Nearing site Exciusiot, go ND 5
capture. . Contro! fire 5007 8 2
700
. sie aeons Prune and load ov >
Endemic Plantation in. ee -
nardwood 6-20 estored thin at high Forest siasning anc.
hardy 5 a vestorac ee arest oe Enc: car
S ste fl ie eos dearees sparen stocking rate 57g pruning and S02 aw,
Biwi’ JEOPESS ae i “9 ensure site racic shinning. a2
» BIOWE) arse SUDDFESSESS Grazing t0 [email protected] m dees mids .
al! weeds. consices ed Searted
Encourge ‘onger term.
native
regeneration
between
plantation
species.Section 87
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Noosa Council
Temporary Local Planning Instrument
(Protected Vegetation Overlay) 2014
Clearfell, Exclusion
Predominately There are ~ontral fre Start >
weeds (Pine, 0-20 only weeds jay 2014
Camphor, degrees here and the Foresi slashin snd
+ Triangle 9.3 Lantana, upper, Patch above odd native to Practice = eine we ENG: 4D from
a Groundsel, 20-30 Ark Paddock Geretained or potential reining ane 3035 top.
; 7 we bent : : soy Punt Ac
some young degrees where for B&B or , Ss b
natives, some lower possinie. ee © Status:
wattie} Plant as | pean Planned
plantation. anger term.
a7
. Start: De
~ . Native So
E Cloeziana, 0-20 Save 2007 Foot oF 33
pet . forest above tracked 2 Oo
. C. Citriadera = cegrees ,. top ae ; . 9 3
Uc ser “ the point of . ‘ Coo! burns . yenicie only. % &
. ; icy ubper, Forest Native Forest Enc: ‘ ss
u No thern 254 an vehicular . . : an < 10 year L Possible x
Intermedia, L. 20-30 _ practice area. Practice . 2035 <5 =
Ric ge - = ,. BCcess a10ng rotation, 4WD access ~ 290
Confertus, E. degrees oo aa tharn f & aes
Microcorys lower noundary Status: hbo go 5 00
sounda ale rs, 2
; Started HEIEABOLTS s 89
23.5
Coal burns os°5
Currently an < 10 year : 8 > ~
wead rotation. = a
infested Start: Ss
pasture. 79 Area next to 7005. S >
Paccocks beused for 2a. K tebe main “76" AR
p29 and cleared farm practice firebreak end:
v Va ley Floor 1.5 Pasture degrees lanc in 2,3 infrastructure Gravine between 5035 Awe.
° and 4th but otherwise 5 i iture Western end © -
vailey completely 3 of farm and Status
planted out the main Started
unless used infrastructure o—
for grazing or area. Burnt
agriculture. and siasnec
< 3 years.
We stera F. Cloeziana, 9-20 Native Forest Native Forest Coo burns = Start; Foot ar
Wi Ric 08 ‘ 7 C. Citriedora degrees forest on practice with Practice “on < 10 year 2007 tracked
. C. upper, Southern very — rotatian, vehicle only.Section 88
88
Noosa Council
Temporary Local Planning Instrument
(Protected Vegetation Overlay) 2014
4D and
intermedia, ¢. tractor
Confertus and occassions! Enc: access fram
many 20-30 harvest 2025 chern
any 20°30 snc Western AVES. 4 SOULACET
Erythring degrees... cycles fess neighbours.
uf . ; fenclines i 7 Speci}
vespertilio an lower then 20 Status: Possidie
the upper years). Started 4wWD access
riege fines. from rear
neigndours.
Lantana = : 4
. Site is Exciusion. To Do
mainly, some North Souch oad py sore! me Start: a8
camphor and deep ravine ainiy arosion 2006/07 % 3
: - itt TOU © 1? fe .
some Brush 30 fram - 23
e a ' iE m ihe
Box in the degree Northern weeds, Keep When End: Foot onl as
X Th: Canyon y Box ins Egree - under watch Conservation recovered , ny <re2
lower area pus on boundary to see if will most 2035 Very steep. es 8
andagood sides with heavy : arn m7 2a
Pee go enhancement likely be too Svea
Tix of natives erosion and 7. oO Status: +5908
in the ugoer ‘and sia plantings are wet to take a Started o 20
fe uppe nF required. fire, ae 23.5
area. os 9
se ~
Very steep S =
and bony <= 3
area where 83
unexplored Regrowth — crainage Start. > eS
di o very area below fines sha *
sean out ridges in commence. euee
_, Steel aa se back thire of Good natives Native Forest Coo! aurns oo
. Th . some Banksia 20-20 |, we te End: Foot oniy.
y Ar pnitheat 6 | stermedia ceorees the along these Practice or an < 19 year 5035 Very steep ‘
m patheatre eeeembeier SSETSS° property. _ lines and Offsets rotation. ie ery steep.
E, citriccara, an and ionty af
mixed Steep ard pienty o Status:
vainfarest inaccessible thick weeds. Planned
rainvorest ay foot, Leave to anne
allow the
forest Lo
recapture.
Sam 0-20 The Riparian . Exciusion. Start: > Foor anly.
z Zo se Wet 4 Oe et aan eee = Conservation Su pos only
rainforest (E. degrees drainage areas foi WHI mot take 2013 Very stees.Section 89
89
Noosa Council
Temporary Local Planning Instrument
(Protected Vegetation Overlay) 2014
5
Grandis with 320 . preservation, Enc:
. features : i “ pg une
dominates in degree above the mand a fire most of 2635
places), BUS ON Tos removal of the time.
, . op Bam "ee .
wattle sides weeds only. Status:
Pignned
Foot or
- tracked
9-20 Native sno. vehicle only.
rhe
£, Cloeziana, | Forest * 4WD and
C. citriodora “© 9E°> featuring Forest Cool burns tractor Bal
c Sp uted m ‘ uoper, fo practice area. Native Forest 7. EW: ws a3
SR : 6 ot. , Spotted - . on < 10 year a access fram Qs
Ric ge - . 20-30 2 Access to Practice ee 2035 mene oO
Intermedia, L. fearees CUS OF “daaline rotation. southern Qs
Confertus lower southern eee Status: neighbours. ga
mes" side rae Tractor <re2
Startec : so 8
access from ees
valley floor, SDL
. a9 9 ©
Start: 952
= . nme 3°53 S
Tallowwoods 2007 os a
growing Forest Coo! . a2
De . oe oo! burns Tractor >
~ Ta: owwood = an 0-20 aroundthe practice area. Native Forest a ENE: ee, so
Te ~ 0.4 & Micrecorys 7. en nf - - ve ees on< 10 year 2.07 access from S¢
Co ner degrees base of ACTESS tC Practice ye 2035 D. fae {ce
= a "Orahien. valiey fioar, Ny
Spotted ridgeline. y N 5
Ridge Status: SS
Started
Arca oetween Exclusion
. . ; the vaile after
Predaminateiy Lantana, : - ¥ . Start: Faot only at
. . Floo” open plantatian. 5 i. .
weeds (Pine, 0-20 Camphor “amet jem ft . , eO10/il the moment.
. . . me pasture (V) Fire may dé in .
Camphor, degrees and Pines anc rhe used to 4WD and
We 2d , Lantana, lower, between . Forest - ~ End: tractor
WW Werder * Groundsel 20-30 9 remnant femnane Practice cone 2035 access frem
We Oe! ° a“ ‘ a de ees areas ang forest (SR). a weeds and “"7" valtey floor
S y 7% srees areas 3 . bs yarey MCco
natives, 5 ne uope" apen . Preferred C'SPOse OF Status: when .
Wa ttie) nme wees paddocks option is the them. underway cleared
wattle; PaTcors mechanical yum
removal! of all Control fireSection 90
90
Noosa Council
Temporary Local Planning Instrument
(Protected Vegetation Overlay) 2014
weeds
present
which is up
to 95% af
the
vegetation.
Ail natives to
be retained
where
practical. '
Immediate
repianting
with a la-ge Sa
scale load Dy 3 3
plantatian {a siashing anc 2 9
further 4Ha)} pruning anc 3
comprising thinning. <re
neany all of Grazing ta be i a 8 8
areas ¥ and considered S > a ©
Www ianger term, : = g o 9
combined S35 §
that will 9s
extend g =
vegetation = a
conzinguousiy N§
across 90% 8 ®
of the rear S53
two thirds of
the praperty
to link
rigarian and :
remnant
areas.