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Attachment C - Rev Fauna and Flora Assessment
FAUNA AND FLORA ASSESSMENT
Vipassana Centre Building Program
Pomona
For Dhamma Rasmi Organisation
Native Foresters
Natural Resource Management Consultants
Email: [email protected]
Mob: 0407 757 872
Document No: 190412 – Revision 1
Date: 25th April 2021
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Native Foresters DISCLAIMER The authors do not accept any form of liability, be it contractual, tortious, or otherwise, for the contents of this document or for any consequences arising from its use or any reliance placed upon it. This report has been compiled on the basis of existing literature, information, and a targeted survey. Native Foresters does not undertake responsibility arising in any way to any persons in respect of the data, errors, or omissions arising, through misinterpretation of information, negligence or otherwise, however caused. Native Foresters is an independent consulting company undertaking projects in Natural Resource Management. All work conducted as part of this survey was conducted under the DERM Scientific Purposes Permit number WISP 10189211 and DEEDI Animal Ethics Committee number CA 2018/01/1150 and in accordance with the relevant regulations. STUDY TEAM Simon McVerry (BASc – NRM) - Project Director Vanessa Moscato (BSc) – GIS mapping and Reporting Jake Hazzard (BSc) – Fieldwork – Flora and Reporting DOCUMENT CONTROL Project: Vipassana Centre Upgrade Pomona Document: Fauna and Flora Assessment Document No.: 190412-Rev 1 Client: Vipassana Meditation Centre Project Manager: John Hanna Vipassana Centre Building Program - Pomona – Fauna and Flora Assessment 2
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Table of Contents
1.0 INTRODUCTION ...................................................................................................... 5
1.1 Objectives of the report ......................................................................................... 5
1.2 Site description ..................................................................................................... 5
1.3 Legislative requirements ....................................................................................... 6
1.4 Proposed works .................................................................................................... 6
1.5 Impacts on fauna habitat ....................................................................................... 7
1.6 Avoidance of environmental impact……………………………………………………..8
2.0 METHODOLOGY ................................................................................................... 11
2.1 Desktop review ................................................................................................... 11
2.2 Field assessment ................................................................................................ 11
2.2.1 Flora survey ................................................................................................. 11
2.2.2 Fauna survey ............................................................................................... 12
2.2.3 Breeding places and fauna habitat assessment ........................................... 12
2.2.4 Justification of survey timing and weather conditions ................................... 14
2.2.5 Survey limitations ......................................................................................... 14
3.0 RESULTS............................................................................................................... 15
3.1 Desktop review ................................................................................................... 15
3.1.1 Regulated Vegetation Management map ..................................................... 15
3.1.2 Regional Ecosystem mapping ...................................................................... 15
3.1.3 Essential Habitat designation ....................................................................... 15
3.1.4 WildNET search ........................................................................................... 17
3.1.5 EPBC Protected Matters .............................................................................. 17
3.1.6 Protected Plants Flora Survey Trigger map ................................................. 17
3.1.7 Koala legislation ........................................................................................... 19
3.1.8 Wetlands and Watercourses ........................................................................ 19
3.2 Flora assessment................................................................................................ 20
3.2.1 Vegetation within the proposed clearing area............................................... 20
3.2.2 Vegetation within 100 metre buffer............................................................... 24
3.2.3 Weeds……………………………………………………………………………....26
3.3 Fauna assessment.............................................................................................. 26
3.4 Assessment of breeding places and fauna habitat quality ................................... 28
4.0 SUMMARY ............................................................................................................. 30
5.0 RECOMMENDATIONS .......................................................................................... 30
REFERENCES ................................................................................................................. 32
APPENDIX A: DHAMMA RASMI MASTERPLAN……………………………………………...33
APPENDIC B: OFFSET PLANTING SPECIES LIST…………………………………………..34
APPENDIX C: SIGNIFICANT TREES AND AND HABITAT FEATURES……………………35
APPENDIX D: CERTIFICATION OF SUITABLY QUALIFIED PERSON…………………….36
APPENDIX E:JUSTIFICATION OF SUITABLY QUALIFIED PERSON FOR FAUNA
SURVEY…………………………………………………………………………...37
APPENDIX F: KOALA MAPPING………………………………………………………………..38
APPENDIX G: VEGETATION CLEARING TABLE……………………………………………..39
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Native Foresters Figures FIGURE 1: Locality map ..................................................................................................... 7 FIGURE 2: Vipassana Meditation Centre survey area......................................................... 9 FIGURE 3: Revised Survey area ………………………………………………………………..16 FIGURE 4: Mapped vegetation communities occurring at Vipassana Meditation Centre…16 FIGURE 5: Protected Plants Flora Survey Trigger map .................................................... 18 FIGURE 6: Northern Fire Management Area Area ............................................................ 22 FIGURE 7: Northern Construction Zone………………...………………………………………22 FIGURE 8: Southern Fire Management Zone and Pond area…………………..……………23 FIGURE 9: Southern Construction Area………………………………………………………...24 FIGURE 9: Breeding Places and Significant Trees…………………………………………….25 FIGURE 10: Arboreal mammal scratchmarks on Grey Gum………………………………….28 FIGURE 11: Eastern Grey Kangaroo grazing onsite…………………………………..………28 FIGURE 12: Stump and woody debris providing fauna habitat onsite……………………….29 Tables TABLE 1: Regional ecosystems mapped over survey site ………………………………......15 TABLE 2: Listed species identified by desktop research within 4 km of survey area..........17 TABLE 3: Results of timed meander flora surveys ……………………………………………25 TABLE 4: Fauna identified in survey area...…….…………………….…....…………………..27 Vipassana Centre Building Program - Pomona – Fauna and Flora Assessment 4
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1.0 INTRODUCTION
Native Foresters has been commissioned by Dhamma Rasmi Organisation to conduct a flora
and fauna survey and habitat assessment of the vegetation surrounding the Vipassana
Meditation Centre on Rules Road, Pomona Queensland. Construction of new accommodation
areas and a meditation building have been proposed for the site.
This report assesses the fauna and flora which are present; the ecological condition of the subject
site, and the presence of breeding habitat for native fauna. Recommendations relating to
mitigating the potential impacts on fauna and flora species of conservation significance are made
where considered relevant to proposed works.
1.1 Objectives of the report
The objectives of the report are as follows:
• To provide the results of the Flora Survey undertaken in compliance with the requirements of
the Flora Survey Guidelines – Protected Plants (Nature Conservation Act 1992);
▪ To provide the results of the Breeding Places Assessment undertaken in compliance with the
DES Species Management Program Requirements for tampering with a protected animal
breeding place, the Nature Conservation Act 1992 and Nature Conservation (Wildlife
Management) Regulation 2006.
▪ To comment on the potential impacts of any proposed works including the implementation of
required Bushfire Management Zones on native flora and fauna, including State and/or
Commonwealth listed species and their breeding habitat.
1.2 Site description
The subject site is the 350 metre by 400 metre section of the Vipassana Centre that contains
existing buildings, gardens, buffering bushland and cleared areas, located at Rules Road,
Pomona. The extent of works includes the internal access road, cleared lawn areas and gardens,
and remnant sclerophyll forest on the outer edges of the existing built environment, including a
proposed fire management buffer. This represents a total area of approximately 14 hectares. The
subject site is under freehold ownership (Lot 6 RP848414) and adjoins a number of other freehold
properties along the boundaries.
An additional 100 metre buffer area was surveyed for EVNT-listed flora species. The 100 metre
buffer covered lands within and beyond the boundaries of the Vipassana Centre. The total
clearing impact area for the site which includes the 100 metre buffer is approximately 33 hectares.
Refer to Figure 1 for a Locality map and Figure 2 for a Survey area map which shows the area
surveyed. It is noted that this survey area has being subsequently refined to reduce the amount
of vegetation clearing required.
Underlying geology has been described by the Department of Environment and Science (DES),
and Wilson and Taylor (2012) as varying from Land Zone 3 in the creek flats (alluvium associated
with recent Quaternary alluvial systems) to Land Zone 9-10 on the elevated areas (sandstone
ranges and sedimentary rocks) and Land Zone 11 in the vegetated pond area (hills and lowlands
on metamorphic rocks).
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Vegetation surrounding the existing Vipassana Centre is maintained in proximity to the existing
buildings and lawn area. There are areas of cleared grassy understorey, lawns and established
gardens with both native and non-native species present. The surrounding bushland is relatively
intact with a significant number of remnant and regrowth canopy trees and understorey plants.
There are a number of remnant and regrowth Eucalyptus, Corymbia and Lophostemon trees
throughout the works site, including some significant trees exhibiting good habitat values.
Topography across the site is gently sloping. Elevation rises from 104 metres AHD at the northern
entranceway/drop-off area to 129 metres at the highest point behind the new meditation centre,
and falls away to 105 metres at the south-west corner.
Existing impacts on the site include:
i) Historical logging/clearing;
ii) Existing residence/meditation buildings and associated
landscaping/gardens/carparks;
iii) Construction site/temporary sheds, toilets and roads;
iv) Bushland walking trails;
v) Some weed presence, including Camphor laurel (Cinnamomum camphora), Easter
Cassia (Senna pendula var. glabrata), and Corky Passionfruit (Passiflora
suberosa);
vi) Edge effects (increased light, wind, dust and noise) along the forest margins;
vii) Pedestrian access and presence of domestic and feral animals.
1.3 Legislative requirements
To evaluate the habitat values on the site for State and Commonwealth listed flora and fauna
species the following legislation was reviewed:
• Environment Protection and Biodiversity Conservation Act 1999 (EPBC Act) –
Commonwealth
• Nature Conservation Act 1992 (NCA) – State
o Nature Conservation (Wildlife Management) Regulation 2006
• Vegetation Management Act 1999 (VMA) – State
• Biosecurity Act 2016 – State
• Planning Act 2016 and Planning Regulation 2017 – State
1.4 Proposed works
The proposed works involve the following:
i) Construction of new accommodation buildings and associated infrastructure on the
outer edge of the existing built environment both in the Northern and Southern sections
of the site;
ii) Clearing of Fire Management Zones on northern and southern edges of the site
adjacent to areas of retained bushland;
iii) Construction of a new meditation building on the eastern edge of the site.
A revised plan of the proposed works is shown in Appendix A.
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Survey Area
FIGURE 1: Locality map
1.5 Impacts on flora and fauna habitat
Potential direct and indirect impacts to existing flora and fauna habitat from the proposed works
include:
• Loss of 8 - 10 significant native trees which have a diameter at breast height (dbh) of
500 – 800mm, which are providing shade, habitat and arboreal connectivity in the
bushland adjacent to the built environment.
• Loss of 24 - 28 native trees which have a dbh of 200 – 500mm, that provide
supplementary shade, habitat and arboreal connectivity in the adjacent bushland.
• Loss of some midstorey and understorey native trees, shrubs, grasses, sedges and
groundcovers that are providing shade and habitat in the bushland surrounding the
Vipassana Centre.
• Loss or alteration of approximately 500 m2 of mapped remnant open forest (‘Least
Concern’ RE 12.9-10.17 and ‘Least Concern’ RE 12.3.11). It is noted that this area is
actually formed by lawn and track areas and is not considered to form remnant
vegetation.
• Loss or alteration of approximately 500 m2 of mapped Essential habitat for ‘Vulnerable’
fauna species: Koala (Phascolarctos cinereus), and Tusked Frog (Adelotus brevis).
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It is noted that this area is actually formed by lawn and track areas and is not
considered to form Essential Habitat.
• Loss of approximately 5800 m2 of vegetation including native vegetation, exotic
species and areas of maintained grass.
• Removal of stumps, logs, woody debris and leaf litter from the forest floor due to fire
management practices which will cause loss and/or disturbance of habitat, including
breeding habitat, for reptiles, amphibians and mammals.
• Potential disturbance of the root structure and/or Tree Protection Zone of various
native trees located adjacent to the proposed clearing areas, via
excavation/reprofiling/vegetation removal works.
• Potential for dispersal and introduction of weeds by machinery.
• Potential release of sediments/ nutrients into Cooroora Creek from earthworks.
• Compaction of soil and destruction of depressions/burrows used by native fauna.
• Disturbance of habitat through stockpiling of cleared vegetation, soil and construction
materials.
1.6 Avoidance of environmental impact
Consultation between the Project Manager, the Site Architect, the Bushfire Management
Consultant and Native Foresters acting in the role as site ecologist has resulted in a number of
modifications to the original plans for the site (refer Appendix A). The objectives of these
modifications and revisions is to effectively reduce the extent of clearing for the project. Figure 3
shows the revised works footprint and the location of trees recommended for retention within the
clearing footprint. These revisions have resulted in the following changes to the proposed works.
• A relocation of the proposed accommodation buildings in the Northern Construction Zone
to ensure no construction and minimal clearing of mature native vegetation in the Northern
Fire Management zone which is located within an area of mapped remnant vegetation and
essential habitat.
• A relocation of the proposed accommodation buildings in the Southern Construction Zone
to avoid impacts on identified habitat trees located in that area.
• A review and revision of the building materials utilised in the Eastern Construction Zone
(new meditation Pagoda) in consultation with the Bushfire Management Consultant to
negate the requirement for an additional bushfire setback and resulting vegetation
clearing.
• The provision of an area onsite to undertake Offset planting works in order to replace any
Koala Trees lost through clearing works associated with the project has been made. Koala
trees will be replanted at the rate of 4 new Koala food trees for each Koala food tree
cleared. This planting is to be maintained by the Centre until canopy closure is achieved.
Figure 3 shows the location of the nominated Offset Area onsite. Appendix B shows the
species to be planted in the Offset Area.
• A reduction in the extent of vegetation clearing required onsite including a reduction in
impacts to mapped regulated vegetation and Essential habitat.
• It is noted that the provision of an Offset Planting is not mandated by the provisions of the
Offset Act (2014) but is a voluntary undertaking made by the Vipassana Centre.
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Native Foresters FIGURE 2: Vipassana Meditation Centre survey area – Original proposed footprint Vipassana Centre Building Program - Pomona – Fauna and Flora Assessment 9
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FIGURE 3: Vipassana Meditation Centre survey area - revised footprint
Labelled trees (ie A1) are recommended for retention (Refer Appendix C)
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2.0 METHODOLOGY
2.1 Desktop review
A desktop review was undertaken to assist in determining the site’s ecological attributes. The
review consisted of searches of local, state and Commonwealth government planning instruments
and databases, as well as relevant academic literature. Sources of information included:
• Regulated Vegetation Management Map (DNRME, 2018)
• Protected Plants Flora Survey Trigger Map (DES, 2019)
• WildNET Database (DSITIA, 2019)
• EPBC Protected Matters Search Tool (DoE, 2018)
• South East Queensland Koala Conservation Strategy (DES, 2020)
• Nature Conservation (Koala) Conservation Plan 2017 (Qld Government, 2020)
2.2 Field assessment
2.2.1 Flora survey
An experienced botanist undertook a systematic botanical analysis on the 9th April 2019 in order
to assess the vegetation communities occurring within and around the survey area. An additional
flora survey of the revised project extent was undertaken on the 25th April 2021. The survey was
consistent with the Flora Survey Guideline – Protected Plants (NCA 1992). The extent of the flora
survey is indicated in Figure 2.
Significant large native trees with diameter at breast height (dbh) in excess of 500 mm were
identified to inform the breeding places assessment (section 2.2.3).
Certification by the suitably qualified person who led and coordinated the flora survey is provided
in Appendix D.
Three timed meander surveys were conducted in the vegetation communities present around the
survey area in order to determine the presence of EVNT (Endangered, Vulnerable, Near
threatened) flora species within the site’s 100 metre buffer zone as shown in Figure 2. The
following methodology was used to conduct the timed meander survey:
• The location of the start point of the surveys was determined by the botanist in order to
maximise the possibility of locating EVNT species (if such species are present).
• The surveys were conducted in a random manner for a period of 30 minutes with the identities
of any EVNT plant species recorded and specimens of any unknown species collected.
• A record of the time was taken every two to five minutes. If the survey was interrupted then
this time was not recorded in the survey results.
• The search was continued until no new EVNT species were recorded for 30 minutes or when
the entire area of habitat type had been surveyed.
• Where multiple habitat types or vegetation communities were present within a clearing impact
area, a timed meander assessment was undertaken within each of these areas.
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• Where certain preferred habitat types or vegetation communities may be extensively
represented within a site, multiple meanders per habitat type were undertaken across the
clearing impact area to increase the probability of detecting an EVNT species.
An estimate of the statistical power of the flora survey has been made for the site. It is determined
that there is a 95% certainty that all EVNT flora species occurring within the survey area and 100
metre buffer zone for the site have been recorded by the survey.
2.2.2 Fauna survey
A diurnal fauna assessment was conducted on the 9th April 2019 to identify the presence of fauna
including reptiles, amphibians, and mammals by an experienced fauna specialist. A further
targeted amphibian survey was undertaken on 2nd September 2019. The following methods were
used in the conduct of the fauna surveys:
• Active search - searching for fauna under logs, rocks, leaf litter and decorticating bark.
• Passive search - identifying species both visually and aurally whenever the opportunity
arises while onsite.
• Tracks and scats – signs of an animal's presence, such as scats and tracks, are
interpreted. This procedure was generally opportunistic and used whenever specimens
were located.
• Aural survey and/or call playback - where recorded calls of the listed frog species are
played to determine their presence.
• Culvert inspection using spot light.
Binoculars were used to identify arboreal species. A hand-held torch was used for inspecting
hollows where accessible.
2.2.3 Breeding places and fauna habitat assessment
A fauna habitat assessment was undertaken during the field investigations. This assessment was
based on the habitats present, the listed threatened species known to occur or potentially
occurring within the locality, and the occurrence of specific breeding places or breeding habitat
for these species.
A statement to justify the suitability and qualifications of the person undertaking the animal
breeding place survey is provided in Appendix E.
For the purposes of this report, the definition of “breeding places” follows that provided in s332 of
the Nature Conservation (Wildlife Management) Regulation 2006. For species such as Koala and
native frogs, who do not use a habitual breeding place, the term ‘breeding habitat’ is used in lieu
of ‘breeding place’. The fauna habitat assessment is important in determining species that may
be in the area but whose presence was not able to be detected.
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Habitat features that were considered significant for assessing the presence of breeding places
and/or habitation value for native fauna, include but are not limited to:
i. Presence of hollow-bearing trees: These may be used by birds, reptiles or arboreal
mammals to incubate or rear offspring;
ii. Presence of bowers, nests, dreys: These structures are commonly used by birds or
mammals to incubate or rear offspring;
iii. Presence of caves, mounds, burrows, ground hollows and/or coarse woody debris: These
structures are commonly used by birds, mammals, reptiles or amphibians to incubate or
rear offspring;
iv. Presence of permanent water, ephemeral ponding, depressions and/or, seasonally
inundated areas: Waterbodies may be used for breeding by aquatic species or
amphibians, or that may provide intermittent breeding habitat for opportunistic species;
v. Presence of large trees: Large trees can be a dominant feature of native vegetation and
are difficult to replace once lost. Their influence for wide-ranging species can extend over
a considerable distance from their location.
vi. Canopy cover: The uppermost stratum of woody vegetation that forms the canopy
functions as habitat for birds and arboreal mammals, provides food and resources, and
determines the degree of light penetration and heat reaching the lower strata and ground
detrital layer.
vii. Weed cover: Weeds can dominate and suppress native plant growth which affects the
diversity of food sources; they can change the fuel or litter characteristics of a site, thereby
altering the fire regime, and also prevent recruitment and succession of native vegetation.
viii. Understorey components: The shrub and herb strata generally contain the greatest plant
species richness and can be a useful indicator of disturbance and changes in condition.
ix. Organic litter, fallen timber and rocks: Litter cover can be indicative of the degree of
disturbance of a site, and can be an important determinant of species recruitment. It will
influence soil microclimates, structure and composition, and provide refugia for
invertebrates, reptiles, amphibians and ground dwelling mammals.
x. Recruitment: Recruitment of plant species, particularly woody perennials, within all strata
reflects the site’s long-term viability.
xi. Landscape context: The size of a patch, its connectivity and distance to a core area of
vegetation (i.e. greater than 50 hectares) can affect both its regenerative capacity and
long-term viability. Species–area relationships suggest that large areas support more
species and populations than smaller ones thus retaining greater genetic variability and
providing refuge for species susceptible to disturbances.
Some areas were obscured by thick vegetation and/or vines, and certain habitat features within
the treetops were difficult to assess due to their height within the canopy. All features that were
able to be effectively assessed are described in section 3.4.
Significant habitat trees >500mm dbh were identified onsite and then further described in
Appendix C in order to inform works, identify specific trees for retention and assist the fauna
spotter-catcher in identification of breeding places during works. Significant habitat trees contain
at least one habitat feature that could be used as a breeding place. For example a tree that
contains an arboreal termite mound, a small hollow, peeling bark, large crevices, or is hollow at
the base.
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Native Foresters 2.2.4 Justification of survey timing and weather conditions Field surveys were conducted in early autumn under fine conditions with temperatures ranging from 16-28 degrees Celsius; relative humidity of 61-67%; and 68mm of rain in the preceding week. Additional amphibian surveys were conducted in warm dry conditions in spring. The timing of the survey is considered suitable for detecting the target EVNT listed plant species: Bosistoa transversa, Cryptocarya foetida, Floydia praealta Macadamia integrifolia, Macadamia ternifolia, Pararistolochia praevenosa, Phaius australis, Samadera bidwillii, Sophora fraseri and Triunia robusta. 2.2.5 Survey limitations Emphasis is placed on surveying listed threatened ecological communities, populations and/or species that are considered likely to occur within the survey area. With respect to opportunistic observations, the possibility exists that certain species may not have been detected during field investigations due to: • seasonal inactivity during field survey; • species present within microhabitats not surveyed; • species that occur at very low abundance or in very small populations; • cryptic species able to avoid detection; • transient wide-ranging species not present during survey period; • absence of reproductive material for flora identification; or • drought induced leaf fall or senescence. The lack of observational data on some species should therefore not be taken as necessarily indicating that a species is absent from the site. The repetition of the survey in different seasons and years is recommended to minimise the effect of this limitation on the survey results. The field assessment for fauna employed passive techniques only (i.e. no live trapping) and the habitat assessment was limited to contracted timeframes. The initial fauna survey was conducted in early autumn following a rain period which is considered suitable for amphibian detection. Most bird species, including Special Least Concern species that are known to breed in eastern Australia, would be in post-breeding activities at the time the survey was conducted (April), although given increasing climatic variability and associated changes to breeding seasons and breeding success, the potential presence of nests cannot be reliably discounted. The precautionary principle was applied in estimating the likelihood of Commonwealth and State listed species based on habitats identified within the subject site. Vipassana Centre Building Program - Pomona – Fauna and Flora Assessment 14
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3.0 RESULTS
3.1 Desktop review
3.1.1 Regulated Vegetation Management map
The Department of Natural Resources, Mines and Energy (DNRME) presents the Regulated
Vegetation Management Mapping (RVMM) as gazetted under the Vegetation Management Act
(1999) (VMA). Analysis of RVMM shows that the survey area contains mapped Regulated
Vegetation in the areas surrounding the Vipassana Centre.
3.1.2 Regional Ecosystem mapping
DNRME presents a Vegetation Management Supporting map which shows the location of
Regional Ecosystems (RE) as gazetted under the VMA (1999). Analysis of this map shows that
the vegetation within and adjacent to the proposed works, including the 100 metre buffer zone
(which contains the riparian zone on the western edge of the Vipassana Centre allotment)
contains ‘Of Concern” RE 12.3.2 and 12.3.11, ‘Least Concern’ RE 12.9-10.17 and ‘Endangered’
RE 12.3.1.
These REs are described in Table 1 and their location is represented in Figure 4.
TABLE 1: Regional Ecosystems mapped over survey area
RE VMA status Biodiversity Description
status
12.3.2 Of concern Of concern Eucalyptus grandis tall open forest on alluvial plains
12.9-10.17 Least No concern at Eucalyptus acmenoides, E. major, E. siderophloia +/-
concern present Corymbia citriodora subsp. variegata woodland on
sedimentary rocks
12.3.1a Endangered Endangered Gallery rainforest (notophyll vine forest) on alluvial plains
12.3.11 Of Concern Of Concern Eucalyptus tereticornis +/- E. siderophloia and Corymbia
intermedia open forest to woodland
3.1.3 Essential Habitat designation
Essential Habitat is a vegetation ecotype that is considered by DES to form potential habitat for a
species that is listed as Endangered, Vulnerable, Rare or Near Threatened under Schedules 2-5
of the Nature Conservation (Wildlife) Regulation (2006). Essential Habitat mapping is provided in
conjunction with Regulated Vegetation Management mapping (DNRME 2016) as gazetted under
the VMA (1999).
The remnant vegetation on the Vipassana Centre allotment (Lot 6 on RP848414) is designated
as Essential Habitat for Vulnerable-listed Tusked Frog (Adelotus brevis) and Koala
(Phascolarctos cinereus).
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FIGURE 4: Mapped vegetation communities occurring at Vipassana Meditation Centre
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3.1.4 WildNET search
DES and DSITIA has compiled a database of wildlife sightings and listings for all flora and fauna
species within a designated area. A database search was conducted for all listed species that
have been identified within one kilometre of the survey area on Lot 6 RP848414. Three EVNT-
listed fauna species were listed on WildNET as shown in Table 2.
TABLE 2: Listed species identified by desktop research within 1km of survey area
NCA EPBC
SCIENTIFIC NAME COMMON NAME SOURCE
STATUS STATUS
EVNT FAUNA
Adelotus brevis Tusked Frog V - WildNET
Calyptorhynchus lathami lathami Glossy Black Cockatoo V - WildNET
Phascolarctos cinereus Koala (SE Qld region) V V RVMM
3.1.5 EPBC Protected Matters
A report was generated using the EPBC Act Protected Matters Search Tool. It noted that there is
potential for 34 Threatened Species and 15 Migratory Species to occur within one kilometre of
the centre of the survey area, including Koala (Phascolarctos cinereus) listed as Vulnerable, and
Giant Barred Frog (Mixophyes iteratus) listed as Endangered.
There is also potential for one listed Ecological Community to occur within one kilometre of the
site: Lowland Rainforest of Subtropical Australia, which is listed as Critically Endangered under
the EPBC Act (1999).
3.1.6 Protected Plants Flora Survey Trigger map
The Protected Plants Survey Trigger Map is a tool provided by DES in order to identify areas that
may contain EVNT plant species. The trigger map is used to determine when a flora survey needs
to meet the requirements of the Flora Survey Guidelines – Protected Plants (NCA, 1992). Figure
5 shows that the Vipassana Centre allotment lies within a Protected Plants high risk area and as
such, is subject to the provisions of the guidelines.
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FIGURE 5: Protected Plants Flora Survey Trigger map
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Native Foresters 3.1.7 Koala legislation Planning Act 2016 The Planning Act 2016 regulates new development including areas of South East Queensland identified as having important Koala habitat values. The Planning Regulation 2017 (Schedule 10) establishes where clearing may be prohibited, where it is assessable by the State, where Koala conservation outcomes will be considered by local governments and what exemptions may apply. The Nature Conservation and Other Legislation (Koala Protection) Amendment Regulation amends the Environmental Offsets Regulation 2014, Planning Regulation 2017, Nature Conservation (Koala) Conservation Plan 2017 and Vegetation Management Regulation 2012 to provide increased protection to Koala habitat areas in South East Queensland. The Nature Conservation (Koala) Conservation Plan 2017 and Koala Conservation Plan Maps identifies Koala Habitat Areas (core and locally refined) and Koala Priority Areas that contain Koala habitat which is essential for the conservation of a viable Koala population in the wild in South East Queensland. Clearing Koala Habitat Areas in a Koala Priority Area is prohibited, except for in certain circumstances (see Schedule 10, 16A of the Planning Regulation 2017). Development in Koala Habitat Areas made assessable under the Planning Regulation 2017 will need to address State Code 25: Development in South East Queensland koala habitat areas. A search of the Koala habitat area and Koala priority area mapping (Refer Appendix F) shows that the site lies in a Koala priority area and that core Koala habitat is mapped within the Northern Fire Management Area as shown in Figure 3. Clearing for essential management which means clearing native vegetation for establishing or maintaining a necessary firebreak to protect infrastructure, if the maximum width of the firebreak is equal to 1.5 times the height of the tallest vegetation next to the infrastructure, or 20m, whichever is the wider is considered ‘exempted development’ under Schedule 24 – Essential Management (Part a) of the Planning Regulation 2017. 3.1.8 Wetlands and Watercourses The quality of natural waters in Queensland (e.g. rivers, creeks, wetlands, lakes, estuaries and coastal areas and ground waters) is protected under the Environmental Protection (Water) Policy 2009 (EPP Water). The EPP Water achieves the object of the EPA 1994 to protect Queensland's waters while supporting ecologically sustainable development. The Map of Referable Wetlands is a statewide regulatory map under the Environmental Protection Regulation 2008 which identifies wetlands of high ecological significance (HES) and general ecological significance (GES) across the state. HES wetlands on the Map of Referable Wetlands are considered ‘matters of state environmental significance’ (MSES) under the Planning and Environmental Offsets legislation (Environmental Offsets Act 2014). Vipassana Centre Building Program - Pomona – Fauna and Flora Assessment 19
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Native Foresters
There are no wetlands of significance in the footprint of proposed works, however the tributary of
Cooroora Creek and its riparian zone on the northern boundary of the Vipassana Centre allotment
is mapped as a wetland of high ecological significance.
3.2 Flora assessment
3.2.1 Vegetation within the proposed clearing area
The proposed construction areas and fire management zones of the subject site contain a
combination of remnant and regrowth vegetation, including some large, relictual native trees. A
total of 40 local native species and eight introduced (weed) species were recorded during the
survey within the proposed works areas. No EVNT flora species were recorded. The vegetation
within the construction areas and fire management zones has been divided into four sections and
are described in more detail below.
Appendix C provides specific information on trees which will be impacted by works and trees that
are recommended for retention. Appendix G details the potential extent of clearing within each
of the identified Fire Management and Construction Zones. Figure 3 shows the Fire Management
and Construction Zones and the location of trees to be impacted by works.
A) Northern Fire Management Zone
• The Northern Fire Management Zone vegetation is remnant sclerophyll forest (Least
concern RE 12.9-10.17 Eucalyptus acmenoides, E. major, E. siderophloia +/- Corymbia
citriodora subsp. variegata woodland on sedimentary rocks) with patches of mowed
grasses and weeds (Digittaria, Setaria, Paspalum, Melinis sp) adjacent to the access road
and on forest margins. Refer to Figure 6.
• There are several native re-vegetation specimens present in patches, planted in areas
that were previously cleared of sclerophyll forest, on soil mounds.
• The remnant forest is dominated by tall Pink Bloodwood (Corymbia intermedia), Brushbox
(Lophostemon confertus) and Tallowwood (Eucalyptus microcorys), with dbh of 200mm
to 600mm and heights of approximately 15-20m, occurring within the proposed fire
management clearing area.
• There are native trees with a dbh of 500mm or more occurring within and adjacent to the
Fire Management Zone that should be retained for their habitat and shading values as
shown in Figure 3 and Appendix C
• The mid stratum consists of smaller trees, shrubs and vines including Alphitonia excelsa,
Macaranga tanarius, Lophostemon suaveolons, Dodonea triquetra, and Cissus
hypoglauca.
• Native and some non-native grasses and forbs occur in the understorey (e.g. Ottochloa
sp, Oplismenus aemulus and Imperata cylindrica, with mown lawn grasses and weeds
(e.g. Blue top and Lantana) occurring.
• Proposed works may impact up to 500 m2 of mapped Essential habitat and another
500m2 of native vegetation and grass areas within the Northern Fire Management Zone.
• Clearing in this mapped Essential Habitat Area is considered ‘exempted development’
under Schedule 24 – Essential Management (Part a) of the Planning Regulation 2017.
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Native Foresters
B) Northern Construction Zone
• The vegetation in this area is remnant/regrowth sclerophyll forest (Least concern RE 12.9-
10.17 Eucalyptus acmenoides, E. major, E. siderophloia +/- Corymbia citriodora subsp.
variegata woodland on sedimentary rocks). Refer to Figure 7.
• Nine significant native trees with dbh 500mm or greater occur to form the canopy, some
with well-formed habitat hollows. One Pink Bloodwood (Corymbia intermedia) with dbh
600mm should be retained with understorey cleared. These specimens to be cleared or
retained are shown in Figure 3 and Appendix C.
• Several native trees and shrubs constitute the dense mid-storey including Macaranga
tanarius, Alphitonia excelsa and Petalostigma triquetra.
• The understorey is formed by a number of native sedges including Lomandra longifolia
and Dianella caerulea, and a grassy turfed area.
• Proposed works may impact up to 1500 m2 of native vegetation within the Northern
Construction Zone.
FIGURE 6: Northern Fire Management Zone – Remnant/regrowth sclerophyll open
forest/woodland with grass patches.
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Native Foresters
FIGURE 7: Northern Construction Zone - Remnant/regrowth sclerophyll open forest
C) Southern Fire Management Zone
• The vegetation in this area demonstrates general consistency with remnant sclerophyll
forest (Least concern RE 12.9-10.17 Eucalyptus acmenoides, E. major, E. siderophloia
+/- Corymbia citriodora subsp. variegata woodland on sedimentary rocks, which is
mapped immediately to the south and east).
• The remnant forest is dominated by tall Pink Bloodwood and Brushbox, with dbh of 200mm
to 800mm and heights of approximately 15-20m, occurring within the proposed fire
management zone.
• There are five significant native trees with a dbh of 500mm or more occurring within and
adjacent to the Fire Management Zone. A minimum of four of these trees should be
retained for their habitat, shading, and canopy connectivity values. These specimens are
as shown in Figure 3 and Appendix C
• The western end of the southern fire management zone contains a pond and riparian
vegetative buffer dominated by a Melaleuca salicina midstorey. Refer to Figure 8.
• The mid stratum consists of smaller trees, shrubs and vines including Alphitonia excelsa,
Macaranga tanarius, Lophostemon suaveolons, Pilidiostigma rhytispermum, and Smilax
australis.
• Native grasses occur in the understorey (e.g. Ottochloa sp, Oplismenus aemulus and
Imperata cylindrica, with some mown lawn grasses and weeds (e.g. Umbrella Tree and
Lantana).
• Proposed works may impact up to 1,100 m2 of native vegetation and grass areas within
the Southern Fire Management Zone.
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Native Foresters
FIGURE 8: Southern Fire Management Zone – Pond with midstorey Melaleuca salicina buffer.
D) Southern Construction Zone
• The vegetation in this construction area demonstrates general consistency with remnant
sclerophyll forest (‘Least concern’ RE 12.9-10.17 Eucalyptus acmenoides, E. major, E.
siderophloia +/- Corymbia citriodora subsp. variegata woodland on sedimentary rocks,
which is mapped immediately to the south and east). Refer to Figure 9.
• The remnant forest is dominated by tall Pink Bloodwood and Turpentine (Syncarpia
glomulifera), with dbh of 200mm to 600mm and heights of approximately 15-20m,
occurring within the proposed clearing area.
• There are seven significant native trees with a dbh of 500mm or more occurring with high
value habitat (some with visible nests), shading, and canopy connectivity. These
specimens are shown in Figure 3 and Appendix C. A minimum of two of these tree
should be retained. An arborist will be required to monitor TPZ’s during works if excavation
is to occur.
• The mid stratum consists of smaller trees, shrubs and vines including Alphitonia excelsa,
Macaranga tanarius, Lophostemon suaveolons, Pilidiostigma rhytispermum, and Smilax
australis.
• Native and some non-native grasses and forbs occur in the understorey (e.g. Ottochloa
sp, Oplismenus aemulus and Imperata cylindrica, with some mown lawn grasses and
weeds (e.g. Blue top and Siratro).
• Proposed works may impact up to 2,200 m2 of native vegetation and grass areas within
the Southern Construction Zone.
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Native Foresters
FIGURE 9: Southern Construction Area - remnant/regrowth sclerophyll forest
E) Eastern Construction Area
The construction footprint for the new meditation centre in the east of the site is composed of
mowed grasses. There is no requirement for clearing of additional native vegetation in this area.
3.2.2 Vegetation within 100 metre buffer
Three timed meanders were undertaken through the 100 metre buffer zone traversing three
remnant ecosystem types on the Vipassana Centre allotment and one neighbouring private
allotment (Lot 2 on RP35094):
i. Least concern RE 12.3.2 - Eucalyptus grandis tall open forest on alluvial plains
ii. Least concern RE 12.9-10.7 - Eucalyptus acmenoides, E. major, E. siderophloia +/-
Corymbia citriodora subsp. variegata woodland on sedimentary rocks
iii. Endangered RE 12.3.1 - Gallery rainforest (notophyll vine forest) on alluvial plains
The location of the timed meander flora surveys is shown in Figure 2. No EVNT flora species
were recorded. The results of timed meander surveys are summarised in Table 3.
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Native Foresters
TABLE 3: Results of timed meander flora surveys
Survey 1 (remnant RE 12.3.2)
Starting point GPS coordinates: -26.378168oE, 152.857264oS
Target species: Bosistoa transversa, Cryptocarya foetida, Diteilis simmondsii, Floydia praealta
Macadamia integrifolia, Macadamia ternifolia, Phaius australis, Samadera bidwillii, Sophora fraseri
and Triunia robusta.
Time Species recorded
1200
Nil
1230
Survey 2 (remnant RE 12.9-10.7)
Starting point GPS coordinates: -26.376790oE, 152.858018oS
Target species: Bosistoa transversa, Cryptocarya foetida, Floydia praealta Macadamia integrifolia,
Macadamia ternifolia, Phaius australis, Samadera bidwillii, Sophora fraseri and Triunia robusta.
Time Species recorded
1230
Nil
0100
Survey 3 (remnant RE 12.3.1)
Starting point GPS coordinates: -26.376528oE, , 152.856544oS
Target species: Bosistoa transversa, Cryptocarya foetida, Floydia praealta Macadamia integrifolia,
Macadamia ternifolia, Pararistolochia praevenosa, Phaius australis, Samadera bidwillii, Sophora
fraseri and Triunia robusta.
Time Species recorded
0100
Nil
0130
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Native Foresters 3.2.3 Weeds Camphor Laurel (Cinnamomum camphora) is a highly invasive evergreen tree that has a tendency to form single species communities and exclude most other desirable native vegetation. It is classified as a Restricted Invasive Plants under the Biosecurity Act 2014. There are numerous Camphor Laurel specimens occurring the understorey and midstorey of the bushland within and adjacent to the clearing impact areas of the proposed developments at Vipassana Meditation Centre. All reasonable and practicable steps must be taken to control the species as part of a general biosecurity obligation under the Biosecurity Act. It is recommended that all Camphor Laurel specimens including fruiting parts be targeted and appropriately removed and disposed of during clearing/site preparation works. 3.3 Fauna assessment The vegetation at Vipassana Meditation Centre supports the breeding and habitation requirements of a diversity of native fauna, including but not limited to: one arboreal mammal species; two terrestrial mammals; one Special Least Concern monotreme; eighteen bird species including one Special Least Concern bird; one amphibian species, and six reptile species, as shown in Table 4. There are recent sightings of Vulnerable-listed Koalas (Phascolarctos cinereus) in the surrounding area. Potential scratch marks were found on a Grey Gum on the eastern side of the Vipassana Centre (Figure 10). Preferred Koala food trees (Eucalyptus microcorys, E. propinqua and Lophostemon confertus) are present across the site. It is considered likely that surrounding bushland may be used as a movement corridor for local Koala populations (and other arboreal mammals) as they disperse from tracts of suitable bushland habitat occurring in the surrounding area. Short-beaked Echidna (Tachyglossus aculeatus) has been identified at the Vipassana Centre grounds. Echidna are listed as Special Least Concern species under the Nature Conservation (Wildlife) Regulation 2006 due to their unique and iconic cultural significance. Rufous Fantail (Rhipidura rufifrons) has been recorded at the site. Rufous Fantail are listed as Special Least Concern species under the Nature Conservation (Wildlife) Regulation 2006. They are migratory, virtually disappearing from Victoria and NSW over the winter period to move to warmer climates in Queensland. There are regular visits by Grey Kangaroo (Macropus giganteus), including females and joeys, utilising the grassy areas of the Vipassana Centre grounds. Least-concern amphibian, Green Tree Frog (Litoria caerulea) have been detected aurally on the Vipassana Centre grounds. The vegetation, ponds and drainage lines may support the breeding, habitation and dispersal requirements of Vulnerable-listed Tusked Frog (Adelotus brevis), although none were detected during the survey. Vipassana Centre Upgrade Pomona – Fauna and Flora Assessment 26
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Native Foresters TABLE 4: Fauna identified in survey area SCIENTIFIC NAME COMMON NAME Birds Alectura lathami Brush Turkey Cacatua galerita Sulphur-crested Cockatoo Calyptorhynchus funereus Yellow-tailed Black Cockatoo Ceyx azureus Azure Kingfisher Coracina novaehollandiae Black-faced Cuckoo Shrike Corvus orru Torresian Crow Cracticus torquatus Grey Butcherbird Dacelo novaeguineae Laughing Kookaburra Eopsaltria australis Eastern Yellow Robin Gymnorhina tibicen Australian Magpie Malurus melanocephalus Red-backed Wren Malurus splendens Splendid Wren Manorina melanocephala Noisy Miner Podargus strigoides Tawny Frogmouth Rhipidura leucophrys Willy Wagtail Rhipidura rufifronsSL Rufous Fantail Scythrops novaehollandiae Channel-billed Cuckoo Trichoglossus haematodus Rainbow Lorikeet Mammals Macropus giganteus Grey Kangaroo Macropus parryi Pretty Faced Wallaby Tachyglossus aculeatusSL Short-beaked Echidna Trichosurus caninus Short-eared Brushtail Possum Reptiles Dendrelaphis punctulata Green Tree Snake Intellagama lesueurii Eastern Water Dragon Lampropholis delicata Garden Skink Morelia spilota Carpet Python Pseudonaja textilis Eastern Brown Snake Tiliqua scincoides Blue Tongue Lizard Amphibians Litoria caerulea Green Tree Frog Rhinella marina* Cane Toad KEY SL Special Least Concern species *Introduced species Vipassana Centre Upgrade Pomona – Fauna and Flora Assessment 27
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Figure 10 – Arboreal mammal scratchmarks on Grey Gum
Figure 11 – Eastern Grey Kangaroos grazing onsite
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Native Foresters
3.4 Assessment of breeding places and fauna habitat quality
The natural vegetation areas within the survey area have been assessed as possessing good
habitat values, providing breeding habitat as well as refuge, roosting habitat and basking sites for
native fauna. All significant habitat trees and breeding places identified during the survey are
shown in Figure 3 and described in Appendix C.
Several arboreal hollows were observed in the mature trees on the northern and southern sides
of the built environment at the Vipassana Centre which provide important habitat and/or breeding
places for microbats, reptiles (skinks, pythons, goannas) and small gliders such as the Squirrel
Glider and Feathertail Glider. Some of the larger trees contain visible nests (bird/possum) and
are providing high value habitat and breeding places with multiple hollows in one tree.
The location of a large hollow stumps has been indicated in Figure 3 and shown in Figure 12.
These habitat features possess cavities and cracks which may be used by small mammals and
reptiles for refuge and/or breeding and should be retained in situ as ground habitat or relocated
further into the surrounding bushland, rather than burnt or chipped.
Breeding habitat for amphibians occurs in a constructed pond on the south-western corner of the
Southern Fire Management Zone as shown on Figure 8. There is potential for works to impact
this area which may result in the loss or modification of this wetland area.
Figure 12: Stump and woody debris located in Northern Fire
Management Zone, providing breeding habitat for reptiles and small
mammals.
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Native Foresters
4.0 SUMMARY
• The vegetation on the northern side of the existing built structures at the Vipassana
Meditation Centre is mapped as remnant and is in relatively good ecological condition,
with a diversity of native species; mature trees with some hollows forming; a developing
structural complexity and evidence of active recruitment.
• There are significant native trees in the northern area with a dbh of 500mm or more
occurring that provide habitat, shading, and canopy connectivity. Clearing works will
result in the loss of 4-5 of these trees. Areas of exotic understorey weeds are present on
the disturbed forest edges and adjacent to the cleared grassy areas.
• Vegetation on the southern side of the existing Vipassana Centre is mapped as non-
remnant. This vegetation is in fair ecological condition, with native species present;
mature trees with some hollows forming and a developing structural complexity.
• There are significant native trees in the Southern area with a dbh of 500mm or more
occurring that provide habitat, shading, and canopy connectivity. Clearing works will
result in the loss of 4-5 of these trees. Minor patches of exotic understorey weeds are
present on the disturbed forest edges and adjacent to the cleared grassy areas.
• No EVNT listed flora species were detected within the survey area.
• A significant number of preferred Koala food and habitat trees (e.g. Tallowwood, Pink
Bloodwood and Grey Gum) occur at the Vipassana Meditation Centre. Occasional use of
this bushland vegetation as a corridor by Koalas is considered likely.
• The whole site is mapped as a Priority Koala Area and there is mapped Koala Habitat
Area (Core) on the Northern Eastern and Southern areas of the site.
• There will be up to 500 m2 of clearing within this mapped Koala Habitat Area (Core). This
clearing is considered ‘exempted development’ under Schedule 24 – Essential
Management (Part a) of the Planning Regulation 2017. It is noted that this area is actually
formed by lawn and track areas and is not considered to form remnant vegetation or
Koala habitat.
• The bushland survey area provides suitable habitat for a range of native fauna, including
but not limited to: one arboreal mammal species; two terrestrial mammals; one Special
Least Concern monotreme; eighteen bird species including one Special Least Concern
bird species; at least one amphibian species, and six reptile species.
• Historical observations indicate the presence of two Special Least Concern listed fauna
species (Echidna and Rufous Fantail) and one Vulnerable listed fauna species (Koala)
in the survey area. There are two WildNET records of Tusked Frog and one WildNET
record of Glossy Black Cockatoo within one kilometre of the Vipassana Meditation
Centre.
• Modification to the site layout through the design stage has resulted in a reduction in the
amount of vegetation clearing required onsite. The amended plan will require minimal
clearing of remnant vegetation within the areas of mapped Regional Ecosystem onsite.
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Native Foresters
5.0 RECOMMENDATIONS
1. The careful placement of new buildings within the identified Northern and Southern
Construction Zones will allow for the retention of additional trees within this area.
Consideration of the potential impact on the Tree Protection Zones (Tree root systems) when
undertaking excavation works should also be made.
2. Clearing within the identified Northern and Southern Fire Management Zones should be
limited to that which is required to achieve the nominated fire setback requirement for the
project. This should allow for the clearing of mid and ground storey vegetation and the
retention of some canopy trees.
3. Hollow-bearing, nest-bearing and/or relictual trees that are of significant size (i.e. 500-800mm
dbh) and that provide structure and breeding habitat for native fauna should be marked for
retention where possible. Where clearing cannot be avoided due to planned expansion of the
facilities, a targeted pre-clearing survey of hollows and nests should be conducted by an
experienced Ecologist immediately prior to the removal or disturbance of mature trees (i.e.
within 48 hours or under suitable conditions).
4. Any hollows from cleared trees should be salvaged and relocated, together with resident
fauna, to the surrounding area.
5. It is recommended that any Koala food trees removed in the conduct of works should be
replaced in a dedicated revegetation Offset Area on the property. These trees should be
replaced at a ratio of at least 4:1.
6. An experienced wildlife spotter-catcher should be present during removal of significant trees.
7. Arboreal habitat supplementation with nest boxes is recommended to compensate for any
loss of existing hollows. Nest boxes need to be regularly monitored to ensure they are not
colonised by ants, bees or other undesirable species.
8. Due consideration should be given to all native fauna, particularly the potential presence of
Koalas, Echidnas, Rufous Fantail during works.
9. Care should be taken to avoid introduction and further spread of undesirable habitat-changing
weeds during works through machinery inspections and hygiene protocols.
10. It is recommended that all Camphor Laurel specimens including fruiting parts be targeted and
appropriately removed and disposed of during clearing/site preparation works.
11. Implementation of sediment control measures to minimise the potential for erosion and
associated adverse effects on water quality and amphibian breeding habitat will be required
to maintain the aquatic ecosystem health of the tributary of Cooroora Creek that flows from
the catchment of proposed works. Monitoring the effectiveness of these measures during
large rainfall events is also recommended.
12. Felled trees should be retained and dispersed in suitable adjacent forest floor areas to
reinstate coarse woody debris, or donated to community revegetation projects to augment
habitat value for reptiles and small mammals.
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Native Foresters REFERENCES Eyre TJ, Ferguson DJ, Hourigan CL, Smith GC, Mathieson MT, Kelly, AL, Venz MF, Hogan, LD and Rowland, J. (2014). Terrestrial Vertebrate Fauna Survey Assessment Guidelines for Queensland. Department of Science, Information Technology, Innovation and the Arts, Queensland Government, Brisbane. Frogs Australia Network 2017. Australian Frogs Database. www.frogsaustralia.net.au Heavey, J. and MacDonald, S. (2013) Weeds of The Sunshine Coast. Noosa Integrated Catchment Association Inc. Leiper, G., Glazebrook, J., Cox, D. and Rathie, K. (2009) Mangroves to Mountains. A Field Guide to the Plants of South East Queensland. Revised Edition. Society for Growing Australian Plants – QLD Region. Meyer E, Hines H and Hero J-M 2001, Wet forest frogs of south-east Queensland, Griffith University, Nathan. Neldner, V.J., Wilson, B.A., Thompson, E.J. and Dillewaard, H.A. (2012) Methodology for Survey and Mapping of Regional Ecosystems and Vegetation Communities in Queensland, Version 3.2, Queensland Herbarium, Queensland Department Parkes, D., Newell, G. and Cheal, D. (2003), Assessing the quality of native vegetation: The ‘habitat hectares’ approach. Ecological Management and Restoration 4: S29–S38. doi: 10.1046/j.1442-8903.4.s.4.x Queensland Government, Department of Environment and Heritage Protection (2015) Flora Survey Guidelines – Protected Plants. Nature Conservation Act 1992. Queensland Government (2006). Nature Conservation (Wildlife Management) Regulation 2006. Queensland Herbarium (2016) Regional Ecosystem Description Database (REDD). Version 10.0 (December 2016) (DSITI: Brisbane). Simpson, K., and Day, N. (1999), Field Guide To The Birds Of Australia, 6th Edition. Penguin Books, Australia. Wilson, P.R. and Taylor, P.M. (2012) Land Zones of Queensland. Queensland Herbarium, Queensland Department of Science, Information Technology, Innovation and the Arts, Brisbane. 79 pp. Vipassana Centre Upgrade Pomona – Fauna and Flora Assessment 32
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APPENDIX A: DHAMMA RASMI MASTER PLAN - Revised
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Native Foresters APPENDIX B: OFFSET PLANTING SPECIES LIST Vipassana Centre Upgrade Pomona – Fauna and Flora Assessment 34
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Native Foresters
APPENDIX C: SIGNIFICANT TREES AND HABITAT FEATURES
Label Species Common Name dbh (mm) Feature/Note Action
A1 Eucalyptus microcorys Tallowwood 550 Peeling bark Retain – clear
undergrowth
A2 Corymbia intermedia Pink Bloodwood 600 Furrowed bark Retain
A3 Eucalyptus microcorys Tallowwood 600 Peeling bark Retain
A4 Eucalyptus microcorys Tallowwood 550-300 Peeling bark Retain
(double)
A5 Corymbia intermedia Pink Bloodwood 500 Hollows Retain
A6 Corymbia intermedia Pink Bloodwood 600 Furrowed bark Retain – clear
undergrowth
A7 Eucalyptus microcorys Tallowwood 500 Peeling bark Retain – clear
undergrowth
B1 Lophostemon confertus Brushbox 700 Peeling bark Remove with
spotter-catcher
B2 Acacia disparrima Hickory Wattle 500 Peeling bark Remove with
spotter-catcher
B3 Corymbia intermedia Pink Bloodwood 500 Furrowed bark Remove with
spotter-catcher
B4 Lophostemon confertus Brushbox 550 Hollow at base Remove with
spotter-catcher
B5 Corymbia intermedia Pink Bloodwood 600 Furrowed bark Remove with
spotter-catcher
B6 Lophostemon confertus Brushbox 550 Peeling bark Remove with
spotter-catcher
B7 Lophostemon confertus Brushbox 500 Peeling bark Remove with
spotter-catcher
B8 Corymbia intermedia Pink Bloodwood 550 Furrowed bark Remove with
spotter-catcher
B9 Corymbia intermedia Pink Bloodwood 600 Furrowed bark Retain – clear
undergrowth
C1 Corymbia intermedia Pink Bloodwood 500 Furrowed bark Retain
C2 Corymbia intermedia Pink Bloodwood 800 Furrowed bark Retain
C3 Corymbia intermedia Pink Bloodwood 550 Furrowed bark Retain
C4 Lophostemon confertus Brushbox 800 Peeling bark Retain
C5 Corymbia intermedia Pink Bloodwood 500 Furrowed bark Retain – clear
undergrowth
D1 Corymbia intermedia Pink Bloodwood 600 Forming riparian zone - Retain with
frog habitat undergrowth
D2 Corymbia intermedia Pink Bloodwood 550 Furrowed bark Remove with
spotter-catcher
D3 Syncarpia glomulifera Turpentine 500 Peeling bark Remove with
spotter-catcher
D4 Corymbia intermedia Pink Bloodwood 600 Furrowed bark Remove with
spotter-catcher
D5 Melaleuca saligna Willow Bottlebrush 500 Peeling bark Remove with
spotter-catcher
D6 Corymbia intermedia Pink Bloodwood 600 Furrowed bark Remove with
spotter-catcher
D7 Corymbia intermedia Pink Bloodwood 600 Multiple nests in Retain – adjust
canopy building layout
E1 Large Tree Stump – Retain in situ
Cultural Heritage
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Native Foresters
APPENDIX D: CERTIFICATION OF SUITABLY QUALIFIED
PERSON FOR FLORA SURVEY
Native Foresters flora surveys are undertaken by competent and trained personnel led by Dave Burrows.
Dave has over 20 years’ experience in conducting botanical surveys, including identification of EVNT
species and extensive knowledge of local ecosystems in the Gympie, Noosa and Sunshine Coast regions.
Dave has a Diploma in Horticulture, and Conservation and Land Management. Examples of botanical
surveys include:
▪ Flora and Fauna Assessment – Cooney Road, Bli Bli – Nambour Landfill Expansion (2015-2017)
▪ Flora and Fauna Assessment – Park Road, Noosa Boardwalk (2015)
▪ Flora and Fauna Assessment – Daintree Estate, Tewantin (2014)
Dave has also authored the following publications:
▪ “Vegetation of Noosa Shire, edition 2” – 2003, Noosa Shire Council planning scheme study
▪ Various Bushland Management Plans for Noosa Council conservation Reserves.
▪ “Seed production and litterfall in some Eucalyptus communities in Central Queensland” Australian
Journal of Botany, Vol 40, 1992.
▪ “Regeneration and survival of Desmanthus virgatus 78382 in grazed and ungrazed pastures”.
Tropical Grasslands. Vol 27, 1993.
Jacob Hazzard (BSc) also undertakes flora surveys as part of the Native Foresters flora survey team.
Jacob has been undertaking flora surveys, including EVNT species surveys for fourteen years, including:
▪ Flora and Fauna Assessment – Central Drive Sippy Downs (2018)
▪ Flora and Fauna Assessment – Bokarina-Buddina Coastal Pathway (2018)
▪ Flora and Fauna Assessment – Zgrajewski Road Upgrade Yandina Creek (2018)
▪ Flora and Fauna Assessment – Bribie Island National Park (2018)
▪ Flora Assessment – Bribe Island Community Arts Centre (2018)
▪ Flora and Fauna Assessment – Flaxton Mill Road Upgrade (2018)
▪ Flora and Fauna Assessment – Tin Can Bay Mens Shed (2017)
▪ Flora and Fauna Assessment – Moondara Drive, Bokarina Coastal Pathway (2014)
▪ Flora and Fauna Assessment – Cottonwood Street, Mudjimba (2014)
The following statement is provided in certification of the suitably qualified person who conducted the flora
survey.
I certify that :
(a) I have adhered to all statutory requirements and flora survey guideline requirements, and
(b) the flora survey report is an accurate and full account of the flora survey.
Name: Jacob Hazzard
Date: 12/04/2019
Vipassana Centre Upgrade Pomona – Fauna and Flora Assessment 36
Page 37
Native Foresters APPENDIX E: JUSTIFICATION OF SUITABLY QUALIFIED AND EXPERIENCED PERSON FOR FAUNA BREEDING PLACE SURVEY Native Foresters fauna surveys and breeding habitat assessments are coordinated and led by Tony Bright. Tony Bright is a native fauna and flora specialist with over 40 years’ experience in the field. He has spent ten years as a guide working in the Fraser Island region and 30 years doing field–based research in Australia and overseas. Tony is a professional wildlife keeper and a licensed Wildlife spotter catcher (Fauna rehabilitation permit holder) specialising in reptile, mammal and amphibian species. Tony Bright is assisted in the field by Jacob Hazzard. Vipassana Centre Upgrade Pomona – Fauna and Flora Assessment 37
Page 38
APPENDIX F: KOALA MAPPING
[OCR of page images]
APPENDIX F: KOALA MAPPING
Lot: 6 Pian:
RPBABAIA
Legend
(4) selected Lot and Pian
HB Koala habitat area (core)
Koala habitat area (locally refined)
Koala priority area
Cadastral Boundaries
Towns
Highway
Connector
Street/Local Road
Major riversicreeks
Queensland
|| Td |
‘The koala habitat mapping within South East
Queensland uses regional ecosystem linework
‘compiled at a scale varying from 1:25,000 to
1:100,000. Linework should be used as a guide
only. The positional accuracy of regional ecosystem
data mapped at a scale of 1:100,000 is +/- 100 metres.
© The State of Queensland, 2020
LOCALITY OwaRaM
Koala priority area and koala habitat area
Disciaimer:
While every care is taken to ensure the accuracy of this product
the Department of Environment and Science acting on behalf of
the State of Queensiand makes no representations or warrantes
‘about its accuracy, reliability, completeness or suitability for any
particular purpose and disclaims all responsibilty and all liability
{including without limitaton, labilty in negigence) for all expenses,
losses, damages (including indirect or onsequential damage) and
costs which you might incur as a result ofthe data being inaccurate
or incomplete in any way and for any reason. Due to varying sources
of data, spatial locations may not coincide when overiaid
The koala conservation plan maps will be updated at least annually
to include any koala habitat areas that have been made, amended
or revoked,
In order to ensure that the most recent map for an area of interest
can be accessed, prior to the annual update, a register of changes
made to koala habitat areas suit of the map amendment process
will be available at
hitps://environment.des.qid. gov awiwilalife/animals/iving-with/koalasimapping!
The register will include lot on plan for the change, the date the decision
was made and the map issued to the landholder which shows areas
determined to be koala habitat areas.
This product is projected into GDA 1994 MGA Zone 56
Page 39
APPENDIX G: VEGETATION CLEARING TABLE
Section Description Total Area
A) Northern Fire Remnant sclerophyll forest, native re-vegetation specimens, present in patches. Pink 500m2
Management Zone Bloodwood, Brushbox, Tallowwood dbh 200-500mm. Mid-stratum trees, shrubs,
(Inside Essential vines Alphitonia excelsa, Macaranga tanarius, Lophostemon suaveolons, Dodonea
Habitat Zone) triquetra, and Cissus hypoglauca. Native and non-native grasses and forbs in
understorey (Ottochloa sp, Oplismenus aemulus and Imperata cylindrica)
A) Northern Fire Remnant sclerophyll forest, native re-vegetation specimens, present in patches. Pink 500m2
Management Zone Bloodwood, Brushbox, Tallowwood dbh 200-500mm. Mid-stratum trees, shrubs,
(Outside Essential vines Alphitonia excelsa, Macaranga tanarius, Lophostemon suaveolons, Dodonea
Habitat Zone) triquetra, and Cissus hypoglauca. Native and non-native grasses and forbs in
understorey (Ottochloa sp, Oplismenus aemulus and Imperata cylindrica)
B) Northern Construction Remnant/regrowth sclerophyll forest, midstorey several native trees and shrubs 3880m2
Area Macaranga tanarius, Alphitonia excelsa and Petalostigma triquetra. Understorey of
native sedges Lomandra longifolia, Dianella caerulea.
C) Southern Fire Remnant/regrowth sclerophyll forest, tall Pink Bloodwood, Brushbox, dbh 200- 1100m2
Management Zone 800mm. Mid stratum smaller trees, shrubs and vines Alphitonia excelsa, Macaranga
tanarius, Lophostemon suaveolons, Pilidiostigma rhytispermum, Smilax australis.
Western end contains pond and riparian vegetative buffer dominated by a Melaleuca
saligna midstorey.
D) Southern Construction Remnant/regrowth sclerophyll forest, Pink Bloodwood, Turpentine dbh 200-600mm. 4380m2
Area Mid stratum smaller trees, shrubs and vines e.g. Alphitonia excelsa, Macaranga
tanarius, Lophostemon suaveolons, Pilidiostigma rhytispermum, and Smilax australis.
Native and some non-native grasses and forbs in understorey (e.g. Ottochloa sp,
Oplismenus aemulus and Imperata cylindrica, lawn grasses and weeds (e.g. Blue top,
Siratro).
TOTAL ESSENTIAL HABITAT VEGETATION CLEARING AREA: 500m2
Page 40