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Biosis Pty Ltd Melbourne Resource Group
38 Bertie Street Phone: 03 9646 9499 ACN 006 175 097 Port Melbourne VIC 3207 Fax: 03 9646 9242 ABN 65 006 175 097 Email: [email protected] biosis.com.au
21 December 2016
Belinda Smith Strategic Planning Manager Victorian Planning Authority Level 25, 35 Collins Street, Melbourne MELBOURNE VIC 3000 Email: [email protected]
Re: Berwick Health and Education Precinct – Native Vegetation Assessment (excluding Southern Drain)
Project no. 23541 Dear Belinda,
Biosis Pty Ltd. was commissioned by the Victorian Planning Authority (VPA) to provide advice on the extent and condition of native vegetation within the Berwick Health and Education Precinct (BHEP), Berwick (Figure 1). This assessment must be read in conjunction with Appendix 3 to this report, Berwick Health and Education Precinct- Vegetation assessment - Southern Drain (Biosis Letter Report, 05/05/2015).
Methods
The assessment was undertaken on 18 November 2016 and a list of plant species observed was collected (#U00J5ZR1). This list will be submitted to the Department of Environment, Land, Water and Planning (DELWP) for incorporation into the Victorian Biodiversity Atlas. Planted species have not been recorded unless they are naturalised.
Native vegetation is defined in the Victoria Planning Provisions as 'plants that are indigenous to Victoria, including trees, shrubs, herbs and grasses' (Clause 72).
The Guidelines classify native vegetation into two categories (DEPI 2013):
• A remnant patch of native vegetation (measured in hectares) is either:
– An area of native vegetation, with or without trees, where at least 25 percent of the totalperennial understorey cover is native plants.
– An area with three or more indigenous canopy trees where the tree canopy cover is at least20 percent.
Remnant patch vegetation is classified into ecological vegetation classes (EVCs). An EVC contains one or more floristic (plant) communities, and represents a grouping of broadly similar environments. Definitions of EVCs and benchmarks (condition against which vegetation quality at the site can be compared) are determined by DELWP.
• A scattered tree is defined as (extent measured by number of trees):
– An indigenous canopy tree that does not form part of a remnant patch of native vegetation.
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CASEYCITY
A rgu s C t
Duke
St
Beau
mont
Rd
Koorang P l
Dillya Ct
Wilona Way
Land
ra Ct
Cremona Pl
Central Tce
Denmark H ill Rd
Daventry Ct
San Rem o Ct
NandinaRd
Euroa
Av
Teesda le Ct
Oxfor
d Ct
Toptani Dr
Dianthus Ct
Mondous C t
Jim Ct
Duffy C t
St M arg arets Pl
Gumnut Ct
Hansford Ct
Che sil Ct
Bernl
y Bvd
Magarra Cr
Neill St
Michael Ct
Hesse
ll Rd
Reid M
ews
Selby
C t
Tor ino C l
Martin Ct
Garde
nia Ct
Hu d son St
Tum ut C t
Messm
ate C t
Wo od ru sh C t
W at so n G d n s
Kenny
Ct
Augustus Dr
Civic P
l
Federation Ct
Curring a C
l
Moon
beam
Cl
Yardley Ct
Song
St
Mill e
r St
Astrid Ct
Celeste Ct
Car te
r Dr
Kelso Pl
Hatten P l
Oakh
ill Ct
Gair C
l
Bushlark Ct
Marina Ct
Su m m er Ct
Burgundy Way
Meadow P l
Roxy C l
Sollya C t
GladeCt
Hall Ct
Am brose Ct
The Q
uadra
n t
Lords Rise
Albens C t
Stefan
Dr
Birch
Ct
S tringybark Ct
Julius
Ct
Armitage Dr
Spe n ce r C t
Melzak W ay
Eusto
n Ct
Oscar
Ct N yon Pl
Wa rne P l
Eucu
mben
e Dr
A lbrecht Av
Floret Pl
Lorikeet Dr
Ettr ick P l
Clyde
Rd
Gan aw ay D r
Bew ley W ay
Old Co
ach Rd
P inna ta Pl
Boyn
ton Pl
Imm y Pde
Centu
ry Rd
Basan
o Rtt
Derw
ent C
t
Ex ford P l
Argyle
Ct
Adare CtChong Ct
Deauville Ct
Gretel
Pl
Asco
t Rise
Per rott P l
Hilda
Ct
Lauder P l
Kim Cl
Sage
P l
Petre
l Pl
Sou th TcePri
m e C t
Mulga
Rise
The M ap les
Beldale Ct
Glove r C t
Gargeney Ct
Tarag
o Ct
Buffa
lo Ct
Jeune
Gr
Monterey Ct
Balwy
n Ct
Larne
C l
Tabak Ct
Gellib
ra nd C
t
Ting le
C l
Molon
ey C t
Aura r
ia Cl
Ellesse Way
Haym an St
Richardson G r
Winnie C t
Euca lpyt Ct
Sach
iko P l
The O
a ks
Strahan Cl
Elm Ct
D enison Ct
Rahn
i Cl
Norham Ct
Panmure Ct
East Tc
e
Cau lf
iel d
Ct
H illtop Cl
Madd
en Rt
t
Mess ina P l
Silver
Birch
Ct
Kona
c Ct
Turner St
Laven der P l
Holder P l
Clark Ct
Fern W
ay
H asken C t
Bund
oora
Ct
K ingsm ill Tce Jamie Mews
Walsh Rtt
Caled
onia
Ct
Shea
re r C t
Kuranda Cr
Angu
s Ct
Shute Av
Th irlm ere Ct
Lakew ood Pl
Dorian Cl
Sweeney Dr Church St
Salinger L ane
Denham Pl
Gra n d view Tce
Shannon Way
Penny LaneJar
rah Ct
Buttonwood Ct
Sue Pl
Rosem
ont D
r
Sturrock C t
Allira Cl
Clendon St
Pen d ula C t
South
gate D
rMc
ilwra i
th Ct
Barina Ct
Sha ne C t
Evergold C l
Kippenross Dr
Chin Ct
Nang
warry C
t
Paris h C t
Hyland C t
Linton
C t
To ttin gt o n R ise
Melaleuca Ct
Maralee Ct
Wilson St
Logan Pl
Dell St
Grenville Ct
Chiltern Ct
Cullen
Cl
Max Dr
Riverg
len Rd
Ke lly M ew s
Nadeen St
Grov
e Gdn
s
Sherbrooke Ct
Walton C tRols tone Ct
Coom a Ct
Bree Ct
Turella
C lFerny Ct
Dulka
ra Pl
Pad stow C t
N atren C t
Renwarl Cl
Ezard
Cl
Pagebrook Rd
Flo ren ce A v
Dunm
ore Pl
Avish
aWay
Fiddlers Grn
Wh itehall Ct
Tarran
gow e
r Pl
Toulou
se Tce
Malla
rd St
Rane
en Pl
Yem aya Pl
Ayr CtSte
phan
ie Cl
W ilm
ott C l
Princes HwyM a itla nd St
Barellan Mew s
Harley C t
Killarn
ey Ct
Hillbr
ick Ct
Ryda
ldene
Way
AprilCl
Tussock St
Wattle
bird C
t
Prestige P l
Jian n i W a y
Roxby CtSh
effield
Ct
Rad iata R ise
Las ian dra C ct
W im m eraCt
Culm
ara C t
B lu e Wr en
P l
O rch ard Sq
M agdalena P l
Bain St
Fantail Way
R e gin ald C l
Marida Ct
BoreeCt
The O val
Willun
ga C t
Coventry Rd
Weron
a Ct
Bishop Pl
St Jam es Ct
Ambleside Cr
W arrock C t
Vegas
Ct
Melba St
W hisken Way
Azure Pl
S t Joh ns C t
Avard
C t
Ro dlarni C r
Ashfo
rd Ct
Eglint
on Cl
Woodrow Ct
D alpura
CtDu
nnell
R ise
Cord
C l
Neilian Rtt
Lia A m ie P l
Aurea
Ct
Dylan
Ct
AttungaCt
Yarrow Ct
W arw ick C t
Kala s
taire
Gr
Kruger St
Bertr
and C
l
P lym tree C t
Harm
on
Cl
Higinb
otham
Rise
T ilba C
t
Cr ib b C ove
Golf Links Rd
M atho ura Ct
AlbertaWay
Brew ster St
Palmerston St
Rutla
nd Rd
V iewm ountCt
M an dura h Ch
Fairview AvHe
rald C
t
Maryn Cl
Millw
ood A
v
Sabre
Ct
Scanlan St
Crowle
y Av
The Elms
Keys Ct
Lexc
en Cl
Kerfer
d St
Q u e en s Ct
JackW illiam W ay
Selkir
k Ct
Carlu
ke C l
Tamara Cl
Jam ie son W ay
Sumner Ct
Slingsby Av
Fin do n W ay
Palmer D r
Bowen Ct
Sha mro ck Cl
Woo dley St
Valda ClAd a m s L an e
Lancaste r AvFie
ldhou
se Lan
e
View p
o int P
l
Graneel G r
Packard St
Gibb St
Glenn
E rin
W ay
Edw ardes StCan
ning D
r
Montham Cl
Hillview Pl
Els Ct
Ocon
nell S
t
M alla
igRis
e
Piccadilly Ct
High St
PenrithCt
Roundhay Ct
Balfo
u r C t
Sallyb
rook C
ct
Orsin
o Pl
Deakin Ct
Avendon Ct
Pione
er Ct
Wauchope Av
Verdun Dr
Buch
anan
Rd
Pendulum Pl
Highvale Cr
Haverbrack D r
Hazeldene Ct
Linco ln AvEm b lin g St
Clock tow er Ct
Braybrook Dr
Clove rfie ld C l
Russel Av
Marga
retS t
Hanle
y St
Panoramic Tce
Mcnabb
St
Gardiner St
The Espla na de
Whistler Dr
Ellen Rd
Tralee
C ct
Innes
Ct
Hedgeley Dr
Kallara Cr
Collins Cr
Coowarra Way
Cheviot AvPiermont Dr
Gran
thamCr
York Rd
Lodge Cr
Sing Cr
Willsl
ie
Cr
Gw endol ineDr
Royston Av
CambridgeDrWe
sley D
r
Sheldon Dr
Strathavan Dr
Marisa
C r
Hillgr
ove C r
Jo hn Fisher Dr
Lantan
a Dr
Rheanva St
Intrepid St
St IvesDr
Cherr
y Tree
Lane
The
Quays
Caserta Dr
Jinda
le eCt
Outlook Dr
Fiddlers
Grn
The SpringsCl
Evan S
t
Upton CrTyr
ell Pl
Southern Bvd
The
Prom
enad
e
Centre Rd
Earls fie ld Dr
Berw
ick
Springs Prom
Ashf
i eld
D rMi
chell
e Dr
Bournevale Dr
Streeton Way
Lyall Rd
County Dr
Clyde
Rd
Golf Links Rd
Vivienne Way
Melville
Park
Dr
Riviera
Dr
TheA
venu
e
Viewgrand Dr
Ardblair Tce
Kurra
jong
Rd
Fairholm e Bvd
Clyde
Rd
Kangan Dr
Avebury Dr
Hick
ory D
r
Inglis Rd
Bryn Mawr Bvd
Hark
away
Rd
Hillcrest Av
Peel St
SaxonwoodDr
Litt lecroft A v
Cresthaven Bvd
Edrington Park Dr
Homestead Rd
Glouc
ester
Av
The Gateway
Chirnside RdCypress Hill Dr
Kingsmere Dr
Manuka Rd
Ernst Wanke Rd
Buch
anan
Rd
Narre
War
ren N
orth
Rd
Reserve St
Greaves Rd
Oshea Rd
Soldi
ers R
d
Mansfield St
Bemersyde Dr
Moond
arra Dr
Ridge
m ont
D r
Fleetwood Dr
Willia
m Rd
Bellevue Dr
Marsh
Gr
DomainDrNorfolk Dr
Howell Dr
Telford Dr
Darling Way
Jerild
erie Dr
Skyli
ne W
ay
Shinners Av
Park
hill D
r
Heritage DrWood Rd
V ictor Cr Monash Fwy
Princes Hwy
High St
Princes Fwy
Hallam Main Drain
Berwick Town Drain
Grasmere Creek
Grasm
ere Cr
eek
Wilson Hill
Berwick Springs
Berwick
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M ildura
Kerang
Sw anHill
Ham ilton Ba llaratArarat
Warrn amb ool
Echuca
Be ndigo
Albu ryWangaratta
Tra ralgonM elbou rn e
GeelongLakesEntra nce
CannRive r
M ansfield
Acknowledgement: VicMap Data ©State of Victoria
Matter: 23541,Date: 13 D ecem ber 2016,Checked by: SN, Drawn by: AC, Last ed ited by: acurtisLocation:P:\23500s\23541\M apping\23541_Prop_F1_locality_autogen
LegendStudy area
Scale 1:25,000 @ A4, GDA 1994 MGA Zone 55
0 250 500 750 1,000
M etres ±Biosis P ty LtdBallarat, B risbane, Canberra , H obart, M elbourne, New castle, Sydney, W angaratta & W ollongong
Figure 1: Location of the study area - Berw ick,Victoria
CASEY CITY
Turel
laCl
Jane St
Collins Cr
Watso
n Gdn
s
Madd
en Rt
t
Cade
ll Pl
Stefan
Dr
Rodla
rni Cr
Glenisla Way
MelzakWay
Clyde
Rd
Ambleside Cr
Derw
ent C
t
Chong CtVe
nture
Dr
Demp
ster W
ay
Wind
emere
St
Craig
Dr
Sing Cr
Prime
Ct Gwendoline Dr
ChinCt
Cindy Ct
Daniher Cl
Golf Links RdMa
rgaret
St
Enterprise Av
Evan S
t
Intrepid StEls
CtOrsin
o Pl
Coun
ty Dr
Clyde
Rd
Clyde
Rd
Kangan Dr
Golf Links Rd
Belle
vue D
r
Princes Fwy
0 30 60 90 120 150
Metres
LegendSouthernDrain (Biosisletter report,05/05/2015)NativeVegetationAs s es s ment –Excludingsouthern drain(Biosis letterreport,21/12/2016)
±Biosis Pty LtdBallarat, Brisbane, Canberra, Hobart, Melbourne, Newcastle, Sydney, Wangaratta & Wollongong
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Mildura
KerangSwan Hill
Hamilton BallaratStawell
Warrnambool
BendigoWodonga
MorwellLakes Entrance
Mansfield
Scale: 1:6,000 @ A4
Fig 1B. Study arealocations within theBerwick Health andEducation Precinct
Coordinate System: GDA 1994 MGA Zone 55
Acknowledgements: Vicmap ©State of Victoria
Matter: 23541, Date: 13 February 2017, Checked by: SN,Drawn by: SSK, Last edited by: snerenbergLocation:P:\23500s\23541\Mapping\ 23541_F1B_StudyAreas
© Biosis 2015 – Leaders in Ecology and Heritage Consulting 4
A canopy tree is a mature tree that is greater than three metres in height and is normally found in the upper layer of a vegetation type. Ecological vegetation class descriptions provide a list of the typical canopy species. A condition score and extent is applied to each scattered tree based on information provided by DELWP's NVIM.
Species nomenclature for flora follows the Flora Information System (2016).
Results:
Vegetation of the study area is not mapped as native vegetation according to DELWP's mapping (see the 2005 EVC layer in the Biodiversity Interactive Map 3.2), with the original vegetation (pre 1750) identified as a mosaic of Plains Grassland (EVC 132) and Plains Grassy Woodland (EVC 55) with low lying areas supporting a mosaic of Swampy Riparian Woodland (EVC 83) and Swamp Scrub (EVC 53). Small remnants of this mosaic are identified by DELWP along the Princes Freeway at the southern boundary of the study area.
The pre-1750 vegetation of this site would have varied throughout the study area according to topography and soil type. Typically, woodland vegetation types would have had an open canopy of River Red-gum Eucalyptus camaldulensis or Swamp Gum Eucalyptus ovata and Narrow-leaf Peppermint Eucalyptus radiata. The understorey typically consisted of shrubs including Black Wattle Acacia mearnsii, Blackwood Acacia melanoxylon, Swamp Paperbark Melaleuca ericifolia and Black Sheoak Allocasuarina littoralis that overtop a species-rich grassy and herbaceous ground layer. Grassland areas would have been dominated by native perennial grasses such as Kangaroo Grass Themda triandra and Wallaby-grass Rytidosperma spp., interspersed with a diversity of herbs. Low-lying areas would have formed seasonal wetlands dominated by semi-aquatic herbaceous vegetation like sedges (Carex spp. ) and rushes (Juncus spp.).
The vegetation throughout the study area is highly modified from its original condition and degraded due to the extensive land clearing that has occurred within Berwick and its surrounds. Overall, the condition of the vegetation is poor due to a lack of canopy trees, loss of native species diversity, and the presence of a high cover of weeds, including a number of noxious weeds such as Blackberry Rubus anglocandicans and Gorse Ulex europaeus (Appendix 1). Most of the study area comprises lawn areas with planted amenity vegetation within the Monash campus and destocked paddocks adjacent to the campus supporting exotic pasture (e.g. Toowoomba Canary Grass Phalaris aquatic and Ryegrass Lolium rigidum) and weeds. Two constructed hydrological features are also included in the study area: an unnamed drainage line draining into the southern drain and a farm dam, which is currently fenced, with access provided by Monash security.
Notwithstanding the above, the site inspection confirms the presence of four patches of native vegetation as defined above. These are mapped in Figure 2a and 2b and described below. These are referred to as Habitat Zones (HZ) and they cover a total area of 0.93 ha. Outside of these patches, native vegetation persists as scattered understorey trees such as Silver Wattle Acacia dealbata and Blackwood and Black Wattle (Figure 2b).
• HZ1. Plains Grassland. These patches are near a sports field and around the dam. They contain no canopy species or shrubs but the perennial component of the ground-layer vegetation includes native grasses consistent with Plains Grassland (Weeping Grass Microlena stipoides, Wallaby-grass and Blown Grass Lachnogrostis filiformis) so has been assessed as a treeless vegetation type. The characteristic herbs of this EVC are no longer present but some native herbs such as Willow Herb Epilobium hirtigerum, Loosetrife Lythrum hyssopifolia, Crane's Bill Geranium sp. and Cotton Fireweed Senecio quadridentatus persist. Weed species typical for the EVC are also found throughout the patch including Cat's Ear Hypochoeris radicata, Toowoomba Canary Grass Phalaris aquatica, Spear Thistle Cirsium vulgare and Ribwort Plantago lanceolata.
© Biosis 2015 – Leaders in Ecology and Heritage Consulting 5
• HZ2. Plains Grassy Wetland. Habitat Zone 2 patch is a small constructed drainage channel that drains into the southern drain. The native vegetation of this patch was observed to largely consist of herbaceous semi-aquatic species including Knob sedge Carex inversa, rushes Juncus spp., Narrow-leaf Cumbungi Typha domingensis and Slender Knotweed Persicaria decipiens. Common Onion-orchid Microtis unifolia was also found. High weed cover was also present in the patch including Umbrella Sedge Cyperus eragrostis, Cocksfoot Dactylis glomerata, Toowoomba Canary Grass, Blue Pigroot Sisyrinchium iridifolium and Pampas Grass Cortaderia selloana. The vegetation was assessment as treeless vegetation and scattered wattles mapped near the patch were not included in the assessment.
• HZ3. Plains Grassy Woodland. Habitat Zone 3 is contiguous with the southern drain section previously assessed by Biosis but is separated from the drain by fencing. While none of the characteristic Plains Grassy Woodland canopy species were found in the patch, understorey trees such as Black Wattle and Blackwood and high native perennial ground-layer consistent with this EVC were still present. The quality of the ground-layer varied throughout the patch but in places was dominated by Spear Grass Austrostipa rudis with almost 100% cover. Other native perennial grass species observed were Kangaroo Grass, Weeping Grass and Common Tussock-grass Poa labillardieri. Some native herbs also persisted including Pale Flax-lily Dianella longifolia and Grassland Wood-sorrel Oxalis perennans. The ground-layer was degraded in places by the presence of noxious weeds such as Blackberry and Gorse and the invasion of pasture species from the adjoining paddock.
• HZ4. Plains Grassy Woodland. Habitat Zone 4 is formed by a mid-layer of Black Wattle consistent with remnants of a Plains Grassy Woodland understorey but the ground-layer and canopy trees of the EVC are no longer present. Instead, the ground-layer is mostly weed and pasture species and includes a high cover of noxious weeds (Blackberry and Gorse). These infestations smother other vegetation and prevent many other species from recolonising the site.
Enterprise Av
Ambleside Cr
H40.391ha
High St
Princes Hwy
Princes Fwy
2 3
1CASEY CITY
Berwick
Matter: 23541,Date: 13 February 2017,Checked by: SN, Drawn by: SSK, Last edited by: snerenbergLocation:\\biosisresearch.local\BIO-
Scale: 1:1,240 @ A3Coordinate System: GDA 1994 MGA Zone 55
Biosis Pty LtdBallarat, Brisbane, Canberra, Hobart, Melbourne,
Newcastle, Sydney, Wangaratta & Wollongong
Figure 2C.1: BerwickHealth and EducationPrecinct - Ecologicalfeatures of the study areas
0 10 20 30 40 50
Metres
LegendEVC
Plains Grassy Woodland
Acknowledgements: State Government of Victoria - VicMap - Nearmap
±
Chong Ct
Melzak Way
Sing C
r
Cindy Ct
Princes Fwy
HZ 1.30.01ha
HZ 1.20.018ha
HZ 1.20.018ha
HZ 3.10.023ha
20150.259ha 2015
0.007ha2015
0.007ha 20150.089ha
20150.071ha
High St
Princes Hwy
Princes Fwy
2 3
1CASEY CITY
Berwick
Matter: 23541,Date: 13 February 2017,Checked by: SN, Drawn by: SSK, Last edited by: snerenbergLocation:\\biosisresearch.local\BIO-
Scale: 1:1,240 @ A3Coordinate System: GDA 1994 MGA Zone 55
Biosis Pty LtdBallarat, Brisbane, Canberra, Hobart, Melbourne,
Newcastle, Sydney, Wangaratta & Wollongong
Figure 2C.2: BerwickHealth and EducationPrecinct - Ecologicalfeatures of the study areas
0 10 20 30 40 50
Metres
LegendEVC
Plains Grassy WoodlandPlains Grassland
Acknowledgements: State Government of Victoria - VicMap - Nearmap
±
Kangan Dr
Clyde
Rd
HZ 1.30.01ha
HZ 1.10.437ha
HZ 1.20.018ha
HZ 20.051ha
HZ 3.10.023ha
20150.259ha 2015
0.007ha2015
0.007ha2015
0.089ha2015
0.009ha
20150.012ha
20150.011ha
20150.007ha
20150.005ha
20150.005ha
20150.007ha
20150.019ha
20150.007ha
20150.011ha
High St
Princes Hwy
Princes Fwy
2 3
1CASEY CITY
Berwick
Matter: 23541,Date: 13 February 2017,Checked by: SN, Drawn by: SSK, Last edited by: snerenbergLocation:\\biosisresearch.local\BIO-
Scale: 1:1,240 @ A3Coordinate System: GDA 1994 MGA Zone 55
Biosis Pty LtdBallarat, Brisbane, Canberra, Hobart, Melbourne,
Newcastle, Sydney, Wangaratta & Wollongong
Figure 2C.3: BerwickHealth and EducationPrecinct - Ecologicalfeatures of the study areas
0 10 20 30 40 50
Metres
LegendEVC
Plains Grassy WoodlandPlains Grassy WetlandPlains Grassland
Acknowledgements: State Government of Victoria - VicMap - Nearmap
±
GF
GFGFGFGF
GF
GFGFGF
GF
GF
GF
GFGF
GF GF
GFGFGF
GFGF
GFGF
GFGF
GFGFGF
GFGFGF
High St
Princes Hwy
Princes Fwy
HighSt
CASEY CITY
Berwick
Matter: 23541,Date: 21 December 2016,Checked by: SN, Drawn by: LH, Last edited by: snerenbergLocation:\\biosisresearch.local\BIO-
Scale: 1:3,841 @ A3Coordinate System: GDA 1994 MGA Zone 55
Biosis Pty LtdBallarat, Brisbane, Canberra, Hobart, Melbourne,
Newcastle, Sydney, Wangaratta & Wollongong
Figure 2B: Berwick Healthand Education Precinct -Ecological features of thestudy area
0 30 60 90 120 150
Metres
LegendStudy Area
GF Scattered Understorey TreePlains Grassy WoodlandPlains Grassy WetlandPlains Grassland
Acknowledgements: State Government of Victoria - VicMap - Nearmap
±
© Biosis 2015 – Leaders in Ecology and Heritage Consulting 10
Condition and health of native vegetation
The extent of native vegetation patches was mapped within the study area (Figure 2) and the condition was assessed in relation to standard methods provided by DSE (2004). The condition of native vegetation was assessed using the DSE Vegetation Quality Assessment Sheet (DSE 2004) and pre-determined EVC benchmarks: http://www.dse.vic.gov.au/conservation-and-environment/ecological-vegetation-class-evc-benchmarks-by-bioregion. DELWP's Native Vegetation Information Management system was also used to determine vegetation extent and condition.
Native vegetation patches were assessed as remnants of the EVCs described above.
Habitat hectares
As noted above, for the purpose of determining vegetation condition, patches are termed ‘habitat zones’. Each EVC was assessed as a separate habitat zone. Some habitat zones consist of multiple patches of the same EVC with the same vegetation quality. Where there was a visually assessed difference in 2 or more habitat components, EVCs were divided into separate habitat zones as per DSE (2004). The condition score of the habitat zone is multiplied by the extent of the zone to give a value in Habitat hectares.
Scores allocated to each of the four habitat zones identified within the study area are outlined in Table 1. Total habitat hectares across all HZs is 0.148 as calculated below.
Table 1: Native vegetation Habitat hectares calculations for the BHEP (excluding Southern Drain)
Habitat Zone ID 1 2 3 4
EVC #: Name PG (132)
PGWet (125)
PGW (55)
PGW (55)
Max Score
Score Score Score Score Total
Site
Co
ndit
ion
Large Old Trees 10 NA NA 0 0 Canopy Cover 5 NA NA 0 0 Lack of Weeds 15 6 6 11 2 Understorey 25 5 15 15 5 Recruitment 10 3 0 3 1 Organic Matter 5 2 4 5 4 Logs 5 NA NA 0 0 Treeless standardiser 1.36 1.36 NA NA Total Site Score 22 34 34 12
Land
scap
e Va
lue
Patch Size 10 2 2 2 1 Neighbourhood 10 0 0 0 0 Distance to Core 5 1 1 1 1 Total Landscape Score 3 3 3 2
HABITAT SCORE 100 25 37 37 14 Habitat points = #/100 1 0.25 0.37 0.37 0.14 Habitat Zone area (ha) 0.465 0.051 0.023 0.391 0.93 Habitat Hectares (Hha) 0.115 0.019 0.009 0.055 0.148
Notes to table: NA = Not Applicable, PG = Plains Grassland, PGW = Plains Grassy Woodland, PGWet = Plains Grassy Wetland
© Biosis 2015 – Leaders in Ecology and Heritage Consulting 11
Vegetation Health
Native vegetation within the study area did not appear to be impacted by any obvious diseases or was otherwise impacted by any obvious insect attack which reduced or would otherwise lead to a conclusion that the vegetation present was in poor health. The two main wattle species present, Blackwood and Black Wattle, were present as a range of age cohorts and appeared to be present as naturally sustaining populations. Some scattered wattles appear to be reaching the end of their natural lifespans and are beginning to die off (senesce).
Implications of the Assessment
Any clearing of native vegetation within the study area may require a permit under the Planning and Environment Act 1987. Applications for the clearing of native vegetation are regulated under Victoria's Biodiversity Assessment Guidelines (DEPI 2013) (the Guidelines). DELWP classify most of the study area as Location A although parts of the study area boundary along Princes Freeway is identified as Location B and Location C.
If the study area is proposed to be impacted by development which would result in the clearing of native vegetation then it is likely that proposal would be assessed under the high risk pathway. This assessment includes relevant information for such an application.
Native vegetation patches are subject to offset requirements under a planning permit application, however, the total habitat hectares of the site is very low. Scattered understorey trees outside of patches would still be subject to a planning permit application should they need to be removed but offsets would not be required.
Conclusion We assessed four habitat zones to be patches of native vegetation as defined under Victoria's Biodiversity Assessment Guidelines. Remaining woody species that formed these remnants appeared to be healthy and were recruiting. The presence of noxious weeds, generally high weed cover and lack of canopy trees in treed EVCs reduced the condition of most of the native vegetation.
Outside of native patches, native vegetation was present only as scattered understorey trees in various stages from seedlings to aging. Remaining areas were paddocks and lawns of mostly introduced species.
The patches of native vegetation identified occupy a total of 0.93 ha. This native vegetation is considered to be degraded in condition and was assessed to have low habitat scores between 14/100 and 37/100. The vegetation therefore represents a total of 0.148 habitat hectares. NB. This is additional to the 0.13 ha identified in the previous report to make a total of 0.278 habitat hectares for the Berwick HEP.
Clearing of native vegetation patches and understorey trees would require a permit under the Planning and Environment Act and it is likely this application would be required to satisfy the information requirements defined under the high risk-based pathway defined by the Guidelines. This report provides the relevant data for any such application.
Please contact me on 8686 4833 or 0429 808 732 if you would like to discuss further. Yours sincerely ,
Steve Mueck Senior Consultant Botanist
© Biosis 2015 – Leaders in Ecology and Heritage Consulting 12
References DEPI 2013. Permitted clearing of native vegetation - Biodiversity assessment guidelines. Victorian Government Department of Environment and Primary Industries, Melbourne (September 2013).
DSE 2004. Native Vegetation: Sustaining a living landscape. Vegetation Quality Assessment Manual – Guidelines for applying the Habitat hectares scoring method. Version 1.3. Victorian Government Department of Sustainability & Environment, Melbourne.
© Biosis 2015 – Leaders in Ecology and Heritage Consulting 13
Appendix 1: Flora
Table A1.1. Flora species (35 native, 67 weeds) recorded from the study area.
Status Scientific Name Common Name Indigenous species
Acacia dealbata Silver Wattle
P Acacia mearnsii Black Wattle
Acacia melanoxylon Blackwood
Alisma plantago-aquatica Water Plantain
Austrostipa rudis Veined Spear-grass
Carex inversa Knob Sedge
P Cassinia arcuata Drooping Cassinia
P Cotula australis Common Cotula
Cynodon dactylon Couch
Dianella longifolia s.l. Pale Flax-lily
Eleocharis acuta Common Spike-sedge
Epilobium hirtigerum Hairy Willow-herb
Gahnia spp. Saw Sedge
Geranium spp. Crane's Bill
Isolepis hookeriana Grassy Club-sedge
Juncus bufonius Toad Rush
Juncus sp. (subgenus Genuini) Rush
Lachnagrostis filiformis s.l. Common Blown-grass
Lemna spp. Duckweed
Lomandra longifolia Spiny-headed Mat-rush
Lythrum hyssopifolia Small Loosestrife
Melaleuca ericifolia Swamp Paperbark
Microlaena stipoides var. stipoides Weeping Grass
P Microtis unifolia Common Onion-orchid
Oxalis perennans Grassland Wood-sorrel
Persicaria decipiens Slender Knotweed
Poa labillardierei Common Tussock-grass
Rumex brownii Slender Dock
Rytidosperma pallidum Silvertop Wallaby-grass
Rytidosperma spp. Wallaby Grass
Schoenus apogon Common Bog-sedge
P Senecio quadridentatus Cotton Fireweed
Solanum aviculare Kangaroo Apple
Themeda triandra Kangaroo Grass
Typha domingensis Narrow-leaf Cumbungi
Introduced species
Acetosella vulgaris Sheep Sorrel
Agrostis capillaris Brown-top Bent
© Biosis 2015 – Leaders in Ecology and Heritage Consulting 14
Anthoxanthum odoratum Sweet Vernal-grass
Arctotheca calendula Cape Weed
Aster subulatus Aster-weed
Avena fatua Wild Oat
Bellis perennis English Daisy
Brassica rapa White Turnip
Briza minor Lesser Quaking-grass
Bromus catharticus Prairie Grass
Bromus diandrus Great Brome
Bromus hordeaceus subsp. hordeaceus Soft Brome
Cenchrus clandestinus Kikuyu
Cerastium glomeratum s.l. Common Mouse-ear Chickweed
RC Cirsium vulgare Spear Thistle
Conyza bonariensis Flaxleaf Fleabane
Cortaderia selloana Pampas Grass
RC Crataegus monogyna Hawthorn
Cyperus eragrostis Drain Flat-sedge
Dactylis glomerata Cocksfoot
Daucus carota Carrot
RC Echium plantagineum Paterson's Curse
Ehrharta erecta var. erecta Panic Veldt-grass
Ehrharta longiflora Annual Veldt-grass
Erica lusitanica Spanish Heath
Festuca arundinacea Tall Fescue
Fumaria muralis subsp. muralis Wall Fumitory
Galium aparine Cleavers
Helminthotheca echioides Ox-tongue
Holcus lanatus Yorkshire Fog
Hypochaeris radicata Flatweed
Isolepis levynsiana Tiny Flat-sedge
Lactuca serriola Prickly Lettuce
Lolium perenne Perennial Rye-grass
Lolium rigidum Wimmera Rye-grass
Lotus spp. Trefoil
Lysimachia arvensis Pimpernel
Malva parviflora Small-flower Mallow
Modiola caroliniana Red-flower Mallow
Paspalum dilatatum Paspalum
Pentameris airoides subsp. airoides False Hair-grass
Phalaris aquatica Toowoomba Canary-grass
Plantago coronopus Buck's-horn Plantain
Plantago lanceolata Ribwort
Poa annua Annual Meadow-grass
Polygonum aviculare s.l. Prostrate Knotweed
Polypogon monspeliensis Annual Beard-grass
© Biosis 2015 – Leaders in Ecology and Heritage Consulting 15
Prunus cerasifera Cherry Plum
Ranunculus spp. Buttercup
Romulea rosea Onion Grass
Rubus anglocandicans Common Blackberry
Rumex conglomeratus Clustered Dock
Rumex crispus Curled Dock
Sisyrinchium iridifolium Striped Rush-leaf
Solanum nigrum Black Nightshade
Sonchus asper Rough Sow-thistle
Sonchus oleraceus Common Sow-thistle
Sporobolus africanus Rat-tail Grass
Taraxacum officinale spp. agg. Garden Dandelion
Tragopogon porrifolius subsp. porrifolius Salsify
Trifolium campestre var. campestre Hop Clover
Trifolium repens var. repens White Clover
Trifolium subterraneum Subterranean Clover
RC Ulex europaeus Gorse
Vicia sativa Common Vetch
Vicia spp. Vetch
Vulpia bromoides Squirrel-tail Fescue
© Biosis 2015 – Leaders in Ecology and Heritage Consulting 16
Appendix 2: Photos of vegetation within the BHEP
Plate 1: Scattered understorey trees outside of defined native vegetation patches. Some appear to be in good health and flowering (top) while others appear to be in decline (bottom).
© Biosis 2015 – Leaders in Ecology and Heritage Consulting 17
Plate 2: Habitat Zone 1: Mown native grass at edge of drains containing Weeping Grass Microlena stipoides and Wallaby Grass Rytidosperma spp. (top) and dam banks colonized by native herbs and grasses (bottom)
© Biosis 2015 – Leaders in Ecology and Heritage Consulting 18
Plate 3: Habitat Zone 2: drain dominated by native rushes and sedges but with weeds also present
© Biosis 2015 – Leaders in Ecology and Heritage Consulting 19
Plate 4: Habitat Zone 3: native grasses along boundary of southern drain with native understorey trees
© Biosis 2015 – Leaders in Ecology and Heritage Consulting 20
Plate 5: Habitat Zone 4: native understorey trees with weedy ground-layer, including Blackberry infestation (bottom)
© Biosis 2015 – Leaders in Ecology and Heritage Consulting 21
Plate 6: Most of the study area is made up of paddocks with introduced pasture species and weeds (top) or lawn and weedy areas within the campus (bottom).
© Biosis 2015 – Leaders in Ecology and Heritage Consulting 22
Appendix 3: Berwick Health and Education Precinct - Vegetation Assessment - Southern Drain
Biosis Pty Ltd
Melbourne Resource Group
38 Bertie Street Phone: 03 9646 9499 ACN 006 175 097
Port Melbourne VIC 3207 Fax: 03 9646 9242 ABN 65 006 175 097 Email: [email protected] biosis.com.au
05 May 2015
Anna Batters
Senior Precinct Structure Planner
Metropolitan Planning Authority
Level 25, 35 Collins Street, Melbourne
MELBOURNE VIC 3000
Email: [email protected]
Re: Berwick Health and Education Precinct- Vegetation assessment - Southern Drain Our Ref job # 19994
Dear Anna,
Biosis Pty Ltd. was commissioned by the Metropolitan Planning Authority to undertake a survey of the
health and condition of the vegetation in the drainage line in the southern section of the Berwick Health and
Education Precinct, 100 Clyde Road, Berwick (Figure 1).
Methods
The survey was undertaken on 24 April 2015 and a list of plant species observed was collected (#T25562).
This list will be submitted to the Department of Environment, Land, Water and Planning (DELWP) for
incorporation into the Victorian Biodiversity Atlas. Planted species have not been recorded unless they are
naturalised.
Native vegetation is defined in the Victoria Planning Provisions as 'plants that are indigenous to Victoria,
including trees, shrubs, herbs and grasses' (Clause 72).
The Guidelines classify native vegetation into two categories (DEPI 2013):
A remnant patch of native vegetation (measured in hectares) is either:
– An area of native vegetation, with or without trees, where at least 25 percent of the total
perennial understorey cover is native plants.
– An area with three or more indigenous canopy trees where the tree canopy cover is at least
20 percent.
Remnant patch vegetation is classified into ecological vegetation classes (EVCs). An EVC contains one or
more floristic (plant) communities, and represents a grouping of broadly similar environments. Definitions
of EVCs and benchmarks (condition against which vegetation quality at the site can be compared) are
determined by DELWP.
A scattered tree is defined as (extent measured by number of trees):
– An indigenous canopy tree that does not form part of a remnant patch of native vegetation.
!
CASEYCASEYCITYCITY
Daniher Cl
Berw
ickBra
eDr
Wilona Way
Jane St
Rutland Rd
Miller St
John B
arr Ct
Kelso Pl
Gair C
l
Summer Ct
Lauder Pl
Peel St
Broxbu
rn Ct
Stefan
Dr
Julius
Ct
Anne StEnmore Cl
Clyde
Rd
Lily Vale Cl
High St
Derw
ent C
t
Chong Ct
Ventur
e Dr
MilparinkaWay
Prime Ct
Whee
ler St Cam
eroun Ct
Chin Ct
Jancol
Ct
Patric
ia Ct
Church
StRichardson Gr
NorhamCt
Fiddlers Grn
Malanda Ct
Ryan C
t
Shute A
v
Sing Cr
Thirlmere Ct
Greenlaw Cr
Linton
Ct
Siand
ra Pl
Tottington Rise
Wilson St
Salisb
ury Ct
Marygat
e Pl
Renwarl Cl
Princes Hwy
Yemaya Pl
Ayr Ct
Wind
emere
St
Paternoster Lane
Hollydale Cl
Audrey Lane
Fyffe St
Kramer Dr
Jomary
Ct
Scanlan St
Bain St
Astrid
Ct
Ambleside Cr
Warrock Ct
Hillview Pl
Hancock Dr
Normanton Pl
Biralee Ct
Palmerston St
Golf Links Rd
Enterprise Av
Vista Ct
Andval Ct
Queens Ct
Adams Lane
Murndal Ct
Gibb St
Escott Gr
Edwardes S
tCa
nning
Dr
Roundhay
Ct
Russe
l Av
Marga
ret St
Langmore Lane
Mcnabb St
Quarry Hills
Dr
Lodg
eCr
Cheviot Av
Newm
anCt
Granth
am Cr
York Rd
Gwendoline Dr
Cindy Ct
Cord Cl
Maso
n Way
Melzak Way
John
Fishe
rDr
Outlook Dr
Millw
ood A
v
Greyst
oke Ct
Rheanva St
Intrepid St
Penrith Ct
Sherm
an
Ct
Fiddlers
Grn
Evan S
t
Edrington Park Dr
Mansfield St
Golf Links Rd
Clyde
Rd
Clyde
Rd
Melville Park Dr
Clyde
Rd
Brisbane St
Fairholme Bvd
Kangan Dr
Harkaway Rd
Peel St
Glouc
ester
Av
Lyall R
d
Reserve St
Coun
ty Dr
High St
Princes Hwy
Princes Fwy
Berwick
!
!
!
!
!
!
Melbourne
Dandenong
RingwoodLilydale
Pakenham
Acknowledgement: VicMap Data Copyright © The State of Victoria, Department of Environment and Primary Industries 2014
Matter: 19994,Date: 29 April 2015,Checked by: SGM, Drawn by: LDM, Last edited by: lmilneLocation:P:\19900s\19994\Mapping\
LegendStudy areaLocal government boundary
Scale 1:10,000 @ A4, GDA 1994 MGA Zone 55
0 100 200 300 400
Metres ±Biosis Pty LtdBallarat, Brisbane, Canberra, Melbourne, Sydney, Wangaratta & Wollongong
Figure 1: Location of the Study Area - Berwick, Victoria
© Biosis 2015 – Leaders in Ecology and Heritage Consulting 3
A canopy tree is a mature tree that is greater than three metres in height and is normally found in the upper
layer of a vegetation type. Ecological vegetation class descriptions provide a list of the typical canopy
species. A condition score and extent is applied to each scattered tree based on information provided by
DELWP's NVIM.
Species nomenclature for flora follows the Flora Information System (FIS 2014 edition).
Results:
Vegetation along the southern drain is not mapped (2005 EVC layer) as native vegetation according to
DELWP mapping (see Biodiversity Interactive Map 3.2), with the original vegetation (pre 1750) identified as a
mosaic of Plains Grassland (EVC 132) and Plains Grassy Woodland (EVC 55). Small remnants of this mosaic
are identified by DELWP along the Princes Freeway in close proximity to the drain.
The pre-1750 vegetation of this site is described as an open eucalypt woodland with a canopy of River Red-
gum Eucalyptus camaldulensis and Gippsland Red-gum Eucalyptus tereticornis. The understorey typically
consists of shrubs including Black wattle Acacia mearnsii, Blackwood Acacia melanoxylon and Black Sheoak
Allocasuarina littoralis that overtop a species-rich grassy and herbaceous ground layer.
The vegetation along the drain is highly modified and degraded due to the extensive land clearing that has
occurred within Berwick and surrounds. The drain itself is not a natural drainage line but an engineered
feature that drains directly into the Berwick town drain to the west of the study area.
Overall, the condition of the vegetation along the drain is poor with a high cover of a number of noxious
weeds (Appendix 1). Infestations of Blackberry Rubus fruticosus spp. agg, Wandering Jew Tradescantia
fluminensis and Flax-leaf Broom Genista linifolia are extensive (Plates 1, 2 & 3). These infestations smother
other vegetation and prevent many other species from recolonising the site.
Notwithstanding the above, the site inspection confirms the presence of small remnant patches of native
vegetation along the drain (Figure 2). This includes areas dominated by shrubs and understorey trees such
as Blackwood Acacia melanoxylon and Black Wattle Acacia mearnsii, narrow bands of aquatic species such as
Narrow-leaf Cumbungi Typha domingensis and Slender Knotweed Persicaria decipiens and small patches of
indigenous grasses including Veined Spear-grass Austrostipa rudis, Kangaroo Grass Themeda triandra,
Weeping Grass Microlaena stipoides, Mat Grass Hemarthria uncinata and wallaby-grass species Rytidosperma
spp as well as other herbs.
The vegetation along the slopes of the drain is devoid of any native eucalypts that would normally
characterise areas of Plains Grassy Woodland. Rather, the remnant patches of native vegetation are
formed by the presence of understorey trees including Blackwood and Black wattle (Plate 4). Scattered
occurrences of other shrubs included Hedge wattle Acacia paradoxa, Prickly Tea-tree Leptospermum
continentale and Drooping Cassinia Cassinia arcuata. Indigenous groundcover species occur as scattered
individuals or small species poor patches.
The eastern end of the study area lacks a native ground layer and is dominated by weedy pasture grasses
such as Couch Cynodon dactylon var. dactylon and Kikuyu Cenchrus clandestinus (Plate 5). However, a small
remnant native grassland is present along the northern bank at the western end of the study an area. This
grassland is dominated by Kangaroo Grass and Veined Spear-grass Austrostipa rudis subsp. rudis (Plate 6).
Isolated occurrences of herbaceous species that characterise Plains Grassland are also recorded. These
include Sheep's Burr Acaena echinata, Pale Flax-lily Dianella longifolia, Kidney Weed Dichondra repens and
fireweeds Senecio spp.
Scale: 1:800 @ A4
Figure 2.1: Ecologicalfeatures of the study area
Coordinate System: GDA 1994 MGA Zone 55
Matter: 19994, Date: 29 April 2015, Checked by: SGM,Drawn by: LDM, Last edited by: lmilneLocation:P:\19900s\19994\Mapping\19994_F2_EcoFeatures_A4
GF
GF GF
Princes Fwy
HZ1.10.259ha
HZ1.150.071ha
Biosis Pty LtdBallarat, Brisbane, Canberra, Melbourne,
Newcastle, Sydney, Wangaratta & Wollongong
±
0 5 10 15 20 25
Metres
21 3
LegendGF Scattered tree
Study area
Native vegetation
Scale: 1:800 @ A4
Figure 2.2: Ecologicalfeatures of the study area
Coordinate System: GDA 1994 MGA Zone 55
Matter: 19994, Date: 29 April 2015, Checked by: SGM,Drawn by: LDM, Last edited by: lmilneLocation:P:\19900s\19994\Mapping\19994_F2_EcoFeatures_A4
HZ1.40.089ha
HZ1.50.009ha
HZ1.10.259ha
HZ1.20.007ha HZ1.3
0.007ha
HZ1.60.012ha
Biosis Pty LtdBallarat, Brisbane, Canberra, Melbourne,
Newcastle, Sydney, Wangaratta & Wollongong
±
0 5 10 15 20 25
Metres
21 3
LegendGF Scattered tree
Study area
Native vegetation
Scale: 1:800 @ A4
Figure 2.3: Ecologicalfeatures of the study area
Coordinate System: GDA 1994 MGA Zone 55
Matter: 19994, Date: 29 April 2015, Checked by: SGM,Drawn by: LDM, Last edited by: lmilneLocation:P:\19900s\19994\Mapping\19994_F2_EcoFeatures_A4
Clyde
Rd
HZ1.140.011ha
HZ1.120.019ha
HZ1.130.007ha
HZ1.100.005ha
HZ1.90.005ha
HZ1.60.012ha HZ1.11
0.007ha
HZ1.70.011ha
HZ1.80.007ha
Biosis Pty LtdBallarat, Brisbane, Canberra, Melbourne,
Newcastle, Sydney, Wangaratta & Wollongong
±
0 5 10 15 20 25
Metres
21 3
LegendGF Scattered tree
Study area
Native vegetation
© Biosis 2015 – Leaders in Ecology and Heritage Consulting 7
The drainage channel and association wetted perimeter also supported patches of native species (Plate 7).
Patches of Slender Knotweed Persicaria decipiens, Narrow-leaf Cumbungi Typha domingensis and Common
Spike-sedge Eleocharis acuta were located along the drain and extended onto the bank. Isolated herbs in
these wetter areas include Shrubby Fireweed Senecio minimus and Crane's Bill Geranium sp. 14 (Plate 8).
These areas were incorporated into patches of vegetation identified as remnants of Plains Grassy Woodland
as the cover of these wetland plants was typically overshadowed by wattles.
Condition and health of native vegetation
The extent of native vegetation patches was mapped within the study area (Figure 2) and the condition was
assessed in relation to standard methods provided by DSE (2004). The condition of native vegetation was
assessed using the DSE Vegetation Quality Assessment Sheet (DSE 2004) and pre-determined EVC
benchmarks: http://www.dse.vic.gov.au/conservation-and-environment/ecological-vegetation-class-evc-
benchmarks-by-bioregion. DELWP's Native Vegetation Information Management system was also used to
determine vegetation extent and condition.
All native vegetation patches were assessed as remnants of Plains Grassy Woodland.
Habitat hectares
Patches are termed ‘habitat zones’. Due to the relatively degraded nature of the native vegetation present
all patches of native vegetation were identified as a single habitat zone. The condition score of the habitat
zone is multiplied by the extent of the zone to give a value in Habitat hectares.
Scores allocated to the habitat zone identified within the study area are outlined in Table 1.
Table 1: Habitat hectares of native vegetation within the study area
Site ID 1
Habitat Zone ID A
EVC #: Name 55 Plains Grassy Woodland
Max Score Score
Sit
e
Co
nd
itio
n
Large Old Trees 10 0
Canopy Cover 5 0
Lack of Weeds 15 4
Understorey 25 10
Recruitment 10 6
Organic Matter 5 2
Logs 5 0
Total Site Score 22
La
nd
sca
pe
Va
lue
Patch Size 10 1
Neighbourhood 10 0
Distance to Core 5 1
Total Landscape Score 2
HABITAT SCORE 100 24
Habitat points = #/100 1 0.24
Habitat Zone area (ha) 0.526
Habitat hectares (Hha) 0.13
© Biosis 2015 – Leaders in Ecology and Heritage Consulting 8
Vegetation Health
Native vegetation within the study area did not appear to be impacted by any obvious diseases or was
otherwise impacted by any obvious insect attack which reduced or would otherwise lead to a conclusion
that the vegetation present was in poor health. The two main wattle species present, Blackwood and Black
Wattle, were present as a range of age cohorts and appeared to be present as a naturally sustaining
population (Plates 1, 4, 5 & 6).
Implications of the Assessment
Any clearing of native vegetation within the study area may require a permit under the Planning and
Environment Act 1988. Applications for the clearing of native vegetation are regulated under Victoria's
Biodiversity Assessment Guidelines (DEPI 2013) (the Guidelines). DELWP classify most of the study area as
Location A although the western end of the drain is identified as Location C.
If the study area is proposed to be impacted by development which would result in the clearing of native
vegetation then it is likely that proposal would be assessed under the high risk pathway. This assessment
includes relevant information for such an application.
Conclusion
The study area supports patches of native vegetation as defined under Victoria's Biodiversity Assessment
Guidelines. Many of the species which formed these remnants appeared to be healthy and were actively
recruiting.
The patches of native vegetation identified occupy a total of 0.526 ha. This native vegetation is considered
to be degraded in condition and was assessed to have a relatively low habitat score (24/100). The
vegetation therefore represents a total of 0.13 habitat hectares.
Clearing of this vegetation would require a permit under the Planning and Environment Act and would likely
be required to satisfy the information requirements defined under the high risk-based pathway defined by
the Guidelines. This report provided the relevant data for any such application.
Please contact me on 8686 4833 if you would like to discuss further.
Yours sincerely
Steve Mueck
Senior Consultant Botanist
0429 808 732
References
DEPI 2013. Permitted clearing of native vegetation - Biodiversity assessment guidelines. Victorian Government
Department of Environment and Primary Industries, Melbourne (September 2013).
© Biosis 2015 – Leaders in Ecology and Heritage Consulting 9
Appendix 1: Flora
Table A1.1. Flora species (32 native, 54 weeds) recorded from the study area.
Status Scientific name Common name
Indigenous Species
Acacia mearnsii Black Wattle
Acacia melanoxylon Blackwood
Acacia paradoxa Hedge Wattle
Acaena echinata Sheep's Burr
Acaena novae-zelandiae Bidgee-widgee
Amyema pendula Drooping Mistletoe
Austrostipa rudis subsp. rudis Veined Spear-grass
Carex inversa Knob Sedge
Cassinia arcuata Drooping Cassinia
Dianella longifolia Pale Flax-lily
Dichondra repens Kidney-weed
Einadia nutans Nodding Saltbush
Eleocharis acuta Common Spike-sedge
Epilobium hirtigerum Hairy Willow-herb
Geranium spp. (?sp. 14, L. Tozer pers. comm.) Valley Crane's Bill
Hemarthria uncinata var. uncinata Mat Grass
Juncus spp. Rush
Leptospermum continentale Prickly Tea-tree
Lomandra filiformis subsp. filiformis Wattle Mat-rush
Lomandra longifolia Spiny-headed Mat-rush
Melaleuca ericifolia Swamp Paperbark
Microlaena stipoides var. stipoides Weeping Grass
Oxalis perennans Grassland Wood-sorrel
Persicaria decipiens Slender Knotweed
Poa labillardierei Common Tussock-grass
Rytidosperma caespitosum Common Wallaby-grass
© Biosis 2015 – Leaders in Ecology and Heritage Consulting 10
Status Scientific name Common name
Rytidosperma semiannulare Wetland Wallaby-grass
Senecio minimus Shrubby Fireweed
Senecio quadridentatus Cotton Fireweed
Themeda triandra Kangaroo Grass
Tricoryne elatior Yellow Rush-lily
Typha domingensis Narrow-leaf Cumbungi
Exotic Species
Acacia iteaphylla Flinders Range Wattle
Agrostis capillaris Brown-top Bent
RR Allium triquetrum Angled Onion
Anthoxanthum odoratum Sweet Vernal-grass
RR Asparagus asparagoides Bridal Creeper
Aster subulatus Aster-weed
Brassica rapa White Turnip
Bromus catharticus Prairie Grass
Bromus hordeaceus subsp. hordeaceus Soft Brome
Callitriche stagnalis Common Water-starwort
Cenchrus clandestinus Kikuyu
Centaurium tenuiflorum Slender Centaury
RC Cirsium vulgare Spear Thistle
Conyza bonariensis Flaxleaf Fleabane
Cortaderia selloana Pampas Grass
RC Crataegus monogyna Hawthorn
Cynodon dactylon var. dactylon Couch
Cyperus eragrostis Drain Flat-sedge
Dactylis glomerata Cocksfoot
Daucus carota Carrot
Ehrharta erecta var. erecta Panic Veldt-grass
Erica lusitanica Spanish Heath
Erigeron karvinskianus Seaside Daisy
Euryops abrotanifolius Winter Euryops
© Biosis 2015 – Leaders in Ecology and Heritage Consulting 11
Status Scientific name Common name
Fraxinus angustifolia Desert Ash
Fumaria spp. Fumitory
Galium aparine Cleavers
Gamochaeta purpurea s.s. Spiked Cudweed
RC Genista linifolia Flax-leaf Broom
Helminthotheca echioides Ox-tongue
Holcus lanatus Yorkshire Fog
Hypochaeris radicata Flatweed
Lonicera japonica Japanese Honeysuckle
Malus spp. Apple
Nasturtium officinale Watercress
Paspalum dilatatum Paspalum
Phalaris aquatica Toowoomba Canary-grass
Pinus radiata Radiata Pine
Plantago lanceolata Ribwort
Prunella vulgaris Self-heal
Prunus cerasifera Cherry Plum
Romulea rosea Onion Grass
RC Rubus fruticosus spp. agg. Blackberry
Rumex conglomeratus Clustered Dock
Rumex crispus Curled Dock
RR Salix spp. Willow
Solanum nigrum s.s. Black Nightshade
Sonchus asper s.s. Rough Sow-thistle
Sporobolus africanus Rat-tail Grass
Stenotaphrum secundatum Buffalo Grass
Tradescantia fluminensis Wandering Jew
RC Ulex europaeus Gorse
Vicia sativa subsp. sativa Common Vetch
Viola odorata Common Violet
© Biosis 2015 – Leaders in Ecology and Heritage Consulting 12
Appendix 2: Photos of vegetation along the Clyde Road drain
Plate 1: A Blackberry infestation along the banks of the drain
Plate 2: A Blackberry infestation along the drain with an introduced wattle flowering in the foreground.
© Biosis 2015 – Leaders in Ecology and Heritage Consulting 13
Plate 3: An area of Blackberry infestation with Flax-leaf Broom and Desert Ash
Plate 4: Blackwoods along the banks of the drain determine the extent of Plains Grassy Woodland.
© Biosis 2015 – Leaders in Ecology and Heritage Consulting 14
Plate 5: Mown pasture grasses flanking the boundary of the Clyde road drain.
Plate 6: Native grassland at the western end of the study area containing Kangaroo Grass and
Veined Spear-grass.
© Biosis 2015 – Leaders in Ecology and Heritage Consulting 15
Plate 7: A patch of native vegetation within the drain containing Narrow-leaf Cumbungi and
Slender Knotweed.
Plate 8: The banks of the drain support scattered native herbs such as Geranium sp. 14.