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NSW National Parks & Wildlife Service − 1:25 000 Map Series − Map 9 of 16
NSW National Parks & Wildlife Service − 1:25 000 Map Series − Map 9 of 16N
ativ
e V
eget
atio
n of
the
Cum
berla
nd P
lain
, Wes
tern
Syd
ney
Nat
ive
Veg
etat
ion
of th
e C
umbe
rland
Pla
in, W
este
rn S
ydne
y
Map Date: October 2002Map Produced by Spatial Vision
Parramatta
Ryde
Hunters Hill
ConcordAuburn
Strathfield
Hargrave Park
BLACKTOWN LGA
BAULKHAM HILLS LGA HORNSBY LGA KU-RING-GAI LGA
RYDE LGA
PARRAMATTA LGA
HOLROYD LGA
WILLOUGHBY LGA
LANE COVE LGA
HUNTERS HILL LGA
AUBURN LGA
CANADA BAY LGA
FAIRFIELD LGA
STRATHFIELD LGA LEICHHARDT LGA
BANKSTOWN LGA
BURWOOD LGA
ASHFIELD LGA
MARRICKVILLE LGA
CANTERBURY LGALIVERPOOL LGA
Lane Cove NP
Lane Cove NP
Wallumatta NR
Parramatta RP
Silverwater NR
Parramatta River RP
PARRA
MATTA
RIVER
BEECROFT RD
BLAC
KT
OW
NR
D
BLAXLAND RD
BLAXLANDRD
BOO
REA
OLYM
PICD
R
BRUNKER RD
ATTA RD
CABRAMATTARD
EAST
CARLINGFORD RD
CEN
TENA
RY D
R
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CH
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CHURCHST
CO
NC
ORD
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CO
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DE
CU
MB
ERLA
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CU
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CUM BERLAND HWY
DELHI RD
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NST
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GR
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US
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T
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MAIN ST
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WESTERN MWY
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WESTERN MWY
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GREAT WESTERN HWY
HUME HWY
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073 083 093 103 113 123 133 143 153 163 173 183 193 203 213 223 233 243 253 263 273 283 293
07 E3 000m 083 093 103 113 123 133 143 153 163 173 183 193 203 213 223 233 243 253 263 273 283 293
45
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+ LAT. / LONG. OFMAP SHEET CORNER
+ LAT. / LONG. OF THEMAP SHEET CORNER
MAP SHEET CORNER+ LAT. / LONG. OF
MAP SHEET CORNER+ LAT. / LONG. OF THE
LATITUDE -33 55 24LONGITUDE 150 54 19
LATITUDE -33 55 39LONGITUDE 151 9 34
LATITUDE -33 45 0LONGITUDE 150 54 34
LATITUDE -33 45 15LONGITUDE 151 9 47
0 250 500 750 1000
metres
Native Vegetationof the
Cumberland PlainMap 9 of 16
Auburn LGA, Concord LGA
Holroyd LGA, Parramata LGA
Ryde LGA & Strathfield LGA
Please view map in conjunction with report"Interpretation Guidelines for the Native
Vegetation of the Cumberland Plain,Western Sydney
NSW NPWS, Hurstville, October 2002"
Vegetation data compiled by the Conservation, Assessment andData Unit, Central CPPD, and the Biodiversity Research Group,Biodiversity Research and Management Division, NSW NPWS.
Base Mapping Data supplied by The Land Information Centre,Panorama Avenue, Bathurst 2795 NSW. (www.lic.gov.au)
Rail data provided by Australian Surveying & Land Information Group.
Copyright NSW National Parks and Wildlife Service, October 2002.This map is not guaranteed to be free of errors or omissions.
The NSW National Parks and Wildlife Service and its employeesdisclaim liability for any act done or omission made on the
information in the map and any consequences of such acts or omissions.
Project jointly sponsored by NPWS, Landcom, UDIA & DUAP.
MAP ANGLE - GRID NORTHHORIZONTAL DATUM: AUSTRALIAN GEODETIC DATUM 1966, ZONE 56
VERTICAL DATUM: AUSTRALIAN HEIGHT DATUMTRANSVERSE MERCATOR PROJECTION
GRID INTERVAL 1000 METRES - ONE GRID SQUARE = 100 HECTARES
Conservation Programs & Planning Division
Central Directorate
NSW National Parks and Wildlife Service
October 2002
PO Box 1967Hurstville NSW 2220Ph:(02) 9585 6444
HAWKESBURY
BLUE MOUNTAINS
BAULKHAM HILLS
HORNSBY
PENRITH
KU-RING-GAI
LIVERPOOL
CAMDEN
CAMPBELLTOWNSUTHERLAND
WOLLONGONG
WINGECARRIBEE
PARRAMATTA
AUBURN
RYDE
BANKSTOWNCANTERBURY
BLACKTOWN
HOLROYD
WOLLONDILLY
FAIRFIELD
Study Area
Shale/Sandstone Transition Forest
1 - Shale/Sandstone Transition Forest (Low Sandstone Influence)
2 - Shale/Sandstone Transition Forest (High Sandstone Influence)
Cooks River/Castlereagh Ironbark Forest
3 - Cooks River/Castlereagh Ironbark Forest
Castlereagh Swamp Woodland
4 - Castlereagh Swamp Woodland
Agnes Banks Woodland
8 - Agnes Banks Woodland
Cumberland Plain Woodland
9 - Shale Hills Woodland
10 - Shale Plains Woodland
Sydney Coastal River-flat Forest
11 - Alluvial Woodland
12 - Riparian Forest
Western Sydney Dry Rainforest
13 - Western Sydney Dry Rainforest
Moist Shale Woodland
14 - Moist Shale Woodland
Sydney Turpentine-Ironbark Forest
15 - Turpentine-Ironbark Forest
43 - Turpentine-Ironbark Margin Forest
Elderslie Banksia Scrub Forest
37 - Elderslie Banksia Scrub Forest
Shale Gravel Transition Forest
103 - Shale Gravel Transition Forest
Blue Gum High Forest
152 - Blue Gum High Forest
6 - Castlereagh Scribbly Gum Woodland
31 - Sandstone Ridgetop Woodland
32 - Upper Georges River Sandstone Woodland
33 - Western Sandstone Gully Forest
34 - Mangrove/Saltmarsh Complex
35 - Riparian Scrub
36 - Freshwater Wetlands
61 - Eastern Gully Forest
62 - Woodland Heath Complex
67 - Vegetation Of Volcanic Substrates
9999 - Unclassified Vegetation, or outside study area
No native vegetation overstorey
Water body
Endangered ecological communities listed under the Threatened
Species Conservation Act 1995 as of 1 June 2002
Ecological communities not listed under the Threatened
Species Conservation Act 1995 as of 1 June 2002
Legend
Vegetation Condition Classes
Note: Condition classes are shown as a shading over the ecologicalcommunity color code. Example shown is for: 1 - Shale/Sandstone Transition Forest (Low Sandstone Influence)
Canopy Cover > 10% (Unless Remnant > 5ha, Where Canopy Cover > 5%)(Areas mapped as classes: A, B, C, SA)
Canopy Cover < 10%(Areas mapped as classes: Cmin, Tx, Txr)
Canopy Cover < 10% (Urban Areas)(Areas mapped as class: Txu)
Study Area Boundary
Local Government Area Boundary
NPWS Estate boundary
Important DisclaimerCare should be taken when interpreting the data displayed on this map. It has beenproduced using a combination of aerial photograph interpretation (API - to identifywhere vegetation remnants exist) and computer modelling of vegetation communitydistribution (to predict which vegetation communities exist in a particular remnant).
Mapping vegetation using aerial photograph interpretation, has a number of limitations:* Drawing the boundary of the remnants is subjective;* Limitations with geo-referencing the data; and* The distortion of aerial photographs towards the edge of the photograph and due to topographic variation.
The limitations of the modelling of the vegetation community distribution relate to:* Assigning a distinct boundary to communities that have a gradual transition between them;* Sampling bias in the vegetation modelling program as the remaining vegetation is highly fragmented and only represents a small portion of the study area; and,* Limits in the accuracy of the other environmental data layers used in the process. eg. the resolution of the soil landscape layer is at 1:100 000.
Finally, the API was conducted using aerial photographs which were taken in the periodlate 1997 to early 1998. Thus areas may have been cleared or may have regrown sincethe photographs were taken.