Rainforests of the
Mallacoota area
Submission prepared by:
Bill Peel on behalf of the East Gippsland Rainforest Conservation
Management Network.
SUBMISSION
CONTENTS
SUMMARY
About the Network
Conservation status of rainforest in the Mallacoota Urban Area
Rainforest values to the environment and the community at large
Constraints imposed by the conservation status of rainforests
Benefits of conserving the existing stands of rainforest and the currently
cleared habitat of rainforest
Depletion through land clearing, coastal recreation, urbanisation, grazing
and weed invasion
Depletion by locality
References
List of Tables
Table 1.
Rainforests of the Mallacoota Urban Area.
Table 2.
Conservation status of rainforests that occur in the Mallacoota UDF study
area and the threats to them.
Table 3.
Rare or threatened plants that occur in the rainforest of the Mallacoota
UDF study area.
Table 4.
Rare or threatened or edge of range animals, which occur (have been
recorded) in the rainforests of the Mallacoota UDF study area.
Table 5.
Depletion of rainforest and planning solutions and benefits
Attachments
Attachment 1.
Mallacoota Inlet Littoral Rainforest floristic community
description.
SUMMARY
Mallacoota retains some of the most significant stands of rainforest left
in Victoria that have both state and national significance, including:
-
A major portion of a nationally significant but (as yet) unnamed
floristic community of Littoral Rainforest (Peel in prep b.):
-
Good examples of Warm Temperate Rainforest in Shady Gully and in the
gully system behind the Oval:
-
Nationally threatened Environmental Protection and Biodiversity
Conservation Act (1999)-listed species;
-
Seven listed Flora and Fauna Guarantee Act (1988)-listed animals that
use rainforests:
-
Black Bittern, Diamond Python, Grey-headed Flying Fox, Powerful Owl,
Sooty Owl, Sooty Owl and White-bellied Sea Eagle.
All of the Littoral Rainforests of the Mallacoota UDF study area are
threatened, many provide habitat for both Environmental Protection and
Biodiversity Conservation Act (1999)-listed animals and an array of rare
plants. Much of this rainforest estate has been cleared and all of the
rainforest vegetation is either listed as rare (the Warm Temperate
Rainforest floristic communities) or is in the final stages of the
nomination process (the Littoral Rainforest floristic community) under the
Federal Environmental Protection and Biodiversity and Conservation Act
(1999).
The Council (and by extension the community that it represents) has
obligations to conserve these threatened rainforest communities as well as
their threatened plants and animals that rely upon them for habitat.
Conservation and maintenance of these values requires rainforest
conservation both through the preservation of existing stands and the
rehabilitation and restoration of a significant proportion of the degraded
or previously cleared rainforest habitat in the UDF study area. If as a
community we choose to conserve and restore these rainforest habitats then
we have taken the biggest step towards conserving the cargo of rare and
threatened species they contain.
Fortunately there are significant synergies available across the UDF study
area between sensible planning overlays that deal with land not suitable
for development, erosion risk and storm water management and nutrient
processing whilst maintaining or restoring rainforests in Mallacoota
area.
These synergies fall into the following groupings:
-
Gully systems with land too steep for development
will allow for the protection and rehabilitation of Warm Temperate
Rainforest;
-
Marginal bluffs would
if managed appropriately, could ensure the conservation of threatened of
newly described (but as yet un-named floristic community) of Littoral
Rainforest (currently in the nomination process under the Environmental
Protection and Biodiversity Conservation Act 1999);
-
Storm water and nutrient processing along gully systems
through the conservation and restoration of listed Warm Temperate
Rainforest communities that have been locally proven to strip 70% of
floodwater phosphorous and 88% of ground water phosphorous (Peel in
prep. a).
Conservation status of rainforest in the Mallacoota Urban Area
There are two ecological vegetation classes of rainforest present in the
study area (Warm Temperate Rainforest and Littoral Rainforest) with two
distinct floristic communities represented (Table 1.). The UDF correctly
identifies rainforest as a significant feature of the area study in the
following terms:
-
Landscape
-
Remnant vegetation
The UDF unfortunately fails to list the following: the floristic
communities (Table 1), their conservation status and the threats to them
(Table 2) and their threatened species [Table 3 (plants) and Table 4
(animals)].
Rainforest values to the environment and the community at large
In
Victoria rainforests conserve 4% of the states plant diversity (30% of
which are rare and threatened species), despite occupying less than 0.14%
of the State’s land area.
-
Rainforests are excellent water processors and have been proven locally
to strip up to 70% of the phosphorous from surface storm water and 88%
from ground water. This works best in streams of up to third order
(which matches all of the stream orders of the gully systems in the UDF
study area);
-
Rainforests are fire retardant and so their presence in the urban
environment is a benefit in this regard;
-
Rainforests consist of species that are restricted in the landscape that
can only be conserved by protecting rainforests and their fringing
ecotones;
-
Rainforest on or adjacent to properties is a major selling point for
real estate; and
-
Rainforests enable urban kids to experience the bush with relative
safety near to home.
Constraints imposed by the conservation status of rainforest
All of the Warm Temperate Rainforest and Littoral Rainforest communities
of East Gippsland are protected by the NVP regulations. All of the Warm
Temperate Rainforest and Littoral Rainforest floristic communities within
the Mallacoota urban area are threatened. None of the rainforests in the
UDF area will survive without concerted local government and community
actions that include zoning to protect existing rainforest remnants and
their ecotones and zoning to conserve currently cleared habitat to ensure
planning and subsequent development allow recovery of the rainforests in
their past habitat.
The largest stand of Littoral Rainforest in the town area (on the northern
shore of Devlin’s Inlet was not noted by the UDF.
Consequently the value of this rainforest has been neglected by this
document. Warm Temperate Rainforests in the gully systems were also not
mentioned in the UDF.
Benefits of conserving existing stands of rainforest and the currently
cleared habitat of rainforest
The following benefits will accrue if the council adopts planning measures
to conserve these areas of the landscape:
-
Obligations under the Federal Environmental Protection and Biodiversity
Conservation Act (1999) and State Flora and Fauna Guarantee Act (1999)
will be met;
-
Nationally and State-listed rainforest vegetation as well as their cargo
of rare and threatened plants and animals will be conserved;
-
Storm water treatment is facilitated by the restoration of rainforests
to gully systems in the Mallacoota UDF study area;
-
Nutrient stripping (particularly phosphorous) will remove up to 70% of
phosphorous and if combined with the reinstatement of wetlands at the
mouths of rainforest gullies nitrogen sequestration is enhanced as well;
-
Urban and landscape amenity is improved and the environment is
conserved.
Table 1.
Rainforests of the Mallacoota Urban Area.
|
Ecological vegetation class
Habitat features |
Floristic community |
Habitat
Localities in the urban area |
|
Warm Temperate Rainforest
Habitat features:
·
Moist localities;
·
Fire protected |
Undefined floristic community of Warm Temperate Rainforest |
Habitat:
alluvial soils and gully sides of all of the major gully systems
Localities:
Shady Creek and gully system behind the oval |
|
Littoral Rainforest
Habitat features:
·
Exposed sites
·
Saline influence (wind, water, water tables or geology);
·
Fire protected |
As yet un-named floristic community of Littoral Rainforest |
Habitat:
marginal bluffs and steep slopes around the estuary.
Localities:
relatively intact and large stand (not noted in the UDF) but present
along the northern shore of Devlin’ s Inlet and would have been
present along the western shore from Captains Point (in the Municipal
Caravan Park) northwards to Karbethong and Mirrabooka. |
Table 2.
Conservation status of rainforests that occur in the Mallacoota UDF study
area and the threats to them.
|
Floristic community |
Conservation status |
Threats |
|
Warm Temperate Rainforest |
Rare |
Habitat loss (land clearing)
Grazing by domestic stock
Feral Deer
Weed invasions
Urban development (subdivision of cleared habitat, weed invasion)
Global warming (increased fire frequency and intensity, rising sea
levels) |
|
As yet un-named floristic community of Littoral Rainforest |
Threatened:
currently under consideration in the nomination process under the
Federal Environmental Protection and Biodiversity Conservation Act
(1999). |
Habitat loss (land clearing)
Grazing by domestic stock
Feral Deer
Weed invasions
Urban development (weed invasion)
Coastal recreation and associated infrastructure
Global warming (increased fire frequency and intensity) |
Table 3.
Rare or threatened plants that occur in the rainforests of the Mallacoota
UDF study area.
|
Name |
IUCN |
EPBC |
AROTS |
VROTS |
FFG |
Action Statement |
Rainforest type |
|
Rough-barked AppleAngophora floribunda |
|
|
|
r |
|
|
LRf;
WTRf |
|
Oyster Bay Pine Callitris rhomboidea |
|
|
|
|
|
|
Regionally significant in LRf |
|
Bolwarra Eupomatia laurina |
|
|
|
r |
|
|
WTRf |
|
Trailing Guinea-flower Hibbertia dentata |
|
|
|
r |
|
|
WTRf |
|
Creeping Shield-fern Lastreopsis microsora subsp. microsora |
|
|
|
r |
|
|
WTRf |
|
Branching Grass-flag Libertia paniculata |
|
|
|
r |
|
|
LRf;
WTRf |
|
Whiteroot Lobelia purpurascens |
|
|
|
r |
|
|
LRf |
|
Giant Honey-myrtle Melaleuca armillaris subsp. armillaris |
|
|
|
r |
|
|
LRf |
|
Coast Mistletoe Muellerina celastroides |
|
|
|
r |
|
|
LRf |
|
Golden Mistletoe Notothixos subaureus |
|
|
|
r |
|
|
LRf |
|
Rough-fruit Pittosporum P. revolutum |
|
|
|
r |
|
|
WTRf |
|
Lilac Lily Schelhammera undulata |
|
|
|
r |
|
|
LRf |
Table 4.
Rare or threatened animals*, which occur (have been recorded) in the
rainforests of the Mallacoota Urban Design Framework study area.
|
Name |
Division Name |
ESP |
AROTS |
VROTS |
FFG |
TR |
CAMBA/ JAMBA |
Notes |
|
Azure Kingfisher
Alcedo azurea |
Birds |
|
|
n |
|
|
|
Nests in
LRf/WTRf |
|
Black Bittern Ixobrychus flavicollis australis |
|
|
|
v |
L |
|
|
Uses
rainforest near water |
|
Diamond Python
Morelia spilota spilota |
Reptiles |
|
|
e |
L |
|
|
WTRf/LRf |
|
Grey Goshawk
Accipiter novaehollandiae |
Birds |
|
|
v |
|
|
|
Nests
and hunts: WTRf |
|
Grey-headed Flying-fox
Pteropus poliocephalus |
Mammals |
VU |
V |
v |
L |
|
|
Food:
LRF/WTRf, roosts: WTRf |
Table 4 cont’d.
Rare or threatened animals*, which occur (have been recorded) in the
rainforests of the Mallacoota Urban Design Framework study area.
|
Name |
Division Name |
ESP |
AROTS |
VROTS |
FFG |
TR |
CAMBA/ JAMBA |
Notes |
|
Powerful Owl
Ninox strenua |
Birds |
|
|
v |
L |
|
|
Hunts
and roosts: WTRf |
|
Sooty Owl
Tyto tenebricosa |
Birds |
|
|
v |
L |
|
|
Likely
but not recorded |
|
Tree Goanna Varanus varius |
Reptiles |
|
|
v |
|
|
|
Inhabits
WTRf |
|
White-bellied Sea-Eagle
Haliaeetus leucogaster |
Birds |
|
|
v |
L |
1 |
1/- |
Nests:
WTRf |
*Bold
are rainforest dependant in the district; underlined are those that
breed in rainforests of the district.
Depletion through land clearing, coastal recreation, urbanisation, grazing
and weed invasion
One of the major reasons for the CMN submission relates to habitat loss
for rainforests in the Mallacoota UDF study area. This habitat loss and
the ongoing threats that continue to degrade and erode the remaining areas
of rainforest in the district are directly related to urban development,
coastal recreation and ongoing weed invasion. Drawing the Council’s
attention to this on a site by site basis should enable the planning
scheme to be amended to accommodate both the urban development and
conservation needs of rainforests in the UDF study area.
Depletion by locality
The causes of depletion of rainforests in the Mallacoota UDF study area,
the planning solutions and benefits are listed in Table 5.
References
Peel, B. (in prep. a). Rainforest Restoration Manual for south eastern
Australia. The how to book on what we have learnt so that you can do it.
Includes: Cool Temperate Rainforests, Warm Temperate Rainforests,
Subtropical Rainforests, Gallery Rainforests, Dry Rainforests and Littoral
Rainforests. C.S.I.R.O.
Peel, B. (in prep. b). Littoral Rainforests of south eastern Australia:
composition, ecology and management.
|
Locality |
Causes of depletion |
Ongoing threats |
Planning solution and benefits |
|
Littoral Rainforests:
Western shore of Mallacoota Inlet along the Mirabooka, Karbethong and
township areas to Captains Point |
Clearing for agriculture and grazing, grazing, weed invasion |
Coastal and urban infrastructure, weed invasion |
Planning solution:
recognise its significance, reserve its habitat, protect existing
stands, restore past habitat which has been cleared.
Benefits:
improved landscape amenity, opportunities for passive recreation,
prevention of erosion, improvement in water quality along lakeshores,
provision of habitat for rare, threatened and listed plants and animals. |
|
Warm Temperate Rainforests:
Mullet Creek, Two Mile Creek, Shady Gully, Jungle Gully and gully behind
the Oval |
Clearing for agriculture and grazing, grazing, weed invasion |
Clearing of fringing ecotone vegetation, urbanisation, weed invasion |
Planning solution:
These steep areas are unsuitable for development and should be reserved
for conservation and as drainage reserves. Further subdivision of these
gullies should be stopped and the reserves consolidated at the point of
development or through covenanting.
Benefits:
Improved health of the Inlet through nutrient processing (phosphorous
and nitrogen sequestration); reduced risk of tunnel erosion and gully
erosion, improved landscape amenity, passive recreation, improved fire
protection. |