MBCL
SUBMISSION TO CITY OF KINGSTON
LOCAL
PLANNING SCHEME AMENDMENT L33
DATE: 11 August 1998
THE GREEN WEDGE
The Framework Plan, a joint review for
Greater City of Dandenong and City of Kingston, concluded that "there is
strong strategic planning, environmental and landscape grounds to reconfirm the
long term value of the non-urban area (the green wedge) from a metropolitan and
local perspective".
The land subject to the L-33 Amendment is in
the green wedge in the City of Kingston. Whilst much of the site is severely
constrained by flooding, opportunities exist for the creation or restoration of
wetlands and open space.
"The
Panel does not accept the notion that . . .the area is unsightly, degraded,
blighted or unattractive and thus ripe for urban development. The Panel
accepts.. .that the adoption and siting in the wedge of beneficial uses which
are incompatible with residential amenity but suited to large lot sizes and
open landscapes was a practical way of providing for the management of this
part of the green wedge"(1).
The Strategic Review recommends that any
development in the green wedge must genuinely address the landscape, amenity,
ecological and hydrological objectives and limitations.
"Conventional residential development in
this section of the study area will not further these objectives and is not
recommended" (2).
Within the green wedge concept a range of
rural and urban related uses are considered appropriate:
Uses that are not considered appropriate are
urban uses such as residential, rural residential, industrial, commercial (3).
700 houses built on a flood plain with a high
water table is a gross over-development of the site and conflicts with the
green wedge concept.

An absolute maximum of 200-250 houses could
possibly be considered as a "low density environmentally based residential
development" but only after "assessment against the detailed
environmentally sustainable design criteria".
City of Kingston's Strategic and Policy
Justification of the Amendment L33 claims:
"Amendment L33 provides a structure plan
for the subject land consistent with the general thrust of the recommendation
of the South East Non-Urban Study (SENUS)".
However SENUS states:
" 5.3. The Principal Finding of the
study is that the concept of the green wedge is supported and must be
maintained. This is consistent with the context of the State government's
policy as outlined in Living Suburbs" and
"Major urban conversion is not
supported. Any such consideration must only be made in context of a
metropolitan wide review of growth areas" (4).
700 houses on the subject land must be
considered as a "major urban conversion" which will set an
unfortunate precedent by encouraging developers to further erode the green
wedge.
OPEN SPACE
The proposed 700 house residential
development and wetland proposal does not allow for public recreational space
therefore extreme pressure will be placed on Braeside Park.. The Keysborough
Non-Urban Review states:
"Visitor rates for Braeside Park have
steadily risen since it opened in 1989. They will continue to rise, especially
since the Government is encouraging increased housing densities and urban
consolidation within the metropolitan area. Smaller backyards may mean that a
greater demand will be placed on public reserves. Braeside Park will need
careful management to ensure that the public recreation function is not
realised at the expense of the Park’s conservation objectives. Conservation can
also be threatened by the urbanisation of surrounding land. The southern
portion of Braeside incorporates wetlands which provide an important bird
habitat and breeding area. The success of the latter depends largely on the
site's isolation from intrusive human activity such as noise bright lights.
This would be jeopardised if urban uses are allowed to encroach onto adjoining
land"(5).
The lack of public recreation space could be partially
overcome by restricting the number of houses (200-250) to the north east corner
of the subject land and reserving all land south of the ‘lake’ for wetlands and
a nature reserve.
THE WETLANDS
The land subject to the L-33 Amendment is
flood prone land at the northern most sector of the Carrum-Carrum Swamp flood
plain. Flood plain drainage work last century connected Mordialloc Creek to
Dandenong Creek via the Mordialloc Main Drain. This brought about significant
changes to the creek estuary. Provision of sufficient exchange and storage of
tidal water is now needed to flush the estuary. Any extension of the estuary
will have to look carefully at the net tidal exchange and projected residence
time of waters in the estuary, particularly at the time of salt water intrusion
(6).
"Potential uses for the Mordialloc Main
Drain segment lie with widening the drain and establishment of verge wetlands
in the flood prone lands north of the levee banks. This area could be developed
into a linear park with wetland habitat similar to that which previously
existed in the area and which would complement or extend Braeside Park"
(7).
However, the area is still liable to
flooding. Areas subject to inundation are the undeveloped properties bounded by
Mordialloc Settlement Drain, Governor Road, Springvale Road and Mordialloc Main
Drain. Studies of flood management schemes have been carried out and the
conclusion reached is that:
"Extensive filling of the Mordialloc
Main Drain flood plain is unacceptable due to significant increases in peak
flows.(around 20% to 50%)" (8).
Whilst some filling of industrial zoned land
at the western end of Canterbury Road may be acceptable,
"The remainder of the Mordialloc Main
Drain flood plain should remain unfilled in this area. The flood plain
of Mordialloc Main Drain to the west of Springvale Road is also of major
significance as a store for flood waters and should be preserved in its
present condition without filling in order to ensure that downstream flood
problems are not exacerbated" (9).
SALINE INTRUSION
Since the proposed wetland on the subject
land is described as a series of freshwater wetlands, it is necessary to
consider possible saline intrusion into the system. This can arise due to a
number of factors. For example, Dr AB. Pittock claims that as a result of
predicted climate change:
"Changes in the water balance will also
lead to changes in the water table. Where rising water tables are indicated
this could lead to increasing problems of soil salinity, particularly in inland
river basins" and
"a concern for future management of
wetlands is the possibility of increased flood frequency due to the greenhouse
effect"(10).
BUFFER ZONES
Any wetland in close proximity to residential
development must have an adequate buffer zone.
"Buffers are essential, particularly in
urban areas, to provide a safety margin in which animals can detect and
hopefully, avoid predators, as well as providing a screen between disturbing
human activities and natural bird behavior. A buffer zone can be a valuable filtering
area to protect the wetland as a whole from pollutants and weeds. The provision
of buffers to wetlands is Government policy" (State Conservation Strategy
1987).
A buffer zone of 20 to 25 metres is
considered completely inadequate. The Wetland Investigation Committee
recommended a 300 metre buffer from the normal winter flood level around
wetlands.
CONCLUSION
Given that there is the inevitability of
increased flooding in the Mordialloc Creek Estuary and upstream due to climate
change and storm surges; and that a buffer zone of 300 metres is necessary to
give adequate protection to the wetlands, the southern section of the proposed
wetland development below the ‘lake’ must remain undeveloped to act as a meadow
wetland/ flood plain to alleviate flooding problems downstream. A 200-250
house low density environmentally-based residential development could be
located in the northern sector of the subject land.
AUTHOR: M. Rimington
END-NOTES
(1) Gutteridge, Haskins & Davey P/L
(1998) Greater City of Dandenong and City of Kingston: Strategic Review of
the Keysborough Wetlands Area: A Framework Plan, Feb.
(2) Ibid., p. 1.
(3) Spiller Gibbins Swan (1997) South-East
Non-Urban Study Final Report, Feb, p. 46.
(4) Ibid.
(5) Dept. of Planning & Housing (1992) Keysborough
Non Urban Area Review: Background Report, Aug., p. 76.
(6) Anthony Moodie & Associates P/L (1989)
Mordialloc Creek Catchment Flood Management Study: Final Report (for DVA),
Oct., p. 41.
(7) Ibid.
(8) Ibid., p. 91.
(9) Ibid.
(10) Pittock, B. (1987) "The greenhouse
effect" in, Engineers Australia, Feb 6.