Lake Warden
Lake Warden is listed as a recovery catchment under the
state salinity action plan (1996) which was developed to
protect significant areas, and in particular wetlands, from
salinity. Projects/studies focussing on flood mitigation in
the Lake Warden catchment were carried out under ARC funding.
These multi-dimensional projects were the bases of two Ph.D.
and a Masters theses.
A field-based project was undertaken to develop and test a mechanism which would allow for correlation of the health of vegetation surrounding playa lakes in south-west Australia with the natural variation in salinity and waterlogging that occurs spatially and temporally in natural systems. A pair of
playa lake ecosystems, surrounded by primary production
land, was modelled with hydro-geological data collected from
March 2006 to March 2007 to determine the hydroperiods of
vegetation communities fringing playa lakes and provide insight into vegetations tolerance or ‘coping’ ranges to waterlogging and salinity conditions.
These lakes are in the Lake Warden recovery catchment. They were chosen because the lakes are very close
together but their groundwater and surface water systems are
disconnected. As they are close it can be assumed they are
subject to the same sort of conditions and degradation processes
but that the varying vegetation health - one of the lakes has
much more degraded vegetation - is a result of the different
hydrological settings of the lakes which predisposes them to
varying levels of waterlogging and salinity levels.
In 1999 and 2007 the Esperance town and region were severely
flooded after large summer rainfall events which, under
anticipated climate change scenarios, are expected to become more
frequent. Hydrological data was collected over the year from
March 2006 - March 2007 which included the summer flood of 2007.
The study looked at the long-term effects of seasonal
waterlogging and salinity and also the impact of the extreme
rainfall events which occurred in 1999 and 2007.
Large rainfall events such as those of 1999 and 2007 are hypothesised to have a significant deleterious effect on the ecosystems.
The study was designed to determine threshold or 'coping'
ranges of vegetation communities using moderately extensive data
over short temporal periods which will guide the design of
potential engineering solutions that manipulate hydrological
regimes to ultimately conserve and protect native vegetation.
The methodology was multi-faceted and included
- a detailed topographical survey;
- vegetation surveys;
- hydrological and hydro-geological monitoring over a 12
month period.
The hydro-geological data and vegetation data was linked with
the topographical survey at a high resolution in a Geographic
Information System (GIS) for spatial analysis to determine the
degree of waterlogging experienced by vegetation communities over
the monitoring period.
The study has found that the spatial and temporal variability
of hydroperiods has been reduced by rising groundwater levels, a
result of extensive clearing of native vegetation, and
consequently populations are becoming extinct locally resulting
in a shift in community composition. Extreme summer rainfall
events also have a significant impact on the health of vegetation
communities by increasing the duration of waterlogging over an
annual cycle and in some areas expanding the littoral zone.
Vegetation is most degraded at lower positions in the
landscape where communities are becoming less diverse and
dominated by salt tolerant halophytic species as a result of
altered hydrological regimes. Some species appear to be able to
tolerate groundwater depths of less than 2.0 m from the surface,
however there are thresholds related to the duration at which
groundwater is maintained at this depth.
Potential engineering solutions include groundwater pumping
and diverting water through drains to maintain sustainable
hydroperiods for vegetation in areas with conservation value. The
effectiveness and efficiency of the engineering solutions can be
maximised by quantifying thresholds for vegetation that include
sustainable durations of waterlogging.
The study has quantified short-term tolerance ranges to
salinity and waterlogging but species may be experiencing a
transition period where they have sustained irreversible damage
that will result in their eventual mortality. With long-term
monitoring, the methodology developed and tested in the study can
be used to quantify the long-term tolerance ranges that are
important for the application of conservation approaches that
include engineering solutions.

Vegetation on the fringe of the lake: dead
melaleucas and halosarcias - salt bush (the
reddish bush). Halosarcias may increase their
dominance by replacing the melaleucas.

This Digital Elevation Model was developed using data from the vegetation survey, aerial photos and the GPS survey. Red lines
indicate the vegetation transects.
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The Lake Warden catchment is a recovery catchment in the state salinity plan. Two small lakes in the catchment were chosen because they are close together but have disconnected surface and ground watersystems.

Vegetation surveys were done across 9 transects, in total covering approx 2.91km. The study used 1m x 1m quadrats across the transects because subtle differences in elevation can buffer the effects of salinity and waterlogging.

Recording vegetation health in small cells enabled the project to capture the sharp zonation which occurs along an
elevation gradient. Using small quadrats also enabled linking the high
resolution GPS survey to the vegetation health in the cells.

A researcher collects
rainfall and data from an automatic logging station.

Detailed topographical surveys
were done using an amphibious wetland vehicle which communicated data
back to its base station. |