
Effectiveness of Current Farming
Systems in the Control of Dryland
Salinity
The
way it was...
In most cases Australia’s
native vegetation comprises trees
or woody shrubs. This perennial vegetation,
with its relatively deep roots, has
become effective at taking full advantage
of any available water. As a result,
it can use most of the water entering
the soil. The ‘leakage’ of
excess water into the deeper soil
below the roots is usually quite
small, if it happens at all. Various
studies have shown that over most
of Australia’s current dryland
grazing and cropping areas, this
leakage was commonly between 1 and
5 mm/year.
Over thousands of years the minimal leakage has allowed
the salts introduced through rainfall or rock weathering
to build up in the soil below the depth of plant roots.
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Changing the
natural conditions
European settlers have changed the Murray- Darling
Basin to a remarkable degree in a relatively short
time. Large-scale clearing of native vegetation
and its replacement with crops and agricultural
systems have substantially increased the amount
of water entering the groundwater systems of the
landscape.
These increased amounts of water now entering the
groundwater under current agricultural production
systems greatly exceed the capacity of the groundwater
systems to discharge the additional water to the
rivers and streams. As the input to the groundwater
exceeds the output, the watertable must rise. As
it rises, more water is discharged to the land surface
as seepage surfaces (usually at lower positions in
the landscape). Wherever this groundwater contains
salt or intercepts salt stored in the landscape,
salt is mobilised to these seepage faces, and hence
to the land surface, rivers and streams.
The amount of water leaking into the groundwater
system depends on various factors that include the
climate (particularly the amount of rainfall), the
permeability of soils and subsoil, and vegetation
characteristics. For example, any water leaking beyond
the root zone does not always end up in groundwater,
since in certain situations it can move laterally
through the soils and end up in surface streams.
In other situations, leakage can occur from the base
of the streams into groundwater systems.

Replacing vegetation with shallow rooted annual
crops and pastures has led to substantial increases
in the amount of water 'leaking' into the soil.
The consequences are rising groundwater levels
and dryland salinity.
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There is too much
leakage
Leakage can be much greater under current agricultural
systems than under natural vegetation. It occurs
when the plant/soil system cannot cope with the amount
of water that has fallen over a period of time. Leakage
is caused by a complex combination of climate and
rainfall patterns, vegetation cover and soil properties.
Climate
The effect of climate and rainfall on leakage to
groundwater can be simplified into two different
types, as follows.
- In wetter areas, normal rainfall can exceed potential
evaporation for a period of the year, leading to
leakage when the excess water cannot be stored
in the soil.
- In drier areas, leakage is likely to
occur mainly as a result of exceptional
circumstances, such as intense rainfall
and flooding that may only occur once every
320 years.
In determining leakage, the distribution of rainfall
is as important as the total amount of rain. The
sequence of rainfall events is critical, particularly
for the episodic nature of deep drainage and recharge.
Seasonalitythe particular time of year when
most rainfall occursis another major climatic
factor that affects leakage amounts.

This map shows the differences in rainfall
seasonality in the Murray-Darling Basin,
with the rain in the northern parts falling
predominantly in summer, and in the south, in winter.
In the winter rainfall dominated southern parts
of the Basin, most of the rainfall occurs during
the cooler part of the year, when evaporation and
hence the amount of water the vegetation is using
is likely to be low. Under these circumstances, the
rainfall infiltrating the land must be stored in
the soil if leakage is to be prevented. If the soil
already contains water that was not used by agricultural
plants in the growing seasons, leakage will occur
more readily.
In the summer rainfall dominated northern parts of
the Basin, most of the rain coincides with the period
of highest evaporation, thus increasing chances for
the vegetation to use the rainfall. However, rainfall
can often be distributed in short periods. In this
case, water moves through the profile more rapidly
than the plants can extract it, causing significant
leakage. Thus while leakage is often lower in summer
dominated rainfall areas, it is also more episodic,
and depends on the rainfall sequence. Summer rainfall
can be as effective in causing leakage as winter
rainfall if it is concentrated over short periods.
Vegetation
Vegetation affects the amount of leakage to groundwater
in two key ways: the depth of plant roots and whether
the plants are perennial.
- Plant root depth. Deeper roots allow plants to
extract water from deeper in the soil, reducing
the opportunity for water to leak below them. For
example, the roots of Eucalypt trees have been
found to depths of 3040 metres. Unfortunately,
as the roots of most of our dryland agricultural
plants are less than 12 metres deep, they
have much less opportunity to extract water from
the soil before it flows below their reach and
becomes leakage.
For example, a water balance study at Katanning
in south-west Western Australia showed that shallow
rooted clover and deep rooted lucerne both dried
out the shallow soil (045 cm) to the same
extent, while the deeper rooted lucerne was able
to dry out the deeper soil (45 cm1.2 m) to
a much greater extent. Leakage from 80 mm under
the clover was reduced to 30 mm because the lucerne
was helping to dry the deeper soil.
Even with deeper rooted crops, leakage can occur
during the early growing stages when they have
established only their shallow roots. A study at
Wagga Wagga showed that in the first year of lucerne
in rotation with wheat, there was a similar amount
of leakage past 1 m to that under wheat, but in
its second and third years, when the deep root
system became established, leakage was dramatically
reduced.
- Perennials. If a plant does not have
leaves that are transpiring and using water
when the soil is wet, it is difficult for
the plant to use the water before it leaks
below the root zone.
Annual plants grow, flower, set seed, then die.
They use water while they grow. Most annuals are
shallow rooted and do not use any of the summer
and early autumn rainfall. They do not need roots
in the deeper soil because they are not present
over the drier period of the year.
In contrast, perennial vegetation grows all year
round. It can send down deeper roots to use extra
water from deeper in the soil. While perennials
may shut down during dry periods, they can respond
to occasional rainfall opportunities in the dry
season. So overall, they have the chance to use
more water than annuals.
Eucalypts in the lower rainfall areas have adapted
to this cycle very well, although perennial crops
such as lucerne and phalaris have the potential
to perform in similar ways in lower rainfall areas.
However, it is extremely difficult for even perennial
pastures to reduce leakage in winter dominated
rainfall areas that have an annual rainfall of
more than 600 mm.

In this example, the summer active vegetation
is unable to control the leakage
that occurs over the winter months, when most of
the rain falls
Soils and geology
Soils can affect the amount of leakage in three
main ways.
- Water holding capacity. This is the amount of
water the soil can hold in between wet and dry
conditions. For example, because sandy or rocky
soils have a low water holding capacity, we would
expect greater amounts of leakage in these types
of soil than in heavier clay or loam soils, all
other things being equal. While clay soils can
store large amounts of water, comparatively little
of it may be available to plants because the clay
holds the water more tightly than the plants can
extract it.
- Soil permeability. The amount of leakage
depends on how easily water can move through
the soils and sub-soils. For example, some
subsurface clays may be less permeable
and reduce the rate that water can leak
into the groundwater systems. Under these
circumstances more water may move laterally
rather than leak vertically into groundwater
systems.
- Impeding plant growth. The physical or
chemical characteristics of a particular
soil may impede plant growth, thus restricting
the depth of plant roots and hence the
opportunity for plants to use water before
it becomes leakage. Physical factors include
soil density, or the presence of hard soil
layers. Chemical factors include soil acidity,
salinity or nutrient changes.
Clearly, estimating the amount of leakage under
different climates, soils and land management systems
is important in designing farming practice strategies
to control dryland salinity. One difficulty in devising
simple ways to determine the precise value of leakage
is that it is highly variable from season to season
and can vary over small distances because of the
factors discussed above. In addition, leakage depends
strongly on climate and Australia has large variations
in climate, further complicating the measurement
and estimation of leakage into our landscape.
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Current
Farming Systems and Managing Dryland Salinity
Key Questions
- How do the current leakage rates
under best practice in our farming
systems compare with leakage rates
under the native vegetation?
- If best practices are
adopted over the majority
of our farming systems,
how effective are these
likely to be in controlling
salinity, over both the
short and long term?
- How does this effectiveness
vary throughout the Murray-Darling
Basin?
- How long will it take
the salinisation rates to
decrease in response to
the reduced leakage (at
rates of native vegetation,
and at rates of current
best practice)?
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