Resilience to grazing
Under conservative grazing practices, Mitchell grass can
withstand extended periods of grazing and drought. It is one of the
most nutritious pasture species to be found in the tropical
savannas and cannot be improved upon, in terms of productivity or
hardiness, by other grasses. One of its most valuable attributes is
that it "hays off" (standing matter dries but does not decay
or lose its nutritive value) during the dry season and continues to
provide nutritious feed. During the wet season stock tend to eat
other short-lived herbage and forbs, and rely solely on Mitchell
grass over the dry season. Mitchell grass tussocks recover well
after the dry-season grazing with the arrival of the next
rains.
Grazing pressure
Mitchell grass country can become degraded if the stocking rates
are heavy, particularly if there is a series of dry years. Areas
around watering points are also vulnerable to overgrazing. Under
grazing can also be a problem, as tillering is stimulated by
moderate grazing pressure. Ungrazed plants can become moribund as
old leaf and roots tie up the supply of available nitrogen in the
soil.
The grass tussocks should not be chewed below 10–15 cm in
height. Grazing pressure greater than this will damage the plant's
productivity in the future by limiting the vigour of root
growth.
Dry-season carrying capacity
The carrying capacity of an area over the dry can be estimated
on the basis of the amount of feed left over at the end of the
growing season. Stock should be in good saleable condition at this
point and so adjustments can be made to the stocking rate.
Occasional and opportunistic spelling is also recommended for
maintaining healthy Mitchell grass pasture (Partridge 1996).
The southern reaches of the Mitchell grass region are some of
the most susceptible to drought over the dry. There are several
measures which producers can take to better prepare for this
possibility. Where viable, some run both sheep and cattle, which
can improve market flexibility and facilitate pasture management.
Supplementary feeding is also carried out, and in some areas
producers cut surplus Mitchell and Flinders grass for hay to be
kept in case of dry spells.
Burning Mitchell grass
Fire is rarely used as part of management strategy in this
region of the savannas, although it would once have been a part of
the natural ecosystem. Burning is not carried out largely because
the grass is considered too valuable. In addition, seasons are far
less reliable in this region and so burning is considered too
risky. Fire is used to control gidgee regrowth after clearing on
the margins of this region. It also can remove undesirable pasture
species such as feathertop and improve the quality of standing
pastures. The major application is firebreaks which are established
to protect the country against uncontrolled fires in the dry.
After burning, the Mitchell grass tussocks need to recover to a
height of around 15 cm before grazing should resume over the area.
Managing kangaroo numbers is important at this juncture,
particularly in the south of the region where their numbers are far
greater.
Watering points
Managing the distribution of water is critical in a semi-arid
area such as the Mitchell grass region. During the dry, cattle
graze within a 5 km radius of water. This limitation can have
enormous impacts on grazing pressure and paddock utilisation. As
this region sits on the great artesian basin, most producers have
in the past relied on bore drains. However at present there is a
push, partly subsidised, for producers to cap these bores in order
to reduce water loss to evaporation. Works completed from the first
year of the project replaced 200 km of bore drains and conserved
around 3000 ML of ground water.
There are many other benefits associated with the shift from
bore drains to piping. Some of these include:
- facilities such as spear traps can be introduced to aid in
mustering
- piping can take water to areas beyond the scope of bore
drains
- stock weakened by drought will not risk getting bogged in the
bore drains
- forms of land degradation associated with these bores,
including weed and feral animal invasion, will be more easily
controlled
Optimum spacing of waters depends on fencing, preferred pasture
types and prevailing wind conditions as cattle find water by smell
(Partridge 1996). Again, kangaroos can significantly contribute to
overall grazing pressure and must be accounted for in property
improvement planning, especially in more southerly reaches of the
region.
Weeds
A major management concern in the Mitchell grass region is the
invasion of prickly acacia (Acacia nilotica), and to a
lesser degree other woody weeds including mesquite
(Prosposis sp.) and Parkinsonia. Prickly acacia has
currently taken more than 500,000 hectares out of production, and
has invaded less intensively around another 6.5 million Ha. Much of
this country is to be found in Queensland in the northern half of
the region.
Prickly acacia was originally introduced as a fodder and shade
tree from the Middle East in the 1890s. The shift in much of the
area from sheep to cattle grazing which occurred in the 1970s saw a
dramatic increase in the distribution of the trees. Cattle do not
digest the seeds of the weed as well as sheep and so act as vectors
for the spread of prickly acacia.
As these trees grow close together they shade out all of the
grasses underneath, limiting food available to cattle and exposing
the soil to erosion. The trees also interfere with mustering
efficiency and with stock access to water as they tend to cluster
around bores and drains. An individual tree may produce more than
175,000 seeds per year which can remain fertile for a decade or
more. Control of prickly acacia can be expensive and time
consuming. Methods of control include bulldozing especially around
water courses and controlling cattle access to infested areas to
slow the spread. Some producers are experimenting with camels which
graze the plants much more successfully than cattle, both in terms
of the height that they reach and seed digestion.
While mesquite is not yet a problem comparable to prickly
acacia, it is widely recognized as having the potential to get out
of control. Strategic burning, which may need to be incorporated
with spelling to allow fuel to build up, seems to be effective in
limiting the distribution of this weed.
Links
Australian Agricultural Company properties
www.aaco.com.au/Properties.aspx
Biograze: Waterpoints and Wildlife
www.cazr.csiro.au/modelling.htm#biograze
This website provides a series of fact sheets for managing the interactions between grazing and biodiversity, covering the following topics:
GIS procedures for regional planning;Regional planning for off-reserve conservation in rangelands;Economic costs of off-reserve conservation in rangelands;Voluntary conservation agreements; andEnvironmental Management Systems and biodiversity.