From Drs Shane Campbell, Qld. Dept. Natural
Resources & Mines and Tony Grice, CSIRO
 |
|
Using fire to manage rubber vine is proving
extremely effective since the release of the biological control
rust
Photo: Mike Whiting, CSIRO
|
Surveys undertaken with land managers in northern Australia
consistently identify control of exotic weeds as one of their key
management issues. Presently there is a suite of weeds invading
large tracts of land.
They range from grasses such as giant rat’s tail and
grader, shrubs such as bellyache bush to larger woody plants like
parkinsonia, mesquite, rubber vine, chinee apple and prickly
acacia. Control techniques include chemicals, machinery, fire and
biological control. Fire is relatively cheap compared to other
options and it can be applied over large areas.
However, Dr Shane Campbell from the Dept. of Natural Resources
& Mines Tropical Weeds Research Centre (TWRC) warns that
burning is not effective against all weeds.
“It is critical that we understand how fires affect the
different life stages of each weed we are trying to control,”
he said. “This information then allows us to incorporate or
exclude fire when developing integrated control strategies.”
Some woody weeds invading our rangelands demonstrate the different
responses that can occur following burning and how this affects
management decisions.
Algaroba, the most widespread of the mesquite species growing in
Australia, is very susceptible to fire. Even very large plants
(greater than 10 metres in height) can be killed and some of the
seed bank is destroyed thereby reducing the number of seedlings
that emerge.
Rubber vine is another highly susceptible species but this was
not always the case. Before 1995 best kills by fire were only
around 50 per cent. Since then a biological control agent—a
rust fungus—has been released. The rust acts as a defoliant,
reducing the vigour of the plant, making it more susceptible to
control. Where once grass was excluded because of the vine’s
dense foliage it has now returned, allowing a fuel load to
accumulate and fire to spread within infestations. The rust also
reduces seed production which in turn reduces the size of the seed
bank. Consequently few seedlings emerge once the original plants
have been controlled. For both algaroba and rubber vine, controlled
burning can be implemented so they have minimal impact on the
productivity of an enterprise or the ecological integrity of the
area.
Bellyache bush plants appear to be highly susceptible to fire,
but seedling recruitment after burning can be substantial. If
follow-up controls are not implemented, the problem can be
exacerbated. A major limitation of using fire to control bellyache
bush is that once infestations thicken, grass is excluded and
burning becomes impossible. In such situations an alternative
primary technique may be needed, with fire used as a secondary
treatment. TWRC’s Dr Faiz Bebawi is currently researching
possible options, such as machinery and chemicals.
Prickly acacia is a plant that is only susceptible at the
seedling stage so fire is definitely not a primary control option.
However, after killing adults with machinery or chemicals, fire may
be used to treat seedling regrowth—particularly after wet
years when large numbers may appear.
Chinee apple is a plant that appears to have no stages that are
susceptible to fire. Even small plants less than 30 cm high can
re-shoot following burning. It is a difficult plant to remove from
an area once infestations become extensive or dense. However, it
appears its seed bank does not live much more than a year or two,
so there will probably not be much regrowth after the original
infestations are killed. Management options are either chemicals or
machinery, and both are expensive for treating thick infestations;
it needs to be controlled while infestations are small.
Wherever fire is used its success will largely depend on pre-
and post-fire grazing management. It is important that enough fuel
is available on which to undertake burning and it is equally
important that after burning, pastures are able to recover so that
they can compete with any weed seedlings. It is important to
remember that while most native species are fairly tolerant of fire
there may be some present within the weed infestations that are
susceptible. In these situations other control options may be more
appropriate. There is also a need to identify grazing and fire
regimes that can be implemented to prevent the build up of weeds.
The removal of fire from grazing systems is often highlighted as
the primary explanation for why we have such weed problems in our
rangelands.
We still don’t know enough about the impact of fire on
many weeds in northern Australia. These include giant rat’s
tail grass, grader grass and parkinsonia. TWRC, in collaboration
with Dr Tony Grice from CSIRO, is about to begin research on
parkinsonia, particularly its susceptibility to fire at different
seasons. This research is part of a broader cooperative project on
the ecology and management of parkinsonia under the auspices of the
CRC Australian Weed Management and involves CSIRO Sustainable
Ecosystems and Entomology and NRM (Qld).
Links
CRC for Australian Weed Management
www.weedscrc.org.au/
The Weeds CRC which closed its doors on June 30, 2008, and will be replaced by a $15 million National Weeds and Productivity Research Program. The website will no longer be updated after September 30, 2008. However, all of the Weeds CRC's resources are available for download and the site will remain online until approximately June 2010.
Qld Dept. Natural Resources & Water: Pest Factsheets
www.nrw.qld.gov.au/factsheets/groups.php?group=Pest&
Weeds Australia
www.weeds.org.au
This website is an Australian Weeds Committee National Initiative, and includes National Weed Strategy and weeds database