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Transcript
Arid Recovery
Restoring Australia’s Arid Lands
Feral Facts
A resource for land owners
Arid Recovery
The Landholder’s Pack
Australia’s arid zone has suffered the country’s highest extinction
rate, particularly for small mammals. Competition with rabbits
and domestic stock, and increased predation from introduced
predators such as feral cats and foxes have largely contributed to
this decline.
The purpose of this pack is to share with landholders
throughout Australia, but particularly in the arid interior, the
findings of various research projects undertaken at Arid
Recovery with the aim to:
• promote best practice and tested methods
• increase efficiency and cost-effectiveness of land management practices
• improve communication throughout the arid interior
of Australia
• offer assistance, support and recommendations
Arid Recovery is a unique ecosystem restoration initiative
located near the township of Roxby Downs in northern South
Australia. Arid Recovery is based around one of Australia’s
largest fenced reserves which covers a total area of 123 km2, of
which 60 km2 is completely free of feral cats, foxes and rabbits.
Our mission is to facilitate the restoration of arid zone ecosystems
through on-ground works, applied research and industry, community
and government partnerships.
Arid Recovery is dedicated to broad-scale restoration, beyond
the fenced reserve throughout Australia’s arid lands. Initiatives
include the development of a more economical rabbit, cat and
fox-proof fence for general use, reintroductions of locally-extinct
fauna, raising public awareness about arid zone conservation
and serving as a demonstration site for broadscale feral species
control, ecosystem restoration and successful partnerships.
The pack is divided into
the following sections:
Section 1 - Impacts of Pest Animals
Section 2 - Arid Recovery Fact Sheets
1. Rabbits and their control
1. What is Arid Recovery?
2. Dingoes
2. Greater Stick-nest Rats
3. Feral cats
3. Burrowing Bettongs
4. Foxes
4. Greater Bilby
5. Cat and fox control methods
5. Western Barred Bandicoot
6. Exclusion fencing
7. Vegetation recovery
For further details regarding the information in this booklet
please contact Arid Recovery.
Arid Recovery
PO Box 147
Roxby Downs
SA 5725
[email protected]
All fact sheets can be found on the Arid Recovery website:
www.aridrecovery.org.au
Section 1
Impacts of pest animals
Feral cats, foxes and rabbits have contributed to the decline of many native mammals in Australia’s arid zone, yet many
myths surround the activities of these pest animals. High numbers of pest animal predators, including dingoes, can also have
negative impacts on livestock. For over a decade Arid Recovery has monitored the activity of feral animals both within the
Arid Recovery Reserve and on surrounding pastoral lands.
Section 1 of this Landholders Pack outlines the impacts of feral animals on native plants and animals and discusses some of
the control methods used both within the Arid Recovery Reserve and in surrounding pastoral lands.
Many of these practices can be implemented on pastoral lands to control feral animal numbers. Controlling the number of
feral animals on the land through efficient and cost-effective practices can increase the overall productivity of land in the
arid zone.
Arid Recovery would like to thank the many landholders and volunteers that have assisted in gathering information about
feral animals.
If you would like any further information regarding control of pest animals in the arid zone, please contact Arid Recovery
on 08 8671 8282 or visit the Arid Recovery website www.aridrecovery.org.au
Map of the Arid Recovery
Reserve showing the various
expansions and habitats.
1. Rabbits and their control
Activity
Rabbits are not native to Australia. Since their introduction in 1859,
rabbits occupy more than more than 60% of Australia and have a
higher breeding rate than any native mammal.
Prior to the release of the rabbit calicivirus, South Australia’s arid
zone livestock industry suffered an estimated loss of
$17.4 million each year due to rabbits.
In summer and winter of 2002, Arid Recovery conducted a study
into the home range, activity and habitat use of the European
rabbit using radio-telemetry in arid Australia to improve
management techniques in the arid zone.
Benefits of rabbit control
Some benefits of controlling rabbits include:
• improving regeneration of native vegetation
• reducing populations of introduced predators such as foxes and feral cats
• minimising a key threatening process
Surface activity was highest at night and lowest during the day.
During winter, rabbits were most likely to be found in their
warrens between 9am and 4pm. During summer, rabbits
were most likely to be found in their warrens between 11am
and 6pm. Rabbits spent considerable amounts of time on the
surface, whether it was during winter or summer. This was
somewhat surprising given that summer temperatures during the
study often exceeded 35 degrees celcius.
Habitat use
Rabbits used both dune and swale habitat but most warrens and
surface fixes were recorded in dune habitat during both Winter
and Summer.
Diet
Rabbits have been found to feed on a variety of plants including
mulga (Acacia aneura), roly poly (Salsola kali), parakeelya
(Calandrinia remota).
Control methods and recommendations
Home range
Average home range in summer: 2.1ha
Average home range in winter: 4.2 ha
No significant correlation between home range size and rabbit
weight.
The most successful control methods of rabbits included
fumigation with phostoxin tablets, pressure fumigation with
chloropicrin and warren ripping, where no significant perennial
vegetation was present over the warren system.
Warren ripping effectiveness was also improved when dogs
were used to flush rabbits down warrens prior to ripping. If dogs
can traverse a 300m buffer around warrens this will increase the
chance that all resident rabbits have been flushed.
All methods should be carried out between 9am and 4pm in
winter and between 11am and 6pm in summer when rabbits are
most likely to be down their warrens.
Warren destruction using shovels and 1080 poisoning was
unsuccessful in this study, however the effectiveness of poison
baiting (using 1080 oats) may be increased by placing bait lines
closer together in summer and concentrated in dune habitat and
also in some warrens.
Arid Recovery staff members using
pressurised fumigation on a rabbit
warren during 2002 study.
2. Dingoes
Australia’s top order predator, the dingo, has been known to cause
extensive damage to livestock during some seasons. Anecdotal
evidence also suggests that dingoes may play a role in suppressing
feral cats and foxes, major predators of Australia’s native fauna.
The relationship between dingoes, cats and foxes has not yet been
established experimentally and Arid Recovery’s ‘Dingo Project’,
which began in 2007 aims to investigate this relationship using a
landscape-scale pen trial – the first of its kind in Australia.
A 37 km2 pen was built north of the dog fence, adjoining the
northern boundary of the existing Arid Recovery Reserve. The
pen was completed in December 2008 with a floppy top on
the inside to stop animals involved in the trial from climbing out
(below).
All feral cats and foxes that were either in the pen when it was
closed or were introduced into the pen were captured and
fitted with GPS data loggers. A male and female dingo that
were introduced into the pen from a neighbouring pastoral
property were also fitted with GPS data loggers (above-male
with radiocollar).
Findings to date
•
•
•
•
•
•
•
All foxes (7 out of 7) were killed by dingoes within 17 days of being introduced to the enclosure
Foxes died at night, late evening or early morning (where time of death was known)
Half the foxes died on sand dunes and half died
on swales
Feral cats died between 20 and 103 days after release into the pen
Half the cats (3 out of 6) were killed by dingoes
Dingoes typically stayed with carcasses for several hours after death and/or returned to the carcass several times in following days.
Deaths were confirmed by autopsy results, inspection of kill sites and GPS locations that were downloaded from the GPS data-loggers of dingoes, cats and foxes
What this means and future steps
Our results support anecdotal evidence that dingoes
may play a role in suppressing introduced, medium-sized
predators, particularly foxes, in arid environments.
Whilst results suggest that dingoes could be used as a
management tool to control introduced species north of
the dog fence, we need to determine if native species will
actually benefit from the reduction of cats and foxes from
dingoes.
Inside the Dingo Pen looking
out. Note the floppy top is
on the inside of the pen.
3. Feral cats
Cats are not native to Australia and were most likely introduced prior
to European settlement. They have adapted extremely well and feral
cat densities often exceed one per square km in central Australia.
Although they have not been exclusively linked to species decline
they have been a contributing factor for many. Feral cats have been
linked to the failure of threatened species re-establishing on islands
and in the arid zone outside fenced reserves.
In 2006, Arid Recovery investigated the home range and
behaviour of feral cats and foxes in the arid zone using GPS
technology (below) with the aim of improving management
techniques using poison baiting.
Home range
Average total home range = 1740 ha
Average core home range = 560 ha
No significant difference in home range size between males or
females.
Activity
Average minimum daily distance moved = 1519 m.
A small male cat moved more than 45 km over 2 days.
Another small male moved more than 26 km over 3 days.
Long range movements such as these indicate that cats are able
to quickly re-invade baited areas from non-baited areas.
Cats preferred sand dunes and creek lines and avoided swales.
Sand dunes and creek lines support thicker vegetation and key
prey items such as rabbits. Cats were also found to take shelter
in rabbit warrens.
Average weight of cats in the Roxby Downs region is 3.8 kg.
Heaviest cat on record from the Roxby Downs region
was 7.3 kg
Diet
When abundant, rabbits are the principal prey for cats. However,
when rabbit numbers are low cats have the capacity to switch to
a variety of small vertebrates including reptiles and mammals. It
is estimated that cat predation accounts for approximately 700
reptiles, 150 birds and 50 native mammals per square km killed
in the Roxby Downs region each year.
4. Foxes
Since the fox was introduced to Australia in the late 1800’s they
have been linked to small mammal decline. Foxes have also been
linked to the killing of lambs and other stock. Findings from Arid
Recovery’s 2006 cat and fox collaring project gave a new insight
into fox behaviour and activity in the arid zone using GPS data
loggers (right-below).
Home range
Average total home range = 1660 ha
Average core home range = 770 ha
What sort of distance do foxes travel?
Average minimum daily distance moved = 4553 m (significantly
higher than cats).
One large male fox moved almost 21 km in 2 days.
Foxes prefer sand dunes and tend to avoid swales. Creek lines
did not feature as a preferred habitat type for foxes. Rabbit
warrens were also used as shelter sites and female foxes were
known to use rabbit warrens as den sites (below).
Average weight of foxes in the Roxby Downs region is 4.6 kg.
Heaviest fox on record from the Roxby Downs region
was 6.8 kg.
Diet
Foxes, like cats, can eat anything but if rabbits are abundant
they are the foxes principal prey.. When rabbit numbers are
low, foxes are opportunists and scavengers and will eat mainly
invertebrates, such as scorpions, grasshoppers, beetles and
centipedes. It is estimated that foxes consume on average 290
reptiles per square km and a few native mammals and birds in
the Roxby Downs region each year.
Feral cat with GPS
data-logger collar.
This cat from the Roxby Downs region
contained 34 animals in its stomach
including 32 reptiles, a zebra finch and
a house mouse from one night’s hunting.
A known fox den site in the sand
dunes of the Roxby Downs region.
Fox under sedation during
radio-collaring process.
Technology to improve trapping
To reduce costs associated with the daily checking of permanent
trap sites, Arid Recovery collaborated with a Melbourne-based
company called Observant (www.observant.com.au) whose
background was in setting up remote monitoring of water points
on pastoral stations. This technology was adapted to enable
remote checking of permanent trap sites via the internet.
5. Cat and Fox Control Methods
For over a decade research has been undertaken on the Arid
Recovery reserve on the methods to control introduced predators.
The large home ranges that cats and foxes occupy in the
arid zone, and the average distances they can travel each day,
means a combination of poison baiting, trapping and shooting is
recommended, rather than relying on a single method.
Benefits of controlling predators:
Some of the benefits of controlling introduced predators include:
• increased productivity
• re-establishment of native fauna to improve ecosystem health
• protecting and increasing wildlife populations
Tip: To find out more about our feral animal control techniques
please contact Arid Recovery on 08 8671 8282.
Trapping
Fixed trap sites should be effective for both cats and foxes as
they move continually throughout their home range. In 2000
and 2001 Arid Recovery investigated the effectiveness of
different lures and found that lures significantly attracted more
cats and foxes to trap sites, compared to trap sites that had no
lures. Lures such as food, plants and cat urine are widely used
to attract predators to traps. Small machines emitting bird/cat/
rabbit noises were found to be effective lures for both cats and
foxes during the summer months.
Arid Recovery has permanent trap sites (top right) around the
perimeter of the Arid Recovery Reserve. These traps have
contributed to the successful reintroduction of threatened
species into the Reserve and have enabled an effective buffer
zone around the Reserve. Each site is made up of a naturallooking corral and a pair of rubber foot-hold traps set at the
entrance to each corral. Rubber foot-hold traps are much more
humane than the older leg-hold jaw traps.
Remote cameras are becoming increasingly popular for both
feral animal control and native species monitoring. Arid Recovery
has used a couple of different brands and has also used a digital
video recorder.
Poison baiting
Handbaiting with 1080 poison baits was found to be most
effective for controlling fox numbers. There are different
requirements for both cats and foxes to ensure the most
effective use of poisons. These have been found to be:
• cats require baits to be laid out at a minimum of 25 baits per square km to detect one bait within 3 days.
• foxes require baits to be laid at a minimum of 2 baits per square km to detect one bait within 3 days, but up to 5 baits per square km is highly recommended to allow for non-target uptake by birds and reptiles.
To reduce the uptake of baits by non-target animals (particularly
sand goannas) it is recommended that baiting is only conducted
from March until November.
Areas to target
Whichever method is used to control cats and foxes in the arid
zone, habitats with thick vegetation, particularly creek line and
dune habitat or areas where there are rabbit warrens should be
targeted for greater results. Waterpoints (including troughs and
dams), homesteads and rubbish dumps are also prime areas to
target.
Poison Baiting
Cat, fox and rabbit
presence on transects
during baiting trials. Note
the significant decline in fox
numbers but almost stable
numbers of cats despite
baiting efforts.
Output photo from one
of the remote cameras
which clearly shows
rabbits, time and even
temperature.
One of the permanent trap sites outside the Arid
Recovery Reserve. Note the corral design.
Problems with exclusion fencing
Popped staples from kangaroos fighting through the fence.
Recommendation: Control the number of bucks inside and
outside fenced area.
6. Exclusion fencing
Small scale exclusion fencing is becoming increasingly popular on
private land to restore small patches of habitat. The unique fence
surrounding the Arid Recovery Reserve is the only fence design in
Australia that has been scientifically proven using pen trials to be an
effective barrier to feral cats, foxes and rabbits.
A number of fence designs were tested for performance to
ensure maximum results in excluding predators and other feral
animals.
Testing
A 20m x 20m pen was constructed (above) to test various
fence designs
Cats
When the floppy top was not in place, cats escaped
by climbing wooden posts or jumping onto the
netting and climbing over the mesh fence.
Foxes
A total of 27 foxes were tested. Foxes were found to bash and
bite at the netting of the fence.
Rabbits
A total of 24 rabbits were tested. Sub-adult rabbits, weighing up
to 500g were discovered getting through conventional 40mm
diameter hexagonal “rabbit-proof ” netting. To ensure fence
is rabbit-proof, high quality 30mm hexagonal netting is highly
recommended.
Fence Features
A total of nine different fence designs were tested and the
following important features were found:
• Floppy top. A 60cm curved ‘floppy’ overhang, bent to
form a rounded arc rather than a 45 degree straight
overhang, was important in excluding cats and foxes
• Aprons. Horizontal foot aprons of no less than 30cm
were sufficient to prevent animals from digging under the
base of fences.
• Corners. Exclusion fences should avoid internal corners
and should use steel posts, rather than wooden posts to
prevent animals from climbing.
• 30mm netting. To ensure rabbit proofing this 30mm
netting should extend 90cm from the ground.
Optimal fence design (for cat,
fox, and rabbit exclusion)
The following fence design was used for the construction of the
Arid Recovery Reserve’s first ‘paddock’ called the Main Exclosure
covering 14 square km. No cats or foxes have breached this
fence since it’s completion in 1998.
The 1.80cm fence design with metal posts includes:
• 60cm floppy overhang
• 30mm netting up to a height of 90cm
• 30cm apron at base
• two electric wires, less than 10cm from the netting, at heights of 1.30cm and 1.60cm
• a minimal number of corners
Footnetting and apron rusting after 9 years in the field.
Recommendation: Replace footnetting by either removing the
old footnetting and clipping on new footnetting, or clip new
footnetting over the top of existing or using plastic coated
netting.
Washouts after rain. Excluded animals could gain access.
Recommendation: Always do post-rain fence checks as soon as
possible and patch washed out areas with netting. Research from
NZ found that it took less than two hours for one rabbit to gain
access through a hole in a fence. Install culverts or flood gates.
Sand build up. This can lower the overall height of the fence but also
the height of the rabbit-proof netting.
Recommendation: Increase height of rabbit-proof netting
and minimise sand drift by encouraging revegetation and
discouraging off road driving in the vicinity of the fencelines and
capping dunes with gravel or clay.
Gully erosion along fenceline destroying tracks. Water struggles to
flow through the fence and creates gully erosion in big rain events.
Recommendation: Consult professional grader operators who
can identify key areas in the landscape for flood mitigation.
During pen trials, a shorter (115cm high), non-electrified version
of this fence design did not reduce the effectiveness of the
design. This shorter design now surrounds Arid Recovery’s Red
Lake Expansion and is being tested at a landscape scale.
Material costs
• At January 2005, the materials for the optimal fence design cost AUD $12, 432 per km.
• For the 115cm fence design, materials cost AUD $8, 814.
Fence products
• Cheaper, imported wire products were highly variable in
diameter size (marketed as 30mm with diameters up to
37mm)
• 30mm netting used is a custom made product and
contributed to 57% of material costs. If there is a greater
demand for this then it might become a standard
product.
Side view of fence designs including
location of selvage wires, electric wires
and ‘floppy’ overhang.
The Arid Recovery Fence.
Section 2
Native animal fact sheets
Australia’s arid lands have changed dramatically since European settlement. sixty per cent of the mammal species at
Roxby Downs have become locally or completely extinct. Exclusion fencing, feral animal control and applied research have
enabled Arid Recovery to bring back species from the brink of extinction.
7. Vegetation recovery
Browsing by cattle and rabbits can limit the growth of some arid
zone tree and shrub species. Rabbits alone can prevent regeneration
of some arid zone shrub species causing population declines or local
plant extinctions.
A study conducted at the Arid Recovery Reserve aimed to
quantify initial growth changes in shrubs after the removal of
cattle and rabbits and the re-introduction of native herbivores
including burrowing bettongs, greater bilbies, and greater sticknest rats.
Growth of mulga, silver cassia and sandhill wattle was reduced or
arrested by even low densities of cattle and/or rabbits.
To improve or assist vegetation recovery:
• fence off regenerating stands of mulga until juveniles have exceeded the browsing height of cattle
• reduce stock density in paddocks where mulgas
are regenerating
Main findings
Bilbies and bettongs are better diggers than goannas and rabbits,
digging deeper and wider and excavating more soil.
Bilby digs in particular, catch a greater amount of leaf litter and
viable seeds (below) and carbon levels in the digs are higher
than surface soils.
Higher germination of seedlings was found in bilby digs.
Bilbies dig up to 30cm for a single grain of rice, illustrating their
great sense of smell.
Bilby and bettongs play an important role in creating fertile
patches in the landscape.
Benefits of Bilbies
What effects do animal digs
have on soil nutrients?
Rabbits, goannas, bilbies and bettongs are all accomplished
diggers. They dig to create shelter in the form of burrows and
warrens and to find food such as insects, roots and shoots. Their
digging abilities and subsequent impact on surface soils have seen
them described as the ecosystem engineers of the arid interior.
However, since the 1930’s, bilbies and bettongs have become
locally extinct throughout many areas of the arid interior. Arid
Recovery, in conjunction with the university of NSW and the
University of Adelaide investigated the impact that this decline
had on soils.
Bilby dig with a variety of
seeds and leaf litter collected
in the base of the dig.
•
•
•
•
Increase seedling germination
Improve soil health
Stimulate plant production
Control insect pests such as locusts
Section 2 provides information on threatened species that have been successfully introduced into the Arid Recovery
Reserve including the Greater Bilby, Greater Stick-nest Rat, Burrowing Bettong and Western Barred Bandicoot.
Through monitoring programs we have identified that Arid Recovery now has five times as many naturally occurring
small native mammals inside the Reserve compared to the outside. Although fenced reserves are important for the
conservation of many of our threatened species, they are typically small in scale and very expensive to construct. Arid
Recovery is also researching methods of restoring large areas of arid zone habitat without the use of fences to create a
more naturally functioning native ecosystem.
Arid Recovery would like to acknowledge the many volunteers, researchers and landholders that have assisted in the
native animal monitoring programs.
If you would like any further information regarding native animals in the arid zone, please contact Arid Recovery on
08 8671 8282 or visit the Arid Recovery website www.aridrecovery.org.au
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All fact sheets are available on our website www.aridrecovery.org.au
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
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
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• 
• 



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


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
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All fact sheets are available on our website www.aridrecovery.org.au
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




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









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
















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
















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











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









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
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• 
• 
• 




• 







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
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
All fact sheets are available on our website www.aridrecovery.org.au

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• 
• 
• 


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

















































1
0.8
0.6
0.4
0.2
0
bilby digs

surface
































average seedling per dig




















































































% carbon






7
6
5
4
3
2
1
0
bilby dig
rabbit dig
surface



All fact sheets are available on our website www.aridrecovery.org.au

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• 
• 
• 
• 

























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
















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





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




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• 
• 
All fact sheets are available on our website www.aridrecovery.org.au
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Contact Us
For further information on any of the topics covered in this pack
please contact Arid Recovery.
Arid Recovery
PO Box 147
Roxby Downs
South Australia 5725
Phone: 08 8671 8282
Email: [email protected]
All Arid Recovery Fact Sheets are available online at:
www.aridrecovery.org.au
Photo credits:
Title: BHP Billiton, H. Crisp, Arid Recovery
Section 1: Arid Recovery
Rabbits and their control: Arid Recovery
Dingoes: T. Moyle and H. Crisp
Feral Cats: K. Moseby, P. Bird and J. Stott
Foxes: H. Crisp and J. Stott
Cat and fox control methods: J. Stott, M Farelly and Arid Recovery
Exclusion FFencing: J. Read and BHP Billiton
Vegetation Recovery: J. Edwards and Arid Recovery
Section 2: A. James
Acknowledgements:
This publication was edited by Helen Crisp, Arid Recovery Ecologist, with input
from Clint Taylor, Arid Recovery Pest Management Officer and Kimberley Jarman,
Arid Recovery Volunteer and Community Liaison Officer.
Useful comments and feedback were received from station managers and
owners from the Outback Lakes (including Billa Kalina Station, Mulgaria Station,
Muloorina Station, Dulkaninna Station, Clayton Station, Farina Station), Bulgunnia
Station and Coondambo Station. Thanks also to (Peter Paisley, John Read and
Katherine Moseby) for their assistance.
1. Rabbits and their control
Moseby KE, De Jong S, Munro, N and Pieck, A (2005) Home range, activity
and habitat use of European rabbits (Oryctolagus cuniculus) in arid Australia:
implications for control, Wildlife Research, 32, 305-311.
Ryan, SA, Moseby KE and Paton, DC (2002) Comparative foraging
preferences of the greater stick nest rat and the European Rabbit:
Implications for regeneration of arid lands.
2. Dingoes
Moseby, KE, Neilly, H, Read, JL, and Crisp, H (In press) Dingoes prevent Red
Fox re-establishment within a landscape scale enclosure: implications for
threatened species in the Australian arid zone.
3. Feral cats
Moseby KE, Stott J and Crisp H (2009) Movement patterns of feral
predators in an arid environment – implications for control through poison
baiting. Wildlife Research, 36, 422-435.
Read JL, and Bowen Zoe (2001) Population dynamics, diet and aspects of
the biology of feal cats and foxes in arid South Australia. Wildlife Research,
28, 195-203.
4. Foxes
Moseby KE, Stott J and Crisp H (2009) Movement patterns of feral
predators in an arid environment – implications for control through poison
baiting. Wildlife Research, 36, 422-435.
Read JL, and Bowen Zoe (2001) Population dynamics, diet and aspects of
the biology of feal cats and foxes in arid South Australia. Wildlife Research,
28, 195-203.
5. Cat and fox control methods
Moseby, KE, Selfe, R and Freeman, A (2004) Attraction of auditory and
olfactory lures to Feral Cats, Red Foxes, European Rabbits and Burrowing
Bettongs. Ecological Management and Restoration, 5, 228-230.
6. Exclusion fencing
Moseby KE and Read JL (2006) The efficacy of feral cat, fox and rabbit
exclusion fence designs for threatened species protection, Biological
Conservation, 127, 429-437.
7. Vegetation Recovery
Munro NT, Moseby KE and Read JL (2009) The effects of browsing by feral
and re-introduced native herbivores on seedling survivorship in the Australia
rangelands. The Rangeland Journal, 31, 417-426.
Edwards J (2001) Monitoring vegetation change under different arid
management regimes, near Olympic Dam, South Australia, using Landsat TM
Imagery, Honours Thesis, The University of Adelaide.
This publication was made possible through funding provided by the South
Australian Government.
© Arid Recovery, 2011
James AI and Elridge DJ (2007) Reintroduction of fossorial native mammals
and potential impacts on ecosystem processes in an Australian desert
landscape. Biological Conservation, 138, 351-359.
Further Reading:
Newell J (2008) The role of the reintroduction of Greater Bilbies (Macrotis
lagotis) and Burrowing Bettongs (Bettongia lesueur) in the ecological
restoration of an arid ecosystem: Foraging diggings, diet, and soil seed banks.
PhD Thesis. The University of Adelaide.
Arid Recovery
Restoring Australia’s Arid Lands
Arid Recovery is a joint initiative between BHP Billiton, SA
Department for Environment and Natural Resources, the University
of Adelaide and the local community.