Indicator: BD-03 Summary of measures being implemented to respond to threats to biodiversity from invasive species
Data
In 2000, plant species that were identified as being in the early stages of establishment and with potential to become a significant threat to biodiversity if their effects are not managed were placed on the National Environmental Alert List. The list is made up of 28 non-native weeds that have established naturalised populations in the wild.
The States and Territories each identify a range of plant species as “noxious weeds”. These are total figures and do not disaggregate agricultural or urban weeds from plants that have the potential to be environmentally invasive.
| Vic | NSW | SA | WA | Tas | Qld | NT | ACT |
|---|---|---|---|---|---|---|---|
| 114 | 152 | 125 | 344 | 104 | 105 | 81 | 36 |
Source: Australian Weeds Committee 2006, Noxious Weeds List - Weeds Australia Database, viewed 7 Jul 2006, http://www.weeds.org.au/noxious.htm.
| Alert List | Eradication from Natural Ecosystems Target List | Eradication from Agricultural Ecosystems Target List | Northern Australia Quarantine Strategy Target Plant List | Weeds of National Significance (WONS) | |
|---|---|---|---|---|---|
| Number of listed invasive plants | 28 | 34 | 26 | 41 | 20 |
| Number and % under no State/Territory legal control | 15 (54%) | 21 (62%) | 7 (27%) | 29 (71%) | 0 (0%) |
| Prohibited for Sale in State/Territory* | 18.3 % | 9.9 % | 25.5 % | 6.7 % | 58.1 % |
| Prohibited for Import into State/Territory | 20.5 % | 12.5 % | 30.3 % | 9.8 % | 53.1 % |
| Subject to Eradication in State/Territory* | 15.2 % | 7.7 % | 19.7 % | 5.5 % | 31.9 % |
| Subject to Control in State/Territory | 4.9 % | 2.9 % | 8.7 % | 0.9 % | 32.5 % |
Note: * Average across all States and Territories
Source: Glanznig, A. and Kessal, O 2004, Invasive plants of national importance and their legal status by state and territory, WWF Australia, Sydney, viewed 7 Jul 2006, http://www.wwf.org.au/publications/invasive_plants/.
| Prohibited for Sale in State/Territory* | Prohibited for Import into State/Territory* | Subject to Eradication in State/Territory* | Subject to Control in State/Territory* | |
|---|---|---|---|---|
| NSW | 26.3% | 22.3% | 27.3% | 7.8% |
| Qld | 41.4% | 41.4% | 29.7% | 9.8% |
| SA | 33.0% | 19.6% | 17.6% | 8.1% |
| Tas | 24.5% | 24.5% | 1.5% | 23.1% |
| Vic | 20.6% | 20.6% | 19.6% | 4.0% |
| WA | 26.1% | 55.7% | 15.5% | 1.5% |
| ACT | 0.0% | 0.0% | 0.0% | 18.1% |
| NT | 16.3% | 16.3% | 8.0% | 6.0% |
| Total | 23.5% | 25.1% | 14.9% | 9.8% |
Note: * Average across all classes of invasive plants of national importance
Source: Glanznig, A. and Kessal, O 2004, Invasive plants of national importance and their legal status by state and territory, WWF Australia, Sydney, viewed 7 Jul 2006, http://www.wwf.org.au/publications/invasive_plants/.
| No. of projects | Approved funding ($) | |
|---|---|---|
| 2004-2005 Threat abatement projects | 21 | 5 364 706 |
| 2003-2004 Threat abatement projects | 14 | 1 986 947 |
| 2002-2003 Threat abatement projects | 14 | 1 496 651 |
| 2004-2005 Weed projects | 25 | 1 785 227 |
| 2003-2004 Weed projects | 11 | 1 157 530 |
| 2002-2003 Weed projects | 14 | 1 701 106 |
Source: Department of the Environment and Heritage 2006, Invasive species national projects, viewed 12 Jul 2006, http://www.deh.gov.au/biodiversity/invasive/projects/index.html.
Funding Stream |
National $ |
Regional $ |
Local $ |
Total $ |
|---|---|---|---|---|
| WONS | 10 338 057 | 6 937 495 | 5 877 936 | 23 153 488 |
| General Weeds | 6 730 320 | 24 293 726 | 15 886 615 | 46 910 661 |
| Priority actions | 0 | 8 915 545 | 0 | 8 915 545 |
| TOTAL NHT2 | 17 068 377 | 40 146 766 | 21 764 551 | 78 979 694 |
Source: Bellamy, J, Metcalfe, D, Weston, N and Dawson, S 2005, Evaluation of invasive species (weeds) outcomes of regional investment, DEH, & DAFF, Canberra, viewed 30 May 2006, http://www.nrm.gov.au/monitoring/national-evaluations/weeds.html.
| 2002/2003 $ |
2003/2004 $ |
2004/2005* $ |
NHT2 Total $ |
|
|---|---|---|---|---|
| WoNs: | 7 560 783 | 7 462 449 | 8 130 256 | 23 153 488 |
| General weeds | 15 788 660 | 16 283 372 | 14 838 629 | 46 910 661 |
| Priority actions | 3 746 796 | 3 672 357 | 1 496 392 | 8 915 545 |
| TOTAL NHT2 (WONS + General+Priority actions) | 27 096 239 | 27 418 178 | 24 465 277 | 78 979 694 |
* to March 2005 only
Source: Bellamy, J, Metcalfe, D, Weston, N and Dawson, S 2005, Evaluation of invasive species (weeds) outcomes of regional investment, DEH, & DAFF, Canberra, viewed 30 May 2006, http://www.nrm.gov.au/monitoring/national-evaluations/weeds.html.
Measures being taken in Tasmania on weeds
Strategic planning
- State weed strategy weedplan and 3 developing regional weed management strategies will identify priority weeds and put in place measures to reduce impact
- 6 draft plans for Weeds of National Significance that occur in Tasmania
- State management strategy for significant beach weeds such as marram grass and sea spurge
Declared Weeds
- Currently 73 declared weeds, each having a statutory management plan.
- 5 authorised weed inspectors and 30 additional weed inspectors operating within local government
Preventing the establishment of new weeds
- Weed alert network that reports new weeds and assists in surveying of newly detected weeds
- Working with industry bodies, such as the Tasmanian Agricultural Productivity Group and Agricultural Contractors of Tasmania, to minimise weed seed introduction and spread
Control
- Highest priority is the prevention of new weed problems from establishing
- Working on eradicating 10 relatively new weeds
- 6 of these are close to eradication, potentially saving millions of dollars in lost production, control costs and impact on biodiversity
Source: Department of Primary Industry, Water and Environment (Unpublished Data) 2005, Unpublished, Contact: Lvl 5 Marine Board Building, 1 Franklin Wharf Hobart Brooke.Craven@dpiwe.tas.gov.au Phone 03 6233 2263 Fax 03 6236 9744 Brooke.Craven@dpiwe.tas.gov.au.
Australian Capital Territory
| 2000-2001 | 2001-2002 | 2002-2003 | |
|---|---|---|---|
| Willows | $0.42 million | $0.47 million | |
| Woody weeds | $0.42 million | $0.37 million | |
| Serrated tussock | $0.17 million | ||
| Other incl pines | $0.19 million | ||
| $1.59 million | 1.82 million | $0.93 million* |
* drought conditions reduced the ability to carry out herbicide-based weed control
Source: ACT Commissioner for the Environment 2003, ACT SoE report, ACT Government, Canberra, viewed 10 Apr 2006, http://www.environment.act.gov.au/yourenvironmenthwp/pests/vertpestmgt.
| Species | Current Management Practices |
|---|---|
| European Rabbit |
|
| European Red Fox |
|
| Feral Goat |
|
| Feral Pig |
|
| Feral Horse |
|
| Dingo/Wild Dog |
|
| Feral Cat |
|
| Brown Hare |
|
| Sambar Deer Fallow Deer |
|
| Common Myna |
|
| Common Starling |
|
| Non-local aviary escapees |
|
| Various native species e.g. Grey Kangaroo, White Cockatoo, Wombat, Pied Currawong |
|
Source: Environment ACT 2002, ACT Vertebrate Pest Management Strategy, Publishing Services for Environment ACT, Canberra, viewed N/A, http://www.environment.act.gov.au/yourenvironmenthwp/pests/vertpestmgt.
Case study South Australia - Bounceback
Since the mid-1800s, grazing and weeds have combined to damage the semi-arid environment of the Flinders region in South Australia. As early as 1900, many small to medium sized mammals and some reptiles had all but disappeared from the area. Even when stock was removed from the region's national parks, threatened species continued to decline because there was little regeneration of native plant communities or improvement in soil conditions and animal habitats.
In response, the Flinders Ranges Bounceback Program has removed foxes and feral goats, destroyed rabbit warrens and regenerated native plants in national parks. In areas surrounding the parks, the focus is on control of wheel cactus and feral goats and rabbits, removal of foxes and protection of endangered species.
Within the national parks, there has been a major reduction in the number of feral goats and rabbits, an increase in the number of yellow-footed rock wallabies, a trial reintroduction of the brush-tailed bettong to the Flinders Ranges National Park, and land reclamation using saltbush.
Source: Department of the Environment and Heritage 2004, Managing invasive species in Australia - success stories. Bounceback, viewed 7 Apr 2005, http://www.deh.gov.au/biodiversity/invasive/publications/bounceback-success.html.
Case study Macquarie Island - cats
Cats were first brought to the island by sealers in 1820. At one time cats were killing up to 60 000 seabirds a year. An intensive trapping program was instigated to eradicate cats from the island because they were perceived to be a threat to the millions of seabirds that come to breed on Macquarie Island each year. Between 1974 and 2000, a total of 2450 cats were caught.
Cats were located and captured by spotlighting and trapping, and were then humanely killed. Towards the end of the program, specially trained dogs were used to make sure that no cats were missed. No cats have been seen on Macquarie Island since June 2000. Recently, the threatened grey petrel has returned and bred there for the first time in over 100 years, and it is possible the absence of cats may have encouraged its return. However, more recently, concerns have been raised that, in the absence of cats which were their primary predator, rabbits are now becoming a problem on Macquarie Island by consuming vegetation needed for seabird nesting sites.
Source: Department of the Environment and Heritage 2004, Managing invasive species in Australia - success stories. Removing cats from Macquarie Island, viewed 7 Apr 2005, http://www.deh.gov.au/biodiversity/invasive/publications/cats-success.html.
Source: Canberra Times 2006, Rabbits devastate Macquarie Island, 21 Oct 2006, p18.
Quarantine
Both the Quarantine Act and the EPBC Act require that live specimens be assessed for their potential impacts. Where there may be a biosecurity risk in importing animals, plants and their products, assessments are made to evaluate the risk and determine appropriate measures to be taken. Biosecurity Australia provides science based quarantine assessments.
Quarantine controls at Australia’s borders help minimise the risk of exotic pests and diseases. These pests and diseases can be carried by people, by animals, in animal products such as meat, in plants or in plant products such as timber, or in soil on machinery. The Australian Quarantine and Inspection Service provides quarantine inspection for international passengers, cargo, mail, animals, plants and animal or plant products arriving in Australia. Quarantine officers use a range of techniques including risk assessment, detector dogs and X-ray machines.
AQIS has:
- 64 X-ray machines - 43 deployed at Australia’s international airports, 11 at international mail centres (Sydney, Melbourne, Brisbane and Perth), four at air cargo depots and six mobile X-ray units for use at seaports and to support fixed units
- 75 detector dog teams - 46 dog teams at airports and 29 dog teams at international mail and air courier depots
Quarantine in northern Australia is important because of our proximity to Southeast Asia and the Pacific, which have many pests and diseases not present in Australia. The Northern Australia Quarantine Strategy early warning system includes a network of ‘sentinel’ cattle herds, pigs and insect traps at key sites. Sentinel animals are regularly tested for early warning of diseases and traps are checked for insects.
What the data mean
Australian jurisdictions have their own legislation intended to limit the introduction and spread of potentially invasive species. Funding of national threat abatement plans increased between 2002-2003 and 2004-2005. Despite many decades of intensive effort, no widespread introduced animal species has ever been eradicated from mainland Australia. In the foreseeable future, these species are here to stay. Furthermore, there has been little research into the ecological impacts of eradicating naturalised species, even if it were practical to do so (see Indicator LD_40 Current research into pressures and contributions of naturalised introduced species ).
Measures to manage invasive species continue to focus on managing the species themselves rather than on the interactions of these species with other aspects of the environment. The eradication of the naturalised cat population on Macquarie Island removed a perceived predator on the native fauna but also effectively removed the primary predator of the naturalised populations of rats, mice and rabbits that are also established on the island. The program is indicative of the risks involved in the approach, currently pervasive across jurisdictions, of focusing on individual species rather than on ecological relationships. The same approach is recognisable in current calls to target rabbits and rats on the Island without consideration of the consequences for invasive vegetation.
A further risk is evident in the fact that most jurisdictions do not distinguish agricultural and urban weeds and pests from naturalised plant and animal species that have the potential to become environmentally invasive.
Data Limitations
The effectiveness of funded projects is unknown at this stage, and will always be difficult to assess. In the absence of data on whether a species is proving to be invasive, or how invasive it is proving to be, monitoring of the effects of control programs, on the rare occasions when such monitoring occurs, can at best show the impacts of the program on the target species, rather than the impact of the program on the aspects of the environment the program is intended to protect.
Issues for which this is an indicator and why
Biodiversity - Species, habitats and ecological communities - Government action on species and ecological communities
Although there are little data to show the extent to which species invasiveness is impacting on the Australian environment, invasive species are perceived to be a significant threat to some native species. Monitoring government action to address the perceived threat is important if the effectiveness of the action in reducing the threat is to be assessed.
Other indicators for this issue:
- BD-02 Conservation status of nationally significant species and ecological communities, compared with previous years
- BD-04 Listed threatened species or ecological communities for which recovery action is showing stable or increasing populations
- BD-05 Alignment of State/Territory and Australian Government listing processes
- BD-24 Government investments to protect biodiversity for public good purposes
- CO-02 Number of marine species that are endangered or threatened and changes in population/ distribution of selected threatened species
- CO-33 Number of species legislatively protected, number with management plans or where management actions have been taken
- CO-34 Number and extent of Marine Protected Areas
Inland Waters - Human response - policy and management - Management of aquatic biota and biodiversity
Management of riparian and aquatic species includes management of introduced species such as mimosa, willows and carp.
Other indicators for this issue:
- IW-36 Willow removal
- IW-45 Groundwater management plans that consider groundwater dependent ecosystems
- IW-48 Ramsar wetlands with implemented management plans
Further Information
- Agricultural Pests and Feral Animals
- National Evaluations of the Natural Heritage Trust and the National Action Plan for Salinity and Water Quality
- Invasive Species National Projects
- Review of existing Red Fox, Wild Dog, Feral Cat, Feral Rabbit, Feral Pig, and Feral Goat control in Australia. I. Audit
- Review of existing Red Fox, Feral Cat, Feral Rabbit, Feral Pig and Feral Goat control in Australia. II. Information Gaps
- Review of Progress on Invasive Species
- Turning back the tide - the invasive species challenge
- The Costs and Benefits of a Proposed Mandatory Invasive Species Labelling Scheme
Further information on Macquarie Island:
- Macquarie Island Marine Park
Key
Links to another web site
Links to data in the DRS
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