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Shoalwater Bay Training Area Overview C DIWA nationally important wetlandAccess wetland mapping in PDF and KML format by selecting the desired 100K map tile below or download the data via the Queensland Government Information Service. The below map is for visual representation purposes only. For more detailed mapping, please download the boundary KML. Drag this bar to relocate the map on your screen Open WetlandMaps interactive map server
Click here for the Australian Government's report on this wetland Catchment stories
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| System | Area (km²) | % wetlands area | % total area |
|---|---|---|---|
| Total | 84.9 | 100.0% | 3.1% |
| Artificial and highly modified | 0.0 | 0.0% | 0.0% |
| Estuarine | 6.9 | 8.2% | 0.3% |
| Palustrine | 9.5 | 11.2% | 0.4% |
| Riverine | 68.5 | 80.7% | 2.5% |
| Habitat | Area (km²) | % wetlands area | % total area |
|---|---|---|---|
| Total | 84.9 | 100.0% | 3.1% |
| Estuarine - mangroves and related tree communities | 3.6 | 4.3% | 0.1% |
| Estuarine - salt flats and saltmarshes | 3.3 | 3.9% | 0.1% |
| Coastal and sub-coastal saline swamp | 0.7 | 0.8% | 0.0% |
| Coastal and sub-coastal non-floodplain tree swamp—Melaleuca spp. and Eucalypus spp. | 5.1 | 6.0% | 0.2% |
| Coastal and sub-coastal non-floodplain wet heath swamp | 0.5 | 0.6% | 0.0% |
| Coastal and sub-coastal non-floodplain grass sedge and herb swamp | 0.0 | 0.0% | 0.0% |
| Coastal and sub-coastal floodplain tree swamp—Melaleuca spp. and Eucalypus spp. | 3.1 | 3.6% | 0.1% |
| Coastal and sub-coastal floodplain grass, sedge, herb swamp | 0.1 | 0.1% | 0.0% |
| Artificial and highly modified wetlands (dams, ring tanks, irrigation channels) | 0.0 | 0.0% | 0.0% |
| Riverine | 68.5 | 80.7% | 2.5% |
Disclaimer
Areas do not include marine or estuarine waters but do include estuarine wetland vegetation
(e.g. mangroves and tidal flats).
All statistics are approximate and generated based on data transformed to a customised Albers equal-area projection, thus allowing wetland extent change for different regions of Queensland to be comparable.
Areas may change over time as mapping approaches improve.
Totals may not match the sum of individually displayed figures due to the rounding of displayed figures.
Wetland extent changes
| System | 2017 area (km²) |
2013 area (km²) |
2009 area (km²) |
2005 area (km²) |
2001 area (km²) |
2017/pre-clear percentage |
|---|---|---|---|---|---|---|
| Total | 84.9 | 84.9 | 84.9 | 84.9 | 85.0 | * 99.6% |
| Artificial and highly modified | 0.0 | 0.0 | 0.0 | 0.0 | 0.0 | n/a |
| Estuarine | 6.9 | 6.9 | 6.9 | 6.9 | 6.9 | 99.7% |
| Palustrine | 9.5 | 9.5 | 9.5 | 9.5 | 9.5 | 99.7% |
| Riverine | 68.5 | 68.5 | 68.5 | 68.5 | 68.5 | 99.6% |
* Total 2017/pre-clear percentage excludes artificial and highly modified
View 2017 wetland system extents for all DIWA nationally important wetlands
View 2013 wetland system extents for all DIWA nationally important wetlands
View 2009 wetland system extents for all DIWA nationally important wetlands
View 2005 wetland system extents for all DIWA nationally important wetlands
View 2001 wetland system extents for all DIWA nationally important wetlands
View 2017/pre-clear wetland system extent percentages for all DIWA nationally important wetlands
| Habitat | 2017 area (km²) |
2013 area (km²) |
2009 area (km²) |
2005 area (km²) |
2001 area (km²) |
|---|---|---|---|---|---|
| Total | 84.9 | 84.9 | 84.9 | 84.9 | 85.0 |
| Estuarine - mangroves and related tree communities | 3.6 | 3.6 | 3.6 | 3.6 | 3.6 |
| Estuarine - salt flats and saltmarshes | 3.3 | 3.3 | 3.3 | 3.3 | 3.3 |
| Coastal and sub-coastal saline swamp | 0.7 | 0.7 | 0.7 | 0.7 | 0.7 |
| Coastal and sub-coastal non-floodplain tree swamp—Melaleuca spp. and Eucalypus spp. | 5.1 | 5.1 | 5.1 | 5.1 | 5.1 |
| Coastal and sub-coastal non-floodplain wet heath swamp | 0.5 | 0.5 | 0.5 | 0.5 | 0.5 |
| Coastal and sub-coastal non-floodplain grass sedge and herb swamp | 0.0 | 0.0 | 0.0 | 0.0 | 0.0 |
| Coastal and sub-coastal floodplain tree swamp—Melaleuca spp. and Eucalypus spp. | 3.1 | 3.1 | 3.1 | 3.1 | 3.1 |
| Coastal and sub-coastal floodplain grass, sedge, herb swamp | 0.1 | 0.1 | 0.1 | 0.1 | 0.1 |
| Artificial and highly modified wetlands (dams, ring tanks, irrigation channels) | 0.0 | 0.0 | 0.0 | 0.0 | 0.0 |
| Riverine | 68.5 | 68.5 | 68.5 | 68.5 | 68.5 |
View 2017 wetland habitat area for all DIWA nationally important wetlands
View 2013 wetland habitat area for all DIWA nationally important wetlands
View 2009 wetland habitat area for all DIWA nationally important wetlands
View 2005 wetland habitat area for all DIWA nationally important wetlands
View 2001 wetland habitat area for all DIWA nationally important wetlands
Disclaimer
Areas do not include marine or estuarine waters but do include estuarine wetland vegetation
(e.g. mangroves and tidal flats).
All statistics are approximate and generated based on data transformed to a customised Albers equal-area projection, thus allowing wetland extent change for different regions of Queensland to be comparable.
Areas may change over time as mapping approaches improve.
Totals may not match the sum of individually displayed figures due to the rounding of displayed figures.
Drainage divisions 
Drainage basins
Drainage sub-basins
Regional natural resource management (NRM) bodies
Local government areas
100K map tiles
Climate zones
Subtropical- Tropical
Bioregions
Biogeographic subregions
IBRA bioregions
IBRA subregions
Bioregional assessment areas
Marine meso-scale bioregions
- Shoalwater Coast (SC)
Marine provincial bioregions
- Northeast Shelf Province
Regional plans
World Heritage areas
Ramsar internationally important wetlands
National parks
Marine parks (Queensland)
Study areas
Report cards
Conservation parks
State forests
- Alligator Creek State Forest
- Byfield State Forest
- Werribee Creek State Forest
Forest reserves
Resources reserves
Timber reserves
Fish habitat areas
Coastal management district
- Available (all have been combined since February 2012)
Nature refuges
Freshwater biogeographic provinces
Aquatic Conservation Assessments (AquaBAMM) and others
Wetland (aquatic ecosystem) type—conceptual models
- Coastal and sub-coastal floodplain grass, sedge, herb swamp
- Coastal and sub-coastal floodplain tree swamp—Melaleuca spp. and Eucalypus spp.
- Coastal and sub-coastal non-floodplain grass sedge and herb swamp
- Coastal and sub-coastal non-floodplain tree swamp—Melaleuca spp. and Eucalypus spp.
- Coastal and sub-coastal non-floodplain wet heath swamp
- Coastal and sub-coastal saline swamp
Wetland (aquatic ecosystem) type—management profiles
Groundwater dependent ecosystem type—conceptual models
Healthy Land and Water conceptual models
Water resource planning areas
Aquatic ecosystem monitoring programs
- Aerial surveys of waterbirds in eastern Australia
- Environmental flows assessment program (EFAP)
- Fitzroy priority neighbourhood catchments water quality monitoring program
- Groundwater water level network
- Long term historical trend water quality monitoring data
- Port Curtis integrated monitoring program (PCIMP)
- Queensland wetland mapping
- Stream and estuary assessment program (SEAP) – freshwater
- Surface water monitoring network
Point source monitoring
Wetland soil indicator case studies
Wetland management case studies
Wetland projects
- A Fish Friendly Fitzroy: Bypassing the Barrage
- Big Dune Surfing Reserve Restoration Project
- Corio Bay Restoration
- Emu Park Community Bushcare Group Coastal Vegetation and Wetlands Protection Project
- Fencing Wetlands and Riparian Zones on Wedderburn
- Feral Pig Control on the Stanage Peninsula
- Fitzroy Water Quality
- Fitzroy Water Quality Project
- Implementing the CQSS Fitzroy Basin Neighbourhood Catchment Plan
- Implementing the CQSS Fitzroy Basin Neighbourhood Catchment Program ‘FB NAP PAP 01’ Final Report December 2004
- Kinka Wetlands
- Kinka Wetlands Quarry Rehabilitation
- Protecting the Values of Our Ramsar Wetlands Shoalwater/Corio Bay
- Ramsar Area Pig and Weed Control 2014-15
- Ramsar Wetlands (DEEDI) CfOC
- Ramsar Wetlands (GA) CfOC
Area specific conceptual model case studies
Water quality improvement plan catchments
EPP (Water) scheduled environmental values and water quality objectives
-
Fitzroy River Sub-basin (WQ1305)
- HEVa2083 (HEV)
- HEVm2087 (HEV)
- HEVm2089 (HEV)
-
Styx River, Shoalwater Creek and Water Park Creek Basins (WQ1271)
- HEV2402 (HEV)
- HEV2403 (HEV)
- HEV2404 (HEV)
- HEV2405 (HEV)
- MD2401 (MD)
-
Styx River, Shoalwater Creek and Water Park Creek Basins (WQ1272)
- HEV2404 (HEV)
- HEV2405 (HEV)
- HEV2423 (HEV)
- HEV2424 (HEV)
- HEV2425 (HEV)
- HEV2426 (HEV)
- HEV2427 (HEV)
Shorebird zones
Biopassage structures
Related legislation/policies
Wildlife
|
Kingdom
Class
|
Native | Introduced | Wetland indicator species |
Rare or threatened species |
All |
|---|---|---|---|---|---|
| TOTAL | 2287 | 226 | 292 | 57 | 2513 |
| Animals | 536 | 13 | 116 | 35 | 549 |
| Mammals | 65 | 8 | 3 | 10 | 73 |
| Birds | 301 | 3 | 72 | 19 | 304 |
| Reptiles | 86 | 1 | 7 | 4 | 87 |
| Amphibians | 26 | 1 | 13 | 1 | 27 |
| Ray-finned fishes | 21 | 0 | 21 | 1 | 21 |
| Insects | 37 | 0 | 0 | 0 | 37 |
| Fungi | 47 | 0 | 0 | 0 | 47 |
| Plants | 1704 | 213 | 176 | 22 | 1917 |
Note: Wildlife statistics are based on information that has been submitted to the DES WildNet database and converted to a 10km² grid. The grid information has been intersected with the mapping polygons to determine the species lists. Click here to view the species grid metadata.
Information from WildNet can also be accessed via Wildlife Online and WetlandMaps.
Rare or threatened includes species listed as extinct, extinct in the wild, critically endangered, endangered, vulnerable or conservation dependent under either the Nature Conservation Act or Environment Protection and Biodiversity Conservation Act
Disclaimer: While every care is taken to ensure the accuracy of this product, the Queensland Government and Australian Government make no representations or warranties about its accuracy, reliability, completeness or suitability for any particular purpose and disclaim all responsibility and all liability (including without limitation, liability in negligence) for all expenses, losses, damages (including indirect or consequential damage) and costs which might be incurred as a consequence of reliance on the product, or as a result of the product being inaccurate or incomplete in any way and for any reason.
This page should be cited as:
Department of Environment and Science, Queensland (2013) Shoalwater Bay Training Area Overview C DIWA nationally important wetland — facts and maps, WetlandInfo website, accessed 1 February 2023. Available at: https://wetlandinfo.des.qld.gov.au/wetlands/facts-maps/diwa-wetland-shoalwater-bay-training-area-overview-c/
— Department of Environment and Science