Indicator: IW-06 Average annual groundwater pressure
Data
| GMU | Trend in artesian bore water pressure |
|---|---|
| Surat | ▲ |
| Warrego | ▲ |
| Flinders | ▲ |
| Barcaldine | ▼ |
| North West | ▼ |
| Gulf | ▼ |
| Central | ▼ |
| East | ▼ |
| Great Artesian Basin | ▼ 416 bores capped + 4156 km of bore drains replaced to June 2002 |
Key to trend:
▲ Improving bore pressure
▼ Declining bore pressure
Adapted from Source: Environmental Protection Authority 2003, State of the Environment Queensland 2003, viewed 2 Feb 2005, http://www.epa.qld.gov.au/environmental_management/
state_of_the_environment/state_of_the_environment_2003/
, 5. Inland Waters, Groundwater - artesian bore pressure, p. 5-7
| State and Zone | Bores controlled pre GABSI | Bores to be controlled at July 1999 | Bores controlled under GABSI to June 2002 (cumulative total) | Bores remaining to be controlled at July 2002 | Bores controlled under GABSI to June 2003 (cumulative total) | Bores remaining to be controlled at July 2003 |
|---|---|---|---|---|---|---|
| Central | 7 | 24 | 12 | 12 | 12 | 12 |
| Surat | 63 | 276 | 44 | 232 | 62 | 214 |
| Warrego | 16 | 202 | 17 | 185 | 27 | 175 |
| Total NSW | 86 | 502 | 73 | 429 | 101 | 401 |
| Flinders | 139 | 194 | 32 | 162 | 45 | 149 |
| Barcaldine | 101 | 165 | 13 | 152 | 29 | 136 |
| Northwest | 17 | 45 | 3 | 42 | 5 | 40 |
| Gulf | 0 | 11 | 9 | 2 | 9 | 2 |
| Central | 15 | 16 | 0 | 16 | 0 | 16 |
| Surat | 5 | 46 | 5 | 41 | 8 | 38 |
| Warrego | 66 | 135 | 7 | 128 | 13 | 122 |
| East | 4 | 24 | 0 | 24 | 0 | 24 |
| Total Qld | 347 | 636 | 69 | 567 | 109 | 527 |
| SW Springs | ||||||
| Central | ||||||
| Western | ||||||
| Total SA | 230 | 36 | 2 | 34 | 3 | 33 |
| Total GAB | 663 | 1 174 | 144 | 1 030 | 213 | 961 |
Source: Hassall and Associates Pty Ltd 2003, Review of the Great Artesian Basin sustainability initiative, Department of Agriculture, Fisheries and Forestry, Canberra, viewed 4 Oct 2005, http://www.affa.gov.au/content/
publications.cfm?ObjectID=07F7F8F9-DD6A-
4E87-93BC79E638BBCDDB, Table 3.1, p. 10
Status of bore capping under the Great Artesian Basin Sustainability Initiative
Source: adapted from Source: Hassall and Associates Pty Ltd 2003, Review of the Great Artesian Basin sustainability initiative, Department of Agriculture, Fisheries and Forestry, Canberra, viewed 4 Oct 2005, http://www.affa.gov.au/content/publications.cfm?ObjectID=07F7F8F9-DD6A-4E87-93BC79E638BBCDDB, Table 3.1, p. 10
| Spring Group | Average Target Pressure Recovery for GABSI (m) | Predicted Average Pressure Recovery for first 3 years of GABSI (m) |
|---|---|---|
| Flinders | 1.2 | 1.4 |
| Recharge | 0.6 | 0.6 |
| Western Qld | 0.9 | 0.2 |
| Dalhousie | 1.4 | 0.8 |
| Eulo | 3.8 | 1.5 |
| Southern SA | 2 | 1.2 |
| All Springs | 2 | 1.1 |
Source: Hassall and Associates Pty Ltd 2003, Review of the Great Artesian Basin sustainability initiative, Department of Agriculture, Fisheries and Forestry, Canberra, viewed 4 Oct 2005, http://www.affa.gov.au/content
/publications.cfm?ObjectID=07F7F8F9-DD6A-4E87-
93BC79E638BBCDDB, Table 3.7, p. 27
| State and Zone | Water savings pre GABSI | Water savings under GABSI to June 2002 | Water savings under GABSI to June 2003 |
|---|---|---|---|
| Central | 2 176 | 3 226 | 3 226 |
| Surat | 5 708 | 8 965 | 12 864 |
| Warrego | 1 167 | 3 522 | 6 053 |
| Total NSW | 9 051 | 15 713 | 22 143 |
| Flinders | 53 530 | 8 652 | 10 178 |
| Barcaldine | Included in Flinders | 3 038 | 6 533 |
| Northwest | Included in Flinders | 648 | 2 368 |
| Gulf | 0 | 345 | 598 |
| Central | Included in Flinders | 1 003 | 2 171 |
| Surat | 1 367 | 3 538 | 5 030 |
| Warrego | 7 011 | 4 604 | 5 120 |
| Total Qld | 61 908 | 21 828 | 31 898 |
| SW Springs | 2 542 | 5 342 | |
| Central | 1 463 | 9 275 | |
| Western | 0 | 1 835 | |
| Total SA | 38 316 | 4 005 | 16 452 |
| Total GAB | 109 275 | 41 546 | 70 493 |
Source: Hassall and Associates Pty Ltd 2003, Review of the Great Artesian Basin sustainability initiative, Department of Agriculture, Fisheries and Forestry, Canberra, viewed 4 Oct 2005, http://www.affa.gov.au/content
/publications.cfm?ObjectID=07F7F8F9-DD6A-4E87-
93BC79E638BBCDDB, Table 3.6, p. 26
What the data mean
There has been some progress under the Great Artesian Basin Sustainability Initiative, with subsequent water savings but a significant number of bores still need capping. Monitoring in Queensland indicates that pressures are still declining in more than half the groundwater management units.
Issues for which this is an indicator and why
Inland Waters - Catchment scale influences - Hydrological condition - Ground-water availability and human use
Throughout Australia there are many artesian bores that require capping to prevent the loss of the resource. Uncapped bores can result in a loss of groundwater pressure and reduction in flows over time. Loss of groundwater pressure can affect dependent ecosystems such as biota in mound springs and other users of the aquifer. Reduced pressure can also lead to a reduction in access by humans to the resource.
Other indicators for this issue:
- IW-05 Average annual groundwater depth
- IW-08 Groundwater used for irrigation
- IW-09 Groundwater used for urban/industrial
- IW-44 Sustainable yield determination
- HS-46 Usage of water efficient appliances
- HS-42 Water consumption per capita
- HS-41 Water consumption by sector
- HS-44 Urban stormwater and wastewater reuse
Inland Waters - Human response - policy and management - Management of surface and groundwaters
An understanding of groundwater pressure issues will improve management of resources that rely on groundwater pressure for their continued existence, such as groundwater dependent ecosystems.
Other indicators for this issue:
- IW-05 Average annual groundwater depth
- IW-08 Groundwater used for irrigation
- IW-09 Groundwater used for urban/industrial
- IW-43 Implementation of National Water Initiative
- IW-44 Sustainable yield determination
- IW-45 Groundwater management plans that consider groundwater dependent ecosystems
- IW-46 Implementation of COAG principles
- IW-48 Ramsar wetlands with implemented management plans
Biodiversity - Pressures on biodiversity - Changed hydrology
Reduced groundwater pressure can lead to insufficient water available to sustain groundwater dependent ecosystems such as mound springs.
Other indicators for this issue:
- BD-14 Examples of impacts of changed hydrology on biodiversity
- LD-06 Area and proportion of land affected by dryland salinity and acidity
- IW-05 Average annual groundwater depth
- IW-10 Assessment of river condition indices
- IW-26 Forested streamlength
- IW-27 Extent of significant wetlands (incl. Ramsar)
- IW-28 Number of effective fishways
- IW-33 Abundance and distribution of waterbirds
- IW-46 Implementation of COAG principles
Human Settlements - Services provided by the environment to human settlements - Water
Reduced groundwater pressure can lead to a reduction in access by humans to the resource.
Other indicators for this issue:
Further Information
- Review of the Great Artesian Basin Sustainability Initiative: Final Report, October 2003
- Farm costs, benefits and risks from bore capping and piping in the GAB - July 2003: abridged report
Key
Links to another web site
Links to data in the DRS
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