Indicator: IW-44 Sustainable yield determination
Data
Developed yield is the average annual volume of water that can be diverted for use with the existing infrastructure. The developed yield demonstrates the extent to which surface water assets are, or can be, used.
| NSW | Vic. | Qld | SA | WA | Tas. | NT | Aust. | |
|---|---|---|---|---|---|---|---|---|
| Mean annual run-off (ML/yr) | 41 926 000 | 20 188 300 | 157 208 576 | 1 936 800 | 43 133 800 | 45 582 113 | 75 428 200 | 385 923 826 |
| Developed yield (ML) | 6 010 171 | 6 326 240 | 3 244 024 | 750 808 | 856 754 | 3 542 690 | 54 383 | 20 870 270 |
Source: Australian Bureau of Statistics 2004, Water Account Australia 2000-2001, Australian Bureau of Statistics, viewed 16 Nov 2005, http://www.abs.gov.au/ausstats/abs@.nsf/Lookup/D828F04237840B07CA256F4C007155B3, Table 10.9, p. 98.
| Level of salinity | NSW | Vic | Qld | SA | WA | Tas | NT | Aust |
|---|---|---|---|---|---|---|---|---|
| Volume (ML) Less than 1500 mg/L Less than 500 mg/L 500–1000 mg/L 1000–1500 mg/L Total |
698215 3927969 34000 4660184 |
193560 827000 386357 1406917 |
1373040 994530 119460 2487030 |
55850 228640 679515 964005 |
1898876 1061380 995171 3955427 |
1585388 766705 449 2352542 |
4412001 287238 454972 5154211 |
10216930 8093462 2669924 20980317 |
| 1500 mg/L and over 1500–3000 mg/L 3000–5000 mg/L 5000–14000 mg/L More than 14000 mg/L Total |
812450 1550 440400 — 1254400 |
243735 707133 200750 797000 1948618 |
113540 29750 62730 — 206020 |
252645 600 761900 — 1015145 |
1467640 588568 841195 370668 3268071 |
178230 — — — 178230 |
139306 182917 — — 322223 |
3207547 1510518 2306975 1167668 8192707 |
| Total sustainable yield | 5 914 584 | 3 355 535 | 2 693 050 | 1 979 150 | 7 223 498 | 2 530 772 | 5 476 434 | 29 173 024 |
| Proportion (%) Less than 1500 mg/L 1500 mg/L and over |
79 21 |
42 58 |
92 8 |
49 51 |
55 45 |
93 7 |
94 6 |
72 28 |
Source: Australian Bureau of Statistics 2004, Water Account Australia 2000-2001, Australian Bureau of Statistics, viewed 16 Nov 2005, http://www.abs.gov.au/ausstats/abs@.nsf/Lookup/D828F04237840B07CA256F4C007155B3, Table 10.10, p. 98.
Sustainable yield is the level of extraction measured over a specified planning time frame that should not be exceeded to protect the higher value social, environmental and economic uses associated with the aquifer.
What the data mean
In 2000 developed yield was approximately 20 870 GL, representing 5.4% of Australia's mean annul runoff.
There are approximately 29 173 gigalitres of groundwater available in Australia but it is not all of equal quality. Dissolved salt concentrations vary and determine the suitability of water use, e.g. a salinity level above 1500 mg/L is not suitable for irrigation.
Data Limitations
Groundwater sustainable yield data, reported in 2001, has not been updated.
Variations in calculating sustainable yields occur between States and Territories.
Issues for which this is an indicator and why
Inland Waters — Human response - policy and management - Management of surface and groundwaters
The sustainable yield of a groundwater or surface water system refers to the volume and/or rate of water that can be extracted from that system while maintaining an acceptable level of aquatic ecosystem health. The sustainable yield can indicate environmental stress on an aquatic ecosystem if water extraction is greater than the sustainable yield. Sustainable yield can also be used to help identify aquatic systems where water use can be increased in a sustainable manner.
Other indicators for this issue:
- IW-05 Average annual groundwater depth
- IW-06 Average annual groundwater pressure
- IW-08 Groundwater used for irrigation
- IW-09 Groundwater used for urban/industrial
- IW-43 Implementation of National Water Initiative
- IW-45 Groundwater management plans that consider groundwater dependent ecosystems
- IW-46 Implementation of COAG principles
- IW-48 Ramsar wetlands with implemented management plans
Inland Waters — Catchment scale influences — Hydrological condition - Ground-water availability and human use
The sustainable yield will help determine availability of water for human and other use.
Other indicators for this issue:
- IW-05 Average annual groundwater depth
- IW-06 Average annual groundwater pressure
- IW-08 Groundwater used for irrigation
- IW-09 Groundwater used for urban/industrial
- 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 — Catchment scale influences — Hydrological condition - Surface-water availability and human use
The sustainable yield will help determine availability of water for human and other use and the pressures placed on the water resource by human use.
Other indicators for this issue:
- IW-01 Annual river discharge
- IW-02 Annual water storage
- IW-03 Surface water used for irrigation
- IW-04 Surface water used for urban/industrial
- HS-40 National water consumption
- HS-41 Water consumption by sector
- HS-42 Water consumption per capita
- HS-44 Urban stormwater and wastewater reuse
- HS-46 Usage of water efficient appliances
Inland Waters — Human response - policy and management - Environmental flows allocation and management
Implementation and continued observance of the COAG water reforms is a requirement for States and Territories to receive their full share of the payments under the National Competition Policy. Monitoring of their implementation should provide critical indicators of the seriousness and effectiveness of environmental flows allocation and management.
Other indicators for this issue:
- IW-10 Assessment of river condition indices
- IW-11 Number of licences dams, weirs, regulators and levees
- IW-43 Implementation of National Water Initiative
- IW-46 Implementation of COAG principles
Inland Waters — Catchment scale influences — Hydrological condition - Ecological aspects of river flow regimes
The COAG principles include provisions for allocating water for the environment. Implementation of the COAG water reforms should enhance the ecological aspects of river flows. Monitoring of their implementation should provide critical indicators of the effectiveness of environmental flows allocation and management, and should ultimately result in improved hydrological and ecological condition of river systems.
Other indicators for this issue:
- IW-10 Assessment of river condition indices
- IW-11 Number of licences dams, weirs, regulators and levees
- IW-26 Forested streamlength
- IW-27 Extent of significant wetlands (incl. Ramsar)
- IW-28 Number of effective fishways
- IW-46 Implementation of COAG principles
- HS-42 Water consumption per capita
Further Information
Year Book Australia 2002; Geography and Climate; Water resources;
Key
Links to another web site
Links to data in the DRS
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