Indicator: IW-01 Annual river discharge
Data
| Stream Name | Years of Record | Long Term Average Daily Flow August (ML/d) |
1982/83 Drought Average Daily Flow August (ML/d) |
Flow at 30 Sept 2004 (ML/d) |
Flow at 30 Sept 2004 as % of Long Term Average | Flow at 30 Sept 2005 (ML/d) |
Flow at 30 Sept 2005 as % of Long Term Average |
|---|---|---|---|---|---|---|---|
| Genoa River | 32 | 339 | 24 | 8.9 | 3 | 26 | 8 |
| Suggan Buggan R | 47 | 265 | 41 | 136 | 51 | 1190 | 449 |
| Snowy River | 26 | 2800 | 420 | 976 | 34 | 1868 | 67 |
| Mitchell River | 67 | 4790 | 1030 | 2629 | 55 | 2819 | 59 |
| Macalister R | 37 | 1640 | 494 | 917 | 56 | 1369 | 83 |
| Moe River | 44 | 301 | 111 | 241 | 81 | 139 | 46 |
| Tarra River | 58 | 174 | 19.2 | 47 | 27 | 45 | 26 |
| Yarra River | 41 | 906 | 173 | 538 | 59 | 898 | 99 |
| Deep Creek | 49 | 480 | 5.9 | 37 | 8 | 46 | 10 |
| Werribee R | 31 | 143 | 1.5 | 35 | 24 | 15.3 | 11 |
| Moorabool R | 59 | 482 | 1.3 | 9.5 | 2 | 6.4 | 1 |
| Barwon River | 33 | 611 | 26 | 128 | 21 | 109 | 18 |
| Woady Yaloak R | 49 | 335 | 7.1 | 30 | 9 | 19.4 | 6 |
| Hopkins R | 74 | 230 | 5.7 | 44 | 19 | 39 | 17 |
| Merri River | 56 | 467 | 26 | 98 | 21 | 35 | 7 |
| Glenelg River | 51 | 4650 | 121 | 1356 | 29 | 161 | 3 |
| Snowy Creek | 72 | 1030 | 198 | 824 | 81 | 3212 | 312 |
| Tallangatta Ck | 29 | 496 | 46 | 182 | 36 | 2009 | 405 |
| Rose River | 42 | 439 | 38 | 132 | 30 | 410 | 93 |
| Hollands Ck | 44 | 574 | 32 | 128 | 22 | 1337 | 233 |
| Sunday Creek | 50 | 211 | 3.4 | 12.5 | 6 | 16.4 | 8 |
| Goulburn R | 50 | 2160 | 415 | 941 | 44 | 1666 | 77 |
| Loddon River | 57 | 257 | 3.8 | 64 | 25 | 93 | 36 |
| Mt Hope Ck | 37 | 177 | 0 | 14 | 8 | 0.3 | 0 |
| Avoca River | 115 | 534 | 14.3 | 11.8 | 2 | 12.8 | 2 |
| Avoca River | 40 | 297 | 6.1 | 0 | 0 | 19.7 | 7 |
| Wimmera R | 58 | 444 | 13.1 | 39 | 9 | 23.7 | 5 |
| Wimmera R | 73 | 196 | 5.3 | 18.3 | 9 | 8.9 | 5 |
adapted from Source: Department of Primary Industries, Victoria 2005, Streamflows: Tabulated Data, viewed 17 Nov 2005, http://www.dpi.vic.gov.au/dpi/vro/vrosite.nsf/
40a2f70b889ac885ca256656002ed378/02333d7bace9aa2f4a25682a001e6d26?OpenDocument, accessed 2 Feb 2005 and 10 November 2005.
Streamflow in Victoria during the drought period as a percentage of the long term average, (ML/d) Flow as at 30 Sept 2004
| Flows under natural conditions, in GL/year | Current flows under regulated conditions, in GL/year | |||
|---|---|---|---|---|
| Mean | Median | Mean | Median | |
| Darling | 3 042 | 1 746 | 2 272 | 1 053 |
| Murrumbidgee | 2 794 | 2 527 | 1 184 | 644 |
| Goulburn, Broken and Campaspe | 3 668 | 3 510 | 1 774 | 1 211 |
| Loddon | 247 | 202 | 100 | 37 |
| Namoi | 872 | 570 | 402 | 177 |
| Gwydir system* | 60 | 11 | 120 | 55 |
| Murray | 13 754 | 11 883 | 4 915 | 2 539 |
Murray-Darling Basin Commission, Water Audit Study, cited in Source: Murray-Darling Basin Commission, The Impacts of Water Regulation and Storage on the Basin's Rivers, viewed 12 Apr 2005, http://kids.mdbc.gov.au/encyclopedia/water_regulation_and_storage Table 1
Yearly Streamflow for Major Surface Water: Sources Impact of water availability - WA
Source: Water Corporation 2003, Yearly Streamflow for Major Surface Water Sources, viewed 7 Sep 2005, http://www.watercorporation.com.au/dams/dams_streamflow.cfm
What the data mean
Examples given for southern Australia show a decrease in river discharge over recent years, mainly due to drought.
Data Limitations
Data on discharge from other river systems are not available.
Issues for which this is an indicator and why
Inland Waters - Catchment scale influences - Hydrological condition - Surface-water availability and human use
This indicator provides a measure of the difference in total flow volume between current and natural conditions. Changes can have impacts on habitat condition. Nutrient enrichment and reduced river flow due to over-extraction of water have increased the frequency and extent of toxic blue-green algal blooms. Other water quality issues arise from reduced flow and decreased flushing.
River discharge can also be an indicator of sediment transport capacity. For example, the rivers of north and central Queensland tend to have high sediment transport capacity because of the high seasonal discharges in the summer wet season.
Other indicators for this issue:
- IW-02 Annual water storage
- IW-03 Surface water used for irrigation
- IW-04 Surface water used for urban/industrial
- IW-44 Sustainable yield determination
- 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
Human Settlements - Services provided by the environment to human settlements - Water
River discharge can influence the quantity and quality of water available for human use. Discharge rates are often reduced by storing flood water in dams or artificial lakes and releasing it during periods of low river flow. This can come at the cost of reducing a river’s capacity for flushing its accumulated sediment load.
Other indicators for this issue:
- IW-02 Annual water storage
- IW-05 Average annual groundwater depth
- IW-06 Average annual groundwater pressure
Further Information
The Impacts of Water Regulation and Storage on the Basin's Rivers - Murray Darling Basin
- The Impacts of Water Regulation and Storage on the Basin's Rivers
- The River Information Centre
- Climate variability and change in south west Western Australia (PDF - 2850 KB)
Key
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