The Glenelg River water management area is located within the South East Coast Drainage Division, in western Victoria. Southern Rural Water is the licensing authority and manages both surface and groundwater diversions across the entire water management area except for the Glenelg River above the bridge on Casterton-Harrow Road, which is managed by Grampians Wimmera Mallee Water.
Grampians Wimmera Mallee Water also manages the Wimmera-Mallee water supply system which includes Rocklands and Moora Moora Reservoirs and several other small diversions weirs in the upper Glenelg and Wannon Rivers. Wannon Water supplies water to the majority of towns in the water management area, with the exception of Harrow which is supplied by Grampians Wimmera Mallee Water. The Glenelg-Hopkins Catchment Management Authority is responsible for waterway management in the Glenelg River water management area.
This chapter draws extensively on the State Water Report 2004/05 (DSE, 2006).

Figure 1 Glenelg River water management area locality map
Download high resolution Map:
Glenelg River water management area locality map (1.2 Meg)
(this document requires the use of Adobe Acrobat Reader)
Related Water Management Areas
The links below provide access to similar reports.
Stage 1 urban water restrictions were in place for Balmoral throughout the 2004-05 period and Stage 2 restrictions continued in Harrow. Between February and July 2005, irrigation bans were in place for Grange Burn Creek (except for May), and the Wannon and Glenelg Rivers.
Rainfall conditions were slightly below the long term average (Figure 3 and Figure 4), as was annual streamflow (DSE, 2006). Figure shows a representative hydrograph from the Glenelg WSPA. The hydrograph shows steadily declining groundwater levels between 1975 and 1999. Over the past 5 years, groundwater levels have been gradually increasing.
Table 1 Summary of Glenelg River water management area contextual information
| Rainfall1 |
|
| Total rainfall 2004-2005 |
654mm |
|
Average annual rainfall for period of record |
718mm |
|
Average annual rainfall 1994-2005 |
670mm |
| Total evapotranspiration2 |
|
|
Evapotranspiration 2004-05 |
564mm |
| Water restrictions in 2004-053 |
|
|
Irrigation / Other |
Between February and July 2005, irrigation bans were in place for Grange Burn Creek (except for May), and the Wannon and Glenelg Rivers |
|
Town water supplies |
Stage 1 urban water restrictions were in place for Balmoral throughout the 2004/05 period and Stage 2 restrictions continued in Harrow |
| Entitlement volumes4 |
|
|
Surface water entitlement volume 2004-05 |
56,670 ML |
|
Ground water entitlement volume 2004-05 |
25,824 ML |
Note 1:
Estimated using data from Bureau of Meteorology Rainfall Districts
Note 2:
Bureau of Rural Sciences Water 2010
Note 3:
Department of Sustainability and Environment (State Water report 2004/05)
Note 4:
ABS (Water Access, Entitlements, Allocations and Trading)
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Figure 2 Annual rainfall for the Glenelg River water management area (modified from BOM, 2006)

Figure 3 Monthly rainfall and evaporation for the Glenelg River water management area (modified from BOM, 2006 & Climate Atlas)

Figure 4 Representative bore hydrograph for the Glenelg River water management area
Summary of the total water resources in the basinThe total volumes of water available and supplied from water resources in the Glenelg Basin are shown in Table 2.
Table 2 Summary of water balance in the Glenelg River water management area, 2004-05
| Captured Rainfall (or total available water, or rainfall for storage) |
177200
(runoff) |
111715
(recharge) |
288915 |
| Evapotranspiration |
13000 |
0 |
13000 |
| Returns from the economy (includes treated effluent) |
1230 |
1000 |
2230 |
| Extraction & Diversions |
58290 |
24412 |
82702 |
| Losses |
24600 |
0 |
24600 |
| GW/SW Interaction Volume |
-9500 |
0 |
0 |
| Transfers In |
0 |
0 |
0 |
| Transfers Out |
32500 |
0 |
32500 |
|
Inflows from other entities |
0 |
0 |
0 |
| Outflows to other entities |
69400 |
0 |
69400 |
|
Error Term |
-1266
|
-97803
|
-99069
|
|
(error as % of inflows) |
-1% |
-80% |
-33% |
| Opening Storage capacity |
|
|
|
| - major storages |
53424 |
|
53424 |
| - farm dams |
0 |
|
0 |
| - other |
0 |
0 |
0 |
| Closing Storage capacity |
|
|
|
| - major storages |
23298 |
|
23298 |
| - farm dams |
0 |
|
0 |
| - other |
0 |
0 |
0 |
|

Figure 5 Water balance summary diagram for Glenelg River water management
Outcomes from the water cycle reportThe following information becomes apparent from Table 2.
- There was a large decline in the overall volume of water stored (56%), despite rainfall conditions and streamflow being close to the long term average.
- The error from unaccounted for groundwater in the water balance was 86%, due to a large volume of unaccounted for groundwater outflows.
- There were no estimates available for the volume of baseflow in the catchment (i.e. the volume of groundwater discharged to surface water features). This may account for the large error in the groundwater balance
- It is understood that evapotranspiration from groundwater is a dominant process in this water management area. This was not reflected in the numbers in the water balance.
- Self-extracted groundwater usage in the Glenelg and Condah WSPAs was metered. Self-extracted groundwater extractions outside these areas were un-metered and estimates contained in the water balance contain a large degree of uncertainty.
- There was a volume in the State Water Report 2004/05 for the combined in-stream infiltration of groundwater, flows to floodplain and evaporation.This volume could not be separated into the relevant components so was incuded in the system losses as one figure. For Glenelg River the volume was 9,500 ML.
- The storage capacity of farm dams in the catchment was estimated to be 77,000 ML (DSE, 2006). Information on start and end of season storage volumes was not available, however it was estimated that 80,100 ML was harvested and 55,500ML used in the 2004-05 season from small catchment dams.
- As outlined in the Victorian State Water Report 2004/05 (DSE, 2006), 2004-05 was the first year of operation of the Bulk Entitlement orders for the Wimmera Mallee system. A Flora and Fauna Bulk entitlement order for the Glenelg and Wimmera Rivers is one of five orders for the region.
- Consistent with the Bulk Entitlement conversion orders, a total of 11,987 ML was allocated to the Glenelg and Wimmera Rivers during the 2004-05 flow season (1 November 2004 – 30th October 2005). In addition, 3,300 ML was allocated to the Glenelg River as a compensation flow to contribute in achieving environmental objectives. The Inter Catchment Advisory Group (ICAG) met to determine the split of environmental allocation between catchments. As a result of these negotiations, and based on recommendations and priorities identified by the Stressed Rivers report, the Glenelg River received 4,900 ML (including the compensation flow) for implementation of a summer baseflow.
- The environment’s share of total flow in 2004-05 was 69,400 ML, which was about 39% of the streamflow in the basin. This amount consists of environmental flow releases and all other water flowing in the basin which was not taken out of the streams for consumptive uses.
- Evapotranspiration from groundwater and surface water and interaquifer flow are understood to be significant in the Glenelg. This is not reflected in the water balance.
- Data could not be obtained for the following items in the water balance:
- Groundwater storage volumes (renewable and non-renewable)
- Soil - unsaturated zone storage volumes
- River channels storage volumes
Download 2004-05 water cycle report:Glenelg River SWMA water cycle report (100 kb) (this document requires the use of Adobe Acrobat Reader)
Summary of data availability and reliabilityThe data for this water balance was variable (Table 3) with most of the surface water information obtained from the State Water Report 2004/05, whilst the groundwater information was less detailed and only covered part of the water management area.
The data for this water balance was predominantly category B, indicating that the majority of the data was of a good standard. However, 62% of fields had no information for them either due to them being not applicable (e.g. conveyance losses from irrigation channels), or not available (e.g. snow pack volumes). The overall reliability index for the water management area was estimated as ±69% (between a C and D rating).
Table 3 Summary of data reliability for the Glenelg water management area
| A (+/- 10%) |
8 |
76722 |
16.59 |
| B (+/- 25%) |
10 |
118120 |
25.54 |
| C (+/- 50%) |
7 |
258100 |
55.81 |
| D (+/- 100%) |
1 |
9500 |
2.05 |
| E (no data) |
27 |
- |
- |
| F (no data currently available) |
1 |
- |
- |
| Not applicable |
10 |
- |
- |
|
Total |
64 |
462442 |
|
| WMA reliability index |
±66% |
|
|
|
Water balance error (%) |
-33% |
|
|
|
| |
The estimate of regional water consumption as prepared by the Australian Bureau of Statistics (ABS) includes water use within the Hopkins River, Portland Coast, and Glenelg River Surface Water Management Areas
Estimated water consumption is 160,849 ML
Agriculture comprises approximately 83% of total water consumption; Other comprises approximately 9% of total water consumption; Household comprises approximately 7% of total water consumption; Mining and Manufacturing comprises the remainder.
PLEASE NOTE: Regional estimates were derived using survey data designed to produce state- and territory-level estimates, and incorporated data from a range of other sources. The degree of confidence that can be attached to individual regional estimates is variable. In general, the estimates should be used with a moderate degree of confidence. For further details see ABS Publication 4610.0.055.002
|
The categories used for the breakdown of water consumption are as per Table 2.9
of the Water Account 2004-05. "Other" in respect of the estimated water consumption
comprises water use within the following industries:
- Water supply, sewerage and drainage services
- Electricity and gas
- Forestry and fishing
- Services to Agriculture
- "Other industries"
Results of the National Water Commission’s Framework for Assessment of River and
Wetland Health for
Glenelg River
SWMA
This page provides a summary of the results of the National Framework for the Assessment of River and Wetland Health (FARWH) for Glenelg water management area.
Table 5 Results of the National Framework for the Assessment of River and Wetland Health (FARWH) for Glenelg water management area
|
Biota
|
0.63 |
The Biota Index provides a measure of the biological health of rivers using data on aquatic macroinvertebrates as assessed by the Index of Stream Condition. |
|
Catchment Disturbance |
0.67 |
The Catchment Disturbance Index provides a measure of human land-use changes that impact the river and wetland condition and the biota.
The catchment disturbance for Victoria were generated using the methods developed in the National Land and Water Resources Audit 2001. |
|
Hydrology Disturbance |
0.78 |
The Hydrological Disturbance Index assesses the flow regimes change that result from river regulation and/or substantial flow diversion or extraction.
For Victoria the Hydrology condition of rivers is based on Flow, Stress, Ranking (FSR). |
|
Physical Form |
0.44 |
Physical Form was assessed for Victorian water management areas based on the Index of Stream Condition methods and includes stream bank and bed condition, presence of, and access to, physical habitat. |
|
Water Quality |
0.47 |
The Water Quality Index includes a range of chemical (nutrient concentrations, turbidity, salinity and acidity) collected by Index of Stream Condition (ISC). |
|
Fringing Zone |
0.46 |
The Fringing Zone Index uses the Streamside Zone data from the Victorian Index of Stream Condition including quantity and quality of streamside vegetation, and condition of billabongs. |
|
Overall Score |
0.51 |
The Overall Index for a Surface Water Management area is a combination of the individual indices (Biota, Fringing Zone, Hydrological Disturbance, Physical Form and Water Quality) to assess the overall health of the river.
For Victoria the indices are integrated at reaches using inverse ranking and weighted by reach length, then aggregated to give the overall score for the Surface Water Management Area. |
|
Figure 6 Results of the National Framework for the Assessment of River and Wetland Health (FARWH) for Glenelg water management areaNote: The ranges associated with the graph are described below.
| 0.0-0.2 |
severely modified |
| 0.2-0.4 |
substantially modified |
| 0.4-0.6 |
moderately modified |
| 0.6-0.8 |
slightly modified |
| 0.8-1.0 |
largely unmodified | See the National Framework for the Assessment of River and Wetland Health (FARWH) report on the Publications page for details on the assessment method.
|
This page provides high level performance indicators of water management for the
Glenelg River
surface water management area (SWMA) based on information provided by the government
of
Victoria.
It provides answers to a range of questions of relevance to the National Water Initiative
(NWI), specifically in relation to:
Please note that a dash means that either the data was not
available, not provided or that the question was not relevant for a particular area.
Surface water management framework
|
What is the status of the water management plan for this surface water management
area?
|
Final - full coverage of water management area |
|
If a final or draft plan has been written, what year was it completed?
|
2004 |
|
If a final or draft plan has been written, does it consider groundwater explicitly? |
No |
|
If yes, how is groundwater considered? |
|
|
Technical assessment |
- |
|
Management decisions |
- |
|
What percentage of the surface water management area is covered by the water management
plan(s)? |
100 |
|
Does your water plan specify water quality objectives to meet environmental and
other public benefit outcomes? |
No |
|
Other items included in the management framework are: |
|
|
Metering program for this area |
Included |
|
Effluent recycling |
Included |
|
Climate change |
Included |
|
Aquifer storage and recovery |
Included |
|
Household rainwater tanks |
Included |
|
Efficient irrigation systems |
Included |
|
Other |
Stormwater included |
|
Management plan available at: |
|
Water resource caps
|
Has a cap been placed on surface water usage / abstraction in this surface water
management area? |
Yes |
|
Is the cap an absolute limit to allocation or provisional limit? |
Absolute |
|
If there is a cap, what year was it implemented? |
2004 |
|
If there is a cap, is it considered to represent the sustainable surface water yield? |
Yes |
|
The following water usage types are included/not included under the cap: |
|
|
Irrigation |
- |
|
Urban supply |
- |
|
Commercial / Industrial |
- |
|
Minor catchment storages |
- |
|
Minor on-stream storages |
- |
|
Minor extracted water storages |
- |
|
Stock and domestic |
- |
|
Mining / Oil and gas |
- |
|
Forestry |
Not included |
|
Floodplain harvesting |
- |
|
Drought supply |
- |
|
Greywater use |
Not included |
|
Effluent recycling |
Not included |
|
Aquifer storage and recovery |
- |
|
Does auditing of compliance with the cap occur? |
Yes |
|
Compliance report available at:
|
Compliance report |
Surface water / groundwater interaction
|
Are surface water and groundwater managed as an integrated water resource in this
surface water management area? |
No |
|
Reason or method: |
Integration has not been assessed |
|
Integrated management plan available at:
|
|
Surface water sustainable yield
|
The sustainable yield within this surface water management area for 2004/05 was: |
253973 ML |
|
The method used to determine the sustainable yield was: |
- |
|
Was the sustainable yield determined for the combined (i.e. surface water and groundwater)
water? |
No |
|
Is the cap considered to be at or below the sustainable yield of surface water? |
At |
|
What is the level of entitlements relative to the sustainable yield? |
High level of development |
Environmental water requirements
|
Have environmental water requirements been determined for this surface water management
area? |
Yes - complete coverage of water management area |
|
If yes, what year were they completed?
|
2004 |
|
For regulated areas, how much of the mean annual flow is not available for allocation
and provided for the environment? (percentage of mean annual flow at locality of
river regulation) |
- |
|
Are there formal environmental water provisions for regulated rivers? |
- |
|
If so, what method was used to determine environmental water provisions for regulated
rivers? |
- |
|
For what percentage of the rivers are provisions made? |
100% |
|
Maps illustrating which rivers have provisions available at: |
|
|
Do the environmental water provisions consider groundwater?
|
No |
|
If yes, how? |
- |
|
Completed Environmental Flows Reports available at: |
|
Surface water diversions
|
The total surface water diversion in the surface water management area for 2004/05
was: |
<%DataBinder.Eval(Container.DataItem, "SSDVOLML_C", " {0} ML") %>
|
|
What percentage of surface water diversion is determined from metered data? |
1 % |
|
What is the level of diversions relative to the sustainable yield? |
Moderate level of diversions (30 - 69%) |
|
For surface water diversion that is NOT metered, how was the surface water diversion
determined for 2004/05? |
|
|
Estimated from irrigated areas |
Yes |
|
Estimated from licence volume |
Yes |
|
Estimated from power usage for pumps |
- |
|
Estimated from models |
Yes |
|
Other |
Yes - Statewide SDL estimates of small catchment dam use |
Surface water entitlements
|
Entitlements for surface water are required/not required for the following usage
types:
|
|
|
Irrigation |
- |
|
Urban supply |
- |
|
Commercial / Industrial |
- |
|
Minor catchment storages |
- |
|
Minor on-stream storages |
- |
|
Minor extracted water storages |
- |
|
Stock and domestic |
- |
|
Mining / Oil and gas |
- |
|
Forestry |
Not required |
|
Floodplain harvesting |
- |
|
Drought supply |
- |
|
Greywater use |
Not required |
|
Effluent recycling |
Not required |
|
Aquifer storage and recovery |
- |
|
Other |
- |
Protected terrestrial areas
|
Each of the following protection types cover a percentage of the surface water management
area as detailed:
|
|
|
Habitat/species management area |
0.09 |
|
Managed resource protected areas |
0.16 |
|
National park |
12.83 |
|
Natural monument |
0.48 |
|
Protected landscape/seascape |
- |
|
Strict nature reserve |
0.58 |
|
Wilderness area |
- |
|
Total |
14.14 |
Related links
The links below provide access to similar data reports for groundwater management
units (GMUs) that overlap this surface water management area (SWMA).
|
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