The Wimmera River water management area is located within the Murray-Darling Basin, and includes the Wimmera, Avon and Richardson River catchments. The Wimmera River flows from the north side of the Great Dividing Range near Elmhurst, and from the Grampians Ranges, to Lake Hindmarsh. During wet periods, Lake Hindmarsh overflows through Outlet Creek, into Lake Albacutya and onto a series of smaller lakes and the Wirrengern Plain in the Mallee. The Avon and Richardson Rivers flow into and terminate in Lake Buloke.
Grampians Wimmera Mallee Water is the licensing authority and manages both surface and groundwater diversions. They are responsible for the Wimmera-Mallee water supply system which delivers water to urban centres and farms in a large part of the water management area. Central Highlands Water supplies the towns of Landsborough and Navarre. The Wimmera Catchment Management Authority is responsible for waterway management in the Wimmera River catchment, while the North Central Catchment Management Authority is responsible for the Avon and Richardson River catchments.
This chapter draws extensively on the State Water Report 2004/05 (DSE, 2006).

Figure 1 Wimmera River water management area locality map
Download high resolution Map:
Wimmera River water management area locality map (1.5 Meg)
(this document requires the use of Adobe Acrobat Reader)
Related Water Management Areas
The links below provide access to similar reports.
As outlined in the Victorian State Water Report 2004/05 (DSE, 2006), urban water restrictions across the Wimmera Water Management area for 2004-05 included:
- Stage 3 restrictions continued (from November 2002) at Berriwillock, Beulah, Charlton, Culgoa, Dooen, Hopetoun, Marnoo, Nullawil, Rainbow, Tarranyurk, Warracknabeal, Watchem and Wycheproof.
- Stage 3 restrictions continued (from February 2003) at Ararat, Birchip, Donald, Glenorchy, Great Western, Halls Gap, Horsham, Jeparit, Minyip, Murtoa, Noradjuha, Pimpinio, Pomonal, St Arnaud, Stawell and Reids (Taits) Lane
- Stage 3 restrictions continued (from November 2003) at Antwerp, Brim, Lascelles, Rupanyup, Woomelang, and Yaapeet.
- Restrictions were increased to Stage 4 (of a five stage system) at Natimuk, Clear Lake, Jung and Dimboola in October 2005.
- Stage 3 restrictions were lifted at Lalbert in January 2005 as a result of the source for the town water supply being changed to the Murray River via the Cannie ridge pipeline system.
In terms of non-urban water restrictions, the 2004-05 summer domestic and stock channel run was limited to the filling of one dam per 250 ha, while the 2005 winter channel run filled only one dam for every 400 ha. Supply-by agreement customers’ allocation for 2004-05 was also low at 40%, while the seasonal allocation to irrigators in the Wimmera basin was approximately 8% of entitlement. Rainfall in 2005-05 in the Wimmera River water management area was close to the long term annual average (Figure 2 and Table 1). Annual streamflow was much lower than the long term average (Figure 4).
Table 1 Summary of Wimmera River water management area contextual information
| Rainfall1 |
|
| Total rainfall 2004-2005 |
418mm |
|
Average annual rainfall for period of record |
438mm |
|
Average annual rainfall 1994-2005 |
402mm |
| Total evapotranspiration2 |
|
|
Evapotranspiration 2004-05 |
391mm |
| Water restrictions in 2004-053 |
|
|
Irrigation / Other |
8% of entitlement |
|
Town water supplies |
Numerous restrictions ranging from level 2 to level 4 |
| Entitlement volumes4 |
|
|
Surface water entitlement volume 2004-05 |
222,600 ML |
|
Ground water entitlement volume 2004-05 |
1,522 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)
|

Figure 2 Annual rainfall for the Wimmera River water management area (modified from BOM, 2006)

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

Figure 4 Streamflow hydrograph for the Wimmera River water management area for the Wimmera River at Glenorchy Weir Tail Gauge (gauge 415201)
Summary of the total water resources in the basinThe total volumes of water available and supplied from water resources in the Wimmera basin are shown in Table 2.
Table 2 Summary of water balance in the Wimmera River water management area, 2004-05
| Captured Rainfall (or total available water, or rainfall for storage) |
73900
(runoff) |
359988
(recharge) |
433888 |
| Evapotranspiration |
14200 |
0 |
14200 |
| Returns from the economy (includes treated effluent) |
0 |
103457 |
103457 |
| Extraction & Diversions |
101080 |
737 |
101817 |
| Losses |
111500 |
0 |
111500 |
| GW/SW Interaction Volume |
-7200 |
0 |
0 |
| Transfers In |
32500 |
0 |
32500 |
| Transfers Out |
0 |
0 |
0 |
|
Inflows from other entities |
0 |
0 |
0 |
| Outflows to other entities |
1240 |
0 |
1240 |
|
Error Term |
110970
|
-469908
|
-358938
|
|
(error as % of inflows) |
51% |
-100% |
-52% |
| Opening Storage capacity |
|
|
|
| - major storages |
65740 |
|
65740 |
| - farm dams |
0 |
|
0 |
| - other |
0 |
0 |
0 |
| Closing Storage capacity |
|
|
|
| - major storages |
47890 |
|
47890 |
| - farm dams |
0 |
|
0 |
| - other |
0 |
0 |
0 |
|

Figure 6 Water balance summary for Wimmera River water management area
Outcomes from the water cycle reportThe following information becomes apparent from Table 2. - There was a significant decline in the volume of water stored (27%), as streamflows were well below long term averages.
- The unaccounted for errors were relatively large due to significant volumes of unaccounted for groundwater outflows and surface water inflows (errors of 100% and 51% respectively). The error in the groundwater balance is likely to be due to no information being available on baseflow.
- Data accuracy for the groundwater usage estimates was low. For instance, groundwater recharge in the Wimmera River water management area is understood to be quite low, however the BRS Water 2010 estimate of deep drainage of 359,988 ML is quite high.
- Water use was predominantly from surface water resources.
- In May 2004, a Bulk Entitlement of 32,240 ML was granted to the Minister for Environment for the Wimmera and Glenelg rivers. This is the environment’s share of water savings from the Northern Mallee Pipeline Scheme which was completed in 2003. While annual allocations to the environment were made as the pipelining progressed, the first formal allocations under the Bulk Entitlement came into force on 1st November 2004. A total of 11,987 ML was allocated to the Glenelg and Wimmera Rivers during the 2004-05 flow season (1st November 2004 – 30th October 2005). The Inter Catchment Advisory Group (ICAG) met to determine the split of environmental allocation between catchments. As a result of these negotiations, the Wimmera River received 5,954 ML in 2004-05, whilst 4,433 ML was carried over in storage for future use.
- In 2004-05 the environments’ share of the total flow in the Wimmera Basin was 10%.
- 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 the Wimmera River the volume was 7,200 ML.
- Information on start and end of season storage volumes was not available, however it was estimated that 22,900 ML was harvested and 14,400 ML used in the 2004-05 season from small catchment dams.
- There was a decline in water availability, largely due to inflows for the period being 23% of the long term average of 316,400 ML (DSE, 2006).
- 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:Wimmera 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 A, indicating that the majority of the data was of a high standard. However, 50% 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 ±57% (between a C and D rating).
Table 3 Summary of Wimmera River water management area data reliability
| A (+/- 10%) |
28 |
232350 |
51.86 |
| B (+/- 25%) |
1 |
73900 |
16.49 |
| C (+/- 50%) |
9 |
141800 |
31.65 |
| D (+/- 100%) |
5 |
0 |
0.00 |
| E (no data) |
30 |
- |
- |
| F (no data currently available) |
0 |
- |
- |
| Not applicable |
10 |
- |
- |
|
Total |
83 |
448050 |
|
| WMA reliability index |
±58% |
|
|
|
Water balance error (%) |
-52% |
|
|
|
| |
The estimate of regional water consumption as prepared by the Australian Bureau of Statistics (ABS) includes water use within the Avoca River, Mallee, and Wimmera River Surface Water Management Areas
Estimated water consumption is 209,662 ML
Agriculture comprises approximately 59% of total water consumption; Other comprises approximately 35% of total water consumption; Household comprises approximately 5% of total water consumption; Mining and Manufacturing comprise 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
Wimmera River
SWMA
This page provides a summary of the results of the National Framework for the Assessment of River and Wetland Health (FARWH) for the Wimmera River water management area. Table 4 Results of the National Framework for the Assessment of River and Wetland Health (FARWH) for the Wimmera River water management area
|
Biota
|
0.77 |
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 |
0.59 |
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 |
0.7 |
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 |
0.53 |
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 |
|
Insufficient water quality data were available to report on for this water management area. |
|
Fringing Zone |
0.54 |
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 |
0.58 |
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 8 Results of the National Framework for the Assessment of River and Wetland Health (FARWH) for the Wimmera River 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
Wimmera 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: |
118400 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? |
Overallocated |
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) |
43% |
|
Are there formal environmental water provisions for regulated rivers? |
Yes |
|
If so, what method was used to determine environmental water provisions for regulated
rivers? |
Flows to mimic natural flows of the system (ie including minimum flows, pulse flows & flood flows at different times of the year) |
|
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? |
85 % |
|
What is the level of diversions relative to the sustainable yield? |
High level of diversions (70 - 100%) |
|
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 |
0.14 |
|
Managed resource protected areas |
0.14 |
|
National park |
8.79 |
|
Natural monument |
0.01 |
|
Protected landscape/seascape |
- |
|
Strict nature reserve |
1.88 |
|
Wilderness area |
0.62 |
|
Total |
11.57 |
Related links
The links below provide access to similar data reports for groundwater management
units (GMUs) that overlap this surface water management area (SWMA).
|
|