Murray–Darling Basin
Water access and use
Water rights, entitlements, allocations and restrictions
a. Introduction
This note provides information about the water access rights granted by jurisdictions to the users of the Murray–Darling Basin (MDB) region's water resources and the associated allocation announcements, diversions, adjustments, and forfeitures. Information about restrictions to water access rights is available through links provided to relevant line items in this note.
High-level information on legislative, administrative and governing arrangements of surface water rights in the MDB region is available under Water entitlements in 'Water rights' in the 'Contextual information'.
Other arrangements, contracts, or inter-basin agreements that may or may not result in the creation of water assets and water liabilities are not reported here but in the Surface water and Groundwater notes, depending on which water resource or system they affect.
The 2013 Account acknowledges the varying jurisdictional legislative water resource management frameworks related to Australian rights to water that support water resource management in Australia. The jurisdictional legislative water resource management frameworks vary greatly between jurisdictions, sometimes making comparisons difficult. To facilitate meaningful comparison between the water accounting reports included in the 2013 Account, the Bureau of Meteorology (the Bureau) has developed and applied an accounting concept to classify and report water rights within a water-asset/water-liability framework.
According to that framework, surface water rights are categorised broadly into:
- water rights that may not create a water liability: 32.1 Other statutory surface water rights and 32.2 Surface water access entitlement for non-allocated diversions
- water rights that may create a water liability: 32.3 Surface water access entitlement for allocated diversions.
Groundwater rights are categorised broadly into:
- water rights that may not create a water liability: 33.1 Other statutory groundwater rights and 33.2 Groundwater access entitlement for non-allocated extractions (no information available for the MDB region)
- water rights that may create a water liability: 33.3 Groundwater access entitlement for allocated extractions.
b. Surface water rights
Summarised information on surface water rights, allocation, abstraction, adjustments, and forfeiture of allocated water is presented in tables 1–3 for the 2012–13 year for the region. Allocation announcement, allocation diversion, adjustments, forfeiture, and carry-over are all linked together. Tables 1–3 do not include carry-over information, which is available in line items 5.1 Surface water allocation remaining and 5.2 Surface water allocation remaining – urban water system. Table 4 provides a breakdown of surface water rights for all categories relevant to the region on water resource plan (WRP) area basis.
Unregulated (called 'unsupplemented' in Queensland) entitlements have been categorised under line item 32.2 Surface water access entitlement for non-allocated diversions. Regulated (called 'supplemented' in Queensland) entitlements have been categorised under line item 32.3 Surface water access entitlement for allocated diversions. See the National Water Account Glossary for definitions of regulated, unregulated, entitlements or other terms used in this note.
The following jurisdiction-specific characteristics apply to the information presented in tables 1–3:
- In Queensland: entitlement giving access to unregulated (unsupplemented) flows may report either the volumetric limit (the maximum volume of water that can be abstracted over a given period), or the nominal volume (for water allocations with flow conditions, the nominal volume approximates the long-term annual average volume of accessible water for the entitlement).
- In Queensland: entitlement giving access to regulated (supplemented) flows may report the nominal volume, against which allocations are announced.
- In New South Wales: entitlements giving access to unregulated flows may report the entitled volume, which specifies an upper limit to the volume of water that can be abstracted over a given period; in case the entitlement exists within a water sharing plan (commenced or in draft), as defined under the New South Wales Water Act 2000 (the Water Act), that period is 12 months, and in case the entitlement exists within an area that is still under the Water Act, and consequently has no water sharing plan, that period can be 12 months or several years. The actual duration of the period is unspecified in the table, as the data source used was the water audit monitoring (WAM) report, which did not contain this information.
- In New South Wales: entitlement giving access to regulated flows may report the entitled volume, against which allocations are announced.
- In Victoria: entitlements giving access to unregulated flows may report the entitled volume, which specifies an upper limit to the volume of water that can be abstracted over a 12-month period.
- In Victoria: entitlement giving access to regulated flows may report the entitled volume, against which allocations are announced.
- In South Australia: all entitlements have been classified as giving access to regulated flow and may report the entitled volume, against which allocations are announced.
Details of the information presented in the following tables and information on water restrictions can be accessed through the links provided.
Water rights (at 30 June 2013) | Water allocation (the 2012–13 year) |
Water abstraction/use (the 2012–13 year) |
Forfeiture, adjustment (the 2012–13 year) |
||||
Account line item | Volume (ML) |
Account line item |
Volume (ML) |
Account line item |
Volume (ML) |
Account line item |
Volume (ML) |
32.1 Other statutory surface water rights | 37,687 |
n/a |
n/a |
17.6 |
37,687 |
n/a |
n/a |
32.2 Surface water access entitlement for non-allocated diversions |
3,666,452 |
n/a |
n/a |
17.7 |
1,398,405 |
n/a |
n/a |
n/a |
n/a |
17.8 |
4,177 |
n/a |
n/a |
||
32.3 Surface water access entitlement for allocated diversions(non-urban) |
1,965,208 |
21.1 |
825,265 |
17.11 |
1,437,049 |
13.1 |
112,563 |
32.3 Surface water access entitlement for allocated diversions (urban) |
42,487 |
21.2 |
42,492 |
17.12 |
21,563 |
13.2 |
20,929 |
Total |
5,711,834 |
Total |
867,757 |
Total |
2,898,881 |
Total |
133,492 |
Water rights (at 30 June 2013) | Water allocation (the 2012–13 year) |
Water abstraction/use (the 2012–13 year) |
Forfeiture, adjustment (the 2012–13 year) |
||||
Account line item | Volume (ML) |
Account line item |
Volume (ML) |
Account line item |
Volume (ML) |
Account line item |
Volume (ML) |
32.1 Other statutory surface water rights | 30,523 |
n/a |
n/a |
17.6 |
30,523 |
n/a |
n/a |
32.2 Surface water access entitlement for non-allocated diversions |
1,170,762 |
n/a |
n/a |
17.7 |
668,541 |
n/a |
n/a |
n/a |
n/a |
17.8 |
8,896 |
n/a |
n/a |
||
32.3 Surface water access entitlement for allocated diversions(non-urban) |
9,993,667 |
21.1 |
6,933,312 |
17.11 |
7,407,128 |
13.1 |
1,894,975 |
32.3 Surface water access entitlement for allocated diversions (urban) |
560,381 |
21.2 |
496,545 |
17.12 |
344,035 |
13.2 |
152,510 |
Total |
11,755,333 |
Total |
7,429,857 |
Total |
8,459,123 |
Total |
2,047,485 |
Water rights (at 30 June 2013) | Water allocation (the 2012–13 year) |
Water abstraction/use (the 2012–13 year) |
Forfeiture, adjustment (the 2012–13 year) |
||||
Account line item | Volume (ML) |
Account line item |
Volume (ML) |
Account line item |
Volume (ML) |
Account line item |
Volume (ML) |
32.1 Other statutory surface water rights | 68,210 |
n/a |
n/a |
17.6 |
68,210 |
n/a |
n/a |
32.2 Surface water access entitlement for non-allocated diversions |
4,837,214 |
n/a |
n/a |
17.7 |
2,066,946 |
n/a |
n/a |
n/a |
n/a |
17.8 |
13,073 |
n/a |
n/a |
||
32.3 Surface water access entitlement for allocated diversions (non-urban) |
11,958,875 |
21.1 |
7,758,577 |
17.11 |
8,844,177 |
13.1 |
2,007,538 |
32.3 Surface water access entitlement for allocated diversions (urban) |
602,868 |
21.2 |
539,037 |
17.12 |
365,598 |
13.2 |
173,439 |
Total |
17,467,167 |
Total |
8,297,614 |
Total |
11,358,004 |
Total |
2,180,977 |
Surface water resource plan area | Jurisdiction |
Basic rights (ML) |
Entitlements for non-allocated diversion1 |
Entitlements for allocated diversion2 |
Total3 (ML) |
||||
Unregulated entitlements (excluding supplementary and environmental entitlements) (ML) |
Supplementary (excluding environmental entitlements) entitlements (ML) |
Environmental (unregulated and supplementary) entitlements (ML) |
Non-urban (ML) |
Urban (ML) |
Environmental (ML) |
||||
SW20 Warrego–Paroo–Nebine | Qld | – |
94,429 |
0 |
21,970 |
2,612 |
0 |
0 |
119,011 |
SW19 Condamine–Balonne | Qld | – |
1,830,143 |
0 |
49,605 |
114,981 |
0 |
0 |
1,994,729 |
SW18 Moonie | Qld | – |
75,065 |
0 |
1,415 |
0 |
0 |
0 |
76,480 |
SW17 Queensland Border Rivers | Qld | – |
399,295 |
0 |
4,286 |
92,555 |
0 |
11,684 |
507,820 |
SW16 NSW Border Rivers | NSW | 10,373 |
32,421 |
120,001 |
0 |
265,442 |
620 |
298 |
429,155 |
SW12 Barwon–Darling watercourse | NSW | 825 |
158,827 |
0 |
25,575 |
0 |
0 |
0 |
185,227 |
SW13 NSW Intersecting Streams | NSW | 2,456 |
18,843 |
0 |
17,826 |
0 |
0 |
0 |
39,125 |
SW15 Gwydir | NSW | 9,555 |
62,923 |
157,807 |
22,240 |
420,295 |
3,836 |
108,241 |
784,897 |
SW14 Namoi | NSW | 6,071 |
129,552 |
115,469 |
0 |
286,409 |
19,186 |
7,212 |
563,899 |
SW11 Macquarie–Castlereagh | NSW | 8,407 |
278,720 |
46,700 |
3,340 |
490,950 |
18,845 |
164,529 |
1,011,491 |
Sub-total Northern Basin | 37,687 |
3,080,218 |
439,977 |
146,257 |
1,673,244 |
42,487 |
291,964 |
5,711,834 |
|
SW10 Lachlan | NSW | 10,697 |
53,386 |
3,125 |
0 |
547,559 |
15,545 |
139,430 |
769,742 |
SW9 Murrumbidgee | NSW | 10,806 |
81,059 |
165,543 |
33,237 |
2,226,652 |
43,585 |
472,026 |
3,032,707 |
SW8 NSW Murray and Lower Darling | NSW | 9,020 |
45,889 |
152,368 |
363,021 |
1,782,460 |
46,827 |
516,459 |
2,916,582 |
SW3 Northern Victoria | Vic. | – |
147,692 |
0 |
0 |
1,291,580 |
97,960 |
455,293 |
1,992,525 |
SW2 Victorian Murray | Vic. | – |
49,090 |
0 |
74,300 |
1,364,620 |
58,154 |
452,998 |
1,999,162 |
SW4 Wimmera–Malee | Vic. | – |
0 |
0 |
0 |
30,960 |
47,310 |
69,560 |
147,830 |
SW5 and SW7 SA Murray Region and Eastern Mount Lofty Ranges | SA | – |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
SW6 South Australian River Murray | SA | – |
0 |
0 |
0 |
498,191 |
180,000 |
145,879 |
824,070 |
SW1 ACT | ACT | – |
2,052 |
0 |
0 |
0 |
71,000 |
0 |
73,052 |
Sub-total Southern Basin | 30,523 |
379,168 |
321,036 |
470,558 |
7,742,022 |
560,381 |
2,251,645 |
11,755,333 |
|
Total for the region | 68,210 |
3,459,386 |
761,013 |
616,815 |
9,415,266 |
602,868 |
2,543,609 |
17,467,167 |
Note
– = Data not available
1 Water rights that may not create a water liability (includes basic rights and entitlements associated with unregulated flows and New South Wales supplementary licences)
2 Water rights that may create a water liability (includes entitlements associated with allocation diversion)
3 Entitlements with different reliabilities have been added to form the values in the Total column
c. Groundwater rights
Summarised information on groundwater rights, allocation, abstraction, adjustments, and forfeiture of allocated water is presented in tables 5–7 for the 2012–13 year for the region. Allocation announcement, allocation abstraction and use, adjustments, forfeiture and carry-over are all linked together. Tables 5–7 do not include carry-over information, which is available in line items 6.1 Groundwater allocation remaining and 6.2 Groundwater allocation remaining – urban water system.
In the tables, water right volumes for non-urban, urban and supplementary groundwater access entitlements are included under 33.3 'Groundwater access entitlement for allocated extractions'. No information is provided in the tables under line item 33.2 'Groundwater access entitlement for non-alloacted extractions' (entitlement or other arrangement that may not produce a groundwater liability). This is because all available entitlement information was provided under line item 33.3 assuming entitled volume is a liability even there was no formal allocation announcement.
Table 8 provides a breakdown of groundwater rights for all categories relevant to the region on Groundwater resource plan area basis.
Water rights (at 30 June 2013) |
Water allocation (the 2012–13 year) |
Water abstraction/use (the 2012–13 year) |
Forfeiture, adjustment (the 2012–13 year) |
||||
Account line item | Volume (ML) |
Account line item |
Volume (ML) |
Account line item |
Volume (ML) |
Account line item |
Volume (ML) |
33.1 Other statutory groundwater rights | 51,769 |
n/a |
n/a |
18.7 |
74,329 |
n/a |
n/a |
33.3 Groundwater access entitlement for allocation extraction | 564,231 |
22.1 |
661,110 |
18.11 |
361,731 |
14.1 |
299,379 |
22.2 |
27,350 |
18.12 |
13,021 |
14.2 |
14,329 |
||
Total | 616,000 |
Total |
688,460 |
Total |
449,082 |
Total |
313,708 |
Water rights (at 30 June 2013) |
Water allocation (the 2012–13 year) |
Water abstraction/use (the 2012–13 year) |
Forfeiture, adjustment (the 2012–13 year) |
||||
Account line item | Volume (ML) |
Account line item |
Volume (ML) |
Account line item |
Volume (ML) |
Account line item |
Volume (ML) |
33.1 Other statutory groundwater rights | 156,087 |
n/a | n/a |
18.7 | 156,087 |
n/a | n/a |
33.3 Groundwater access entitlement for allocation extraction | 1,725,306 |
22.1 | 1,485,883 |
18.11 | 580,611 |
14.1 | 905,863 |
22.2 | 41,466 |
18.12 | 24,003 |
14.2 | 17,463 |
||
Total | 1,881,392 |
Total | 1,527,349 |
Total | 760,701 |
Total | 923,326 |
Water rights (at 30 June 2013) | Water allocation (the 2012–13 year) |
Water abstraction/use (the 2012–13 year) |
Forfeiture, adjustment (the 2012–13 year) |
||||
Account line item | Volume (ML) |
Account line item |
Volume (ML) |
Account line item |
Volume (ML) |
Account line item |
Volume (ML) |
33.1 Other statutory groundwater rights | 207,855 |
n/a | n/a |
18.7 | 230,416 |
n/a | n/a |
33.3 Groundwater access entitlement for allocation extraction | 2,289,537 |
22.1 | 2,146,993 |
18.11 | 942,343 |
14.1 | 1,205,242 |
22.2 | 68,816 |
18.12 | 37,024 |
14.2 | 31,792 |
||
Total | 2,497,392 |
Total | 2,215,809 |
Total | 1,209,782 |
Total | 1,237,034 |
Groundwater resource plan area | Jurisdiction |
Other statutory groundwater rights1 (ML) |
Entitlements2 |
Total (ML) |
||
Non-urban (ML) |
Urban (ML) |
Supplementary3 (ML) |
||||
GW18 New South Wales Border Rivers Alluvium | NSW | 380 | 17,435 | 45 | 0 | 17,860 |
GW17 New England Fractured Rock and Northern Basalts | NSW | 17,961 | 11,531 | 562 | 0 | 30,054 |
GW16 Eastern Porous Rock | NSW | 6,243 | 19,930 | 420 | 0 | 26,593 |
GW 15 Gwydir Alluvium | NSW | 773 |
30,048 |
3,632 |
13,930 |
48,383 |
GW 14 Namoi Alluvium | NSW | 10,489 |
260,945 |
11,706 |
58,657 |
341,797 |
GW13 New South Wales Great Artesian Basin Shallow | NSW | 3,268 |
5,694 |
50 |
0 |
9,012 |
GW 12 Macquarie–Castlereagh Alluvium | NSW | 2,220 |
114,231 |
11,280 |
2,396 |
130,127 |
GW 11 Lachlan and South Western Fractured Rock | NSW | 8,154 |
1,519 |
0 |
0 |
9,673 |
GW7 Darling Alluvium | NSW | 2,281 |
0 |
220 |
0 |
2,501 |
Sub-total Northern Basin | 51,769 |
461,333 |
27,915 |
74,983 |
616,000 |
|
GW 11 Lachlan and South Western Fractured Rock | NSW | 79,524 |
85,551 |
3,076 |
0 |
168,151 |
GW7 Darling Alluvium | NSW | 730 |
928 |
0 |
0 |
1,658 |
GW 10 Lachlan Alluvium | NSW | 10,316 |
283,480 |
9,900 |
21,238 |
324,934 |
GW 9 Murrumbidgee Alluvium | NSW | 4,824 |
331,080 |
27,914 |
41,196 |
405,014 |
GW 8 Murray Alluvium | NSW | 3,550 |
212,297 |
1,822 |
47,782 |
265,451 |
GW6 Western Porous Rock | NSW | 26,747 |
32,272 |
0 |
0 |
59,019 |
GW 2 Goulburn–Murray | Vic | 24,778 |
450,886 |
n/a | n/a | 475,664 |
GW 3 Wimmera–Mallee (groundwater) | Vic | 2,488 |
91,956 |
n/a | n/a | 94,444 |
GW 5 Eastern Mount Lofty Ranges | SA | 270 |
11,156 |
0 |
0 |
11,426 |
GW 4 South Australian Murray Region | SA | 2,860 |
71,821 |
0 |
0 |
74,681 |
GW1 Australian Capital Territory (groundwater) | ACT | 0 |
951 |
0 |
0 |
951 |
Sub-total Southern Basin | 156,087 |
1,572,378 |
42,712 |
110,216 |
1,881,392 |
|
Total for the region | 207,855 |
2,033,711 |
70,627 |
185,199 |
2,497,392 |
Notes
1 Other statutory groundwater rights are an estimate of the rights existing at the commencement of the management plans in New South Wales. Volumes from other states were not available for this table. The rights enable individuals to abstract water for stock and domestic purposes where licences are not normally formally issued for these rights.
2 Licensed entitlements include all licences issued under the respective management plans, excluding New South Wales supplementary licenses. Volumes from Australian Capital Territory or Queensland were not available for this table.
3 Supplementary licenses are a category of licence within New South Wales only, where it has already been established that the total volume being extracted from the aquifer needs to be reduced. These licenses have reducing allocations to zero over the life of the management plans.
d. Combined surface water and groundwater rights
For the 2012–13 year, combined surface water and groundwater access entitlements were available in the Australian Capital Territory within the Southern Basin of the MDB region. There were 39 active entitlements with a total volume of 2,508 ML that may abstract water from either groundwater or surface water in the Australian Capital Territory.
e. Landscape water rights
Runoff harvesting entitlements are the water rights under which landscape runoff is harvested into Off-channel water storages (line item 27.1 Off-channel water storages). Reliable information on runoff harvesting entitlement volumes was not available for inclusion in the water account. Information on volume of water diverted under these entitlements during the 2012–13 year is available in line item 30.3 Runoff harvesting into off-channel water store and in the Off-channel storages note.
Following is an explanation of the different terms used within the MDB and how each jurisdiction manages runoff that may be harvested from the land, thus preventing it from reaching a watercourse.
Queensland
Queensland uses the term overland flow. Overland flow is water that runs across the land after rainfall, either before it enters a watercourse, after it leaves a watercourse as floodwater, or after it rises to the surface naturally from underground. Most water in rivers and underground reserves originates as overland flow. If too much water is intercepted before it reaches a watercourse, or if too much floodwater is intercepted before it returns to a watercourse, there can be serious implications for:
- towns, industries and farms that rely on watercourses for water supplies
- landholders who rely on beneficial flooding
- the maintenance of healthy waterways
- groundwater recharge
- ecosystems relying on periodic inundation.
A person may harvest overland flow for any purpose unless there is a moratorium notice, a water resource plan or wild river declaration that limits or alters the water that may be harvested. Rules in water resource plans established under the Queensland Water Act 2000regulate the building of works that harvest overland flow either actively or passively.
Works that harvest overland flow actively include:
- pumps, storages, sumps, drains and pipes used to harvest and store it
- any storage connected to another one used to harvest it, and the connecting infrastructure
- structures used to hold it for ponded pastures.
Works that harvest overland flow passively include:
levees or diversion banks used to direct it into dams, or to slow it down to increase the amount harvested. This does not include works used in soil conservation.
Water resource plans do not regulate works that interfere with, but were not built specifically to harvest overland flow; however, local planning laws may still regulate the building of these structures which include:
- contour banks
- fences
- roads.
Where the construction of overland flow works is regulated, the development may be either assessable or self-assessable development under the Queensland Sustainable Planning Act 2009. Currently, the harvesting of overland flow is regulated in the following water resource plan areas:
- Border Rivers
- Condamine and Balonne
- Moonie
- Warrego, Paroo and Nebine.
In all of these areas, it is required to have:
- an authorisation to harvest overland flow for purposes other than stock and domestic
- a development permit under the Queensland Sustainable Planning Act 2009 for most works for harvesting overland flow.
New South Wales
Landholders in most New South Wales rural areas are allowed to collect a proportion of the rainfall runoff on their property and store it in one or more dams up to a certain size. This is known as a harvestable right. Harvestable right water is generally intended for essential stock and household use but can be used for any purpose.
All rural landholders in New South Wales are able to maintain or build farm dams. There are several categories of farm dams that do not require a licence:
- harvestable right dams
- dams built before 1999 used only for stock and domestic purposes
- dams up to one mega litre on small properties.
In addition to rainfall runoff harvesting, New South Wales has addressed floodplain harvesting. Floodplain harvesting is the collection, abstraction or impoundment of water flowing across floodplains.
Harvesting of on-farm rainfall runoff is not included within the definition of floodplain harvesting; however, because rainfall runoff can be harvested by the same infrastructure as floodplain abstractions, it is important to specify the regulatory distinction between the two types of water abstraction. All rainfall runoff harvesting must be in accordance with the harvestable rights order by which the area is constituted as provided for under Chapter 3, Part 1, Division 2 of the New South Wales Water Management Act 2000. Within most of New South Wales, the allowable maximum harvestable right is currently 10% of average annual runoff. The runoff is primarily a function of rainfall, evaporation, soil type, topography, and vegetation cover. The allowable runoff harvesting volume is converted to a maximum harvestable right dam capacity, using a publicly available, web-based calculator. The allowable harvestable right volume of runoff will be assumed to have been abstracted and will be factored into the assessment of floodplain harvesting abstractions.
New South Wales Floodplain Harvesting Policy (NSW Office of Water 2013) outlines how floodplain harvesting abstractions will be managed within long-term average annual abstraction limits under water sharing plans and the Murray–Darling Basin Ministerial Council Cap where applicable. There will be no growth in overall abstractions on a valley-wide basis as a result of the implementation of this policy. All floodplain harvesting activities will require a water supply work approval and a floodplain harvesting water access licence issued under the New South Wales Water Management Act 2000.
Victoria
The Northern Region Sustainable Water Strategy for Victoria discusses the impacts of interception activities. Interception activities are a risk to water availability because they capture rainfall before it becomes surface runoff or groundwater recharge. These activities include small catchment dams (for farms or domestic and stock use), changes in land use and the impact of forest regeneration due to bushfires. These activities have not historically required a water entitlement (except for small catchment dams for irrigation or commercial purposes, which have required a licence since 2002); however, they can reduce the amount of water available to downstream entitlement holders and the environment.
Unlike dams for commercial and irrigation use, dams for domestic and stock use are not licensed and therefore can continue to be built without scrutiny of their impact on downstream users and the environment. In Victoria, rights to water for domestic and stock use (private rights) are specified in Section 8 of the Victorian Water Act 1989. Under this section, people are able to access water without a formal entitlement and free of charge under specific arrangements in the Victorian Water Act 1989. This includes farm dams for domestic and stock purposes.
Based on current estimates, unlicensed dams capture six per cent of the available runoff generated by landscape in northern Victoria. At a local level, the impact of unlicensed dams can be even greater.
Several actions have been highlighted in the Northern Region sustainable water strategy to manage the impacts of stock and domestic use. Some key actions will be:
- requiring the registration of all new or altered domestic and stock dams within rural residential areas and promoting sustainable use in accordance with guidelines for reasonable domestic and stock use;
- monitoring growth in domestic and stock use
- clarifying the need to obtain a Section 51 licence for harvesting water for uses other than domestic and stock purposes.
South Australia
The South Australia Government's Water for Good strategy identifies a number of projects to increase the volume of water collected from stormwater harvesting, both within Adelaide and in rural South Australia. These projects involve storing and treating stormwater in wetlands and aquifers to improve water quality. Only a small number of such projects are within the South Australian MDB region. Landscape water rights within the South Australian MDB region include water access entitlements in the Marne Saunders and Eastern Mount Lofty Ranges for water flowing over the land, whether modified or not, excluding water contained in a watercourse.
Australian Capital Territory
The Australian Capital Territory government's Think Water Act Water strategy (Australian Capital Territory Government 2011b) for sustainable water resource management in the Australian Capital Territory, outlines actions the Australian Capital Territory government plans to improve management of stormwater runoff, including adopting water sensitive urban design principles.
f. Water restrictions
Table 9 provides information on water restrictions applicable during the 2012–13 year for different entitlement classes within the region.
Sustainable diversion limit area | Entitlement class |
State/Territory |
Details of water restriction |
|
Code | Name |
|||
SS15 | Murrumbidgee NSW | High security – urban and local water utility | NSW | Restrictions for urban water supply related to urban entitlements were at the discretion of local urban councils. Details of implemented restrictions were not available at the data collection stage for the 2013 Account. |
SS14 | NSW Murray | High security – urban and local water utility | NSW | Restrictions for urban water supply related to urban entitlements were at the discretion of local urban councils. Details of implemented restrictions were not available at the data collection stage for the 2013 Account. |
SS4 | Ovens | Urban bulk entitlements – regulated | Vic. | Town supplies are restricted by the Victorian permanent water savings rules. |
SS5 | Broken | Urban bulk entitlements – Broken | Vic. | Town supplies are restricted by the Victorian permanent water savings rules. |
SS6 | Goulburn | Urban bulk entitlements: Goulburn 'channel', Goulburn to Coliban and Goulburn 'river' | Vic. | Town supplies are restricted by the Victorian permanent water savings rules. |
SS7 | Campaspe | Urban and rural bulk entitlements: Coliban, Campaspe 'channel' and Campaspe regulated river | Vic. | Town supplies are restricted by the Victorian permanent water savings rules. |
SS8 | Loddon | Urban bulk entitlements – Loddon | Vic. | Town supplies are also restricted by the Victorian permanent water savings rules. |
SS2 | Victorian Murray | Urban bulk entitlements – regulated | Vic. | Town supplies are also restricted by the Victorian permanent water savings rules. |
SS9 | Wimmera–Mallee | High reliability water share | Vic. | Town supplies are also restricted by the Victorian permanent water savings rules. |
SS11 | SA Murray | Class 2 – SA country towns and Class 6 – metropolitan Adelaide and associated country areas) | SA | Permanent water savings conservation measures came into effect from 1 December 2010. |
SS1 | ACT | ACTEW Water – reservoir extractions | ACT | Due to minimal inflows and low storage volumes, restrictions operated for this class of entitlement. Stage 2 water restrictions were lifted in the ACT on 1 November 2010 and have been replaced by permanent water conservation measures. |
Information on limitations related to available water for New South Wales sustainable diversion limit areas is available in New South Wales Office of Water's Available water determinations 2012–13 (NSW Office of Water 2014b).
Information on limitations on allocations for high and low reliability water shares (non-urban use) in Victorian sustainable diversion limit areas in 2012–13 is available in Victorian Department of Environment and Primary Industries' Monthly water Reports (Department of Environment and Primary Industries 2014a).
For the sustainable diversion limit areas not included in the above table, water restriction information is not available.
Water market activity
This note reports on water market activities that occurred in the MDB region during the 2012–13 year.
Both surface water and groundwater trade is reported for the MDB Region during the 2012–13 year. The following information on water trades is included in this note:
- approved permanent trade of surface water and groundwater entitlements
- approved lease of surface water and groundwater entitlements
- approved trade of surface water and groundwater allocations
- impact of inter-valley trade on regions' water assets and liabilities.
During the 2012–13 year, no water was traded into or out of the MDB region.
Table 10 summarises entitlement and allocation surface water and groundwater trade within the MDB region during the 2012–13 year.
Line item | Volume (ML) |
||
Northern Basin |
Southern Basin |
Whole region |
|
Surface water entitlement trade | |||
35.1 Trade of surface water entitlement within region | 350,079 |
611,255 |
961,334 |
35.2 Trade of surface water entitlement into region | 0 |
0 |
0 |
35.3 Trade of surface water entitlement out of region | 0 |
0 |
0 |
Surface water entitlement lease | |||
36.1 Lease of surface water entitlement within region | 0 |
19,433 |
19,433 |
Surface water allocation and tagged trade | |||
37.1 Surface water allocation trade within region |
565,923 |
5,419,706 |
5,985,629 |
37.2 Surface water allocation trade into region | 0 |
0 |
0 |
37.3 Surface water allocation trade out of region | 0 |
0 |
0 |
Groundwater entitlement trade | |||
38.1 Trade of groundwater entitlement within region | 15,357 |
66,908 |
82,265 |
Groundwater entitlement lease | |||
39.1 Lease of groundwater entitlement within region | 0 |
0 |
0 |
Groundwater allocation and tagged trade | |||
40.1 Groundwater allocation trade within region | 14,681 |
60,177 |
74,858 |
– = Data not available
The volumes provided in the above table were based on data available at the sources (see line items 35.1 to 40.1 for data sources).
Surface water entitlement trade
Surface water entitlement trade for the MDB region was reported only under line item 35.1 Trade of surface water entitlement within region for the reporting year. This line item includes the volume of permanent entitlement sales within and between sustainable diversion limit (SDL) areas approved during the 2012–13 year. No entitlement water trade occurred between two segments (the Northern Basin and the Southern Basin) defined on the MDB region or between the segments and outside the region.
Surface water entitlement lease
Information on surface water entitlement lease for the MDB region was reported under line item 36.1 Lease of surface water entitlement within region for the reporting year. Seasonal water flow associated with lease of surface water entitlements is included in allocation and tagged trade within the region (in line item 37.1 Surface water allocation trade within region).
Surface water allocation trade
Surface water allocation trade for the MDB region was reported under line item 37.1 Surface water allocation trade within region for the reporting year. This line item includes the volume of allocation trade within and into (from other SDL areas) SDL areas, and within and out of (to other SDL areas) SDL areas. Allocation trade volumes provided in this note include tagged trade and environmental water trades.
No allocation trade occurred between the segments and outside the region. Trade of consumptive water (for the purposes irrigation, urban and industrial etc.) between the Southern Basin and the Northern Basin is prohibited.
The following table presents information on inter-state allocation trade during the 2012–13 year.
Purchased from | Purchased to (SDL area) |
Volume (ML) |
||
State | SDL area | State |
SDL area |
|
Qld | Qld Border Rivers | NSW | NSW Border Rivers | 500 |
NSW | NSW Border Rivers | Qld | Qld Border Rivers | 22,827 |
Vic. | Vic Murray | NSW | Lower Darling | 14,135 |
Vic. | Goulburn | NSW | Lower Darling | 633 |
Vic. | Loddon | NSW | Lower Darling | 104 |
Vic. | Vic Murray | NSW | Murrumbidgee NSW | 33,269 |
Vic. | Goulburn | NSW | Murrumbidgee NSW | 11,754 |
Vic. | Campaspe | NSW | Murrumbidgee NSW | 120 |
Vic. | Loddon | NSW | Murrumbidgee NSW | 422 |
Vic. | Vic Murray | NSW | NSW Murray | 79,927 |
Vic. | Goulburn | NSW | NSW Murray | 15,859 |
Vic. | Campaspe | NSW | NSW Murray | 650 |
Vic. | Loddon | NSW | NSW Murray | 2,748 |
SA | SA Murray | NSW | Lower Darling | 10,700 |
SA | SA Murray | NSW | Murrumbidgee NSW | 7,240 |
SA | SA Murray | NSW | NSW Murray | 7,751 |
NSW | Lower Darling | Vic. | Vic Murray | 1,555 |
NSW | Lower Darling | Vic. | Goulburn | 200 |
NSW | Lower Darling | Vic. | Loddon | 1,500 |
NSW | Murrumbidgee NSW | Vic. | Vic Murray | 10978 |
NSW | Murrumbidgee NSW | Vic. | Goulburn | 606 |
NSW | Murrumbidgee NSW | Vic. | Loddon | 253 |
NSW | NSW Murray | Vic. | Vic Murray | 34,198 |
NSW | NSW Murray | Vic. | Goulburn | 620 |
NSW | NSW Murray | Vic. | Loddon | 1,547 |
SA | SA Murray | Vic. | Vic Murray | 41,728 |
SA | SA Murray | Vic. | Goulburn | 7,857 |
SA | SA Murray | Vic. | Loddon | 4,243 |
NSW | Lower Darling | SA | SA Murray | 55,260 |
NSW | Murrumbidgee NSW | SA | SA Murray | 64,895 |
NSW | NSW Murray | SA | SA Murray | 293,577 |
Vic. | Vic Murray | SA | SA Murray | 578,705 |
Vic. | Goulburn | SA | SA Murray | 8,260 |
Vic. | Campaspe | SA | SA Murray | 1,638 |
Vic. | Loddon | SA | SA Murray | 2,253 |
Trading volumes include environmental trade volumes. Reliable data source for details of environmental trades was not available at the time of data collection for the 2013 Account.
Inter-state allocation trade shown in the above table during the 2012–13 year resulted in net inward movement of water for Queensland and South Australia and net outward movement for New South Wales and Victoria as shown in the following table. A similar trend of net allocation trade was observed for the 2011–12 year.
From | To |
Net allocation trade (ML) |
New South Wales | Queensland | 22,327 |
New South Wales | South Australia | 388,041 |
Victoria | New South Wales | 108,164 |
Victoria | South Australia | 537,028 |
During the 2012–13 year, no groundwater was traded into or out of the MDB region.
Table 10 above summarises entitlement and allocation groundwater trade within the MDB region during the 2012–13 year.
Groundwater entitlement trade for the MDB region was reported only under line item 38.1 Trade of groundwater entitlement within region for the reporting year. This line item includes the volume of permanent entitlement sales within and between groundwater sustainable diversion limit (SDL) areas approved during the 2012–13 year. No entitlement trade occurred between two segments (the Northern Basin and the Southern Basin) defined on the MDB region or between the segments and outside the region.
There was no lease of groundwater entitlement during the 2012–13 year (Table 10 and line item 39.1 Lease of groundwater entitlement within region).
Groundwater allocation trade for the MDB region was reported under line item 40.1 Groundwater allocation trade within region for the reporting year. This line item includes the volume of allocation trade within and into (from other SDL areas) SDL areas, and within and out of (to other SDL areas) SDL areas. Allocation trade volumes provided in this note include tagged trade trades. No allocation trade occurred between the segments and outside the region.
All water trades occurred within the boundaries of the MDB region and no water trade crossed the boundary between the northern and southern basins.
Nevertheless, water trades between different water resource planning areas of the MDB had a significant impact on the allocations announced, diverted, forfeited, and carried-over. This is reflected in the water assets and liabilities of the water resource plan area. These transactions are not reported in this note; however, movement of water as a result of those transactions has impacted on diversions volumes (reported in line items 17.11 Entitled diversion of allocated surface water to users and 17.12 Entitled diversion of allocated surface water to urban water system in the water accounting statements). Any water availability imbalances associated with the transactions have been considered in line items 21.1 Surface water allocation announcements and 21.2 Surface water allocation announcements – urban water system.
Impact of inter-valley trade on water assets and water liabilities
Water traded into or out of valleys within the MDB region impacts on the valleys' water assets and water liabilities in several ways including:
- creation of claims and obligations between valleys
- transfer of the obligation to deliver allocated water to the water users.
In the case of trade into a valley:
- when the trade transaction is approved, there is the creation of a claim (non-physical water asset) by the destination valley of the trade (i.e. where the purchaser is registered), against the source valley (i.e., where the seller is registered)
- delivery obligation is moved from the selling valley to buying valley
- when water is physically transferred to the destination valley, it decreases its claim (non-physical water asset) against the source valley.
Creation of claims and obligations between valleys
In the case of trade out of a valley, the reverse occurs:
- when the trade transaction is approved, there is the creation of an obligation (water liability) in the source valley of the trade towards the destination valley
- when water is physically transferred out of the source valley, it decreases its obligation (water liability) towards the destination valley.
Note that in both cases the inter-valley transfer may occur in a subsequent water year to the year to when the trade was approved. The inter-valley transfer may be cancelled by back-trade or the inter-valley transfer account may spill which cancels the obligation to the destination valley. For instance, water traded to South Australia up to 31 March in a water year is delivered from September to April in that water year in the same pattern of delivery as the remaining South Australian monthly diversion entitlements from the month following when the trade occurred to the end of April. Water traded from 01 April – 30 June is adjusted for over the following September–April.
Transfer of the obligation to deliver water to the users
When water is traded from a source valley to a destination valley, the obligation (water liability) to deliver the allocated water to the user is transferred from the source to the destination valley. The newly created liability in the destination valley will be settled when the allocated water is diverted by the purchaser of the water trade.
Water use
a. Economic, social and cultural benefit
Town water supplies are made for various purposes including residential needs, and industrial and commercial purposes. They have been categorised under the social benefit category, assuming their main purpose within the MDB region is to serve residential needs. With that assumption, water right or entitlement classes directly related to social and cultural benefits identified in the MDB region for the 2012–13 year were:
- surface water entitlements – high security – Aboriginal cultural
- surface water basic right – stock and domestic
- surface water entitlements – stock and domestic
- surface water entitlements – urban supplies
- surface water entitlements – high security – community and education
- groundwater basic right – stock and domestic
- groundwater entitlements – urban supplies.
It is also possible that water supplies made under entitlement categories other than stated in the above list have contributed to social and cultural benefits. The 2013 Account does not recognise those contributions.
Water supplies made under some of the entitlement classes relevant to the following entitlement categories have contributed to economic benefits:
- Surface water access entitlement for non-allocated diversions (line item 32.2)
- Surface water access entitlement for allocated diversions (line item 32.3)
- Groundwater access entitlement for allocated extractions (line item 33.3)
The 2013 Account does not recognise details of economic contributions made under the entitlement classes of those entitlement categories.
It is also possible that water supplies made under other statutory surface water and groundwater rights (line items 32.1 and 33.1) have contributed to economic benefits. The 2013 Account does not recognise those contributions.
The 2013 Account assumes that the water right/entitlement class represents its purpose; however, it is likely that people use water for other activities in addition to the intended purpose of the right/entitlement class. This is the case particularly in valleys where trade has been conducted. With trades, it is possible that water moved from different classes and changed the volume for the intended purpose. The 2013 Account provides information based on the class or categorisation of rights or entitlement, but it does not provide information about where or how water was finally used.
Cultural basic right allows abstraction of water by anyone who holds native title rights with respect to water, as determined under the Australian Government Native Title Act 1993. The right holders can abstract water for a range of needs without holding a water access licence. This includes accessing water for personal, domestic and non-commercial communal purposes such as:
- manufacture of traditional artefacts
- hunting, fishing, and gathering
- recreation
- cultural purposes
- ceremonial purposes.
Stock and domestic licences for surface water and groundwater basic rights allow the right holders to abstract water to meet basic requirements for household and stock purposes.
Urban water entitlements associated with surface water and groundwater allow water utilities and local councils to provide water for residential needs.
Queensland
Queensland water resource plans identify that (as outcomes for sustainable water management, among others) the following social and cultural benefits are required (Queensland Government 2009b). Water is to be allocated and managed in a way that seeks to achieve a balance in the following outcomes:
- to make water available to support economic activity in the plan area while recognising the social and cultural values of communities in the MDB region
- to build social cohesiveness in the community by recognising the multiple users of water, including both Indigenous and non-Indigenous social and cultural needs
- to promote improved understanding of social and cultural resources.
Water management rules have been adopted in water resources plan areas to achieve these outcomes.
New South Wales
The vision in the Water Sharing Plan for the Murrumbidgee Regulated River Water Source 2003 is to provide for equitable sharing of limited water resources to sustain a healthy and productive river, to contribute to the welfare and well-being of Murrumbidgee regional communities.
The objectives of the Murrumbidgee plan are to:
- protect basic landholder rights, as specified in the New South Wales Water Management Act 2000, including native title rights
- protect town water supply
- provide for identified recreational water needs
- protect identified Indigenous and traditional uses of water.
Town water supplies are protected by water access licences. In addition, the Murrumbidgee plan also makes provisions for regulated river—high security—Aboriginal cultural supplies.
Other water sharing plans that have commenced in New South Wales have similar visions and objectives with respect to social and cultural benefits.
The New South Wales plans have also generally adopted an approach that indicates sites of Aboriginal significance, including wetlands, are managed through the environmental watering regime. Although 506 ML has been recorded as Aboriginal cultural supplies in Murrumbidgee sustainable diversion limit (SDL) area, no specific information is available to identify details of Aboriginal sites benefitted from the supply in the 2012–13 year.
Australian Capital Territory
Limited information was available to explain how the Australian Capital Territory addresses the social and cultural benefits of water.
An objective of the Australian Capital Territory Water Resources Act 1998 is to ensure that the use and management of the water resources of the Australian Capital Territory sustain the physical, economic, and social well-being of the people of the territory while protecting the ecosystems that depend on those resources.
Victoria
Some of the strategies for managing water for social benefit in Victoria are addressed through the:
- Victorian permanent water saving rules;
- incentive and rebate schemes;
- actions to increase water recycling and alternative water supplies;
- stormwater and urban water recycling projects; and
- upgrading of existing treatment facilities.
South Australia
The Water Allocation Plan for the River Murray Prescribed Watercourse sets out provisions for country towns and urban supplies. It also prescribes an allocation for recreation class.
Rights related to social and cultural aspects, and relevant water use in the 2012–13 year in the MDB region are listed in the following table.
Type of water supply | Type of water right |
Entitlement class |
Water right (ML) |
Volume used in the 2012–13 year (ML) |
Line item for details of water right |
Line itemfor details of water used |
Remarks |
Surface water rights | |||||||
cultural water supplies | surface water access entitlement for allocated diversions | high security – Aboriginal cultural | 2,150 |
506 |
32.3 Surface water access entitlement for allocated diversions | 17.11Entitled diversion of allocated surface water to users | only for Murrumbidgee SDL area in New South Wales |
social water supplies | surface water basic rights | n/a | 68,210 |
68,210 |
32.1 Other statutory surface water rights | 17.6 Surface water diversions – other statutory rights | only for New South Wales |
surface water access entitlement for non-allocated diversions | stock and domestic | 12,100 |
– |
32.2 Surface water access entitlement for non-allocated diversions | 17.7 Entitled diversion of non-allocated surface water to users | ||
urban supplies | 91,422 |
13,073 |
17.8 Entitled diversion of non-allocated surface water to urban water system | For some SDL areas, entitlements and associated water use for urban supplies are included in other entitlement classes: separate information is not available. Stated entitlement volume does not include major utility entitlement (15,876 ML) for Macquarie–Castlereagh SDL area. | |||
surface water access entitlement for allocated diversions | stock and domestic | 88,060 |
47,203 |
32.3 Surface water access entitlement for allocated diversions | 17.11 Entitled diversion of allocated surface water to users | water right information only for New South Wales and South Australia, diversion information only for New South Wales. | |
high security – community and education | 47 |
28 |
only for Murray SDL area in New South Wales | ||||
domestic, stock and urban supplies | 3,242 |
– |
for Northern Mallee supplies in Murray SDL area in Victoria | ||||
urban supplies | 602,868 |
365,598 |
17.12 Entitled diversion of allocated surface water to urban water system | Water right information applies to all jurisdictions; however, water use information for Queensland (included in line item 17.11) is excluded. | |||
Total known/applicable surface water rights | 868,099 |
494,618 |
|||||
Groundwater rights | |||||||
social water supplies | groundwater – stock and domestic, and other lumped basic right | n/a | 207,855 |
230,416 |
33.1 Other statutory groundwater rights | 18.7 Groundwater extractions – other statutory rights | For Queensland, the extracted volume has been estimated as 22,561 ML; however, information on right volume is not available. |
groundwater access entitlement for allocated extractions | stock and domestic | – |
– |
33.3 Groundwater access entitlement for allocated extractions | 18.11 Entitled extraction of allocated groundwater to users | ||
urban supplies | – |
37,024 |
18.12 Entitled extraction of allocated groundwater to urban water system | ||||
Total known/applicable groundwater rights | 207,855 |
267,440 |
|||||
Total known/applicable | 1,072,416 |
762,461 |
– = no separate information is available
b. Environmental benefit
This note provides following details for the MDB region:
- environmental water management instruments and strategies
- the water management categorisations under which environmental benefits are provided.
Information on legislative, administrative, and governing arrangements of environmental water in the MDB region is available in Environmental water provisions in 'Administration' in the 'Contextual information'. It also includes information on organisations responsible for environmental water management in the jurisdictions.
In the MDB, environmental benefit is delivered through two broad management categorisations: planned environmental water and held environmental water.
Planned environmental water management is further categorised into:
- Planned partly regulated (or supplemented) surface water — the dominant feature of environmental water management in this categorisation is the ability to control or influence flow by operational releases from storage.
- Planned unregulated surface water — in this categorisation, water is managed for environmental benefit through controlling the water access regime.
Planned environmental water is water committed by a water resource plan (WRP) or legislation to achieve environmental outcomes. The Water management plans in 'Administration' in the 'Contextual information' includes links to jurisdictional water management plans that detail planned environmental water provisions within the MDB region.
Held environmental water is water available under a water right (entitlement or allocation) for the purpose of achieving environmental outcomes.
For each categorisation, the information, if available, is structured as follows:
- Environmental water determinations: the environmental objectives. They are represented by environmental water provisions defining specific water levels and flow criteria at key representative sites and given times that the water regime provided must meet.
- Environmental water commitments: the instruments in place to achieve the environmental water determination, e.g. environmental water storage release rules, water access rules to limit abstractions, rules on diversion to wetlands and annual environmental watering plans.
- Environmental water outcomes: the water regime that were provided and the extent of the compliance with respect to the criteria set in the environmental water provisions and the environmental water commitments.
General environmental water management information applicable to the MDB region can be found in the National Water Commission's Australian environmental water management report 2010 (National Water Commission 2010).
Some key features of the environmental water regime within the MDB region are:
- Each jurisdiction has legislative goals and mechanisms for managing surface water and groundwater systems. This includes managing environmental water delivery and use across the MDB region.
- Within each jurisdiction, the water management plans that have been developed address requirements to provide water for the environment, by setting aside volumes that cannot be extracted from the system and through releasing volumes from a storage in a controlled manner to achieve a set of conditions downstream. The restrictions on extraction also apply to groundwater systems.
- Not all areas of the MDB region have water management plans developed and approved.
- In addition to water management plans, other programs have been introduced by governments to increase the volume of water that is provided for the environment. For example, the Australian Government has introduced the Sustainable Rural Water Use and Infrastructure Program (SRWUIP), which is a national program investing in rural water use, management and efficiency projects, including improved water knowledge and market reforms. Under the program, water savings are recovered for the environment through three main components: irrigation infrastructure projects; supply measures; and water purchase (Australian Government Department of the Environment 2014a). The water rights acquired by the Commonwealth under this program become part of the Commonwealth environmental water holdings. These holdings are managed by the Commonwealth Environmental Water Holder (CEWH). More information about Commonwealth environmental water holdings can be obtained from the Commonwealth environmental water annual report 2012–13 (Australian Government Department of the Environment 2014b) and the Commonwealth Environmental Water Office website.
- Jurisdictions have also delivered significant water recovery programmes over recent past, such as New South Wales River Bank, Rivers Environmental Restoration Program and Wetland Recovery Program.
- Entitlements are held for the purpose of watering the environment as a result of the above mentioned and other programs (e.g. environmental entitlements held by the Minister for Environment in New South Wales, the Murray–Darling Basin Authority for The Living Murray program.
- All environmental entitlements held by the Victorian Minister for Environment were transferred to the Victorian Environmental Water Holder in Victoria with effect from 1 July 2011.
Queensland
The structure of the Queensland WRPs is primarily aimed at providing planned environmental water rather than using held environmental water.
There is no environmental water holder within Queensland. The Commonwealth government has acquired entitlements in Queensland for environmental benefit.
New South Wales
The Office of Water within the Department of Primary Industries is responsible for water licence and regulation, including oversight of planned environmental water. The Office of Environment and Heritage (OEH) within the Department of Premier and Cabinet collaborates with many other partners to manage environmental water in New South Wales, including delivery of allocations from held environmental water and utilising planned environmental water to deliver environmental benefits. Environmental entilements (including TLM entitlements) managed by OEH as at 30 June 2013 was 397,000 ML (NSW Office of Environment and Heritage 2014).
Australian Capital Territory
The Department of Environment, Climate Change Energy and Water has developed Environmental Flow Guidelines 2006. The objectives set in the guidelines are met by releases from the storages, as planned partly regulated surface water management, rather than using held environmental water.
There is no environmental water holder within the Australian Capital Territory and the Commonwealth government has not purchased any entitlements for environmental benefit in the Australian Capital Territory.
Victoria
The Victorian Environmental Water Holder (VEWH) held entitlements that could be used for environmental benefit during the 2012–13 year. A mixture of planned environmental water, which is addressed in the bulk entitlements and other rules, and water entitlements are used to deliver environmental benefits.
South Australia
The South Australian Department of Environment, Water and Natural Resources manages environmental water. A mixture of planned environmental water and held environmental water is delivered to improve the ecological health of the River Murray, including wetlands, floodplain, and Lake Coorong. See the River Murray Water Allocation Plan for details (Government of South Australia 2009).
Commonwealth environmental water programmes
Information about Commonwealth environmental water management involving the Commonwealth Environmental Water Holder can be found in the Commonwealth environmental water annual report 2012–13 (Australian Government Department of the Environment 2014b).
The CEWH can trade Commonwealth environmental water and water holdings subject to conditions in the Australian Government Water Act 2007. Commonwealth environmental water holdings are published in the CEWH's annual report, and are updated each month on the Commonwealth environmental water holdings web site.
Information about environmental water delivery under the Living Murray Initiative can be obtained from Murray–Darling Basin Authority (2012a).
Planned partly regulated (or supplemented) surface water
This type of environmental water delivery occurs in some river reaches in the MDB region through the active release of environmental entitlements from a storage at the direction of the respective environmental entitlement holder.
The water regime to attain at given locations on the rivers (environmental water determination) and the storage release rules (environmental water commitments) are specified in approved water sharing and management plans that are listed under Water management plans in 'Administration' in the 'Contextual information'.
Planned unregulated surface water
Environmental water determination for planned unregulated surface water categorisation is based on provisions made in approved water sharing and management plans. Water management plans in 'Administration' in the 'Contextual information' includes details of these plans within the MDB region.
Held environmental water
Entitlements listed in the following tables were available during the 2012–13 year (as recorded on 30 June 2013) as held environmental entitlements. The entitlements held by the CEWH and under the Living Murray (TLM) Program are included in the tables.
Entitlement volumes shown reflect only those that have been recorded as being legally held (or under the administrative operations of the environmental water manager). The entitlement volumes will be subject to change as water continues to be acquired under some programmes. In particular, the volumes held by the CEWH will increase as more entitlements are acquired.
Water resource plan area | State |
Total volume of entitlements (ML) |
Name | ||
SW20 Warrego–Paroo–Nebine | Qld | 21,970 |
SW19 Condamine-Balonne | Qld | 49,605 |
SW18 Moonie | Qld | 1,415 |
SW17 Qld Border Rivers | Qld | 15,970 |
SW16 NSW Border Rivers | NSW | 298 |
SW12 Barwon–Darling Watercourse | NSW | 25,575 |
SW13 NSW Intersecting Streams | NSW | 17,826 |
SW15 Gwydir | NSW | 130,481 |
SW14 Namoi | NSW | 7,212 |
SW11 Macquarie–Castlereagh | NSW | 167,869 |
Sub-total Northern Basin | 438,221 |
|
SW10 Lachlan | NSW | 139,430 |
SW9 Murrumbidgee | NSW | 505,263 |
SW8 NSW Murray and Lower Darling | NSW | 879,480 |
SW3 Northern Victoria | Vic. | 455,293 |
SW2 Vic. Murray | Vic. | 527,298 |
SW4 Wimmera–Mallee | Vic. | 69,560 |
SW6 SA River Murray | SA | 145,879 |
Sub-total Southern Basin | 2,722,203 |
|
Total | 3,160,424 |
Water resource plan area | Sustainable diversion limit area1 |
State |
Unregulated and supplementary flow entitlements2 (ML) |
Regulated flow entitlements3 (ML) |
Total (ML) |
|
Name | Code |
Name |
||||
Warrego – Paroo – Nebine | SS 28 | Warrego | Qld | 16,050 |
0 |
16,050 |
SS 27 | Nebine | 5,920 |
0 |
5,920 |
||
Condamine-Balonne | SS 26 | Condamine-Balonne | Qld | 49,605 |
0 |
49,605 |
Moonie | SS 25 | Moonie | Qld | 1,415 |
0 |
1,415 |
Qld Border Rivers | SS 24 | Qld Border Rivers | Qld | 4,286 |
11,684 |
15,970 |
Sub-total Queensland | 77,276 |
11,684 |
88,960 |
|||
NSW Border Rivers | SS 23 | NSW Border Rivers | NSW | 0 |
298 |
298 |
Barwon–Darling Watercourse | SS 19 | Barwon–Darling Watercourse | NSW | 25,575 |
0 |
25,575 |
NSW Intersecting Streams | SS 17 | NSW Intersecting Streams | NSW | 17,826 |
0 |
17,826 |
Gwydir | SS 22 | Gwydir | NSW | 22,240 |
108,241 |
130,481 |
Namoi | SS 21 | Namoi | NSW | 0 |
7,212 |
7,212 |
Macquarie–Castlereagh | SS 20 | Macquarie–Castlereagh | NSW | 3,340 |
164,529 |
167,869 |
Lachlan | SS 16 | Lachlan | NSW | 0 |
139,430 |
139,430 |
Murrumbidgee | SS 15 | Murrumbidgee NSW | NSW | 33,237 |
472,026 |
505,263 |
NSW Murray and Lower Darling | SS 14 | NSW Murray | NSW | 113,021 |
467,667 |
580,688 |
SS 18 | Lower Darling | NSW | 250,000 |
48,792 |
298,792 |
|
Sub-total New South Wales | 465,239 |
1,408,195 |
1,873,434 |
|||
Northern Victoria | SS 4 | Ovens | Vic. | 0 |
70 |
70 |
SS 5 | Broken | Vic. | 0 |
51 |
51 |
|
SS 6 | Goulburn | Vic. | 0 |
436,378 |
436,378 |
|
SS 7 | Campaspe | Vic. | 0 |
12,024 |
12,024 |
|
SS 8 | Loddon | Vic. | 0 |
6,770 |
6,770 |
|
Vic Murray | SS 2 | Vic Murray | Vic. | 74,300 |
452,998 |
527,298 |
Wimmera – Mallee | SS 9 | Wimmera – Mallee | Vic. | 0 |
69,560 |
69,560 |
Sub-total Victoria | 74,300 |
977,851 |
1,052,151 |
|||
SA River Murray | SS 11 | SA Murray | SA | 0 |
145,879 |
145,879 |
Sub-total South Australia | 0 |
145,879 |
145,879 |
|||
Total | 616,815 |
2,543,609 |
3,160,424 |
1 Only the SDL areas for which information is available are included in the table.
2 The entitlement volumes shown in the table are a subset of line item 32.2 Surface water access entitlement for non-alloacted diversions. The same line item provides other information associated with the volumes shown in the table.
3 The entitlement volumes shown in the table are a subset of line item 32.3 Surface water access entitlement for allocated diversions. The same line item provides other information associated with the volumes shown in the table.
The tables include CEWH-managed 1,629,000 ML of water entitlements during the year, which has a long-term average yield of 1,190,000 ML per year (Australian Government Department of the Environment 2014b). They also include TLM-managed 988,000 ML of water entitlements during the year, which has a long-term average yield of 480,000 ML per year (Murray–Darling Basin Authority 2012a). Entitlement volumes shown in tables 13 and 14 reflect only those that have been recorded as being legally held (or under the administrative operations of the environmental water manager) at the time of compiling the 2013 Account. The volumes on issue of entitlements held for the environment are continually changing as more water is acquired under various programmes and when water is traded between valleys. In particular, the volumes held by the CEWH increases as more entitlements are being acquired. The volumes reported in tables 13 and 14 are probably an under-estimation of the volumes on issue at the end of the 2012–13 year, as not all water recovery transactions had been settled by the time information was collected for the 2013 Account.
Groundwater environmental entitlements
Following groundwater environmental entitlements for salinity and water table management have been reported for the 2012–13 year from New South Wales:
- 1,500 ML in Billabong Creek Alluvium SDL area
- 236 ML in Lachlan Fold Belt SDL area
- 20,010 ML in Lower Murray Alluvium SDL area
- 10,700 ML in Western Porous Rock SDL area.
Consolidated information on water released under entitlements held for the benefit of the environment was not available for the 2012–13 year. Available information on environmental water outcomes primarily on held environmental water categorisation is provided here.
New South Wales
Table 15 includes summarised information on environmental water use within New South Wales SDL areas during the 2012–13 year. The volume for the 2012–13 year is lower than the volume reported for the 2011–12 year.
Sustainable diversion limit area | Use of environmental water allocation (ML) |
|
Unregulated flow and supplementary entitlements |
Regulated flow entitlements |
|
NSW Border Rivers | 0 | 269 |
Barwon–Darling Watercourse | 0 | 0 |
NSW Intersecting Streams | 0 | 0 |
Gwydir | 10,123 | 37,951 |
Namoi | 0 | 7,728 |
Macquarie–Castlereagh | 0 | 137,718 |
Lachlan | 0 | 66,283 |
Murrumbidgee NSW | 3,894 | 177,946 |
NSW Murray | 16,237 | 48,422 |
Lower Darling | 32,903 | 0 |
Total | 63,157 | 476,317 |
Source of information: water audit monitoring data received from New South Wales (24 March 2014) and stored in the Murray–Darling Basin Authority HYDRO database.
The volumes shown in the table reflects releases made for environmental water needs under various environmental water allocation programmes. The volumes include use of allocations from supplementary entitlements. It is possible that the total volume delivered during the year could be higher than the volume shown in the above table due to data availability issues. Information on consumptive use out of the volumes shown in the table is not available.
Victoria
Information about environmental watering in Victoria is available in Victorian environmental water holder's watering update. Table 16 includes summarised information on environmental water use within Victorian SDL areas during the 2012–13 year. The volume for the 2012–13 year is slightly lower than the volume reported for the 2011–12 year.
Sustainable diversion limit area | Use of environmental water allocation1 (ML) |
|
Regulated flow entitlements |
Supplementary entitlements |
|
Ovens | 20 | |
Broken | 41,230 | |
Goulburn | 255,427 | |
Campaspe | 16,887 | |
Loddon | 10,680 | |
Vic. Murray | 4,562 | 17,119 |
Wimmera–Mallee | 30,890 | |
Total | 359,696 |
17,119 |
1 Allocation use includes environmental water used in the water source and water diverted from the water source.
Source of information: Victorian Environmental Water Holder (2014), and water audit monitoring data received from Victoria (14 February 2014) and stored in the Murray–Darling Basin Authority HYDRO database.The volumes include use of allocations from supplementary entitlements. It is possible that the total volume delivered during the year could be higher than the volume shown in the above table due to data availability issues.
South Australia
Environmental water management for South Australia was undertaken by the staff from the Department for Water until abolition and then the Department of Environment, Water and Natural Resources. Table 17 includes summarised information on environmental water use in South Australia (within MDB) during the 2012–13 year. The areas benefitting from water allocated under Commonwealth environmental water holdings include Lower Lakes, Coorong and Murray Mouth.
Description | Allocation use1 (ML) |
Volume diverted from the water source (ML) |
The Living Murray (TLM) program | 198,356 | 135 |
Commonwealth Environmental Water Office (CEWO) | 877,665 | 54 |
Other | 14,000 | 0 |
Total | 1,090,021 | 189 |
Source of information: water audit monitoring data received from South Australia (17 March 2014) and stored in the Murray–Darling Basin Authority HYDRO database. It is possible that the total volume delivered during the year could be higher than the volume shown in the above table due to data availability issues.
Queensland
A summary of information about environmental watering in Queensland can be obtained from the 2012–13 annual report for Queensland's WRPs produced by the Department of Natural Resources and Mines. A full copy of the annual report is available on request by emailing WRPWebCoordinator@dnrm.qld.gov.au. Information on the environmental water held by the Commonwealth in Queensland is available from the website. Table 18 summarises information on environmental water use in SDL areas within Queensland during the 2012–13 year. The volume for the 2012–13 year is higher than the volume reported for the 2011–12 year.
Sustainable diversion limit area | Regulated environmental water use (ML) |
Use of unregulated environmental water allocation (ML) |
Total use (ML) |
Warrego | 0 | 0 | 0 |
Nebine | 0 | 0 | 0 |
Condamine–Balonne | 0 | 64,946 | 64,946 |
Moonie | 0 | 1,415 | 1,415 |
Qld Border Rivers | 626 | 1,664 | 2,290 |
Total | 626 | 68,025 | 68,651 |
Source of information: water audit monitoring data received from Queensland (5 February 2014) and stored in the Murray–Darling Basin Authority HYDRO database. It is possible that the total volume delivered during the year could be higher than the volume shown in the above table due to data availability issues.
As indicated in the Queensland WAM data sources, the volumes provided in the table were considered as non-consumptive uses. In addition to environmental water uses provided in the table, there are the other environmental flow provisions which are primarily rule based in Queensland WRP areas. For these provisions, delivered volume is not available.
Australian Capital Territory
No annual report is published by the Australian Capital Territory Government on environmental watering activities.
Commonwealth
The CEWH has delivered 1,272,000 ML of environmental water to environmental assets across the region during the 2012–13 year. Commonwealth environmental water was used for the first time in a number of locations, including the Namoi River, the Mallowa wetlands in the Gwydir catchment, Whirlpool Corner, Disher Creek and Berri Basin in South Australia, Tuppal and Gwynnes Creeks of the Edward–Wakool catchment, and wetland areas of the western lower Murrumbidgee floodplain near Balranald (Australian Government Department of the Environment 2014b).
Under the Living Murray program, a total of 296,953 ML of water was delivered to Murray River icon sites excluding Gunbower–Koondrook–Perricoota Forests and Hattah Lakes during the 2012–13 year up to April 2013 (Murray–Darling Basin Authority 2014b). This volume is included in the environmental water delivery volumes cited for the States.