Water resources - Management and Development - New South Wales
Basin & Surface Water Management Area: Hastings River
Introduction
As resource demands and pressure increases so to do the requirements of both management and information needs. Outlined below are the key issues facing the region as determined by the State / Territory water management agency.
What is the estimated demand for surface water in Hastings River?
| Use and Sustainable Yield | |
|---|---|
Comment about sustainable yield figure: | NSW is introducing volumetric licenses for the management of unregulated valleys and is currently collecting a wide range of data in unregulated basins. The sustainable yield concept, ie the amount of water that can be diverted from rivers in perpetuity, is recognised in NSW. However NSW's current management practices views the sustainable yield as an allowable daily extraction volume as opposed to an annual yield figure. As well future reviews of the performance of the management rules to be adopted in each valley plus additional knowledge at that time may result in changes to the rules and hence changes to the "Sustainable Yield". NSW has taken the approach that it is better to await the availability of data on the unregulated basins based on reliable and realistic analysis than to divert limited resources from this process to provide data based on unreliable information and inappropriate analysis. Accordingly the Sustainable Yield has not been calculated for the unregulated basins in NSW. However an attempt was made to obtain a categorisation for the catchment based on the work done for the stressed streams. A variable P was determined for the total catchment on the basis of the combined stress classsification results from the stressed streams analysis, where P = Total area of sub-catchments with high combined stress / Total area of classsified sub- catchments in basin Categorisation was on the basis that: Category 1 applies for 0% <= P < 30% Category 2 applies for 30% <= P < 70% Category 3 applies for 70% <= P <100% Category 4 applies for P = 100% Please refer to the NSW Department of Land and Water Conservation's website for further information about this Basin. |
Sustainable yield (ML/yr): | no data |
Threshold year for sustainable year: | no data |
Diversion Volume 1996 (ML): | no data |
Current resource development categorisation: | MEDIUM DEVELOPMENT |
| Estimated in 2020 | |
|---|---|
Estimated use in 2020(ML): | no data |
% change from 1996: | no data |
Resource development categorisation: | no data |
| Estimated in 2050 | |
|---|---|
Estimated use in 2050(ML): | no data |
% change from 1996: | no data |
Resource development categorisation: | no data |
How was this assessment undertaken in the Hastings River Surface Water Management Area?
Development Potential:
NSW has adopted different approaches to the determination of water sharing arrangements in its regulated and unregulated systems. There are fundamental differences in the rights to access water and the sharing arrangements between both systems. In regulated systems users are assured some reliability of supply through the regulation and delivery of water from headwater and re- regulating structures. Shares are allocated annually and by volume. In unregulated systems shares are subject to the occurrence of flow in the stream and meeting certain downstream flows with volume extracted limited solely by the size of pump, area of development and duration of flow event. Action is being taken to move to volumetric management in the unregulated systems. Due to the CAP constraints it is not expected that there will be any development potential for inland unregulated stream. Identification of the surface water development potential in the unregulated coastal SWMA's is not possible until such time as bulk extraction volumes have been determined. Current entitlements in unregulated valleys are not volumetric. Entitlements are issued as an area authorised for irrigation, maximum pump capacity and purpose of use. The water useage at for each licence or even an average figure is difficult to obtain with any accuracy. Staged action is currently being taken as part of the NSW Water Reform to apply volumetric conversions to entitlements in unregulated valleys. This will be followed by the issuiong of daily extraction rights derived from an assessment of the volume available for extraction. Determination of available extractable returns is initially focused on highly stressed valleys and is being developed on a sub-catchment basis.
Management goals and objectives:
The Department aims to manage the natural resources of NSW in a sustainable way - ensuring that the state has healthy and productive environments which are preserved for the future.
Natural resources are closely linked and activities which affect one resource will impact on all others. Because of this dependent relationship, DLWC takes a coordinated approach known as Total Catchment Management. This involves considering decisions which impact on the soil water, vegetation and fauna, and taking into account their effect on the whole catchment.
The NSW Government has introduced a package of Water Reforms aimed at achieving a better balance in sharing of water between all water users and the environment. The management and implementation of the Water Reforms will be coordinated by a whole-of-government perspective, involving primarily the Department of Land and Water Conservation, the Environment Protection Authority, NSW Agriculture, National Parks and Wildlife Service and NSW Fisheries.
A key part of the the Water Reform involves working with the community to establish environmental objectives for future water management. The DLWC is identifying the stresses on the States rivers and creating efficiencies in government water services and administration. Other government initiatives include establishing river management committees in which the local community has a say in the management of its rivers, assessing the socio-economic impact of the water reforms, monitoring environmental conditions, implementing a State Weirs policy to review the environmental effects of individual weirs and preparing a water conservation strategy for NSW.
The specific surface water management goals and objectives are:
a. to protect river health
b. to protect the reliability and security of supplies for existing users
c. provide incentives and flexibility for more efficient water use.
See NSW Water Resources Assessment 2000 Report and Water Resources Assessment 2000 Technical Report for comment on methods and assumptions.
| Current 2000 | Desired 2000 | Desired 2020 | Desired 2050 | |
|---|---|---|---|---|
Management information | ||||
Scale of allocation planning | NONE | CATCHMENT | CATCHMENT | |
Inputs to allocation | NA | BROAD RESOURCE INVESTIGATION | BROAD RESOURCE INVESTIGATION | |
Type of monitoring - quantity | BROAD-SCALE | BROAD-SCALE | BROAD-SCALE | |
Type of monitoring - quality | SALINITY AND OTHER LIMITED PARAMETERS | SALINITY AND OTHER LIMITED PARAMETERS | SALINITY AND OTHER LIMITED PARAMETERS | |
Distribution efficiency (H,M,L) | NA | NA | NA | |
Use efficiency (H,M,L) | NA | NA | NA | |
Resource management efficiency (H,M,L) | NA | NA | NA | |
Degree of licensing | ALL USES | ALL USES | ALL USES | |
Water trading (None, Limited, Significant) | NONE | LIMITED | LIMITED | |
Mechanism of trading | ||||
Volume traded (ML/yr) | no data | no data | no data | |
Number of transactions | ||||
Inter-basin transfers | NONE | NONE | NONE | |
Volume transferred (ML/yr) | no data | no data | no data | |
Environmental allocation category:
| no data |
Comments on Management Responses in the Hastings River Surface Water Management Area
Current Management Response:
Desired (Current) Management Response:
2020 Management Response:
The water reform process in NSW began in the 1980s, with increasing recognition of environmental needs and changes to institutional and pricing arrangements.
This was recogn ised formally in 1995 and again in 1997, with the development of Water Reform Policies. These policies have been developed and implemented through a whole of government approach with the involvement of other key natural resource agencies. The 1995 water policy reforms aimed to:
- commence development of interim river flow and water quality objectives
- provide guidance in this task by the establishment of the Healthy Rivers commission
- provide water to the environment in the Macquarie and Gwydir River systems
- introduce water pricing reform
- establish a Water Advisory Council of Community and industry representatives to advise Government on reform policy
- separate the roles of operator, regulator and manager
The 1997 water policy reforms aimed to:
- introduce better sharing of available water by
- developing and implementing environmental flow rules on the regulated rivers and the Barwon-Darling River
- working with the community to establish environmental flow objectives
- identifying stressed unregulated rivers and groundwater systems, and preparing ,management plans to meet agreed environmental objectives
- enhance investment strategies for rural sector by
- providing stronger investment confidence for water users through water access rights and better water markets
- providing Government support for a range of water related activities including structural adjustment
- ensuring balance in cost sharing arrangements through the Independent Pricing and Review Tribunal (IPART) process
- change the way water management is delivered by
- setting up a partnership approach through water management committees
- creating efficiencies in Government water management
- having more efficient administration of Government processes
These policies are not static and can be expected to change with time. The preasent management and planning horizon is 10 years which will take the state to 2010. While major changes to the existing policies are not expected
2050 Management Response:
No information supplied, see above.
See NSW Water Resources Assessment 2000 Report for comment on management responses.
Assessment of Monitoring
Efficacy of the network:
The Department of Land and Water Conservation undertakes extensive monitoring and data collection of the States water resources. These activities include monitoring of surface and groundwater resources (quantity and quality), water diversions and usage and biological monitoring. In addition it maintains registrars of information on structures on watercourses used for water storage and diversion.
The data is collected to meet the objectives of the states Water Reform Programs and to satisfy the needs of other stakeholders including industry, local government and the community. Data use includes surface and groundwater assessments, river operations and flood warning, water quality and river health auditing.
A review of the Departments surface water monitoring network has recently been undertaken. This showed that
90% of current surface water sites (700 sites statewide) are currently meeting water reform or stakeholder objectives. Of these 700 sites, approximately 350 sites are on unregulated watercourses in coastal and inland catchments. It is anticipated, that in the medium term, additional surface water monitoring sites will be established in unregulated stressed coastal catchments to support Water Reform objectives. These reforms include water trading and water and environmental assessments to improve water use efficiency and environmental sustainability.
Data management requirements:
The major trend in data mangement requirements relates primarily to the data access and data delivery.
There is now the perception among managers that they must have the "latest", "real-time" data. This is pushing the development and implementation of "real-time" data collection and data delivery systems.
This also creates a set of data management issues related to the handling and storage of real time data as well as integration of real-time data as opposed to the traditionally collected "assessment" data.
The LAN/WAN systems and the Inter/Intra-net are also now seen as a major data delivery system, typically via a spatial interface. This has increased the already important links between water resources data and spatial/GIS systems. It has also increased the need for more flexible data storage facilities with data access transparency to a wide range of external applications and systems.
Additionally there has also been the need to develop a range of other data dissemination options including voice, e-mail, fax-back, etc. All these requirements impact on the data storage and data management.
Technology itself, or rather its rate of change, is also impacting on data management requirements
Protective management:
There are a number of issues that will effect NSWs ability to achieve sustainable management of its surface water resources. The following are some of the important issues:
1. As the use of water in water resource management units approach sustainable development levels, there will be increasing need for experienced personnel, information and decision tools, particularly with NSW approach to management of environmental flows. Therefore the ability to achieve effective and reliable management across NSW will require continued financial committment of government.
2. The development and implementation of water resource management plans for unregulated flow rivers throughout the NSW will remain a high priority for a number of years. The challenge for water managers and the community will be to resolve the contentious sharing issues and adopt plans and implementation rules that are simple and easy to implement. Because of the small number of users in unregulated valleys many with marginal economic value, the cost of managing unregulated rivers for sustainable outcomes may be beyond the ability of user to pay.
3. NSW will focus on achieving sustainable management of surface resources by managing the access to use over the full flow regime and not by using a cap on water use as the only management tool.
4. As knowledge on the links between flow and the river environment is still developing, as is the operational implementation, NSW will not lock up valley sharing rules in perpetuity. However, as sharing plans enter their second implementation phase they will operate for periods up to ten years to give users security for financial planning.
5. NSW will continue to market operation to offset the limits on additional growth through infrastructure development. A key issue for effective water trading will be clarification of access and use rights and the security of those rights. The proposed provision of a register of water entitlements with details of volumes, security, third party interests and full disclosure of prices paid will assist market operation.
6. The expansion of dryland salinity in the uplands of the NSW portion of the Murray-Darling basin will place increasing pressure on maintaining flows within those river valleys for dilution needs. Dealing with the problem at its source is the preferred solution.
7. As the implementation of flow sharing rules are being undertaken by separate operational bodies the water resource manager will require improved performance indicators for flow and environmental outcomes. Annual operating plans will be an increasing requirement of the regulator with annual disclosure of performance as an important compliance tool. Sanctions or penalties for non-compliance are an area that needs further work.
8. It is unlikely that there will be many major government funded infrastructure developments in the foreseeable future. Water needs to be freed up for sustainable development through privately funded water savings and new development schemes facilitated by transfers. The community attitude to reclaimed water needs to be improved and on farm water use efficiency needs to be accelerated.
9. Community acceptance of drought as a reality rather than an abnormality also needs some attention. Users need to understand the reality of the trade-off between security, the price of water and the risk of restrictions. Annual availability of water for use on rivers is subject to climatic variability; user decisions are assisted by information on future water availability. The opportunity to use improving seasonal climate
forecast methods need s to be added to the existing forecasts that are based on historical flow data.
10. Water resource system models have been the main management decision tools. These tools provide information on water shares and availability to assist economic assessment. To achieve sustainable management of water resources, future decisions will need a balance between economic, social and environmental outcomes. These decisions will require economic, financial, social and environmental response models linked to water shares and availability in the water resource system models.
11. Water resource system models will be increasingly used for audit purposes, requiring reliable information on water use, crop types, irrigated areas and user management decisions.
Options for monitoring:
At a meta data level there is a need for an Australian wide body similar to the AWRC to co-ordinate, promote and disseminate a range of water related information.
For example NSW as part of its Stressed Stream review and assessment of the State has revised parts of its inland catchment boundaries.
AWRC boundaries have been recognised as the "official" catchment boundaries since the 1970's and are displayed in all national and state water resources publications. They could almost be regarded as a national dataset.
With the better topological information data available NSW has been able to more accurately define watershed boundaries. However these new boundaries adopted for NSW's Surface Water Management Areas now differ from the AWRC boundaries in some areas. NSW thinks that the AWRC basin boundaries should be changed to mirror the latest informatiom.
Currently there does not appear to be a clear path for these changes (and possibly changes from other states) to be communicated to other federal and state agencies so that their copies of NSW's AWRC basin boundaries can be adjusted.
See NSW Water Resources Assessment 2000 Technical Report for an assessment of monitoring
Data Availability, Gaps and Recommendations
Data Availability:
Data availability for the coastal unregulated streams is generally fair to good.
In this Basin there are some 15 surface water gauging stations sites run by the Department of Land and Water Conservation and there are 6 sites at which flow data is currently being collected. There are also sites in this basin where water levels are monitored for coastal flood management.
As well there is one water quality sites which is part of a regular monitoring program (Key Sites Program).
The Department currently lacks detailed knowledge of water usage in unregulated basins.
Current Gaps and Recommendations:
Data Gaps: Better knowledge of water usage has been identified as a major gap in all basins.
The Stressed Streams Reports have also highlighted that in the unregulated basins, of which the Hastings basin is one, more monitoring sites will be required to enable envisaged management practices to be adopted. Recommendations: The Department has instigated projects to ensure more usage data is collected in the regulated areas and is investigating methods of collecting this data in unregulated areas. As well submissions have been made to the National Heritage Trust for additional funding to improve the Departments knowledge of water usage.
The Department has nearing completion of a major review of the state's surface water monitoring network. A key part of this project has been the identification and prioritisation of new monitoring sites.
Future Gaps:
Water resource system models are the main management decision tools, which in future will need to be linked to improved economic, financial, social and environmental response models. Obviously good data and information are fundamental to the accuracy and validity of these tools. Some of the general gaps in this area are:
1. Australian Bureau of Agriculture and Resource Economics (ABARE) data does not match SWMAs.
2. Links between environmental health and river flows that are representative of regional ecological populations.
3. Financial data (cash flow, equity etc) for representative water user units in SWMAs or groups of SWMAs.
4. Representative user risk management decision criteria in SWMAs or groups of SWMAs.
5. Reliable and cost effective methods of obtaining information on water use, crop types and irrigated areas for unregulated rivers, which are not metered, and GMUs.
6. Water resource system models for unregulated rivers and accuracy of those models where they are not supported by stream flow data.
7. Operational decision tools for unregulated rivers.
8. Environmental flow performance measures.
9. Interrelationships between surface water and groundwater, i.e. impacts on stream flow losses.
10. Forestry and other land use impacts on stream flow.
11. Cumulative impacts of farm dams on the hydrology of rivers and basins.
12. Environmental impacts of flow pulsing in regulated rivers to mimic natural flow patterns in regulated rivers.
13. Ecological value of small streams in providing colonisation and food supply to main stream ecology.
14. Level of management uncertainty derived from models based on long term climatic data but calibrated with short water system management data.
15. The collection and storage of time series salinity data
16. Establishment of effective groundwater data systems that address quality control, accessibility and timeliness
See NSW Water Resources Assessment 2000 Technical Report for a review of data availability,gaps and recommendations.
Further information
- New South Wales Water Resources Assessment 2000 Technical Report
- Link to data available for download on the Surface Water Management Areas
- Link to the Map Maker to make a map using this information.
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