
Water resources across the Northern Agricultural Region (NAR) support communities, agriculture and industry, as well as rivers, wetlands, estuaries and groundwater-dependent ecosystems. These resources are increasingly affected by a drying climate, changing patterns of water availability and growing demand.
The NARvis Water Goals set five regional targets for 2030. Progress has been assessed using available water allocation plans and evaluations, monitoring information, project records and other publicly available evidence. For project-based goals, the figures below represent qualifying projects identified to date and may not capture all relevant activity undertaken across the NAR. This Report Card considers progress towards those goals alongside available indicators of the condition of the region’s surface water and groundwater resources.
2026 Assessment: Progressing
Climate change is increasingly incorporated into water allocation planning within the NAR.
The Gingin groundwater and surface-water allocation plans have been evaluated in response to declining rainfall, groundwater levels and streamflow. Updated management arrangements introduced following the 2024 evaluation include caps on some groundwater resources and revised surface-water management. A new combined Gingin water allocation plan is being developed using updated climate projections.
The older Arrowsmith and Jurien groundwater allocation plans recognise pressures associated with a drying climate, and supporting work used to establish and review allocation limits has considered climatic change. However, these plans pre-date more recent climate projections and do not demonstrate the same level of explicit climate-change adaptation as the more recent Gingin planning process.
Formal water allocation plans do not cover every water resource within the NAR, and available information does not provide a comprehensive assessment of how all water distribution systems are adapting to climate change.
Overall, substantial progress is evident, but available evidence does not support considering the regional 2030 goal fully achieved.
2026 Assessment: Progressing
Water allocation planning provides mechanisms for balancing consumptive water use with environmental, social, cultural and economic requirements. Allocation limits, licensing conditions, water reserves, monitoring and adaptive management are used to manage pressure on water resources and protect environmental and other values.
However, some NAR water resources are under increasing pressure from declining rainfall, reduced recharge and streamflow, and water demand.
The 2024 evaluation of the Gingin groundwater and surface-water allocation plans found continuing declines in some groundwater levels and streamflow associated with climate change and abstraction. Of the 35 groundwater resources managed under the Gingin groundwater allocation plan, 10 were fully allocated and a further eight were capped at existing licensed entitlements. The volume of groundwater available for additional licensing had fallen from 68 GL in 2015 to 20 GL by the time of the 2024 evaluation. Management arrangements have been strengthened in response to these pressures, demonstrating adaptive management towards sustainable use.
Available information does not, however, provide an objective measure of whether water is distributed equitably between all environmental, cultural, social and economic interests across the NAR. The evidence therefore demonstrates active management towards sustainable water distribution, but does not establish that this 2030 goal has yet been achieved across the region.
Projects identified to date: at least 8 of 25
Projects identified through available records include:
Other ongoing activities, including recreational-water-quality and groundwater monitoring programs, also contribute important information about water quality but have not been included in this project count where they could not be clearly identified as discrete projects for the purposes of the NARvis target.
The figure represents projects that could be verified through available information and should be regarded as a minimum rather than a complete record of water-quality activity across the NAR.
Projects identified to date: at least 7 of 25
Verified examples include:
These projects include river-health assessment, wetland and estuary monitoring, riparian restoration, hydrological rehabilitation, weed and pest management, erosion control and other actions intended to maintain or improve the ecological function of water-dependent environments.
A project may contribute to both Goal 3 and Goal 4 where it demonstrably addresses both water quality and ecosystem health. Projects operating at multiple sites are counted as a single project rather than counting each monitoring or works site separately.
As with Goal 3, this represents projects identified through available records and does not necessarily capture all relevant activity undertaken across the NAR.
Progress towards the NARvis Water Goals is only one part of the picture. Project delivery and management activity do not necessarily indicate whether the condition of the region’s water resources is improving or declining.
Available monitoring provides important indicators of changes in streamflow, salinity and groundwater levels.
These data were sourced from the Department of Water and Environmental Regulation’s Water Information Reporting system. Data on total annual stream discharge, measured in megalitres (ML), are presented for selected monitoring stations on the Chapman, Hutt, Hill, Irwin, Moore and Murchison rivers.
Individual monitoring stations represent conditions at particular locations and should not be interpreted as measuring the condition of every river or catchment across the NAR.
Long-term streamflow records show considerable year-to-year variability across NAR waterways, reflecting the region’s highly variable rainfall and runoff.
Declining rainfall and a drying climate are affecting water availability in parts of the region. Reduced rainfall does not translate directly into an equivalent reduction in streamflow: as catchments dry, a greater proportion of rainfall is absorbed by soils and vegetation before reaching waterways.
The streamflow graphs below provide long-term context for selected monitoring stations across the NAR:
These data were sourced from the Department of Water and Environmental Regulation’s River Monitoring Stations. Data is recorded in megalitres.

These data were sourced from the Department of Water and Environmental Regulation’s River Monitoring Stations. Data is recorded in megalitres.

These data were sourced from the Department of Water and Environmental Regulation’s River Monitoring Stations. Data is recorded in megalitres.

These data were sourced from the Department of Water and Environmental Regulation’s River Monitoring Stations. Data is recorded in megalitres.

These data were sourced from the Department of Water and Environmental Regulation’s River Monitoring Stations. Data is recorded in megalitres.

These data were sourced from the Department of Water and Environmental Regulation’s River Monitoring Stations. Data is recorded in megalitres.

Salinity remains a significant water-management issue in parts of the NAR. It is influenced by groundwater processes, land use, rainfall, streamflow and catchment characteristics and can vary substantially between waterways and between years. Long-term monitoring of the Chapman River provides an indicator of changes in river salinity.
These data were sourced from the Department of Water and Environmental Regulation’s Water Information Reporting system. Conductivity data provide a long-term indicator of changes in salinity in the Chapman River, and is measured in microsiemens per centimetre (µS/cm).
Groundwater is critically important to communities, agriculture, industry and groundwater-dependent ecosystems throughout much of the NAR. Levels respond to rainfall and recharge, abstraction and local hydrogeology. Long-term monitoring is therefore important for identifying trends and informing water allocation and management.
Groundwater levels are shown for five selected Department of Water and Environmental Regulation monitoring bores across the NAR. These records provide an indication of changes in groundwater levels over time. The period of record and frequency of observations vary between monitoring sites according to data availability.
The groundwater hydrographs below show available records from selected monitoring bores.

Source: DWER Water Information Reporting

Source: DWER Water Information Reporting

Source: DWER Water Information Reporting

Source: DWER Water Information Reporting

Source: DWER Water Information Reporting
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