Salinity - Risk and Hazard - New South Wales
New South Wales

Where is there a dryland salinity risk or hazard and how was this determined?
Areas of risk are based on groundwater levels and air photo interpretation. The merged data, at a nominal scale of 1:250 000, show actual areas where dryland salinity or watertables less than 2 m have been measured. For the extent map, every delineated area is underpinned by either air photo data or by one or more groundwater bores. Therefore, the area at risk is regarded as conservative due to limitations in the spatial coverage of air photo and bore data. A number of techniques to spatially extrapolate these data to infer potential areas at risk were trialled but were considered scientifically or statistically inadequate. Estimates of impacts are based on areas at risk having groundwater levels of less than 2 m. An impact assessment based on groundwater less than 5 m and rising was considered inappropriate. Total areas affected with groundwater less than 5 m and rising have been presented, but only for improved consistency with other States.
Areas affected are based on groundwater levels and air photo interpretation. The methodology applied for NSW is documented in Appendix 1 of NSW Dryland Salinity Assessment 2000 Report. The merged data, at a nominal scale of 1:250 000, shows actual areas where dryland salinity or water tables <2m below the surface have been measured. For current extent, every delineated area is underpinned by either air photo data or by one or more groundwater bores. There is high confidence in the accuracy of each of the delineated areas shown in the map above. It must be acknowledged that there will be other areas currently affected by dryland salinity. These have not been identified due to a combination of the inadequacies in the spatial coverage of available data and the currently available methods to spatially generalise water table maps from point data. Therefore, the area at risk is regarded as conservative. A number of techniques to spatially extrapolate these data to infer potential areas at risk were trialed but were considered scientifically or statistically invalid or data limited. All assessments of risk in this report are based on the criteria that each area at risk has groundwater levels of < 2 m below the surface. An assessment based on groundwater < 5 m and rising was considered inappropriate because it would result in disproportionate areas being identified as currently at risk. Those areas currently at 5m and rising were considered at risk in the short to medium terms and hence, would likely be included in the areas forecasted at risk in 2020 or 2050.
In areas that were spatially data rich, there is high confidence in the data presented in the map above. A major area with limited data was the Gwydir catchment. According to the analyses presented in this report, there are no areas currently affected by dryland salinity in the Gwydir. This is simply due to limited data available for these analyses. Therefore, the predictions in this report, particularly for the Gwydir catchment should be seen as conservative under-predictions of the true current status of dryland salinity in NSW.
Groundwater trends
The forecasted areas of risk for 2020 and 2050 are based on water table rises calculated from a network of monitored groundwater bores in NSW. These are fully described in Appendix 1 and are summarised as catchment average water table rises in the table below.
Highest rates of rise are evident for the southernmost catchments in NSW. Rates of water table rise tend to decrease in a northerly direction. This suggests that the impacts of rising water tables will take longer to surface in the northernmost catchments of NSW. High rates of water table rise for the southern catchments is one factor explaining the larger extent of current shallow water tables and dryland salinity in southern NSW.
| Catchment | Rise (m/yr) |
|---|---|
| Murray | 0.15 |
| Murrumbidgee | 0.14 |
| Lachlan | 0.11 |
| Macquarie | 0.09 |
| Castlereagh | 0.11 |
| Namoi | 0.06 |
| Gwydir | 0.04 |
| Macintyre | -0.01 |
How can dryland salinity risk change over time?
Areas of risk are based on groundwater levels and air photo interpretation. The merged data, at a nominal scale of 1:250 000, show actual areas where dryland salinity or watertables less than 2 m have been measured. For the extent map, every delineated area is underpinned by either air photo data or by one or more groundwater bores. Therefore, the area at risk is regarded as conservative due to limitations in the spatial coverage of air photo and bore data. A number of techniques to spatially extrapolate these data to infer potential areas at risk were trialled but were considered scientifically or statistically inadequate. Estimates of impacts are based on areas at risk having groundwater levels of less than 2 m. An impact assessment based on groundwater less than 5 m and rising was considered inappropriate. Total areas affected with groundwater less than 5 m and rising have been presented, but only for improved consistency with other States.
Maps depicting the forecasted extent of dryland salinity in the years 2020 and 2050 reveal large areas of future shallow water tables, particularly in the Murray, Murrumbidgee, Castlereagh and Macintyre catchments.
Area of land affected by depth of water tables less than 2m, 5m and 10m, have been calculated for the major catchments of the eastern Murray-Darling Basin. There are large increases in areas affected by shallow water tables for all eastern Murray-Darling Basin catchments. The largest increases are within the Murrumbidgee, Murray and Castlereagh catchments. The large areas estimated with water tables less than 5m below the surface in 2050, indicates a continuing risk into the longer term. Assuming the current risk is based on a criterion of depth to water table less than 2m, there is approximately 150 000 ha of land currently affected in the eastern catchments of the Murray-Darling Basin. If an alternative criterion of less than 5m and rising is considered, this increases to over 560 000 ha currently affected. This indicates the sensitivity of the results to changes to just one of the criteria used to ascertain current risk. All analyses undertaken in this study have been designed to ensure that results err on the side on conservatism.
| Catchment | 2000 | 2020 | 2050 |
|---|---|---|---|
| Lake Hume | 127 | 3 973 | 19 254 |
| Murray | 39 526 | 168 978 | 293 191 |
| Murrumbidgee | 58 098 | 286 848 | 469 500 |
| Lachlan | 19 793 | 38 845 | 153 264 |
| Macintyre | 3 800 | 25 500 | 67 224 |
| Gwydir | 0 | 0 | 2 973 |
| Namoi | 2 896 | 4 288 | 27 837 |
| Castlereagh | 1 197 | 12 005 | 174 666 |
| Macquarie | 25 072 | 36 767 | 90 848 |
| Richmond | 155 | n/a | n/a |
| Clarence | 91 | n/a | n/a |
| Bellinger | 27 | n/a | n/a |
| Manning | 34 | n/a | n/a |
| Hunter | 22 954 | n/a | n/a |
| Hawkesbury-Nepean | 4806 | n/a | n/a |
| Georges-Cooks | 13 | n/a | n/a |
| Deua | 11 | ||
| Total | 180 600 | 579 224 | 1 300 807 |
n/anot available
The best available estimates of rates of groundwater rise indicate that by 2020 rising watertables will occur in large areas of the Murrumbidgee and Murray catchments. By 2050, large areas of the Lachlan, Castlereagh and Macintyre catchments will also be affected (Tables below).
| Catchment | 2000 | 2020 | 2050 |
|---|---|---|---|
| Lake Hume | 3 973 | 12 999 | 37 496 |
| Murray | 168 978 | 227 187 | 293 514 |
| Murrumbidgee | 156 319 | 483 300 | 997 058 |
| Lachlan | 72 726 | 153 105 | 294 524 |
| Macintyre | 24 259 | 63 871 | 127 385 |
| Gwydir | 661 | 10 024 | 24 169 |
| Namoi | 10 244 | 20 427 | 57 528 |
| Castlereagh | 12 015 | 110 396 | 243 245 |
| Macquarie | 47 548 | 106 856 | 324 974 |
| Total | 496 722 | 1 188 163 | 2 399 892 |
Further information
- New South Wales Dryland Salinity Assessment 2000 report
- Australian Dryland Salinity Assessment 2000 report
- National Technical Overview Report of the State-based dryland salinity assessments
- Australian Groundwater Flow Systems Report
- New South Wales Department of Land and Water Conservation
- National Dryland Salinity Program
- National Action Plan for Salinity and Water Quality
New South Wales Dryland Salinity Assessment 2000
Link to Map maker to make a map using this information.
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