Indicator: IW-13 Catchment sediment load
Data
Suspended sediment loads for 500 km2 sub catchments
Source: National Land and Water Resources Audit 2002, Australian Catchment, River and Estuary Assessment 2002, volumes 1 and 2, Land and Water Australia, viewed 16 Dec 2005, http://audit.ea.gov.au/anra//coasts/docs/estuary_assessment/River_Findings.cfm.
Condition of river reaches based on the nutrient and suspended sediment load subindex
Source: National Land and Water Resources Audit 2002, Australian Catchment, River and Estuary Assessment 2002, volumes 1 and 2, Land and Water Australia, viewed 16 Dec 2005, http://audit.ea.gov.au/anra//coasts/docs/estuary_assessment/River_Findings.cfm.
| Region | Hillslope | Gully | Bank | Floodplain sedimentation | Reservoir sedimentation |
|---|---|---|---|---|---|
| Far North Qld | 2 942 | 106 | 144 | 1 184 | 0 |
| North Qld | 3 966 | 129 | 187 | 1 292 | 140 |
| Burdekin | 1 909 | 1 271 | 309 | 8 185 | 2 960 |
| Fitzroy | 9 526 | 1 008 | 519 | 8 377 | 919 |
| Moreton Bay | 971 | 93 | 209 | 538 | 254 |
| Qld South | 2 426 | 336 | 277 | 1 748 | 362 |
| Murray-Darling Basin | 10 719 | 4 387 | 4 434 | 16 295 | 3 977 |
| NSW North | 987 | 277 | 396 | 572 | 10 |
| NSW South | 1 902 | 667 | 428 | 1 314 | 279 |
| Vic East | 207 | 183 | 216 | 303 | 13 |
| Vic West | 41 | 213 | 174 | 285 | 17 |
| SA Gulf | 146 | 204 | 78 | 309 | 19 |
| WA South | 53 | 1 009 | 299 | 1 254 | 17 |
| Indian | 46 | 342 | 111 | 466 | 0 |
| Tasmania | 244 | 87 | 358 | 73 | 25 |
| Totals/averages | 46 086 | 10 312 | 8 138 | 42 194 | 8 992 |
Adapted from Source: National Land and Water Resources Audit 2001, Rivers - nutrient loads and transport, Land and Water Australia, Canberra, viewed 16 Apr 2005, http://audit.ea.gov.au/ANRA/water/water_frame.cfm?region_type=AUS®ion_code=AUS&info=river_nutrient.
| Region | Hillslope | Gully | Bank | Floodplain sedimentation | Reservoir sedimentation |
|---|---|---|---|---|---|
| Far North Qld | 15,457 | 425 | 575 | 5,826 | 0 |
| North Qld | 15,789 | 515 | 746 | 5,123 | 559 |
| Burdekin | 33,615 | 5,084 | 1,234 | 23,528 | 7,695 |
| Fitzroy | 29,108 | 4,033 | 2,077 | 27,086 | 3,112 |
| Moreton Bay | 5,205 | 373 | 837 | 2,035 | 1,747 |
| Qld South | 9,179 | 1,346 | 1,108 | 6,501 | 1,290 |
| Murray-Darling Basin | 36,352 | 17,556 | 17,736 | 53,309 | 15,952 |
| NSW North | 7,759 | 1,108 | 1,583 | 3,682 | 38 |
| NSW South | 8,926 | 2,666 | 1,710 | 5,364 | 1,590 |
| Vic East | 1,500 | 731 | 865 | 1,222 | 39 |
| Vic West | 527 | 851 | 694 | 1,167 | 78 |
| SA Gulf | 905 | 815 | 313 | 1,294 | 65 |
| WA South | 982 | 4,038 | 1,196 | 4,481 | 57 |
| Indian | 445 | 1,368 | 444 | 1,972 | 0 |
| Tasmania | 1,536 | 348 | 1,432 | 369 | 255 |
| Totals/averages | 170,264 | 43,999 | 34,130 | 148,605 | 32,559 |
Source: National Land and Water Resources Audit 2001, Rivers - nutrient loads and transport, Land and Water Australia, Canberra, viewed 16 Apr 2005, http://audit.ea.gov.au/ANRA/water/water_frame.cfm?region_type=AUS®ion_code=AUS&info=river_nutrient.
| Total length of reach (km) in each category and percentage of total in parentheses | Percentage of total length with data | ||||
|---|---|---|---|---|---|
| Largely unmodified | Moderately modified | Substantially modified | Extensively modified | ||
| Queensland | 2809 (4) | 12660 (20) | 40347 (64) | 7573 (12) | 88 |
| New South Wales | 1692 (3) | 23784 (41) | 27630 (48) | 4678 (8) | 97 |
| Australian Capital Territory | 9 (3) | 89 (33) | 172 (64) | 0 (0) | 100 |
| Victoria | 4419 (29) | 5067 (33) | 5287 (35) | 410 (3) | 96 |
| Tasmania | 3233 (59) | 1811 (33) | 429 (8) | 0 (0) | 98 |
| South Australia | 210 (3) | 2860 (39) | 4112 (55) | 203 (3) | 76 |
| Western Australia | 870 (4) | 2988 (15) | 15759 (78) | 461 (2) | 98 |
| Total | 13242 (8) | 49258 (29) | 93736 (55) | 13324 (8) | 81 |
Source: National Land and Water Resources Audit 2001, Rivers - nutrient loads and transport, Land and Water Australia, Canberra, viewed 16 Apr 2005, http://audit.ea.gov.au/ANRA/water/water_frame.cfm?region_type=AUS®ion_code=AUS&info=river_nutrient.
Murray Darling Basin
Total sediment supply to rivers in the basin is estimated at 29 million tonnes per year, which is 41 times the natural rate. River channels in over 60% of the Basin carry sediment loads that are more than 20 times the natural loads.
Less than 1% of this sediment is exported to the coast. The rest of the sediment is deposited on floodplains (46%), in river beds (33%) or in reservoirs (21%).
Source: Gehrke, P Gawne, B and Cullen, P 2003, What is the status of river health in the Murray-Darling Basin?, CSIRO Land and Water, Canberra, viewed 14 Oct 2005, http://www.clw.csiro.au/priorities/.
What the data mean
Nutrient and suspended sediment loads are greater than natural levels for over 90% of river length, and are severely modified in almost 10% the total river length.
Areas with the highest increase in phosphorus and suspended sediment loads include the north-east part of the Murray-Darling Basin, and areas subject to intense summer storms where gully erosion occurs on erodible and bare soils.
Some Queensland catchments (e.g. the Herbert River Basin) are severely modified in terms of sediment loads and this reflects the intense summer rainfall and seasonally low vegetation cover associated with large areas of cattle grazing.
In Western Australia, the natural sediment yield is very low, so even a relatively small increase in suspended sediment load can be significant.
The major sink for phosphorus and nitrogen is floodplain sedimentation.
Data Limitations
NLWRA 2001 data has not been updated.
Issues for which this is an indicator and why
Inland Waters - Catchment scale influences - Land and vegetation condition - Nutrients and sediments - sources and loads
Sediment loads is a direct measure of the pressure of nutrients and sediments on land and vegetation condition.
Other indicators for this issue:
- IW-12 Catchment nitrogen and phosphorus load
- IW-17 Exceedance of turbidity water quality triggers
- IW-18 Exceedance of suspended solids water quality triggers
- IW-24 Extent of sedimentation (incl sand slugs)
- LD-04 Area and change in area of exposed soil surface contributing to erosion
Inland Waters - Catchment scale influences - Land and vegetation condition - Erosion
Catchment erosion can lead to sedimentation, which can significantly alter the physical habitat of instream environments. Sediment loads in inland water catchments is one measure of the quantity of soil being eroded into waterways.
Other indicators for this issue:
- LD-04 Area and change in area of exposed soil surface contributing to erosion
- IW-17 Exceedance of turbidity water quality triggers
- IW-18 Exceedance of suspended solids water quality triggers
- IW-24 Extent of sedimentation (incl sand slugs)
Inland Waters - Habitat scale influences - In-stream habitat - woody debris and sand slugs
Catchment sediments can accumulate in streams and smother bed habitats and fill deep pools, which can significantly alter the physical habitat of instream environments. Sediments also supply nutrients and change the food web structure of an ecosystem. Sediment loads in inland water catchments is one measure of the quantity of soil being eroded into waterways.
Other indicators for this issue:
- IW-18 Exceedance of suspended solids water quality triggers
- IW-24 Extent of sedimentation (incl sand slugs)
- IW-25 Number and extent of re-snagging programs
- IW-30 Macroinvertebrate condition
Inland Waters - Habitat scale influences - Water Quality (for surface and groundwater) - Sediment and turbidity
Sediment can disrupt habitats by bringing with it nitrogen and phosphorous and through increased turbidity. Sediment loads in inland water catchments is one measure of the likelihood of turbidity occurring.
Other indicators for this issue:
- IW-12 Catchment nitrogen and phosphorus load
- IW-17 Exceedance of turbidity water quality triggers
- IW-18 Exceedance of suspended solids water quality triggers
- IW-19 Exceedance of total nitrogen and phosphorus water quality triggers
- IW-24 Extent of sedimentation (incl sand slugs)
- LD-04 Area and change in area of exposed soil surface contributing to erosion
- HS-61 Water quality in human settlements
Agricultural land use disturbs soils and can change loads of sediment entering inland waters, placing pressure aquatic species as well as on terrestrial species that rely on the water source. Quantities of sediment concentrating in surface water catchments are a direct measure of this pressure.
Other indicators for this issue:
- LD-04 Area and change in area of exposed soil surface contributing to erosion
- LD-06 Area and proportion of land affected by dryland salinity and acidity
- IW-12 Catchment nitrogen and phosphorus load
- IW-26 Forested streamlength
- HS-41 Water consumption by sector
Agricultural land use disturbs soils and can change loads of sediment entering inland waters and ending up in coastal waters where in can place pressure aquatic and estuarine species as well as on other coastal species that rely on the water source. Quantities of sediment concentrating in surface water catchments are a direct measure of this pressure.
Other indicators for this issue:
- CO-29 Change in area of coastal potential acid sulphate soils under development for human use
- IW-12 Catchment nitrogen and phosphorus load
Coasts and Oceans - Contributions and pressures between the coasts and oceans and inland water - Effect of changes in inland waters on the coasts and oceans
Sediment loads carried by inland waters can end up in coastal waters where sediments can place pressure aquatic and estuarine species as well as on other coastal species that rely on the water source. Quantities of sediment in surface water catchments are a direct measure of this pressure.
Other indicators for this issue:
- CO-01 Trends in selected groups of coastal and marine species and habitats
- CO-28 Quantity of discharges of different substances from humans activities to coastal and marine waters
- CO-29 Change in area of coastal potential acid sulphate soils under development for human use
- CO-46 Comparative water quality of coastal lakes and lagoons (water quality gradient from north to south)
- IW-12 Catchment nitrogen and phosphorus load
Coasts and Oceans - Contributions and pressures between the coasts and oceans and land - Effects of changes in the land on the oceans
Sediments and nutrients from the land can place pressure on coastal and estuarine waters.
Other indicators for this issue:
- CO-29 Change in area of coastal potential acid sulphate soils under development for human use
- CO-01 Trends in selected groups of coastal and marine species and habitats
- IW-12 Catchment nitrogen and phosphorus load
Further Information
NLWRA 2002
- Australian Catchment, River and Estuary Assessment 2002
- CSIRO Land and Water - Technical reports 2003
- CSIRO Land and Water - Technical reports 2001
- Report card 2003: for the waterways and catchments of South East Queensland (PDF - 1520 KB)
- The healthy waterways vision for south-east Queensland
- Australian Centre for Tropical Freshwater Research - Publications
Key
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