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1370.0 - Measuring Australia's Progress, 2002  
Previous ISSUE Released at 11:30 AM (CANBERRA TIME) 19/06/2002   
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Contents >> The supplementary commentaries >> Inland waters: Looking more closely

The headline commentary discusses the sustainability of water extraction across Australia. This commentary looks in more detail at the history of water use in Australia, and how the water that is extracted today is used. It goes on to discuss some of the ways in which some of our inland waters are deteriorating.


Dams greater than 100 gigalitres
Graph - Dams greater than 100 gigalitres



Water resource development has been integral to the growth of Australia's economy, towns and cities. It has also affected the health of many river systems.

As human settlements and agriculture increased in the nineteenth century, so did the need for reliable water supplies. Australia's unpredictable climate caused highly variable river flows which could not support intensive settlement.(SEE FOOTNOTE 1) Dams were constructed to regulate rivers and store water, primarily for domestic, industrial and agricultural use.

The number of dams in Australia increased during the first half of the twentieth century, but the increase was particularly rapid after the 1950s. Australia now has around 90 major dams, each with a capacity greater than 100 gigalitres (GL). (One hundred gigalitres is the volume of water contained in 100,000 Olympic-size swimming pools). (SEE FOOTNOTE 2) Dam construction and water diversions have influenced the hydrology and ecology of a number of Australian river systems. The patterns of flow in some rivers, once highly variable, have been stabilised and the flow of water has been reduced. Some of the impacts of these changes are discussed below.


GROUNDWATER

Groundwater is also an important resource. Up to four million Australians are totally or partly dependent on groundwater for domestic water supplies. (SEE FOOTNOTE 3) In 1996-97 approximately 5,000 GL of groundwater were extracted. (SEE FOOTNOTE 4) Relatively little is known about the impact of groundwater extraction on the Australian environment: many land and water ecosystems are dependent on groundwater for at least some of the time, but the interactions between groundwater and these systems are poorly understood. (SEE FOOTNOTE 3)
River condition (biota index), by State

% of sites
assessed
where biota was
Significantly
Severely
Extremely
impaired
impaired
impaired

State
%
%
%
NSW
34
13
3
Vic.
20
13
1
Qld
17
2
1
SA
12
1
4
WA
29
6
1
Tas.
20
3
2
NT
10
2
. .
ACT
29
7
. .
Aust.
23
6
2

Source: National Land and Water Resources Audit.(SEE FOOTNOTE 5)
The National Land and Water Resources Audit (NLWRA) has recently published an index of river condition. (SEE FOOTNOTE 5) NLWRA's assessment collated and interpreted data for rivers in the more intensively used parts of Australia. The assessment builds on other river assessment initiatives such as the National River Health Program. The data are based on the work of scientists who examined the water to measure the diversity of macroinverterbrates (bugs) that inhabit different stretches of river. Because macroinvertebrates are sensitive to changes to river catchments (e.g. land clearing) as well as changes to the condition of the river (e.g. water quality) and spend much of their life in the river, they are good indicators of river condition.

The data show that 23% of assessed sites were significantly impaired, and had lost 20-50% of macroinverterbrates expected to be present. A further 6% were severely impaired (had lost 50-80% of expected macroinvertebrates) and 2% were extremely impaired (had lost more than 80% of expected macroinverterbrates). The majority of impaired river basins were in New South Wales.

Net water use(a)
Graph - Net water use(a)



NET WATER USE

In 1983-84, Australia used an estimated 14,600 GL of water. By 1996-97 this had risen to 22,200 GL, an increase of over 50% in 14 years. (SEE FOOTNOTE 6)

There was some fluctuation in use through the mid-1990s, perhaps in part because of the influence of our highly variable climate, but overall the trend was one of increasing use. Water use rose by 3,600 GL between 1993-94 and 1996-97; a large proportion of this increase is attributed to agricultural activity, in particular livestock, pasture, grains (excluding rice) and other agriculture. (SEE FOOTNOTE 6) There were also increases in the use of water in the rice and cotton industries, with smaller increases for use among farmers growing grapes, or other fruit and vegetables.


EFFECTS OF DEVELOPMENT - WATER QUALITY

The development of water resources has had many effects on our freshwater ecosystems. In 2002, the NLWRA produced an Environment Index that assesses river condition depending on the nutrient and sediment suspended in the water, the catchment and hydrological disturbance, and the condition of streamside vegetation. (SEE FOOTNOTE 5) The degree of modification depends on the extent of change from these factors. A moderately modified river, for example, has a catchment dominated by land uses that disturb the river, with associated water extraction, habitat changes (such as a reduction in streamside vegetation of 50-75% of original cover) and loads of sediment or nutrients above natural levels. Some 90% of Australian rivers were assessed. Among these rivers, the index found that:
  • 66% of river length was moderately modified;
  • 19% was substantially modified; and
  • 1% was severely modified.

Two-thirds of river length assessed in the Northern Territory is in largely unmodified condition, as is about two-fifths of Tasmanian river length assessed. In the other States and Territories more than 80% of assessed river length was moderately modified or worse. (SEE FOOTNOTE 5)

Irrigation and tree clearing have caused rising water tables and increased the salt in groundwater in many places. This increasing salinity is one of the most significant threats to the health of our aquatic ecosystems and our water supplies.(SEE FOOTNOTE 3)

Drinking water for most of South Australia and many inland towns in New South Wales is at risk from increasing salinity. (SEE FOOTNOTE 3) If salinity is not controlled in the Murray River, Adelaide's drinking water has been predicted to exceed guidelines for salinity on two days in five by the year 2020. (SEE FOOTNOTE 3) Nationwide, 80 important wetlands are affected by salinity, and this is predicted to rise to 130 by the year 2050. Many of these wetlands contain species at risk from salinity. (SEE FOOTNOTE 3) The causes of salinity and its impact are discussed in the commentary Land degradation.

The removal of streamside vegetation allows increased sediment into the river, which can add nutrients and pollution harmful to aquatic species and overall river health. This vegetation is seriously degraded in many catchments from clearing, grazing and salinity: in some areas of Western Australia, for example, 50% of rivers and creeks have lost their streamside vegetation and fewer than 10% of wetlands have healthy fringing vegetation. (SEE FOOTNOTE 3)

There are as yet few nationwide data on the extent and impacts of pollutants entering inland waters. Although Australia uses much lower levels of pesticides than other OECD countries, pesticide use is thought to have increased strongly here since the early 1980s. (SEE FOOTNOTE 3) Cotton, rice, sugar cane and horticultural crops are the highest users of pesticides. (SEE FOOTNOTE 3) Since 1990 at least 20 fish kills in New South Wales rivers have been attributed to pesticides. (SEE FOOTNOTE 3) Other pollutants, such as heavy metals and oil, may have localised effects. But in some States and Territories at least, the management of these sources has improved in the views of the State of the Environment Committee. (SEE FOOTNOTE 3) For example, stormwater management plans have been set up for all urban catchments in New South Wales, while the use of pollution licensing systems has increased throughout Australia. (SEE FOOTNOTE 3)

EFFECTS OF DEVELOPMENT - RIVER FLOW

Water resource development has altered the seasonal characteristics, rate and variability of flows in many river systems. For example the flow of the Murray River at Albury would naturally peak in September and be at a minimum in February. Now, water is stored in spring and summer for irrigation, and peak flows, which are reduced, occur in summer, with minimum flows in July. (SEE FOOTNOTE 7)

Ecological processes have been altered by changes in flow patterns and reductions in the size and variability of flows. Natural wetting and drying processes have changed, and many in-stream habitats, floodplains and wetlands have become permanently flooded. (SEE FOOTNOTE 8) This, in tandem with the overall decrease in flows, has led to a reduction in available habitat and also reduced the reproductive cues of many aquatic species. (SEE FOOTNOTE 8, 9) And so the reproductive patterns of both wetlands water birds and native freshwater fish have been affected, leading to a decline in their abundance.

The release of cold water from storages has also affected the reproductive cycle of many aquatic species, (SEE FOOTNOTE 7) while changes in flow patterns have helped exotic species, such as carp, to spread and out-compete native species. (SEE FOOTNOTE 9) Reduced flows are one factor that can lead to more severe algal bloom outbreaks because of stagnation (see box below).

Natural and actual flows per month, Murray River at Albury - 1998-99
Graph - Natural and actual flows per month, Murray River at Albury - 1998-99

ALGAL BLOOMS

Algae are tiny organisms and an important part of the food chain. But when some algae multiply in sufficient concentrations to 'bloom' they can poison the water, affecting people, wildlife and livestock. Some types of algae are not toxic, but others carry poisons that can cause liver damage or tumour growth, acute poisoning and paralysis in animals, and skin and eye irritation. (SEE FOOTNOTE 10)

Outbreaks of algal blooms have been recorded as far back as 1878 in Australia; (SEE FOOTNOTE 10) but they are now far more common. Blooms are often indicative of a decline in the ecological health of freshwater systems. They are not caused by a single factor and can occur in urban or rural areas. They are most common in storages, lakes, wetlands and stretches of rivers that have still waters and are enriched with plant nutrients, nitrogen and phosphorus (these substances can enter water from fertiliser run-off, fish farms, sewage and stock manure as well as from urban storm water). They are a significant problem in reservoirs and other water storage areas because of the increased costs of treatment, management and sometimes provision of alternative water supplies.

The location and frequency of algal blooms vary across Australia, but they are common and persistent in many waterways throughout Australia where they impose a significant economic cost on the community, industry and government in both urban and rural areas. (SEE FOOTNOTE 3) It has been estimated that algal blooms cost Australian water users over $150m annually. (SEE FOOTNOTE 11)


NATIVE FRESHWATER FISH

Of over 200 native species of freshwater fish in Australia, the Commonwealth lists (SEE FOOTNOTE 11) species as endangered and (SEE FOOTNOTE 10) as vulnerable to extinction. (SEE FOOTNOTE 12) There are at least six threats to our fish: degradation of habitat; pollution; reduced environmental flows; barriers to fish migration; introduced species; and fishing pressures. The extent of each threat varies across Australia, reflecting differences in water resources and urban and agricultural development. While fishing has played a role in the decline of fish populations, the modification and degradation of fish habitats have had the most substantial impact. (SEE FOOTNOTE 13)

The construction of dams, for example, has altered fish habitat by creating a barrier to movement, altering flow patterns and reducing water flow. Changes to natural flooding regimes have had different effects, such as allowing exotic fish like the European Carp to dominate or out-compete native species (the latter are less able to adjust to the new regimes). This has led to the decline of native fish in the lowland regions of the Murray and Murrumbidgee rivers. (SEE FOOTNOTE 9)

Some 35 exotic fish species have become established in inland waters, with eight identified as having a significant impact. (SEE FOOTNOTE 3) Many were introduced into Australia for ornamental or fishing purposes (and in 1998-99 around half of the fish stocked in inland waters were exotic species). (SEE FOOTNOTE 14) Some of these species, such as trout and carp, are having detrimental effects on native fish. Carp feed by uprooting and killing aquatic plants which native species feed on. The carp thereby disrupt the river bank and stir up sediments which free nutrients that enhance toxic algae (they also contribute to algal blooms by preying on the species which feed on the algae). (SEE FOOTNOTE 15)

Five species of trout and salmon have been introduced to Australia, and over 5.5 million exotic trout and salmon were stocked into our inland waters in 1998-99 alone, although some of these were into artificial compounds where exotic stock can be monitored to try to prevent risk to native fish. (SEE FOOTNOTE 14) Trout have had an impact on the native galaxid family of fish, nine species of which are considered to be at risk. Adult trout are known to eat galaxids, while juvenile trout compete with galaxids for food. (SEE FOOTNOTE 16)


PROTECTING AUSTRALIA'S INLAND WATERS

Australian governments and others are responding in a number of ways to the continuing deterioration in the health of many bodies of water. Although overall water use has risen (most of Australia's water is used by agriculture, which is also largely responsible for the increase), there was a decline in domestic water use for most large urban centres during the 1990s. The decline has been linked to a combination of water pricing, consumer education, the use of water-saving appliances and higher residential densities (linked to smaller gardens and lower outdoor water use). (SEE FOOTNOTE 3) Although the use of water supplies has exceeded sustainable limits in some places, in parts of tropical Australia there is probably scope to collect more water without causing significant environmental damage. And there is potential to get more from the water we extract: on average only 77% of diverted water reaches the customer; the rest is lost to seepage or evaporation. (SEE FOOTNOTE 4)

The key pressures on our inland waters relate to each other and the land that surrounds the water. For example, increasing river salinity caused by dryland salinity can result in water becoming too saline for drinking or irrigation. It can also kill streamside vegetation. This, in turn, can increase erosion in river banks, which can cause further deterioration in water quality and loss of aquatic species.

Governments have introduced a range of reforms to the water industry, which have included creating a market for water so that it can be reallocated to higher value crops or uses. And in southern and eastern Australia, caps on extraction (such as that operating in the Murray - Darling Basin) are being introduced to try to prevent further degradation of inland waters and provide better security of supply for industry. Although there is still much to learn, research and reporting into Australia's water resources by the National Land and Water Resources Audit, the ABS, State of the Environment Reporting programs and State and Territory water management agencies are improving our knowledge of this valuable resource.


FOOTNOTES

1 Murray-Darling Basin Commission (MDBC) 1990, The River Murray system, The Regulation and distribution of River Murray Waters, MDBC, Canberra.

2 With an olympic swimming pool being 20m x 50m x 1m.

3 State of the Environment Advisory Council 2001, Australia - State of the Environment Report 2001, CSIRO Publishing, Melbourne.

4 National Land and Water Resources Audit. (NLWRA) 2001, Australian Water Resources Assessment 2000, Surface Water and Groundwater - Availablity and Quality, NLWRA, Canberra.

5 National Land and Water Resources Audit. (NLWRA) 2001, Australian Catchment, River and Estuary Assessment 2001, NLWRA, Canberra.

6 Australian Bureau of Statistics 2000, Water Account for Australia 1993-94 to 1996-97, Cat. no. 4610.0, ABS, Canberra.

7 Murray-Darling Basin Commission (MDBC) 2000, Impacts of Water Regulation and Storage on the Basin's Rivers, MDBC, Canberra.

8 Kingsford, R.T. 2000, "Ecological impacts of dams, water diversions and river management on floodplain wetlands in Australia", Austral Ecology, Vol. 25, pp. 109-127.

9 Gehrke, P.C., Brown, P., Schiller, C.B., Moffatt, D.B. and Bruce, A.M. 1995, "River regulation and fish communities in the Murray-Darling River System, Australia", Regulated Rivers: Research and Management. Vol. 11, pp. 363.375.

10 Flett, D. and Thoms, M.C. 1994, "Blue-green algae and our degraded waterways", in (eds) Hirsh, P. and Thoms, M.C., Australasian Geography for the 1990s, Department of Geography, University of Sydney, Sydney.

11 Land and Water Resources and Development Corporation (LWRDC) 1999, Cost of Algal Blooms. Submitted by the Atech Group to the Land and Water Resources and Development Corporation and The Murray-Darling Basin Commission, LWRDC Occasional Paper 26/99, Canberra.

12 The Environment Protection and Biodiversity Conservation Act 1999, Commonwealth Government of Australia.

13 Davies, K.M., Kearney, R.E. and Beggs, K.E. 2000, "Research priorities for Australia's Freshwater Fisheries", Australian Journal of Environmental Management, pp. 28-37.

14 Australian Bureau of Statistics 2001, Australia's Environment: Issues and Trends, Cat. no. 4613.0, ABS, Canberra.

15 Crabb, P. 1997, Murray-Darling Basin Resources, Murray-Darling Basin Commission, Canberra.

16 Cadwaller, P.L. 1996, Overview of the Impacts of Introduced Salmonids on Australian Native Fauna. Australian Nature Conservation Agency, Canberra.

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