Learning from history: land and pasture degradation episodes in Australia’s rangelands
G.M. McKeon1, W.B. Hall1, J. Yee Yet1, G.S. Stone1, S.J. Crimp1, A. Peacock1, R. Richards2,
R.W. Tynan3, I.W. Watson4 and S.B. Power5
1
Queensland Department of Natural Resources, 80 Meiers Road, Indooroopilly Qld 40682
Department of Land and Water Conservation PO Box 77, Condobolin NSW 28773
Department of Environment, Heritage and Aboriginal Affairs (DEHAA), GPO Box1047, Adelaide South Australia 5001
4
Agriculture Western Australia, PO Box 483, Northam WA 64015
Bureau of Meteorology, PO Box 1289K, Melbourne VIC 3001Summary
The history of Australia’s rangelands includes regional episodes of land and pasture degradation. Many of these episodes follow a sequence of increasing animal numbers (domestic stock and other herbivores), in response to several years of favourable rainfall, and changing economic conditions. The subsequent return to ‘normal’ and/or drought conditions resulted in severe over-grazing. Knowledge of the causes of climatic variation, for example the Inter-decadal Pacific Oscillation, might help to prevent the repetition of these episodes.
The history of grazing of sheep and cattle in Australia’s rangelands over the last hundred years is the story of successful property development in a harsh environment. Grazing enterprises have been developed over time against a background of both high rainfall and commodity price variability occurring at annual and decadal time scales.
History also tells a story of degradation episodes often associated with extreme drought. Many of these have led to major government inquiries and intervention (Table 1). Sometimes these degradation episodes have been followed by recovery periods in which favourable seasons (and a pulse of mineralised nitrogen) resulted in luxurious plant and animal growth. Sometimes, however, the productivity of land for grazing purposes did not return, and scalds and woody weeds have remained.
There are a number of paradoxes resulting from the interaction of land management and climate variability:
The German philosopher Hegel commented in the early 19th century that ‘we can learn from history that we do not learn from history’. In fact it may be that ‘history’ does not lend itself to teaching unless we can understand how the processes of climate, ecology, management and policy interacted. In an attempt to overcome this human dysfunction, a group of idealistic scientists, supported by some visionary funding, have set out to build a drought/degradation alert system, ‘Aussie GRASS’, that would objectively assess and communicate the year-to-year change in degradation risk (Carter et al. 2000).
Carter et al. (2000) described eight major historical degradation episodes in Australia’s rangelands. Seven of the eight episodes involved severe drought periods (Table 1) lasting two to six years. Land and pasture degradation processes documented at the time of these episodes included loss of desirable perennial vegetation, dust storms, drifting sands, loss of surface soil, reduced infiltration capacity, water-driven soil erosion and woody weed infestation. Other features of these episodes were increased animal and human mortalities and financial failure of enterprises.
Most of the episodes were preceded by a buildup of stock numbers (and other herbivores such as rabbits) in response to periods of good seasons and substantial price variation. In eastern Australia, good seasons occurred in the early 1890s, late 1910s, early 1920s, mid 1950s, early 1970s and late 1990s. Because of the work of Power et al. (1999), we now suspect that quasi-decadal changes in the Pacific Ocean sea surface temperatures (the Inter-decadal Pacific Oscillation or IPO) may result in the amplification of the effects of La Niña conditions on rainfall in eastern Australia (IPO negative phase). The retention of high stock numbers through subsequent drought periods resulted in the regional degradation episodes described in Table 1. Thus the impact of current favourable seasons in eastern Australia on stock numbers should be closely monitored as an early indicator of increasing risk of degradation, especially when the mode of Pacific Ocean behaviour returns to conditions that appear to make ‘big wets’ unlikely (i.e. positive IPO condition). Historical evidence indicates that where conservative stocking policies have been adopted, or when rapid reduction in stock numbers occurred in response to the onset of drought, degradation appears to have been minimal.
Other more specific causes of degradation were:
Although the IPO is not yet fully understood, its behaviour appears to have had a strong effect on historical degradation and recovery episodes. Paradoxically, wet periods, associated with negative IPO, have contributed to degradation episodes by: (a) raising expectations of the land’s carrying capacity which proved too high to be sustained through subsequent dry and drought periods; and (b) providing the conditions for woody weed establishment which, in the absence of fire, have caused the loss of desirable perennial grasses and reduction in carrying capacity. However, the wet periods have also provided the opportunity for some recovery of vegetation following historical degradation episodes through regeneration of desirable perennial species. Thus this aspect of the Pacific Ocean behaviour (La Niña and negative IPO conditions) seems to be a very important component of the resilience of eastern Australia’s rangelands. The uncertain impact of future global warming on this aspect of Pacific Ocean behaviour indicates that we should not take this climatic component of resource resilience for granted.
Acknowledgements
The funding from AGO and CVAP (LWRRDC) is very gratefully acknowledged.
References
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Table 1. Regional degradation episodes in Australia’s rangelands.
|
Episode |
Degradation Episodes |
Severe Drought Period |
|
1 |
1890s in western NSW involving soil erosion, woody weed increase, rabbit plagues, substantial financial losses and financial hardship and resulting in Royal Commission of 1901 (Anon. 1901, Noble 1997) |
1897-1902 |
|
2 |
1920/30s in South Australia involving substantial loss of perennial vegetation and soil erosion (Ratcliffe 1937) resulting in government legislation for regulation of carrying capacity (Donovan 1995) |
1927-1931 |
|
3 |
1930s in Gascoyne region of Western Australia involving substantial loss of perennial shrubs, soil erosion and animal losses documented in the Royal Commission of 1940 (Willcox and McKinnon 1972) and subsequent inquiries (Jennings 1979) |
1935-1941 |
|
4 |
1940s in western NSW involving substantial dust storms and animal losses graphically portrayed in Russell Drysdale’s paintings and Newman’s newspaper reports (Condon 1999) and supporting the need for government action (Beadle 1948) |
1943-1945 |
|
5 |
1950s in western NSW involving large increases in woody weeds resulting in reduced carrying capacity and income (Anon. 1969, Hodgkinson et al. 1984) |
- |
|
6 |
1960s in central Australia involving wind and water erosion resulting in extensive surveys and re-assessment of carrying capacity (Condon et al. 1969, Purvis 1986) |
1960-1966 |
|
7 |
1960/70s in south-west Queensland involving soil erosion and woody weed invasion resulting in the government-sponsored South-West Strategy supporting review of recommended carrying capacities and property amalgamation (Warrego Graziers Association 1988, Johnston et al. 1996) |
1964-1966 |
|
8 |
1980s in north-east Queensland involving soil erosion and loss of desirable perennial grasses resulting in extensive government-sponsored surveys (De Corte et al. 1994) and dramatic grazier response (Landsberg et al. 1998) |
1984-1988 |