Australia — Conservationists should take heart that Australia is finally waking up to the biodiversity crisis in Australias north. It is an urgent problem: right now, a diverse assortment of our small mammals bandicoots, tree-rats, possums are rapidly vanishing from northern Australias most iconic biodiversity strongholds.
Work in Kakadu National Park has shown that between 1996 and 2009 mammal populations crashed, with species richness and total abundance decreasing by 65% and 75% respectively.
Most alarming is that scientists cant tell us why this is happening, let alone how to stop it.
Prominent conservationist Tim Flannery recently drew attention to the plight of northern Australian mammals in his Quarterly Essay and accompanying article in The Conversation (as have others writing in The Conversation and other media). Though valuable, these articles tend to oversimplify the complex and unresolved ecological questions that must underpin an appropriate management response.
Flannery asserts that the main driver appears to be changes in fire regime, compounded by the presence of feral cats. This overstates our current understanding.
Unlike most other conservation issues in Australia, the most immediate obstacle is lack of knowledge. We simply dont know why mammals are declining or what management interventions could halt the decline. Frequent fire hazards
There is widespread agreement that the mammal decline has something to do with fire. However, scientists have failed to answer the critical question with a large budget, what type of fire regime should (and could) land managers implement to benefit small mammals?
The managers of Kakadu the epicentre of the northern mammal decline have been roundly criticised by conservation scientists for their excessive use of prescribed burning to prevent high-intensity wildfires. However, these same scientists have been remarkably silent on alternative management approaches.
There is evidence that high fire frequencies are detrimental to small mammals, demonstrated most significantly in the work by John Woinarski and colleagues. They found that in Kakadu, sites that had been most frequently burnt experienced the greatest small mammal declines over the period 1996-2009.
The challenge is understanding exactly what it is about fire regimes that has changed. The breakdown of traditional Aboriginal fire management and possible increase in the size and intensity of fires is often suggested as a trigger. However, in places like Kakadu this occurred many decades before mammal populations crashed. A tinderbox landscape
There is a widely held view that there is too much fire in parks like Kakadu. However, calls for widespread reductions in fire frequency in the north tend to overlook the fundamental ecology of fire.
Fire is so prevalent in this region not because of people, but because of the intense monsoon climate. A reliable wet season promotes rapid grass growth, and a long dry season promotes drying of grassy fuels.
Abundant lightning at the end of the dry season ensures high fire activity. The effect of humans is to merely jump start the fire season, providing an ignition source earlier in the year.
It is inevitable that a large proportion of the landscape burns each year. For Kakadu, this figure is remarkably constant at around 45%.
The only lever available to land managers is whether burning occurs predominantly in the early (AprilJuly) or late (AugustNovember) dry season.
This fact has driven the prevailing approach to fire management in northern Australia that of extensive early dry season burning to pre-empt intense late dry season fires. Fighting fire with fire
Because they occur under milder fire conditions, early dry season fires tend to be significantly less intense, smaller, and patchier than late dry season fires.
It is well known that many fire-sensitive plants (such as the northern cypress pine, and to a lesser extent sandstone heaths) benefit from an earlier fire regime. There is also evidence that this applies to small mammals too.
Based on satellite-derived fire mapping since 1980, we know that the proportion of Kakadu that burns each year has not changed over the last 32 years. However, it is clear that there has been a dramatic switch from late dry season to early dry season fires. Although such a shift in fire season is thought to be good for biodiversity, including mammals, there may be more insidious changes that have taken place.
For example, retired Kakadu ranger Greg Miles has suggested that a vicious grassfire cycle is now firmly established in Kakadu. The theory is that highly flammable speargrass (Sorghum species) increased in abundance following the breakdown of Aboriginal fire management, and now fuels fires of much greater intensity.
Even in the early dry season, speargrass fires tend to be of high intensity and low patchiness. Hence, abundant speargrass effectively negates the advantages of early dry season prescribed burning.
It is noteworthy that the introduced swamp buffalo was virtually eradicated from Kakadu in the 1980s, after more than a century in the park. Some suggest that this may have further promoted an increase in speargrass abundance and fire intensity. The only major change to have immediately preceded the mammal collapse in Kakadu was the eradication of the buffalo.
Whether a grass-fire cycle can be reversed is not clear. One option put forward is to burn heavily infested areas in the wet season, before the speargrass can produce seed. Another option that warrants objective consideration is grazing by exotic herbivores, especially as highly-flammable exotic grasses overtake the park.
We need a better understanding of how fire regimes have changed over the last century. Despite Kakadu having the best-described fire regimes in northern Australia, the available fire records are still relatively short (from 1980 on). These satellite-derived records are also limited to fire frequency, size and season. Recent changes in a broader spectrum of fire regime attributes, such as intensity and fine-scale patchiness, are highly uncertain. Testing the critics’ claims
Vague calls for less fire are unhelpful. Instead, we need to specifically identify what kinds of fire management work best for mammals at landscape scales. This means considering the intervals between fires, fire intensity, size and patchiness.
We also need to determine whether areas of long, unburnt vegetation are important for small mammals’ survival, and how different species are affected by mosaic burning practices, in which fires of varying intensities, scales and times are burnt to create a patchwork or mosaic effect in the landscape.
Some researchers suggest that Aboriginal fire management would have resulted in such a mosaic, and the loss of this mosaic has triggered biodiversity declines. Although intuitively appealing, there is remarkably little direct evidence to support this hypothesis, especially in relation to small mammals.
The greatest challenge will be to translate these research findings into explicit management actions.
For example, Alan Andersen and colleagues described an approach to increasing the abundance of long unburnt areas, without actually decreasing the proportion of the landscape burnt each year. The trick is to decrease the randomness of burning, by concentrating prescribed burning on recently burnt areas, avoiding long unburnt areas.
If the current model of extensive early dry season burning is so obviously failing, then there is an onus on its critics to propose something new. Unlocking answers from the land
Land managers need to do their bit too by facilitating collaborative research in conservation areas.
Sadly, national parks can be difficult places to conduct research in northern Australia, hindered by slow-moving bureaucracies and priorities other than biodiversity conservation.
The quantity and quality of research coming out of Australian Wildlife Conservancy properties in the Kimberley demonstrates how much easier it can be to conduct conservation research on private land.
Close collaboration between scientists and land managers is essential, ideally within an adaptive management framework. This is where new management interventions can be repeatedly tried, evaluated, improved or potentially abandoned.
Most importantly, unorthodox management interventions need to be objectively evaluated. These might range from grazing by large exotic herbivores (such as buffalo and cattle) to reduce fuel loads, to wet season burning of annual grasses.
As Tim Flannery points out, things are now so dire that we cannot afford to persist with business as usual. The failure was in the forest areas.Advertisement
Following a 10-year strategy, ACT fire managers have created a mosaic across the landscape of different fuel levels, burning at every opportunity.
But forests have been too wet to burn this spring and the past two summers.
A network of 500 fire trails and strategic burns along the north-west urban edge, heavy grazing and extra grass slashing will create a fortress for the territory which forecasters say faces a higher than average risk this summer.
After a fire-fuelled tornado in January 2003 killed four Canberrans and frightened thousands more, CSIRO fire expert Phil Cheney told the subsequent inquiry the fire’s penetration into urban areas under extreme conditions did not reflect a failure of fuel management on the urban interface.