Fire regimes, fire‐sensitive vegetation and fire management of the sandstone Arnhem Plateau, monsoonal northern Australia

Abstract

Summary 1.A fire history (1980 to the present) developed for Kakadu National Park, derived mostly from manual interpretation of LANDSAT MultiSpectral Scanner (MSS) imagery, was used as the temporal basis for undertaking rapid assessment of the effects of fire regimes on floristically diverse vegetation containing many regionally endemic species, occupying sandstone formations of the Arnhem Plateau, monsoonal northern Australia. 2. Three broad vegetation types were identified through TWINSPAN classification of floristic composition at 108 sample plots: AIIosyrzcavpia-dominated closed forest; open forest/woodland savanna with an annual grass understorey; and open shrubby heath interspersed with perennial hummock grasses. All sampled vegetation occurred on freely draining, oligotrophic substrates derived from sandstone parent materials; grazing and browsing of sampled vegetation were not significant factors. 3. The three fire frequency parameters derived from the assembled fire history ('years unburnt', 'fire frequency', 'shortest interfire interval') were autocorrelated. Correlative analyses between vegetation structure and soil nutrient variables, and 'years unburnt', demonstrated generally increasing shrub densities, fuel loads and soil fertilities with increasing time since last burnt. Identified limitations in assembled data included: substantial between-plot structural variation for respective vegetation types, reflecting diverse ecological and fire histories of individual plots; and inability to describe accurately the important fire regime variable 'fire intensity' from the imagery used. 4. Assessment of the reproductive maturity of obligate seeder shrub species indicated that, whereas vegetation at some sites could tolerate burning after 3-year intervals without loss of floristic diversity, many species required fire-free intervals of more than 5 years, particularly those occupying harsher, rocky sites. In contrast, fine grass and litter fuels were sufficient to support intense fires in all representative situations under late dry season climatic conditions within 1-3 years of having been burnt previously. 5. Published fire history data for the period 1980-94 show that 40% of vegetation occupying sandstone-derived landforms in Kakadu National Park have been burnt at frequencies of at least 1 in 3 years; such fire frequencies evidently cannot be sustained without substantial loss of obligate seeder species, comprising 54% of the sampled shrubby heath flora.

Stemming the tide: progress towards resolving the causes of decline and implementing management responses for the disappearing mammal fauna of northern Australia

“…The breakdown of Aboriginal fire management leading to a fire regime characterised by frequent and spatially extensive late dry season fires has been well-documented on the Arnhem Plateau in northern Australia, and has led to significant impacts on a range of plant taxa and communities, including cypress-pine, sandstone heathland and rainforest (Russell-Smith et al 2002;Russell-Smith et al 1998). A critical aspect of Aboriginal fire management is that it reportedly maintains a fine-scale mosaic of vegetation of varying time since fire (Bliege Bird et al 2008;Bowman et al 2004), and spatiotemporal heterogeneity of fire regimes -sometimes called 'pyrodiversity' (Martin and Sapsis 1992).…”

Managing the matrix: decadal responses of eucalypt‐dominated savanna to ambient fire regimes

“…Even in rugged sandstone formations, accumulation of fine grass and litter fuels is sufficient to support intense fires (.5000 kW/m) in all but exposed rock situations under late-dry-season climatic conditions within 1-3 years of having been burned previously (Russell-Smith et al 1998). Fires in the region are almost invariably anthropogenic in origin and ground-borne.…”

Indigenous participation in Australian economies : Historical and anthropological perspectives

“…Backed by Western science (for example, Edwards et al 2003;Russell-Smith et al 1998), park managers try to simulate these, mainly by dropping from helicopters permanganate-filled ping-pong balls injected with glycol. These little balls ignite on reaching the ground and theoretically take the place of the former hunter-gatherers and their fire-sticks.…”