Oxford University, UK
Ben Sharp
Background |
Alluvial floodplains | Lowland habitats | Sandstone
plateaus |Future Directions |
Savanna environments worldwide are notoriously dynamic; the
identities and relative abundances of woody plant species have been
known to change dramatically over time in response to a whole range
of management and environmental factors, such as fire, grazing,
climate, and natural cycles of die-back and recovery. Vegetation
changes may be natural or they may be caused by human activity;
regardless of the causes such changes often have serious
implications for land use. Pastoral productivity, conservation
value, landscape-scale carbon storage, and physical access to the
landscape are all affected by changes in woody vegetation.
Anecdotal historical evidence (see Savanna Links,
Issue 14, link below.) suggests that significant and in some places
dramatic changes may be occurring in savanna landscapes in the
Victoria River District.
This was the first study to systematically examine patterns of
woody vegetation change across a range of savanna environments in
the Victoria River region with explicit consideration of the
burning and grazing history of the area.
The study was located on Bradshaw Field Training Area, near
Timber Creek, Northern Territory. Historical (1948) and recent
(1993-7) aerial photographs were digitally processed and analysed
to assess woody vegetation change over the past 50 years, and a
variety of vegetation surveys were conducted on the ground to
verify the results of the air-photo mapping and to identify the
mechanisms responsible for observed changes. There are clearly
different change mechanisms operating on three distinct savanna
habitats within the study area:
Within the seasonally flooded alluvial zone near the Victoria
River and tributaries there has been a clear and dramatic increase
in woody vegetation across the full range of floodplain habitats
since 1948. In some locations formerly treeless plains have become
virtually closed woodlands since that time.
Invasion and proliferation by two identified tree species is
responsible for all observed vegetation increases. Evidence
strongly suggests that these increases are a direct consequence of
extreme overgrazing, most likely in the 1970s, which rendered the
landscape not flammable and permitted the rapid increase of woody
plants in the absence of fire mortality. The change is clearly
irreversible and almost certainly implies reduced pastoral
productivity.
By comparing edaphically-similar habitats that have been grazed
intensively for different lengths of time, the impact of grazing on
lowland savanna vegetation was assessed. It is clear that
multiple-change mechanisms are occurring simultaneously on
different portions of grazed lowland habitats. Low-lying areas and
drainage areas are experiencing woody vegetation increase as the
result of proliferation by a single species of melaleuca.
This effect is apparently climate-driven, but fire/grazing
interactions may mediate the extent of the climatic effect. On
lowland rises dominant bloodwood (genus Corymbia) woodlands
are in decline on heavily-grazed areas as a consequence of invasion
by several species of fire-sensitive shrubs following
fire-exclusion by cattle. The invasive shrubs presumably
competitively exclude bloodwood regeneration, and may even drive
established adults to an early death where grazing pressure has
been consistently high. In contrast, ungrazed/ frequently-burnt
lowland savannas are stable and continuously-regenerating. Corymbia
woodland instability under heavy grazing has implications for
pastoral productivity, conservation, and landscape-scale carbon
storage, but research suggests that the effect may be reversible
with proper periodic application of fire.
Sandstone plateaus were surveyed to assess vegetation dynamics
in habitats remote from the effects of ungulate grazing. The
condition of fire-sensitive Callitris intratropica
populations clearly indicates that there has been a widespread
increase in the frequency and/or intensity of fire on sandstone
plateau habitats within the study area, likely as a consequence of
the cessation of traditional Aboriginal burning activities.
While areas of both vegetation increase and vegetation decline
are evident in the study area, it is apparent that all dominant
savanna woodland species on this habitat (genera Eucalyptus and
Corymbia) are resilient to the altered fire regime. What changes
have occurred are the result of natural cycles of die-back and
regeneration in response to stochastic variables that vary on a
small scale, such as patchy early-wet-season rainfall events. Total
net woody vegetation cover has been relatively unchanged in the
past 45-50 years.
It is hoped that this research will inform better
decision-making and predictive capability for the sustainable use
and management of grazed savanna landscapes in northern
Australia.
*Operational funding.