Hot Topic

Burning giants in the tropics

Wednesday, 1 January 2014  | 

Authors: DYP Tng (University of Tasmania), GJ Jordan (University of Tasmania) and DMJS Bowman (University of Tasmania)

The need to maintain a mosaic of rainforest and eucalypt forest in the Australian Wet Tropics World Heritage Area poses a perplexing conundrum for land managers. Rose Gum (Eucalyptus grandis) dominated giant eucalypt forests at the margins of World Heritage tropical rainforests are habitats for threatened marsupials like the Yellow-Bellied Glider. Rainforest developing in the understoreys of these forests is believed to threaten the dominant overstorey eucalypts and associated fauna. Land managers prescribe frequent low-intensity fires to try to stop rainforest species from establishing in Rose Gum forests understory. However, these practices are not consistent with the ecology of Rose Gum forest:

1. Rose Gums are obligate seeders and need rare, large, high-intensity landscape fires for successful regeneratation. Low-intensity fires do not stimulate Rose Gum regeneration because they do not release seeds stored in the canopy or create conditions suitable for initial growth. Repeated fires may kill young Rose Gum trees that do not have fully developed bark and these fires can reduce the protective capacity of the bark of mature trees.

2. Under current climatic conditions, rainforest expansion averages 0.6m/decade, and is occuring across all landscape conditions likely due to a global driver like increased atmospheric CO2. Using low-intensity fire to control this process is difficult because rainforest will only burn under exceptional conditions. Also, many rainforest species recover from a single fire. Natural and rare high-intensity fires will likely enable Rose Gum regeneration throughout the landscape.

The landscape ecology and plant functional biology of Rose Gum forest suggest that they are ecologically like secondary rainforest. Abstaining from prescribed burning and letting Rose Gum forests regenerate naturally from rare large fire events best approximates their regeneration ecology.

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Link to peer-reviewed article via Austral Ecology –

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Supporting Research

Title
Aims
Tng D. Y. P., Williamson G. J., Jordan G. J. & Bowman D. M. J. S. (2012) Giant eucalypts – globally unique fire-adapted rain-forest trees?. New Phytol. 196, 1001-1014.
Globally contextualized review of the literature of the functional biology and ecology of giant eucalypts and their relation to rain forest in Australia
Tng D. Y. P., Murphy B. P., Weber E., Sanders G., Williamson G. J., Kemp J. & Bowman D. M. J. S. (2012) Humid tropical rain forest has expanded into eucalypt forest and savanna over the last 50 years. Ecol. Evol. 2, 34-45.
experimentally examines the ecological correlates of rain forest expansion in Far North Queensland and projecting the effect of this expansion into giant eucalypt forest
Tng D. Y. P., Jordan G. J. & Bowman D. M. J. S. (2013) Plant traits demonstrate that giant eucalypt forests are ecologically convergent with rainforest not savanna. PLoS One 8, e84378.
experimentally examines if giant eucalypt forest in the tropics and temperate zones are ecologically convergent with each other and with their respective associated rain forest
Tng D. Y. P., Goosem S., Jordan G. J. & Bowman D. M. J. S. (2014) Letting giants be– rethinking active fire management of old growth eucalypt forest in the Australian tropics. J. App. Ecol. (in press).
A synthetic review of recent literature on the fire management of old growth forest, with an emphasis on tropical giant eucalypt forest in Australia
Harrington G.N. & Sanderson K.D. (1994) Recent contraction of wet sclerophyll forest in the wet tropics of Queensland due to invasion by rainforest. Pacific Conservation Biology, 1, 319-327.
Documents the contraction of giant eucalypt forest due to rainforest incursion
Little J.K., Prior L.D., Williamson G.J., Williams S.E. & Bowman D.M.J.S. (2012) Fire weather risk differs across rainforest - savanna boundaries in the humid tropics of northeastern Australia. Aust Ecol, 37, 915-925.
Evaluate the microclimatic conditions and fire risk across a rainforest-savanna boundary
Stanton P, Parsons M, Stanton D & Stott M. (2014) Fire exclusion and the changing landscape of Queensland’s Wet Tropics Bioregion 2. The dynamics of transition forests and implications for management Australian Forestry, 77, 58-68.
A synthesis of the need for fire management in the Wet Tropics of Australia
Stanton P, Stanton D, Stott M & Parsons M. (2014) Fire exclusion and the changing landscape of Queensland’s Wet Tropics Bioregion 1. The extent and pattern of transition. Australian Forestry, 77, 51-57.
Mapping of landscape change in the Wet Tropics of Australia
Unwin GL. (1989) Structure and composition of the abrupt rainforest boundary in the Herberton Highland, north Queensland. Australian Journal of Botany, 37, 413-428.
A transect study to describe the structural and floristic features of a tropical rainforest-eucalypt forest boundary
Warman L. & Moles A.T. (2009) Alternative stable states in Australia's Wet Tropics: a theoretical framework for the field data and a field-case for the theory. Landscape Ecology, 24, 1-13.
Reviews the landscape ecology of rain forests, giant eucalypt forest and savanna in the context of Alternative Stable States models
Williams P.R., Parsons M., Jensen R. & Tran C. (2012) Mechanisms of rainforest persistence and recruitment in frequently burnt wet tropical eucalypt forests. Austral Ecol. 37, 268-275.
Evaluate proposed mechanisms of rainforest expansion and retreat in wet tropical eucalypt forests
Bowman D.M.J.S., Murphy B.P., Boer M.M., Bradstock R.A., Cary G.J., Cochrane M.A., Fensham R.J., Krawchuk M.A., Price O.F. & Williams R.J. (2013) Forest fire management, climate change, and the risk of catastrophic carbon losses. 11, 66-67.
reviews the fire management of forest types in relation to fire return time and Alternative Stable States ecosystem theory