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Australian Journal of Botany Australian Journal of Botany Society
Southern hemisphere botanical ecosystems
RESEARCH ARTICLE

What limits the distribution and abundance of the native conifer Callitris glaucophylla (Cupressaceae) in the West MacDonnell Ranges, central Australia?

Lynda D. Prior A C , Zoe Lee A , Chris Brock B , Grant J. Williamson A and David M. J. S. Bowman A
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- Author Affiliations

A School of Plant Science, University of Tasmania, Private Bag 55, Hobart, Tas. 7001, Australia.

B Parks and Wildlife Service of the Northern Territory, PO Box 2130, Alice Springs, NT 0871, Australia.

C Corresponding author. Email: lynda.prior@utas.edu.au

Australian Journal of Botany 58(7) 554-564 https://doi.org/10.1071/BT10045
Submitted: 17 February 2010  Accepted: 4 September 2010   Published: 27 October 2010

Abstract

The conifer Callitris glaucophylla J.Thompson & L.A.S.Johnson (Cupressaceae) is a fire-sensitive obligate seeder with a heavily fragmented distribution across the Australian continent. We undertook a broad-scale biophysical survey and analysed the population structure of 21 populations in the West MacDonnell Ranges of central Australia. C. glaucophylla had a patchy distribution associated with steep, rocky metamorphic areas with limited evidence of fire. Variation in population structures was clearly related to recent fire history. Nearly half of ‘adult’ C. glaucophylla trees (>5-cm stem diameter) from the sampled stands were dead, with the proportion at individual sites related to evidence of fire. Fire scars were evident on 48% of all live trees we measured. The overall density of live adult trees conformed to a negative exponential size-class distribution, consistent with a regionally stable population structure. However, we found higher sapling densities and lower seedlings densities than expected by this distribution. This regional peak in the sapling size class reflects a pulse of recruitment, possibly associated with a wet period in the 1970s. Low seedling densities are probably due to subsequent drought. We conclude that fire controls the distribution of Callitris on the West MacDonnell Ranges, and the timing of recruitment depends on rainfall patterns.


Acknowledgements

We thank staff of the Parks and Wildlife Service of the Northern Territory for logistical support, especially Chris Day, Mark Trower and Dan Adams. We also thank Janelle Dennis, Sophie Edwards and Stephen Lee for field assistance. This work was partly funded by CERF Grant B0016193.


References


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Appendix 1.  Demographic attributes of individual sites, showing the number of live and dead Callitris glaucophylla adults (≥5 cm DBH), saplings (<5 cm DBH and ≥1.3 m high) and seedlings (<1.3 m high) at each)
The parameters of the equation relating tree density to size class are also shown, with the significant relationships indicated in bold. Log10(density + 1) = a × (size class) + b, where density is trees per ha and size class is numbered from 1 to 5 and a and b are fitted parameters corresponding to the slope and intercept, respectively
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Appendix 2.  Size-class distributions at the individual sites, and of the isolated trees pooled. Live trees are indicated by black bars, dead by grey bars. Full site names are given in Appendix 1. A ‘0’ indicates no trees, dead or alive, in that size class.
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