How do rare Boronia species differ from their more widespread congeners?
A. Shapcott A B , R. W. Lamont A and A. Thomson AA University of the Sunshine Coast, Maroochydore DC 4558, Qld, Australia.
B Corresponding author. Email: ashapcot@usc.edu.au
Australian Journal of Botany 53(2) 171-183 https://doi.org/10.1071/BT03183
Submitted: 18 December 2003 Accepted: 21 October 2004 Published: 31 March 2005
Abstract
The vulnerable Boronia keysii Domin. (Rutaceae; BK) and the rare B. rivularis White. (BR), endemic to the Sunshine Coast region of Queensland, and the more widespread B. safrolifera Cheel. (BS) and B. falcifolia (BF), were studied. The taxonomic distinctiveness between the morphologically similar B. rivularis and its more southern congener B. safrolifera had previously been in question. This study clearly confirmed the long genetic separation of these two species. High levels of reproductive activity (%R) were observed in both of the threatened species (B. keysii: %R = 84; B. rivularis: %R = 66), which were also found to differ fundamentally in response to fire (obligate seed regenerators) from the more widespread species (facultative resprouters). Genetic diversity was not consistently related to rarity since B. keysii (vulnerable; He = 0.282) and B. falcifolia (common; He = 0.294) had significantly (P < 0.05) higher genetic diversity than did B. rivularis (rare; He = 0.155) and B. safrolifera (common; He = 0.197). There was no relationship between population differentiation and geographic distribution of species since B. keysii (FST = 0.293) and B. safrolifera (FST = 0.283) exhibited lower between-population diversity than did B. rivularis (FST = 0.360) and B. falcifolia (FST = 0.324). The average number of migrants per generation was less than one in all species (Nm = 0.604 for BK; 0.444 for BR; 0.634 for BS; 0.522 for BF). All four species are effectively inbred; however, B. keysii (F = 0.85) and B. falcifolia (F = 0.90) had significantly (P < 0.05) higher levels of inbreeding than did B. rivularis (F = 0.621) and B. safrolifera (F = 0.472), indicating that inbreeding was not determined by conservation status.
Acknowledgments
The project was funded by Queensland Parks and Wildlife Service (QPWS) and the University of the Sunshine Coast. We thank Julia Playford, Rowena, Thomas, Bill French, Mark Dargusch, Ivan Thrash, Ian Lawnton, Damian Head, Adrian Walker from QPWS; Paul Forster, Tony Bean, Ailsa Holland, Bill McDonald from Qld Herbarium; Brian Wilson from Department of Natural Resources; Rosalie Eustace, Jonathon Moore from Redland Shire Council; Dave Burrows from Noosa Shire Council; Noosa Landcare, Arthur Harrold and Noosa Parks Association; John Ward from Bribie Island Wallum Action Group; Tim Perry, Brian McLachlan from New South Wales National Parks and Wildlife Service. Thanks go to landowners for access to their property, and to Andrew Benwell and Carolyn Sandercoe for access to species data.
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