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

Plant traits predict impact of invading species: an analysis of herbaceous vegetation in the subtropics

S. McIntyre A B , T. G. Martin A , K. M. Heard A and J. Kinloch A
+ Author Affiliations
- Author Affiliations

A CSIRO Sustainable Ecosystems, Queensland Bioscience Precinct, 306 Carmody Rd, St Lucia, Qld, Australia.

B Corresponding author. Current address: CSIRO Sustainable Ecosystems, GPO Box 284, Canberra, ACT 2601. Email: Sue.McIntyre@csiro.au

Australian Journal of Botany 53(8) 757-770 https://doi.org/10.1071/BT05088
Submitted: 16 May 2005  Accepted: 11 October 2005   Published: 14 December 2005

Abstract

The need to predict potential invasion impact of plant species is important for setting weed-management priorities and determining quarantine restrictions for newly imported plant material. We analysed the naturalised plant component of a herbaceous plant community in sub-tropical eucalypt woodlands subjected to various disturbances associated with agricultural activities. The native and naturalised plant species did not differ in the proportions of different life forms, although life-history differed, with the naturalised group having more annual and biennial, and relatively fewer perennial species. We classified the naturalised assemblage into high- and low-impact species and compared the plant-trait and habitat characteristics of the two groups. Low-impact species covered a range of levels of habitat specialisation whereas high-impact species tended to have moderate to low levels of specialisation and to be less tolerant of grazing. Seven traits were found to be significantly associated with impact. Stepwise regression indicated a high level of redundancy in the data, owing to attributes being correlated. For all species, four attributes were significant in determining impact: very wide lateral spread, C4 photosynthesis, tall height and large leaves. For forbs, only two attributes (large seeds, adhesion/ingestion mode of seed dispersal) were significant in the overall model. We identified the following eight functional types amongst the naturalised species: (i) high-impact C4 lawn grasses, (ii) high-impact C4 bulky tussock grasses, (iii) moderate-impact annual grasses, (iv) moderate-impact tall annual forbs, (v) moderate-impact spreading forbs, (vi) moderate-impact woody forbs, (vii) low-impact legumes and (viii) low-impact small ruderals. In the subtropical woodland environment perennial C4 grasses appear to present the greatest invasive threat to herbaceous native communities, whereas forbs of wide lateral spread, with large animal-dispersed seeds are also problematic. The results support a case for limiting further importation of horticultural and forage material into Australia.


Acknowledgments

This work was supported by the Weed Management CRC (Project 1.2.2). Dane Panetta, Gabrielle Vivian-Smith and Graeme Hastwell contributed to the development of the project. Thanks go to David Doley for assistance with photosynthetic pathway allocations. Thanks also go to the Parton family for access to their properties for sampling.


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Appendix 1.  Species sorted by group membership derived from agglomerative hierarchical fusion with flexible unweighted pair group arithmetic averaging
Growth form: 1 = rhizomatous/stoloniferous, 2 = tussock grass or sedge, 3 = erect forbs, 4 = scrambling or mat forbs, 5 = rosette/partial rosette forbs; life-form: 1 = therophyte (annuals and biennials), 2 = hemicryptophyte, 3 = chamaephyte (defined in Cornelissen et al. 2003); height: 1 = <20 cm, 2 = 20–40 cm, 3 = > 40 cm; lateral spread: (cm) 1 = <10, 2 = 11–25 cm, 3 = 26–100, 4 = > 100; above-ground cover density: 1 = low, 2 = moderate, 3 = high (density of above-ground biomass in the projected canopy area, McIntyre et al. 1999); growth season: 1 = summer, 2 = year-round; photosynthetic pathway: 1 = C3, 2 = C4 (from published sources Downtown 1975; Waller and Lewis 1979; Sage and Monson 1999; Sayed 2001; Peter and Katinas 2003); dispersal mode: 1 = undefined, 2 = wind (pappus or equivalent structure), 3 = adhesion/ingestion, 4 = mobile (<0.3 mg)
A1