Book contents
- Frontmatter
- Contents
- List of contributors
- Preface
- Part I Introduction
- Part II Historical background
- Part III Biogeography of taxa
- Part IV Applied aspects of mediterranean invasions
- 26 Weed invasion in agricultural areas
- 27 Plant invasions in the rangelands of the isoclimatic mediterranean zone
- 28 Forest plantations and invasions in the mediterranean zones of Australia and South Africa
- 29 The importation of mediterranean-adapted dung beetles (Coleoptera: Scarabaeidae) from the northern hemisphere to other parts of the world
- Part V Overview
- Index of scientific names
- Subject index
28 - Forest plantations and invasions in the mediterranean zones of Australia and South Africa
Published online by Cambridge University Press: 02 December 2009
- Frontmatter
- Contents
- List of contributors
- Preface
- Part I Introduction
- Part II Historical background
- Part III Biogeography of taxa
- Part IV Applied aspects of mediterranean invasions
- 26 Weed invasion in agricultural areas
- 27 Plant invasions in the rangelands of the isoclimatic mediterranean zone
- 28 Forest plantations and invasions in the mediterranean zones of Australia and South Africa
- 29 The importation of mediterranean-adapted dung beetles (Coleoptera: Scarabaeidae) from the northern hemisphere to other parts of the world
- Part V Overview
- Index of scientific names
- Subject index
Summary
Forest plantations tend to be the source of propagules if tree species become invasive. Such plantations in the part of southern Australia with a mediterraneantype climate are largely of pines, especially Pinus radiata. There is a smaller component of Pinus pinaster, particularly on soils of low fertility in south-west Western Australia. Small trial plots have been established in arboreta of many other species in the genus, especially P. laricio, P. ponderosa, P. contorta, P. muricata, P. halepensis, and some other coniferous genera such as Cupressus.
Forest plantations of these species have been established principally on sites which formerly carried tall open-forest or open-woodland (Specht, 1970), inwhich Eucalyptus species were the main trees, and species of Acacia (either shrubs or small trees) were associated species. After establishment it has usually been necessary to remove regrowth of the indigenous species, either as coppice shoots from stumps, as regenerated seedlings, or as root suckers in the case of some Acacia species, to ensure establishment of the pines. Such persistent plants are often referred to as ‘woody weeds’, although in no way do they possess invasive characteristics.
At a rotation age of about 30 to 40 years, the pine stand is typically without associated species, either indigenous or introduced, except for a few lowgrowing herbs on the forest floor and some bryophytes on wetter sites. Occasionally, in moist localities, European blackberry (Rubus spp.) may enter the stand and persist as an undesirable species in the management system.
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- Biogeography of Mediterranean Invasions , pp. 405 - 412Publisher: Cambridge University PressPrint publication year: 1991
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