Translator Disclaimer
1 November 2007 Roadside Weeds of the Snowy Mountains, Australia
Catherine Pickering, Wendy Hill
Author Affiliations +
Abstract

Weeds are an increasing threat to the biodiversity of mountain regions worldwide, including in Australia. We reviewed 18 surveys of 401 sites conducted between 1986 and 2004 and examined the distribution and characteristics of common weeds on roadsides in the Snowy Mountains, Australia, to determine the range of natural habitats these weeds are found in, whether they are limited to disturbed sites, whether they are also common in other mountain regions including the Australian Alps, and whether they have invasive traits. There are only 8 common weeds in the Snowy Mountains: Acetosella vulgaris (also known as Rumex acetosella), Hypochaeris radicata, Trifolium repens, Taraxacum officinale, Agrostis capillaris, Dactylis glomerata, Anthoxanthum odoratum, and Achillea millefolium. They occur in areas disturbed by humans, such as along roadsides and around buildings and tracks, from the low-altitude montane zone to the high-altitude high subalpine/alpine zone. They also occur to varying extents in undisturbed native vegetation, reflecting their invasive capacity. These species are all perennial, with high vegetative and/or sexual reproduction, native to Europe, and are found growing on roadsides and in native vegetation in mountains in Europe, North America, South America, and New Zealand. Therefore, it appears that these plants are the usual suspects: common mountain weeds, which may be found worldwide at high altitude.

Introduction

Mountain regions worldwide are important reservoirs of vegetal biodiversity, accounting for 4% of all known vascular plants (Körner 1999). However, increasingly important components of mountain flora are exotic species that have been deliberately or accidentally introduced by humans (Körner 1999; Jesson et al 2002; Carbutt and Edwards 2004; Daehler 2005). They can be found growing along roads, tracks, and around ski slopes and buildings, as weeds generally benefit from human disturbance (Tyser and Worley 1992; Johnston and Pickering 2001; Jesson et al 2002; Tsuyuzaki 2002; Pauchard and Alaback 2004; Arévalo et al 2005). For example, many of the 274 exotic plants in the Australian Alps are disturbance-oriented, ie they are largely limited to areas where native vegetation has been damaged and there are areas of bare ground. However, some have spread from disturbed sites into natural vegetation, with a few becoming important environmental weeds (Johnston and Pickering 2001; Godfree et al 2004; Bear et al 2006). Weeds that are able to establish and spread in mountain regions tend to have similar traits. They tend to be polycarpic, perennial, with vegetative reproduction, wide climatic tolerance, benefit from disturbance, and have high seed output that is often wind pollinated (Godfree et al 2004; Alaska Natural Heritage Program 2005).

We examined the distribution of exotic plants in the Snowy Mountains in the Australian Alps to determine: (1) which are the most common exotics; (2) what types of habitats they are found in; (3) whether they are limited to disturbed sites or also occur in natural vegetation; (4) whether they are also common in the rest of the Australian Alps; (5) whether they are found in mountains elsewhere in the world; and (6) whether they have traits that make them a high risk for invasion.

Methods

The Snowy Mountains, which include continental Australia's highest mountain, Mount Kosciuszko (2228 m), are part of the Australian Alps in southeastern Australia (Figure 1). There are 3 main floristic zones in the Snowy Mountains: montane, subalpine, and alpine, with the zones strongly correlating with altitudinal/climatic gradients.

FIGURE 1

Location of the 401 sites surveyed from 1986–2004 in 18 vegetation surveys in the Snowy Mountains. Sites with exotic taxa and those with only native species are marked. (Map generated by the authors in ArcGIS, using spatial layers provided by New South Wales National Parks and Wildlife Service)

i0276-4741-27-4-359-f01.gif

The montane zone occurs between ∼500 m and ∼1500 m (Good 1992) and is dominated by Eucalyptus pauciflora alliance woodlands in association with other eucalypt species (Good 1992). The subalpine zone occurs between the lower winter snow line at ∼1500 m and the climatic limit of tree growth at ∼1850 m (Costin 1954). Winter temperatures average 0°C with continuous snow cover for at least one month per year (Green and Osborne 1994). The dominant vegetation type is Eucalyptus niphophila woodland interspersed with areas of bog, fen, heath, and subalpine grasslands (Costin et al 2000). The alpine zone in the Snowy Mountains occurs at lower elevations than in many other mountain regions; it extends from the climatic treeline at approximately 1850 m to the top of Mt Kosciuszko, at 2228 m, and covers an area of approximately 250 km2 (Costin et al 2000). Annual precipitation ranges from 1800 mm to 3100 mm, about 60% of which falls as snow in winter, persisting for more than 4 months in some areas (Green and Osborne 1994). Low-growing shrubs, grasses, and herbs characterize the alpine zone and occur in a number of different communities according to the biotic and abiotic characteristics of a site.

The most common weeds in the Snowy Mountains

We identified the most common weeds using a database of exotic taxa recorded in vegetation surveys undertaken from 1986 to 2004 in the Snowy Mountains. These surveys were published in research papers, PhD and Honors theses, and management agency reports (New South Wales National Parks and Wildlife Service), or were data from unpublished research by the authors and other members of the School of Environmental and Applied Sciences at Griffith University (Table 1). For each of the 401 sites for which there were detailed site data, the presence/absence of all exotics was recorded, as well as the spatial coordinates, vegetation zone, altitude, and native vegetation community or anthropogenic disturbance type of the site. From these data it was possible to identify the most common exotics (defined as occurring in more than 5% of sites), which habitats they occurred in, at what frequencies, their altitudinal ranges, and whether there were differences in their distribution between disturbed and natural sites.

TABLE 1

Details of the 18 vegetation surveys (1986–2004) analyzed in this study, covering a total of 401 sites in the Snowy Mountains. NB: this excludes 98 additional sites used in Bear et al 2006, as detailed information about the sites was not available.

i0276-4741-27-4-359-t101.gif

TABLE 1

Continued.

i0276-4741-27-4-359-t102.gif

We reviewed other vegetation surveys to determine whether these exotics were also common in the rest of the Australian Alps, and whether they were found in mountains elsewhere in the world. We also examined the invasive risk of the species, using information on the species' biological traits, distribution, and potential to be controlled (Alaska Natural Heritage Program 2005).

Results

Of the 156 exotic taxa recorded in the 401 sites surveyed in the Snowy Mountains (Bear et al 2006), there were only 8 weeds that occurred in more than 5% of the sites, and hence could be considered “common:” Acetosella vulgaris (also known as Rumex acetosella), Hypochaeris radicata, Trifolium repens, Taraxacum officinale, Agrostis capillaris, Dactylis glomerata, Anthoxanthum odoratum, Achillea millefolium, and Cerastium spp. (Table 2).

TABLE 2

Frequency of occurrence of the 8 most common weeds in the Snowy Mountains between 1986 and 2004, based on analysis of 18 general vegetation surveys of 401 sites (1004 records of exotics); for comparison, frequency of these species in 1222 floristic quadrats in treeless vegetation sampled across Australian Alps (McDougall and Walsh 2007).

i0276-4741-27-4-359-t02.gif

Sheep sorrel (Acetosella vulgaris in flora of New South Wales, Rumex acetosella in many European floras) is by far the most common species, recorded in 46% of all sites, including 43% of all natural sites (Table 2). It has a broad altitudinal range in the Snowy Mountains, extending from the lowest surveys to just below continental Australia's highest mountain (Mt Kosciuszko at 2228 m) along the Main Ridge of the Snowy Mountains at 2129 m. It was found on road and track verges, in ski resorts, and in disturbed subalpine grassland. It was also common in natural subalpine grasslands, woodlands, heaths, and tall alpine herbfields (Tables 2 and 3). It was found in other vegetation surveys or general listings of the flora for areas within the Australian Alps, indicating that it is ubiquitous in this region. Recorded in the earliest surveys of the high-altitude areas of the Snowy Mountains (Maiden 1898), this forb is a primary colonizer of bare ground.

TABLE 3

Ecological distribution of the 8 most common weeds on 401 sites surveyed in 18 general vegetation surveys in the Snowy Mountains between 1986 and 2004.

i0276-4741-27-4-359-t03.gif

Sheep sorrel is also found in mountain regions in South America, New Zealand, and North America, and on some islands (Table 4). In New Zealand it is one of the most abundant weeds, and is often the only naturalized weed species present at higher altitudes (Ullman et al 1995; Jesson et al 2002; Rose et al 2004). It is considered an environmental weed in some regions of the world, and can invade grass and heath, freshwater wetlands, costal beaches, and rock outcrops (Weber 2003). It has a range of traits that make it highly invasive (extensive vegetative spread, many seeds that are easily spread by human activities; Table 5). Although extensively naturalized, it is not considered an important environmental weed in the Australian Alps as it tends to be out-competed by native species in the absence of continued disturbance (Pickering et al 2003). Control of the species would be expensive and difficult, and does not appear warranted (Table 5).

TABLE 4

Occurrence in other mountain regions of the world of the 8 most common exotics found in the Snowy Mountains, according to published vegetation surveys of roadside and natural vegetation. AF = Africa; R = Road, N = Natural vegetation, S = semi-natural vegetation, SS = Ski slope, G = General species list for region. Sources: (1) Ullmann et al 1995, (2) Jesson et al 2002, (3) Rose et al 2004, (4) Pauchard and Alaback 2004, (5) Finckh and Thomas (1997) cited in Pauchard and Alaback 2004, (6) Sarmiento et al 2003, (7) Carbutt and Edwards 2004, (8) Meurk et al 1994, (9) Chapuis et al 2004, (10) Frenot et al 2005, (11) Parendes and Jones 2000, (12) Rentch et al 2005, (13) Tyser and Worley 1992, (14) Lausi and Nimis 1985, (15) Leege et al 1981, (16) Wiser et al 1996, (17) Godefroid and Koedam 2004, (18) Acar 2003, (19) Berge and Hestmark 1997, (20) Schmidt 1989, (21) Austrheim 2002, (22) Odland and Birks 1999, (23) Vandvik and Birks 2004, (24) Tsuyuzaki 2002, (25) Arévalo et al 2005, (26) Daehler 2005, (27) D'Antonio et al 2000.

i0276-4741-27-4-359-t401.gif

TABLE 4

Continued.

i0276-4741-27-4-359-t402.gif

TABLE 5

Biological traits, distribution, impact, and control of the 8 most common weeds in the Snowy Mountains, Australia. Categories based on weed risk assessment methodology used in Alaska (1). Sources: (1) Alaska Natural Heritage Program 2005, (2) Lamp and Collet 1999, (3) Tables 2, 3, and 4 in this paper, (4) Weber 2003, (5) Johnston 2005, (6) Blood 2001, (7) Harden 1990, (8) Lamp et al 2001.

i0276-4741-27-4-359-t501.gif

TABLE 5

Continued.

i0276-4741-27-4-359-t502.gif

Catsears (Hypochaeris radicata or Hypochoeris radicata) is also a common forb (26% of all sites), both in disturbed sites (45%) and in natural vegetation (18%) in the Snowy Mountains (Table 2). It was found on road verges, tracks in ski resorts including gardens, in disturbed and natural subalpine grasslands, woodlands, tall alpine herbfields, and heaths (Table 3). It was recorded in the first surveys of the region (Maiden 1898) and is regularly recorded in vegetation surveys and general records of the flora of the Australian Alps, including in the alpine zone (Table 2). It is also commonly recorded in vegetation surveys in mountains, along roads, and in natural vegetation in South America, New Zealand, on roadsides of North America, and in natural vegetation of the Hawaiian Islands (Table 4). It is an environmental weed in many parts of the world, including Australia (Table 4, Weber 2003). In addition to disturbed habitats, it can be found colonizing grassland, riparian, seasonal freshwater wetlands and coastal beaches (Weber 2003). This perennial herb can spread vegetatively using perinating buds, and has high seed output that is wind dispersed (Table 5). It has moderate competitive ability, including in the Snowy Mountains, and would be difficult to control due to the high seed output and innate potential for long-distance dispersal (Table 5).

The third most common species, yarrow (Achillea millefolium), is found along roadsides in the subalpine and montane zones where it can spread into adjacent grasslands in wet areas. Once established it appears to be able to out-compete natives and is difficult to remove (Tables 2 and 3, Johnston 2005). Away from roads, however, it is not common (Table 3, McDougall and Walsh 2007) and is not considered as much of a problem in other parts of the Australian Alps (Johnston 2005; McDougall and Walsh 2007). It has been recorded on mountain roadsides, including in New Zealand, North America, and Hawaii (Table 4). It can reproduce vegetatively from small stolons and is a prolific flowerer that produces many seeds, giving it a highly aggressive mode of reproduction (Table 5, Johnston 2005). Although it can be spread by human activities, it has limited innate potential for long-distance dispersal, with most seed falling within a few meters of adult plants. However, once established, it is highly competitive, able to exclude other species, and difficult to control due to the large seedbank and potential for vegetative reproduction (Table 5, Johnston 2005).

White clover (Trifolium repens) is a forb that was deliberately introduced into the Australian Alps, as a species used to revegetate areas damaged by cattle and sheep grazing, and also in ski resorts (Johnston and Pickering 2001). As a result, it was common in disturbed sites (44%) including road and track verges, ski resorts, and disturbed subalpine grasslands. In contrast it was uncommon in natural sites (3%), only occurring in a few subalpine/montane woodland and grassland sites (Tables 2 and 3).

At lower altitudes it is considered invasive of natural areas in Australia (Weber 2003). Recorded in mountains in South America, North America, New Zealand, Japan, and the Hawaiian Islands, it is considered a high weed risk in Alaska (Table 4). It does have many weed traits, including high reproductive and vegetative output and moderate competitive ability. It is difficult to control due to the large seedbank and its capacity for vegetative spread (Table 5).

Sweet vernal grass (Anthoxanthum odoratum) occurs in disturbed (29%) and natural sites (5%) in the montane and subalpine areas in the Snowy Mountains, mostly on road verges and natural subalpine grasslands (Table 2). It was not found in any of the 184 alpine sites sampled here, although other studies have found it at high altitudes (Table 3, Costin et al 2000). Although it has been found in most of the Australian Alps, it is less common than the 7 other species, in these and other mountain regions of the world (Table 4). It has been introduced into Africa, temperate Asia, New Zealand, western USA, and South America, and is considered invasive in Australia, Chile and Argentina, and the islands of Mascarenes, Micronesia, and Hawaii (Weber 2003). It does well on nutrient-poor soils, and can be highly competitive with other grass species (Weber 2003). Although it has high seed output, it does not reproduce vegetatively, unlike many other invasive exotics in mountains (Table 5, Godfree et al 2004).

Dandelion (Taraxacum officinale) is a moderately common forb in alpine, subalpine and montane natural (8%) and disturbed (25%) sites in the Snowy Mountains (Table 2). It was found in most habitats including road and track verges, ski resort gardens, natural subalpine grasslands, woodlands, tall alpine herbfields, and heaths (Table 3). Recorded in the earliest surveys of the mountains, it is commonly found in vegetation surveys and general reviews of the flora of the Australian Alps (Table 2). Although it is not always considered an important weed internationally (Weber 2003) and in Australia (Parsons and Cuthbertson 2001), it occurs in vegetation surveys in mountains in North America, South America, New Zealand, Hawaii, Tenerife/Canary Islands and on at least one subantarctic island (Table 4). It is also ranked as a highly invasive species in Alaska. Although it does not reproduce vegetatively, it produces large numbers of wind-dispersed seed, and has moderate competitive ability once established (Table 5). Control can be difficult because of the seedbank and capacity for long-distance dispersal (Table 5).

Cocksfoot (Dactylis glomerata) can be found in disturbed (20%) and a few (2.5%) natural montane and subalpine sites, but is not very common even at these lower altitudes (< 1% of treeless vegetation, Table 2). It was found on road verges and in ski resort gardens, and in a few sites in natural subalpine grasslands, woodlands, and a heath site (Table 3). Although recorded in general vegetation surveys of the Australian Alps, predominantly in disturbed sites, it is often not found in specific field surveys. It has been introduced into Southern Africa, New Zealand, some parts of the USA, and South America, and is considered invasive in Australia and Hawaii (Weber 2003). It has been recorded in natural and roadside vegetation surveys in South America, New Zealand, on roadsides in North America, ski slopes in Japan, and in natural vegetation in Hawaii (Table 4). It can reproduce vegetatively and has prolific wind-, water-, and animal-dispersed seed, making it difficult to control (Table 5).

Brown top bent (Agrostis capillaris) was deliberately introduced into the Australian Alps for revegetation (Johnston and Pickering 2001). It is less common than the other species (6.7% of the sites), and is mainly restricted to disturbed sites (17%) such as roadsides and around buildings, with few records on natural sites (2%) (Table 3). It has been recorded in general vegetation surveys on roadsides and in natural areas in mountains of South America and New Zealand, but appears uncommon in North American roadside vegetation surveys (Table 4). It has been introduced to Southern Africa, tropical Asia, New Zealand, North America, South America, and Hawaii, and is considered invasive in Australia and New Zealand, where it can be found in grasslands, shrublands, pastures, and other disturbed sites (Weber 2003). This species is a major weed in pastures, but unlike the other common weeds, it is not considered generally invasive in Australia, nor is it as difficult to control as other species (Table 5).

Discussion

The most common exotics in the Snowy Mountains are native to Europe, but are currently found in many mountain regions worldwide where they are associated with human disturbances such as roads and ski slopes. They are all naturalized in Australia, and 5 of them (sheep sorrel, catsears, yarrow, white clover and dandelions) can be found spreading into native vegetation adjacent to roads and tracks in the Snowy Mountains (Table 3). They show many general weed traits, including high seed output and/or vegetative spread, and wide climatic tolerance—including of temperate regions (Lamp et al 2001; Godfree et al 2004; Alaska Natural Heritage Program 2005). They are all relatively hard to remove, either mechanically or through spraying, due to their large seed output that can be spread by wind and/or animals, and their capacity to spread vegetatively (Csurhes and Edwards 1998; Blood 2001; Lamp et al 2001; Weber 2003; Alaska Natural Heritage Program 2005).

It is also clear that human disturbance in mountain regions, such as the construction and use of roads and tracks, provides the opportunity for the establishment of these and other weeds that can then spread into adjacent native vegetation, with some species becoming naturalized and competing with native taxa (Mallen 1986; Godfree et al 2004; Johnston 2005; McDougall and Walsh 2007). These results highlight that despite the many differences in the diversity and ecology of mountain regions, they appear to be similarly susceptible to invasion by a common group of alien plants that share many of the same traits, making them the usual suspects.

Acknowledgments

We thank the Cooperative Research Centre for Sustainable Tourism for their financial support. We also thank all the people who provided us with original data for use in the database, and two anonymous reviewers for their comments on the paper.

REFERENCES

1.

C. Acar 2003. A study on the ground layer species composition in rocky, roadside and forest habitats in Trabzon Province. Turkish Journal of Botany 27:255–275. Google Scholar

2.

Alaska Natural Heritage Program 2005. Weed Ranking Project. Alaska Natural Heritage Program. Anchorage, AK University of Alaska.  http://akweeds.uaa.alaska.edu/akweeds_ranking_page.htm#table1; accessed on 12 December 2006. Google Scholar

3.

J. R. Arévalo, J. D. Delgado, R. Otto, A. Naranjo, M. Salas, and J. M. Fernández-Palacios . 2005. Distribution of alien vs native plant species in roadside communities along an altitudinal gradient in Tenerife and Gran Canaria (Canary Islands). Perspectives in Plant Ecology, Evolution and Systematics 7:185–202. Google Scholar

4.

G. Austrheim 2002. Plant diversity patterns in semi-natural grasslands along an elevational gradient in southern Norway. Plant Ecology 161:193–205. Google Scholar

5.

R. Bear, W. Hill, and C. M. Pickering . 2006. Distribution and diversity of exotic plant species in montane to alpine areas of Kosciuszko National Park. Cunninghamia 9 4:559–570. Google Scholar

6.

G. Berge and G. Hestmark . 1997. Composition of seed banks of roadsides, stream verges and agricultural fields in southern Norway. Annals of Botany Fennici 34:77–90. Google Scholar

7.

K. Blood 2001. Environmental Weeds: A Field Guide for SE Australia. Melbourne, Australia CH Jerram. Google Scholar

8.

C. Carbutt and T. J. Edwards . 2004. The flora of the Drakensberg alpine centre. Edinburgh Journal of Botany 60:581–607. Google Scholar

9.

J. L. Chapuis, Y. Fernot, and M. Lebouvier . 2004. Recovery of native plant communities after eradication of rabbits from the subantarctic Kerguelen Islands and the influence of climate change. Biological Conservation 117:167–179. Google Scholar

10.

A. B. Costin 1954. A Study of the Ecosystems of the Monaro Region of New South Wales. Sydney, Australia Government Printer. Google Scholar

11.

A. B. Costin, M. Gray, C. Totterdell, and D. Wimbush . 2000. Kosciuszko Alpine Flora. Melbourne, Australia Commonwealth Scientific and Industrial Research Organisation. Google Scholar

12.

S. Csurhes and R. Edwards . 1998. Potential Environmental Weeds in Australia. Canberra, Australia Environment Australia. Google Scholar

13.

C. M. D'Antonio, J. T. Tunison, and R. K. Loh . 2000. Variation in the impact of exotic grasses on native plant composition in relation to fire across an elevational gradient in Hawaii. Austral Ecology 25:507–522. Google Scholar

14.

C. C. Daehler 2005. Uppermontane plant invasions in the Hawaiian Islands: Patterns and opportunities. Perspectives in Plant Ecology, Evolution and Systematics 7:203–216. Google Scholar

15.

M. Finckh and S. Thomas . 1997. Struktur und Genese von Hudelandschaften in Südchile (mit einem Ausblick auf Mitteleuropa). Tuexenia 17:159–172. Google Scholar

16.

Y. Frenot, S. L. Chown, J. Whinam, P. M. Selkirk, P. Convey, M. Skotnicki, and D. M. Bergstrom . 2005. Biological invasions in the Antarctic: Extent, impacts and implications. Biological Review 80:45–72. Google Scholar

17.

S. Godefroid and N. Koedam . 2004. The impact of forest paths upon adjacent vegetation: Effects of the path surfacing material on the species composition and soil compaction. Biological Conservation 119:405–419. Google Scholar

18.

R. Godfree, B. Lepschi, and D. Mallinson . 2004. Ecological filtering of exotic plants in an Australian subalpine environment. Journal of Vegetation Sciences 15:227–236. Google Scholar

19.

R. B. Good 1992. Kosciuszko Heritage. Sydney, Australia National Parks and Wildlife Service of New South Wales. Google Scholar

20.

K. Green and W. Osborne . 1994. Wildlife of the Australian Snow-country. Sydney, Australia Reed Books. Google Scholar

21.

G. J. Harden 1990. Flora of New South Wales. Volume 1.Sydney, Australia NSW University Press. Google Scholar

22.

L. Jesson, D. Kelly, and A. Sparrow . 2002. The importance of dispersal, disturbance and competition for exotic plant invasions in Arthur's Pass National Park, New Zealand. New Zealand Journal of Botany 38:451–468. Google Scholar

23.

F. Johnston 2005. Exotic Plants in the Australian Alps Including a Case Study of the Ecology of Achillea millefolium in Kosciuszko National Park. [PhD thesis]. Gold Coast, Australia School of Environmental and Applied Sciences, Griffith University. Google Scholar

24.

F. M. Johnston and C. M. Pickering . 2001. Exotic plants in the Australian Alps. Mountain Research and Development 21:284–291. Google Scholar

25.

C. Körner 1999. Alpine Plant Life: Functional Plant Ecology of High Mountain Ecosystems. Berlin, Germany Springer-Verlag. Google Scholar

26.

C. Lamp and F. Collet . 1999. Field Guide to Weeds in Australia. Melbourne, Australia Inkata Press. Google Scholar

27.

C. A. Lamp, S. J. Forbes, and J. W. Cade . 2001. Grasses of Temperate Australia: A Field Guide. Melbourne, Australia CH Jerram. Google Scholar

28.

D. Lausi and P. L. Nimis . 1985. Roadside vegetation in boreal South Yukon and adjacent Alaska. Phytocoenologia 13:103–138. Google Scholar

29.

T. A. Leege, D. J. Herman, and B. Zamora . 1981. Effects of cattle grazing on mountain meadows in Idaho. Journal of Range Management 34:324–328. Google Scholar

30.

J. H. Maiden 1898. A contribution towards a flora of Mount Kosciusko. Agricultural Gazette of N.S.W 9:720–740. Google Scholar

31.

J. Mallen 1986. Introduced vascular plants in the high altitude and high latitude areas of Australasia, with particular reference to the Kosciuszko Alpine area, New South Wales. In B. A. Barlow editor. Flora and Fauna of the Alpine Australasia Ages and Origins. Melbourne, Australia CSIRO. pp. 249–258. Google Scholar

32.

K. McDougall and N. G. Walsh . 2007. Treeless vegetation of the Australian Alps. Cunninghamia 10 1:1–57. Google Scholar

33.

C. D. Meurk, M. N. Foggo, and J. B. Wilson . 1994. The vegetation of subantarctic Campbell Island. New Zealand Journal of Ecology 18:123–168. Google Scholar

34.

A. Odland and H. J. B. Birks . 1999. The altitudinal gradient of vascular plant richness in Aurland, western Norway. Ecography 22:548–566. Google Scholar

35.

L. A. Parendes and J. A. Jones . 2000. Role of light availability and dispersal in exotic plant invasions along roads and streams in the H.J. Andrews Experimental Forest, Oregon. Conservation Biology 14:64–75. Google Scholar

36.

W. T. Parsons and E. G. Cuthbertson . 2001. Noxious Weeds of Australia. Melbourne, Australia Commonwealth Scientific and Industrial Research Organisation. Google Scholar

37.

A. Pauchard and P. B. Alaback . 2004. Influence of elevation, land use and landscape context on patterns of alien plant invasions along roadsides in protected areas of South-Central Chile. Conservation Biology 18:238–248. Google Scholar

38.

C. M. Pickering, A. Kirkwood, and J. M. Arthur . 2003. Habitat and sex specific differences in the dioecious weed Acetosella vulgaris (Polygonaceae). Austral Ecology 28:396–403. Google Scholar

39.

J. S. Rentch, R. H. Fortney, S. L. Stephenson, H. S. Adams, W. N. Grafton, and J. T. Anderson . 2005. Vegetation-site relationships of roadside plant communities in West Virginia, USA. Journal of Applied Ecology 42:129–138. Google Scholar

40.

A. B. Rose, P. A. Suisted, and C. M. Frampton . 2004. Recovery, invasion and decline over 37 years in a Marlborough short-tussock grassland, New Zealand. New Zealand Journal of Botany 42:77–87. Google Scholar

41.

L. Sarmiento, L. D. Llambi, A. Escalona, and N. Marquez . 2003. Vegetation patterns, regeneration rates and divergence in an old-field succession of the high tropical Andes. Plant Ecology 166:67–75. Google Scholar

42.

W. Schmidt 1989. Plant dispersal by motor cars. Vegetatio 80:147–152. Google Scholar

43.

S. Tsuyuzaki 2002. Vegetation development patterns on ski slopes in lowland Hokkaido, northern Japan. Biological Conservation 108:239–246. Google Scholar

44.

R. W. Tyser and C. A. Worley . 1992. Alien flora in grasslands adjacent to roads and trails in Glacier National Park, Montana (U.S.A.). Conservation Biology 6:253–262. Google Scholar

45.

I. Ullmann, P. Bannister, and W. J. Bastow . 1995. The vegetation of roadside verges with respect to environmental gradients in southern New Zealand. Journal of Vegetation Sciences 6:131–142. Google Scholar

46.

V. Vandvik and H. J. B. Birks . 2004. Mountain summer farms in Roldal, western Norway—vegetation classification and patterns in species turnover and richness. Plant Ecology 170:203–222. Google Scholar

47.

E. Weber 2003. Invasive Plant Species of the World: A Reference Guide to Environmental Weeds. London, United Kingdom CABI Publishing. Google Scholar

48.

S. Wiser, P. Robert, and P. S. White . 1996. High-elevation rock outcrop vegetation of the Southern Appalachian Mountains. Journal of Vegetation Science 7:703–722. Google Scholar
Catherine Pickering and Wendy Hill "Roadside Weeds of the Snowy Mountains, Australia," Mountain Research and Development 27(4), 359-367, (1 November 2007). https://doi.org/10.1659/mrd.0805
Received: 1 December 2006; Accepted: 1 March 2007; Published: 1 November 2007
JOURNAL ARTICLE
9 PAGES


SHARE
ARTICLE IMPACT
Back to Top