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A. J. Brown1 and E. A. James2

1Agriculture Victoria, Department of Natural Resources and Environment,
Royal Botanic Gardens Melbourne


The distribution and habitats of Australian native blown-grasses (Agrostis spp.) in the Western District of Victoria were observed over a number of seasons. Growth habit and flowering pattern were noted for each species. A survey of surface soil salinity, indicates that native Agrostis species, growing in lowland environments, have decreasing salt tolerance in the order; A. billardierei var. robusta = A. adamsonii > A. avenacea = A. billardierei var. filifolia > A. aemula = A. venusta. A. adamsonii and A. billardieri var. robusta can grow in soils with total soluble salt contents of at least 2 % and have potential for use in reclamation of saline discharge sites.

Key Words: Agrostis spp., native grasses, grassland, soil salinity, biodiversity

Agrostis forms a genus of about 200 species worldwide, with 22 species occurring in Australia and 14 species in Victoria (1). Three species are naturalised introductions viz. A. capillaris (brown-top bent), A. stolonifera (creeping bent) and A. gigantea (red-top bent), of which the former two are important grasses in the turf industry, but can be serious weeds of pastures and crops. Of the native Victorian species, six are largely confined to cool forests and alpine regions, three are found in both highland and lowland situations and the remaining two are only found in lowland situations. All species appear to prefer moist or at least seasonally wet soil conditions.

Species and varieties recorded for the plains of western Victoria, are A. avenacea (common blown-grass), A. aemula var. aemula (blown-grass), A. aemula var. setifolia, A. venusta (misty bent), A. billardierei var. robusta, A. billardierei var. filifolia (varieties of coastal blown-grass) and A. adamsonii (Adamson's bent). Of these, only A. avenacea is regarded as widely spread and common in the region. Despite some of their common names, all these species have similar growth habit and overall appearance and are collectively referred to here as Blown-grasses.

In the course of recent work with A. adamsonii by the senior author, it became apparent that the status and distribution of other native Agrostis spp. required review. These species are often overlooked in native grasslands, taking second place to Themeda, Stipa and Danthonia spp. This paper reports a survey of 616 sites (mainly roadsides) examined as potential habitats for Agrostis spp. (ie. flats, swamps, depressions, gullies and drains) from 1993-97.

Results and discussion

Distribution and habitat

Table 1 shows the percentage of examined sites that contained each Agrostis spp. under study, a description of the main habitat and some of the other plant genera (both native and introduced) present. In addition, soil moisture and EC were determined for 28 selected sites during early November 1997.

Table 1. Occurrence, habitat, associated genera and mean and range of soil moisture and EC for each Agrostis spp. under study.


% of 616 sites

Habitat description

Other common genera in plant community

Mean and (range) soil moisture, %

Mean and (range) soil EC, dS/m

A. avenacea


Wetter grasslands and roadsides (often extensive) and margins of swamps

Numerous because of wide range of habitats (eg. Phalaris, Lolium, Danthonia, Poa, Critesion, Trifolium, Cotula, Plantago)



A. aemula


Moist slopes and depressions of open grasslands

Themeda, Stipa, Danthonia, Poa, Pentapogon, Calotis, Eryngium, Wahlenbergia, Chrysocephalum



A. venusta


As above

As above



A. adamsonii


Confined to saline flats and marshes

Cotula, Plantago, Triglochin, Juncus, Critesion, Polypogon, Puccinellia, Samolus, Sarcocornia



A. billardieri var. robusta


As above

As above



A. billardieri var. filifolia


Moist slopes and depressions of open grasslands and flats

As for A. aemula and A. adamsonii



Growth habit and utilisation

A. avenacea is regarded as a minor nuisance to local farmers. After shedding its seed, the plants' dried inflorescences break off from their culms during summer and are blown by the wind for considerable distances to accumulate against bushes, fences and buildings. The species main flowering period is from November to January but sometimes will have a second flowering with late summer rains. It mainly acts as an annual but some perennial forms have been observed. It does provide some green feed on swamps during the summer.

A. aemula and A. venusta are annual species, flower mainly during October and November and would be expected to contribute little to a grazing enterprise. However, A. aemula can form small tussocks (up to 15 cm diameter) under favourable site conditions and may have some feed potential in low input grazing systems that utilise native vegetation.

A. adamsonii appears to be a short-term perennial while A. billardierei var. robusta mainly acts as an annual. Main flowering periods are from November to January for A. adamsonii and from January to February for A. billardierei var. robusta although both species will persist longer, given favourable soil moisture conditions. A. adamsonii, in particular, tends to grow larger and more vigorously near or on the edge of permanent water. Both species can grow in soils with total soluble salt contents of 2 % or more and have potential for use in reclamation of saline discharge sites. They have been observed to colonise bare sites that have been fenced off from stock. Although these species appear to persist only under very light grazing, they may provide a short-term green pick. For many sites (eg. reclaimed gullies, highly saline flats), where soil protection is of primary importance, no other grazing management is warranted.

A. billardierei var. filifolia has been found in plant communities with A. aemula/A. venusta and with A. adamsonii on lesser saline flats. It flowers from October to December and appears to be a short-term perennial or annual. It, like A. venusta, has little feed value due to its small leaf bulk.


As components of wet grasslands, native Agrostis spp. are an integral part of the biodiversity of such sites and need to be maintained. In particular, consideration needs to be given to the preservation of the salt dependent, A. adamsonii and A. billardierei, as drainage and land reclamation continues to reduce their habitat.


1. Walsh, N.G. 1994. In: Flora of Victoria. Volume 2. (Ed. N.G. Walsh and T.J. Entwisle). Inkata Press, Sydney. pp. 467-476.

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