CSIRO Livestock Industries, Private Bag 5, Wembley, WA 6913, Australia. Hayley.Norman@csiro.au
Abstract
Species composition within two typical saline paddocks in southwestern Australia was assessed in the spring and autumn. Plant diversity within the paddocks was much higher than the diversity that is often found in non-saline pastures in these areas. The Meckering paddock contained 31 plant species, and the Tammin paddock contained 24 plant species. It is expected that high levels of plant diversity within paddocks are maintained by niche differentiation; i.e. no one species can dominate in all of the functional niches within the paddock. In light of the inherent variation within saline areas, it is unlikely that monocultures of sown species will be optimal when revegetating saline land.
Key Words
Salinity, halophyte, ecology, saltbush.
Introduction
In southwestern Australia, 10 % or 1.8 million ha of the farmed area is affected by dryland salinity and a further 6 million ha are threatened (1). One option for farmers is to plant salt-tolerant grasses, trees and shrubs in saline areas. These plants improve the visual amenity of saline land, provide feed for livestock, may reduce the spread of salinity and probably increase the biodiversity value of saline land. However, vegetation on saline land tends to remain patchy and there are few planting options available to farmers. The aim of this study was to assess botanical diversity within two paddocks that were once cropped and were subsequently sown with salt-tolerant species in the early 1980’s after becoming saline. It was predicted that botanical diversity would be low due to salinity, waterlogging and past farming practice.
Methods
The paddocks that were studied in 2001 are situated near Meckering (130 km east of Perth) and Tammin (180 km east of Perth). Soil samples were collected across paddocks in March 2001 to measure electrical conductivity and peizometers were used to monitor the water table. Botanical composition was assessed in autumn and spring using the dry-weight rank method of Mannetje and Haydock (2). Briefly, the paddocks were crossed by five transects in both autumn and spring, with botanical assessments made every 15 m along transects. For each assessment, the three herbaceous plant species that appeared to contribute most biomass were ranked in descending order from 1-3. Rankings were totalled and multiplied by a weighting factor to give a percentage of biomass/species.
Results
The Meckering paddock (19 ha) was the more saline and waterlogged site as 20% of the area had become a bare salt scald. On average the soil was highly saline (ECe 48 dSm-1) and the saline water table (ECw 27 dSm-1) was 66 cm below the soil surface in March. The soils in the Tammin paddock (12 ha) were on average highly saline (ECe 25 dSm-1) and the groundwater (164 cm below the soil surface in March) was highly saline (ECw 56 dSm-1). The topography of both paddocks was undulating.
Table 1 summarises the results. The Meckering paddock contained 31 herbaceous plant species, of which five were sown (early 1980’s) and 26 were volunteers. Only 23 % of the species were native to Australia. The most common species at the site in autumn were the grass Puccinellia ciliata and the halophytes Atriplex undulata, A. lentiformis, A. semibaccata and Halosarcia spp. In spring, the annual herbs Mesembryanthemum nodiflorum and Cotula coronopifolia formed 16.5 % of the botanical composition. The Tammin paddock contained 24 plant species of which five were sown and 19 had volunteered. One third of the recorded species were native to Australia. The most common species were Maireana brevifolia, Halosarcia spp. and Lolium rigidum.
Table 1. Botanical composition (%) in autumn and spring of two salt-affected paddocks.
Species |
Common name |
Status |
Origin |
Tammin |
Meckering | ||
autumn |
spring |
autumn |
spring | ||||
Halophytes | |||||||
Atriplex amnicola |
river saltbush |
sown |
Australia } |
2.7 |
< 1.0 | ||
Atriplex nummularia |
oldman saltbush |
sown |
Australia } |
6.9 |
4.1 |
- |
- |
Atriplex semibaccata |
creeping saltbush |
sown |
Australia } |
4.2 |
1.0 | ||
Atriplex undulata |
wavy-leaf saltbush |
sown |
Argentina } |
19.2 |
6.5 | ||
Atriplex lentiformis |
Quailbrush |
sown |
USA |
- |
- |
6.1 |
7.5 |
Haloscaria spp. |
Samphire |
volunteer |
Australia |
21.2 |
27.9 |
9.5 |
8.4 |
Maireana brevifolia |
small-leaved bluebush |
volunteer |
Australia |
32.1 |
20.4 |
1.5 |
2.3 |
Grasses | |||||||
Avena fatua |
wild oat |
volunteer |
Mediterranean |
< 1.0 |
< 1.0 |
< 1.0 |
< 1.0 |
Chloris virgata |
windmill grass |
sown |
Australia |
< 1.0 |
< 1.0 |
- |
- |
Eragostis curvula |
African lovegrass |
volunteer |
South Africa |
- |
- |
< 1.0 |
< 1.0 |
Eragostis dielsii |
prostrate lovegrass |
volunteer |
Australia |
10.5 |
3.6 |
7.1 |
3.3 |
Hordeum leporinum |
barley grass |
volunteer |
Mediterranean |
< 1.0 |
< 1.0 |
< 1.0 |
< 1.0 |
Hordeum marinum |
sea barley grass |
volunteer |
Southern Europe |
8.8 |
3.9 |
2.3 |
3.7 |
Lolium rigidum |
annual ryegrass |
volunteer |
Mediterranean |
8.3 |
17.7 |
6.4 |
3.5 |
Parapholis incurva |
coast barbgrass |
volunteer |
Mediterranean |
< 1.0 |
< 1.0 |
- |
- |
Paspalum vaginatum |
saltwater couch |
volunteer |
America |
< 1.0 |
< 1.0 |
1.1 |
< 1.0 |
Puccinellia ciliata |
Puccinellia |
sown |
Turkey |
- |
- |
34.0 |
30.8 |
Vulpia spp. |
silver grass |
volunteer |
Mediterranean |
10 |
2.8 |
< 1.0 |
3.4 |
Other | |||||||
Arctotheca calendula |
Capeweed |
volunteer |
South Africa |
< 1.0 |
< 1.0 |
< 1.0 |
3.6 |
Conyza spp. |
Fleabane |
volunteer |
America |
- |
- |
< 1.0 |
< 1.0 |
Cotula coronopifolia |
Cotula |
volunteer |
Australia |
< 1.0 |
9.7 |
< 1.0 |
7.7 |
Heliotropium curassavicum |
Heliotrope |
volunteer |
cosmopolitan |
- |
- |
< 1.0 |
< 1.0 |
Hypochaeris radicata |
Flatweed |
volunteer |
Europe |
< 1.0 |
3.4 |
< 1.0 |
< 1.0 |
Juncus bufonius |
Toadrush |
volunteer |
cosmopolitan |
< 1.0 |
< 1.0 |
< 1.0 |
< 1.0 |
Juncus acutus |
sharp rush |
volunteer |
Europe |
- |
- |
< 1.0 |
2.7 |
Mesembryanthemum nodiflorum |
Iceplant |
volunteer |
South Africa |
- |
- |
< 1.0 |
8.6 |
Plantago coronopus |
Buckshorn plaintain |
volunteer |
Europe |
- |
- |
< 1.0 |
< 1.0 |
Ploygonum aviculare |
wire weed |
volunteer |
Europe |
- |
- |
< 1.0 |
< 1.0 |
Ptilotus polystachyus |
mulla mulla |
volunteer |
Australia |
- |
- |
< 1.0 |
< 1.0 |
Romulea rosea |
onion grass |
volunteer |
South Africa |
- |
- |
< 1.0 |
3.8 |
Rumex acetosella |
Sorrel |
volunteer |
Europe & Asia |
< 1.0 |
< 1.0 |
- |
- |
Trifolium arvense |
haresfoot clover |
volunteer |
Mediterranean |
< 1.0 |
< 1.0 |
1.9 |
< 1.0 |
Trifolium glomeratum |
cluster clover |
volunteer |
Mediterranean |
< 1.0 |
< 1.0 |
< 1.0 |
< 1.0 |
Trifolium subterraneum |
Subterranean clover |
volunteer |
Mediterranean |
< 1.0 |
< 1.0 |
< 1.0 |
< 1.0 |
Trifolium tomentosum |
woolly clover |
volunteer |
Mediterranean |
< 1.0 |
< 1.0 |
< 1.0 |
< 1.0 |
Conclusion
Plant diversity within the paddocks was as high or higher than the diversity generally found in non-saline pastures in the same areas. The presence of so many species suggests that there is either little competitive exclusion, little agronomic exclusion or the paddocks are divided into botanical niches. It is likely that high levels of plant diversity within paddocks are maintained by niche differentiation; i.e. no one species can dominate (or perhaps even survive) in all of the functional niches within the paddock. The suggestion of niche differentiation was supported by successional changes in species composition across salinity and waterlogging gradients at both sites (data not presented). This diversity should be considered when evaluating options for revegetating saline land.
References
National Land and Water Resources Audit. 2001. Australian Dryland Salinity. Canberra.
Mannetje L.‘t and Haydock, K. P. 1963. J. Brit. Grassl. Soc., 18: 268-275.



