Sitemap

SG7

Site SG7 Landscape

Surface Soil			Site SG7 Profile
A1	0-10 cm	Black (10YR2/1); light silty clay loam; weak blocky structure; hardsetting surface condition; weak consistence moist; pH 5.5; abrupt change to:
A2	10-25 cm	Greyish brown (10YR5/2) (with some yellowish brown); conspicuously bleached; light silty clay loam; weak coarse blocky structure; very strong consistence dry; pH 5.3; sharp change to:
Subsoil
B21	25-55 cm	Brown (10YR5/3) with yellowish brown (10YR5/8) mottles; heavy clay; strong coarse prismatic, parting to strong coarse blocky structure; dark stains present on ped faces; very firm consistence moist; pH 5.4; clear change to:
B22	55-100 cm	Greyish brown (10YR5/2) with strong brown (7.5YR5/8) mottles; heavy clay; strong fine polyhedral structure (with shiny faced peds); pH 5.5; gradual change to:
B31	100-120 cm	Reddish yellow (7.5YR6/8) with red (2.5YR5/8) mottles; medium heavy clay; contains a band of ferromanganiferous segregations (up to 10 mm size) at 100-110 cm depth; pH 5.4; gradual change to:
B32	120+ cm	Reddish yellow (7.5YR6/8) and white (10YR8/1); medium heavy clay; pH 5.4.

• Strong texture contrast between surface (A) and subsoil (B) horizons.

The soil profile is strongly acid throughout.	Levels of soluble salts are very low throughout the profile.	Exchangeable aluminium levels become high in the subsoil horizons.	The clay content increases sharply at the A/B horizon boundary, i.e. there is a strong texture contrast between surface and subsoil horizons.

• Plant Available Water Capacity (PAWC) is considered to be medium (estimated at approximately 120 mm) for the top metre of the soil profile. This is based on available laboratory data and assumes an effective rooting depth of 100 cm. If rooting depth is restricted by the coarsely structured B21 horizon, then PAWC will be significantly lower (i.e. approximately 32 mm for the A horizons).

• The exchangeable aluminium level measured in the laboratory is not high in the strongly acid surface soil. This could be due to the effect of organic matter. In the A2 horizon, the levels have increased and may affect aluminium sensitive species. A pH/aluminium test sampled across the paddock may be appropriate to determine whether lime is needed to raise the surface soil pH. Other factors need to be considered before lime is recommended (e.g pasture species grown, method of application, local trial responses, soil surface structure and likely cost/benefit).

• The surface soil has a very high silt (42%) and fine sand (35%) content. Such soils tend to be unstable when rapidly wet which can result in the formation of surface crusts upon drying. However, the organic matter content is quite high at this site which results in surface soil aggregates being water-stable. Organic matter is important for promoting soil aggregation on such soils.
  
  
• The high level of exchangeable magnesium (i.e. 38%) may induce potassium deficiency (Baker and Eldershaw, 1993). Any deficiency can be assessed by plant tissue analysis.
  
  
• In strongly acid surface soils, deficiencies in molybdenum and phosphorus may occur.
  
  
• The A2 horizon sets very hard when dry and will become "spewy" when wet.

• The clay content increases sharply at the boundary between the light silty clay loam surface soils and the heavy clay B21 horizon. The B21 horizon is also dense and coarsely structured which will result in water and root movement being restricted. The presence of a bleached A2 horizon above the subsoil indicates that water movement is being restricted. On slopes, lateral movement of water may occur along the top of the relatively less permeable subsoil.
  
  
• The cation exchange is dominated by magnesium ions. This could result in a cation imbalance (e.g. potassium and/or calcium deficiency could occur). The high level of exchangeable magnesium in relation to calcium may also contribute to poor subsoil structure.
  
  
• From 25 cm depth in the profile, the level of exchangeable aluminium measured in the laboratory is high (230 mg/kg) and may restrict the growth of many aluminium sensitive species (such as lucerne, phalaris, subclover, white clover and tall fescue) and may affect more tolerant species, such as cocksfoot and ryegrass.

• "Pugging" problems can occur in winter.
• 2.5 cows/hectare is the usual carrying capacity.
• Potash and super responses occur.

This page contains material sourced from the Victorian Resources Online (VRO) website, originally published by the State Government of Victoria.

The content is provided under the Creative Commons Attribution 4.0 Australia licence (CC BY 4.0 AU).

This material is presented in an archived form and is no longer maintained or updated. It is provided for general information only and should not be relied upon as current advice.

This site is hosted by the Centre for eResearch and Digital Innovation (CeRDI), Federation University Australia. It is not endorsed by Agriculture Victoria.

Agriculture Victoria does not accept liability for any loss, damage or consequences arising from the use of, or reliance on, this material.