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Fact Sheets Measuring Soil Texture in the Lab

Measuring Soil Texture in the Laboratory

 

Key points

  • Particle size analysis breaks a soil into texture classes – sand, silt or clay.
  • Soil texture influences nutrient retention, water storage and drainage.
  • Particles greater than 2 mm are removed before analysis.
  • The soil textural triangle is used to determine soil type based on sand, silt and clay percentages.

 

Background

Particle size analysis (PSA) determines the relative amounts of sand, silt and clay in a soil. These size fractions are the mineral component of a soil and together determine soil texture. PSA is a laboratory alternative to field texturing (see Measuring Soil Texture in the Field fact sheet) and offers a more reliable determination of particle size distribution. There is only an approximate correlation between hand texturing and PSA (McDonald et al., 1998), because hand texturing relies on qualitative interpretation of texture while PSA measures exact amounts of individual particle sizes.
Soil texture is an inherent soil quality property that has a major influence on several other properties that influence agricultural potential (White, 1997). In particular soil texture influences nutrient retention, water storage and drainage. Soils with a higher proportion of sand retain less nutrients and water compared to clay soils.

 

Mineral components of soil

Coarse fragments

Greater than 2 mm and include coarse quartz, rock fragments and cemented material. This is commonly called the ‘gravel fraction’.

Sand

Comprise quartz and resistant primary minerals such as mica. Sand particles are between 2 mm and 20 microns in size (Note: there are 1000 microns in 1 mm).

Silt

Silts are typically composed of quartz and small mineral particles such as feldspars and mica, and are between 2 and 20 microns in diameter.

Clay

Clays are made up of secondary clay minerals and oxides/oxyhydroxides of iron and aluminium, and are less than 2 microns in diameter.

 

South-western Australia

Soil data from a range of projects conducted across the state is constantly added to the soils database managed by the Department of Agriculture and Food, Western Australia. Figure 1, taken from McArthur (1991), shows the soil types characteristic of south-western Australia.

 


Figure 1: Characteristic soils of the agricultural region of south-western Australia. Image courtesy of Natural Resources Assessment Group, DAFWA.

 

Particle Size Analysis

PSA is a reliable, reproducible technique that eliminates factors that may affect field texture such as organic matter content, clay mineralogy, cation composition and the presence of cementing agents (Bowman and Hutka, 2002). The method comprises two parts, dispersion of the soil and separation of the particles into size groups.

Dispersion and pre-treatment

Pre-treatment of the soil may be needed to remove organic matter and salts such as gypsum. Iron oxides, calcium carbonate and magnesium carbonate should also be removed as they are common cementing agents in Australian soils (Bowman and Hutka, 2002). Pre-treatment of the soil will allow it to disperse completely.

Fractionation

Fractionation involves removing each particle size group (sand, silt and clay) from a pretreated soil and water mixture settled in a cylinder (figure 2). This is achieved by allowing the soil particles of different size to settle out of solution at different times (small clay particles take the longest). The fractions are subsequently dried and weighed and the sand, silt and clay must add
up to 100%. Some calculations are needed for this method including the use of a scaling factor for the pipette analysis and a calculation for the sieve analysis. For a complete method, refer to Bowman and Hutka (2002).

 


Figure 2: Cylinder used for fractionation of sand, silt and clay particles. The sand fraction settles first followed by the silt then the clay fractions.

 

Using the soil texture triangle

The soil texture triangle (figure 3) is used to convert particle size distribution into a recognised texture class based on the relative amounts of sand, silt and clay as a percentage, for example:

 


Figure 3: Once soil fractionation is complete a soil textural triangle is used to determine soil texture. Image adapted from Hunt and Gilkes (1992).

 

A – Sand 50% + Silt 30% + Clay 20% = SILTY LOAM

The grid on the triangle allows you to move to the left or the right of your position running parallel with either side of the triangle. It is best to start at the base with the sand. Position your finger along the base line at the 50% mark. Move your finger up the line running parallel with the right side of the triangle. Simultaneously use another finger to trace a line from the 30% silt mark until the two meet. Your two fingers will always meet at clay for the remaining percentage, in this case 20%. This is always the case that the first two sizes chosen will lead you to the third.

B – Sand 80% + Silt 5% + Clay 15% = SANDY LOAM

Trace your finger along the 80% sand line while simultaneously tracing another finger along the 5% silt line until the two meet. This should be where clay is 15%.

 

Further reading and references

Bowman GM and Hutka J (2002) Particle Size Analysis. In Soil Physical Measurement and Interpretation for Land Evaluation
(Eds N McKenzie, K Coughlan, H Cresswell) pp 224-239. CSIRO Publishing: Victoria.

Hunt N and Gilkes R (1992) Farm Monitoring Handbook. The University of Western Australia: Nedlands, WA.

McKenzie N, Coughlan K and Cresswell H (2002) Soil Physical Measurement and Interpretation For Land Evaluation.
CSIRO Publishing: Collingwood, Victoria.

McKenzie NJ, Jacquier DJ, Isbell RF, Brown KL (2004) Australian Soils and Landscapes An Illustrated Compendium. CSIRO Publishing: Collingwood, Victoria.

NLWRA (2001) Australian Agricultural Assessment 2001. National Land and Water Resources Audit.

 

Authors: Katharine Brown ( The University of Western Australia) and Andrew Wherrett (Department of Agriculture and Food, Western Australia).

 

This soilquality.org.au fact-sheet has been funded by the Healthy Soils for Sustainable Farms programme, an initiative of the Australian Government’s Natural Heritage Trust in partnership with the GRDC, and the WA NRM regions of Avon Catchment Council and South Coast NRM, through National Action Plan for Salinity and Water Quality and National Landcare Programme investments of the WA and Australian Governments.
The Chief Executive Officer of the Department of Agriculture and Food, The State of Western Australia and The University of Western Australia accept no liability whatsoever by reason of negligence or otherwise arising from the use or release of this information or any part of it.

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