One-off tillage options for water repellent gravel soils. Tillage options for severely repellent sands - which methods work?

2016
CC BY 4.0

Research organisatons
Funding source

Trial details

Researcher(s) Stephen Davies (DAFWA)
Laura Dorman (MIG)
Debbie Gillam (DAFWA)
Chad Reynolds (DAFWA)
Jo Walker (DAFWA)
Year(s) 2016
Contributor West Midlands Group
Trial location(s) Badgingarra, WA
Dandaragan, WA
One-off tillage options for water repellent gravel soils. Tillage options for severely repellent sands - which methods work? locations
Aims

Assessing practical soil management options for overcoming severe water repellence on sandy gravels in the West Midlands.

Key messages

On deep sandy profiles subsoil compaction and acidity are major constraints. At this site the limited cropping history resulted in an expectation that the site would not be compacted but compaction was severe, indicating how susceptible these pale sands can be to compaction. For many deep sands, liming followed by deep ripping with topsoil slotting may be one of the most economical ways of effectively overcoming subsoil compaction and acidity to depths of 40-60cm.

On severely repellent sands however, it may be that deep ripping alone is inadequate and options which overcome the repellence and assist with weed control while at the same time addressing subsoil compaction and acidity may be required to get sustained productivity benefits (Davies et. al. 2017). The impact of deep ripping on highly repellent soils is variable with anecdotal reports that ripping can sometimes worsen the expression of repellence and result in poorer crop establishment. Other reports indicate substantial productivity gains can also be achieved (Blackwell et. al. 2016). Deep ripping may help overcome soil water repellence by: 1) creating a rougher soil surface allowing water to pond and infiltrate over time; 2) loosening the dry topsoil making it a more effective mulch, reducing soil moisture loss from the subsurface soil; 3) delving some seams of subsoil to the surface which act as pathways for water entry, with some ripper tine designs and attachments facilitating this more than others. Conversely the negative effects of deep ripping can include: 1) enhanced drying of the repellent topsoil from the loosening action; 2) increased expression of the water repellence when the soil is ripped when it is quite dry. Repellence severity, or expression, is increased with these negative effects which was the case for this site. For other sites where repellence is more moderate any benefits of deep ripping may outweigh the negative impacts. The mixed effects of deep ripping on repellent soils needs further research to be better understood. It is likely that rippers with C-shaped or parabolic shaped tines with broader points and wider ‘face’ plates will achieve more subsoil delving into the topsoil. Some rippers can also be fitted with wings which can also increase the degree of soil mixing. A greater degree of subsoil delving could result in development of more effective infiltration paths and longer lasting reductions in topsoil water repellence.

In this study rotary spading and modified one-way ploughing were effective in improving water infiltration on severely repellent sand even if they did not remove the deeper compaction. Second-hand one-way disc ploughs have a relatively low capital and operating cost (Table 1) and are relatively cheap to modify into a simple but robust tool for partial soil inversion (Davies et. al. 2016), although good seed bed preparation is still essential.

Lead research organisation Department of Agriculture and Food WA
Host research organisation West Midlands Group
Trial funding source GRDC DAW00244
Related program N/A
Acknowledgments

GRDC DAW00244 Repellence Project: DAFWA; Paul Kelly


Other trial partners Not specified
Download the trial report to view additional trial information

Method

Crop type Cereal (Grain): Wheat
Treatment type(s)
  • Soil Improvement
Trial type
Trial design

Badgingarra 2016

Sow rate or Target density Not specified
Sow date Not specified
Harvest date Not specified
Plot size Not specified
Plot replication Not specified

Dandaragan 2016

Sow rate or Target density 83kg/ha
Sow date 20 May 2016
Harvest date Not specified
Plot size 12m x 1200m
Plot replication Not specified
Download the trial report to view additional method/treatment information
Trial source data and summary not available
Check the trial report PDF for trial results.
Observed trial site soil information
Trial site soil testing
Not specified
Soil conditions
Trial site Soil texture
Badgingarra, WA Not specified
Dandaragan, WA Non-wetting sand
Derived trial site soil information
Australian Soil Classification Source: ASRIS
Trial site Soil order
Badgingarra, WA Chromosol
Dandaragan, WA Tenosol
Soil Moisture Source: BOM/ANU
Average amount of water stored in the soil profile during the year, estimated by the OzWALD model-data fusion system.
Year Badgingarra WA Dandaragan WA
2016 211.2mm103.9mm
2015 209.7mm103.9mm
2014 226.8mm94.8mm
2013 251.5mm121.8mm
2012 236.0mm132.3mm
2011 224.8mm96.9mm
2010 209.6mm84.2mm
2009 228.5mm110.1mm
2008 246.8mm97.5mm
2007 198.9mm51.3mm
2006 196.0mm74.4mm
2005 242.6mm95.5mm
2004 204.2mm91.7mm
2003 230.9mm90.5mm
2002 212.7mm32.9mm
2001 192.5mm35.4mm
2000 206.7mm114.0mm
National soil grid Source: CSIRO/TERN
NOTE: National Soil Grid data is aggregated information for background information on the wider area
Actual soil values can vary significantly in a small area and the trial soil tests are the most relevant data where available

Soil properties

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Climate

Dandaragan WA 2016


Observed climate information

Rainfall trial gsr (mm) 413mm

Derived climate information

Badgingarra WA

Dandaragan WA

Badgingarra WA

NOTE: Exact trial site locality unknown - Climate data may not be accurate
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Dandaragan WA

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Some data on this site is sourced from the Bureau of Meteorology

SILO weather estimates sourced from https://www.longpaddock.qld.gov.au/silo/
Jeffrey, S.J., Carter, J.O., Moodie, K.B. and Beswick, A.R. (2001). Using spatial interpolation to construct a comprehensive archive of Australian climate data , Environmental Modelling and Software, Vol 16/4, pp 309-330. DOI: 10.1016/S1364-8152(01)00008-1.

Trial report and links

2016 trial report



Trial last modified: 06-08-2019 07:54am AEST