Soil productivity depends on its ability to meet plants’ water and nutrient demands. Often, a soil may have multiple physical or chemical limitations. Practical and profitable management options can reduce these constraints, improving yields and profitability. Recognising soil constraints and their impact on agriculture is challenging but essential.
Many of the department's soil research and development activities are carried out in partnership and collaboration with other research institutions.
Dispersive clay soils are common in the agricultural areas of WA, where they occur mainly as duplex or gradational profiles. Soils with more than about 18% sodic clay are susceptible to dispersion when wet. Dispersed clay clogs soil pores, restricting water infiltration, storage, and drainage. In low rainfall environments, sodic and dispersive clays are often associated with alkalinity, transient salinity, and boron toxicity that limit soil water availability to crops. In medium to higher rainfall environments, sodic duplex soils are particularly susceptible to waterlogging due to poor drainage. These soils are difficult to manage in adverse seasons, where multiple constraints can limit crop and pasture growth.
The department provides information and support to grain growers to address this soil constraint, including through our research partner SoilsWest and Soil Quality Knowledge Base website.
Related Links
- Deep ripping with amendments trial for yield improvement of sodic soil
- Diagnosing sodic and alkaline soil
- Soil Quality: 8 Sodic and Alkaline Soil
- SoilsWest
- Sodic and alkaline soil
- Impacts of sodic and alkaline soils
- Managing sodic and alkaline soil
- Testing for dispersion and slaking – modified Emerson dispersion test
- Soil pH can affect soil dispersion
- Understanding your soils: sodicity and salinity
- Managing grey clays: to maximise production and sustainability
- Gypsum quality
Soil acidity is a major constraint to farming in Western Australia. Extensive surveys of soil pH profiles across the south-west of the state show that more than 70% of surface soils and almost half of subsurface soils are below appropriate pH levels. Most growers now place soil acidity in their top 3 management priorities. Managing soil acidity is both achievable and profitable.
The department supports landholders in reducing the impact of soil acidity by providing technical information on diagnosis and management options and is currently researching innovative approaches to managing subsoil acidity with support from the Grains Research and Development Corporation (GRDC).
Related Links
- Agricultural Lime
- GRDC Groundcover TV – liming acid soils
- Lime quality and liming rates
- Managing soil acidity
- Report Card Soil Acidity - Status and trend in the agricultural areas of the south-west of Western Australia
- Soil acidity
- Soil acidity : a guide for WA farmers and consultants
- Soil Quality: 4 Soil Acidity - Soil Quality ebook series
- SoilsWest
Increasing soil organic carbon is widely regarded as beneficial to soil function and fertility and can be associated with increased agricultural productivity.
Soil is considered a major world carbon sink and source of carbon emissions. Increasing the amount of organic carbon in agricultural and rangeland soils is a recognised mechanism for the abatement of greenhouse gases. Projects that aim to accumulate soil carbon can be registered with the Clean Energy Regulator to receive Australian carbon credit units (ACCU’s).
Soil type, rainfall, and temperature limit the amount of soil organic carbon generated and stored. The department is involved in quantifying how soil type and land management practices impact soil carbon.
The increase of soil organic carbon requires continuous inputs from external sources, which can be logistically difficult and expensive. Increases in soil organic carbon will generally be an incidental benefit, potentially from good agronomic practices.
Related Links
- Agriculture methods - ACCU Scheme methods
- Carbon sequestration Looc-c tool - CSIRO
- Managing Soil Organic Matter: A practical guide
- Measuring soil organic carbon
- Profit from soil carbon video
- Report card on sustainable natural resource use in agriculture : status and trend in the agricultural areas of the south-west of Western Australia
- Soil Quality
- Soil Quality: 2 Integrated soil management (DPIRD)
All surface and subsurface soils can be compacted - some more easily than others. Surface soil can easily be compacted by livestock and machinery and can be induced by natural soil conditions such as wetting and drying.
Compacted subsoil, resulting from machinery traffic, restricts crop and pasture root growth. Almost no Western Australian agricultural soils have capacity to resist compaction or self-repair following compaction.
The department provides information and support to help growers manage this soil constraint on their properties.
Related Links
- Developing a controlled traffic (tramline) farming system (DPIRD)
- Land resources in the South-West Agricultural Region: a shire-based summary of land degradation and land capability (DPIRD)
- Managing south coast sandplain soils to yield potential (DPIRD)
- Soil Quality: 6 Soil Compaction - Soil Quality ebook series (DPIRD)
- Soil Guide – a handbook for understanding and managing agricultural soils (DPIRD)
- SoilsWest
- Soil compaction (Soil Quality Knowledge Base)
- Factors influencing soil compaction (Soil Quality Knowledge Base)
- Managing soil compaction (Soil Quality Knowledge Base)
- Subsurface compaction: a guide for WA farmers and consultants (DPIRD)
- Controlled traffic farming (Soil Quality Knowledge Base)
Plant essential nutrients are required for profitable and sustainable agricultural production. An insufficient amount of any essential nutrient will lead to poor crop or pasture growth and limit production, reducing profit for growers. Fertiliser represents the largest farm input cost and overuse will reduce growers’ profits and can lead to run-off and leaching into waterways.
WA soils are inherently infertile, so many farmers have built up soil nutrient levels and adopted a replacement approach to fertiliser management. This needs to be carefully managed and it is recommended that growers undertake regular monitoring of soil and plant nutrient levels.
The department provides information with is research partner SoilsWest (soilswest.org.au) via the website, soilqualityknowledgebase.org.au, to help grain growers address this constraint on their properties.
Related links
- Soil Quality: 10 Plant Nutrition - Soil Quality ebook series (DPIRD)
- SoilsWest
- Crop and soil interactions (Soil Quality Knowledge Base)
- Soil chemical attributes (Soil Quality Knowledge Base)
- Why is nitrogen important for soil and plants? (Soil Quality Knowledge Base)
- Soil phosphorus (Soil Quality Knowledge Base)
- Why is potassium important for soil and plants?
- What are trace nutrients? (Soil Quality Knowledge Base)
- What is fertiliser? (Soil Quality Knowledge Base)
- Soil and water pollutants (Soil Quality Knowledge Base)
- Integrated nutrient management (Soil Quality Knowledge Base)
Soils in Western Australia are affected by three forms of salinity.
- Natural or primary salinity develops naturally, mainly in areas where rainfall is insufficient to leach salts from the soil profile, and evaporation is high. Moist and wet primary saline areas have very high natural diversity in Western Australia (WA), and are at risk from increased flooding, waterlogging, and increasing salinisation. Natural salt lake chains in WA follow ancient drainage lines.
- Dryland salinity is a major form of land degradation in WA; it is associated with the presence of a shallow watertable in the soil. Dryland salinity is caused by increased recharge under annual agricultural systems, leading to rising watertables and salt transport into the root zone. More than one million hectares of broadacre farmland are estimated to be affected by dryland salinity in WA. Most of this land is highly to extremely saline and is therefore too saline for cropping.
- Transient salinity is associated with soil sodicity and alkalinity. Transient salinity is present on many of the heavy textured soils in low rainfall areas of WA. Most of this land is slightly to moderately saline, and this land is therefore routinely cropped. About 3.5 million hectares of broadacre farmland could be affected by transient salinity in WA.
The Soil and Land Conservation Act, 1945 regulates the conservation of soil and land resources. Land degradation includes water and wind erosion, salinity, eutrophication, and flooding; and the removal or deterioration of natural or introduced vegetation that may be detrimental to the present or future use of land.
There are several practical options for increasing productivity from saline sites and reducing environmental damage.
The department provides technical information to assist landholders and the community to diagnose the extent and effect of salinity and manage the impacts.
Related links
- Assessing saline areas in WA
- Managing subsurface water in WA
- Dryland salinity – Soil Quality: 8 Sodic and Alkaline Soil (DPIRD)
- Saltland recovery and production (DPIRD)
- Soil and Landscape Grid of Australia (CSIRO)
- Soil and Land Conservation Act 1945
- Dryland salinity - Farmer case studies
- Dense saltbush plantings
- Establishing saltbush and understorey
- Measuring soil salinity
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Ed Barrett-LennardGrains Senior Principal Research Scientist+61 0418 133 611
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John SimonsFisheries and Agriculture Resource Management Senior Research Officer+61 8 9083 1128
Dryland farming systems rely on the soil to store and release water and nutrients to meet crop demand. Soil water storage is dynamic due to changes in water inputs, for example, rainfall, irrigation, and outputs, including evaporation, plant transpiration, runoff, and deep drainage beyond the root zone.
The aim of soil water management is to improve the efficiency with which rainfall is converted into crop and pasture yield. This involves increasing the amount and depth of water storage (for example, via soil amelioration) and optimising the production system for a given level of water storage.
Soil texture cannot be readily changed, so soil water storage amelioration focuses on enabling water flow into the soil profile and increasing access through increased rooting depth. Optimisation of the production system requires management of inputs (for example, fertiliser, pesticides) and relies on knowing how much plant available water is stored. This enables farmers to predict yields and maximise profits.
Waterlogging occurs when there is too much water in a plant’s root zone, which decreases the oxygen available to roots. Waterlogging can be a major constraint to plant growth and production and, under certain conditions, will cause plant death. This constraint may not be apparent until the whole soil profile is saturated, and water appears on the surface.
The department provides landholders with technical information and support on management options to recognise and reduce the impacts of waterlogging.
Related links
- Soil Quality: 8 Sodic and Alkaline Soils (DPIRD)
- Waterlogging (Soil Quality Knowledge Base)
- Impacts of waterlogging on plant health (Soil Quality Knowledge Base)
- Management of waterlogging (Soil Quality Knowledge Base)
- Waterlogging and salt interactions (Soil Quality Knowledge Base)
- Sodic and alkaline soil profiles in the south-western agricultural region (Soil Quality Knowledge Base)
- Adoption of GRDC research: Late sowing of cereals due to waterlogging (Grains Research and Development Corporation)
- Late sowing of cereals due to waterlogging (Grains Research and Development Corporation)
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Ed Barrett-LennardGrains Senior Principal Research Scientist+61 0418 133 611
Soil water repellence is a widespread problem that mostly affects soils with low clay content or high organic matter levels in the topsoil, in the medium to high rainfall zones. The expression of water repellence appears to be increasing in WA due to an increase in cropping frequency, dry and earlier sowing, minimum tillage, and reduced break of season rainfall.
The department can provide technical information on a range of management options and new techniques to assist landholders to reduce water repellence impacts.
Related Links
- Claying to ameliorate soil water repellence
- Effective furrow sowing for water repellent soils
- Estimating soil texture by hand
- Rotary spading to ameliorate soil water repellence
- Setting up mouldboard plough to optimise soil inversion (Soil Quality Knowledge Base)
- Soil inversion to ameliorate soil water repellence
- Soil Quality: 7 Soil Water Repellence - Soil Quality ebook series (DPIRD)
- Soil water repellence (Soil Quality Knowledge Base)
- Causes of soil water repellence (Soil Quality Knowledge Base)
- Assessing options for managing water repellent gravel soils (SoilsWest)
- Comparing soil strategic deep tillage implements (Soil Quality Knowledge Base)
- Ten years of managing water repellent soils research in Western Australia – a review of current progress and future opportunities (Grains Research and Development Corporation)
- Managing South Coast Sandplain soils to yield potential (DPIRD)
Water erosion is a significant form of land degradation in Western Australian (WA) agriculture that is caused by intense rainfall and surface water runoff. The annual direct cost of water erosion to dryland farming in WA is estimated to be more than $10 million.
The Soil and Land Conservation Act, 1945 regulates the conservation of soil and land resources. Land degradation includes water and wind erosion, salinity, eutrophication, and flooding; and the removal or deterioration of natural or introduced vegetation that may be detrimental to the present or future use of land.
Water erosion on rainfed land (dryland) is associated with intense rainfall and land conditions that increase the risk of erosion. Risk factors include insufficient ground cover steep slopes, land surfaces on which tillage or livestock have detached soil, land features that concentrate water flow into long runs, controlled traffic lines, fences and vegetated alleys, steep slopes, and insufficient or inappropriate surface water flow-control structures.
Soil loss from water erosion is a significant problem across large tracts of the rangelands, including the east Kimberley, west Pilbara, Gascoyne, and upper Murchison catchments. Water erosion during large storms in the southwest agricultural areas has caused major losses on farms and public infrastructure (for example, roads and rail).
Water erosion on irrigated land is often associated with flooding that inundates the floodplains on which irrigation relies.
The department provides information to landholders to reduce water erosion risk and recover from erosion. Advice and support are also available from our technical specialists.
Related links
- Developing a controlled traffic (tramline) farming system
- Disaster Recovery Funding Arrangements
- Functions and duties of the Commissioner of Soil and Land Conservation
- Groundwater management
- Repairing gully erosion
- Soil and Land Conservation Act 1945
- Soil erosion, status and trend in the pastoral rangelands of WA
- Surface water management
- Water erosion control after fire
- Water erosion in the south-west of Western Australia
- Water erosion, status and trend in the pastoral rangelands of WA
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Paul GallowayFisheries and Agriculture Resources Management Senior Research Scientist+61 8 9083 1127
Wind erosion is a major form of land degradation in Western Australia due to the interaction of the Mediterranean climate and predominantly sandy surfaced soils. Wind erosion involves the detachment, transportation, and redeposition of soil by wind.
Productivity of crops and pastures is reduced by the removal of the most fertile component of the soil from the paddock and through sand-blasting of crops. Wind erosion can degrade infrastructure and dust particles can create air pollution. In 2022, DPIRD estimated the opportunity cost from wind erosion for the agricultural region as $62 million.
The Soil and Land Conservation Act, 1945 regulates the conservation of soil and land resources. Land degradation includes water and wind erosion, salinity, eutrophication, and flooding; and the removal or deterioration of natural or introduced vegetation that may be detrimental to the present or future use of land.
All soils are susceptible to wind erosion, which can be minimised by maintaining more than 50% ground cover to reduce wind-speed at ground level, and minimising soil disturbance. Where water erosion is also of concern, groundcover should exceed 70%.
Wind erosion risk can be increased by some agronomic practices if not carried out as recommended.
The department provides information and technical support for farmers to reduce the wind erosion risk and options to rehabilitate wind eroded sites.
See also
Related links
- Diagnosing wind erosion risk
- Report card on sustainable natural resource use in agriculture: status and trend in the agricultural areas of the south-west of WA (DPIRD)
- The impact of tillage practices and crop residue (stubble) retention in the cropping system of WA (DPIRD)
- Managing stubble for wind erosion control in WA
- Wind erosion after fire in WA
- Wind erosion
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Justin LaycockFisheries and Agriculture Resource Management Research Scientist+61 8 9892 8407
Dryland salinity (salinity on non-irrigated land) is one of the greatest environmental threats facing Western Australia's agricultural land, water, biodiversity and infrastructure. It's commonly defined as salinity at or near the soil surface causing reduced plant growth, reduced water quality and damage to infrastructure.
The department recommends that saltland management is part of a whole farm, or preferable whole catchment, plan.