What changes your mind? A RiskWi$e decision exercise at the WMG N banking trial

By Simon Kruger, WMG Project Communications Officer

The group at the Velyere N banking trial during the WMG Spring Field Day, 17 September 2026.

At the WMG Spring Field Day on 17 September 2026, WMG Project Communications Officer Simon Kruger trialled a different style of field day session at the WMG RiskWi$e N banking trial at Velyere Farm, Dandaragan. Rather than simply standing in front of the plots and presenting the trial treatments and results, the session was designed to get the 92 people in attendance moving, making a prediction and thinking about the information behind their decision.

Participants were first asked to back one of six canola plots to produce the highest yield this year, based only on what they could see. They were then given three additional pieces of information about the site and treatments, revealed one at a time. After each reveal, they could stay with their original choice or move to another plot if the new information changed their thinking.

The interactive session was co-designed with assistance from Dr Brendan Brown of CSIRO, who leads the behavioural science work within RiskWi$e. The aim was not to find the ‘right’ answer on the day, but to explore how additional information changed people’s predictions, which information mattered to them, and how differently they weighed the same evidence.

This article runs the same exercise ‘on paper’. The canola has not been harvested, so nobody knows the answer, WMG included. At each stage, pick the plot you would back and note the letter before reading on.

WMG Project Communications Officer Simon Kruger runs the session, with plots A to F marked by sheets on pegs. The details for each plot sat underneath.
Where do your decisions sit?

Before looking at the plots, the group lined up according to how they make N decisions, with gut feel, past experience and rules of thumb at one end and test results and calculations at the other. About 20 per cent placed themselves at the analytical end, 70 per cent used a mix of analysis and intuition, and 10 per cent leaned mainly on gut feel.

Before reading on, place yourself somewhere on the same line and think about why.

Round 1: Look only
Plots A to F, photographed individually on 5 October 2026.

These photos were taken on 5 October, about two and a half weeks after the field day, so the canola is further through pod fill than it was on the day.

The site was sown to wheat in 2025 and is in canola this year. On the day, the only other thing the group heard was a working definition of N banking: applying more N than the current crop needs, on the chance it pays back in yield or remains in the soil for the next crop.

While the field day group could walk through and inspect each plot firsthand, the same challenge applies here: based on what you can see, which plot would you back?

The field day group spread across all six. Plot B drew the most support with 22 people, followed by F with 20, E with 18 and C with 16. Plots A and D had eight each.

Round 2: Site background

The trial was established in 2025. The soil is a deep red brown sandy loam, with sand to more than 2 m. From April to October 2025 the site received 526 mm, against a long-term average of 425 mm. The season followed a very dry summer, with a wet July and August and a dry finish. Before sowing in 2025, the soil held 72 kg N/ha to 50 cm.

With that in mind, stay with your plot or move to another.

Round 3: N applied in 2025

On the day, each plot’s details sat under its marker sheet and were uncovered at this point.

Every plot received 10 kg N/ha as urea at sowing in 2025. Plot D, the seeding N only treatment, received nothing further. The other five went on to receive between 125 and 240 kg N/ha in total, applied as follows.

PlotTreatmentAt sowing~4 weeks post sowing~8 weeks post sowingTotal
AGrower practice104075125
BYield Prophet, decile 5100180190
CN bank, economic optimum100140150
DSeeding N only100010
EGrower experiment1080150240
FHigh N bank100230240

*All figures kg N/ha, applied as urea to wheat.

Plots A and E split their in crop N across two applications, with E receiving twice the in crop N of grower practice. Plots B, C and F received theirs in a single application at first node. E and F reached the same total of 240 kg N/ha by different routes.

Now that you know how much N went on and when, stay or move.

At the field day, approximately 30 of the 92 people, about a third, changed plots after hearing the rates.

Round 4: What was left after harvest

Each plot was soil sampled in January 2026, after the wheat was harvested, by Ethan Sirr of Moora Soil and Plant Contracting.

 ABCDEF
N applied in 202512519015010240240
Soil mineral N, 0 to 50 cm599811339144137
Soil mineral N, 0 to 90 cm8015814648201188

*kg N/ha, nitrate plus ammonium. These are results from six individual plots, one per treatment, chosen for the exercise. They are not treatment averages.

The two plots that received 240 kg N/ha held the most mineral N after harvest, and plot D, with 10 kg N/ha, held the least. Against the 72 kg N/ha measured to 50 cm before sowing in 2025, plots A and D finished lower, while the other four finished higher. This is consistent with some of the N applied to the wheat in those four plots remaining in the profile in January, although these figures cannot show how much of the rest was taken up, lost or tied up.

Knowing some of that N was still in the soil, stay or move.

Approximately 15 people changed plots at this stage, although most of the group stayed with their previous choice.

Same information, different decisions

Some people stayed with their first choice through every reveal, while others moved as new information arrived. Given the same three cards, people weighed them differently and reached different conclusions.

Three cards are not enough to make a case for or against N banking, and the session was not designed to make one. The intent, in line with the RiskWi$e approach, was to slow the decision down, work out which information matters, and make the best-informed call available. That does not guarantee the right result, because the season still has a large say, but it should give more confidence in the decision, make it easier to explain why it was made.

If you played along, compare the plot you picked from the photos with the one you finished on, and think about which piece of information moved you, if any did, and why?

The 2025 wheat result

After the session, a couple of growers and advisers asked how the wheat yielded in 2025. Treatment average yields ranged from 4.5 to 4.9 t/ha, with no statistically significant differences in yield or grain protein between treatments. Across rates from 10 to 240 kg N/ha, the trial did not detect a yield or protein response in its first season. The 2026 canola result is not yet known, and WMG will report it once the plots are harvested and analysed.

Benchmark your own decision making

A Decision Benchmarking survey, shared with WMG by Dr. Brendan Brown of CSIRO, compares your decision default settings with those of more than 1,000 other growers who have completed it, and returns a personalised benchmark.

Complete the survey at https://farmvoice.au?module=decision_benchmarking or scan the QR code below.

Whether you joined us at the field day or played along through this article, we hope the exercise prompted you to think about how you make decisions and what information carries the most weight. More information does not guarantee the right outcome, but taking the time to seek out the information that matters can help make a better-informed decision and give you greater confidence in why you made it.

If you would like to learn more about the RiskWi$e decision-making work, or have a decision you would like to explore, get in touch with WMG Project Communications Officer Simon Kruger.

Acknowledgements

Thanks to Chris Spencer, farm manager at Velyere, for hosting the trial and the field day group, to Kalyx for managing the plots, and to WMG’s Chanel Duggan and Gabby Carrivick, the volunteers who held the plot markers on the day and everyone who interacted and got involved.

RiskWi$e is GRDC’s National Risk Management Initiative, a five-year, $30 million investment running from 2023–2028 that aims to help Australian grain growers strengthen decision making under risk and uncertainty for enduring profitability.

RiskWi$e helps growers understand the trade-off between potential reward and downside risk across a range of farm management decisions. The initiative brings together 26 grower, adviser and extension groups, 10 research partners and six Action Research Groups to help Australian grain growers and advisers get decisions ‘more right more often’.

CSIRO leads the initiative nationally, with the Grower Group Alliance leading in WA.

Clay, compost and spading at Walyoo Farm: WMG’s new soil amendments trial

By Simon Kruger and Chanel Duggan, WMG

WMG’s long-term stacked soil amendments trial at Wathingarra, Badgingarra, concluded at the end of 2025 after five seasons. The site tested the combined effects of mechanical amelioration and organic and mineral amendments on deep brown sand with severe soil water repellence. Results from each season are available on WMG’s website project pages.

Two findings from Wathingarra stood out consistently. The first was the durability of the amelioration effect, with mouldboard ploughing and rotary spading applied in 2021 continuing to produce meaningfully higher yields four years later without further mechanical intervention. The second was the performance of organic carbon amendments, particularly compost, and of local clay in the amendment strips. Both lifted yield above the site mean in 2025 and showed a pattern of improved nutrient supply and soil function across the trial period.

Those two amendments are what the new trial at Regans Ford carries forward. The site is on deep sand at Walyoo Farm near Dandaragan, managed by Mark Drake of Lawson Grains, and takes compost and clay from the Wathingarra treatment list into a replicated trial on a different deep sand under commercial grower conditions. Five seasons of results at one site establishes that the amendments worked there. Whether they perform the same way on a different soil in a different part of the district is the question the new trial exists to answer.

Trial design

The Regans Ford trial is structured as a randomised complete block design with five treatments and four replicated blocks, giving 40 plots in total. Each plot is 12m in seeded length with a 10m cutback, and 4 m wide in 2026. In 2027 the plots will be split to 2m width to allow fertiliser treatment variations to be overlaid, adding a second dimension to the experiment in the second season. The total trial footprint runs approximately 201m along the seeding direction and 60m wide, with spaded buffer zones between treatment blocks and additional buffers to account for clay overthrow during spreading.

Figure 1. The Regans Ford site post clay spreading

The crop is Jurien lupin, sown on 7 May 2026 at 100kg/ha to a depth of 4cm on 22cm row spacing. The previous rotation was wheat in 2025 and canola in 2024. Fertiliser across the full site in 2026 is MacroProPlus and Agflow Mn at 100kg/ha, with fertiliser treatment splits deferred to 2027 once the baseline amendment effects are established.

Treatments

The five treatments test spading alone, the two most promising individual amendments from Wathingarra applied with spading, and their combination, against an untreated control.

TreatmentDescriptionAmendment rate
1Untreated controlNil
2Spading onlyNil
3Spading + compost12 t/ha
4Spading + clay300 t/ha
5Spading + compost + clay12 t/ha + 300 t/ha
Figure 2. Spading of treatments at the Regans Ford site

All spaded treatments were incorporated using an Imants Plot Spader to approximately 30cm depth prior to seeding. Compost was weighed and spread by hand before incorporation. Clay was applied using Mark’s grader spreader before incorporation by spading, with the spread pattern confirming an average application rate close to the 300t/ha target. Commercial clay spreaders tend to deliver a peaked distribution across the spread width, and sampling across the plots confirmed that was the case here. Measurements through the season and at harvest will account for the within-plot distribution.

The untreated control provides the baseline against which amendment and amelioration effects will be assessed. The spading only treatment isolates the effect of mechanical soil disturbance from any nutrient or physical contribution of the amendments. Treatments 3 and 4 test compost and clay individually in combination with spading, while Treatment 5 asks whether applying both amendments together with spading delivers an additional benefit beyond either alone.

Soil baseline
Figure 3. Comprehensive soil testing being carried out at the Regans Ford site by Moora Soil & Plant Contracting

Pre-treatment soil sampling was carried out across 20 plots in May 2026 by Ethan Sirr of Moora Soil and Plant Contracting, with samples taken to 50cm depth in three increments and analysed by CSBP. The results confirm the site is typical deep sand country for the Dandaragan district. Texture across the profile is uniformly sandy to the full sampling depth, transitioning from a brown-grey surface layer to an orange subsoil below 30cm. Organic carbon in the top 10cm averaged around 0.65% across sampled plots, declining to around 0.45% in the 10 to 30cm layer and below 0.30% in the 30 to 50cm layer, consistent with the low organic matter retention characteristic of this soil type.

Soil pH at the surface is moderately acidic to neutral, ranging from around pH 5.6 to 6.9 (CaCl?) across sampled plots in the top 10cm, becoming more acidic with depth and dropping to around pH 4.6 to 6.2 in the 30 to 50cm layer. Colwell phosphorus at the surface was modest across all plots, generally in the range of 12 to 23mg/kg, and Colwell potassium was variable but broadly adequate at the surface. The baseline soil data will serve as the reference point against which any amendment-driven changes in soil chemistry are assessed in subsequent seasons.

Soil biological sampling was also conducted prior to seeding using the SARDI Predicta B platform, providing a pre-treatment picture of the nematode and soil pathogen community across the site. Results showed no detectable cereal cyst nematode or root lesion nematodes (Pratylenchus thornei and P. quasitereoides) across any of the sampled plots. Low levels of a third root lesion nematode species, P. neglectus, were detected in some control and compost treatment plots, though counts were very low and unlikely to be of agronomic significance at this stage. The Predicta B baseline will allow any treatment effects on the soil biological community to be tracked as the trial develops.

Crop establishment

Plant establishment counts were conducted across all 40 plots on 8 June 2026, approximately four weeks after seeding. Mean plant density by treatment is summarised below.

TreatmentMean plants/m²
1. Untreated control134
2. Spading only147
3. Spading + compost159
4. Spading + clay134
5. Spading + compost + clay151

All treatments recorded mean establishment well above the DPIRD-recommended optimum range of 40 to 45 plants/m² for narrow-leafed lupin in Western Australia, above which there is generally no yield penalty and which provides good competitive suppression of weeds. The high establishment across all treatments reflects good seedbed conditions at the time of sowing and provides a clean agronomic starting point for assessing treatment effects through the season. Some variability in establishment was noted within the clay treatment plots, consistent with the peaked spread distribution described above.

Figure 4. Jurien lupin growth at the Regans Ford site

At the time of writing, early biomass sampling and plant tissue testing were yet to be completed.

What the trial is testing

The question at Regans Ford is whether the amendment combinations that performed well at Wathingarra translate to yield and soil improvements under a different set of conditions: a new deep sand soil type, a different location and in 2026 a lupin crop rather than wheat.

The spading only treatment gives the clearest early read on what mechanical amelioration alone contributes on this soil, establishing the baseline improvement from soil disturbance before any amendment contribution is considered. The compost and clay treatments then sit on top of that, with the stacked treatment asking whether combining both amendments with spading produces an outcome that neither delivers on its own.

Lupins bring a further dimension. As a legume, the crop contributes nitrogen fixation back to the system. The 2027 season, when fertiliser treatment splits are overlaid on the existing amendment plots, will allow the trial to examine whether amended soils respond differently to fertiliser inputs, which is relevant to how growers would manage nutrition in crops following amelioration investment.

As with the Wathingarra site, the economics will be worked through at the end of the season using a partial budget that sets the cost of each amendment treatment against any measured yield benefit, giving growers a basis for assessing the investment case on comparable sandy country in the district.

What comes next

First flower biomass and tissue sampling will be completed in July and August, with results reported through WMG’s enewsletter and website shortly after. A crop walk at the site is planned as part of the CSBP & WMG Agronomy Event on the 4th of August. Peak biomass sampling is planned for September to October, with harvest yield data collected at the end of the season. Post-harvest soil sampling and the partial budget analysis will follow in early 2027.

Growers with questions about the trial or about soil amendment options on sandy soils in the Dandaragan district are welcome to contact Chanel Duggan at projects@wmgroup.org.au.

This research is supported by the Soil CRC through funding from the Australian Government’s Future Drought Fund. The project is led by Murdoch University in partnership with WMG. WMG thanks Mark Drake and Lawson Grains for hosting the trial and for their support of the project.

Composted chicken manure on cover cropped perennial pastures: WMG’s first Sandy Soils demonstration site

By Simon Kruger and Chanel Duggan, WMG

During the knowledge gathering phase of the Sustainable Solutions for Sandy Soils project earlier this year, growers and advisers across the region repeatedly raised organic amendments, composted manures among them, as an option they were interested in but had little local evidence for. WMG’s first demonstration site for the project is now in the ground at Gillingarra, looking at how a composted chicken manure application performs in an established perennial pasture on sandy country.

The site

The site is at Pine Break paddock, Gillingarra, hosted by Murray Grey and Colin Crane. It sits on light sandy soils with some small pockets of gravel, typical of the country across much of WMG’s project area. The paddock carries an established perennial pasture of Rhodes grass, Megamax panic and buffel grass, sown in August 2025. Prior to that it carried only volunteer annuals, and the paddock has no history of soil amelioration or fertiliser application in recent years.

Composted chicken manure was applied to approximately half the paddock in April 2026, with the other half left unamended as a control. A cover crop was sown across the full paddock on 23 May 2026, comprising wheat (50kg/ha), lupins (40kg/ha), triticale (20kg/ha), serradella pod (10kg/ha) and a clover mix of rose and arrowleaf (1.5kg/ha), sown with Seed Enhance (Fertitech) at 500ml/ha.

The demonstration design
Figure 1. Pine Break paddock trial measurement zones

The site is structured as a split paddock demonstration, with the 56ha paddock divided into two treatment zones of approximately 28ha each. Both zones have been divided into four monitoring quadrants of approximately 7ha, giving eight sampling zones in total. Sampling from all eight, rather than from a single location in each half, allows within-treatment variability to be observed and gives a more spatially representative picture of the paddock.

The design is unreplicated, reflecting the demonstration intent of the site and the practical constraints of a working farm. A single site over a single season gives a local indication rather than a result that transfers directly to other paddocks, and the data will be reported with that in mind.

The amendment

Composted chicken manure was applied to the amended half of the paddock at 38t/ha in April 2026. The material was sourced from a local chicken farm and composted in situ for approximately 12 months prior to spreading.

A sample of the composted material was submitted to APAL for full nutrient analysis, including trace elements. The headline macronutrients on an as received basis are set out below. Moisture content of the material at analysis was 16%, and the carbon to nitrogen ratio was 7.9 on an as received basis.

NutrientContent (% w/w, as received)
Total nitrogen (N)3.56
Phosphorus (P)1.22
Potassium (K)3.40
Sulphur (S)0.64
Calcium (Ca)1.68
What is being measured

Monitoring across the site runs from establishment through to the end of the 2026 growing season. The program is designed to capture the production picture across both treatment zones through the year rather than at a single point in time.

A pre-treatment groundcover baseline was completed across the paddock in March 2026 using SLATS satellite groundcover measurement, prior to manure application. That gives a starting reference point against which in-season and end-of-season cover can be compared, with a second measurement planned for August 2026.

Dry matter cuts will be taken from each of the eight monitoring quadrants at three points through the season: early season in July, peak biomass in September, and post-graze in November. Cuts are taken to ground level and weighed fresh, with a subsample dried to calculate dry matter percentage and results reported as kg DM/ha.

At the peak biomass cut in September, pasture samples from each treatment zone will be submitted to Eurofins APAL for feed quality analysis covering crude protein, metabolisable energy and fibre fractions. Where practicable, perennial and cover crop species will be sampled separately.

Soil sampling across all eight quadrants was carried out by DPIRD on 16 June 2026, assessing pH, nutrition profile and soil compaction to 30 cm depth. That data provides the soil constraint baseline for the site. Visual observations of crop and pasture health, weed presence and groundcover condition will be recorded at each site visit, with photos taken throughout.

Figure 2. Early observations suggest a slight visual difference between treated and untreated sides of the paddock
What comes next

Results from the July dry matter cut and the August groundcover measurement will be reported through WMG’s enewsletter and website as they become available. The full dataset, including all three dry matter cuts, the feed test and the groundcover monitoring, will be available in early 2027, alongside an assessment of the economics of the amendment.

Pine Break paddock is the first of WMG’s demonstration sites for the Sustainable Solutions for Sandy Soils project. Further sites across the WMG project area will be established and reported on as the project develops through 2026 and beyond.

Growers interested in finding out more about the project, or in discussing organic amendment options for their own sandy soil paddocks, are welcome to contact WMG at projects@wmgroup.org.au.

This demonstration site is part of the Sustainable Solutions for Sandy Soils project, funded through the Australian Government’s Future Drought Fund Resilient Landscapes Program with co-investment from the Government of Western Australia. The project is led by DPIRD in partnership with WMG, Mingenew-Irwin Group and Edith Cowan University. WMG thanks Colin Crane and Murray Grey for hosting the site and for their involvement in the project.

Wheat after chickpeas: How much nitrogen does the legume break actually deliver?

By Simon Kruger and Chanel Duggan, WMG

The 2025 chickpea crop at Jim Hamilton’s property near Moora came through a difficult season and still recorded near-complete biological nitrogen fixation. The proportion of nitrogen derived from the atmosphere sat at or near 90% across all treatments, with total nitrogen fixed estimated between 59 and 83kg N/ha depending on treatment. The paddock averaged 2.34t/ha across the whole area, following a failed April establishment, a reseed in June and prolonged waterlogging through winter.

Fixation of that order raises a question the chickpea season alone could not answer. How much of that nitrogen becomes available to the following cereal, and what does that mean for the rate a grower applies?

Post-harvest soil sampling in January 2026 gave an early indication. Nitrate-N in the top 10cm of the profile was 10mg/kg, declining to 4 to 5mg/kg below that, with ammonium-N low throughout. Most legume-fixed nitrogen is held in crop residues and root biomass rather than sitting in the soil as mineral nitrogen immediately after harvest. How much of it becomes plant available during the critical growth stages of the following wheat crop is difficult to predict on any given soil type or in any given season.

In 2026 the paddock is in wheat, which gives WMG and Jim the opportunity to track that question directly, under commercial conditions, on the same heavy grey clay that hosted the chickpeas.

Why this paddock

The site is in the same 42ha paddock that carried the 2025 chickpeas, which is intentional. Keeping it in the same location means the nitrogen response data can be read against the 2025 fixation results and the January 2026 soil nitrogen baseline, rather than having to account for a different soil type or management history. The paddock was in wheat in 2023 and 2024, so the legume break is a single season sitting between cereal phases.

Figure 1. The Moora site 2025 Chickpea crop
What the site is testing

Calibre wheat was sown on 15 May 2026 at 90kg/ha. The site is structured as four unreplicated demonstration strips running the full length of the paddock, each approximately 400m long and 36m wide, matching Jim’s seeder and sprayer width. Strips run parallel to the direction of sowing, which keeps the boundaries clean when the GS30 application is made by sprayer.

The four treatments span a range of total seasonal nitrogen rates, from a base only control through to a rate intended to sit above the likely agronomic optimum.

TreatmentTotal seasonal N (kg/ha)At seeding (kg N/ha)GS30 topdress (kg N/ha)
Control32320
Low N603228
Typical N903258
High N1203288

All strips received the same base application of liquid nitrogen down the tube at seeding, delivering 32kg N/ha. This is consistent with Jim’s standard practice on this soil type. The heavy grey clay reduces leaching risk relative to the sandier soils more common across the broader West Midlands region, which makes a larger single application at seeding appropriate. A second application is made by sprayer at approximately GS30, with the rate varied by strip to reach the target total for each treatment. The control strip receives no second application.

The control at 32kg N/ha asks what the paddock can produce on the residual nitrogen from the legume phase alone. The low N strip sits below Jim’s typical seasonal rate and tests whether a reduced application is sufficient when following chickpeas on this soil. The typical N strip reflects Jim’s normal wheat program and provides the commercial reference point. The high N strip is intended to sit above the likely agronomic optimum, giving the site the headroom to show where the response flattens.

Keeping the application timing consistent across all strips, with only the GS30 rate varying, means any differences at harvest can be attributed to nitrogen rate rather than to timing or application method. This is a demonstration on a working commercial farm rather than a replicated small plot experiment, and the results will be read with that in mind. Yield analysis will draw on the middle 12m harvest pass from each strip to reduce edge effects between adjacent treatments, with spatial variability assessed using Jim’s yield map data at harvest.

Season to date

The 2026 season opened below average on rainfall across the Moora district. Total rainfall from January through May reached 92.2mm against a long-term average of 128.1mm for the same period. April was the exception, recording 32.6mm against a long-term average of 23.6mm. May came in at just 17.6mm compared with the historical average of 55.7mm. By 16 June a further 44.8mm had fallen at the nearest DPIRD weather station, bringing the running 2026 total to 137mm.

 JanFebMarAprMayJun (to 16th)
2026022.219.832.617.644.8
LTA (1911–2025)13.616.019.223.655.783.7

Rainfall (mm) at Moora DPIRD weather station. LTA = long-term average.

The dry May was a feature across much of the northern agricultural region and will be a factor in how this season develops at the site.

Crop establishment

Plant establishment counts were conducted across all four treatment strips on 16 June 2026, approximately four weeks after seeding. At the time of counting, all strips had received only the base application at seeding. No GS30 topdress had been applied, so the counts reflect the agronomic starting point from which nitrogen response will be assessed rather than any treatment effect.

Figure 2. Plant establishment counts at the Moora site – June 2026
TreatmentMean plant density (plants/m²)
Control176
Low N185
Typical N161
High N158

Mean plant density ranged from 158 to 185 plants/m² across the four strips, all comfortably above the GRDC-recommended optimum population range of 110 to 150 plants/m² for the yield expectations typical of the Moora district. Establishment was good and reasonably uniform across the paddock. Some within-strip variability was noted, consistent with the clay-dominated soil type and the normal variation in a commercial sowing operation, and that will be taken into account when the yield map data is interpreted at harvest.

What is being measured

The GS30 topdress applications were yet to be made at the time of writing. Biomass sampling and plant tissue testing will follow at GS30, with a second biomass assessment planned for peak biomass in September or October. Harvest yield, protein and screenings data will be collected by Jim at the end of the season, with post-harvest soil nitrogen sampling to follow in January 2027. A gross margin comparison across the four treatments will be worked through at the end of the season, using nitrogen input costs and harvest grain prices.

The site is a single season on one soil type at one location. The heavy grey clay at Jim’s property has different nitrogen dynamics to the pale deep sands and sandy duplexes that dominate much of the West Midlands cropping area, so the results will be most directly relevant to growers farming similar heavy country in the Moora district.

What comes next

Results from the GS30 monitoring will be reported through WMG’s enewsletter and website as the season progresses. The full dataset, including yield, protein, screenings, biomass, tissue tests and post-harvest soil nitrogen, will be available in early 2027 and will be read alongside the 2025 chickpea fixation data to give a two-season picture of the legume nitrogen cycle at this site.

Growers farming heavy country in the Moora district who have chickpeas or other pulse crops in their rotation and want to discuss nitrogen management in the following cereal are welcome to contact WMG at extension@wmgroup.org.au.

This trial is part of the Grain Legumes Project (GGA2110-002SAX), led by the Grower Group Alliance and funded by GRDC. WMG thanks Jim Hamilton for hosting the trial and for his continued involvement across both the 2025 and 2026 seasons.

Helping build extension capacity across grower groups with the Soil CRC

By Simon Kruger, WMG

Between late 2023 and early 2026, WMG led a Soil CRC project on how grower groups build their capacity to design, deliver and evaluate extension work, which is the layer that sits beneath much of the on-farm research that eventually reaches growers. The project was not about a single practice or result. Its purpose was to strengthen how groups assess whether a soil practice is worth the money and to improve the methods behind that assessment.

WMG did not carry this alone. The work brought together four grower groups from across the country, WMG, Corrigin Farm Improvement Group, Riverine Plains and Agricultural Innovation and Research Eyre Peninsula, alongside research partners at three universities.

What the project set out to do

The Soil CRC’s Program 1 produced a body of work on how soil management practices are extended and adopted, including a set of tools for grower groups to use. Having the tools available and having groups use them well are different things. Grower groups run extension under real constraints, tight timelines, limited staff, and project funding that rarely covers the design and evaluation work that makes extension effective. Across the four partner groups, those constraints looked much the same despite very different regions and farming systems.

The project, Soil CRC Project 1.2.008, “Packaging Soil CRC tools to enhance the extension and adoption of improved soil management practices”, set out to close part of that gap. It aimed to package the Program 1 tools into a form groups could pick up and apply, to build the internal capability that lets a group design and evaluate its own extension rather than treating each project as a one-off, and to develop a way of measuring whether that extension delivered value. That last aim became the Benefit-Cost Analysis tool.

None of this was framed as solving extension. The project was upfront that its hardest constraints, project timing, whether the evidence is ready to extend, and resourcing, sit beyond what any tool or toolkit can fix. What it could do was give groups better structure and a shared method to work with, and put the case that extension design deserves to be funded and treated as research in its own right.

A national collaboration

The grower groups supplied the real-world settings the work had to fit, spanning very different regions, soils and farming systems, which kept the tools grounded in how groups actually operate rather than how they might in principle. Through Professor Vaughan Higgins, the University of Tasmania facilitated the early work that established a shared picture across the groups, running focus group interviews with each partner and drawing the findings into a common analysis. That analysis showed the constraints on extension were broadly consistent across the groups despite their very different circumstances.

Associate Professor Hanabeth Luke at Murdoch University contributed expertise in extension tool application and knowledge sharing, drawing on her earlier Soil CRC work including the Knowledge Sharing project, and the University of Newcastle, through Professor Frank Agbola with Dr Mesfin Genie, developed the economic side of the work into the Benefit-Cost Analysis tool. WMG led and coordinated the project while also taking part as one of the four groups, which meant testing the emerging tools on its own extension work as they developed.

What the project produced

Two main outputs came out of the work.

The first is an Extension Toolkit, a set of seven structured tools, each with an onboarding guide and template, that together give a group a complete process for designing, delivering and evaluating its own extension. It steps a group through scoping a project, judging what the evidence can support, identifying what farmers need, building a plain-language account of the risks and rewards of a practice, and planning delivery across the season. One of the tools works as a check on evidence readiness, helping a group decide what can be communicated with confidence and what is not yet ready to put in front of farmers, which several groups found as useful as the material they produced.

The second is the Benefit-Cost Analysis tool. It gives grower groups a way to run their own trial and project data through a consistent economic assessment, estimating whether a practice stacks up on a per-hectare basis and testing how sensitive that result is to changes in prices and costs. It is built as a decision aid rather than a predictor, meant to show under what conditions a practice makes economic sense rather than to forecast a single figure. The tool began as a contracted Excel model and grew into a full online platform, well beyond the original scope, and now includes a feature that drafts an extended written report from the analysis. It is useful in that form and still developing, with Frank and his team continuing to improve it and welcoming feedback from anyone who puts it to use.

Both tools are built for groups and extension providers to use rather than for the individual grower. What reaches a farmer is indirect but real. The BCA tool was made for groups to run their own trial results through, and the value a grower feels is a more consistent, better-founded assessment of what pays, sitting behind the results and advice they see.

Availability and acknowledgements

Both outputs are available to others working in grower groups, extension or industry. The BCA tool is on the University of Newcastle website at www.newcastle.edu.au/soil-crc-bca-tool and can be used now, and the Extension Toolkit will be accessible through the Soil CRC Knowledge Hub shortly. A workshop to demonstrate the BCA tool and support its wider use is planned for later in 2026.

This was a substantial piece of work, and it is a small contribution to a much larger effort to lift how soil research reaches and changes practice on farm. WMG was glad to lead it, and to have the chance to do so through the Soil CRC, whose decision to make extension and adoption a research focus in its own right, through Program 1, is what made the project possible. The work depended on the four grower groups and their university partners, each of whom carried a part of it.

For more information, contact WMG at extension@wmgroup.org.au.

Soil CRC Project 1.2.008 was supported by the Cooperative Research Centre for High Performance Soils (Soil CRC), led by West Midlands Group and delivered in partnership with Corrigin Farm Improvement Group, Riverine Plains, Agricultural Innovation and Research Eyre Peninsula, the University of Tasmania, Murdoch University and the University of Newcastle.

Managing water repellent soils: What three sites showed in 2025

By Simon Kruger & Chanel Duggan, WMG

Soil water repellence is a longstanding problem across the Geraldton and Kwinana West port zones. The region’s sandy soils are low in clay and low in surface area, and waxy compounds from decomposing organic matter build up on the sand particles over time. Water then struggles to move into the soil. The result is patchy emergence, uneven crops, lower yields, and flow-on problems for weed control and fertiliser use.

Amelioration is the main response. Deep tillage that mixes, inverts or delves the soil breaks up the repellent surface layer and lets water back in. On the region’s deep sands, where few rocks get in the way, growers have used these methods for years with consistent yield gains. The harder question, and the one this project is working through, is what happens on the more variable soils, the shallow sands over gravel and the true gravels, where the return on a heavy, upfront investment is far less certain.

In 2025 the project ran across three sites and three soil types. The continuing site at Dandaragan (Site 1) entered its second year of monitoring on shallow sand over gravel. Two new sites were added, sand over gravel and true gravel near Gillingarra (Site 2), and deep sand near Moora (Site 3). All three use unreplicated demonstration strips rather than replicated plots, so the figures here are best read as indicative. First-year differences at the new sites in particular cannot be cleanly separated from where each strip sits in the paddock.

Two patterns recurred across all three sites. Strong biomass early in the season did not always translate into proportional grain, and weed management after amelioration turned out to be the clearest practical lesson of the year.

Dandaragan, shallow sand over gravel (Site 1)

Site 1 carries the longest record of the three. It was ameliorated in 2024 and carried a lupin crop in 2025, giving a second year of data on the same ground under a different crop.

The first thing the second year showed is that the 2024 amelioration held. Surface water repellence was absent in every treated strip when the soil was tested in March 2025, a full season on, while one of the two untreated controls still carried a low repellence reading. Penetrometer readings told a similar story below ground. The leading treatments, the Plozza Plow and the Nufab single pass, kept a workable root zone well past the depth at which the controls became limiting, with the controls reaching the root-limiting threshold by around 100 to 125 mm. The deeper root zone opened up by the 2024 work was still there a year later.

Yield followed the same ranking as the year before. The Plozza Plow returned the highest grain yield on the measured swath at 2.24t/ha, 54% above the average of the two controls, with the Nufab double pass next at 2.06t/ha. This is the second season running that the Plozza has come out on top at this site. It also produced the highest yield and harvest index in the 2024 oat crop, and in both years it did so off modest biomass rather than high early bulk. In 2024 that reflected a dry finish, where strips carrying less biomass into a dry spring converted the moisture on hand more efficiently to grain. Mid-season biomass that year pointed to other treatments, and the dry finish reshaped the order by harvest. A yield result that repeats across two seasons and two crops is far harder to put down to chance or paddock position than a single year would be.

Figure 1. Grain yield by treatment at Site 1, middle harvested swath. The Plozza Plow and Nufab double pass lead the two controls, while the Fanger sits below them.

Not every treatment beat the controls. The Nufab single pass and the Fanger Plow both fell below the control average on yield. The Nufab single pass shows the gap between early growth and final yield most clearly. It produced the highest peak biomass of any strip at Site 1, at 5,240kg/ha, yet its grain yield sat just under the control average. Strong early bulk did not carry through to grain. A high-biomass, low-yield result like this can come from a poor harvest index, late-season moisture stress during grain fill, or variability within the strip, and the 2024 season showed the same disconnect where moisture was tight through the reproductive stages.

Weeds were the other clear result. Weed density was lower in all four ameliorated strips than in the worst of the controls, ranging from 26 to 37 weeds/m² against 122 in Control 1. Ryegrass was the dominant species throughout. Burying or redistributing the surface seed bank through amelioration appears to have set the weed burden back, at least in this first post-amelioration season. The grower also noted that most of the ryegrass counted at sampling was already dead, and that chemical control looked more effective on the ameliorated ground, though that last point is a field observation rather than something the trial measured directly.

Figure 2. Weed counts by treatment at Site 1. All four ameliorated strips sit well below Control 1.

Moora, deep sand (Site 3)

Site 3 gave the clearest first-year response of the three. It is deep grey-yellow sand, uniform and free of the gravel and rock that complicate the other two sites, and it was ameliorated in May 2025 ahead of a wheat crop.

Baseline testing found surface water repellence on this sand, with a moderate reading at the top of the profile. Deep, uniform sand of this kind is the soil growers in the region already have most confidence treating, and the results here fit that longer record.

The below-ground response was marked. The untreated control became limiting to root growth by around 450mm, while every ameliorated strip carried the probe deeper, with the Plozza Plow and Horsch Tiger strips reaching the full 750mm measurement depth. On this clean sand the penetrometer reading is a fairly direct measure of soil strength, without the rock contacts that can throw off readings on gravel, so the depth gain is easier to trust here than at the other sites.

Establishment followed the same pattern. Every ameliorated strip established more plants than the control, and the crop was visibly denser and more even across the ameliorated ground.

Figure 3. The PDS treatment (left of centre) against the untreated control at Site 3, showing denser, more uniform establishment on the ameliorated ground.

Peak biomass was where the response showed most clearly. The Plozza and Horsch strips reached around 10,800 and 10,910kg/ha, both close to 48% above the control. This was the strongest treatment response at this timing anywhere in the trial, and it came in the first year after amelioration. Two features of that response are worth noting. Stacking treatments did not build more crop, with the two single deep treatments, the Plozza and the Horsch, producing more biomass than the Plozza-Delver-Horsch and Plozza-Delver-Spader combinations, not less. And the response arrived late, with no clear difference at GS30 earlier in the season, a reminder that early growth on deep sand can understate what the crop does later.

Figure 4. Peak biomass by treatment at Site 3. The Plozza and Horsch strips sit around 48% above the control.

That biomass lead did not carry through to yield. The Plozza and Horsch strips, close to 48% up on biomass, converted it to a yield gain of only 2 to 3% over the control. The strongest strip yield came instead from the PDH combination at 5.37t/ha, 12% above the control, off a much more modest biomass gain. The rest sat within a few percentage points of each other.

Figure 5. Grain yield by treatment at Site 3. The biomass ranking above does not carry through to yield.

The whole trial sat on a better than average part of the paddock, with every strip, control included, yielding above the paddock average of 4.10t/ha, and a north-south yield gradient ran across the ground as well. In a single unreplicated year those factors cannot be separated cleanly from treatment. What the site shows plainly is the gap itself. On this deep sand, early crop bulk overstated the first-year payoff, and a decision made on biomass alone would have picked the wrong strips. Yield, measured across more than one season, is the figure that matters for the investment, and the full economic analysis planned for the end of the project will rest on it, not on early growth.

Gillingarra, sand over gravel and true gravel (Site 2)

Site 2 was the most difficult ground in the trial, which is what makes it useful. It carries two soil types, sand over gravel and true gravel, and 2025 was the host grower’s first amelioration on this ground, done with his own process. It was also the first outing at this site for the Fanger Plow. The results here are best read as early learning on a new tool and a first attempt on hard ground, not as a verdict on either.

The difficulty was evident from the outset. Large rock sat below the surface across both soil types, and some treatments pulled it up during amelioration, the Fanger most of all. A rock roller was needed to flatten the ground enough to seed. Seeding depth suffered as a result, with some barley plants found still under the surface weeks after sowing, and establishment across the site was uneven.

Water repellence at this site was not straightforward either. Laboratory testing returned no surface repellence, yet in the paddock the grower and the field team saw water still moving only down the previous year’s furrows, with volunteer wheat germinating along those lines while bare ground between them stayed dry. Areas holding stubble supported more even germination. The lab number and the paddock behaviour did not match. This is an observation across the site rather than a measured result, but it points to why paddock-scale assessment matters, and why a single lab test can miss what the soil is doing in the field.

Figure 6. Site 2 before seeding, with the top layer uncovered. Water movement was limited to the previous year’s furrows, visible as the darker lines.

Establishment and biomass showed no clear treatment differences at either sub-site, which is not surprising given the variability. Yield was harder to read still. In the sand sub-site the two untreated control strips yielded 0.89t/ha apart on their own, a wider gap than separated most of the treatments from each other. When two strips that received no amelioration differ by that much, position in the paddock is clearly driving a large part of the result, and treatment effects cannot be pulled out from underneath it in a single year.

The Fanger result is where the weed lesson comes through most plainly. Heavy ryegrass came up in the Fanger strips at both sub-sites. The two implements move soil differently, and it shows in the weed response. The Plozza inverts the profile and buries weed seed, while the Fanger mixes and lifts it, bringing dormant ryegrass seed up into the germination zone where moisture and light favour it. The flush is in part a sign of a soil that has been loosened and made more active by the disturbance, but on the true gravel it came at a cost. The Fanger strip carried the heaviest weed burden at the site and returned the lowest yield of any strip, at 2.09t/ha against 3.35 for the control and 3.17 for the Plozza, close to 40% down. On the same gravel the Plozza held level with the untreated control on both biomass and yield.

Figure 7. Heavy ryegrass in the Fanger strip at Site 2. The implement’s soil mixing action does not distinguish crop germination from weed germination.

Figure 8. Grain yield on the true gravel sub-site at Site 2. The Fanger strip, carrying the heaviest weed burden, sits close to 40% below the control.

None of this is a mark against the tool on its own terms. It is a first year, on the hardest ground in the trial, with a new implement and a grower ameliorating here for the first time. Whether the Fanger gap closes as the site settles will be one of the more useful things a second year tells us.

What the season points to

The clearest practical lesson from 2025 was about weeds. Aggressive soil mixing moves weed seed into the germination zone, and the implements do not tell crop from weed. Where amelioration buried the surface seed bank, as at Sites 1 and 3, weed density fell. Where it brought seed up, as in the Fanger strips at Site 2, ryegrass came away with the crop. Weed control belongs in the amelioration plan from the outset, not as an afterthought once the crop is up, particularly for implements that bring more soil to the surface.

Across the three sites the picture is uneven, which is the honest position after this much data. Site 1 shows a benefit holding into a second year on shallow sand over gravel. Site 3 shows a clear first-year response on deep sand, the soil type growers already treat with most confidence. Site 2 shows how much the outcome depends on the soil, the equipment and the operator’s experience once the ground gets difficult.

These are demonstration strips, not replicated plots, and one season cannot separate a treatment effect from where a strip happens to sit. Site 1 enters its third year in 2026 and the two new sites their second. A response that holds across seasons and crops is far harder to explain away as paddock position than one seen once, and the economic picture will firm up as yield builds across seasons, ahead of the full analysis at the project’s end.

The Soil Water Repellence Project (WMG2404-001SAX) is delivered by West Midlands Group with investment from the Grains Research and Development Corporation.

Clay on sand: How much helps and how much costs you

By Simon Kruger, WMG

Clay is drawing renewed interest as a way to lift the productivity of sandy soils. On deep sands that hold water and nutrients poorly, and that often repel water at the surface, working clay into the profile offers something wetting agents and other seasonal treatments cannot, a change that lasts. The appeal comes with a catch. How much the practice pays depends heavily on how much clay ends up in the soil, and a rate that lifts yield on one paddock can hold it back on another.

Guidance on where that balance sits comes from Soil CRC Project 3.3.003, Organic and clay amendments to improve the productivity of sandy soils, led by Emeritus Professor Richard Bell at Murdoch University. As part of that project, researchers brought together 270 records from clay and organic amendment trials across southern Australia and analysed them for the effect of amendment on yield and soil organic carbon. Western Australia contributed 66 of those records, second only to South Australia, so the findings reflect local conditions rather than a single site or season. Pooling results this way gives up the detail of any one trial in return for the patterns that hold across many soils and seasons.

The productive band

The clearest finding to come out of the analysis is that there is a band of surface clay concentration where sands perform best. Treatments that lifted clay in the amended sand to between 6 and 10 per cent were optimal for crop productivity. That sits comfortably alongside the rules of thumb already in use across the southern cropping regions. Around 3 per cent clay is commonly considered enough to overcome water repellence, 6 per cent is often the target growers work to in Western Australia, and 9 per cent is more typical of South Australian practice. The analysis suggests the WA target sits at the lower edge of the productive band rather than in the middle of it, which leaves some room to move for growers whose goal is production rather than repellence alone.

Figure 1. Surface clay concentration bands in amended sand, showing the band optimal for productivity, the range the evidence does not resolve, and the point at which a yield penalty appears.

Where more clay starts to cost

Where the findings become more useful is at the upper end. Once clay concentration in the amended sand rose above 15 per cent, a yield penalty appeared. More clay did not keep delivering more production, and past a point it started to take yield away. For a practice that is expensive to apply and effectively permanent once the clay is in the profile, that is the more consequential half of the result. Overshooting is not a matter of spending more than you needed to, it is a matter of spending more to end up worse off, with no practical way to reverse the decision.

Yield and carbon do not move together

The picture changes if the goal shifts from yield to soil carbon. The greatest increases in organic carbon occurred when clay concentration went above 15 per cent, the same range where the yield penalty appeared. The analysis also found a relationship between organic carbon and yield, but only within a window: where carbon in the top 10 centimetres sat between 0.75 and 1.5 per cent, more carbon went with higher yields. Below 0.75 per cent there was no relationship at all, and above 1.5 per cent the yield response flattened out. The researchers suggest that where carbon is very low, other factors are probably limiting production or limiting the conversion of organic inputs into stable carbon in the first place. A grower weighing a clay rate against both production and carbon goals is not choosing between two settings on the same dial, and the evidence does not say which way that call should go on any given paddock.

Concentration is not a spread rate

One point of clarification sits underneath all of these figures. They describe the concentration of clay in the amended soil, not the rate of clay spread on the surface. The tonnage required to reach a given concentration varies enormously with the clay source and with the depth it is mixed through. Work in the same project makes the scale of that variation plain: reaching a 3 per cent clay concentration took 18 tonnes per hectare of bentonite but 56 tonnes per hectare of subsoil kaolinite, and reaching 6 per cent took 70 tonnes of bentonite against 224 tonnes of kaolinite. Those figures come from a pot experiment rather than a paddock, so they are not spread rates to work from directly, but the ratio between them is the useful part. A target concentration only becomes a spread rate once the clay content of the source material and the intended incorporation depth are both known, which is a soil test and a calculation rather than a rule of thumb.

No single number decides it

Running through all of this is a caution the researchers state directly. Amendments for sands cannot be chosen on a single soil characteristic. The analysis found that responses differed according to water repellence, water holding capacity, low pH, the rate applied, the incorporation depth chosen, and the depth of sand sitting over clay. Clay concentration is one variable among several, and a rate that suits one paddock’s combination of constraints will not necessarily suit the next. The same work found that seasonal rainfall distribution influenced both organic carbon and biomass production, which puts a limit on how precisely any target can be set in advance.

The other caution concerns time. Organic carbon accumulates well after any productivity gain shows up, so a season or two of yield data will not tell a grower whether the carbon side of the investment has worked. The recommendation from the project is to sample to at least 30 centimetres and to resample over periods of five to 20 years, which is a longer commitment to measurement than most amelioration decisions come with. For growers weighing clay against other options on sand, the figures here are worth treating as a starting point for a conversation with an agronomist about a particular paddock, rather than as a rate to order against.

Tools and guidance for a WA context

The figures from this research describe what happens once clay is in the soil. Turning that into a decision on a particular paddock takes local information about the clay source, the cartage, and the soil being amended.

DPIRD’s EasyClay Calculator, on the WA Soil Knowledge Base, converts between the two figures this article has kept separate. It will calculate the resulting clay percentage from a given application rate, or work backwards to the rate needed to reach a target percentage, using the clay content of the subsoil being spread and the intended mixing depth. A more detailed setting takes on-farm data including bulk density, gravel content and subsoil nutrient levels. The calculator assumes clay is mixed evenly through the profile, which the developers note is often not achieved in the paddock with current machinery, so the result is a starting approximation rather than a prescription. It is described as an initial prototype and is being developed further.

DPIRD’s factsheet Claying to ameliorate soil water repellence covers the question this article does not, which is whether a given clay source is worth using. It advises testing the subsoil before committing, looking for 30 to 50 per cent clay content, aggregates that slake or disperse in water, and acceptable pH, salinity and boron levels. It also addresses cartage distance, which often decides whether the exercise is viable, and notes that claying is best suited to the medium and higher rainfall parts of the WA cropping zone.

For the operational side, Spread, Delve, Spade, Invert (Davenport and Hughes 2011) remains the best practice guide to adding clay to sandy soils and is among the references drawn on by the Soil CRC project. GRDC’s GroundCover has also reported on WA work combining clay spreading with strategic tillage, including the finding that clay applied without adequate shallow incorporation can hard-set the topsoil and reduce early establishment.

Further reading

The full research reports from this project are available on the Soil CRC Knowledge Hub, under New amendments for sandy soils. The clay concentration and organic carbon findings discussed here are set out in detail in the meta-analysis milestone report (Schapel and Bell 2021). A fact sheet covering the project’s findings and a recorded webinar on sandy soils are also available.

Acknowledgement

This article was produced as part of Soil CRC Project 1.4.007, Accelerated Adoption Program, which supports farming systems groups to extend completed Soil CRC research to growers. The underpinning research is from Soil CRC Project 3.3.003, Organic and clay amendments to improve the productivity of sandy soils. This research was funded by the CRC for High Performance Soils (Soil CRC), an Australian Government Cooperative Research Centre bringing together researchers, industry and farmers to develop practical solutions for Australia’s soils. This article further supports the West Midlands Group’s work in the Sustainable Solutions for Sandy Soils Project, jointly funded through the Australian Government’s Future Drought Fund Resilient Landscapes Program and the Government of Western Australia, led by the Department of Primary Industries and Regional Development, supported by the Mingenew Irwin Group and Edith Cowan University.

Source: Bell, R.W., Yeap, S., Schapel, A. and Robinson, N. (2025). Sandy soils: Organic and clay amendments to improve the productivity of sandy soils. Final report for research project 3.3.003. CRC for High Performance Soils, Callaghan, NSW.

Nitrogen, rainfall and the season still to come: Putting some data behind the top-up decision

By Simon Kruger, WMG

Nitrogen is one of the harder inputs to get right, because much of the decision has to be made before the season shows what it will do. Growers with later applications still to come face that squarely by mid-July. Should they stick to the plan, add more, or pull back? If the season is running well, the extra nitrogen may pay. If it’s not, it may be money spent on a crop that can’t use it. This in-season call is harder to bring evidence to than the autumn budget, because it depends on how the rest of the season plays out, and nobody yet knows that. Nothing removes the uncertainty, but some tools can help put a shape around it.

One of the tools that can be of use with this decision point is the Rainfall to Date tool from the Department of Primary Industries and Regional Development (DPIRD). It’s free, WA-based, and shows where a season sits now against the historical record, then sketches what a poor, average or good finish might look like from here. WMG’s interest is in putting it in front of growers and thinking through what it might offer the top-up decision.

Where three stations sit as of mid-July

The Rainfall to Date tool draws on DPIRD’s network of weather stations across the state. It plots cumulative growing-season rainfall for a chosen station against that station’s own record from 1975 onward. The three solid green lines are the historical decile 1, 5 and 9 tracks. Decile 5 is the median, the line half of all years on record fell below and half above. Decile 1 is the level only the driest 10% of years fell below, and decile 9 the level only the wettest 10% exceeded. The purple line is the rainfall received so far this season. From the current date, three lighter blue lines project what a decile 1, decile 5 and decile 9 finish would look like from here. The historical tracks are in green, the projections from today in blue.

Figure 1. Example of how to interpret Rainfall to Date Graph

Run for three DPIRD stations across the region on 14 July 2026, the tool shows a season tracking below to around average across the board.

Figure 2. Badgingarra, Rainfall to Date, 14 July 2026

Figure 3. Moora, Rainfall to Date, 14 July 2026

Figure 4. Dandaragan West, Rainfall to Date, 14 July 2026

Badgingarra had received 199.8mm of growing-season rainfall, sitting on decile 5, the median, with a summer at decile 4 behind it.

Moora had received 136.3mm, sitting at decile 4 and the lowest of the three in absolute terms, on a summer at decile 4.

Dandaragan West had received the most rain of the three at 209.1mm, yet sits at decile 4, just below Badgingarra despite the higher total, on a summer at decile 4.

The three stations tell a reasonably consistent story this year. The season is running a little below to around its long-term middle by mid-July. Dandaragan West is the one worth pausing on. It had received more rain than Badgingarra, 209.1mm against 199.8mm, yet sits a decile lower. The decile is measured against each station’s own record rather than an absolute total, so the same amount of rain can read differently from one location to the next depending on what that station usually receives.

There is still a question worth sitting with, even in a year where the three stations sit close together. The tool compares each season against the record of the station nearest to it, which may be a more useful reference than a district average or a general sense of how the year is going. Which station sits closest to a grower’s own property, and how well its rainfall reflects what has fallen on the paddock, are the grower’s own to judge.

Reading the finish from here

The three blue projection lines are where the tool earns its place in a nitrogen conversation. Each extends the season forward from today’s rainfall to a historical finish. The bottom line runs to a decile 1 finish, the middle to a decile 5 finish, the top to a decile 9 finish. Between them they set out a question a grower is already weighing. If the rest of the season comes in poor, average or good, where does the year end up?

Reading the projected finishes off the three graphs, rounded to the nearest sensible figure, gives a feel for the range at each station by early November.

Badgingarra, sitting at 199.8mm now, projects to somewhere around 300mm on a poor finish, about 450mm on an average one, and close to 585mm if the rest of the season is wet.

Moora, the driest of the three at 136.3mm, projects to around 215mm on a poor finish, roughly 300 to 330mm on an average one, and about 360mm on a good one.

Dandaragan West, at 209.1mm now, projects to around 380mm on a poor finish, roughly 460mm on an average one, and around 520mm on a good one.

Two things in those ranges are worth considering.

The gap between a poor and a good finish at each station is wide. At Badgingarra it is most of 300mm, at Dandaragan West around 140mm, at Moora around 150mm. Even at the station sitting on the median, the finish is a long way from decided. Most of the season, on these numbers, is still to come.

The second is that all three stations are starting from a similar place, a little below to around their long-term middle. None of them has banked the kind of wet start that would take the pressure off a nitrogen decision, and none is so dry that the season is already lost. That leaves each of them with a genuinely open range, where a poor finish and a good one are both still in reach.

From a rainfall range to a nitrogen question

The step from a rainfall finish to a nitrogen rate is not a clean one, and it is worth being upfront about why. Rainfall is one input into yield, not the whole of it. Stored soil moisture at the break, soil type and water holding capacity, nitrogen already in the profile, and the timing of the rain through the season all sit between a millimetre total and a tonne of grain. The tool measures rainfall and nothing else. It can’t tell a grower their yield potential, and it certainly can’t tell them a rate.

What it can do is give some shape to the range a crop might be growing into, which is the thing the top-up decision is really about. A later nitrogen application assumes the crop will have the yield potential to use it. The wider and lower that range looks, the more that assumption is exposed. The narrower and higher it looks, the safer it becomes.

Set against the three stations, the picture this year is more consistent than it sometimes is. None of the three has the kind of wet profile that would make a later application look low risk, and none is so far behind that the case for holding back is clear cut. Each sit in the middle ground where the decision is genuinely open.

Moora is the driest of the three, and the one where the downside case is closest to hand. A decile 1 finish from 136.3mm would leave the season well short, and that is the situation where extra nitrogen is most at risk of going onto a crop that cannot convert it. A grower on that country might reasonably want to see more of the season before committing, and to look hard at stored moisture and crop condition rather than rainfall alone.

Badgingarra and Dandaragan West sit a little more comfortably, closer to their long-term middle, but not by enough to change the shape of the decision much. The range of finishes at both is wide enough that a later application could pay in a good year or be stranded in a poor one. The rain each has received matters less than the rain still to come, which no one can yet see.

None of that is a recommendation. It is the same tool read across three stations that happen to be telling a similar story this season, showing a decision that is open at all three rather than settled at any.

The trade-off both ways

The reason this decision is hard isn’t just the uncertainty. It’s that the two directions don’t cost the same, and they don’t cost the same in every season.

Underdo the nitrogen on a season that turns out well, and the cost is forgone yield. The crop had the potential to do more, and the nitrogen was not there to let it. That is a real cost, but an opportunity one. The grain could have been grown and was not.

Overdo the nitrogen on a season that turns out poorly, and the cost is different. It’s money spent on a product the crop couldn’t use, and in a dry finish it can be worse than neutral. A crop pushed with nitrogen into a dry spring can run its water down faster and hay off harder than it otherwise would. So, the downside is the input cost, plus in some cases a yield penalty on top.

Those two costs are not symmetric, and which one a grower is more exposed to shifts with the season and with the numbers in front of them. Two things this year press on that balance.

The first is the price of nitrogen. Urea prices spiked sharply earlier in 2026 on the back of global supply disruption, as WMG covered in the May newsletter. Prices have eased from that high since, though the volatility has not gone away, and the direction from here is unsettled. That instability is itself part of the decision. A later application is being weighed against an input cost that may have moved since the autumn budget, in either direction, so the price at the time of the call is worth checking rather than assumed. A higher price raises what is at stake in getting the decision wrong, both the cost of nitrogen that a poor season strands and the value of yield that a good season leaves unfilled. It sharpens the decision rather than settling it, which is the same reason it is worth bringing information to, not just a feel for whether fertiliser seems dear this year.

The second is where a station sits. This year the three stations point much the same way, all tracking a little below to around their long-term middle, so the reading is fairly consistent across the region rather than pulling growers in different directions. Moora, the driest, is where the downside case is closest, since a poor finish from an already low position is the scenario where nitrogen is most likely to be stranded. Badgingarra and Dandaragan West sit a little higher but not far enough to change the picture. In a year like this one, the tool is less about separating one station’s prospects from another and more about showing that none of them has yet had the season it would need to make a later application look comfortable.

That is the whole of what the tool offers this decision. Not an answer, but a clearer view of which way a grower is exposed. Where a season sits locally, and what nitrogen costs at the time of the call, both change the balance of what is at stake without deciding it. The point of setting them out is not to land on hold or push, but to see the exposure clearly enough that the decision is made on information rather than instinct. Even the clearest reading is something to weigh against the crop, the stored moisture and the paddock plan, not a rule to follow.

The limits of the tool

The tool is built to be read with its limits in mind, and DPIRD is clear about them. Rainfall to date is a useful narrative for how a season is tracking, but it isn’t the same as yield potential, and the tool doesn’t claim to be.

The things sitting between rainfall and yield have already been noted: stored moisture, soil type and water holding capacity, nitrogen in the profile, the timing of the rain. A few of them bear especially on how the tool should be read. Summer rainfall gives only a partial signal of stored soil moisture at the break. Non-wetting, waterlogging and leaching on lighter country each separate the rain that falls from the yield it produces, in ways rainfall alone will not show. A high rainfall position is not the same as a high yield, and the tool doesn’t suggest otherwise.

The projections carry their own caveat too. The decile 1, 5 and 9 finishes are drawn from the historical record for each station, not from a forecast. They describe how seasons have finished from a similar mid-July position in the past. They are not a prediction of how this one will, and a season can still do something the record has not seen.

None of that makes the tool less useful for the top-up decision. It sets what the tool is for. It puts a defensible range around a season that is still open, so a grower is weighing a real spread of outcomes rather than a single guess. The narrowing of that range, from rainfall to stored moisture to what the crop is actually showing in the paddock, is work the grower and their agronomist do from here.

What the tool is for

The Rainfall to Date tool will not make the nitrogen call for anyone, and it’s not meant to. What it offers is a way to slow the top-up decision down and put some data behind it. Where does the season sit against the local record, how wide is the range of finishes still open, and which way is a particular paddock exposed if the season runs poor or finishes well.

That distinction, between a good decision and a good outcome, sits at the centre of what RiskWi$e is about. Whether a nitrogen call turns out right is usually only known after harvest, and it depends heavily on how the season finishes, which no one controls in July. What a grower does control is how the decision is made. A call reached by slowing down, looking at where the season sits, and weighing the exposure both ways is a better decision than one made on a feeling about the year, even if the season later turns and the numbers don’t come off. The aim isn’t to be proven right by the outcome – it’s to be able to say the decision was a sound one, based on what could be known at the time.

The tool is free and takes a few minutes to run for the station nearest a grower’s farm. It’s available through the DPIRD website at https://www.dpird.wa.gov.au/online-tools/rain-and-irrigation-calculators/rainfall-to-date-tool/. For growers wanting to think through nitrogen decisions on their own paddocks, talk over how the season is shaping in the West Midlands or learn how they can be involved in RiskWi$e, please get in contact with the team at WMG.

This article was produced through WMG’s involvement in the RiskWi$e National Risk Management Initiative, led nationally by CSIRO and by GGA in WA and funded by the Grains Research and Development Corporation. The Rainfall to Date tool is developed and maintained by DPIRD.

Rethinking when you service the seeder: a whole-farm efficiency question

By Chanel Duggan, WMG Project Officer

Seeder maintenance is a standard part of every broadacre operation. The timing of it, however, is rarely questioned. For most businesses, the seeder gets serviced in late summer or early autumn, shortly before it is needed. That is how it has always been done, and in many cases it works fine.

But as farms scale up and seeding windows tighten, the pre-season period is carrying more and more competing demands. Workshop time, labour, parts sourcing and machinery readiness all converge in the same few weeks. For some businesses, that concentration of pressure is worth examining.

One question worth considering is whether completing major seeder maintenance immediately after seeding, rather than immediately before it, might suit some operations better.

The case for post-seeding maintenance

The logic is straightforward. Pack the seeder away in June or July with the season still fresh in everyone’s mind, fix what needs fixing, and park it ready to go. By the time February arrives, the pre-season workload is already one task lighter.

Judeen Farm near Warradarge is one example of an operation that has moved in this direction, with post-seeding maintenance allowing fault identification while wear patterns are still visible and operators can clearly recall what gave them grief during the run. Rather than relying on memory months later, issues can be assessed and acted on while machine performance is still recent.

There are broader efficiency arguments too. Moving major seeder servicing into winter may spread workshop workload more evenly across the year, reduce congestion in the already busy pre-seeding period, and make better use of staff during quieter operational phases. Machinery can be parked fully serviced and genuinely ready, rather than arriving at seeding with maintenance still in progress or recently rushed.

Trade-offs worth considering

This approach is not without its own complications, and whether it suits a given business depends on several factors.

Storage is the most obvious one. A fully serviced seeder sitting unused for eight to ten months needs appropriate undercover protection, and some operations may not have the shed space to accommodate that. A pre-season check before the machinery goes back to work is also worthwhile regardless of when the major service was done.

Winter labour is not always available. June and July compete with spraying, fertiliser applications, livestock operations and other servicing programs depending on the enterprise mix. For some businesses, the pre-seeding window is actually quieter and therefore a better fit for workshop time than the middle of winter.

Cashflow timing is worth considering too. Bringing maintenance expenditure forward by several months may not suit every business’s financial position or preferred payment timing.

A systems question more than a machinery question

The practical value of reconsidering maintenance timing is not really about the seeder itself. It is about how that timing decision sits within the broader operation.

If moving maintenance to winter reduces pre-seeding bottlenecks, improves machine reliability, smooths labour demand across the year, and increases readiness for a compressed sowing window, then the benefit extends well beyond the workshop. For businesses where the pre-seeding period is already stretched, that is worth examining carefully.

A few questions worth sitting with: Are machinery issues from the current season being forgotten by the time servicing comes around? Is pre-seeding workshop pressure creating bottlenecks that flow into the sowing program? Does winter genuinely offer better labour availability in your business? Is your machinery storage set up for long-term readiness? And if the break of season arrives in a narrow May window, will your seeder be ready to go when it does?

There is no universally correct answer on timing. What suits one business may not suit another, and the decision depends on labour availability, storage capacity, enterprise mix and how the pre-seeding period sits within the broader operation. For businesses where pre-seeding pressure is a recurring challenge, it may be worth reviewing whether maintenance timing is contributing to that and whether shifting the schedule would help.

Further information and resources
GRDC Machinery Investment Guide: grdc.com.au/resources-and-publications/resources/machinery-investment-guide
Kondinin Group machinery research and benchmarking: farmingahead.com.au

Visit the WMG RiskWi$e project page for more articles on how growers across the region are approaching machinery and operational decisions.

Sandy soils, groundcover and what growers are actually doing: inside the Sustainable Solutions for Sandy Soils project

By Simon Kruger, WMG Project Communications Officer

Across the West Midlands region, pale deep sands and sandy duplex soils are among the most challenging country to manage. Shorter seasons, more variable breaks and declining rainfall reliability have made it harder to maintain groundcover, leaving exposed soils more vulnerable to wind erosion, moisture loss and declining productivity. Around 21% of farmland in the region lacks adequate groundcover during the periods of highest erosion risk, a figure substantially higher than comparable regions in the broader WA grainbelt.

The Sustainable Solutions for Sandy Soils project, is a five-year initiative running from 2025 to 2030 aimed at helping growers manage these risks in a practical way. The project is led by Department of Primary Industries and Regional Development (DPIRD) in partnership with WMG, the Mingenew-Irwin Group (MIG) and Edith Cowan University (ECU), and is funded through the Australian Government’s Future Drought Fund Resilient Landscapes Program with co-investment from the Government of Western Australia. The project area extends from Gingin in the south to Geraldton in the north.

Rather than promoting a single solution, the project is designed to look at how combinations of proven practices can be integrated into real farming systems on sandy soils, under local conditions and with the seasonal variability that growers in this region know well.

What the knowledge-gathering phase found

In early 2026, WMG, MIG and DPIRD conducted structured interviews and conversations with producers and advisers across the project area, covering localities from Regans Ford and Dandaragan in the south through to the Mingenew-Irwin district in the north. The interviews covered current practices, attitudes to groundcover, barriers to adoption and emerging approaches.

All interviews were conducted on the basis of anonymity. The findings below reflect the collective picture across the interview group rather than any individual producer or adviser.

How growers are thinking about groundcover

Across all enterprise types, producers described groundcover as a practical management priority with direct consequences for productivity, carrying capacity and long-term soil condition. The language used was consistently economic rather than environmental: cover protects soil, retains moisture, supports crop establishment and underpins livestock carrying capacity.

Adviser observations suggested that producer attitudes have shifted over time. Producers are now less tolerant of low cover than they used to be, a change attributed partly to a run of difficult seasons that made the consequences of poor management more visible and more costly. The 2021 season, which combined a false autumn break, the aftermath of Cyclone Seroja and a grasshopper plague, was raised in virtually every interview as a reference point for how quickly groundcover can deteriorate under compounding pressures.

What is working

Producers across the project area described a wide range of practices in use for maintaining or improving groundcover on sandy soils. No single approach dominated. In most cases, growers were managing cover through a combination of practices rather than relying on any one strategy.

In livestock and mixed systems, planned rotational grazing with defined rest periods and disciplined destocking windows were consistently identified as the foundational practices. Confinement feeding during high-risk periods was identified by advisers as a practice that had produced measurable improvements for clients.

In cropping systems, reducing stubble burning frequency was consistently identified as one of the most accessible and impactful changes available. Multiple producers described a target of no more than one burn per paddock per three-year rotation, though they were clear that this involved genuine trade-offs with weed management and pre-emergent herbicide performance.

Soil amelioration, including clay spreading, delving, mouldboard ploughing and deep ripping, was the dominant practice category across cropping and mixed enterprise interviews. Clay spreading at high rates was identified as the highest-impact available practice on pale deep sands. Identifying a suitable clay source and understanding what application rate is needed for a meaningful and durable improvement were consistently cited as practical challenges where producers wanted better guidance calibrated to local soil types.

Emerging approaches worth watching

Virtual fencing using GPS livestock collars attracted the strongest interest of any emerging practice across the interview group. The appeal is practical: excluding stock from the most vulnerable sandy areas within a paddock without the cost of permanent infrastructure, and adjusting exclusion zones as conditions change through the season. Two producers in the project area were already using the technology with cattle at meaningful scale.

Deep incorporation of clay through delving at depth was described as producing more durable profile improvements than surface application alone. One documented case involved a profile of 80 centimetres of sand over clay transformed through deep spading, producing what was described as above-average cropping country from previously marginal sandy ground.

Perennial C4 grass systems are well established on a number of properties in the northern portions of the project area and were consistently described as strong contributors to year-round cover. Reliable establishment on pale deep sands remained an unresolved challenge, with the fertiliser history of the soil identified as a potentially important factor.

What the barriers are

Cost was the most frequently cited barrier, particularly for soil amelioration. The difficulty of justifying capital investment with long payback periods within normal farm business planning timeframes was a recurring theme.

Technical uncertainty was a significant barrier in several practice areas. Uncertainty about clay assessment and application rates, unresolved questions about perennial species selection for local conditions, and the lack of practical guidance on post-fire erosion management on sandy soils were all identified as specific information gaps.

Social and behavioural barriers were described by advisers as at least as important as economic and technical ones. Producers most likely to have persistent groundcover problems were also described as least likely to attend group extension events, requiring fundamentally different engagement approaches. One-on-one contact framed around seeking producer input, very local peer role models, and well-designed demonstration sites with visible control strips were identified as the approaches most likely to reach this group.

What’s coming through the project

The SSS project is currently in its early stages. Demonstration sites and peer learning groups are being established across the project area, with trials and monitoring activities running through to 2029. WMG’s involvement covers the southern portion of the project area, broadly south of Eneabba, including localities around Dandaragan, Regans Ford, Yathroo, Badgingarra and Moora.

As demonstration sites are established and monitoring data becomes available, WMG will share findings through the enewsletter and website. For more information about the project or to find out how to get involved, contact Gabby Carrivick at eo@wmgroup.org.au or visit dpird.wa.gov.au.