• Treatments were a single application of 10 kg/ha of Zn as zinc sulfate monohydrate (ZSM) (35% Zn) in 1996 or 4 applications of 1.25kg/ha or 2.5 kg/ha Zn as Incitec.
• Granulock ST-Z (10 %N, 19.5 % P, 2.5% Zn) between 1996 and 1999. Soil samples were collected at the commencement of the experiment, after the first application and post-harvest from the fourth crop.
• Samples were analysed for DTPA extractable Zn.
• The percentage of soil extractable Zn available from applied Zn after 4 cereal crops was about 12 % for the single application of 10 kg/ha Zn as ZSM, 22% for multiple applications of 1.25 kg/ha Zn and 20 % for 2.5 kg/ha Zn as STZ.
• It would appear that provided there is no compromise in crop productivity, a multiple low rate strategy of Zn fertiliser addition may be more effective in building available soil Zn concentration than a single higher rate.

Magenta yeilded higher than Mace in Both seeding systems.

• Single row yielded higher than twin row at Binnu, also looked much healthier (better) through-out the season. This has not been a consistent observation in other research trials. Likely cause is poor P nutrition due to fertiliser placemnt in twin row and low P site.
• Increasing seeding rates reduced the yield potential of Magenta. In contrast, plant desities of 150 plants/m2 were the most productive for Mace.

Average yields ranged from 2.1 to 2.5t/ha.

Soil amendments applied in 2004 did not significantly improve wheat yields in 2005.

The high fertiliser regime yielded significantly higher than the district practice regime and the low fertiliser regime.

No significant result and more testing required.

• Western Flat (Ramseys) soil modification work. Site was established in 2009. After 2 seasons, the area that organic matter was spaded into is performing well.
• Wolseley (Matthews’); alternative fertiliser demonstration; no differences were found between soil biology after a 12 month period.
• Lochaber Ag Bureau (Clothiers); Peries Wightman subsoil manuring project
• Dairy sites with Dairy SA based around the Mt Gambier region
• Coonalpyn Ag Bureau Soil pit days
• Coonawarra Grape Growers – historical composting trial sites revisited
• Sherwood – soil modifications in conjunction with additional carbon project

• Soil and solution culture studies were conducted to examine the relative contribution of different mechanisms of zinc efficiency at the whole plant level in bread and durum wheat during early vegetative stage.
• While there are a number of mechanisms of zinc efficiency, zinc uptake appears to be the most important mechanism • Seed zinc remobilisation and root to shoot translocation do not appear to be important to zinc efficiency.
• Visual scores of zinc deficiency were significantly correlated with zinc efficiency, and they provide a useful criterion for an initial screen of zinc efficiency.
• This study was based on vegetative growth and the conclusions need to be verified under field conditions.
• The percentage deviation technique provided a straight forward means of comparing the relative effects of different components of zinc efficiency and the method could be extended to studies that use grain yield as the measure of zinc efficiency.

Early application of selective herbicide (Group 1, A) gave excellent control of barley grass. While fewer barley grass plants meant less pasture biomass, it’s important to remember that the seeds on the mature barley grass would injure livestock. Further, these barley grass plants could host cereal crop disease.

Spray topping prevented viable seed set of barley grass while leaving the greatest pasture biomass.

Good barley grass control in the 2019 pasture was still evident in the 2020 and 2021 crops.

Late sowing of barley in 2020 (delayed 4 weeks) was relatively ineffective in controlling barley grass and crop yield was slightly reduced.

Late sowing of oats in 2021 (delayed 7 weeks) gave excellent weed control, but the crop yield was severely reduced.

This work has demonstrated that N2O emissions from trafficked soil were consistently and significantly greater (by an average factor of 2.2) than those from non-trafficked soil. At the same time, soil CH4 consumption was significantly increased in the CTF beds compared to random-trafficked or permanent traffic lanes, although overall CH4 fluxes were small. Permanent traffic lanes normally represent only 10%–15% of field area on controlled traffic farms, compared with ∼50% or more trafficked area on non-controlled traffic farms. Thus, the results indicate that adoption of controlled traffic should reduce soil emissions of C2O-e by 30%–50%, and this effect would be greater if N fertiliser could be excluded from permanent traffic lanes.  The reduction in emissions also indicates that less N has been lost by denitrification, an effect which might be in the range of 3 – 20 kg/ha.

The work has demonstrated that CTF will reduce the GHG emissions from grain production, in addition to providing economic and other environmental benefits.
 

• Main areas at risk from Inglewood and Yelbaron in the south to Tara and Condamine in the north.
• Occurs on grey or grey brown clays or sandy clays which carried belah and brigalow in their native state.
• Variance in triticale varieties in responsiveness to copper sulphate.
• When copper fertiliser was placed in dry soil it was unable to be taken up by plants and grain yield, but not straw production, was severely compromised.

The program demonstrated that:
• At some sites where copper deficiency was historically assumed, no response to any form of copper application was observed. Copper response is likely to vary by site and season.
• Yield loss caused by copper deficiency can be devastating to wheat yield.
• Soil and tissue testing can be useful in helping to detect low levels, but are not always definitive. Copper response appears to be dependent on other complex interactions such as soil moisture, yield potential and other constraints (N fertility etc.) and thus soil/tissue tests alone are not a definitive guide to future responses.
• Foliar applications performed better than in-furrow liquids.
• Chelate and sulphate products performed equally well when applied as foliar applications.
• Timing did not appear to be critical, with a wide band of opportunity from mid-tiller to early head emergence providing similar results

Soil DTPA was 0.27 mg/kg soil.

Grain yield increase by 32 % for both granular and fluid applied Cu.  About 1.3 kg Cu /ha was required for maximum grain yield of 3.2 t/ha.

Foliar application reached 85% of the maximum yield when applied at flag leaf before flowering; earlier application at first node was effective but only reached about 75% of the maximum.  

At this site seed coating had a small effect on germination of seedlings and was insufficient Cu for wheat seedling to recover from Cu deficiency.

Flag leaf Cu concentrations were 1.3 mg Cu/kg and grain Cu concentration from nil Cu treatments were 1.3  mg/kg

Soil DTPA was 0.32 mg/kg soil.

Grain yield increased by 2 % for both granular and fluid applied Cu.  About 1.5 kg Cu /ha was required for maximum grain yield of 3.32 t/ha.

Foliar application reached 97% of the maximum grain yield when applied at flag leaf before flowering; earlier application at first node was effective but only reached about 95% of the maximum.  GY

At this site seed coating had no effect on germination of seedlings..

Flag leaf Cu concentrations were 1.5 mg Cu/kg and grain Cu concentration from nil Cu treatments were 1.4  mg/kg

• The addition of copper and zinc fertiliser applied Cu was applied in 1959.

• Barley responded to Cu; applied as Cu ore @ 35 kg/ha.

• ZnO at 3.3 kg/ha depressed yield without Cu for both levels of N, applied as ammonium sulphate

• Cu increased yield by about 30% with nil ammonium sulphate applied.

• Application of Ammonioum sulphate appeared to decrease the respponse to Cu.

• The addition of copper and zinc fertiliser applied Cu was applied in 1957.

• Oats responded to Cu

• Area very Cu deficient as responses in grain yield to Cu in oats are not frequently obtained

• Cu additions in aabsence of Zn induced more sebere Zn deficierncy in oats.

• However, yields showed no Cu x Zn interaction.

• The addition of copper and zinc fertiliser applied Cu was applied in 1953.

• !953 experiment a Cu & Zn experiment on oats.

• In 1959 Cu and Zn reapllied on half plots.

• Zn applied in 1953 had the same grain yield as  Cu & Zn applied in 1959

• Residual value of previous applied Cu & Zn were  good

• No further response  of oats to second addition of Cu and or Zn after 6 years.

• The addition of copper and zinc fertiliser applied Cu was applied in 1957.

• Zn applied in 1957 reduced grain yield where Nil Cu.

• Zn oxide was not reduced until 4 kg/ha was applied

• Cu  applied in 1959  did not increased grain yield of wheat. 

• Residual value of previous applied Cu & Zn were  good

• Copper was applied as Cu ore equivalent to about 5 kg Cu sul/ha.

• No further response  addition of Cu and or Zn.

• The addition of copper and zinc fertiliser applied in 1955.

• Cu  applied in 1959  did not increased grain yield of wheat. 

• Copper was applied as Cu ore equivalent to about 5 kg Cu sul/ha.

• No further response ti addition of Cu and or Zn.

• The addition of copper and zinc fertiliser applied in 1955.

• Cu  applied in 1959  did not increased grain yield of wheat. 

• Copper was applied as Cu ore equivalent to about 5 kg Cu sul/ha.

• No further response ti addition of Cu and or Zn.

• The addition of copper and zinc fertiliser applied in 1952.

• Cu  applied in 1959 increased grain yield of wheat. 

• Copper was applied as Cu ore equivalent to about 5 kg Cu sul/ha.

• THe response of wheat  to Cu in 1959 was not annticipated .

• As there was very large responses to Cu in 1959, doubts arose as to whether Cu was originally applied. However, clover grew well in 1952 suggestion Cu had been applied, along with the plain supper Zinc 

• Conclusion a second application of Cu is required to the soil type.

• The addition of copper and zinc fertiliser applied in 1953 was adequate in 1959. 

• Copper was applied as Cu ore

• Further additions in combination or alone had no further effect on grain yileld 

• 6 years of clover ley; Addition N as ammonia sulphate (112 kg/ha) increased grain yield by 300 kg/ha; profitable application

• Nitrogen did not induce Cu & Zn deficiency.

• The addition of copper and zinc fertiliser applied in 1953.

• Cu  applied in 1959  did not increased grain yield of wheat. 

• Copper was applied as Cu ore equivalent to about 5 kg Cu sul/ha.

• No further response ti addition of Cu and or Zn.

• The addition of copper and zinc fertiliser applied Cu was applied in 1957.

• Cu ore, Cu sulfate and zinc chloride source used.

• In 1957 Zn chloride reduced yields. There were no reduction in yield in 1959

• Zn applied in 1957 reduced grain yield where Nil Cu.

• Cu  applied in 1959  did not increased grain yield of wheat. 

• Residual value of previous applied Cu & Zn were  good

• Copper was applied as Cu ore equivalent to about 5 kg Cu sul/ha. There was no difference between Cu ore and bluestone [Cu sulfate] compared at the same rate of Cu applioed.

• No further response  addition of Cu and or Zn.

• The addition of copper and zinc fertiliser applied in 1953 was adequate in 1959. 

• Copper was applied as Cu ore

• Further additions in combination or alone had no further effect on grain yileld 

• 6 years of clover ley; Addition N as ammonia sulphate (112 kg/ha) reduced seedling stands & reduced grain yield.

• Anticipated a response to Cu

• The addition of copper and zinc fertiliser applied Cu was applied in 1953.

• !953 experiment a Cu & Zn experiment on wheat.

• Zn reduced yield in 1953 when applied without Cu 

• Cu & Zn applied in 1953 had the same grain yield as  Cu & Zn applied in 1959

• Residual value of previous applied Cu & Zn were  good

• No further response  of wheat to second addition of Cu and or Zn after 6 years.

• The addition of copper and zinc fertiliser applied in 1956.

• Cu  applied in 1959  did not increased grain yield of wheat. 

• Copper was applied as Cu ore equivalent to about 5 kg Cu sul/ha.

• No further response ti addition of Cu and or Zn.

• The addition of copper and zinc fertiliser applied in 1954 was adequate in 1959. 

• Copper was applied as Cu ore

• Further additions in combination or alone had no further effect on grain yileld 

• 5 years of clover ley; Addition N as ammonia sulphate (112 kg/ha) no effect on  grain yield by 300 kg/ha; profitable application.

• In poorer seasons there is no positive economic reward for high nitrogen fertiliser inputs.
• Oats and vetch for either grazing or hay consistently provided positive gross margins.
• Wheat crops which followed a chemical fallow provided the best gross margin in both trials.
• Aim to maximise profits, not necessarily yields.

• Wheat sown after break crops produced up to 1 t/ha more than wheat after wheat
• The greatest benefit of the break crop was produced at the earliest sowing
• Safflower produced the break crop effect but produced low wheat yields, small grain but high protein due to drying out the soil profile.

• Time of Sowing; get it right after the break crop.
• Effects of the break crops are often realised for at least 2 seasons after being planted.
• Beans consistently fixed the most nitrogen over the 3 year period; averaging 15Kg N/ha per tonne of dry matter produced (above the ground).
• Financial benefit of a break crop needs to be worked out over life of rotation.

• The no-till sowing system had significantly higher grain yields at Hart in 2011.
• Higher fertiliser nutrition significantly increased protein, but not grain yield.
• The strategic treatment produced the most dry matter and shoot nitrogen.
• Mice damage significantly reduced crop emergence in the disc treatment.

• There was no significant difference between sowing systems or level of nutrition on grain yield but higher grain yield at the higher nitrogen rate.
• Levels of brome grass were higher under the early sowing no-till plots and annual ryegrass was lower in the disc system.

• There was no significant difference between sowing systems or level of nutrition on grain yield.
• Levels of brome grass were higher under the early sowing no-till plots and annual ryegrass was lower in the disc system.
• There is very little difference in long term gross margin between seeding system or level of nutrition.

• The disc and the early sown no-till tillage systems produced the highest grain yields, 1.41t/ha and 1.36t/ha respectively.
• The early sown no-till system had the lowest protein and the highest screenings.
• The disc tillage treatment had the least available soil nitrogen in autumn.

• All the legumes sown - peas, lupins, sub clover and faba beans - were equal in terms of their nitrogen-fixing capabilities, reflecting the importance of having well nodulated legumes.
• The average amount of N fixed by the legumes was calculated at approx. 86kg/ha.
• In year 2, this residual N gave rise to a approx. 1 t/ha canola yield advantage.
• In yera 3, no differences in residual nitrogen from legumes were measured.
• Linseed extracted more moisture, from a greater depth, than the faba beans in the same year and all subsequent crops - canola and oats.
• The linseed was able to dry the soil profile in a decile 10 year (812mm rainfall). This is a potential solution for farmers wanting to dry out their soil profile.
• Two years after growing linseed, soil moisture levels were even.

Based on this trial it appears CG could be used as a substitute for DAP fertiliser in cereal production however blending with urea to ensure adequate N would be essential. 

• There was no statistically significatn difference between the control and the CFF treated plots.
• The dry conditions experienced in 2007 impacted on this demonstration which indicated a need for further reserach into the effectiveness of this product in a more favourable season.

There are no significant differences in yields between the control and the CFF plots on a wodjil soil type.

Key findings:

• Nitrogen (N) decision making requires a good understanding of background soil and plant science, and soil test interpretation.
• Training for new agronomists needs to be a priority issue.
• Senior NSW agronomists identified crop yield expectation as guided by soil moisture at sowing (or at the time of N decision making) as the most important determinant of N fertiliser requirement.
• Further research is needed to increase the understanding of how management practices affect potentially large gaseous N losses. 
• Changing from legume pasture-crop sequences to continuous cropping in many central and southern areas of New South Wales is posing new questions for managing N supply. The absence of N-fixation by pasture legumes is seen as a substantial loss of N-buffering capacity.
• Despite most advisers choosing soil testing as a key approach for determining N fertiliser required, many of their clients had a lower confidence in soil testing, citing ‘high perceived variability in soil nitrate results in the lead up to sowing’.
• Conclusions and Recommendations Senior advisers highlighted the importance of quality training in N decision-making, understanding the background soil and plant science involved, and soil test interpretation for the next generation of agronomists, with training courses including representation from highly experienced local agronomists.
• The understanding of gaseous N losses requires further research, development and extension to the grains industry. Recent field research in the north was limited in scope and produced challenging outcomes that can potentially lead to large practice changes in when and how N fertiliser is applied. Further research and development work is warranted to answer more of the practical questions growers and advisers are asking in regards to losses associated with various alternative practices.

• The northern results on N loss pathways are less relevant to advisers in the central and southern regions where N application timing, soil type and climatic differences are generally quite different from the dominant medium-heavy clays of the north. New N loss research is recommended for the lighter textured soils in regards to the potential for N volatilization losses from surface N application of various products. Economic outcomes from the various strategies being practiced are also needed. Nitrogen loss research should focus less on expensive slow-release products and more on optimising results from urea, the cheapest N source.

• Research into better soil water measurement was seen as a priority area, especially given the importance all advisers place on knowing this when making expensive N-fertiliser decisions for a coming cropping season. Zonal management within paddocks is not possible with single site characterisations, so atypical areas of paddocks are over or under-fertilised.

• The very early application of N fertiliser ahead of a winter cropping season is well established, but what is not known is how well the subsoil N may be protected or at risk from denitrification in flooding events. Also, better knowledge on specific N use within the profile during the cropping season will help growers to know when late-applied N is likely to be inaccessible to crop use.

• Nitrogen mineralisation was highlighted by agronomists from all three regions as an area for greater understanding with regards to the differences caused by climatic conditions, especially rainfall. They also require better understanding of the N produced from both native organic matter and recent legume pasture residues.

• There are a number of good decision support tools available currently, with several advisers suggesting that combining the best points of each into one package, even one available as an app, would be highly useful, particularly one with good grower-friendly reports.

• Many farmers have low confidence in soil testing.  This may be related to a range of factors from poor sampling strategies, to poor sample handling, to poor service from laboratory analysts, to insufficient sample numbers or poor interpretation of the results. It is seen as an expensive option for many, with some advisers looking for quicker and cheaper means of estimating soil mineral N.

• Variety-specific N management packages were seen by some senior advisers as key areas for continued research funding, as results from some new varieties have been quite different in terms of N uptake and protein outcomes.

• Making nitrogen (N) management decisions requires an understanding of soil and plant science, and soil test interpretation.
• Training new agronomists is a priority.
• Senior NSW agronomists identified crop yield expectation as guided by soil moisture at sowing (or at the time of N decision making) as the most important determinant of N fertiliser requirement.
• Further research will increase the understanding of how management practices affect potentially large gaseous N losses.
• Changing from legume pasture-crop sequences to continuous cropping in many central and southern areas of New South Wales is posing new questions for managing N supply. Less frequent pasture legume phases with their N-fixation benefits to the soil is seen as a substantial loss of N-buffering capacity.
• Despite most advisers choosing soil testing as a key approach for determining N fertiliser required, many of their clients had a lower confidence in soil testing, citing ‘high perceived variability in soil nitrate results in the lead up to sowing’.

• Deep ripping enabled the crop to access about an extra 40kg of soil N/ha.
• The crop was as responsive to Flexi-N after deep ripping.
• There was no yield penalty from delaying Flexi-N application until the end of tillering. Deep ripping and Flexi-N were very profitable at this site.  

Sub-soil compaction, caused primarily by the unmanaged movement of heavy machinery, is having a negative effect on grain yield and quality across the Geraldton Port Zone (as well other port zones in WA).  Compaction limits plant root growth, reduces plant available water capacity (PAWC) and in turn limits yield potential.

The profitability of a crop is dependent on the crop maximising the use of rainfall received and the PAWC of the soil is critical to this. This applies to all rainfall zones. Climate change however, has influenced the number of dry periods occurring during the growing season, so it’s more important than ever for crop roots to be able to explore the soil profile to the fullest possible extent.

Growers report that some soils on their property continue to underperform despite their fertiliser and system management strategy matching their soil type. The introduction of deeper deep-rippers to the region (550 – 700mm) has shown encouraging results, prompting growers to question current strategies and investigate the rippers as options for soil improvement.

In 2016 four growers within a 100km of each other currently employing deeper ripping strategies were asked to compare the performance of ‘deeper’ deep ripping (550-700mm) to standard deep ripping (250 – 350mm) and no ripping.  A full soil, plant tissue and grain yield analysis was performed at each site to gather information on the base site parameters and breakdown of how each soil responded to the treatments.

There was an increasing response to deeper ripping associated with a decline in rainfall at the sites (about 100mm variance across sites). To achieve the best return on investment growers are recommended to identify the sub soil constraints in their paddock before choosing the right tillage machine to alleviate them.

• Ripping below the hard pan (greater than 500mm) in pale sands, yellow sands and yellow loams in wheat or canola increases yield.
• Soil moisture probes show ripping deeper (below 500mm) allows more plant roots to access moisture deeper in the profile for longer in the season. Water infiltration also increase with depth of ripping.
• Leaving a firm even seed bed after deeper ripping is important to reduce seeding establishment issues.
• A negative yield response to deeper ripping in lupins on yellow sand was measured at Binnu in 2016.
• Crop yield response to ripping does vary depending on seasonal conditions and crop type therefore the economics of ripping must be considered over multiple seasons and timing of ripping in the rotation.

• Deep ripping to 500-600mm in coarse textured sandy soils increased yield by 21-66% compared to 6-24% with ripping to 300mm in wheat and canola in 2016 and 2017 in the Geraldton port zone.
• There was only a small yield response to ripping the red loam in 2016 and no difference in 2017.
• Soil moisture measurements and visual observations of plant root growth indicated deeper ripping allowed the plant roots to access more water from deeper down the soil profile. This is particularly beneficial in sandy soils that have a low plant available water capacity(PAWC) per 10cm down the profile therefore roots need access deeper into the soil profile to gain the same amount of water as heavier textured soils that have a higher PAWC per 10cm.
• Economic analysis found the higher cost of deeper ripping gave a positive return on investment up to $5/ha for every dollar invested at 3 sandy sites but not on the red loam where the return on investment was negative with a return of $0.63/Ha for every dollar invested. On the sand at Ogilvie there was a yield penalty in lupins in 2016, resulting in a negative return on investment which could not be recouped in the following dry season of 2017.
• If ripping below 400mm, consideration must be given to crop selection in year one (lupins are higher risk); leaving an even seed bed post ripping to reduce bogging and plant establishment issues; and managing weeds as due to poor competition and better access to water and nutrients can increase the weed burden as these factors can have a negative impact on yield reducing the return on investment.

Soils in the Wharminda and Stokes area of Eyre Peninsula were mapped and areas of micronutrient deficiency established by applying micronutrients (copper, zinc, manganese, iron, boron and molybdenum) in 24 factorial field experiments.

Fertiliser applications were made at the 1-2 leaf , tillering and booting stages.

• Grain yields were increased by copper application at 11 of the 24 sites.
• Zinc application increased yield at one site, manganese at one, iron at two and molybdenum at two sites, no increased due to boron application were recorded.
• Copper deficiency occurred in deep siliceous sands, calcareous sands, solodized solonetz and solodic soils with light brown sand at Wharminda.
• Zinc and manganese deficiencies were mostly confined to soils with a high carbonate content near the surface.
• Copper in the grain was a better indicator of deficiency than copper in the soil.
• Grain yield responses to copper application were indicated by grain copper of <2.5 ppm.

At Minnipa in 2013 there were cereal yield responses to fungicide treatments in both wheat (up to 14% better than no fungicide) and barley (up to 12 % better than no fungicide but not all strategies were effective). However there were still visual Rhizoctonia patches present. In-furrow fungicide applications were more effective than seed treatments. Tillage, starter nitrogen and zinc produced similar yields to many of the fungicide treatments. A three week delay in seeding reduced yield by nearly one third. Fungicide treatments did not prevent an increase in Rhizoctonia inoculum levels during a cereal phase.

• Three direct drill seeders were compared (Gason, Jenke, Daybreak) to sow wheat into a canola stubble.
• The season was very dry (decile 2) with an average wheat yield of 1.4t/ha in the demonstration.
• There were no differences in crop yield between the three seeders.

While incidence of root rot was high (83-95%), the disease severity was low on the trial site ranging from 14.3 to 19.5% for treatment averages; many plants had a low level of root disease. Distinct patches were not evident in the trial.

Despite low levels of disease severity observed in the trial and only minor treatment effects on root rot, two in-furrow treatments were found to significantly improve the yield by more than 0.24 t/ha compared to the Untreated control. These were the granular fertiliser treated with Uniform® and the split application of Uniform® above and below the furrow.

In a site with a moderate rhizoctonia disease risk, as indicated by PreDicta B, the majority of plants had root rot however severity was low and patch development did not occur. Under low disease pressure, the Uniform treatments as a whole were able to provide a small reduction in disease incidence which subsequently resulted in yield increase from two treatments. Under higher disease pressure these products can be included as part of an integrated management approach for rhizoctonia.

Nitrifying archaea and bacteria live at different soil depths, with nitrifying bacteria inhabiting the surface soil and nitrifying archaeal populations inhabiting the sub-soil (10-90 cm). Nitrifying bacteria are the most numerous overall when compared to the nitrifying archaea, and their decline in abundance with soil depth matches the decline in soil nitrification rates. In these soils, nitrification rates are low, suggesting the amount of NH4+ is low, leaving little available for nitrification. Understanding the ecology of these microbes and their role in soil nitrification rates, may lead to improved management strategies to decrease N losses from the soil and improve N use efficiency. 

• Zinc deficiency caused production losses in cereals of up to 25% and in medic of up to 300% in biomass.
• Critical level for zinc deficiency in wheat was established as 18 mg/kg in YEBs at late tillering.
• Zinc deficiency in crops can be corrected with foliar sprays, zinc coated fertilisers or zinc applied to the soil and thoroughly incorporated by tillage. Fertilisers which are a mix of NP granules and zinc granules are poorly effective.
• Zinc applied to the soil will provide residual benefits for 3-10 years, the longer persistence in sandier mallee soils.
• 70% of cereal crops in the SA mallee were zinc deficient in the early 1990s.
• An application of 2 kg zinc/ha to the soil (as an incorporated soil spray or zinc coated fertiliser) will correct zinc deficiency in broadacre crops and pastures.

• There were adequate levels of nitrogen in the soil profile which limited response to any applied fertiliser.
• There were significant yield increases from enhanced efficiency products such as Entec at sowing.

• The application of 40kg/ha at sowing resulted in significant yield responses from all products over the control where only starter fertiliser was applied.
• Fertilisers banded at sowing generally resulted in higher yields and grain N recovery than top dress applications, while the inverse was true for grain protein levels.
• Low grain protein levels (<10.5%) for all treatments and application timings generally indiates that yield was not optimised due to the limited nitrogen supply.
• There were no significant responses found from the use of inhibitors in this trial.

• There were good dry matter responses to starter fertilisers at either 16 or 32 kg/ha of P although only certain treatments gave a significant dry matter inrease when raising P rate from 16 to 32 kg/ha. The best dry matter response was from Gree Top which supplied all the nutrients lacking in the soil test report.
• Potassium seed burn was not apparent possibly due to the relatively wet conditions.
• Both DAP and Gree Top grew over 70 kg DM/ha/kg P at the lower rate of 80 kg/ha, which supplied 16 kg/ha of P.
• Only Green Top, Croplift and Superfect+Mo increased yields with increasing rate of application indicating they supplied the lacking nutrient required to make use of the extra P available.

• There were adequate levels of phosphorus in the soil profile, but we still saw a response to phosphorus fertiliser.
• There were some differences within different products at the 12 kg P rate - with sulfur enhances products delivering a better outcome.
• Other additive to phosphorus fertilisers delivered no additional benefits.

• Both the grazed disc and grazed tyne treatments yield the same.
• In contrast to one of the initial years where the tyne treatments saw greater Patterson’s Curse density, there have not been any further or continual patterns of weeds within the site.
• Disc seeder saw limitations in ungrazed stubble, when stubble lodged along with soft wet soil. Solutions will include reducing stubble harvest height, to lower risk of post-harvest lodging, however even spread across header width will be essential.
• Addition of “residue managers” to brush material aside from path of disc openers would reduce level of poor establishment and ensure discs continue to roll and cut.
• Poor establishment means that it is behind on tiller density and ultimately head density. This is the basis of building yield potential and water use efficiency. Focus on maximum and consistent establishment to efficiently use nutrient and moisture resources.
• Tyne seeder is more “forgiving” in troublesome conditions, as there are fewer variables to manage.
• To date, total yields are virtually level, signifying there is no silver bullet to seeding machine or stubble management.
• To manage the variables which pose risk to any such system will be the key to limit downfalls (as seen this year with the ungrazed disc) and maximise profitability. This is the silver bullet!

Fertiliser decisions are economic decisions based on the relative prices of fertiliser and grain – at higher grain prices, investments even in higher cost fertilisers can still be attractive. Do your sums and calculate the best option.

• Zinc is an essential nutrient to crops on alkaline soils in hte Mallee and Wimmera zinc deficiencies are common.
• The regular (once every three to four years) use of a fertiliser with a zinc additive overcomes most of these dificiencies.
• Some crops such as faba beans may require more zinc.

Growers should continue to be encouraged to employ land management practises that increase SOC in Western Australia’s cropping soils. Increasing soil C benefits crop production, and has the potential to decrease N and other fertiliser needs. Although increasing SOC increased soil N2O emissions (and inhibited CH4 uptake) in the present study, these losses were relatively low.

The greatest risk of N2O emissions from a sandy soil in the Western Australian grain belt occurred in response to summer-autumn rainfall events, and more so with increasing SOC. This observation is consistent with previous observations for semi-arid soils where a large proportion of annual N2O emissions occurred between crop growing seasons, when the soil was fallow, and in response to soil wetting following summer and autumn rainfall. Approaches to decreasing N2O emissions following summer rainfall events is limited to decreasing N2O emissions from nitrification (e.g., liming, nitrification), and increasing soil N immobilisation and plant N update during summer and autumn.

Nitrogen supply (via mineralisation) prior to seeding varied depending on soil type and summer rainfall, and needs to be included when determining annual N fertiliser requirements. Optimising N fertiliser input will increase farm profitability and decrease the risk of N2O emissions arising from under-utilised N fertiliser.

The proportion of N fertiliser applied that was lost as N2O from a sandy soil in the Western Australian grain belt ranged from 0.08 to 0.12%. This finding, plus past research in the Western Australian grain belt, supports further lowering current Australia’s emission factor (0.3%) for calculating N2O emissions from the application of N fertiliser to non-irrigated, cropped soils in Australia’s semi-arid regions.

• Canola yield was increased and oil % marginally decreased with increasing N rate applied.
• The highest yield (4.2 t/ha) was achieved at the highest N rate (160 kgN/ha).
• With adequate starting soil N (67 kgN/ha) and good spring rain, N application timing made little difference.
• 30% N fertiliser recovery in grain remains a good ‘rule of thumb’ for canola N budgeting.
• Easy N® application shows promise for topping up N at early flower.
   

• Changing the pre-plant N fertiliser from the non-irrigated side of the plant bed to the irrigated side of the plant bed did not affect soil mineral nitrogen (N), plant growth or cotton lint yield.
• The pattern of nitrous oxide (N2O) emissions after the first irrigation event differed according to N fertiliser placement treatment, but the total amount of N2O released was the same.
• Pre-plant N fertiliser placement did affect N2O emitted after the second irrigation (with water-run N), with more lost from the irrigated, non-fertilised side of the hill.
• The cumulative N2O losses summed over all the measurement events showed no treatment differences resulting from pre-plant N fertiliser location, indicating that there is no agronomic or environmental benefit to changing N fertiliser location.
   

• Changing the pre-plant nitrogen (N) fertiliser location from beside the non-irrigated furrow to beside the irrigated furrow increased nitrous oxide (N2O) emissions, primarily from the fertiliser band location.
• Irrigating every single furrow instead of every second furrow did not significantly change N2O emissions.
• Altering irrigation furrows in relation to pre-plant N fertiliser did not significantly affect mineral N in the surface soil, nor did it affect any measure of crop production.
• These results do not support changing from the current irrigation and N fertiliser placement system in use.
   

• The results of this demonstration indicate that by reducing fertiliser granule size, while maintaining the amount of fertiliser applied, can be beneficial to crop yield.
• It is assumed that this benefit is derived from better spatial arrangement of the fertiliser allowing crop roots better access to the nutrients.
• Crops with fibrous root systems (cereals and pulses) are better able to exploit this than those with tap roots (canola).

• The results of this demonstration indicate that by reducing fertiliser granule size, while maintaining the amount of fertiliser applied, can be beneficial to crop yield.
• It is assumed that this benefit is derived from better spatial arrangement of the fertiliser allowing crop roots better access to the nutrients.
• Crops with fibrous root systems (cereals and pulses) are better able to exploit this than those with tap roots (canola).

• The results of this demonstration indicate that by reducing fertiliser granule size, while maintaining the amount of fertiliser applied, can be beneficial to crop yield.
• It is assumed that this benefit is derived from better spatial arrangement of the fertiliser allowing crop roots better access to the nutrients.
• Crops with fibrous root systems (cereals and pulses) are better able to exploit this than those with tap roots (canola).

• Nitrous oxide (N2O) emissions at the Gunnedah site were approximately three times higher than at the Emerald site, probably because of the heavier clay soil at Gunnedah.
• High and highly variable N2O emissions occurred at both sites during the week following the first irrigation event after the pre-planting nitrogen (N) application. There was no significant effect from the amount of N applied at pre-planting on these first emissions, nor overall at Gunnedah. At Emerald, overall N2O losses were greater from the split N treatment.
• N2O emissions were low–negligible following the subsequent 4–5 irrigation events, except where N was water-run, which caused small and temporary increases in N2O.
• The greatest N2O emission came from the soil above the pre-plant N fertiliser bands. More was emitted from the non-irrigated side of the plant bed, even when both sides of the bed had been fertilised (Emerald).
• Cotton lint yield was not affected by N timing treatment, however, plant biomass was smaller and more N-concentrated from the split N treatment at Gunnedah.
• The 2015–16 weather conditions did not favour either N-timing treatment agronomically or environmentally, but different rainfall patterns in other years may be more influential.
   

• Stubble height did not affect fallow efficiency at Weethallee following the 2013 or 2014 harvests.
• Stubble height during the 2014 fallow did not impact on 2015 crop yields.
• Leaving higher stubbles may reduce harvest cost but may also cause issues during fallow sprays and sowing. Individual producers need to target a stubble height that best suits their equipment and techniquies.

• Simulated dry sowing was not shown to have any detrimental effect on Zn fertiliser use efficiency.

• Commercial granular and liquid monoammonium phosphate fertilizers enriched with zinc were incubated under dry and wet conditions to test the effects of dry sowing on fertilizer diffusion, lability, and subsequent availability to wheat (Tritium aestivum L. ‘Axe’) plants in the growth chamber using isotopic techniques.
• Fertilizer incubated in dry soil tended to have a much greater lability than in wet soil, but diffusion was limited.
• The restricted diffusion during the incubation did not negatively impact nutrient availability to plants subsequently grown in the growth chamber, however, and simulated dry sowing was not shown to have a detrimental effect on fertilizer efficiency.

Grain protein, but not grain yield was significantly affected by the type of pasture legume previously grown.

The annual medics were the most persistent species after cropping. 

The findings will be used to prioritise further research and development of novel pasture species on sandy soils.

Volga vetch produced the most biomass in the establishment year at both sites. 

• Neither previous chickpea sowing rate or pre-sowing stubble management had any significant effect on the following durum wheat yields or grain protein.
• Calculated stubble residues showed no difference as a result of variable chickpea seeding rates.
• NDVI measurements demonstrated that there was little influence on canopy development from either previous seeding rate or pre-sowing preparation.
• Durum wheat has a considerable requirement for N to achieve DR1 quality and so the contribution from the chickpea stubble is a relatively small part of the total N budget.
• Water use efficiency was 17.8 kg/mm.

• Following the wet winter soil N cores in late August revealed only 47kg N/ha in the 90cm profile with approximately 30kg N/ha in the top 30cm.
• As a result, all N fertilised plots were significantly higher yielding than the unfertilised control which yielded 4.87t/ha at 10.3% protein with a total N offtake of 138kg N/ha at harvest.
• The indication from the unfertilised plots were that the soil mineralised an additional 80kg N/ha on top of the 46kg N/ha available in the soil in late August.
• In N fertilised plots there were no significant differences in yield between 100 – 350kg N/ha applied with a yield range covered by 0.34t/ha.
• In contrast, grain protein levels continued to increase as the applied N fertiliser increased with over 13% achieved with 200kg N/ha, 150 N applied producing 12.5% protein.
• The highest grain proteins were achieved with 350 kg N/ha applied at 16.3%.
• N offtakes in the crop at harvest ranged from 137 – 300 kg N/ha but there was no significant difference in N offtake between 150-300kg N/ha fertiliser N applied with a range of 263 – 307kg N/ha.
• Applied fertiliser N had no significant impact on harvest index or dry matter and averaged only 35%.
• Durum grew similar amounts of dry matter at harvest compared to 2020, approximately 16-17t/ha but in 2021 harvest index was 35% as opposed to 43% and yields were peaked at 6.74t/ha compared 7.43t/ha in 2020.
• At high levels of applied N fertiliser (300, 350kg N/ha) there was no benefit to splitting the N three times, however at lower N fertiliser inputs (see Trial 4 – N timing) this is not the case.

• A grain yield of 8.98 t/ha was achieved with an application of 250 kg/ha of nitrogen (N).
• There was no significant difference in yield for nitrogen applications ranging from 250 – 350 kg N/ha.

• Applying 200 kg/ha of nitrogen was enough to raise the grain protein above the 10.5% required to achieve APW1 compared to the lower N application rates that only achieved ASW1.
• An additional 50 kg N/ha (250 total) pushed the protein above 11.5% and achieved a bin grade of H2, the highest quality achieved in this trial.
• The highest gross margin was achieved with 250 kg N/ha applied as urea 46% N.
• There was little difference in final harvest biomass between 100 and 350 kg N/ha applied with a range of 16.7 – 19.0 t/ha. When no nitrogen was applied final biomass was significantly lower at 14.2 t/ha and a grain yield of 6.55t/ha.

• With 47kg N/ha available in the soil profile (0-90cm) in early spring there was no effect of N timing (50:50 split applications) on grain yield.
• At the different N timings grain yield increased significantly up to a N rate of 200kg N/ha.
• Grain protein in contrast was significantly increased by N rates up to 300kg N/ha and applying N at a later timing split (GS32 and GS39) also significantly increased protein compared to earlier timings
• Later N timings under irrigation are more efficient with applied N, since N removed in the grain was greater with later timings in comparison to earlier timings.
• Grain yields were optimised with DR1 protein levels (13% or higher) at N rates of 100 to 200kg N/ha.
• In 2020 with much higher soil N reserves at sowing (232kg N/ha 0-90cm) it was noted that increasing applied nitrogen fertiliser had no negative yield effects when applied later in stem elongation compared to earlier N timings of the same amounts.

• With 66kg N/ha available in the soil profile (0-90cm) pre sowing there was an effect of N timing (50:50 split applications) on grain yield where the earlier (PSPE & GS30) and later (GS32 & GS37) applications were significantly lower yielding than the intermediate application timing (GS30 & GS32).
• Head numbers were also significantly higher with the GS30/32 timing than both the early or late N timings.
• At the different N timings grain yield increased significantly up to an N rate of 200kg N/ha with no additional response at 300kg N/ha.
• There was a significant interaction between N timing and N rate on grain protein.
• With the earlier application timings (GS00 /GS30 & GS30/GS32) grain protein was maximised with 300 kg N/ha while in the late application timing (GS32/GS37) grain protein was maximised at 200 kg N/ha.
• 200kg N/ha applied in a 50:50 split generated the best margin after N cost and quality considerations were taken into account.
• The highest gross margin was achieved with 200 kg N/ha applied as urea (46% N) split at GS30 and GS32.

• Biomass at harvest was no different between the N timing strategies. However, the higher N rates did result in more biomass and higher heads/m2.
• The later the N was applied the greater the N accumulation in the crop canopy at harvest, however this was only apparent at the higher N rates applied (i.e. greater N efficiency of applied N).
• Delayed application of nitrogen did not result in yield reduction, but lower N rates did.
• Grain protein meeting DR1 specification was only achieved by applying 300 kg N/ha at either of the later split N timings either GS30/GS32 or GS32/GS39.
• Harvest index averaged 0.40 and was higher at the lower N rates as was observed in Trial 3.

• Yield was below expectations which appears to be due to inadequate soil moisture in late winter, with irrigation not possible due to the irrigation season being closed.

• Establishment rate for the trial averaged 76% but was lower at the highest populations.
• There were differences in biomass at GS30, with the trend to lower biomass at lower • seeding rates and this was reflected in shoot numbers.
• Yield was not influenced by seeding rate in either variety, although plant populations below 100plants/m2 tended to be the lowest yielding, however there was little or no difference in grain yield between 150 – 240plants/m2.
• Yield was below expectations which appears to be due to inadequate soil moisture in late winter, with irrigation not possible due to the irrigation season being closed.
• Winter drought is a risk that is greater under overhead irrigation as the soil profile is unlikely to be full at the beginning of winter as is the case under flood irrigated circumstances.
• Water use efficiency was 16.1 kg/mm

• Two wheat trials sown during mid-April 2015 showed no difference in grain yield or quality as a result of being grown on 22.5cm, 30cm and 37.5cm row spacings, when averaged across four varieties.
• Although crops grown on a 22.5cm row spacing produced more dry matter (DM), this did not correspond to increased yield.
• The results were identical to that seen with wheat sown in mid-April 2014.
• There were no differences in yields of the four wheat varieties, although Bolac produced higher screenings than the other three varieties in both trials.
• There was no difference in the overall water use efficiency (WUE) between narrow and wide row spacing, although calculated water losses (soil evaporation, drainage or unused water) were greater with wide spacing than the narrow spacing.

• Four wheat trials sown during mid-April 2014 and 2015 showed no difference in grain yield or qualityas a result of being grown on 22.5cm, 30cm and 37.5cm row spacings, when averaged across four varieties (Bolac/Kiora, Lancer, Trojan and EGA Wedgetail).
• The 2016 trial sown during mid-April again showed no difference in yield between 22.5cm and 30cm row spacings, however yields were significantly less with the widest row spacing (37.5cm).
• Trial yields in 2016 were 1.5t/ha higher than 2014 and 2015 (3–4.25t/ha), with the higher yield potential likely to be a key factor in the poor performance of the widest row spacing (37.5cm).
• The Riverine Plains Water Use Efficiency (WUE) project (2009–13) showed that when crops weresown in the traditional sowing window, the 22.5cm spacing was more successful than the 30cm spacing, except in drier years with lower yield potential (2.5–3.0t/ha).
• In the three years (2014–16) of trialling row spacing on early-sown crops, crops grown on a 22.5cm row spacing produced more dry matter (DM) than crops grown on wider rows. However, the 2016 trial was the first to show a yield disadvantage to the widest
row spacing (37.5cm) when sown early.
• As a result of lower yields, the 37.5cm row spacing gave significantly poorer water use efficiency (WUE) than 30cm row spacing, with a greater proportion of calculated water losses (soil evaporation, drainage or unused water).
• A barley row spacing trial, sown at the same time alongside the wheat, provided some usefulcomparative observations during 2016, with La Trobe barley producing higher DM and yields thanwheat with a harvest index (HI) of approximately 50% compared with wheat at 40%.

• Improving water use efficiency across mixed cropping and livestock systems thorughout Eastern South Australia
• Improving whole farm profitability, whole farm sustainability and whole farm ground cover across Eastern South Australia.

1. Differences of $204-670/year were found between systems across sites.
2. Cropping intensity is the major factor driving good/poor economic performance.
3. A system water use efficiency of $2.50 of crop income/mm of rainfall over the cropping sequence is achievable and could be used to benchmark current farming systems.

• Summary of 2 seasons esperiments

• Soil extractable B was 0.4 mg/kg.

• B fertiliser had no effect on September Dry matter (DM) (3.1 t/ha); Seed yield (1.1 t/ha) or N % in DM (3% N) or N in the seed (3.55%).

• B had no effect on %oil (42.8) or on oil yield .

  Notwithstanding the marginal B levels on acid sands of the SWA region, care needs to be taken on use of borax fertilizer as toxicity was induced in canola and lupin; with 0.34 to 1 kg B ha−1(3-10 kg borax ha−1) at sowing depressing seed yield, mostly by decreasing plant density. Rather than making general recommendation for B fertilizer application based on 0.01M CaCl2 soil extractable B, soil and plant analysis should be used to diagnose B deficiency and B fertilizer use limited to calcium borate or foliar borax rather than soil-applied borax on low B sands.

• Boron not required

• Summary 1994 experiments

• Soil extractable B was 0.3 mg/kg.

• B concentration in dry matter (DM) 20 mg/kg

• B fertiliser had no effect on September Dry matter (DM) (2.9 t/ha); Seed yield (1.2 t/ha) or N % in DM (3% N) or N in the seed (3.50%).

• B had no effect on %oil (43.1) or on oil yield (515 kg/ha) .

  Notwithstanding the marginal B levels on acid sands of the SWA region, care needs to be taken on use of borax fertilizer as toxicity was induced in canola and lupin; with 0.34 to 1 kg B ha−1(3-10 kg borax ha−1) at sowing depressing seed yield, mostly by decreasing plant density. Rather than making general recommendation for B fertilizer application based on 0.01M CaCl2 soil extractable B, soil and plant analysis should be used to diagnose B deficiency and B fertilizer use limited to calcium borate or foliar borax rather than soil-applied borax on low B sands.

• Boron not required

• Summary 1994 experiment

• Soil extractable B was 0.7 mg/kg.

• B fertiliser decreased seedling density (71 to 48).

• B concentration in dry matter (DM) 24 mg/kg B nil; 31 mg B kg for highest B application

• B fertiliser decreased the  September Dry matter (DM) by 0.62 t/ha; decreased Seed yield by 0.32 t/ha  &  increased N % in DM (by 0.46%) and  N in the seed (0.33% increase).

• B had decreased %oil (1.2% decrease in Oil%) & decreased oil yield by 142 kg/ha .

  Care needs to be taken on use of borax fertilizer as toxicity was induced in canola and lupin; with 0.34 to 1 kg B ha−1(3-10 kg borax ha−1) at sowing depressing seed yield, mostly by decreasing plant density. Rather than making general recommendation for B fertilizer application based on 0.01M CaCl2 soil extractable B, soil and plant analysis should be used to diagnose B deficiency and B fertilizer use limited to calcium borate or foliar borax rather than soil-applied borax on low B sands.

• Boron not required for the site with 0.7 soil extractable B.

• Summary 1994 experiment

• Soil extractable B was 1..1 mg/kg.

• B concentration in dry matter (DM) 30 mg/kg B nil; 36 mg B kg for highest B application

• B fertiliser decreased the  September Dry matter (DM) by 0.35 t/ha; decreased Seed yield by .27 t/ha  &  increased N % in DM (by 0.26%) and  N in the seed (0.33% increase).

• B had decreased %oil (1.63% decrease in Oil%) & decreased oil yield by 128 kg/ha .

  Care needs to be taken on use of borax fertilizer as toxicity was induced in canola and lupin; with 0.34 to 1 kg B ha−1(3-10 kg borax ha−1) at sowing depressing seed yield, mostly by decreasing plant density. Rather than making general recommendation for B fertilizer application based on 0.01M CaCl2 soil extractable B, soil and plant analysis should be used to diagnose B deficiency and B fertilizer use limited to calcium borate or foliar borax rather than soil-applied borax on low B sands.

• Boron not required for the site

• Summary 1994 experiment

• Soil extractable B was 0..4 mg/kg.

• B decreased seedling density (53 to 38).

• B concentration in dry matter (DM) 15 mg/kg B nil; 19 mg B kg for highest B application

• B fertiliser decreased the  September Dry matter (DM) by 0.48 t/ha; decreased Seed yield by 0.32 t/ha  &  increased N % in DM (by 0.3%) and  N in the seed (0.12% increase).

• B had decreased %oil (0.59% decrease in Oil%) & decreased oil yield by 144 kg/ha .

  Care needs to be taken on use of borax fertilizer as toxicity was induced in canola and lupin; with 0.34 to 1 kg B ha−1(3-10 kg borax ha−1) at sowing depressing seed yield, mostly by decreasing plant density. Rather than making general recommendation for B fertilizer application based on 0.01M CaCl2 soil extractable B, soil and plant analysis should be used to diagnose B deficiency and B fertilizer use limited to calcium borate or foliar borax rather than soil-applied borax on low B sands.

• Boron not required for the site with 0.40 soil extractable B.

• Summary 1995 experiment

• Soil extractable B was 0..4 mg/kg.

• B decreased seedling per sq. metre (50 to 39).

• B concentration in dry matter (DM) 17 mg/kg B nil; 22 mg B kg for highest B application

• B fertiliser decreased the  September Dry matter (DM) by 0.40 t/ha; decreased Seed yield by 0.2 t/ha  &  had no effect 0n N % in DM  and  N in the seed.

• B had decreased %oil (1.4 % decrease in Oil%) & decreased oil yield by 100 kg/ha .

  Care needs to be taken on use of borax fertilizer as toxicity was induced in canola and lupin; with 0.34 to 1 kg B ha−1(3-10 kg borax ha−1) at sowing depressing seed yield, mostly by decreasing plant density. Rather than making general recommendation for B fertilizer application based on 0.01M CaCl2 soil extractable B, soil and plant analysis should be used to diagnose B deficiency and B fertilizer use limited to calcium borate or foliar borax rather than soil-applied borax on low B sands.

• Boron not required for the site with 0.40 soil extractable B.

• Summary 1996 : summary of 2  experiment 

• Soil extractable B was 0.6 & 0.7 mg/kg.

• B application decreased seedling per square metre (63 to 48).

• B concentration in dry matter (DM) 27 mg/kg B nil; 36 mg B kg for highest B application

• B fertiliser decreased the  September Dry matter (DM) by 0.21 t/ha; decreased Seed yield by 0.137 t/ha  &  had no effect 0n N % in DM  and  N in the seed.

• B had decreased %oil (0.58 % decrease in Oil%) & decreased oil yield by 70 kg/ha .

  Care needs to be taken on use of borax fertilizer as toxicity was induced in canola and lupin; with 0.34 to 1 kg B ha−1(3-10 kg borax ha−1) at sowing depressing seed yield, mostly by decreasing plant density. Rather than making general recommendation for B fertilizer application based on 0.01M CaCl2 soil extractable B, soil and plant analysis should be used to diagnose B deficiency and B fertilizer use limited to calcium borate or foliar borax rather than soil-applied borax on low B sands.

• Boron not required for the site with 0.40 soil extractable B.

• Summary 1994 experiment

• Soil extractable B was 0.7 mg/kg.

• B application (Borax) decrease seedling emergence (57 to 42)

• B concentration in dry matter (DM) 22 mg/kg B nil; 27 mg B kg for highest B application

• B fertiliser decreased the  September Dry matter (DM) by 0.37 t/ha; decreased Seed yield by 0.17 t/ha  &  had no effect 0n N % in DM  and  N in the seed.

• B had decreased %oil (0.29 % decrease in Oil%) & decreased oil yield by 90 kg/ha .

  Care needs to be taken on use of borax fertilizer as toxicity was induced in canola and lupin; with 0.34 to 1 kg B ha−1(3-10 kg borax ha−1) at sowing depressing seed yield, mostly by decreasing plant density. Rather than making general recommendation for B fertilizer application based on 0.01M CaCl2 soil extractable B, soil and plant analysis should be used to diagnose B deficiency and B fertilizer use limited to calcium borate or foliar borax rather than soil-applied borax on low B sands.

• Boron not required for the site with 0.40 soil extractable B.

• Summary 1994 experiment

• Soil extractable B was 0.37 mg/kg.

• B fertiliser decreased seedling density (67 to 41).

• B concentration in dry matter (DM) 28 mg/kg B nil; 36 mg B kg for highest B application

• B fertiliser decreased the  September Dry matter (DM) by 0.62 t/ha; decreased Seed yield by 0.29 t/ha  &  increased N % in DM (by 0.43%) and  N in the seed (0.11% increase).

• B had decreased %oil (0.5% decrease in Oil%) & decreased oil yield by 124 kg/ha .

  Care needs to be taken on use of borax fertilizer as toxicity was induced in canola and lupin; with 0.34 to 1 kg B ha−1(3-10 kg borax ha−1) at sowing depressing seed yield, mostly by decreasing plant density. Rather than making general recommendation for B fertilizer application based on 0.01M CaCl2 soil extractable B, soil and plant analysis should be used to diagnose B deficiency and B fertilizer use limited to calcium borate or foliar borax rather than soil-applied borax on low B sands.

• Boron not required for the site with 0.37 soil extractable B.

• Summary 1996 : summary of 2  experiment 

• Soil extractable B was 0.6 & 0.7 mg/kg.

• B concentration in dry matter (DM) 27 mg/kg B nil; 36 mg B kg for highest B application

• B fertiliser decreased the  September Dry matter (DM) by 0.7 t/ha; decreased Seed yield by 0.217 t/ha  &  had no effect 0n N % in DM  and  N in the seed.

• B had decreased %oil (0.8 % decrease in Oil%) & decreased oil yield by 100 kg/ha .

  Care needs to be taken on use of borax fertilizer as toxicity was induced in canola and lupin; with 0.34 to 1 kg B ha−1(3-10 kg borax ha−1) at sowing depressing seed yield, mostly by decreasing plant density. Rather than making general recommendation for B fertilizer application based on 0.01M CaCl2 soil extractable B, soil and plant analysis should be used to diagnose B deficiency and B fertilizer use limited to calcium borate or foliar borax rather than soil-applied borax on low B sands.

• Boron not required for the site with 0.40 soil extractable B.

• Summary of   experiment

• Soil extractable B was 0.6 mg/kg.

• Plant density were not effected by B fertiliser (55-56 plants/m2)

• Plant B concentrations 19 -23 mg/kg.

• B fertiliser had no effect on seedling density; September Dry matter (DM) (3.43 t/ha); Seed yield (1.23 t/ha) or N % in DM (3.0 % N) or N in the seed (3.45 %).

• B had no effect on %oil (42.52) or on oil yield (535 kg/ha).

• Soil extractable B Hot CaCl2 of 0.6 was adequate

  Care needs to be taken on use of borax fertilizer as toxicity was induced in canola with 0.34 to 1 kg B ha−1(3-10 kg borax ha−1) at sowing depressing seed yield, mostly by decreasing plant density. Rather than making general recommendation for B fertilizer application based on 0.01M CaCl2 soil extractable B, soil and plant analysis should be used to diagnose B deficiency and B fertilizer use limited to calcium borate or foliar borax rather than soil-applied borax on low B sands.

• Boron not required

• Summary of   experiment

• Soil extractable B was 0.3 mg/kg.

• Plant density were not effected by B fertiliser (55-56 plants/m2)

• Plant B concentrations 15 -19 mg/kg.

• B fertiliser had no effect on seedling density; September Dry matter (DM) (3.8 t/ha); Seed yield (1.23 t/ha) or N % in DM (3.4 % N) or N in the seed (3.65 %).

• B had no effect on %oil (42.52) or on oil yield (485 kg/ha).

• Soil extractable B Hot CaCl2 of 0.3 was adequate

  Care needs to be taken on use of borax fertilizer as toxicity was induced in canola with 0.34 to 1 kg B ha−1(3-10 kg borax ha−1) at sowing depressing seed yield, mostly by decreasing plant density. Rather than making general recommendation for B fertilizer application based on 0.01M CaCl2 soil extractable B, soil and plant analysis should be used to diagnose B deficiency and B fertilizer use limited to calcium borate or foliar borax rather than soil-applied borax on low B sands.

• Boron not required

• Summary of  experiment

• Soil extractable B was 0.5 mg/kg.

• Planr density were not effected by B fertiliser (55 plants/m2)

• Plant B concentrations 21 -25 mg/kg.

• B fertiliser had no effect on seedling density; September Dry matter (DM) (3.84 t/ha); Seed yield (1.2 t/ha) or N % in DM (3.2 % N) or N in the seed (3.54%).

• B had no effect on %oil (43.8) or on oil yield (510 kg/ha).

• Soil extractable B Hot CaCl2 of 0.5 was adequate

  Care needs to be taken on use of borax fertilizer as toxicity was induced in canola with 0.34 to 1 kg B ha−1(3-10 kg borax ha−1) at sowing depressing seed yield, mostly by decreasing plant density. Rather than making general recommendation for B fertilizer application based on 0.01M CaCl2 soil extractable B, soil and plant analysis should be used to diagnose B deficiency and B fertilizer use limited to calcium borate or foliar borax rather than soil-applied borax on low B sands.

• Boron not required

• Summary of  experiment

• Soil extractable B was 0.5 mg/kg.

• Planr density were not effected by B fertiliser (55 plants/m2)

• Plant B concentrations 21 -25 mg/kg.

• B fertiliser had no effect on seedling density; September Dry matter (DM) (3.84 t/ha); Seed yield (1.2 t/ha) or N % in DM (3.2 % N) or N in the seed (3.54%).

• B had no effect on %oil (43.8) or on oil yield (510 kg/ha).

• Soil extractable B Hot CaCl2 of 0.5 was adequate

  Care needs to be taken on use of borax fertilizer as toxicity was induced in canola with 0.34 to 1 kg B ha−1(3-10 kg borax ha−1) at sowing depressing seed yield, mostly by decreasing plant density. Rather than making general recommendation for B fertilizer application based on 0.01M CaCl2 soil extractable B, soil and plant analysis should be used to diagnose B deficiency and B fertilizer use limited to calcium borate or foliar borax rather than soil-applied borax on low B sands.

• Boron not required

• Summary of 2 seasons experiments

• Soil extractable B was 0.94 mg/kg.

• B fertiliser had no effect on seedling density; September Dry matter (DM) (5.5 t/ha); Seed yield (1.71 t/ha) or N % in DM (3% N) or N in the seed (4%).

• B had no effect on %oil (40.8) or on oil yield (680 kg/ha).

• Soil extractable B Hot CaCl2 of o.9 was adequate

  Notwithstanding the marginal B levels on acid sands of the SWA region, care needs to be taken on use of borax fertilizer as toxicity was induced in canola with 0.34 to 1 kg B ha−1(3-10 kg borax ha−1) at sowing depressing seed yield, mostly by decreasing plant density. Rather than making general recommendation for B fertilizer application based on 0.01M CaCl2 soil extractable B, soil and plant analysis should be used to diagnose B deficiency and B fertilizer use limited to calcium borate or foliar borax rather than soil-applied borax on low B sands.

• Boron not required

• Summary of 2 seasons experiments

• Soil extractable B was 0.4 mg/kg.

• Plant B concentration 20 -23 mg/kg.

• B fertiliser had no effect on seedling density; September Dry matter (DM) (5.5 t/ha); Seed yield (1.71 t/ha) or N % in DM (3% N) or N in the seed (4%).

• B had no effect on %oil (40.8) or on oil yield (680 kg/ha).

• Soil extractable B Hot CaCl2 of o.9 was adequate

  Notwithstanding the marginal B levels on acid sands of the SWA region, care needs to be taken on use of borax fertilizer as toxicity was induced in canola with 0.34 to 1 kg B ha−1(3-10 kg borax ha−1) at sowing depressing seed yield, mostly by decreasing plant density. Rather than making general recommendation for B fertilizer application based on 0.01M CaCl2 soil extractable B, soil and plant analysis should be used to diagnose B deficiency and B fertilizer use limited to calcium borate or foliar borax rather than soil-applied borax on low B sands.

• Boron not required

• Summary of  experiment

• Soil extractable B was 0.6 mg/kg.

• Planr density were not effected by B fertiliser (53 plants/m2)

• Plant B concentrations 21 -24  mg/kg.

• B fertiliser had no effect on seedling density; September Dry matter (DM) (3.3 t/ha); Seed yield (1.0 t/ha) or N % in DM (3.0 % N) or N in the seed (4.30%).

• B had no effect on %oil (38.8) or on oil yield (350 kg/ha).

• Soil extractable B Hot CaCl2 of 0.5 was adequate

  Care needs to be taken on use of borax fertilizer as toxicity was induced in canola with 0.34 to 1 kg B ha−1(3-10 kg borax ha−1) at sowing depressing seed yield, mostly by decreasing plant density. Rather than making general recommendation for B fertilizer application based on 0.01M CaCl2 soil extractable B, soil and plant analysis should be used to diagnose B deficiency and B fertilizer use limited to calcium borate or foliar borax rather than soil-applied borax on low B sands.

• Boron not required

• Summary of  2 experiment

• Soil extractable B was 0.3 mg/kg.

• Planr density were not effected by B fertiliser (53 plants/m2)

• Plant B concentrations 18 -21   mg/kg.

• B fertiliser had no effect on seedling density; September Dry matter (DM) (5.9 t/ha); Seed yield (2.23 t/ha) or N % in DM (3.0 % N) or N in the seed (3.60 %).

• B had no effect on %oil (42.8) or on oil yield (950 kg/ha).

• Soil extractable B Hot CaCl2 of 0.3 was adequate

  Care needs to be taken on use of borax fertilizer as toxicity was induced in canola with 0.34 to 1 kg B ha−1(3-10 kg borax ha−1) at sowing depressing seed yield, mostly by decreasing plant density. Rather than making general recommendation for B fertilizer application based on 0.01M CaCl2 soil extractable B, soil and plant analysis should be used to diagnose B deficiency and B fertilizer use limited to calcium borate or foliar borax rather than soil-applied borax on low B sands.

• Boron not required

• Summary of   experiment

• Soil extractable B was 0.7 mg/kg.

• Plant density were not effected by B fertiliser (64 plants/m2)

• Plant B concentrations 22 -27 mg/kg.

• B fertiliser had no effect on seedling density; September Dry matter (DM) (5.1 t/ha); Seed yield (1.73 t/ha) or N % in DM (3.0 % N) or N in the seed (3.5 %).

• B had no effect on %oil (44.2) or on oil yield (750 kg/ha).

• Soil extractable B Hot CaCl2 of 0.7 was adequate

  Care needs to be taken on use of borax fertilizer as toxicity was induced in canola with 0.34 to 1 kg B ha−1(3-10 kg borax ha−1) at sowing depressing seed yield, mostly by decreasing plant density. Rather than making general recommendation for B fertilizer application based on 0.01M CaCl2 soil extractable B, soil and plant analysis should be used to diagnose B deficiency and B fertilizer use limited to calcium borate or foliar borax rather than soil-applied borax on low B sands.

• Boron not required