• 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

• Summary of   experiment

• Soil extractable B was 0.7 mg/kg.

• Plant density were not effected by B fertiliser (71-66 plants/m2)

• Plant B concentrations 29 -33 mg/kg.

• B fertiliser had no effect on seedling density; September Dry matter (DM) (3.63 t/ha); Seed yield (1.2 t/ha) or N % in DM (3.4 % N) or N in the seed (3.55 %).

• B had no effect on %oil (42.5) or on oil yield (500 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

• Summary of   experiment

• Soil extractable B was 0.6 mg/kg.

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

• Plant B concentrations 23 -27 mg/kg.

• B fertiliser had no effect on seedling density; September Dry matter (DM) (3.4 t/ha); Seed yield (1.43 t/ha) or N % in DM (2.9 % N) or N in the seed (4.0 %).

• B had no effect on %oil (40.0) or on oil yield (540 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 2 experiments

• Soil extractable B was 0.4 mg/kg.

• Plant B concentrations 20 -23 mg/kg.

• B fertiliser had no effect on seedling density; September Dry matter (DM) (4.76 t/ha); Seed yield (1.23 t/ha) or N % in DM (3.2 % N) or N in the seed (4%).

• B had no effect on %oil (44.8) or on oil yield (580 kg/ha).

• Soil extractable B Hot CaCl2 of 0.4 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 0.4 mg/kg.

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

• Plant B concentrations 15 -18 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 (3.4 % N) or N in the seed (3.45 %).

• B had no effect on %oil (44.52) or on oil yield (775 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

• Summary of  2 experiments

• Soil extractable B was 0.8 mg/kg.

• Plant density were not effected by B fertiliser (70-65 plants/m2)

• Plant B concentrations 31 -36 mg/kg.

• B fertiliser had no effect on seedling density; September Dry matter (DM) (3.0 t/ha); Seed yield (1.02 t/ha) or N % in DM (3.3 % N) or N in the seed (3.6 %).

• B had no effect on %oil (41.9) or on oil yield (420 kg/ha).

• Soil extractable B Hot CaCl2 of 0.8 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 experiments

• Soil extractable B was 0.7 mg/kg.

• Plant density were not effected by B fertiliser (59-56 plants/m2)

• Plant B concentrations 26 -30 mg/kg.

• B fertiliser had no effect on seedling density; September Dry matter (DM) (2.0 t/ha); Seed yield (1.55 t/ha) or N % in DM (3.43 % N) or N in the seed (3.6 %).

• B had no effect on %oil (41.9) or on oil yield (650 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

• Summary of 1 year.
• Cu fertiliser previously drilled with wheat appeared more availalble  than current drilled.
• CuSulfate @ 5.5  kg/ha gave maximum dry matter yield.
• Zn & Mo basalled for clover growth.
• Cu  at 5.5 kg Cu sulfate gave maximum yield of barley in year 2..
• Copper deficiency of wheat, barley and poor clover growth has been recorded by many farmers.
•  

• Plants grown in small pots containing Mn deficient calcareous (pH 8.5, 80% CaCO3) sand collected from Wangary, S.A with 0-50 ppm added Mn in growth room at 15°C.
• Plants harvested at approx. 4 weeks (early tillering). Also 30 wheat cultivars were screened at Wangary using plant breeders' plots (4 rows x 5 m) with a split plot application of foliar MnSO (1 kg/ha ).
• Effects of seed soaking were evaluated for wheat and barley by soaking for 6 h with 1.5% MnSO4 prior to sowing.
• Without Mn, all cultivars showed no differences in growth and Mn uptake at 4 weeks (pots) but significant differences at 8 weeks in the field. With Mn supplied either in soil or on seed large cultivar differences were apparent at 4 weeks.
• Conclude that use of Mn efficient varieties coupled with a suitable seed Mn content will lessen the need for Mn fertilisers.

• Just 50 kg DAP/ha knife point drilled with 70 kg/ha wheat seed is enough to reduce wheat plant  establishment.
• Wheat fertilised with DAP with seed yielded 0.5 t/ha (20%) less than wheat with DAP placed below seed in 2016.
• The addition of 35 kg urea/ha below the seed overcame the yield penalty in the DAP-with-seed plots, suggesting access to N was a driver.

• Just 50 kg DAP/ha knife point drilled with 70 kg/ha wheat seed is enough to reduce wheat plant establishment
• Wheat fertilised with DAP with seed yielded 0.5 t/ha (20%) less than wheat with DAP placed below seed in 2016. 
• The addition of 35 kg urea/ha below the seed overcame the yield penalty in the DAP-with-seed plots, suggesting access to N was a driver.

• Our results suggest shifting investment from nutrients to lime and cultivation and maintaining profit in the first year for the 2 sites we ran is a feasible proposition.  However, this is dependent on the soil constraints and existing soil fertility.  In this trial, it appears that the cultivation response was driven by an increase in the mineralisation rate of organic matter. The incorporation of lime did not provide any yield benefit; while the rotary spader provided adequate mixing of the lime this had no impact on growth because soil pH was already above target levels.  The yield benefit from cultivation was enough to offset the cost of the cultivation and most of the lime application, and the net margin in the year of application could be improved by reducing fertiliser rates.
•  

• Summary of  2 experiments

• Soil extractable Cu was 0.23 mg/kg.

• Plant density were not effected by Cu or N fertiliser (29-36 plants/m of row2)

• Plant B concentrations 26 -30 mg/kg.

• Cu fertiliser had no effect on seedling density; September Dry matter (DM) (2.0 t/ha); Seed yield (1.55 t/ha) or N % in DM (3.43 % N) or N in the seed (3.6 %).

• B had no effect on %oil (41.9) or on oil yield (650 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

• Rosalind (fast maturity) had the highest grain yield at all rates of applied nitrogen.
• Higher lodging at higher nitrogen rates reduced yield response to applied nitrogen in Compass, Commander and scope CL
• High spring rainfall and mild growng conditions resulted in high yields and full use of applied nitrogen

• There was no significant interaction between sowing time and phosphorus (P) in response in 2014 and 2015.
• Both sites and years responded positively to P fertiliser with 10kg P/ha achieving a relative yield of 88% and 97% in 2014 and 2015 respectively.
• Further research is required to determine if winter canola requires less applied P than slow spring phenology types (due to teh longer vegetative phase to accumulate biomass by flowering. 

• The variety Beckom sown on 5 May yielded highest (5.67 t/ha).
• Grain yield reductions up to 4t/ha occured when varieties were not sown at the correct time (due to flowering throughout August - September frost events).
• Greatest yield losses occured when quick maturing varieties were sown early rather than longer season varieties sown late.
• Winter wheats and very long springs spring wheats performed better in 2015 than 2014, presumably due to less aphid pressure (BYDV) in 2015. 
• Grain yield was maximised when winter wheats were sown early (mid-April) or mid to mid-fast varieties were sown in teh first week of May. If spring conditions had been favourable, the winter whaets may have outperformed the mid to mid-fast varities when sown in late May.
• Screening increased as sowing was delayed. 

• The combination of extra stored water (20mm) and early sowing (17 April) resulted in the highest grain yield in this experiment.
• Early sowing without extra stored water gave a higher yield than late sowing (4 May), regardless of teh irrigation treatment at the later sowing date.
• The extra grain yield from early sowing and irrigation was due to increased biomass accumulation and imprved harvest index.
• Oil concentration was low overall, but was higher from the early sowing (33.6%) than th elater sowing (30.5%).

• Three field trials assessed the relative effectiveness of a range of products for correcting zinc deficiency in wheat.
• These trials were conducted during the 1996 growing season and were located in representative areas of the Lower Eyre Peninsula and Lower North regions of SA and the Wimmera of Vic.
• They were predicted to be Zn deficient but moderate responses to Zn fertilisers were recorded at only the two SA sites.
• Responses to Zn in grain yield at these two sites were too small to assess any relative differences between fertiliser sources but assessments of dry matter production and Zn uptake during the season allowed some relative comparisons to be made.
• The technique of spraying a zinc sulphate solution onto the soil surface and incorporating prior to seeding was the most effective technique at supplying Zn to the wheat crop under the conditions of these trials.
• Under the conditions of the trials reported here there was no clear evidence that DAP sources of Zn enriched fertilisers were less effective than MAP sources.
• However, the behaviour of these two different product types was not tested under severe Zn deficiency conditions.

In this trial, there has been a positive response to phosphorus fertiliser applied at 9kg/ha at sowing and a positive response to nitrogen fertiliser applied at 20kg/ha. There has been a negative response to applied nitrogen both at sowing and top-dressing at higher than 20kg N/ha rates, which can be attributed to low growing season rainfall (GSR), which has occurred through prolonged periods over the course of the trial.

Note Predecimal. However, all data are converted to for application kg/ha &

grain yield kg/ha.

Atleast 8 kg of bluestone (Cu sulfate) required for first year.

Application of 1 to 1.5 kg Zn oxide to red sandy earths, yellow earthy sands and leached grey sands is a "safe" policy.

 

• Several sites where the main soil is grey sand over a yellow gravelly sandy loam {Altas of Australian Soils sheet 5; CSIRO Division of Soils).
• Neither Cu nor Zn applied alone gave increase grain yield.
• Increased grain yield resulted where Cu & Zn were applied together
• Application of greater than 2.75 - 5.5 kg bluestone (Cu sulfate] and about 1.5 -2.0 kg Zinc oxide drilled with a cereal crop gave maximum yields
• Aerophos treatements with low Zn content showed extrememly low grain yield compared to super; illustrating the value of Zn in plain super.

• 15 acid soils from 8 soil groups were used to examine the effects of lime yields and phosphorus uptake white clover in relation to changes in exchangeable and soluble phosphorus, manganese and aluminium. There were yield responses to lime in 8 soils, 6 of which occurred only in the absence of phosphate and 2 only in the presence of phosphate.
• Clover only responded to lime when it contained more than 100 ppm manganese.
• Clover failed to respond to lime when it contains less than 80 ppm manganese, regardless of the lime effect soil phosphorus.

At Hart, higher N-fertiliser rate (180 and 240 kg N/ha) produced lower grain yields compared to lower N rates (0, 60 and 120 kg N/ha).

• Zinc oxide fertilisers had lower solubility and dissolution than zinc sulphates.
• Zinc oxide was as effective as zinc sulphate if it was mixed with the soil but not when banded near the seed.
• Zinc sulphate would be preferable to zinc oxide in no-till systems where fertiliser is banded.

Although the N2O emissions did not seem to correlate with the rate of N fertilizer applied the demonstration did clearly show that despite extremely wet conditions at and soon after application N2O emissions are still relatively low (less than 10%) compared to irrigation sites. These emissions are likely to be well above average in this soil and rainfall indicating the emissions from N2O in these cropping systems is relatively insignificant. The demonstration will be conducted again in 2014 using several rates of Non a single soil type to get a clearerpicture of the variation in emissions.

• Trial work with Southern Farming Systems over the past four years has demonstrated significant improvements in nitrogen efficiency from applying ENTEC treated urea to wheat crops, compared to untreated urea.
• The experiment this year showed no response to nitrogen, but did highlight some important tools for predicting the liklihood of nitrogen response.

• The trial showed up to a five-fold increase in dry matter at DC41 when 20 kg/ha of phosphorus was applied. This translated into a doubling of yield, despite waterlogging and stripe rust at the site.
• A low rate of P (5 kg/ha) did not provide a statistically significant yield response while higher rates (10 and 20 kg/ha) did.
• Soils continue to be highly responsirve to phosphorus even at higher Colwell P levels.
• There is some evidence of adequate phosphorus nutrition improving grain quality (screenings) through earlier maturity.

• Phosphorus rates of 10 and 20 kg/ha applied in various straight, compound, coated and liquid fertiliser forms were not found to result in any significant responses in grain yield or quality.
• Results were impacted by the failure to control a population of herbicide-resistant annual ryegrass at this trial site using both pre- and post-em herbicide options, resulting in a high variability between plot measurement.

A fertiliser additive was applied to standing stubble and compared with untreated stubble. The fertiliser additive was applied with and without a sticker or molasses. There was no significant difference in the amount of stubble dry matter remaining after 6 months i.e. the rate of stubble breakdown was comparable between all treatments. Similarly there were no consistent effects on feed and chemical
characteristics. Addition of nutrients and molasses did not improve intake by grazing sheep.

A combination of fertiliser inputs and irrigation can rapidly breakdownincorporated cereal stubble and allow sowing 4 weeks later. Getting the balance of fertiliser, in particular N rates, to ensure rapid breakdown, but creating neither N deficiency or excessive N remains elusive.

Measuring soil organic carbon following incorporation is giving mixed results as to the ability to increase soil OC via incorporation with fertiliser

Burning the stubble gave greater yield and oil content

There has been widespread use of continuous cereal in the Mallee over the past decade, and with many drought years throughout this period fertiliser inputs have generally been greater than crop demand. As a consequence, soil phosphoruslevels are often well above the critical level. By identifying soils and conditions where continuous cereal systems perform best and where inputs can be most effectively targeted, there is an opportunity to reduce input costs and increase profitability. This trial used PA methods to identify soil types for targeted soil sampling to achieve a greater understanding of soil phosphorus levels in different soil zones. Yield mapping was then used to identify if and where fertiliser applied to the crop impacted grain yield.

Application of DAP fertiliser at time of sowing improves yield in barley. Application of additional nitrogen lifts yields further, and improves protein levels in the grain. Results suggest efficiencies in nitrogen application can be achieved with placement in the root zone compared to surface application. Further work needs to be undertaken to better understand the process. 

• Zinc was applied at four rates as either zinc sulphate (35% Zn), zinc oxide (83% Zn), zinc oxysulphate (18% Zn) or as granulock STZ (20.4% P, 2.5% Zn).
• Dry matter yield, tissue Zn concentration and plant Zn uptake were measured. Co-granulated zinc oxide and MAP (ST-Z) produced the dry matter response similar to zinc sulphate, with zinc oxysulphate and zinc oxide producing similar but lower yields.
• It is proposed that the difference in effectiveness between STZ (zinc oxide based) and zinc oxide is as a result of a synergistic effect between the close proximity of the P and Zn in each particle rather than any change in chemical composition during manufacture.
• The mechanism for enhanced Zn uptake with STZ may be a result of root proliferation around P concentrations aiding Zn uptake.

(i) The most significant outcome from these trials was the very strong effect of increasing grain protein. In nearly all cases, the higher rate of 50kgN/ha had a more significant effect, as did delaying the timing until GS55. (ii) There were no differences between product type and rate had a small effect. (iii) The higher rate of 50kgN/ha had a higher yield than 25kgN/ha. (iv) For the majority of sites, the key timing that influenced yield was GS39. This timing is slightly later than previously thought suitable for applying N for yield, with GS32 being the recognised standard. The data needs to be interpreted with the 2013 season in mind because a tighter finish in spring could mean plant uptake of late applied N would be limited.

Application of metconazole to canola resulted in a reduction in plant height but in this trial there was no effect on grain yield. Tebuconazole had no effect on plant height or final yield. In seasons where excess vegetative growth is a problem increases in grain yield following treatment could be expected through improved harvest efficiency (less lodging and/or redirection of plant assimilates to the grain).

In this survey, 76% of the paddocks had a Colwell P greater than 20mg/kg.

In this survey, 76% of the paddocks had a Colwell P greater than 20mg/kg.

In this survey, 76% of the paddocks had a Colwell P greater than 20mg/kg.

In this survey, 76% of the paddocks had a Colwell P greater than 20mg/kg.

In this survey, 76% of the paddocks had a Colwell P greater than 20mg/kg.

In this survey, 76% of the paddocks had a Colwell P greater than 20mg/kg.

In this survey, 76% of the paddocks had a Colwell P greater than 20mg/kg.

In this survey, 76% of the paddocks had a Colwell P greater than 20mg/kg.

In this survey, 76% of the paddocks had a Colwell P greater than 20mg/kg.

In this survey, 76% of the paddocks had a Colwell P greater than 20mg/kg.

In this survey, 76% of the paddocks had a Colwell P greater than 20mg/kg.

In this survey, 76% of the paddocks had a Colwell P greater than 20mg/kg.

In this survey, 76% of the paddocks had a Colwell P greater than 20mg/kg.

In this survey, 76% of the paddocks had a Colwell P greater than 20mg/kg.

Removal of subsoil compaction by deep ripping resulted in a 370 kg/ha (45%) yield benefit with spading giving an additional benefit of 12% (100 kg/ha) and mouldboard ploughing 39% (320 kg/ha) compared with the deep ripping treatment. Higher biomass and increased head density in the cultivation treatments are indicative of improved nutrient access and effcient use of available water through the season. Water use efficiency was 4.9 kg/ha/mm of growing season rainfall for the control treatment compared with 7.1 kg/ha/mm for ripped, 7.6 kg/ha/mm for spaded and 8.9 kg/ha/mm for mouldboard ploughing. Recent research is showing that nutrient availability is improved when top soil is buried by spading or mouldboard 
ploughing because nutrients become concentrated in the rootzone and less suscpetible to soil drying from evaporation, which can be the case when majority of the nutrients are on the soil surface, (Davies et al, 2012).

• On average the wide row lupins yielded 115kg/ha higher than the narrow lupins.
• Simazine damage was very pronounced in this particular crop. However, damage in the wider rows appeared to be much less than that in the narrow rows.
• The same seeding and fertiliser rates were used for both treatments which made changing the bar over relatively quick.