Getting nitrogen (N) into the crop efficiently and effectively

Author: | Date: 03 Apr 2014

Rob Norton,

International Plant Nutrition Institute

Take home messages

  • Efficiency and effectiveness are different dimensions of nutrient use efficiency (NUE). A system level assessment of NUE can be made using a partial nutrient balance (N removed in grain/N applied) and partial factor productivity (grain produced/N applied). What are your numbers?
  • Early N is generally used more efficiently, but the source, rate, timing and placement of N all affect the efficiency with which the crop can access N.
  • When comparing N sources; rate, timing and placement all interact so that efficiency options vary and no single source is a “silver bullet” to all situations.
  • There would need to be compelling circumstances to justify moving away from top-dressed urea applied to the crop as the season unfolds.

Introduction

Because nitrogen (N) use on grain crops has now become a tactical issue in response to seasonal conditions, it is always a topic of conversation. Some worry that they have skimped and missed yield, others worry that what they applied either did not work or gave only a small response and still others worry that there were big losses in what they applied, so they have wasted a lot of the N applied.

In developing an N management strategy, these tactical issues need to be considered but within the general approach of a soundly based and regularly reviewed N budget. Making and reviewing yield estimates is critical, as the yield potential will be a function of the N demand in our rain fed environments. The budget should include N supplied from the soil as profile N, plus in-crop mineralisation, as well as the efficiency with which the nutrient gets to the product; termed nitrogen use efficiency (NUE).

What do efficiency and effective use mean?

While the term NUE seems simple, there are many ways it can be assessed. There are differences in the numerator and denominator of the equation, as well as the temporal and spatial scale adopted. Some of the more common terms are explained in Table 1. Some such as Apparent Recovery Efficiency or Agronomic Efficiency rely on having a nil fertiliser control, which makes them less suited to paddock or regional scale and more suited to experimental comparisons. Alone, none of these indicators are of particular value, but Partial Factor Productivity (PFP) helps understand the return in grain from the use of fertiliser, while Partial Nutrient Balance (PNB) tells something of the source of the nutrients removed in the crop. In terms of fertilisers, PFP tells us about effective nutrient use, while PFP tells use about efficient nutrient use. Both can be assessed at paddock or farm scale, and do give some idea of two long term NUE measures that can be used to assess system level performance, much in the same way growers and advisers are comfortable using water use efficiency (WUE) for the same purpose. For example, a grower who produces 1000 t of 11% protein wheat using 40 t of urea has a PFP of 55 kg grain/kg N applied and PNB of 1.1 kg N removed/kg N applied.

Table 1. Examples of ways to derive nutrient use efficiency (after Dobermann 2007)

Term    

Calculation

Range for N in cereal crops

Partial Nutrient Balance (Nutrient Removal Ratio)

PNB = kg nutrient removed kg-1 applied

        = Ug/F

0.1 to 0.9 kg/kg; >0.5 where background supply is high and/or where nutrient losses are low.

Australian figure for cereals is 0.82 kg N removed/kg N applied.

Partial Factor Productivity

PFP = kg yield kg-1 nutrient applied

        = Y/F = (Y0/F)

40-80 kg/kg: >60 in well managed systems, at low N use or at low soil N supply.

Australian figure for cereals is 52 kg grain/kg N applied.

Recovery Efficiency

RE  = kg increase in uptake kg-1 applied

      = (U – U0)/F (whole plant)

      = (Ug-U0g)/F (grain only)

0.3 to 0.5 kg/kg; 0.5 to 0.8 in well managed systems, at low N use level or at low soil N supply.

Physiological Efficiency

PE  = kg yield increase kg-1 fertiliser nutrient uptake

      = (Y-Y0)/(U-U0)

40 to 60 kg/kg; >50 in well-managed systems, at low N use level or at low soil N supply.

Internal utilization efficiency

IE   = (kg yield kg-1 nutrient uptake)

      = (Y/U)

30 to 90 kg/kg; 55 to 65 is the optimal range for balanced nutrition at high yield levels.

Agronomic Efficiency

AE = kg yield increase kg-1 nutrient applied

      = (Y-Y0)/F = RE x PE

10 to 30 kg/kg; >25 in well managed systems, at low N use or at low soil N supply.

Y=crop yield with applied nutrients; Y0=crop yield with no applied nutrients; F=fertiliser applied; U=plant nutrient uptake of above ground biomass at maturity; U0=plant uptake with zero fertiliser; Ug=grain nutrient content with applied nutrients; U0g=grain nutrient content with no applied nutrients.

Assessing NUE on farms

Table 1 also shows the mean PFP and PNB estimates for Australian cereal production systems. Both values should be considered because a high PFP with a low PNB indicates that the high productivity is drawing on soil N reserves rather than from fertilisers. Alternatively, a very high PNB (>1) with a low PFP suggests that losses of nutrients are occurring. In our farming systems, growers may have very high PFP and PNB because they rely on soil reserves (say N from a pasture ley) to sustain productivity.  These indicators, like WUE, can help understand something of the system efficiency for farmers, but the interpretation is far more important than the numbers themselves. The most efficient way to use fertilisers is not to use any, but that is not effective, as production is likely to be nutrient limited.

Using the above metrics can be useful in looking at broad-scale efficiency, but at a crop level, grain protein can be an estimate of the degree of N limitation a crop has undergone. Providing grain size is good, wheat grain protein concentration generally has a strong inverse relationship with grain yield.  However, with increasing N supply yield and protein converge (Figure 1). This relationship has a large genetic component, so some varieties express higher levels than others.  The response is also affected by rainfall/water supply, particularly after anthesis.

If the upper limit to grain protein for a variety is known, then grain protein can help us understand the degree of N limitation during the season. Figure 1 shows the yield and protein relationship that is generally held, and as N supply increases, yield initially increases to a maximum, but protein is slower to resolve.  Consequently, if grain protein is low with a higher yield, it suggests that N was limited. 

Figure 1 Grain yield (t/ha) and protein concentration (%) from 10 wheat varieties with 0, 30, 60, 90 and 120 kg/ha applied nitrogen in a trial at Parkes in 2011 (Brill et al, 2012)

Figure 1 Grain yield (t/ha) and protein concentration (%) from 10 wheat varieties with 0, 30, 60, 90 and 120 kg/ha applied nitrogen in a trial at Parkes in 2011 (Brill et al, 2012)

Agronomic manipulation using 4R nutrient stewardship

The first aspect of ensuring N is used efficiently and effectively is to ensure that other issues such as sodicity, salinity, acidity, other nutrients, pests, weeds or diseases are not the limitation. A simple way to do this is to use an N-rich strip in a paddock. This will serve as a reference for later in the season as well as give some early indications if additional N is giving a response, and even if further N could provide extra benefit.

Given the above, there are some indicators however, that can be considered around effective and efficient N use:

Right Time

The earlier N is applied, the larger the yield increase, whereas the later the N is supplied, the larger the protein increase.  Basically, the N supplied will most affect the tissue that is actively growing at that time. Early N stimulates shoots or tillers, whereas later N can increase stem growth. Once active stem growth slows, later N can be used in grain filling.

Table 2 shows the results of a small experiment where 20 kg N/ha was applied as urea at different times to a wheat crop at Horsham. The later applications gave progressively smaller yield responses, while the protein response increased except when applied during early dough. Table 2 shows that 20 kg N applied showed lower recovery as application was delayed.

Table 2. Responses of wheat (cv Yitpi, 2001, Longerenong) to 20 kg N/ha applied at different crop stages, relative to nil added N

Responses
N applied at:   
Nil N DC31 DC42 DC65 DC72 LSD p>0.05
Yield (t/ha) 3.31 3.94 3.23 3.29 3.14 0.31
Protein (%) 8.6 9.4 10.4 9.8 8.9 0.4
N recovered (kg N/ha) 50 65 59 57 49  
% Recovery   75% 44% 33% -4%  

The other aspect of timing to consider is timing of application relative to rainfall. Most growers would try to time application of urea ahead of rainfall so that the losses of N as volatilized urea are reduced. The amount of N lost from surface applied urea has been a topic of significant research over the past few years, especially with the commercialization of urease inhibitors. Experiments in cropping systems in the Wimmera and Mallee showed losses of up to 23% from urea, and this loss can halve where there was rain within a day of application (Turner et al. 2012). Soil texture, wind-speed, crop cover, stubble load, soil organic matter and temperature all affect the rate of volatilization. The detail of how much N is lost due to particular rainfall events probably causes more grief than a Collingwood grand final win, but addressing ammonia losses is only one part of the actual efficiency.

Right rate

While timing and form often get the most interest, getting the rate right is as important. The key question here is, is the crop actually N limited?  Unless this is the case, there will be no response to N and so a low efficiency. Nitrogen budgets reviewed with yield estimates such as from Yield Prophet® are vital to estimate demand, while supply from deeper in the soil or mineralised N will also be important (but often not estimated). The rate can be determined based on having adequate N in the crop by anthesis to match the yield and protein target. A 3.5 t/ha grain yield will probably come from a biomass at anthesis of 7 t/ha and to meet an 11% protein target, the crop should have around 120 kg N (do the maths up or down). If the post-anthesis conditions are better than target, then N will be diluted by the extra growth and grain protein will decline. If conditions are worse, then grain protein will increase. Therefore, the actual yield response will depend on the N rate meeting the gap between the target demand and expected supply (neither of which we know in advance). Consequently, there is some luck in what outcome does occur.

Right place

Having the N isolated from losses due to ammonification, denitrification and leaching means that if the crop really needs the N, it can access it with minimal loss.  Applying the entire N up-front would suggest a good efficiency.  However, this is when seasonal conditions are least known, and so demand is still being formed.  If all application of N is up-front, the decision on rate can only be adjusted up, not down.

It is also important to caution about placing fertiliser, especially urea, in a seed-row. Poor establishment due to fertiliser damage to germinating seeds can be significant with the use of wide rows, narrow points, light soils and dry conditions (http://anz.ipni.net/article/ANZ-3076).  A 3-5 cm separation between fertiliser and seed is adequate to minimise damage.

Inter-row banding pre-crop or even in-crop (side-banding) is an attractive option as it buries the N.  However the technologies around these application options require more refinement.

In most situations however, the placement for in-crop application will be over the top of the crop. For dry fertilisers, most will end up on the soil and the fate for urea is to become either ammonia which can be lost, or plant available ammonium or nitrate. Leaves can absorb inorganic and organic nitrogen sources. Small pores within leaf cuticles can take up urea, ammonium and nitrate. These pores are lined with negatively charged molecules, and therefore, uptake of cations (such as ammonium) is faster than anions (such as nitrate). Uptake of small, uncharged molecules, like urea, is fast. Urea is commonly used for foliar fertilization because it’s uncharged, has high solubility and can be rapidly and efficiently absorbed by leaves (Fernandez et al. 2013).

For fluid fertilisers, such as urea or urea/ammonium nitrate solutions, depending on the application equipment used, some proportion of the material will intercept the crop canopy and some will hit the soil. Once on the soil, the loss processes are the same for dry fertilisers, but the N on the canopy can be taken up through the leaves.

Foliar applied N has been proposed as the most efficient method to present N, and urea is rapidly and effectively taken directly through the leaf surfaces. For highest efficiency, coverage should be good, but crops are susceptible to damage both from urea itself as well as the salt effect of the solution. This urea toxicity will dictate the upper level for effective N uptake, and it is probably around 10-15 kg N/ha depending on crop cover, ambient conditions, and application technology. Streaming nozzles place fluids on the inter-row rather than the canopy, and while reducing canopy damage, they do expose the material to soil surface losses under the canopy.

Right source

Many of the comparisons of N sources (products) confound the source with both the placement and the timing effects.  However, where N for N comparisons at similar timings is made, differences in recovery of applied N and yield responses are small (Gooding et al. 2007).  There are however, quite large differences in cost (Doyle 2013) that need to be balanced against benefits gained.

For surface applied N, two experiments showed losses to ammonification as urea (23%), urea/ammonium nitrate (12% and sulfate of ammonia (12%) for 9 days between application and light rainfall on an alkaline vertosol (Turner et al. 2012). In a similar earlier experiment, the loss of N from urea can be reduced from 10% to 1% of applied N through the use of an urease inhibitor (Turner et al. 2010), although the efficiency of this reduction was reduced at higher temperatures and higher soil organic C content (Suter et al. 2011).

At Birchip in 2013 (McClelland, pers. comm.) trials showed that N uptake from both UAN (streaming nozzles), urea solution (flat fan nozzles) and dry urea (top-dressed) was similar 10 days after application (DC31). However, by anthesis the UAN (streaming nozzles) and dry urea had more N in the crop than the urea solution. By maturity there were no yield differences, although the UAN and dry urea had higher grain protein contents than the urea solution. 

Fluid fertilisers offer the opportunity to combine two operations, thereby reducing paddock traffic, as well as giving application options for additional nutrients such as S or micronutrients.

There are however, many other factors at play to achieve a profitable yield response from N application.  However, in my opinion there would need to be compelling circumstances where expected losses are high, to justify moving away from top-dressed urea, applied as the season unfolds.

The way forward

1.            Try N-rich strips in fields to see where the response could be sitting.

2.            Unless springs are good to very good, there will be little benefit from N applied later than booting, and much of this will be as a protein response.

References

Brill et al. 2012 http://www.grdc.com.au/Research-and-Development/GRDC-Update-Papers/2012/04/Comparison-of-grain-yield-and-grain-protein-concentration-of-commercial-wheat-varieties)

Doyle (2013) http://www.grdc.com.au/Research-and-Development/GRDC-Update-Papers/2013/03/Liquid-Nitrogen-pros-and-cons-of-different-formulations

Fernandez et al. 2013. Foliar Fertilization, Scientific Principle and Field Practices. International Fertiliser Industry Association. (http://www.fertiliser.org/HomePage/LIBRARY/Our-selection2/Fertiliser-use.html/Foliar-Fertilization-Scientific-Principles-and-Field-Practices.html)

Gooding and Davies. 1992. Fertiliser Research, 32, 209-222.

Gooding et al. 2007. Field Crops Research, 100, 143-154.

Suter et al. 2011. Soil Research, 49, 315-319.

Turner et al. 2010. Agriculture, Ecosystems and Environment, 137, 261-266.

Turner et al. 2012. Nutrient Cycling in Agroecosystems,93, 113-126.

Contact details

Rob Norton

0428 877 119

rnorton@ipni.net

http://anz.ipni.net