Nitrogen (N)

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Nitrogen - Fact sheet

Calcium Ammonium Nitrate (CAN 27% N): Major straight N product, Contains calcium. The form of N is 50% Nitrate [NO

3

] and 50% Ammonium [NH

4

+ .]. The calcium will help reduce acidifying effects of ammonium.

Urea: Contains 46% N. Ammonium is positively charged, clay particles are negative charged, and therefore urea is held by clay particles provided moisture is present.

Cost per kg N (Jan 2013) – CAN €330/t 270kg N = €1.22c / kg N

– Urea €450/t 460kg N = €0.98c / kg N

Urea - Prills vs.

Granular: Prills are small and soft, granular is larger and harder making it more suited to blends. Prills are suitable up to 12m spread widths; granular is suitable up to 18m spread widths.

Plant uptake of N: Plants take up N either as Nitrate - N and/or Ammonium - N.

Ammonium is more easily taken up in cold weather.

Urea versus CAN: Urea is a cheaper source of N and but requires soil moisture to avoid being lost to air by ammonia volatilisation.

Volatilisation : Loss of ammonia (NH

3

) gas to the atmosphere. Increases when soils are dry, high temperature (>12°C) and high pH or freshly limed soils.

Urea in summer: Urea needs moisture to be converted to ammonia.

CO (NH

2

)

2

+ H

2

0 + urease 2NH

3

+ CO

2

. At high temperatures there is rapid conversion of urea to ammonia; lack of moisture will prevent ammonium being held by the soil.

Denitrification: Nitrate is converted to Nitrogen (N

2

), Nitrous Oxide (N

2

O) or

Nitric Oxide (NO) which is lost to the atmosphere. Soil bacteria cause this process when soil is wet or waterlogged.

Mineralisation: Soil contains a reservoir of N that can be as high as 7,000 kg/ha.

Most of this is tied up in organic matter. Following microbial action in the soil, some of this N is made available in a form that can be taken up by the grass roots. The average quantity of this background-N made available is approximately

145 kg N/ha/year.

Leaching: Nitrate is water soluble and may be lost by leaching (percolates down through soil) or by surface run-off (sloped land).

Fertilizer N and Slurry: Slurry applied on fertilizer N creates ideal conditions for denitrification, i.e., anaerobic conditions and high carbon compounds. Leave 7 days between spreading either slurry or artificial N fertiliser to reduce the risk of N loss.

Nitrogen and frost: Ideally N applications in frosty conditions should be avoided as there is the risk of N loss through run off when soils thaw and also N fertilisers may remain on the soil surface leading to N loss through volatilisation

Urea & Lime : Lime increases soil pH which increases rate of volatilisation of ammonia. Do not spread urea for 3-6 months after lime application.

N fertiliser and heavy rain: Nitrogen can be lost as nitrate by either run-off or leaching

How quick is N available: Once fertilizer N is applied, it is not all taken up at once, it is taken up over a period of 4 to 8 weeks after application. Nitrate is available immediately for plant growth. Urea takes 2/4 days to convert to ammonia provided moisture is present.

Nitrogen in Slurry and lime: Lime increases soil pH which increases rate of volatilisation of ammonia. Do not spread slurry on recently limed soils and leave

3-6 months between lime and slurry applications.

Response rates to applied Nitrogen

Jan – Feb:

March:

April

June

– May:

– August:

0 – 10 kg Grass Dry matter per kg N applied.

0

– 25

15

– 50

15 – 35

September: 15 – 25

Response rates will vary from year to year due to temperature, sunshine, rainfall, ground conditions, type of grass sward, reseed or not, etc

Soil pH & Nitrogen: Maintaining a soil of pH 6.3 – 6.5 will improve N recycling and release from soils. Soil maintained in the optimum soil pH range can release

60 to 80kgN/ha on an annual basis.

Fertiliser Spreaders and application rates: Calibrate fertiliser spreaders as fertiliser batches change. Check evenness of spread by tray test and calibrate to ensure correct application rate. Set up correctly on the tractor - spreader is set even from side to side, level back to front and set at correct operating height.

N in slurry: N in slurry behaves similarly N in urea. To maximise the recovery of

N from slurry apply in the spring time under cool, moist conditions. Typical N recovery with splash plate application in the spring is 25%. Summer application with splash plate 5%

Splash plate V’s Trailing shoe & N recovery: Trailing shoe application method will approximately increase the N recovery by 10% over the splash plate application method for spring (25 v 35%) and summer (9 v 18%) application timings.

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