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HCS412 Forage Crops
Nitrogen - Chapter 4 pg 84-87 & Chapter 12 pg 267-275

Introduction

N-balance

N-fixation

Fertilizer N

Losses in hay, silage and animal products

Other components of the N balance

 

 

 

 

 

 

 

Introduction

N is the most limiting nutrient in all of agriculture
soil N is generally related to soil fertility - both are extremely difficult to measure and quantify (although N is so important, farmers have no test for soil N).
soil N forms include NO3 and NH4, and also numerous organic-N molecules which vary in plant availability
NO3 and NH4 are extremely soluble and don't stay in the soil for long.
Forage production is poorly related to soil N, it is more closely related to flow through the soil N pool than the size of the soil N pool.
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N-balance

NB "balance" approach varies from a "cycling" approach
For any site, change in soil N status = inputs - losses

inputs =

N-fixation + fertilizer N + release from soil organic matter +

atmospheric deposition

Losses =

atmospheric losses + leaching + loss to plant & animal products

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Legumes and N-fixation (pg 85)

  • symbiosis between legumes roots (nodules) and Rhizobium bacteria
  • species specificity
  • white clover and alfalfa can fix 150-250 kgN/ha/yr crop rotations

rhizobia nodules on alfalfa

 

Key attributes of legumes

  1. N2 -fixation to grassland and subsequent crops
  2. high nutritive value (digestibility and protein), hence high animal intake

Disadvantages

  1. unreliability (pests, competition, drought)
  2. potential antiquality problems (bloat)
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Fertilizer N

Fertilizer nitrogen (pg 273)

Anhydrous (crops only)
82-0-0-0
Urea
46-0-0-0
NH4NO3
34-0-0-0
(NH4)2SO4
21-0-0-0
manure 0.5% N for cattle, 1% N for poultry


fertilizer N suppresses N fixation
"rule of thumb" - every 2 lb of N applied will prevent 1 lb of legume N
split dressings (20-50 kgN per application)
strategic applications (new pasture or in fall for winter stockpile)

responses to applied N are 0-60 kg DM/kgN - typically 20 kg DM/kg N

 

 

Losses in hay/silage and animal products

Removal in hay/silage or animal products
Often underestimated - but is usually the greatest loss of N from the soil
Hay typically 25% protein (protein is 16% N = hay is 4%N)
Typical alfalfa harvest 4 crops each of 1.5 ton/acre (12,000 lb/acre, 13.4 T/ha)
= 480 lbN/ac (540 kgN/ha)
Cow-calf operation
Grazing 1 cow per acre, producing a 600 lb (275 kg) stocker calf per acre
60% protein (16%N)
= 58 lbN/acre
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Other Components of the N-balance

Atmospheric deposition
= pollution
20 kgN/ha/yr in North America
50 kgN/ha/yr in Europe
Volatilization
Release of NH3 from fertilizers - results in inefficiency of fertilizer application
Unless nitrogenous fertilizers are washed into the soil by rainfall soon after application they can "evaporate" as NH3 and reduce the fertilizer response
Leaching
Not usually significant for most soils (being N deficient)
Can be extremely high if total N inputs (fixation and fertilizer) exceed 250 kgN/ha
Is usually high in areas with repeated applications of effluent
Nitrification & Denitrification
An environmental issue. In extreme cases can account for up 30% of N losses from soil
Nitrification = oxidation of NH4 to NO3
Denitrification = reduction of NO3 to N2O, NO2 and N2 (released to the atmosphere), high in wet soils


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