nutrient cycling in soils: the big 3 and carbon · 2017-06-27 · n.c. brady, 1974 luxury...
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Nutrient Cycling in Soils:The Big 3 and Carbon
Gurpal ToorDepartment of Environmental Science & Technology
University of Maryland–College Park
Fundamentals of Nutrient Management
@ToorUMD
Nutrients: Plant food; essential for crop production
P deficiency in Corn
N deficiency in Corn
K deficiency in Corn
Images from Better Crops (1997), Vol. 81. No. 3
Nitrogen: NPhosphorus: PPotassium: K
What is Nutrient Cycling: Use, movement, and recycling of nutrients
Image Credit: USGS
Carbon Cycle: Plants use (photosynthesis) carbon
dioxide (CO2) to grow. When plants decompose, CO2 is returned to atmosphere via respiration.
Nitrogen
Most complicated & fascinating Many reactions mediated by soil organisms
Wonderful oxidation and reduction reactions
N has gaseous forms
Atmosphere contains 78% N gas
Hu
man
s (b
illio
ns)
Hab
er-B
osc
h (
Tera
gram
of
N)
1 Tera Gram = 1 billion kg or 2.54 billion pounds
Image Credit: Galloway and Cowling (2002). Ambio.
Nitrogen Cycle
Inputs:
Crop & animal residues
Biosolids
Compost
Fertilizers
N fixation
Nitrogen Cycle
N Fixation Mechanisms
Natural fixation
• Atmospheric additions
– electrical discharge of lightning
• Biological processes
– symbiotic – for example between Rhizobiumbacteria and leguminous plants
– non-symbiotic – carried out by free living bacteria and blue-green algae
N2 Gas
Photo credits: Harold Evans, OSU
Soybean Nodules
Biological N Fixation
Calculating Legume Credits
Crop lbs N/Ac
Perennial Crops
Alfalfa 100 to 150
Red Clover 40
Winter Annual Crops
Hairy Vetch 75 to 150
Crimson Clover 50 to 100
Summer Annual Crops
Lespedeza 20
Soybeans 15 to 40
Photo credit: Ray Weil
Synthetic or industrial processes
Industrial fixation – for fertilizer manufacturing
Haber-Bosch process: N2 + 3H2 2NH3 (g)
High temperature fixation – internal combustion engines
N Fixation Mechanisms
Transformations of Organic N
NH4+
NO3-
NO2-
2-5% of total soil N
ProteinsAmino sugarsAmino acids
Mineralization (a transformation)
Conversion of organic N to inorganic N,
ammonium (NH4+)
Mediated by bacteria and fungi
Immobilization (a transformation)
Conversion of inorganic N (NH4+ & NO3
-) to organic N Soil organisms assimilate nutrients into biomass
Soil organisms are extremely numerous and very well distributed in the soil Outcompete plants for available nutrients under
many circumstances
Nitrification (a transformation)
Biological transformation of ammonium (NH4
+) to nitrate (NO3- )
Aerobic conditions and moderate pH suppressed below pH 5.5
Soil bacteria Nitrosomonas and Nitrobacter carry out nitrification
Nitrification: A Two-Step Process
Nitrosomonas
2 NH4+ + 3 O2 2 NO2
- + 2 H2O + 4 H+ + eAmmonium Nitrite Hydrogen
Nitrobacter
2 NO2- + O2 2 NO3
- + e
Nitrite Nitrate
Soil N Cycle: A Biological Phenomenon
Influenced by: pH: most bacteria suppressed at low pH
Temperature: is the key
Moisture: dictates oxidation or reduction
oxygen status (aeration)
Effect of Temperature on N Cycling:
Water freezes
“Biological” zero
Optimum
for
nitrification
Optimum
for
mineralization
Most
microbes
killed
Optimum for growth of corn, cotton, potatoes
Effect of Moisture & Oxygen Status on N Cycling:
Fate of N in Organic Additions
C:N ratio is the amount of C relative to the amount of N in a given material
A high C:N ratio (>25:1) N immobilized
A low C:N ratio (<20:1) N mineralized
a Cornell On-Farm Composting Handbook, Rynk et al, 1992b The Nature and Properties of Soils, Brady and Weil, 1999
Changes in NO3- levels when organic additions have wide C/N
Adapted from F.J. Stevenson, 1986
Managing C:N Ratio of Inputs
Manage cover crops Incorporate cover crops while in vegetative
state
Leave mature cover crops on surface
Monitor soil N and plant growth when incorporating straw, sawdust, and other high C:N materials
Plant-available N in soil solution
Ammonium (NH4+)
Nitrate (NO3-)
Small organic molecules present in dissolved organic N (DON) pool
Days/wks
Weeks/months
Years
Decades
Nitrate leaching
(J.J. Meisinger, USDA)
3. Denitrification:
waterlogged soils
1. Volatilization:
hot, dry weather
2. Erosion/runoff:
slopes; heavy rain
5. Leaching:
soil texture; rain amount
Losses:
4. Crop uptake
1. Leaching (a liquid loss)
Primarily as Nitrate (NO3-)
Moves freely in soil profile• Transported by drainage water, especially important in
sandy soils
can lead to pollution of groundwater
An economic loss with environmental consequences
Nitrate leaching
Minimal under natural vegetation (forests)
Greater under modern row-crop productions
A risk if N management is sub-optimal
Reasons for Excessive NO3- Leaching
Inefficient N management
Heavy one-time applications
Improper timing
Over-application of manure/sludge
Enhanced by periods of heavy rainfall
Enhancing Synchrony: Minimize Vulnerable Nitrogen
If the N is not yet applied, it can not be lost
Importance of split applications (Penn State Agronomy 12)
2. Ammonia Volatilization (a gaseous loss)
Loss of ammonia-N to the atmosphere
Ammonium in the presence of hydroxyl (OH-) can produce ammonia gas
NH4+ + OH-
H2O + NH3
Affects all surface-applied N sources−Urea, ammonium nitrate, manure
Enhanced by warm, dry atmospheric conditions
Diurnal variations
(Pote & Meisinger, 2014. J. Soil & Water Cons.)
Managing Ammonia Losses
Know where and when ammonia loss occursFirst day of application
Sunny, warm, low humidity, breezy conditions
Incorporation is required under many circumstances in Maryland
Spread and incorporate manures in the early morning or evening (when dew still present)
3. Denitrification (a gaseous loss)
NO3- N2O N2
nitrate ions nitrous oxide gas dinitrogen gas
Biological reduction of nitrate to N2 gas
NO3- transformed to gaseous compounds
Favored by saturation of the soil (anaerobic
conditions)
A Visual on Denitrification in Field
Photo credit: www. Agleader.com
Principles of N Management
Maintain soil pH appropriate for crop
Reduce runoff/erosion losses
Apply N fertilizers and manure when plants need it, where they need it
Timely incorporation of manures and sewage sludge when practical
Use cover crops to scavenge residual N
Practice Question #1
In which form is nitrogen most likely to be lost in the greatest quantity from soils in Maryland?
a) dinitrogen gas (N2)
b) nitrate (NO3- )
c) ammonium (NH4+)
d) organic N
Phosphorus (P) Cycle
Simpler cycle than N No gaseous
forms
Soluble P can be “fixed” to less available forms
Image Credit: Jaisi and Blake (2014). Advances in Agronomy
Transformation of Organic P
P mineralization and immobilization
occur simultaneously in the soil
ORGANIC PHOSPHORUS
POOL
INORGANIC PHOSPHORUS
POOL
HPO4-2
H2PO4-
Plant-available P
Orthophosphate (water-soluble phosphate) H2PO4
- at pH 5 to 7.2 HPO4
2- at pH > 7.2
Phosphate moves slowly in soil by diffusion
Image Credits: Utah State and University of Minnesota
P Fixation (a transformation)
A set of processes through which P is converted to less available formsPrecipitation
Adsorption
P fixation
Adsorption or Sorption
In acid soils, P is adsorbed to surfaces of Al/Fe oxides and clay minerals
In neutral and calcareous soils, P is adsorbed to surfaces of CaCO3 and clay minerals
P Fixation
Precipitation as secondary P compounds In acid soils, P combines with
iron (Fe) and aluminum (Al) to form insoluble compounds
In neutral and calcareous soils, P combines with (Ca) to form insoluble compounds
N.C. Brady,
1974
Mn
Availability of Fixed P
P relatively available when first fixed dissolution from newly formed minerals
desorption from sorption sites
Availability decreases as time passes
Occluded P
‘Sorbed P’ tends to become ‘occluded P’ as time passes
Sorbed P covered by coatings of iron, aluminum, or manganese oxides
Unavailable
Summary of different P pools in soils
Image Credit: Frossard et al. (2011).
(tiles)
(ditches)
Phosphate leaching
1. Eroded and runoff P:
slopes; heavy rain
3. Leaching losses:
tile drains; ditches, coarse textured soils; high P fertilization
P Loss Pathways:
2. Crop uptake
Principles of P Management
Maintain soil pH for desired crop
Apply P fertilizers when needed, where most efficiently utilized
Band starter fertilizer
When practical, incorporate manure
Utilize practices that reduce soil erosion and runoff
Practice Question #2
What is the optimum pH range for maximizing plant-available P in soils?
a) 5.0-5.5
b) 5.5-6.8
c) 6.5-7.7
d) >7.5
Potassium (K) Cycle
Simpler cycle than N no oxidation and reduction
no gaseous forms
Soluble K can be “fixed” to less available forms in some soils different mechanism than P
minimal water quality issues
Maryland Cooperative Extension, 2000
SourcesLosses
PLANT RESIDUES
Plant-available K
K+ dissolved in soil solution
Exchangeable K+
Moves primarily by diffusion along moist soil pores
Soil solution K
Only 0.1 – 0.2% of
total K in soils
Readily available for
plant uptake
Exchangeable K
K+ at exchange sites on soil colloids in dynamic equilibrium
with K+ in soil solution replenishes the soil
solution
Readily available for plant uptakeUsually less than 1% of
total K in soils
Fixed K
Fixed as K+
trapped in interlayers of clay minerals
Non-exchangeable
Minimally available by weathering
About 1-10% of total K in soil
N.C. Brady, 1974
Mineral (structural) K
K is a structural component of primary minerals such as feldspars and micas
90 – 98% of total K in soil
Relatively unavailable
K Loss Pathways
Leaching coarse soils/high
rainfall
Erosion
Crop removal luxury
consumption
N.C. Brady, 1974
Luxury consumption of potassium by plants. If excess amounts of potash fertilizers are applied to soil, plants will absorb potassium in quantities exceeding that required for optimum yields. This may be wasteful if crops are completely removed from the soil.
Principles of K Management
Maintain soil pH for desired crop
Utilize practices that reduce soil erosion
Split application
reduce losses to luxury consumption
Practice Question #3
Potassium is lost from the soils by:
a) Microbial transformation to gaseous K+
b) Leaching through clayey, fine-textured soils
c) Luxury consumption by plants
Summary: Nutrient Cycling in Soils