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Denitrification, nitrous oxide emissions and the EPA Amitava Chatterjee Soil Science, NDSU

Denitrification, nitrous oxide emissions and the EPA denitrification 3. Nitrification 4. Nitrate ammonification NH 3 NH 2OH NO 2-NO N 2O N 2 N 2O NO 3-NO 2-NH 4 + N 2O NO N 2O N 2

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Page 1: Denitrification, nitrous oxide emissions and the EPA denitrification 3. Nitrification 4. Nitrate ammonification NH 3 NH 2OH NO 2-NO N 2O N 2 N 2O NO 3-NO 2-NH 4 + N 2O NO N 2O N 2

Denitrification, nitrous oxide emissions and the EPA

Amitava ChatterjeeSoil Science, NDSU

Page 2: Denitrification, nitrous oxide emissions and the EPA denitrification 3. Nitrification 4. Nitrate ammonification NH 3 NH 2OH NO 2-NO N 2O N 2 N 2O NO 3-NO 2-NH 4 + N 2O NO N 2O N 2

Greenhouse effect

Page 3: Denitrification, nitrous oxide emissions and the EPA denitrification 3. Nitrification 4. Nitrate ammonification NH 3 NH 2OH NO 2-NO N 2O N 2 N 2O NO 3-NO 2-NH 4 + N 2O NO N 2O N 2

Nitrous oxide (N2O) & climate change

Stratosphere

Troposphere

N2O +infrared      Climate Chage

Source: Wuebbles 2009

N2O ‐> NOX ‐ > Ozone effect

Page 4: Denitrification, nitrous oxide emissions and the EPA denitrification 3. Nitrification 4. Nitrate ammonification NH 3 NH 2OH NO 2-NO N 2O N 2 N 2O NO 3-NO 2-NH 4 + N 2O NO N 2O N 2

Different greenhouse gases

Page 5: Denitrification, nitrous oxide emissions and the EPA denitrification 3. Nitrification 4. Nitrate ammonification NH 3 NH 2OH NO 2-NO N 2O N 2 N 2O NO 3-NO 2-NH 4 + N 2O NO N 2O N 2

U.S. GHG Emissions

Page 6: Denitrification, nitrous oxide emissions and the EPA denitrification 3. Nitrification 4. Nitrate ammonification NH 3 NH 2OH NO 2-NO N 2O N 2 N 2O NO 3-NO 2-NH 4 + N 2O NO N 2O N 2

Agriculture and nitrous oxide

Source: US EPA 2007

Page 7: Denitrification, nitrous oxide emissions and the EPA denitrification 3. Nitrification 4. Nitrate ammonification NH 3 NH 2OH NO 2-NO N 2O N 2 N 2O NO 3-NO 2-NH 4 + N 2O NO N 2O N 2

N2O emission from cropped soil

Source: USDA

Page 8: Denitrification, nitrous oxide emissions and the EPA denitrification 3. Nitrification 4. Nitrate ammonification NH 3 NH 2OH NO 2-NO N 2O N 2 N 2O NO 3-NO 2-NH 4 + N 2O NO N 2O N 2

Source: USEPA 2009

Page 9: Denitrification, nitrous oxide emissions and the EPA denitrification 3. Nitrification 4. Nitrate ammonification NH 3 NH 2OH NO 2-NO N 2O N 2 N 2O NO 3-NO 2-NH 4 + N 2O NO N 2O N 2

Microbial sources of soil N2O

Page 10: Denitrification, nitrous oxide emissions and the EPA denitrification 3. Nitrification 4. Nitrate ammonification NH 3 NH 2OH NO 2-NO N 2O N 2 N 2O NO 3-NO 2-NH 4 + N 2O NO N 2O N 2

4. Nitrate ammonification

NH3 NH2OH NO2- NO N2O N2

N2O

NO3-

NO2-

NH4+

NON2O

N2O

N2

1. Denitrification

2. Nitrifier denitrification 

3. Nitrification

Page 11: Denitrification, nitrous oxide emissions and the EPA denitrification 3. Nitrification 4. Nitrate ammonification NH 3 NH 2OH NO 2-NO N 2O N 2 N 2O NO 3-NO 2-NH 4 + N 2O NO N 2O N 2

4. Nitrate ammonification

NH3 NH2OH NO2- NO N2O N2

N2O

NO3-

NO2-

NH4+

NON2O

N2O

N2

1. Denitrification

2. Nitrifier denitrification 

3. Nitrification

Page 12: Denitrification, nitrous oxide emissions and the EPA denitrification 3. Nitrification 4. Nitrate ammonification NH 3 NH 2OH NO 2-NO N 2O N 2 N 2O NO 3-NO 2-NH 4 + N 2O NO N 2O N 2

4. Nitrate ammonification

NH3 NH2OH NO2- NO N2O N2

N2O

NO3-

NO2-

NH4+

NON2O

N2O

N2

1. Denitrification

2. Nitrifier denitrification 

3. Nitrification

Page 13: Denitrification, nitrous oxide emissions and the EPA denitrification 3. Nitrification 4. Nitrate ammonification NH 3 NH 2OH NO 2-NO N 2O N 2 N 2O NO 3-NO 2-NH 4 + N 2O NO N 2O N 2

4. Nitrate ammonification

NH3 NH2OH NO2- NO N2O N2

N2O

NO3-

NO2-

NH4+

NON2O

N2O

N2

1. Denitrification

2. Nitrifier denitrification 

3. Nitrification

Page 14: Denitrification, nitrous oxide emissions and the EPA denitrification 3. Nitrification 4. Nitrate ammonification NH 3 NH 2OH NO 2-NO N 2O N 2 N 2O NO 3-NO 2-NH 4 + N 2O NO N 2O N 2

Measuring N2O emission

• Bottom‐up ‐ soil surface gas flux and models (DAYCENT)based on soil N application 

• Top‐down ‐changes in concentration of atmospheric N2O and sink estimates

• At sufficiently large scales, the use of both approaches yield similar estimates 

• “convergence of …approaches increases confidence…rudimentary understanding of factors controlling large spatial & temporal scales.” – Del Grosso et al. (2008)

Page 15: Denitrification, nitrous oxide emissions and the EPA denitrification 3. Nitrification 4. Nitrate ammonification NH 3 NH 2OH NO 2-NO N 2O N 2 N 2O NO 3-NO 2-NH 4 + N 2O NO N 2O N 2

Measuring soil N2O emission

• Chamber-based gas flux measurementSource: http://www.ars.usda.gov/research/GRACEnet

N2O concentration in air sample is measured by Gas chromatograph with ECD detector

Page 16: Denitrification, nitrous oxide emissions and the EPA denitrification 3. Nitrification 4. Nitrate ammonification NH 3 NH 2OH NO 2-NO N 2O N 2 N 2O NO 3-NO 2-NH 4 + N 2O NO N 2O N 2

N2O emission reduction protocol (NERP)

29844/28Fertilizer N quantity

Organic N quantity N2O @ control

Page 17: Denitrification, nitrous oxide emissions and the EPA denitrification 3. Nitrification 4. Nitrate ammonification NH 3 NH 2OH NO 2-NO N 2O N 2 N 2O NO 3-NO 2-NH 4 + N 2O NO N 2O N 2

Controls of denitrifier activity

• Soil nitrogen availability

• organic matter 

• Soil oxygen concentration 

• Soil pH

• Soil temperature

Page 18: Denitrification, nitrous oxide emissions and the EPA denitrification 3. Nitrification 4. Nitrate ammonification NH 3 NH 2OH NO 2-NO N 2O N 2 N 2O NO 3-NO 2-NH 4 + N 2O NO N 2O N 2

Soil N availability & Fertilizer N

4 Factors control the soil N availability and N2O emissions during growing season

1.Quantity (Full, split)

2.N source (NH4/NO3 based, inhibitor)

3.Application time (Early spring vs. late spring)

4.Application zone/place (side‐dress/dribbled)

Page 19: Denitrification, nitrous oxide emissions and the EPA denitrification 3. Nitrification 4. Nitrate ammonification NH 3 NH 2OH NO 2-NO N 2O N 2 N 2O NO 3-NO 2-NH 4 + N 2O NO N 2O N 2

Fertilizer N quantity and N emission

Loam, Michigan, Corn Source Hoben et al. 2010

Page 20: Denitrification, nitrous oxide emissions and the EPA denitrification 3. Nitrification 4. Nitrate ammonification NH 3 NH 2OH NO 2-NO N 2O N 2 N 2O NO 3-NO 2-NH 4 + N 2O NO N 2O N 2

Source: Smith 2010

Glyndon, Wheat

Page 21: Denitrification, nitrous oxide emissions and the EPA denitrification 3. Nitrification 4. Nitrate ammonification NH 3 NH 2OH NO 2-NO N 2O N 2 N 2O NO 3-NO 2-NH 4 + N 2O NO N 2O N 2

Fertilizer N sources effect on N2O

Source: Halvorson et al. 2011

ESN_ssb= Polymercoated urea subsurface banded, Nfus = Nfusion and Agrot = AgrotainPlus

Page 22: Denitrification, nitrous oxide emissions and the EPA denitrification 3. Nitrification 4. Nitrate ammonification NH 3 NH 2OH NO 2-NO N 2O N 2 N 2O NO 3-NO 2-NH 4 + N 2O NO N 2O N 2

Fertilizer N sources-N2O loss -grain yield

Page 23: Denitrification, nitrous oxide emissions and the EPA denitrification 3. Nitrification 4. Nitrate ammonification NH 3 NH 2OH NO 2-NO N 2O N 2 N 2O NO 3-NO 2-NH 4 + N 2O NO N 2O N 2

Timing influences N2O emission

Source: Philips et al. 2009

Silt loam, Mandan, ND, Corn,April 1 vs. May 15 

Page 24: Denitrification, nitrous oxide emissions and the EPA denitrification 3. Nitrification 4. Nitrate ammonification NH 3 NH 2OH NO 2-NO N 2O N 2 N 2O NO 3-NO 2-NH 4 + N 2O NO N 2O N 2

Placement influences N2O emission

Deep placement increase the N2O emission by 26% for in clay loam soils in eastern Canada!

Source: Drury et al. 2006

Page 25: Denitrification, nitrous oxide emissions and the EPA denitrification 3. Nitrification 4. Nitrate ammonification NH 3 NH 2OH NO 2-NO N 2O N 2 N 2O NO 3-NO 2-NH 4 + N 2O NO N 2O N 2

Liu et al. 2006

50% reduction in N20 emission from change of 5 to 10 cm for both tillage practice for fine loamy corn soil, CO

Tillage and placement treatment significant at 90% sign. level

Page 26: Denitrification, nitrous oxide emissions and the EPA denitrification 3. Nitrification 4. Nitrate ammonification NH 3 NH 2OH NO 2-NO N 2O N 2 N 2O NO 3-NO 2-NH 4 + N 2O NO N 2O N 2

Fertilizer induced N2O emission reduction

Performance Level

Right Source Right Rate Right Time Right Place

Basic *NH4 based *Recommended*Apply in spring*Split*Fall (<50°F)

Bands/Injection

Intermediate

*NH4 based *Slow release*Inhibitor*Stabilized

*Soil test*landscape*soil variability

*Apply in spring*Split*Fall (<50°F) + inhibitor

Bands/Injection

Advanced

*NH4 based *Slow release*Inhibitor*Stabilized

*Digitized soil maps*grid sampling*satellite imagery*real time crop sensors*Seasonal crop monitoring

*Apply in spring*Split*Fall (<50°F) + inhibitor

Bands/Injection

Page 27: Denitrification, nitrous oxide emissions and the EPA denitrification 3. Nitrification 4. Nitrate ammonification NH 3 NH 2OH NO 2-NO N 2O N 2 N 2O NO 3-NO 2-NH 4 + N 2O NO N 2O N 2

Tillage and Soil texture control

Source: Rochette et al. 2008Crop‐ Barley and location: Quebec City, Canda

Page 28: Denitrification, nitrous oxide emissions and the EPA denitrification 3. Nitrification 4. Nitrate ammonification NH 3 NH 2OH NO 2-NO N 2O N 2 N 2O NO 3-NO 2-NH 4 + N 2O NO N 2O N 2

Precision tillage reduced N2O emission

Precision till – Nu-Till

(Ag Spectrum) utilizing

(1) Martin row cleaners,

(2) Keeton seed firmers,

(3) Martin spader and

(4) a dagger chain

Soil- Silt loam

Lafayette, InSource: Smith et al. 2011

Page 29: Denitrification, nitrous oxide emissions and the EPA denitrification 3. Nitrification 4. Nitrate ammonification NH 3 NH 2OH NO 2-NO N 2O N 2 N 2O NO 3-NO 2-NH 4 + N 2O NO N 2O N 2

Above normal precipitation triggers tile use

Page 30: Denitrification, nitrous oxide emissions and the EPA denitrification 3. Nitrification 4. Nitrate ammonification NH 3 NH 2OH NO 2-NO N 2O N 2 N 2O NO 3-NO 2-NH 4 + N 2O NO N 2O N 2

Tile facilitates stand establishment

• Warm up and dry out the soils in spring• Allows earlier field operations

• Optimum soil moisture condition• Root development

Page 31: Denitrification, nitrous oxide emissions and the EPA denitrification 3. Nitrification 4. Nitrate ammonification NH 3 NH 2OH NO 2-NO N 2O N 2 N 2O NO 3-NO 2-NH 4 + N 2O NO N 2O N 2

Soil porosity controls N2O formation

Page 32: Denitrification, nitrous oxide emissions and the EPA denitrification 3. Nitrification 4. Nitrate ammonification NH 3 NH 2OH NO 2-NO N 2O N 2 N 2O NO 3-NO 2-NH 4 + N 2O NO N 2O N 2

Tile and N2O emissions

Drainage loss (‐) of NO3‐

Plant N uptake (+)

Fertilizer N rate (±?)

N mineralization rate/availability (+)

Denitrification loss of  N2O (+?)

Page 33: Denitrification, nitrous oxide emissions and the EPA denitrification 3. Nitrification 4. Nitrate ammonification NH 3 NH 2OH NO 2-NO N 2O N 2 N 2O NO 3-NO 2-NH 4 + N 2O NO N 2O N 2

Soil management practices to reduce N2O

Page 34: Denitrification, nitrous oxide emissions and the EPA denitrification 3. Nitrification 4. Nitrate ammonification NH 3 NH 2OH NO 2-NO N 2O N 2 N 2O NO 3-NO 2-NH 4 + N 2O NO N 2O N 2

EPA’s stands on GHG emission

• The Clean Air Act of 1970 requires EPA to curb the emissions of any air pollutant

• Since its enactment,  GDP rise to 207%, 1.6 million jobs and $40 billion in exports 

• Supreme court ruled out 2007 case Massachusetts vs. EPA that GHG are chemical substance emitted into the air and are air pollutants

Page 35: Denitrification, nitrous oxide emissions and the EPA denitrification 3. Nitrification 4. Nitrate ammonification NH 3 NH 2OH NO 2-NO N 2O N 2 N 2O NO 3-NO 2-NH 4 + N 2O NO N 2O N 2

EPA Taking action under the law

• EPA issued “endangerment finding in 2009: GHG, a threat to public health, welfare and climate.

• First phase, safeguard’s for power plants and oil refineries enacted on January 2, 2011

• Clean Car Agreement: 35.5 mpg by 2016

• New EPA standards were “ a victory for car companies…pay less at the pump; for our security, and for the environment as we reduce pollution” – President Barack Obama

Page 36: Denitrification, nitrous oxide emissions and the EPA denitrification 3. Nitrification 4. Nitrate ammonification NH 3 NH 2OH NO 2-NO N 2O N 2 N 2O NO 3-NO 2-NH 4 + N 2O NO N 2O N 2

EPA’s Tailoring Rule

• July 1, 2011: emit>100,000 tons yr‐1 required operating permits to account for GHG

• By June 30, 2013:550 sources need to obtain operating permits

• 900 new facilities per year will trigger New Source Review permitting requirements 

• emit >50,000 tons yr‐1 will not be subject to permitting requirements until at least April, 2016

• Every State (except Texas) says they are ready to enact EPA safeguards

Page 37: Denitrification, nitrous oxide emissions and the EPA denitrification 3. Nitrification 4. Nitrate ammonification NH 3 NH 2OH NO 2-NO N 2O N 2 N 2O NO 3-NO 2-NH 4 + N 2O NO N 2O N 2