Denitrification, nitrous oxide emissions and the EPA denitrification 3. Nitrification 4. Nitrate...

37
Denitrification, nitrous oxide emissions and the EPA Amitava Chatterjee Soil Science, NDSU

Transcript of Denitrification, nitrous oxide emissions and the EPA denitrification 3. Nitrification 4. Nitrate...

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