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Ammonia from space: how good are current measurements and what could future instruments tell us Karen Cady-Pereira 1 , Mark Shephard 2 , Daven Henze 3 , Juliet Zhu 3 , Jonathan Wrotny 1 , Jesse Bash 5 , Armin Wisthaler 6 , Kang Sun 7 , Amy Jo Scarino 4 , Ming Luo 8 1. Atmospheric and Environmental Research (AER) 2. Environment Canada 3. University of Colorado 4. NASA Langley 5. Environmental Protection Agency (EPA) 6. University of Innsbruck 7. Princeton University 8. NASA Jet Propulsion Laboratory (JPL)

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Page 1: Ammonia from space: how good are current measurements and ...acmg.seas.harvard.edu/presentations/aqast/jun2014/Day2_PM/2-tes_cris... · Ammonia from space: how good are current measurements

Ammonia from space: how good are current measurements and what could future

instruments tell us

Karen Cady-Pereira1, Mark Shephard2, Daven Henze3, Juliet Zhu3, Jonathan Wrotny1, Jesse Bash5, Armin Wisthaler6,

Kang Sun7, Amy Jo Scarino4, Ming Luo8

1. Atmospheric and Environmental Research (AER) 2. Environment Canada 3. University of Colorado

4. NASA Langley 5. Environmental Protection Agency (EPA)

6. University of Innsbruck 7. Princeton University

8. NASA Jet Propulsion Laboratory (JPL)

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NH3 Sources

Bi-directional Flux

AGRICULTURE •  Animal waste

(temperature dependent) •  Fertilizer application

Industry •  Fertilizer •  Coal Mining •  Power generation

Biomass burning

Automobiles (catalytic converters) •  Large urban centers

•  50% of NH3 in LA area

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NH3 in the atmosphere

Long-range import

Long-range export

PM2.5 Particles

NH3 + HNO3NH4NO3 2 NH3 + H2SO4(NH4)2SO4

•  Increase incidence of cardiovascular and respiratory diseases

•  Increase number of CCN #•  Affect cloud radiative properties #•  Climate change

!"#!$#$"#$$#%"#%$#&"#&$#'"#'$#

("""# ("("# ("!"# ("%"# ("'"# ()""#

!"#$%&'()#

*+,-.+#$%&#/01221,32#

*+,-.#/#012#(3%# +4541,+#/#012#!3$#

,*+#/#012#%3"# +.66,-.#/#012#'3$#

SO2, NOX decreasing but NH3 forecast to increase

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Monitoring NH3 is difficult

NH3 is highly reactive highly variable in space and time

•  Data from an Open path Quantum Cascade Laser (QCL) on a moving platform in the San Joaquin Valley during DISCOVER-AQ 2013.

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NH3 from aircraft DISCOVER-AQ campaign in January 2013 in the San Joaquin Valley

Aircraft campaigns provide high quality data, but are not feasible for long term monitoring over large areas

Janu

ary

30

PBL from airborne HSRL

backscatter

NH3 from PTR and Picarro

Janu

ary

21

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TES and CrIS instruments

Two TES observation modes: •  Global Surveys: 26 hours

long, return to starting point every 16 days

•  Special Observations: higher sampling density over shorter tracks

TES CrIS Satellite AURA NPP Launch July 2004 October 2011 Resolution 0.06 cm-1 0.625 cm-1

Footprint 5x8 km rectangle 14 km diameter circle Repeat cycle Once every 16 days Daily Equatorial crossing 1:30 am and 1:30 pm 1:30 am and 1:30 pm Noise in NH3 window 0.09 – 0.12 K 0.03 – 0.06 K

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NH3 from TES and CrIS Simulated spectra and NH3 signal

18 ppbv at surface

•  Detectability is ~ 1 ppbv under ideal conditions

•  But thermal contrast also plays a role

TES

CrIS

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NH3 from TES and CrIS

•  Both instruments most sensitive to NH3 between 950 and 600 mbar •  TES is more sensitive to amounts lower in the atmosphere •  1 piece of information or less: DOFS<1.0 •  Collapse all information to a single point: RVMR

•  Easier to compare with in situ measurements, models and other instruments

TES CrIS

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Global NH3 results TES NH3 from GS: 2004-2011

•  Large increase from NH winter to summer

•  Hotspot over

India •  Biomass burning

signal over South America and Africa

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Eastern China: 2007-2009

Surface NH3

Seasonal means from TES

TES NH3 TES transect path

Bei

jing Beijing

Beijing Shangdianzi

Meng et al., ACP, 2011

Shangdianzi

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TES and aircraft NH3 from DAQ January 30: aircraft tracks under TES transect

•  P3B aircraft @ 300 m •  TES maximum sensitivity between 1 and 2 km

Total Column RVMR

TES and aircraft NH3 are well correlated

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Surface and satellite NH3 in DISCOVER-AQ 2013

•  Satellite and QCL NH3 measured in January 2013 are spatially well correlated

•  QCL almost directly under TES transect in the San Joaquin Valley on January 28, 2013

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Measuring NH3 daily variations •  North Carolina in situ data •  CMAQ model with different temporal emission profiles

•  Static profile •  Dynamic profile

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NH3 from a geostationary platform

CMAQ vs Simulated Retrievals •  TES-like instument •  Geostationary platform •  Provides data every three hours •  CMAQ profiles over California for

a warm July day •  Difference in CMAQ NH3 matches

difference in retrieved NH3

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Final comments

•  Limitations •  TES and CrIS are sensitive to only higher amounts (> 1.0 ppbv) of NH3 •  Require some thermal contrast to detect NH3 •  Clouds reduce amount of useful data

•  TES and CrIS data •  Show seasonal and spatial variability consistent with in situ

measurements •  Have greater temporal and spatial coverage than aircraft campaigns or

surface networks

•  TES-like instrument on a geostationary platform could provide information on daily variability

•  TES NH3 are operational data available at:

•  http://avdc.gsfc.nasa.gov/index.php?site=635564035&id=10&go=list&path=/NH3

•  netcdf files with all NH3 retrievals for each month since September 2004

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Acknowledgements •  Markus Mueller and Tomas Mikoviny from the PTR instrument team •  PICARRO instrument team •  TES team at JPL •  Jesse Bash and Rober Pinder from the EPA •  Research was supported by

•  the Jet Propulsion Laboratory, California Institute of Technology under contract to the National Aeronautics and Space Administration (NASA).

•  NOAA Climate Program Office (CPO) Grant number NA130AR4310060 •  CU support from NASA grant NNX10AG63G and EPA-STAR RD83455901

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Better emissions with TES NH3

April

July

October April

July

October

GC

(p

pb

) I

nit

ial

GC

(p

pb

) O

pti

miz

ed

AMoN obs (ppb) 0 1 2 3 4 5 6

01

23

45

6

Observation NH3, (ppb)

GE

OS!

Ch

em

, N

H3

, (p

pb

)

October

y =

0.494

+

0.564

x

0 1 2 3 4 5 6

01

23

45

6

Observation NH3, (ppb)

GE

OS!

Ch

em

, O

ptim

ize

d,

NH

3,

(pp

b)

October

y =

0.455

+

0.999

x

0 1 2 3 4 5 6

01

23

45

6

Observation NH3, (ppb)

GE

OS!

Chem

, N

H3, (p

pb)

October

y =

0.494

+

0.564

x

0 1 2 3 4 5 6

01

23

45

6

Observation NH3, (ppb)

GE

OS!

Chem

, O

ptim

ized, N

H3, (p

pb)

October

y =

0.455

+

0.999

x

R2=0.545 RMSE=0.952

NMB=-0.138

R2=0.693 RMSE=0.862

NMB=0.166

0 2 4 6 8 10 12

02

46

81

01

2Observation NH3, (ppb)

GE

OS!

Ch

em

, N

H3

, (p

pb

)

July

y =

1.5

+

0.51

x

0 2 4 6 8 10 12

02

46

81

01

2

Observation NH3, (ppb)

GE

OS!

Ch

em

, O

ptim

ize

d,

NH

3,

(pp

b)

July

y =

2.22

+

1

x

0 2 4 6 8 10 12

02

46

81

01

2

Observation NH3, (ppb)G

EO

S!

Ch

em

, N

H3

, (p

pb

)

July

y =

1.5

+

0.51

x

0 2 4 6 8 10 12

02

46

81

01

2

Observation NH3, (ppb)

GE

OS!

Ch

em

, O

ptim

ize

d,

NH

3,

(pp

b)

July

y =

2.22

+

1

x

R2=0.281 RMSE=1.990

NMB=-0.045

R2=0.365 RMSE=3.534

NMB=0.659

0 2 4 6 8 10

02

46

81

0

Observation NH3, (ppb)

GE

OS!

Ch

em

, N

H3

, (p

pb

)

April

y =

0.215

+

0.225

x

0 2 4 6 8 10

02

46

81

0

Observation NH3, (ppb)

GE

OS!

Ch

em

, O

ptim

ize

d,

NH

3,

(pp

b)

April

y =

!0.189

+

1.02

x

0 2 4 6 8 10

02

46

810

Observation NH3, (ppb)

GE

OS!

Chem

, N

H3, (p

pb)

April

y =

0.215

+

0.225

x

0 2 4 6 8 10

02

46

810

Observation NH3, (ppb)

GE

OS!

Chem

, O

ptim

ized, N

H3, (p

pb)

April

y =

!0.189

+

1.02

x

R2=0.497 RMSE=1.834

NMB=-0.069

R2=0.406 RMSE=2.107

NMB=-0.678

Largest changes western US and Mexico

•  Used GEOS-Chem adjoint with TES NH3 profiles, averaging kernels and error covariances to optimize model

•  Optimized GC shows better agreement with AMoN network measurements

Zhu et al., 2013, JGR

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South Asia: July-August 2007

Indus River Valley High NH3 north of New Delhi and in the northern Indus valley

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TES NH3 and CO Monthly NH3 RVMR

July 2010

Aug 2010

Sept 2010

Monthly CO at 681 hPa

NH3 from TES V005 operational product

Biomass burning in South America is evident in both CO and NH3 maps

High NH3 values over northern India

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CalNex 2010: California spring CalNex: Campaign focused on air quality and climate change

Aircraft and surface measurements and TES transects

Central Valley, southern California basin, Pacific Ocean

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CALNEX: TES vs Aircraft TES May 14 transect @13:15 local

Partial P3 May 12 track (flying at ~ 300 AGL @ 17:30 local)

NH3 measurements from TES and aircraft are well correlated

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Day vs Night: TES DAY • Lower NH3 values • Sensitivity peaks between 900 and 750 mbar

NIGHT • Greater range of NH3 values

• More high values • Sensitivity peaks between surface and 900 mbar

Collapse of boundary layer Pooling of NH3

CMAQ simulated NH3 profile

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And now …

NH3

Shephard et al.[2011]

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TES NH3 Validation

North Carolina Intense livestock

farming (hogs, chickens, turkeys)

• EPA CAMNet NH3 monitoring network

• TES high spatial density observations (transects)

• Feb – Dec 2009

• Allows detection of spatial variability and seasonal trends CHALLENGE

• TES: instantaneous profile over 5x8 km

• CAMNet: two week average at a surface point

•  Cloudy summers!

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Seasonal and spatial variability

NH3 vs time NH3 vs source concentration

TES and surface measurements are qualitatively well correlated

Pinder et al., GRL, 2011