Measurements of pollutants and their spatial distributions over the Los Angeles Basin

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Measurements of pollutants and their spatial distributions over the Los Angeles Basin Ross Cheung 1,2 , Olga Pikelnaya 1,2 , Catalina Tsai 1 , Jochen Stutz 1,2 , Dejian Fu 2,3 , and Stanley P. Sander 2,3 5/16/2011 1 Department of Atmospheric and Oceanic Sciences, UCLA 2 Joint Institute for Regional Earth System Science and Engineering, UCLA 3 NASA Jet Propulsion Laboratory, Caltech

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Measurements of pollutants and their spatial distributions over the Los Angeles Basin. Ross Cheung 1,2 , Olga Pikelnaya 1,2 , Catalina Tsai 1 , Jochen Stutz 1,2 , Dejian Fu 2,3 , and Stanley P. Sander 2,3 5/16/2011. 1 Department of Atmospheric and Oceanic Sciences, UCLA - PowerPoint PPT Presentation

Transcript of Measurements of pollutants and their spatial distributions over the Los Angeles Basin

Page 1: Measurements of pollutants and their spatial distributions over the Los Angeles Basin

Measurements of pollutants and their spatial distributions over the

Los Angeles BasinRoss Cheung1,2, Olga Pikelnaya1,2, Catalina

Tsai1, Jochen Stutz1,2, Dejian Fu2,3, and Stanley P. Sander2,3

5/16/2011

1Department of Atmospheric and Oceanic Sciences, UCLA2Joint Institute for Regional Earth System Science and Engineering, UCLA3NASA Jet Propulsion Laboratory, Caltech

Page 2: Measurements of pollutants and their spatial distributions over the Los Angeles Basin

Motivation

• Observation of spatial and temporal distribution of trace gases in the LA Basin

• Study pollution transport of criteria pollutants in the LA basin

• Provide data for assimilation into air quality models

• Use inverse modeling to validate emissions inventories

Page 3: Measurements of pollutants and their spatial distributions over the Los Angeles Basin

California Laboratory for Atmospheric Remote Sensing (CLARS)Mt. Wilson, CA, in San Gabriel Mountains, with a near full view of the LA basin

Longitude: 34° 13' 28'' NLatitude: 118° 3' 25'' WAltitude: 1706 meters/5597 feet ASLMost of the time above the boundary layer

• UCLA Multi-AXis Differential Optical Absorption Spectrometer (MAX-DOAS)• JPL Near-IR FTS (Fourier Transform Spectrometer) – see talk by Dejian Fu, Tuesday May 17th, 9:10 am

Measurements started in mid-May 2010 and are still continuing

CLARS observatory at Mt. Wilson

Page 4: Measurements of pollutants and their spatial distributions over the Los Angeles Basin

Viewing Geometry

Azimuth Angles

147.4°, 160°, 172.5°, 182°, 240.6°

Elevation Angles

-10°, -8°, -6°, -4°, -2°, 0°, 3°, 6°, 90°

Continuous scans in elevation and azimuth. Cycle length: 60-80 minutes

147.4 °

240.6 °

182°

Page 5: Measurements of pollutants and their spatial distributions over the Los Angeles Basin

UCLA MAX-DOAS

Scattered sunlight from the sky (positive a)

Scattered sunlight from the basin (negative a)

Spectralon

Wavelength interval (nm)

Trace gases measured

316.4 – 448.2 NO2, HCHO, Glyoxal, O4

463.5 – 591.9 NO2, O4

MAX-DOAS can point in virtually any direction, measures scattered sunlight from sunrise to sunset

Field of view: 0.4°

Acquisition time: ~1 minute

Page 6: Measurements of pollutants and their spatial distributions over the Los Angeles Basin

αα

MAX-DOAS at Mt. Wilson

Viewing geometry

Scattering both in atmosphere and off ground

MAX-DOAS measures path-integrated concentration along path s: Slant Column Density (SCD) :

Differential slant column densities (DSCD) obtained by removing zenith SCD:

O4 vertical profile zenithaxisoff SCDSCDDSCD

L

dsscSCD0

Page 7: Measurements of pollutants and their spatial distributions over the Los Angeles Basin

αα

MAX-DOAS at Mt. Wilson

Viewing geometry

Scattering both in atmosphere and off ground

MAX-DOAS measures path-integrated concentration along path s: Slant Column Density (SCD) :

Differential slant column densities (DSCD) obtained by removing zenith SCD:

O4 gives important information about atmospheric path length

O4 vertical profile zenithaxisoff SCDSCDDSCD

L

dsscSCD0

Page 8: Measurements of pollutants and their spatial distributions over the Los Angeles Basin

-0.06-0.04-0.02 NO2 reference

Retrieved NO2

500 520 540 560 580 600-0.025

-0.02

-0.015

-0.01

-0.005

0

wavelength (nm)

log[

Inte

nsity

]

NO2 reference

NO2 plus residual

460 470 480 490 500 510-0.035

-0.03

-0.025

-0.02

-0.015

-0.01

-0.005

wavelength (nm)

log[

Inte

nsity

]

NO2 reference

NO2 plus residual

420 430 440 450-0.05

-0.045

-0.04

-0.035

-0.03

-0.025

wavelength (nm)

log[

Inte

nsity

]

NO2 reference

NO2 plus residual

320 330 340 350 360 370-0.03

-0.025

-0.02

-0.015

-0.01

wavelength (nm)

log[

Inte

nsity

]

NO2 reference

NO2 plus residual

All figures are in the same viewing direction

Path length is wavelength dependent due to scattering effects

Wavelength Dependence of DSCDDSCD: (5.3 ± 0.3) x 1016

DSCD: (7.4 ± 0.2) x 1016

DSCD: (7.3 ±0.1) x 1016

DSCD: (10 ± 0.2) x 1016

323-362 nm

419-447 nm

464-507 nm

520-588 nm

Page 9: Measurements of pollutants and their spatial distributions over the Los Angeles Basin

0

5

10

x 1016

12:00 15:00 18:00 21:00 00:00 03:000

2

4

6

8x 1043

Time (UTC), 5/30/2010

323-362 nm419-447 nm464-507 nm520-588 nm

350-390 nm464-507 nm520-588 nm

Scattering Effects

Obtaining NO2 and O4 DSCDs at different wavelengths adds valuable information on radiative transfer

DSCDs increase with increasing path lengths

Elevation -4o

Azimuth 182o

NO

2 DSC

Dm

olec

/cm

2

O4 D

SCD

mol

ec2 /

cm5

Page 10: Measurements of pollutants and their spatial distributions over the Los Angeles Basin

0

5

10

x 1016

12:00 15:00 18:00 21:00 00:00 03:000

2

4

6

8x 1043

Time (UTC), 5/30/2010

323-362 nm419-447 nm464-507 nm520-588 nm

350-390 nm464-507 nm520-588 nm

Scattering Effects

Obtaining NO2 and O4 DSCDs at different wavelengths adds valuable information on radiative transfer

NO2 DSCDs increase close to Mt. Wilson

Elevation -4o

Azimuth 182o

NO

2 DSC

Dm

olec

/cm

2

O4 D

SCD

mol

ec2 /

cm5

No strong RT effects seen in O4

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0

2

4

6

8

10x 10

17

NO

2 DS

CD

, mol

ec/c

m2

Azimuth 147º Azimuth 160º Azimuth 172º Azimuth 182º

Azimuth 241º

elevation 6ºelevation 3ºelevation 0ºelevation -2ºelevation -4ºelevation -6ºelevation -8ºelevation -10º0

5

10

15x 10

16

HC

HO

DS

CD

, mol

ec/c

m2

12:00 00:000

5

10

15x 10

43

O4 D

SC

D, m

olec

2 /cm

5

12:00 00:00 12:00 00:00Time (UTC) for May 31st, 2010

12:00 00:00 12:00 00:00

40 viewing directions in 2 wavelengths, every 60-80min

Overview of May 31 data

Looking westward (towards Santa Monica)

Looking eastwards (towards Baldwin Park and West Covina)

NO

2 DSC

Dm

olec

/cm

2

HCHO

DSC

Dm

olec

/cm

2O

4 DSC

Dm

olec

2 /cm

5

Az 160oAz 147o Az 172o Az 182o Az 241o

Page 12: Measurements of pollutants and their spatial distributions over the Los Angeles Basin

0

5

10 x 1017

0

5

10 x 1016

15:00 18:00 21:00 00:000

5

10

x 1043

Time (UTC) for May 31st, 2010

elevation 6ºelevation 3ºelevation 0ºelevation -2ºelevation -4ºelevation -6ºelevation -8ºelevation -10º

HCHO

DSC

Dm

olec

/cm

2

DSCDs at 172° Azimuth

O4 surprisingly constant throughout this day

Increase in NO2 later in day – transport of pollution

NO2 above boundary layer relatively constant

NO

2 DSC

Dm

olec

/cm

2O

4 DSC

Dm

olec

2 /cm

5

Page 13: Measurements of pollutants and their spatial distributions over the Los Angeles Basin

0

5

10 x 1017

0

5

10 x 1016

15:00 18:00 21:00 00:000

5

10

x 1043

Time (UTC) for May 31st, 2010

elevation 6ºelevation 3ºelevation 0ºelevation -2ºelevation -4ºelevation -6ºelevation -8ºelevation -10º

HCHO

DSC

Dm

olec

/cm

2

DSCDs at 172° AzimuthN

O2 D

SCD

mol

ec/c

m2

O4 D

SCD

mol

ec2 /

cm5

O4 greater in horizontal elevation angles

NO2 and HCHO greatest when looking into boundary layer

Page 14: Measurements of pollutants and their spatial distributions over the Los Angeles Basin

Downwards looking Upwards looking

Overview of May 31 data by elevation angle

0

5

10x 10

17

0

5

10

15x 10

16

12:00 00:000

5

10

15 x 1043

12:00 00:00 12:00 00:00Time (UTC) for May 31st, 2010

12:00 00:00 12:00 00:00

Azimuth 147ºAzimuth 160ºAzimuth 172ºAzimuth 182ºAzimuth 241º

NO

2 DSC

Dm

olec

/cm

2

HCHO

DSC

Dm

olec

/cm

2O

4 DSC

Dm

olec

2 /cm

5

Elev. -6o Elev. -4o Elev. -2o Elev. 0o Elev. 3o

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0

5

10x 10

17

0

5

10

15x 10

16

12:00 00:000

5

10

15 x 1043

12:00 00:00 12:00 00:00Time (UTC) for May 31st, 2010

12:00 00:00 12:00 00:00

Azimuth 147ºAzimuth 160ºAzimuth 172ºAzimuth 182ºAzimuth 241º

NO

2 DSC

Dm

olec

/cm

2

HCHO

DSC

Dm

olec

/cm

2O

4 DSC

Dm

olec

2 /cm

5

Elev. -6o Elev. -4o Elev. -2o Elev. 0o Elev. 3o

Overview of May 31 data by elevation angle

O4 values increase with elevation angle – increasing path length

241° Azimuth behaves differently from others

Page 16: Measurements of pollutants and their spatial distributions over the Los Angeles Basin

0

5

10x 10

17

0

5

10

15x 10

16

12:00 00:000

5

10

15 x 1043

12:00 00:00 12:00 00:00Time (UTC) for May 31st, 2010

12:00 00:00 12:00 00:00

Azimuth 147ºAzimuth 160ºAzimuth 172ºAzimuth 182ºAzimuth 241º

NO

2 DSC

Dm

olec

/cm

2

HCHO

DSC

Dm

olec

/cm

2O

4 DSC

Dm

olec

2 /cm

5

Elev. -6o Elev. -4o Elev. -2o Elev. 0o Elev. 3o

Clear vertical gradient in NO2 and HCHO DSCDs

Diurnal variability in NO2, HCHO

Overview of May 31 data by elevation angle

Page 17: Measurements of pollutants and their spatial distributions over the Los Angeles Basin

Quantifying the Effect of Radiative Transfer

Weighing factor for each atmospheric layer’s contribution to absorption and scattering at each elevation angle: Differential Box Air-Mass Factor (DBAMF)

m

jjjiji ChDBAMFDSCD

1

][)(a

DBAMFs calculated with TRACY II Monte- Carlo Radiative Transfer Model

0

1

2

3

4

5

0 10 20 30 40 50

Differential Box Air Mass Factor (DBAMF)

Alti

tude

(km

)

Elevation 6o

Elevation 3o

Elevation 0o

Elevation -2o

Elevation -4o

Elevation -6o

Elevation -8o

Elevation -10o

Weight moves lower in atmosphere with decreasing elevation angle

DBAMFs for May 31st

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Quantifying the Effect of Radiative Transfer

Weighing factor for each atmospheric layer’s contribution to absorption and scattering at each elevation angle: Differential Box Air-Mass Factor (DBAMF)

m

jjjiji ChDBAMFDSCD

1

][)(a

DBAMFs calculated with TRACY II Monte- Carlo Radiative Transfer Model

0

1

2

3

4

5

0 10 20 30 40 50

Differential Box Air Mass Factor (DBAMF)

Alti

tude

(km

)

Elevation 6o

Elevation 3o

Elevation 0o

Elevation -2o

Elevation -4o

Elevation -6o

Elevation -8o

Elevation -10o

Weight moves lower in atmosphere with decreasing elevation angle

DBAMFs for May 31st

Page 19: Measurements of pollutants and their spatial distributions over the Los Angeles Basin

Quantifying the Effect of Radiative Transfer

Weighing factor for each atmospheric layer’s contribution to absorption and scattering at each elevation angle: Differential Box Air-Mass Factor (DBAMF)

m

jjjiji ChDBAMFDSCD

1

][)(a

DBAMFs calculated with TRACY II Monte- Carlo Radiative Transfer Model

Weight moves lower in atmosphere with decreasing elevation angle

0

1

2

3

4

5

0 10 20 30 40 50

Differential Box Air Mass Factor (DBAMF)

Alti

tude

(km

)

Elevation 6o

Elevation 3o

Elevation 0o

Elevation -2o

Elevation -4o

Elevation -6o

Elevation -8o

Elevation -10o

DBAMFs for May 31st

Page 20: Measurements of pollutants and their spatial distributions over the Los Angeles Basin

Retrieval of BL and FT NO2 concentrations

MAX-DOAS @ Mt. Wilson

Ctop

CBL

HM

AX-DOAS = 1550m

HBL

adownward

aupwardConcentration Cj for each atmospheric layer j is:

)()(a

aDBAMFhDSCD

Cj

jj

•NO2 elevated and well-mixed in in boundary layer (BL). •Boundary layer height was determined by Ceilometer at Caltech.•NO2 concentration free troposphere from horizontal elevation scan

Page 21: Measurements of pollutants and their spatial distributions over the Los Angeles Basin

0

500

1000Boundary Layer Height

Alti

tude

(met

ers)

0

0.5

1

1.5"Top" layer Mixing Ratio (C

top)

NO

2, ppb

12:00 15:00 18:00 21:00 00:00 03:000

5

10

15

Time/Date (UTC) for May 31st, 2010

NO

2, ppb

Boundary Layer Height Mixing Ratio (CBL

)

160º172º182ºLP-DOAS

NO2 mixing ratios, May 31st

Boundary Layer Height courtesy of C. Haman and B. Lefer, University of Houston

Values in 3 azimuths agree well

Page 22: Measurements of pollutants and their spatial distributions over the Los Angeles Basin

0

500

1000Boundary Layer Height

Alti

tude

(met

ers)

0

0.5

1

1.5"Top" layer Mixing Ratio (C

top)

NO

2, ppb

12:00 15:00 18:00 21:00 00:00 03:000

5

10

15

Time/Date (UTC) for May 31st, 2010

NO

2, ppb

Boundary Layer Height Mixing Ratio (CBL

)

160º172º182ºLP-DOAS

NO2 mixing ratios, May 31st

Boundary Layer Height courtesy of C. Haman and B. Lefer, University of Houston

For more on the Long-path DOAS, see talk by Catalina Tsai, Tuesday, May 17th, 1:30 pm

Page 23: Measurements of pollutants and their spatial distributions over the Los Angeles Basin

Conclusions and Outlook

• UCLA MAX-DOAS measured spatial and temporal distribution of NO2, HCHO, and O4 (aerosol extinction) during CalNex

• Raw data clearly shows the change of trace gas levels with location and altitude in the LA basin

• Initial radiative transfer calculations result in reasonable boundary layer NO2 mixing ratios

• More detailed radiative transfer calculations are currently performed

• Retrieval of concentration distributions will be performed directly and through an adjoint 3D air quality model (see talk by Dan Chen, Tuesday May 17th 4:10 pm)

Page 24: Measurements of pollutants and their spatial distributions over the Los Angeles Basin

Acknowledgements

We would like to thank the NOAA and the California Air Resources Board (CARB) for providing funding, and the NASA Jet Propulsion Laboratory for providing access to the CLARS facility on Mt. Wilson