4 Methanol PTR-MS Acetone R B Northwest Asian … 1...reference VOC (de Gouw, 2006), based on Figure...

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Observations of Volatile Organic Compounds in Biomass Burning Plumes During POLARCAT/ARCTASRebecca Hornbrook1, Eric Apel1, Dan Riemer2, Paul Wennberg3, John Crounse3, Jason St. Clair3, Stephanie Vay4,

Glenn Diskin4, Don Blake5, Armin Wisthaler6, Tomas Mikoviny6, Andreas Kürten7 & the ARCTAS science teamE-mail: rsh@ucar.edu, 1 National Center for Atmospheric Research, Atmospheric Chemistry Division, Boulder CO,

2 University of Miami, Miami FL, 3 California Institute of Technology, Pasadena CA,4 NASA Langley Research Center, Hampton VA,5 University of California, Irvine CA, 6 University of Innsbruck, Austria, 7 University of Frankfurt, Germany

A43A-0229

BIOMASS BURNING PLUMESDuring the POLARCAT/ARCTAS study in 2008, the NASA DC-8

sampled biomass burning plumes of varying ages and origins

over Alaska, the Canadian Arctic, California, and the Boreal

Region of Central Canada.

Several instruments on the DC-8 made observations of volatile

organic compounds (VOCs), including the Trace Organic Gas

Analyzer (TOGA), a Proton-transfer mass spectrometer (PTR-MS),

Chemical ionization mass spectrometers (CIMS), and whole-air

samples (WAS) analyzed by laboratory gas chromatography (GC).

Biomass burning

plumes were

identified by

elevated HCN

(CIMS), acetonitrile

(CH3CN; TOGA, PTR-

MS), and CO mixing

ratios. Ages and

origins were

estimated using

back trajectories

and sampling

location.

Figure 1. All ARCTAS

flight tracks, with

identified biomass

burning plume

encounters colored

by estimated age.

VOC INTERCOMPARISONSIn general, there is very good agreement between the

observations of VOCs measured by more than one instrument,

as shown in these

comparison plots.

Figure 2. Plots of

TOGA v. PTR-MS

observations of

selected VOCs

(top six plots), and

plots of TOGA v.

WAS observations

of selected VOCs

(lower six plots).

The solid black

best-fit lines were

determined using

orthogonal

distance

regression. The

dotted grey lines

show y = x.

Four Corners

Power Plant

Oil Sands

TO

GA

, p

ptv

TO

GA

, p

ptv

PTR-MS, pptv PTR-MS, pptv PTR-MS, pptv

TO

GA

, p

ptv

TO

GA

, p

ptv

WAS, pptv WAS, pptv WAS, pptv

RATIO OF BUTANE ISOMERSThe ratio [i-butane]/[n-butane] in North America is believed to be between

0.4 and 0.6 in the troposphere due to similar kOH (Parrish, 1998). This

implies consistent emission ratios across sources. However, emission ratios

of butane isomers can vary significantly with source type. Thus, the history

of an air mass should be considered when assessing the quality of

observed butane mixing ratios.

Figure 3. (left) Log-log correlation plot of butane

isomers as measured by TOGA and WAS during

entire ARCTAS mission.

Figure 4. (below) Plots of [i-C4]/[n-C4] from

selected regions and biomass burning sources

sampled during ARCTAS.

Figure 5. Ratios of butane

isomers in selected regions

and from various biomass

burning source regions as

measured by TOGA. Error

bars are the standard errors

in the slopes of the data (see

Figure 4 plots above).

Figure 6. Ratios of butane

isomers Enhancement

Ratios (ERs) from biomass

burning plume encounters,

colored by the estimated

age of the biomass burning

plume.

D. D. Parrish et al., J. Geophys. Res.

103, 1998.

Los Angeles Region (non-fire)

Aged Canadian Fires

Fresh Californian Fires

Aged Asian Fires

Aged Californian Fires

Fresh Canadian Fires

1

10

100

1000

i-B

uta

ne, p

ptv

1 10 100 1000

n-Butane, pptv

TOGA[i-C4]/[n-C4]

= 0.631 ± 0.003

WAS[i-C4]/[n-C4]

= 0.729 ± 0.005

0.2 0.4 0.6 0.8

California, Fresh Fires

California, Aged Fires

Asian Fires

Canada, Fresh Fires

Canada, Aged Fires

Northwest Asian Fires

California, non-Fire

Barrow Region

Barrow, Strong Source

Prudhoe Bay Region

Alberta, Oil Sands

Four Corners Power Plant

[i-Butane]/[n-Butane]1.0

0.8

0.6

0.4

0.2

0.0

ER

i-buta

ne/E

Rn

-bu

tan

e

24222018161412108

Flight No.

WASTOGA

86420

Estimated Plume Age, days

ENHANCEMENT RATIOSUsing data from the biomass burning plume encounters, we determined

enhancement ratios, ER ( VOC/ CO), for selected VOCs in individual fire

plumes. Although ERs of some VOCs vary significantly between plumes of

different ages or origins, there is generally good agreement between the

measurement instruments for plume-specific ERs.

Figure 7. Observed VOC enhancement ratios versus CO for individual plume

groups by flight and colored by estimated plume age.

T. J. Christian et al., J. Geophys. Res. 112, 2007. J. A. de Gouw et al., J. Geophys. Res. 111, 2006.

T. J. Duck et al., J. Geophys. Res. 112, 2007. H. R. Friedli et al., Glob. Biogeochem. Cyc. 15, 2001.

C. Jost et al., J. Geophys. Res. 108, 2003. R. J. Yokelson et al., Atmos. Chem. Phys. 9, 2009.

Compound Ethane Propane n-Butane i-Butane Benzene Toluene HCN CH3CN Methanol Acetone

Friedli 4.3 0.825 0.19 0.055 1.15 0.55

Christian 0.5-5.3

de Gouw 0.80-1.41 0.06-0.44 1.2-3.2 2-21 2.9-22.8

Duck 1.51

Jost 3.0-4.4 0.6-0.8 0.17-0.2 0.06-0.07 0.72-1.2 0.73-0.82 3.7-4.1 3.6-5.1

Yokelson 3.4 3.2-15.2 4.3 25.4 6.6

Literature Enhancement Ratios ( VOC/ CO, ppt/ppb)

12

10

8

6

4

2

0

En

ha

ncem

en

t R

ati

o,

pp

tV/p

pb

V

24222018161412108

HCN 86420

Est. Plume Age, days

CARB Canada Greenland Calif. Alaska

3.0

2.5

2.0

1.5

1.0

0.5

0.0

En

ha

ncem

en

t R

ati

o,

pp

tV/p

pb

V

24222018161412108

BenzenePTR-MS WASTOGA

5

4

3

2

1

0

24222018161412108

Acetonitrile PTR-MS TOGA

80

60

40

20

0

24222018161412108

MethanolPTR-MSWASTOGA

25

20

15

10

5

0

En

ha

nc

em

en

t R

ati

o,

pp

tV/p

pb

V

24222018161412108

Acetone PTR-MS WAS TOGA

1.5

1.0

0.5

0.0

24222018161412108

ToluenePTR-MS WASTOGA

20

15

10

5

0

Pro

pa

ne

ER

, pp

tV/p

pb

V

242016128

Flight No.

40

30

20

10

0E

tha

ne

ER

, p

ptV

/pp

bV

EthaneWAS

PropaneWAS

3.0

2.5

2.0

1.5

1.0

0.5

0.0

i-B

uta

ne

ER

, p

ptV

/pp

bV

242016128

Flight No.

6

5

4

3

2

1

0

n-B

uta

ne E

R, p

ptV

/pp

bV

n-ButaneTOGA

i-Butane TOGA

PROCESSING V. EMISSION PROFILESIt has been shown previously that the extent of photochemical

processing a biomass burning plume has undergone can be

inferred from plots of VOC ERs as a function of ERs of a

reference VOC (de Gouw, 2006), based on

Figure 8. Observed VOC ERs versus CO, plotted as a function

of a reference VOC’s observed ERs.

This principle does not appear to hold for observed ERs of

light alkanes (below). This is likely due to the variability of

emission ratios of light alkanes versus CO from biomass

burning. However, there are strong indications of linear

correlations between observed alkane enhancement ratios

with CO that are independent of plume age and most likely

due to correlated emission profiles from fires.

Figure 9. Observed VOC enhancement ratios versus CO, as a

function of n-butane versus CO. The alkane ER outlier value

from Flight 19 is not shown for clarity, although an orthogonal

distance regression fit to the data was performed with and

without the outlier and both results are included on the plots.

Calculated (298 K) From Fit Calculated (298 K) From Fit

5.50 3.26 ± 0.08 1.30 1.22 ± 0.05

(k ethylbenzene -k CO )/(k toluene - k CO ) (k toluene -k CO )/(k benzene - k CO )

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