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The Importance and Challenge(s) of Organic Aerosol Globally OA makes up 25-75% of total fine aerosol at the surface. Models have difficulty in reproducing the concentration and variability of OA. [Heald et al., 2011] Average aerosol composition for 37 campaigns in the NH [Zhang et al., 2007] 10,000’s of (unidentified?) compounds with variable properties How Global Model Simulation (GEOS-Chem) stacks up to OA measured in 17 airborne field studies
Citation preview
Organic aerosol composition and aging in the atmosphere:
How to fit laboratory experiments, field data, and modeling together
American Chemical Society Meeting, Denver, COMarch 24, 2015
Colette L. Heald and Qi Chen
My Conceptual View of Atmospheric Chemistry Research
The Importance and Challenge(s) of Organic Aerosol
Globally OA makes up 25-75% of total fine aerosol at the surface. Models have difficulty in reproducing the concentration and variability of OA.
[Heald et al., 2011]
Average aerosol composition for 37 campaigns in the NH
[Zhang et al., 2007]
10,000’s of (unidentified?) compounds with variable properties
How Global Model Simulation (GEOS-Chem) stacks up to OA measured in 17 airborne field studies
[Jimenez et al. 2009][Cappa et al. 2011]
Elemental Composition: Simple Description of Chemical Composition Providing Links to Climate-Relevant Properties
Radiative PropertiesHygroscopicity (Cloud-Forming Properties)
Bulk elemental ratios10,000’s of (unidentified?) compounds with variable properties
O:CH:C
Van Krevelen Diagram: Insight Into OA Aging
[Heald et al., 2010]
Need to re-visit: (1) more data (2) corrected AMS elemental ratios (Canagaratna et al., 2014)
Total OA (AMS data) fell on -1 slope, suggesting that aging (mixing,
chemistry, volatilization) follow consistent path.
We noted levelled off at higher O:C (alcohol addition, fragmentation?)
Atmospheric aging
Updated Van Krevelen of Ambient Measurements
See clear progression in OSc.Fitted slope shallower (-0.6 slope) than Heald et al., 2014 (-1 slope),
largely because AMS correction affects O:C more than H:C.
2.6
2.4
2.2
2.0
1.8
1.6
1.4
1.2
1.0
0.8
H:C
-1.0 -0.5 0.0 0.5 1.0OSc
(a)
Mexico City
Whistler Peak
Mace Head
2.6
2.4
2.2
2.0
1.8
1.6
1.4
1.2
1.0
0.8
H:C
1.61.20.80.40
O:C
n nn nn
nnn
n
ppp
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aaaaaaaaa aaaaaaaaaaaaaaaaaa aaaaaX X
X
X
X
TTT
ZZZ
rrrrrr
rrrr rr
b
bbb
b
bb
bb
bI
III IIIII III
InInInInSSSSSSSS
S
S MMMMMMM MMLLLLLLL
dg
dd
dt
tcc
c cccGGG
EE
R
e
(c)
Ground Urban Downwind Remote/Rural (HR-AMS) Urban Downwind Remote/Rural (Q-AMS)
Aircraft (HR-AMS) MILAGRO <0.5km MILAGRO 6-8km DC-3 <0.5km DC-3 6-8km
— Fitted to Ambient Means (R2 = 0.67)Slope = -0.58 ± 0.04 (1); Intercept = 1.96 ± 0.03 Fitted to invididual datasets (HR-AMS)(shown for the data range) — Urban — Downwind — Remote/Rural — Aircraft Laboratory-generated (all methods)Biomass burning OA (b)Anthropogenic POA(d/g - diesel/gasoline exhaust; c - cooking; t - trash burning)Biogenic SOA (I - isoprene; L - limonene; M - monoterpene; S - sesquiterpene)Aromatic SOA(X - xylene; T - toluene; Z - benze; r - others)Fresh IVOC SOA(n - naphthalene; p - phenol; o - o-cresol; x - dimethylphenol; a - C8 to C19 alkane)Glyoxal aqueous uptake (G)IEPOX-SOA (E)monoterpene ELVOC (e)(all at low-NOx except that *n represents high NOx) Other types of OAMarine Emissions (R) Laboratory photochemical aging
1.61.20.80.40
O:C
Anthropogenic (POA+SVOC/IVOC)
(d)
SOA (gas + particle)
1086420Biomass burning (POA+SVOC/IVOC)
(days)Heterogeneous Oxidation
squalane OA Lubricating oil particles glyoxal OA (aquesous)
(b)
Riverside
Mexico City (T0)
Fresno
Borneo
DC-3
AmazonSGP
BEACHON
Melpitz
Cool
Davis
SPC
UptonMILAGROWhistler Mtn.
2.6
2.4
2.2
2.0
1.8
1.6
1.4
1.2
1.0
0.8
H:C
-1.0 -0.5 0.0 0.5 1.0OSc
(a)
Mexico City
Whistler Peak
Mace Head
2.6
2.4
2.2
2.0
1.8
1.6
1.4
1.2
1.0
0.8
H:C
1.61.20.80.40
O:C
n nn nn
nnn
n
ppp
ooooxxxx
aaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaa
aaaaaaaaa aaaaaaaaaaaaaaaaaa aaaaaX X
X
X
X
TTT
ZZZ
rrrrrr
rrrr rr
b
bbb
b
bb
bb
bI
III IIIII III
InInInInSSSSSSSS
S
S MMMMMMM MMLLLLLLL
dg
dd
dt
tcc
c cccGGG
EE
R
e
(c)
Ground Urban Downwind Remote/Rural (HR-AMS) Urban Downwind Remote/Rural (Q-AMS)
Aircraft (HR-AMS) MILAGRO <0.5km MILAGRO 6-8km DC-3 <0.5km DC-3 6-8km
— Fitted to Ambient Means (R2 = 0.67)Slope = -0.58 ± 0.04 (1); Intercept = 1.96 ± 0.03 Fitted to invididual datasets (HR-AMS)(shown for the data range) — Urban — Downwind — Remote/Rural — Aircraft Laboratory-generated (all methods)Biomass burning OA (b)Anthropogenic POA(d/g - diesel/gasoline exhaust; c - cooking; t - trash burning)Biogenic SOA (I - isoprene; L - limonene; M - monoterpene; S - sesquiterpene)Aromatic SOA(X - xylene; T - toluene; Z - benze; r - others)Fresh IVOC SOA(n - naphthalene; p - phenol; o - o-cresol; x - dimethylphenol; a - C8 to C19 alkane)Glyoxal aqueous uptake (G)IEPOX-SOA (E)monoterpene ELVOC (e)(all at low-NOx except that *n represents high NOx) Other types of OAMarine Emissions (R) Laboratory photochemical aging
1.61.20.80.40
O:C
Anthropogenic (POA+SVOC/IVOC)
(d)
SOA (gas + particle)
1086420Biomass burning (POA+SVOC/IVOC)
(days)Heterogeneous Oxidation
squalane OA Lubricating oil particles glyoxal OA (aquesous)
(b)
Riverside
Mexico City (T0)
Fresno
Borneo
DC-3
AmazonSGP
BEACHON
Melpitz
Cool
Davis
SPC
UptonMILAGROWhistler Mtn.
2.6
2.4
2.2
2.0
1.8
1.6
1.4
1.2
1.0
0.8
H:C
-1.0 -0.5 0.0 0.5 1.0OSc
(a)
Mexico City
Whistler Peak
Mace Head
2.6
2.4
2.2
2.0
1.8
1.6
1.4
1.2
1.0
0.8
H:C
1.61.20.80.40
O:C
n nn nn
nnn
n
ppp
ooooxxxx
aaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaa
aaaaaaaaa aaaaaaaaaaaaaaaaaa aaaaaX XX
X
XTTT
ZZZ
rrrrrr
rrrr rr
b
bbb
b
bb
bb
bI
III IIIII III
InInInInSSSSSSSS
S
S MMMMMMM MMLLLLLLL
dg
dd
dt
tcc
c cccGGG
EE
R
e
(c)
Ground Urban Downwind Remote/Rural (HR-AMS) Urban Downwind Remote/Rural (Q-AMS)
Aircraft (HR-AMS) MILAGRO <0.5km MILAGRO 6-8km DC-3 <0.5km DC-3 6-8km
— Fitted to Ambient Means (R2 = 0.67)Slope = -0.58 ± 0.04 (1); Intercept = 1.96 ± 0.03 Fitted to invididual datasets (HR-AMS)(shown for the data range) — Urban — Downwind — Remote/Rural — Aircraft Laboratory-generated (all methods)Biomass burning OA (b)Anthropogenic POA(d/g - diesel/gasoline exhaust; c - cooking; t - trash burning)Biogenic SOA (I - isoprene; L - limonene; M - monoterpene; S - sesquiterpene)Aromatic SOA(X - xylene; T - toluene; Z - benze; r - others)Fresh IVOC SOA(n - naphthalene; p - phenol; o - o-cresol; x - dimethylphenol; a - C8 to C19 alkane)Glyoxal aqueous uptake (G)IEPOX-SOA (E)monoterpene ELVOC (e)(all at low-NOx except that *n represents high NOx) Other types of OAMarine Emissions (R) Laboratory photochemical aging
1.61.20.80.40
O:C
Anthropogenic (POA+SVOC/IVOC)
(d)
SOA (gas + particle)
1086420Biomass burning (POA+SVOC/IVOC)
(days)Heterogeneous Oxidation
squalane OA Lubricating oil particles glyoxal OA (aquesous)
(b)
Riverside
Mexico City (T0)
Fresno
Borneo
DC-3
AmazonSGP
BEACHON
Melpitz
Cool
Davis
SPC
UptonMILAGROWhistler Mtn.
But There is Diversity Among Campaigns
All individual slopes steeper (-0.7 to -1.0) than bulk …overall fitting compensating for various intercepts
2.6
2.4
2.2
2.0
1.8
1.6
1.4
1.2
1.0
0.8
H:C
-1.0 -0.5 0.0 0.5 1.0OSc
(a)
Mexico City
Whistler Peak
Mace Head
2.6
2.4
2.2
2.0
1.8
1.6
1.4
1.2
1.0
0.8
H:C
1.61.20.80.40
O:C
n nn nn
nnn
n
ppp
ooooxxxx
aaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaa
aaaaaaaaa aaaaaaaaaaaaaaaaaa aaaaaX X
X
X
X
TTT
ZZZ
rrrrrr
rrrr rr
b
bbb
b
bb
bb
bI
III IIIII III
InInInInSSSSSSSS
S
S MMMMMMM MMLLLLLLL
dg
dd
dt
tcc
c cccGGG
EE
R
e
(c)
Ground Urban Downwind Remote/Rural (HR-AMS) Urban Downwind Remote/Rural (Q-AMS)
Aircraft (HR-AMS) MILAGRO <0.5km MILAGRO 6-8km DC-3 <0.5km DC-3 6-8km
— Fitted to Ambient Means (R2 = 0.67)Slope = -0.58 ± 0.04 (1); Intercept = 1.96 ± 0.03 Fitted to invididual datasets (HR-AMS)(shown for the data range) — Urban — Downwind — Remote/Rural — Aircraft Laboratory-generated (all methods)Biomass burning OA (b)Anthropogenic POA(d/g - diesel/gasoline exhaust; c - cooking; t - trash burning)Biogenic SOA (I - isoprene; L - limonene; M - monoterpene; S - sesquiterpene)Aromatic SOA(X - xylene; T - toluene; Z - benze; r - others)Fresh IVOC SOA(n - naphthalene; p - phenol; o - o-cresol; x - dimethylphenol; a - C8 to C19 alkane)Glyoxal aqueous uptake (G)IEPOX-SOA (E)monoterpene ELVOC (e)(all at low-NOx except that *n represents high NOx) Other types of OAMarine Emissions (R) Laboratory photochemical aging
1.61.20.80.40
O:C
Anthropogenic (POA+SVOC/IVOC)
(d)
SOA (gas + particle)
1086420Biomass burning (POA+SVOC/IVOC)
(days)Heterogeneous Oxidation
squalane OA Lubricating oil particles glyoxal OA (aquesous)
(b)
Riverside
Mexico City (T0)
Fresno
Borneo
DC-3
AmazonSGP
BEACHON
Melpitz
Cool
Davis
SPC
UptonMILAGROWhistler Mtn.
2.6
2.4
2.2
2.0
1.8
1.6
1.4
1.2
1.0
0.8
H:C
-1.0 -0.5 0.0 0.5 1.0OSc
(a)
Mexico City
Whistler Peak
Mace Head
2.6
2.4
2.2
2.0
1.8
1.6
1.4
1.2
1.0
0.8
H:C
1.61.20.80.40
O:C
n nn nn
nnn
n
ppp
ooooxxxx
aaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaa
aaaaaaaaa aaaaaaaaaaaaaaaaaa aaaaaX X
X
X
X
TTT
ZZZ
rrrrrr
rrrr rr
b
bbb
b
bb
bb
bI
III IIIII III
InInInInSSSSSSSS
S
S MMMMMMM MMLLLLLLL
dg
dd
dt
tcc
ccccGGG
EE
R
e
(c)
Ground Urban Downwind Remote/Rural (HR-AMS) Urban Downwind Remote/Rural (Q-AMS)
Aircraft (HR-AMS) MILAGRO <0.5km MILAGRO 6-8km DC-3 <0.5km DC-3 6-8km
— Fitted to Ambient Means (R2 = 0.67)Slope = -0.58 ± 0.04 (1); Intercept = 1.96 ± 0.03 Fitted to invididual datasets (HR-AMS)(shown for the data range) — Urban — Downwind — Remote/Rural — Aircraft Laboratory-generated (all methods)Biomass burning OA (b)Anthropogenic POA(d/g - diesel/gasoline exhaust; c - cooking; t - trash burning)Biogenic SOA (I - isoprene; L - limonene; M - monoterpene; S - sesquiterpene)Aromatic SOA(X - xylene; T - toluene; Z - benze; r - others)Fresh IVOC SOA(n - naphthalene; p - phenol; o - o-cresol; x - dimethylphenol; a - C8 to C19 alkane)Glyoxal aqueous uptake (G)IEPOX-SOA (E)monoterpene ELVOC (e)(all at low-NOx except that *n represents high NOx) Other types of OAMarine Emissions (R) Laboratory photochemical aging
1.61.20.80.40
O:C
Anthropogenic (POA+SVOC/IVOC)
(d)
SOA (gas + particle)
1086420Biomass burning (POA+SVOC/IVOC)
(days)Heterogeneous Oxidation
squalane OA Lubricating oil particles glyoxal OA (aquesous)
(b)
Riverside
Mexico City (T0)
Fresno
Borneo
DC-3
AmazonSGP
BEACHON
Melpitz
Cool
Davis
SPC
UptonMILAGROWhistler Mtn.
2.6
2.4
2.2
2.0
1.8
1.6
1.4
1.2
1.0
0.8
H:C
-1.0 -0.5 0.0 0.5 1.0OSc
(a)
Mexico City
Whistler Peak
Mace Head
2.6
2.4
2.2
2.0
1.8
1.6
1.4
1.2
1.0
0.8
H:C
1.61.20.80.40
O:C
n nn nn
nnn
n
ppp
ooooxxxx
aaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaa
aaaaaaaaa aaaaaaaaaaaaaaaaaa aaaaaX X
X
X
X
TTT
ZZZ
rrrrrr
rrrr rr
b
bbb
b
bb
bb
bI
III IIIII III
InInInInSSSSSSSS
S
S MMMMMMM MMLLLLLLL
dg
dd
dt
tcc
ccccGGG
EE
R
e
(c)
Ground Urban Downwind Remote/Rural (HR-AMS) Urban Downwind Remote/Rural (Q-AMS)
Aircraft (HR-AMS) MILAGRO <0.5km MILAGRO 6-8km DC-3 <0.5km DC-3 6-8km
— Fitted to Ambient Means (R2 = 0.67)Slope = -0.58 ± 0.04 (1); Intercept = 1.96 ± 0.03 Fitted to invididual datasets (HR-AMS)(shown for the data range) — Urban — Downwind — Remote/Rural — Aircraft Laboratory-generated (all methods)Biomass burning OA (b)Anthropogenic POA(d/g - diesel/gasoline exhaust; c - cooking; t - trash burning)Biogenic SOA (I - isoprene; L - limonene; M - monoterpene; S - sesquiterpene)Aromatic SOA(X - xylene; T - toluene; Z - benze; r - others)Fresh IVOC SOA(n - naphthalene; p - phenol; o - o-cresol; x - dimethylphenol; a - C8 to C19 alkane)Glyoxal aqueous uptake (G)IEPOX-SOA (E)monoterpene ELVOC (e)(all at low-NOx except that *n represents high NOx) Other types of OAMarine Emissions (R) Laboratory photochemical aging
1.61.20.80.40
O:C
Anthropogenic (POA+SVOC/IVOC)
(d)
SOA (gas + particle)
1086420Biomass burning (POA+SVOC/IVOC)
(days)Heterogeneous Oxidation
squalane OA Lubricating oil particles glyoxal OA (aquesous)
(b)
Riverside
Mexico City (T0)
Fresno
Borneo
DC-3
AmazonSGP
BEACHON
Melpitz
Cool
Davis
SPC
UptonMILAGROWhistler Mtn.
2.6
2.4
2.2
2.0
1.8
1.6
1.4
1.2
1.0
0.8
H:C
-1.0 -0.5 0.0 0.5 1.0OSc
(a)
Mexico City
Whistler Peak
Mace Head
2.6
2.4
2.2
2.0
1.8
1.6
1.4
1.2
1.0
0.8
H:C
1.61.20.80.40
O:C
n nn nn
nnn
n
ppp
ooooxxxx
aaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaa
aaaaaaaaa aaaaaaaaaaaaaaaaaa aaaaaX XX
X
X
TTT
ZZZ
rrrrrr
rrrr rr
b
bbb
b
bb
bb
bI
III IIIII III
InInInInSSSSSSSS
S
S MMMMMMM MMLLLLLLL
dg
dd
dt
tcc
ccccGGG
EE
R
e
(c)
Ground Urban Downwind Remote/Rural (HR-AMS) Urban Downwind Remote/Rural (Q-AMS)
Aircraft (HR-AMS) MILAGRO <0.5km MILAGRO 6-8km DC-3 <0.5km DC-3 6-8km
— Fitted to Ambient Means (R2 = 0.67)Slope = -0.58 ± 0.04 (1); Intercept = 1.96 ± 0.03 Fitted to invididual datasets (HR-AMS)(shown for the data range) — Urban — Downwind — Remote/Rural — Aircraft Laboratory-generated (all methods)Biomass burning OA (b)Anthropogenic POA(d/g - diesel/gasoline exhaust; c - cooking; t - trash burning)Biogenic SOA (I - isoprene; L - limonene; M - monoterpene; S - sesquiterpene)Aromatic SOA(X - xylene; T - toluene; Z - benze; r - others)Fresh IVOC SOA(n - naphthalene; p - phenol; o - o-cresol; x - dimethylphenol; a - C8 to C19 alkane)Glyoxal aqueous uptake (G)IEPOX-SOA (E)monoterpene ELVOC (e)(all at low-NOx except that *n represents high NOx) Other types of OAMarine Emissions (R) Laboratory photochemical aging
1.61.20.80.40
O:C
Anthropogenic (POA+SVOC/IVOC)
(d)
SOA (gas + particle)
1086420Biomass burning (POA+SVOC/IVOC)
(days)Heterogeneous Oxidation
squalane OA Lubricating oil particles glyoxal OA (aquesous)
(b)
Riverside
Mexico City (T0)
Fresno
Borneo
DC-3
AmazonSGP
BEACHON
Melpitz
Cool
Davis
SPC
UptonMILAGROWhistler Mtn.
A Disconnect Between Laboratory and Ambient Elemental Composition?
Most of the laboratory data lies below the ambient line…Except isoprene SOA (low NOx) and glyoxal uptake.
2.6
2.4
2.2
2.0
1.8
1.6
1.4
1.2
1.0
0.8
H:C
-1.0 -0.5 0.0 0.5 1.0OSc
(a)
Mexico City
Whistler Peak
Mace Head
2.6
2.4
2.2
2.0
1.8
1.6
1.4
1.2
1.0
0.8
H:C
1.61.20.80.40
O:C
n nn nn
nnn
n
ppp
ooooxxxx
aaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaa
aaaaaaaaa aaaaaaaaaaaaaaaaaa aaaaaX X
X
X
X
TTT
ZZZ
rrrrrr
rrrr rr
b
bbb
b
bb
bb
bI
III IIIII III
InInInInSSSSSSSS
S
S MMMMMMM MMLLLLLLL
dg
dd
dt
tcc
ccccGGG
EE
R
e
(c)
Ground Urban Downwind Remote/Rural (HR-AMS) Urban Downwind Remote/Rural (Q-AMS)
Aircraft (HR-AMS) MILAGRO <0.5km MILAGRO 6-8km DC-3 <0.5km DC-3 6-8km
— Fitted to Ambient Means (R2 = 0.67)Slope = -0.58 ± 0.04 (1); Intercept = 1.96 ± 0.03 Fitted to invididual datasets (HR-AMS)(shown for the data range) — Urban — Downwind — Remote/Rural — Aircraft Laboratory-generated (all methods)Biomass burning OA (b)Anthropogenic POA(d/g - diesel/gasoline exhaust; c - cooking; t - trash burning)Biogenic SOA (I - isoprene; L - limonene; M - monoterpene; S - sesquiterpene)Aromatic SOA(X - xylene; T - toluene; Z - benze; r - others)Fresh IVOC SOA(n - naphthalene; p - phenol; o - o-cresol; x - dimethylphenol; a - C8 to C19 alkane)Glyoxal aqueous uptake (G)IEPOX-SOA (E)monoterpene ELVOC (e)(all at low-NOx except that *n represents high NOx) Other types of OAMarine Emissions (R) Laboratory photochemical aging
1.61.20.80.40
O:C
Anthropogenic (POA+SVOC/IVOC)
(d)
SOA (gas + particle)
1086420Biomass burning (POA+SVOC/IVOC)
(days)Heterogeneous Oxidation
squalane OA Lubricating oil particles glyoxal OA (aquesous)
(b)
Riverside
Mexico City (T0)
Fresno
Borneo
DC-3
AmazonSGP
BEACHON
Melpitz
Cool
Davis
SPC
UptonMILAGROWhistler Mtn.
2.6
2.4
2.2
2.0
1.8
1.6
1.4
1.2
1.0
0.8
H:C
-1.0 -0.5 0.0 0.5 1.0OSc
(a)
Mexico City
Whistler Peak
Mace Head
2.6
2.4
2.2
2.0
1.8
1.6
1.4
1.2
1.0
0.8
H:C
1.61.20.80.40
O:C
n nn nn
nnn
n
ppp
ooooxxxx
aaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaa
aaaaaaaaa aaaaaaaaaaaaaaaaaa aaaaaX X
X
X
X
TTT
ZZZ
rrrrrr
rrrr rr
b
bbb
b
bb
bb
bI
III IIIII III
InInInInSSSSSSSS
S
S MMMMMMM MMLLLLLLL
dg
dd
dt
tcc
c cccGGG
EE
R
e
(c)
Ground Urban Downwind Remote/Rural (HR-AMS) Urban Downwind Remote/Rural (Q-AMS)
Aircraft (HR-AMS) MILAGRO <0.5km MILAGRO 6-8km DC-3 <0.5km DC-3 6-8km
— Fitted to Ambient Means (R2 = 0.67)Slope = -0.58 ± 0.04 (1); Intercept = 1.96 ± 0.03 Fitted to invididual datasets (HR-AMS)(shown for the data range) — Urban — Downwind — Remote/Rural — Aircraft Laboratory-generated (all methods)Biomass burning OA (b)Anthropogenic POA(d/g - diesel/gasoline exhaust; c - cooking; t - trash burning)Biogenic SOA (I - isoprene; L - limonene; M - monoterpene; S - sesquiterpene)Aromatic SOA(X - xylene; T - toluene; Z - benze; r - others)Fresh IVOC SOA(n - naphthalene; p - phenol; o - o-cresol; x - dimethylphenol; a - C8 to C19 alkane)Glyoxal aqueous uptake (G)IEPOX-SOA (E)monoterpene ELVOC (e)(all at low-NOx except that *n represents high NOx) Other types of OAMarine Emissions (R) Laboratory photochemical aging
1.61.20.80.40
O:C
Anthropogenic (POA+SVOC/IVOC)
(d)
SOA (gas + particle)
1086420Biomass burning (POA+SVOC/IVOC)
(days)Heterogeneous Oxidation
squalane OA Lubricating oil particles glyoxal OA (aquesous)
(b)
Riverside
Mexico City (T0)
Fresno
Borneo
DC-3
AmazonSGP
BEACHON
Melpitz
Cool
Davis
SPC
UptonMILAGROWhistler Mtn.
Do Photochemical Aging Experiments Resolve This Disconnect?
Trajectory of photochemical aging lines up with ambient trajectory. Few aging experiments get to high O:C within ~10 days of aging.
2.6
2.4
2.2
2.0
1.8
1.6
1.4
1.2
1.0
0.8
H:C
-1.0 -0.5 0.0 0.5 1.0OSc
(a)
Mexico City
Whistler Peak
Mace Head
2.6
2.4
2.2
2.0
1.8
1.6
1.4
1.2
1.0
0.8
H:C
1.61.20.80.40
O:C
n nn nn
nnn
n
ppp
ooooxxxx
aaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaa
aaaaaaaaa aaaaaaaaaaaaaaaaaa aaaaaX X
X
X
X
TTT
ZZZ
rrrrrr
rrrr rr
b
bbb
b
bb
bb
bI
III IIIII III
InInInInSSSSSSSS
S
S MMMMMMM MMLLLLLLL
dg
dd
dt
tcc
ccccGGG
EE
R
e
(c)
Ground Urban Downwind Remote/Rural (HR-AMS) Urban Downwind Remote/Rural (Q-AMS)
Aircraft (HR-AMS) MILAGRO <0.5km MILAGRO 6-8km DC-3 <0.5km DC-3 6-8km
— Fitted to Ambient Means (R2 = 0.67)Slope = -0.58 ± 0.04 (1); Intercept = 1.96 ± 0.03 Fitted to invididual datasets (HR-AMS)(shown for the data range) — Urban — Downwind — Remote/Rural — Aircraft Laboratory-generated (all methods)Biomass burning OA (b)Anthropogenic POA(d/g - diesel/gasoline exhaust; c - cooking; t - trash burning)Biogenic SOA (I - isoprene; L - limonene; M - monoterpene; S - sesquiterpene)Aromatic SOA(X - xylene; T - toluene; Z - benze; r - others)Fresh IVOC SOA(n - naphthalene; p - phenol; o - o-cresol; x - dimethylphenol; a - C8 to C19 alkane)Glyoxal aqueous uptake (G)IEPOX-SOA (E)monoterpene ELVOC (e)(all at low-NOx except that *n represents high NOx) Other types of OAMarine Emissions (R) Laboratory photochemical aging
1.61.20.80.40
O:C
Anthropogenic (POA+SVOC/IVOC)
(d)
SOA (gas + particle)
1086420Biomass burning (POA+SVOC/IVOC)
(days)Heterogeneous Oxidation
squalane OA Lubricating oil particles glyoxal OA (aquesous)
(b)
Riverside
Mexico City (T0)
Fresno
Borneo
DC-3
AmazonSGP
BEACHON
Melpitz
Cool
Davis
SPC
UptonMILAGROWhistler Mtn.
2.6
2.4
2.2
2.0
1.8
1.6
1.4
1.2
1.0
0.8
H:C
-1.0 -0.5 0.0 0.5 1.0OSc
(a)
Mexico City
Whistler Peak
Mace Head
2.6
2.4
2.2
2.0
1.8
1.6
1.4
1.2
1.0
0.8
H:C
1.61.20.80.40
O:C
n nn nn
nnn
n
ppp
ooooxxxx
aaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaa
aaaaaaaaa aaaaaaaaaaaaaaaaaa aaaaaX X
X
X
X
TTT
ZZZ
rrrrrr
rrrr rr
b
bbb
b
bb
bb
bI
III IIIII III
InInInInSSSSSSSS
S
S MMMMMMM MMLLLLLLL
dg
dd
dt
tcc
ccccGGG
EE
R
e
(c)
Ground Urban Downwind Remote/Rural (HR-AMS) Urban Downwind Remote/Rural (Q-AMS)
Aircraft (HR-AMS) MILAGRO <0.5km MILAGRO 6-8km DC-3 <0.5km DC-3 6-8km
— Fitted to Ambient Means (R2 = 0.67)Slope = -0.58 ± 0.04 (1); Intercept = 1.96 ± 0.03 Fitted to invididual datasets (HR-AMS)(shown for the data range) — Urban — Downwind — Remote/Rural — Aircraft Laboratory-generated (all methods)Biomass burning OA (b)Anthropogenic POA(d/g - diesel/gasoline exhaust; c - cooking; t - trash burning)Biogenic SOA (I - isoprene; L - limonene; M - monoterpene; S - sesquiterpene)Aromatic SOA(X - xylene; T - toluene; Z - benze; r - others)Fresh IVOC SOA(n - naphthalene; p - phenol; o - o-cresol; x - dimethylphenol; a - C8 to C19 alkane)Glyoxal aqueous uptake (G)IEPOX-SOA (E)monoterpene ELVOC (e)(all at low-NOx except that *n represents high NOx) Other types of OAMarine Emissions (R) Laboratory photochemical aging
1.61.20.80.40
O:C
Anthropogenic (POA+SVOC/IVOC)
(d)
SOA (gas + particle)
1086420Biomass burning (POA+SVOC/IVOC)
(days)Heterogeneous Oxidation
squalane OA Lubricating oil particles glyoxal OA (aquesous)
(b)
Riverside
Mexico City (T0)
Fresno
Borneo
DC-3
AmazonSGP
BEACHON
Melpitz
Cool
Davis
SPC
UptonMILAGROWhistler Mtn.
2.6
2.4
2.2
2.0
1.8
1.6
1.4
1.2
1.0
0.8
H:C
-1.0 -0.5 0.0 0.5 1.0OSc
(a)
Mexico City
Whistler Peak
Mace Head
2.6
2.4
2.2
2.0
1.8
1.6
1.4
1.2
1.0
0.8
H:C
1.61.20.80.40
O:C
n nn nn
nnn
n
ppp
ooooxxxx
aaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaa
aaaaaaaaa aaaaaaaaaaaaaaaaaa aaaaaX X
X
X
X
TTT
ZZZ
rrrrrr
rrrr rr
b
bbb
b
bb
bb
bI
III IIIII III
InInInInSSSSSSSS
S
S MMMMMMM MMLLLLLLL
dg
dd
dt
tcc
c cccGGG
EE
R
e
(c)
Ground Urban Downwind Remote/Rural (HR-AMS) Urban Downwind Remote/Rural (Q-AMS)
Aircraft (HR-AMS) MILAGRO <0.5km MILAGRO 6-8km DC-3 <0.5km DC-3 6-8km
— Fitted to Ambient Means (R2 = 0.67)Slope = -0.58 ± 0.04 (1); Intercept = 1.96 ± 0.03 Fitted to invididual datasets (HR-AMS)(shown for the data range) — Urban — Downwind — Remote/Rural — Aircraft Laboratory-generated (all methods)Biomass burning OA (b)Anthropogenic POA(d/g - diesel/gasoline exhaust; c - cooking; t - trash burning)Biogenic SOA (I - isoprene; L - limonene; M - monoterpene; S - sesquiterpene)Aromatic SOA(X - xylene; T - toluene; Z - benze; r - others)Fresh IVOC SOA(n - naphthalene; p - phenol; o - o-cresol; x - dimethylphenol; a - C8 to C19 alkane)Glyoxal aqueous uptake (G)IEPOX-SOA (E)monoterpene ELVOC (e)(all at low-NOx except that *n represents high NOx) Other types of OAMarine Emissions (R) Laboratory photochemical aging
1.61.20.80.40
O:C
Anthropogenic (POA+SVOC/IVOC)
(d)
SOA (gas + particle)
1086420Biomass burning (POA+SVOC/IVOC)
(days)Heterogeneous Oxidation
squalane OA Lubricating oil particles glyoxal OA (aquesous)
(b)
Riverside
Mexico City (T0)
Fresno
Borneo
DC-3
AmazonSGP
BEACHON
Melpitz
Cool
Davis
SPC
UptonMILAGROWhistler Mtn.
Statistical Mixtures Demonstrate the Consistencies and Inconsistencies of Lab and Field Measurements
Mixtures can explain some of the difference in trajectory observed
across regions.
Mis-match suggests that either/both
(1)Have not identified important OA source types
(2)Laboratory studies are not representative of ambient composition (mixtures?)
[Chen et al., submitted]1.20.80.40.0
O:C
(f) Rural TSOA & Aging(g/p)
SGPMelpitz(s)
Add Aged ASOAAdd Aged BBOA
1.20.80.40.0
(g) Rainforest TSOA & Aging(g/p)ISOA & Aging(g/p)IEPOXp, ELVOC
AmazonBorneo
Add Aged (APOA, BBOA, ASOA)
Marine OA
2.4
2.0
1.6
1.2
0.8
H:C
1.20.80.40.0
(e) Monoterpene dominant
TSOA & Aging(g/p)
Add ELVOCAdd Aged (APOA, BBOA, ASOA)
ManitouWhistlerMountain
2.4
2.0
1.6
1.2
0.8
H:C
(a) Riverside TSOAISOA(NOx)
ASOA
Add APOA
(b) Fresno TSOAISOA(NOx)
ASOA
Add APOA, BBOA
(d) downwind TSOA & Aging(g/p)ISOA(NOx)
ASOA & Aging(g/p)BBOA & Aging(g/p)APOA & Aging(g/p)
SPC
(c) Mexico City TSOAISOA(NOx)
ASOABBOAAPOA
Add Aged (APOA, BBOA)
1.61.20.80.40.0
ISOA & Aging(g/p),IEPOXpAdd GSOA & Aging
TSOA & Aging(g/p)ISOA(NOx)
ASOA & Aging(g/p)BBOA & Aging(g/p)APOA & Aging(g/p)
ELVOC
(h) AircraftDC3
1.20.80.40.0
O:C
(f) Rural TSOA & Aging(g/p)
SGPMelpitz(s)
Add Aged ASOAAdd Aged BBOA
1.20.80.40.0
(g) Rainforest TSOA & Aging(g/p)ISOA & Aging(g/p)IEPOXp, ELVOC
AmazonBorneo
Add Aged (APOA, BBOA, ASOA)
Marine OA
2.4
2.0
1.6
1.2
0.8
H:C
1.20.80.40.0
(e) Monoterpene dominant
TSOA & Aging(g/p)
Add ELVOCAdd Aged (APOA, BBOA, ASOA)
ManitouWhistlerMountain
2.4
2.0
1.6
1.2
0.8
H:C
(a) Riverside TSOAISOA(NOx)
ASOA
Add APOA
(b) Fresno TSOAISOA(NOx)
ASOA
Add APOA, BBOA
(d) downwind TSOA & Aging(g/p)ISOA(NOx)
ASOA & Aging(g/p)BBOA & Aging(g/p)APOA & Aging(g/p)
SPC
(c) Mexico City TSOAISOA(NOx)
ASOABBOAAPOA
Add Aged (APOA, BBOA)
1.61.20.80.40.0
ISOA & Aging(g/p),IEPOXpAdd GSOA & Aging
TSOA & Aging(g/p)ISOA(NOx)
ASOA & Aging(g/p)BBOA & Aging(g/p)APOA & Aging(g/p)
ELVOC
(h) AircraftDC3
1.20.80.40.0
O:C
(f) Rural TSOA & Aging(g/p)
SGPMelpitz(s)
Add Aged ASOAAdd Aged BBOA
1.20.80.40.0
(g) Rainforest TSOA & Aging(g/p)ISOA & Aging(g/p)IEPOXp, ELVOC
AmazonBorneo
Add Aged (APOA, BBOA, ASOA)
Marine OA
2.4
2.0
1.6
1.2
0.8
H:C
1.20.80.40.0
(e) Monoterpene dominant
TSOA & Aging(g/p)
Add ELVOCAdd Aged (APOA, BBOA, ASOA)
ManitouWhistlerMountain
2.4
2.0
1.6
1.2
0.8
H:C
(a) Riverside TSOAISOA(NOx)
ASOA
Add APOA
(b) Fresno TSOAISOA(NOx)
ASOA
Add APOA, BBOA
(d) downwind TSOA & Aging(g/p)ISOA(NOx)
ASOA & Aging(g/p)BBOA & Aging(g/p)APOA & Aging(g/p)
SPC
(c) Mexico City TSOAISOA(NOx)
ASOABBOAAPOA
Add Aged (APOA, BBOA)
1.61.20.80.40.0
ISOA & Aging(g/p),IEPOXpAdd GSOA & Aging
TSOA & Aging(g/p)ISOA(NOx)
ASOA & Aging(g/p)BBOA & Aging(g/p)APOA & Aging(g/p)
ELVOC
(h) AircraftDC3
1.20.80.40.0
O:C
(f) Rural TSOA & Aging(g/p)
SGPMelpitz(s)
Add Aged ASOAAdd Aged BBOA
1.20.80.40.0
(g) Rainforest TSOA & Aging(g/p)ISOA & Aging(g/p)IEPOXp, ELVOC
AmazonBorneo
Add Aged (APOA, BBOA, ASOA)
Marine OA
2.4
2.0
1.6
1.2
0.8
H:C
1.20.80.40.0
(e) Monoterpene dominant
TSOA & Aging(g/p)
Add ELVOCAdd Aged (APOA, BBOA, ASOA)
ManitouWhistlerMountain
2.4
2.0
1.6
1.2
0.8
H:C
(a) Riverside TSOAISOA(NOx)
ASOA
Add APOA
(b) Fresno TSOAISOA(NOx)
ASOA
Add APOA, BBOA
(d) downwind TSOA & Aging(g/p)ISOA(NOx)
ASOA & Aging(g/p)BBOA & Aging(g/p)APOA & Aging(g/p)
SPC
(c) Mexico City TSOAISOA(NOx)
ASOABBOAAPOA
Add Aged (APOA, BBOA)
1.61.20.80.40.0
ISOA & Aging(g/p),IEPOXpAdd GSOA & Aging
TSOA & Aging(g/p)ISOA(NOx)
ASOA & Aging(g/p)BBOA & Aging(g/p)APOA & Aging(g/p)
ELVOC
(h) AircraftDC3
1.20.80.40.0
O:C
(f) Rural TSOA & Aging(g/p)
SGPMelpitz(s)
Add Aged ASOAAdd Aged BBOA
1.20.80.40.0
(g) Rainforest TSOA & Aging(g/p)ISOA & Aging(g/p)IEPOXp, ELVOC
AmazonBorneo
Add Aged (APOA, BBOA, ASOA)
Marine OA
2.4
2.0
1.6
1.2
0.8
H:C
1.20.80.40.0
(e) Monoterpene dominant
TSOA & Aging(g/p)
Add ELVOCAdd Aged (APOA, BBOA, ASOA)
ManitouWhistlerMountain
2.4
2.0
1.6
1.2
0.8
H:C
(a) Riverside TSOAISOA(NOx)
ASOA
Add APOA
(b) Fresno TSOAISOA(NOx)
ASOA
Add APOA, BBOA
(d) downwind TSOA & Aging(g/p)ISOA(NOx)
ASOA & Aging(g/p)BBOA & Aging(g/p)APOA & Aging(g/p)
SPC
(c) Mexico City TSOAISOA(NOx)
ASOABBOAAPOA
Add Aged (APOA, BBOA)
1.61.20.80.40.0
ISOA & Aging(g/p),IEPOXpAdd GSOA & Aging
TSOA & Aging(g/p)ISOA(NOx)
ASOA & Aging(g/p)BBOA & Aging(g/p)APOA & Aging(g/p)
ELVOC
(h) AircraftDC3
1.20.80.40.0
O:C
(f) Rural TSOA & Aging(g/p)
SGPMelpitz(s)
Add Aged ASOAAdd Aged BBOA
1.20.80.40.0
(g) Rainforest TSOA & Aging(g/p)ISOA & Aging(g/p)IEPOXp, ELVOC
AmazonBorneo
Add Aged (APOA, BBOA, ASOA)
Marine OA
2.4
2.0
1.6
1.2
0.8
H:C
1.20.80.40.0
(e) Monoterpene dominant
TSOA & Aging(g/p)
Add ELVOCAdd Aged (APOA, BBOA, ASOA)
ManitouWhistlerMountain
2.4
2.0
1.6
1.2
0.8
H:C
(a) Riverside TSOAISOA(NOx)
ASOA
Add APOA
(b) Fresno TSOAISOA(NOx)
ASOA
Add APOA, BBOA
(d) downwind TSOA & Aging(g/p)ISOA(NOx)
ASOA & Aging(g/p)BBOA & Aging(g/p)APOA & Aging(g/p)
SPC
(c) Mexico City TSOAISOA(NOx)
ASOABBOAAPOA
Add Aged (APOA, BBOA)
1.61.20.80.40.0
ISOA & Aging(g/p),IEPOXpAdd GSOA & Aging
TSOA & Aging(g/p)ISOA(NOx)
ASOA & Aging(g/p)BBOA & Aging(g/p)APOA & Aging(g/p)
ELVOC
(h) AircraftDC3
Polluted
Isoprene Aircraft
Terpenes
Riverside
Goal: Develop an Observationally-Based Model Simulation of OA Elemental Composition (and Aging)
Step 1: Re-fit 2 product SOA yields Step 2: Assign elemental ratios to POA/SOA types simulated in model based on lab data
Simulated surface composition occupies a narrow range (O:C = 0.3 to 0.5), compared to wider range seen in ambient.
2.6
2.4
2.2
2.0
1.8
1.6
1.4
1.2
1.0
0.8
H:C
-1.0 -0.5 0.0 0.5 1.0OSc
(a)
Mexico City
Whistler Peak
Mace Head
2.6
2.4
2.2
2.0
1.8
1.6
1.4
1.2
1.0
0.8
H:C
1.61.20.80.40
O:C
n nn nn
nnn
n
ppp
ooooxxxx
aaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaaa
aaaaaaaaa aaaaaaaaaaaaaaaaaa aaaaaX X
X
X
X
TTT
ZZZ
rrrrrr
rrrr rr
b
bbb
b
bb
bb
bI
III IIIII III
InInInInSSSSSSSS
S
S MMMMMMM MMLLLLLLL
dg
dd
dt
tcc
ccccGGG
EE
R
e
(c)
Ground Urban Downwind Remote/Rural (HR-AMS) Urban Downwind Remote/Rural (Q-AMS)
Aircraft (HR-AMS) MILAGRO <0.5km MILAGRO 6-8km DC-3 <0.5km DC-3 6-8km
— Fitted to Ambient Means (R2 = 0.67)Slope = -0.58 ± 0.04 (1); Intercept = 1.96 ± 0.03 Fitted to invididual datasets (HR-AMS)(shown for the data range) — Urban — Downwind — Remote/Rural — Aircraft Laboratory-generated (all methods)Biomass burning OA (b)Anthropogenic POA(d/g - diesel/gasoline exhaust; c - cooking; t - trash burning)Biogenic SOA (I - isoprene; L - limonene; M - monoterpene; S - sesquiterpene)Aromatic SOA(X - xylene; T - toluene; Z - benze; r - others)Fresh IVOC SOA(n - naphthalene; p - phenol; o - o-cresol; x - dimethylphenol; a - C8 to C19 alkane)Glyoxal aqueous uptake (G)IEPOX-SOA (E)monoterpene ELVOC (e)(all at low-NOx except that *n represents high NOx) Other types of OAMarine Emissions (R) Laboratory photochemical aging
1.61.20.80.40
O:C
Anthropogenic (POA+SVOC/IVOC)
(d)
SOA (gas + particle)
1086420Biomass burning (POA+SVOC/IVOC)
(days)Heterogeneous Oxidation
squalane OA Lubricating oil particles glyoxal OA (aquesous)
(b)
Riverside
Mexico City (T0)
Fresno
Borneo
DC-3
AmazonSGP
BEACHON
Melpitz
Cool
Davis
SPC
UptonMILAGROWhistler Mtn.
Updated (Very Simple) Aging SchemeStep 3: Account for semi-volatile POA emissionsStep 4: Age gas-phase organics based on flow-tube data, but end point constrained by field obs
End point:O:C=1.1H:C=1.4(defined by field obs)
Emissions FromFossil Fuel
BiofuelBiomass Burning
VOC
HydrophobicO-POAn
Oxidation Products
SOGi
Gas-phase Particle-phase
*,i iCSOAi
HydrophilicI-POAn
Marine Emissions
Biogenic Emissions
×0.5
1.15d
IsopreneMonoterpenesSesquiterpenes
Aromatics
×0.5
OH, O3
NO3
OH, O3
NO3
kage, jSVOCj SVOC-SOA2, j
SOG-SOA1, i
kcarbon, j×85%
×15%
SVOC-SOA1, j
SOG-SOA2, i kage, ikcarbon, i
Marine POA
(GEOS-Chem v9-01-03)
New Scheme Dramatically Alters Simulation of Elemental Composition
Now simulate a wider range of oxygen content, and also more pronounced seasonality in continental regions.
O:C Base O:C Updated Aging OSc Updated Aging
1.2
1.0
0.8
0.6
0.4
0.2
0.0
Bas
e
1.2
1.0
0.8
0.6
0.4
0.2
0.0
Agi
ng
1.2
1.0
0.8
0.6
0.4
0.2
0.0
Agi
ngO
:Cfo
ssil
fuel
of 0
.03
inst
ead
of 0
.1
1.21.00.80.60.40.20.0
Observed O:C
2.2
2.0
1.8
1.6
1.4
1.22.2
2.0
1.8
1.6
1.4
1.22.2
2.0
1.8
1.6
1.4
1.2
2.22.01.81.61.41.2
Observed H:C
0.1
1
10
0.1
1
10
0.1
1
10
0.1 1 10
Observed OA [µg m-3
]
UrbanDownwindRemote/Rural
Urban (JJA)
1.2
1.0
0.8
0.6
0.4
0.2
0.0
Bas
e
1.2
1.0
0.8
0.6
0.4
0.2
0.0
Agi
ng
1.2
1.0
0.8
0.6
0.4
0.2
0.0
Agi
ngO
:Cfo
ssil
fuel
of 0
.03
inst
ead
of 0
.1
1.21.00.80.60.40.20.0
Observed O:C
2.2
2.0
1.8
1.6
1.4
1.22.2
2.0
1.8
1.6
1.4
1.22.2
2.0
1.8
1.6
1.4
1.2
2.22.01.81.61.41.2
Observed H:C
0.1
1
10
0.1
1
10
0.1
1
10
0.1 1 10
Observed OA [µg m-3
]
UrbanDownwindRemote/Rural
Urban (JJA)
Comparison With Surface AMS Observations1.2
1.0
0.8
0.6
0.4
0.2
0.0
Bas
e
1.2
1.0
0.8
0.6
0.4
0.2
0.0
Agi
ng
1.2
1.0
0.8
0.6
0.4
0.2
0.0
Agi
ngO
:Cfo
ssil
fuel
of 0
.03
inst
ead
of 0
.1
1.21.00.80.60.40.20.0
Observed O:C
2.2
2.0
1.8
1.6
1.4
1.22.2
2.0
1.8
1.6
1.4
1.22.2
2.0
1.8
1.6
1.4
1.2
2.22.01.81.61.41.2
Observed H:C
0.1
1
10
0.1
1
10
0.1
1
10
0.1 1 10
Observed OA [µg m-3
]
UrbanDownwindRemote/Rural
Urban (JJA)
1.2
1.0
0.8
0.6
0.4
0.2
0.0
Bas
e
1.2
1.0
0.8
0.6
0.4
0.2
0.0
Agi
ng
1.2
1.0
0.8
0.6
0.4
0.2
0.0
Agi
ngO
:Cfo
ssil
fuel
of 0
.03
inst
ead
of 0
.1
1.21.00.80.60.40.20.0
Observed O:C
2.2
2.0
1.8
1.6
1.4
1.22.2
2.0
1.8
1.6
1.4
1.22.2
2.0
1.8
1.6
1.4
1.2
2.22.01.81.61.41.2
Observed H:C
0.1
1
10
0.1
1
10
0.1
1
10
0.1 1 10
Observed OA [µg m-3
]
UrbanDownwindRemote/Rural
Urban (JJA)
Aging drastically improves ability to capture high O:C in remote regions.But H:C underestimated, consistent with missing sources/pathways for high H:C
New scheme also demonstrates better match to observed mass.
Vertical Comparison From Airborne Campaigns
10
8
6
4
2
0
Altit
ude (
km)
1.21.00.80.60.4O:C
Observation Base Aging Aging w/. SOA heterogeneous aging Aging w/. 5xSOG -> SOA Aging w/. 25 KJ/mol enthalpy Aging w/. 2xEpoa
2.5
2.0
1.5
1.0
0.5
0.0
OA
(µg
sm-3
)
7654321Altitude (km)
(a) IMPEX
Similarly, aging is critical to reproducing observed O:C. Cannot simulate O:C>1, or variability in observed H:C. But for airborne measurements, including heterogeneous
oxidation helps to reproduce the vertical gradient.[Chen et al., in prep]
10
8
6
4
2
0
Altit
ude (
km)
1.21.00.80.60.4O:C
Observation Base Aging Aging w/. SOA heterogeneous aging Aging w/. 5xSOG -> SOA Aging w/. 25 KJ/mol enthalpy Aging w/. 2xEpoa
1086420OA
(b) DC-3
1.701.601.501.401.30H:C
4.03.02.01.00.0OA
10
8
6
4
2
0
Altit
ude (
km)
1.21.00.80.60.4O:C
(a) IMPEX
Conclusions
We use the Van Krevelen diagram to explore the composition of OA in lab and field experiments•Mixing of OA types can explain much of the ambient variation•Missing pathways which maintain high H:C•Lab data cannot explain very highest O:C
We develop a simple, measurement-based aging scheme for OA•Dramatically improves simulation of OA mass (global burden increases by 40%) and elemental composition in remote conditions •Including heterogeneous oxidation important for remote/aloft•Need better observational constraints for aging
Funding Acknowledgement: