2013 FL A&WMA Conference
Min Zhong and Myoseon Jang
Sept. 24, 2013
Department of Environmental Engineering Sciences
University of Florida
Aerosol: Key to improve climate prediction cooling heating
Green House Gases, small uncertainty
Atmospheric aerosol, large uncertainty
• scattering
• absorbing
• modifying cloud properties
3
1 Only absorption causes heating
2
Only a few types of aerosol absorb light,
BC, OC , and mineral dusts.
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POA & SOA
Direct
Emission
P rimary
O rganic
A erosol
VOC
Emissions
Oxidation
Reactions
(OH, O
3
, NO
3
)
Nucleation or
Condensation
S econdary
O rganic
A erosol
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Role of OC in climate forcing
5%
22%
1. OC is 95 wt% of carbonaceous aerosol
73%
BC POA SOA global OC budget (154 Tg/yr)
Source: IPCC 2007
2. Climate effect of OC has been poorly understood
Current model assumption: OC has no light absorption
(Maria et al. 2004 ; Hoyle et al. 2009)
Recent research: OC has light absorbing capacity, d-limonene SOA, POA
(Bones et al. 2010; Laskin et al. 2010 )
SOA
Non-absorbing aerosol POA Black carbon
Motivation: What is the role of OC in climate system?
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Objectives
To quantify aerosol’s climate impact, light absorption parameter is required.
MAC: mass absorption cross section (m 2 /g)
Light absorption property
SOA
Warming or cooling
POA
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Integrating sphere
Principle of the method: Beer Lambert’s law ln(I
0
/I) = b v
V/A detector filter sample ln(I
0
/I) = C b v
V/A
UV/Vis light
How to obtain mass absorption cross section(MAC) ?
MAC = b v
/M b v
: absorption coefficient (m -1 ) V: the volume of air drawn through the filter during a given sampling time, A is the area of the sample spot, M : aerosol mass concentration,
C=1.4845
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•
SOA generation SOA UV-Vis spectra recording
NO x
O
3
UV lamp
2 m 3 Teflon Chamber
GC-FID filter holder pump
UV/Vis light
SMPS filter sample
VOCs, NO x
Inorganic seed
RUV-IS
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15
Toluene
(TOL)
12
9
6
MAC of SOAs d -limonene
(DL)
α -pinene
(AP)
1,0
TOL SOA
DL SOA
AP SOA
0,8
0,6 toluene d-limonene
α-pinene
0,4
3
0,2
0
280 330 380 430 480 530 580 wavelength(nm)
0,0
λ = 350nm λ = 450nm
MAC of TOL is 10 times higher than DL and AP
more double bond , higher light absorbing
Zhong and Jang, AE, 2011
East
52m 3
West
52m 3
TUVR
T/RH
TUVR T/RH
Wood smoke
O
3
SMPS
FTIR
NO x
GC-MS
TEOM
RUV-IS
OC/EC
Hickory wood
Smoldering burning to reduce the formation of BC
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b abs ( OC )
1 A
Abs
OC ln
C V
MAC
OC
b abs ( OC )
M
OC
Increase in morning : chromophore formation in SOA or POA
Decrease in afternoon : sunlight bleach
Zhong and Jang, ACPD, 2013 12
RF of SOA is -0.09 ~ -0.06 w/m 2 (Hoyle et al. 2009)
“Aerosol optical properties of SOA were taken to be similar to POA”
(Hoyle et al. 2009).
In Myhre et al. (2007), they assume POA optical properties are equal to sulfate…
SOA = POA = Sulfate ?
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Extinction cross section Aerosol asymmetry factor Single scattering albedo
1. Particle size distribution assume lognormal distribution, with count median diameter of
138nm, geometric standard of 2 nm (Kaul at el. 2012)
2. Complex refractive index
assume n=1.44 (measured by Kim and Paulson, 2013), same from 280nm to 900nm.
k is from my measurement k
MAC
4
,
Mie code from: http://www.hiwater.org/ , shared by Dr. Tami Bond
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Extinction cross section Aerosol asymmetry factor Single scattering albedo
Extinction cross section: similar
Asym >0 scattering in the forward direction
SSA (SOA) > SSA(POA)
Mie code from: http://www.hiwater.org/
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simple radiative efficiency: watts/(cm 3 aerosol)
2
Chylek, P. and Wong, 1995
1,5
1
0,5
0
-0,5
-1
-1,5
-2
280 380 sulfate RH=0%
POA RH=0%
SOA RH=0%
480 580 wavelength (nm)
680 780
1. SOA and sulfate are similar, cooling aerosol
2. POA is warming aerosol.
3. It should be cautious to replace with each other.
SOA = Sulfate ≠ POA
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Radiative efficiency code from: http://www.hiwater.org/
MAC of toluene SOA was the highest compared with MAC values for α-pinene SOA and d-limonene SOA
MAC of POA increased in the morning and decreased in the afternoon due to the competition between chromophore formation and sunlight bleaching
SOA is a cooling aerosol, with negative radiative forcing similar to sulfate. POA is a warming aerosol, with positive net forcing
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This work was supported by grants from the National
Science Foundation (ATM-0852747) and the Alumni
Scholarship from the University of Florida.
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