gas/particle partitioning of primary and secondary organic aerosol products in a boreal forest...
TRANSCRIPT
Gas/particle partitioning of primary Gas/particle partitioning of primary and secondary organic aerosol and secondary organic aerosol
products in a boreal forestproducts in a boreal forest
Euripides G. Stephanou, Maria Apostolaki and Manolis Tsapakis
Environmental Chemical Processes Laboratory (ECPL)Department of Chemistry
School of Sciences and Engineering University of Crete
Biogenic Organic AerosolBiogenic Organic Aerosol
Temp. Wind Epicuticular Epicuticular waxeswaxes
MonoterpenesMonoterpenes
Low-vapor pressureLow-vapor pressuremulti-functional compoundsmulti-functional compounds
OH O3 NO3
0.01 0.1 1 100.001Diameter (Diameter (μμm)m)
???
Gas phase Particle phase
Pankow’s (1994) model of gas/particle partitioning of semi-volatile organic compounds in an amorphous organic particle:
omMW910
omfTR7.501
logiom,
logγoL
logpip,
logK
Kp,i: partitioning coefficient of the i-compound (in m3 μg-1) between the two phases Po
L: vapor pressure (torr) of the subcooled compound i om,i : activity coefficient of the compound i in the aerosol mixture R: constant of ideal gases (8.314 J mol-1 K-1) T: ambient temperature (K) fom:weight fraction of the total suspended particulate matter that is absorbing om phase (includes inorganic species and water that may be present) MWom: mean molecular weight of the species constituting the liquid organic matter (om) phase (g mol-1)
Organic Vapors “seed” particles If the compound i attains its Csat,i
SecondarySpecies
In laboratory experiments initial monoterpene concentration is very high (up to 700 ppbv) and saturation concentrations are rapidly surpassed.
The absence of pre-existing aerosol causes that both organic content (fom) and activity coefficient (γi) values approach unity.
The presence of other biogenic semi-volatile organic compounds emitted as primary aerosol cannot be understood and evaluated under laboratory conditions.
pump
GFF
PUF
Oxidant Denuder system
aerosol
PUF = Cgas,i
GFF = Caer,i
Mean concentration (ng m-3) of secondary aerosol components in gas (Cgas,i) and the particulate (Caer,i) phase
Sampling Period 6 - 12 12 - 18 18 - 6
Mean Temp. (Range)
K 287.3 (277.5 – 295.7)
294.3 (290.3 – 295.5)
287.5 (281.0 – 296.7)
cis- and trans-Pinonic Acid
Cgas,i 8.52 3.91 1.53
Caer,i 9.68 1.16 3.99
cis- and trans-nor Pinonic Acid
Cgas,i 2.65 0.32 3.18
Caer,i 1.94 0.14 1.51
cis-Pinic AcidCgas,i 3.77 2.37 0.41
Caer,i 2.38 0.49 3.03
PinonaldehydeCgas,i 0.73 5.06 1.06
Caer,i 0.78 0.27 0.88
NopinoneCgas,i 0.56 1.04 0.38
Caer,i 0.17 0.02 0.24
Sampling Period 6 - 12 12 - 18 18 - 6
Mean Temp. (Range) K 287.3(277.5 – 295.7)
294.3(290.3 – 295.5)
287.5(281.0 – 296.7)
n-Alkanols (C20 and C22)
Cgas,i 0.33 1.04 0.50
Caer,i 1.08 0.90 0.25
n-Alkanoic Acids (C12-C30)
Cgas,i 324. 08 85.44 57.56
Caer,i 84.95 27.38 31.44
n-Alkenoic Acids (C15:1-C18:1)
Cgas,i 47.52 11.54 11.63
Caer,i 32.30 10.10 16.68
α,ω-Dicarboxylic Acids (α,ω-C9)
Cgas,i 2.59 0.69 0.22
Caer,i 0.47 0.16 0.31
Mean concentration (ng m-3) of primary aerosol components in gas (Cgas,i) and the particulate (Caer,i) phase
Compound Stoichiometric Factor
i (dimensionless)
Partitioning Coefficient
Kom (m3 μg-1)
cis- and trans-Pinonic Acid (C10) 0.078 0.170
cis- and trans- nor-Pinonic Acid (C9) 0.013 0.097
cis-Pinic Acid (C10) 0.073 0.253
Pinonaldehyde (C9) 0.014 0.042
Nopinone (C9) 0.007 0.029
0
20
40
60
80
100
120
0 6 12 18 0 6 12
O3
(ppb
v) /
OH
. 105
cm-3
0,0
0,5
1,0
1,5
2,0
Mon
oter
pene
s (p
pbv)
Oxidation Content OH radicalsMonoterpenes
280
285
290
295
300
0 6 12 18 0 6 12
Tem
pera
ture
(K
)
0
100
200
300
400
0 6 12 18 0 6 12
PS
Con
cent
ratio
n (n
g m-3
)
PS (PP)
PS (GP)
Aerosol Formation Mechanism[OH, O3, T : from Harrison et al. (2001), Greasy eta l. (2001), Carslaw et al. (2001)]
8129,333336766,15385
2486,66667
0
2000
4000
6000
8000
10000
0 6 12 18 0 6 12Time period
Par
ticl
e N
um
ber
(p
art/
cm3
)
Primary organic aerosol components represented an important fraction of the atmospheric gas phase organic content.
The gas and particle atmospheric concentration of organic compounds directly-emitted from conifer leaf epicuticular wax and of those formed through the photo-oxidation of α- and β-pinene were simultaneously collected and measured in a conifer forest.
The saturation concentrations (Csat) of photo-oxidation products were estimated, by taking into consideration primary gas- and particle-phase organic species.
…
Summary
The results of this study indicated that primarily emitted organic species and ambient temperature
play a crucial role in secondary organic aerosol formation.
Csat of photo-oxidation products have been lowered facilitating new particle formation between molecules of photo-oxidation products and semi-volatile organic compounds.
From the measured concentrations of the above-mentioned compounds, (Csat) of α- and β-pinene photo-oxidation products were calculated for non-ideal conditions using a previously developed absorptive model.
Acknowledgements
• Dr. M. Mandalakis (University of Crete) for sampling • The OSOA group
• The European Commission (Environment and Climate Programme) project Origin and Formation of Secondary Organic Aerosol (OSOA)
• Research Committee of the University of Crete