CCN activity and volatility of β-caryophyllene secondary organic aerosol

In a series of smog chamber experiments, the cloud condensation nuclei (CCN) activity of secondary organic aerosol (SOA) generated from ozonolysis of β-caryophyllene was characterized by determining the CCN derived hygroscopicity parameter, κ<sub>CCN</sub>,...

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Main Authors: M. Frosch, M. Bilde, A. Nenes, A. P. Praplan, Z. Jurányi, J. Dommen, M. Gysel, E. Weingartner, U. Baltensperger
Format: Article
Language:English
Published: Copernicus Publications 2013-02-01
Series:Atmospheric Chemistry and Physics
Online Access:http://www.atmos-chem-phys.net/13/2283/2013/acp-13-2283-2013.pdf
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author M. Frosch
M. Bilde
A. Nenes
A. P. Praplan
Z. Jurányi
J. Dommen
M. Gysel
E. Weingartner
U. Baltensperger
author_facet M. Frosch
M. Bilde
A. Nenes
A. P. Praplan
Z. Jurányi
J. Dommen
M. Gysel
E. Weingartner
U. Baltensperger
author_sort M. Frosch
collection DOAJ
description In a series of smog chamber experiments, the cloud condensation nuclei (CCN) activity of secondary organic aerosol (SOA) generated from ozonolysis of β-caryophyllene was characterized by determining the CCN derived hygroscopicity parameter, κ<sub>CCN</sub>, from experimental data. Two types of CCN counters, operating at different temperatures, were used. The effect of semi-volatile organic compounds on the CCN activity of SOA was studied using a thermodenuder. <br><br> Overall, SOA was only slightly CCN active (with κ<sub>CCN</sub> in the range 0.001–0.16), and in dark experiments with no OH scavenger present, κ<sub>CCN</sub> decreased when particles were sent through the thermodenuder (with a temperature up to 50 °C). <br><br> SOA was generated under different experimental conditions: In some experiments, an OH scavenger (2-butanol) was added. SOA from these experiments was less CCN active than SOA produced in experiments without an OH scavenger (i.e. where OH was produced during ozonolysis). In other experiments, lights were turned on, either without or with the addition of HONO (OH source). This led to the formation of more CCN active SOA. <br><br> SOA was aged up to 30 h through exposure to ozone and (in experiments with no OH scavenger present) to OH. In all experiments, the derived κ<sub>CCN</sub> consistently increased with time after initial injection of β-caryophyllene, showing that chemical ageing increases the CCN activity of β-caryophyllene SOA. κ<sub>CCN</sub> was also observed to depend on supersaturation, which was explained either as an evaporation artifact from semi-volatile SOA (only observed in experiments lacking light exposure) or, alternatively, by effects related to chemical composition depending on dry particle size. <br><br> Using the method of Threshold Droplet Growth Analysis it was also concluded that the activation kinetics of the SOA do not differ significantly from calibration ammonium sulphate aerosol for particles aged for several hours.
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spelling doaj.art-b8e4bae3c77c4cc1a132d2f1a5da0d782022-12-22T03:56:58ZengCopernicus PublicationsAtmospheric Chemistry and Physics1680-73161680-73242013-02-011342283229710.5194/acp-13-2283-2013CCN activity and volatility of β-caryophyllene secondary organic aerosolM. FroschM. BildeA. NenesA. P. PraplanZ. JurányiJ. DommenM. GyselE. WeingartnerU. BaltenspergerIn a series of smog chamber experiments, the cloud condensation nuclei (CCN) activity of secondary organic aerosol (SOA) generated from ozonolysis of β-caryophyllene was characterized by determining the CCN derived hygroscopicity parameter, κ<sub>CCN</sub>, from experimental data. Two types of CCN counters, operating at different temperatures, were used. The effect of semi-volatile organic compounds on the CCN activity of SOA was studied using a thermodenuder. <br><br> Overall, SOA was only slightly CCN active (with κ<sub>CCN</sub> in the range 0.001–0.16), and in dark experiments with no OH scavenger present, κ<sub>CCN</sub> decreased when particles were sent through the thermodenuder (with a temperature up to 50 °C). <br><br> SOA was generated under different experimental conditions: In some experiments, an OH scavenger (2-butanol) was added. SOA from these experiments was less CCN active than SOA produced in experiments without an OH scavenger (i.e. where OH was produced during ozonolysis). In other experiments, lights were turned on, either without or with the addition of HONO (OH source). This led to the formation of more CCN active SOA. <br><br> SOA was aged up to 30 h through exposure to ozone and (in experiments with no OH scavenger present) to OH. In all experiments, the derived κ<sub>CCN</sub> consistently increased with time after initial injection of β-caryophyllene, showing that chemical ageing increases the CCN activity of β-caryophyllene SOA. κ<sub>CCN</sub> was also observed to depend on supersaturation, which was explained either as an evaporation artifact from semi-volatile SOA (only observed in experiments lacking light exposure) or, alternatively, by effects related to chemical composition depending on dry particle size. <br><br> Using the method of Threshold Droplet Growth Analysis it was also concluded that the activation kinetics of the SOA do not differ significantly from calibration ammonium sulphate aerosol for particles aged for several hours.http://www.atmos-chem-phys.net/13/2283/2013/acp-13-2283-2013.pdf
spellingShingle M. Frosch
M. Bilde
A. Nenes
A. P. Praplan
Z. Jurányi
J. Dommen
M. Gysel
E. Weingartner
U. Baltensperger
CCN activity and volatility of β-caryophyllene secondary organic aerosol
Atmospheric Chemistry and Physics
title CCN activity and volatility of β-caryophyllene secondary organic aerosol
title_full CCN activity and volatility of β-caryophyllene secondary organic aerosol
title_fullStr CCN activity and volatility of β-caryophyllene secondary organic aerosol
title_full_unstemmed CCN activity and volatility of β-caryophyllene secondary organic aerosol
title_short CCN activity and volatility of β-caryophyllene secondary organic aerosol
title_sort ccn activity and volatility of β caryophyllene secondary organic aerosol
url http://www.atmos-chem-phys.net/13/2283/2013/acp-13-2283-2013.pdf
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