Understanding in situ ozone production in the summertime through radical observations and modelling studies during the Clean air for London project (ClearfLo)
Measurements of OH, HO<sub>2</sub>, RO<sub>2</sub><i>i</i> (alkene and aromatic-related RO<sub>2</sub>) and total RO<sub>2</sub> radicals taken during the ClearfLo campaign in central London in the summer of 2012 are presented. A photost...
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Copernicus Publications
2018-02-01
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Series: | Atmospheric Chemistry and Physics |
Online Access: | https://www.atmos-chem-phys.net/18/2547/2018/acp-18-2547-2018.pdf |
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Article |
collection |
DOAJ |
language |
English |
format |
Article |
sources |
DOAJ |
author |
L. K. Whalley L. K. Whalley D. Stone R. Dunmore J. Hamilton J. R. Hopkins J. R. Hopkins J. D. Lee J. D. Lee A. C. Lewis A. C. Lewis P. Williams P. Williams J. Kleffmann S. Laufs R. Woodward-Massey D. E. Heard D. E. Heard |
spellingShingle |
L. K. Whalley L. K. Whalley D. Stone R. Dunmore J. Hamilton J. R. Hopkins J. R. Hopkins J. D. Lee J. D. Lee A. C. Lewis A. C. Lewis P. Williams P. Williams J. Kleffmann S. Laufs R. Woodward-Massey D. E. Heard D. E. Heard Understanding in situ ozone production in the summertime through radical observations and modelling studies during the Clean air for London project (ClearfLo) Atmospheric Chemistry and Physics |
author_facet |
L. K. Whalley L. K. Whalley D. Stone R. Dunmore J. Hamilton J. R. Hopkins J. R. Hopkins J. D. Lee J. D. Lee A. C. Lewis A. C. Lewis P. Williams P. Williams J. Kleffmann S. Laufs R. Woodward-Massey D. E. Heard D. E. Heard |
author_sort |
L. K. Whalley |
title |
Understanding in situ ozone production in the summertime through radical observations and modelling studies during the Clean air for London project (ClearfLo) |
title_short |
Understanding in situ ozone production in the summertime through radical observations and modelling studies during the Clean air for London project (ClearfLo) |
title_full |
Understanding in situ ozone production in the summertime through radical observations and modelling studies during the Clean air for London project (ClearfLo) |
title_fullStr |
Understanding in situ ozone production in the summertime through radical observations and modelling studies during the Clean air for London project (ClearfLo) |
title_full_unstemmed |
Understanding in situ ozone production in the summertime through radical observations and modelling studies during the Clean air for London project (ClearfLo) |
title_sort |
understanding in situ ozone production in the summertime through radical observations and modelling studies during the clean air for london project (clearflo) |
publisher |
Copernicus Publications |
series |
Atmospheric Chemistry and Physics |
issn |
1680-7316 1680-7324 |
publishDate |
2018-02-01 |
description |
Measurements of OH, HO<sub>2</sub>, RO<sub>2</sub><i>i</i> (alkene
and aromatic-related RO<sub>2</sub>) and total RO<sub>2</sub> radicals taken during the
ClearfLo campaign in central London in the summer of 2012 are presented. A
photostationary steady-state calculation of OH which considered measured OH
reactivity as the OH sink term and the measured OH sources (of which
HO<sub>2</sub>+ NO reaction and HONO photolysis dominated) compared well with the
observed levels of OH. Comparison with calculations from a detailed box model
utilising the Master Chemical Mechanism v3.2, however, highlighted a
substantial discrepancy between radical observations under lower NO<sub><i>x</i></sub>
conditions ([NO] < 1 ppbv), typically experienced during the
afternoon hours, and indicated that the model was missing a significant
peroxy radical sink; the model overpredicted HO<sub>2</sub> by up to a factor of
10 at these times. Known radical termination steps, such as HO<sub>2</sub> uptake
on aerosols, were not sufficient to reconcile the model–measurement
discrepancies alone, suggesting other missing termination processes. This
missing sink was most evident when the air reaching the site had previously
passed over central London to the east and when elevated temperatures were
experienced and, hence, contained higher concentrations of VOCs. Uncertainties
in the degradation mechanism at low NO<sub><i>x</i></sub> of complex biogenic and diesel
related VOC species, which were particularly elevated and dominated OH
reactivity under these easterly flows, may account for some of the model–measurement disagreement. Under higher [NO] (> 3 ppbv) the box
model increasingly underpredicted total [RO<sub>2</sub>]. The modelled and
observed HO<sub>2</sub> were in agreement, however, under elevated NO
concentrations ranging from 7 to 15 ppbv.
<br><br>
The model uncertainty under low NO conditions leads to more ozone production
predicted using modelled peroxy radical concentrations
( ∼ 3 ppbv h<sup>−1</sup>) versus ozone production from peroxy radicals
measured ( ∼ 1 ppbv h<sup>−1</sup>). Conversely, ozone production derived
from the predicted peroxy radicals is up to an order of magnitude lower than
from the observed peroxy radicals as [NO] increases beyond 7 ppbv due to the
model underprediction of RO<sub>2</sub> under these conditions. |
url |
https://www.atmos-chem-phys.net/18/2547/2018/acp-18-2547-2018.pdf |
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doaj-4eeade2d08a4414682e843368a19c9a32020-11-24T20:45:30ZengCopernicus PublicationsAtmospheric Chemistry and Physics1680-73161680-73242018-02-01182547257110.5194/acp-18-2547-2018Understanding in situ ozone production in the summertime through radical observations and modelling studies during the Clean air for London project (ClearfLo)L. K. Whalley0L. K. Whalley1D. Stone2R. Dunmore3J. Hamilton4J. R. Hopkins5J. R. Hopkins6J. D. Lee7J. D. Lee8A. C. Lewis9A. C. Lewis10P. Williams11P. Williams12J. Kleffmann13S. Laufs14R. Woodward-Massey15D. E. Heard16D. E. Heard17School of Chemistry, University of Leeds, Leeds, LS2 9JT, UKNational Centre for Atmospheric Science, University of Leeds, Leeds, LS2 9JT, UKSchool of Chemistry, University of Leeds, Leeds, LS2 9JT, UKDepartment of Chemistry, University of York, York, YO10 5DD, UKDepartment of Chemistry, University of York, York, YO10 5DD, UKDepartment of Chemistry, University of York, York, YO10 5DD, UKNational Centre for Atmospheric Science, University of York, YO10 5DD, UKDepartment of Chemistry, University of York, York, YO10 5DD, UKNational Centre for Atmospheric Science, University of York, YO10 5DD, UKDepartment of Chemistry, University of York, York, YO10 5DD, UKNational Centre for Atmospheric Science, University of York, YO10 5DD, UKCentre for Atmospheric Sciences, School of Earth, Atmospheric & Environmental Sciences, University of Manchester, Manchester, M13 9PL, UKNational Centre for Atmospheric Sciences, University of Manchester, Manchester, M13 9PL, UKInstitute for Atmospheric & Environmental Research, Bergische Universität Wuppertal (BUW), Gaußstr. 20, 42119 Wuppertal, GermanyInstitute for Atmospheric & Environmental Research, Bergische Universität Wuppertal (BUW), Gaußstr. 20, 42119 Wuppertal, GermanySchool of Chemistry, University of Leeds, Leeds, LS2 9JT, UKSchool of Chemistry, University of Leeds, Leeds, LS2 9JT, UKNational Centre for Atmospheric Science, University of Leeds, Leeds, LS2 9JT, UKMeasurements of OH, HO<sub>2</sub>, RO<sub>2</sub><i>i</i> (alkene and aromatic-related RO<sub>2</sub>) and total RO<sub>2</sub> radicals taken during the ClearfLo campaign in central London in the summer of 2012 are presented. A photostationary steady-state calculation of OH which considered measured OH reactivity as the OH sink term and the measured OH sources (of which HO<sub>2</sub>+ NO reaction and HONO photolysis dominated) compared well with the observed levels of OH. Comparison with calculations from a detailed box model utilising the Master Chemical Mechanism v3.2, however, highlighted a substantial discrepancy between radical observations under lower NO<sub><i>x</i></sub> conditions ([NO] < 1 ppbv), typically experienced during the afternoon hours, and indicated that the model was missing a significant peroxy radical sink; the model overpredicted HO<sub>2</sub> by up to a factor of 10 at these times. Known radical termination steps, such as HO<sub>2</sub> uptake on aerosols, were not sufficient to reconcile the model–measurement discrepancies alone, suggesting other missing termination processes. This missing sink was most evident when the air reaching the site had previously passed over central London to the east and when elevated temperatures were experienced and, hence, contained higher concentrations of VOCs. Uncertainties in the degradation mechanism at low NO<sub><i>x</i></sub> of complex biogenic and diesel related VOC species, which were particularly elevated and dominated OH reactivity under these easterly flows, may account for some of the model–measurement disagreement. Under higher [NO] (> 3 ppbv) the box model increasingly underpredicted total [RO<sub>2</sub>]. The modelled and observed HO<sub>2</sub> were in agreement, however, under elevated NO concentrations ranging from 7 to 15 ppbv. <br><br> The model uncertainty under low NO conditions leads to more ozone production predicted using modelled peroxy radical concentrations ( ∼ 3 ppbv h<sup>−1</sup>) versus ozone production from peroxy radicals measured ( ∼ 1 ppbv h<sup>−1</sup>). Conversely, ozone production derived from the predicted peroxy radicals is up to an order of magnitude lower than from the observed peroxy radicals as [NO] increases beyond 7 ppbv due to the model underprediction of RO<sub>2</sub> under these conditions.https://www.atmos-chem-phys.net/18/2547/2018/acp-18-2547-2018.pdf |