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Atmospheric OH reactivity in central London: observations, model predictions and estimates of in situ ozone production
Near-continuous measurements of hydroxyl radical (OH) reactivity in the urban background atmosphere of central London during the summer of 2012 are presented. OH reactivity behaviour is seen to be broadly dependent on air mass origin, with the highest reactivity and the most pronounced diurnal profi...
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Published in: | Atmospheric chemistry and physics 2016-02, Vol.16 (4), p.2109-2122 |
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description | Near-continuous measurements of hydroxyl radical (OH) reactivity in the urban background atmosphere of central London during the summer of 2012 are presented. OH reactivity behaviour is seen to be broadly dependent on air mass origin, with the highest reactivity and the most pronounced diurnal profile observed when air had passed over central London to the east, prior to measurement. Averaged over the entire observation period of 26 days, OH reactivity peaked at ∼ 27 s−1 in the morning, with a minimum of ∼ 15 s−1 during the afternoon. A maximum OH reactivity of 116 s−1 was recorded on one day during morning rush hour. A detailed box model using the Master Chemical Mechanism was used to calculate OH reactivity, and was constrained with an extended measurement data set of volatile organic compounds (VOCs) derived from a gas chromatography flame ionisation detector (GC-FID) and a two-dimensional GC instrument which included heavier molecular weight (up to C12) aliphatic VOCs, oxygenated VOCs and the biogenic VOCs α-pinene and limonene. Comparison was made between observed OH reactivity and modelled OH reactivity using (i) a standard suite of VOC measurements (C2–C8 hydrocarbons and a small selection of oxygenated VOCs) and (ii) a more comprehensive inventory including species up to C12. Modelled reactivities were lower than those measured (by 33 %) when only the reactivity of the standard VOC suite was considered. The difference between measured and modelled reactivity was improved, to within 15 %, if the reactivity of the higher VOCs (⩾ C9) was also considered, with the reactivity of the biogenic compounds of α-pinene and limonene and their oxidation products almost entirely responsible for this improvement. Further improvements in the model's ability to reproduce OH reactivity (to within 6 %) could be achieved if the reactivity and degradation mechanism of unassigned two-dimensional GC peaks were estimated. Neglecting the contribution of the higher VOCs (⩾ C9) (particularly α-pinene and limonene) and model-generated intermediates increases the modelled OH concentrations by 41 %, and the magnitude of in situ ozone production calculated from the production of RO2 was significantly lower (60 %). This work highlights that any future ozone abatement strategies should consider the role that biogenic emissions play alongside anthropogenic emissions in influencing London's air quality. |
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OH reactivity behaviour is seen to be broadly dependent on air mass origin, with the highest reactivity and the most pronounced diurnal profile observed when air had passed over central London to the east, prior to measurement. Averaged over the entire observation period of 26 days, OH reactivity peaked at ∼ 27 s−1 in the morning, with a minimum of ∼ 15 s−1 during the afternoon. A maximum OH reactivity of 116 s−1 was recorded on one day during morning rush hour. A detailed box model using the Master Chemical Mechanism was used to calculate OH reactivity, and was constrained with an extended measurement data set of volatile organic compounds (VOCs) derived from a gas chromatography flame ionisation detector (GC-FID) and a two-dimensional GC instrument which included heavier molecular weight (up to C12) aliphatic VOCs, oxygenated VOCs and the biogenic VOCs α-pinene and limonene. Comparison was made between observed OH reactivity and modelled OH reactivity using (i) a standard suite of VOC measurements (C2–C8 hydrocarbons and a small selection of oxygenated VOCs) and (ii) a more comprehensive inventory including species up to C12. Modelled reactivities were lower than those measured (by 33 %) when only the reactivity of the standard VOC suite was considered. The difference between measured and modelled reactivity was improved, to within 15 %, if the reactivity of the higher VOCs (⩾ C9) was also considered, with the reactivity of the biogenic compounds of α-pinene and limonene and their oxidation products almost entirely responsible for this improvement. Further improvements in the model's ability to reproduce OH reactivity (to within 6 %) could be achieved if the reactivity and degradation mechanism of unassigned two-dimensional GC peaks were estimated. Neglecting the contribution of the higher VOCs (⩾ C9) (particularly α-pinene and limonene) and model-generated intermediates increases the modelled OH concentrations by 41 %, and the magnitude of in situ ozone production calculated from the production of RO2 was significantly lower (60 %). This work highlights that any future ozone abatement strategies should consider the role that biogenic emissions play alongside anthropogenic emissions in influencing London's air quality.</description><identifier>ISSN: 1680-7324</identifier><identifier>ISSN: 1680-7316</identifier><identifier>EISSN: 1680-7324</identifier><identifier>DOI: 10.5194/acp-16-2109-2016</identifier><language>eng</language><publisher>Katlenburg-Lindau: Copernicus GmbH</publisher><subject>Air masses ; Air pollution ; Air quality ; Aliphatic compounds ; Analysis ; Anthropogenic factors ; Biogenic emissions ; Cities ; Diurnal ; Emission measurements ; Environmental aspects ; Flame ionization detectors ; Gas chromatography ; Hydrocarbons ; Hydroxyl radicals ; Intermediates ; Limonene ; Mathematical models ; Measurement ; Molecular weight ; Morning ; Organic compounds ; Oxidation ; Oxygenation ; Ozone ; Ozone production ; Pollution abatement ; Reactivity ; Urban studies ; VOCs ; Volatile organic compounds ; α-Pinene</subject><ispartof>Atmospheric chemistry and physics, 2016-02, Vol.16 (4), p.2109-2122</ispartof><rights>COPYRIGHT 2016 Copernicus GmbH</rights><rights>Copyright Copernicus GmbH 2016</rights><rights>2016. 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OH reactivity behaviour is seen to be broadly dependent on air mass origin, with the highest reactivity and the most pronounced diurnal profile observed when air had passed over central London to the east, prior to measurement. Averaged over the entire observation period of 26 days, OH reactivity peaked at ∼ 27 s−1 in the morning, with a minimum of ∼ 15 s−1 during the afternoon. A maximum OH reactivity of 116 s−1 was recorded on one day during morning rush hour. A detailed box model using the Master Chemical Mechanism was used to calculate OH reactivity, and was constrained with an extended measurement data set of volatile organic compounds (VOCs) derived from a gas chromatography flame ionisation detector (GC-FID) and a two-dimensional GC instrument which included heavier molecular weight (up to C12) aliphatic VOCs, oxygenated VOCs and the biogenic VOCs α-pinene and limonene. Comparison was made between observed OH reactivity and modelled OH reactivity using (i) a standard suite of VOC measurements (C2–C8 hydrocarbons and a small selection of oxygenated VOCs) and (ii) a more comprehensive inventory including species up to C12. Modelled reactivities were lower than those measured (by 33 %) when only the reactivity of the standard VOC suite was considered. The difference between measured and modelled reactivity was improved, to within 15 %, if the reactivity of the higher VOCs (⩾ C9) was also considered, with the reactivity of the biogenic compounds of α-pinene and limonene and their oxidation products almost entirely responsible for this improvement. Further improvements in the model's ability to reproduce OH reactivity (to within 6 %) could be achieved if the reactivity and degradation mechanism of unassigned two-dimensional GC peaks were estimated. Neglecting the contribution of the higher VOCs (⩾ C9) (particularly α-pinene and limonene) and model-generated intermediates increases the modelled OH concentrations by 41 %, and the magnitude of in situ ozone production calculated from the production of RO2 was significantly lower (60 %). This work highlights that any future ozone abatement strategies should consider the role that biogenic emissions play alongside anthropogenic emissions in influencing London's air quality.</description><subject>Air masses</subject><subject>Air pollution</subject><subject>Air quality</subject><subject>Aliphatic compounds</subject><subject>Analysis</subject><subject>Anthropogenic factors</subject><subject>Biogenic emissions</subject><subject>Cities</subject><subject>Diurnal</subject><subject>Emission measurements</subject><subject>Environmental aspects</subject><subject>Flame ionization detectors</subject><subject>Gas chromatography</subject><subject>Hydrocarbons</subject><subject>Hydroxyl radicals</subject><subject>Intermediates</subject><subject>Limonene</subject><subject>Mathematical models</subject><subject>Measurement</subject><subject>Molecular weight</subject><subject>Morning</subject><subject>Organic compounds</subject><subject>Oxidation</subject><subject>Oxygenation</subject><subject>Ozone</subject><subject>Ozone production</subject><subject>Pollution abatement</subject><subject>Reactivity</subject><subject>Urban studies</subject><subject>VOCs</subject><subject>Volatile organic 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OH reactivity in central London: observations, model predictions and estimates of in situ ozone production</title><author>Whalley, Lisa K ; Stone, Daniel ; Bandy, Brian ; Dunmore, Rachel ; Hamilton, Jacqueline F ; Hopkins, James ; Lee, James D ; Lewis, Alastair C ; Heard, Dwayne E</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c574t-fe5a72de0af061f830366c9567a81fc12c9eb9efa8b086dfd95e28d8f9f766b13</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2016</creationdate><topic>Air masses</topic><topic>Air pollution</topic><topic>Air quality</topic><topic>Aliphatic compounds</topic><topic>Analysis</topic><topic>Anthropogenic factors</topic><topic>Biogenic emissions</topic><topic>Cities</topic><topic>Diurnal</topic><topic>Emission measurements</topic><topic>Environmental aspects</topic><topic>Flame ionization detectors</topic><topic>Gas chromatography</topic><topic>Hydrocarbons</topic><topic>Hydroxyl 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production</atitle><jtitle>Atmospheric chemistry and physics</jtitle><date>2016-02-24</date><risdate>2016</risdate><volume>16</volume><issue>4</issue><spage>2109</spage><epage>2122</epage><pages>2109-2122</pages><issn>1680-7324</issn><issn>1680-7316</issn><eissn>1680-7324</eissn><abstract>Near-continuous measurements of hydroxyl radical (OH) reactivity in the urban background atmosphere of central London during the summer of 2012 are presented. OH reactivity behaviour is seen to be broadly dependent on air mass origin, with the highest reactivity and the most pronounced diurnal profile observed when air had passed over central London to the east, prior to measurement. Averaged over the entire observation period of 26 days, OH reactivity peaked at ∼ 27 s−1 in the morning, with a minimum of ∼ 15 s−1 during the afternoon. A maximum OH reactivity of 116 s−1 was recorded on one day during morning rush hour. A detailed box model using the Master Chemical Mechanism was used to calculate OH reactivity, and was constrained with an extended measurement data set of volatile organic compounds (VOCs) derived from a gas chromatography flame ionisation detector (GC-FID) and a two-dimensional GC instrument which included heavier molecular weight (up to C12) aliphatic VOCs, oxygenated VOCs and the biogenic VOCs α-pinene and limonene. Comparison was made between observed OH reactivity and modelled OH reactivity using (i) a standard suite of VOC measurements (C2–C8 hydrocarbons and a small selection of oxygenated VOCs) and (ii) a more comprehensive inventory including species up to C12. Modelled reactivities were lower than those measured (by 33 %) when only the reactivity of the standard VOC suite was considered. The difference between measured and modelled reactivity was improved, to within 15 %, if the reactivity of the higher VOCs (⩾ C9) was also considered, with the reactivity of the biogenic compounds of α-pinene and limonene and their oxidation products almost entirely responsible for this improvement. Further improvements in the model's ability to reproduce OH reactivity (to within 6 %) could be achieved if the reactivity and degradation mechanism of unassigned two-dimensional GC peaks were estimated. Neglecting the contribution of the higher VOCs (⩾ C9) (particularly α-pinene and limonene) and model-generated intermediates increases the modelled OH concentrations by 41 %, and the magnitude of in situ ozone production calculated from the production of RO2 was significantly lower (60 %). This work highlights that any future ozone abatement strategies should consider the role that biogenic emissions play alongside anthropogenic emissions in influencing London's air quality.</abstract><cop>Katlenburg-Lindau</cop><pub>Copernicus GmbH</pub><doi>10.5194/acp-16-2109-2016</doi><tpages>14</tpages><orcidid>https://orcid.org/0000-0002-9114-1823</orcidid><orcidid>https://orcid.org/0000-0002-0447-2633</orcidid><orcidid>https://orcid.org/0000-0002-0357-6238</orcidid><orcidid>https://orcid.org/0000-0001-5397-2872</orcidid><orcidid>https://orcid.org/0000-0001-5610-0463</orcidid><oa>free_for_read</oa></addata></record> |
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subjects | Air masses Air pollution Air quality Aliphatic compounds Analysis Anthropogenic factors Biogenic emissions Cities Diurnal Emission measurements Environmental aspects Flame ionization detectors Gas chromatography Hydrocarbons Hydroxyl radicals Intermediates Limonene Mathematical models Measurement Molecular weight Morning Organic compounds Oxidation Oxygenation Ozone Ozone production Pollution abatement Reactivity Urban studies VOCs Volatile organic compounds α-Pinene |
title | Atmospheric OH reactivity in central London: observations, model predictions and estimates of in situ ozone production |
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