Long-term total OH reactivity measurements in a boreal forest

<p>Total hydroxyl radical (OH) reactivity measurements were conducted at the second Station for Measuring Ecosystem–Atmosphere Relations (SMEAR II), a boreal forest site located in Hyytiälä, Finland, from April to July 2016. The measured values were compared with OH reactivity calculated from...

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Main Authors: A. P. Praplan, T. Tykkä, D. Chen, M. Boy, D. Taipale, V. Vakkari, P. Zhou, T. Petäjä, H. Hellén
Format: Article
Language:English
Published: Copernicus Publications 2019-11-01
Series:Atmospheric Chemistry and Physics
Online Access:https://www.atmos-chem-phys.net/19/14431/2019/acp-19-14431-2019.pdf
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author A. P. Praplan
T. Tykkä
D. Chen
M. Boy
D. Taipale
V. Vakkari
V. Vakkari
P. Zhou
T. Petäjä
H. Hellén
spellingShingle A. P. Praplan
T. Tykkä
D. Chen
M. Boy
D. Taipale
V. Vakkari
V. Vakkari
P. Zhou
T. Petäjä
H. Hellén
Long-term total OH reactivity measurements in a boreal forest
Atmospheric Chemistry and Physics
author_facet A. P. Praplan
T. Tykkä
D. Chen
M. Boy
D. Taipale
V. Vakkari
V. Vakkari
P. Zhou
T. Petäjä
H. Hellén
author_sort A. P. Praplan
title Long-term total OH reactivity measurements in a boreal forest
title_short Long-term total OH reactivity measurements in a boreal forest
title_full Long-term total OH reactivity measurements in a boreal forest
title_fullStr Long-term total OH reactivity measurements in a boreal forest
title_full_unstemmed Long-term total OH reactivity measurements in a boreal forest
title_sort long-term total oh reactivity measurements in a boreal forest
publisher Copernicus Publications
series Atmospheric Chemistry and Physics
issn 1680-7316
1680-7324
publishDate 2019-11-01
description <p>Total hydroxyl radical (OH) reactivity measurements were conducted at the second Station for Measuring Ecosystem–Atmosphere Relations (SMEAR II), a boreal forest site located in Hyytiälä, Finland, from April to July 2016. The measured values were compared with OH reactivity calculated from a combination of data from the routine trace gas measurements (station mast) as well as online and offline analysis with a gas chromatographer coupled to a mass spectrometer (GC–MS) and offline liquid chromatography. Up to 104 compounds, mostly volatile organic compounds (VOCs) and oxidized VOCs, but also inorganic compounds, were included in the analysis, even though the data availability for each compound varied with time. The monthly averaged experimental total OH reactivity was found to be higher in April and May (ca. 20&thinsp;s<span class="inline-formula"><sup>−1</sup></span>) than in June and July (7.6 and 15.4&thinsp;s<span class="inline-formula"><sup>−1</sup></span>, respectively). The measured values varied much more in spring with high reactivity peaks in late afternoon, with values higher than in the summer, in particular when the soil was thawing. Total OH reactivity values generally followed the pattern of mixing ratios due to change of the boundary layer height. The missing reactivity fraction (defined as the difference between measured and calculated OH reactivity) was found to be high. Several reasons that can explain the missing reactivity are discussed in detail such as (1) missing measurements due to technical issues, (2) not measuring oxidation compounds of detected biogenic VOCs, and (3) missing important reactive compounds or classes of compounds with the available measurements. In order to test the second hypothesis, a one-dimensional chemical transport model (SOSAA) has been used to estimate the amount of unmeasured oxidation products and their expected contribution to the reactivity for three different short periods in April, May, and July. However, only a small fraction (<span class="inline-formula">&lt;4.5</span>&thinsp;%) of the missing reactivity can be explained by modelled secondary compounds (mostly oxidized VOCs). These findings indicate that compounds measured but not included in the model as well as unmeasured primary emissions contribute the missing reactivity. In the future, non-hydrocarbon compounds from sources other than vegetation (e.g. soil) should be included in OH reactivity studies.</p>
url https://www.atmos-chem-phys.net/19/14431/2019/acp-19-14431-2019.pdf
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spelling doaj-27ac57bbbdc9414ba59f5863ba02a30b2020-11-25T01:35:07ZengCopernicus PublicationsAtmospheric Chemistry and Physics1680-73161680-73242019-11-0119144311445310.5194/acp-19-14431-2019Long-term total OH reactivity measurements in a boreal forestA. P. Praplan0T. Tykkä1D. Chen2M. Boy3D. Taipale4V. Vakkari5V. Vakkari6P. Zhou7T. Petäjä8H. Hellén9Atmospheric Composition Research, Finnish Meteorological Institute, P. O. Box 503, 00101 Helsinki, FinlandAtmospheric Composition Research, Finnish Meteorological Institute, P. O. Box 503, 00101 Helsinki, FinlandInstitute for Atmospheric and Earth System Research/Physics, Faculty of Science, P. O. Box 64, 00014 University of Helsinki, Helsinki, FinlandInstitute for Atmospheric and Earth System Research/Physics, Faculty of Science, P. O. Box 64, 00014 University of Helsinki, Helsinki, FinlandInstitute for Atmospheric and Earth System Research/Physics, Faculty of Science, P. O. Box 64, 00014 University of Helsinki, Helsinki, FinlandAtmospheric Composition Research, Finnish Meteorological Institute, P. O. Box 503, 00101 Helsinki, FinlandUnit for Environmental Sciences and Management, North-West University, 2520 Potchefstroom, South AfricaInstitute for Atmospheric and Earth System Research/Physics, Faculty of Science, P. O. Box 64, 00014 University of Helsinki, Helsinki, FinlandInstitute for Atmospheric and Earth System Research/Physics, Faculty of Science, P. O. Box 64, 00014 University of Helsinki, Helsinki, FinlandAtmospheric Composition Research, Finnish Meteorological Institute, P. O. Box 503, 00101 Helsinki, Finland<p>Total hydroxyl radical (OH) reactivity measurements were conducted at the second Station for Measuring Ecosystem–Atmosphere Relations (SMEAR II), a boreal forest site located in Hyytiälä, Finland, from April to July 2016. The measured values were compared with OH reactivity calculated from a combination of data from the routine trace gas measurements (station mast) as well as online and offline analysis with a gas chromatographer coupled to a mass spectrometer (GC–MS) and offline liquid chromatography. Up to 104 compounds, mostly volatile organic compounds (VOCs) and oxidized VOCs, but also inorganic compounds, were included in the analysis, even though the data availability for each compound varied with time. The monthly averaged experimental total OH reactivity was found to be higher in April and May (ca. 20&thinsp;s<span class="inline-formula"><sup>−1</sup></span>) than in June and July (7.6 and 15.4&thinsp;s<span class="inline-formula"><sup>−1</sup></span>, respectively). The measured values varied much more in spring with high reactivity peaks in late afternoon, with values higher than in the summer, in particular when the soil was thawing. Total OH reactivity values generally followed the pattern of mixing ratios due to change of the boundary layer height. The missing reactivity fraction (defined as the difference between measured and calculated OH reactivity) was found to be high. Several reasons that can explain the missing reactivity are discussed in detail such as (1) missing measurements due to technical issues, (2) not measuring oxidation compounds of detected biogenic VOCs, and (3) missing important reactive compounds or classes of compounds with the available measurements. In order to test the second hypothesis, a one-dimensional chemical transport model (SOSAA) has been used to estimate the amount of unmeasured oxidation products and their expected contribution to the reactivity for three different short periods in April, May, and July. However, only a small fraction (<span class="inline-formula">&lt;4.5</span>&thinsp;%) of the missing reactivity can be explained by modelled secondary compounds (mostly oxidized VOCs). These findings indicate that compounds measured but not included in the model as well as unmeasured primary emissions contribute the missing reactivity. In the future, non-hydrocarbon compounds from sources other than vegetation (e.g. soil) should be included in OH reactivity studies.</p>https://www.atmos-chem-phys.net/19/14431/2019/acp-19-14431-2019.pdf