Importance of gas-particle partitioning of ammonia in haze formation in the rural agricultural environment

<p>Ammonia in the atmosphere is essential for the formation of fine particles that impact air quality and climate. Despite extensive prior research to disentangle the relationship between ammonia and haze pollution, the role of ammonia in haze formation in high ammonia-emitting regions is stil...

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Main Authors: J. Xu, J. Chen, N. Zhao, G. Wang, G. Yu, H. Li, J. Huo, Y. Lin, Q. Fu, H. Guo, C. Deng, S.-H. Lee, K. Huang
Format: Article
Language:English
Published: Copernicus Publications 2020-06-01
Series:Atmospheric Chemistry and Physics
Online Access:https://www.atmos-chem-phys.net/20/7259/2020/acp-20-7259-2020.pdf
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author J. Xu
J. Chen
N. Zhao
G. Wang
G. Yu
H. Li
J. Huo
Y. Lin
Q. Fu
H. Guo
C. Deng
S.-H. Lee
J. Chen
K. Huang
K. Huang
author_facet J. Xu
J. Chen
N. Zhao
G. Wang
G. Yu
H. Li
J. Huo
Y. Lin
Q. Fu
H. Guo
C. Deng
S.-H. Lee
J. Chen
K. Huang
K. Huang
author_sort J. Xu
collection DOAJ
description <p>Ammonia in the atmosphere is essential for the formation of fine particles that impact air quality and climate. Despite extensive prior research to disentangle the relationship between ammonia and haze pollution, the role of ammonia in haze formation in high ammonia-emitting regions is still not well understood. Aiming to better understand secondary inorganic aerosol (sulfate, nitrate, ammonium – SNA) formation mechanisms under high-ammonia conditions, 1-year hourly measurement of water-soluble inorganic species (gas and particle) was conducted at a rural supersite in Shanghai. Exceedingly high levels of agricultural ammonia, constantly around 30&thinsp;<span class="inline-formula">µ</span>g&thinsp;m<span class="inline-formula"><sup>−3</sup></span>, were observed. We find that gas-particle partitioning of ammonia (<span class="inline-formula"><i>ε</i></span><span class="inline-formula"><math xmlns="http://www.w3.org/1998/Math/MathML" id="M4" display="inline" overflow="scroll" dspmath="mathml"><mrow class="chem"><mo>(</mo><msubsup><mi mathvariant="normal">NH</mi><mn mathvariant="normal">4</mn><mo>+</mo></msubsup><mo>)</mo></mrow></math><span><svg:svg xmlns:svg="http://www.w3.org/2000/svg" width="31pt" height="15pt" class="svg-formula" dspmath="mathimg" md5hash="91d49abe6d72fd4b0e5a1f1b4385a2d5"><svg:image xmlns:xlink="http://www.w3.org/1999/xlink" xlink:href="acp-20-7259-2020-ie00001.svg" width="31pt" height="15pt" src="acp-20-7259-2020-ie00001.png"/></svg:svg></span></span>), as opposed to ammonia concentrations, plays a critical role in SNA formation during the haze period. From an assessment of the effects of various parameters, including temperature (<span class="inline-formula"><i>T</i></span>), aerosol water content (AWC), aerosol pH, and activity coefficient, it seems that AWC plays predominant regulating roles for <span class="inline-formula"><i>ε</i></span><span class="inline-formula"><math xmlns="http://www.w3.org/1998/Math/MathML" id="M7" display="inline" overflow="scroll" dspmath="mathml"><mrow class="chem"><mo>(</mo><msubsup><mi mathvariant="normal">NH</mi><mn mathvariant="normal">4</mn><mo>+</mo></msubsup><mo>)</mo></mrow></math><span><svg:svg xmlns:svg="http://www.w3.org/2000/svg" width="31pt" height="15pt" class="svg-formula" dspmath="mathimg" md5hash="459544f7453cdb23fbb6134fb577afe9"><svg:image xmlns:xlink="http://www.w3.org/1999/xlink" xlink:href="acp-20-7259-2020-ie00002.svg" width="31pt" height="15pt" src="acp-20-7259-2020-ie00002.png"/></svg:svg></span></span>. We propose a self-amplifying feedback mechanism associated with <span class="inline-formula"><i>ε</i></span><span class="inline-formula"><math xmlns="http://www.w3.org/1998/Math/MathML" id="M9" display="inline" overflow="scroll" dspmath="mathml"><mrow class="chem"><mo>(</mo><msubsup><mi mathvariant="normal">NH</mi><mn mathvariant="normal">4</mn><mo>+</mo></msubsup><mo>)</mo></mrow></math><span><svg:svg xmlns:svg="http://www.w3.org/2000/svg" width="31pt" height="15pt" class="svg-formula" dspmath="mathimg" md5hash="b3dc5eafd33a1d448ae2e5721d3e9b65"><svg:image xmlns:xlink="http://www.w3.org/1999/xlink" xlink:href="acp-20-7259-2020-ie00003.svg" width="31pt" height="15pt" src="acp-20-7259-2020-ie00003.png"/></svg:svg></span></span> for the formation of SNA, which is consistent with diurnal variations in <span class="inline-formula"><i>ε</i></span><span class="inline-formula"><math xmlns="http://www.w3.org/1998/Math/MathML" id="M11" display="inline" overflow="scroll" dspmath="mathml"><mrow class="chem"><mo>(</mo><msubsup><mi mathvariant="normal">NH</mi><mn mathvariant="normal">4</mn><mo>+</mo></msubsup><mo>)</mo></mrow></math><span><svg:svg xmlns:svg="http://www.w3.org/2000/svg" width="31pt" height="15pt" class="svg-formula" dspmath="mathimg" md5hash="9035a82d717fef1a3b8f58fb0723e83a"><svg:image xmlns:xlink="http://www.w3.org/1999/xlink" xlink:href="acp-20-7259-2020-ie00004.svg" width="31pt" height="15pt" src="acp-20-7259-2020-ie00004.png"/></svg:svg></span></span>, AWC, and SNA. Our results imply that a reduction in ammonia emissions alone may not reduce SNA effectively, at least at rural agricultural sites in China.</p>
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spelling doaj.art-1b519b58f6b64200a65a052dec5c1b442022-12-22T00:34:57ZengCopernicus PublicationsAtmospheric Chemistry and Physics1680-73161680-73242020-06-01207259726910.5194/acp-20-7259-2020Importance of gas-particle partitioning of ammonia in haze formation in the rural agricultural environmentJ. Xu0J. Chen1N. Zhao2G. Wang3G. Yu4H. Li5J. Huo6Y. Lin7Q. Fu8H. Guo9C. Deng10S.-H. Lee11J. Chen12K. Huang13K. Huang14Shanghai Key Laboratory of Atmospheric Particle Pollution and Prevention (LAP3), Department of Environmental Science and Engineering, Fudan University, Shanghai, 200433, ChinaShanghai Key Laboratory of Atmospheric Particle Pollution and Prevention (LAP3), Department of Environmental Science and Engineering, Fudan University, Shanghai, 200433, ChinaShanghai Key Laboratory of Atmospheric Particle Pollution and Prevention (LAP3), Department of Environmental Science and Engineering, Fudan University, Shanghai, 200433, ChinaShanghai Key Laboratory of Atmospheric Particle Pollution and Prevention (LAP3), Department of Environmental Science and Engineering, Fudan University, Shanghai, 200433, ChinaShanghai Key Laboratory of Atmospheric Particle Pollution and Prevention (LAP3), Department of Environmental Science and Engineering, Fudan University, Shanghai, 200433, ChinaShanghai Key Laboratory of Atmospheric Particle Pollution and Prevention (LAP3), Department of Environmental Science and Engineering, Fudan University, Shanghai, 200433, ChinaShanghai Environmental Monitoring Center, Shanghai, 200030, ChinaShanghai Environmental Monitoring Center, Shanghai, 200030, ChinaShanghai Environmental Monitoring Center, Shanghai, 200030, ChinaCooperative Institute for Research in Environmental Sciences and Department of Chemistry, University of Colorado, Boulder, Colorado 80309, USAShanghai Key Laboratory of Atmospheric Particle Pollution and Prevention (LAP3), Department of Environmental Science and Engineering, Fudan University, Shanghai, 200433, ChinaDepartment of Atmospheric Science, University of Alabama in Huntsville, Huntsville, Alabama 35758, USAShanghai Key Laboratory of Atmospheric Particle Pollution and Prevention (LAP3), Department of Environmental Science and Engineering, Fudan University, Shanghai, 200433, ChinaShanghai Key Laboratory of Atmospheric Particle Pollution and Prevention (LAP3), Department of Environmental Science and Engineering, Fudan University, Shanghai, 200433, ChinaInstitute of Eco-Chongming (IEC), No.20 Cuiniao Road, Chen Jiazhen, Shanghai, 202162, China<p>Ammonia in the atmosphere is essential for the formation of fine particles that impact air quality and climate. Despite extensive prior research to disentangle the relationship between ammonia and haze pollution, the role of ammonia in haze formation in high ammonia-emitting regions is still not well understood. Aiming to better understand secondary inorganic aerosol (sulfate, nitrate, ammonium – SNA) formation mechanisms under high-ammonia conditions, 1-year hourly measurement of water-soluble inorganic species (gas and particle) was conducted at a rural supersite in Shanghai. Exceedingly high levels of agricultural ammonia, constantly around 30&thinsp;<span class="inline-formula">µ</span>g&thinsp;m<span class="inline-formula"><sup>−3</sup></span>, were observed. We find that gas-particle partitioning of ammonia (<span class="inline-formula"><i>ε</i></span><span class="inline-formula"><math xmlns="http://www.w3.org/1998/Math/MathML" id="M4" display="inline" overflow="scroll" dspmath="mathml"><mrow class="chem"><mo>(</mo><msubsup><mi mathvariant="normal">NH</mi><mn mathvariant="normal">4</mn><mo>+</mo></msubsup><mo>)</mo></mrow></math><span><svg:svg xmlns:svg="http://www.w3.org/2000/svg" width="31pt" height="15pt" class="svg-formula" dspmath="mathimg" md5hash="91d49abe6d72fd4b0e5a1f1b4385a2d5"><svg:image xmlns:xlink="http://www.w3.org/1999/xlink" xlink:href="acp-20-7259-2020-ie00001.svg" width="31pt" height="15pt" src="acp-20-7259-2020-ie00001.png"/></svg:svg></span></span>), as opposed to ammonia concentrations, plays a critical role in SNA formation during the haze period. From an assessment of the effects of various parameters, including temperature (<span class="inline-formula"><i>T</i></span>), aerosol water content (AWC), aerosol pH, and activity coefficient, it seems that AWC plays predominant regulating roles for <span class="inline-formula"><i>ε</i></span><span class="inline-formula"><math xmlns="http://www.w3.org/1998/Math/MathML" id="M7" display="inline" overflow="scroll" dspmath="mathml"><mrow class="chem"><mo>(</mo><msubsup><mi mathvariant="normal">NH</mi><mn mathvariant="normal">4</mn><mo>+</mo></msubsup><mo>)</mo></mrow></math><span><svg:svg xmlns:svg="http://www.w3.org/2000/svg" width="31pt" height="15pt" class="svg-formula" dspmath="mathimg" md5hash="459544f7453cdb23fbb6134fb577afe9"><svg:image xmlns:xlink="http://www.w3.org/1999/xlink" xlink:href="acp-20-7259-2020-ie00002.svg" width="31pt" height="15pt" src="acp-20-7259-2020-ie00002.png"/></svg:svg></span></span>. We propose a self-amplifying feedback mechanism associated with <span class="inline-formula"><i>ε</i></span><span class="inline-formula"><math xmlns="http://www.w3.org/1998/Math/MathML" id="M9" display="inline" overflow="scroll" dspmath="mathml"><mrow class="chem"><mo>(</mo><msubsup><mi mathvariant="normal">NH</mi><mn mathvariant="normal">4</mn><mo>+</mo></msubsup><mo>)</mo></mrow></math><span><svg:svg xmlns:svg="http://www.w3.org/2000/svg" width="31pt" height="15pt" class="svg-formula" dspmath="mathimg" md5hash="b3dc5eafd33a1d448ae2e5721d3e9b65"><svg:image xmlns:xlink="http://www.w3.org/1999/xlink" xlink:href="acp-20-7259-2020-ie00003.svg" width="31pt" height="15pt" src="acp-20-7259-2020-ie00003.png"/></svg:svg></span></span> for the formation of SNA, which is consistent with diurnal variations in <span class="inline-formula"><i>ε</i></span><span class="inline-formula"><math xmlns="http://www.w3.org/1998/Math/MathML" id="M11" display="inline" overflow="scroll" dspmath="mathml"><mrow class="chem"><mo>(</mo><msubsup><mi mathvariant="normal">NH</mi><mn mathvariant="normal">4</mn><mo>+</mo></msubsup><mo>)</mo></mrow></math><span><svg:svg xmlns:svg="http://www.w3.org/2000/svg" width="31pt" height="15pt" class="svg-formula" dspmath="mathimg" md5hash="9035a82d717fef1a3b8f58fb0723e83a"><svg:image xmlns:xlink="http://www.w3.org/1999/xlink" xlink:href="acp-20-7259-2020-ie00004.svg" width="31pt" height="15pt" src="acp-20-7259-2020-ie00004.png"/></svg:svg></span></span>, AWC, and SNA. Our results imply that a reduction in ammonia emissions alone may not reduce SNA effectively, at least at rural agricultural sites in China.</p>https://www.atmos-chem-phys.net/20/7259/2020/acp-20-7259-2020.pdf
spellingShingle J. Xu
J. Chen
N. Zhao
G. Wang
G. Yu
H. Li
J. Huo
Y. Lin
Q. Fu
H. Guo
C. Deng
S.-H. Lee
J. Chen
K. Huang
K. Huang
Importance of gas-particle partitioning of ammonia in haze formation in the rural agricultural environment
Atmospheric Chemistry and Physics
title Importance of gas-particle partitioning of ammonia in haze formation in the rural agricultural environment
title_full Importance of gas-particle partitioning of ammonia in haze formation in the rural agricultural environment
title_fullStr Importance of gas-particle partitioning of ammonia in haze formation in the rural agricultural environment
title_full_unstemmed Importance of gas-particle partitioning of ammonia in haze formation in the rural agricultural environment
title_short Importance of gas-particle partitioning of ammonia in haze formation in the rural agricultural environment
title_sort importance of gas particle partitioning of ammonia in haze formation in the rural agricultural environment
url https://www.atmos-chem-phys.net/20/7259/2020/acp-20-7259-2020.pdf
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