Lake Michigan air quality: The 1994–2003 LADCO Aircraft Project (LAP)
The goal of the 1994 to 2003 LADCO Airplane Project (LAP) was to study ozone formation over Lake Michigan so that equitable regional control strategies could be devised. This paper for the first time documents LAP in the peer-reviewed literature. Dye et al. (1995) found that the atmosphere over Lake...
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description | The goal of the 1994 to 2003 LADCO Airplane Project (LAP) was to study ozone formation over Lake Michigan so that equitable regional control strategies could be devised. This paper for the first time documents LAP in the peer-reviewed literature.
Dye et al. (1995) found that the atmosphere over Lake Michigan is stable in the summer due to the airwater temperature difference, which creates an efficient reaction chamber for ozone formation. They also hypothesize that the southwest winds characteristic of ozone-conducive conditions transport ozone further north over the lake before it crosses the shoreline onto land. This statistical analysis of LAP data support the hypothesis of Dye et al.
Below 200 m above the lake, ozone formation is VOC-limited in the morning and becomes NO
x limited in the afternoon. Above 200 m, ozone formation is NO
x-limited throughout the day. The onshore NO
x and VOC diurnal cycles peak during the early morning rush hour and are clearly linked to traffic patterns. Over the lake, VOC and NO
y concentrations peak during the mid-morning rather than the early morning, supporting the hypothesis that the land breeze transports VOC and NO
y over the lake. The diurnal NO
x pattern over Lake Michigan is less clearly defined than the VOC pattern possibly as a result of emissions from five coal-burning power plants located on the Lake Michigan shoreline.
Using a “photochemical clock” model, we estimate the climatological average hydroxyl radical concentration over the lake to be (9.43 ± 5.88) × 106 molecule cm
−3 near Chicago and (8.43 ± 3.68) × 106 molecule cm
−3 near Milwaukee.
► First report of a decade-long airplane study of ozone episodes over Lake Michigan. ► O
3 formation is first VOC-limited then NO
x-limited at low altitudes over the lake. ► Average HO
• concentration was estimated using a “photochemical clock”. |
doi_str_mv | 10.1016/j.atmosenv.2011.02.033 |
format | Article |
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Dye et al. (1995) found that the atmosphere over Lake Michigan is stable in the summer due to the airwater temperature difference, which creates an efficient reaction chamber for ozone formation. They also hypothesize that the southwest winds characteristic of ozone-conducive conditions transport ozone further north over the lake before it crosses the shoreline onto land. This statistical analysis of LAP data support the hypothesis of Dye et al.
Below 200 m above the lake, ozone formation is VOC-limited in the morning and becomes NO
x limited in the afternoon. Above 200 m, ozone formation is NO
x-limited throughout the day. The onshore NO
x and VOC diurnal cycles peak during the early morning rush hour and are clearly linked to traffic patterns. Over the lake, VOC and NO
y concentrations peak during the mid-morning rather than the early morning, supporting the hypothesis that the land breeze transports VOC and NO
y over the lake. The diurnal NO
x pattern over Lake Michigan is less clearly defined than the VOC pattern possibly as a result of emissions from five coal-burning power plants located on the Lake Michigan shoreline.
Using a “photochemical clock” model, we estimate the climatological average hydroxyl radical concentration over the lake to be (9.43 ± 5.88) × 106 molecule cm
−3 near Chicago and (8.43 ± 3.68) × 106 molecule cm
−3 near Milwaukee.
► First report of a decade-long airplane study of ozone episodes over Lake Michigan. ► O
3 formation is first VOC-limited then NO
x-limited at low altitudes over the lake. ► Average HO
• concentration was estimated using a “photochemical clock”.</description><identifier>ISSN: 1352-2310</identifier><identifier>EISSN: 1873-2844</identifier><identifier>DOI: 10.1016/j.atmosenv.2011.02.033</identifier><language>eng</language><publisher>Kidlington: Elsevier Ltd</publisher><subject>air quality ; aircraft ; Applied sciences ; atmospheric chemistry ; Atmospheric pollution ; coasts ; emissions ; Exact sciences and technology ; hydroxyl radicals ; Lake breeze ; Lake Michigan ; Lakes ; Land ; Morning ; Ozone ; Ozone trends ; Photochemical age ; Photochemical clock ; Pollution ; power plants ; Shorelines ; statistical analysis ; summer ; temperature ; Transport ; Volatile organic compounds ; wind</subject><ispartof>Atmospheric environment (1994), 2011-06, Vol.45 (18), p.3192-3202</ispartof><rights>2011 Elsevier Ltd</rights><rights>2015 INIST-CNRS</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c431t-1b0e21f1679a7a2337b6d7802909e8339abb59c7dcc5fea796132eec6a0f73a93</citedby><cites>FETCH-LOGICAL-c431t-1b0e21f1679a7a2337b6d7802909e8339abb59c7dcc5fea796132eec6a0f73a93</cites></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><linktohtml>$$Uhttps://www.sciencedirect.com/science/article/pii/S1352231011001671$$EHTML$$P50$$Gelsevier$$H</linktohtml><link.rule.ids>314,776,780,3537,27903,27904,65309</link.rule.ids><backlink>$$Uhttp://pascal-francis.inist.fr/vibad/index.php?action=getRecordDetail&idt=24199687$$DView record in Pascal Francis$$Hfree_for_read</backlink></links><search><creatorcontrib>Foley, Theresa</creatorcontrib><creatorcontrib>Betterton, Eric A.</creatorcontrib><creatorcontrib>Robert Jacko, P.E.</creatorcontrib><creatorcontrib>Hillery, John</creatorcontrib><title>Lake Michigan air quality: The 1994–2003 LADCO Aircraft Project (LAP)</title><title>Atmospheric environment (1994)</title><description>The goal of the 1994 to 2003 LADCO Airplane Project (LAP) was to study ozone formation over Lake Michigan so that equitable regional control strategies could be devised. This paper for the first time documents LAP in the peer-reviewed literature.
Dye et al. (1995) found that the atmosphere over Lake Michigan is stable in the summer due to the airwater temperature difference, which creates an efficient reaction chamber for ozone formation. They also hypothesize that the southwest winds characteristic of ozone-conducive conditions transport ozone further north over the lake before it crosses the shoreline onto land. This statistical analysis of LAP data support the hypothesis of Dye et al.
Below 200 m above the lake, ozone formation is VOC-limited in the morning and becomes NO
x limited in the afternoon. Above 200 m, ozone formation is NO
x-limited throughout the day. The onshore NO
x and VOC diurnal cycles peak during the early morning rush hour and are clearly linked to traffic patterns. Over the lake, VOC and NO
y concentrations peak during the mid-morning rather than the early morning, supporting the hypothesis that the land breeze transports VOC and NO
y over the lake. The diurnal NO
x pattern over Lake Michigan is less clearly defined than the VOC pattern possibly as a result of emissions from five coal-burning power plants located on the Lake Michigan shoreline.
Using a “photochemical clock” model, we estimate the climatological average hydroxyl radical concentration over the lake to be (9.43 ± 5.88) × 106 molecule cm
−3 near Chicago and (8.43 ± 3.68) × 106 molecule cm
−3 near Milwaukee.
► First report of a decade-long airplane study of ozone episodes over Lake Michigan. ► O
3 formation is first VOC-limited then NO
x-limited at low altitudes over the lake. ► Average HO
• concentration was estimated using a “photochemical clock”.</description><subject>air quality</subject><subject>aircraft</subject><subject>Applied sciences</subject><subject>atmospheric chemistry</subject><subject>Atmospheric pollution</subject><subject>coasts</subject><subject>emissions</subject><subject>Exact sciences and technology</subject><subject>hydroxyl radicals</subject><subject>Lake breeze</subject><subject>Lake Michigan</subject><subject>Lakes</subject><subject>Land</subject><subject>Morning</subject><subject>Ozone</subject><subject>Ozone trends</subject><subject>Photochemical age</subject><subject>Photochemical clock</subject><subject>Pollution</subject><subject>power plants</subject><subject>Shorelines</subject><subject>statistical analysis</subject><subject>summer</subject><subject>temperature</subject><subject>Transport</subject><subject>Volatile organic compounds</subject><subject>wind</subject><issn>1352-2310</issn><issn>1873-2844</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2011</creationdate><recordtype>article</recordtype><recordid>eNqFkc9u1DAQhy1EJcqWVwBfEOWQMP6TOObEaoG2UlAr0Z6tWe-k9ZJNWjtbqTfegTfkSfCyhSOcZg7f_Gb0DWMvBZQCRP1uXeK0GRMN96UEIUqQJSj1hB2KxqhCNlo_zb2qZCGVgGfseUprAFDGmkN20uI34l-CvwnXOHAMkd9tsQ_Tw3t-eUNcWKt_fv8hM8_b-cfFOZ-H6CN2E7-I45r8xI_b-cXbI3bQYZ_oxWOdsavPny4Xp0V7fnK2mLeF10pMhVgCSdGJ2lg0KJUyy3plGpAWLDVKWVwuK-vNyvuqIzS2FkoS-RqhMwqtmrE3-9zbON5tKU1uE5KnvseBxm1yjamlrLTWmTz-JymMMUIqXe3Qeo_6OKYUqXO3MWwwPjgBbufYrd0fx27n2IF02XEefP24A5PHvos4-JD-Tkud9dX5CzP2as91ODq8jpm5-pqDKgBhTfWb-LAnKMu7DxRd8oEGT6sQs2S3GsP_jvkFfeObSQ</recordid><startdate>20110601</startdate><enddate>20110601</enddate><creator>Foley, Theresa</creator><creator>Betterton, Eric A.</creator><creator>Robert Jacko, P.E.</creator><creator>Hillery, John</creator><general>Elsevier Ltd</general><general>Elsevier</general><scope>FBQ</scope><scope>IQODW</scope><scope>AAYXX</scope><scope>CITATION</scope><scope>7SU</scope><scope>8FD</scope><scope>C1K</scope><scope>FR3</scope><scope>H8D</scope><scope>KR7</scope><scope>L7M</scope><scope>7ST</scope><scope>7TG</scope><scope>7TV</scope><scope>7U6</scope><scope>KL.</scope><scope>SOI</scope></search><sort><creationdate>20110601</creationdate><title>Lake Michigan air quality: The 1994–2003 LADCO Aircraft Project (LAP)</title><author>Foley, Theresa ; Betterton, Eric A. ; Robert Jacko, P.E. ; Hillery, John</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c431t-1b0e21f1679a7a2337b6d7802909e8339abb59c7dcc5fea796132eec6a0f73a93</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2011</creationdate><topic>air quality</topic><topic>aircraft</topic><topic>Applied sciences</topic><topic>atmospheric chemistry</topic><topic>Atmospheric pollution</topic><topic>coasts</topic><topic>emissions</topic><topic>Exact sciences and technology</topic><topic>hydroxyl radicals</topic><topic>Lake breeze</topic><topic>Lake Michigan</topic><topic>Lakes</topic><topic>Land</topic><topic>Morning</topic><topic>Ozone</topic><topic>Ozone trends</topic><topic>Photochemical age</topic><topic>Photochemical clock</topic><topic>Pollution</topic><topic>power plants</topic><topic>Shorelines</topic><topic>statistical analysis</topic><topic>summer</topic><topic>temperature</topic><topic>Transport</topic><topic>Volatile organic compounds</topic><topic>wind</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Foley, Theresa</creatorcontrib><creatorcontrib>Betterton, Eric A.</creatorcontrib><creatorcontrib>Robert Jacko, P.E.</creatorcontrib><creatorcontrib>Hillery, John</creatorcontrib><collection>AGRIS</collection><collection>Pascal-Francis</collection><collection>CrossRef</collection><collection>Environmental Engineering Abstracts</collection><collection>Technology Research Database</collection><collection>Environmental Sciences and Pollution Management</collection><collection>Engineering Research Database</collection><collection>Aerospace Database</collection><collection>Civil Engineering Abstracts</collection><collection>Advanced Technologies Database with Aerospace</collection><collection>Environment Abstracts</collection><collection>Meteorological & Geoastrophysical Abstracts</collection><collection>Pollution Abstracts</collection><collection>Sustainability Science Abstracts</collection><collection>Meteorological & Geoastrophysical Abstracts - Academic</collection><collection>Environment Abstracts</collection><jtitle>Atmospheric environment (1994)</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Foley, Theresa</au><au>Betterton, Eric A.</au><au>Robert Jacko, P.E.</au><au>Hillery, John</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Lake Michigan air quality: The 1994–2003 LADCO Aircraft Project (LAP)</atitle><jtitle>Atmospheric environment (1994)</jtitle><date>2011-06-01</date><risdate>2011</risdate><volume>45</volume><issue>18</issue><spage>3192</spage><epage>3202</epage><pages>3192-3202</pages><issn>1352-2310</issn><eissn>1873-2844</eissn><abstract>The goal of the 1994 to 2003 LADCO Airplane Project (LAP) was to study ozone formation over Lake Michigan so that equitable regional control strategies could be devised. This paper for the first time documents LAP in the peer-reviewed literature.
Dye et al. (1995) found that the atmosphere over Lake Michigan is stable in the summer due to the airwater temperature difference, which creates an efficient reaction chamber for ozone formation. They also hypothesize that the southwest winds characteristic of ozone-conducive conditions transport ozone further north over the lake before it crosses the shoreline onto land. This statistical analysis of LAP data support the hypothesis of Dye et al.
Below 200 m above the lake, ozone formation is VOC-limited in the morning and becomes NO
x limited in the afternoon. Above 200 m, ozone formation is NO
x-limited throughout the day. The onshore NO
x and VOC diurnal cycles peak during the early morning rush hour and are clearly linked to traffic patterns. Over the lake, VOC and NO
y concentrations peak during the mid-morning rather than the early morning, supporting the hypothesis that the land breeze transports VOC and NO
y over the lake. The diurnal NO
x pattern over Lake Michigan is less clearly defined than the VOC pattern possibly as a result of emissions from five coal-burning power plants located on the Lake Michigan shoreline.
Using a “photochemical clock” model, we estimate the climatological average hydroxyl radical concentration over the lake to be (9.43 ± 5.88) × 106 molecule cm
−3 near Chicago and (8.43 ± 3.68) × 106 molecule cm
−3 near Milwaukee.
► First report of a decade-long airplane study of ozone episodes over Lake Michigan. ► O
3 formation is first VOC-limited then NO
x-limited at low altitudes over the lake. ► Average HO
• concentration was estimated using a “photochemical clock”.</abstract><cop>Kidlington</cop><pub>Elsevier Ltd</pub><doi>10.1016/j.atmosenv.2011.02.033</doi><tpages>11</tpages></addata></record> |
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subjects | air quality aircraft Applied sciences atmospheric chemistry Atmospheric pollution coasts emissions Exact sciences and technology hydroxyl radicals Lake breeze Lake Michigan Lakes Land Morning Ozone Ozone trends Photochemical age Photochemical clock Pollution power plants Shorelines statistical analysis summer temperature Transport Volatile organic compounds wind |
title | Lake Michigan air quality: The 1994–2003 LADCO Aircraft Project (LAP) |
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