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The effect of outdoor air and indoor human activity on mass concentrations of PM sub(1) sub(0), PM sub(2) sub(.) sub(5), and PM sub(1) in a classroom
The 12-h mass concentration of PM sub(1) sub(0), PM sub(2) sub(.) sub(5), and PM sub(1) was measured in a lecturing room by means of three co-located Harvard impactors. The filters were changed at 8 AM and at 8 PM to cover the periods of presence and absence of students. Concentrations were assessed...
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Published in: | Environmental research 2005-10, Vol.99 (2), p.143-149 |
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creator | Branis, M Rezacova, P Domasova, M |
description | The 12-h mass concentration of PM sub(1) sub(0), PM sub(2) sub(.) sub(5), and PM sub(1) was measured in a lecturing room by means of three co-located Harvard impactors. The filters were changed at 8 AM and at 8 PM to cover the periods of presence and absence of students. Concentrations were assessed by gravimetry. Ambient PM sub(1) sub(0) data were available for corresponding 12-h intervals from the nearest state air-quality-monitoring network station. The data were pooled into four periods according to the presence and absence of students-Monday-Thursday day (workday daytime), Monday-Thursday night (workday night), Friday-Sunday day (weekend daytime), and Friday-Sunday night (weekend night). Average indoor workday daytime concentrations were 42.3, 21.9 and 13.7 mu gm super(-) super(3), workday night were 20.9, 19.1 and 15.2 mu gm super(-) super(3), weekend daytime were 21.9, 18.1 and 11.4 mu gm super(-) super(3), and weekend night were 24.5, 21.3, and 15.6 mu gm super(-) super(3) for PM sub(1) sub(0), PM sub(2) sub(.) sub(5), and PM sub(1), respectively. The highest 12-h mean, median, and maximum (42.3, 43.0, and 76.2 mu gm super(-) super(3), respectively) indoor concentrations were recorded on workdays during the daytime for PM sub(1) sub(0). The statistically significant (r=0.68,P |
doi_str_mv | 10.1016/j.envres.2004.12.001 |
format | article |
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The filters were changed at 8 AM and at 8 PM to cover the periods of presence and absence of students. Concentrations were assessed by gravimetry. Ambient PM sub(1) sub(0) data were available for corresponding 12-h intervals from the nearest state air-quality-monitoring network station. The data were pooled into four periods according to the presence and absence of students-Monday-Thursday day (workday daytime), Monday-Thursday night (workday night), Friday-Sunday day (weekend daytime), and Friday-Sunday night (weekend night). Average indoor workday daytime concentrations were 42.3, 21.9 and 13.7 mu gm super(-) super(3), workday night were 20.9, 19.1 and 15.2 mu gm super(-) super(3), weekend daytime were 21.9, 18.1 and 11.4 mu gm super(-) super(3), and weekend night were 24.5, 21.3, and 15.6 mu gm super(-) super(3) for PM sub(1) sub(0), PM sub(2) sub(.) sub(5), and PM sub(1), respectively. The highest 12-h mean, median, and maximum (42.3, 43.0, and 76.2 mu gm super(-) super(3), respectively) indoor concentrations were recorded on workdays during the daytime for PM sub(1) sub(0). The statistically significant (r=0.68,P<0.0009) correlation between the number of students per hour per day and the indoor coarse fraction calculated as PM sub(1) sub(0) sub(-) sub(2) sub(.) sub(5) during daytime on workdays indicates that the presence of people is an important source of coarse particles indoor. On workdays, the daytime PM sub(1) sub(0) indoor/outdoor ratio was positively associated (r=0.93) with an increasing indoor coarse fraction (PM sub(1) sub(0) sub(-) sub(2) sub(.) sub(5)), also indicating that an important portion of indoor PM sub(1) sub(0) had its source inside the classroom. With the exception of the calculated coarse fraction (PM sub(1) sub(0) sub(-) sub(2) sub(.) sub(5)), all of the measured indoor particulate matter fractions were significantly highly correlated with outdoor PM sub(1) sub(0) and negatively correlated with wind velocity, showing that outdoor levels of particles influence their indoor concentrations.</description><identifier>ISSN: 0013-9351</identifier><identifier>DOI: 10.1016/j.envres.2004.12.001</identifier><language>eng</language><ispartof>Environmental research, 2005-10, Vol.99 (2), p.143-149</ispartof><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><link.rule.ids>314,780,784,27924,27925</link.rule.ids></links><search><creatorcontrib>Branis, M</creatorcontrib><creatorcontrib>Rezacova, P</creatorcontrib><creatorcontrib>Domasova, M</creatorcontrib><title>The effect of outdoor air and indoor human activity on mass concentrations of PM sub(1) sub(0), PM sub(2) sub(.) sub(5), and PM sub(1) in a classroom</title><title>Environmental research</title><description>The 12-h mass concentration of PM sub(1) sub(0), PM sub(2) sub(.) sub(5), and PM sub(1) was measured in a lecturing room by means of three co-located Harvard impactors. The filters were changed at 8 AM and at 8 PM to cover the periods of presence and absence of students. Concentrations were assessed by gravimetry. Ambient PM sub(1) sub(0) data were available for corresponding 12-h intervals from the nearest state air-quality-monitoring network station. The data were pooled into four periods according to the presence and absence of students-Monday-Thursday day (workday daytime), Monday-Thursday night (workday night), Friday-Sunday day (weekend daytime), and Friday-Sunday night (weekend night). Average indoor workday daytime concentrations were 42.3, 21.9 and 13.7 mu gm super(-) super(3), workday night were 20.9, 19.1 and 15.2 mu gm super(-) super(3), weekend daytime were 21.9, 18.1 and 11.4 mu gm super(-) super(3), and weekend night were 24.5, 21.3, and 15.6 mu gm super(-) super(3) for PM sub(1) sub(0), PM sub(2) sub(.) sub(5), and PM sub(1), respectively. The highest 12-h mean, median, and maximum (42.3, 43.0, and 76.2 mu gm super(-) super(3), respectively) indoor concentrations were recorded on workdays during the daytime for PM sub(1) sub(0). The statistically significant (r=0.68,P<0.0009) correlation between the number of students per hour per day and the indoor coarse fraction calculated as PM sub(1) sub(0) sub(-) sub(2) sub(.) sub(5) during daytime on workdays indicates that the presence of people is an important source of coarse particles indoor. On workdays, the daytime PM sub(1) sub(0) indoor/outdoor ratio was positively associated (r=0.93) with an increasing indoor coarse fraction (PM sub(1) sub(0) sub(-) sub(2) sub(.) sub(5)), also indicating that an important portion of indoor PM sub(1) sub(0) had its source inside the classroom. With the exception of the calculated coarse fraction (PM sub(1) sub(0) sub(-) sub(2) sub(.) sub(5)), all of the measured indoor particulate matter fractions were significantly highly correlated with outdoor PM sub(1) sub(0) and negatively correlated with wind velocity, showing that outdoor levels of particles influence their indoor concentrations.</description><issn>0013-9351</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2005</creationdate><recordtype>article</recordtype><recordid>eNqNT01LQzEQzEGh9eMf9LAnsWBj9sUn9CyKF8FD7yWm-2jKe1nNJgV_SP9v01bx6mF3mNmZgVVqgkajwcf7jaa4TSS6MeZBY6ONwTM1rtvO5rbFkboQ2VSKrTVjtVusCajryGfgDrjkFXMCF-rEFYR4pOsyuAjO57AN-Rs4wuBEwHP0FHNyOXCUQ_79DaR83OL0CGZ696s0J0WfoK2HQ_2fPdR68H1tTczDlTrvXC90_YOX6ublefH0OvtM_FVI8nII4qnvXSQussR5fa2x1v7buAcymFyw</recordid><startdate>20051001</startdate><enddate>20051001</enddate><creator>Branis, M</creator><creator>Rezacova, P</creator><creator>Domasova, M</creator><scope>7ST</scope><scope>7T4</scope><scope>7TG</scope><scope>7TV</scope><scope>7U6</scope><scope>C1K</scope><scope>KL.</scope></search><sort><creationdate>20051001</creationdate><title>The effect of outdoor air and indoor human activity on mass concentrations of PM sub(1) sub(0), PM sub(2) sub(.) sub(5), and PM sub(1) in a classroom</title><author>Branis, M ; Rezacova, P ; Domasova, M</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-proquest_miscellaneous_199352333</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2005</creationdate><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Branis, M</creatorcontrib><creatorcontrib>Rezacova, P</creatorcontrib><creatorcontrib>Domasova, M</creatorcontrib><collection>Environment Abstracts</collection><collection>Human Population & Natural Resource Management</collection><collection>Meteorological & Geoastrophysical Abstracts</collection><collection>Pollution Abstracts</collection><collection>Sustainability Science Abstracts</collection><collection>Environmental Sciences and Pollution Management</collection><collection>Meteorological & Geoastrophysical Abstracts - Academic</collection><jtitle>Environmental research</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Branis, M</au><au>Rezacova, P</au><au>Domasova, M</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>The effect of outdoor air and indoor human activity on mass concentrations of PM sub(1) sub(0), PM sub(2) sub(.) sub(5), and PM sub(1) in a classroom</atitle><jtitle>Environmental research</jtitle><date>2005-10-01</date><risdate>2005</risdate><volume>99</volume><issue>2</issue><spage>143</spage><epage>149</epage><pages>143-149</pages><issn>0013-9351</issn><abstract>The 12-h mass concentration of PM sub(1) sub(0), PM sub(2) sub(.) sub(5), and PM sub(1) was measured in a lecturing room by means of three co-located Harvard impactors. The filters were changed at 8 AM and at 8 PM to cover the periods of presence and absence of students. Concentrations were assessed by gravimetry. Ambient PM sub(1) sub(0) data were available for corresponding 12-h intervals from the nearest state air-quality-monitoring network station. The data were pooled into four periods according to the presence and absence of students-Monday-Thursday day (workday daytime), Monday-Thursday night (workday night), Friday-Sunday day (weekend daytime), and Friday-Sunday night (weekend night). Average indoor workday daytime concentrations were 42.3, 21.9 and 13.7 mu gm super(-) super(3), workday night were 20.9, 19.1 and 15.2 mu gm super(-) super(3), weekend daytime were 21.9, 18.1 and 11.4 mu gm super(-) super(3), and weekend night were 24.5, 21.3, and 15.6 mu gm super(-) super(3) for PM sub(1) sub(0), PM sub(2) sub(.) sub(5), and PM sub(1), respectively. The highest 12-h mean, median, and maximum (42.3, 43.0, and 76.2 mu gm super(-) super(3), respectively) indoor concentrations were recorded on workdays during the daytime for PM sub(1) sub(0). The statistically significant (r=0.68,P<0.0009) correlation between the number of students per hour per day and the indoor coarse fraction calculated as PM sub(1) sub(0) sub(-) sub(2) sub(.) sub(5) during daytime on workdays indicates that the presence of people is an important source of coarse particles indoor. On workdays, the daytime PM sub(1) sub(0) indoor/outdoor ratio was positively associated (r=0.93) with an increasing indoor coarse fraction (PM sub(1) sub(0) sub(-) sub(2) sub(.) sub(5)), also indicating that an important portion of indoor PM sub(1) sub(0) had its source inside the classroom. With the exception of the calculated coarse fraction (PM sub(1) sub(0) sub(-) sub(2) sub(.) sub(5)), all of the measured indoor particulate matter fractions were significantly highly correlated with outdoor PM sub(1) sub(0) and negatively correlated with wind velocity, showing that outdoor levels of particles influence their indoor concentrations.</abstract><doi>10.1016/j.envres.2004.12.001</doi></addata></record> |
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title | The effect of outdoor air and indoor human activity on mass concentrations of PM sub(1) sub(0), PM sub(2) sub(.) sub(5), and PM sub(1) in a classroom |
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