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<rdf:RDF xmlns:rdf="http://www.w3.org/1999/02/22-rdf-syntax-ns#"><channel rdf:about="http://onlinelibrary.wiley.com/rss/journal/10.1111/(ISSN)1600-0668" xmlns="http://purl.org/rss/1.0/"><title>Indoor Air</title><description> Wiley Online Library : Indoor Air</description><link>http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2F%28ISSN%291600-0668</link><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc</dc:publisher><dc:language xmlns:dc="http://purl.org/dc/elements/1.1/">en</dc:language><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/">© 2013 John Wiley &amp; Sons A/S</dc:rights><prism:issn xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">0905-6947</prism:issn><prism:eIssn xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">1600-0668</prism:eIssn><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2013-06-01T00:00:00-05:00</dc:date><prism:coverDisplayDate xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">June 2013</prism:coverDisplayDate><prism:volume xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">23</prism:volume><prism:number xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">3</prism:number><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">173</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">264</prism:endingPage><image rdf:resource="http://onlinelibrary.wiley.com/store/10.1111/ina.2013.23.issue-3/asset/cover.gif?v=1&amp;s=9f546c8d0371b589f3013327df566ad7eef0519c"/><items><rdf:Seq><rdf:li rdf:resource="http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12050"/><rdf:li rdf:resource="http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12048"/><rdf:li rdf:resource="http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12034"/><rdf:li rdf:resource="http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12033"/><rdf:li rdf:resource="http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12047"/><rdf:li rdf:resource="http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12049"/><rdf:li rdf:resource="http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12046"/><rdf:li rdf:resource="http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12045"/><rdf:li rdf:resource="http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12044"/><rdf:li rdf:resource="http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12042"/><rdf:li rdf:resource="http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12043"/><rdf:li rdf:resource="http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12041"/><rdf:li rdf:resource="http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12040"/><rdf:li rdf:resource="http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12039"/><rdf:li rdf:resource="http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12029"/><rdf:li rdf:resource="http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12031"/><rdf:li rdf:resource="http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12038"/><rdf:li rdf:resource="http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12032"/><rdf:li rdf:resource="http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12036"/><rdf:li rdf:resource="http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12037"/><rdf:li rdf:resource="http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12035"/><rdf:li rdf:resource="http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12027"/><rdf:li rdf:resource="http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12021"/><rdf:li rdf:resource="http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12025"/><rdf:li rdf:resource="http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12024"/><rdf:li rdf:resource="http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12022"/><rdf:li rdf:resource="http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12018"/><rdf:li rdf:resource="http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12020"/><rdf:li rdf:resource="http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12009"/><rdf:li rdf:resource="http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12030"/><rdf:li rdf:resource="http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12019"/><rdf:li rdf:resource="http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12013"/><rdf:li rdf:resource="http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12015"/><rdf:li rdf:resource="http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12017"/><rdf:li rdf:resource="http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12016"/><rdf:li rdf:resource="http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12002"/><rdf:li rdf:resource="http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12010"/><rdf:li rdf:resource="http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12012"/><rdf:li rdf:resource="http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12028"/></rdf:Seq></items></channel><item rdf:about="http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12050" xmlns="http://purl.org/rss/1.0/"><title>Non-linear Eddy Viscosity Modelling and Experimental Study of Jet Spreading Rates</title><link>http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12050</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Non-linear Eddy Viscosity Modelling and Experimental Study of Jet Spreading Rates</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Christian Heschl, Kiao Inthavong, Wolfgang Sanz, Jiyuan Tu</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2013-05-13T20:30:25.184883-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/ina.12050</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/ina.12050</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12050</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Original Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[
<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Abstract</h3>
<div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Indoor airflow pattern are strongly influenced by turbulent shear and turbulent normal stresses which are responsible for entrainment effects and turbulence-driven secondary motion. Therefore an accurate prediction of room airflows requires reliable modelling of these turbulent quantities. The most basic turbulence models include RANS-based models which provide quick solutions but are known to fail in turbulent free shear and wall effected flows. In order to cope with this difficulty this paper presents a non-linear k-ε turbulence model and evaluates it along with linear k- ε models for an indoor isothermal linear diffuser jet flow measured in two model rooms using PIV. The results show that the flow contains a free jet near the inlet region and a wall affected region downstream where the jet is pushed towards the ceiling by entrainment through the well-known Coanda effect. The CFD results showed that an accurate prediction of the entrainment process is very important and that the nonlinear eddy viscosity model is able to predict the turbulence-driven secondary motions. Furthermore, turbulence models which are calibrated for high-Reynolds free- shear layer flows were not able to reproduce the measured velocity distributions and it is suggested that the model constants of turbulence models should be adjusted before they are used for room airflow simulations.</p></div>
<div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>This article is protected by copyright. All rights reserved.</p></div>
]]></content:encoded><description>

Indoor airflow pattern are strongly influenced by turbulent shear and turbulent normal stresses which are responsible for entrainment effects and turbulence-driven secondary motion. Therefore an accurate prediction of room airflows requires reliable modelling of these turbulent quantities. The most basic turbulence models include RANS-based models which provide quick solutions but are known to fail in turbulent free shear and wall effected flows. In order to cope with this difficulty this paper presents a non-linear k-ε turbulence model and evaluates it along with linear k- ε models for an indoor isothermal linear diffuser jet flow measured in two model rooms using PIV. The results show that the flow contains a free jet near the inlet region and a wall affected region downstream where the jet is pushed towards the ceiling by entrainment through the well-known Coanda effect. The CFD results showed that an accurate prediction of the entrainment process is very important and that the nonlinear eddy viscosity model is able to predict the turbulence-driven secondary motions. Furthermore, turbulence models which are calibrated for high-Reynolds free- shear layer flows were not able to reproduce the measured velocity distributions and it is suggested that the model constants of turbulence models should be adjusted before they are used for room airflow simulations.
This article is protected by copyright. All rights reserved.
</description></item><item rdf:about="http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12048" xmlns="http://purl.org/rss/1.0/"><title>Analysis of selected phthalates in Canadian indoor dust collected using a household vacuum and a standardized sampling techniques</title><link>http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12048</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Analysis of selected phthalates in Canadian indoor dust collected using a household vacuum and a standardized sampling techniques</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">C. Kubwabo, P. E. Rasmussen, X. Fan, I. Kosarac, F. Wu, A. Zidek, S.L. Kuchta</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2013-04-28T20:57:04.928531-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/ina.12048</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/ina.12048</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12048</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Original Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[
<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Abstract</h3>
<div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Phthalates have been used extensively as plasticizers to improve the flexibility of polymers, and they also have found many industrial applications. They are ubiquitous in the environment and have been detected in a variety of environmental and biological matrices. The goal of this study was to develop a method for the determination of 17 phthalate esters in house dust. This method involved sonication extraction, sample clean-up using solid phase extraction, and isotope dilution GC/MS/MS analysis. Method detection limits and recoveries ranged from 0.04 to 2.93 μg/g, and from 84 to 117 %, respectively. The method was applied to the analysis of phthalates in 39 paired household vacuum samples (HD) and fresh dust (FD) samples. HD and FD samples compared well for the majority of phthalates detected in house dust. Data obtained from 126 household dust samples confirmed the historical widespread use of bis(2-ethylhexyl) phthalate (DEHP), with a concentration range of 36 μg/g to 3840 μg/g. Dibutyl phthalate (DBP), benzyl butyl phthalate (BzBP), diisononyl phthalate (DINP), and diisodecyl phthalate (DIDP) were also found in most samples at relatively high concentrations. Another important phthalate, diisobutyl phthalate (DIBP), was detected at a frequency of 98.4% with concentrations ranging from below the MDL of 0.51 μg/g to 69 μg/g. Household and fresh dust samples compared well for the majority of phthalates detected in house dust.</p></div>
<div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>This article is protected by copyright. All rights reserved.</p></div>
]]></content:encoded><description>

Phthalates have been used extensively as plasticizers to improve the flexibility of polymers, and they also have found many industrial applications. They are ubiquitous in the environment and have been detected in a variety of environmental and biological matrices. The goal of this study was to develop a method for the determination of 17 phthalate esters in house dust. This method involved sonication extraction, sample clean-up using solid phase extraction, and isotope dilution GC/MS/MS analysis. Method detection limits and recoveries ranged from 0.04 to 2.93 μg/g, and from 84 to 117 %, respectively. The method was applied to the analysis of phthalates in 39 paired household vacuum samples (HD) and fresh dust (FD) samples. HD and FD samples compared well for the majority of phthalates detected in house dust. Data obtained from 126 household dust samples confirmed the historical widespread use of bis(2-ethylhexyl) phthalate (DEHP), with a concentration range of 36 μg/g to 3840 μg/g. Dibutyl phthalate (DBP), benzyl butyl phthalate (BzBP), diisononyl phthalate (DINP), and diisodecyl phthalate (DIDP) were also found in most samples at relatively high concentrations. Another important phthalate, diisobutyl phthalate (DIBP), was detected at a frequency of 98.4% with concentrations ranging from below the MDL of 0.51 μg/g to 69 μg/g. Household and fresh dust samples compared well for the majority of phthalates detected in house dust.
This article is protected by copyright. All rights reserved.
</description></item><item rdf:about="http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12034" xmlns="http://purl.org/rss/1.0/"><title>Limitations of climate chamber studies into thermal comfort and workers’ performance</title><link>http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12034</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Limitations of climate chamber studies into thermal comfort and workers’ performance</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Joe L. Leyten, Stanley R. Kurvers</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2013-02-18T07:59:33.074398-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/ina.12034</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/ina.12034</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12034</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Letter to the Editor</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[
<div class="para" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib" xmlns="http://www.w3.org/1999/xhtml"><p>We would like to respond to the article by Lan et al. (2011). In this study subjects in a climate chamber were exposed to two temperatures: 22 and 30°C. In both conditions the clo-value was 0.9. The subjects performed mental tests and simulated office work. During and after exposure physiological tests were taken, among them heart rate and respiratory ventilation.</p></div>
<div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>© 2013 John Wiley &amp; Sons A/S. Published by Blackwell Publishing Ltd</p></div>
]]></content:encoded><description>
We would like to respond to the article by Lan et al. (2011). In this study subjects in a climate chamber were exposed to two temperatures: 22 and 30°C. In both conditions the clo-value was 0.9. The subjects performed mental tests and simulated office work. During and after exposure physiological tests were taken, among them heart rate and respiratory ventilation.
© 2013 John Wiley &amp; Sons A/S. Published by Blackwell Publishing Ltd
</description></item><item rdf:about="http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12033" xmlns="http://purl.org/rss/1.0/"><title>Warmth and performance: reply to the letter from Leyton and Kurvers (2013)</title><link>http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12033</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Warmth and performance: reply to the letter from Leyton and Kurvers (2013)</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Li Lan</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2013-02-18T07:59:24.13848-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/ina.12033</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/ina.12033</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12033</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Letter to the Editor</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[
<div class="para" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib" xmlns="http://www.w3.org/1999/xhtml"><p>Thank you for giving us an opportunity to reply to the letter from Leyten and Kurvers (2013) concerning our recent paper on the effects of thermal discomfort in an office (Lan et al. 2011). Our experiment does not show which of several possibly driving factors caused our subjects to perform simulated office work about 10% more slowly when they felt too hot at 30°C. It could indeed have been the fact that they felt too hot, in which case the effect would not occur if they did not feel too hot at that temperature.</p></div>
<div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>© 2013 John Wiley &amp; Sons A/S. Published by Blackwell Publishing Ltd</p></div>
]]></content:encoded><description>
Thank you for giving us an opportunity to reply to the letter from Leyten and Kurvers (2013) concerning our recent paper on the effects of thermal discomfort in an office (Lan et al. 2011). Our experiment does not show which of several possibly driving factors caused our subjects to perform simulated office work about 10% more slowly when they felt too hot at 30°C. It could indeed have been the fact that they felt too hot, in which case the effect would not occur if they did not feel too hot at that temperature.
© 2013 John Wiley &amp; Sons A/S. Published by Blackwell Publishing Ltd
</description></item><item rdf:about="http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12047" xmlns="http://purl.org/rss/1.0/"><title>Indoor airborne bacterial communities are influenced by ventilation, occupancy, and outdoor air source</title><link>http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12047</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Indoor airborne bacterial communities are influenced by ventilation, occupancy, and outdoor air source</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">J. F. Meadow, A. E. Altrichter, S. W. Kembel, J. Kline, G. Mhuireach, M. Moriyama, D. Northcutt, T. K. O'Connor, A. M. Womack, G. Z. Brown, J. L . Green, B. J. M. Bohannan</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2013-05-24T00:05:57.231788-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/ina.12047</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/ina.12047</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12047</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Original Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[
<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Abstract</h3>
<div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Architects and engineers are beginning to consider a new dimension of indoor air: the structure and composition of airborne microbial communities. A first step in this emerging field is to understand the forces that shape the diversity of bioaerosols across space and time within the built environment. In an effort to elucidate the relative influences of three likely drivers of indoor bioaerosol diversity – variation in outdoor bioaerosols, ventilation strategy, and occupancy load – we conducted an intensive temporal study of indoor airborne bacterial communities in a high-traffic university building with a hybrid HVAC (mechanically and naturally ventilated) system. Indoor air communities closely tracked outdoor air communities, but human-associated bacterial genera were more than twice as abundant in indoor air compared with outdoor air. Ventilation had a demonstrated effect on indoor airborne bacterial community composition; changes in outdoor air communities were detected inside following a time lag associated with differing ventilation strategies relevant to modern building design. Our results indicate that both occupancy patterns and ventilation strategies are important for understanding airborne microbial community dynamics in the built environment.</p></div>
]]></content:encoded><description>

Architects and engineers are beginning to consider a new dimension of indoor air: the structure and composition of airborne microbial communities. A first step in this emerging field is to understand the forces that shape the diversity of bioaerosols across space and time within the built environment. In an effort to elucidate the relative influences of three likely drivers of indoor bioaerosol diversity – variation in outdoor bioaerosols, ventilation strategy, and occupancy load – we conducted an intensive temporal study of indoor airborne bacterial communities in a high-traffic university building with a hybrid HVAC (mechanically and naturally ventilated) system. Indoor air communities closely tracked outdoor air communities, but human-associated bacterial genera were more than twice as abundant in indoor air compared with outdoor air. Ventilation had a demonstrated effect on indoor airborne bacterial community composition; changes in outdoor air communities were detected inside following a time lag associated with differing ventilation strategies relevant to modern building design. Our results indicate that both occupancy patterns and ventilation strategies are important for understanding airborne microbial community dynamics in the built environment.
</description></item><item rdf:about="http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12049" xmlns="http://purl.org/rss/1.0/"><title>Identifying and quantifying secondhand smoke in source and receptor rooms: logistic regression and chemical mass balance approaches</title><link>http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12049</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Identifying and quantifying secondhand smoke in source and receptor rooms: logistic regression and chemical mass balance approaches</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">P. J. Dacunto, K.-C. Cheng, V. Acevedo-Bolton, R.-T. Jiang, N. E. Klepeis, J. L. Repace, W. R. Ott, L. M. Hildemann</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2013-05-23T10:05:56.136575-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/ina.12049</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/ina.12049</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12049</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Original Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[
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<div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Identifying and quantifying secondhand tobacco smoke (SHS) that drifts between multiunit homes is critical to assessing exposure. Twenty-three different gaseous and particulate measurements were taken during controlled emissions from smoked cigarettes and six other common indoor source types in 60 single-room and 13 two-room experiments. We used measurements from the 60 single-room experiments for (i) the fitting of logistic regression models to predict the likelihood of SHS and (ii) the creation of source profiles for chemical mass balance (CMB) analysis to estimate source apportionment. We then applied these regression models and source profiles to the independent data set of 13 two-room experiments. Several logistic regression models correctly predicted the presence of cigarette smoke more than 80% of the time in both source and receptor rooms, with one model correct in 100% of applicable cases. CMB analysis of the source room provided significant PM<sub>2.5</sub> concentration estimates of all true sources in 9 of 13 experiments and was half-correct (i.e., included an erroneous source or missed a true source) in the remaining four. In the receptor room, CMB provided significant estimates of all true sources in 9 of 13 experiments and was half-correct in another two.</p></div>
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Identifying and quantifying secondhand tobacco smoke (SHS) that drifts between multiunit homes is critical to assessing exposure. Twenty-three different gaseous and particulate measurements were taken during controlled emissions from smoked cigarettes and six other common indoor source types in 60 single-room and 13 two-room experiments. We used measurements from the 60 single-room experiments for (i) the fitting of logistic regression models to predict the likelihood of SHS and (ii) the creation of source profiles for chemical mass balance (CMB) analysis to estimate source apportionment. We then applied these regression models and source profiles to the independent data set of 13 two-room experiments. Several logistic regression models correctly predicted the presence of cigarette smoke more than 80% of the time in both source and receptor rooms, with one model correct in 100% of applicable cases. CMB analysis of the source room provided significant PM2.5 concentration estimates of all true sources in 9 of 13 experiments and was half-correct (i.e., included an erroneous source or missed a true source) in the remaining four. In the receptor room, CMB provided significant estimates of all true sources in 9 of 13 experiments and was half-correct in another two.
</description></item><item rdf:about="http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12046" xmlns="http://purl.org/rss/1.0/"><title>Progress in thermal comfort research over the last twenty years</title><link>http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12046</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Progress in thermal comfort research over the last twenty years</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">R. J. Dear, T. Akimoto, E. A. Arens, G. Brager, C. Candido, K. W. D. Cheong, B. Li, N. Nishihara, S. C. Sekhar, S. Tanabe, J. Toftum, H. Zhang, Y. Zhu</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2013-05-16T12:47:58.326603-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/ina.12046</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/ina.12046</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12046</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Review Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[
<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Abstract</h3>
<div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Climate change and the urgency of decarbonizing the built environment are driving technological innovation in the way we deliver thermal comfort to occupants. These changes, in turn, seem to be setting the directions for contemporary thermal comfort research. This article presents a literature review of major changes, developments, and trends in the field of thermal comfort research over the last 20 years. One of the main paradigm shift was the fundamental conceptual reorientation that has taken place in thermal comfort thinking over the last 20 years; a shift away from the physically based determinism of Fanger's comfort model toward the mainstream and acceptance of the adaptive comfort model. Another noticeable shift has been from the undesirable toward the desirable qualities of air movement. Additionally, sophisticated models covering the physics and physiology of the human body were developed, driven by the continuous challenge to model thermal comfort at the same anatomical resolution and to combine these localized signals into a coherent, global thermal perception. Finally, the demand for ever increasing building energy efficiency is pushing technological innovation in the way we deliver comfortable indoor environments. These trends, in turn, continue setting the directions for contemporary thermal comfort research for the next decades.</p></div>
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Climate change and the urgency of decarbonizing the built environment are driving technological innovation in the way we deliver thermal comfort to occupants. These changes, in turn, seem to be setting the directions for contemporary thermal comfort research. This article presents a literature review of major changes, developments, and trends in the field of thermal comfort research over the last 20 years. One of the main paradigm shift was the fundamental conceptual reorientation that has taken place in thermal comfort thinking over the last 20 years; a shift away from the physically based determinism of Fanger's comfort model toward the mainstream and acceptance of the adaptive comfort model. Another noticeable shift has been from the undesirable toward the desirable qualities of air movement. Additionally, sophisticated models covering the physics and physiology of the human body were developed, driven by the continuous challenge to model thermal comfort at the same anatomical resolution and to combine these localized signals into a coherent, global thermal perception. Finally, the demand for ever increasing building energy efficiency is pushing technological innovation in the way we deliver comfortable indoor environments. These trends, in turn, continue setting the directions for contemporary thermal comfort research for the next decades.
</description></item><item rdf:about="http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12045" xmlns="http://purl.org/rss/1.0/"><title>Ultrafine particle removal by residential heating, ventilating, and air-conditioning filters</title><link>http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12045</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Ultrafine particle removal by residential heating, ventilating, and air-conditioning filters</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">B. Stephens, J. A. Siegel</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2013-05-13T06:41:03.475009-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/ina.12045</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/ina.12045</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12045</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Original Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[
<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Abstract</h3>
<div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>This work uses an <em>in situ</em> filter test method to measure the size-resolved removal efficiency of indoor-generated ultrafine particles (approximately 7–100 nm) for six new commercially available filters installed in a recirculating heating, ventilating, and air-conditioning (HVAC) system in an unoccupied test house. The fibrous HVAC filters were previously rated by the manufacturers according to ASHRAE Standard 52.2 and ranged from shallow (2.5 cm) fiberglass panel filters (MERV 4) to deep-bed (12.7 cm) electrostatically charged synthetic media filters (MERV 16). Measured removal efficiency ranged from 0 to 10% for most ultrafine particles (UFP) sizes with the lowest rated filters (MERV 4 and 6) to 60–80% for most UFP sizes with the highest rated filter (MERV 16). The deeper bed filters generally achieved higher removal efficiencies than the panel filters, while maintaining a low pressure drop and higher airflow rate in the operating HVAC system. Assuming constant efficiency, a modeling effort using these measured values for new filters and other inputs from real buildings shows that MERV 13–16 filters could reduce the indoor proportion of outdoor UFPs (in the absence of indoor sources) by as much as a factor of 2–3 in a typical single-family residence relative to the lowest efficiency filters, depending in part on particle size.</p></div>
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This work uses an in situ filter test method to measure the size-resolved removal efficiency of indoor-generated ultrafine particles (approximately 7–100 nm) for six new commercially available filters installed in a recirculating heating, ventilating, and air-conditioning (HVAC) system in an unoccupied test house. The fibrous HVAC filters were previously rated by the manufacturers according to ASHRAE Standard 52.2 and ranged from shallow (2.5 cm) fiberglass panel filters (MERV 4) to deep-bed (12.7 cm) electrostatically charged synthetic media filters (MERV 16). Measured removal efficiency ranged from 0 to 10% for most ultrafine particles (UFP) sizes with the lowest rated filters (MERV 4 and 6) to 60–80% for most UFP sizes with the highest rated filter (MERV 16). The deeper bed filters generally achieved higher removal efficiencies than the panel filters, while maintaining a low pressure drop and higher airflow rate in the operating HVAC system. Assuming constant efficiency, a modeling effort using these measured values for new filters and other inputs from real buildings shows that MERV 13–16 filters could reduce the indoor proportion of outdoor UFPs (in the absence of indoor sources) by as much as a factor of 2–3 in a typical single-family residence relative to the lowest efficiency filters, depending in part on particle size.
</description></item><item rdf:about="http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12044" xmlns="http://purl.org/rss/1.0/"><title>Indoor aerosols: from personal exposure to risk assessment</title><link>http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12044</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Indoor aerosols: from personal exposure to risk assessment</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">L. Morawska, A. Afshari, G. N. Bae, G. Buonanno, C. Y. H. Chao, O. Hänninen, W. Hofmann, C. Isaxon, E. R. Jayaratne, P. Pasanen, T. Salthammer, M. Waring, A. Wierzbicka</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2013-05-13T06:41:01.267345-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/ina.12044</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/ina.12044</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12044</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Review Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[
<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Abstract</h3>
<div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Motivated by growing considerations of the scale, severity, and risks associated with human exposure to indoor particulate matter, this work reviewed existing literature to: (i) identify state-of-the-art experimental techniques used for personal exposure assessment; (ii) compare exposure levels reported for domestic/school settings in different countries (excluding exposure to environmental tobacco smoke and particulate matter from biomass cooking in developing countries); (iii) assess the contribution of outdoor background vs indoor sources to personal exposure; and (iv) examine scientific understanding of the risks posed by personal exposure to indoor aerosols. Limited studies assessing integrated daily residential exposure to just one particle size fraction, ultrafine particles, show that the contribution of indoor sources ranged from 19% to 76%. This indicates a strong dependence on resident activities, source events and site specificity, and highlights the importance of indoor sources for total personal exposure. Further, it was assessed that 10–30% of the total burden of disease from particulate matter exposure was due to indoor-generated particles, signifying that indoor environments are likely to be a dominant environmental factor affecting human health. However, due to challenges associated with conducting epidemiological assessments, the role of indoor-generated particles has not been fully acknowledged, and improved exposure/risk assessment methods are still needed, together with a serious focus on exposure control.</p></div>
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Motivated by growing considerations of the scale, severity, and risks associated with human exposure to indoor particulate matter, this work reviewed existing literature to: (i) identify state-of-the-art experimental techniques used for personal exposure assessment; (ii) compare exposure levels reported for domestic/school settings in different countries (excluding exposure to environmental tobacco smoke and particulate matter from biomass cooking in developing countries); (iii) assess the contribution of outdoor background vs indoor sources to personal exposure; and (iv) examine scientific understanding of the risks posed by personal exposure to indoor aerosols. Limited studies assessing integrated daily residential exposure to just one particle size fraction, ultrafine particles, show that the contribution of indoor sources ranged from 19% to 76%. This indicates a strong dependence on resident activities, source events and site specificity, and highlights the importance of indoor sources for total personal exposure. Further, it was assessed that 10–30% of the total burden of disease from particulate matter exposure was due to indoor-generated particles, signifying that indoor environments are likely to be a dominant environmental factor affecting human health. However, due to challenges associated with conducting epidemiological assessments, the role of indoor-generated particles has not been fully acknowledged, and improved exposure/risk assessment methods are still needed, together with a serious focus on exposure control.
</description></item><item rdf:about="http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12042" xmlns="http://purl.org/rss/1.0/"><title>Association of classroom ventilation with reduced illness absence: a prospective study in California elementary schools</title><link>http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12042</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Association of classroom ventilation with reduced illness absence: a prospective study in California elementary schools</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">M. J. Mendell, E. A. Eliseeva, M. M. Davies, M. Spears, A. Lobscheid, W. J. Fisk, M. G. Apte</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2013-04-22T00:35:23.237158-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/ina.12042</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/ina.12042</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12042</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Original Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[
<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Abstract</h3>
<div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Limited evidence associates inadequate classroom ventilation rates (VRs) with increased illness absence (IA). We investigated relationships between VRs and IA in California elementary schools over two school years in 162 3rd–5th-grade classrooms in 28 schools in three school districts: South Coast (SC), Bay Area (BA), and Central Valley (CV). We estimated relationships between daily IA and VR (estimated from two year daily real-time carbon dioxide in each classroom) in zero-inflated negative binomial models. We also compared IA benefits and energy costs of increased VRs. All school districts had median VRs below the 7.1 l/s-person California standard. For each additional 1 l/s-person of VR, IA was reduced significantly (p&lt;0.05) in models for combined districts (−1.6%) and for SC (−1.2%), and nonsignificantly for districts providing less data: BA (−1.5%) and CV (−1.0%). Assuming associations were causal and generalizable, increasing classroom VRs from the California average (4 l/s-person) to the State standard would decrease IA by 3.4%, increase attendance-linked funding to schools by $33 million annually, and increase costs by only $4 million. Further increasing VRs would provide additional benefits. These findings, while requiring confirmation, suggest that increasing classroom VRs above the State standard would substantially decrease illness absence and produce economic benefits.</p></div>
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Limited evidence associates inadequate classroom ventilation rates (VRs) with increased illness absence (IA). We investigated relationships between VRs and IA in California elementary schools over two school years in 162 3rd–5th-grade classrooms in 28 schools in three school districts: South Coast (SC), Bay Area (BA), and Central Valley (CV). We estimated relationships between daily IA and VR (estimated from two year daily real-time carbon dioxide in each classroom) in zero-inflated negative binomial models. We also compared IA benefits and energy costs of increased VRs. All school districts had median VRs below the 7.1 l/s-person California standard. For each additional 1 l/s-person of VR, IA was reduced significantly (p&lt;0.05) in models for combined districts (−1.6%) and for SC (−1.2%), and nonsignificantly for districts providing less data: BA (−1.5%) and CV (−1.0%). Assuming associations were causal and generalizable, increasing classroom VRs from the California average (4 l/s-person) to the State standard would decrease IA by 3.4%, increase attendance-linked funding to schools by $33 million annually, and increase costs by only $4 million. Further increasing VRs would provide additional benefits. These findings, while requiring confirmation, suggest that increasing classroom VRs above the State standard would substantially decrease illness absence and produce economic benefits.
</description></item><item rdf:about="http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12043" xmlns="http://purl.org/rss/1.0/"><title>Coarse particulate matter and airborne endotoxin within wood stove homes</title><link>http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12043</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Coarse particulate matter and airborne endotoxin within wood stove homes</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">M. McNamara, J. Thornburg, E. Semmens, T. Ward, C. Noonan</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2013-04-18T08:17:34.493247-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/ina.12043</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/ina.12043</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12043</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Original Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[
<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Abstract</h3>
<div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Emissions from indoor biomass burning are a major public health concern in developing areas of the world. Less is known about indoor air quality, particularly airborne endotoxin, in homes burning biomass fuel in residential wood stoves in higher income countries. A filter-based sampler was used to evaluate wintertime indoor coarse particulate matter (PM<sub>10-2.5</sub>) and airborne endotoxin (EU/m<sup>3</sup>, EU/mg) concentrations in 50 homes using wood stoves as their primary source of heat in western Montana. We investigated number of residents, number of pets, dampness (humidity), and frequency of wood stove usage as potential predictors of indoor airborne endotoxin concentrations. Two 48-h sampling events per home revealed a mean winter PM<sub>10-2.5</sub> concentration (± s.d.) of 12.9 (± 8.6) μg/m<sup>3</sup>, while PM<sub>2.5</sub> concentrations averaged 32.3 (± 32.6) μg/m<sup>3</sup>. Endotoxin concentrations measured from PM<sub>10-2.5</sub> filter samples were 9.2 (± 12.4) EU/m<sup>3</sup> and 1010 (± 1524) EU/mg. PM<sub>10-2.5</sub> and PM<sub>2.5</sub> were significantly correlated in wood stove homes (<em>r</em> = 0.36, <em>P</em> &lt; 0.05). The presence of pets in the homes was associated with PM<sub>10-2.5</sub> but not with endotoxin concentrations. Importantly, none of the other measured home characteristics was a strong predictor of airborne endotoxin, including frequency of residential wood stove usage.</p></div>
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Emissions from indoor biomass burning are a major public health concern in developing areas of the world. Less is known about indoor air quality, particularly airborne endotoxin, in homes burning biomass fuel in residential wood stoves in higher income countries. A filter-based sampler was used to evaluate wintertime indoor coarse particulate matter (PM10-2.5) and airborne endotoxin (EU/m3, EU/mg) concentrations in 50 homes using wood stoves as their primary source of heat in western Montana. We investigated number of residents, number of pets, dampness (humidity), and frequency of wood stove usage as potential predictors of indoor airborne endotoxin concentrations. Two 48-h sampling events per home revealed a mean winter PM10-2.5 concentration (± s.d.) of 12.9 (± 8.6) μg/m3, while PM2.5 concentrations averaged 32.3 (± 32.6) μg/m3. Endotoxin concentrations measured from PM10-2.5 filter samples were 9.2 (± 12.4) EU/m3 and 1010 (± 1524) EU/mg. PM10-2.5 and PM2.5 were significantly correlated in wood stove homes (r = 0.36, P &lt; 0.05). The presence of pets in the homes was associated with PM10-2.5 but not with endotoxin concentrations. Importantly, none of the other measured home characteristics was a strong predictor of airborne endotoxin, including frequency of residential wood stove usage.
</description></item><item rdf:about="http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12041" xmlns="http://purl.org/rss/1.0/"><title>Numerical investigation of wind-induced airflow and interunit dispersion characteristics in multistory residential buildings</title><link>http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12041</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Numerical investigation of wind-induced airflow and interunit dispersion characteristics in multistory residential buildings</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Z. T. Ai, C. M. Mak, J. L. Niu</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2013-04-18T08:17:20.313093-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/ina.12041</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/ina.12041</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12041</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Original Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[
<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Abstract</h3>
<div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Compared with the buoyancy-dominated upward spread, the interunit dispersion of pollutants in wind-dominated conditions is expected to be more complex and multiple. The aim of this study is to investigate the wind-induced airflow and interunit pollutant dispersion in typical multistory residential buildings using computational fluid dynamics. The mathematical model used is the nonstandard <em>k</em>–ε model incorporated with a two-layer near-wall modification, which is validated against experiments of previous investigators. Using tracer gas technique, the reentry of exhaust air from each distinct unit to other units on the same building, under different practical conditions, is quantified, and then, the possible dispersion routes are revealed. The units on the floor immediately below the source on the windward side, and vertically above it on the leeward side, where the reentry ratios are up to 4.8% and 14.9%, respectively, should be included on the high-infection list. It is also found that the presence of balconies results in a more turbulent near-wall flow field, which in turn significantly changes the reentry characteristics. Comparison of the dispersion characteristics of the slab-like building and the more complicated building in cross (#) floorplan concludes that distinctive infectious control measures should be implemented in these two types of buildings.</p></div>
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Compared with the buoyancy-dominated upward spread, the interunit dispersion of pollutants in wind-dominated conditions is expected to be more complex and multiple. The aim of this study is to investigate the wind-induced airflow and interunit pollutant dispersion in typical multistory residential buildings using computational fluid dynamics. The mathematical model used is the nonstandard k–ε model incorporated with a two-layer near-wall modification, which is validated against experiments of previous investigators. Using tracer gas technique, the reentry of exhaust air from each distinct unit to other units on the same building, under different practical conditions, is quantified, and then, the possible dispersion routes are revealed. The units on the floor immediately below the source on the windward side, and vertically above it on the leeward side, where the reentry ratios are up to 4.8% and 14.9%, respectively, should be included on the high-infection list. It is also found that the presence of balconies results in a more turbulent near-wall flow field, which in turn significantly changes the reentry characteristics. Comparison of the dispersion characteristics of the slab-like building and the more complicated building in cross (#) floorplan concludes that distinctive infectious control measures should be implemented in these two types of buildings.
</description></item><item rdf:about="http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12040" xmlns="http://purl.org/rss/1.0/"><title>Prediction of residential radon exposure of the whole Swiss population: comparison of model-based predictions with measurement-based predictions</title><link>http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12040</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Prediction of residential radon exposure of the whole Swiss population: comparison of model-based predictions with measurement-based predictions</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">D. D. Hauri, A. Huss, F. Zimmermann, C. E. Kuehni, M. Röösli, </dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2013-04-09T05:21:19.104385-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/ina.12040</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/ina.12040</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12040</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Original Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[
<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Abstract</h3>
<div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Radon plays an important role for human exposure to natural sources of ionizing radiation. The aim of this article is to compare two approaches to estimate mean radon exposure in the Swiss population: model-based predictions at individual level and measurement-based predictions based on measurements aggregated at municipality level. A nationwide model was used to predict radon levels in each household and for each individual based on the corresponding tectonic unit, building age, building type, soil texture, degree of urbanization, and floor. Measurement-based predictions were carried out within a health impact assessment on residential radon and lung cancer. Mean measured radon levels were corrected for the average floor distribution and weighted with population size of each municipality. Model-based predictions yielded a mean radon exposure of the Swiss population of 84.1 Bq/m<sup>3</sup>. Measurement-based predictions yielded an average exposure of 78 Bq/m<sup>3</sup>. This study demonstrates that the model- and the measurement-based predictions provided similar results. The advantage of the measurement-based approach is its simplicity, which is sufficient for assessing exposure distribution in a population. The model-based approach allows predicting radon levels at specific sites, which is needed in an epidemiological study, and the results do not depend on how the measurement sites have been selected.</p></div>
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Radon plays an important role for human exposure to natural sources of ionizing radiation. The aim of this article is to compare two approaches to estimate mean radon exposure in the Swiss population: model-based predictions at individual level and measurement-based predictions based on measurements aggregated at municipality level. A nationwide model was used to predict radon levels in each household and for each individual based on the corresponding tectonic unit, building age, building type, soil texture, degree of urbanization, and floor. Measurement-based predictions were carried out within a health impact assessment on residential radon and lung cancer. Mean measured radon levels were corrected for the average floor distribution and weighted with population size of each municipality. Model-based predictions yielded a mean radon exposure of the Swiss population of 84.1 Bq/m3. Measurement-based predictions yielded an average exposure of 78 Bq/m3. This study demonstrates that the model- and the measurement-based predictions provided similar results. The advantage of the measurement-based approach is its simplicity, which is sufficient for assessing exposure distribution in a population. The model-based approach allows predicting radon levels at specific sites, which is needed in an epidemiological study, and the results do not depend on how the measurement sites have been selected.
</description></item><item rdf:about="http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12039" xmlns="http://purl.org/rss/1.0/"><title>Effects of 6-h exposure to low relative humidity and low air pressure on body fluid loss and blood viscosity</title><link>http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12039</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Effects of 6-h exposure to low relative humidity and low air pressure on body fluid loss and blood viscosity</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">N. Hashiguchi, A. Takeda, Y. Yasuyama, A. Chishaki, Y. Tochihara</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2013-03-28T02:48:35.696277-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/ina.12039</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/ina.12039</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12039</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Original Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[
<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Abstract</h3>
<div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>The purpose of this study was to investigate the effects of 6-h exposure to low relative humidity (RH) and low air pressure in a simulated air cabin environment on body fluid loss (BFL) and blood viscosity. Fourteen young healthy male subjects were exposed to four conditions, which combined RH (10% RH or 60% RH) and air pressure (NP: sea level or LP: equivalent to an altitude of 2000 m). Subjects remained seated on a chair in the chamber for 6 h. Their diet and water intake were restricted before and during the experiment. Insensible water loss (IWL) in LP10% condition was significantly greater than in NP60% condition; thus, combined 10%RH and LP conditions promoted a greater amount of IWL. The BFL under the LP condition was significantly greater than that under the NP condition. Blood viscosity significantly increased under LP conditions. Increases in red blood cell counts (RBCs) and BFL likely contributed to the increased blood viscosity. These findings suggest that hypobaric-induced hypoxia, similar to the conditions in the air cabin environment, may cause increased blood viscosity and that the combined low humidity and hypobaric hypoxia conditions increase IWL.</p></div>
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The purpose of this study was to investigate the effects of 6-h exposure to low relative humidity (RH) and low air pressure in a simulated air cabin environment on body fluid loss (BFL) and blood viscosity. Fourteen young healthy male subjects were exposed to four conditions, which combined RH (10% RH or 60% RH) and air pressure (NP: sea level or LP: equivalent to an altitude of 2000 m). Subjects remained seated on a chair in the chamber for 6 h. Their diet and water intake were restricted before and during the experiment. Insensible water loss (IWL) in LP10% condition was significantly greater than in NP60% condition; thus, combined 10%RH and LP conditions promoted a greater amount of IWL. The BFL under the LP condition was significantly greater than that under the NP condition. Blood viscosity significantly increased under LP conditions. Increases in red blood cell counts (RBCs) and BFL likely contributed to the increased blood viscosity. These findings suggest that hypobaric-induced hypoxia, similar to the conditions in the air cabin environment, may cause increased blood viscosity and that the combined low humidity and hypobaric hypoxia conditions increase IWL.
</description></item><item rdf:about="http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12029" xmlns="http://purl.org/rss/1.0/"><title>Indoor air quality, air exchange rates, and radioactivity in new built temporary houses following the Great East Japan Earthquake in Minamisoma, Fukushima</title><link>http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12029</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Indoor air quality, air exchange rates, and radioactivity in new built temporary houses following the Great East Japan Earthquake in Minamisoma, Fukushima</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">N. Shinohara, M. Tokumura, M. Kazama, H. Yoshino, S. Ochiai, A. Mizukoshi</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2013-03-21T08:52:30.48052-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/ina.12029</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/ina.12029</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12029</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Original Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[
<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Abstract</h3>
<div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>This study measured air exchange rates, indoor concentrations of aldehydes and volatile organic compounds (VOCs), and radioactivity levels at 19 temporary houses in different temporary housing estate constructed in Minamisoma City following the Great East Japan Earthquake. The 19 surveyed houses represented all of the companies assigned to construct temporary houses in that Minamisoma City. Data were collected shortly after construction and before occupation, from August 2011 to January 2012. Mean air exchange rates in the temporary houses were 0.28/h, with no variation according to housing types and construction date. Mean indoor concentrations of formaldehyde, acetaldehyde, toluene, ethylbenzene, <em>m</em>/<em>p</em>-xylene, <em>o</em>-xylene, styrene, <em>p</em>-dichlorobenzene, tetradecane, and total VOCs (TVOCs) were 29.2, 72.7, 14.6, 6.35, 3.05, 1.81, 7.29, 14.3, 8.32, and 901 μg/m<sup>3</sup>, respectively. The levels of acetaldehyde and TVOCs exceeded the indoor guideline (48 μg/m<sup>3</sup>) and interim target (400 μg/m<sup>3</sup>) in more than half of the 31 rooms tested. In addition to guideline chemicals, terpenes (<em>α</em>-pinene and <em>d</em>-limonene) and acetic esters (butyl acetate and ethyl acetate) were often detected in these houses. The indoor radiation levels measured by a Geiger–Müller tube (Mean: 0.22 μSv/h) were lower than those recorded outdoors (Mean: 0.42 μSv/h), although the shielding effect of the houses was less than for other types of buildings.</p></div>
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This study measured air exchange rates, indoor concentrations of aldehydes and volatile organic compounds (VOCs), and radioactivity levels at 19 temporary houses in different temporary housing estate constructed in Minamisoma City following the Great East Japan Earthquake. The 19 surveyed houses represented all of the companies assigned to construct temporary houses in that Minamisoma City. Data were collected shortly after construction and before occupation, from August 2011 to January 2012. Mean air exchange rates in the temporary houses were 0.28/h, with no variation according to housing types and construction date. Mean indoor concentrations of formaldehyde, acetaldehyde, toluene, ethylbenzene, m/p-xylene, o-xylene, styrene, p-dichlorobenzene, tetradecane, and total VOCs (TVOCs) were 29.2, 72.7, 14.6, 6.35, 3.05, 1.81, 7.29, 14.3, 8.32, and 901 μg/m3, respectively. The levels of acetaldehyde and TVOCs exceeded the indoor guideline (48 μg/m3) and interim target (400 μg/m3) in more than half of the 31 rooms tested. In addition to guideline chemicals, terpenes (α-pinene and d-limonene) and acetic esters (butyl acetate and ethyl acetate) were often detected in these houses. The indoor radiation levels measured by a Geiger–Müller tube (Mean: 0.22 μSv/h) were lower than those recorded outdoors (Mean: 0.42 μSv/h), although the shielding effect of the houses was less than for other types of buildings.
</description></item><item rdf:about="http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12031" xmlns="http://purl.org/rss/1.0/"><title>Determination of radon exhalation from construction materials using VOC emission test chambers</title><link>http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12031</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Determination of radon exhalation from construction materials using VOC emission test chambers</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">M. Richter, O. Jann, J. Kemski, U. Schneider, C. Krocker, B. Hoffmann</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2013-03-21T08:52:15.900867-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/ina.12031</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/ina.12031</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12031</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Original Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[
<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Abstract</h3>
<div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>The inhalation of <sup>222</sup>Rn (radon) decay products is one of the most important reasons for lung cancer after smoking. Stony building materials are an important source of indoor radon. This article describes the determination of the exhalation rate of stony construction materials by the use of commercially available measuring devices in combination with VOC emission test chambers. Five materials – two types of clay brick, clinker brick, light-weight concrete brick, and honeycomb brick – generally used for wall constructions were used for the experiments. Their contribution to real room concentrations was estimated by applying room model parameters given in ISO 16000-9, RP 112, and AgBB. This knowledge can be relevant, if for instance indoor radon concentration is limited by law. The test set-up used here is well suited for application in test laboratories dealing with VOC emission testing.</p></div>
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The inhalation of 222Rn (radon) decay products is one of the most important reasons for lung cancer after smoking. Stony building materials are an important source of indoor radon. This article describes the determination of the exhalation rate of stony construction materials by the use of commercially available measuring devices in combination with VOC emission test chambers. Five materials – two types of clay brick, clinker brick, light-weight concrete brick, and honeycomb brick – generally used for wall constructions were used for the experiments. Their contribution to real room concentrations was estimated by applying room model parameters given in ISO 16000-9, RP 112, and AgBB. This knowledge can be relevant, if for instance indoor radon concentration is limited by law. The test set-up used here is well suited for application in test laboratories dealing with VOC emission testing.
</description></item><item rdf:about="http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12038" xmlns="http://purl.org/rss/1.0/"><title>Indoor exposure to particulate matter and the incidence of acute lower respiratory infections among children: A birth cohort study in urban Bangladesh</title><link>http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12038</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Indoor exposure to particulate matter and the incidence of acute lower respiratory infections among children: A birth cohort study in urban Bangladesh</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">E. S. Gurley, N. Homaira, H. Salje, P. K. Ram, R. Haque, W. Petri, J. Bresee, W. J. Moss, P. Breysse, S. P. Luby, E. Azziz-Baumgartner</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2013-03-21T08:44:20.234369-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/ina.12038</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/ina.12038</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12038</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Original Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[
<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Abstract</h3>
<div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Approximately half of all children under two years of age in Bangladesh suffer from an acute lower respiratory infection (ALRI) each year. Exposure to indoor biomass smoke has been consistently associated with an increased risk of ALRI in young children. Our aim was to estimate the effect of indoor exposure to particulate matter (PM<sub>2.5</sub>) on the incidence of ALRI among children in a low-income, urban community in Bangladesh. We followed 257 children through two years of age to determine their frequency of ALRI and measured the PM<sub>2.5</sub> concentrations in their sleeping space. Poisson regression was used to estimate the association between ALRI and the number of hours per day that PM<sub>2.5</sub> concentrations exceeded 100 μg/m<sup>3</sup>, adjusting for known confounders. Each hour that PM<sub>2.5</sub> concentrations exceeded 100 μg/m<sup>3</sup> was associated with a 7% increase in incidence of ALRI among children aged 0–11 months (adjusted incidence rate ratio (IRR) 1.07, 95% CI 1.01–1.14), but not in children 12–23 months old (adjusted IRR 1.00, 95% CI 0.92–1.09). Results from this study suggest that reducing indoor PM<sub>2.5</sub> exposure could decrease the frequency of ALRI among infants, the children at highest risk of death from these infections.</p></div>
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Approximately half of all children under two years of age in Bangladesh suffer from an acute lower respiratory infection (ALRI) each year. Exposure to indoor biomass smoke has been consistently associated with an increased risk of ALRI in young children. Our aim was to estimate the effect of indoor exposure to particulate matter (PM2.5) on the incidence of ALRI among children in a low-income, urban community in Bangladesh. We followed 257 children through two years of age to determine their frequency of ALRI and measured the PM2.5 concentrations in their sleeping space. Poisson regression was used to estimate the association between ALRI and the number of hours per day that PM2.5 concentrations exceeded 100 μg/m3, adjusting for known confounders. Each hour that PM2.5 concentrations exceeded 100 μg/m3 was associated with a 7% increase in incidence of ALRI among children aged 0–11 months (adjusted incidence rate ratio (IRR) 1.07, 95% CI 1.01–1.14), but not in children 12–23 months old (adjusted IRR 1.00, 95% CI 0.92–1.09). Results from this study suggest that reducing indoor PM2.5 exposure could decrease the frequency of ALRI among infants, the children at highest risk of death from these infections.
</description></item><item rdf:about="http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12032" xmlns="http://purl.org/rss/1.0/"><title>Effect of moisture-damage intervention on the immunotoxic potential and microbial content of airborne particles and on occupants' upper airway inflammatory responses</title><link>http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12032</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Effect of moisture-damage intervention on the immunotoxic potential and microbial content of airborne particles and on occupants' upper airway inflammatory responses</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">M. Roponen, T. Meklin, H. Rintala, A. Hyvärinen, M.-R. Hirvonen</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2013-03-21T08:31:51.918771-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/ina.12032</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/ina.12032</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12032</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Original Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[
<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Abstract</h3>
<div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>This intervention study evaluated the effect of moisture-damage repairs on the exposure and on the upper airway inflammatory responses of the occupants. The airborne microbial exposure was followed by quantitative PCR analyses of 13 microbial species in repeated long-term indoor air samples before (<em>N</em> = 26) and after (<em>N</em> = 28) repairs of the school building. Airborne particulate matter was collected similarly from the same premises (before <em>N</em> = 25, after <em>N</em> = 34) for determination of nitric oxide (NO), tumor necrosis factor α (TNFα), and interleukin-6 (IL-6), measured in the cell culture medium of mouse macrophages. NO, TNFα, IL-6, and IL-4 were also analyzed in the nasal lavage (NAL) samples of the occupants (<em>N</em> = 13) to characterize their upper airway inflammatory responses during the exposure and after its cessation. After the repairs, concentrations of the measured airborne microbes decreased, the difference being significant for six of 13 species. After renovation, airborne particulate matter also caused significantly lower production of IL-6 and TNF-α in mouse macrophages than the material collected before the renovation. The concentration of IL-4 in the NAL samples was significantly lower after the renovation. These results show that the inflammatory potential of the airborne material decreases after intensive repair of the moisture damage.</p></div>
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This intervention study evaluated the effect of moisture-damage repairs on the exposure and on the upper airway inflammatory responses of the occupants. The airborne microbial exposure was followed by quantitative PCR analyses of 13 microbial species in repeated long-term indoor air samples before (N = 26) and after (N = 28) repairs of the school building. Airborne particulate matter was collected similarly from the same premises (before N = 25, after N = 34) for determination of nitric oxide (NO), tumor necrosis factor α (TNFα), and interleukin-6 (IL-6), measured in the cell culture medium of mouse macrophages. NO, TNFα, IL-6, and IL-4 were also analyzed in the nasal lavage (NAL) samples of the occupants (N = 13) to characterize their upper airway inflammatory responses during the exposure and after its cessation. After the repairs, concentrations of the measured airborne microbes decreased, the difference being significant for six of 13 species. After renovation, airborne particulate matter also caused significantly lower production of IL-6 and TNF-α in mouse macrophages than the material collected before the renovation. The concentration of IL-4 in the NAL samples was significantly lower after the renovation. These results show that the inflammatory potential of the airborne material decreases after intensive repair of the moisture damage.
</description></item><item rdf:about="http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12036" xmlns="http://purl.org/rss/1.0/"><title>Health benefits of particle filtration</title><link>http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12036</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Health benefits of particle filtration</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">W. J. Fisk</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2013-03-21T08:31:41.917488-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/ina.12036</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/ina.12036</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12036</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Review Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[
<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Abstract</h3>
<div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>The evidence of health benefits of particle filtration in homes and commercial buildings is reviewed. Prior reviews of papers published before 2000 are summarized. The results of 16 more recent intervention studies are compiled and analyzed. Also, reviewed are four studies that modeled health benefits of using filtration to reduce indoor exposures to particles from outdoors. Prior reviews generally concluded that particle filtration is, at best, a source of small improvements in allergy and asthma health effects; however, many early studies had weak designs. A majority of recent intervention studies employed strong designs and more of these studies report statistically significant improvements in health symptoms or objective health outcomes, particularly for subjects with allergies or asthma. The percentage improvement in health outcomes is typically modest, for example, 7% to 25%. Delivery of filtered air to the breathing zone of sleeping allergic or asthmatic persons may be more consistently effective in improving health than room air filtration. Notable are two studies that report statistically significant improvements, with filtration, in markers that predict future adverse coronary events. From modeling, the largest potential benefits of indoor particle filtration may be reductions in morbidity and mortality from reducing indoor exposures to particles from outdoor air.</p></div>
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The evidence of health benefits of particle filtration in homes and commercial buildings is reviewed. Prior reviews of papers published before 2000 are summarized. The results of 16 more recent intervention studies are compiled and analyzed. Also, reviewed are four studies that modeled health benefits of using filtration to reduce indoor exposures to particles from outdoors. Prior reviews generally concluded that particle filtration is, at best, a source of small improvements in allergy and asthma health effects; however, many early studies had weak designs. A majority of recent intervention studies employed strong designs and more of these studies report statistically significant improvements in health symptoms or objective health outcomes, particularly for subjects with allergies or asthma. The percentage improvement in health outcomes is typically modest, for example, 7% to 25%. Delivery of filtered air to the breathing zone of sleeping allergic or asthmatic persons may be more consistently effective in improving health than room air filtration. Notable are two studies that report statistically significant improvements, with filtration, in markers that predict future adverse coronary events. From modeling, the largest potential benefits of indoor particle filtration may be reductions in morbidity and mortality from reducing indoor exposures to particles from outdoor air.
</description></item><item rdf:about="http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12037" xmlns="http://purl.org/rss/1.0/"><title>Submicrometer particle removal indoors by a novel electrostatic precipitator with high clean air delivery rate, low ozone emissions, and carbon fiber ionizer</title><link>http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12037</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Submicrometer particle removal indoors by a novel electrostatic precipitator with high clean air delivery rate, low ozone emissions, and carbon fiber ionizer</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">H.-J. Kim, B. Han, Y.-J. Kim, T. Oda, H. Won</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2013-03-18T23:44:02.819922-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/ina.12037</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/ina.12037</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12037</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Original Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[
<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Abstract</h3>
<div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>A novel positive-polarity electrostatic precipitator (ESP) was developed using an ionization stage (0.4 × 0.4 × 0.14 m<sup>3</sup>) with 16 carbon fiber ionizers in each channel and a collection stage (0.4 × 0.4 × 0.21 m<sup>3</sup>) with parallel metallic plates. The single-pass collection efficiency and clean air delivery rate (CADR) were measured by standard tests using KCl particles in 0.25–0.35 μm. Performance was determined using the Deutsch equation and established diffusion and field charging theories and also compared with the commercialized HEPA filter-type air cleaner. Experimental results showed that the single-pass collection efficiency of the ESP ranged from 50 to 95% and decreased with the flow rate (10–20 m<sup>3</sup>/min), but increased with the voltage applied to the ionizers (6 to 8 kV) and collection plates (−5 to −7 kV). The ESP with 18 m<sup>3</sup>/min achieved a CADR of 12.1 m<sup>3</sup>/min with a voltage of 8 kV applied to the ionization stage and with a voltage of −6 kV applied to the collection stage. The concentration of ozone in the test chamber (30.4 m<sup>3</sup>), a maximum value of 5.4 ppb over 12 h of continuous operation, was much lower than the current indoor regulation (50 ppb).</p></div>
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A novel positive-polarity electrostatic precipitator (ESP) was developed using an ionization stage (0.4 × 0.4 × 0.14 m3) with 16 carbon fiber ionizers in each channel and a collection stage (0.4 × 0.4 × 0.21 m3) with parallel metallic plates. The single-pass collection efficiency and clean air delivery rate (CADR) were measured by standard tests using KCl particles in 0.25–0.35 μm. Performance was determined using the Deutsch equation and established diffusion and field charging theories and also compared with the commercialized HEPA filter-type air cleaner. Experimental results showed that the single-pass collection efficiency of the ESP ranged from 50 to 95% and decreased with the flow rate (10–20 m3/min), but increased with the voltage applied to the ionizers (6 to 8 kV) and collection plates (−5 to −7 kV). The ESP with 18 m3/min achieved a CADR of 12.1 m3/min with a voltage of 8 kV applied to the ionization stage and with a voltage of −6 kV applied to the collection stage. The concentration of ozone in the test chamber (30.4 m3), a maximum value of 5.4 ppb over 12 h of continuous operation, was much lower than the current indoor regulation (50 ppb).
</description></item><item rdf:about="http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12035" xmlns="http://purl.org/rss/1.0/"><title>Stenotrophomonas, Mycobacterium, and Streptomyces in home dust and air: associations with moldiness and other home/family characteristics</title><link>http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12035</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Stenotrophomonas, Mycobacterium, and Streptomyces in home dust and air: associations with moldiness and other home/family characteristics</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">E. Kettleson, S. Kumar, T. Reponen, S. Vesper, D. Méheust, S. A. Grinshpun, A. Adhikari</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2013-03-18T23:43:57.185685-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/ina.12035</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/ina.12035</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12035</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Original Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[
<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Abstract</h3>
<div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Respiratory illnesses have been linked to children's exposures to water-damaged homes. Therefore, understanding the microbiome in water-damaged homes is critical to preventing these illnesses. Few studies have quantified bacterial contamination, especially specific species, in water-damaged homes. We collected air and dust samples in twenty-one low-mold homes and twenty-one high-mold homes. The concentrations of three bacteria/genera, <em>Stenotrophomonas maltophilia, Streptomyces</em> sp., and <em>Mycobacterium</em> sp., were measured in air and dust samples using quantitative PCR (QPCR). The concentrations of the bacteria measured in the air samples were not associated with any specific home characteristic based on multiple regression models. However, higher concentrations of <em>S. maltophilia</em> in the dust samples were associated with water damage, that is, with higher floor surface moisture and higher concentrations of moisture-related mold species. The concentrations of <em>Streptomyces</em> and <em>Mycobacterium</em> sp. had similar patterns and may be partially determined by human and animal occupants and outdoor sources of these bacteria.</p></div>
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Respiratory illnesses have been linked to children's exposures to water-damaged homes. Therefore, understanding the microbiome in water-damaged homes is critical to preventing these illnesses. Few studies have quantified bacterial contamination, especially specific species, in water-damaged homes. We collected air and dust samples in twenty-one low-mold homes and twenty-one high-mold homes. The concentrations of three bacteria/genera, Stenotrophomonas maltophilia, Streptomyces sp., and Mycobacterium sp., were measured in air and dust samples using quantitative PCR (QPCR). The concentrations of the bacteria measured in the air samples were not associated with any specific home characteristic based on multiple regression models. However, higher concentrations of S. maltophilia in the dust samples were associated with water damage, that is, with higher floor surface moisture and higher concentrations of moisture-related mold species. The concentrations of Streptomyces and Mycobacterium sp. had similar patterns and may be partially determined by human and animal occupants and outdoor sources of these bacteria.
</description></item><item rdf:about="http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12027" xmlns="http://purl.org/rss/1.0/"><title>Chimney stoves modestly improved Indoor Air Quality measurements compared with traditional open fire stoves: results from a small-scale intervention study in rural Peru</title><link>http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12027</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Chimney stoves modestly improved Indoor Air Quality measurements compared with traditional open fire stoves: results from a small-scale intervention study in rural Peru</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">S. M. Hartinger, A. A. Commodore, J. Hattendorf, C. F. Lanata, A. I. Gil, H. Verastegui, M. Aguilar-Villalobos, D. Mäusezahl, L. P. Naeher</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2013-02-11T09:55:22.649813-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/ina.12027</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/ina.12027</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12027</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Original Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[
<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Abstract</h3>
<div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Nearly half of the world's population depends on biomass fuels to meet domestic energy needs, producing high levels of pollutants responsible for substantial morbidity and mortality. We compare carbon monoxide (CO) and particulate matter (PM<sub>2.5</sub>) exposures and kitchen concentrations in households with study-promoted intervention (OPTIMA-improved stoves and control stoves) in San Marcos Province, Cajamarca Region, Peru. We determined 48-h indoor air concentration levels of CO and PM<sub>2.5</sub> in 93 kitchen environments and personal exposure, after OPTIMA-improved stoves had been installed for an average of 7 months. PM<sub>2.5</sub> and CO measurements did not differ significantly between OPTIMA-improved stoves and control stoves. Although not statistically significant, a <em>post hoc</em> stratification of OPTIMA-improved stoves by level of performance revealed mean PM<sub>2.5</sub> and CO levels of fully functional OPTIMA-improved stoves were 28% lower (<em>n</em> = 20, PM<sub>2.5,</sub> 136 μg/m<sup>3</sup> 95% CI 54–217) and 45% lower (<em>n</em> = 25, CO, 3.2 ppm, 95% CI 1.5–4.9) in the kitchen environment compared with the control stoves (<em>n</em> = 34, PM<sub>2.5</sub>, 189 μg/m<sup>3</sup>, 95% CI 116–261; <em>n</em> = 44, CO, 5.8 ppm, 95% CI 3.3–8.2). Likewise, although not statistically significant, personal exposures for OPTIMA-improved stoves were 43% and 17% lower for PM<sub>2.5</sub> (<em>n</em> = 23) and CO (<em>n</em> = 25), respectively. Stove maintenance and functionality level are factors worthy of consideration for future evaluations of stove interventions.</p></div>
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Nearly half of the world's population depends on biomass fuels to meet domestic energy needs, producing high levels of pollutants responsible for substantial morbidity and mortality. We compare carbon monoxide (CO) and particulate matter (PM2.5) exposures and kitchen concentrations in households with study-promoted intervention (OPTIMA-improved stoves and control stoves) in San Marcos Province, Cajamarca Region, Peru. We determined 48-h indoor air concentration levels of CO and PM2.5 in 93 kitchen environments and personal exposure, after OPTIMA-improved stoves had been installed for an average of 7 months. PM2.5 and CO measurements did not differ significantly between OPTIMA-improved stoves and control stoves. Although not statistically significant, a post hoc stratification of OPTIMA-improved stoves by level of performance revealed mean PM2.5 and CO levels of fully functional OPTIMA-improved stoves were 28% lower (n = 20, PM2.5, 136 μg/m3 95% CI 54–217) and 45% lower (n = 25, CO, 3.2 ppm, 95% CI 1.5–4.9) in the kitchen environment compared with the control stoves (n = 34, PM2.5, 189 μg/m3, 95% CI 116–261; n = 44, CO, 5.8 ppm, 95% CI 3.3–8.2). Likewise, although not statistically significant, personal exposures for OPTIMA-improved stoves were 43% and 17% lower for PM2.5 (n = 23) and CO (n = 25), respectively. Stove maintenance and functionality level are factors worthy of consideration for future evaluations of stove interventions.
</description></item><item rdf:about="http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12021" xmlns="http://purl.org/rss/1.0/"><title>Variation in residential radon levels in new Danish homes</title><link>http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12021</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Variation in residential radon levels in new Danish homes</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">E. V. Bräuner, T. V. Rasmussen, L. Gunnarsen</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2013-02-04T03:28:52.919812-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/ina.12021</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/ina.12021</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12021</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Original Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[
<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Abstract</h3>
<div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Radon-222 gas arises from the radioactive decay of radium-226 and has a half-life of 3.8 days. This gas percolates up through soil into buildings, and if it is not evacuated, there can be much higher exposure levels indoors than outdoors, which is where human exposure occurs. Radon exposure is classified as a human carcinogen, and new Danish homes must be constructed to ensure indoor radon levels below 100 Bq/m<sup>3</sup>. Our purpose was to assess how well 200 newly constructed single detached homes perform according to building regulations pertaining to radon and identify the association between indoor radon in these homes and municipality, home age, floor area, floor level, basement, and outer wall and roof construction. Median (5–95 percentile) indoor radon levels were 36.8 (9.0–118) Bq/m<sup>3</sup>, but indoor radon exceeded 100 Bq/m<sup>3</sup> in 14 of these new homes. The investigated variables explained nine percent of the variation in indoor radon levels, and although associations were positive, none of these were statistically significant. In this study, radon levels were generally low, but we found that 14 (7%) of the 200 new homes had indoor radon levels over 100 Bq/m<sup>3</sup>. More work is needed to determine the determinants of indoor radon.</p></div>
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Radon-222 gas arises from the radioactive decay of radium-226 and has a half-life of 3.8 days. This gas percolates up through soil into buildings, and if it is not evacuated, there can be much higher exposure levels indoors than outdoors, which is where human exposure occurs. Radon exposure is classified as a human carcinogen, and new Danish homes must be constructed to ensure indoor radon levels below 100 Bq/m3. Our purpose was to assess how well 200 newly constructed single detached homes perform according to building regulations pertaining to radon and identify the association between indoor radon in these homes and municipality, home age, floor area, floor level, basement, and outer wall and roof construction. Median (5–95 percentile) indoor radon levels were 36.8 (9.0–118) Bq/m3, but indoor radon exceeded 100 Bq/m3 in 14 of these new homes. The investigated variables explained nine percent of the variation in indoor radon levels, and although associations were positive, none of these were statistically significant. In this study, radon levels were generally low, but we found that 14 (7%) of the 200 new homes had indoor radon levels over 100 Bq/m3. More work is needed to determine the determinants of indoor radon.
</description></item><item rdf:about="http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12025" xmlns="http://purl.org/rss/1.0/"><title>People who live in a cold climate: thermal adaptation differences based on availability of heating</title><link>http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12025</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">People who live in a cold climate: thermal adaptation differences based on availability of heating</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">J. Yu, G. Cao, W. Cui, Q. Ouyang, Y. Zhu</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2013-01-31T09:41:25.780078-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/ina.12025</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/ina.12025</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12025</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Original Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[
<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Abstract</h3>
<div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Are there differences in thermal adaptation to cold indoor environments between people who are used to living in heating and non-heating regions in China? To answer this question, we measured thermal perceptions and physiological responses of young men from Beijing (where there are indoor space heating facilities in winter) and Shanghai (where there are not indoor space heating facilities in winter) during exposures to cold. Subjects were exposed to 12°C, 14°C, 16°C, 18°C, 20°C for 1 h. Subjects from Beijing complained of greater cold discomfort and demonstrated poorer physiological acclimatization to cold indoor environments than those from Shanghai. These findings indicate that people's chronic indoor thermal experience might be an important determinant of thermal adaptation.</p></div>
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Are there differences in thermal adaptation to cold indoor environments between people who are used to living in heating and non-heating regions in China? To answer this question, we measured thermal perceptions and physiological responses of young men from Beijing (where there are indoor space heating facilities in winter) and Shanghai (where there are not indoor space heating facilities in winter) during exposures to cold. Subjects were exposed to 12°C, 14°C, 16°C, 18°C, 20°C for 1 h. Subjects from Beijing complained of greater cold discomfort and demonstrated poorer physiological acclimatization to cold indoor environments than those from Shanghai. These findings indicate that people's chronic indoor thermal experience might be an important determinant of thermal adaptation.
</description></item><item rdf:about="http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12024" xmlns="http://purl.org/rss/1.0/"><title>Formaldehyde concentrations in household air of asthma patients determined using colorimetric detector tubes</title><link>http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12024</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Formaldehyde concentrations in household air of asthma patients determined using colorimetric detector tubes</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">K. C. Dannemiller, J. S. Murphy, S. L. Dixon, K. G. Pennell, E. M. Suuberg, D. E. Jacobs, M. Sandel</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2013-01-31T08:50:23.496654-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/ina.12024</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/ina.12024</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12024</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Original Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[
<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Abstract</h3>
<div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Formaldehyde is a colorless, pungent gas commonly found in homes and is a respiratory irritant, sensitizer, carcinogen, and asthma trigger. Typical household sources include plywood and particleboard, cleaners, cosmetics, pesticides, and others. Development of a fast and simple measurement technique could facilitate continued research on this important chemical. The goal of this research is to apply an inexpensive short-term measurement method to find correlations between formaldehyde sources and concentration, and formaldehyde concentration and asthma control. Formaldehyde was measured using 30-min grab samples in length-of-stain detector tubes in homes (<em>n</em> = 70) of asthmatics in the Boston, MA area. Clinical status and potential formaldehyde sources were determined. The geometric mean formaldehyde level was 35.1 ppb and ranged from 5 to 132 ppb. Based on one-way ANOVA, <em>t</em>-tests, and linear regression, predictors of log-transformed formaldehyde concentration included absolute humidity, season, and the presence of decorative laminates, fiberglass, or permanent press fabrics (<em>P</em> &lt; 0.05), as well as temperature and household cleaner use (<em>P</em> &lt; 0.10). The geometric mean formaldehyde concentration was 57% higher in homes of children with very poorly controlled asthma compared to homes of other asthmatic children (<em>P</em> = 0.078). This study provides a simple method for measuring household formaldehyde and suggests that exposure is related to poorly controlled asthma.</p></div>
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Formaldehyde is a colorless, pungent gas commonly found in homes and is a respiratory irritant, sensitizer, carcinogen, and asthma trigger. Typical household sources include plywood and particleboard, cleaners, cosmetics, pesticides, and others. Development of a fast and simple measurement technique could facilitate continued research on this important chemical. The goal of this research is to apply an inexpensive short-term measurement method to find correlations between formaldehyde sources and concentration, and formaldehyde concentration and asthma control. Formaldehyde was measured using 30-min grab samples in length-of-stain detector tubes in homes (n = 70) of asthmatics in the Boston, MA area. Clinical status and potential formaldehyde sources were determined. The geometric mean formaldehyde level was 35.1 ppb and ranged from 5 to 132 ppb. Based on one-way ANOVA, t-tests, and linear regression, predictors of log-transformed formaldehyde concentration included absolute humidity, season, and the presence of decorative laminates, fiberglass, or permanent press fabrics (P &lt; 0.05), as well as temperature and household cleaner use (P &lt; 0.10). The geometric mean formaldehyde concentration was 57% higher in homes of children with very poorly controlled asthma compared to homes of other asthmatic children (P = 0.078). This study provides a simple method for measuring household formaldehyde and suggests that exposure is related to poorly controlled asthma.
</description></item><item rdf:about="http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12022" xmlns="http://purl.org/rss/1.0/"><title>Survey of the reliability of carbon monoxide alarms deployed in domestic homes and efficacy of use by consumers</title><link>http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12022</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Survey of the reliability of carbon monoxide alarms deployed in domestic homes and efficacy of use by consumers</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">S. Naylor, P. T. Walsh, K. P. Dowker</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2013-01-25T09:30:43.161365-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/ina.12022</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/ina.12022</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12022</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Original Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[
<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Abstract</h3>
<div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Carbon monoxide (CO) alarms are extensively used in domestic premises in the UK to help protect against CO poisoning. Their expected lifetime has been increasing, and some current models now have a replacement period of more than 6 years under normal operation. However, concerns have been expressed as to the reliability of alarms over an extended period. In this study, 110 households with a CO alarm were surveyed, during which the alarm was uninstalled and replaced and a household survey questionnaire administered. Alarm reliability was assessed under laboratory conditions by testing conformity to the alarm condition gas tests in either the British (European) standard, BS EN 50291 for UK certified models, or the US standard, UL 2034 for US certified models. The questionnaire recorded the alarm make and model, its age, its location, whether it was correctly sited, and how often it was tested. General information on the property was also collected. Results of laboratory testing suggest that the reliability of the most common models of CO alarms used by UK consumers has improved over the last 7 years. However, findings from the household survey suggest that the way alarms are used in many homes may not maximize their ability to detect abnormal levels CO.</p></div>
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Carbon monoxide (CO) alarms are extensively used in domestic premises in the UK to help protect against CO poisoning. Their expected lifetime has been increasing, and some current models now have a replacement period of more than 6 years under normal operation. However, concerns have been expressed as to the reliability of alarms over an extended period. In this study, 110 households with a CO alarm were surveyed, during which the alarm was uninstalled and replaced and a household survey questionnaire administered. Alarm reliability was assessed under laboratory conditions by testing conformity to the alarm condition gas tests in either the British (European) standard, BS EN 50291 for UK certified models, or the US standard, UL 2034 for US certified models. The questionnaire recorded the alarm make and model, its age, its location, whether it was correctly sited, and how often it was tested. General information on the property was also collected. Results of laboratory testing suggest that the reliability of the most common models of CO alarms used by UK consumers has improved over the last 7 years. However, findings from the household survey suggest that the way alarms are used in many homes may not maximize their ability to detect abnormal levels CO.
</description></item><item rdf:about="http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12018" xmlns="http://purl.org/rss/1.0/"><title>Characterization of decay and emission rates of ultrafine particles in indoor ice rink</title><link>http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12018</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Characterization of decay and emission rates of ultrafine particles in indoor ice rink</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">J. Kim, K. Lee</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2013-01-25T09:30:40.895928-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/ina.12018</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/ina.12018</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12018</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Original Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[
<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Abstract</h3>
<div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>The purposes of this study were to determine indoor ultrafine particle (UFP, diameter &lt;100 nm) levels in ice rinks and to characterize UFP decay and emission rates. All 15 public ice rinks in Seoul were investigated for UFP and carbon monoxide (<span class="fixed-roman">CO</span>) concentrations. Three ice rinks did not show peaks in UFP concentrations, and one ice rink used two resurfacers simultaneously. High peaks of UFP and <span class="fixed-roman">CO</span> concentrations were observed when the resurfacer was operated. The average air change rate in the 11 ice rinks was 0.21 ± 0.13/h. The average decay rates of UFP number concentrations measured by the P-Trak and DiSCmini were 0.54 ± 0.21/h and 0.85 ± 0.34/h, respectively. The average decay rate of UFP surface area concentration was 0.33 ± 0.15/h. The average emission rates of UFP number concentrations measured by P-Trak and DiSCmini were 1.2 × 10<sup>14</sup> ± 6.5 × 10<sup>13</sup> particles/min and 3.3 × 10<sup>14</sup> ± 2.4 × 10<sup>14</sup> particles/min, respectively. The average emission rate of UFP surface area concentration was 3.1 × 10<sup>11</sup> ± 2.0 × 10<sup>11</sup> μm<sup>2</sup>/min. UFP emission rate was associated with resurfacer age. DiSCmini measured higher decay and emission rates than P-Trak due to their different measuring mechanisms and size ranges.</p></div>
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The purposes of this study were to determine indoor ultrafine particle (UFP, diameter &lt;100 nm) levels in ice rinks and to characterize UFP decay and emission rates. All 15 public ice rinks in Seoul were investigated for UFP and carbon monoxide (CO) concentrations. Three ice rinks did not show peaks in UFP concentrations, and one ice rink used two resurfacers simultaneously. High peaks of UFP and CO concentrations were observed when the resurfacer was operated. The average air change rate in the 11 ice rinks was 0.21 ± 0.13/h. The average decay rates of UFP number concentrations measured by the P-Trak and DiSCmini were 0.54 ± 0.21/h and 0.85 ± 0.34/h, respectively. The average decay rate of UFP surface area concentration was 0.33 ± 0.15/h. The average emission rates of UFP number concentrations measured by P-Trak and DiSCmini were 1.2 × 1014 ± 6.5 × 1013 particles/min and 3.3 × 1014 ± 2.4 × 1014 particles/min, respectively. The average emission rate of UFP surface area concentration was 3.1 × 1011 ± 2.0 × 1011 μm2/min. UFP emission rate was associated with resurfacer age. DiSCmini measured higher decay and emission rates than P-Trak due to their different measuring mechanisms and size ranges.
</description></item><item rdf:about="http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12020" xmlns="http://purl.org/rss/1.0/"><title>Isolation of Aspergillus fumigatus from sputum is associated with elevated airborne levels in homes of patients with asthma</title><link>http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12020</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Isolation of Aspergillus fumigatus from sputum is associated with elevated airborne levels in homes of patients with asthma</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">A. Fairs, J. Agbetile, M. Bourne, B. Hargadon, W. R. Monteiro, J. P. Morley, R. E. Edwards, A. J. Wardlaw, C. H. Pashley</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2013-01-25T05:08:58.7768-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/ina.12020</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/ina.12020</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12020</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Original Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[
<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Abstract</h3>
<div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Indoor bioaerosols, such as mold spores, have been associated with respiratory symptoms in patients with asthma; however, dose–response relationships and guidelines on acceptable levels are lacking. Furthermore, a causal link between mold exposure and respiratory infections or asthma remains to be established. The aim of this study was to determine indoor concentrations of <em>Aspergillus fumigatus</em> and a subset of clinically relevant fungi in homes of people with asthma, in relation to markers of airways colonization and sensitization. Air and dust samples were collected from the living room of 58 properties. Fungal concentrations were quantified using mold-specific quantitative PCR and compared with traditional microscopic analysis of air samples. Isolation of <em>A. fumigatus</em> from sputum was associated with higher airborne concentrations of the fungus in patient homes (<em>P</em> = 0.04), and a similar trend was shown with <em>Aspergillus</em>/<em>Penicillium-</em>type concentrations analyzed by microscopy (<em>P</em> = 0.058). No association was found between airborne levels of <em>A. fumigatus</em> and sensitization to this fungus, or dustborne levels of <em>A. fumigatus</em> and either isolation from sputum or sensitization. The results of this study suggest that the home environment should be considered as a potential source of fungal exposure, and elevated home levels may predispose people with asthma to airways colonization.</p></div>
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Indoor bioaerosols, such as mold spores, have been associated with respiratory symptoms in patients with asthma; however, dose–response relationships and guidelines on acceptable levels are lacking. Furthermore, a causal link between mold exposure and respiratory infections or asthma remains to be established. The aim of this study was to determine indoor concentrations of Aspergillus fumigatus and a subset of clinically relevant fungi in homes of people with asthma, in relation to markers of airways colonization and sensitization. Air and dust samples were collected from the living room of 58 properties. Fungal concentrations were quantified using mold-specific quantitative PCR and compared with traditional microscopic analysis of air samples. Isolation of A. fumigatus from sputum was associated with higher airborne concentrations of the fungus in patient homes (P = 0.04), and a similar trend was shown with Aspergillus/Penicillium-type concentrations analyzed by microscopy (P = 0.058). No association was found between airborne levels of A. fumigatus and sensitization to this fungus, or dustborne levels of A. fumigatus and either isolation from sputum or sensitization. The results of this study suggest that the home environment should be considered as a potential source of fungal exposure, and elevated home levels may predispose people with asthma to airways colonization.
</description></item><item rdf:about="http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12009" xmlns="http://purl.org/rss/1.0/"><title>Dose–response relationships between mouse allergen exposure and asthma morbidity among urban children and adolescents</title><link>http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12009</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Dose–response relationships between mouse allergen exposure and asthma morbidity among urban children and adolescents</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">E. N. Torjusen, G. B. Diette, P. N. Breysse, J. Curtin-Brosnan, C. Aloe, E. C. Matsui</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-11-23T05:02:50.683021-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/ina.12009</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/ina.12009</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12009</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Original Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[
<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Abstract</h3>
<div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Home mouse allergen exposure is associated with asthma morbidity, but little is known about the shape of the dose–response relationship or the relevance of location of exposure within the home. Asthma outcome and allergen exposure data were collected every 3 months for 1 year in 150 urban children with asthma. Participants were stratified by mouse sensitization, and relationships between continuous measures of mouse allergen exposure and outcomes of interest were analyzed. Every tenfold increase in the bed mouse allergen level was associated with an 87% increase in the odds of any asthma-related health care use among mouse-sensitized [Odds Ratio (95% CI): 1.87 (1.21–2.88)], but not non-mouse-sensitized participants. Similar relationships were observed for emergency department visit and unscheduled doctor visit among mouse-sensitized participants. Kitchen floor and bedroom air mouse allergen concentrations were also associated with greater odds of asthma-related healthcare utilization; however, the magnitude of the association was less than that observed for bed mouse allergen concentrations. In this population of urban children with asthma, there is a linear dose–response relationship between mouse allergen concentrations and asthma morbidity among mouse-sensitized asthmatics. Bed and bedroom air mouse allergen exposure compartments may have a greater impact on asthma morbidity than other compartments.</p></div>
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Home mouse allergen exposure is associated with asthma morbidity, but little is known about the shape of the dose–response relationship or the relevance of location of exposure within the home. Asthma outcome and allergen exposure data were collected every 3 months for 1 year in 150 urban children with asthma. Participants were stratified by mouse sensitization, and relationships between continuous measures of mouse allergen exposure and outcomes of interest were analyzed. Every tenfold increase in the bed mouse allergen level was associated with an 87% increase in the odds of any asthma-related health care use among mouse-sensitized [Odds Ratio (95% CI): 1.87 (1.21–2.88)], but not non-mouse-sensitized participants. Similar relationships were observed for emergency department visit and unscheduled doctor visit among mouse-sensitized participants. Kitchen floor and bedroom air mouse allergen concentrations were also associated with greater odds of asthma-related healthcare utilization; however, the magnitude of the association was less than that observed for bed mouse allergen concentrations. In this population of urban children with asthma, there is a linear dose–response relationship between mouse allergen concentrations and asthma morbidity among mouse-sensitized asthmatics. Bed and bedroom air mouse allergen exposure compartments may have a greater impact on asthma morbidity than other compartments.
</description></item><item rdf:about="http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12030" xmlns="http://purl.org/rss/1.0/"><title>Chemical versus biological contamination indoors: trade-offs versus win–win opportunities for improving indoor air quality</title><link>http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12030</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Chemical versus biological contamination indoors: trade-offs versus win–win opportunities for improving indoor air quality</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Nicola Carslaw, Abigail Hathway, Louise Fletcher, Jacqueline Hamilton, Trevor Ingham, Catherine Noakes</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2013-04-19T01:15:56.688471-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/ina.12030</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/ina.12030</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12030</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Editorial</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">173</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">174</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[]]></content:encoded><description/></item><item rdf:about="http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12019" xmlns="http://purl.org/rss/1.0/"><title>A randomized double-blind crossover study of indoor air filtration and acute changes in cardiorespiratory health in a First Nations community</title><link>http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12019</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">A randomized double-blind crossover study of indoor air filtration and acute changes in cardiorespiratory health in a First Nations community</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">S. Weichenthal, G. Mallach, R. Kulka, A. Black, A. Wheeler, H. You, M. St-Jean, R. Kwiatkowski, D. Sharp</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2013-01-19T06:30:28.535455-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/ina.12019</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/ina.12019</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12019</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Original Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">175</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">184</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[
<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Abstract</h3>
<div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Few studies have examined indoor air quality in First Nations communities and its impact on cardiorespiratory health. To address this need, we conducted a crossover study on a First Nations reserve in Manitoba, Canada, including 37 residents in 20 homes. Each home received an electrostatic air filter and a placebo filter for 1 week in random order, and lung function, blood pressure, and endothelial function measures were collected at the beginning and end of each week. Indoor air pollutants were monitored throughout the study period. Indoor PM<sub>2.5</sub> decreased substantially during air filter weeks relative to placebo (mean difference: 37 μg/m<sup>3</sup>, 95% CI: 10, 64) but remained approximately five times greater than outdoor concentrations owing to a high prevalence of indoor smoking. On average, air filter use was associated with a 217-ml (95% CI: 23, 410) increase in forced expiratory volume in 1 s, a 7.9-mm Hg (95% CI: −17, 0.82) decrease in systolic blood pressure, and a 4.5-mm Hg (95% CI: −11, 2.4) decrease in diastolic blood pressure. Consistent inverse associations were also observed between indoor PM<sub>2.5</sub> and lung function. In general, our findings suggest that reducing indoor PM<sub>2.5</sub> may contribute to improved lung function in First Nations communities.</p></div>
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Few studies have examined indoor air quality in First Nations communities and its impact on cardiorespiratory health. To address this need, we conducted a crossover study on a First Nations reserve in Manitoba, Canada, including 37 residents in 20 homes. Each home received an electrostatic air filter and a placebo filter for 1 week in random order, and lung function, blood pressure, and endothelial function measures were collected at the beginning and end of each week. Indoor air pollutants were monitored throughout the study period. Indoor PM2.5 decreased substantially during air filter weeks relative to placebo (mean difference: 37 μg/m3, 95% CI: 10, 64) but remained approximately five times greater than outdoor concentrations owing to a high prevalence of indoor smoking. On average, air filter use was associated with a 217-ml (95% CI: 23, 410) increase in forced expiratory volume in 1 s, a 7.9-mm Hg (95% CI: −17, 0.82) decrease in systolic blood pressure, and a 4.5-mm Hg (95% CI: −11, 2.4) decrease in diastolic blood pressure. Consistent inverse associations were also observed between indoor PM2.5 and lung function. In general, our findings suggest that reducing indoor PM2.5 may contribute to improved lung function in First Nations communities.
</description></item><item rdf:about="http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12013" xmlns="http://purl.org/rss/1.0/"><title>Pilot study of high-performance air filtration for classroom applications</title><link>http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12013</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Pilot study of high-performance air filtration for classroom applications</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">A. Polidori, P. M. Fine, V. White, P. S. Kwon</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-12-20T10:47:27.197708-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/ina.12013</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/ina.12013</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12013</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Original Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">185</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">195</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[
<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Abstract</h3>
<div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>A study was conducted to investigate the effectiveness of three air purification systems in reducing the exposure of children to air contaminants inside nine classrooms of three Southern California schools. Continuous and integrated measurements were conducted to monitor the indoor and outdoor concentrations of ultrafine particles (UFPs), fine and coarse particulate matter (PM<sub>2.5</sub> and PM<sub>10</sub>, respectively), black carbon (BC), and volatile organic compounds. An heating, ventilating, and air conditioning (HVAC)-based high-performance panel filter (HP-PF), a register-based air purifier (RS), and a stand-alone air cleaning system (SA) were tested alone and in different combinations for their ability to remove the monitored pollutants. The combination of a RS and a HP-PF was the most effective solution for lowering the indoor concentrations of BC, UFPs, and PM<sub>2.5</sub>, with study average reductions between 87% and 96%. When using the HP-PF alone, reductions close to 90% were also achieved. In all cases, air quality conditions were improved substantially with respect to the corresponding baseline (preexisting) conditions. Data on the performance of the gas-absorbing media included in the RS and SA unit were inconclusive, and their effectiveness, lifetime, costs, and benefits must be further assessed before conclusions and recommendations can be made.</p></div>
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A study was conducted to investigate the effectiveness of three air purification systems in reducing the exposure of children to air contaminants inside nine classrooms of three Southern California schools. Continuous and integrated measurements were conducted to monitor the indoor and outdoor concentrations of ultrafine particles (UFPs), fine and coarse particulate matter (PM2.5 and PM10, respectively), black carbon (BC), and volatile organic compounds. An heating, ventilating, and air conditioning (HVAC)-based high-performance panel filter (HP-PF), a register-based air purifier (RS), and a stand-alone air cleaning system (SA) were tested alone and in different combinations for their ability to remove the monitored pollutants. The combination of a RS and a HP-PF was the most effective solution for lowering the indoor concentrations of BC, UFPs, and PM2.5, with study average reductions between 87% and 96%. When using the HP-PF alone, reductions close to 90% were also achieved. In all cases, air quality conditions were improved substantially with respect to the corresponding baseline (preexisting) conditions. Data on the performance of the gas-absorbing media included in the RS and SA unit were inconclusive, and their effectiveness, lifetime, costs, and benefits must be further assessed before conclusions and recommendations can be made.
</description></item><item rdf:about="http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12015" xmlns="http://purl.org/rss/1.0/"><title>Filtration effectiveness of HVAC systems at near-roadway schools</title><link>http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12015</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Filtration effectiveness of HVAC systems at near-roadway schools</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">M. C. McCarthy, J. F. Ludwig, S. G. Brown, D. L. Vaughn, P. T. Roberts</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2013-01-25T09:30:37.15102-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/ina.12015</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/ina.12015</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12015</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Original Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">196</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">207</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[
<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Abstract</h3>
<div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Concern for the exposure of children attending schools located near busy roadways to toxic, traffic-related air pollutants has raised questions regarding the environmental benefits of advanced heating, ventilation, and air-conditioning (HVAC) filtration systems for near-road pollution. Levels of black carbon and gaseous pollutants were measured at three indoor classroom sites and at seven outdoor monitoring sites at Las Vegas schools. Initial HVAC filtration systems effected a 31–66% reduction in black carbon particle concentrations inside three schools compared with ambient air concentrations. After improved filtration systems were installed, black carbon particle concentrations were reduced by 74–97% inside three classrooms relative to ambient air concentrations. Average black carbon particle concentrations inside the schools with improved filtration systems were lower than typical ambient Las Vegas concentrations by 49–96%. Gaseous pollutants were higher indoors than outdoors. The higher indoor concentrations most likely originated at least partially from indoor sources, which were not targeted as part of this intervention.</p></div>
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Concern for the exposure of children attending schools located near busy roadways to toxic, traffic-related air pollutants has raised questions regarding the environmental benefits of advanced heating, ventilation, and air-conditioning (HVAC) filtration systems for near-road pollution. Levels of black carbon and gaseous pollutants were measured at three indoor classroom sites and at seven outdoor monitoring sites at Las Vegas schools. Initial HVAC filtration systems effected a 31–66% reduction in black carbon particle concentrations inside three schools compared with ambient air concentrations. After improved filtration systems were installed, black carbon particle concentrations were reduced by 74–97% inside three classrooms relative to ambient air concentrations. Average black carbon particle concentrations inside the schools with improved filtration systems were lower than typical ambient Las Vegas concentrations by 49–96%. Gaseous pollutants were higher indoors than outdoors. The higher indoor concentrations most likely originated at least partially from indoor sources, which were not targeted as part of this intervention.
</description></item><item rdf:about="http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12017" xmlns="http://purl.org/rss/1.0/"><title>Endotoxin, extracellular polysaccharides, and β(1-3)-glucan concentrations in dust and their determinants in four European birth cohorts: results from the HITEA project</title><link>http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12017</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Endotoxin, extracellular polysaccharides, and β(1-3)-glucan concentrations in dust and their determinants in four European birth cohorts: results from the HITEA project</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">L. Casas, C. Tischer, I. M. Wouters, M. Valkonen, U. Gehring, G. Doekes, M. Torrent, J. Pekkanen, R. Garcia-Esteban, A. Hyvärinen, J. Heinrich, J. Sunyer</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-12-21T03:43:13.580541-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/ina.12017</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/ina.12017</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12017</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Original Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">208</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">218</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[
<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Abstract</h3>
<div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Early-life exposure to microbial agents may play a protective role in asthma and allergies development. Geographical differences in the prevalence of these diseases exist, but the differences in early-life indoor microbial agent levels and their determinants have been hardly studied. We aimed to describe the early-life levels of endotoxin, extracellular polysaccharides (EPS), and β(1-3)-glucans in living room dust of four geographically spread European birth cohorts (LISA in Germany, PIAMA in the Netherlands, INMA in Spain, and LUKAS2 in Finland) and to assess their determinants. A total of 1572 dust samples from living rooms of participants were analyzed for endotoxin, Penicillium/Aspergillus EPS, and β(1-3)-glucans. Information on potential determinants was obtained through questionnaires. Concentrations of endotoxin, EPS, and β(1-3)-glucans were different across cohorts. Concentrations of endotoxin and EPS were respectively lower and higher in INMA than in other cohorts, while glucans were higher in LUKAS2. Season of sampling, dog ownership, dampness, and the number of people living at home were significantly associated with concentrations of at least one microbial agent, with heterogeneity of effect estimates of the determinants across cohorts. In conclusion, both early-life microbial exposure levels and exposure determinants differ across cohorts derived from diverse European countries.</p></div>
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Early-life exposure to microbial agents may play a protective role in asthma and allergies development. Geographical differences in the prevalence of these diseases exist, but the differences in early-life indoor microbial agent levels and their determinants have been hardly studied. We aimed to describe the early-life levels of endotoxin, extracellular polysaccharides (EPS), and β(1-3)-glucans in living room dust of four geographically spread European birth cohorts (LISA in Germany, PIAMA in the Netherlands, INMA in Spain, and LUKAS2 in Finland) and to assess their determinants. A total of 1572 dust samples from living rooms of participants were analyzed for endotoxin, Penicillium/Aspergillus EPS, and β(1-3)-glucans. Information on potential determinants was obtained through questionnaires. Concentrations of endotoxin, EPS, and β(1-3)-glucans were different across cohorts. Concentrations of endotoxin and EPS were respectively lower and higher in INMA than in other cohorts, while glucans were higher in LUKAS2. Season of sampling, dog ownership, dampness, and the number of people living at home were significantly associated with concentrations of at least one microbial agent, with heterogeneity of effect estimates of the determinants across cohorts. In conclusion, both early-life microbial exposure levels and exposure determinants differ across cohorts derived from diverse European countries.
</description></item><item rdf:about="http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12016" xmlns="http://purl.org/rss/1.0/"><title>Are cats and dogs the major source of endotoxin in homes?</title><link>http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12016</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Are cats and dogs the major source of endotoxin in homes?</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">D. R. Ownby, E. L. Peterson, G. Wegienka, K. J. Woodcroft, C. Nicholas, E. Zoratti, C. C. Johnson</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2013-02-08T00:24:34.912179-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/ina.12016</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/ina.12016</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12016</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Original Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">219</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">226</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[
<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Abstract</h3>
<div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Previous studies have suggested that exposure to cats and dogs during early childhood reduces the risk of allergic disease, possibly by increasing home endotoxin exposure. This study asked the question of whether cats and dogs are the dominant influence on dust endotoxin concentrations in homes after considering other variables reportedly associated with endotoxin. The presence of cats or dogs in homes, household and home characteristics, and dust endotoxin concentrations from 5 locations were assessed in 966 urban and suburban homes. Whether considered together as pets or as cats and dogs separately, the presence of cats and dogs significantly contributed to living room and bedroom floor endotoxin concentrations, but not to bed endotoxin concentrations. However, the two variables consistently related to endotoxin in all home sites were the home occupant density (occupants/room) and cleanliness of the home. Our data suggest that reducing occupant density and improving home cleanliness would reduce home endotoxin concentrations more than removing pet cats or dogs from the home.</p></div>
]]></content:encoded><description>

Previous studies have suggested that exposure to cats and dogs during early childhood reduces the risk of allergic disease, possibly by increasing home endotoxin exposure. This study asked the question of whether cats and dogs are the dominant influence on dust endotoxin concentrations in homes after considering other variables reportedly associated with endotoxin. The presence of cats or dogs in homes, household and home characteristics, and dust endotoxin concentrations from 5 locations were assessed in 966 urban and suburban homes. Whether considered together as pets or as cats and dogs separately, the presence of cats and dogs significantly contributed to living room and bedroom floor endotoxin concentrations, but not to bed endotoxin concentrations. However, the two variables consistently related to endotoxin in all home sites were the home occupant density (occupants/room) and cleanliness of the home. Our data suggest that reducing occupant density and improving home cleanliness would reduce home endotoxin concentrations more than removing pet cats or dogs from the home.
</description></item><item rdf:about="http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12002" xmlns="http://purl.org/rss/1.0/"><title>Acute effects of exposure to vapors of 3-methyl-1-butanol in humans</title><link>http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12002</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Acute effects of exposure to vapors of 3-methyl-1-butanol in humans</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">L. Ernstgård, D. Norbäck, T. Nordquist, G. Wieslander, R. Wålinder, G. Johanson</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-08-29T05:30:27.65793-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/ina.12002</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/ina.12002</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12002</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Original Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">227</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">235</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[
<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Abstract</h3>
<div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>The secondary alcohol 3-methyl-1-butanol (3MB, isoamyl alcohol) is used, for example, as a solvent in a variety of applications and as a fragrance ingredient. It is also one of the microbial volatile organic compounds (MVOCs) found in indoor air. There are little data on acute effects. The aim of the study was to assess the acute effects of 3MB in humans. Thirty healthy volunteers (16 men and 14 women) were exposed in random order to 1 mg/m<sup>3</sup> 3MB or clean air for 2 h at controlled conditions. Ratings with visual analogue scales revealed slightly increased perceptions of eye irritation (<em>P</em> = 0.048, Wilcoxon) and smell (<em>P</em> &lt; 0.0001) compared with control exposure. The other ratings were not significantly affected (irritation in nose and throat, dyspnea, headache, fatigue, dizziness, nausea, and intoxication). No significant exposure-related effects were found in blinking frequency, tear film break-up time, vital staining of the eye, nasal lavage biomarkers, lung function, and nasal swelling. In conclusion, this study suggests that 3MB is not a causative factor for health effects in damp and moldy buildings.</p></div>
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The secondary alcohol 3-methyl-1-butanol (3MB, isoamyl alcohol) is used, for example, as a solvent in a variety of applications and as a fragrance ingredient. It is also one of the microbial volatile organic compounds (MVOCs) found in indoor air. There are little data on acute effects. The aim of the study was to assess the acute effects of 3MB in humans. Thirty healthy volunteers (16 men and 14 women) were exposed in random order to 1 mg/m3 3MB or clean air for 2 h at controlled conditions. Ratings with visual analogue scales revealed slightly increased perceptions of eye irritation (P = 0.048, Wilcoxon) and smell (P &lt; 0.0001) compared with control exposure. The other ratings were not significantly affected (irritation in nose and throat, dyspnea, headache, fatigue, dizziness, nausea, and intoxication). No significant exposure-related effects were found in blinking frequency, tear film break-up time, vital staining of the eye, nasal lavage biomarkers, lung function, and nasal swelling. In conclusion, this study suggests that 3MB is not a causative factor for health effects in damp and moldy buildings.
</description></item><item rdf:about="http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12010" xmlns="http://purl.org/rss/1.0/"><title>On the suitability of steady RANS CFD for forced mixing ventilation at transitional slot Reynolds numbers</title><link>http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12010</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">On the suitability of steady RANS CFD for forced mixing ventilation at transitional slot Reynolds numbers</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">T. van Hooff, B. Blocken, G. J. F. van Heijst</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-11-29T09:13:46.007671-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/ina.12010</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/ina.12010</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12010</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Original Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">236</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">249</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[
<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Abstract</h3>
<div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Accurate prediction of ventilation flow is of primary importance for designing a healthy, comfortable, and energy-efficient indoor environment. Since the 1970s, the use of computational fluid dynamics (CFD) has increased tremendously, and nowadays, it is one of the primary methods to assess ventilation flow in buildings. The most commonly used numerical approach consists of solving the steady Reynolds-averaged Navier–Stokes (RANS) equations with a turbulence model to provide closure. This article presents a detailed validation study of steady RANS for isothermal forced mixing ventilation of a cubical enclosure driven by a transitional wall jet. The validation is performed using particle image velocimetry (PIV) measurements for slot Reynolds numbers of 1000 and 2500. Results obtained with the renormalization group (RNG) <em>k</em>-ε model, a low-Reynolds <em>k</em>-ε model, the shear stress transport (SST) <em>k</em>-ω model, and a Reynolds stress model (RSM) are compared with detailed experimental data. In general, the RNG <em>k</em>-ε model shows the weakest performance, whereas the low-Re <em>k</em>-ε model shows the best agreement with the measurements. In addition, the influence of the turbulence model on the predicted air exchange efficiency in the cubical enclosure is analyzed, indicating differences up to 44% for this particular case.</p></div>
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Accurate prediction of ventilation flow is of primary importance for designing a healthy, comfortable, and energy-efficient indoor environment. Since the 1970s, the use of computational fluid dynamics (CFD) has increased tremendously, and nowadays, it is one of the primary methods to assess ventilation flow in buildings. The most commonly used numerical approach consists of solving the steady Reynolds-averaged Navier–Stokes (RANS) equations with a turbulence model to provide closure. This article presents a detailed validation study of steady RANS for isothermal forced mixing ventilation of a cubical enclosure driven by a transitional wall jet. The validation is performed using particle image velocimetry (PIV) measurements for slot Reynolds numbers of 1000 and 2500. Results obtained with the renormalization group (RNG) k-ε model, a low-Reynolds k-ε model, the shear stress transport (SST) k-ω model, and a Reynolds stress model (RSM) are compared with detailed experimental data. In general, the RNG k-ε model shows the weakest performance, whereas the low-Re k-ε model shows the best agreement with the measurements. In addition, the influence of the turbulence model on the predicted air exchange efficiency in the cubical enclosure is analyzed, indicating differences up to 44% for this particular case.
</description></item><item rdf:about="http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12012" xmlns="http://purl.org/rss/1.0/"><title>Use of personalized ventilation for improving health, comfort, and performance at high room temperature and humidity</title><link>http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12012</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Use of personalized ventilation for improving health, comfort, and performance at high room temperature and humidity</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">A. K. Melikov, M. A. Skwarczynski, J. Kaczmarczyk, J. Zabecky</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-12-07T08:01:47.88716-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/ina.12012</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/ina.12012</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12012</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Original Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">250</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">263</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[
<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Abstract</h3>
<div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>The effect of personalized ventilation (PV) on people's health, comfort, and performance in a warm and humid environment (26 and 28°C at 70% relative humidity) was studied and compared with their responses in a comfortable environment (23°C and 40% relative humidity). Thirty subjects participated in five 4-h experiments in a climate chamber. Under the conditions with PV, the subjects were able to control the rate and direction of the supplied personalized flow of clean air. Subjective responses were collected through questionnaires. During all exposures, the subjects were occupied with tasks used to assess their performance. Objective measures of tear film stability, concentration of stress biomarkers in saliva, and eye blinking rate were taken. Using PV significantly improved the perceived air quality (PAQ) and thermal sensation and decreased the intensity of Sick Building Syndrome (SBS) symptoms to those prevailing in a comfortable room environment without PV. Self-estimated and objectively measured performance was improved. Increasing the temperature and relative humidity, but not the use of PV, significantly decreased tear film quality and the concentration of salivary alpha-amylase, indicating lower mental arousal and alertness. The use of PV improved tear film stability as compared to that in a warm environment without PV.</p></div>
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The effect of personalized ventilation (PV) on people's health, comfort, and performance in a warm and humid environment (26 and 28°C at 70% relative humidity) was studied and compared with their responses in a comfortable environment (23°C and 40% relative humidity). Thirty subjects participated in five 4-h experiments in a climate chamber. Under the conditions with PV, the subjects were able to control the rate and direction of the supplied personalized flow of clean air. Subjective responses were collected through questionnaires. During all exposures, the subjects were occupied with tasks used to assess their performance. Objective measures of tear film stability, concentration of stress biomarkers in saliva, and eye blinking rate were taken. Using PV significantly improved the perceived air quality (PAQ) and thermal sensation and decreased the intensity of Sick Building Syndrome (SBS) symptoms to those prevailing in a comfortable room environment without PV. Self-estimated and objectively measured performance was improved. Increasing the temperature and relative humidity, but not the use of PV, significantly decreased tear film quality and the concentration of salivary alpha-amylase, indicating lower mental arousal and alertness. The use of PV improved tear film stability as compared to that in a warm environment without PV.
</description></item><item rdf:about="http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12028" xmlns="http://purl.org/rss/1.0/"><title>Corrigendum</title><link>http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12028</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Corrigendum</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2013-04-19T01:15:56.688471-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1111/ina.12028</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1111/ina.12028</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://onlinelibrary.wiley.com/resolve/doi?DOI=10.1111%2Fina.12028</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Corrigendum</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">264</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">264</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[]]></content:encoded><description/></item></rdf:RDF>