<?xml version="1.0" encoding="ISO-8859-1"?>

<rdf:RDF
 xmlns:rdf="http://www.w3.org/1999/02/22-rdf-syntax-ns#"
 xmlns="http://purl.org/rss/1.0/"
 xmlns:taxo="http://purl.org/rss/1.0/modules/taxonomy/"
 xmlns:dc="http://purl.org/dc/elements/1.1/"
 xmlns:syn="http://purl.org/rss/1.0/modules/syndication/"
 xmlns:prism="http://purl.org/rss/1.0/modules/prism/"
 xmlns:admin="http://webns.net/mvcb/"
>

<channel rdf:about="http://annhyg.oxfordjournals.org">
<title>Annals of Occupational Hygiene - Advance Access</title>
<link>http://annhyg.oxfordjournals.org</link>
<description>Annals of Occupational Hygiene - RSS feed of articles</description>
<prism:eIssn>1475-3162</prism:eIssn>
<prism:publicationName>Annals of Occupational Hygiene</prism:publicationName>
<prism:issn>0003-4878</prism:issn>
<items>
 <rdf:Seq>
  <rdf:li rdf:resource="http://annhyg.oxfordjournals.org/cgi/content/short/men037v1?rss=1" />
  <rdf:li rdf:resource="http://annhyg.oxfordjournals.org/cgi/content/short/men032v1?rss=1" />
  <rdf:li rdf:resource="http://annhyg.oxfordjournals.org/cgi/content/short/men036v1?rss=1" />
  <rdf:li rdf:resource="http://annhyg.oxfordjournals.org/cgi/content/short/men034v1?rss=1" />
  <rdf:li rdf:resource="http://annhyg.oxfordjournals.org/cgi/content/short/men031v1?rss=1" />
  <rdf:li rdf:resource="http://annhyg.oxfordjournals.org/cgi/content/short/men024v3?rss=1" />
  <rdf:li rdf:resource="http://annhyg.oxfordjournals.org/cgi/content/short/men020v3?rss=1" />
  <rdf:li rdf:resource="http://annhyg.oxfordjournals.org/cgi/content/short/men029v1?rss=1" />
  <rdf:li rdf:resource="http://annhyg.oxfordjournals.org/cgi/content/short/men028v2?rss=1" />
  <rdf:li rdf:resource="http://annhyg.oxfordjournals.org/cgi/content/short/men023v2?rss=1" />
  <rdf:li rdf:resource="http://annhyg.oxfordjournals.org/cgi/content/short/men030v1?rss=1" />
  <rdf:li rdf:resource="http://annhyg.oxfordjournals.org/cgi/content/short/men026v1?rss=1" />
  <rdf:li rdf:resource="http://annhyg.oxfordjournals.org/cgi/content/short/men027v1?rss=1" />
  <rdf:li rdf:resource="http://annhyg.oxfordjournals.org/cgi/content/short/men025v1?rss=1" />
  <rdf:li rdf:resource="http://annhyg.oxfordjournals.org/cgi/content/short/men022v1?rss=1" />
  <rdf:li rdf:resource="http://annhyg.oxfordjournals.org/cgi/content/short/men021v1?rss=1" />
  <rdf:li rdf:resource="http://annhyg.oxfordjournals.org/cgi/content/short/men019v1?rss=1" />
  <rdf:li rdf:resource="http://annhyg.oxfordjournals.org/cgi/content/short/men017v1?rss=1" />
  <rdf:li rdf:resource="http://annhyg.oxfordjournals.org/cgi/content/short/men018v1?rss=1" />
 </rdf:Seq>
</items>
</channel>

<item rdf:about="http://annhyg.oxfordjournals.org/cgi/content/short/men037v1?rss=1">
<title><![CDATA[Assessment of Occupational Genotoxic Risk among Brazilian Hairdressers]]></title>
<link>http://annhyg.oxfordjournals.org/cgi/content/short/men037v1?rss=1</link>
<description><![CDATA[
<p><b>Objectives: To evaluate the genotoxic risk to hairdressers exposed daily to chemical substances such as hair dyes, waving and straightening preparations and manicurists' products by the Comet assay test (single-cell gel electrophoresis).</b></p>
<p><b>Methods: The Comet assay was performed on blood samples from 69 female hairdressers (36.4 &plusmn; 10.7 years old) currently employed in 21 different beauty institutes in S&atilde;o Paulo, Brazil, and on 55 female control blood donors (32.6 &plusmn; 10.0 years old) from the S&atilde;o Paulo University Clinical Hospital blood bank. All the control subjects had occupations other than hairdresser. Comet assays were performed by evaluating 100 blood lymphocytes per individual and graded by visual score according to comet tail length.</b></p>
<p><b>Results: The hairdressers showed a higher frequency of DNA damage revealed by Comet Score (159.8 &plusmn; 71) when compared to the control group (125.4 &plusmn; 64.1), and the difference was statistically significant by the Student's <I>t</I>-test (<I>P</I> = 0.005). Multiple regression analysis showed that in addition to the hairdressers' profession, tobacco use contributed to the higher frequency of cells with comets (<I>P</I> &lt; 0.05).</b></p>
<p><b>Conclusions: The observed DNA damage could be associated with the hairdressers' occupational environment, where different chemicals are chronically manipulated and inhaled. Considering that this profession in many countries, including Brazil, is not officially regulated, more attention should focus on these professionals not only by legislative bodies but also by multidisciplinary teams able to develop and implement risk prevention and control strategies for chemical, physical and biological agents to which hairdressers are exposed.</b></p>
]]></description>
<dc:creator><![CDATA[Galiotte, M. P., Kohler, P., Mussi, G., Figaro Gattas, G. J.]]></dc:creator>
<dc:date>2008-07-01</dc:date>
<dc:identifier>info:doi/10.1093/annhyg/men037</dc:identifier>
<dc:title><![CDATA[Assessment of Occupational Genotoxic Risk among Brazilian Hairdressers]]></dc:title>
<dc:publisher>British Occupational Hygiene Society</dc:publisher>
<prism:publicationDate>2008-07-01</prism:publicationDate>
<prism:section>Article</prism:section>
</item>

<item rdf:about="http://annhyg.oxfordjournals.org/cgi/content/short/men032v1?rss=1">
<title><![CDATA['Stoffenmanager', a Web-Based Control Banding Tool Using an Exposure Process Model]]></title>
<link>http://annhyg.oxfordjournals.org/cgi/content/short/men032v1?rss=1</link>
<description><![CDATA[
<p>In the scope of a Dutch programme to reinforce the working conditions policy on hazardous substances, an internet-based tool was developed to help small- and medium-sized companies to handle hazardous substances with more care. The heart of this tool, called the Stoffenmanager, is a risk banding scheme. It combines a hazard banding scheme similar to that of COSHH Essentials and an exposure banding scheme based on an exposure model originally presented by Cherrie <I>et al</I>. (1996) and further developed by Cherrie and Schneider (1999). The exposure model has been modified to allow non-expert users to understand and use the model. Exposure scores are calculated based on categorization of determinants of emission, transmission and immission. These exposure scores are assigned to exposure bands. The comparison of exposure bands and hazard bands leads to a risk band or priority band. Following the evaluation of the priority of tasks done with products, generic exposure control measures can be evaluated for their possibility to lower the risks. Relevant control measures can be put into an action plan and into workplace instruction cards. The tool has several other functionalities regarding registration and storage of products. The exposure model in the Stoffenmanager leads to exposure scores. These have been compared with measured exposure levels. The exposure scores correlated well with measured exposure levels. The development of the Stoffenmanager has facilitated a whole range of further developments of useful tools for small- and medium-sized enterprises.</p>
]]></description>
<dc:creator><![CDATA[Marquart, H., Heussen, H., Le Feber, M., Noy, D., Tielemans, E., Schinkel, J., West, J., Van Der Schaaf, D.]]></dc:creator>
<dc:date>2008-06-27</dc:date>
<dc:identifier>info:doi/10.1093/annhyg/men032</dc:identifier>
<dc:title><![CDATA['Stoffenmanager', a Web-Based Control Banding Tool Using an Exposure Process Model]]></dc:title>
<dc:publisher>British Occupational Hygiene Society</dc:publisher>
<prism:publicationDate>2008-06-27</prism:publicationDate>
<prism:section>Article</prism:section>
</item>

<item rdf:about="http://annhyg.oxfordjournals.org/cgi/content/short/men036v1?rss=1">
<title><![CDATA[Asbestos Fibre Concentrations in the Lungs of Brake Workers: Another Look]]></title>
<link>http://annhyg.oxfordjournals.org/cgi/content/short/men036v1?rss=1</link>
<description><![CDATA[
<p>Objective: To reanalyse data on the lung content of asbestos fibres among brake mechanics.</p>
<p>Methods: I re-analysed data published by Butnor, Roggli and colleagues on the lung content of chrysotile and tremolite asbestos fibres among brake mechanics and controls. Statistics of the distributions were estimated by maximum likelihood to accommodate observations below the detection limit. Mean concentrations were compared by the <I>t</I>-test, bootstrap resampling and interval-censored survival methods.</p>
<p>Results: The mean concentrations of fibres were higher among the brake workers than the controls. The concentration of tremolite fibres was higher than the concentration of chrysotile, a pattern similar to that observed among Quebec chrysotile miners and millers.</p>
<p>Conclusions: Re-analysis of published data does not support the interpretation that, in automotive brake repair workers with malignant mesothelioma, asbestos content is within the normal range. The alternative interpretation that brake mechanics have a greater than background burden of asbestos fibres, attributable to occupational exposure to dusts from friction products manufactured from Canadian chrysotile, appears more credible. This asbestos burden might be associated with an increased risk of asbestos-associated cancers.</p>
]]></description>
<dc:creator><![CDATA[Finkelstein, M. M.]]></dc:creator>
<dc:date>2008-06-23</dc:date>
<dc:identifier>info:doi/10.1093/annhyg/men036</dc:identifier>
<dc:title><![CDATA[Asbestos Fibre Concentrations in the Lungs of Brake Workers: Another Look]]></dc:title>
<dc:publisher>British Occupational Hygiene Society</dc:publisher>
<prism:publicationDate>2008-06-23</prism:publicationDate>
<prism:section>Article</prism:section>
</item>

<item rdf:about="http://annhyg.oxfordjournals.org/cgi/content/short/men034v1?rss=1">
<title><![CDATA[Measurement Uncertainty]]></title>
<link>http://annhyg.oxfordjournals.org/cgi/content/short/men034v1?rss=1</link>
<description><![CDATA[
<p>The reporting of measurement uncertainty has recently undergone a major harmonization whereby characteristics of a measurement method obtained during establishment and application are combined componentwise. For example, the sometimes-pesky systematic error is included. A bias component of uncertainty can be often easily established as the uncertainty in the bias. However, beyond simply arriving at a value for uncertainty, meaning to this uncertainty if needed can sometimes be developed in terms of prediction confidence in uncertainty-based intervals covering what is to be measured. To this end, a link between concepts of accuracy and uncertainty is established through a simple yet accurate approximation to a random variable known as the non-central Student's <I>t</I>-distribution.</p>
<p><I>Without a measureless and perpetual uncertainty, the drama of human life would be destroyed.</I> Winston Churcill</p>
]]></description>
<dc:creator><![CDATA[Bartley, D., Liden, G.]]></dc:creator>
<dc:date>2008-06-23</dc:date>
<dc:identifier>info:doi/10.1093/annhyg/men034</dc:identifier>
<dc:title><![CDATA[Measurement Uncertainty]]></dc:title>
<dc:publisher>British Occupational Hygiene Society</dc:publisher>
<prism:publicationDate>2008-06-23</prism:publicationDate>
<prism:section>Commentaries</prism:section>
</item>

<item rdf:about="http://annhyg.oxfordjournals.org/cgi/content/short/men031v1?rss=1">
<title><![CDATA[Estimation of Benchmark Dose for Bone Damage and Renal Dysfunction in a Chinese Male Population Occupationally Exposed to Lead]]></title>
<link>http://annhyg.oxfordjournals.org/cgi/content/short/men031v1?rss=1</link>
<description><![CDATA[
<p>Objectives: The aim of this study was to examine a possible relationship between lead nephropathy and its effects on the skeleton in male population occupationally exposed to lead in China.</p>
<p>Methods: One hundred and fifty-five lead-exposed male workers in a storage battery plant in Shanghai were selected as the exposed subjects while the 36 healthy male officers in the plant who were not occupationally exposed to lead were treated as the control. Blood lead (BPb) and urine lead were used as biomarkers for exposure. <I>Z</I> score, urine hydroxyproline (HYP), serum alkaline phosphatase (bone isoenzyme) (BALP) and serum osteocalcin (BGP) were used as biomarkers for bone effects. Urine <I>N</I>-acetyl-&beta;-<scp>D</scp>-glucosaminidase (UNAG) and urine albumin (UALB) were applied as biomarkers of renal tubular and glomerular dysfunction. Bone mineral density was measured by the monophoton absorptiometry (SPA-4).</p>
<p>Results: It was found that there were linear correlate relationships between lead exposure and NAG, ALB, BALP, BGP, HYP, <I>Z</I> score (<I>P</I> &lt; 0.01), after controlling confounders such as age and work year. NAG, ALB, BALP, BGP and HYP would increase with the increase of lead exposure. <I>Z</I> score would decrease with the increase of lead exposure. Of 21 subjects with osteoporosis, nine subjects were suffering from renal dysfunction. The prevalence of renal dysfunction (42.86%) was significantly higher in the subjects with osteoporosis than in those without osteoporosis (17.65%) (<sup>2</sup> = 7.310, <I>P</I> = 0.007). The prevalence of osteoporosis had relationship with renal tubular damage, but not with renal glomerular damage. This showed that glomerular dysfunction plays a smaller role than tubular dysfunction in the causation of bone damage. Benchmark dose in terms of BPb was calculated using Benchmark Dose Software Version 1.3.2 software. The benchmark dose lower limit of a one-sided 95% confidence interval (BMDL) for 10% excess risk was also determined. It was found that BMDL<SUB>&ndash;05</SUB> for BALP, UNAG, BGP, HYP, <I>Z</I> score and UALB of BPb increased sequentially. The BMDL values for UNAG (10.13 &micro;g dL<sup>&ndash;1</sup>) were lower than those of <I>Z</I> score (14.17 &micro;g dL<sup>&ndash;1</sup>).</p>
<p>Conclusions: The present study has thus demonstrated the combined adverse effects (osteoporosis and renal dysfunction) caused by occupational exposure to lead. There was a dose&ndash;response relationship between lead exposure and prevalence of osteoporosis, renal dysfunction and bone metabolism. The renal dysfunction might develop earlier than osteoporosis. Osteoporosis caused by lead was related to the change of bone metabolism and renal dysfunction, which was especially to tubular damage but not to glomerular damage.</p>
]]></description>
<dc:creator><![CDATA[Sun, Y., Sun, D., Zhou, Z., Zhu, G., Lei, L., Zhang, H., Chang, X., Jin, T.]]></dc:creator>
<dc:date>2008-06-20</dc:date>
<dc:identifier>info:doi/10.1093/annhyg/men031</dc:identifier>
<dc:title><![CDATA[Estimation of Benchmark Dose for Bone Damage and Renal Dysfunction in a Chinese Male Population Occupationally Exposed to Lead]]></dc:title>
<dc:publisher>British Occupational Hygiene Society</dc:publisher>
<prism:publicationDate>2008-06-20</prism:publicationDate>
<prism:section>Article</prism:section>
</item>

<item rdf:about="http://annhyg.oxfordjournals.org/cgi/content/short/men024v3?rss=1">
<title><![CDATA[Variability in Endotoxin Exposure Levels and Consequences for Exposure Assessment]]></title>
<link>http://annhyg.oxfordjournals.org/cgi/content/short/men024v3?rss=1</link>
<description><![CDATA[
<p><b>Objectives: Workers in many industries are exposed to endotoxins, which may cause adverse health effects. In exposure assessment, information about exposure variability is essential. However, variability in exposure has rarely been investigated for biological agents and more specifically for endotoxin. Therefore, variance components and determinants of exposure were studied in a large database with &gt;2000 endotoxin measurements.</b></p>
<p><b>Methods: Data from 10 individual studies were combined to create a database with 2010 personal inhalable dust and endotoxin measurements, of which 1650 were repeated measurements. Exposure groups were defined based on job codes. Between- and within-worker variance components were estimated for different grouping strategies, and determinants of exposure were studied using mixed effects models.</b></p>
<p><b>Results: Inhalable dust and endotoxin exposure levels are summarized for 46 industries and 4 broadly defined sectors. The between-worker variability exceeded the within-worker variability overall and within sectors and subsectors, and variance components were larger for endotoxin than for dust. Between-worker variability also exceeded within-worker variability in nearly half of the exposure groups based upon industries or job code within industries for endotoxin exposure and in 10% of the groups for dust exposure. Among other things, dustiness of the process, contact with animals, bulk production, presence of plant material or a cyclic process appeared as determinants of exposure, which largely explained the between-worker variability.</b></p>
<p><b>Conclusions: Exposure groups were much less homogeneous for endotoxin exposure than for dust exposure. This is distinctly different than for chemical exposure. Large variability in measured exposure levels is inherent to endotoxin exposure, which is caused in part by determinants that influence growth of microorganisms. These findings have major consequences for the design of future occupational intervention and epidemiological studies. The measurement effort needs to be greater than exposure assessment for chemical agents which demonstrate lower exposure variability, especially when evaluating endotoxin exposure for compliance testing. The established determinants of exposure give direction for potential exposure control, although more information about determinants of day-to-day variability in exposure is still needed to be able to effectively control endotoxin exposure.</b></p>
]]></description>
<dc:creator><![CDATA[Spaan, S., Schinkel, J., Wouters, I. M., Preller, L., Tielemans, E., Nij, E. T., Heederik, D.]]></dc:creator>
<dc:date>2008-06-12</dc:date>
<dc:identifier>info:doi/10.1093/annhyg/men024</dc:identifier>
<dc:title><![CDATA[Variability in Endotoxin Exposure Levels and Consequences for Exposure Assessment]]></dc:title>
<dc:publisher>British Occupational Hygiene Society</dc:publisher>
<prism:publicationDate>2008-06-12</prism:publicationDate>
<prism:section>Article</prism:section>
</item>

<item rdf:about="http://annhyg.oxfordjournals.org/cgi/content/short/men020v3?rss=1">
<title><![CDATA[Trends in Occupational Exposure to Styrene in the European Glass Fibre-Reinforced Plastics Industry]]></title>
<link>http://annhyg.oxfordjournals.org/cgi/content/short/men020v3?rss=1</link>
<description><![CDATA[
<p>Aim: This study presents temporal trends of styrene exposure for workers in the European glass fibre-reinforced plastics (GRP) industry during the period 1966&ndash;2002.</p>
<p>Methods: Data of personal styrene exposure measurements were retrieved from reports, databases and peer-reviewed papers. Only sources with descriptive statistics of personal measurements were accepted. The styrene exposure data cover personal air samples and biological monitoring data, that is, urinary styrene metabolites (mandelic acid and/or phenylglyoxylic acid) and styrene in blood. Means of series of measurements were categorized by year, country, production process, job and sampling strategy. Linear mixed models were used to identify temporal trends and factors affecting exposure levels.</p>
<p>Results: Personal exposure measurements were available from 60 reports providing data on 24145 1&ndash;8-h time-weighted average shift personal air samples. Available data of biological exposure indicators included measurements of mandelic acid in post-shift urine (6361 urine samples being analysed). Trend analyses of the available styrene exposure data showed that the average styrene concentration in the breathing zone of open-mould workers in the European GRP industry has decreased on average by 5.3% per year during the period 1966&ndash;1990 and by only 0.4% annually in the period after 1990. The highest exposures were measured in Southern Europe and the lowest exposures in Northern Europe with Central Europe in between. Biological indicators of styrene (mandelic acid in post-shift urine) showed a somewhat steeper decline (8.9%), most likely because urine samples were collected in companies that showed a stronger decrease of styrene exposure in air than GRP companies where no biological measurements were carried out.</p>
]]></description>
<dc:creator><![CDATA[Van Rooij, J. G. M., Kasper, A., Triebig, G., Werner, P., Jongeneelen, F. J., Kromhout, H.]]></dc:creator>
<dc:date>2008-06-12</dc:date>
<dc:identifier>info:doi/10.1093/annhyg/men020</dc:identifier>
<dc:title><![CDATA[Trends in Occupational Exposure to Styrene in the European Glass Fibre-Reinforced Plastics Industry]]></dc:title>
<dc:publisher>British Occupational Hygiene Society</dc:publisher>
<prism:publicationDate>2008-06-12</prism:publicationDate>
<prism:section>Article</prism:section>
</item>

<item rdf:about="http://annhyg.oxfordjournals.org/cgi/content/short/men029v1?rss=1">
<title><![CDATA[Exposure to Fibres, Crystalline Silica, Silicon Carbide and Sulphur Dioxide in the Norwegian Silicon Carbide Industry]]></title>
<link>http://annhyg.oxfordjournals.org/cgi/content/short/men029v1?rss=1</link>
<description><![CDATA[
<p>Objectives: The aim of this study was to assess personal exposure to fibres, crystalline silica, silicon carbide (SiC) and sulphur dioxide in the Norwegian SiC industry.</p>
<p>Methods: Approximately 720 fibre samples, 720 respirable dust samples and 1400 total dust samples were collected from randomly chosen workers from the furnace, processing and maintenance departments in all three Norwegian SiC plants. The respirable dust samples were analysed for quartz, cristobalite and non-fibrous SiC content. Approximately 240 sulphur dioxide samples were collected from workers in the furnace department.</p>
<p>Results: The sorting operators from all plants, control room and cleaning operators in Plant A and charger, charger/mix and payloader operators in Plant C had a geometric mean (GM) of fibre exposure above the Norwegian occupational exposure limit (OEL) (0.1 fibre cm<sup>&ndash;3</sup>). The cleaner operators in Plant A had the highest GM exposure to respirable quartz (20 &micro;g m<sup>&ndash;3</sup>). The charger/mix operators in Plant C had the highest GM exposure to respirable cristobalite (38 &micro;g m<sup>&ndash;3</sup>) and the refinery crusher operators in Plant A had the highest GM exposure to non-fibrous SiC (0.65 mg m<sup>&ndash;3</sup>). Exposure to the crystalline silica and non-fibrous SiC was generally low and between 0.4 and 2.1% of the measurements exceeded the OELs. The cleaner operators in Plant A had the highest GM exposure to respirable dust (1.3 mg m<sup>&ndash;3</sup>) and total dust (21 mg m<sup>&ndash;3</sup>). GM exposures for respirable dust above the Norwegian SiC industry-specific OEL of 0.5 mg m<sup>&ndash;3</sup> were also found for refinery crusher operators in all plants and mix, charger, charger/mix and sorting operators in Plant C. Only 4% of the total dust measurements exceeded the OEL for nuisance dust of (10 mg m<sup>&ndash;3</sup>). Exposure to sulphur dioxide was generally low. However, peaks in the range of 10&ndash;100 p.p.m. were observed for control room and crane operators in Plants A and B and for charger and charger/mix operators in Plant C.</p>
<p>Conclusion: Workers in the SiC industry are exposed to a mixture of several agents including SiC fibres, quartz, cristobalite, non-fibrous SiC and sulphur dioxide. Exposure levels were generally below the current Norwegian OELs; however, high exposure to fibres and respirable dust still occurs in the furnace department.</p>
]]></description>
<dc:creator><![CDATA[Foreland, S., Bye, E., Bakke, B., Eduard, W.]]></dc:creator>
<dc:date>2008-06-11</dc:date>
<dc:identifier>info:doi/10.1093/annhyg/men029</dc:identifier>
<dc:title><![CDATA[Exposure to Fibres, Crystalline Silica, Silicon Carbide and Sulphur Dioxide in the Norwegian Silicon Carbide Industry]]></dc:title>
<dc:publisher>British Occupational Hygiene Society</dc:publisher>
<prism:publicationDate>2008-06-11</prism:publicationDate>
<prism:section>Article</prism:section>
</item>

<item rdf:about="http://annhyg.oxfordjournals.org/cgi/content/short/men028v2?rss=1">
<title><![CDATA[Exposure to Chrysotile Asbestos Associated with Unpacking and Repacking Boxes of Automobile Brake Pads and Shoes]]></title>
<link>http://annhyg.oxfordjournals.org/cgi/content/short/men028v2?rss=1</link>
<description><![CDATA[
<p>Industrial hygiene surveys and epidemiologic studies of auto mechanics have shown that these workers are not at an increased risk of asbestos-related disease; however, concerns continue to be raised regarding asbestos exposure from asbestos-containing brakes. Handling new asbestos-containing brake components has recently been suggested as a potential source of asbestos exposure. A simulation study involving the unpacking and repacking of 105 boxes of brakes (for vehicles ca. 1946&ndash;80), including 62 boxes of brake pads and 43 boxes of brake shoes, was conducted to examine how this activity might contribute to both short-term and 8-h time-weighted average exposures to asbestos. Breathing zone samples on the lapel of a volunteer worker (<I>n</I> = 80) and area samples at bystander (e.g., 1.5 m from worker) (<I>n</I> = 56), remote area (<I>n</I> = 26) and ambient (<I>n</I> = 10) locations collected during the unpacking and repacking of boxes of asbestos-containing brakes were analyzed by phase contrast microscopy and transmission electron microscopy. Exposure to airborne asbestos was characterized for a variety of parameters including the number of boxes handled, brake type (i.e. pads versus shoes) and the distance from the activity (i.e. worker, bystander and remote area). This study also evaluated the fiber size and morphology distribution according to the International Organization for Standardization analytical method for asbestos. It was observed that (i) airborne asbestos concentrations increased with the number of boxes unpacked and repacked, (ii) handling boxes of brake pads resulted in higher worker asbestos exposures compared to handling boxes of brake shoes, (iii) cleanup and clothes-handling tasks produced less airborne asbestos than handling boxes of brakes and (iv) fiber size and morphology analysis showed that while the majority of fibers were free (e.g. not associated with a cluster or matrix), &lt;30% were respirable and even fewer were of the size range (&gt;20 &micro;m length) considered to pose the greatest risk of asbestos-related disease. It was found that average airborne chrysotile concentrations (30 min) ranged from 0.086 to 0.368 and 0.021 to 0.126 f cc<sup>&ndash;1</sup> for a worker unpacking and repacking 4&ndash;20 boxes of brake pads and 4&ndash;20 boxes of brake shoes, respectively. Additionally, average airborne asbestos exposures (30 min) at bystander locations ranged from 0.004 to 0.035 and 0.002 to 0.011 f cc<sup>&ndash;1</sup> when 4&ndash;20 boxes of brake pads and 4&ndash;20 boxes of brake shoes were handled, respectively. These data show that a worker handling a relatively large number of boxes of brakes over short periods of time will not be exposed to airborne asbestos in excess of its historical or current short-term occupational exposure limits.</p>
]]></description>
<dc:creator><![CDATA[Madl, A. K., Scott, L. L., Murbach, D. M., Fehling, K. A., Finley, B. L., Paustenbach, D. J.]]></dc:creator>
<dc:date>2008-06-11</dc:date>
<dc:identifier>info:doi/10.1093/annhyg/men028</dc:identifier>
<dc:title><![CDATA[Exposure to Chrysotile Asbestos Associated with Unpacking and Repacking Boxes of Automobile Brake Pads and Shoes]]></dc:title>
<dc:publisher>British Occupational Hygiene Society</dc:publisher>
<prism:publicationDate>2008-06-11</prism:publicationDate>
<prism:section>Article</prism:section>
</item>

<item rdf:about="http://annhyg.oxfordjournals.org/cgi/content/short/men023v2?rss=1">
<title><![CDATA[The Meaning of the Bias Uncertainty Measure]]></title>
<link>http://annhyg.oxfordjournals.org/cgi/content/short/men023v2?rss=1</link>
<description><![CDATA[
<p>Characterization of measurement uncertainty in terms of root sums of squares of both unknown systematic as well as random error components is given meaning in the sense of prediction intervals. Both types of errors are commonly encountered with industrial hygiene air monitoring of hazardous substances. Two extreme types of measurement methods are presented for illustrating how confidence levels may be ascribed to prediction intervals defined by such uncertainty values. In the case of method calibration at each measurement, systematic error or bias may enter from a biased calibrant. At another extreme, a single initial method evaluation may leave residual bias owing to random error in the evaluation itself or to the use of a biased reference method. Analysis is simplified through new simple approximations to probabilistic limits (quantiles) on the magnitude of a non-central Student <I>t</I>-distributed random variable. Connection is established between traditional confidence limits, accuracy measures in the case of bias minimization and an uncertainty measure.</p>
]]></description>
<dc:creator><![CDATA[Bartley, D. L.]]></dc:creator>
<dc:date>2008-06-06</dc:date>
<dc:identifier>info:doi/10.1093/annhyg/men023</dc:identifier>
<dc:title><![CDATA[The Meaning of the Bias Uncertainty Measure]]></dc:title>
<dc:publisher>British Occupational Hygiene Society</dc:publisher>
<prism:publicationDate>2008-06-06</prism:publicationDate>
<prism:section>Article</prism:section>
</item>

<item rdf:about="http://annhyg.oxfordjournals.org/cgi/content/short/men030v1?rss=1">
<title><![CDATA[Linking Expert Judgement and Trends in Occupational Exposure into a Job-Exposure Matrix for Historical Exposure to Asbestos in The Netherlands]]></title>
<link>http://annhyg.oxfordjournals.org/cgi/content/short/men030v1?rss=1</link>
<description><![CDATA[
<p>The aim of this article was to describe the structure and content of a job-exposure matrix (JEM) for historical asbestos exposure in The Netherlands. The JEM contained 309 occupational job title groups in 70 branches of industry during 10 periods of 5 years during 1945&ndash;1994, resulting in 3090 evaluations. Dutch sources on asbestos exposure measurements provided quantitative guidance for 69 evaluations (2.2%) in 25 occupational title groups. In addition, three databases from the UK Health and Safety Executive contributed to 222 evaluations (7.2%) and several other sources aided in another 133 evaluations (4.3%). These evaluations resulted in seven categories of exposure levels for all 3090 combinations of occupational title groups and periods. A verification process with five experts was used to adjust the assignments of exposure categories. The trends in exposure patterns over time were described in relation to production activities, operational control measures and the presence of dust control measures. For the majority of asbestos-related diseases in the past decades, reliable information on their historical exposure patterns was lacking. The limited availability of exposure measurements in the past illustrates the need for a structured assessment of historical asbestos exposure through a JEM.</p>
]]></description>
<dc:creator><![CDATA[Swuste, P., Dahhan, M., Burdorf, A.]]></dc:creator>
<dc:date>2008-06-03</dc:date>
<dc:identifier>info:doi/10.1093/annhyg/men030</dc:identifier>
<dc:title><![CDATA[Linking Expert Judgement and Trends in Occupational Exposure into a Job-Exposure Matrix for Historical Exposure to Asbestos in The Netherlands]]></dc:title>
<dc:publisher>British Occupational Hygiene Society</dc:publisher>
<prism:publicationDate>2008-06-03</prism:publicationDate>
<prism:section>Article</prism:section>
</item>

<item rdf:about="http://annhyg.oxfordjournals.org/cgi/content/short/men026v1?rss=1">
<title><![CDATA[Particulate Matter Exposure during Domestic Work in Nepal]]></title>
<link>http://annhyg.oxfordjournals.org/cgi/content/short/men026v1?rss=1</link>
<description><![CDATA[
<p><b>Aims: To measure particulate matter (PM) exposure of people involved in domestic work (i.e. housework by a resident, not paid work) in urban and rural Nepal, with exposure to biomass smoke in the rural areas, and to examine the performance of photometric devices in collecting these data. This paper details the results of these measurements and derives calibration factors for two photometric devices compared to gravimetric measures.</b></p>
<p><b>Methods: Between April 2006 and February 2007, respirable dust and PM<SUB>2.5</SUB> levels were measured over a 24-h period in 490 households in a range of urban and rural settings in the Kathmandu valley of Nepal. Sampling was carried out by photometric and gravimetric methods with the co-located gravimetric data used to derive a calibration factor for the photometric devices.</b></p>
<p><b>Results: The time-weighted average (TWA) (24 h) respirable dust levels measured by gravimetric sampler ranged from 13 to 2600 &micro;g m<sup>&ndash;3</sup> in the rural settings and 3 to 110 &micro;g m<sup>&ndash;3</sup> in the urban settings. The co-located photometric and gravimetric devices indicate that the SidePak Personal Aerosol Monitor device required a calibration factor of 0.48 and 0.51 for rural and urban data, respectively, whereas the DustTrak device required a factor of 0.31 and 0.35 for rural and urban settings to correct for the particle size and density of the biomass smoke. The photometric devices provide time history data on PM concentration levels and generally indicate two distinct peaks around a morning and early evening cooking time.</b></p>
<p><b>Conclusions: Those involved in domestic work in rural Nepal are exposed to average respirable dust concentrations of ~1400 &micro;g m<sup>&ndash;3</sup>. Converted to an 8-h TWA, this equates to more than the current UK limit for respirable dust (4000 &micro;g m<sup>&ndash;3</sup>). Homemakers, primarily women, spend a large proportion of their lives indoors in these high respirable dust concentrations and these exposures are likely to produce respiratory illness. Exposure can be controlled by the use of different fuel types and/or the use of flued stoves.</b></p>
]]></description>
<dc:creator><![CDATA[Kurmi, O. P., Semple, S., Steiner, M., Henderson, G. D., Ayres, J. G.]]></dc:creator>
<dc:date>2008-06-03</dc:date>
<dc:identifier>info:doi/10.1093/annhyg/men026</dc:identifier>
<dc:title><![CDATA[Particulate Matter Exposure during Domestic Work in Nepal]]></dc:title>
<dc:publisher>British Occupational Hygiene Society</dc:publisher>
<prism:publicationDate>2008-06-03</prism:publicationDate>
<prism:section>Article</prism:section>
</item>

<item rdf:about="http://annhyg.oxfordjournals.org/cgi/content/short/men027v1?rss=1">
<title><![CDATA[Occupational PAH Exposures during Prescribed Pile Burns]]></title>
<link>http://annhyg.oxfordjournals.org/cgi/content/short/men027v1?rss=1</link>
<description><![CDATA[
<p>Wildland firefighters are exposed to particulate matter and gases containing polycyclic aromatic hydrocarbons (PAHs), many of which are known carcinogens. Our objective was to evaluate the extent of firefighter exposure to particulate and PAHs during prescribed pile burns of mainly ponderosa pine slash and determine whether these exposures were correlated with changes in urinary 1-hydroxypyrene (1-HP), a PAH metabolite. Personal and area sampling for particulate and PAH exposures were conducted on the White Mountain Apache Tribe reservation, working with 21 Bureau of Indian Affairs/Fort Apache Agency wildland firefighters during the fall of 2006. Urine samples were collected pre- and post-exposure and pulmonary function was measured. Personal PAH exposures were detectable for only 3 of 16 PAHs analyzed: naphthalene, phenanthrene, and fluorene, all of which were identified only in vapor-phase samples. Condensed-phase PAHs were detected in PM2.5 area samples (20 of 21 PAHs analyzed were detected, all but naphthalene) at concentrations below 1 &micro;g m<sup>&ndash;3</sup>. The total PAH/PM2.5 mass fractions were roughly a factor of two higher during smoldering (1.06 &plusmn; 0.15) than ignition (0.55 &plusmn; 0.04 &micro;g mg<sup>&ndash;1</sup>). There were no significant changes in urinary 1-HP or pulmonary function following exposure to pile burning. In summary, PAH exposures were low in pile burns, and urinary testing for a PAH metabolite failed to show a significant difference between baseline and post-exposure measurements.</p>
]]></description>
<dc:creator><![CDATA[Robinson, M. S., Anthony, T. R., Littau, S. R., Herckes, P., Nelson, X., Poplin, G. S., Burgess, J. L.]]></dc:creator>
<dc:date>2008-05-31</dc:date>
<dc:identifier>info:doi/10.1093/annhyg/men027</dc:identifier>
<dc:title><![CDATA[Occupational PAH Exposures during Prescribed Pile Burns]]></dc:title>
<dc:publisher>British Occupational Hygiene Society</dc:publisher>
<prism:publicationDate>2008-05-31</prism:publicationDate>
<prism:section>Article</prism:section>
</item>

<item rdf:about="http://annhyg.oxfordjournals.org/cgi/content/short/men025v1?rss=1">
<title><![CDATA[Toward Better Exposure Assessment Strategies--The New NIOSH Initiative]]></title>
<link>http://annhyg.oxfordjournals.org/cgi/content/short/men025v1?rss=1</link>
<description><![CDATA[
<p>NIOSH has embarked on a project to update its exposure sampling strategies manual. The current NIOSH strategy has a number of limitations. This is an opportunity to develop a robust and comprehensive exposure assessment strategy. Some of the key features of such a strategy are outlined. The importance of accurate professional judgment and exposure modeling is discussed. Bayesian statistics offers a rational approach to integrating sampling data, professional judgments, and the outputs of exposure models in a comprehensive framework.</p>
]]></description>
<dc:creator><![CDATA[Ramachandran, G.]]></dc:creator>
<dc:date>2008-05-31</dc:date>
<dc:identifier>info:doi/10.1093/annhyg/men025</dc:identifier>
<dc:title><![CDATA[Toward Better Exposure Assessment Strategies--The New NIOSH Initiative]]></dc:title>
<dc:publisher>British Occupational Hygiene Society</dc:publisher>
<prism:publicationDate>2008-05-31</prism:publicationDate>
<prism:section>Commentaries</prism:section>
</item>

<item rdf:about="http://annhyg.oxfordjournals.org/cgi/content/short/men022v1?rss=1">
<title><![CDATA[Visualization of the Airflow around a Life-Sized, Heated, Breathing Mannequin at Ultralow Windspeeds]]></title>
<link>http://annhyg.oxfordjournals.org/cgi/content/short/men022v1?rss=1</link>
<description><![CDATA[
<p>During the past two decades, there has been considerable progress in developing particle size-selective criteria for aerosol sampling and exposure assessment that relate more realistically to actual human exposures than previously. An important aspect has been the aspiration efficiency&mdash;the &lsquo;inhalability&rsquo;&mdash;with which particles enter through the nose and mouth of aerosol-exposed individuals during breathing. Most of the reported experiments to determine inhalability have been conducted in wind tunnels with life-sized, breathing mannequins, for windspeeds from 0.5 m s<sup>&ndash;1</sup> and above. A few experiments have been reported for calm air. However, nothing has been reported for the intermediate range from 0.5 m s<sup>&ndash;1</sup> downward, and it so happens&mdash;as we now know&mdash;that this corresponds to most industrial workplaces. The research described in this paper represents a first step toward filling this knowledge gap. It focuses on identifying the features of the airflow near the mannequin at such low windspeeds that might have important influences on the nature of particle transport, and hence on inhalability, and eventually the performances of personal aerosol samplers mounted in the breathing zone. We have carried out flow visualization experiments for the realistic range of windspeeds indicated, investigating specifically the effect of the air jet released into the freestream during expiration and the effect of the upward-moving boundary layer near the body associated with the buoyancy of air in that region as a result of heat received from the warm body. We set out to identify the combinations of conditions&mdash;external windspeed, breathing mode (nose versus mouth breathing), breathing rate and body temperature&mdash;where such factors need to be taken into account. We developed an experimental system that allowed the visualization of smoke traces, providing very good observation of how the flow was modified as conditions changed. From inspection of a large number of moving pictures, we developed a matrix of regimes&mdash;categorized by windspeed and breathing rate&mdash;where the effect of the expired air is sufficient to permanently and seriously destabilize the airflow approaching the mannequin. It was found that the effect of body temperature was minimal. Such results will be important in the interpretation of current and future inhalability experiments carried out at realistic low windspeeds.</p>
]]></description>
<dc:creator><![CDATA[Schmees, D. K., Wu, Y.-H., Vincent, J. H.]]></dc:creator>
<dc:date>2008-05-22</dc:date>
<dc:identifier>info:doi/10.1093/annhyg/men022</dc:identifier>
<dc:title><![CDATA[Visualization of the Airflow around a Life-Sized, Heated, Breathing Mannequin at Ultralow Windspeeds]]></dc:title>
<dc:publisher>British Occupational Hygiene Society</dc:publisher>
<prism:publicationDate>2008-05-22</prism:publicationDate>
<prism:section>Article</prism:section>
</item>

<item rdf:about="http://annhyg.oxfordjournals.org/cgi/content/short/men021v1?rss=1">
<title><![CDATA[Exposure to Bioaerosols in Poultry Houses at Different Stages of Fattening; Use of Real-time PCR for Airborne Bacterial Quantification]]></title>
<link>http://annhyg.oxfordjournals.org/cgi/content/short/men021v1?rss=1</link>
<description><![CDATA[
<p>Previous studies have demonstrated that poultry house workers are exposed to very high levels of organic dust and consequently have an increased prevalence of adverse respiratory symptoms. However, the influence of the age of broilers on bioaerosol concentrations has not been investigated. To evaluate the evolution of bioaerosol concentration during the fattening period, bioaerosol parameters (inhalable dust, endotoxin and bacteria) were measured in 12 poultry confinement buildings in Switzerland, at three different stages of the birds&rsquo; growth; samples of air taken from within the breathing zones of individual poultry house employees as they caught the chickens ready to be transported for slaughter were also analysed. Quantitative polymerase chain reaction (Q-PCR) was used to assess the quantity of total airborne bacteria and total airborne <I>Staphylococcus</I> species. Bioaerosol levels increased significantly during the fattening period of the chickens. During the task of catching mature birds, the mean inhalable dust concentration for a worker was 26 &plusmn; 1.9 mg m<sup>&ndash;3</sup> and endotoxin concentration was 6198 &plusmn; 2.3 EU m<sup>&ndash;3</sup> air, &gt;6-fold higher than the Swiss occupational recommended value (1000 EU m<sup>&ndash;3</sup>). The mean exposure level of bird catchers to total bacteria and <I>Staphylococcus</I> species measured by Q-PCR is also very high, respectively, reaching values of 53 (&plusmn;2.6) <FONT FACE="arial,helvetica">x</FONT> 10<sup>7</sup> cells m<sup>&ndash;3</sup> air and 62 (&plusmn;1.9) <FONT FACE="arial,helvetica">x</FONT> 10<sup>6</sup> m<sup>&ndash;3</sup> air. It was concluded that in the absence of wearing protective breathing apparatus, chicken catchers in Switzerland risk exposure beyond recommended limits for all measured bioaerosol parameters. Moreover, the use of Q-PCR to estimate total and specific numbers of airborne bacteria is a promising tool for evaluating any modifications intended to improve the safety of current working practices.</p>
]]></description>
<dc:creator><![CDATA[Oppliger, A., Charriere, N., Droz, P.-O., Rinsoz, T.]]></dc:creator>
<dc:date>2008-05-22</dc:date>
<dc:identifier>info:doi/10.1093/annhyg/men021</dc:identifier>
<dc:title><![CDATA[Exposure to Bioaerosols in Poultry Houses at Different Stages of Fattening; Use of Real-time PCR for Airborne Bacterial Quantification]]></dc:title>
<dc:publisher>British Occupational Hygiene Society</dc:publisher>
<prism:publicationDate>2008-05-22</prism:publicationDate>
<prism:section>Article</prism:section>
</item>

<item rdf:about="http://annhyg.oxfordjournals.org/cgi/content/short/men019v1?rss=1">
<title><![CDATA[Filter Performance of N99 and N95 Facepiece Respirators Against Viruses and Ultrafine Particles]]></title>
<link>http://annhyg.oxfordjournals.org/cgi/content/short/men019v1?rss=1</link>
<description><![CDATA[
<p>The performance of three filtering facepiece respirators (two models of N99 and one N95) challenged with an inert aerosol (NaCl) and three virus aerosols (enterobacteriophages MS2 and T4 and <I>Bacillus subtilis</I> phage)&mdash;all with significant ultrafine components&mdash;was examined using a manikin-based protocol with respirators sealed on manikins. Three inhalation flow rates, 30, 85, and 150 l min<sup>&ndash;1</sup>, were tested. The filter penetration and the quality factor were determined. Between-respirator and within-respirator comparisons of penetration values were performed. At the most penetrating particle size (MPPS), &gt;3% of MS2 virions penetrated through filters of both N99 models at an inhalation flow rate of 85 l min<sup>&ndash;1</sup>. Inhalation airflow had a significant effect upon particle penetration through the tested respirator filters. The filter quality factor was found suitable for making relative performance comparisons. The MPPS for challenge aerosols was &lt;0.1 &micro;m in electrical mobility diameter for all tested respirators. Mean particle penetration (by count) was significantly increased when the size fraction of &lt;0.1 &micro;m was included as compared to particles &gt;0.1 &micro;m. The filtration performance of the N95 respirator approached that of the two models of N99 over the range of particle sizes tested (~0.02 to 0.5 &micro;m). Filter penetration of the tested biological aerosols did not exceed that of inert NaCl aerosol. The results suggest that inert NaCl aerosols may generally be appropriate for modeling filter penetration of similarly sized virions.</p>
]]></description>
<dc:creator><![CDATA[Eninger, R. M., Honda, T., Adhikari, A., Heinonen-Tanski, H., Reponen, T., Grinshpun, S. A.]]></dc:creator>
<dc:date>2008-05-13</dc:date>
<dc:identifier>info:doi/10.1093/annhyg/men019</dc:identifier>
<dc:title><![CDATA[Filter Performance of N99 and N95 Facepiece Respirators Against Viruses and Ultrafine Particles]]></dc:title>
<dc:publisher>British Occupational Hygiene Society</dc:publisher>
<prism:publicationDate>2008-05-13</prism:publicationDate>
<prism:section>Article</prism:section>
</item>

<item rdf:about="http://annhyg.oxfordjournals.org/cgi/content/short/men017v1?rss=1">
<title><![CDATA[Size-Separated Sampling and Analysis of Isocyanates in Workplace Aerosols. Part I. Denuder--Cascade Impactor Sampler]]></title>
<link>http://annhyg.oxfordjournals.org/cgi/content/short/men017v1?rss=1</link>
<description><![CDATA[
<p>Isocyanates in the workplace atmosphere are typically present both in gas and particle phase. The health effects of exposure to isocyanates in gas phase and different particle size fractions are likely to be different due to their ability to reach different parts in the respiratory system. To reveal more details regarding the exposure to isocyanate aerosols, a denuder&ndash;impactor (DI) sampler for airborne isocyanates was designed. The sampler consists of a channel-plate denuder for collection of gaseous isocyanates, in series with three-cascade impactor stages with cut-off diameters (d<SUB>50</SUB>) of 2.5, 1.0 and 0.5 &micro;m. An end filter was connected in series after the impactor for collection of particles smaller than 0.5 &micro;m. The denuder, impactor plates and the end filter were impregnated with a mixture of di-<I>n</I>-butylamine (DBA) and acetic acid for derivatization of the isocyanates. During sampling, the reagent on the impactor plates and the end filter is continuously refreshed, due to the DBA release from the impregnated denuder plates. This secures efficient derivatization of all isocyanate particles. The airflow through the sampler was 5 l min<sup>&ndash;1</sup>. After sampling, the samples containing the different size fractions were analyzed using liquid chromatography-mass spectrometry (LC-MS)/MS. The DBA impregnation was stable in the sampler for at least 1 week. After sampling, the DBA derivatives were stable for at least 3 weeks. Air sampling was performed in a test chamber (300 l). Isocyanate aerosols studied were thermal degradation products of different polyurethane polymers, spraying of isocyanate coating compounds and pure gas-phase isocyanates. Sampling with impinger flasks, containing DBA in toluene, with a glass fiber filter in series was used as a reference method. The DI sampler showed good compliance with the reference method, regarding total air levels. For the different aerosols studied, vast differences were revealed in the distribution of isocyanate in gas and different particle size fractions. The opportunity to obtain detailed information regarding the distribution of isocyanates in aerosols in addition to the total air levels make the DI sampler a valuable tool for studies of possible health effects in the different parts of the airways.</p>
]]></description>
<dc:creator><![CDATA[Dahlin, J., Spanne, M., Karlsson, D., Dalene, M., Skarping, G.]]></dc:creator>
<dc:date>2008-05-05</dc:date>
<dc:identifier>info:doi/10.1093/annhyg/men017</dc:identifier>
<dc:title><![CDATA[Size-Separated Sampling and Analysis of Isocyanates in Workplace Aerosols. Part I. Denuder--Cascade Impactor Sampler]]></dc:title>
<dc:publisher>British Occupational Hygiene Society</dc:publisher>
<prism:publicationDate>2008-05-05</prism:publicationDate>
<prism:section>Article</prism:section>
</item>

<item rdf:about="http://annhyg.oxfordjournals.org/cgi/content/short/men018v1?rss=1">
<title><![CDATA[Size-Separated Sampling and Analysis of Isocyanates in Workplace Aerosols--Part II: Aging of Aerosols from Thermal Degradation of Polyurethane]]></title>
<link>http://annhyg.oxfordjournals.org/cgi/content/short/men018v1?rss=1</link>
<description><![CDATA[
<p>A new type of isocyanate sampler has been used to investigate aging aerosols generated during thermal degradation of polyurethane (PUR). The sampler consists of a denuder connected in series with a three-stage cascade impactor and a filter. The denuder collects gas-phase isocyanates. The three impactor stages had cut-off diameters (<I>d</I><SUB>50</SUB>) of 2.5, 1.0 and 0.5 &micro;m, respectively. The end filter collects particles &lt;0.5 &micro;m. For derivatization of isocyanates in the sampler, di-n-butylamine mixed with an equimolar amount of acetic acid was used for impregnation of the sampler stages. Consecutive sampling using three denuder&ndash;impactor samplers was performed in a test chamber, with a total sampling time of 9 min. Analysis of air samples was performed using liquid chromatography-mass spectrometry (LC-MS)/MS. Particle size measurements were performed using a scanning mobility particle sizer (SMPS). A time-dependent behavior was observed for aromatic diisocyanates during aging of the aerosol. Thermal degradation of different PUR materials showed different distribution of isocyanates between gas and particles. Aromatic diisocyanates (toluene diisocyanate (TDI) and methylene diphenyl diisocyanate) were initially in gas phase and associated to very small particles. After a few minutes most of these isocyanates were associated with particles &lt;1 &micro;m. Monoisocyanates and hexamethylene diisocyanate (HDI) were not found to be associated with particles.</p>
]]></description>
<dc:creator><![CDATA[Dahlin, J., Spanne, M., Dalene, M., Karlsson, D., Skarping, G.]]></dc:creator>
<dc:date>2008-04-30</dc:date>
<dc:identifier>info:doi/10.1093/annhyg/men018</dc:identifier>
<dc:title><![CDATA[Size-Separated Sampling and Analysis of Isocyanates in Workplace Aerosols--Part II: Aging of Aerosols from Thermal Degradation of Polyurethane]]></dc:title>
<dc:publisher>British Occupational Hygiene Society</dc:publisher>
<prism:publicationDate>2008-04-30</prism:publicationDate>
<prism:section>Article</prism:section>
</item>

</rdf:RDF>