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<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>
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  <rdf:li rdf:resource="http://annhyg.oxfordjournals.org/cgi/content/short/mep058v1?rss=1" />
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<item rdf:about="http://annhyg.oxfordjournals.org/cgi/content/short/mep072v2?rss=1">
<title><![CDATA[Proposed British-Dutch Guidance on Measuring Compliance with Occupational Exposure Limits]]></title>
<link>http://annhyg.oxfordjournals.org/cgi/content/short/mep072v2?rss=1</link>
<description><![CDATA[]]></description>
<dc:creator><![CDATA[Ogden, T. L.]]></dc:creator>
<dc:date>Tue, 03 Nov 2009 14:47:49 PST</dc:date>
<dc:identifier>info:doi/10.1093/annhyg/mep072</dc:identifier>
<dc:title><![CDATA[Proposed British-Dutch Guidance on Measuring Compliance with Occupational Exposure Limits]]></dc:title>
<dc:publisher>British Occupational Hygiene Society</dc:publisher>
<prism:publicationDate>2009-11-03</prism:publicationDate>
<prism:section>Editorials</prism:section>
</item>

<item rdf:about="http://annhyg.oxfordjournals.org/cgi/content/short/mep070v2?rss=1">
<title><![CDATA[Evaluation of Five Decontamination Methods for Filtering Facepiece Respirators]]></title>
<link>http://annhyg.oxfordjournals.org/cgi/content/short/mep070v2?rss=1</link>
<description><![CDATA[
<p>Concerns have been raised regarding the availability of National Institute for Occupational Safety and Health (NIOSH)-certified N95 filtering facepiece respirators (FFRs) during an influenza pandemic. One possible strategy to mitigate a respirator shortage is to reuse FFRs following a biological decontamination process to render infectious material on the FFR inactive. However, little data exist on the effects of decontamination methods on respirator integrity and performance. This study evaluated five decontamination methods [ultraviolet germicidal irradiation (UVGI), ethylene oxide, vaporized hydrogen peroxide (VHP), microwave oven irradiation, and bleach] using nine models of NIOSH-certified respirators (three models each of N95 FFRs, surgical N95 respirators, and P100 FFRs) to determine which methods should be considered for future research studies. Following treatment by each decontamination method, the FFRs were evaluated for changes in physical appearance, odor, and laboratory performance (filter aerosol penetration and filter airflow resistance). Additional experiments (dry heat laboratory oven exposures, off-gassing, and FFR hydrophobicity) were subsequently conducted to better understand material properties and possible health risks to the respirator user following decontamination. However, this study did not assess the efficiency of the decontamination methods to inactivate viable microorganisms. Microwave oven irradiation melted samples from two FFR models. The remainder of the FFR samples that had been decontaminated had expected levels of filter aerosol penetration and filter airflow resistance. The scent of bleach remained noticeable following overnight drying and low levels of chlorine gas were found to off-gas from bleach-decontaminated FFRs when rehydrated with deionized water. UVGI, ethylene oxide (EtO), and VHP were found to be the most promising decontamination methods; however, concerns remain about the throughput capabilities for EtO and VHP. Further research is needed before any specific decontamination methods can be recommended.</p>
]]></description>
<dc:creator><![CDATA[Viscusi, D. J., Bergman, M. S., Eimer, B. C., Shaffer, R. E.]]></dc:creator>
<dc:date>Tue, 03 Nov 2009 14:47:48 PST</dc:date>
<dc:identifier>info:doi/10.1093/annhyg/mep070</dc:identifier>
<dc:title><![CDATA[Evaluation of Five Decontamination Methods for Filtering Facepiece Respirators]]></dc:title>
<dc:publisher>British Occupational Hygiene Society</dc:publisher>
<prism:publicationDate>2009-11-03</prism:publicationDate>
<prism:section>Article</prism:section>
</item>

<item rdf:about="http://annhyg.oxfordjournals.org/cgi/content/short/mep056v2?rss=1">
<title><![CDATA[Airborne Asbestos Concentrations Associated with Heavy Equipment Brake Removal]]></title>
<link>http://annhyg.oxfordjournals.org/cgi/content/short/mep056v2?rss=1</link>
<description><![CDATA[
<p>Asbestos-containing brake linings were used in heavy-duty construction equipment such as tractors, backhoes, and bulldozers prior to the 1980s. While several published studies have evaluated exposures to mechanics during brake repair work, most have focused on automobiles and light trucks, not on heavy agricultural or construction vehicles. The purpose of this study is to characterize the airborne concentration of asbestos to workers and bystanders from brake wear debris during brake removal from 12 loader/backhoes and tractors manufactured between 1960 and 1980. Asbestos content in brake lining (average 20% chrysotile by polarized light microscopy) and brake wear debris [average 0.49% chrysotile by transmission electron microscopy (TEM)] was also quantified. Breathing zone samples on the lapel of mechanics (<I>n</I> = 44) and area samples at bystander (<I>n</I> = 34), remote (<I>n</I> = 22), and ambient (<I>n</I> = 12) locations were collected during 12 brake changes and analyzed using phase contrast microscopy (PCM) [National Institute for Occupational Safety and Health (NIOSH) 7400] and TEM (NIOSH 7402). In addition, the fiber distribution by size and morphology was evaluated according to the International Organization for Standardization method for asbestos. Applying the ratio of asbestos fibers:total fibers (including non-asbestos) as determined by TEM to the PCM results, the average airborne chrysotile concentrations (PCM equivalent) were 0.024 f/cc for the mechanic and 0.009 f/cc for persons standing 1.2&ndash;3.1 m from the activity during the period of exposure (~0.5 to 1 h). Considering the time involved in the activity, and assuming three brake jobs per shift, these results would convert to an average 8-h time-weighted average of 0.009 f/cc for a mechanic and 0.006 f/cc for a bystander. The results indicate that (i) the airborne concentrations for worker and bystander samples were significantly less than the current occupational exposure limit of 0.1 f/cc; (ii) ~2% of respirable fibers were &gt;20 &micro;m in length; and (iii) ~95% of chrysotile in the brake linings degraded in the friction process. The industrial hygiene data presented here should be useful for conducting retrospective and current exposure assessments of individuals, as well as hazard assessments of work activities that involve repairing and replacing asbestos-containing brakes in heavy construction equipment.</p>
]]></description>
<dc:creator><![CDATA[Madl, A. K., Gaffney, S. H., Balzer, J. L., Paustenbach, D. J.]]></dc:creator>
<dc:date>Mon, 12 Oct 2009 06:15:12 PDT</dc:date>
<dc:identifier>info:doi/10.1093/annhyg/mep056</dc:identifier>
<dc:title><![CDATA[Airborne Asbestos Concentrations Associated with Heavy Equipment Brake Removal]]></dc:title>
<dc:publisher>British Occupational Hygiene Society</dc:publisher>
<prism:publicationDate>2009-10-12</prism:publicationDate>
<prism:section>Article</prism:section>
</item>

<item rdf:about="http://annhyg.oxfordjournals.org/cgi/content/short/mep066v1?rss=1">
<title><![CDATA[Comparison of Direct and Indirect Methods of Measuring Airborne Chrysotile Fibre Concentration]]></title>
<link>http://annhyg.oxfordjournals.org/cgi/content/short/mep066v1?rss=1</link>
<description><![CDATA[
<p>Transmission electron microscopy observations most frequently form a basis for estimating asbestos fibre concentration in the environment and in buildings with asbestos-containing materials. Sampled fibres can be transferred to microscope grids by applying either a direct [ISO (1995) Draft International ISO/DIS 10312. Ambient air. Determination of asbestos fibres. Direct transfer transmission electron microscopy procedure. Geneva, Switzerland: International Standardization Organization] or an indirect [AFNOR (1996) D&eacute;termination de la concentration en fibres d'amiante par microscopie &eacute;lectronique &agrave; transmission&mdash;M&eacute;thode indirecte. Cedex, France: AFNOR, p. 42; ISO (1997) Draft International ISO/DIS 13794. Ambient air. Determination of asbestos fibres. Indirect-transfer transmission electron microscopy procedure. Geneva, Switzerland: International Standardization Organization] method. In the latter case, ISO Standard 13794 recommends filtering calcination residues either on a polycarbonate (PC) filter (PC indirect method) or on a cellulose ester (CE) membrane (CE indirect method). The PC indirect method requires that fibres deposited on a PC filter be covered by a carbon layer, whereas in the CE indirect method, the CE membrane has to be directly processed using a method described in ISO Standard 10312. The purpose of this study was to compare results obtained using, on the one hand, direct preparation methods and, on the other hand, PC indirect or CE indirect methods, for counting asbestos fibres deposited on filters as a result of liquid filtration or air sampling. In direct method-based preparation, we observed that an etching time of 6&ndash;14 min does not affect the measured densities, except for fibres &lt;1 &micro;m deposited by liquid filtration. Moreover, in all cases, the direct method gives higher densities than the PC indirect method because of possible fibre disappearance when using the carbon evaporator implemented in the PC indirect method. The CE membrane used for sample preparation in the CE indirect method is collapsed prior to passing it through the carbon evaporator, so the fibres are less likely to disappear at this stage. We then note that the resulting fibre densities for chrysotile-loaded filters prepared using the direct method are close to those obtained with filters prepared using the CE indirect method. Our study therefore shows that, under the implemented experimental conditions, the PC and CE indirect preparation methods described in ISO Standard 13794 are not equivalent.</p>
]]></description>
<dc:creator><![CDATA[Eypert-Blaison, C., Veissiere, S., Rastoix, O., Kauffer, E.]]></dc:creator>
<dc:date>Wed, 07 Oct 2009 07:38:15 PDT</dc:date>
<dc:identifier>info:doi/10.1093/annhyg/mep066</dc:identifier>
<dc:title><![CDATA[Comparison of Direct and Indirect Methods of Measuring Airborne Chrysotile Fibre Concentration]]></dc:title>
<dc:publisher>British Occupational Hygiene Society</dc:publisher>
<prism:publicationDate>2009-10-07</prism:publicationDate>
<prism:section>Article</prism:section>
</item>

<item rdf:about="http://annhyg.oxfordjournals.org/cgi/content/short/mep071v1?rss=1">
<title><![CDATA[Effects of Headspace and Oxygen Level on Off-gas Emissions from Wood Pellets in Storage]]></title>
<link>http://annhyg.oxfordjournals.org/cgi/content/short/mep071v1?rss=1</link>
<description><![CDATA[
<p>Few papers have been published in the open literature on the emissions from biomass fuels, including wood pellets, during the storage and transportation and their potential health impacts. The purpose of this study is to provide data on the concentrations, emission factors, and emission rate factors of CO<SUB>2</SUB>, CO, and CH<SUB>4</SUB> from wood pellets stored with different headspace to container volume ratios with different initial oxygen levels, in order to develop methods to reduce the toxic off-gas emissions and accumulation in storage spaces. Metal containers (45 l, 305 mm diameter by 610 mm long) were used to study the effect of headspace and oxygen levels on the off-gas emissions from wood pellets. Concentrations of CO<SUB>2</SUB>, CO, and CH<SUB>4</SUB> in the headspace were measured using a gas chromatograph as a function of storage time. The results showed that the ratio of the headspace ratios and initial oxygen levels in the storage space significantly affected the off-gas emissions from wood pellets stored in a sealed container. Higher peak emission factors and higher emission rates are associated with higher headspace ratios. Lower emissions of CO<SUB>2</SUB> and CO were generated at room temperature under lower oxygen levels, whereas CH<SUB>4</SUB> emission is insensitive to the oxygen level. Replacing oxygen with inert gases in the storage space is thus a potentially effective method to reduce the biomass degradation and toxic off-gas emissions. The proper ventilation of the storage space can also be used to maintain a high oxygen level and low concentrations of toxic off-gassing compounds in the storage space, which is especially useful during the loading and unloading operations to control the hazards associated with the storage and transportation of wood pellets.</p>
]]></description>
<dc:creator><![CDATA[Kuang, X., Shankar, T. J., Sokhansanj, S., Lim, C. J., Bi, X. T., Melin, S.]]></dc:creator>
<dc:date>Sun, 04 Oct 2009 19:24:36 PDT</dc:date>
<dc:identifier>info:doi/10.1093/annhyg/mep071</dc:identifier>
<dc:title><![CDATA[Effects of Headspace and Oxygen Level on Off-gas Emissions from Wood Pellets in Storage]]></dc:title>
<dc:publisher>British Occupational Hygiene Society</dc:publisher>
<prism:publicationDate>2009-10-04</prism:publicationDate>
<prism:section>Article</prism:section>
</item>

<item rdf:about="http://annhyg.oxfordjournals.org/cgi/content/short/mep069v1?rss=1">
<title><![CDATA[Quantitative Plasma Biomarker Analysis in HDI Exposure Assessment]]></title>
<link>http://annhyg.oxfordjournals.org/cgi/content/short/mep069v1?rss=1</link>
<description><![CDATA[
<p>Quantification of amines in biological samples is important for evaluating occupational exposure to diisocyanates. In this study, we describe the quantification of 1,6-hexamethylene diamine (HDA) levels in hydrolyzed plasma of 46 spray painters applying 1,6-hexamethylene diisocyanate (HDI)-containing paint in vehicle repair shops collected during repeated visits to their workplace and their relationship with dermal and inhalation exposure to HDI monomer. HDA was detected in 76% of plasma samples, as heptafluorobutyryl derivatives, and the range of HDA concentrations was &le;0.02&ndash;0.92 &micro;g l<sup>&ndash;1</sup>. After log-transformation of the data, the correlation between plasma HDA levels and HDI inhalation exposure measured on the same workday was low (<I>N</I> = 108, <I>r</I> = 0.22, <I>P</I> = 0.026) compared with the correlation between plasma HDA levels and inhalation exposure occurring ~20 to 60 days before blood collection (<I>N</I> = 29, <I>r</I> = 0.57, <I>P</I> = 0.0014). The correlation between plasma HDA levels and HDI dermal exposure measured on the same workday, although statistically significant, was low (<I>N</I> = 108, <I>r</I> = 0.22, <I>P</I> = 0.040) while the correlation between HDA and dermal exposure occurring ~20 to 60 days before blood collection was slightly improved (<I>N</I> = 29, <I>r</I> = 0.36, <I>P</I> = 0.053). We evaluated various workplace factors and controls (i.e. location, personal protective equipment use and paint booth type) as modifiers of plasma HDA levels. Workers using a downdraft-ventilated booth had significantly lower plasma HDA levels relative to semi-downdraft and crossdraft booth types (<I>P</I> = 0.0108); this trend was comparable to HDI inhalation and dermal exposure levels stratified by booth type. These findings indicate that HDA concentration in hydrolyzed plasma may be used as a biomarker of cumulative inhalation and dermal exposure to HDI and for investigating the effectiveness of exposure controls in the workplace.</p>
]]></description>
<dc:creator><![CDATA[Flack, S. L., Fent, K. W., Trelles Gaines, L. G., Thomasen, J. M., Whittaker, S., Ball, L. M., Nylander-French, L. A.]]></dc:creator>
<dc:date>Sun, 04 Oct 2009 19:24:30 PDT</dc:date>
<dc:identifier>info:doi/10.1093/annhyg/mep069</dc:identifier>
<dc:title><![CDATA[Quantitative Plasma Biomarker Analysis in HDI Exposure Assessment]]></dc:title>
<dc:publisher>British Occupational Hygiene Society</dc:publisher>
<prism:publicationDate>2009-10-04</prism:publicationDate>
<prism:section>Article</prism:section>
</item>

<item rdf:about="http://annhyg.oxfordjournals.org/cgi/content/short/mep067v1?rss=1">
<title><![CDATA[Dermal and Inhalation Exposure to Methylene Bisphenyl Isocyanate (MDI) in Iron Foundry Workers]]></title>
<link>http://annhyg.oxfordjournals.org/cgi/content/short/mep067v1?rss=1</link>
<description><![CDATA[
<p>Diisocyanates are a group of chemically reactive agents, which are used in the production of coatings, adhesives, polyurethane foams, and parts for the automotive industry and as curing agents for cores in the foundry industry. Dermal and inhalation exposure to methylene bisphenyl isocyanate (MDI) is associated with respiratory sensitization and occupational asthma. However, limited research has been performed on the quantitative evaluation of dermal and inhalation exposure to MDI in occupationally exposed workers. The objective of this research was to quantify dermal and inhalation exposure levels in iron foundry workers. Workers involved in mechanized moulding and mechanized production of cores were monitored: 12 core makers, 2 core-sand preparers, and 5 core installers. Personal breathing-zone levels of MDI were measured using impregnated filter sampling. Dermal exposure to MDI was measured using a tape-strip technique. Three or five consecutive tape-strip samples were collected from five exposed skin areas (right and left forefingers, left and right wrists, and forehead). The average personal air concentration was 0.55 &micro;g m<sup>&ndash;3</sup>, 50-fold lower than the Swedish occupational exposure limit of 30 &micro;g m<sup>&ndash;3</sup>. The core makers had an average exposure of 0.77 &micro;g m<sup>&ndash;3</sup>, which was not significantly different from core installers&rsquo; and core-sand preparers&rsquo; average exposure of 0.16 &micro;g m<sup>&ndash;3</sup> (<I>P</I> = 0.059). Three core makers had a 10-fold higher inhalation exposure than the other core makers. The core makers&rsquo; mean dermal exposure at different skin sites varied from 0.13 to 0.34 &micro;g while the two other groups&rsquo; exposure ranged from 0.006 to 0.062 &micro;g. No significant difference was observed in the MDI levels between the skin sites in a pairwise comparison, except for left forefinger compared to left and right wrist (<I>P</I> &lt; 0.05). In addition, quantifiable but decreasing levels of MDI were observed in the consecutive tape strip per site indicating MDI penetration into the skin. This study indicates that exposure to MDI can be quantified on workers&rsquo; skin even if air levels are close to unquantifiable. Thus, the potential for uncured MDI to deposit on and penetrate into the skin is demonstrated. Therefore, dermal exposure along with inhalation exposure to MDI should be measured in the occupational settings where MDI is present in order to shed light on their roles in the development of occupational isocyanate asthma.</p>
]]></description>
<dc:creator><![CDATA[Liljelind, I., Norberg, C., Egelrud, L., Westberg, H., Eriksson, K., Nylander-French, L. A.]]></dc:creator>
<dc:date>Sat, 26 Sep 2009 00:04:06 PDT</dc:date>
<dc:identifier>info:doi/10.1093/annhyg/mep067</dc:identifier>
<dc:title><![CDATA[Dermal and Inhalation Exposure to Methylene Bisphenyl Isocyanate (MDI) in Iron Foundry Workers]]></dc:title>
<dc:publisher>British Occupational Hygiene Society</dc:publisher>
<prism:publicationDate>2009-09-26</prism:publicationDate>
<prism:section>Article</prism:section>
</item>

<item rdf:about="http://annhyg.oxfordjournals.org/cgi/content/short/mep068v1?rss=1">
<title><![CDATA[Characterization and Assessment of Dermal and Inhalable Nickel Exposures in Nickel Production and Primary User Industries]]></title>
<link>http://annhyg.oxfordjournals.org/cgi/content/short/mep068v1?rss=1</link>
<description><![CDATA[
<p>The aim of this study was to measure the levels of nickel in the skin contaminant layer of workers involved in specific processes and tasks within the primary nickel production and primary nickel user industries. Dermal exposure samples were collected using moist wipes to recover surface contamination from defined areas of skin. These were analysed for soluble and insoluble nickel species. Personal samples of inhalable dust were also collected to determine the corresponding inhalable nickel exposures. The air samples were analysed for total inhalable dust and then for soluble, sulfidic, metallic, and oxidic nickel species. The workplace surveys were carried out in five different workplaces, including three nickel refineries, a stainless steel plant, and a powder metallurgy plant, all of which were located in Europe. Nickel refinery workers involved with electrolytic nickel recovery processes had soluble dermal nickel exposure of 0.34 &micro;g cm<sup>&ndash;2</sup> [geometric mean (GM)] to the hands and forearms. The GM of soluble dermal nickel exposure for workers involved in packing nickel salts (nickel chloride hexahydrate, nickel sulphate hexahydrate, and nickel hydroxycarbonate) was 0.61 &micro;g cm<sup>&ndash;2</sup>. Refinery workers involved in packing nickel metal powders and end-user powder operatives in magnet production had the highest dermal exposure (GM = 2.59 &micro;g cm<sup>&ndash;2</sup> soluble nickel). The hands, forearms, face, and neck of these workers all received greater dermal nickel exposure compared with the other jobs included in this study. The soluble nickel dermal exposures for stainless steel production workers were at or slightly above the limit of detection (0.02 &micro;g cm<sup>&ndash;2</sup> soluble nickel). The highest inhalable nickel concentrations were observed for the workers involved in nickel powder packing (GM = 0.77 mg m<sup>&ndash;3</sup>), although the soluble component comprised only 2% of the total nickel content. The highest airborne soluble nickel exposures were associated with refineries using electrolytic processes for nickel recovery (GM = 0.04 mg m<sup>&ndash;3</sup> total nickel, containing 82% soluble nickel) and those jobs involving contact with soluble nickel compounds (GM = 0.02 mg m<sup>&ndash;3</sup> total nickel content, containing 76% soluble nickel). The stainless steel workers were exposed to low concentrations of relatively insoluble airborne nickel species (GM = 0.03 mg m<sup>&ndash;3</sup> total nickel, containing 1% soluble nickel). A statistically significant correlation was observed between dermal exposures for all anatomical areas across all tasks. In addition, the dermal and inhalable (total) nickel exposures were similarly associated. Overall, dermal exposures to nickel, nickel compounds, and nickel alloys were relatively low. However, exposures were highly variable, which can be explained by the inconsistent use of personal protective equipment, varying working practices, and different standards of automation and engineering controls within each exposure category.</p>
]]></description>
<dc:creator><![CDATA[Hughson, G. W., Galea, K. S., Heim, K. E.]]></dc:creator>
<dc:date>Wed, 16 Sep 2009 07:05:53 PDT</dc:date>
<dc:identifier>info:doi/10.1093/annhyg/mep068</dc:identifier>
<dc:title><![CDATA[Characterization and Assessment of Dermal and Inhalable Nickel Exposures in Nickel Production and Primary User Industries]]></dc:title>
<dc:publisher>British Occupational Hygiene Society</dc:publisher>
<prism:publicationDate>2009-09-16</prism:publicationDate>
<prism:section>Article</prism:section>
</item>

<item rdf:about="http://annhyg.oxfordjournals.org/cgi/content/short/mep055v2?rss=1">
<title><![CDATA[Oxygen Depletion and Formation of Toxic Gases following Sea Transportation of Logs and Wood Chips]]></title>
<link>http://annhyg.oxfordjournals.org/cgi/content/short/mep055v2?rss=1</link>
<description><![CDATA[
<p>Several recent accidents with fatal outcomes occurring during discharge of logs and wood chips from ships in Swedish ports indicate the need to better understand the atmospheric conditions in holds and connecting stairways. The principal aim of the present study was to assess the air levels of oxygen and toxic gases in confined spaces following sea transportation of logs and wood chips. The focus of the study was the conditions in the stairways, as this was the location of the reported accidents. Forty-one shipments of logs (pulpwood) and wood chips carried by 10 different ships were investigated before discharge in ports in northern Sweden. A full year was covered to accommodate variations due to seasonal temperature changes. The time from completion of loading to discharge was estimated to be 37&ndash;66 h (mean 46 h). Air samples were collected in the undisturbed air of altogether 76 stairways before the hatch covers were removed. The oxygen level was measured on-site by handheld direct-reading multi-gas monitors. On 16 of the shipments, air samples were additionally collected in Tedlar&reg; bags for later analysis for carbon dioxide, carbon monoxide, and hydrocarbons by fourier transform infrared spectroscopy. The mean oxygen level was 10% (<I>n</I> = 76) but in 17% of the samples the oxygen level was 0%. The oxygen depletion was less pronounced during the cold season. The mean CO2 and CO levels were 7.5% (<I>n</I> = 26) and 46 p.p.m. (<I>n</I> = 28), respectively. More than 90% of the hydrocarbons were explained by monoterpenes, mainly -pinene (mean 41 p.p.m., (<I>n</I> = 26). In conclusion, the measurements show that transport of logs and wood chips in confined spaces may result in rapid and severe oxygen depletion and CO<SUB>2</SUB> formation. Thus, apparently harmless cargoes may create potentially life-threatening conditions. The oxygen depletion and CO<SUB>2</SUB> formation are seemingly primarily caused by microbiological activity, in contrast to the oxidative processes with higher CO formation that predominate in cargoes of wood pellets. Improved technical and organizational measures are considered necessary to prevent future accidents. Recommendations given regarding safe entry procedures and technical preventive methods may also apply to other oxygen-depleting products.</p>
]]></description>
<dc:creator><![CDATA[Svedberg, U., Petrini, C., Johanson, G.]]></dc:creator>
<dc:date>Tue, 15 Sep 2009 03:56:07 PDT</dc:date>
<dc:identifier>info:doi/10.1093/annhyg/mep055</dc:identifier>
<dc:title><![CDATA[Oxygen Depletion and Formation of Toxic Gases following Sea Transportation of Logs and Wood Chips]]></dc:title>
<dc:publisher>British Occupational Hygiene Society</dc:publisher>
<prism:publicationDate>2009-09-15</prism:publicationDate>
<prism:section>Article</prism:section>
</item>

<item rdf:about="http://annhyg.oxfordjournals.org/cgi/content/short/mep061v1?rss=1">
<title><![CDATA[Particle Emission and Exposure during Nanoparticle Synthesis in Research Laboratories]]></title>
<link>http://annhyg.oxfordjournals.org/cgi/content/short/mep061v1?rss=1</link>
<description><![CDATA[
<p>Real-time size, mass and number particle concentrations, and emission rates in university laboratories producing nanoparticles by scalable flame spray pyrolysis are quantified. Measurements were conducted in four laboratories using various technological set-ups and during production of particles of a range of compositions with differing physical&ndash;chemical properties, from NaCl salt, BiPO<SUB>4</SUB>, CaSO<SUB>4</SUB>, Bi<SUB>2</SUB>O<SUB>3</SUB>, insoluble TiO<SUB>2</SUB>, SiO<SUB>2</SUB>, and WO<SUB>3</SUB> to composites such as Cu/ZnO, Cu/SiO<SUB>2</SUB>, Cu/ZrO<SUB>2</SUB>, Ta<SUB>2</SUB>O<SUB>5</SUB>/SiO<SUB>2</SUB>, and Pt/Ba/Al<SUB>2</SUB>O<SUB>3</SUB>. Production time ranged from 0.25 to 400 min and yields from 0.33 to 183 g. Temporal and spatial analyses of the particle concentrations were performed indicating that elevated number concentrations in the workplace can occur. Airborne submicron number concentrations increased from background levels of 2100 up to 106 000 cm<sup>&ndash;3</sup> during production, while the mass concentration ranged from a background of 0.009 to 0.463 mg m<sup>&ndash;3</sup>. Maximum particle number emission rates amounted to 1.17 <FONT FACE="arial,helvetica">x</FONT> 10<sup>12</sup> min<sup>&ndash;1</sup>. The size distributions displayed concentration peaks mainly between 110 and 180 nm. However, changes in the operating conditions and the production of certain nanoparticles resulted in concentration peaks in the nanoparticle size range &lt;100 nm. The effectiveness and limitations of current technology in assessing researchers&rsquo; exposure to nanoparticles during production are examined, and further measures for workers&rsquo; protection are proposed.</p>
]]></description>
<dc:creator><![CDATA[Demou, E., Stark, W. J., Hellweg, S.]]></dc:creator>
<dc:date>Mon, 24 Aug 2009 03:01:43 PDT</dc:date>
<dc:identifier>info:doi/10.1093/annhyg/mep061</dc:identifier>
<dc:title><![CDATA[Particle Emission and Exposure during Nanoparticle Synthesis in Research Laboratories]]></dc:title>
<dc:publisher>British Occupational Hygiene Society</dc:publisher>
<prism:publicationDate>2009-08-24</prism:publicationDate>
<prism:section>Article</prism:section>
</item>

<item rdf:about="http://annhyg.oxfordjournals.org/cgi/content/short/mep062v1?rss=1">
<title><![CDATA[Large Particle Penetration through N95 Respirator Filters and Facepiece Leaks with Cyclic Flow]]></title>
<link>http://annhyg.oxfordjournals.org/cgi/content/short/mep062v1?rss=1</link>
<description><![CDATA[
<p>The aim of this study was to investigate respirator filter and faceseal penetration of particles representing bacterial and fungal spore size ranges (0.7&ndash;4 &micro;m). First, field experiments were conducted to determine workplace protection factors (WPFs) for a typical N95 filtering facepiece respirator (FFR). These data (average WPF = 515) were then used to position the FFR on a manikin to simulate realistic donning conditions for laboratory experiments. Filter penetration was also measured after the FFR was fully sealed on the manikin face. This value was deducted from the total penetration (obtained from tests with the partially sealed FFR) to determine the faceseal penetration. All manikin experiments were repeated using three sinusoidal breathing flow patterns corresponding to mean inspiratory flow rates of 15, 30, and 85 l min<sup>&ndash;1</sup>. The faceseal penetration varied from 0.1 to 1.1% and decreased with increasing particle size (<I>P</I> &lt; 0.001) and breathing rate (<I>P</I> &lt; 0.001). The fractions of aerosols penetrating through the faceseal leakage varied from 0.66 to 0.94. In conclusion, even for a well-fitting FFR respirator, most particle penetration occurs through faceseal leakage, which varies with breathing flow rate and particle size.</p>
]]></description>
<dc:creator><![CDATA[Cho, K. J., Reponen, T., Mckay, R., Shukla, R., Haruta, H., Sekar, P., Grinshpun, S. A.]]></dc:creator>
<dc:date>Fri, 21 Aug 2009 05:21:27 PDT</dc:date>
<dc:identifier>info:doi/10.1093/annhyg/mep062</dc:identifier>
<dc:title><![CDATA[Large Particle Penetration through N95 Respirator Filters and Facepiece Leaks with Cyclic Flow]]></dc:title>
<dc:publisher>British Occupational Hygiene Society</dc:publisher>
<prism:publicationDate>2009-08-21</prism:publicationDate>
<prism:section>Article</prism:section>
</item>

<item rdf:about="http://annhyg.oxfordjournals.org/cgi/content/short/mep060v1?rss=1">
<title><![CDATA[Direct Detection of Salmonella Cells in the Air of Livestock Stables by Real-Time PCR]]></title>
<link>http://annhyg.oxfordjournals.org/cgi/content/short/mep060v1?rss=1</link>
<description><![CDATA[
<p>A SYBR<sup>&reg;</sup> Green real-time quantitative polymerase chain reaction (qPCR) assay for specific detection and quantification of airborne <I>Salmonella</I> cells in livestock housings is presented. A set of specific primers was tested and validated for specific detection and quantification of <I>Salmonella</I>-specific <I>invA</I> genes of DNA extracted from bioaerosol samples. Application of the method to poultry house bioaerosol samples showed concentrations ranging from 2.2 <FONT FACE="arial,helvetica">x</FONT> 10<sup>1</sup> to 3 <FONT FACE="arial,helvetica">x</FONT> 10<sup>6</sup> <I>Salmonella</I> targets m<sup>&ndash;3</sup> of air. <I>Salmonella</I> were also detected by a cultivation-based approach in some samples, but concentrations were two to three magnitudes lower than the concentrations detected by molecular biological results. Specificity of results was demonstrated by cloning analyses of PCR products, which were exclusively assigned to the genus <I>Salmonella</I>. However, by molecular methods, microorganisms are detected independently of their viability status, leading to an overestimation of concentration. Hence, the survival rate of <I>Salmonella</I> cells was measured on filter surfaces during filtration samplings where 82% of the cells died within 20 min of filtration. The results clearly show the specificity and practicability of the established qPCR assay for analysis and quantification of salmonellae in bioaerosols. The results demonstrate airborne <I>Salmonella</I> workplace concentrations in poultry production of up to 3.3% of 4',6-Diamidino-2-phenylindole-counted total cell numbers.</p>
]]></description>
<dc:creator><![CDATA[Fallschissel, K., Kampfer, P., Jackel, U.]]></dc:creator>
<dc:date>Wed, 12 Aug 2009 07:42:38 PDT</dc:date>
<dc:identifier>info:doi/10.1093/annhyg/mep060</dc:identifier>
<dc:title><![CDATA[Direct Detection of Salmonella Cells in the Air of Livestock Stables by Real-Time PCR]]></dc:title>
<dc:publisher>British Occupational Hygiene Society</dc:publisher>
<prism:publicationDate>2009-08-12</prism:publicationDate>
<prism:section>Article</prism:section>
</item>

<item rdf:about="http://annhyg.oxfordjournals.org/cgi/content/short/mep057v1?rss=1">
<title><![CDATA[CFD Simulation of Contaminant Decay for High Reynolds Flow in a Controlled Environment]]></title>
<link>http://annhyg.oxfordjournals.org/cgi/content/short/mep057v1?rss=1</link>
<description><![CDATA[
<p>This study examines the usage of computational fluid dynamics (CFDs) for estimating the time-elapsed decay of contaminants within a chamber experiencing high Reynolds flow. CFD results were compared with measurements taken at a controlled facility. In addition, parameters of the CFD simulation were examined; namely the effects of turbulence and inertial transport at high Reynolds number ventilating flows, as well as inlet duct configuration and its effect on the inlet velocity profile. The agreement between the computational and experimental clearance times was quite good, with percent errors as low as &ndash;5.32% at high flow rate and &ndash;11.8% at the lower flow rate. This study determined that for high Reynolds flow, diffusive transport effects may be ignored as the majority of mass is transported via the bulk stream, i.e. momentum transport. In addition, resolving the inlet velocity profile was of prime importance for accurate simulation of ventilating flows and prediction of contaminant washout. This was done by including the inlet duct geometry in the computational domain. In addition, it was found that despite different flow rates, the predicted contaminant washout took ~12&ndash;13% longer than predicted assuming instantaneous mixing. Furthermore, percent error between computational and experimental data as low as &ndash;5.32% shows that CFD is a useful tool for studying ventilation phenomena.</p>
]]></description>
<dc:creator><![CDATA[Lambert, A. R., Lin, C.-L., Mardorf, E., O'shaughnessy, P.]]></dc:creator>
<dc:date>Tue, 11 Aug 2009 09:29:25 PDT</dc:date>
<dc:identifier>info:doi/10.1093/annhyg/mep057</dc:identifier>
<dc:title><![CDATA[CFD Simulation of Contaminant Decay for High Reynolds Flow in a Controlled Environment]]></dc:title>
<dc:publisher>British Occupational Hygiene Society</dc:publisher>
<prism:publicationDate>2009-08-11</prism:publicationDate>
<prism:section>Article</prism:section>
</item>

<item rdf:about="http://annhyg.oxfordjournals.org/cgi/content/short/mep058v1?rss=1">
<title><![CDATA[Emission of Volatile Aldehydes and Ketones from Wood Pellets under Controlled Conditions]]></title>
<link>http://annhyg.oxfordjournals.org/cgi/content/short/mep058v1?rss=1</link>
<description><![CDATA[
<p>Different qualities of biofuel pellets were made from pine and spruce sawdust according to an industrial experimental design. The fatty/resin acid compositions were determined by gas chromatography-mass spectrometry for both newly produced pellets and those after 2 and 4 weeks of storage. The aldehydes/ketones compositions were determined by high performance liquid chromatography at 0, 2, and 4 weeks. The designs were analyzed for the response variables: total fatty/resin acids and total aldehydes/ketones. The design showed a strong correlation between the pine fraction in the pellets and the fatty/resin acid content but the influence decreased over storage time. The amount of fatty/resin acids decreased ~40% during 4 weeks. The influence of drying temperature on the aldehyde/ketone emission of fresh pellets was also shown. The amounts of emitted aldehydes/ketones generally decreased by 45% during storage as a consequence of fatty/resin acid oxidation. The matrices of individual concentrations were subjected to multivariate data analysis. This showed clustering of the different experimental runs and demonstrated the important mechanism of fatty/resin acid conversion.</p>
]]></description>
<dc:creator><![CDATA[Arshadi, M., Geladi, P., Gref, R., Fjallstrom, P.]]></dc:creator>
<dc:date>Mon, 10 Aug 2009 03:02:11 PDT</dc:date>
<dc:identifier>info:doi/10.1093/annhyg/mep058</dc:identifier>
<dc:title><![CDATA[Emission of Volatile Aldehydes and Ketones from Wood Pellets under Controlled Conditions]]></dc:title>
<dc:publisher>British Occupational Hygiene Society</dc:publisher>
<prism:publicationDate>2009-08-10</prism:publicationDate>
<prism:section>Article</prism:section>
</item>

<item rdf:about="http://annhyg.oxfordjournals.org/cgi/content/short/mep049v1?rss=1">
<title><![CDATA[Rate and Peak Concentrations of Off-Gas Emissions in Stored Wood Pellets--Sensitivities to Temperature, Relative Humidity, and Headspace Volume]]></title>
<link>http://annhyg.oxfordjournals.org/cgi/content/short/mep049v1?rss=1</link>
<description><![CDATA[
<p>Wood pellets emit CO, CO<SUB>2</SUB>, CH<SUB>4</SUB>, and other volatiles during storage. Increased concentration of these gases in a sealed storage causes depletion of concentration of oxygen. The storage environment becomes toxic to those who operate in and around these storages. The objective of this study was to investigate the effects of temperature, moisture, and the relative size of storage headspace on emissions from wood pellets in an enclosed space. Twelve 10-l plastic containers were used to study the effects of headspace ratio (25, 50, and 75% of container volume) and temperatures (10&ndash;50&deg;C). Another eight containers were set in uncontrolled storage relative humidity (RH) and temperature. Concentrations of CO<SUB>2</SUB>, CO, and CH<SUB>4</SUB> were measured by gas chromatography (GC). The results showed that emissions of CO<SUB>2</SUB>, CO, and CH<SUB>4</SUB> from stored wood pellets are more sensitive to storage temperature than to RH and the relative volume of headspace. Higher peak emission factors are associated with higher temperatures. Increased headspace volume ratio increases peak off-gas emissions because of the availability of oxygen associated with pellet decomposition. Increased RH in the enclosed container increases the rate of off-gas emissions of CO<SUB>2</SUB>, CO, and CH<SUB>4</SUB> and oxygen depletion.</p>
]]></description>
<dc:creator><![CDATA[Kuang, X., Shankar, T. J., Bi, X. T., Lim, C. J., Sokhansanj, S., Melin, S.]]></dc:creator>
<dc:date>Wed, 05 Aug 2009 00:44:35 PDT</dc:date>
<dc:identifier>info:doi/10.1093/annhyg/mep049</dc:identifier>
<dc:title><![CDATA[Rate and Peak Concentrations of Off-Gas Emissions in Stored Wood Pellets--Sensitivities to Temperature, Relative Humidity, and Headspace Volume]]></dc:title>
<dc:publisher>British Occupational Hygiene Society</dc:publisher>
<prism:publicationDate>2009-08-05</prism:publicationDate>
<prism:section>Article</prism:section>
</item>

<item rdf:about="http://annhyg.oxfordjournals.org/cgi/content/short/mep043v1?rss=1">
<title><![CDATA[Determinants of Use of Hearing Protection Devices in Canadian Lumber Mill Workers]]></title>
<link>http://annhyg.oxfordjournals.org/cgi/content/short/mep043v1?rss=1</link>
<description><![CDATA[
<p>Background: In a cohort study of lumber mill workers&rsquo; exposure to noise and incidence of heart disease, initial noise estimates were likely overestimated because they did not account for reductions afforded by the use of hearing protection. As such information was seldom available for individual workers, modeling was necessary to predict hearing protection use and derive adjusted noise measures.</p>
<p>Objective: To develop a multilevel model of the likelihood of use of hearing protection devices (HPDs) for British Columbia (Canada) lumber mill workers.</p>
<p>Method: The study population included 13 147 workers in 14 sawmills for whom we had information on HPD use. Subjects self-reported their use of hearing protectors during routine hearing tests over their work history period. Separate multilevel logistic regression models with increasing complexity were developed for a subcohort of workers with complete information (<I>n</I> = 1493) and for a subcohort comprised subjects with hearing tests coinciding with their jobs (<I>n</I> = 10 203). The models included random intercepts for worker and for sawmill.</p>
<p>Results: HPD use was associated in both subcohorts with factors such as noise exposure and age. We also showed that specific jobs (such as sawfiling) and departments (planer, in particular) were strongly associated with the use of HPDs. The model illustrates the quantitative importance of including a hierarchical structure which allows for explaining potential sources of outcome variability.</p>
<p>Conclusions: We developed a hierarchical model to predict hearing protection use to enable correction of exposure assessments for use in retrospective epidemiological studies. We showed that this was feasible even in the absence of complete determinant information.</p>
]]></description>
<dc:creator><![CDATA[Sbihi, H., Teschke, K., Macnab, Y. C., Davies, H. W.]]></dc:creator>
<dc:date>Wed, 01 Jul 2009 08:27:30 PDT</dc:date>
<dc:identifier>info:doi/10.1093/annhyg/mep043</dc:identifier>
<dc:title><![CDATA[Determinants of Use of Hearing Protection Devices in Canadian Lumber Mill Workers]]></dc:title>
<dc:publisher>British Occupational Hygiene Society</dc:publisher>
<prism:publicationDate>2009-07-01</prism:publicationDate>
<prism:section>Article</prism:section>
</item>

</rdf:RDF>