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1.
Ann Occup Hyg ; 54(2): 247-54, 2010 Mar.
Article in English | MEDLINE | ID: mdl-20007342

ABSTRACT

This article describes a device intended to produce replicas on filters by liquid deposition of anion or metal solutions. Schematically, the filters are housed in cassettes labelled automatically by means of a code. An automatic arm takes each cassette, reads the code, and deposits the amount of element required. Weighing before and after deposition allows the amount deposited to be accurately checked and determined. This automated system allows the production of replicas with high deposition regularity, replica dispersion for the most part being <1%. The samples produced can be used during proficiency tests where the assigned value is determined either by the participants or by the organizer.


Subject(s)
Automation, Laboratory/methods , Chemistry Techniques, Analytical/methods , Clinical Laboratory Techniques , Environmental Monitoring/methods , Filtration/instrumentation , Metals/analysis , Automation, Laboratory/standards , Clinical Laboratory Techniques/standards , Filtration/methods , Occupational Health
2.
Ann Occup Hyg ; 51(6): 501-7, 2007 Aug.
Article in English | MEDLINE | ID: mdl-17625218

ABSTRACT

As part of a wider epidemiological research programme, an occupational hygiene study was carried out during 1995-1996 to assess workers' current exposures to airborne materials in six European refractory ceramic fibre (RCF) plants. These plants had also participated in a cross-sectional occupational hygiene survey in 1987. The sampling strategy focussed principally on personal shift-average exposures of workers, by occupation, to respirable fibres. Monitoring was undertaken in two integrated phases: a 1-week cross-sectional survey followed by a prospective, and ongoing, programme by the RCF industry. Statistical (analysis of variance) analyses to identify patterns of variability by plant, occupational group (OG) and occupations within group were based on 464 individual shift samples, the greatest amount of data being available for production occupations. Concentrations of respirable fibres showed marked differences between plants and between OGs. Average respirable fibre concentrations among Primary and Secondary Production and Ancillary workers ranged from <0.1 f ml(-1) to up to 0.4 f ml(-1), depending on OG and plant. Individual shift-average measurements were almost invariably <1 f ml(-1). Within Secondary Conversion and Finishing, plant-specific averages ranged from 0.3 f ml(-1) to 1.25 f ml(-1). Respirable fibre concentrations were, in some plants, less than half those found in 1987. In other plants, mainly those where concentrations had been relatively low in 1987, the dust exposure had remained essentially unchanged or increased slightly. An ongoing programme of sampling is being carried out by the participating companies, generating additional information that could assist research in the long term and in improving control.


Subject(s)
Air Pollutants, Occupational/analysis , Ceramics/adverse effects , Chemical Industry , Occupational Exposure/adverse effects , Workplace , Air Pollutants, Occupational/adverse effects , Cross-Sectional Studies , Dust/analysis , Europe/epidemiology , Humans , Inhalation Exposure/adverse effects , Inhalation Exposure/analysis , Mineral Fibers/adverse effects , Mineral Fibers/analysis , Occupational Exposure/analysis , Occupations , Prospective Studies
4.
Ann Occup Hyg ; 49(8): 661-71, 2005 Nov.
Article in English | MEDLINE | ID: mdl-15972798

ABSTRACT

In this study, the alpha-quartz contents measured by different analytical techniques (X-ray diffraction, direct method; and infrared spectrophotometry, direct and indirect methods) were compared. The analyses were carried out on filters sampled in an industrial setting by means of a Dorr-Oliver cyclone. To verify the methodology used, filters loaded with pure alpha-quartz were also analysed. By and large, the agreement between the two direct methods was close on average, but on the basis of a comparison of the individual results, considerable differences exist. In absolute value, the mean relative deviation between the two techniques was <25% in only 47.8% of the cases. The results obtained by the indirect method (infrared) were on average 13% lower than the results obtained by the two direct methods with a more important difference (23%) for samples where calcite was identified by X-ray diffraction in comparison with those where it was not (8%). This underestimation, which was not owing to dust losses during preparation, is probably explained by the elimination of organic compounds during dust calcinations or by the transformation of mineral compounds. The indirect method introduces additional sample handling operations with more risk of material loss. When the quantity of calcined material was <0.4 mg, the weighing operations necessary to correct any losses of material resulted in considerable variability. In terms of overall uncertainty, it would be better in this case not to carry out correction and to employ an operating mode favouring the recovery of a maximum of material while accepting a bias of about 5-7%.


Subject(s)
Air Pollutants/analysis , Dust , Environmental Monitoring/methods , Extraction and Processing Industry , Quartz , Calibration , Humans , Spectrophotometry, Infrared , X-Ray Diffraction
5.
Ann Occup Hyg ; 49(4): 325-34, 2005 Jun.
Article in English | MEDLINE | ID: mdl-15845604

ABSTRACT

Three methods of classifying laboratories during fibre counting proficiency tests were compared. The first two are those used in France (classification according to the mean and coefficient of variation of the results) and in Great Britain (classification according to the proportion of normalized results situated within predefined limits). The third is a variation of the Workplace Analysis Scheme for Proficiency (WASP) programme adapted to fibre counting tests. In the latter case, the laboratory classification is based on comparing the variance characterizing the dispersion of the results of a laboratory with a reference variance, which is considered as the variance of experienced analysts or laboratories. This mode of processing has the advantage of allowing the comparison of magnitudes. For example, the variance of the reference value can be compared with the reference variance. The same applies if a proficiency test is organized on the basis of replicas distributed to different analysts, the variability of these replicas can be compared with the reference variance. It emerged that the modified WASP method produces results close to those obtained by the other two methods. Moreover, the selectivity of the three methods is evaluated.


Subject(s)
Air Pollutants, Occupational/analysis , Environmental Monitoring/standards , Laboratories , Mineral Fibers/analysis , Occupational Health , Quality Control , Environmental Monitoring/methods , Humans , Reference Values
6.
Ann Occup Hyg ; 49(6): 481-92, 2005 Aug.
Article in English | MEDLINE | ID: mdl-15790615

ABSTRACT

The counting of fibres on membrane filters could be facilitated by using size-selective samplers to exclude coarse particulate and fibres that impede fibre counting. Furthermore, the use of thoracic size selection would also remove the present requirement to discriminate fibres by diameter during counting. However, before thoracic samplers become acceptable for sampling fibres, their performance with fibres needs to be determined. This study examines the performance of four thoracic samplers: the GK2.69 cyclone, a Modified SIMPEDS cyclone, the CATHIA sampler (inertial separation) and the IOM thoracic sampler (porous foam pre-selector). The uniformity of sample deposit on the filter samples, which is important when counts are taken on random fields, was examined with two sizes of spherical particles (1 and 10 microm) and a glass fibre aerosol with fibres spanning the aerodynamic size range of the thoracic convention. Counts by optical microscopy examined fields on a set scanning pattern. Hotspots of deposition were detected for one of the thoracic samplers (Modified SIMPEDS with the 10 microm particles and the fibres). These hotspots were attributed to the inertial flow pattern near the port from the cyclone pre-separator. For the other three thoracic samplers, the distribution was similar to that on a cowled sampler, the current standard sampler for fibres. Aerodynamic selection was examined by comparing fibre concentration on thoracic samples with those measured on semi-isokinetic samples, using fibre size (and hence calculated aerodynamic diameter) and number data obtained by scanning electron microscope evaluation in four laboratories. The size-selection characteristics of three thoracic samplers (GK2.69, Modified SIMPEDS and CATHIA) appeared very similar to the thoracic convention; there was a slight oversampling (relative to the convention) for d(ae) < 7 microm, but that would not be disadvantageous for comparability with the cowled sampler. Only the IOM thoracic sampler tended to undersample the fibres relative to the thoracic convention. With the data divided into four classes based on fibre length, the size-selection characteristics appeared to be unaffected by fibre length for GK2.69, Modified SIMPEDS and CATHIA. Only the IOM thoracic sampler (with the foam selector) showed slightly lower selection for longer length classes of fibres. These results indicate that the tested samplers follow the thoracic sampling convention for fibres, and may be used to improve the quality and reliability of samples that are taken when there is likely to be significant background dust.


Subject(s)
Air Pollutants/analysis , Environmental Monitoring/instrumentation , Mineral Fibers/analysis , Environmental Monitoring/methods , Filtration , Inhalation Exposure/analysis , Particle Size
7.
Inhal Toxicol ; 15(10): 1017-27, 2003 Sep.
Article in English | MEDLINE | ID: mdl-12928977

ABSTRACT

Transgenic BigBlue rats were exposed to CM 44 glass fibers (6.3 mg/m3) by nose only, 6 h/day for 5 days. Two endpoints were examined 1, 3, 14, 28, and 90 days following exposure: fiber biopersistence and mutations in lung DNA. The half-time of the fibers >20 microm was 12.8 days, and mutant frequencies of control and exposed rats were similar across all time points. The mutation spectra of both series were similar after 28 days of fixation time. These results showed that a glass fiber with a high clearance in the lung seems to not present any significant effect on mutagenesis on lung DNA and are in marked contrast to results for asbestos, which caused a twofold mutant frequency increase as described in a previous study.


Subject(s)
DNA Damage , Glass , Inhalation Exposure , Animals , Animals, Genetically Modified , Bronchoalveolar Lavage , Half-Life , Male , Mutagenicity Tests , Rats/genetics , Rats, Inbred F344 , Risk Assessment
8.
Ann Occup Hyg ; 47(5): 413-26, 2003 Jul.
Article in English | MEDLINE | ID: mdl-12855491

ABSTRACT

The use of direct-reading instruments to measure the airborne fibre number concentration is on the increase. The response of two of these instruments (FM-7400 and Fibrecheck FC-2) was compared with the conventional method of sampling on filters and counting by phase contrast microscopy. Four types of fibres were studied at different concentrations and relative humidity levels. The FM-7400 can be calibrated by the manufacturer for two different levels of sensitivity (standard and high). For the tests where it was set to the sensitivity level with which it had been calibrated, the ratio of the concentration measured by the instrument to the concentration obtained by the conventional method varied in the range 0.5-1 for the different types of fibres studied (chrysotile, glass wool and ceramic fibres). The Fibrecheck FC-2 is a much less versatile instrument. On the basis of a calibration allowing correct detection of asbestos fibres, it greatly overestimated the concentration of man-made mineral fibres. In its normal calibration state a fine chrysotile aerosol was poorly detected. For man-made mineral fibres, the response was highly dependent on the nature of the fibres. These instruments require calibration with the type of fibres to be studied. Unfortunately, this operation is not always accessible to the user and may require the services of a specialized laboratory, as the manufacturer is not always in a position to carry this out.


Subject(s)
Air Pollutants/analysis , Environmental Monitoring/instrumentation , Mineral Fibers/analysis , Aerosols/analysis , Calibration/standards , Equipment Design , Humans , Light , Microscopy, Phase-Contrast , Scattering, Radiation , Sensitivity and Specificity
9.
Ann Occup Hyg ; 46(4): 409-21, 2002 Jun.
Article in English | MEDLINE | ID: mdl-12176710

ABSTRACT

The aim of this study was to compare the X-ray diffraction and infrared spectrophotometric patterns of two samples of alpha quartz (QUIN1 and QUIN2) with that of NIST SRM 1878a alpha quartz certified 100% crystalline. As it is known that the intensity diffracted and the absorbance per mass unit for a given type of alpha quartz depend on its particle size, this factor was taken into account. To do this, different types of alpha quartz were sampled on filters using a Dorr-Oliver cyclone to select particle size. Variation in the flow rate of the cyclone in the range 1.2-2.8 l/min allowed the volume median diameter of the sampled particles to be varied. For the four strongest diffraction lines it was observed that the intensity per mass unit increased with the volume median diameter of the particles. For infrared spectrophotometry for analytical band wavelengths close to 12.5 micro m, it was observed that the absorbance per mass unit decreased as particle size increased. The opposite effect was noted for analytical band wavelengths >14.4 micro m. Compared with SRM 1878a alpha quartz, certified 100% crystalline, the purity of QUIN1 alpha quartz was 93.1% (confidence interval 92.4-93.8%) when measured by X-ray diffraction and 91.5% (confidence interval 90.1-92.9%) when measured by infrared spectrophotometry. In the case of QUIN2 alpha quartz the purity was globally lower.


Subject(s)
Quartz/analysis , Quartz/standards , Calibration/standards , Particle Size , Spectroscopy, Fourier Transform Infrared , X-Ray Diffraction
10.
Ann Occup Hyg ; 45(1): 61-9, 2001 Jan.
Article in English | MEDLINE | ID: mdl-11137700

ABSTRACT

In France, the owners of buildings have been obliged since February 1996 to ascertain whether asbestos has been incorporated into surfacing materials, insulation products or false ceilings. In certain circumstances, there is also a requirement to measure the airborne asbestos fibre concentration. Three years (1996-1998) of asbestos fibre count reporting are evaluated for the proficiency testing scheme organized in France to evaluate the performance of laboratories using an indirect-transfer transmission electron microscopy procedure to measure the airborne asbestos fibre concentration. Each year eight filters are distributed to each participating laboratory. These filters are obtained by filtering a suspension containing chrysotile or amphibole fibres. In 1996, 36% of the laboratories were rated 1 (the best performers; i.e. those providing counts close to the reference value). Performance improved appreciably in the last round where 85% of the laboratories were rated 1.


Subject(s)
Air Pollution, Indoor/analysis , Asbestos/analysis , Laboratories/standards , Microscopy, Electron , France , Humans , Mineral Fibers , Quality Control
11.
Environ Health Perspect ; 108(4): 341-6, 2000 Apr.
Article in English | MEDLINE | ID: mdl-10753093

ABSTRACT

We used transgenic mice carrying the lacI reporter gene to study the mutagenesis potential of asbestos crocidolite. The animals were exposed by nose-only inhalation to an aerosol containing 5.75 mg/m(3) crocidolite dust for 6 hr/day and 5 consecutive days. After 1, 4, and 12 weeks, we examined four end points: the cytology of bronchoalveolar lavage, the lung load of crocidolite, the hydrophobic DNA adducts, and the mutations in the lacI reporter gene. Twelve weeks after exposure, nearly 10% of the inhaled fibers remained in the lung (227 +/- 103 ng/mg lung). There was evidence of a typical inflammatory response consisting of multinucleate macrophages at weeks 4 and 12, whereas immediately after the exposure, we observed numerous polymorphonuclear neutrophils. The mutant frequency significatively increased during the fourth week after the exposure: 13.5 [time] 10(-5) in the exposed group versus 6. 9 10(-5) in the control group. The induction factor, defined by the ratio of checked mutants of exposed mice to checked mutants of control mice, was 1.96. The mutation spectrum of control lung DNA and exposed lung DNA was similar, suggesting the possible involvement of a DNA repair decrease in crocidolite-treated animals. We used the (32)P-postlabeling method and did not detect any increase of either 5 mC or bulky adduct in treated mice. This is the first study that demonstrates asbestos mutagenicity in vivo after a nose-only inhalation.


Subject(s)
Air Pollutants/adverse effects , Asbestos, Crocidolite/adverse effects , DNA Adducts/genetics , DNA Damage/genetics , Lung/drug effects , Animals , Asbestos, Crocidolite/administration & dosage , Inhalation Exposure , Lung/pathology , Macrophages, Alveolar/physiology , Male , Mice , Mice, Transgenic , Mutagenicity Tests
12.
Rev Mal Respir ; 16(6 Pt 2): 1212-8, 1999 Dec.
Article in French | MEDLINE | ID: mdl-10897842

ABSTRACT

Since the beginning of this century a wide range of methods were used to evaluate the asbestos exposure of workers. Instruments such as the konimeter, thermal precipitator, impinger or tyndallometer were employed to collect dust samples. Currently, the membrane filter method associated with phase contrast optical microscopy is widely accepted. These different sampling methods are presented in this paper and the relationships between asbestos concentration recorded by means of methods used in the past and with the current membrane filter method or with direct-reading instruments are discussed. Emphasis is put on the difficulty to use such relationships which were often established for specific situations (in the mine industry for instance). For non occupational exposure the use of electron microscopy methods is evaluated.


Subject(s)
Air Pollution/analysis , Asbestos/analysis , Environmental Monitoring/methods , Humans , Mineral Fibers/analysis , Occupational Exposure
13.
Ann Occup Hyg ; 42(7): 453-65, 1998 Oct.
Article in English | MEDLINE | ID: mdl-9793476

ABSTRACT

A specific version of the personal aerosol sampler CIP 10 was designed, named CIP10-T, for sampling the conventional CEN thoracic fraction. A static sampler, named CATHIA, was also designed. It uses the same sampling head, but the size selected particles are collected onto a filter. The combined particle efficiency of the aspiration slot and the selector was measured in a horizontal wind tunnel at low air velocity, close to 16 cm s-1. The flow rate of both samplers was fixed at its nominal value, i.e., 71 min-1. Two different methods were used: the former was based on the Aerodynamic Particle Sizer (TSI); the latter used the measurement of particle size distribution of the collected samples by the Coulter technique. For the CIP10-T sampler, the particle collection efficiency onto the rotating cup was also measured. For both samplers bias and accuracy maps have been calculated, following the recommendations of a new CEN standard about sampler performance. The bias does not exceed 10% in absolute value for both samplers, within a large range of particle size distribution of the total aerosol. For the CIP10-T sampler, the accuracy map exhibits a large area where the accuracy is better than 10%, corresponding for example to 4 microns < or = MMAD < or = 14 microns for GSD = 2. For the same geometric standard deviation, the accuracy is still better than 20% for 15 microns < or = MMAD < or = 21 microns. For the CATHIA-T sampler, the accuracy map can be roughly divided into two parts. The accuracy remains better than 10% for MMAD < or = 12 microns, and it remains between 10 and 20% for coarser aerosols, with 13 microns < or = MMAD < or = 20 microns, provided GSD > or = 2.


Subject(s)
Occupational Exposure , Occupational Health , Aerosols , Equipment Design , Filtration , Humans , Particle Size
14.
Ann Occup Hyg ; 40(3): 311-9, 1996 Jun.
Article in English | MEDLINE | ID: mdl-8694492

ABSTRACT

A new static device, the CATHIA sampling head, based on the collection of the thoracic fraction is proposed for the assessment of the airborne concentration of asbestos fibres by transmission electron microscopy. By comparison with a standard aerosol sampling head, it has been shown that this sampler reduces the total mass concentration, but does not introduce any change in the most common index used to characterize an asbestos aerosol fibre, that is the concentration of fibres with length greater than 5 microns, diameter less than 3 microns and length to diameter ratio greater than 3. The homogeneity of the deposited dust on the collection filter favours the use of this sampling head with both the indirect and direct preparation methods.


Subject(s)
Air Pollutants, Occupational/analysis , Asbestos/analysis , Asbestosis/prevention & control , Environmental Monitoring/instrumentation , Microscopy, Electron , Humans , Maximum Allowable Concentration
15.
Toxicology ; 109(2-3): 147-56, 1996 May 17.
Article in English | MEDLINE | ID: mdl-8658545

ABSTRACT

A nose-only inhalation chamber is described: this chamber being computer automated has been particularly designed for mice on which it was validated using a crocidolite aerosol at a nominal concentration of 13.6 mg/m3, 6 h/day during 5 days. A month later the mice showed typical inflammatory bronchoalveolar liquids with many polynucleated or activated macrophages and asbestos bodies. The burden of crocidolite fibers ranged from 345,000 to 1,300,000 fibers per mg of dried lung. This study demonstrates that during the month that followed a short-term mice exposure to crocidolite fibers, the inflammatory response was still persistent. These toxicological endpoints validate the nose-only inhalation chamber to be useful for common or transgenic mice.


Subject(s)
Asbestos, Crocidolite/toxicity , Bronchoalveolar Lavage Fluid/cytology , Lung/pathology , Administration, Inhalation , Animals , Asbestos, Crocidolite/administration & dosage , Asbestos, Crocidolite/analysis , Bronchoalveolar Lavage Fluid/chemistry , Macrophages, Alveolar/ultrastructure , Male , Mice , Mice, Inbred BALB C , Microscopy, Electron , Microscopy, Electron, Scanning , Mineral Fibers/toxicity , Nebulizers and Vaporizers , Particle Size , Reproducibility of Results , Tumor Necrosis Factor-alpha/biosynthesis
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