Exposure to Refractory Ceramic Fibres in the Metal Industry

Refractory ceramic fibres (RCF) are used in thermal isolation in the metal industry where high temperatures are regularly employed. Asbestos materials were earlier commonly used for these purposes. In this work, two Finnish steel plants, three foundries and a repair shop were studied for the ceramic...

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Veröffentlicht in:The Annals of occupational hygiene 2007-08, Vol.51 (6), p.509-516
Hauptverfasser: LINNAINMAA, MARKKU, KANGAS, JUHANI, MÄKINEN, MILJA, METSÄRINNE, SIRPA, TOSSAVAINEN, ANTTI, SÄNTTI, JAAKKO, VETELI, MARIKA, SAVOLAINEN, HEIKKI, KALLIOKOSKI, PENTTI
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container_issue 6
container_start_page 509
container_title The Annals of occupational hygiene
container_volume 51
creator LINNAINMAA, MARKKU
KANGAS, JUHANI
MÄKINEN, MILJA
METSÄRINNE, SIRPA
TOSSAVAINEN, ANTTI
SÄNTTI, JAAKKO
VETELI, MARIKA
SAVOLAINEN, HEIKKI
KALLIOKOSKI, PENTTI
description Refractory ceramic fibres (RCF) are used in thermal isolation in the metal industry where high temperatures are regularly employed. Asbestos materials were earlier commonly used for these purposes. In this work, two Finnish steel plants, three foundries and a repair shop were studied for the ceramic fibre exposure of their workers under normal production and during the replacement of oven insulation. Personal and stationary sampling was used together with a novel nasal lavage sampling for the evaluation of personal exposure. Fibres were counted with optical and electron microscopy and they were identified using an energy-dispersive X-ray analyser. Ceramic fibres were found in most production phases [range
doi_str_mv 10.1093/annhyg/mem027
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Asbestos materials were earlier commonly used for these purposes. In this work, two Finnish steel plants, three foundries and a repair shop were studied for the ceramic fibre exposure of their workers under normal production and during the replacement of oven insulation. Personal and stationary sampling was used together with a novel nasal lavage sampling for the evaluation of personal exposure. Fibres were counted with optical and electron microscopy and they were identified using an energy-dispersive X-ray analyser. Ceramic fibres were found in most production phases [range &lt;0.01–0.29 fibres per cubic centimetre (f cm−3)]. Considerably higher fibre counts were obtained during the maintenance work (range &lt;0.01–14.2 f cm−3). Nasal sampling was found to correlate with the airborne fibre concentrations at the group level. The mean fibre concentrations varied from 34 to 6680 f ml−1 of lavage liquid. Use of personal respiratory protectors diminished the exposure on the average as analysed in the lavage specimens, but the effect of respirator use did not appear clearly in the results. Because of the heat conditions, the workers used the respirators for a strict minimum period. A considerable exposure to RCF occurs in the studied plants. Its risk should be evaluated and managed more closely in view that the material is carcinogenic. Use of personal respiratory protectors should be encouraged. 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Toxic occupational diseases ; Dust - analysis ; exposure ; Finland ; foundries ; Humans ; Inhalation Exposure - adverse effects ; Inhalation Exposure - analysis ; Medical sciences ; Metallurgy ; Metals and various inorganic compounds ; Microscopy, Electron, Scanning - methods ; Mineral Fibers - analysis ; Mineral Fibers - toxicity ; Nasal Lavage Fluid - chemistry ; nasal sampling ; Occupational Exposure - adverse effects ; Occupational Exposure - analysis ; refractory ceramic fibres ; respirators ; Steel ; steel plants ; Toxicology</subject><ispartof>The Annals of occupational hygiene, 2007-08, Vol.51 (6), p.509-516</ispartof><rights>The Author 2007. 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Asbestos materials were earlier commonly used for these purposes. In this work, two Finnish steel plants, three foundries and a repair shop were studied for the ceramic fibre exposure of their workers under normal production and during the replacement of oven insulation. Personal and stationary sampling was used together with a novel nasal lavage sampling for the evaluation of personal exposure. Fibres were counted with optical and electron microscopy and they were identified using an energy-dispersive X-ray analyser. Ceramic fibres were found in most production phases [range &lt;0.01–0.29 fibres per cubic centimetre (f cm−3)]. Considerably higher fibre counts were obtained during the maintenance work (range &lt;0.01–14.2 f cm−3). Nasal sampling was found to correlate with the airborne fibre concentrations at the group level. The mean fibre concentrations varied from 34 to 6680 f ml−1 of lavage liquid. 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Toxic occupational diseases</topic><topic>Dust - analysis</topic><topic>exposure</topic><topic>Finland</topic><topic>foundries</topic><topic>Humans</topic><topic>Inhalation Exposure - adverse effects</topic><topic>Inhalation Exposure - analysis</topic><topic>Medical sciences</topic><topic>Metallurgy</topic><topic>Metals and various inorganic compounds</topic><topic>Microscopy, Electron, Scanning - methods</topic><topic>Mineral Fibers - analysis</topic><topic>Mineral Fibers - toxicity</topic><topic>Nasal Lavage Fluid - chemistry</topic><topic>nasal sampling</topic><topic>Occupational Exposure - adverse effects</topic><topic>Occupational Exposure - analysis</topic><topic>refractory ceramic fibres</topic><topic>respirators</topic><topic>Steel</topic><topic>steel plants</topic><topic>Toxicology</topic><toplevel>online_resources</toplevel><creatorcontrib>LINNAINMAA, MARKKU</creatorcontrib><creatorcontrib>KANGAS, JUHANI</creatorcontrib><creatorcontrib>MÄKINEN, MILJA</creatorcontrib><creatorcontrib>METSÄRINNE, SIRPA</creatorcontrib><creatorcontrib>TOSSAVAINEN, ANTTI</creatorcontrib><creatorcontrib>SÄNTTI, JAAKKO</creatorcontrib><creatorcontrib>VETELI, MARIKA</creatorcontrib><creatorcontrib>SAVOLAINEN, HEIKKI</creatorcontrib><creatorcontrib>KALLIOKOSKI, PENTTI</creatorcontrib><collection>Istex</collection><collection>Pascal-Francis</collection><collection>Medline</collection><collection>MEDLINE</collection><collection>MEDLINE (Ovid)</collection><collection>MEDLINE</collection><collection>MEDLINE</collection><collection>PubMed</collection><collection>CrossRef</collection><collection>Health and Safety Science Abstracts (Full archive)</collection><collection>Pollution Abstracts</collection><collection>Risk Abstracts</collection><collection>Safety Science and Risk</collection><collection>Toxicology Abstracts</collection><collection>Environmental Sciences and Pollution Management</collection><jtitle>The Annals of occupational hygiene</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>LINNAINMAA, MARKKU</au><au>KANGAS, JUHANI</au><au>MÄKINEN, MILJA</au><au>METSÄRINNE, SIRPA</au><au>TOSSAVAINEN, ANTTI</au><au>SÄNTTI, JAAKKO</au><au>VETELI, MARIKA</au><au>SAVOLAINEN, HEIKKI</au><au>KALLIOKOSKI, PENTTI</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Exposure to Refractory Ceramic Fibres in the Metal Industry</atitle><jtitle>The Annals of occupational hygiene</jtitle><addtitle>Ann Occup Hyg</addtitle><date>2007-08-01</date><risdate>2007</risdate><volume>51</volume><issue>6</issue><spage>509</spage><epage>516</epage><pages>509-516</pages><issn>0003-4878</issn><issn>1475-3162</issn><eissn>1475-3162</eissn><coden>AOHYA3</coden><abstract>Refractory ceramic fibres (RCF) are used in thermal isolation in the metal industry where high temperatures are regularly employed. Asbestos materials were earlier commonly used for these purposes. In this work, two Finnish steel plants, three foundries and a repair shop were studied for the ceramic fibre exposure of their workers under normal production and during the replacement of oven insulation. Personal and stationary sampling was used together with a novel nasal lavage sampling for the evaluation of personal exposure. Fibres were counted with optical and electron microscopy and they were identified using an energy-dispersive X-ray analyser. Ceramic fibres were found in most production phases [range &lt;0.01–0.29 fibres per cubic centimetre (f cm−3)]. Considerably higher fibre counts were obtained during the maintenance work (range &lt;0.01–14.2 f cm−3). Nasal sampling was found to correlate with the airborne fibre concentrations at the group level. The mean fibre concentrations varied from 34 to 6680 f ml−1 of lavage liquid. Use of personal respiratory protectors diminished the exposure on the average as analysed in the lavage specimens, but the effect of respirator use did not appear clearly in the results. Because of the heat conditions, the workers used the respirators for a strict minimum period. A considerable exposure to RCF occurs in the studied plants. Its risk should be evaluated and managed more closely in view that the material is carcinogenic. Use of personal respiratory protectors should be encouraged. Their effective use could be verified by the nasal sampling for fibres after the work shift.</abstract><cop>Oxford</cop><pub>Oxford University Press</pub><pmid>17607019</pmid><doi>10.1093/annhyg/mem027</doi><tpages>8</tpages><oa>free_for_read</oa></addata></record>
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subjects Air Pollutants, Occupational - analysis
Air Pollutants, Occupational - toxicity
Biological and medical sciences
Ceramics - analysis
Ceramics - toxicity
Chemical and industrial products toxicology. Toxic occupational diseases
Dust - analysis
exposure
Finland
foundries
Humans
Inhalation Exposure - adverse effects
Inhalation Exposure - analysis
Medical sciences
Metallurgy
Metals and various inorganic compounds
Microscopy, Electron, Scanning - methods
Mineral Fibers - analysis
Mineral Fibers - toxicity
Nasal Lavage Fluid - chemistry
nasal sampling
Occupational Exposure - adverse effects
Occupational Exposure - analysis
refractory ceramic fibres
respirators
Steel
steel plants
Toxicology
title Exposure to Refractory Ceramic Fibres in the Metal Industry
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