1988European Respiratory JournalOpen access

Electron microscopic analysis of asbestos body cores from the Belgian urban population

Estelle Moulin, N Yourassowsky, Pascal Dumortier, Paul De Vuyst, JC Yernault

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Abstract

Typical ferruginous bodies considered as asbestos bodies (AB) were collected from the lungs of 19 asbestos-exposed and 25 non-exposed urban subjects. Of the 319 body cores analysed by energy dispersive spectrometry (EDS), 315 were asbestos. The non-asbestos cores were talc and crystalline silica. 89.2% of the asbestos cores were commercial amphiboles (amosite/crocidolite), 7% were chrysotile and 3.8% were non-commercial amphiboles (anthophyllite/tremolite). The commercial amphibole bodies were found in exposed and non-exposed subjects and chrysotile bodies mostly in exposed subjects. The non-commercial amphibole bodies were detected in non-exposed patients with low lung AB levels; this background contamination would be more difficult to detect in lungs containing large amounts of bodies due to occupational exposure. Chrysotile bodies and tremolite/anthophyllite bodies were not observed together. We suggest that in Belgium the source of non-commercial amphiboles exposure is not contamination by chrysotile.

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Typical ferruginous bodies considered as asbestos bodies (AB) were collected from the lungs of 19 asbestos-exposed and 25 non-exposed urban subjects. Of the 319 body cores analysed by energy dispersive spectrometry (EDS), 315 were asbestos. The non-asbestos cores were talc and crystalline silica. 89.2% of the asbestos cores were commercial amphiboles (amosite/crocidolite), 7% were chrysotile and 3.8% were non-commercial amphiboles (anthophyllite/tremolite). The commercial amphibole bodies were found in exposed and non-exposed subjects and chrysotile bodies mostly in exposed subjects. The non-commercial amphibole bodies were detected in non-exposed patients with low lung AB levels; this background contamination would be more difficult to detect in lungs containing large amounts of bodies due to occupational exposure. Chrysotile bodies and tremolite/anthophyllite bodies were not observed together. We suggest that in Belgium the source of non-commercial amphiboles exposure is not contamination by chrysotile.

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Available abstract

Typical ferruginous bodies considered as asbestos bodies (AB) were collected from the lungs of 19 asbestos-exposed and 25 non-exposed urban subjects. Of the 319 body cores analysed by energy dispersive spectrometry (EDS), 315 were asbestos. The non-asbestos cores were talc and crystalline silica. 89.2% of the asbestos cores were commercial amphiboles (amosite/crocidolite), 7% were chrysotile and 3.8% were non-commercial amphiboles (anthophyllite/tremolite). The commercial amphibole bodies were found in exposed and non-exposed subjects and chrysotile bodies mostly in exposed subjects. The non-commercial amphibole bodies were detected in non-exposed patients with low lung AB levels; this background contamination would be more difficult to detect in lungs containing large amounts of bodies due to occupational exposure. Chrysotile bodies and tremolite/anthophyllite bodies were not observed together. We suggest that in Belgium the source of non-commercial amphiboles exposure is not contamination by chrysotile.

Key concepts: Chrysotile, Tremolite, Amphibole, Asbestos, Talc, Population, Mineralogy, Chemistry

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