Occupational exposure to chrysotile in an asbestos cement factory in Kyrgyzstan

Author:

Kurzhunbaeva Zhyldyz1,Spinazzè Andrea2ORCID,Campagnolo Davide2,Rovelli Sabrina2,Fanti Giacomo2,Kasymov Omor3,Cattaneo Andrea2ORCID,Colosio Claudio4,Cavallo Domenico M2

Affiliation:

1. Department of Health Sciences; Course of Research Doctorate in Public Health Sciences, University of Milan , via di Rudinì, 8, 20142 Milan , Italy

2. Department of Science and High Technology, University of Insubria , via Valleggio 11, 22100 Como , Italy

3. National Institute of Public Health under the Ministry of Health of the Kyrgyz Republic , st. Akhunbaeva 92, Bishkek , Kyrgyz Republic

4. Department of Health Sciences, University of Milan, Occupational Health Unit & International Centre for Rural Health of the Santi Paolo and Carlo Hospitals , via di Rudinì, 8, 20142 Milan , Italy

Abstract

Abstract Objectives An increasing number of countries are banning the production and use of asbestos, in compliance with the ratification of the C162 Asbestos Convention and the Basel Convention, and in response to the call for its elimination in the ILO resolution and WHO reports on the health risks associated with asbestos. Nevertheless, several countries, including Kyrgyzstan, are still miners and/or manufacturers of asbestos. The main objective of the study is to assess the occupational exposure to chrysotile of workers engaged in a production facility of asbestos-cement products in Kyrgyzstan. Methods Monitored workers (n = 16, for a total of n = 18 samples) were divided into 3 “Similar Exposure Groups” (SEGs; SEG-1: asbestos loading; SEG-2; asbestos-cement mixing; SEG-3: cutting of asbestos-cement sheets) according to EN 689 standard. Samples were collected through personal sampling and subsequently examined by means of scanning electron microscope equipped with an energy-dispersive spectrometer for the compositional analysis of each fibre. The numerical concentration of airborne asbestos fibres was henceforward determined by dividing the number of fibres and the volume of sampled air (expressed in the number of fibres per millilitre of air: ff/ml). Results Investigated workers resulted to be exposed to chrysotile fibres. Results (GM ± GSD) outlined extremely high exposure levels for SEG-1 (2.2 ± 2.1 ff/ml) and SEG-3 (4.7 ± 1.6 ff/ml) workers and lower—but still relevant—exposure values for SEG-2 (0.91 ± 2.6 ff/ml) workers. Conclusions The results obtained in this case study can help to document potentially critical situations of occupational exposure to asbestos that can still occur nowadays in low and middle-income countries where asbestos is still mined and processed.

Publisher

Oxford University Press (OUP)

Reference32 articles.

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2. History of knowledge and evolution of occupational health and regulatory aspects of asbestos exposure science: 1900–1975;Barlow;Crit Rev Toxicol,2017

3. Testing Compliance with Occupational Exposure Limits for Airborne Substances;British Occupational Hygiene Society (BOHS) and Nederlandse Vereniging voor Arbeidshygiëne (NVvA),2022

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