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[1] O ccupational Exposure to Titanium Dioxide. Current Intelligence Bulletin 63. Department of Health and Human Services, Centers for Disease Control and Prevention, National Institute for Occupational Safety and Health DHHS (NIOSH) Publication No. 2011–160. Published online 2011, available at https://www.cdc.gov/niosh/docs/2011-160/pdfs/2011-160.pdf (accessed 17 February 2019).
[2] S widwińska-Gajewska AM & Czerczak S., Titanium dioxide nanoparticles: occupational exposure limits, MEDICAL – Prestigious, 65(3), pp. 407–418, 2014
[3] S tockmann-Juvala, H., Taxell, P. & Tiina Santonen, T., Formulating exposure limits values (OELs) (Inhalation & dermal), Scaffold Public Documents - Ref.: Scaffold SPD7, 30 Apr. 2014. Published online 2014, available at http://scaffold.eu-vri.eu/filehandler. ashx?file=13717 (accessed 17 February 2019).
[4] van Broekhuizen, P., van Veelen, W., Streekstra, W.-H., Schulte, P. & Rejinders, L., Exposure limits for nanoparticles: report of an international workshop on nano reference values. The Annals of Occupational Hygiene, 56(5), pp. 515–524, 2012. [Crossref]
[5] G orbunov B., Muir R. & Jackson P., Aerosol and Air Quality Research, 13, pp. 1678–1692, 2013. ISSN: 1680-8584 print / 2071-1409 online. [Crossref]
[6] Würth B., Emissions of engineered and unintentionally produced nanoparticles to the soil an exposure assessment for Switzerland. Diploma thesis. 2007. ETH Zurich Department of Environmental Sciences. online. [Crossref]
[7] F ito-López, C., Domat-Rodriguez, M., Van Tongeren, M. & Spankie, S. Nanoparticle release in indoor workplaces: emission sources, release determinants and release categories based on workplace measurements. The Handbook of Environmental Chemistry, vol 48. Springer, Cham, pp. 93–126. [Crossref]
[8] Voliotis, A. & Bezantakos, S., et al., Nanoparticle emissions from traditional pottery manufacturing. Environmental Science: Processes & Impacts, 16, pp. 1489–1494, 2014.
[9] Wake, D., Mark, D. & Northage, C., Ultrafine aerosols in the workplace. Annals of Occupational Hygiene, 46(supplement 1), pp. 235–238, 2002. [Crossref]
[10] H irtle, B., Teschke, K., Van Netten, C. & Brauer, M., Kiln Emission and Pottterrs‘ Exposures. American Industrial Hygiene Association Journal, 59, pp. 706–714, 1998.
[11] ICRP , International Commission on Radiological Protection. Human Respiratory Tract Model for Radiological Protection. Annals of the ICRP, Publication 66 Tarrytown, E lsevier Science Inc., N.Y., 1994
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Open Access
Research article

The Emission of Ultrafine Particles in the Manufacture of Fireplace Ceramic Tiles

Karel Lach,
Ivona Smolová
Institute of Public Health Ostrava, Czech Republic
International Journal of Environmental Impacts
|
Volume 2, Issue 4, 2019
|
Pages 325-335
Received: N/A,
Revised: N/A,
Accepted: N/A,
Available online: N/A
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Abstract:

Studies in the field of the adverse effect of inhaled particles show that not only particle mass is crucial but also particle size and specific surface are. The main objective of this study was to investigate and characterise ultrafine particle (UFP) emissions on workplace in the manufacture of ceramic tiles at two problematic places - at ceramic tiles kiln and spraying glazing suspension. The process of creating of glaze on the surface of stove tiles is performed at temperatures reaching up to 1,100oC. At this high temperature occurs fugitive emissions from glaze and ceramic consist of vapours and UFP containing various heavy metals such as Pb, Cr, Cu, Mo, Zr, etc. from glaze and ceramic, respectively. The data obtained from the measurements confirmed the significant emissions of UFP at the two chosen workplaces, but the composition of particles, their size distribution and other parameters differed from one to another. In case of the workplace near the kiln, the following parameters were noted: total concentration of particles ranging from 5.6 nm to 560 nm is 2×105–4×105 N/cm3; median of size distribution is 37 nm, median of mass distribution is 153 nm, particle surface deposited in tracheobronchial (TB) part of lungs is 200 μm2/cm3, particle surface deposited in alveolar (A) part of lungs is 450 μm2/cm3 and the concentration of Pb is 3,744 μg/m3. In the case of the manual spraying of the glaze suspension on tiles, the following parameters were noted: total concentration of particles is 2×105 N/cm3; median of size distribution is 11 nm, median of mass distribution is 177 nm, particle surface deposited in TB part of lungs is 50 μm2/cm3, particle surface deposited in A part of lungs is 170 μm2/cm3 and the concentration of Pb is 1.9 μg/m3. It can be concluded from the data above that both the measured workplaces meet the permissible exposure limit for lead, which is 50 μg/m3. It is important to note that, in this study, the health impacts of UFP on staff and employees were not studied.

Keywords: air emission, heavy metals, lead, pottery kiln emissions, scanning electron microscopy, size resolved sampling, solid aerosols, ultrafine particles.

Data Availability

The data used to support the findings of this study are available from the corresponding author upon request.

Conflicts of Interest

The authors declare that they have no conflicts of interest.

References
[1] O ccupational Exposure to Titanium Dioxide. Current Intelligence Bulletin 63. Department of Health and Human Services, Centers for Disease Control and Prevention, National Institute for Occupational Safety and Health DHHS (NIOSH) Publication No. 2011–160. Published online 2011, available at https://www.cdc.gov/niosh/docs/2011-160/pdfs/2011-160.pdf (accessed 17 February 2019).
[2] S widwińska-Gajewska AM & Czerczak S., Titanium dioxide nanoparticles: occupational exposure limits, MEDICAL – Prestigious, 65(3), pp. 407–418, 2014
[3] S tockmann-Juvala, H., Taxell, P. & Tiina Santonen, T., Formulating exposure limits values (OELs) (Inhalation & dermal), Scaffold Public Documents - Ref.: Scaffold SPD7, 30 Apr. 2014. Published online 2014, available at http://scaffold.eu-vri.eu/filehandler. ashx?file=13717 (accessed 17 February 2019).
[4] van Broekhuizen, P., van Veelen, W., Streekstra, W.-H., Schulte, P. & Rejinders, L., Exposure limits for nanoparticles: report of an international workshop on nano reference values. The Annals of Occupational Hygiene, 56(5), pp. 515–524, 2012. [Crossref]
[5] G orbunov B., Muir R. & Jackson P., Aerosol and Air Quality Research, 13, pp. 1678–1692, 2013. ISSN: 1680-8584 print / 2071-1409 online. [Crossref]
[6] Würth B., Emissions of engineered and unintentionally produced nanoparticles to the soil an exposure assessment for Switzerland. Diploma thesis. 2007. ETH Zurich Department of Environmental Sciences. online. [Crossref]
[7] F ito-López, C., Domat-Rodriguez, M., Van Tongeren, M. & Spankie, S. Nanoparticle release in indoor workplaces: emission sources, release determinants and release categories based on workplace measurements. The Handbook of Environmental Chemistry, vol 48. Springer, Cham, pp. 93–126. [Crossref]
[8] Voliotis, A. & Bezantakos, S., et al., Nanoparticle emissions from traditional pottery manufacturing. Environmental Science: Processes & Impacts, 16, pp. 1489–1494, 2014.
[9] Wake, D., Mark, D. & Northage, C., Ultrafine aerosols in the workplace. Annals of Occupational Hygiene, 46(supplement 1), pp. 235–238, 2002. [Crossref]
[10] H irtle, B., Teschke, K., Van Netten, C. & Brauer, M., Kiln Emission and Pottterrs‘ Exposures. American Industrial Hygiene Association Journal, 59, pp. 706–714, 1998.
[11] ICRP , International Commission on Radiological Protection. Human Respiratory Tract Model for Radiological Protection. Annals of the ICRP, Publication 66 Tarrytown, E lsevier Science Inc., N.Y., 1994

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Lach, K. & Smolová, I. (2019). The Emission of Ultrafine Particles in the Manufacture of Fireplace Ceramic Tiles. Int. J. Environ. Impacts., 2(4), 325-335. https://doi.org/10.2495/EI-V2-N4-325-335
K. Lach and I. Smolová, "The Emission of Ultrafine Particles in the Manufacture of Fireplace Ceramic Tiles," Int. J. Environ. Impacts., vol. 2, no. 4, pp. 325-335, 2019. https://doi.org/10.2495/EI-V2-N4-325-335
@research-article{Lach2019TheEO,
title={The Emission of Ultrafine Particles in the Manufacture of Fireplace Ceramic Tiles},
author={Karel Lach and Ivona Smolová},
journal={International Journal of Environmental Impacts},
year={2019},
page={325-335},
doi={https://doi.org/10.2495/EI-V2-N4-325-335}
}
Karel Lach, et al. "The Emission of Ultrafine Particles in the Manufacture of Fireplace Ceramic Tiles." International Journal of Environmental Impacts, v 2, pp 325-335. doi: https://doi.org/10.2495/EI-V2-N4-325-335
Karel Lach and Ivona Smolová. "The Emission of Ultrafine Particles in the Manufacture of Fireplace Ceramic Tiles." International Journal of Environmental Impacts, 2, (2019): 325-335. doi: https://doi.org/10.2495/EI-V2-N4-325-335
LACH K, SMOLOVÁ I. The Emission of Ultrafine Particles in the Manufacture of Fireplace Ceramic Tiles[J]. International Journal of Environmental Impacts, 2019, 2(4): 325-335. https://doi.org/10.2495/EI-V2-N4-325-335