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Tobacco-specific and combustion pollutants in settled house dust in Malta
AIM: Most of the carcinogenic pollutants coming from tobacco smoking or other combustion processes tend to accumulate in settled house dust (SHD) over time. This study evaluated the load of these pollutants in smokers and non-smokers’ houses from relatively fresh SHD collected in five different dist...
Autores principales: | , , , |
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Formato: | Online Artículo Texto |
Lenguaje: | English |
Publicado: |
2022
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Acceso en línea: | https://www.ncbi.nlm.nih.gov/pmc/articles/PMC9056077/ https://www.ncbi.nlm.nih.gov/pubmed/35497707 http://dx.doi.org/10.20517/jeea.2021.09 |
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author | Aquilina, Noel J. Havel, Christopher M. Benowitz, Neal L. Jacob, Peyton |
author_facet | Aquilina, Noel J. Havel, Christopher M. Benowitz, Neal L. Jacob, Peyton |
author_sort | Aquilina, Noel J. |
collection | PubMed |
description | AIM: Most of the carcinogenic pollutants coming from tobacco smoking or other combustion processes tend to accumulate in settled house dust (SHD) over time. This study evaluated the load of these pollutants in smokers and non-smokers’ houses from relatively fresh SHD collected in five different districts on the island of Malta. METHODS: An improved, efficient extraction method to obtain three fractions from a 200 mg of SHD was developed. It was validated for the analysis of nicotine and polycyclic aromatic hydrocarbons (PAH) by GC-MS/MS and nicotelline and TSNA by LC-MS/MS. Kruskal-Wallis H tests were used to evaluate differences across districts, while a Mann-Whitney U test was used to check differences between smokers and non-smokers’ houses. Diagnostic ratios were used to evaluate the carcinogenicity of PAH in SHD in Malta. RESULTS: For all analytes, no statistical difference was observed across different districts, but, in smokers’ houses, 97.9% of the total concentration of all target analytes found in SHD is nicotine, 0.1% is TSNA, and 2.0% is PAH. In non-smokers’ houses, nicotine represents 16.8% of the load, while 0.4% and 82.8% are TSNA and PAH, respectively. The carcinogenicity of the PAH mixture in Maltese SHD, expressed as the mean benzo(a)pyrene equivalent (BaP(eq)) is 371 ng/g. CONCLUSION: Indoor activities, ventilation practices, and infiltration of outdoor pollutants contribute to a complex SHD composition. Although the BaP(eq) is on the lower end of carcinogenicity, the effects of a mixture including tobacco-related potent carcinogens in SHD are largely unknown. In view of indoor, continuous exposure to SHD through several pathways, further research is warranted. |
format | Online Article Text |
id | pubmed-9056077 |
institution | National Center for Biotechnology Information |
language | English |
publishDate | 2022 |
record_format | MEDLINE/PubMed |
spelling | pubmed-90560772022-04-30 Tobacco-specific and combustion pollutants in settled house dust in Malta Aquilina, Noel J. Havel, Christopher M. Benowitz, Neal L. Jacob, Peyton J Environ Expo Assess Article AIM: Most of the carcinogenic pollutants coming from tobacco smoking or other combustion processes tend to accumulate in settled house dust (SHD) over time. This study evaluated the load of these pollutants in smokers and non-smokers’ houses from relatively fresh SHD collected in five different districts on the island of Malta. METHODS: An improved, efficient extraction method to obtain three fractions from a 200 mg of SHD was developed. It was validated for the analysis of nicotine and polycyclic aromatic hydrocarbons (PAH) by GC-MS/MS and nicotelline and TSNA by LC-MS/MS. Kruskal-Wallis H tests were used to evaluate differences across districts, while a Mann-Whitney U test was used to check differences between smokers and non-smokers’ houses. Diagnostic ratios were used to evaluate the carcinogenicity of PAH in SHD in Malta. RESULTS: For all analytes, no statistical difference was observed across different districts, but, in smokers’ houses, 97.9% of the total concentration of all target analytes found in SHD is nicotine, 0.1% is TSNA, and 2.0% is PAH. In non-smokers’ houses, nicotine represents 16.8% of the load, while 0.4% and 82.8% are TSNA and PAH, respectively. The carcinogenicity of the PAH mixture in Maltese SHD, expressed as the mean benzo(a)pyrene equivalent (BaP(eq)) is 371 ng/g. CONCLUSION: Indoor activities, ventilation practices, and infiltration of outdoor pollutants contribute to a complex SHD composition. Although the BaP(eq) is on the lower end of carcinogenicity, the effects of a mixture including tobacco-related potent carcinogens in SHD are largely unknown. In view of indoor, continuous exposure to SHD through several pathways, further research is warranted. 2022 2022-02-17 /pmc/articles/PMC9056077/ /pubmed/35497707 http://dx.doi.org/10.20517/jeea.2021.09 Text en https://creativecommons.org/licenses/by/4.0/Open Access This article is licensed under a Creative Commons Attribution 4.0 International License (https://creativecommons.org/licenses/by/4.0/), which permits unrestricted use, sharing, adaptation, distribution and reproduction in any medium or format, for any purpose, even commercially, as long as you give appropriate credit to the original author(s) and the source, provide a link to the Creative Commons license, and indicate if changes were made. |
spellingShingle | Article Aquilina, Noel J. Havel, Christopher M. Benowitz, Neal L. Jacob, Peyton Tobacco-specific and combustion pollutants in settled house dust in Malta |
title | Tobacco-specific and combustion pollutants in settled house dust in Malta |
title_full | Tobacco-specific and combustion pollutants in settled house dust in Malta |
title_fullStr | Tobacco-specific and combustion pollutants in settled house dust in Malta |
title_full_unstemmed | Tobacco-specific and combustion pollutants in settled house dust in Malta |
title_short | Tobacco-specific and combustion pollutants in settled house dust in Malta |
title_sort | tobacco-specific and combustion pollutants in settled house dust in malta |
topic | Article |
url | https://www.ncbi.nlm.nih.gov/pmc/articles/PMC9056077/ https://www.ncbi.nlm.nih.gov/pubmed/35497707 http://dx.doi.org/10.20517/jeea.2021.09 |
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