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Health risk assessment of gaseous elemental mercury (GEM) in Mexico City

Emissions of gaseous elemental mercury (GEM or Hg(0)) from different sources in urban areas are important subjects for environmental investigations. In this study, atmospheric Hg measurements were conducted to investigate air pollution in the urban environment by carrying out several mobile surveys...

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Autores principales: Schiavo, Benedetto, Morton-Bermea, Ofelia, Salgado-Martínez, Elias, García-Martínez, Rocío, Hernández-Álvarez, Elizabeth
Formato: Online Artículo Texto
Lenguaje:English
Publicado: Springer International Publishing 2022
Materias:
Acceso en línea:https://www.ncbi.nlm.nih.gov/pmc/articles/PMC9130986/
https://www.ncbi.nlm.nih.gov/pubmed/35612636
http://dx.doi.org/10.1007/s10661-022-10107-7
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author Schiavo, Benedetto
Morton-Bermea, Ofelia
Salgado-Martínez, Elias
García-Martínez, Rocío
Hernández-Álvarez, Elizabeth
author_facet Schiavo, Benedetto
Morton-Bermea, Ofelia
Salgado-Martínez, Elias
García-Martínez, Rocío
Hernández-Álvarez, Elizabeth
author_sort Schiavo, Benedetto
collection PubMed
description Emissions of gaseous elemental mercury (GEM or Hg(0)) from different sources in urban areas are important subjects for environmental investigations. In this study, atmospheric Hg measurements were conducted to investigate air pollution in the urban environment by carrying out several mobile surveys in Mexico City. This work presents atmospheric concentrations of GEM in terms of diurnal variation trends and comparisons with criteria for pollutant concentrations such as CO, SO(2), NO(2), PM(2.5), and PM(10). The concentration of GEM was measured during the pre-rainy period by using a high-resolution active air sampler, the Lumex RA 915 M mercury analyzer. In comparison with those for other cities worldwide, the GEM concentrations were similar or slightly elevated, and they ranged from 0.20 to 30.23 ng m(−3). However, the GEM concentration was significantly lower than those in contaminated areas, such as fluorescent lamp factory locations and gold mining zones. The GEM concentrations recorded in Mexico City did not exceed the WHO atmospheric limit of 200 ng m(−3). We performed statistical correlation analysis which suggests equivalent sources between Hg and other atmospheric pollutants, mainly NO(2) and SO(2), emitted from urban combustion and industrial plants. The atmospheric Hg emissions are basically controlled by sunlight radiation, as well as having a direct relationship with meteorological parameters. The area of the city studied herein is characterized by high traffic density, cement production, and municipal solid waste (MSW) treatment, which constantly release GEM into the atmosphere. In this study, we included the simulation with the HYSPLIT dispersion model from three potential areas of GEM release. Emissions from industrial corridors and volcanic plumes localized outside the urban area contribute to the pollution of Mexico City and mainly affect the northern area during specific periods and climate conditions. Using the USEPA model, we assessed the human health risk resulting from exposure to inhaled GEM among residents of Mexico City. The results of the health risk assessment indicated no significant noncarcinogenic risk (hazard quotient (HQ) < 1) or consequent adverse effects for children and adults living in the sampling area over the study period. GEM emissions inventory data is necessary to improve our knowledge about the Hg contribution and effect in urban megacity areas with the objective to develop public safe policy and implementing the Minamata Convention. SUPPLEMENTARY INFORMATION: The online version contains supplementary material available at 10.1007/s10661-022-10107-7.
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spelling pubmed-91309862022-05-25 Health risk assessment of gaseous elemental mercury (GEM) in Mexico City Schiavo, Benedetto Morton-Bermea, Ofelia Salgado-Martínez, Elias García-Martínez, Rocío Hernández-Álvarez, Elizabeth Environ Monit Assess Article Emissions of gaseous elemental mercury (GEM or Hg(0)) from different sources in urban areas are important subjects for environmental investigations. In this study, atmospheric Hg measurements were conducted to investigate air pollution in the urban environment by carrying out several mobile surveys in Mexico City. This work presents atmospheric concentrations of GEM in terms of diurnal variation trends and comparisons with criteria for pollutant concentrations such as CO, SO(2), NO(2), PM(2.5), and PM(10). The concentration of GEM was measured during the pre-rainy period by using a high-resolution active air sampler, the Lumex RA 915 M mercury analyzer. In comparison with those for other cities worldwide, the GEM concentrations were similar or slightly elevated, and they ranged from 0.20 to 30.23 ng m(−3). However, the GEM concentration was significantly lower than those in contaminated areas, such as fluorescent lamp factory locations and gold mining zones. The GEM concentrations recorded in Mexico City did not exceed the WHO atmospheric limit of 200 ng m(−3). We performed statistical correlation analysis which suggests equivalent sources between Hg and other atmospheric pollutants, mainly NO(2) and SO(2), emitted from urban combustion and industrial plants. The atmospheric Hg emissions are basically controlled by sunlight radiation, as well as having a direct relationship with meteorological parameters. The area of the city studied herein is characterized by high traffic density, cement production, and municipal solid waste (MSW) treatment, which constantly release GEM into the atmosphere. In this study, we included the simulation with the HYSPLIT dispersion model from three potential areas of GEM release. Emissions from industrial corridors and volcanic plumes localized outside the urban area contribute to the pollution of Mexico City and mainly affect the northern area during specific periods and climate conditions. Using the USEPA model, we assessed the human health risk resulting from exposure to inhaled GEM among residents of Mexico City. The results of the health risk assessment indicated no significant noncarcinogenic risk (hazard quotient (HQ) < 1) or consequent adverse effects for children and adults living in the sampling area over the study period. GEM emissions inventory data is necessary to improve our knowledge about the Hg contribution and effect in urban megacity areas with the objective to develop public safe policy and implementing the Minamata Convention. SUPPLEMENTARY INFORMATION: The online version contains supplementary material available at 10.1007/s10661-022-10107-7. Springer International Publishing 2022-05-25 2022 /pmc/articles/PMC9130986/ /pubmed/35612636 http://dx.doi.org/10.1007/s10661-022-10107-7 Text en © The Author(s), under exclusive licence to Springer Nature Switzerland AG 2022 This article is made available via the PMC Open Access Subset for unrestricted research re-use and secondary analysis in any form or by any means with acknowledgement of the original source. These permissions are granted for the duration of the World Health Organization (WHO) declaration of COVID-19 as a global pandemic.
spellingShingle Article
Schiavo, Benedetto
Morton-Bermea, Ofelia
Salgado-Martínez, Elias
García-Martínez, Rocío
Hernández-Álvarez, Elizabeth
Health risk assessment of gaseous elemental mercury (GEM) in Mexico City
title Health risk assessment of gaseous elemental mercury (GEM) in Mexico City
title_full Health risk assessment of gaseous elemental mercury (GEM) in Mexico City
title_fullStr Health risk assessment of gaseous elemental mercury (GEM) in Mexico City
title_full_unstemmed Health risk assessment of gaseous elemental mercury (GEM) in Mexico City
title_short Health risk assessment of gaseous elemental mercury (GEM) in Mexico City
title_sort health risk assessment of gaseous elemental mercury (gem) in mexico city
topic Article
url https://www.ncbi.nlm.nih.gov/pmc/articles/PMC9130986/
https://www.ncbi.nlm.nih.gov/pubmed/35612636
http://dx.doi.org/10.1007/s10661-022-10107-7
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