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EDITORIAL article

Front. Environ. Sci., 04 January 2022
Sec. Toxicology, Pollution and the Environment
This article is part of the Research Topic Physicochemical Characterization of Aerosols in Diverse Environments and Climatic Conditions View all 5 articles

Editorial: Physicochemical Characterization of Aerosols in Diverse Environments and Climatic Conditions

  • 1Laboratory of Atmospheric Chemistry, Paul Scherrer Institute, Villigen, Switzerland
  • 2Environmental Radioactivity Laboratory, INRASTES, NCSR Demokritos, Athens, Greece
  • 3MRC Centre for Environment and Health, Environmental Research Group, Imperial College London, London, United Kingdom
  • 4HPRU in Environmental Exposures and Health, Imperial College London, London, United Kingdom

This research topic gathers a number of contributions that describe the effects of emission sources on the atmospheric concentrations of gaseous pollutants and aerosols, as well as results and methods for the physicochemical characterization of aerosol samples. The studies that were included in the topic took place in Thailand, China, UAE (United Arab Emirates), and Brazil, providing data from very different environments.

The first study tackles the issue of smoke haze pollution in Northern Thailand (Khodmanee and Amnuaylojaroen). Biomass burning is a significant source of O3 and its precursors in Southeast Asia. The target of the study was to quantify the impact of biomass burning on the surface concentration levels of O3, CO, and NO2 in Northern Thailand, using a modeling procedure. Specifically, the authors used the Weather Research and Forecasting Model with Chemistry (WRF-Chem, version 3.8.1). The model simulations were conducted for two scenarios: 1) simulations including biomass burning related emissions; and 2) simulations excluding biomass burning related emissions. A comparison of WRF-CHEM results for the aforementioned two scenarios indicated an increase in O3, CO, and NOx levels due to biomass burning. Biomass combustion contributed by over 60% to CO and NO2 concentration levels through direct emissions, and by approximately 7% to surface O3 levels, through indirect effects. The model’s performance was evaluated by comparing modeled precipitation and temperature (at 2 m) and modeled O3, CO, and NO2 concentrations to ground-level measurements made by the Pollution Control Department of Thailand.

A fundamental characteristic of ambient particulate matter is its size distribution, which determines its physicochemical and optical properties and can also reflect the variability in local and regional sources and formation mechanisms. In Khan et al., different PM components’ size distributions (carbonaceous, ionic, elemental, and saccharide species) were investigated, through size segregated PM samples (PM1, PM1–2.5, and PM2.5–10) collected in Tianjin, China. The carbonaceous and ionic species exhibited bimodal distribution, with a higher presence in the fine mass fraction (PM1) than coarse (PM2.5–10). The elemental species exhibited unimodal distribution and were primarily distributed to the coarse size fraction of PM. The saccharide species showed different size distributions depending on their dominant emission sources. Glucose, fructose, and arabitol had a unimodal size distribution to the coarse size fraction of PM, indicating biogenic contributions as the dominant emission source. On the contrary, levoglucosan’s bimodal mass size distribution (fine and coarse size fractions) indicated the significance of biomass burning-related emission in its ambient concentration.

The Middle East and North Africa are regions with increased particulate pollution due to anthropogenic (increased fossil fuel burning and other activities) and natural sources (dust storms). In the study of Hamdan et al., that took place in Sharjah, UAE, the authors present results on the PM chemical composition using various analytical techniques (x-ray fluorescence, XRF, x-ray diffraction, XRD, scanning electron microscopy, energy dispersive spectroscopy, SEM/EDS, and Multi-wavelength Absorption Black Carbon Instrument, MABI). The average mass concentration of PM10 during the cold season was 137 μg/m3, while it was 210 μg/m3 during the warm season. The warm season is associated with more frequent dust storm events, which are a significant source of PM10 in the region. XRF results indicated that the elements related to dust, such as Si, Ca, Al, and Fe, have high seasonal variation, with higher concentrations during the warm period (due to the dust storms), while other elements that originate from anthropogenic sources, such as S, displayed no seasonal variation. As dust was the source with the highest contribution, XRD, SEM, and EDS elemental maps were used to identify different mineral phases present in PM10. Calcite, quartz, gypsum, halite, and nitratine were the most commonly observed phases in both the XRD and the elemental maps for most of the samples. Other minerals, such as palygorskite and chlorite-serpentine, were also observed in the XRD patterns. In addition to these natural minerals, secondary phases such as mascagnite and koktaite were also observed in most samples.

Several studies have indicated that the carcinogenic potential of PM is mainly due to the presence of polycyclic aromatic hydrocarbons (PAHs) and their oxy- and nitro-PAH derivatives. In the study of Scaramboni et al., the authors describe the optimization of an extraction method using small solvent volumes, for simultaneous determination of PAHs and their oxy- and nitro-derivatives by GC-MS. Additionally, they investigate the application of the methodology for the simultaneous extraction of levoglucosan. The method, which is based on ultrasonic extraction, is both simpler and faster when compared to other extraction techniques, such as Soxhlet refluxing. By following this approach, it was possible to reduce the required solvent volume by 97%, with no need to use the potentially hazardous solvent dichloromethane. The accuracy and precision were good, with low limits of quantification. The method can be applied to samples collected by both high- and low-volume samplers, and it is a good alternative to the most commonly used procedures.

This compilation of articles illustrates the wide range of techniques and methodological approaches that can be used for the study of particulate-related pollution specifically and air pollution in general, as well as the synergies between different techniques.

Author Contributions

All authors listed have made a substantial, direct, and intellectual contribution to the work and approved it for publication.

Conflict of Interest

The authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.

Publisher’s Note

All claims expressed in this article are solely those of the authors and do not necessarily represent those of their affiliated organizations, or those of the publisher, the editors and the reviewers. Any product that may be evaluated in this article, or claim that may be made by its manufacturer, is not guaranteed or endorsed by the publisher.

Keywords: air pollution, aerosols, PM composition, ozone, PAHs

Citation: Manousakas M, Diapouli E and Tremper AH (2022) Editorial: Physicochemical Characterization of Aerosols in Diverse Environments and Climatic Conditions. Front. Environ. Sci. 9:832499. doi: 10.3389/fenvs.2021.832499

Received: 09 December 2021; Accepted: 13 December 2021;
Published: 04 January 2022.

Edited and reviewed by:

Oladele Ogunseitan, University of California, Irvine, United States

Copyright © 2022 Manousakas, Diapouli and Tremper. This is an open-access article distributed under the terms of the Creative Commons Attribution License (CC BY). The use, distribution or reproduction in other forums is permitted, provided the original author(s) and the copyright owner(s) are credited and that the original publication in this journal is cited, in accordance with accepted academic practice. No use, distribution or reproduction is permitted which does not comply with these terms.

*Correspondence: M. Manousakas, manousos.manousakas@psi.ch

Disclaimer: All claims expressed in this article are solely those of the authors and do not necessarily represent those of their affiliated organizations, or those of the publisher, the editors and the reviewers. Any product that may be evaluated in this article or claim that may be made by its manufacturer is not guaranteed or endorsed by the publisher.