Elsevier

Environmental Pollution

Volume 269, 15 January 2021, 116124
Environmental Pollution

Assessment and statistical modelling of airborne microorganisms in Madrid

https://doi.org/10.1016/j.envpol.2020.116124Get rights and content

Highlights

  • High temperature favours Actinobacteria/Proteobacteria relative abundance ratio.

  • Microbial relative abundance correlates with PM10 and O3 in some cases.

  • Proteobacteria show a positive correlation with pollen.

  • Generalized Additive Models (GAM) able to capture non-linear relationships.

  • Coefficient of determination up to 0.76 for microbial relative abundances predictions.

Abstract

The limited evidence available suggests that the interaction between chemical pollutants and biological particles may intensify respiratory diseases caused by air pollution in urban areas. Unlike air pollutants, which are routinely measured, records of biotic component are scarce. While pollen concentrations are daily surveyed in most cities, data related to airborne bacteria or fungi are not usually available. This work presents the first effort to understand atmospheric pollution integrating both biotic and abiotic agents, trying to identify relationships among the Proteobacteria, Actinobacteria and Ascomycota phyla with palynological, meteorological and air quality variables using all biological historical records available in the Madrid Greater Region. The tools employed involve statistical hypothesis contrast tests such as Kruskal-Wallis and machine learning algorithms. A cluster analysis was performed to analyse which abiotic variables were able to separate the biotic variables into groups. Significant relationships were found for temperature and relative humidity. In addition, the relative abundance of the biological phyla studied was affected by PM10 and O3 ambient concentration. Preliminary Generalized Additive Models (GAMs) to predict the biotic relative abundances based on these atmospheric variables were developed. The results (r = 0.70) were acceptable taking into account the scarcity of the available data. These models can be used as an indication of the biotic composition when no measurements are available. They are also a good starting point to continue working in the development of more accurate models and to investigate causal relationships.

Introduction

Mortality and morbidity are associated with poor air quality through a breadth of respiratory causes, including cardiovascular diseases and lung cancer (WHO, 2016). Up to 8.9 million excess deaths are attributed to long-term exposure to outdoor PM2.5 (particulate matter with an average aerodynamic diameter of up to 2.5 μm) alone (Burnett et al., 2018). Moreover, the contribution of air pollution to premature mortality could double by 2050 (Lelieveld et al., 2015). Air pollution has significant impacts all over the world, including Europe. Over 500000 premature annual deaths are attributed to population exposure to PM2.5, NO2 (nitrogen dioxide) and O3 (ozone) in Europe (EEA, 2019). Further reductions or ambient concentrations of these pollutants would bring considerable health benefits in major urban areas including Madrid (Izquierdo et al., 2020).

In addition to traditional abiotic air pollutants (PM, NO2, SO2 (sulphur dioxide), O3, etc.), the presence of airborne biological particles is gaining interest within the air quality field since they also pose a risk for human health. Many fungal spores present in the air (Cladosporium spp, Epiccocum spp., Alternaria spp., Aspergillus spp.) cause allergic asthma (Vacher et al., 2015), which in combination with pollen allergies affect several million people around the world (Bousquet et al., 2008). Although the knowledge in the field remains insufficient to reach conclusions, current evidence suggests that the interaction between chemical pollutants and biological particles would intensify respiratory diseases such as asthma, allergic rhinitis and bacterial infection (Baldacci et al., 2015), and also induce changes in lung microbiota (Yang et al., 2019).

Accordingly, the European Union has incorporated new documents about pollen and fungal spores sampling normalization in ambient air because of their association with allergy (European Technical Specification note CEN/TS 16868:2019; and British adaptation BS EN 16868:2019). Furthermore, pathogenic bacteria such as Legionella pneumophila (Legionnaires’ disease), Mycobacterium tuberculosis (tuberculosis) or Haemophilus influenzae (pneumonia, meningitis) are transmitted via aerosols. Moreover, recent studies have also stated that pollen grains, another major biotic component of the air, not only may reduce the immune response to other pathogens like viruses (Gilles et al., 2020) but also act as important carriers of bacteria and endotoxins (bacterial antigens), promoting the allergic sensitization to pollen (Obersteiner et al., 2016; Oteros et al., 2019).

While pollen concentrations are daily monitored in the urban areas to publish alerts related to allergy for the population, airborne fungi and bacteria are not routinely analysed in most cities. The processing and identification of airborne microorganisms requires expertise, it is time-consuming and costly (especially for bacteria). New technologies based on DNA sequencing (Next-generation sequencing/high-throughput sequencing) have enabled a more accurate identification of these entities from environmental samples. Thus, specific works have characterized the microbial component (bacteria and/or fungi) in the urban atmosphere (Bertolini et al., 2013; Bowers et al., 2013; Du et al., 2018; Fan et al., 2019a; Gandolfi et al., 2015; Lee et al., 2017; Lu et al., 2018; Núñez et al., 2019; Uetake et al., 2019; Yamamoto et al., 2012; Yan et al., 2016, 2018; Zhen et al., 2017). These studies consistently point out that biological diversity present in the air is wider than previously thought, but no conclusive relationships have been stated with the abiotic variables, mostly because of the large number of factors involved (local sources, microenvironments, seasonality, meteorology, long-distance transport, etc.) and the lack of long-term studies (Núñez et al., 2016; Zhai et al., 2018). They frequently correlate chemical pollutants, environmental and meteorological factors with the microbial communities, providing general tendencies. For instance, Wei et al. (2020) discovered that a moderately polluted atmosphere promoted the microbial growth due to higher nutrients availability. Some works also attempted to develop predictive models, mostly using Multiple Linear Regression for fungi (Molina et al., 1998; Pyrri and Kapsanaki-Gotsi, 2017; Recio et al., 2012), or more sophisticated non-linear algorithms for bacteria (Fan et al., 2019b; Yoo et al., 2018).

The main objective of the present work, part of the AIRTEC-CM (urban air quality and climate change integral assessment) research project, is to obtain a wider vision of the atmospheric pollution in Madrid (Spain) by discovering potential relationships among abiotic and biotic pollutants and environmental variables. In this first approach, we made use of all the available observations of biotic agents in Madrid (Proteobacteria, Actinobacteria, Ascomycota relative abundance) and records of the main allergenic pollen types: “Cupressaceae”, “Olea”, “Platanus”, “Poaceae”) in addition to meteorological and air quality data. We performed a number of statistical analyses, including clustering techniques to identify significant relationships. Finally, we fitted Generalized Additive Models (GAMs) that could be used to predict biotic components relative abundance in the absence of conventional DNA analyses, usually unavailable.

Section snippets

Materials and methods

This study relies on the analysis of historical records of biotic and abiotic variables obtained from different sources and locations within the Madrid Greater Region (Community of Madrid) shown in Fig. S1 within the supplementary material. Observations of the main airborne biotic agents (bacteria, fungi and pollen) were collected at 10 locations (Table S1 in supplementary material). These monitoring points belong to the aeropalynological network of Madrid PALINOCAM where pollen is routinely

Descriptive statistics

Firstly, as part of Stage 0 and in order to have an overview of the data, we analysed the distributions of the relative abundances (%) of the biotic phyla studied (bacteria: Proteobacteria, Actinobacteria; fungi: Ascomycota). While they resemble a normal distribution for Proteobacteria N(31.2, 9.4) and Actinobacteria N(21.0, 6.8), a dispersed pattern that could be interpreted as a bi-normal distribution was observed for the fungal group Ascomycota (Supplementary Information Fig. S2).

Next, we

Discussion

The descriptive Stage 0 identified T, RH, PM10 as predictors of the airborne microbial abundances; while others seem to intervene only for particular groups like O3 or specific pollen grains. Previous studies described T and RH as the main drivers for airborne microbial communities in urban environments (Adhikari et al., 2006; Bowers et al., 2013; Díez Herrero et al., 2006; Fan et al., 2019a; Genitsaris et al., 2017; Gioulekas et al., 2004; Kowalski and Pastuszka, 2018; Lee et al., 2017; Liu

Conclusions

We found significant relationships between the relative abundance of Proteobacteria, Actinobacteria and Ascomycota, and environmental variables (T and RH) and air pollutants (PM10 and O3). These meteorological and air quality variables, with much higher availability than biological records, can be used as predictors of the airborne microbial abundances. Interestingly, palynological data can contribute significantly to build predictive models and should be appended to improve such models when

Credit author statement

José María Cordero: Software, Validation, Formal analysis, Data Curation, Writing - Original Draft, Visualization. Andrés Núñez: Formal analysis. Investigation, Resources, Data Curation, Writing - Original Draft. Ana M. García: Conceptualization, Investigation, Resources, Writing - Review & Editing. Rafael Borge: Conceptualization, Validation, Writing - Review & Editing, Supervision, Funding acquisition.

Declaration of competing interest

The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.

Acknowledgements

This study was carried out within the AIRTEC-CM (urban air quality and climate change integral assessment) scientific project funded by the Directorate General for Universities and Research of the Madrid Greater Region (S2018/EMT-4329) and it made use of bacteria and fungi data from the AIRBIOTA-CM (S2013/MAE-2874) programme. We thank our colleagues Adolfo Narros, A. Montserrat Gutiérrez-Bustillo, David de la Paz and Diego A. Moreno for their valuable contributions to this multi-disciplinary

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