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. 2012 Oct;6(10):1801-11.
doi: 10.1038/ismej.2012.30. Epub 2012 Apr 5.

Particle-size distributions and seasonal diversity of allergenic and pathogenic fungi in outdoor air

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Particle-size distributions and seasonal diversity of allergenic and pathogenic fungi in outdoor air

Naomichi Yamamoto et al. ISME J. 2012 Oct.

Abstract

Fungi are ubiquitous in outdoor air, and their concentration, aerodynamic diameters and taxonomic composition have potentially important implications for human health. Although exposure to fungal allergens is considered a strong risk factor for asthma prevalence and severity, limitations in tracking fungal diversity in air have thus far prevented a clear understanding of their human pathogenic properties. This study used a cascade impactor for sampling, and quantitative real-time PCR plus 454 pyrosequencing for analysis to investigate seasonal, size-resolved fungal communities in outdoor air in an urban setting in the northeastern United States. From the 20 libraries produced with an average of ∼800 internal transcribed spacer (ITS) sequences (total 15 326 reads), 12 864 and 11 280 sequences were determined to the genus and species levels, respectively, and 558 different genera and 1172 different species were identified, including allergens and infectious pathogens. These analyses revealed strong relationships between fungal aerodynamic diameters and features of taxonomic compositions. The relative abundance of airborne allergenic fungi ranged from 2.8% to 10.7% of total airborne fungal taxa, peaked in the fall, and increased with increasing aerodynamic diameter. Fungi that can cause invasive fungal infections peaked in the spring, comprised 0.1-1.6% of fungal taxa and typically increased in relative abundance with decreasing aerodynamic diameter. Atmospheric fungal ecology is a strong function of aerodynamic diameter, whereby through physical processes, the size influences the diversity of airborne fungi that deposit in human airways and the efficiencies with which specific groups of fungi partition from outdoor air to indoor environments.

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Figures

Figure 1
Figure 1
ITS-based proportional distributions of atmospheric fungal phyla (a). Fungal class proportional distribution of the Ascomycota phylum (b). Fungal order proportional distribution of the Basidiomycota phylum (c). *Greater than 95% of Basidiomycota belonged to the Agaricomycetes class, thus order-level classification was used to provide additional higher-level taxonomic information.
Figure 2
Figure 2
Relative abundances of fungal genera identified in the atmosphere. The most abundant fungal genera, genera containing known allergens (in red) and genera containing infectious pathogenic species (underlined) are listed. A tree was constructed based on taxonomic classifications provided by Index Fungorum. Seven taxonomic levels, that is, phylum, subphylum, class, subclass, order, family and genus, are used to define nodes of the tree. The allergenic and pathogenic genera are defined as genera with allergenic or pathogenic species listed in Supplementary Tables 3 and 4, respectively. Genera shown represent 56% of the outdoor air sequences.
Figure 3
Figure 3
Relative abundances of total allergenic (a) and pathogenic (b) fungal species. The allergenic and pathogenic genera are defined as genera with allergenic or pathogenic species listed in Supplementary Tables 3 and 4, respectively. Average values indicate means of the relative abundances of all particle sizes.
Figure 4
Figure 4
The seasonal particle-size distributions of airborne fungi determined by qPCR (y axis, ΔN/Δlog da (cell m−3)). An upper limit of particle size for the stage of >9.0 μm is set at 20 μm to calculate geometric means of aerodynamic diameter (dg) and geometric s.d. (σg) of particle-size distributions of airborne fungi. The abbreviation n.d. means ‘not determined' owing to the skewed particle-size distributions.

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