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Spatial analysis of PM.sub.2.5 using a concentration similarity index applied to air quality sensor networks

Air quality sensor (AQS) networks are useful for mapping PM.sub.2.5 (particles with a diameter of 2.5 µm or smaller) in urban environments, but quantitative assessment of the observed spatial and temporal variation is currently underdeveloped. This study introduces a new metric - the concentration...

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Bibliographic Details
Published in:Atmospheric measurement techniques 2024-09, Vol.17 (17), p.5129
Main Authors: Byrne, Rosin, Wenger, John C, Hellebust, Stig
Format: Article
Language:English
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Summary:Air quality sensor (AQS) networks are useful for mapping PM.sub.2.5 (particles with a diameter of 2.5 µm or smaller) in urban environments, but quantitative assessment of the observed spatial and temporal variation is currently underdeveloped. This study introduces a new metric - the concentration similarity index (CSI) - to facilitate a quantitative and time-averaged comparison of the concentration-time profiles of PM.sub.2.5 measured by each sensor within an air quality sensor network. Following development on a dataset with minimal unexplained variation and robust tests, the CSI function is used to represent an unbiased and fair depiction of the air quality variation within an area covered by a monitoring network. The measurement data is used to derive a CSI value for every combination of sensor pairs in the network, yielding valuable information on spatial variation in PM.sub.2.5 . This new method is applied to two separate AQS networks, in Dungarvan and in the city of Cork, Ireland. In Dungarvan there was a lower mean CSI value (x-CSI, Dungarvan=0.61, x-CSI, Cork=0.71), indicating lower overall similarity between locations in the network. In both networks, the average diurnal plots for each sensor exhibit an evening peak in PM.sub.2.5 concentration due to emissions from residential solid-fuel burning; however, there is considerable variation in the size of this peak. Clustering techniques applied to the CSI matrices identify two different location types in each network; locations in central or residential areas that experience more pollution from solid-fuel burning and locations on the edge of the urban areas that experience cleaner air. The difference in mean PM.sub.2.5 between these two location types was 6 µg m.sup.-3 in Dungarvan and 2 µg m.sup.-3 in Cork. Furthermore, the examination of winter and summer months (January and May) indicates that higher PM.sub.2.5 levels during periods of increased residential solid-fuel burning act as a major driver for greater differences (lower similarity indices) between locations in both networks, with differences in mean seasonal CSI values exceeding 0.25 and differences in mean seasonal PM.sub.2.5 exceeding 7 µg m.sup.-3 . These findings underscore the importance of including wintertime PM data in analyses, as the differences between locations is enhanced during periods when solid-fuel burning activities are at a peak. Additionally, the CSI method facilitates the assessment of the representativeness of th
ISSN:1867-1381