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Phenomenology of ultrafine particle concentrations and size distribution across urban Europe

Authors :
Pedro Trechera
Meritxell Garcia-Marlès
Xiansheng Liu
Cristina Reche
Noemí Pérez
Marjan Savadkoohi
David Beddows
Imre Salma
Máté Vörösmarty
Andrea Casans
Juan Andrés Casquero-Vera
Christoph Hueglin
Nicolas Marchand
Benjamin Chazeau
Grégory Gille
Panayiotis Kalkavouras
Nikos Mihalopoulos
Jakub Ondracek
Nadia Zikova
Jarkko V. Niemi
Hanna E. Manninen
David C. Green
Anja H. Tremper
Michael Norman
Stergios Vratolis
Konstantinos Eleftheriadis
Francisco J. Gómez-Moreno
Elisabeth Alonso-Blanco
Holger Gerwig
Alfred Wiedensohler
Kay Weinhold
Maik Merkel
Susanne Bastian
Jean-Eudes Petit
Olivier Favez
Suzanne Crumeyrolle
Nicolas Ferlay
Sebastiao Martins Dos Santos
Jean-Philippe Putaud
Hilkka Timonen
Janne Lampilahti
Christof Asbach
Carmen Wolf
Heinz Kaminski
Hicran Altug
Barbara Hoffmann
David Q. Rich
Marco Pandolfi
Roy M. Harrison
Philip K. Hopke
Tuukka Petäjä
Andrés Alastuey
Xavier Querol
Source :
Environment International, Vol 172, Iss , Pp 107744- (2023)
Publication Year :
2023
Publisher :
Elsevier, 2023.

Abstract

The 2017–2019 hourly particle number size distributions (PNSD) from 26 sites in Europe and 1 in the US were evaluated focusing on 16 urban background (UB) and 6 traffic (TR) sites in the framework of Research Infrastructures services reinforcing air quality monitoring capacities in European URBAN & industrial areaS (RI-URBANS) project. The main objective was to describe the phenomenology of urban ultrafine particles (UFP) in Europe with a significant air quality focus.The varying lower size detection limits made it difficult to compare PN concentrations (PNC), particularly PN10-25, from different cities. PNCs follow a TR > UB > Suburban (SUB) order. PNC and Black Carbon (BC) progressively increase from Northern Europe to Southern Europe and from Western to Eastern Europe. At the UB sites, typical traffic rush hour PNC peaks are evident, many also showing midday-morning PNC peaks anti-correlated with BC. These peaks result from increased PN10-25, suggesting significant PNC contributions from nucleation, fumigation and shipping.Site types to be identified by daily and seasonal PNC and BC patterns are: (i) PNC mainly driven by traffic emissions, with marked correlations with BC on different time scales; (ii) marked midday/morning PNC peaks and a seasonal anti-correlation with PNC/BC; (iii) both traffic peaks and midday peaks without marked seasonal patterns. Groups (ii) and (iii) included cities with high insolation.PNC, especially PN25-800, was positively correlated with BC, NO2, CO and PM for several sites. The variable correlation of PNSD with different urban pollutants demonstrates that these do not reflect the variability of UFP in urban environments. Specific monitoring of PNSD is needed if nanoparticles and their associated health impacts are to be assessed. Implementation of the CEN-ACTRIS recommendations for PNSD measurements would provide comparable measurements, and measurements of

Details

Language :
English
ISSN :
01604120
Volume :
172
Issue :
107744-
Database :
Directory of Open Access Journals
Journal :
Environment International
Publication Type :
Academic Journal
Accession number :
edsdoj.499e6e4b2cc4059aa24b78b809af541
Document Type :
article
Full Text :
https://doi.org/10.1016/j.envint.2023.107744