the Creative Commons Attribution 4.0 License.
the Creative Commons Attribution 4.0 License.
Measurement report: Wintertime aerosol characterization at an urban traffic site in Helsinki Finland
Abstract. Physical and chemical properties of particulate matter and concentrations of trace gases were measured at an urban site in Helsinki, Finland for five-weeks to investigate the effect of wintertime conditions on pollutants. The measurement took place in a street canyon (Traffic Supersite) in January–February 2022. In addition, measurements were conducted in an urban background station (UB Supersite, SMEAR III, located approx. 0.9 km from the Traffic Supersite) and with a mobile laboratory in the adjacent side streets as well as by driving back and forth along the street along the Traffic Supersite. A source apportionment was performed for the SP-AMS measurements to identify organic factors connected to different particulate sources. Particle number concentration time series and the pollution detection algorithm (PDA) were used to compare local pollution level differences between the sites.
During the campaign three different pollution events were observed with increased pollutant concentrations. The increased concentration during these episodes were due to both trapping of local pollutants near the boundary layer and long-range and regional transport of pollutants to Helsinki metropolitan area. The local road vehicle emissions increased the particle number concentrations, especially sub-10 nm particles, and long-range and regional transported aged particles increased the PM mass and particle size.
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Status: open (until 16 Dec 2024)
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RC1: 'Comment on egusphere-2024-2235', Anonymous Referee #1, 19 Nov 2024
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The manuscript reports a comprehensive study of urban air quality in Helsinki, Finland. The work was carried out at two supersites using a bunch of instrumentation: traffic pollutant dominated measurement site and urban background station less affected by traffic. Interestingly, the urban station is less that one hundred meters further from the major traffic roads than the traffic station, but the observations were quite different. I have a few minor comments before its final publication.
Throughout the manuscript, measurement uncertainties should be added.
Line24-27, long sentence, please reword it.
L94-95, Please add references for the mentioned figures.
Section 2.2.1 Please make it clear if the intracavity Nd-YAG laser was used in the AMS. If laser was used, the RIE for BC should be mentioned too. How well does AMS-derived BC compare to other BC results?
L141, are you saying the transmission efficiency for the particles in the size range of 76-650 nm is 50%? This is not true, as the transmission efficiency is nearly 100% in the size range of 60 – 400nm.
Line 163, consist->consists
Line195-204, are the data used anywhere in the manuscript?
Section 2.2.1. The section does a good job describing the instrumentations. For a quick grab of the idea of this section, it could also be nice to tabulate all the instruments used at the traffic superstation. You can also add additional instruments not listed in Table S2 at UB station.
L376, Add a period at the end of bracket.
L385, it is unclear how the traffic frequencies were counted.
L410, which instrument was PN measurement from?
L422 Is SP-AMS derived BC concentration comparable to MAAP results?
L459, Please add reference(s) for your argument.
L472, can you guess the sources of a-pinene? In addition to the background concentrations, is it from regional or long-range transport?
L531, …are due to..
Section 3.1.6 PMF did a nice job in distinguishing six organic factors. A few more words describing the Tr-LVOOA, LVOOA and LVOOA-BB would also help to understand these three factors and their sources.
Citation: https://doi.org/10.5194/egusphere-2024-2235-RC1
Data sets
MEASUREMENT REPORT: WINTERTIME AEROSOL CHARACTERIZATION AT AN URBAN TRAFFIC SITE IN HELSINKI FINLAND Kimmo Teinilä https://doi.org/10.5281/zenodo.13254916
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