Articles | Volume 26, issue 16
https://doi.org/10.5194/acp-26-11817-2026
© Author(s) 2026. This work is distributed under the Creative Commons Attribution 4.0 License.
New insights into traffic emissions: the role of hydrocarbons and oxygenated organic species in traffic-derived aerosol
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- Final revised paper (published on 20 Aug 2026)
- Supplement to the final revised paper
- Preprint (discussion started on 29 Apr 2026)
- Supplement to the preprint
Interactive discussion
Status: closed
Comment types: AC – author | RC – referee | CC – community | EC – editor | CEC – chief editor
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RC1: 'Comment on egusphere-2026-1511', Anonymous Referee #2, 27 May 2026
- AC1: 'Reply on RC1', Sanna Saarikoski, 03 Jul 2026
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RC2: 'Comment on egusphere-2026-1511', Anonymous Referee #1, 27 May 2026
- AC2: 'Reply on RC2', Sanna Saarikoski, 03 Jul 2026
Peer review completion
AR – Author's response | RR – Referee report | ED – Editor decision | EF – Editorial file upload
AR by Sanna Saarikoski on behalf of the Authors (03 Jul 2026)
Author's response
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Manuscript
ED: Publish subject to technical corrections (19 Jul 2026) by Benjamin A Nault
AR by Sanna Saarikoski on behalf of the Authors (01 Aug 2026)
Manuscript
Saarikoski et al. present a conventional PMF paper using aerodyne SPAMS. The work is composed of results from four independent measurement campaigns conducted in different seasons, covering a variety of meteorological and weather conditions in a traffic-influenced urban environment in Helsinki. As expected, the PMF showed several common aerosol components across all campaigns, while also revealed different factors in different seasons. The study is particularly strengthened by the identification of organic traffic aerosol (TrOA) that differs from conventional HOA and exhibits characteristic oxygenated ions commonly associated with biomass burning. The manuscript further explores diagnostic ion ratios and hydrocarbon patterns to distinguish TrOA from HOA and BBOA. Overall, the manuscript is well written, and I do not have any major concerns.
line110, the statement “its sources were identified using PMF” is somehow misleading. PMF factors in AMS data are not always direct sources, but rather chemically or process-defined components that can sometimes be linked to sources after interpretation.
Fig. 2. The diurnal cycles are presented as normalized concentration. Please clarify which parameter was used for normalization.
line210-213, It is difficult to attribute the relatively flat HOA diurnal pattern in spring 2018 solely to airflow and temperature. Moreover, the cycle does not appear truly flat but instead shows a noticeable peak around midnight. Are the air masses in the Helsinki region primarily influenced by southerly or southwesterly winds during the warmer season (spring to autumn)? Considering that the 2018 and 2019 campaigns represent meteorologically similar periods in terms of temperature and air mass influence, one might expect comparable HOA diurnal patterns for these two seasons.
line213-214, it looks to me that HOA shows higher concentrations in the day than at night in the diurnal cycle (Fig. 2), contradictory to the statements here.
line288-289, can you reason BBOA from a dominant local source?
line295, laser vaporizer should enable the detection refractory organic species due to the presence of BC. How does this capability affect the PMF factors compared to results from conventional thermal vaporizer results? This aspect is not discussed in the manuscript and would benefit from clarification.