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Aircraft measurements of aerosol and trace gas chemistry in the eastern North Atlantic

  • Maria A. Zawadowicz
  • , Kaitlyn Suski
  • , Jiumeng Liu
  • , Mikhail Pekour
  • , Jerome Fast
  • , Fan Mei
  • , Arthur J. Sedlacek
  • , Stephen Springston
  • , Yang Wang
  • , Rahul A. Zaveri
  • , Robert Wood
  • , Jian Wang
  • , John E. Shilling*
  • *Corresponding author for this work
  • Pacific Northwest National Laboratory
  • Brookhaven National Laboratory
  • Juul Labs, Inc.
  • School of Environment, Harbin Institute of Technology
  • Washington University St. Louis
  • Missouri University of Science and Technology
  • University of Washington

Research output: Contribution to journalArticlepeer-review

Abstract

The Aerosol and Cloud Experiment in the Eastern North Atlantic (ACE-ENA) investigated properties of aerosols and subtropical marine boundary layer (MBL) clouds. Low subtropical marine clouds can have a large effect on Earth s radiative budget, but they are poorly represented in global climate models. In order to understand their radiative effects, it is imperative to understand the composition and sources of the MBL cloud condensation nuclei (CCN). The campaign consisted of two intensive operation periods (IOPs) (June-July 2017 and January-February 2018) during which an instrumented G-1 aircraft was deployed from Lajes Field on Terceira Island in the Azores, Portugal. The G-1 conducted research flights in the vicinity of the Atmospheric Radiation Measurement (ARM) Eastern North Atlantic (ENA) atmospheric observatory on Graciosa Island. An Aerodyne high-resolution time-of-flight aerosol mass spectrometer (HR-ToF-AMS) and Ionicon protontransfer- reaction mass spectrometer (PTR-MS) were deployed aboard the aircraft, characterizing chemistry of nonrefractory aerosol and trace gases, respectively. The eastern North Atlantic region was found to be very clean, with an average non-refractory submicrometer aerosol mass loading of 0.6 gm-3 in the summer and 0.1 gm-3 in the winter, measured by the AMS. Average concentrations of the trace reactive gases methanol and acetone were 1-2 ppb; benzene, toluene and isoprene were even lower, < 1 ppb. Mass fractions of sulfate, organics, ammonium and nitrate in the boundary layer were 69 %, 23 %, 7% and 1% and remained largely similar between seasons. The aerosol chemical composition was dominated by sulfate and highly processed organics. Particulate methanesulfonic acid (MSA), a well-known secondary biogenic marine species, was detected, with an average boundary layer concentration of 0.021 gm-3, along with its gas-phase precursor, dimethyl sulfide (DMS). MSA accounted for no more than 3% of the submicron, non-refractory aerosol in the boundary layer. Examination of vertical profiles of aerosol and gas chemistry during ACE-ENA reveals an interplay of local marine emissions and long-range-transported aged aerosol. A case of transport of biomass burning emissions from North American fires has been identified using back-trajectory analysis. In the summer, the non-refractory portion of the background CCN budget was heavily influenced by aerosol associated with ocean productivity, in particular sulfate formed from DMS oxidation. Episodic transport from the continents, particularly of biomass burning aerosol, periodically increased CCN concentrations in the free troposphere. In the winter, with ocean productivity lower, CCN concentrations were overall much lower and dominated by remote transport. These results show that anthropogenic emissions perturb CCN concentrations in remote regions that are sensitive to changes in CCN number and illustrate that accurate predictions of both transport and regional aerosol formation from the oceans are critical to accurately modeling clouds in these regions.

Original languageEnglish
Pages (from-to)7983-8002
Number of pages20
JournalAtmospheric Chemistry and Physics
Volume21
Issue number10
DOIs
StatePublished - 26 May 2021
Externally publishedYes

UN SDGs

This output contributes to the following UN Sustainable Development Goals (SDGs)

  1. SDG 13 - Climate Action
    SDG 13 Climate Action

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