Atmospheric Measurement Techniques (Aug 2022)

Comparison of airborne measurements of NO, NO<sub>2</sub>, HONO, NO<sub><i>y</i></sub>, and CO during FIREX-AQ

  • I. Bourgeois,
  • I. Bourgeois,
  • J. Peischl,
  • J. Peischl,
  • J. A. Neuman,
  • J. A. Neuman,
  • S. S. Brown,
  • S. S. Brown,
  • H. M. Allen,
  • P. Campuzano-Jost,
  • P. Campuzano-Jost,
  • M. M. Coggon,
  • M. M. Coggon,
  • J. P. DiGangi,
  • G. S. Diskin,
  • J. B. Gilman,
  • G. I. Gkatzelis,
  • G. I. Gkatzelis,
  • G. I. Gkatzelis,
  • H. Guo,
  • H. Guo,
  • H. A. Halliday,
  • H. A. Halliday,
  • T. F. Hanisco,
  • C. D. Holmes,
  • L. G. Huey,
  • J. L. Jimenez,
  • J. L. Jimenez,
  • A. D. Lamplugh,
  • A. D. Lamplugh,
  • Y. R. Lee,
  • J. Lindaas,
  • R. H. Moore,
  • B. A. Nault,
  • B. A. Nault,
  • B. A. Nault,
  • J. B. Nowak,
  • D. Pagonis,
  • D. Pagonis,
  • D. Pagonis,
  • P. S. Rickly,
  • P. S. Rickly,
  • M. A. Robinson,
  • M. A. Robinson,
  • M. A. Robinson,
  • A. W. Rollins,
  • V. Selimovic,
  • J. M. St. Clair,
  • J. M. St. Clair,
  • D. Tanner,
  • K. T. Vasquez,
  • P. R. Veres,
  • C. Warneke,
  • P. O. Wennberg,
  • P. O. Wennberg,
  • R. A. Washenfelder,
  • E. B. Wiggins,
  • C. C. Womack,
  • C. C. Womack,
  • L. Xu,
  • L. Xu,
  • L. Xu,
  • K. J. Zarzana,
  • K. J. Zarzana,
  • K. J. Zarzana,
  • T. B. Ryerson,
  • T. B. Ryerson

DOI
https://doi.org/10.5194/amt-15-4901-2022
Journal volume & issue
Vol. 15
pp. 4901 – 4930

Abstract

Read online

We present a comparison of fast-response instruments installed onboard the NASA DC-8 aircraft that measured nitrogen oxides (NO and NO2), nitrous acid (HONO), total reactive odd nitrogen (measured both as the total (NOy) and from the sum of individually measured species (ΣNOy)), and carbon monoxide (CO) in the troposphere during the 2019 Fire Influence on Regional to Global Environments and Air Quality (FIREX-AQ) campaign. By targeting smoke from summertime wildfires, prescribed fires, and agricultural burns across the continental United States, FIREX-AQ provided a unique opportunity to investigate measurement accuracy in concentrated plumes where hundreds of species coexist. Here, we compare NO measurements by chemiluminescence (CL) and laser-induced fluorescence (LIF); NO2 measurements by CL, LIF, and cavity-enhanced spectroscopy (CES); HONO measurements by CES and iodide-adduct chemical ionization mass spectrometry (CIMS); and CO measurements by tunable diode laser absorption spectrometry (TDLAS) and integrated cavity output spectroscopy (ICOS). Additionally, total NOy measurements using the CL instrument were compared with ΣNOy (= NO + NO2 + HONO + nitric acid (HNO3) + acyl peroxy nitrates (APNs) + submicrometer particulate nitrate (pNO3)). Other NOy species were not included in ΣNOy as they either contributed minimally to it (e.g., C1–C5 alkyl nitrates, nitryl chloride (ClNO2), dinitrogen pentoxide (N2O5)) or were not measured during FIREX-AQ (e.g., higher oxidized alkyl nitrates, nitrate (NO3), non-acyl peroxynitrates, coarse-mode aerosol nitrate). The aircraft instrument intercomparisons demonstrate the following points: (1) NO measurements by CL and LIF agreed well within instrument uncertainties but with potentially reduced time response for the CL instrument; (2) NO2 measurements by LIF and CES agreed well within instrument uncertainties, but CL NO2 was on average 10 % higher; (3) CES and CIMS HONO measurements were highly correlated in each fire plume transect, but the correlation slope of CES vs. CIMS for all 1 Hz data during FIREX-AQ was 1.8, which we attribute to a reduction in the CIMS sensitivity to HONO in high-temperature environments; (4) NOy budget closure was demonstrated for all flights within the combined instrument uncertainties of 25 %. However, we used a fluid dynamic flow model to estimate that average pNO3 sampling fraction through the NOy inlet in smoke was variable from one flight to another and ranged between 0.36 and 0.99, meaning that approximately 0 %–24 % on average of the total measured NOy in smoke may have been unaccounted for and may be due to unmeasured species such as organic nitrates; (5) CO measurements by ICOS and TDLAS agreed well within combined instrument uncertainties, but with a systematic offset that averaged 2.87 ppbv; and (6) integrating smoke plumes followed by fitting the integrated values of each plume improved the correlation between independent measurements.