Abstract

Abstract. Simultaneous measurements of CH3O2 radical concentrations have been performed using two different methods in the Leeds HIRAC (Highly Instrumented Reactor for Atmospheric Chemistry) chamber at 295 K and in 80 mbar of a mixture of 3:1 He∕O2 and 100 or 1000 mbar of synthetic air. The first detection method consisted of the indirect detection of CH3O2 using the conversion of CH3O2 into CH3O by excess NO with subsequent detection of CH3O by fluorescence assay by gas expansion (FAGE). The FAGE instrument was calibrated for CH3O2 in two ways. In the first method, a known concentration of CH3O2 was generated using the 185 nm photolysis of water vapour in synthetic air at atmospheric pressure followed by the conversion of the generated OH radicals to CH3O2 by reaction with CH4∕O2. This calibration can be used for experiments performed in HIRAC at 1000 mbar in air. In the second method, calibration was achieved by generating a near steady state of CH3O2 and then switching off the photolysis lamps within HIRAC and monitoring the subsequent decay of CH3O2, which was controlled via its self-reaction, and analysing the decay using second-order kinetics. This calibration could be used for experiments performed at all pressures. In the second detection method, CH3O2 was measured directly using cavity ring-down spectroscopy (CRDS) using the absorption at 7487.98 cm−1 in the A←X (ν12) band with the optical path along the ∼1.4 m chamber diameter. Analysis of the second-order kinetic decays of CH3O2 by self-reaction monitored by CRDS has been used for the determination of the CH3O2 absorption cross section at 7487.98 cm−1, both at 100 mbar of air and at 80 mbar of a 3:1 He∕O2 mixture, from which σCH3O2=(1.49±0.19)×10-20 cm2 molecule−1 was determined for both pressures. The absorption spectrum of CH3O2 between 7486 and 7491 cm−1 did not change shape when the total pressure was increased to 1000 mbar, from which we determined that σCH3O2 is independent of pressure over the pressure range 100–1000 mbar in air. CH3O2 was generated in HIRAC using either the photolysis of Cl2 with UV black lamps in the presence of CH4 and O2 or the photolysis of acetone at 254 nm in the presence of O2. At 1000 mbar of synthetic air the correlation plot of [CH3O2]FAGE against [CH3O2]CRDS gave a gradient of 1.09±0.06. At 100 mbar of synthetic air the FAGE–CRDS correlation plot had a gradient of 0.95±0.024, and at 80 mbar of 3:1 He∕O2 mixture the correlation plot gradient was 1.03±0.05. These results provide a validation of the FAGE method to determine concentrations of CH3O2.

Highlights

  • Methyl peroxy (CH3O2) radicals are important intermediates during atmospheric oxidation (Orlando and Tyndall, 2012) and combustion chemistry (Zador et al, 2011), and they are produced mainly by the oxidation of CH4 and larger hydrocarbons followed by the termolecular reaction between the CH3 radical, O2 and a third body M (Reaction R1).CH3 + O2 + M → CH3O2 + M (R1)In environments influenced by anthropogenic NOx emissions, CH3O2 predominantly reacts with NO to produce NO2 and CH3O (Reaction R2).CH3O2 + NO → CH3O + NO2 (R2)CH3O subsequently reacts with O2 (Reaction R3) to generate HO2, which in turn oxidises another NO molecule to NO2 (Reaction R4)

  • The fluorescence assay by gas expansion (FAGE) inlet was translated across the width of the chamber and the CH3O2 signal was observed to show no decrease within the ∼ 10 % 1σ statistical error of each measurement up until the point at which the pinhole was level with the chamber walls

  • The conversion of the FAGE signals into [CH3O2] at 1000 mbar air for the intercomparison with cavity ring-down spectroscopy (CRDS) shown in Fig. 8a and b was based on the average of the results of the water vapour calibration method and the kinetic decay calibration method, which gives CCH3O2 = (9.81 ± 2.03) × 10−10 counts cm3 molecule−1 s−1 mW−1, Sect. 2.2.2)

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Summary

Introduction

Methyl peroxy (CH3O2) radicals are important intermediates during atmospheric oxidation (Orlando and Tyndall, 2012) and combustion chemistry (Zador et al, 2011), and they are produced mainly by the oxidation of CH4 and larger hydrocarbons followed by the termolecular reaction between the CH3 radical, O2 and a third body M (Reaction R1). RO2 radicals such as CH3O2 have been selectively measured in CIMS laboratory experiments with detection limits between ∼ 1 × 108 and 1 × 109 molecule cm−3 (Noziere and Hanson, 2017). CIMS with NO−3 reagent ion has been employed in field measurements to record diurnal profiles of some highly oxygenated low-vapour-pressure RO2 radicals produced in the ozonolysis of monoterpenes peaking at a few 107 molecule cm−3 (Jokinen et al, 2014). We intercompared measurements of HO2 concentrations by the indirect FAGE method and the direct and absolute CRDS method within HIRAC, and we demonstrated good agreement, within 10 % and 16 % at 150 mbar and 1000, respectively (Onel et al, 2017b), which validates the FAGE method for HO2. CH3O2 measurements by FAGE and CRDS within HIRAC are intercompared at 80 mbar for a mixture of 3 : 1 He/O2 and at 100 and 1000 mbar for air

CH3O2 generation in HIRAC
FAGE instrument and calibration for CH3O2
Calibration using kinetics of the CH3O2 temporal decay
FAGE measurements of CH3O2 concentration gradient across the HIRAC diameter
CRDS set-up
CH3O2 absorption spectrum and comparison with the literature
Determination of the CRDS limit of detection
Intercomparison of CRDS and FAGE CH3O2 measurements
Conclusions

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