Abstract

Abstract. The University of Miami (UM) deployed a sequential two-photon laser-induced fluorescence (2P-LIF) instrument for the in situ measurement of gaseous elemental mercury, Hg(0), during the Reno Atmospheric Mercury Intercomparison Experiment (RAMIX) campaign. A number of extended sampling experiments, typically lasting 6–8 h but on one occasion extending to ∼ 24 h, were conducted, allowing the 2P-LIF measurements of Hg(0) concentrations to be compared with two independently operated instruments using gold amalgamation sampling coupled with cold vapor atomic fluorescence spectroscopic (CVAFS) analysis. At the highest temporal resolution, ∼ 5 min samples, the three instruments measured concentrations that agreed to within 10–25 %. Measurements of total mercury (TM) were made by using pyrolysis to convert total oxidized mercury (TOM) to Hg(0). TOM was then obtained by difference. Variability in the ambient Hg(0) concentration limited our sensitivity for measurement of ambient TOM using this approach. In addition, manually sampled KCl-coated annular denuders were deployed and analyzed using thermal dissociation coupled with single-photon LIF detection of Hg(0). The TOM measurements obtained were normally consistent with KCl denuder measurements obtained with two Tekran speciation systems and with the manual KCl denuder measurements but with very large uncertainty. They were typically lower than measurements reported by the University of Washington (UW) Detector for Oxidized Hg Species (DOHGS) system. The ability of the 2P-LIF pyrolysis system to measure TM was demonstrated during one of the manifold HgBr2 spikes but the results did not agree well with those reported by the DOHGS system. The limitations of the RAMIX experiment and potential improvements that should be implemented in any future mercury instrument intercomparison are discussed. We suggest that instrumental artifacts make a substantial contribution to the discrepancies in the reported measurements over the course of the RAMIX campaign. This suggests that caution should be used in drawing significant implications for the atmospheric cycling of mercury from the RAMIX results.

Highlights

  • The environmental and health impacts of mercury pollution are well recognized with impacts on human health and broader environmental concerns (US EPA, 2000; UNEP, 2013; Mergler et al, 2007; Díez, 2009; Scheuhammer et al, 2007)

  • A number of extended sampling experiments, typically lasting 6–8 h but on one occasion extending to ∼ 24 h, were conducted, allowing the 2P-LIF measurements of Hg(0) concentrations to be compared with two independently operated instruments using gold amalgamation sampling coupled with cold vapor atomic fluorescence spectroscopic (CVAFS) analysis

  • Reno Atmospheric Mercury Intercomparison Experiment (RAMIX) was primarily an intercomparison of the University of Miami (UM) 2P-LIF instrument, the University of Washington (UW) Detector for Oxidized Hg Species (DOHGS) that is based on two Tekran 2537 instruments, and a Tekran 2537 and two 2537/1130/1135 speciation systems deployed by University of Nevada Reno (UNR)

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Summary

Introduction

The environmental and health impacts of mercury pollution are well recognized with impacts on human health and broader environmental concerns (US EPA, 2000; UNEP, 2013; Mergler et al, 2007; Díez, 2009; Scheuhammer et al, 2007). The Reno Atmospheric Mercury Intercomparison Experiment (RAMIX) offered an opportunity to deploy the 2P-LIF instrument as part of an informal field intercomparison at the University of Nevada Agricultural Experiment Station (Gustin et al, 2013; Ambrose et al, 2013; Finley et al, 2013). RAMIX was primarily an intercomparison of the UM 2P-LIF instrument, the UW Detector for Oxidized Hg Species (DOHGS) that is based on two Tekran 2537 instruments, and a Tekran 2537 and two 2537/1130/1135 speciation systems deployed by UNR. Under these circumstances, we were not able to compare 2PLIF measurements made at high temporal resolution with the CRDS instrument. We offer a contrasting view with different conclusions

RAMIX intercomparison
The 2P-LIF system
Measurements of TM and TOM
Manual denuder sampling of RGM
RAMIX manifold
UM Tekran performance
Interference tests
Limits of 2P-LIF detection of TOM
Manual denuder measurements
Implications of RAMIX results
Comparison of total oxidized mercury
Future mercury intercomparisons
Conclusions
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