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Nitrogen oxide measurements at rural sites in Switzerland: Bias of conventional measurement techniques
Author(s) -
Steinbacher M.,
Zellweger C.,
Schwarzenbach B.,
Bugmann S.,
Buchmann B.,
Ordóñez C.,
Prevot A. S. H.,
Hueglin C.
Publication year - 2007
Publication title -
journal of geophysical research: atmospheres
Language(s) - English
Resource type - Journals
SCImago Journal Rank - 1.67
H-Index - 298
eISSN - 2156-2202
pISSN - 0148-0227
DOI - 10.1029/2006jd007971
Subject(s) - ozone , molybdenum , nitrogen , peroxyacetyl nitrate , environmental science , nitrogen oxide , environmental chemistry , nox , atmospheric sciences , materials science , analytical chemistry (journal) , chemistry , meteorology , inorganic chemistry , physics , combustion , organic chemistry
Nitrogen oxides (NO x = NO + NO 2 ) in the atmosphere are often measured using instruments equipped with molybdenum converters. NO 2 is catalytically converted to NO on a heated molybdenum surface and subsequently measured by chemiluminescence after reaction with ozone. The drawback of this technique is that other oxidized nitrogen compounds such as peroxyacetyl nitrate and nitric acid are also partly converted to NO. Thus such NO 2 measurements are really surrogate NO 2 measurements because the resultant values systematically overestimate the true value because of interferences of these compounds, especially when sampling photochemically aged air masses. However, molybdenum converters are widely used, and a dense network of surrogate NO 2 measurements exists. As an alternative with far less interference, photolytic converters using ultraviolet light are nowadays applicable also for long‐term measurements. This work presents long‐term collocated NO 2 measurements using molybdenum and photolytic converters at two rural sites in Switzerland. On a relative scale, the molybdenum converter instruments overestimate the NO 2 concentrations most during spring/summer because of prevalent photochemistry. On a monthly basis, only 70–83% of the “surrogate” NO 2 can be attributed to “real” NO 2 at the non‐elevated site and even less (43–76%) at the elevated one. The observed interferences have to be taken into account for monitoring and regulatory issues and to be considered when using these data for ground‐truthing of satellite data or for validation of chemical transport models. Alternatively, an increased availability of artifact‐free data would also be beneficial for these issues.

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