J. Tidblad et C. Leygraf, ATMOSPHERIC CORROSION EFFECTS OF SO2 AND NO2 - A COMPARISON OF LABORATORY AND FIELD-EXPOSED COPPER, Journal of the Electrochemical Society, 142(3), 1995, pp. 749-756
Laboratory exposures of copper have been performed at exposure conditi
ons comparable to those in the UN ECE exposure program with respect to
air flow conditions, relative humidity, and concentration of the gase
ous pollutants sulfur dioxide and nitrogen dioxide. Extrapolation of t
he weight increases in the laboratory experiments match well those obt
ained at the test sites with high sulfur dioxide and nitrogen dioxide
pollution levels. At these sites, sulfate and nitrate were the dominat
ing surface constituents, as in the laboratory exposures. Additional c
onstituents, detected in the laboratory, but not in the field, were su
lfite and nitrite. At test sites with low pollution levels of sulfur d
ioxide and nitrogen dioxide, weight increases were much higher than in
the laboratory exposures. At these sites, sulfate and nitrate were de
tected, but the relative amount of nitrate was much lower compared to
the sites with high levels of sulfur dioxide and nitrogen dioxide. How
ever, the amount of sulfate was practically the same. In addition, Cu2
O was identified as an important compound at some sites. Characteristi
c of all sites with low pollution levels of nitrogen dioxide are the h
igh levels of ozone. Ozone was not included in the laboratory experime
nts which could explain the discrepancy in weight increase. Laboratory
experiments, investigating the combined effects of sulfur dioxide and
ozone are presented in another publication. Both chloride and ammonia
were detected as surface constituents on all field samples,confirming
that salts and/or gaseous pollutants, other than sulfur dioxide, nitr
ogen dioxide and ozone, also are important for the understanding of at
mospheric copper corrosion. However, the present investigation does no
t focus on these pollutants.