People working in the nickel refining industry are known to have a higher c
oncentration of nickel in lung tissue than the general population. To be ab
le to evaluate a potential nickel exposure from other sources, e.g., weldin
g, it is important to have sufficient data on what is normal for a local po
pulation. Several local factors such as the content of nickel in air and so
il can have a significant impact on this so-called normal value. As almost
all surgical equipment contains nickel, the sampling process can in itself
be a source of contamination. The scope of this work was to investigate if
there was any measurable contamination from the sampling instruments routin
ely used in hospitals, and if the presence of a nickel refinery had any eff
ect on the nickel content in the lungs of the general population. Autopsy l
ung tissue samples were collected in situ from 50 people who had lived in t
he county of Vest Agder in Norway. Two samples were collected from each per
son; one with a regular scalpel (Swarn-Norton) and forceps, and one with a
titanium knife and plastic forceps. None of the persons had any known conne
ction to the nickel refinery. The samples were collected at random and no s
pecial attention was given to age, sex and place of residence. The autopsie
s were performed according to Norwegian law and in understanding with the n
ext of kin. The arithmetic mean value fs of nickel was 0.64 +/- 0.56 mu g g
(-1) and 0.29 +/- 0.20 mu g g(-1) dry weight, respectively, for samples col
lected with a regular scalpel and a titanium knife (P < 0.0001). For people
who lived 8 km and closer to the refinery by the time of death, the nickel
content was 0.41 +/- 0.19 mu g g(-1) and for those who had lived between 8
and 70 km away from the refinery it was 0.18 +/- 0.13 mu g g(-1) (P<0.015)
. No statistical difference was established between results for males and f
emales. Previous investigations have shown that the nickel content in lung
tissue varies in the so-called normal population. This work has shown that
factors such as sampling equipment and place of residence have an impact on
the results. It thus demonstrates that reliable background values can pres
umably only be obtained by collecting samples from individuals not exposed
to known environmental nicker sources and to use nickel-free instruments in
the sampling process.