The mean Pb-206/Pb-207 ratio of 1.131 +/- 0.015 (range 1.112-1.150) fo
und for lead in the teeth of 'low-lead exposure' children in Edinburgh
is intermediate between the observed ratios for leaded petrol (1.075
+/- 0.013) and tap water in contact with lead pipes (1.160 +/- 0.012)
and comparable with that reported for food in the UK. Quantitative sou
rce apportionment on the basis of one lead isotopic ratio, however, ma
y well be hindered by the wide range of Pb-206/Pb-207 values (1.098-1.
183; mean 1.142 +/- 0.031) found for old, high-lead (> 1.0%) paint and
the similarity of the mean ratio (1.159 +/- 0.011) for high-lead (> 0
.1%) dust in older houses to that for tap water. The potential benefit
of using more than one stable lead isotopic ratio in such investigati
ons is endorsed by the identification of two distinct groups of childr
en close to the excellent best-fit line (r = -0.976) through the Pb-20
8/Pb-206 versus Pb-206/Pb-207 plot for the extensive series of environ
mental (petrol, atmospheric particulates, street dust, paint (< 1.0%),
house dust, tap water) data, while the samples of high-lead (> 1.0%)
paint all lie clearly to one side of the line, and by the differences
sometimes observed between the enamel and dentine fractions of individ
ual adult teeth for the Pb-208/Pb-206 and Pb-208/Pb-207, but not Pb-20
6/Pb-207, ratios.