M. Vahter et al., EXTENSIVE LEAD-EXPOSURE IN CHILDREN LIVING IN AN AREA WITH PRODUCTIONOF LEAD-GLAZED TILES IN THE ECUADORIAN ANDES, International archives of occupational and environmental health, 70(4), 1997, pp. 282-286
We have determined the concentrations of lead (Pb), cadmium (Cd), and
mercury (Hg) in the blood of children living in two Andean villages in
Ecuador with many family-owned cottage-type industries using Pb fi-om
discarded car batteries and occasionally, utility batteries containin
g Cd and Hg or the product-ion of glazed tiles, The battery metals are
ground together with water to a suspension, which is applied manually
onto the tiles and then fused at about 1,200 degrees C in sawdust-fir
ed kilns. Children aged 4-15 years were recruited from the schools wit
h the assistance of the school-teachers, Children from homes with and
without tile-glazing activities were to be included, Blood metal conce
ntrations were determined by inductively coupled plasma mass spectrome
try (ICP-MS). The children had extremely high blood lead concentration
s (B-Pb), which ranged between 100 and 1,100 mu g/l (median 510 mu g/l
n = 82). Children from families engaged in tile-glazing production ha
d significantly higher B-Pb (median 600 mu g/l) than those living in h
omes with no such activity (median 210 mu g/l), although the B-Pb of t
he latter were nonetheless clearly elevated. B-Cd and B-Hg; were low (
medians 0.25 mu g Cd/l and 1.6 mu g Hg/l respectively) indicating that
the exposure from utility batteries containing Cd and Hg was low. The
blood hemoglobin concentrations decreased significantly with rising B
-Pb, indicating an effect on the heme synthesis, This was supported by
a marked increase in the blood concentration of protoporphyrins with
increasing B-Pb, It can be concluded that children from families with
cottage industries producing glazed tiles are at risk for severe healt
h effects due to high lead exposure.