Sediment ingestion has been identified as an important exposure route for t
oxicants in waterfowl. The toxicity of lead-contaminated sediment from the
Coeur d'Alene River Basin (CDARB) in Idaho was examined on posthatching dev
elopment of mallard (Anas platyrhynchos) ducklings for 6 weeks. Day-old duc
klings received either untreated control diet, clean sediment (24%) supplem
ented control diet, CDARB sediment (3,449 mu g/g lead) supplemented diets a
t 12% or 24%, or a positive control diet containing lead acetate equivalent
to that found in 24% CDARB. The 12% CDARB diet resulted in a geometric mea
n blood lead concentration of 1.41 ppm (WW) with over 90% depression of red
blood cell ALAD activity and over threefold elevation of free erythrocyte
protoporphyrin concentration. The 24% CDARB diet resulted in blood lead of
2.56 ppm with over sixfold elevation of protoporphyrin and lower brain weig
ht. In this group the liver lead concentration was 7.92 ppm (WW), and there
was a 40% increase in hepatic reduced glutathione concentration. The kidne
y lead concentration in this group was 7.97 ppm, and acid-fast inclusion bo
dies were present in the kidneys of four of nine ducklings. The lead acetat
e positive control group was more adversely affected in most respects than
the 24% CDARB group. With a less optimal diet (mixture of two thirds corn a
nd one third standard diet), CDARB sediment was more toxic; blood lead leve
ls were higher, body growth and liver biochemistry (TBARS) were more affect
ed, and prevalence of acid-fast inclusion bodies increased. Lead from CDARB
sediment accumulated more readily in duckling blood and liver than reporte
d in goslings, but at given concentrations was generally less toxic to duck
lings. Many of these effects are similar to ones reported in wild mallards
and geese within the CDARB.