The potential risk of surface and ground water contamination by trace metal
s leached from contaminated land-disposed dredged sediment is a major envir
onmental concern. The objective of this study was to evaluate trace metal l
eachability, leachate quality, and environmental effects of land-disposed d
redged sediments (LDDS), In addition to chemical characterization and deter
mination of potential and actual leachability, dredged sediments were also
subjected to solid phase fractionation using a sequential extraction proced
ure, Potential leachability, defined as the maximum metal pool that may bec
ome available fur leaching at a constant pH 4, decreased in the following o
rder: Zn similar to Cd > Mn > Ni > Co > Cu similar to As > Pb > Cr, Potenti
al metal leachability was controlled mainly by solid phase distribution of
metals in sediments. The acid-extractable fraction of most metals correlate
d well with the potentially leachable metals extracted with a solution of p
H 4 (r(2) > 0.67), except for Pb. The kinetics of metal release were determ
ined using the cascade leaching test (CLT) with water at pH ii, Except for
Ni and Zn in the first traction. metal concentrations in all consecutive le
aching fractions remained below the maximum permissible level in water for
human consumption. Actual metal leachability expressed as a percentage of p
otential leachability varied widely among trace metals and decreased in the
order: As > Cu > Cr > Ni > Zn > Cd > Co > Pb, Our results indicate low ris
k of surface and ground water contamination resulting from land disposal of
dredged sediments.