Soils doped with cadmium were effectively immobilized by thermal treat
ment in a bench-scale fluidized- and fixed-bed incinerator. Toxicity c
haracteristics leachability procedure (TCLP) was conducted to evaluate
the effectiveness of Cd immobilization by thermal treatment of the do
ped soils. USEPA SW846 Methods 3050 and 3051 were performed to determi
ne the presumptive total Cd content in the untreated and treated soils
. Experimental parameters include thermal treatment temperature and ti
me, Cd content in acidic and noncalcareous soils, sorbent type and amo
unt added, soil particle diameter, and incinerator mode. Results illus
trate that Cd in soils of smaller diameter is less effectively immobil
ized. At a temperature of 600 degrees C, a treating time of 30 minutes
, and a Cd content of 91.3 ppm in pre-treated sample, thermal treatmen
t in fluidized-bed mode reduces Cd leaching percentage from 47% and 75
% (untreated soil) to 12 and 22% for soils of particle size 16-20 mesh
and 45-50 mesh, respectively. Data of treating 150-ppm Cd-doped soils
in fluidized-bed mode at 600 degrees C for different times, viz. 10,
20, and 30 minutes indicate only a minimal difference in Cd leaching p
ercentage that are between 7.6% and 8.5%. The Cd content in soils does
not affect the leaching percentage of fluidized-bed treated soils, wh
ile the results of fixed-bed treatments of Cd soils at 600 degrees C f
or 30 minutes show an increase of leaching percentage from 8.8 to 13%
as Cd content in soils is increased from 75.0 to 175.0 ppm. The consta
ncy of leaching percentage from soils treated in fluidized-bed mode is
obviously due to high degree of mixing. As the treating temperature i
ncreases (from 150 degrees C to 750 degrees C). Cd is better immobiliz
ed in mixtures. Excessive addition of sorbents will reduce their adsor
ption effectiveness of Cd for each unit mass of sorbent. Both the Lang
muir and Freundlich isotherms fit the sorption data quite successfully
with all correlation coefficients (r) greater than 0.984.