Environmental problems associated with heavy metals in agricultural soils a
re increasing as a result of reuse of reclaimed sewage water for irrigation
, disposal of wastewater sludge and municipal refusal, application of anima
l waste and atmospheric fallout. The fractional loading isotherm, proposed
here, depicts relationships of heavy metals between the total input and ind
ividual solid-phase fractions in contaminated soils by combining isotherm a
nd selective sequential dissolution techniques. The redistribution and tran
sformations of copper (Cu), chromium (Cr), nickel (Ni), and zinc (Zn) in an
arid-zone soil were demonstrated through the fractional loading isotherm.
The results showed that linear adsorption model better described fractional
adsorption data than Freundlich model, and these metals retained in all so
lid-phase fractions were characterized by linear partitioning behavior unde
r the loading levels used in the present experiments. Fractional loading is
otherms not only effectively depicted the transformation direction and path
ways, but also reflected effects of the nature of the metals and time perio
d. Compared to the traditional isotherm, fractional loading isotherm is mor
e informative in exploring the adsorption and binding mechanisms, mobility
and (bio)availability of metals in the solid-phase components of contaminat
ed soils.