Arsenic (As) is the biggest environment contaminant in most of the soils wh
ere fly ash is applied. Usually, it is not mobile and strongly adsorbed on
to soil particles. However, in gypsum and phosphorus amended soils As may b
e much more mobile. A study in repacked columns was conducted to determine
whether or not As becomes mobile when Ca(H2PO4)(2) and CaSO4 are used as le
aching solutions, and to compare the competitive interactions between PO4-A
sO4 and SO4-AsO4. Arsenic concentration in leachate was found to be approxi
mately ten times greater when Ca(H2PO4)(2) was used to leach the columns as
compared to CaSO4. A maximum concentration of 800 mu g As L-1 was found in
the leachate in this case, which is much higher than the groundwater limit
of 50 mu g L-1 for drinking water established by the United States Environ
mental Protection Agency. In fly ash, the portion of arsenate non-specifica
lly adsorbed is believed to be much lower than that of specifically adsorbe
d. Sulfate anions were able to displace only non-specifically adsorbed arse
nate. In this case the concentration of As in leachate was found to be with
in acceptable limits. On the other hand, phosphate can compete with arsenat
e for all available adsorption sites, non-specific and specific. Phosphate
displacement of both forms of arsenates increases As mobility in both contr
ol and fly ash treatments.