Fluoride in soil solution may cause substantially increased leaching of dis
solved organic carbon (DOC), Al, and heavy metals from soils. Our objective
was to examine whether increased metal solubility is attributable to forma
tion of fluoro- or organo-complexes. The A horizon of a: Slovak soil contam
inated with heavy metals and F by Al smelter emissions was used to conduct
two column experiments under saturated and steady-state water flow conditio
ns. The columns were leached with 5 mM Na2SO4, 1 mM NaCl, and 9 mM NaF solu
tions at pH 5.5 and an electrical conductivity of 1000 mu S cm(-1). Samples
were collected in 70-min intervals for approximately 7 d. Two experiments
were performed. In the first experiment (single F pulse), a fluoride (F) pu
lse was applied for 36 pore volumes (PVs), while in the second experiment (
dual F pulse), two consecutive F pulses (each for 2.8 PVs) were applied. Fo
r both experiments, Cl breakthrough curves (BTCs) revealed a convection-dom
inated transport regime. The breakthrough of Cd, Cr, Fe, Ni, and Pb paralle
led DOC breakthrough in both experiments indicating metal leaching as organ
o-complex. In the dual F pulse experiment, peak separation of the DOC and t
he complexed F (F-bound) breakthrough was achieved. The highest F-bound con
centration occurred 3.8 PVs later than that of DOG. The Al BTC paralleled t
hat of F-bound but showed tailing with a turning point simultaneous to the
highest DOC concentration. Thus, the increase in Al solubility was mainly c
aused by fluoro-complexation and only to a lesser extent by organo-complexa
tion.