Synthetic chelating agents such as EDTA form strong complexes with heavy me
tals and therefore have the potential to remobilize metals from sediments a
nd aquifers. In natural waters EDTA is present almost exclusively in the fo
rm of metal-complexes. Therefore, remobilization of metals is always a meta
l-metal-EDTA exchange reaction. We have investigated, to our knowledge for
the first time, the remobilization of metals from the surface of synthetic
iron oxides and from a river sediment by different metal-EDTA complexes. Th
e metals are exchanged as follows:
MeEDTA(dissolved) + Me-adsorbed* --> Me*EDTA(dissolved) + Me-adsorbed
The order of the remobilization rate of Zn2+ from goethite is CaEDTA > Fe(I
II)EDTA, reflecting the slow exchange reaction of Fe(III)EDTA. For the remo
bilization of Pb2+ from goethite, the rate was found to be Fe(III)EDTA > Ca
EDTA > ZnEDTA. Here, Fe(III)EDTA has surprisingly the fastest exchange rate
. Only very limited remobilization of Pb2+ is possible from hydrous ferric
oxide at pH 8 due to the very strong adsorption of Pb2+. The order of remob
ilization of Zn2+ from a natural river sediment was found to be CaEDTA > Cu
EDTA > Fe(III)EDTA. The remobilization rate of Zn2+ with Fe(III)EDTA is onl
y 12% of the rate with CaEDTA, illustrating the importance of EDTA speciati
on for assessing remobilization.