Free Cd2+ concentration and Cd complexation by natural organic ligands
in fresh water were determined by a technique involving ethylene diam
ine (EN,1,2-diaminoethane) ligand exchange and measurement by differen
tial pulse anodic stripping voltammetry. The validity of the ligand ex
change approach was demonstrated in a synthetic solution containing ED
TA as a model ligand. The technique was applied to water samples colle
cted from the lakes Greifen. Sempach and Lucerne with different trophi
c states, a polluted lake (Orta), a polluted river (Glatt) and groundw
ater at an infiltration site of this river. The dissolved Cd concentra
tions range from 0.03 to 0.09 nM, the free Cd2+ ion concentrations exp
ressed as pCd=-log[Cd2+]=11.5-12.2, and the conditional stability cons
tants of stable organic complexes are log K=10.2+/-0.1 (pH 7.8-8), wit
h ligand concentrations of 1-6 nM in the lakes Greifen, Sempach and Lu
cerne. 80% of the dissolved Cd is free Cd2+ in Lake Orta with lower pH
(<7.3) and higher dissolved Cd (0.7 nM). In the Glatt river and the i
nfiltrated groundwaters, polluted by effluents from sewage treatment p
lants, dissolved Cd concentrations of 0.2-2 nM, pCd=10.5+/-0.2, log K=
9.4+/-0.1 (pH 7.9-8) and ligand concentrations of 2.8-3.8 nM are obser
ved. The reliability of the technique and relevant implications of the
results in these waters are discussed. The extent of Cd complexation
is linked to the biological primary productivity in the lakes studied,
suggesting biological sources for the organic ligands. (C) 1998 Elsev
ier Science B.V.