Swiss chard (Beta vulgaris L., cv. Fordhook Giant) was grown in nutrie
nt solution with C1 concentrations varying between 0.01 mM and 120 mM.
Solution Na concentration and ionic strength were maintained in all t
reatments by compensating with NaNO3. All solutions contained Cd (50 n
M, spiked with Cd-109). Three different Cd2+ buffering systems were us
ed. In one experiment, Cd2+ activity was unbuffered; its activity decr
eased with increased C1 concentration as a result of the formation of
CdCln2-n species. In the other experiments, Cd2+ activity was buffered
by the chelator nitrilotriacetate (NTA, 50 mu M) and ethylene-bis-(ox
yethylenenitrilo)-tetraacetate (EGTA, 50 mu M) at about 10(-9) M and 1
0(-11) M respectively. Plant growth was generally unaffected by increa
sing C1 concentrations in the three experiments. In unbuffered solutio
ns, Cd concentrations in plant tissue decreased significantly (p<0.01)
(approximately 2.4-fold) as solution C1 concentration increased from
0.01 mM to 120 mM. However, this decrease was smaller in magnitude tha
n the 4.7-fold decrease in Cd2+ activity as calculated by the GEOCHEM-
PC program for the same range of C1 concentrations. In solutions where
Cd2+ activity was buffered by NTA, Cd concentrations in plant tissue
increased approximately 1.4-fold with increasing C1 concentration in s
olution, while the Cd2+ activity was calculated to decrease 1.3-fold.
In solutions where Cd2+ activity was buffered by EGTA, Cd concentratio
ns in the roots increased 1.3-fold with increasing C1 concentration in
solution but there was no effect of C1 on shoot Cd concentrations. Th
e data suggest that either CdCln2-n species can be taken up by plant r
oots or that CI enhances uptake of Cd2+ through enhanced diffusion of
the uncomplexed metal to uptake sites.