Uptake of cadmium from aqueous solutions by beech leaves has been studied. The effect of several factors on both rate and amount of this uptake has been studied. These factors include concentration of leaves, concentration of cadmium, pH, competing ions and drying leaves. The pattern of the curves showing the loss of cadmium from solution has been explained. Applicability of the Freündlich adsorption isotherm on the present results has been examined and the parameters of this isotherm have been calculated. The order of reaction between cadmium ions and beech leaves has been determined and a mechanism for this reaction has been suggested.
Several factors affecting the growth and the uptake of cadmium by
okra plants were studied using both root ‐ treatment and foliar ‐
treatment. These factors were the concentration of cadmium , type of
treatment, soil composition, presence of foreign ions, salinity, acidity
and temperature.
Both growth of plant and cadmium
uptake by plant were affected highly by the concentration of cadmium,
type of treatment, soil composition, salinity and temperature. Acidity
of solutions has only a little and irregular effect. A synergistic
combined effect of lead, copper and zinc with cadmium was observed on
the growth of plant but not regular on the uptake of cadmium.
The effect of root‐treatment of cauliflower, spinach, and parsley
plants with lead and cadmium were studied. Both metal ions showed
obvious growth inhibition of treated plants with cadmium having higher
toxicity on growth than lead.
Cadmium was more concentrated in the
edible parts of the three treated plants whereas lead was more
concentrated in the edible parts of cauliflower and spinach plants only.
Metal
ion concentrations and total metal ion content of treated plants
increased with the increase of concentration of cadmium or lead ions in
solutions used for treatment. The uptake of metal ion per unit
concentration decreased in treated plants with the increase of
concentration of cadmium or lead ions in solutions used for treatment.
Metal ion concentration and metal uptake were higher in the plants treated with cadmium than those treated with lead.
Toxicity of cadmium and lead on the growth of carrot plants has been
studied. Cadmium has been found to be more toxic than lead especially on
the shoots of carrot plants.
Foliar treatment has been compared with root‐treatment for the two elements on carrots and on their roots and shoots.
Concentrations
and total contents of lead and cadmium in whole plant in roots and in
shoots have been determined for treated carrot plants and compared in
root‐treatment with foliar‐treatment. Explanations have been suggested
whenever possible to illucidate the results obtained.
Percentages
of the metals taken by plants from the whole amounts of metal added
during treatment have been calculated and related to type of metal used,
concentration of metal in solutions used for treatment and the way of
treatment.
In this study the effects of root and foliar treatments of marrow
plants with cadmium and lead solutions on the growth of the various
parts of plant (roots, stem, leaves and fruits) have been studied.
Growth inhibition of the various parts of treated plants has been
compared with each other and for the two types of treatment. The
toxicity of cadmium on the growth of plant has been compared with the
toxicity of lead on the various parts of plants treated by root or by
foliar‐treatment with metal ions.
Cadmium and lead uptake by
plants and the distribution of this uptake between the various parts of
treated plants have been determined and commented on.
Percentages of cadmium or lead taken by plant from the total amount of cadmium or
lead added during treatment have been calculated and found to be very
small. This percentage has been found to be higher in foliar‐treated
plants and from dilute solutions than in root‐treated plants and from
more concentrated cadmium or lead solutions.