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It should be emphasized that the initial concentrations of Cd2+ were high and that the contaminated solution was processed only once.
Since t calculated > t observed, null hypothesis that the experiment did not bring any change in the concentration of zinc ions in the solution is rejected and alternate hypothesis that the experiment in removing zinc ions from contaminated solution was succeccful accepted (Fig. 3).
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Results as removal percentages of the metal Cd2+ from contaminated solutions were employed to obtain the amount of metal in the solutions after the adsorption process.
For one specific system, the electrophoretic zeta potential,, of the contaminated matrix in the solution was found to be related to the electroosmotic averaged ζ in the experiment and not to the efficiency in the extraction.
In the present study, CA was found to be unsuitable for washing Pb-contaminated agricultural soil, whereas the FeCl3 solution was the most stable washing agent tested, as it had high removal efficiency and low release of Pb after washing.
Bioremediation with strain MSR33 of two mercury-contaminated aqueous solutions was evaluated.
A 4% Tween 80 solution was then flushed through PCE-contaminated boxes at several flow velocities, with periods of flow interruption.
The influence of temperature and the effect of aggressive anions on the electrochemical behaviour of UNS N08031 stainless steel in a contaminated phosphoric acid solution were evaluated.
The electrochemical behaviour of the highly alloyed austenitic stainless steel UNS N08031 (Alloy 31) in a contaminated phosphoric acid solution is studied using potentiodynamic curves, EIS and Mott Shottky.
The same contaminated CSF solutions were used over the total 46 days of incubation but only 3 different protein conc.
In such situations, application of dissolved nutrients to a contaminated beach in a freshwater solution is superior to their application in a seawater solution.
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