Each standard solution was individually mixed with 20 mg of dry SG-N-PhenacylPyrNTf2 phase.
Selected metal ions of 2 mg L−1 were individually mixed with 20 mg SG-N-PhenacylPyrNTf2 phase.
For the effect of temperature, standard solutions of 5.0 mgL-1 Cu II) were prepared, adjusted to the pH 6.0 as above, and individually mixed with 25.0 mg LC3.
For the study of La III) adsorption capacity, standard solutions of 0, 5, 10, 20, 30, 40, 60, 80, 100, 125, 150, 200, and 500 mg L−1 were prepared as above, adjusted to the optimum pH value of 6.0 with the buffered aqueous solution (0.1 mol L−1 CH3COOH/CH3COONandand individually mixed with 20 mg SG-N-PhenacylPyrNTf2.
For the investigation of Fe(III) static adsorption capacity, the standard solutions of 0, 5.0, 125.0, and 150.0, 25.0, 30.0, 50.0, 75.0, 125.0, and 150.0 mgL−1 were prepared and adjusted to the optimum pH value of 5.0 and individually mixed with 25.0 mg CuO-TiO2 NSs.
For determination of the static uptake capacity of Fe III) on CuO-TiO2 NSs phase, 25.0 mL of Fe III) sample solutions with different concentrations (0 150.0 mgL−1) were adjusted to pH 5.0 and individually mixed with 25.0 mg of CuO-TiO2 NSs.
Roasting vegetables, either individually or mixed, in the oven or toaster oven was another popular suggestion.
Sponge preparation involved dissolving both polymers (either individually or mixed) in 1% acetic acid and freeze-drying the corresponding solutions.
The aim of the present study was to investigate the ability of bacterial strains either pure (individually) or mixed (combinations), isolated from POME to degrade and metabolize organic load from POME.
The main aim of the present study was to investigate the ability of bacterial strains either pure (individually) or mixed (combinations), to degrade and metabolize organic load from palm oil mill effluent.
In the competitive DNA binding assay, wild-type and mutated GATA3 DBDs were used individually or mixed in equimolar proportion.
