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The use of a Cu2O-modified electrode was found to be efficient for the determination of the sorption mechanism and for the screening of the experimental conditions allowing an optimum uptake of I− species by Cu2O.
The optimum uptake of F− is considered to take place at 1 g/100 mL.
The optimum uptake of F− was achieved within 30 min and decreased gradually up to 60 min.
Their root system may be too small for optimum uptake of water and nutrients and maximum grain yield.
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Secondly, the calculated optimum uptake rate of acetate to maintain biomass growth under heterotrophic conditions was fixed and H2 production was maximized to find the main metabolic changes.
The optimum uptake occurred at pH 3.0 when 81.0% of the Fe(III) was eliminated from the solution.
ZnO showed slow adsorbate uptake at relative pressure range of 0.0 – 0.4 and reaches the optimum uptake at 8 cm3/g while ZCA intercalation compound showed rapid adsorption around relative pressure range, 0.0 – 0.7 and reached the maximum adsorption at 37 cm37g.
An optimum cadmium uptake of 6.71 mg/g biomass was achieved at initial cadmium ion concentration of 26.46 mg/L and S. cerevisiae dosage of 2.13 g/L.
Using a distinct ratio of carboxyl-terminated poly ethylene glycol -block-poly(ε-caprolactone) (HOOC–PEglycol -block-polyy-poly(ethylene glycol -block-poly(ε-caprolactone (CHOOC PEG-b-PCL polymers, we formulated a series of micellar formulations HOOC PEG-b-PCLnt surface densities of EILDV and observed optimum cellular uptake of micelles witHOOC PEG-b-PCLrface densito by B16F10 cells.
Conditions for optimum cellular uptake of antisense oligonucleotides were established using an FITC-labelled oligonucleotide (Biognostik, TCS Biologicals, Buckingham, UK; Schlingensiepen et al, 1997).
Optimum conditions for the uptake of silver (I), chromium (III) and lead (II) by microorganisms used in this study were determined.
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