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The kinetics of phenol sorption has been studied spectrophotometrically at different temperatures (25 40 °C; ±0.1 range).
Sorption has been shown to be largely reversible, dependent on the absolute concentrations involved and on the finite sorptive capacity of the rock.
The use of biomass sorption has been proposed as an alternative to conventional methods for metal ion removal from wastewater, and the research on this topic has become very important.
Since phenol sorption has been reported to be affected by the pH of the adsorbate (Singh et al. 1994), the adsorption of phenol by natural and activated clay were studied at various pH values of the phenol solution (100 mL, 5 mg/L).
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Much faster sorption have been found for milled alloy as compared to un-milled one [6].
The influence of temperature on the sorption and the activation energies of sorption have been calculated.
Activation parameters for diffusion and sorption have been evaluated and these results are discussed in terms of the molecular size of the liquids and the temperature.
Additionally, for comparison purposes similar studies have been carried out for carbon nanotube model structures and the effect of pore shape/size as well as elements of the role of confinement on sorption have been highlighted.
A direct correlation among specific surface area, defect concentration, and maximum sorption capacity has been established, and the sorption kinetics of the graphene for iodine capture was determined.
Thus, internal surfaces of HMO are evidently contributing to DOM sorption, as has been observed for As III) sorption [61, 75], and attenuating the decrease in N2-BET SSA that is observed for goethite.
Its strong sorption mechanism has been well documented in different iron oxyhydroxide minerals.
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