The pK and pK′ (polarographic pK) of this substance are calculated both polarographically and spectrophotometrically.
Finally, the hydration enthalpy of the cation of the substance was calculated by designing a thermochemical cycle.
The dose-dependence of the superoxide anion scavenging effect of extracts, fractions and caffeic acid (reference substance) was calculated against different concentrations (1, 2, 3, 4, 5, 10, 25, 50 µg/ml).
The concentrations of these calibration solutions were compared with the concentrations of the in vitro microdialysis samples, and the relative recovery for each substance was calculated.
Subsequently, the NaOH volume used was recorded and the acidic percentage of the substance was calculated using the chemical formula described below, whose result had to be adjusted due to the dilution process and expressed as percentage of citric acid [ 17].
The individual toxic substances were calculated in line with an AVL BOOST model of this engine.
For each case study, mass flow rates of individual toxic substances were calculated.
The diffusion coefficients of these polymer membranes in contact with different redox substances were calculated qualitatively by electrochemical techniques such as cyclic voltammetry (CV).
Using a dispersion model and worst-case assumptions (a combination of high solar radiation, high temperature and low wind speed), the evaporated substances were calculated to be present in only relatively low concentrations in the air above an STP.
In this article, the Hildebrand solubility parameter of over 250 substances were calculated by the modified ER (Esmaeilzadeh Roshanfekr) equation of state and some others (the Peng Robinson, Soave Redlich Kwong, Patel Teja and Schmidt Wenzel) and compared with the experimental data.
