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The amount of sugars was calculated based on the remaining organic material following the equation: (1) sugars = NFES × 100 100 − RH, where RH is the relative humidity of the sample and NFES (nitrogen-free extractive substances) is calculated as follows: (2) NFES = 100 − RH − proteins − lipids − fibre.
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The individual toxic substances were calculated in line with an AVL BOOST model of this engine.
Mass flow (daily loads) for individual substances was calculated for several pollutants.
For each case study, mass flow rates of individual toxic substances were calculated.
The frequency of use of the different active substances was 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).
The toxicity of a combination product with n active substances was calculated according to CA using the equation given in Figure 1.
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.
The percentage of treated children for the 10 most prescribed active substances was calculated at the regional and LHU levels.
Thiobarbituric acid-reactant substances were calculated by comparison with OD650 of standard solutions of 1,1,3,3-tetramethoxypropan 1,1,3,3-tetramethoxypropan 99thyl acetal) 99% (malondialdehyde
The determined mass of mineral substances was calculated in proportion to 100 g of bone mass determined directly after the isolation.
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