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The initial rate of reaction at different concentrations was calculated from the initial slope of absorbance time curve.
From the value of b, a dimensionless parameter R L at different initial metal ion concentrations was calculated and the values are shown in Table 1.
A groundwater quality index based on nitrate and chloride concentrations was calculated, which had a positive correlation with the specific vulnerability index.
Similarly, the "relative" decrease in lactate concentrations was calculated as follows: [(lactate at 6 h lactate on admission)/lactate on admission × 100]%, [(lactate at 12 h lactate on admission)/lactate on admission × 100]% and [(lactate at 24 h lactate on admission)/lactate on admission × 100]% [8, 14].
After the determination of dehydrogenase activity toward 1.2 and 2% (w/v) methanol, that towards 20% (w/v) glycerol in the presence of various methanol concentrations was calculated by subtracting the value of the activity toward methanol from that toward glycerol in the presence of methanol.
As an index of serotonin turnover, the ratio between 5-HIAA and serotonin concentrations was calculated.
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Concentrations were calculated according to a standard curve.
IR concentrations are calculated with two different A values (cm−2).
Inhibitory concentrations were calculated using the probit regression method [23].
The MB concentrations were calculated from a calibration curve.
Concentrations were calculated using a four-point calibration curve.
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