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A potentially smaller feature vector is the quantization of concentration observations made by taking aggregate mean concentrations over several consecutive elements of c(k).
Proportions of subjects with elevated γ-GT and geometric mean concentrations over covariables are also presented in Table 1.
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None of the L. monocytogenes growth challenge study designs currently being considered are likely to provide an F-test with α = 0.05 and power ≥ 0.8 to detect a 1 log10 increase in mean concentration over the entire range of measurement uncertainty values for enumeration of L. monocytogenes reported in food samples in a validation study of ISO Method 11290-2.
This difference was greatest when a value of 125.3 days was chosen for the parameter q, which is used in calculating the weighted mean concentration over the days prior to the focal day (Fig. 4).
The modeled mean concentration over the whole 12-year period was 6% lower than the measured concentrations for NOx and 12% lower for NO2 [ 36].
The modelled mean concentration over the whole 12-year period was 6% lower than the measured concentrations of NOx and 12% lower than those of NO2[ 21].
The modeled mean concentration over the whole 12-year period was 6% lower than the measured concentrations for NOx and 12% lower for NO2 (Ketzel M, unpublished observations).
The ASA concentration in the synovial fluid (n = 6) reached a maximum of 4 μg/mL, the mean concentration over the entire perfusion period was 2 μg/mL.
The mean concentrations (calculated over 5 hours) of plasma Val and Leu + Iso were significantly higher following the consumption of CM (P=0.050 and P=0.017, respectively) as compared to PM. Significantly greater percent increases were noted at 180 minutes postprandially (P<0.01) for Val and Leu + Iso in those who consumed CM compared to PM.
In the present study we consider gradients only between the front and back of the surface of the tip cell, with mean concentrations ([V]Tip) defined over the tip cell's entire surface.
Mean concentrations of CO over a 24-hr period are also high (ranging from 2 to 50 ppm in households using solid cooking fuels) and often exceed the health-based WHO guidelines of 9 ppm (in an 8-hr period) (Bruce et al. 2000; Saksena et al. 2003).
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