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The correction formula can be expressed as: beta [Attenuation Monitor Concentration] (μg/m3) = 0.80 [Dusttrak Monitor Concentration] (μg/m3) + 10.4 [15].
At each site, four field stations were installed to monitor concentration of air pollutants including nitrogen oxides (NOx).
A detailed study of these processes requires selective and reversible sensing of Ca2+ and an ability to quantify and monitor concentration changes in a biological setting.
The ability to monitor concentration and stratification in situ may greatly aid in developing efficient separators and allow more accurate modeling of these processes.
City = average of monitors within the city; Near = nearest monitor concentration; LUR = land use regression; Disp = dispersion modeling; Inter = interpolation.
Models using the nearest monitor concentration estimates and the primary set of health covariates (Model 2) were considered as our primary analytic models.
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The standard deviation method was used to monitor concentrations of different anions.
In essence, the central monitor concentrations serve as direct estimates of the daily time effect.
The prediction equation also included central monitor concentrations as a predictor to reflect average concentration for a given day.
To insure clinical effect and to avoid side-effects, it is crucial to monitor concentrations very carefully.
The prediction equation also used central monitor concentrations as an independent variable to reflect average concentration levels for a given day.
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