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Figures 5 and 6 show the simulation plots for succinic acid, fumaric acid, and malic acid and the transformation coefficients from citric to malic acids for average concentrations of acids in the leaves of plants.
The difference between the estimates based upon the linear and log models increased for average concentrations above approximately 40 µg/m.
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Based on the LUR models, we generated a predicted spatial surface for annual average concentrations for each pollutant in a GIS with a resolution of 10 m.
The design of a fibre optic sequential multipoint sensor using a single DFB laser source for measurement of average concentration of methane has been reported.
However, compared to uncertainties of about 4% observed for single vial analysis, smaller as well as higher fluctuations were found for the average concentrations.
Similarly, the rule base representation in Fig. 5 indicate that probable value of FIS2 is 2.03 for the average concentrations of Ca, Mg, Fe and As are 150, 60, 0.6 and 0.1 mg/l, respectively.
The rule base representation in Fig. 7 indicate that probable value of FIS3 is 2.09 for the average concentrations of sulphate, nitrate and fluoride are 400, 90 and 3 mg/l, respectively.
Consistent with the epidemiology studies, we used seasonal average 1-hr daily maximum concentrations for O3 and annual average concentrations for PM2.5.
ClO4− concentrations obtained from the California Drinking Water Program provided source-specific data for estimating weighted average concentrations in community water.
We used simulated concentrations in the first model layer for surface concentrations, and used annual average concentrations for PM2.5 and the maximum 6-month average of the 1-hr daily maximum for ozone, consistent with the epidemiology studies.
There is a substantial range in annual average concentrations for NO2 and for PM.
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