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The maximum concentration value at the workplace is 0.3 ppm.
All concentration values are derived from an interlaboratory measurement program.
Upon declaring this original domain, the acceptable range of concentration values could be requested.
Compare the measured concentration value to the LoQ for air.
This would then calculate the stress concentration value.
The pH is then equal to minus the logarithm of the concentration value.
In addition, confidence in the methylmercury concentration value is low because only one sample was analysed.
The standard concentration values are corrected for the standard blank (steps C14-C17).
Bolded concentration values indicate beverages (alcoholic) that would not normally be consumed by children.
Recommended concentration values for thirteen constituents of these materials were established from results obtained in an interlaboratory measurement program.
Together these factors result in the formation of an approximately constant, boundary concentration value, in the external surface layer.
The table of results, showing the conversion of concentration values to units appropriate for the risk assessment, may also be viewed in Appendix 1.
This splits up the different PFTs, so a concentration value can be determined for each one.
This measurement provides a more quantitative indication of rates of metabolite flux than do simple concentration values.
Electronic circuits convert the relative currents into linear transmission percentages and/or absorbance/concentration values.
The concentration values are based on human and eco-toxicological considerations and define the risk of pollution, i.e. the transition to poor status.
The concentration values are in micrograms/gram as measured by HPLC.
Typical concentration values fall somewhere in this range and are tailored to produce the desired properties in the device that the semiconductor is intended for.
Mean concentration values were used (rather than higher percentile figures) in consideration of the chronic nature of the potential health effects of exposure to benzene.
The method aims to quantify the uncertainty of the contaminant concentration values, including uncertainty arising from field sampling techniques.
The signal is temperature compensated for the solubility of oxygen in water and the fluorophore characteristics to obtain the DO concentration value.
Changes in pulp density affect the degree of attenuation, which results in a change in the carbon concentration value recorded and displayed by the meter.
Primer3 uses the same salt concentration value for calculating both the primer melting temperature and the oligo melting temperature.
At larger concentrations, however, the value of K deviates from its small concentration value as a result of the nonideality of the solution.
Dry deposition is estimated by multiplying the measured air concentration values by a site-specific factor called a "deposition velocity".