Page 477 - Air pollution and greenhouse gases from basic concepts to engineering applications for air emission control
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458                                                 15  Air Monitoring

              In general, air emission monitoring is completed by gas sampling followed by
            gas characterization. In addition, the properties of total gas flow from the source
            must also be determined accurately before calculating the corresponding air
            emission rates. If a gas sample with a sampling flow rate of Q s is taken from a
            continuous emission source with a total flow rate of Q, typical value of Q s is much
            less than Q, Q s ≪ Q. Characterization of the sample leads to the concentration of
            certain air pollutant in the sample as C s . If this sample can be used to represent the
            total gas, one can claim that the concentration of the corresponding air pollutant in
            the main stream C 0 is the same as c s .
              Now consider a simplified case as follows. The total gas flow rate discharged
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            from a stack to the atmosphere is Q (m /s), and a sample is taken with a volume
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            flow rate of Q s (m /s) for a period of time, t(s). Analysis of this sample, either in situ
            or in a laboratory setting, shows that the mass of air pollutant of interest is m (kg).
            With this information, one can calculate the mass concentration of the air pollutant
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            in the sample c ¼ m=Q s t (kg/m ). If the sample is representative, it can be used to
            represent the concentration of the air pollutant in the stack: C = c. Then the mass
            flow rate, _ m, of this air pollutant in the stack is determined as

                                           Qm
                                       _ m ¼  ðkg=sÞ                    ð15:16Þ
                                           Q s t

              The emission rate of the air pollutants can be calculated with the data obtained
            from the samples. However, the samples taken from different stacks are different in
            temperature, pressure, and moisture contents. The calculated results shall be cor-
            rected to a standard temperature and pressure and expressed on a dry basis. This
            standardized measure allows the source test results under different conditions to be
            comparable to regulatory standards or the results of other similar tests.
              A common standard for emission test report is to correct the concentrations
            against 50 % excess air, 7 or 12 % of CO 2 ,or7%ofO 2 . Take 12 % of CO 2 as an
            example, the calculated emission rate is converted using the equation that follows.
            Actual procedure is much more complex, and readers are encouraged to seek local
            guidelines for more information.
                                                   12 %
                               C std 12 % CO 2 Þ ¼ C s                  ð15:17Þ
                                  ð
                                                100 %   y CO 2
                     is the mole fraction of CO 2 in the stack gas measured (e.g., following
            where y CO 2
            US EPA Method 3).
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