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IV. Measurement Systems                   47

       the primary pollutant -• that react are termed the precursors of the secondary
       pollutants. With the ki owledge that each secondary pollutant arises from
       specific chemical reactions involving specific primary reactants, we must
       control secondary pollute its by controlling how much of each primary
        pollutant is allowed to be e.Tiitted.



                          IV. MEASUREMENT SYSTEMS

          Many methods of air quality measurement have inherent averaging
        times. In selecting methods for measuring air quality or assessing air pollu-
       tion effects, this fact must be borne in mind (Table 4-1). Thus, an appropriate
       way to assess the influence of air pollution on metals is to expose identical
        specimens at different locations and compare their annual rates of corrosion
        among the several locations. Since soiling is mainly due to the sedimenta-
        tion of particulate matter from the air, experience has shown that this can
       be conveniently measured by exposing open-topped receptacles to the
       atmosphere for a month and weighing the settled solids. Human health
        seems to be related to day-to-day variation in pollutant level. It is accepted
       practice the world over to assess suspended particulate matter levels in the
       air by a 24-hour filter sample, which in the United States is acquired by a
       high-volume sampler, known to workers in the field as a hi-vol.
          Because a filter sample includes particles both larger and smaller than
       those retained in the human respiratory system (see Chapter 7, Section
       III), other types of samplers are used which allow measurement of the size
       ranges of particles retained in the respiratory system. Some of these are
       called dichotomous samplers because they allow separate measurement of the
       respirable and nonrespirable fractions of the total. Size-selective samplers rely
       on impactors, miniature cyclones, and other means. The United States has
       selected the size fraction below an aerodynamic diameter of 10 /-tm (PM 10)
       for compliance with the air quality standard for airborne particulate matter.


                                     TABLE 4-1

                                Air Quality Measurement
         Measure of    Cyclic factor  Measurement method with  Effect with same
        averaging time  measured       same averaging time    averaging time
           Year       Annual trend    Metal specimen        Corrosion
           Month      Seasonal cycle  Dustfall              Soiling
           Day        Weekly cycle    Hi-vol                Human health
           Hour       Diurnal cycle   Sequential sampler    Vegetation damage
           Minute     Turbulence      Continuous instrument  Irritation (odor)
   66   67   68   69   70   71   72   73   74   75   76