Page 182 - Fundamentals of Air Pollution
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148          10. Effects on the Atmosphere, Soil, and Water Bodies

       to atmospheric haze problems associated with power plants, urban plumes,
       and agricultural activities.
         Average airport visibilities over the eastern half of the United States have
       been determined over a period of approximately 25 years (1948-1974) (6).
       Although seasonal variations occur, the long-term trend has been decreased
       visual air quality over the time period.



                                 IV. VISIBILITY

          Holzworth and Maga (16) developed a technique for examining the trend
        in visibility and analyzed data for several California airports. Bakersfield's
        visibility deteriorated over the period 1948-1957, and Sacramento's visibility
        decreased over the period 1935-1958. Los Angeles had decreasing visibility
        from 1932 to 1947, with little change over the period 1948-1959.
          Holzworth (17) reported on the frequency of visibility of less than 7 miles
        for 28 cities. Two periods of record were compared for each city. There
        were increases in low visibility in only 26% of the comparisons from the
        early period (around 1930-1940) to a later period (around the mid-1950s).
          Miller et al. (18), using analyses for Akron, Ohio; Lexington, Kentucky;
        and Memphis, Tennessee, concluded that "summer daytime visibilities
        were significantly lower during the period 1966-69 than visibilities for the
        preceding 4-year period."
          Faulkenberry and Craig (19), in examining the trends at three Oregon
        cities, utilized a modification of the Holzworth-Maga technique by which
        a single statistic can be calculated for each year, indicating the probability
        of observing better visibility at Salem, Oregon, with no trends at Portland
        and Eugene, Oregon over the period 1950-1971.
          Arizona has traditionally been a large copper-producing state. SO X emis-
        sions from copper smelters near Phoenix and Tucson are shown in Fig. 10-
        10 (1). Phoenix is located 100 km from the nearest smelter, and Tucson is
        60 km from the nearest smelter. The improvement in visibility in the
        1967-1968 period was due to a decrease in SO* emissions when there was
        9-month shutdown caused by a strike. Improvement in visibility in the
        mid-1970 was the result of better control technology and process changes.
          Zannetti et al. (20) did an analysis of visual range in the eastern United
        States again showing the importance of humidity but also showing the
        importance of air mass type, which is usually related to its direction of
        origin.
          Mathai (21) summarized the specialty conference on atmospheric visibil-
        ity. With the exception of water content of particles and the measurement
        of organic species, analytical laboratory techniques are readily available
        for particle analysis. Regulatory approaches to mitigate existing visibility
        impairment and to prevent further impairment are being formulated. A
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