Page 149 - Fundamentals of Air Pollution
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III. Effects on Forests                117

         Forests can act as sources of some of the trace gases in the atmosphere,
       such as hydrocarbons, hydrogen sulfide, NO X, and NH 3. Forests have been
       identified as emitters of terpene hydrocarbons. In 1960, Went (10) estimated
       that hydrocarbon releases to the atmosphere were on the order of 108 tons
       per year. Later work by Rasmussen (11) suggested that the release of
                                          8
       terpenes from forest systems is 2 x 10  tons of reactive materials per year
       on a global basis. This is several times the anthropogenic input. Yet, it is
       important to remember that forest emissions are much more widely dis-
       persed and less concentrated than anthropogenic emissions. Table 8-2
       shows terpene emissions from different types of forest systems in the
       United States.
         Forest systems also act as sources of CO 2 when controlled or uncontrolled
       burning and decay of litter occur. In addition, release of ethylene occurs
       during the flowering of various species. One additional form of emission
       to the atmosphere is the release of pollen grains. Pollen is essential to the
       reproductive cycle of most forest systems but becomes a human health
       hazard for individuals susceptible to hay fever. The contribution of sulfur
       from forests in the form of dimethyl sulfide is considered to be about
       10-25% of the total amount released by soils and vegetation (12).
         Trees and soils of forests act as sources of NH 3 and oxides of nitrogen.
       Ammonia is formed in the soil by several types of bacteria and fungi. The
       volatilization of ammonia and its subsequent release to the atmosphere are
       dependent on temperature and the pH of the soil. Fertilizers are used as
       a tool in forest management. The volatilization of applied fertilizers may
       become a source of ammonia to the atmosphere, especially from the use
       of urea.
         Nitrogen oxides are formed at various stages of the biological denitrifica-
       tion process. This process starts with nitrate; as the nitrate is reduced
       through various steps, NO 2, NO, N 2O, and N 2 can be formed and, de-
       pending on the conditions, released to the atmosphere.
         The interactions of air pollutants with forests at low-dose concentrations
       result in imperceptible effects on the natural biological cycles of these spe-
       cies. In some instances, these interactions may be beneficial to the forest
       ecosystem. Forests, as well as other natural systems, act as sinks for the
       removal of trace gases from the atmosphere.


       B. Intermediate-Dose Levels
         The second level of interaction, the intermediate-dose level, can result
       in measurable effects on forest ecosystems. These effects consist of a reduc-
       tion in forest growth, change in forest species, and susceptibility to forest
       pests. Both laboratory investigations and field studies show SO 2 to be an
       inhibitor of forest growth. When various saplings have been exposed to SO 2
       in the laboratory, they show reduction in growth compared with unexposed
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