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For CO2, of course, canopies form a tremendous sink due to carbon uptake
by leaves. Other gases and airborne particles, including potentially polluting
aerosols such as SO4-2, NH4+, and NO3-, generally exhibit a slight depletion
from canopy top to bottom (e.g., Wimen and Agren
1985, Lovett and Lindberg 1992). Models to predict the severity and
effects airborne pollution on forest ecosystems have been generated, including
models based on wind tunnel simulations (Ould-Dada
2002) and direct measurement of airborne particle concentrations (Kwiecien
1997; Figure 1).

Figure 1. Deposition of pollutants in the canopy
of a mixed pine-oak forest in the Rybnik Coal Basin, Poland.
Values indicate the quantity, in kg per hectare per growing season,
of inorganic particulate aerosols. Inputs to the system (deposition)
include inorganic dust (D) and aerosols trapped by the canopy (A). These
are partitioned into the inorganic particles that remain on leaves (L),
and those that fall through to the forest floor (F). From Kwiecien
(1997).
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