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Air Quality Criteria for Lead Volume II of II - (NEPIS)(EPA) - US ...

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Figure AX7-1.2.1. Long-term (1982-1989) annual trends in lead concentrations (µg/L) in<br />

Lewes, Delaware precipitation.<br />

Source: Scudlark et al. (1994)<br />

The role <strong>of</strong> dry deposition in the total deposition <strong>of</strong> Pb to terrestrial ecosystems is not<br />

constrained well. Researchers have estimated that dry deposition accounts <strong>for</strong> anywhere<br />

between 10 to >90% <strong>of</strong> total Pb deposition (Galloway et al., 1982; Wu et al., 1994; Sabin et al.,<br />

2005). Migon et al. (1997) found total, wet, and dry Pb deposition to be 8.6, 1.6 and<br />

7.0 µg/m2/d, respectively, over the Ligurian Sea, France. Dry deposition velocities were<br />

estimated at approximately 0.2 cm/sec, similar to anthropogenic element deposition velocities<br />

measured at remote lakes around Lake Michigan (Yi et al., 2001). Yi et al. (2001) found that dry<br />

deposition velocities <strong>for</strong> elements were correlated with particle concentrations in the following<br />

order: coarse > total particle > fine particle. Refer to Table 2-21 <strong>for</strong> additional in<strong>for</strong>mation on<br />

dry, wet, and total Pb deposition velocities and fluxes.<br />

Arid environments appear to have a much higher fraction <strong>of</strong> dry deposition: total<br />

deposition (Sabin et al., 2005). Furthermore, it is possible that Clean <strong>Air</strong> Act Legislation enacted<br />

in the late 1970s preferentially reduced Pb associated with fine particles, so the relative<br />

AX7-35

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