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Gschwend%20thesis.pdf

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-174-<br />

2 A=lcm<br />

z = lO<br />

-2<br />

em corresponding to a wind velocity of 4.5 m/sec<br />

3<br />

V = 200 cm<br />

then DA/zV = 3 x<br />

-6<br />

10 / sec<br />

(Kanwisher, 1963)<br />

depth at CD ca. 2 meters.<br />

and af ter i hour C exp (-DA! zV) x (t) = 0.99C<br />

0 0<br />

af ter i day<br />

= 0.78C 0<br />

af ter 3 day<br />

= 0.46C 0<br />

af ter i week = O. 16C 0<br />

Thus, if 30 ng o-xylene/kg were added to a 5 ng o-xylene/kg background,<br />

degassing would reduce an observed concentratiòn of 35 ng o-xylene/kg<br />

to 10 ng o-xylene/kg within 1 week. This reduction would be even faster<br />

if wind speeds were greater or if other sinks such as mixing with cleaner<br />

wa ter also were available.<br />

SUMRY<br />

Several independent approaches have been taken in an effort to assess<br />

the transport öf C2- and C3-bè zenes to coastal seawater.<br />

The data suggest that the atmosphere was not an important route of<br />

delivery of these aromatic compounds to the seawater in the summer. The<br />

highest concentrations of C2- and C3-benzenes ever observed at CD were<br />

associated with motorboat traffic on a summer weekend. Two other lines of<br />

evidence suggest that the air was not a source of these compounds to coastal<br />

seawater in the period from late spring through fall. First, the inhomogeeity<br />

of concentrations in surface seawater from Vineyard Sound indicated that

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