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Gschwend%20thesis.pdf

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-173-<br />

but that direct inputs (e.g. from boating activities) dominate. However,<br />

even at this time, the atmosphere may operate as a buffer and .act as a<br />

sink until the return of concentrations to background levels after summer<br />

weekends. A brief calculation, utilizing the stagnant boundary layer model<br />

of the air-sea interface (Broecker and Peng, 1974; Liss and Slater, 1974)<br />

can show that exchange to the atmosphere may diminish a suddenly increased<br />

concentration of a volatile compound in seawater to less than 20% of the<br />

size of the spike within a week:<br />

.dC D A<br />

flux after spike input = dt =- _ -; x V (Cexcess)<br />

where C = concentration of the organic compound,<br />

t = time<br />

D = diffusion coefficient<br />

z = stagnant boundary layer thickness<br />

A = cross sectional area of diffusion<br />

v = volume of water column under A<br />

C = spike concentration over and above concentration in<br />

excess<br />

equilibrium<br />

rearranging and integrating<br />

for the region of CD,<br />

ln C/C o<br />

C<br />

DA<br />

= -- x t<br />

zV<br />

= C exp C DA x t)<br />

o zV<br />

D = 0.6 x 10-5 cm2/sec based on diffusion coefficient of methane and the<br />

proportion of the square roots of molecular weights<br />

(Witherspoon and Bonoli, 1969; Liss and Slater, 1974).

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