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Gschwend%20thesis.pdf

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-122-<br />

The winter peaks of heptadecane are of unknown origin. Possibly,<br />

they reflect the return to the water from the sediments of previously<br />

deposited material.<br />

The increased concentrations of all the n-alkanes in late May, 1978<br />

wi th "cpr" of 1. 4 indicate<br />

a pollution event. However, only acenaphthalene<br />

and 2-ethyl naphthalene covary with the n~,alkanes among the various naphtha-<br />

lene isomers investigated. Possibly the source was of a higher boiling<br />

or weathered petroleum fraction.<br />

As was the case for naphthalene, the n-alkanes were also found in<br />

abundance in the restrips (figure 3-16). The filtering experiments also<br />

demonstrated that about half the concentrations of these compounds could<br />

be retained by a glass fiber filter. One concludes that these compounds<br />

occur in seawater either adsorhed to particles or associated with<br />

microorganisms.<br />

(The hexadecane peak in March and April was due to the occurrence<br />

of another compound coeluting (figure 3-l6); this is supported by GCMS.)<br />

Aldehydes. A group of straight chain aldehydes (C6-CIO) were recovered<br />

throughout the year from the seawater at CD (figure 3-18). These<br />

compounds represent a highly reactive, both biochemically and chemically 1<br />

group of volatiles. The temporal variation of the aldehydes in restrips<br />

is similar to that seen in the initial (figure 3-18) strips and would be<br />

expec ted to be so from the known poor recoveries of these compounds.<br />

The most important feature of the year-round patterns for these aldehydes<br />

was the concentration maxima in the spring and fall corresponding to<br />

periods of algal blooms (see discus.sion of nutrients and chlorophyll ~).<br />

This was most pronounced in the spring when the phytoplankton bloom was<br />

most intense (figure 3~19). These compounds may be the result of direct

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