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-53-<br />

Mass plots for ro/e l09 in the CI-CH4 GCMS analyses showed that,<br />

while only one "octatriene" was found at station 3, additional isomers<br />

had appeared in the surface seawater at station 6. Mass spectra<br />

showed that these compounds were very closely related.<br />

Pentadecane was also found in the upwelling region near Peru<br />

(figurè 2-7). Surface samples contained the highest concentrations<br />

except at the most nearshore station. The 20-m and 100-m samples at<br />

the most offshore station showed atypically high pentadecane concen-<br />

trations.<br />

A comparison of filtered and unfiltered 5- and 20-m samples from<br />

the Peru upwelling region showed 2 samples with 50-60% losses of<br />

pentadecane and i sample with no significant difference on filtering<br />

(Appendix I, Table 1-3). A filtering experiment done on coastal<br />

seawater from Vineyard Sound also showed about one-half removal of<br />

pentadecane on filtering. These losses may be due to a particle<br />

association of a significant fraction of this hydrocarbon.<br />

A particle association of pentadecane may also explain the high<br />

variability observed for this compound in the Atlantic surface<br />

seawater samples (Table 2-1). Replicate samples from the same depth<br />

(e.g., Sargasso Seal lO m and w. Eq. Atl. 24/7 m) showed very poor<br />

reproducibility. Gardner (1977) has found that a large fraction of<br />

the particulate matter in a seawater sample will settle below the<br />

outlet of a 30-liter Niskin. Particle concentrations may be 2-20 times<br />

higher in the dregs of the 30 liter Niskin than in the remainder of<br />

the water. Thus, factors such as the time of standing of the sampler<br />

after retrieval and the sequence of subsampling may have affected the<br />

particle distributions in the subsamples of this work, and as a<br />

resul t, the pentadecane concentrations may have also varied.

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