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1,700 cm -1 ; (Figure 6). The elemental analyses of<br />

the resins confirm this tendency toward oxidation over time (oxygen<br />

levels in March 1978 were 5.4 % ; in June 1980, 7 %).<br />

3400 3000 1700 1100 700 cm<br />

1600<br />

31 03-78<br />

22-11-78<br />

20 06-79<br />

17-01-80<br />

24-06-80<br />

Station 5 - FIGURE 6. Infra-red spectrometry of the resins.<br />

The distribution of saturated hydrocarbons determined by gas<br />

phase chromatography (Fig. 7) demonstrates the evolution which led to<br />

the degradation of the n-alkanes (5.99 % to 3.33 %) to n-C30 (Table 1).<br />

It should be noted that by March 31, 1978, this degradation appears to<br />

have begun. Thus there was an increase in the ratios of pristane/n-Cl7<br />

and phytane/n-Cl8 (Table 1). The isoprenoids degraded less easily than<br />

the n-alkanes (TISSOT and al . ) , but by June 1980 these <strong>com</strong>pounds could<br />

no longer be detected. As degradation advanced, the contribution of the<br />

biogenic hydrocarbons increased, and n-alkanes of odd carbon numbers<br />

between n-C25 and n-C35 -- characteristic of the cuticle waxes of higher<br />

plants (Eglington and Hamilton - 1963) — appeared, confirming the terrestrial<br />

contribution to the contents of organic matter in the sediments.<br />

Moreover, the disappearance of the n-paraffins points up<br />

a relative<br />

enrichment in the unresolved <strong>com</strong>plex mixture of the isoalkane and cycloalkane<br />

<strong>com</strong>pounds, and generally in the <strong>com</strong>pounds around n-C30 . It was<br />

possible to demonstrate these last <strong>com</strong>pounds by GPC/MS by measuring<br />

the masses : m/e 217 being characteristic of the tetracyclic<br />

117

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