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and phytane/n-Cl8 were among the highest and that this degradation was<br />

among the most advanced (Table I). In figure 5, a continual decrease<br />

in saturated hydrocarbons is noted over time (33 % on March 31, 1978<br />

— 22 % on June 24, 1980). In spite of a maximum aromatic hudrocarbons<br />

content observed in June 1979, they underwent the same type of evolution<br />

(34.3 % on March 31, 1978 -> 24.8 % on June 24, 1980). The result<br />

is an increase in the relative contents of resins ; but it should be<br />

noted that in March 1978, polar <strong>com</strong>pound contents (24.6 %) were higher<br />

at this station, which is located in the outer part of the Aber, than<br />

at Station 5 (17.2 %) where the marine character is more pronounced.<br />

This level held true until June 1979, when the increase became the<br />

same as at Station 5 .<br />

This phenomenon can be explained by the presence of polar <strong>com</strong>pounds<br />

of terrestrial origin deposited by the river which flows into<br />

the Aber. This contribution of autochthonous organic matter is seen<br />

in the presence of n-alkanes of odd carbon numbers (n-C25, 27, 29, 31,<br />

33) in the aliphatic fraction, all the more accentuated by the significant<br />

acceleration in the degradation of the normal fossil paraffins<br />

(Fig. 12) The result is a relative enrichment in cyclic satured hydrocarbons<br />

(cycloparaf fins) — particularly of 3-, 4-, and 5-membered<br />

rings around n-C30 — which are less easily degradable .<br />

Chromatogram profiles of the aromatic hydrocarbons indicate how<br />

polluted the station is, principally in the FDP response (Fig. 13),<br />

where the persistence of dibenzothiophene and its alkylate derivatives<br />

(and also of naphthobenzothiophenes) may be noted. The stability of<br />

these <strong>com</strong>pounds made it possible for us to use these chromatograms as<br />

the "fingerprints" of the pollution.<br />

As a matter of fact, according to the DGMK. report, biogenic<br />

hydrocarbons of terrestrial origin (recent sediments) are poor in<br />

aromatic <strong>com</strong>pounds (< 5 %) , and particularly low in sulfurous <strong>com</strong>pounds<br />

of the thiophenic type.<br />

The evolutions observed in the resins are similar to those at<br />

Station 5 ; an oxidizing degradation increases the oxygen contents<br />

(8.5 % in June 1980), and an upward curve is noted in the infra-red<br />

absorption bands of the hydroxyls and carbonyls, the latter of which<br />

are predominantly carboxylic acid <strong>com</strong>pounds (Fig. 14). Metal and sulfur<br />

contents remain fairly constant over time.<br />

Station 8<br />

This station was distinguished in being the farthest from the<br />

sea, in an area of sandy mud. Hydrocarbon contents show that the<br />

decontamination process at this station was virtually nil (Fig. 4) .<br />

An anomaly is noted in January 1980, when the hydrocarbon contents<br />

went over 5,000 mg-/kg of sediment. As we shall see below, this<br />

is due to pollution from petroleum cuts or fuel oil which was later<br />

deposited on top of the pollution under study (Fig. 15 and 16). Althrough<br />

information is lacking on some samples, which were too small,<br />

it can be seen that metal and sulfur contents remained very stable<br />

over time.<br />

123

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