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Chemical Hydrocarbon Analyses Performed at ERCO<br />

For hydrocarbon analyses the samples were thawed, dried with<br />

methanol and extracted by high energy shaking with a mixture of<br />

methylene chloride-methanol (9:1). The extract was fractionated into an<br />

aliphatic (f ) fraction and an aromatic (f ) fraction using silica<br />

gel/alumina column chromatography. A 1 cm diameter X 25 cm column (1 cm<br />

alumina on top of 15 cm silica gel) was used. The f. fraction was<br />

eluted with 18 ml hexane; the f fraction subsequently was eluted with<br />

21 ml of a 1:1 mixture of hexane-methylene chloride. After reducing the<br />

volume of solvent by evaporation, the gross amount (weight) of<br />

hydrocarbon in each fraction was determined gravimetrically from an<br />

evaporated and dried aliquot of the extract. The extracts were<br />

subjected to quantitative glass capillary-gas chromatographic (GC)<br />

analysis. Selected aromatic fractions also were analysed by <strong>com</strong>bined<br />

glass capillary gas chromatographic/mass spectrometric (GC/MS) analysis<br />

for qualitative identification of individual <strong>com</strong>pounds and<br />

quantification of minor <strong>com</strong>ponents. Participation in an<br />

intercalibration exercise under the direction of the National Analytical<br />

Laboratory indicated that these analyses were at the state^ of the art<br />

with repeatable ± 20% detection of hydrocarbons in the ng g dry weight<br />

sediment range. The details of GC and GC/MS analysis employed are as<br />

follows:<br />

CC: Hewlett Packard 5840A reporting GC with glass; splitless<br />

injection inlet system; 30 m glass capillary column coated with SE-30 (s<br />

100,000 theoretical plates); FID detector; temperature programmed at<br />

60-275°C min ; helium carrier gas 1 ml min ; transmission of<br />

integrated peak areas and retention time through HP 18846A digital<br />

<strong>com</strong>munications interface to a PDP-10 <strong>com</strong>puter for storage, retention<br />

index and concentration calculations. Deuterated anthracene (f.) and<br />

androstane (f ) were used as internal standards and response factors<br />

were determined with known concentrations of the reported <strong>com</strong>pounds. GC<br />

analysis was used to quantitate <strong>com</strong>ponents of the f. fraction.<br />

GC/MS: Hewlett Packard 5985 quadrapole system (GC/MS Computer);<br />

mass spectrometer conditions: ionization voltage=70 eV, electron<br />

multiplier voltage=2200 V, scan conditions 40 amu to 500 amu at 225 amu<br />

s~ . Quantification of <strong>com</strong>ponents of the f fraction was ac<strong>com</strong>plished<br />

by mass f ragraentography wherein the stored GC/MS data is scanned for<br />

parent ions (m ) . The tabulated total ion currents for each parent ion<br />

is <strong>com</strong>pared with deuterated anthracene (internal standard) and an<br />

instrumental response factor applied. Authentic polynuclear aromatic<br />

hydrocarbon standards were used to determine relative response factors<br />

(when no standard was available a response factor was assigned by<br />

extrapolation) .<br />

In vitro Biodegradation<br />

Sediment was collected at sites 6 and 7 in November, 1979 for in<br />

vitro biodegradation experiments. Replicate one hundred gram portions<br />

of sediment were placed into 250 ml flasks to which 50 ml of a sterile<br />

solution containing 0.5% KNO + 0.5% KH 2 P0 4 and 0.5 ml of light Arabian<br />

crude oil were added. The flasks were agitated on a rotary shaker at

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