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-179-<br />

gas chromatograph equipped with a flame ionization detector (FID) and<br />

splitless injector. Samples were chromatographed on an SE 54 glass<br />

i.d. x 20 m long) supplied by Dr. K. Grob (EAWAG, Dubendorf, Switzerland).<br />

The columns were held at room temperature for 8 min. and then programmed<br />

from 20 to 2000C at 30C/min. for the SE54 or 20 to l800C at 30C/min. for<br />

the UCON. Helium was the carrier gas (ca. i ml/min.) Compound cone<br />

trations were calculated based on peak height relative to the l-cl-nC8<br />

standard and were not corrected for stripping efficiency and FIU response<br />

(e. g. the Fin is about 4 times more sensitive to l-cl-nC~ than to bromo-<br />

form on a weight basis).<br />

Gas chromatography-mass spectrometry was performed on a Finnigan<br />

3200 GC-MS system using an SE52 glass capillary column (0.3 mm i.d. x 20 m<br />

long). Electron impact spectra were acquired with an electron potential<br />

of 70 eV. Chemical ionization spectra were obtained with methane as the<br />

reagent gas at 950 ~ and with electron energy of l30 eV.<br />

RESULTS<br />

Table 5-2 lists the major components identified, the GC retention times<br />

on the two columns, and whether EI or CI spectra were acquired. Sample<br />

spectra are shown in Appendix V.<br />

relative to the even l-chloro-n-alkanes.<br />

Retention indices were calculated<br />

Algal production and release of individual volatile organic compounds<br />

has been estimated by subtracting the seawater control concentration from<br />

that observed with the algae, and then dividing by the weight<br />

en-<br />

of the sample.<br />

These results are shown in Table 5-3 for the hydrocarbons and Table 5-4 for the<br />

halogenated methanes. Most of the discussion will be restricted to samples<br />

which showed more than 5 times the concentration of a given compound relative<br />

i i<br />

to the control seawater. Increases of only 2 - 5 times over control levels

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