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Gschwend%20thesis.pdf

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-32-<br />

A third set of seawater samples was collected at 6 stations in<br />

March, 1978 on cruise 73 of the R/V Knorr to the upwelling region off<br />

the coast of Peru (figure 2-1). A single 30-liter Niskin was used.<br />

Water was drawn from the bottle through a polypropylene tube and an<br />

in-line filter (precombusted 142 mm glass fiber filter in a stainless<br />

steel holder) which were rinsed with a portion of the sample. Reagent<br />

bottles (2-liter) with ground-glass stoppers were filled with seawater,<br />

poisoned with O. 5ml HgCl2 solution (40 mg HgCl2 per ml water), and<br />

then tightly stoppered. Filtering and poisoning were done to prevent<br />

biological activity from altering the volatile organic compound<br />

content of the samples during storage.<br />

. 0<br />

Samples were stored at 4 C in<br />

the dark for 3 to 6 weeks until being returned to the lab at Woods Hole.<br />

IIi order to check for the effects of filtering and poisoning<br />

treatments, some replicate samples were left untreated while others<br />

were only poisoned. Untreated samples were always drawn first, then<br />

unfiltered samples, and finally those that were filtered.<br />

Samples for salinity, oxygen, nutrients, chlorophyll ~, and<br />

phaeophytin were drawn from the same Niskin bottle and analyzed on<br />

board.<br />

Analysis of Volatile Organic Compounds<br />

The seawater samples from the Sargasso Sea and the western<br />

Equatorial Atlantic were analyzed for volatile organic compounds<br />

using the "Tenax method." Details of this method are provided in<br />

Appendix I. It is chiefly adapted from methods reported in the<br />

literature (Zlatkis et al., 1973; Bellar and Lichtenberg, 1974; May<br />

et aL., 1975).

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