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-93-<br />

Lillick, 1937). Possibly, the benthic algae were responsible for these<br />

autumn nutrient depletions.<br />

Phytoplankton ~<br />

Chlorophyll ~ concentration peaked in late winter in both years<br />

(figure 3-7). Beginning in December, 1977 phaeophytin was determined<br />

and showed increased importance suggesting either the active degradation<br />

of chlorophyll ~ or the return of degradation products to the water<br />

column as winter storms stirred up the sediment.<br />

Phytoplankton counts revealed a tremendous late-winter bloom of<br />

Thalassiosira nordenskioeldii. Several million cells per liter were<br />

found at the peak of this bloom. The appearance of this diatom bloom<br />

coincided with the February, 1978 chlorophyll ~ maximum and the disap-<br />

- -3<br />

pearance of N03, PO 4 ' and Si02. More than 85% of the bloom population<br />

(by cell numbers) consisted of this species.<br />

Other Observations<br />

In the fall (end of September and again at the beginning of November)<br />

large beach washups of the seagrass, Zostera marina, and associated<br />

macroalgae occurred with the incidence of strong storm activity. These<br />

washups may not be solely attributable to stormy weather, but also to a<br />

weakening of the plants by physiological changes generally thought to<br />

occur at this time of year (Sand-Jensen, 1975; Ragen and Jensen, 1978).<br />

These plant materials could be seen to be pulverized in the surf zone<br />

and were responsible for greatly increasing the turbidity of the shallow<br />

water.

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