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-135-<br />

polysulfide volatiles. Particularly attractive candidates are compounds<br />

like the bis-(3-oxoundecyl) di-, tri- and tetra sulfides or bis-(3-acetoxyundec-<br />

5-enyl) disulfide found in the red alga, Dictyopteris spp. (Roller et al.,<br />

1971; Moore, 1971; Moore et al., 1972).<br />

A simple calculation suggests the importance of these polysulfides to<br />

the sulfur cycle. The seawater at CD contained about LO ng-S/kg in the form<br />

of these polysulfides; this represented a standing stock of 20 ~g_S/m2. If<br />

this material was swept into the atmosphere in about 3-4 days<br />

.<br />

(Schwarzenbach<br />

2<br />

et al., 1978), this amounts to the local introduction of about 2 mg-S/m /yr<br />

to the air. This figure is similar to the 2 mg/m2/yr calculated for H2S<br />

and the 6-10 mg/m2/yr for dimethyl sulfide found in the coastal region of<br />

Chesapeake Bay (Maroulis and Bandy, 1977). However, a global biological<br />

source of about 130 mg-S/m2/yr is needed to balance the sulfur cycle (Friend,<br />

1973) .<br />

Other Volatile Organic Compounds. Two halogenated volatiles were observed<br />

in seawater at CD. The first was tetrachloroethylene at about lng/kg.<br />

This value is similar to that reported for the Northeast Atlantic of 0.5<br />

ng/kg, but much lower than the concentration in Liverpool Bay (l20 ng/kg)<br />

(Murray and Riley, 1973). The source of this compound was most likely<br />

anthropogenic as it<br />

et al., 1975).<br />

is heavily used in a direct disperal manner (McConnell<br />

Bromoform (CHBr 3) was also found, particularly in the summer. The<br />

source of this compound was probably the benthic algae (chapter 5 and<br />

Burreson et al., 1975).<br />

Total Volatile Organic Compounds. Figure 3-23 shows the total volatile<br />

organic compound concentrations over a six-month period as measured by

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