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Hydrography of the Russian River Estuary - Sonoma County Water ...

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Figure 3.41. Change in dissolved oxygen from 7 September. Units are mg/L.<br />

The change in DO (Figure 3.41) was calculated in <strong>the</strong> same way as for salt (Figure<br />

3.38), by directly obtaining <strong>the</strong> difference between observed values and values<br />

observed on 7 September. Fur<strong>the</strong>r, as for salt, one can calculate <strong>the</strong> total mass <strong>of</strong><br />

oxygen dissolved in <strong>the</strong> estuary from data obtained from CTD pr<strong>of</strong>iles – see Figure 3.37<br />

and associated description <strong>of</strong> how DO values are integrated over estuary volume. For<br />

<strong>the</strong> outer estuary (from Sheephouse Creek to <strong>the</strong> mouth), and below <strong>the</strong> elevation <strong>of</strong> <strong>the</strong><br />

water level at closure, <strong>the</strong> total oxygen mass is shown in Figure 3.42. The DO mass<br />

decreased by about 40% during <strong>the</strong> closure (7 September to 5 October). A small<br />

increase in DO mass on 26 September coincides with a possible wave overwash event<br />

(Figure 3.40), but this may also be due to an error associated with tilting <strong>of</strong> <strong>the</strong><br />

pycnocline owing to strong winds that day (see next section).<br />

62

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