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The Determination of Minimum Flows for Sulphur Springs, Tampa

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DRAFT<br />

presented in this report. Dissolved oxygen is also measured at three continuous<br />

recorders operated by <strong>Tampa</strong> Bay Water at Sligh Avenue, Columbus Avenue and the<br />

Crosstown Expressway (kilometers 10.6, 3.7, and 0.2 respectively). However, the DO<br />

data presented below are limited to vertical pr<strong>of</strong>ile measurements included in the three<br />

data sets first described, due to their large number <strong>of</strong> observations and good spatial<br />

coverage in the area between the dam and <strong>Sulphur</strong> <strong>Springs</strong>.<br />

DO concentrations in the Lower Hillsborough River are related to the amount <strong>of</strong><br />

freshwater inflow, particularly in the reach <strong>of</strong> the river above <strong>Sulphur</strong> <strong>Springs</strong>. Box and<br />

whisker plots <strong>of</strong> surface and bottom DO data in segments <strong>of</strong> the river taken from the<br />

combined <strong>Tampa</strong> Bay Water HBMP/HIMP data are presented in Figure 3-22 <strong>for</strong> flow<br />

and no-flow conditions at the Hillsborough River dam. Different patterns are observed<br />

between the upstream and downstream reaches <strong>of</strong> the lower river. Downstream <strong>of</strong> km<br />

7, the distribution <strong>of</strong> surface DO values is generally higher <strong>for</strong> no-flow conditions.<br />

Conversely, upstream <strong>of</strong> <strong>Sulphur</strong> <strong>Springs</strong> (km 12.9), surface DO values are higher <strong>for</strong><br />

flow conditions at the dam. A similar pattern holds <strong>for</strong> bottom DO values in the<br />

HBMP/HIMP data - values <strong>for</strong> no-flow conditions are higher below km 7 and values <strong>for</strong><br />

flow conditions are higher above km 13. It should be noted that bottom DO<br />

concentrations are lowest in the segment nearest to <strong>Sulphur</strong> <strong>Springs</strong> (km 12), which is<br />

probably related to the steep density gradients that occur there during no-flow<br />

conditions (Figures 3-13 and 3-16).<br />

Only some <strong>of</strong> these patterns are apparent in the box and whisker plots <strong>for</strong> the EPCHC<br />

stations (Figure 3-23), which <strong>for</strong> three <strong>of</strong> the stations represent a much longer period <strong>of</strong><br />

record (Figure 3-12). In contrast to the HBMP/HIMP data, distributions <strong>of</strong> surface and<br />

bottom DO concentrations in the EPCHC data appear similar between flow and no-flow<br />

conditions at the two downstream stations (km 0.0 and km 3.5). An important similarity<br />

in the two data sets is they both show that surface and bottom DO concentrations<br />

improve with flow in the reach <strong>of</strong> the river above <strong>Sulphur</strong> <strong>Springs</strong> (upstream <strong>of</strong> km 13).<br />

At Sligh Avenue (km 10.6) the EPCHC data show a pattern similar to the HBMP in that<br />

surface DO values are similar between flow and no-flow conditions, while bottom DO<br />

concentrations are somewhat higher during flow conditions. <strong>The</strong>se results reflect that<br />

the water column is highly stratified in this reach <strong>of</strong> the river during no-flow conditions,<br />

partly due to the effect <strong>of</strong> <strong>Sulphur</strong> <strong>Springs</strong>, which lowers salinity in the surface layers<br />

(Figure 3-16). <strong>The</strong> improvement in DO during flow conditions is likely due to the<br />

inclusion <strong>of</strong> high flow values in those data, which diminish vertical stratification at that<br />

location (Figures 3-18 and 3-19).<br />

3.9.4 Effects <strong>of</strong> low flows on salinity distributions and dissolved oxygen<br />

concentrations between the dam and Sligh Avenue<br />

<strong>The</strong> effects <strong>of</strong> freshwater inflow will be examined throughout the river as part <strong>of</strong> the reevaluation<br />

<strong>of</strong> minimum flows <strong>for</strong> the Lower Hillsborough River. For the evaluation <strong>of</strong><br />

minimum flows <strong>for</strong> <strong>Sulphur</strong> <strong>Springs</strong>, special attention is given in this report to the reach<br />

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