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Weeki Wachee River System Recommended Minimum Flows and ...

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probably accounts in part for the diminishing r 2 values associated with the higher salinity<br />

isohalines.<br />

The location of the higher isohalines during high flow conditions is beyond the domain of<br />

the volume <strong>and</strong> area by river kilometer regressions which were truncated at Rkm =0.<br />

Thus, estimation of volume (or area) is based on extrapolation of the14 ppt results from<br />

inside the river mouth. Given these uncertainties <strong>and</strong> in order not to unduly weight the<br />

higher isohalines, it was decided to establish the <strong>Weeki</strong> <strong>Wachee</strong> MFL on the mean<br />

percent of flow reduction. The mean of all criteria utilized is 10.1 percent for the Block 1<br />

period <strong>and</strong> is 10.7 percent for the Block 3 period.<br />

8.2 Compliance St<strong>and</strong>ards <strong>and</strong> <strong>Recommended</strong> <strong>Minimum</strong> <strong>Flows</strong> for the<br />

<strong>Weeki</strong> <strong>Wachee</strong> <strong>System</strong>.<br />

In consideration of the results presented, it is recommended that both the wet season<br />

<strong>and</strong> dry season flows for the <strong>Weeki</strong> <strong>Wachee</strong> <strong>River</strong> system be maintained at 90 % of the<br />

baseline flows adjusted for anthropogenic impacts. In the absence of consistent, longterm<br />

flow measurements for Mud Springs, Salt Springs, Mud <strong>River</strong>, Jenkins Springs or<br />

Twin Dees Spring. to evaluate these individually, the assumed MFL for these<br />

waterbodies is also a ten percent reduction in baseline flows. Long-term compliance<br />

st<strong>and</strong>ards in the form of five <strong>and</strong> ten year mean <strong>and</strong> median flows were developed to<br />

accommodate variations in climate. These minimum long-term flow statistics should be<br />

maintained in the presence of withdrawals.<br />

In order to define the compliance st<strong>and</strong>ards <strong>and</strong> to accommodate variations in climate,<br />

the recommended MFL (10% reduction) was applied to the adjusted baseline flows <strong>and</strong><br />

the average daily flow for each calendar year was calculated for the years1967 through<br />

2004. Next a running five year average was determined from these annual averages for<br />

the period of record <strong>and</strong> the minimum five year period identified. The process was<br />

repeated for a ten year moving average. Finally the procedure was repeated using the<br />

median daily flow for the years 1967 through 2004. The results are given in Table 8-2.<br />

Table 8-2<br />

Long-Term <strong>Minimum</strong> <strong>Flows</strong> Corresponding to <strong>Recommended</strong> MFL<br />

<strong>Minimum</strong><br />

Criterion<br />

Flow (cfs)<br />

<strong>Minimum</strong> 10 yr Moving Average<br />

(Based On Annual Average <strong>Flows</strong>) 141<br />

<strong>Minimum</strong> 10 yr Moving Average<br />

(Based On Annual Median <strong>Flows</strong>) 131<br />

<strong>Minimum</strong> 5 yr Moving Average<br />

(Based On Annual Average <strong>Flows</strong>) 136<br />

<strong>Minimum</strong> 5 yr Moving Average<br />

(Based On Annual Median <strong>Flows</strong>) 128<br />

____________________________________________________________________________________________<br />

Proposed <strong>Minimum</strong> <strong>Flows</strong> <strong>and</strong> Levels for <strong>Weeki</strong> <strong>Wachee</strong> <strong>River</strong><br />

Conclusions <strong>and</strong> Recommendations Page 116 of 164

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