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Weeki Wachee River System Recommended Minimum Flows and ...

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similarly across the springsheds examined, then anthropogenic factors acting<br />

disproportionately between one springshed <strong>and</strong> another should show up as departures<br />

between plotted z-sores. Converting spring flows (or water well elevations) to z-scores<br />

allows a direct comparison between spring flows of different springsheds or water<br />

levels. In the absence of anthropogenic effects in the two watersheds, it might be<br />

expected that the normalized historic flows should be correlated. For example, flows for<br />

<strong>Weeki</strong> <strong>Wachee</strong> <strong>River</strong>, <strong>and</strong> Rainbow <strong>River</strong> were converted to z-scores using the mean<br />

<strong>and</strong> st<strong>and</strong>ard deviations for the period 1935 to 1965. The data were then plotted for the<br />

entire period of record with the assumption that the relationship between z-scores for<br />

the st<strong>and</strong>ardization period (1935 to 1965 in this case) should be maintained for other<br />

periods as long as other effects (e.g., anthropogenic withdrawals) did not vary among<br />

the periods examined. Any deviation represents the anthropogenic affect relative to the<br />

st<strong>and</strong>ardization period. To minimize reliance on a particular reference period, a number<br />

of different st<strong>and</strong>ardization periods (1935-65, 1945-65, 1951-63 etc) were evaluated<br />

<strong>and</strong> the strongest relationships were used (See Kelly et al. 2006 for examples). In<br />

application, the mean difference in z-scores of the non-reference period is converted<br />

back into flow by multiplying the difference by the st<strong>and</strong>ard deviation (in cfs) of the<br />

reference period.<br />

Using the z-score approach, the estimated anthropogenic loss (relative to Rainbow<br />

<strong>River</strong> <strong>and</strong> 1951- 63 st<strong>and</strong>ardization period) is 11 cfs. A similar comparison with the<br />

Sharpes Ferry water level resulted in an estimated loss of 16.3 cfs.<br />

2.5.2 Wavelet Analysis<br />

Wavelet transformation of times-series discharge data was undertaken to reduce the<br />

short-term fluctuations for the period 1941 through 2004. The application is described in<br />

more detail in a technical memor<strong>and</strong>um by Schultz (2007) which is included as<br />

Appendix 2-1. The untransformed annual values <strong>and</strong> the wavelet filtered time series is<br />

given in Figure 2-14. Using the smoothed data as input to a regression model, Schultz<br />

analyzed the relationship to rainfall as a continuous variable <strong>and</strong> to the impact of<br />

pumpage as a categorical variable using a regression of the form:<br />

Smoothed Discharge = β o + β 1 * Rain + β 2 * Impact + ε<br />

"Impact" was defined as insignificant (= 0) or significant (=1) <strong>and</strong> was assumed to<br />

continue through time once the impact of withdrawals became significant.<br />

The solution employed was to allow the regression model to determine the point at<br />

which pumpage impacts became significant. The initial run (1941-2004) assumed that<br />

all years were impacted. The second run assumed that years 1942 – 2004 were<br />

impacted. The third run assumed that years 1943 – 2004 were impacted etc until the<br />

point of impact was evaluated for all 64 starting points. F-test <strong>and</strong> r 2 results were<br />

compared. Same year (Lag 0 ), prior year (Lag 1 ) <strong>and</strong> rainfall from two years ago (Lag 2 )<br />

____________________________________________________________________________________________<br />

Proposed <strong>Minimum</strong> <strong>Flows</strong> <strong>and</strong> Levels for <strong>Weeki</strong> <strong>Wachee</strong> <strong>River</strong> Page 30 of 164<br />

Watershed Characteristics

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