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Alafia River Minimum Flows and Levels - Southwest Florida Water ...

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flow reductions that would result in more than a 15% reduction in the number of<br />

days of inundation during Block 3. Analyses of similar decreases in the number<br />

of days a range of flows at the USGS Lithia gage were exceeded was also used<br />

to identify a percent-of-flow reduction for the block. These percent-of-flow<br />

reductions were considered to be limiting factors <strong>and</strong> used for development of a<br />

prescribed flow reduction (PFR3) for Block 3.<br />

4.9 Prescribed Flow Reductions for Lithia Springs Major <strong>and</strong><br />

Buckhorn Springs Main<br />

Because the range of flows or discharge from Lithia Springs Major <strong>and</strong> Buckhorn<br />

Springs Main is substantially less than that of the <strong>Alafia</strong> <strong>River</strong> (e.g., see Figures<br />

2-18, 2-28 <strong>and</strong> 2-31 ), prescribed flow reductions were evaluated for application<br />

on a year-round basis rather than for seasonal blocks. To develop prescribed<br />

flow reductions for both springs, changes in the availability of aquatic habitat for<br />

selected fish species <strong>and</strong> macroinvertebrate populations were evaluated using<br />

the Physical Habitat Simulation Model (PHABSIM). Flow requirements for<br />

recreational swimming at Lithia Springs Major were also considered to determine<br />

whether this factor could be used to identify a prescribed flow reduction.<br />

4.9.1.1 PHABSIM – Application for Lithia Springs Major <strong>and</strong> Buckhorn<br />

Springs Main (Buckhorn Creek)<br />

PHABSIM was used to evaluate potential habitat changes associated with<br />

variation in flow in the Lithia Springs Major run <strong>and</strong> in Buckhorn Creek,<br />

downstream from Buckhorn Springs Main. Simulations were conducted for<br />

various life-history stages of spotted sunfish, largemouth bass, bluegill <strong>and</strong> for<br />

macroinvertebrate community diversity. Maximum flow reductions that resulted<br />

in no more than a 15% reduction in habitat from historic conditions were<br />

determined to be limiting factors. These factors were used for consideration in<br />

the development of prescribed flow reductions for the springs.<br />

For the Lithia Springs Major run, PHABSIM data were collected at three crosssections<br />

at a single site between April <strong>and</strong> July of 2004. Reconstructed flows<br />

from 1983 through 2002 (see Section 2.3.4.3.2) were used for the time series<br />

component of the analysis. For the sampled site on Buckhorn Creek, field-data<br />

were collected at thee PHABSIM cross-sections in July <strong>and</strong> August of 2004.<br />

Because the <strong>Alafia</strong> <strong>River</strong> controls water level in Buckhorn Creek when river stage<br />

rises, due to flow events or tidal influences, sampling was conducted with<br />

consideration of the local tide schedule. Reconstructed low flows from Buckhorn<br />

Springs Main from 1988 through 2002 (see Section 2.3.4.3.2) were used for the<br />

time series component of the analysis. A second time series analysis was also<br />

performed for Buckhorn Springs using the flow record for Buckhorn Creek.<br />

4-26

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