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

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flow regimes <strong>and</strong> these life history requirements can be used to develop<br />

protective minimum flows.<br />

To achieve this goal, Physical Habitat Simulation (PHABSIM) protocols have<br />

been added to the District's approach for establishing minimum flows for river<br />

systems. PHABSIM is the single most widely used methodology for establishing<br />

"minimum flows" on rivers (Postel <strong>and</strong> Richter 2003), <strong>and</strong> its use was<br />

recommended in the peer review of proposed MFLs for the upper Peace <strong>River</strong><br />

(Gore et al. 2002). The technique has, however, been criticized, because it is<br />

based on the specific requirements of a few select species (typically fish of<br />

economic or recreational value), <strong>and</strong> it is argued that such an approach ignores<br />

many ecosystem components. This criticism is overcome in the current District<br />

approach for MFLs development, since PHABSIM represents only one of several<br />

tools used to evaluate flow requirements. Results of PHABSIM analyses are<br />

used to assess flow needs during periods of low to medium flows.<br />

3.3.4 Woody Habitats<br />

Stream ecosystem theory emphasizes the role of instream habitats in<br />

maintaining ecosystem integrity. These habitats form a mosaic of<br />

geomorphically defined substrate patches (Brussock et al. 1985), each with<br />

characteristic disturbance regimes <strong>and</strong> macroinvertebrate assemblages (Huryn<br />

<strong>and</strong> Wallace 1987). For instance, invertebrate community composition <strong>and</strong><br />

production in a blackwater river varies greatly among different habitat types,<br />

where the habitats are distinguished by substrates of different stability (e.g.,<br />

s<strong>and</strong>, mud <strong>and</strong> woody debris) (Benke et al. 1984, Smock et al. 1985, Smock <strong>and</strong><br />

Roeding 1986). Ecosystem dynamics are influenced by the relative abundance<br />

of these different habitat types. Changes in community composition <strong>and</strong> function<br />

occurring along the river continuum are in part a consequence of the relative<br />

abundance of different habitat patches, which are under the control of channel<br />

geomorphology <strong>and</strong> flow. For determining MFLs, we identify key habitats <strong>and</strong><br />

features that play a significant role in the ecology of a river system using a<br />

habitat-based approach that includes a combination of best available data,<br />

published research, <strong>and</strong> site specific field work.<br />

Among the various instream habitats that can be influenced by different flow<br />

conditions, woody habitats (snags <strong>and</strong> exposed roots) are especially important.<br />

In low-gradient streams of the southeastern U.S.A. coastal plain, wood is<br />

recognized as important habitat (Cufney <strong>and</strong> Wallace 1980; Benke et al. 1984,<br />

Wallace <strong>and</strong> Benke 1984; Thorp et al. 1990; Benke <strong>and</strong> Wallace 1990). Wood<br />

habitats harbor the most biologically diverse instream fauna <strong>and</strong> are the most<br />

productive habitat on a per unit area basis (Benke et al. 1985). Comparisons of<br />

different instream habitats in a southeastern stream indicates that production on<br />

snags is at least twice as high as that found in any other habitat (Smock et al.<br />

1985).<br />

3-5

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