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

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level, whenever possible. Immature or damaged specimens were identified to<br />

the lowest level possible, given the condition of the organism. To facilitate<br />

identification, Oligochaeta, Chironomidae, <strong>and</strong> Ceratopogonidae were slidemounted<br />

in CMC-10, then examined at up to 100X magnification with a phasecontrast<br />

compound microscope.<br />

4.2.6 Fish Community Assessment <strong>and</strong> Fish Diet Analyses<br />

Fish were collected using habitat-specific backpack electrofishing from dominant<br />

habitats in the <strong>Alafia</strong> <strong>River</strong> corridor. The sampled area was the main stem of the<br />

<strong>Alafia</strong> <strong>River</strong>, approximately 50 yards downstream from Vegetation Transect 64,<br />

located within Alderman Ford Park. Three habitat types (woody debris,<br />

overhanging root wads, <strong>and</strong> bare s<strong>and</strong>/bedrock) were selected for sampling,<br />

based on identification of dominant habitats. On each sample date,<br />

electrofishing was conducted in three sampling reaches, each containing all three<br />

habitat types, resulting in nine total habitat sites per sampling trip. Sampling was<br />

conducted during January <strong>and</strong> March 2004 via electrofishing. Fish were<br />

collected by investigators wading downstream through each habitat. Total<br />

electrofishing time(s) was recorded for each habitat. Upon collection, fish<br />

samples were placed in bags <strong>and</strong> returned to the laboratory for sample<br />

processing.<br />

At the laboratory, fish were identified to species using fish keys <strong>and</strong> individual<br />

fish were measured for total length (TL, mm) <strong>and</strong> weight (nearest 0.01 g).<br />

Electrofishing catch-per-minute (CPM) was used as an index of fish abundance<br />

for each habitat unit. Species-specific CPM values were used as an index of<br />

relative abundance for each species at each habitat type for comparison of<br />

richness <strong>and</strong> community composition across habitats.<br />

Redbreast sunfish, Lepomis auritus, were separated from other species <strong>and</strong> diet<br />

contents were assessed for individuals collected from woody debris <strong>and</strong><br />

overhanging root wad habitats. Fish stomachs were removed <strong>and</strong> diet contents<br />

separated under a dissecting microscope. Prey items were identified to Order or<br />

Family depending on the taxa. Items were counted <strong>and</strong> weighed to the nearest<br />

0.0001 g using an Ohaus AR 2140 balance. Prey item frequency of occurrence<br />

<strong>and</strong> mean composition by number <strong>and</strong> weight were estimated for both habitat<br />

types.<br />

4.3 Modeling Approaches<br />

A variety of modeling approaches were used to develop minimum flows <strong>and</strong><br />

levels for the <strong>Alafia</strong> <strong>River</strong> corridor. HEC-RAS models were developed to<br />

characterize flows at all study sites. Physical Habitat Simulation (PHABSIM)<br />

4-9

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