07.09.2014 Views

The Determination of Minimum Flows for Sulphur Springs, Tampa

The Determination of Minimum Flows for Sulphur Springs, Tampa

The Determination of Minimum Flows for Sulphur Springs, Tampa

SHOW MORE
SHOW LESS

Create successful ePaper yourself

Turn your PDF publications into a flip-book with our unique Google optimized e-Paper software.

DRAFT<br />

northern shore <strong>of</strong> the upper spring run (Figure 2-5C). Plants that are common along this<br />

reach include leatherfern (Acrostichum danaeifolium), cattail (Typha domingensis),<br />

elderberry (Sambucus canadensis), and brazilian pepper (Schinus terebinthefolius).<br />

Other species that occur along the northern shore <strong>of</strong> the upper run include groundsel<br />

tree (Baccharis halimifolia), string lily (Crinum americanum), peppervine (Ampelopsis<br />

arborea), rosary pea (Arbrus precatorius), s<strong>of</strong>tstem bulrush (Scirpus tabernaemontani)<br />

and giant bulrush (Scripus cali<strong>for</strong>nicus). <strong>The</strong>re are no shoreline plants established along<br />

the southern bank <strong>of</strong> the upper spring run, as a retaining wall reaches to the water's<br />

edge.<br />

<strong>The</strong> banks <strong>of</strong> the lower spring run (below the weir) are steep with scattered concrete<br />

rubble. Vegetation along this reach <strong>of</strong> the run is dominated by leatherfern, brazilian<br />

pepper, with some string-lilly, Ceaser weed (Urena lobata) and climbing aster (Aster<br />

caroliniana). With the exception <strong>of</strong> brazilian pepper, the plants along both the upper and<br />

lower spring run are native wetland species that are common along the tidal freshwater<br />

and oligohaline reaches <strong>of</strong> southwest Florida rivers (Clewell et al. 2000).<br />

3.7.3 Benthic macroinvertebrates<br />

3.7.3.1 1997 Macroinvertebrate survey<br />

Historic data <strong>for</strong> macroinvertebrates in the <strong>Sulphur</strong> <strong>Springs</strong> system are limited, but<br />

in<strong>for</strong>mative. On November 19, 1997, staff from SWFWMD and FDEP did a qualitative<br />

sampling <strong>of</strong> the benthic macroinvertebrates in <strong>Sulphur</strong> <strong>Springs</strong> run. Macroinvertebrates<br />

were sampled by sweeps <strong>of</strong> a D-frame dip net (600 micron mesh) from unvegetated<br />

portions <strong>of</strong> the channel bottom, shoreline plant communities, and small woody snags in<br />

the spring run. Flow from the spring pool was at a rate <strong>of</strong> 41 cfs, and as described in<br />

Section 2.3, this collection occurred during a several-year period when withdrawals<br />

were limited to only a few days in April <strong>of</strong> 1997. On the day <strong>of</strong> sampling, dissolved<br />

oxygen concentrations measured at one pr<strong>of</strong>ile in the middle <strong>of</strong> the spring run were 5.2<br />

mg/l; pH was 6.94; and surface and bottom salinity values were near 1.6 ppt. <strong>The</strong><br />

collection occurred during a high flow event from the Hillsborough River Reservoir and<br />

the lower Hillsborough River was fresh near the mouth <strong>of</strong> the spring run.<br />

Taxonomic identifications were per<strong>for</strong>med by staff from the FDEP. A list <strong>of</strong><br />

macroinvertebrate taxa collected from the spring run is provided in Appendix B, along<br />

with species that were collected in later years by the Florida Fish and Wildlife<br />

Conservation Commission. <strong>The</strong> invertebrate species collected in 1997 included<br />

freshwater taxa and a number <strong>of</strong> euryhaline species common to tidal creeks and coastal<br />

springs. <strong>The</strong> crustacean fauna was characterized by amphipods, isopods, decapods, a<br />

cumacean and a mysid species that are common to tidal creeks and other low salinity<br />

habitats. Though not quantified, the amphipods and isopods seemed particularly<br />

abundant. Although these species are most common in low salinity waters, most can<br />

3 - 12

Hooray! Your file is uploaded and ready to be published.

Saved successfully!

Ooh no, something went wrong!