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
DRAFT abundance estimates in number per square meter, they do give perspective on the relative dominance of different taxa in the sampled habitats. Percent composition values for the two dates are included as Appendices C and D. Shoreline vegetation supported the most taxa of any habitat: 27 taxa in the 2001 collection and 33 taxa in the 2003 collection. Cattail habitat had 27 taxa in the 2003 collection, 13 of which were not recorded in the shoreline vegetation category. Since cattails are shoreline plants, a total of 46 taxa were recorded in combined shoreline vegetation in the 2003 collection. Cattails were also sampled in 2001 but not listed as a separate category. Thus, the shoreline vegetation category exhibited a large increase in species richness with the return to normal flows. In 2001 the percent composition of the shoreline vegetation was dominated by Tarebia granifera (41.5%), snails of the family Hydrobiidae (34.8%) and oligochaetes (13.6%), primarily of the family Naididae. In 2003 the shoreline vegetation community had much less Tarebia (6.4%) and oligochaetes (0.4%), but a higher percent compositions of isopods (38%), Zygoptera (5.4%) and Tricoptera (16.7%) compared to 2001. Bare sand and filamentous algae had 8 and 10 taxa, respectively, in the 2001 collection. The number of taxa in these habitats increased markedly in the 2003 collection, with 25 taxa reported for bare sand and 27 taxa for filamentous algae. Qualitative sweeps from concrete structures were made in 2001 with 10 taxa reported. This habitat was not sampled in 2003. Snags (submersed wood) and organic debris packs in the channel were sampled in 2003, although the snag habitat was very limited. Tarebia continued to be a dominant species in these habitats with 30% and 41.7% compostion in snags and organic debris. Both of these habitats had significant percentages of amphipods and isopods, the latter being particulary dominat in snags (43.3%). Aquatic insects were common in organic debris packs, which contributed to a fairly high count of total taxa (30) in this habitat. No aquatic insects were reported from snags in 2003, but this may have been due to the very limited amount of snag habitat available for sampling. 3.7.3.5 Quantitative samples from May 2000, November 2001, and December 2003 The FWC collected quantitative samples of macroinvertebrates from benthic habitats in the channel of the spring run on three of the collection dates: May 25, 2000, November 8, 2001, and December 9, 2003. Samples were collected using a petite ponar dredge with an sampling area of 232 cm 2 . Samples were sieved in the field using 300 micron sieve buckets and preserved in 95% ethanol. A full description of the field and laboratory methods for site selection, sample processing, taxonomic identification and enumeration can be found in Allen et al. (2001). The findings of the May 2000 sampling, including discussions or species abundance, evenness and diversity, are presented in the report Allen et al. (2001). The results of the latter two collections will be discussed by the FWC in a final report to be published in 2005. The results from these samples, however, were made available to the District and are presented below. 3 - 18
DRAFT The FWC using a modified stratified sampling design to allocate samples in the two dominant benthic habitats in the spring run; bare sediments and filamentous algae. Although historic quantitative data are not available, it appeared that filamentous algal mats first became common in the spring run during the winter and spring of 2000, when withdrawals reduced spring flow to zero or low rates of flow for successive months in the dry season. These withdrawals greatly reduced current velocities and allowed water from the Hillsborough River to back into the spring run. Algae coverage averaged 38 percent bottom coverage at sites visited in 2000 by Allen et al., with no bare sediments reported in the most downstream sampling zone. However, the return of normal flows has reduced the abundance of filamentous algae in the spring. Benthic algal coverage during December 2003 reported by the University of Florida averaged 6 percent, with coverage exceeding 20 percent at only two of the twenty sites sampled. Abundance values from the three quantitative collections are summarized in Appendix E. Tarebia granifera was by far the most abundant species in all habitats sampled in the 2000 collection, accounting for 84.4 percent of all organisms in the quantitative samples. Nematodes and the crownsnail Pyrgophorus platyrachis were the second and third most abundant taxa. Aside from T. granifera, Nematoda, and P. platyrachis, no other invertebrate taxon accounted for more than two percent of the total organisms in any sample. Pyrgophorus platyrachis was the only taxon that had a statistically significant difference in abundance between habitats, being abundant in algal mats than on bare sediment. Based on evenness (Pielou 1969) and diversity (Krebs 1999) values calculated for the combined habitats, the FWC concluded that the invertebrate community in 2000 was characterized by low species richness and extreme dominance by one species. Even when the qualitative collections were included, the FWC noted (in Allen et al. 2001) that the species composition in 2000 was very different from that reported by the District and FDEP in 1997. The FWC also reported that that invertebrate community evaluations of other coastal spring runs on Florida's west coast (Homosassa and Weeki Wachee) were indicative of more evenly distributed populations and the presence of many more euryhaline species (Sloan 1954; 1956). Data from low salinity zones of the Weeki Wachee and Crystal Rivers sampled by Mote Marine Laboratory (Culter 1996) also support this statement. Compared to the 2000 collection, quantitative sampling in November 2001 found marked changes in the abundance of a number of taxa (Appendix E). Although differences in abundance between these collections have not been statistically tested, some changes seem apparent. The mean density of oligochaetes in combined habitats increased by over a factor of eight between the two periods, from 1,172 to 9,779 number per square meter (/m 2 ), with large increases for members of both the families Naididae and Tubificidae. The total number of mollusks decreased between 2000 and 2001, due largely to decreases in Tarebia granifera. Tarebia decreased from 47,839 to 8,766 numbers/m 2 in the combined habitats. In contrast, the crownsnail Pyrgophorus platyachis increased by over a factor of six, from 3,058 to 19,458 number/m 2 . 3 - 19
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DRAFT<br />
abundance estimates in number per square meter, they do give perspective on the<br />
relative dominance <strong>of</strong> different taxa in the sampled habitats.<br />
Percent composition values <strong>for</strong> the two dates are included as Appendices C and D.<br />
Shoreline vegetation supported the most taxa <strong>of</strong> any habitat: 27 taxa in the 2001<br />
collection and 33 taxa in the 2003 collection. Cattail habitat had 27 taxa in the 2003<br />
collection, 13 <strong>of</strong> which were not recorded in the shoreline vegetation category. Since<br />
cattails are shoreline plants, a total <strong>of</strong> 46 taxa were recorded in combined shoreline<br />
vegetation in the 2003 collection. Cattails were also sampled in 2001 but not listed as a<br />
separate category. Thus, the shoreline vegetation category exhibited a large increase in<br />
species richness with the return to normal flows. In 2001 the percent composition <strong>of</strong> the<br />
shoreline vegetation was dominated by Tarebia granifera (41.5%), snails <strong>of</strong> the family<br />
Hydrobiidae (34.8%) and oligochaetes (13.6%), primarily <strong>of</strong> the family Naididae. In 2003<br />
the shoreline vegetation community had much less Tarebia (6.4%) and oligochaetes<br />
(0.4%), but a higher percent compositions <strong>of</strong> isopods (38%), Zygoptera (5.4%) and<br />
Tricoptera (16.7%) compared to 2001.<br />
Bare sand and filamentous algae had 8 and 10 taxa, respectively, in the 2001 collection.<br />
<strong>The</strong> number <strong>of</strong> taxa in these habitats increased markedly in the 2003 collection, with 25<br />
taxa reported <strong>for</strong> bare sand and 27 taxa <strong>for</strong> filamentous algae. Qualitative sweeps from<br />
concrete structures were made in 2001 with 10 taxa reported. This habitat was not<br />
sampled in 2003. Snags (submersed wood) and organic debris packs in the channel<br />
were sampled in 2003, although the snag habitat was very limited. Tarebia continued to<br />
be a dominant species in these habitats with 30% and 41.7% compostion in snags and<br />
organic debris. Both <strong>of</strong> these habitats had significant percentages <strong>of</strong> amphipods and<br />
isopods, the latter being particulary dominat in snags (43.3%). Aquatic insects were<br />
common in organic debris packs, which contributed to a fairly high count <strong>of</strong> total taxa<br />
(30) in this habitat. No aquatic insects were reported from snags in 2003, but this may<br />
have been due to the very limited amount <strong>of</strong> snag habitat available <strong>for</strong> sampling.<br />
3.7.3.5 Quantitative samples from May 2000, November 2001, and December 2003<br />
<strong>The</strong> FWC collected quantitative samples <strong>of</strong> macroinvertebrates from benthic habitats in<br />
the channel <strong>of</strong> the spring run on three <strong>of</strong> the collection dates: May 25, 2000, November<br />
8, 2001, and December 9, 2003. Samples were collected using a petite ponar dredge<br />
with an sampling area <strong>of</strong> 232 cm 2 . Samples were sieved in the field using 300 micron<br />
sieve buckets and preserved in 95% ethanol. A full description <strong>of</strong> the field and<br />
laboratory methods <strong>for</strong> site selection, sample processing, taxonomic identification and<br />
enumeration can be found in Allen et al. (2001).<br />
<strong>The</strong> findings <strong>of</strong> the May 2000 sampling, including discussions or species abundance,<br />
evenness and diversity, are presented in the report Allen et al. (2001). <strong>The</strong> results <strong>of</strong> the<br />
latter two collections will be discussed by the FWC in a final report to be published in<br />
2005. <strong>The</strong> results from these samples, however, were made available to the District and<br />
are presented below.<br />
3 - 18