Regular Papers
Differences in Bacterial Community Structure on Hydrilla verticillata and Vallisneria americana in a Freshwater Spring
2014 年 29 巻 1 号 p. 67-73
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2014 年 29 巻 1 号 p. 67-73
The phylogenetic composition of the epiphytic bacterial community of an invasive aquatic plant (Hydrilla verticillata) and a native species (Vallisneria americana [eelgrass]) of the Wakulla Spring (Florida) was investigated, along with the water column bacterial composition, using clone libraries of the 16S rRNA genes. The bacterial clones from three clone libraries were classified into 182 operational taxonomic units (OTUs), most of which were affiliated with bacterial divisions commonly found in freshwater ecosystems. Based on the identified classes, the bacterial communities on eelgrass and Hydrilla were distinct, such that Planctomycetes, Cyanobacteria, Bacilli and Actinobacteria were found on eelgrass and in the water column but not on Hydrilla. On the other hand, Deltaproteobacteria and Verrucomicrobiae were found on Hydrilla and in the water column but not on eelgrass. Further distinctions observed were that Armatimonadia and Deinococci were found only on Hydrilla while Gemmatimonadetes was found only on eelgrass. Our results indicated differences between the epiphytic bacterial community on the two plants and the water column at the species level, but an even representation of the most abundant phylogenetic taxa (classes) in all three libraries was revealed. Statistical comparison of the retrieved sequences confirmed that the three libraries did not differ significantly at the community level (LIBSHUFF, p <0.05).
Hydrilla (Hydrilla verticillata, [L.F. Royle]), a known global species (25) and native to the warm water regions of Asia (17), is a major invasive aquatic plant and one of the most studied submerged vascular plants. The predominance of Hydrilla in the macrophytic communities of infested water bodies is attributed to its mat-forming tendency, the absence of indigenous biological control agents and the relatively low light levels needed to achieve half-maximal photosynthetic rates (12).
Hydrilla was first revealed in the USA around 1960 at two sites in Florida, a canal near Miami and in Crystal River (3, 25). Due to its rapid rate of spread (25), by the 1970s Hydrilla was distributed throughout the state of Florida (USA), affecting most major freshwater bodies of all drainage basins (25). The invasive plant has become a major problem in water bodies (3, 25) such as Wakulla Spring, which is part of the longest and deepest known submerged freshwater cave systems in the world (9) and is classified as a natural treasure. In Wakulla Spring, dense stands of Hydrilla have crowded out V. americana, the predominant native submerged plant, causing its decline and in some locations complete displacement (43). This occurs because canopy-forming species such as Hydrilla reduce light to deeper waters and sediments where the major portion of the V. americana shoot biomass is distributed (1).
The loss of V. americana, commonly called eelgrass, tape grass or vallis, can result in profound shifts in fauna, including commercial and recreational species. Freshwater eelgrass is a dioecious, perennial, aquatic bottom-rooted submerged (27) macrophyte (20) that produces long ribbon-like, lightgreen leaves varying in length (2 m or more) based on the depth and movement of the water (20). Eelgrass beds have ecological significance as they provide refuge, feeding grounds, or habitats to many animals (24), including manatees and various species of fish.
In addition, Hydrilla destroys native fish and wildlife habitats, out-competes indigenous species, resulting in biodiversity reduction (2), alters nutrient cycling and possibly changes habitat structure (13). Whether Hydrilla invasion alters the bacterial community, which plays major roles in ecosystem function has not been widely addressed. According to several reports (10, 42), epiphytic bacterial communities tend to vary based on the plant species. A change in the plant species in an aquatic system could possibly result in a shift in the bacterial community structure of the system. Since bacteria play a vital role in biogeochemical cycles, a change in their community structure could alter certain functions in an entire ecosystem. It has been reported that plant leaf surfaces may serve as hot spots for bacteria since they are able to obtain their supply of carbon from plant exudates (23). Epiphytic bacteria found on aquatic plants are reported to be high in abundance (30, 32) and productivity (4, 23) and are generally larger than free-living bacteria (22). These epiphytic bacteria are likely to contribute significantly to bacterial activity in the ecosystem (41).
Therefore, the replacement of native plant species by the invasive Hydrilla has the potential to harbor and/or introduce a new community of bacteria which may impact the bacterial community structure of the water column and result in ecological changes in the spring ecosystem. On the other hand, both Hydrilla and eelgrass belong to the same family, Hydrocharitaceae, and studies have demonstrated that close plant phylogeny is usually correlated to phylogenetically similar bacterial community structure (33). Thus, to address this potential, the aim of this study was to compare and show distinctions between the bacterial communities of the phyllosphere of the invasive Hydrilla and the native eelgrass and the surrounding spring water to assess evidence that the presence of Hydrilla contributes to changes in the bacteria community structure of the spring water column.
The study site for this investigation was Wakulla Spring, located in Wakulla County State Park, Florida, USA. The spring is a first-magnitude spring discharging water at an average of 16.9 m3 s−1 into the Wakulla River, which flows 14 km to the southeast where it joins St. Mark’s River, which empties into the Gulf of Mexico. The Wakulla Spring bowl is approximately 0.000012 km2 while the Wakulla River is approximately 0.29 km2. The Wakulla Spring/River is protected in a 24. 28 km2 preserve known as the Edward Ball Wakulla Springs State Park (34). Since 1997, the spring has been infested with Hydrilla verticillata. During Hydrilla bloom, the spring is approximately 70–80% covered with Hydrilla.
For this study, two sites were selected during spring 2012 within the Wakulla Spring/River area, Site 1 (N30°14.155′, W084°17.747′) and Site 2 (N30°14.162′, W084°17.777′) (Fig. 1). The two sites selected have similar nutrient availability and water variables (Table 1). They are very close in proximity (approximately 100 m apart) and were two of the regular sampling sites for other objectives of an ongoing study. The water temperature of the spring was measured on site using a YSI instrument (YSI Incorporated, Yellow Springs, OH), while water pH (AR15-Fisher Scientific, Pittsburg, PA) was determined in the laboratory.
Wakulla Spring with sampling sites.
| Water Environmental Variables | Site 1 | Site 2 |
|---|---|---|
| Temperature (°C) | 21.3 | 21.3 |
| pH | 8.33 | 8.30 |
| NH3-N(mg L−1) | 0.50 | 0.56 |
| Total phosphate (mg L−1) | 0.02 | 0.02 |
| Chlorophyll-a (μg L−1) | 5.90 | 7.40 |
| Dissolved organic carbon (mg L−1) | 0.35 | 0.35 |
Leaves and stems from Hydrilla, as well as leaves from eelgrass plants, were collected along with 2 L water samples in duplicate from the two selected sites in the spring. The plant parts were gathered using a mesh that traps the upper sections of eelgrass and Hydrilla. Plants were transferred to sterile plastic bags containing spring water from the collection site. Water samples were collected in sterile bottles using a Vertical Point Water Sampler (Aquatic Research Instrument, Hope, ID). In addition, water samples for nutrient analysis were collected for subsequent delivery to the City of Tallahassee Water Quality Laboratory (Tallahassee, FL) for analyses following various EPA methods (Chlorophyll by SMI0200H, Nitrogen Nitrite plus Nitrate by EPA 353, Total phosphorus as P by EPA 365.4 and Organic Carbon Dissolved by SM5310B). Water and plant samples were immediately transported on ice to the laboratory where leaves and stems of Hydrilla and leaves of eelgrass were rinsed 3 times with sterilized water to remove loosely attached bacteria and then sectioned into small pieces (approximately 1.2 cm). Twenty grams of each plant sample (wet weight) were stored at −20°C for subsequent DNA extraction. Three liters of composited water samples from both sites were filtered through 0.2 μm Nucleopore track-etched membrane filters (Whatman Laboratory, NJ) to capture bacteria and the filters were stored at −20°C for subsequent DNA extraction.
DNA extraction, amplification and cloningDNA was extracted from the Hydrilla and eelgrass plant parts following the protocol of Burke et al. (8) with some modification. Briefly, 20 g plant material from Hydrilla and eelgrass from each site were placed in 500 mL sterilized water (in triplicate) and incubated at room temperature for 2 hours while shaking at 80 rpm to dislodge attached bacteria. Following incubation, plants parts were removed and the remaining water was filtered through 0.2 μm Nucleopore track-etched membrane filters (Whatman Laboratory). Community DNA was extracted from the 0.2 μm filters using the MoBio PowerWater DNA Isolation Kit (MoBio, Carlsbad, CA) following the manufacturer’s instructions. Total DNA was also extracted directly from 200 mg of the leaves and stems of Hydrilla and leaves of eelgrass (kept at −20°C) in duplicate using the MoBio PowerPlant Pro DNA Isolation Kit (MoBio) and also from the filter membranes containing bacterial cells from the original water samples using the MoBio PowerWater DNA Isolation Kit (MoBio) according to the manufacturer’s instructions.
Universal eubacterial primers 27F (5′-AGAGTTTGATCCTGG CTCAG-3′ and 1492R (5′-TACGGCTACCTTGTTACGACTT-3′ (35) were used to amplify 16S rRNA gene fragments. The polymerase chain reaction (PCR) mixture was prepared using Taq Mastermix (Denville Scientific, Metuchen, NJ) with 2 μL template DNA, PCR grade sterile water and 5 pmol μL−1 of each primer in a total reaction fluid of 25 μL. Sterile water was used as negative controls in each batch of PCR reactions. The PCR reactions were performed in a Biorad thermocycler (Hercules, CA) under the following conditions: initial denaturation at 94°C for 5 min, followed by 30 cycles at 94°C for 1 min, annealing at 55°C for 1 min, 72°C for 1 min and a final extension at 72°C for 10 min. Product size and purity were confirmed by electrophoresis in 1% agarose gels stained with ethidium bromide. PCR products were composited to generate 2 clone libraries (Hydrilla and eelgrass). A third clone library was generated from the DNA extracted from the water sample. Composited PCR products were purified using MoBio UltraClean PCR Clean-up DNA Purification Kit (MoBio) and cloned into pCR-XL-TOPO vector using the TOPO XL PCR cloning kit (Invitrogen, Carlsbad, CA) in accordance with the manufacturer’s instructions. For each clone library, randomly selected clones containing the insert of the appropriate length (~1,500 bp) were grown in liquid LB medium with kanamycin and their plasmids were purified using the MoBio UltraClean Standard Mini Plasmid Prep Kit for DNA sequencing (MoBio). Purified plasmids were amplified with the cloning kit M13F and M13R primers to confirm the presence of the insert. PCR products were purified with MoBio UltraClean PCR Clean-up DNA Purification Kit (MoBio) and sequenced by the DNA Sequencing Laboratory at Florida State University using M13F and M13R primers. Forward and reverse sequence reads were obtained for each clone and assembled manually using the ClustalW aligning utility tool (http://www.ebi.ac.uk/Tools/clustalw2/index.html), after manually removing vector contamination. The final length of each clone was approximately 1,400 bp. The sequences were screened for chimeras using the DECIPHER program (http://decipher.cee.wisc.edu/FindChimeras.html). Chimerical sequences were excluded from further analysis.
Phylogenetic analysisPhylogenetic analysis was performed using the mothur pipeline v. 1.26.0 by Schloss et al. (38). Cleaned sequences were aligned using the Silva reference database via the mothur alignment command. Aligned sequences were screened and filtered to remove problematic sequences and sequences classified as chloroplasts. DNA distance matrices were calculated and used to define the number of operational taxonomic units (OTUs) at sequence divergences of 3% (38). All OTUs were compared with GenBank entries using BLAST (http://www.ncbi.nlm.nih.gov/blast) to find the nearest relatives. Phylogenetic trees were constructed from the combined clone libraries with reference sequences from GenBank by the neighbor-joining algorithm based on distances calculated by the Jukes-Cantor model and implemented in the MEGA4 (Molecular Evolutionary Genetics Analysis) software package (40). To confirm the robustness of the tree, bootstrapping was performed with 1,000 replications. Sequences shorter than 1,000 bp were excluded from phylogenetic analysis. OTU-based analysis was performed to determine the number of OTU, Shannon index, chao1 estimates and library coverage. Dendrogram using the thetaYC calculator was generated to determine similarities among the bacterial communities in the clone libraries and LIBSHUFF was used to test comparisons among all the OTUs from all three libraries at 97% similarity. A Venn diagram was constructed to visualize the comparisons and overlaps.
The 16S rRNA gene sequences generated in this study have been deposited in GenBank under accession numbers KC189621– KC189809.
Water physical and chemical variables (Table 1) were similar at the two sites except for the chlorophyll-a concentration. The reason for this difference is not known because both sites share similar characteristics and are close in proximity. However, based on a report by the Florida Department of Environmental Protection, the chlorophyll-a concentration in the spring occurs over a wide range of 1 μg L−1–7.2 μg L−1 (16).
Richness and evenness of the bacterial communitiesThe richness (Chao1), diversity indices (Shannon), and biodiversity coverage of the clone libraries are shown in Table 2. Similarity (97%) analysis revealed 182 OTUs (54 from the Hydrilla library, 48 from the eelgrass library, and 80 from the water library) (Table 2). The Shannon diversity index ranged from 3.7–4.1 with the water column having the highest values. The Chao1, a nonparametric richness estimate of true species diversity in a sample, ranged from 151–335 (Table 2) with eelgrass having the highest value. Coverage analyses indicated that the libraries contained 34% to 58% (Table 2) of the total number of OTUs in the samples.
| Shannon | Chao1 | Coverage | # of clones | # of OTUs | |
|---|---|---|---|---|---|
| Hydrilla | 3.6 | 151 | 58% | 96 | 54 |
| Eelgrass | 3.7 | 335 | 34% | 64 | 48 |
| Water | 4.1 | 206 | 52% | 125 | 80 |
The construction of clone libraries to determine the composition of bacterial assemblages on leaves and stems of aquatic plants and water samples yielded 143, 145 and 118 clones from Hydrilla, water and eelgrass, respectively, from the two combined sampling sites in Wakulla Spring. Following chimera and chloroplast removal, 96, 125 and 64 clones of Hydrilla, water and eelgrass, respectively, were subjected to further analysis.
The composition of the clone libraries is shown in Fig. 2, Fig. S1–S4, and Table S1. Based on the 182 OTUs retrieved across the three libraries (Table 2), 15 known classes were identified (Fig. 2). Phylogenetic analysis showed that most of the commonly identified freshwater bacterial classes were present in the two plant species and the surrounding water column. The Alphaproteobacteria, Betaproteobacteria, Gammaproteobacteria, Sphingobacteria, and Flavobacteria were the dominant classes in all of the three clone libraries; Deltaproteobacteria and Cytophagia were also present in all three samples but in much lower abundance. The term “abundance” is used in an abstract sense and refers to relative abundance of ribotypes (16S rRNA gene OTUs) and not to cell abundance.
Relative abundance of different bacterial classes found in the clone libraries of Hydrilla, eelgrass and water collected from Wakulla Spring.
Planctomycetes, Cyanobacteria, Bacilli, and Actinobacteria were detected in the eelgrass and water clone libraries but not in the Hydrilla library. Verrucomicrobiae were retrieved from both the Hydrilla and water column clone libraries but not from the eelgrass. Deltaproteobacteria were also only detected in Hydrilla and water. Armatimonadia and Deinococci were present only in the Hydrilla clone library, while Gemmatimonadetes was detected only in the eelgrass clone library.
At the genus level, the identified genera differed among the three libraries. Flavobacterium and Rhodobacter were the only common genera found among the libraries (Table 3). Rhodobacter and Flavobacterium were also the most abundant genera in both eelgrass and Hydrilla clone libraries, while Rhodobacter and Ilumatobacter were the most abundant in the water.
| Bacterial class/Genera | Eelgrass | Hydrilla | Water |
|---|---|---|---|
| Class; Gemmatimonadetes | + | − | − |
| Gemmatimonas | + | − | − |
| Class; Armatimonadia | − | + | − |
| Armatimonas/Armatimonadetes_gp1 | − | + | − |
| Class; Cytophagia | + | + | + |
| Flexibacter sp. | − | + | − |
| Class; Deinococci | − | + | − |
| Truepera | − | + | − |
| Class; Betaproteobacteria | + | + | + |
| Undibacterium | + | − | + |
| Hydrogenophaga | + | − | − |
| Acidovorax | − | + | + |
| Inhella | − | + | − |
| Limnobacter | − | + | − |
| Limnohabitans | − | − | + |
| Polynucleobacter | − | − | + |
| Class; Alphaproteobacteria | + | + | + |
| Methylophilus | − | + | − |
| Sphingopyxis | − | − | + |
| Rhizobium | + | − | + |
| Porphyrobacter | + | − | − |
| Rhodobacter | + | + | + |
| Sandarakinorhabdus | + | − | − |
| Novosphingobium | − | + | − |
| Sphingomonas | − | + | + |
| Devosia | − | − | + |
| Class; Gammaproteobacteria | + | + | + |
| Coxiella | + | − | − |
| Pseudomonas | − | + | + |
| Cellvibrio | − | + | + |
| Steroidobacter | − | + | − |
| Legionella | − | − | + |
| Vibrio | − | − | + |
| Class; Sphingobacteria | + | + | + |
| Leadbetterella | − | − | + |
| Arcicella | + | − | − |
| Haliscomenobacter | + | − | + |
| Ferruginibacter | + | − | − |
| Chitinophaga | − | − | + |
| Class; Planctomycetia | + | − | + |
| Planctomyces | − | − | + |
| Class; Actinobacteria | + | − | + |
| Ilumatobacter | + | − | + |
| Class; Cyanobacteria | + | − | + |
| Gp1 | + | − | − |
| Class; Flavobacteria | + | + | + |
| Flavobacterium | + | + | + |
| Class; Verrucomicrobia | − | + | + |
| Prosthecobacter | − | − | + |
| Luteolibacter | − | − | + |
| Class; Bacilli | + | − | + |
| Pasteuria | − | − | + |
| Class; Deltaproteobacteria | − | + | + |
| Bdellovibrio | − | + | − |
Similarity in the community structure from Hydrilla, eelgrass, and the water column were measured using thetaYC calculator in mothur (Fig. 3). The results from the library comparison showed low similarity among the three clone libraries based on the relative abundance of OTUs in each library; however, the Hydrilla bacteria appeared to be more closely related to the water column bacteria than to eelgrass bacteria. Nevertheless, LIBSHUFF analysis showed that the three clone libraries were not significantly different (Table 4). No OTUs (Fig. 4) common to all three samples (two plants and water) were detected.
Cluster analysis of the bacterial community in the water column and the epiphytic bacteria on aquatic plants from Wakulla Spring.
| eelgrass | water | |
|---|---|---|
| Hydrilla | 0.015, 0.004 | 0.010, 0.020 |
| eelgrass | 0.004, 0.020 |
Venn diagram of the bacterial OTUs detected on samples of the epiphytic communities from eelgrass and Hydrilla and the water in Wakulla Spring. Numbers in the diagram represent the OTUs retrieved from each library with those in the overlapped areas shared between the overlapping libraries.
The Shannon diversity index showed the water column to have the greatest diversity and abundance of bacteria. This should not be surprising because water is more likely to accommodate a higher diversity of bacteria due to the many various sources through which bacteria can be introduced into the spring. In contrast, the bacterial community on the phyllosphere of the two plants is expected to be more established and stable (11). Bacteria from the native eelgrass had the highest Chao1 richness estimate, exhibiting higher species richness than the Hydrilla and the water column communities. Chao1 takes into account the number of OTUs that appear either once or twice in a library. In our study, the eelgrass library was under-sampled (only 34% coverage) compared to the water and the Hydrilla libraries (52% and 58%, respectively), mainly due to the removal of many chloroplast-like sequences. Although the number of clones screened and sequenced did not represent a full inventory of those present on the plants and water samples based on the findings from this and previous studies (18, 29, 44, 45), the coverage was adequate to provide a full inventory of the dominant species.
Phylogenetic analysisPhylogenetic analysis showed Alphaproteobacteria, Betaproteobacteria, Gammaproteobacteria, Sphingobacteria, and Flavobacteria as the dominant classes in each of the three clone libraries, while Deltaproteobacteria and Cytophagia were also present in all three samples but in much lower abundance. These findings are consistent with the results reported by Crump and Koch (10) who found the phylum Proteobacteria to be dominant on leaf surfaces of angiosperms from Chesapeake Bay. Buesing et al. (7) found Alphaproteobacteria to be the second most abundant group of bacteria after the CFB group on submerged macrophytes in brackish water.
In a study similar to ours in Lake Taihu, He et al. (18) found a high abundance of Cyanobacteria on both eelgrass and Hydrilla whereas in our study, Cyanobacteria was found in low abundance on eelgrass and was completely absent on Hydrilla. Also, rare freshwater phyla such as Gemmatimonadetes, Armatimonadia, Cytophagia, Deinococci, and Verrucomicrobia, were not detected in Lake Taihu. The differences between the epiphytic bacterial communities found in Taihu and Wakulla Spring could be due to geographic location and individuality of the plant species studied.
Other known aquatic classes such as Planctomycetes, Cyanobacteria, Bacilli, and Actinobacteria were found only in the eelgrass and water clone libraries, but not in the Hydrilla library. Among them, Planctomycetes are found in a wide variety of habitats (6) of diverse tropic statuses (37) and are known to be epiphytic (6).
Deltaproteobacteria was found only in the water and Hydrilla libraries, but not in eelgrass, as was the Verrucomicrobiae. Verrucomicrobiae are reported to be active polysaccharide degraders in freshwater environments (28). Boucheret et al. (5) reported that the Verrucomicrobia serve functions similar to those of Bacteroidetes, which are known to degrade biopolymers such as cellulose and chitin (21). Lindström et al. (26) found that they favored increased phosphorus availability. Such correlations between the retrieved taxa and observed ecological functions here and throughout the discussion are used to elucidate the potential role of these taxa in the ecosystems but by no means do they imply that such functions are carried out in the Wakulla Spring system, as we did not conduct any functional analysis.
Other rare taxa found sporadically either in the Hydrilla or in the eelgrass clone library were Armatimonadia and Deinococci, and Gemmatimonadetes, respectively. Although their functions were not studied in this investigation, rare taxa can be important to ecosystem functions (15).
At the genus level, Flavobacterium and Rhodobacter were the only two shared genera among all libraries. Rhodobacter has been associated with active denitrification in the presence of sulfide-free flow water in the Kama River (36) and is commonly found in freshwater. Flavobacteria are also wellknown inhabitants of freshwater systems and are reported to carry out functions such as degradation of complex biopolymers in lake ecosystems (31).
Differences observed in the bacterial taxa between the Hydrilla and eelgrass could be due to variations in the types of plant exudates produced (39). Varieties of plants are reported to contain different leaching metabolites and proportions of chemicals (14). It has been reported that Hydrilla contains compounds such as loliolide, thymidine, octadecanedioic acid (46) and caffeic acid ester (19). Whether the bacteria can utilize these carbon compounds as energy sources is not fully understood; however, this could be an important area for future investigation and contribute to knowledge on the factors that govern the colonization of Hydrilla and eelgrass surfaces.
Differences in the leaf structure of eelgrass and Hydrilla may also affect the bacterial community on them. Hydrilla has small, strap-like leaves that are pointed and grow in whorls of four to eight around the stem, which may provide a more protective habitat for bacterial colonizers. Eelgrass has a broad, straight, flat leaf surface ranging up to 25 mm in width, which could be a challenging habitat for some bacteria to colonize, especially those that have not evolved to survive on surfaces exposed to constant flowing water such as in Wakulla Spring.
Although plant-host specificity is crucial for the structure of the epiphytic bacterial community, the role of the surrounding water is still understudied. Both Hydrilla and eelgrass co-exist in the same habitat, and the samples were taken from plants in close proximity (100 m). The exposure of both plants to the same bacterial milieu (water) has the potential to render all three communities phylogenetically similar (33). In addition, the close phylogenetic relationship of Hydrilla and eelgrass raises the expectation that they may harbor similar bacterial communities at the phylogenetic level (33). However, other special characteristics of each plant such as leaf structure and exudates could have a greater role in dictating the types of microbes that thrive on them (33) and could account for differences in the species retrieved from the two plants.
In one of the first studies comparing the epiphytic bacterial communities on Hydrilla verticillata, eelgrass, and the water column, differences were found at the species level between the epiphytic bacterial community on the two plants and the water column. However, the distribution of bacterial classes was similar in all three communities. Further investigation with a more extensive sampling strategy of the specific phyllosphere bacterial communities on Hydrilla and eelgrass is encouraged to confirm the results from this and other studies (18) and to provide greater insights into the ecological impacts of Hydrilla’s introduction into aquatic systems. Also, further work on the chemical composition of Hydrilla, eelgrass, and other aquatic plant species may provide additional information as to the factors that select the bacterial communities on the two plant species. The results of this study serve as a segue to future studies in this area.
This project was supported by funding from the National Science Foundation HBCU-RISE Program (NSF Grant No. HRD-0932137). We are grateful to Scott Savery from the Wakulla Spring State Park and Scott Barrett Dyer from the Florida Department of Environmental Protection for their help with sample collection from the Wakulla Spring State Park.
