The sulfidic Frasassi cave system affords a unique opportunity to investigate niche relationships among sulfur-oxidizing bacteria, including epsilonproteobacterial clades with no cultivated representatives. Oxygen and sulfide concentrations in the cave waters range over more than two orders of magnitude as a result of seasonally and spatially variable dilution of the sulfidic groundwater. A full-cycle rRNA approach was used to quantify dominant populations in biofilms collected in both diluted and undiluted zones. Sulfide concentration profiles within biofilms were obtained in situ using microelectrode voltammetry. Populations in rock-attached streamers depended on the sulfide/oxygen supply ratio of bulk water (r=0.97; P<0.0001). Filamentous epsilonproteobacteria dominated at high sulfide to oxygen ratios (>150), whereas Thiothrix dominated at low ratios (<75). In contrast, Beggiatoa was the dominant group in biofilms at the sediment–water interface regardless of sulfide and oxygen concentrations or supply ratio. Our results highlight the versatility and ecological success of Beggiatoa in diffusion-controlled niches, and demonstrate that high sulfide/oxygen ratios in turbulent water are important for the growth of filamentous epsilonproteobacteria.
Sulfidic caves form in limestone (CaCO3) rocks where sulfide-rich groundwater interacts with oxygen at the water table. The Frasassi cave system hosts a rich, sulfur-based lithoautotrophic microbial ecosystem (Sarbu et al., 2000; Vlasceanu et al., 2000; Macalady et al., 2006, 2007; Jones et al., 2008). Previous studies of the geochemistry of the cave waters have revealed that they are mixtures of slightly salty, sulfidic groundwater diluted 10–60% by oxygen-rich, downward-percolating meteoric water (Galdenzi et al., 2007). Initial observations of the abundant biofilms in cave streams and pools suggested that they respond dynamically to seasonal and episodic hydrologic changes. In particular, we noted that changes in specific conductivity (tracking freshwater dilution) and water flow characteristics correspond with morphological differences in the biofilms. Our initial observations motivated a systematic, multi-year study of the population structure of biofilms collected from cave waters with a wide range of hydrological and geochemical characteristics. The goal of this study was to identify the ecological niches (defined as the range of environmental conditions that permit growth) of major biofilm-forming populations.
Unraveling the effects of changing hydrologic conditions on microbial growth within the cave system is not trivial because dilution of the sulfidic groundwater has multiple effects relevant to microbial metabolism. The input of meteoric water increases water depth and flow rates, dilutes dissolved species in the sulfidic aquifer and adds dissolved oxygen. Water flow conditions that increase turbulence also increase sulfide degassing from the water and oxygen transport into the water from the oxygenated cave air. We investigated microbial populations using a full-cycle rRNA approach. Environmental conditions were measured using microelectrode voltammetry and bulk water geochemical analyses. We found that both sulfide/oxygen ratios and physical water flow characteristics are important for determining the distributions of sulfur-oxidizing groups.
Materials and methods
Field site, sample collection and geochemistry
The Grotta Grande del Vento-Grotta del Fiume (Frasassi) cave system is actively forming in Jurassic limestone in the Appennine Mountains of the Marches Region, Central Italy. The waters of the cave system are near neutral (pH 6.9–7.4) and have specific conductivities ranging from 1200 to 3500 μS cm−1, or roughly 4–5% of average marine salinity. The major ions are Na+, Ca2+, Cl−, HCO3− and SO42− (Galdenzi et al., 2007). Concentrations of electron donors and acceptors other than sulfur species and oxygen are as follows: bicarbonate (5.3–7.1 mM), ammonium (30–175 μM), methane (1–20 μM), dissolved iron (<0.1 μM), dissolved manganese (<0.04 μM), nitrate (not detected, <0.7 μM) and nitrite (not detected, <2.0 μM). Organic carbon concentrations range between 0.16 and 4.5 mg l−1.
Biofilms from cave springs and streams were collected from 5 to 40 cm water depth at sample locations shown in Figure 1 in May (wet season) and August (dry season) in 2005, 2006 and 2007. Biofilms were harvested using sterile plastic transfer pipettes into sterile tubes, stored on ice and processed within 4–6 h of collection. Subsamples for fluorescence in situ hybridization (FISH) were fixed in 4% (w/v) paraformaldehyde and stored at −20 °C. Samples for clone library construction were preserved in four parts RNAlater (Ambion/Applied Biosystems, Foster City, CA, USA) to one part sample (v/v). Water samples were filtered (0.2 μm) into acid-washed polypropylene bottles and stored at 4 °C until analyzed. Conductivity, pH and temperature of the waters were measured in the field using sensors attached to a 50i multimeter (WTW, Weilheim, Germany). Dissolved sulfide and oxygen concentrations were measured in the field using a portable spectrophotometer (Hach Co., Loveland, CO, USA) using the methylene blue and indigo carmine methods, respectively. Duplicate sulfide analyses were within 1% of each other. Replicate oxygen analyses were within 20% of each other. Nitrate, nitrite, ammonium and sulfate were measured at the Osservatorio Geologico di Coldigioco Geomicrobiology Lab using a portable spectrophotometer within 12 h of collection according to the manufacturer's instructions (Hach Co.). Light microscopy was performed on live samples within 8 h of collection on a Zeiss Model 47-30-12-9901 optical microscope ( × 1250) at the Osservatorio Geologico di Coldigioco Geomicrobiology Lab.
Voltammetric signals are produced when dissolved or colloidal species interact with the surface of a gold amalgam working electrode. Electron flow resulting from redox half-reactions at a 100 μm diameter tip is registered as a current that is proportional to concentration (Skoog et al., 1998; Taillefert and Rozan, 2002). The gradients associated with microbial metabolism in biofilms are thus readily measured using this technique. Aqueous and colloidal species that are electroactive at gold amalgam electrode surfaces include: H2S, HS−, S8, polysulfides, S2O32−, S4O62−, HSO3−, Fe2+, Fe3+, FeS(aq), Mn2+, O2 and H2O2 (Luther et al., 1991, 2001; Xu et al., 1998; Taillefert et al., 2000; Druschel et al., 2003, 2004; Glazer et al., 2004, 2006). Voltammetric analyses of dissolved sulfur, iron and other species in the field were accomplished using a DLK-60 potentiostat powered with a 12 V battery and controlled with a GETAC ruggedized computer. To protect the electrochemical system from drip waters and high humidity, the potentiostat was contained inside a storm case containing dryrite humidity sponges and modified with rubber stripping to allow the communication ribbon cable and electrode cables to go outside the case while keeping the inside sealed. Electrodes were constructed as described in Brendel and Luther (1995).
Voltammetric analyses in the cave system involved placing working (gold amalgam) electrodes into a narishege three-axis micromanipulator with a two-arm magnetic base on a steel plate. At each sampling location, the reference and counter electrodes were placed in the flowing water near the biofilm. The working electrode was lowered to the air–water interface, then to the biofilm–water interface and subsequently lowered in increments to profile the biofilm. We used both cyclic voltammetry between −0.1 and −1.8 V (vs Ag/AgCl) at scan rates from 200 to 2000 mV s−1 with a 2 s conditioning step, and square wave voltammetry between −0.1 and −1.8 V (vs Ag/AgCl) at scan rates from 200 to 1000 mV s−1, with a pulse height of 25 mV. Analyses were carried out in sets of at least 10 sequential scans at each sampling point in space, with the first three scans discarded.
Clone library construction
Environmental DNA was obtained using phenol–chloroform extraction as described in Bond et al. (2000) using 1 × buffer A (100 mM Tris, 100 mM NaCl, 25 mM EDTA, 1 mM sodium citrate, pH 8.0) instead of phosphate-buffered saline for the first washing step. Small subunit ribosomal RNA genes were amplified by PCR from the bulk environmental DNA. Libraries were constructed from four samples using the bacteria-specific primer set 27f and 1492r. Each 50 μl reaction mixture contained environmental DNA template (1–150 ng), 1.25 U ExTaq DNA polymerase (TaKaRa Bio Inc., Shiga, Japan), 0.2 mM each dNTPs, 1 × PCR buffer, 0.2 μM 1492r universal reverse primer (5′-GGTTACCTTGTTACGACTT-3′) and 0.2 μM 27f primer (5′-AGAGTTTGATCCTGGCTCAG-3′). A universal library was constructed from sample FS06-12 using universal forward primer 533f (5′-GTGCCAGCCGCCGCGGTAA-3′) and 1492r. Thermal cycling was as follows: initial denaturation 5 min at 94 °C, 25 cycles of 94 °C for 1 min, 50 °C for 25 s and 72 °C for 2 min followed by a final elongation at 72 °C for 20 min. PCR products were cloned into the pCR4-TOPO plasmid and used to transform chemically competent OneShot MACH1 T1 Escherichia coli cells as specified by the manufacturer (TOPO TA cloning kit; Invitrogen, Carlsbad, CA, USA). Colonies containing inserts were isolated by streak plating onto Luria–Bertoni agar containing 50 μg ml−1 kanamycin. Plasmid inserts were screened using colony PCR with M13 primers (5′-CAGGAAACAGCTATGAC-3′ and 5′-GTAAAACGACGGCCAG-3′). Colony PCR products of the correct size were purified using the QIAquick PCR purification kit (Qiagen Inc., Valencia, CA, USA) following the manufacturer's instructions. Full-length sequences for 70–80 clones from each bacterial library were obtained, in addition to 60 sequences from the universal library constructed from sample FS06-12.
Sequencing and phylogenetic analysis
Clones were sequenced at the Penn State University Biotechnology Center using T3 and T7 plasmid-specific primers. Sequences were assembled with Phred base calling using CodonCode Aligner v.1.2.4 (CodonCode Corp., Dedham, MA, USA) and manually checked for ambiguities. The nearly full-length gene sequences were compared against sequences in public databases using BLAST (Altschul et al., 1990) and submitted to the online analyses CHIMERA_CHECK v.2.7 (Cole et al., 2003) and Bellerophon 3 (Huber et al., 2004). Putative chimeras were excluded from subsequent analyses. Non-chimeric sequences were aligned using the NAST aligner (DeSantis et al., 2006), added to an existing alignment containing >150 000 nearly full-length bacterial sequences in ARB (Ludwig et al., 2004), and manually refined. Alignments were minimized using the Lane mask (1286 nucleotide positions) (Lane, 1991). Phylogenetic trees were computed using neighbor joining (general time-reversible model) with 1000 bootstrap replicates. Neighbor-joining trees were compared with maximum likelihood trees (general time-reversible model, site-specific rates and estimated base frequencies). Both analyses were computed using PAUP* 4.0b10 (Swofford, 2000).
Probe design and FISH
Probes were designed and evaluated as described in Hugenholtz et al. (2001), including checks against all publicly available sequences using megaBLAST searches of the non-redundant databases at National Center for Biotechnology Information (NCBI). FISH experiments were carried out as described in Amann (1995) using the probes listed in Table 1. Oligonucleotide probes were synthesized and labeled at the 5′ ends with fluorescent dyes (Cy3, Cy5 and FLC) at Sigma-Genosys (St Louis, MO, USA). Cells were counterstained after hybridization with 4′,6′-diamidino-2-phenylindole (DAPI), mounted with Vectashield (Vectashield Laboratories Inc., Burlingame, CA, USA) and viewed on a Nikon E800 epifluorescence microscope. Images were collected and analyzed using NIS Elements AR 2.30, Hotfix (Build 312) image analysis software. The object count tool was used to measure areas covered by cells hybridizing with specific probes. Ten images were collected for each sample, taking care to represent the sample variability, and a total DAPI-stained area of approximately 3 × 104 μm2 (equivalent to the area of 5 × 104 E. coli cells) was analyzed for quantitation.
The program MINITAB (Minitab Inc., State College, PA, USA) was used for all statistical analyses. A two-sided Student's t-test was used to compare sulfide/oxygen ratios associated with Thiothrix and epsilonproteobacteria, and correlations between parameters were analyzed using the Pearson method.
Nucleotide sequence accession numbers
Field observations and geochemistry
Two common biofilm morphologies were collected from a variety of sample sites in the cave system (Figure 1) over a 3-year period: (1) rock-attached streamers and (2) biofilms developed on the surface of fine sediment. Streamers 1–5 mm thick and 5–20 cm long were attached to rocks in quickly flowing or turbulent water (Supplementary Figure 1, upper panel). Sediment surface biofilms <1 mm thick were present in eddies or stream reaches with slower flow, at the interface between the water column and fine gray sediment (Supplementary Figure 1, lower panel). We commonly observed the two biofilm types coexisting in a patchwork corresponding to spatial variations in water flow. All of the biofilms contained abundant elemental sulfur particles, as evidenced by microscopic observations of the particles under polarized light and by rapid dissolution of the particles in ethanol (Nielsen et al., 2000).
Dissolved ion concentrations, including concentrations of electron donors and acceptors such as sulfides, ammonium and sulfate, were strongly correlated with specific conductivity (0.89 <r<0.98; P<0.0001). This result is consistent with previous work showing that the cave water geochemistry is controlled primarily by physical mixing processes rather than biological activity (Galdenzi et al., 2007). In contrast, dissolved oxygen concentrations were not strongly correlated with specific conductivity (r=−0.39; P=0.04). Total dissolved sulfide and oxygen concentrations for each biofilm sample collected in the study are plotted in Figure 2.
Voltammetric microelectrodes were used to investigate the spatial variability of sulfide and other redox-active species within biofilms and the surrounding bulk water. Iron species were not detected (Fe2+ and Fe3+ <5 μM, FeS <∼0.5 μM as FeS monomer), consistent with total dissolved Fe concentrations <0.1 μM measured using inductively coupled plasma mass spectrometry. Oxygen concentrations were at or below 15 μM (detection limit) for all waters analyzed, as expected based on values obtained from spectrophotometric tests at the same sites. Microelectrode profiles of sulfide concentrations within biofilms (Figure 3) are discussed below.
16S rDNA clone libraries
Clone libraries were constructed to investigate evolutionary relationships among the most abundant biofilm populations and to facilitate the evaluation of 16S rRNA probes. We recently described the phylogeny of clones from two Frasassi stream biofilms dominated by Beggiatoa species (Macalady et al., 2006). Four additional biofilms were selected for 16S rDNA cloning to capture a wide range of geochemical conditions and biofilm morphologies (Figure 2, cloned samples indicated by large circles). Libraries were constructed using bacteria-specific primers because FISH analyses indicated that the biofilms contained few archaea (described below). Sample FS06-12 was also cloned using universal primers in an attempt to retrieve archaeal sequences, but we only obtained bacterial sequences. Bacterial and universal primer sets yielded similar clones, with sequences most closely related to ‘Thiobacillus baregensis’ accounting for 91% in the universal library and 86% in the bacterial library.
The taxonomy of clones from each library is summarized in Figure 4 and Supplementary Table 1. Between 25 and 97% of the clones in each library were associated with known or putative sulfur-oxidizing clades within gamma-, beta- and epsilonproteobacteria (Figure 4). Gammaproteobacterial clones (Figure 5) include representatives of sulfur-oxidizing groups Beggiatoa (86–92% identity), Thiothrix (92–99% identity) and an unnamed clade containing ‘Thiobacillus baregensis’ (94–99% identity) and the recently described sulfur-oxidizing lithoautotroph Thiovirga sulfuroxydans (86–93% identity) (Ito et al., 2005). Beggiatoa clones were retrieved from four sample locations (Figure 4) and form a coherent clade most closely related to non-vacuolate, freshwater Beggiatoa strains (Ahmad et al., 2006). Most betaproteobacterial clones were related to species of the sulfur-oxidizing genera Thiobacillus (>97% identity) or Thiomonas (90–99% identity).
Epsilonproteobacterial clones (Figure 6) were phylogenetically related to Arcobacter species or to members of the Sulfurovumales, Sulfuricurvales and 1068 groups, which have few or no cultivated representatives. The majority of the clones were associated with the Sulfurovumales clade (Figure 4) and were distantly related to cultivated strains, including the named species Sulfurovum lithotrophicum (88–94% identity). Sulfuricurvales group clones were rare and shared 96–97% identity with Sulfuricurvum kujiense. Frasassi clones in both Sulfurovumales and Sulfuricurvales were most closely related to clones from other sulfidic caves and springs (98–99% identity), including filaments from Lower Kane Cave (LKC) groups I and II (Engel et al., 2003). Arcobacter clones were diverse and only distantly related to the closest cultivated strains (91–94% identity). The 1068 group has no cultivated representatives and contains clones from deep subsurface igneous rocks, sulfidic caves and springs, groundwater and wetland plant rhizospheres. Frasassi clones associated with the 1068 group included phylotypes that shared less than 92% identity with each other, and add significantly to the known diversity within this clade. There was support in both neighbor-joining and maximum likelihood phylogenies for the placement of the 1068 group at the base of the epsilonproteobacteria (Figure 6).
Biofilm morphology and population structure
Twenty-eight biofilms, including those selected for 16S rDNA cloning, were homogenized and examined using epifluorescence microscopy after FISH. Probes and hybridization conditions are listed in Table 1. Probe BEG811 was designed to bind specifically to Beggiatoa populations in environmental samples from Frasassi (Macalady et al., 2006), and matches new Beggiatoa clones retrieved in this study (Figure 5). Probe EP404, targeting epsilonproteobacteria, has no mismatches with Frasassi clones from this or previous studies (n>120), with the exception of seven clones within the Arcobacter and 1068 groups (Figure 6). The EP404 probe does not match any publicly available sequences outside the epsilonproteobacteria.
FISH experiments revealed three major biofilm types, as shown in Figure 2. The dominant group in each biofilm sample accounted for more than 50% of the total DAPI cell area (Figure 2, colored symbols) with one exception (PC05-11). Sediment surface biofilms (n=15) were dominated by 5–8 μm diameter Beggiatoa filaments with abundant large sulfur inclusions and gliding motility. Streamers (n=13) were dominated either by 1.5 μm diameter gammaproteobacterial filaments with holdfasts and sulfur inclusions (Thiothrix), or by filamentous epsilonproteobacteria with holdfasts and no sulfur inclusions (1–2.5 μm diameter). Non-filamentous cells targeted by EP404 made up less than 5% of the EP404-positive cell area in each sample. As reported previously (Macalady et al., 2006), the 23S rDNA probe GAM42a produces no signal from Frasassi Beggiatoa filaments at 35% (v/v) formamide concentration. GAM42a-positive filaments with holdfasts and sulfur inclusions did not bind with probes EP404 or Delta495a. Given these observations, GAM42a-positive filaments could be assumed to be members of the Thiothrix clade. Archaeal cells in the biofilms were rare or not detected using the probe ARCH915. Consistent with this result, bacterial cell area measured using the EUBMIX probe was consistently within 15% of the area measured using the nucleic acid stain DAPI, which stains both archaeal and bacterial DNA. Representative FISH photomicrographs of the three major biofilm types are shown in Supplementary Figure 2.
Niches of sulfur-oxidizing populations
Niche differentiation is defined as the tendency for coexisting populations to have different niches or environmental requirements. This concept is rarely explored in field studies of microorganisms but is one of the processes commonly invoked to explain the enormous complexity of natural microbial communities. This study reveals that at least three niche dimensions (sulfide, oxygen and water flow characteristics) are critical for niche differentiation among major groups of sulfur-oxidizing bacteria present in the cave waters. Filamentous epsilonproteobacteria dominate in waters with high sulfide and low oxygen, while Thiothrix dominate in waters with low sulfide and high oxygen. A similar pattern was suggested by 16S rDNA clone frequencies in a study of LKC (Engel et al., 2004), but has not been demonstrated until now. Figure 2 also shows that either sulfide or oxygen concentrations alone are poor predictors of biofilm compositions. All three of the dominant sulfur-oxidizing groups tolerate very low oxygen concentrations (<5 μM). Furthermore, Beggiatoa-dominated biofilms colonize the entire range of sulfide and oxygen concentrations measured in the cave waters, but only in locations where the shear stress caused by the flowing water is low enough to permit the accumulation of fine sediment.
The role of sulfide and oxygen concentrations in determining the composition of the biofilms is most clearly demonstrated in Figure 7, showing biofilm community composition plotted against sulfide/oxygen ratios. We observed a strong linear correlation between filamentous epsilonproteobacterial area % and the sulfide/oxygen ratio of water hosting streamers (r=0.97; P<0.0001). Correlations between epsilonproteobacterial area % and either sulfide or oxygen concentrations alone were weaker, with r values of 0.82 (P=0.002) and −0.80 (P=0.003), respectively. In sharp contrast to streamer populations, Beggiatoa filaments colonized the entire range of sulfide, oxygen and sulfide/oxygen ratios observed in the cave waters (Figures 2 and 7). Consistent with this result, Beggiatoa biofilms were observed immediately adjacent to both Thiothrix and filamentous epsilonproteobacterial streamers in situ, always in less turbulent or more slowly flowing water.
Although changes in turbulence and water depth have the potential to alter gas exchange and therefore water chemistry, our data suggest that physical effects of water flow are more significant under the range of conditions present in the cave system. Because Beggiatoa filaments lack holdfasts, they can be washed out by flows that are too strong to allow the accumulation of fine sediment. Likewise, non-motile Thiothrix or epsilonproteobacteria filaments may become buried below the zone where oxidants are available in stream reaches that are accumulating sediment.
Our results support the idea that morphological and behavioral adaptations to physical constraints are responsible for the separate niches colonized by large, filamentous bacteria (Schulz and Jorgensen, 2001; Preisler et al., 2007). Similar to Beggiatoa described from other environments, Beggiatoa at Frasassi inhabit diffusion-controlled sediments, and can respond to changing geochemical conditions by gliding vertically in the sediment column. Sulfide concentration profiles through Beggiatoa mats reflect diffusion-controlled transport, although Frasassi sediments differ from typical marine or lacustrine sediments in that sulfide diffuses both from water above and sediment below the biofilms (Figure 3). Non-motile filaments with holdfasts (Thiothrix, filamentous epsilonproteobacteria) colonized niches with strong currents and a narrower supply ratio of turbulently mixed sulfide and oxygen (Figure 7). Interestingly, vacuolated marine Beggiatoa with holdfasts have recently been identified at cold seeps (Kalanetra et al., 2004). Frasassi clones are only distantly related (∼88% identity) to Beggiatoa species with holdfasts (Ahmad et al., 2006), and we did not observe Beggiatoa with holdfasts in any of the cave samples.
Among streamer populations, we observed a strong niche differentiation between Thiothrix and filamentous epsilonproteobacteria based on sulfide/oxygen ratios of bulk water. Microbial activity within biofilms modifies sulfide/oxygen ratios on a submillimeter scale due to oxygen consumption at the biofilm surface and sulfide production from sulfate reduction or sulfur disproportionation deeper in the biofilm. Sulfide concentrations based on microelectrode voltammetry varied up to several fold with depth in individual biofilms, typically reaching the highest values in the center. A representative sulfide concentration profile through epsilonproteobacterial biofilm sample PC06-110 is shown in Figure 3b. Sulfide concentrations within Thiothrix streamers could not be profiled due to their small size and rapid motions in the stream flow. The sulfide concentration just outside biofilm RS05-21 was approximately 200 μM, compared to 350 μM in the interior. On the basis of these values, the approximate range of conditions inside the Thiothrix biofilm are shown as a blue dashed box in Figure 2, and clearly overlap with those permitting the growth of filamentous epsilonproteobacteria. Nonetheless, Thiothrix-dominated biofilms contained at most 3.6 area % epsilonproteobacterial filaments. The lack of epsilonproteobacteria in the interior of Thiothrix biofilms with appropriate sulfide/oxygen ratios can be explained by factors such as competition for other limiting resources, or antagonistic interactions such as antibiotic production.
Both Thiothrix and filamentous epsilonproteobacteria tolerate extremely low oxygen (<3 μM) and low sulfide (<50 μM) concentrations. However, Thiothrix-dominated biofilms do not occur at sulfide concentrations above 210 μM, suggesting that sulfide toxicity may play a role in excluding them from high-sulfide environments. The absence of epsilonproteobacterial filaments in waters with oxygen concentrations above 3 μM is also striking, suggesting that oxygen toxicity may be limiting to epsilonproteobacteria. Functional genomic studies provide some evidence that epsilonproteobacteria are uniquely sensitive to oxygen among proteobacteria inhabiting sulfidic and microoxic environments due to electron transport proteins with the potential to produce millimolar levels of superoxide anions during oxidative stress (St Maurice et al., 2007). Filamentous epsilonproteobacteria are also apparently unable to store elemental sulfur intracellularly, an attribute that may limit their ability to consume toxic levels of oxygen in the absence of high sulfide concentrations. The inability to store intracellular So may also be a disadvantage in permanently or transiently low-sulfide environments such as those where Thiothrix thrive.
Filamentous epsilonproteobacteria have previously been described from LKC, Wyoming (Engel et al., 2003). Frasassi sequences differ significantly from LKC clones, and do not hybridize with previously published oligonucleotide probes LKC59 and LKC1006 targeting environmental groups (Engel et al., 2003). LKC waters have an order of magnitude lower sulfide concentrations than those hosting filamentous epsilonproteobacteria at Frasassi (Figure 2). Nonetheless, Figure 7 shows that the LKC epsilonproteobacteria colonize waters within the niche defined by high sulfide/oxygen supply ratios. As in LKC, no sulfur inclusions were observed in epsilonproteobacterial filaments, suggesting that this is a consistent physiological attribute.
Frasassi biofilms host a wide variety of other known or putatitive sulfur-oxidizing taxa as shown in Figure 4. Close relatives of ‘Thiobacillus baregensis’ are present in all clone libraries analyzed to date, sometimes comprising the majority of clones (for example, sample FS06-12). Circumstantial evidence suggests that members of this novel clade are sulfur oxidizers (Elshahed et al., 2003; Ito et al., 2005). This study is the first to our knowledge to retrieve a significant percentage of Arcobacter clones from a freshwater environment. A marine strain (Candidatus Arcobacter sulfidicus) that grows attached to solid substrates via filamentous sulfur strands in high-flow, microoxic, sulfidic environments has recently been described (Wirsen et al., 2002). Sulfide concentrations for growth of the marine Arcobacter (400–1200 μM) are broadly consistent with the Frasassi environment. Further work will be required to evaluate the ecological roles of Arcobacter and other sulfur cycling populations in Frasassi cave waters.
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This paper was improved by the comments of three anonymous reviewers. We thank A Montanari for logistical support and the use of facilities and laboratory space at the Osservatorio Geologico di Coldigioco (Italy) and S Mariani, S Galdenzi and S Cerioni for expert advice and field assitance. We also thank P D’Eugenio, M Mainiero, S Recanatini, R Hegemann, H Albrecht, K Freeman and R Grymes for assistance in the field. We thank B Thomas and J Moore for water analyses, and L Albertson and T Stoffer for laboratory assistance. E Fleming provided valuable comments on the paper. DE contributed to this research as an undergraduate student and was supported in 2006 by a Barrett Foundation scholarship. This work was supported by grants to JLM from the Biogeosciences Program of the National Science Foundation (EAR 0311854 and EAR 0527046) and NASA NAI (NNA04CC06A). GKD acknowledges support from the American Chemical Society Petroleum Research Fund (43356-GB2) and NSF-EPSCoR-VT (EPS 0236976).
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Macalady, J., Dattagupta, S., Schaperdoth, I. et al. Niche differentiation among sulfur-oxidizing bacterial populations in cave waters. ISME J 2, 590–601 (2008). https://doi.org/10.1038/ismej.2008.25
- Frasassi cave
- microelectrode voltammetry
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