Introduction

Recent studies have broadened the perspective of global microbial diversity in hydrothermal environments. Worldwide, these include deep-sea and continental hydrothermal systems, as well as the increasingly recognized shallow-sea hydrothermal vent systems. Diversity in hydrothermal ecosystems is linked directly to highly variable geochemistry, the corresponding array of potential metabolisms in the form of redox disequilibria, and input of nutrients from external sources (Shock et al. 2005, 2010; Spear et al. 2005, Swingley et al. 2012). The myriad geochemical environments created by water–gas–rock interactions inherent to hydrothermal systems provide energy, nutrients, and essential trace elements, as well as potentially toxic substances (Amend and Shock 2001; Meyer-Dombard et al. 2012a; Pol et al. 2013). For example, many terrestrial hot springs contain elevated concentrations of trace or toxic elements, including As (Aiuppa et al. 2003; Arnorsson 2003; Baba and Sözbilir 2012; Bundschuh et al. 2013; Landrum et al. 2009; Le Guern et al. 2003; Nordstrom et al. 2005; Planer-Friedrich et al. 2006; Price and Pichler 2005; Stauffer and Thompson 1984; Summers Engel et al. 2013). Relevant to the Ambitle Island hydrothermal systems, redox reactions involving arsenic have been shown to drive metabolic processes in continental hydrothermal ecosystems in Yellowstone National Park (Donahoe-Christiansen et al. 2004; Inskeep et al. 2004; Langner et al. 2001; Macur et al. 2004). In fact, the fastest rate of arsenic oxidation in a natural aquatic system was recorded in one Yellowstone National Park hot spring in the Norris Geyser Basin, where arsenite oxidation, ferrihydrite precipitation, and biogenesis of arsenate-rich hydrous ferric oxide (HFO) mats appear to be directly influenced by the presence of sulfide and its consumption by archaeal and bacterial taxa (Donahoe-Christiansen et al. 2004; Inskeep et al. 2004; Macur et al. 2004).

The volcanic Ambitle Island (Papua New Guinea) has received recent attention due to elevated concentrations of arsenic in hydrothermal fluids in Tutum Bay (Akerman et al. 2011; Meyer-Dombard et al. 2012b, 2013; Price and Pichler 2005; Price et al. 2007). Ambitle Island features shallow-sea hydrothermal vents in Tutum Bay and several on-land hot springs characterized by highly elevated levels of bioavailable arsenic that is released into the local ecosystem (Pichler and Dix 1996; Price and Pichler 2005; Price et al. 2013b). While Ambitle Island is sparely populated, the reported >2 ppm total As (two orders of magnitude above the EPA declared safe level for drinking water) may present acute health risk to the local inhabitants, who live in close proximity to the springs. In the shallow-sea sediments of Tutum Bay, diverse bacterial populations dominate the microbial communities, but metabolic functions are poorly constrained because most of the community members are only distantly related to characterized isolates (Meyer-Dombard et al. 2012b). Gene surveys of DNA extracted from biofilms and vent fluid, however, showed that microorganisms are likely involved in the oxidation of arsenite (AsIII) and ferrous iron (FeII) (Meyer-Dombard et al. 2013). Here, we extend the study of Ambitle Island hydrothermal ecosystems to include several terrestrial (on-land) hot springs that feature some of the highest reported arsenic concentrations in terrestrial hydrothermal systems, ~1000× higher than the above-mentioned Norris Geyser Basin system in Yellowstone National Park. We use culture-dependent and culture-independent approaches to assess the archaeal and bacterial diversity and metabolic function in two alkaline, high-arsenic springs, and interpret the findings within a geochemical context. These data add to the global inventory of data garnered from island-based hydrothermal ecosystems, and are compared to other previously published island-based datasets.

Methods

Sample collection

Sediments and associated biofilms were sampled with sterile technique at Kapkai and Waramung springs on Ambitle Island, Papua New Guinea during a one-time research expedition in 2005. Samples were placed in 15-mL Falcon tubes, and either stored at 4 °C (for future culturing) or frozen at −20 °C (for DNA extraction) on return to the lab several hours later. At Waramung Spring, the upper ~1 cm of a fine-grained, black mud was taken from the edge of a small pool. At Kapkai Spring, two locations in an outflow channel were sampled. The first (Kapkai 3) was a fine-grained, light gray sediment covered with a green biofilm, and the second (Kapkai 4) was a soft, light gray, gelatinous sediment capped with a ~2-mm hard siliceous crust. At each Kapkai location, the crust/biofilm and ~0.2 cm of underlying sediment were sampled and homogenized.

Enrichment culturing

Enrichment growth media were designed from available geochemical data for Waramung and Kapkai hot springs (Pichler 2005; Pichler et al. 1999a). A base solution contained (per liter of water): 21.1 g NaCl, 10.5 g Na2SO4, 2.83 g KCl, 0.848 g NaHCO3, 0.71 g Na2SiO3·5H2O, and 10 mL of a 100× trace element solution (containing per liter of water: 3.6 g NaBr, 28.4 g H3BO3, 2.86 g LiCl, 0.69 mg MnCl2·4H2O, 0.432 g RbCl, 0.72 g SrCl2·6H2O, 18.24 mg SbCl3, 0.3864 g NaAsO3, 2.14 mg TiCl, 63.12 mg CsCl, 0.712 g MgCl2·6H2O, 0.06 mg CoCl2, 3.3 mg ZnCl2, 7.7 mg CuCl2·2H2O, 1.32 g AlCl3·6H2O, 0.18 mg Na2MoO4·2H2O, 0.44 mg NiCl2·6H2O). From this base solution, six different media—each at two pHs (6.5 and 8.5)—were designed to target different metabolisms. The medium targeting anaerobic heterotrophy included per liter of base solution: 3 g yeast extract, 3 g peptone, 3.7 mL PNG N/P solution (per liter of water: 14.4 g NH4Cl and 3.6 g KH2PO4), 1.05 mL PNG NO3 solution (per liter of water: 100 g NaNO3), 3 g PIPES (pH 6.5) or AMPSO (pH 8.5) pH buffer, and 0.5 mL 0.2 % resazurin as an oxygen indicator. The headspace gas was N2. The medium targeting aerobic heterotrophy was the same as the anaerobic heterotrophy medium, except that 1.5-mL filtered (0.2 μm) air was added to the headspace and resazurin was omitted. The sulfate-reduction medium targeted both heterotrophic and autotrophic sulfate reducers, and included per liter of base solution: 10 mg yeast extract, 3 g sodium lactate, 3 g sodium acetate, 7.5 mL PNG N/P solution, 3 g PIPES or AMPSO pH buffer, and 0.5 mL 0.2 % resazurin. The headspace gas was a mixture of H2:CO2 (80:20). The medium targeting aerobic arsenite oxidation included per liter of base solution: 10 mg yeast extract, 7.3 mL NO3/PO4 solution (per liter of water: 28.4 g NaNO3 and 3.6 g KH2PO4), 2 mL As(III) solution (per liter of water: 3.2 g NaAsO2), and 3 g PIPES or AMPSO pH buffer. The headspace gas was a mixture of N2:CO2 (70:30), with 1.5 mL filtered (0.2 μm) air. The medium targeting anaerobic chemolithoautotrophy contained per liter of base solution: 10 mg yeast extract, 3.7 mL PNG N/P solution, 1.05 mL PNG NO3 solution, 3 g PIPES or AMPSO pH buffer, and 0.5 mL 0.2 % resazurin. The headspace gas was a mixture of H2:CO2 (80:20), and each tube was amended with elemental sulfur (see below). The medium targeting aerobic chemolithoautotrophy was the same as the anaerobic heterotrophy medium, except that 1.5 mL filtered (0.2 μm) air was added to the headspace and resazurin was omitted. The pH of each medium was adjusted prior to autoclaving. After autoclaving, the following filter-sterilized (0.2 μm) solutions were added to all media: 0.5 mL vitamins (per liter of water: 0.04 g biotin, 0.04 g folic acid, and 0.1 g each of pyridoxine–HCl, thiamine-HCl·2H2O, riboflavin, nicotinic acid, D-Ca-pantothenate, cobalamin, p-aminobenzoic acid and lipoic acid) (Robb and Place 1995), 1.0 mL Fe/EDTA solution (per liter of water: 1.54 g FeSO4·7H2O and 2.06 g Na2EDTA), and 10 mL CaCl2 solution (2.2 g CaCl2·2H2O per liter of water). The media were then heated to a low boil and degassed under a steady stream of the prescribed headspace. Ten milliliter of medium was then transferred to sterile, acid-washed 25-mL Balch tubes. Tubes for aerobic and anaerobic chemolithoautotrophy also contained ~0.3 g S0 (sterilized by heating to 98 °C in an oven for at least 3 days with occasional stirring). Tubes were capped with butyl-rubber stoppers and aluminum seals and then pressurized to 3 bar with the prescribed gas. If appropriate, filtered air or filtered 2.5 % Na2S solution (0.3 mL) was added, prior to inoculation.

Sediment samples from Kapkai and Waramung were mixed with a pH-balanced aqueous base solution to form a slurry for inoculations. Tubes were inoculated using 2 mL of the slurry and incubated at 45 and 80 °C.

Assessment of cell growth

Cells were regularly observed using epifluorescence microscopy at 1300× magnification using a Zeiss Axioskop2 microscope. Cultures (0.5 mL) were fixed with 0.25 mL 10 % formalin solution (Sigma-Aldrich, St. Louis, MO) and stained with 0.75 mL 10 ppm DAPI (4′, 6′ diamidino-2-phenylindole, Sigma) solution for 15 min in the dark. This was then filtered through 0.2 µm, 25-mm black polycarbonate filters (GE/Thermo-Fisher Scientific) and mounted on glass slides using paraffin oil. Cells were enumerated by microscopy to determine growth, and results were binned as follows: “no growth”, “minimal growth” (fewer than 2 doublings observed), “growth” (more than 2 doublings observed), and “growth and successful transfer” (one or more transfers of cells followed by growth as defined by more than 2 doublings).

DNA extraction and 16S rRNA gene amplification

DNA extraction was performed on cell pellets of selected pure cultures, and environmental samples (thawed to room temperature), followed by PCR amplification of both the archaeal and bacterial 16S rRNA gene. Three different extraction methods were used: bead-beating using the PowerSoil DNA Isolation Kit (MoBio Laboratories Inc., Carlsbad, CA), alternative extraction method using heat in the PowerSoil DNA Isolation Kit, and bead-beating using the FastDNA SPIN Kit for Soil (Qbiogene, Carlsbad, CA).

Polymerase chain reaction (PCR) of both archaeal and bacterial 16S rRNA genes was completed with archaeal (21F:5′-TTC CGG TTG TAC CYG CCG GA-3′, 1391R: 5′-GAC GGG CGG TGT GTR CA-3′), modified from DeLong (1992), and bacterial (27F: 5′-AGA GTT TGA TCC TGG CTC AG-3′, 1492F: 5′-GGT TAC CTT GTT ACG ACT T-3′) primers (Lane 1991). Several PCR conditions were used to maximize amplification using a Hybaid PCR Express thermal cycler. PCR for archaea consisted of an initial denaturing step at 95 °C for 5 min followed by 30 cycles of 95 °C for 1 min, 55 °C for 1 min, and 72 °C for 2 min. The final extension step was at 72 °C for 15 min. PCR for bacterial 16S rRNA was similar with an initial denaturing step at 95 °C for 5 min, but followed by 35 cycles of 95 °C for 1 min, 52 °C for 1 min, and 72 °C for 2 min. The extension step was at 72 °C for 5 min. Each 20-µL PCR reaction mixture consisted of 1.8–2.8 µL of 25 mM MgCl2 solution, 2 µL of 10 × PCR Buffer II (Applied Biosystems, Carlsbad, CA), 0.2 µL of 100 mM dNTP Mix (Bioline USA Inc., Taunton, MA), 0.25 µL of 5 U µL−1 AmpliTaq Gold DNA polymerase (Applied Biosystems), 0.5 µL each of forward and reverse primers (1 µM), and 1 µL template DNA. Some of the reactions contained 0.5 µg µL−1 BSA. Products were visualized on a 1.5 % agarose gel using SYBR Green I Nucleic Acid Gel Stain (Cambrex Bio Science Rockland, Inc., Rockland, ME) combined with the PCR product. Products were then cleaned using the Wizard SV Gel and PCR Clean-up System (Promega Corp., Madison, WI) using the manufacturer’s instructions.

16S rRNA gene cloning and sequencing

DNA extraction using the bead-beading method (MoBio PowerSoil kit) was the most successful, and PCR products were cloned and plated on LB agar plates using the Qiagen PCR Cloning Kit (Qiagen, Inc., Valencia, CA) according to manufacturer’s instructions. Colonies were randomly selected and incubated overnight in 3-mL Luria Broth medium with ampicillin. Plasmid DNA was extracted and purified using the QIAPrep Spin Miniprep Kit (Qiagen). Purified DNA concentrations were determined using spectrophotometry, and template DNA was sequenced at Polymorphic DNA Technologies, Inc. (Alameda, CA) and MCLAB (South San Francisco, CA) with either the T7 promoter and SP6 promoter or M13 forward and M13 reverse sequencing primers. Some plasmids were also sequenced using either 958R [5′-YCC GGC GTT GAM TCC AAT T-3′, (DeLong 1992)] for archaea or 907R [5′-CCG TCA ATT CCT TTG AGT TT-3′, (Lane 1991)] for bacteria for optimum overlapping in the middle of the 16S rRNA gene. The total number of bacterial clones sequenced was 358, with 113 for Kapkai 3, 46 for Kapkai 4, and 199 for Waramung. The total number of archaeal clones was 263, with 168 for Kapkai 3, 49 for Kapkai 4, and 46 for Waramung.

Phylogenetic analysis

Contiguous sequences were assembled using Sequencher v. 4.8 (Gene Codes Corporation, Ann Arbor, MI) and compared to the NCBI (National Center for Biotechnology Information) database using BLAST (Altschul et al. 1997) and the Ribosomal Database Project’s Classifier tool (Wang et al. 2007). All archaeal and bacterial sequences from each site were grouped based on 97 % similarity in Sequencher, and a representative from each group was used for phylogenetic analysis. Representative sequences were aligned using the Greengenes NAST server (DeSantis et al. 2006) and checked for chimeras using the Bellerophon v.3 server at Greengenes. For phylogenetic analysis, BLAST searches were used to find the closest relatives of the representative, non-chimeric sequences in the clone libraries from both archaea and bacteria at each site for use as reference sequences. The representative sequences and references sequences were manually aligned using the software BioEdit v. 7.5.0.3 (Hall 1999). Phylogenetic analysis of homologous positions in the alignment was performed using neighbor-joining (NJ) and maximum parsimony (MP) methods in the program PAUP v. 4b.10 (Sinhauer Associates, Sutherland, MA). MP analyses were performed with random addition of taxa (1000 replicates). All trees were evaluated using only unambiguously aligned nucleotides and bootstrapped (1000 replicates). Reference information concerning clonal taxonomic identity and abundance for these clone libraries can be found in Supplemental Table 1. The 16S rRNA sequences reported here have been deposited in the Genbank database (NCBI) under the accession numbers JF935152-JF935232.

Calculation of community diversity indices

Standard indices of diversity and evenness were calculated for all samples and reference datasets. These are Shannon-Weiner (H′), Chao1, and Pielou (J′) diversity indices, and Pielou evenness (E) (Shannon and Weaver 1949; Pielou 1969, 1977; Chao et al. 2005). The equations for (H′), (J′), and (E) are conveniently reviewed in Smith and Wilson 1996. The Chao1 index is calculated by;

$${\text{Chao1}} = S_{\text{obs}} + n_{ 1} \left( {n_{ 1} - 1} \right)/ 2(n_{ 2} + 1)$$

where S obs is the number of observed taxa, n 1 is the number of observed taxa with a single representative (a “singlet”) and n 2 is the number of observed taxa with two representatives (a “doublet”). The Chao1 index is often utilized as a means of assessing whether the full taxonomic diversity of a site has been realized with the sampling/analysis effort.

Results and discussion

Site description

Ambitle Island (4.08°S, 153.62°E) is at the southern end of the Tabar-Feni island arc in eastern Papua New Guinea (PNG). It is part of a Quaternary stratovolcano atop Oligocene marine limestone (Wallace et al. 1983). Active thermal features are found primarily along the west coast, both above and below sea level (Pichler and Dix 1996). Off-shore, shallow-sea (5–10 m) venting (previously described) occurs in Tutum Bay (Pichler and Veizer 1999). Of particular note are the high levels of arsenic, which reach ~1000 ppb in the venting fluids (as arsenite, AsIII) and up to 76000 ppb adsorbed by FeIII-oxyhydroxides (as arsenate, AsV) directly next to the venting orifices (Pichler et al. 1999a, b, 2006).

The array of on-land hot mud pools, springs, and fumaroles on Ambitle Island reaches temperatures up to 100 °C and varies in pH from 1.9 to 9.1 (Licence et al. 1987; Wallace et al. 1983). The source springs of the two locations investigated in the present study (Kapkai and Waramung, see Fig. 1) are hot (>90 °C), and alkaline (pH 8.5)—in contrast to many other island-based hydrothermal systems which are often acidic. Additional geochemical data for Kapkai and Waramung are given in Table 1. The geochemistry of the Ambitle Island locations, both on-shore and shallow-submarine, is compared with the geochemistry of other representative hot springs for reference in Supplementary Table 2. These reference locations are used in the discussion below to provide context, and include other island-based, alkaline, and/or high-arsenic sites. Where possible, reference locations were chosen which also reported corresponding biological data.

Fig. 1
figure 1

Photographs of Ambitle Island on-shore hot springs. a Kapkai and b Waramung. c Kapkai 3, thermometer for scale. d Kapkai 4, 15 ml centrifuge tube for scale

Table 1 Geochemical data from the source pools at the Kapkai and Waramung terrestrial hot springs

Kapkai and Waramung springs undergo moderate water–rock interaction, based on [SiO2] and the ratio of Ca+2:Mg+2, similar to many other island-based, and shallow-sea springs (Fig. 2a). The Ambitle Island on-shore and off-shore sites have similar [SiO2], [Ca+2] and [Mg+2], indicating a likely shared source fluid (Pichler et al. 1999a). However, the [SO −24 ] and [Cl] in the Kapkai and Waramung locations exceed nearly all other reference hydrothermal locations shown in Fig. 2b, including the Ambitle Island shallow-sea locations. As previous work has shown that the fluid in PNG springs is of meteoric and not marine origin (Pichler et al. 1999a), the elevated [SO −24 ] and [Cl] may indicate a larger degree of water–gas interaction and longer fluid residence time as compared to the reference locations. Alternatively, a 1:1 correspondence in Fig. 2b indicates that the on-shore locations at Ambitle are proportionally higher in [SO −24 ] and [Cl] than the shallow-sea vents, suggesting that while they share a common hydrothermal source, the on-shore locations are experiencing some degree of evaporation that has increased [SO −24 ] and [Cl] during phase separation.

Fig. 2
figure 2

Site fluid geochemistry (SiO2, SO −24 , Cl, Ca+2, Mg+2) shown with data from other hot spring and hydrothermal systems for reference. a [SiO2] and the molar ratio of Ca+2:Mg+2. b [SO −24 ] and [Cl]. Key for both a and b gray circles = Island and shallow-sea hydrothermal vents (Amend et al. 2003; Dotsika 2012; Kaasalainen and Stefánsson 2012; Kim Phuong et al. 2012; Joseph et al. 2013; Price et al. 2013a); open squares = Continental systems, typically chosen from alkaline or high As sites (Ozler 2000; Langner et al. 2001; Tarcan and Gemici 2003; McCleskey et al. 2004; Shock et al. 2010; Baba and Sözbilir 2012; Guo and Wang 2012; Loiacono et al. 2012; Meyer-Dombard et al. 2012b; Swingley et al. 2012; Pürschel et al. 2013); blue circles = Waramung Spring (Pichler et al. 1999a); purple circles = Kapkai Spring (Pichler et al. 1999a); black circles = PNG shallow-sea vents; red and orange circles = PNG 4A03-2.5 0 cm and PNG 4A03-2.5 10 cm, respectively (Meyer-Dombard et al. 2012a)

While redox sensitive species, such as sulfide and dissolved oxygen, are rarely reported for hydrothermal systems, these are important components of microbial metabolism. A comparison of dissolved oxygen and total sulfide concentrations in the PNG systems with other available published data can be seen in Fig. 3a. Sulfide concentrations at Kapkai and Waramung are higher than at other terrestrial locations and the Tutum Bay shallow-sea vent 4A, but lower than in several shallow-sea locations in Sicily (Fig. 3a). Comparison with sulfide concentrations in other published island-based on-land hydrothermal systems (e.g., on Iceland, Java, Greece, and St. Lucia, supplemental Table 2) is not possible as sulfide is not reported for these sites. The high sulfide in the Kapkai and Waramung ecosystems likely plays an important role in microbial metabolism and the cycling of iron and arsenic, potentially interfering with microbial transformations of arsenic (Langner et al. 2001). Further, Kapkai and Waramung springs also contain some of the highest total arsenic concentrations reported in hydrothermal systems (Fig. 3b), including comparisons with other island locations, as well as shallow-sea and continental locations. Higher total arsenic in the on-land Ambitle Island locations relative to the vent fluid compositions may be partially due to an evaporative effect during phase separation of the source fluid at depth (Pichler et al. 1999a).

Fig. 3
figure 3

Redox sensitive chemical species in Kapkai and Waramung Springs, shown with data from other hot spring and hydrothermal systems for reference. a Sulfide and dissolved oxygen concentrations. Key for a black circles = PNG locations (this work); gray circles = Sicily and shallow-sea vent systems (Amend et al. 2003; Price et al. 2013a); open squares = Continental hydrothermal systems (Langner et al. 2001; McCleskey et al. 2004; Shock et al. 2010; Loiacono et al. 2012; Meyer-Dombard et al. 2012b; Swingley et al. 2012). b Total arsenic concentrations. Key is the same as in Fig. 2

Microbial diversity

The bacterial and archaeal diversity at Kapkai 3, Kapkai 4, and Waramung was assessed by full length 16S rRNA gene sequences and phylogenetic analysis with representative sequences (Fig. 4; Supplemental Table 1).

Fig. 4
figure 4figure 4

Maximum parsimony phylogenetic analysis of the Bacteria from 16S rRNA gene sequences. Bootstrap values (only those <90 % are shown) represent 1000 replicates. Sequences from this study are in bold, with numbers in parentheses indicating the abundance within the representative sequence

Bacteria

The bacterial diversity at Kapkai and Waramung springs is shown in Fig. 4, with 59 representative sequences, spread across 13 major bacterial phyla (identified using a 97 % similarity cutoff). The bacterial diversity of on-land Ambitle Island springs as a group is widely spread among many bacterial taxa, including clones that affiliate with Aquificae, Thermotogae, Thermodesulfobacteria, Deinococcus–Thermus, Deferribacteres, Spirochaetes, Planctomycetes, Firmicutes, Actinobacteria, Proteobacteria (α, β, γ, δ), Bacteroidetes–Chlorobi, and Fibrobacteres–Acidobacteria. In addition, several sequences formed a clade with sequences from the candidate group UB-40. The richness and evenness of Bacteria in Kapkai 3, Kapkai 4, and Waramung springs are readily observed in Fig. 5, and Supplemental Table 3.

Fig. 5
figure 5

Taxonomic diversity of Bacteria in PNG Kapkai and Waramung locations, and several additional published datasets for reference. Data are presented as percentages of the total reported dataset (values can be found in Supplemental Table 3). Shown are published submarine locations from Ambitle Island (Meyer-Dombard et al. 2012b, 2013) and Milos, Greece (Price et al. 2013a), several other island-based systems (Niederberger et al. 2008; Stout et al. 2009; Kato et al. 2011), and continental, alkaline and/or high-arsenic systems (Jackson et al. 2001; Meyer-Dombard et al. 2011; Coman et al. 2013; Hou et al. 2013 and pers. com.)

The clone library from Kapkai 3 featured nine different phyla with >2 clones. The dominant group within the clone library was the Proteobacteria (40 %), followed by Deinococcus/Thermus and Bacteroidetes/Chlorobi (both at 15 %) and Planctomycetes (12 %). Other taxa each accounted for only a few percent in the clone library; of note is UB-40 (6 %), which is the only clade at this site without any cultured representatives. Among the Proteobacteria at Kapkai 3, the subdivision levels were represented in the clone libraries as follows: Alphaproteobacteria (27 %), Betaproteobacteria (40 %), Gammaproteobacteria (9 %), and Deltaproteobacteria (24 %). Very few of the bacterial clones at Kapkai 3 fall into the typically thermophilic and hyperthermophilic phyla. This is consistent with the moderate temperature of 45 °C at this site.

In contrast, the bacterial diversity at the higher temperature Kapkai 4 site is low, represented by only four phyla. Here, the Thermodesulfobacteria dominate the clone library (74 %), followed by Deinococcus/Thermus (13 %) and Thermotogales (11 %). Note that the three dominant phyla are all typically thermophilic or hyperthermophilic, consistent with the elevated temperature (72 °C) at this location.

The Waramung clone library features nine bacterial phyla with >2 clones, dominated by the thermophilic Aquificales (39 %) and Thermodesulfobacteria (20 %). Two other identified groups—Deinococcus/Thermus (13 %) and Thermotogales (9 %)—also feature high temperature organisms. The temperature of the Waramung source pool was near boiling (98.6 °C). This explains the ~60 % Aquificales and Thermotogales in this clone library, the two bacterial phyla featuring hyperthermophilic strains with maximum growth temperatures up to and exceeding 90 °C (Huber et al. 1986; Jannasch et al. 1988; Huber et al. 1992, 1998). The abundance of Aquificales, specifically those closely related to strains of Persephonella, may also be related to the groups’ ability to oxidize sulfide.

The Proteobacteria, represented in the Kapkai 3 (45/113 clones) and Waramung (20/199 clones) libraries, are gram-negative and metabolically diverse. The majority are mesophilic, but some are moderately to extremely thermophilic. The Alphaproteobacteria at Kapkai and Waramung are most closely related to uncultured clones. However, three clones from Kapkai 3 share >99 % sequence identity with Albidovulum inexpectatum, an aerobic moderate thermophile isolated from a marine hot spring in the Azores (Albuquerque et al. 2002). In addition, three clones from Waramung are >97 % similar to Nitratireductor, a genus of mesophilic nitrate reducers with very broad pH (5.5–12) and salinity (0–8 % NaCl) tolerances (Kang et al. 2009; Kim et al. 2009; Labbé et al. 2004). Note also the high nitrate concentrations (~0.2 mM, Table 1) at Waramung and Kapkai, which could support nitrate reduction as a viable metabolic strategy. The Kapkai and Waramung clones identified with Betaproteobacteria fall into three operational taxonomic units (OTUs), one of which affiliates closely with the genus Tepidimonas, a group of moderate thermophiles found in circumneutral to slightly alkaline hot springs (Chen et al. 2006; Moreira et al. 2000). In addition, Waramung clone B31 is closely related to a Tutum Bay clone (PNG_TBSL_B73) indicating a possible link to the shallow-sea communities. The Gammaproteobacteria at Kapkai and Waramung affiliated closely (>98 %) with Thermomonas or Thioalkalivibrio. A few known Thermomonas strains are moderately thermophilic, including T. hydrothermalis isolated from a hot spring in Portugal that grows optimally at ~50 °C at circumneutral to slightly alkaline pH (Alves et al. 2003; Busse et al. 2002). The Deltaproteobacteria in the Kapkai 3 and Waramung clone libraries affiliated most often with uncultured clones, but one Kapkai 3 OTU was most similar (92 %) to Desulfovibrio, a cosmopolitan group of sulfate reducers that includes thermophiles and alkaliphiles.

OTUs affiliating with Bacteroidetes/Chlorobi, Deinococcus/Thermus, Thermodesulfobacteria, and Thermotogae were observed in all three clone libraries. However, only the Deinococcus/Thermus group accounted for >10 % of each library. Isolates of this phylum are predominantly from terrestrial hydrothermal areas where the pH ranges from mildly acidic to moderately alkaline (da Costa et al. 2006). The Thermodesulfobacteria account for a large fraction of the Kapkai 4 and Waramung libraries, with uncultured clones the closest relatives. Many Thermodesulfobacteria have been identified in and isolated from terrestrial and marine hydrothermal systems worldwide; they are obligately thermophilic anaerobes, and most respire sulfate (Alain et al. 2009; Jeanthon et al. 2002; Zeikus et al. 1983). Note that at 66–74 mM (Table 1), the sulfate levels at Kapkai and Waramung are about 2.5× seawater levels, providing an available oxidant in anaerobic portions of the pools.

The Thermotogae and Aquificae represent the deepest-branching phyla in the Bacteria (Winker and Woese 1991), and both feature numerous extreme thermophiles isolated from terrestrial and marine hydrothermal systems (Wagner and Wiegel 2008). Thermotogae were present at all three sites, with the closest relative (>99 % identity) of seventeen OTUs being Thermotoga neapolitana, an anaerobic, chemoheterotrophic hyperthermophile isolated from hot springs near Naples, Italy (Jannasch et al. 1988). Aquificae were only noted at Waramung, but there they accounted for 78 of the 199 clones, 74 of which were closely related (>97 % identity) to the genus Persephonella. The known strains of Persephonella are chemolithoautotrophic, microaerophilic thermophiles from deep-sea hydrothermal vent systems (Götz et al. 2002; Nakagawa et al. 2003). Waramung clone B70 is closely related to a clone (PNG_TBSL_B73) reported at the shallow-sea vent system in Tutum Bay, suggesting that subsurface contact between the on-land and shallow-submarine sites may exist.

Archaea

The archaeal diversity is shown in supplemental Table 1 as nearest neighbors (determined by BLAST) with twenty-one representative sequences (>97 % similarity) from Kapkai and Waramung. These sequences affiliate with several major taxonomic groups, including the Thermoproteales and Desulfurococcales among the Crenarchaeota, the Thermococcales among the Euryarchaeota, and the recently described Thaumarchaeota (Brochier-Armanet et al. 2008). However, a number of the representative sequences affiliate with uncultured Crenarchaeota and uncultured Euryarchaeota. Several uncultured Crenarchaeotal and Euryarchaeotal clones from Kapkai 3 and Kapkai 4 are closely related to archaeal clones reported in shallow-sea hydrothermal systems, such as Vulcano, Italy (Rogers and Amend 2005) and Tutum Bay, PNG (Akerman 2009), again suggesting that the on-land sites at Ambitle Island may share a subsurface biological reservoir with hydrothermal fluids emanating from the shallow-sea systems in the bay.

At all three sites, the (hyper)thermophilic Thermococcales are the dominant taxa—65 % at Kapkai 3, 86 % at Kapkai 4, and 74 % at Waramung, as shown in Fig. 6. Two sequences at Kapkai 3 are identified as Thaumarchaeota, a proposed third archaeal phylum of predominantly mesophiles, including Cenarchaeum symbiosum (Brochier-Armanet et al. 2008). Uncultured Euryarchaeota (18 % at Kapkai 3) and uncultured Crenarchaeota (10 % at Kapkai 3, 14 % at Kapkai 4) were the only other taxa of note.

Fig. 6
figure 6

Taxonomic diversity of Archaea in PNG Kapkai and Waramung locations, and several additional published datasets for reference. Data are presented as percentages of the total reported dataset (values can be found in Supplemental Table 3). Shown are published submarine locations from Ambitle Island (Meyer-Dombard et al. 2012b, 2013) and Milos, Greece (Price et al. 2013a), several other island-based systems (Niederberger et al. 2008; Stout et al. 2009; Kato et al. 2011), and continental, alkaline and/or high-arsenic systems (Jackson et al. 2001; Meyer-Dombard et al. 2011; Coman et al. 2013; Hou et al. 2013 and pers. com.)

Of the 186 Thermococcales clones in this study, 174 affiliated very closely (>99 % sequence identity) with strains of Thermococcus. This genus features strictly anaerobic moderate and extreme thermophiles that grow on complex organic matter. The numerous species (~30 according to Wagner and Wiegel 2008), have been isolated predominantly from terrestrial, shallow-sea, and deep-sea hydrothermal systems, and grow over broad temperature (40–103 °C), salinity (~0–8 % NaCl), and pH (3.5–10.5) ranges. The Thermoproteales, found at Kapkai 3, are most closely related to uncultured clones of the genus Thermoproteus, which includes obligately anaerobic, sulfur-respiring hyperthermophiles first isolated from terrestrial hot springs in Russia and Iceland (Bonch-Osmolovskaya et al. 1990; Zillig and Reysenbach 2001; Zillig et al. 1981). The typically sulfur-respiring Desulfurococcales are found only in the Waramung clone library, with >80 % of the clones affiliating most closely with Ignisphaera aggregans, an anaerobic chemoheterotrophic hyperthermophile isolated from terrestrial thermal areas in New Zealand (Niederberger and Gotz 2006). Both Thermoproteales and Desulfurococcales are common community members in many terrestrial hot spring systems, including other alkaline systems (Meyer-Dombard et al. 2005; Spear et al. 2005; Childs et al. 2008; Niederberger and Gotz 2006), and are often represented by novel, uncultured organisms.

Community diversity and evenness

The richness and evenness of microbial communities at Kapkai and Waramung are shown in Figs. 5 and 6 and Supplemental Table 3, with comparison to other reference sites calculated using the Chao1, Shannon, and Pielou diversity indices (Pielou 1977; Smith and Wilson 1996). These reference sites, a collection of data available from PNG, and other shallow-sea, island-based, high-arsenic, and alkaline continental systems, were chosen because they represent some of the few available published accounts with both sufficient geochemical and microbial diversity datasets, as well as their relevance to the on-land Ambitle Island systems investigated here. Of the three on-land PNG samples, Kapkai 3 is the most rich (both with respect to bacterial and archaeal communities) of the sample locations, and has the most even bacterial community of all sites shown in Fig. 5. Despite being nearly 34 °C warmer than the Kapkai 3 site, Waramung has one of the most diverse bacterial communities in Fig. 5, only marginally lower than that of site “PNG 4A05-0 rust,” a rust-colored biofilm from a shallow-sea vent site in Tutum Bay at Ambitle Island (Meyer-Dombard et al. 2012b). In general, all other reference sites are of lower bacterial diversity than the on-land and shallow-sea PNG sites. The on-land Ambitle Island locations show lower archaeal diversity than many of the Tutum Bay shallow-sea locations, but have higher or comparable diversity than the shown island-based and continental reference datasets.

In addition, it can be seen in Figs. 5 and 6 that the microbial communities of the on-land Ambitle Island sites at Kapkai and Waramung bear very little similarity to any of the reference sites shown. While most high temperature and alkaline locations shown (see Supplemental Table 2) are dominated by Aquificales, of the three on-land Ambitle Island locations, only Waramung supports a population of Aquificales. The Kapkai 4 and Waramung communities also host some of the largest populations of Thermotogales and Thermodesulfobacteriales. The on-land Ambitle Island sites are the only locations considered herein to support large proportions of Thermococcales. Hence, the archaeal communities are more similar to each other than to any other reference location.

Our data yield evenness (E) values (in order of decreasing evenness) for bacterial communities of 0.79 for Kapkai 3, 0.56 for Kapkai 4, and 0.55 for Waramung. For comparison, bacterial E values were also computed for the reference hydrothermal systems (Supplemental Table 3). The E values for the Tutum Bay shallow-sea bacterial communities were also high (0.60–0.77), while the evenness of continental and island-based systems ranged widely, but were typically <0.5. By comparison, most archaeal E values, including those at Kapkai 3, Kapkai 4, and Waramung, were low (<0.5), with exceptions at Milos and Romania (both 0.77), and Yellowstone (0.97).

In general, diversity metrics may be employed to describe the stability of a given community. Thus, these data suggest that the Kapkai 3 and Waramung microbial communities enjoy greater functional redundancy, implied by high species richness relative to communities in reference locations. Further, the evenness of the Kapkai 3 bacterial community suggests a reduced need for competition within the community, perhaps pointing to resource abundance in this system. Indeed, the lower temperature of the Kapkai 3 sample allows for both chemo- and phototrophic metabolic functions. While measurements of dissolved organic carbon were not made, it can be assumed that the dense vegetation surrounding the on-land sites, and the shallow marine ecosystem in the bay, both provide an abundance of nutrients to support the hydrothermal ecosystems, lending to community stability and less necessity for resource competition.

Enrichment of thermophiles

Six different growth media—each at pH 6.5 and 8.5—were inoculated with sediment slurries from Kapkai 3, Kapkai 4, and Waramung and incubated at two temperatures (45 and 80 °C). The media were designed to target the following metabolisms: anaerobic heterotrophy, aerobic heterotrophy, heterotrophic sulfate reduction, aerobic arsenite oxidation, anaerobic chemolithoautotrophy, and aerobic chemolithoautotrophy. The base medium and trace element solution were designed from chemical analyses given in Table 1 and data tabulated in Pichler et al. (1999a) and Pichler (2005).

Results can be found in Supplemental Table 4. Definitive growth (defined here as the categories ‘*’ and ‘+’ in Supplementary Table 4) was observed in 20 of 72 enrichment experiments; an additional 21 tubes showed minimal growth (‘◦’ in Supplementary Table 4). No growth (‘–’ in Supplementary Table 4) was observed in the other 31 tubes even following 3–4 months of incubation. The most successful media were those that targeted aerobic heterotrophy (definitive growth in 6/12 tubes) and anaerobic heterotrophy (5/12). These media yielded mixed cultures that supported various Bacillus, Anoxybacillus, and Thermococcus sp. (Supplemental Table 4). While Bacillus-type taxa were not retrieved in the Kapkai or Waramung libraries, Anoxybacillus and Thermococcus taxa were identified in the clone libraries built from the sediments (Figs. 4, 5; and Supplemental Table 1). No growth or minimal growth was observed in the aerobic arsenite oxidation medium—at either temperature or pH—despite the high arsenite concentrations found in the Waramung and Kapkai fluids (Pichler et al. 1999a).

In comparing culturing success among the three different inocula (see Supplementary Table 4), Kapkai 3 and Kapkai 4 each yielded more positive enrichments than Waramung. Kapkai 4 showed definitive growth (*, +) in 9 tubes, minimal growth (◦) in another 12 tubes, and no growth (–) in only 3 tubes. At Kapkai 3, the results were 8 (*, +), 5 (◦), and 11 (–), and at Waramung, they were 3 (*, +), 4 (◦), and 17 (–).

Understanding the chemical composition and setting of Kapkai and Waramung springs helps to interpret these culturing successes and failures. Ambitle Island is a heavily vegetated tropical forest averaging ~200 mm of precipitation a year. Both springs are located within the dense foliage, and therefore there are ample opportunities for input of exogenous organic carbon to enter the spring ecosystems, in the form of plants, soil, insects, or even occasionally mammals and birds. It is thus perhaps not surprising that heterotrophic growth media were the most successful of the metabolic strategies attempted. This interpretation is also supported by the calculations of richness and evenness for the Kapkai 3 and Waramung sites as discussed above. Further, while the sites contain some of the highest concentrations of total arsenic measured in hydrothermal systems, they also have high sulfide concentrations that may inhibit arsenite oxidation in these ecosystems. It is thus far unknown if the microbial communities at Kapkai and Waramung springs have the genetic capacity for arsenite oxidation, arsenate reduction, or arsenic detoxification strategies, as have been previously demonstrated in other hydrothermal systems (Macur et al. 2004; Meyer-Dombard et al. 2013; Price et al. 2013a; Summers Engel et al. 2013; Takai et al. 2003). However, given the high concentrations of sulfide and sulfate, and the potential for both aerobic and anaerobic microniches (as typically found in terrestrial hydrothermal systems), the heterotrophic and sulfur-respiring taxa identified in the Kapkai and Waramung clone libraries are likely driving the primary productivity of these springs.

Concluding remarks

Our global census of terrestrial hot spring geobiology is heavily weighted by studies from a few bonanza sites, especially at Yellowstone National Park (USA). A few recent investigations have drawn attention to lesser-known, but geochemically and microbiologically intriguing locales. The microbial diversity study at Kapkai and Waramung on Ambitle Island, Papua New Guinea adds fundamentally to this global effort. Certainly, the microbial community of a previously unknown environment cannot be definitively, or fully, characterized by culturing successes and/or clonal sequences. However, much can be learned from such data if they are interpreted in the context of detailed geochemical analyses.

The bulk of the archaeal (227/263) and bacterial (197/358) clones in the Kapkai 3, Kapkai 4, and Waramung libraries share >97 % 16S rRNA gene sequence identity with previously identified clones or cultured isolates in well-characterized groups. Many of these groups—Thermotogae, Aquificae, Deinococcus/Thermus, Thermodesulfobacteria, Thermococcales, Thermoproteales, Desulfurococcales—feature exclusively or predominantly (hyper)thermophiles. Further, the cultured representatives closely related to Ambitle Island clones were often isolated from terrestrial hot springs, not unlike those at Kapkai and Waramung. While some of these isolates can respire oxygen, others rely on sulfate, sulfur, or nitrate as terminal electron acceptors; the observed high levels of sulfate, nitrate, and sulfide (as a metabolic waste product) are consistent with these findings. Note also the culturing successes in diverse growth media (aerobic and anaerobic, lithoautotrophic and heterotrophic, circumneutral and alkaline, moderately thermophilic and hyperthermophilic), which are consistent with both our phylogenetic interpretations and geochemical data.

Based on evidence from cultured closest neighbors, our own culturing efforts, and the available geochemistry, we can characterize the ecosystems at Kapkai and Waramung as supporting an array of thermophilic heterotrophs, including those that may use sulfate or nitrate as electron acceptors. Enrichments targeting arsenic-based metabolisms were not successful, however, the high sulfide may suppress these functions in Kapkai and Waramung. Further, the presence of potential archaeal ammonia oxidizers (the Thaumarchaeota) in these and other PNG springs indicates a potentially important nitrogen cycling role in these ecosystems. These observations are supported by on-site observations and geochemistry, including great potential for exogenous carbon and nitrogen input, high sulfate, nitrate, sulfide, and arsenic concentrations, relative to other island-based and shallow-sea hydrothermal systems. The abundance of marine-related and sulfate-utilizing nearest relatives to Kapkai and Waramung clones in both the bacterial and archaeal libraries, including several examples of nearest neighbors from Tutum Bay samples, further suggests that there may be a subterranean hydrologic link between the shallow-sea venting and the on-land springs of Ambitle Island.

The on-land Ambitle Island hydrothermal springs are unique geochemically and microbiologically when compared to other (scantily) available reference datasets. While similar geochemically to the Ambitle Island shallow-sea locations, Kapkai and Waramung springs host microbial communities which bear minimal resemblance to their shallow-sea counterparts. Exceptions include a few shared taxa that are commonly associated with marine hydrothermal ecosystems. The Kapkai and Waramung sites are also diverse relative to available reference data from other island-based, alkaline, or high [As] systems. These hot springs represent a valuable new resource, adding to a currently small global dataset of island-based, high [As] hydrothermal ecosystems.