Owing to the extreme salinity (∼10 times saltier than the oceans), near toxic magnesium levels (∼2.0 M Mg2+), the dominance of divalent cations, acidic pH (6.0) and high-absorbed radiation flux rates, the Dead Sea represents a unique and harsh ecosystem. Measures of microbial presence (microscopy, pigments and lipids) indicate that during rare bloom events after exceptionally rainy seasons, the microbial communities can reach high densities. However, most of the time, when the Dead Sea level is declining and halite is precipitating from the water column, it is difficult to reliably measure the presence of microorganisms and their activities. Although a number of halophilic Archaea have been previously isolated from the Dead Sea, polar lipid analyses of biomass collected during Dead Sea blooms suggested that these isolates were not the major components of the microbial community of these blooms. In this study, in an effort to characterize the perennial microbial community of the Dead Sea and compare it with bloom assemblages, we performed metagenomic analyses of concentrated biomass from hundreds of liters of brine and of microbial material from the last massive Dead Sea bloom. The difference between the two conditions was reflected in community composition and diversity, in which the bloom was different and less diverse from the residual brine population. The distributional patterns of microbial genes suggested Dead Sea community trends in mono- and divalent cation metabolisms as well as in transposable elements. This may indicate possible mechanisms and pathways enabling these microbes to survive in such a harsh environment.
The Dead Sea, located on the border between Israel, Jordan and the Palestinian Authority (area approximately 632 km2, maximum depth of 300 m), presents fascinating challenges to the understanding of biological processes and the limits of life in one of the most extreme environments on earth (Boetius and Joye, 2009). Its waters currently contain approximately 347 g l–1 of salts, and have a highly unusual ionic composition: divalent cations (1.98 M Mg2+, 0.47 M Ca2+) dominate over monovalent cations (1.54 M Na+, 0.21 M K+). The anions are 99% Cl– (6.48 M) and 1% Br– (0.08 M) (values for the year 2007 (Bodaker et al., 2009)). Sulfate concentrations are low (0.004 M), and the brine has a pH of approximately 6.0. The water budget of the Dead Sea is negative, and during the past decade it has dropped by an average of 1 m per year. The water is supersaturated with respect to Na+, and massive amounts of halite (NaCl) precipitate to the bottom.
Currently, the conditions of the Dead Sea are too extreme to support high growth of microorganisms. Although many halophilic and halotolerant microorganisms are known to inhabit NaCl-dominated (‘thalassohaline’) brines up to halite saturation, only a few organisms can live in the Dead Sea's ‘athalassohaline’ environment, dominated by divalent cations. Systematic monitoring since 1980 (Oren, 1999) has shown that microbial blooms consisting of the unicellular green alga Dunaliella and extremely halophilic Archaea of the Halobacteriaceae family develop only after significant dilution of the upper meters of the water column after exceptionally rainy winters. Two such events have been documented: in 1980, and even more dramatically in 1992, when the upper 5 m of the water column was diluted up to 70%, supporting a density of Archaea up to 3.5 × 107 ml–1, coloring the Dead Sea water red (Oren and Gurevich, 1995). A number of species of halophilic Archaea have been isolated from the Dead Sea, including Haloferax volcanii (Mullakhanbhai and Larsen, 1975), Haloarcula marismortui (Oren et al., 1990), Halorubrum sodomense (Oren, 1983) and Halobaculum gomorrense (Oren et al., 1995). However, polar lipid analyses of biomass collected during Dead Sea blooms suggested that these isolates were not the major components of the microbial community at the time (Oren and Gurevich, 1993). From 1996 onward, Dunaliella cells were no longer observed in the water, and the numbers of prokaryotes remained below 5 × 105 ml–1.
Materials and methods
Sample collection and fosmid library construction
Fosmid libraries were constructed from samples collected in the Dead Sea during a massive bloom in 1992 and in non-bloom conditions in 2007. The 1992 bloom sample was collected in 1992 at the Ein Gedi 310 station (31°25′N, 31°29′E), the deepest point at the center of the Dead Sea and had been cryopreserved since then. The 2007 sample was collected on March 8, 2007 at the Ein Gedi 100 station located 4 km east of Ein Gedi, at the location of the moored meteorological station (31° 25′ N, 35° 26′ E), in which the depth of the Dead Sea is approximately 100 m. Approximately, 800 l of Dead Sea surface water were mixed with 1/10 volumes of prefiltered double-distilled freshwater (790 l of brine with 10 l freshwater) and concentrated by tangential flow filtration with a Pellicon 2 unit (Millipore, Billerica, MA, USA) equipped with a C screen 0.22 μm Durapore 0.5 m2 cartridge. Freshwater addition was a prerequisite to avoid salts crystallizing inside the 0.22 μm cartridge. Cells were collected by centrifugation of the retentate (4 °C, 38 900 × g, 0.5 h) and the pellet was embedded in agarose plugs (Béjà et al., 2000). The 1992 bloom sample was collected from surface waters and cells from ∼5 l were concentrated by centrifugation and the reddish cell pellet was stored in −80 °C. For plug preparation, the 1992 bloom pellet was thawed on ice in July 2008 and the cells were embedded in agarose plugs. DNA was extracted from the agarose plugs using lysozyme and proteinase K treatments ((Béjà et al., 2000); detailed description could be found in (Sabehi and Béjà, 2007)) from both samples. Before cloning, DNA from both the 2007 and the crypreserved 1992 plugs were run in agarose gels and were shown to be intact (data not shown). The DNA was cloned into the pCC1fos vector (Epicentre, Madison, WI, USA) according to manufacturer's instructions to construct two fosmid libraries. Ten 96-well plates were taken for random end sequencing from both fosmid ends for each library.
Out of the 1920 BAC-end sequences performed on each library, 1773 (1992 library) and 1759 (2007 library) were used for further analyses after quality control (low-quality sequence ends were removed from all sequences from the 1992 bloom and 2007 data sets using Phred (Ewing and Green, 1998; Ewing et al., 1998).) and the removal of duplicates. On average, the read length was 734 or 844 bp for the 1992 or 2007 libraries, respectively. In addition, all sequences were scanned for possible vector contamination by BLASTing, the clone ends against the sequence libraries and removing all 100% hits. Multiple copies of clones coming from the same cultures were detected and removed.
Archaeal 16S rRNA amplification and construction of 16S rRNA tree
PCR 16S ribosomal RNA (rRNA) gene amplification was carried out using the 16S rRNA archaeon-specific primers Ar20F (5′-TTCCGGTTGATCCYGCCRG-3′) and Ar958R (5′-YCCGGCGTTGAMTCCAATT-3′) (Hallam et al., 2003). The 20-μl amplification reaction mixtures contained 1 μl of template DNA, 2 μl of 10 × optibuffer, 0.4 μl each of 10 μM forward and reverse primer, 0.3 μl of BIO-X-ACT short DNA polymerase (Bioline, Berlin, Germany), 1 μl of 50 mM co-factor (MgCl2) and 2 μl of 10 mM stock deoxynucleoside triphosphate mixture. Amplifications were carried out with the following profile: 94 °C for 2 min, then 29 cycles of 94 °C for 30 s, 54 °C for 30 s and 68 °C for 40 s, followed by a final extension at 68 °C for 10 min. Forty partial (ca. 920 bp) 16S rRNA sequences from the Dead Sea were verified for chimeras using BELLEROPHON (Huber et al., 2004) and a single putatively chimeric sequence was excluded from further analyses. The reminder sequences, a sequence from a saltern in Croatia (DQ889331) and the sequences of Halomicrobium katesii AI-5 (EF333994) and Halobaculum gomorrense DSM9297 (sequenced in this study) were imported into the SSUref_96 tree from the Silva project (Pruesse et al., 2007) using ARB (Ludwig et al., 2004). Sequences were automatically aligned, and the alignments manually verified against a set of sequences composed of: (1) All sequences of strains of officially named species (Deutsche Sammlung von Mikroorganismen und Zellkulturen, www.dmsz.org) in the Halobacteriaceae family (International Committee on Systematics of Prokaryotes, www.the-icsp.org); (2) Previously published sequences longer than 1300 bp from uncultured microorganisms labeled as ‘Halobacteriales’ in the silva project tree tree_SSURef _1200_svl_96; and (3) Methanospirillum hungatei JF1 as the outgroup. A total of 280 sequences were used to construct a neighbor-joining phylogenetic tree using the F84 substitution model (Kishino and Hasegawa, 1989; Felsenstein and Churchill, 1996). This analysis used alignment positions that were selected based on a filter (mask) that included all positions common to more than 50% of the sequences, and excluded any position with ambiguities in any of the sequences. A total of 714 sequence positions were used to construct a tree and to calculate bootstrap values based on 100 random resamplings using PHYLIP (Felsenstein, 2005).
Metabolic potential was determined with the IMG/M (Integrated Microbial Genome with Microbiome Sample) (Markowitz et al., 2008a) of the Joint Genome Institute server (http://img.jgi.doe.gov/m). Frequency estimations of the different protein families were computed based on the statistical framework from (Sharon et al., 2009). Briefly, the frequency Fp of a protein family P in a sample D is given by
where is an estimator for the number of occurrences of P in the sample, Ĉp. Given that P is observed on Rp reads, is given by
where L(P) is P's length, g is the average read length, T is the minimum segment of P required for the gene to be discovered, and α is the sample coverage. It is to be noted that α is eliminated when FP is computed.
Cluster of Orthologous Group (COG) assignment was performed using the IMG/M system (Markowitz et al., 2008b). The COG assignment of the nine environments was tabulated and is presented in Supplementary Table S1. We used the Expander 4.0.2 for clustering (Shamir et al., 2005). From all COGs, we chose the 1000 most variable, performed a standardization (mean 0, variance 1 transformation) and hierarchical clustering with complete linkage (Figure 6).
Measurement of library-to-library similarities was made after BLASTx querying of all environments against each other and themselves using the following parameters (-p tblastx -e 1e-2 -F F). This very low expectation cutoff value was chosen because the different environments compared (three hypersaline environments and nine different marine samples) were very different from each other. The data set was computed according to (Rusch et al., 2007) with a cutoff value of 80% and only for fragments of more than 200 bp.
The (Figure 3) two Dead Sea (1992 bloom and 2007) as well as the Spanish Salterns (Legault et al., 2006) data sets were blasted (-p blastn –r 2 –q -3 –F F –e 1e-2) against the genomes of Haloarcula marismortui ATCC 43049, Halobacterium salinarum R1, Halobacterium sp. NRC-1, Haloferax volcanii DS2, Haloquadratum walsbyi DSM 16790, Natronomonas pharaonis DSM 2160 and Salinibacter ruber DSM 13855. For each read with at least one hit of which alignment was longer than 400 bp with percent identity higher than 60% the best hit was plotted on Figure 3.
Nucleotide sequence accession numbers
Fosmid end sequences were deposited in GenBank under accession #s GQ444463-GQ446233 (1992) and GQ446234-GQ447987 (2007), and 16S rRNA gene sequences GQ861381-GQ861393 (1992) and GQ861355-GQ861378 & GQ861380 (2007).
Results and discussion
We embarked on a detailed metagenomic study of two different Dead Sea environments using the random bidirectional DNA sequencing of fosmid clones approach that was recently developed and used by DeLong et al. to characterize microbial communities in the ALOHA station (DeLong et al., 2006). We analyzed uncultivated microbial population structures and predicted metabolic activities in samples from the year 2007 and from the 1992 microbial bloom material that had been cryopreserved for nearly 16 years. The DNA of the cryopreserved sample appeared to be intact, however, the influence of such a long cryopreservation on the integrity of the bloom population verified could not be ruled out. The cell morphology of the 2007 population was pleomorphic, not different from the morphology observed with the 1992 bloom (see Figure 2 in Oren and Gurevich, 1993). Total Dead Sea community DNA from 2007 was purified from ∼800 lof concentrated brine. Technically, Dead Sea brine microbes could not be concentrated because of massive salt precipitation inside the tangential flow device. Sample concentration was therefore achieved only after previous dilution with 1/10 volume of prefiltered freshwater, which lowered salt concentrations to below the precipitation point. The DNA was cloned into fosmids and both ends of clones were sequenced.
A PCR-based survey with archaeal-specific 16S rRNA primers was performed directly on Dead Sea samples as well as on fosmid clones. Not surprisingly, the analysis revealed a diverse community of halophiles; however, most rRNAs had <93% similarity to any rRNA sequence currently in the GenBank (either from cultured organisms or from environmental clones, Figure 1). Of the different rRNA phylotypes recovered from the fosmids, three were somewhat similar to Haloplanus natans (96% in the 2007 sample), Halorhabdus utahensis (93% in the 2007 sample) and Halobacterium noricense (95% in the 1992 bloom), while the rest were <89–92% identical to any known halophilic isolate or environmental 16S rRNA sequence. A similar trend was observed with rRNAs found at the fosmid ends (both 16S and 23S rRNA, some with <88% similarity to known halophiles). These results indicate that the community that adapted to survive in the brine is unique to the Dead Sea environment, and is likely adapted to survive under the harsh conditions of the Dead Sea. Interestingly, although rRNAs retrieved from the 2007 sample were affiliated with different haloarchaeal groups, the rRNAs from the bloom were found only as one cluster somewhat related to Halobacterium salinarum, but also without other closer published sequences. Morphologically, the Archaea in the bloom were of a flat, pleomorphic type, and not long rods as all Halobacterium species. Moreover, analysis of the polar lipid composition of the bloom community did not show the characteristic glycolipids of the genus Halobacterium (Oren and Gurevich, 1993). The dominant type of archaeon thus belonged to a new genus with 93% 16S rRNA gene similarity to Halobacterium salinarum.
Analysis of bacterial 16S rRNA obtained from the environment showed sequences belonging to Firmicutes (93–99% similarity) and Fusobacteria (89% similarity). However, we failed to detect the presence of bacterial rRNA in our fosmid library, which might indicate the absence or very low quantity of Bacteria in the Dead Sea samples.
We used a pyro-tag sequencing strategy that combines the use of amplicons of the V6 hypervariable region of the 16S rRNA as proxies for the presence of individual phylotypes (operational taxonomic units) with massively parallel sequencing (Sogin et al., 2006). Our goal was to provide assessments of archaeal diversity, evenness and community structure at a resolution two to three orders of magnitude greater than what we achieved by cloning and capillary sequencing of longer 16S rRNA amplicons. Indeed, as hinted by the long 16S rRNA amplicons analysis, the 1992 bloom was composed of several dominant Halobacteriaceae phylotypes that are not present in the 2007 community (Figure 2) as well as contained a larger number of moderate-to-high abundance taxa, and significantly higher ACE and Chao1 values (Table 1 ).
Recruitment of randomly sequenced fosmid ends against the non redundant GenBank database (BLASTn (Altschul et al., 1997)) showed that the majority of ends from the Dead Sea 1992 bloom, as well as from the 2007 residual community, had best hits at approximately 75–80% identity (Figure 3). This is in sharp contrast to the 95–100% identity observed earlier with fosmid ends retrieved under bloom conditions in a Spanish saltern crystallizer pond in which the population was dominated by square Archaea based on similar criteria (Legault et al., 2006). This suggests that many of the Archaea present in the Dead Sea have no cultured counterparts in collections.
Taxonomic bins of protein homologs found at the fosmid ends (BLASTx high-scoring sequence pair against the non-redundant GenBank database using the Joint Genome Institute blast tool confirmed the rRNA-based observations of archaeal dominance (∼95% of assigned genes). Archaea distribution suggested that the residual community of the Dead Sea in 2007 was composed of different haloarchaeal groups with no dominance of a specific group (Figure 4). Under bloom conditions, however, Halobacterium-like high-scoring sequence pairs reached 50% from archaeal assigned hits. This is also in contrast to the observations made under bloom conditions in the Spanish saltern crystallizer pond (Legault et al., 2006) in which the population was dominated by environmental ‘Haloquadratum walsbyi’. Small numbers of bacterial high-scoring sequence pairs were also observed in the Dead Sea metagenome, adding up to 5–7% of the protein homologs. These could be the result of a small yet significant bacterial presence in the Dead Sea residual community or could alternatively be coming from bacterial-like sequences embedded in archaeal genomes (Nelson et al., 1999; Worning et al., 2000).
To find Dead Sea communities’ enriched traits, fosmid end sequences were compared against the COG database (Tatusov et al., 1997; Tatusov et al., 2003) in comparison with fosmid or Bacteria Artificial Chromosome (BAC) libraries from the Spanish saltern data set (Legault et al., 2006) and from different marine environments (DeLong et al., 2006; Martín-Cuadrado et al., 2007; Feingersch et al., 2009). Interestingly, although the Spanish sample was composed of a different archaeal repertoire and had, on average, a much different percent G+C content (GC%) content (Figure 5), it clustered with the Dead Sea samples based on COG categories and was somewhat more similar to the 2007 sample (Figure 6 and Supplementary Table S1). This indicates that the metabolic capacity required to survive under high salt conditions is shared between different high salt environments. Enrichment in COGs related to transposable elements (Supplementary Figure S1), intein and homing endonucleases, Na+/H+ and K+/H+ antiporters, as well as divalent cation (Mg2+ and Co2+) channels (Figure 7a) was observed in the Dead Sea environments. Enrichment in transposases was also observed earlier in the Spanish saltern environment (Legault et al., 2006) and is consistent with the high number of transposable elements observed in halophile genomes (Charlebois and Doolittle, 1989; Grogan, 2007).
The enrichment in putative archaeal (see phylogenetic tree in Figure 7b) CorA magnesium channels (up to 11-fold for COG 0598; see Figure 7a) in the highly magnesium-enriched Dead Sea environment points to a potential, yet unknown, resistance mechanism used by Dead Sea halophiles. Although CorA (COG 0598) is usually associated with Mg2+ influx activity, when exposed to high extracellular Mg2+ concentrations, CorA can mediate Mg2+ efflux (Gibson et al., 1991; Papp-Wallace and Maguire, 2008). Interestingly, the Mg2+/Co2+/Ni2+ channel MgtE (COG 2239; Figure 7a) was completely absent from the Dead Sea libraries.
Mg2+ is a chaotropic ion, and as such is toxic at high concentrations. In the absence of compensating (kosmotropic) ions such as Na+, a Mg2+ concentration of 2.3 M appears to be the upper limit for life (Hallsworth et al., 2007). In the Dead Sea, the Mg2+ concentration rapidly approaches this upper value when the Na+ content of the water decreases. Little is known regarding the intracellular Mg2+ and Ca2+ concentrations of halophilic Archaea in the Dead Sea. Experiments to estimate such concentrations in the Dead Sea isolate Hrr. sodomense grown in up to 0.95 M Mg2+ and 0.5 M Ca2+ yielded values that were <40% of the concentrations in their surrounding medium, and those values were probably overestimations because of methodological problems (Oren, 1986). In any case, it is clear that efficient removal of divalent cations is an essential function for microorganisms in the Dead Sea, and therefore the enrichment in putative CorA magnesium channels in the active community of 1992 may well point to a special adaptation of life in the high-magnesium waters of the Dead Sea.
Drying out of the Dead Sea with a further increase in divalent cation concentrations is expected to continue in the years to come. It will be interesting to repeat these metagenomics studies in the future (providing that microbial communities will still be found in the Dead Sea) to monitor further adaptations of life to the increasingly extreme conditions of the unique environment of the Dead Sea.
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We thank the late M Gonen and the crew of the RV Taglit for their logistic support and technical assistance at sea, and N Kyrpides and VM Markowitz for their assistance and support with the IMG/M system. This work was supported by grants from the Bridging the Rift (BTR) Foundation (IB, SB, AO and OB) and the NASA Astrobiology Institute Cooperative Agreement, NASA NNA04CC04A (MLS).
This paper is dedicated to the memory of Moti Gonen, the skipper of the RV Taglit.
Supplementary Information accompanies the paper on The ISME Journal website (http://www.nature.com/ismej)
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Bodaker, I., Sharon, I., Suzuki, M. et al. Comparative community genomics in the Dead Sea: an increasingly extreme environment. ISME J 4, 399–407 (2010). https://doi.org/10.1038/ismej.2009.141
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