Abstract
Until recently, ammonia oxidation, a key process in the global nitrogen cycle, was thought to be mediated exclusively by a few bacterial groups. It has been shown now, that also Crenarchaeota are capable to perform this initial nitrification step. The abundance of ammonia oxidizing Bacteria and Archaea was determined using the bacterial and archaeal ammonia monooxygenase-α subunit (amoA) gene as functional markers in a quantitative PCR approach and related to the abundance of Bacteria and Archaea in the Eastern Mediterranean Sea. Archaeal amoA copy numbers decreased from 4000–5000 copies ml−1 seawater from the 200–500 m depth layer to 20 copies ml−1 at 1000 m depth. β-Proteobacterial amoA genes were below the detection limit in all the samples. The archaeal amoA copy numbers were correlated with NO2− concentrations, suggesting that ammonia-oxidizing Archaea may play a significant role in the nitrification in the mesopelagic waters of the Eastern Mediterranean Sea. In the bathypelagic waters, however, archaeal amoA gene abundance was rather low although Crenarchaeota were abundant, indicating that Crenarchaeota might largely lack the amoA gene in these deep waters. Terminal restriction fragment length polymorphism analysis of the archaeal community revealed a distinct clustering with the mesopelagic community distinctly different from the archaeal communities of both, the surface waters and the 3000–4000 m layers. Hence, the archaeal community in the Eastern Mediterranean Sea appears to be highly stratified despite the absence of major temperature and density gradients between the meso- and bathypelagic waters of the Mediterranean Sea.
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Introduction
In the oceanic water column, the archaeal contribution to prokaryotic abundance varies among different regions, water masses and depths (Karner et al., 2001; Herndl et al., 2005). Crenarchaeota appear to be more variable in abundance than Euryarchaeota as revealed by catalyzed reporter deposition fluorescence in situ hybridization (CARD-FISH) (Teira et al., 2006a; Varela et al., 2008). Using genomic approaches, light has been shed onto the potential role of archaeal communities in the oceanic carbon and nitrogen cycle (Hallam et al., 2006; Lam et al., 2007). It has been firmly established now that at least some Crenarchaeota are chemoauotrophs fixing CO2 (Herndl et al., 2005; Kirchman et al., 2007) and using ammonia as an electron donor and energy source (Francis et al., 2005; Könneke et al., 2005). Crenarchaeota might be more important than Bacteria in oxidizing ammonia as a higher abundance of the archaeal gene encoding for a subunit of the enzyme ammonia monooxygenase A, amoA, was detectable than bacterial amoA gene abundance in the North Sea and the mesopelagic waters of the North Atlantic (Wuchter et al., 2006).
There are only a few studies on the prokaryotic community composition of the water column of the Eastern Mediterranean Sea (Moeseneder et al., 2001a, 2001b, 2005). One of the most peculiar features of the Eastern Mediterranean Sea is its highly oligotrophic nature, its extremely low concentration of inorganic phosphorus (Thingstad et al., 2005) and the warm deep waters (about 14 °C). The latter is a general characteristic of the bathypelagic realm of the Mediterranean. The composition of the water masses in the individual basins of the Eastern Mediterranean Sea differs remarkably (Zervakis et al., 2004). In the northern Aegean Sea, outflow of Black Sea water introduces inorganic nutrients with decreasing influence towards the south. Several deep-water basins of the Eastern Mediterranean Sea harbor fairly isolated deep-water bodies (Zervakis et al., 2004). The differences in the physical and chemical characteristics of the water bodies from north to south in the Eastern Mediterranean Sea are also reflected by considerable changes in the bacterial community composition as revealed by terminal restriction fragment length polymorphism (T-RFLP) fingerprinting (Moeseneder et al., 2001a).
The aim of this study was to determine the spatial abundance of Crenarchaeota, Euryarchaeota and Bacteria and the distribution of archaeal and bacterial amoA genes throughout the water column of the Eastern Mediterranean Sea along the north to south gradient, using CARD-FISH and quantitative-PCR (Q-PCR), respectively. T-RFLP was also used to compare the archaeal community composition among the stations and depth horizons. Our results suggest that ammonia-oxidizing Archaea may play a significant role in the nitrification in the mesopelagic realm of the Eastern Mediterranean Sea, while in the bathypelagic waters, Archaea are apparently lacking the amoA gene.
Materials and methods
Study site and sampling
The cruise in the Eastern Mediterranean Sea was conducted with the RV AEGAEO (Hellenic Center for Marine Research, Greece) occupying five stations in May 2007 (Figure 1). The stations were located in the North Aegean (St. 1; 48° 7.0′N, 24° 32.5′E), Mid Aegean (St. 2; 37° 42.1′N, 25° 26.0′E), Western Cretan Sea (St. 3; 36° 13.2′N, 23° 18.3′E), Ionian Sea (St. 4; 36° 15.9′N, 21° 30.1′E) and South Aegean (St. 5; 35° 47.2′N, 24° 54.7′E). Water samples were obtained from the mixed surface waters (10 m depth) and the meso- and bathypelagic layers (down to a maximum depth of 4350 m) with 5L-Niskin bottles mounted on a conductivity-temperature-depth rosette sampler. Dissolved oxygen concentrations were determined with a SBE oxygen sensor mounted on the conductivity-temperature-depth and nutrient concentrations (that is, phosphate, nitrate and nitrite) with a nutrient auto-analyzer (Bran & Luebbe Autoanalyzer II, Norderstedt, Germany).
For later molecular analyses of the prokaryotic community, 10 l of seawater was filtered through a 0.22 μm Sterivex filter cartridge (Millipore, Millford, MA, USA) to collect prokaryotes for molecular analyses. Thereafter, 1.8 ml of lysis buffer (40 mM EDTA, 50 mM Tris-HCL, 0.75 M sucrose) was added to the filter cartridge and the filter cartridges were stored at −80 °C.
Composition of specific phylogenetic groups
The composition of Bacteria, Crenarchaeota and Euryarchaeota was determined by CARD-FISH (Teira et al., 2004). Water samples of 10–80 ml were collected from the Niskin bottles and preserved in paraformaldehyde (2% final concentration) at 4 °C in the dark for 18 h. Thereafter, the samples were filtered onto 0.2 μm polycarbonate filters (Millipore, GTTP) supported by 0.45 μm cellulose nitrate filters (Millipore, HAWP), rinsed with Milli-Q water, dried and stored in microfuge vials at −20 °C until further processing in the laboratory.
Filters for CARD-FISH were embedded in low-gelling-point agarose and incubated either with lysozyme for the Bacteria probe mix (Eub338, Eub338II and Eub338III) or with proteinase-K for marine Euryarchaeota Group II probe Eury806 and for the marine Crenarchaeota Group I probes Cren537 (Teira et al., 2006a) and GI-554 (Massana et al., 1997) following the method described by Teira et al. (2004). Filters were cut in sections and hybridized with horseradish peroxidase-labeled oligonucleotide probes and subsequently incubated with tyramide-Alexa488 for signal amplification. Thereafter, the filter sections were stained with a DAPI (4,6-diamidino-2-phenylindole) mix (5.5 parts of Citifluor (Citifluor, London, UK), 1 part of Vectashield (Vector Laboratories, Burlingame, CA, USA) and 0.5 parts of phosphate-buffered saline with DAPI (final concentration 5 μg ml−1)).
Hybridized and DAPI-stained cells were detected under a Zeiss Axioplan 2 epifluorescence microscope equipped with a 100 W Hg-lamp and appropriate filter sets for Alexa488 and DAPI. More than 600 DAPI-stained cells were counted per sample. For each microscope field, two categories were determined: total DAPI-stained cells and cells stained with the specific probe.
DNA extraction
The cartridges of the Sterivex filters were cracked open and the filters and the lysis buffer transferred into 50 ml sterile centrifuge tubes. DNA extraction was performed using the Mega Kit extraction (MoBIO laboratories, Carlsbad, CA, USA) and the protocol of the manufacturer. DNA extracts were concentrated (approximately 10 times) with a Centricon device (Millipore).
Q-PCR analysis
We conducted Q-PCR targeting 16S rRNA gene fragments of Marine Crenarchaeota Group I (MCGI) and the pSL12 cluster and archaeal amoA genes for the samples collected at Sts. 1, 2 and 4 (St. 1: 100, 200 and 950 m; St. 2: 300, 400 and 750 m; St. 4: 1000, 3000 and 4350 m). β-Proteobacterial amoA genes were targeted using amoA-1F (5′-GGGGTTTCTACTGGTGGT)/amoAr-new (5′-CCCCTCBGSAAAVCCTTCTTC) (Hornek et al., 2006). A mix of 25% of Nitrosomonas europaea, 25% of N. eutropha, 25% of N. marina and 25% of Nitrosospira briensis was used as a standard. β-Proteobacterial amoA genes, however, were not detected at any of the stations, although the same primer set readily detected β-Proteobacterial amoA in the coastal North Sea and the open North Atlantic (Wuchter et al., 2006). All Q-PCR experiments were performed on an iCycler iQ 5 thermocycler (Bio-Rad, Philadelphia, PA, USA) equipped with iCycler iQ software (version 3.1, Bio-Rad). The amoA copy numbers in the standards and environmental samples were determined in triplicate with three different dilutions. The reaction mixture (20 μl) contained 1 unit of Pico Maxx polymerase, 2 ml of 10 × Pico Maxx PCR buffer (Stratagene, La Jolla, CA, USA), 0.25 mM of each dNTP, 8 μg of bovine serum albumin, 0.2 mM of primers, 50 000 times diluted SYBR Green I (Molecular Probes), a final concentration of 10 nM fluorescein, 3 mM MgCl2 and ultra-pure sterile water (Wuchter et al., 2006). The efficiency of the quantification reaction ranged between 74.5 and 111.5% with an r2 ranging from 0.983 to 1.000. Marine Crenarchaeota Group I (MCGI) 16S rRNA gene fragments were detected using the primer set MCGI-391f (5′-AAGGTTARTCCGAGTGRTTTC) and MCGI-554r (5′-TGACCACTTGAGGTGCTG) with plasmid 88exp4 as a standard and primer annealing at 61 °C for 40 s (Wuchter et al., 2006). The pSL12 16S rRNA gene fragments were detected using the primer set pSL 12-750F (5′-GGTCCRCCAGAACGCGC) and pSL12-876R (5′-GTACTCCCCAGGCGGCAA) with fosmid HF770_041/11 as a standard and primer annealing at 65 °C for 40 s (Mincer et al., 2007). Archaeal amoA genes were detected using the specific archaeal amoA primer set arch-amoA-for (5′-CTGAYTGGGCYTGGACATC) and arch-amoA-rev (5′-TTCTTCTTTGTTGCCCAGTA) with Nitrosopumilus maritimus as a standard and primer annealing at 58.5 °C for 40 s (Wuchter et al., 2006). The PCR efficiencies and correlation coefficients for the standard curves were as follows: for the MCGI 16S rDNA assay, 87.9–105.8% and r2=0.991–0.999, for the pSL12-like 16S rDNA assay, 94.7–110.5% and r2=0.949–0.999, for the archaeal amoA assay, 86.5–97% and r2=0.983–0.999 and for the β-proteobacterial amoA assay, 77.8–88.3% and r2=0.989–0.999.
PCR and T-RFLP
PCR conditions and chemicals were applied as described by Moeseneder et al. (2001a). One μl of the DNA extract was used as a template in a 50 μl PCR mixture. For PCR, the universal primer 1492R-JOE (Lane, 1991) and the Archaea-specific primers 21F-FAM and 958R-JOE were used (Moeseneder et al., 2001a). Samples were amplified by an initial denaturation step at 94 °C (for 3 min), followed by 35 cycles of denaturation at 94 °C (1 min), annealing at 55 °C (1 min), and an extension at 72 °C (1 min). Cycling was completed by a final extension at 72 °C for 7 min. The PCR products were run on 1.0% agarose gel. The gel was stained with a working solution of SYBR Gold and the obtained bands were excised, purified with the Quick gel extraction kit (Genscript, Piscataway, NJ, USA), and quantified using a Nanodrop spectrophotometer. Fluorescently labeled PCR products were digested at 37 °C overnight. Each reaction contained 30 ng of cleaned PCR product, 5 U of tetrameric restriction enzyme (HhaI) and the respective buffer filled up to a final volume of 50 ml with ultra-pure water (Sigma, St Louis, MO, USA). The restriction enzyme was heat inactivated and precipitated by adding 4.5 μl LPA solution and 100 μl of 100% isopropanol. The samples were kept at room temperature for 15 min followed by centrifugation at 15 000 g for 15 min. Thereafter, the supernatant was discarded and the pellet rinsed with 100 μl 70% isopropanol and precipitated again by centrifugation (15 000 g for 5 min). Subsequently, the supernatant was removed again and the sample dried in the cycler at 94 °C for 1 min and stored at −20 °C until further analysis.
The pellet was resuspended in 2 ml of ultra-pure water and the product denatured in 7.8 ml of Hi-Di formamide at 94 °C for 3 min. Each sample contained 0.2 ml GeneTace 1000 (ROX) marker (Applied Biosystems, Foster City, CA, USA). Fluorescently labeled fragments were separated and detected with an ABI Prism 310 capillary sequencer (Applied Biosystem) run under GeneScan mode (van der Maarel et al., 1998; Moeseneder et al., 1999). The size of the fluorescently labeled fragment was determined by comparison with the internal GeneTace 1000 (ROX) size standard. Injection was performed electrokinetically at 15 kV for 15 s (adjustable) at 60 °C.
The output from the ABI Genescan software was transferred to the Fingerprinting II (Bio-Rad) to determine the peak area and for standardization using size markers. The obtained matrix was further analyzed with Primer software (Primer-E) to determine similarities of the T-RFLP fingerprints between samples.
Results
There was little variability in temperature and salinity among the five stations (Table 1). Phosphate and nitrate concentrations exhibited the common depth-related trend with low concentrations in the top 100 m layer and increasing with depth (Table 1). Oxygen concentrations remained rather constant with depth exhibiting no pronounced oxygen minimum layer.
Prokaryotic community composition determined by CARD-FISH
The mean contribution of Bacteria to total prokaryotic abundance (that is, DAPI-stained cell) was 45±10% (n=29) averaged over all the stations and depth layers (Figure 2). Overall, the variability in the relative abundance of Crenarchaeota and Euryarchaeota was higher than that for Bacteria. Both, the Cren537 and the GI-554 probe, target the same crenarchaeal phylotypes with an additional 5 and 14% of phylotypes covered by the probe Cren537 and GI-554, respectively (Figure 3). The relative contribution of Cren537- and GI-554-positive cells to total prokaryotic abundance was 7±9% (average±s.d., n=29), and 12±9% (n=29), respectively (Figure 2). The ratio of GI-554- to Cren537-positive cells ranged from 0.12 to 39.70. At St. 2, the relative abundance of Cren537-positive cells was higher than of GI-554-positive cells throughout the water column, whereas GI-554-positive cells dominated at St. 5 (Figure 2). At St. 5, the maximum percentage of GI-554-positive cells was 35% at 250 m decreasing with depth. Eury806-positive cells represented only a minor fraction of total prokaryotic abundance (1±3%, n=29) at all the stations and were detected only in the top 400 m of the water column (Figure 2).
Abundance of specific phylogenetic groups determined by CARD-FISH and Q-PCR
In 14 out of 29 samples, the difference in abundance between Cren537- and GI-554-positive cells was larger than a factor of 2 (Figure 4). These differences in abundance between Crenarchaeota enumerated by the Cren537 and GI-554 probe were highest in the upper mesopelagic realm.
Copy numbers of the 16S rRNA gene of the crenarchaeal MCGI and the pSL12 cluster were determined by Q-PCR from several depths at Sts. 1, 2 and 4. The average copy numbers of the 16S rRNA gene of MCGI was 10.9±11.1 × 103 copies ml−1 seawater (n=9), while the corresponding copy numbers of the pSL12 cluster were about three times lower (3.4±6.5 × 103 copies ml−1, n=9) (Figure 4). There was a distinct difference in the spatial distribution pattern between MCGI and the pSL12 cluster. Higher copy numbers of the 16S rRNA gene of MCGI were obtained for the mesopelagic layer (200–1000 m) than for the surface and bathypelagic waters (>1000 m), while copy numbers of the pSL12 cluster did not exhibit major fluctuations with depth (Figure 4).
Archaeal community composition based on T-RFLP fingerprinting
The T-RFLP pattern of the archaeal community revealed in total 27 operational taxonomic units (OTUs) on the 16S rDNA level ranging from 13.2 to 1016 bp fragments (Figure 5a). Only one of the 27 OTUs (248.2 bp fragment) was present at all stations and depths and the OTUs of 580.99 and 591.29 pb were presented in almost all the samples without a clear vertical pattern. The OTU of 129.79 bp was detectable in all the samples until 1400 m depth but not at greater depth. Among all the stations, St. 4 exhibited the highest and lowest number of OTUs detectable in a specific sample, 13 OTUs at 750 m depth and 2 OTUs at 3000 m depth (Figure 5a). The Jaccard similarity cluster analysis indicated three distinct clusters, a subsurface water, a meso- and a bathypelagic cluster (Figure 5b). Analysis of similarities (ANOSIM) revealed significant differences in archaeal community composition between the surface layer (45–100 m depth) and the mesopelagic layer (200–1000 m depth, r=0.69, significant level: 0.1) and between the mesopelagic layer and the bathypelagic layer (>1400 m, r=0.60, significant level: 5.5).
Depth profile of archaeal amoA copy numbers
Copy numbers of the archaeal amoA gene were readily detectable (Figure 6a), while β-proteobacterial amoA genes were undetectable at all the stations. Copy numbers of the archaeal amoA gene were, on average, 3.9±1.2 × 103 copies ml−1 (mean±s.d., n=4) in the 200–500 m layer and 1.6 × 103 copies ml−1 at 750 m depth. Below 950 m depth, archaeal amoA copy numbers never exceeded 10 copies ml−1 (n=4).
Ratios of archaeal amoA gene copy numbers to 16S rRNA gene copy numbers (sum of MCGI and pSL12) decreased drastically with depth (Figure 6b). The ratios decreased from 0.49 at 100 m to 0.12 at 400 m depth. Below 750 m depth, the ratios were below 0.05 (0.01±0.02, n=5). The ratios of archaeal amoA gene copy numbers to crenarchaeal abundance, determined by CARD-FISH with the probes Cren537 and GI-554 (Figure 6c), were not significantly different from those obtained using the sum of the 16S rRNA copy numbers of MCGI and pSL12 (ANOVA on ranks, χ2=0.222, P=0.895). Copy numbers of the archaeal amoA gene correlated with nitrite concentrations (r=0.79, P<0.01, n=9), while no relation was found with nitrate (P>0.05, n=9); unfortunately no data are available for ammonium.
Discussion
Prokaryotic community composition
Bacteria contributed between 24 and 72% to total prokaryotic abundance at the sampling stations in the Eastern Mediterranean Sea. Although the contribution of Bacteria to total prokaryotes did not differ significantly among the stations and did not show any depth-related pattern, the bacterial contribution to total prokaryotic abundance is more variable in the Eastern Mediterranean Sea than in the North Atlantic determined by essentially the same approach as used here (Teira et al., 2006a; Varela et al., 2008).
The mean contribution of the Euryarchaeota to total prokaryotic abundance averaged only 1.4% and they are confined to the subsurface and mesopelagic layers (Figure 2). Other studies also report only a minor contribution of Euryarchaeota to the prokaryotic community such as for the western Arctic Ocean (average: 3.5% in Table 1 of Kirchman et al. (2007)), the north-west Mediterranean coastal waters (average: 2.5% in Table 2 of Alonso-Saez et al. (2007)) and the (sub)tropical North Atlantic region (<5%, (Varela et al., 2008)). Thus, the minor contribution of Euryarchaeota to prokaryotic abundance appears to be a common feature for this group, however, higher contributions than that reported by the above studies have been found in some deep waters of the North Atlantic (Teira et al., 2006a) and by shotgun sequencing of fosmid clone libraries in the North Pacific (DeLong et al., 2006). Euryarchaeota inhabiting the surface waters have been shown to harbor the proteorhodopsin gene allowing them to use light to drive the membrane proton pump, while deep-water Euryarchaeota lacked the proteorhodopsin gene (Frigaard et al., 2006).
The relative contribution of Cren537- and GI-554-positive cells to total prokaryotic abundance was 7±9 and 12±9%, respectively (Figure 2). Cren537 covers 866 out of 3873 phylotypes of Crenarchaeota and all the MCGI present in the SILVA database as of 4 April 2008, while GI-554 covers 957 crenarchaeal phylotypes resulting in an overlapping coverage of 813 phylotypes (Figure 3). Applying both probes separately using CARD-FISH on the same sample, we detected a variable number of Crenarchaeota. At St. 5, GI-554-positive cells dominated throughout the water column, while at St. 2, Cren537-positive cells dominated (Figure 2). These large variations in the relative abundance of Cren537 (range: 0–37%) and GI-554 (range: 0–35%) might suggest compositional differences in the crenarchaeotal community among stations. Recent studies showed that the relative abundance of marine Crenarchaeota Group I increases with depth in the North Atlantic and the Arctic Ocean (Herndl et al., 2005; Kirchman et al., 2007). However, no consistent depth-related trends in the relative abundance of both Cren537-positive and GI-554-positive cells are detectable in the Eastern Mediterranean Sea (Figure 2). The lack of a depth-related trend in the distribution of Crenarchaeota contrasts the pronounced decrease in the copy numbers of archaeal amoA genes with depth and the compositional differences in the archaeal community structure revealed by T-RFLP, discussed in more detail below.
The recovery efficiency with our CARD-FISH approach, that is, the sum of Bacteria determined by the EUB338 probe mix (average recovery efficiency: 44.7±10.0%, n=29), Euryarchaeota (detected by Eury806, 1.4±3.6%, n=19) and Crenarchaeota (detected either by Cren537 (6.8±9.5%, n=29) or GI-554 (11.7±9.1%, n=29)), ranged from 28 to 75%. Considering the almost complete coverage of all the bacterial groups with the EUB338 probe mix (Amann and Fuchs, 2008), the occasionally low recovery efficiency might be caused by a low coverage of the crenarchaeal community with the probes Cren537 and GI-554, by inefficient permeabilization of the cell membranes of certain prokaryotic cells or a variable contribution of dead or decaying cells still stainable with DAPI but lacking sufficient RNA (Del Giorgio and Gasol, 2008).
Abundance of specific phylogenetic groups determined by CARD-FISH and Q-PCR
Both, the abundance of Cren537- and GI-554-positive cells were within the range previously reported for Crenarchaeota (using the probe Cren537) in the North Atlantic and the Arctic Ocean (Herndl et al., 2005; Kirchman et al., 2007). Commonly, the crenarchaeal abundance determined by the Cren537 probe closely matched to that obtained by the GI-554 probe (Figure 4). Remarkable differences were noticed at specific stations and depths such as at St. 3 at 400 m depth, where the abundance of GI-554-positive Crenarchaeota was more than twice as high as the abundance of Cren537-positive cells. At St. 5, a pronounced peak in abundance of GI-554-positive Crenarchaeota was detected at around 200 m depth, while Cren537-positive Crenarchaeota were very low in abundance throughout the water column of this station (Figure 4).
The two crenarchaeal groups, MCGI and pSL12, have recently also been detected in the mespelagic zone at St. ALOHA in the subtropical gyre of the Pacific (Mincer et al., 2007). Using Q-PCR, the abundance of MCGI was always higher than the abundance of the pSL12 cluster (Figure 4). Generally, the abundance of MCGI determined by Q-PCR should not be higher than that obtained by the Cren537 probe using CARD-FISH, because the latter targets all the known partial sequences of the MCGI (Figure 3). However, in two out of nine samples, MCGI copy numbers were higher than the crenarchaeal abundance determined by either the Cren537 or GI-554 oligonucleotide probe. This might be due to PCR bias (Becker et al., 2000) or variable DNA extraction efficiency. Besides these two major discrepancies between the Q-PCR approach and CARD-FISH, both methods were in good agreement in seven out of the nine samples analyzed.
Archaeal community composition
Generally, the number of archaeal OTUs was almost twice as high in the top 100 m layer (8.9±2.2 OTUs) than in the layers below 1000 m depth (4.8±1.9 OTUs) (Figure 5a). The lowest number of OTUs was found at St. 4 at 3000 m with only 2 OTUs, while the highest number of OTUs was found at St.4 at 750 m with 13 OTUs. Only one OTU (248.23 bp) out of a total of 27 OTUs was ubiquitously present and 3 OTUs were present in almost every sample (Figure 5a). The rest of the OTUs are responsible for the observed distinct surface water and mesopelagic clusters of archaeal communities (Figure 5b). Despite the rather homogenous water column structure in the Eastern Mediterranean Sea with only small variations in salinity and temperature with depth, the surface water archaeal community is distinctly different from that in the other water layers reflecting the depth-related distribution pattern of archaeal amoA gene copy numbers discussed below. Overall, considerable spatial heterogeneity in the archaeal community composition between the individual depth layers of the different stations is apparent.
Depth profiles of archaeal amoA gene
Although bacterial amoA genes were not detected, archaeal amoA genes were readily detectable in the surface and mesopelagic waters (Figure 6a). A dominance of archaeal amoA over bacterial amoA genes was also found in the coastal North Sea and the mesopelagic waters of the North Atlantic (Wuchter et al., 2006), as well as in soils (Leininger et al., 2006). Our results support previous studies suggesting that marine Crenarchaeota are, at least partly, ammonia oxidizers (Francis et al., 2005; Könneke et al., 2005). Copy numbers of the archaeal amoA gene decreased with the depth and were essentially absent below 1000 m depth (Figure 6a). Thus, the copy numbers of archaeal amoA decreased more rapidly with depth than the abundance of Crenarchaeota determined by CARD-FISH and of MCGI and pSL12 determined by Q-PCR (Figure 4). This becomes evident, if the ratio of archaeal amoA gene copy numbers to crenarchaeal abundance (16S rRNA copy numbers, Cren537- and GI-554-positive cells) is calculated (Figures 6b and c). While in subsurface waters the ratio of amoA gene copy numbers: (MCGI+pSL12) is about 0.5, the corresponding ratios using crenarchaeal abundance determined by probes Cren537 and GI-554 range between 0.2 and 0.3 in subsurface waters. Genomic studies on Cenarchaeum symbiosum and Nitrosopumilus maritimus revealed that both isolates contain one amoA copy per cell (Hallam et al., 2006; D Stahl, personal communication). The ratios we obtained indicate that even in the surface waters and at St. 1 at 500 m depth not all of the detected Crenarchaeota harbor an amoA gene (Figures 6b and c). This ratio decreases rapidly with depth down to 1000 m implying that other energy sources than ammonia might be utilized to sustain the observed crenarchaeotal abundance. It has been shown that Crenarchaeota are also capable of utilizing organic substrates (Ouverney and Fuhrman, 2000) and that crenarchaeotal heterotrophy increases with depth (Teira et al., 2006b).
For surface and mesopelagic waters, a positive relation between Crenarchaeota abundance and the concentration of ammonia was reported (Wuchter et al., 2006; Kirchman et al., 2007; Varela et al., 2008), as well as with nitrite (Teira et al., 2006a; Lam et al., 2007). In this study, nitrite concentration explains about 60% of the variation in archaeal amoA copy numbers in the water column of the Eastern Mediterranean Sea (data not shown). This suggests that Crenarchaeota in the surface waters and in the mesopelagic realm are most likely oxidizing ammonia as an energy source (Lam et al., 2007), while in the bathypelagic waters, crenarchaeal abundance is most likely sustained by other energy sources, probably by organic compounds.
In conclusion, we have shown that in the Eastern Mediterranean Sea, crenarchaeal abundance remains fairly constant with depth and that the number of archaeal phylotypes identified by T-RFLP decreases with depth. The ratio archaeal amoA copy numbers/crenarchaeal abundance rapidly declines with depth indicating that putatively ammonia oxidizing Crenarchaeota are largely confined to the surface and mesopelagic waters, while in bathypelagic waters of the Eastern Mediterranean Sea, Crenarchaeota are likely utilizing energy sources other than ammonia, presumably organic sources as recently reported for the crenarchaeal community in the North Atlantic.
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Acknowledgements
We thank Dr Aleka Gogou (HCMR) and Dr Georgina Spyres (HCMR) for all the logistic arrangements prior and during the cruise, and the captain and crew of R/V Aegaeo for their help at sea. Maaike Brink, Judith van Bleijswijk and Harry Witte helped throughout the molecular analyses. TY was supported by the Japanese Society for the Promotion of Science (JSPS) Postdoctoral Fellowship for research abroad and DDC received a fellowship of the University of Groningen. Laboratory work and molecular analyses were supported by a grant of the Earth and Life Science Division of the Dutch Science Foundation (ARCHIMEDES project, 835.20.023) to GJH. The work was carried out within the frame of the ‘Networks of Excellence’ MarBef and EurOceans supported by the 6th Framework Program of the European Union. This work is in partial fulfillment of the requirements for a Ph.D. degree from the University of Groningen by DDC.
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De Corte, D., Yokokawa, T., Varela, M. et al. Spatial distribution of Bacteria and Archaea and amoA gene copy numbers throughout the water column of the Eastern Mediterranean Sea. ISME J 3, 147–158 (2009). https://doi.org/10.1038/ismej.2008.94
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DOI: https://doi.org/10.1038/ismej.2008.94
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