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Applied and Environmental Microbiology, June 2007, p. 3975-3983, Vol. 73, No. 12
0099-2240/07/$08.00+0 doi:10.1128/AEM.02532-06
Copyright © 2007, American Society for Microbiology. All Rights Reserved.

Max Planck Institute for Marine Microbiology, Celsiusstrasse 1, D-28359 Bremen, Germany,1 CNRS and Université Montpellier II UMR 5119, Case 093, Place Eugène Bataillon, F-34095 Montpellier Cedex 05, France,2 Delft University of Technology, Postbox 5048, NL-2600 GA Delft, The Netherlands3
Received 31 October 2006/ Accepted 11 April 2007
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-carotene, pigments known to be produced by phototrophic CLB. Oxygen microsensor measurements for intact mats revealed a NIR (710 to 770 nm) light-dependent decrease in aerobic respiration, a phenomenon that we also observed in an axenic culture of Chloroflexus aurantiacus. The metabolic ability of phototrophic CLB to switch from anoxygenic photosynthesis under NIR illumination to aerobic respiration under non-NIR illumination was further used to estimate the contribution of these organisms to mat community respiration. Steady-state oxygen profiles under dark conditions and in the presence of visible (VIS) light (400 to 700 nm), NIR light (710 to 770 nm), and VIS light plus NIR light were compared. NIR light illumination led to a substantial increase in the oxygen concentration in the mat. The observed impact on oxygen dynamics shows that CLB play a significant role in the cycling of carbon in this hypersaline microbial mat ecosystem. This study further demonstrates that the method applied, a combination of microsensor techniques and VIS and NIR illumination, allows rapid establishment of the presence and significance of CLB in environmental samples. |
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Characterization of CLB in Lake Chiprana microbial mats. (i) Oxygen and hydrogen sulfide dynamics in intact mats.
In order to characterize the intact microbial mat, profiles of oxygen and hydrogen sulfide concentrations were determined at 100-µm intervals in the laboratory in a flowthrough chamber with artificial illumination (83 and 300 µmol photons m2 s1) using a fiber optic lamp (Schott KL 1500) which has a halogen lamp as the light source. Oxygen profiles were also determined under dark conditions and with 33 and 166 µmol photons m2 s1. Clark-type amperometric oxygen (tip diameter, 10 µm) and hydrogen sulfide (tip diameter, 15 µm) microsensors were used. Details concerning the use of oxygen and hydrogen sulfide sensors and calibration procedures have been described previously (17, 35). Microsensors were mounted on a motorized micromanipulator connected to a heavy stand. Positioning and data acquisition were performed automatically with a laptop computer. Before profiling, the microsensor tip was positioned on the sediment surface of the microbial mat with the aid of a binocular microscope.
(ii) Microscopic observations.
The topmost 2-mm green stratum (i.e., the photic zone of the mat) was suspended in filtered lake water, and aliquots were removed and used for fluorescence microscopy. Microscopic samples were excited with blue light, and in combination with a long-pass filter (>520 nm) filamentous bacteria that were fluorescent (cyanobacteria) or nonfluorescent in the visible part of the light spectrum could be distinguished. Nonfluorescent thin filaments without visible sulfur inclusions were considered CLB. The diversity of CLB morphotypes was determined on the basis of filament width and length. The ratio of nonfluorescent filaments to fluorescent filaments was determined visually using multiple sample preparations.
(iii) Photopigment analysis.
The photic zone (0- to 2-mm surface layer) was cut off frozen microbial mat samples and freeze-dried. Pigments were extracted after sonication in high-performance liquid chromatography (HPLC)-grade acetone. The extracts from two subsequent extractions were combined, and the carboxylic groups of extracted pigments were methylated with 2 or 3 drops of diazomethane dissolved in acetone using a modification of the method recommended by Sigma-Aldrich (catalog no. Z411736; Aldrich, Milwaukee, WI) using 1-methyl-3-nitro-1-nitrosoguanidine as the precursor. The solvent was evaporated using a speed vacuum machine for a few hours until the preparation was completely dry, leaving pigments in the tube. Pigments were redissolved in a 2-ml HPLC elution solution containing 45% acetonitrile, 50% methanol, and 5% water-based 50 mM ammonium-acetate buffer (pH 7.2). The liquid was filtered through a sterile 0.2-µm-pore-size filter, and a 100-µl aliquot was injected into an HPLC for pigment identification and quantification using a binary protocol as described previously (5).
(iv) CLB phylotype diversity: DNA extraction, PCR amplification, and cloning.
In order to estimate the diversity of CLB phylotypes in the mat studied, a clone library was constructed. Genomic DNA was extracted from 0.2-g mat samples as described previously (1) and purified with a Wizard DNA clean-up system (Promega). An approximately 400-bp fragment of the 16S rRNA gene was amplified from genomic DNA using two primers specific for bacteria of the phylum Chloroflexi (green nonsulfur bacteria) (11), GNSB-941F (5'AGCGGAGCGTGTGGTTT3') and GNSB-1340R (5'CGCGGTTACTAGCAAC3'). Two microliters of template was added to a 50-µl reaction mixture containing 0.5 U Eppendorf Taq, 1x buffer, 4 mM of MgCl2, 4 mM of each deoxynucleoside triphosphate, and 1 µM of each primer. The reaction was performed in a Mastercycler thermocycler (Eppendorf, Hamburg, Germany) with the following cycling conditions: 95°C for 2 min and then 30 cycles of 95°C for 30 s, 55°C for 30 s, and 72°C for 1 min, followed by a final incubation at 72°C for 10 min. The PCR product was visualized on an agarose gel, and the 16S rRNA band was excised. The excised PCR product was then purified using a QIAquick gel extraction kit (QIAGEN, Hilden, Germany). Two microliters of purified product was then ligated into the pGEM-T Easy vector (Promega, Madison, WI) and then transformed into Escherichia coli TOP10 cells (Invitrogen, Carlsbad, CA) according to the manufacturer's recommendations. Overnight cultures were prepared from positive transformants in a 2-ml 96-well culture plate. Plasmid DNA was extracted and purified using a Montage 96 plasmid miniprep kit (Millipore, Billerica, MA).
(v) DNA sequencing and analysis.
Purified plasmids were sequenced in one direction with the M13F primer, using a BigDye Terminator v3.0 cycle sequencing kit (Applied Biosystems, Foster City, CA). Samples were run on an Applied Biosystems 3100 genetic analyzer (Foster City, CA). A phylogenetic tree was constructed with the ARB software package (http://www.arb-home.de) (21). First, the partial sequences retrieved and amplified from the mat were grouped into phylotypes based on the criterion that sequences of the same phylotype share more than 96% similarity. Phylogenetic trees were constructed with the maximum likelihood, maximum parsimony, and neighbor joining methods, using publicly available sequences that were at least 1,100 bp long. Representative sequences from each phylotype were then added to the phylogenic trees by parsimony.
Functional analysis of CLB in mats and culture. (i) Aerobic respiration of C. aurantiacus.
In order to determine the influence of different types of light (VIS and/or NIR illumination) on the metabolism of CLB (phototrophy versus aerobic respiration), an axenic culture of the hyperthermophilic strain C. aurantiacus DSM 635 was used as model for CLB in the natural environment (even though C. aurantiacus might be quite different from CLB present in hypersaline environments, pure cultures of hypersaline CLB species are not available). C. aurantiacus was cultured according to DSMZ recommendations in yeast extract medium amended with 1 mM sulfide. Cultures were incubated anaerobically at 55°C under a light-dark regimen consisting of 16 h of illumination with incandescent light (approximately 25 µmol photons m2 s1) and 8 h of darkness. Oxygen consumption under different light conditions was determined with sulfide-depleted cultures. Just before oxygen consumption measurement, culture aliquots were aerated and then incubated in 25-ml glass tubes in a water bath at 55°C. An oxygen microsensor, fitted in a butyl rubber stopper, was inserted into the culture (protein content, 0.58 ± 0.03 mg ml1) without introduction of air bubbles and sealed to avoid contact with ambient air during the measurement. The change in the oxygen concentration over time was recorded. Cultures killed with formaldehyde (final concentration, 2%) were used to correct for abiotic oxygen consumption. Two sets of light-dark shift experiments were performed; the set of first experiments was performed with a combined VIS and NIR light source, and the second set of experiments was performed with only a VIS light source. In the first set of experiments light was provided by a 25-W incandescent (VIS plus NIR) light bulb in combination with two 40-mA NIR light-emitting diodes (LEDs) with a peak wavelength at 740 nm and a spectral full-width at half-maximum bandwidth of a 30-nm angle (LED-740-524; Roithner LaserTechnik, Austria). The light intensity as determined with a scalar irradiance light sensor (LI-250A; LI-COR Biosciences) was 15 µmol photons m2 s1 near the surface of the culture tube; however, the specific intensity of the NIR light was unknown as the light meter used is not sensitive in the NIR (>700-nm) light spectrum. The light source used in the second set of experiments was two warm white high-power LEDs (LXHL-MWGC; Lumileds, United States). The light range of these LEDs is restricted to the VIS part of the spectrum (400 to 700 nm). With this light source a light intensity of 60 µmol photons m2 s1 was measured at the surface of the inundated culture tube.
(ii) Aerobic respiration of intact mats under different illumination conditions.
In order to elucidate the effect of NIR light illumination on oxygen dynamics, intact mat pieces were incubated in a flowthrough chamber at room temperature and illuminated with LEDs with VIS radiance (400 to 700 nm: LXHL-MWGC; Lumileds) and/or with two 40-mA NIR LEDs (LED-740-524; Roithner LaserTechnik, Austria). The advantage of using separate LEDs instead of using VIS/NIR filters in combination with a full-spectrum light source is that the light intensity of the light source with one type of spectrum is not changed when the light source with the other spectral type is switched on or off. VIS LEDs were used to illuminate mats at 60 µmol photons m2 s1 with or without additional NIR light illumination, and oxygen profiles were recorded after steady-state conditions were reached. The microbial mat areal net oxygen production rates were calculated from the change in oxygen fluxes in the diffusion boundary layer using an oxygen diffusion coefficient of 2.1 x 105 (25°C, 75 ppt) (see reference 35 for details concerning the procedure used). In order to determine whether oxygen evolution occurred with NIR light illumination, the oxygen profiles in NIR light-illuminated mats were measured before and after the addition of 3-(3,4-dichlophenyl)-1-1-dimethylurea (DCMU), a specific inhibitor of the oxygen-evolving photosystem II. DCMU was added from a stock solution (1 mM dissolved in 70% ethanol) to a final concentration of 5 µM.
Nucleotide sequence accession numbers.
The partial 16S rRNA gene sequences determined in this study have been submitted to the GenBank database and assigned accession numbers DQ973818 to DQ 973833.
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FIG. 1. Steady-state oxygen and sulfide profiles in Lake Chiprana microbial mats at different light intensities. (A) Oxygen concentration profiles with 0, 33, 83, 166, and 300 µmol photons m2 s1. The oxygen concentration reaches up to six times the air saturation level at higher light intensities, indicating that CLB in the photic zone have to cope with high and fluctuating oxygen concentrations. (B) Oxygen and sulfide (H2S) concentration profiles at light intensities of 83 and 300 µmol photons m2 s1. Oxygen and sulfide cooccur in the zone between 1 and 1.5 mm deep, a zone where CLB are able to oxidize sulfide both phototrophically and chemotrophically, in the latter case using oxygen as the electron acceptor. µE, microeinsteins.
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(iii) Microbial mat photopigment analysis.
HPLC analysis of the pigments of the microbial mat studied revealed the presence of BChla, BChlc, and BChld, as well as
-carotene, pigments that are known to be produced by photosynthetic members of the family Chloroflexaceae (12). Figure 2 shows the chromatograms at 440, 660, and 760 nm for a sample from the top layer of the mat, and the peaks are identified in Table 1. The pigment composition reflects a phototrophic community comprising cyanobacteria (chlorophyll a [Chla], zeaxanthin, and ß-carotene) and CLB (BChlc/d,
-carotene, and minor amounts of BChla). In addition, degradation products of these compounds were observed. The BChlc/d allomers eluted between 13 and 27 min (Fig. 2, peaks 5 to 10, 12, and 13). These retention times were longer than those observed for the farnesol-esterified BChlc homologs (BChlcF) found in a culture of Chlorobium tepidum. This indicates that the BChlc/d homologs were more hydrophobic than the BChlcF homologs and were thus esterified with another alcohol. C. aurantiacus contains different allomers of BChlc esterified with stearyl, phytyl, and geranylgeranyl alcohols. Further identification of the BChlc/d homologs requires HPLC-mass spectrometry. In addition, BChla (peak 11) was found in the mats, and we also observed two late-eluting BChld-like compounds. Different bacteriochlorophyll degradation products were identified as bacteriopheophorbide c and bacteriopheophytins a, c, and d. A number of peaks were quantified (Table 2). The ratio of BChlc to BChld to BChla was 72:26:1 on average.
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FIG. 2. HPLC chromatograms at 440, 660, and 760 nm for a sample from the top 5 mm of the Lake Chiprana microbial mat. Identified pigment molecules, indicated by numbers, are described in Table 1. The main pigments are Chla (peak 17) and BChlc allomers (peaks 5, 6, 8, 12 to 14, and 16).
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TABLE 1. Pigment identification, retention times, and max for the different peaks shown in the chromatograms in Fig. 2
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TABLE 2. Quantification of pigments of the Lake Chiprana microbial mat in September 2004a
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FIG. 3. 16S rRNA gene maximum parsimony tree for representative sequences obtained in this study (bold type) and sequences retrieved from the database. Sequences from this study in the tree represent groups of sequences that shared more than 96% identity; the numbers in parentheses indicate the numbers of sequences in the groups. Asterisks indicate known phototrophic species, and number signs indicate previously isolated and described species. The bootstrap values at the nodes are percentages based on 1,000 replications. Sequences from this study, as well as LO4675, AJ09636, and AJ309642, were excluded from the bootstrap analysis. Group I represents sequences recovered in this study, which formed a separate clade that included H. oregonesis (a chlorosome-less, BChla- but not BChlc- or BChld-producing species) and "Candidatus Chlorothrix" (chlorosome-containing, BChla- and BChlc-producing species); group II represents sequences obtained in this study that formed a clade with Chloroflexus, Chloronema, and Oscillochloris (chlorosome-containing, BChla- plus BChlc- or BChld-producing species). Groups III to VIII represent sequences from this study which cluster with sequences distantly related to the family Chloroflexaceae but are still in the phylum Chloroflexi.
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FIG. 4. Oxygen consumption in aerated axenic cultures of C. aurantiacus under different illumination conditions. (A) Alternating illumination with NIR light (25-W incandescent light bulb plus two 40-mA NIR LEDs [710 to 770 nm]) and darkness. (B) Alternating illumination with VIS light (two VIS LEDs [400 to 700 nm]) and darkness, as well as the formaldehyde-killed control. See Table 3 for calculated specific respiration rates.
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TABLE 3. C. aurantiacus aerobic respiration rates in aerated axenic culture aliquots (n = 4) under different illumination conditions
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FIG. 5. Steady-state oxygen concentration profiles in the Lake Chiprana microbial mat under four different light conditions: (i) darkness, (ii) NIR light (two 40-mA NIR LEDs [710 to 770 nm]), (iii) VIS light (two VIS LEDs [400 to 700 nm]; 60 µmol photons m2 s1), and (iv) two NIR LEDs plus two VIS LEDs.
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TABLE 4. Net areal oxygen production rates calculated from oxygen concentration profiles in Lake Chiprana microbial mats under different illumination conditionsa
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The role that CLB play in the local carbon cycle can be inferred from their respiration rate under non-NIR light conditions. Axenic culture experiments with C. aurantiacus showed that the oxygen respiration decreased by about 50% upon illumination with NIR light. CLB can switch from anoxygenic phototrophy, which provides energy due to cyclic electron transport in photosystem I, to aerobic respiration to sustain energy generation under dark conditions (13). It can thus be assumed that the amount of oxygen respired under non-NIR light conditions at least equals the equivalent energy that was produced by anoxygenic photosynthesis by active CLB illuminated with NIR light. Therefore, one way to estimate the role of CLB in the local carbon cycle is to compare their non-NIR light respiration to the total community respiration. In the dark, the total community respiration, as inferred from microbial mat areal oxygen uptake, decreased from 0.13 to 0.10 nmol O2 cm2 s1, a decrease of 25%, upon illumination with NIR light. When NIR light was supplied along with VIS light, the net community areal oxygen production increased from 0.03 to 0.07 nmol O2 cm2 s1; thus, the apparent net primary production more than doubled, likely as a result of a decrease in CLB respiration due to a switch to anoxygenic phototrophy for energy generation.
The measurable change in oxygen dynamics upon illumination with NIR light (740 nm) of intact mats can thus be attributed to CLB activity. However, as this metabolic shift is directly linked to the mode of energy generation, no conclusions can be drawn as to whether a shift in the electron donor for autotrophic growth (e.g., reduced sulfur compounds) or a shift in the carbon source (organic or inorganic) for hetero- or autotrophic growth also occurs. CLB are known to be able to use various inorganic compounds as electron donors during autotrophic growth, as well as inorganic and various organic compounds as carbon sources during phototrophic or heterotrophic growth (13, 34). The fact that CLB can be found at high densities in microbial mats is likely due to this versatile metabolism. In mats light intensity and oxygen, reduced sulfur compound, and dissolved inorganic and organic carbon concentrations change rapidly during a full 24-h diel cycle, conditions to which CLB are maximally adapted. In such systems these bacteria would have a competitive advantage over more specialized but metabolically more restricted organisms.
The capacity to switch from anoxygenic photosynthesis to respiration has thus been clearly demonstrated for C. aurantiacus in culture experiments and has been inferred for the CLB in a microbial mat from oxygen profiles. This ability, which is apparently widespread among CLB, has important consequences for the quantification of gross photosynthesis in mats using the traditional light/dark shift method, which was introduced by Revsbech et al. in 1981 (30) and has been used in numerous studies since. This method is based on the assumption (among others) that in a microbial mat under steady-state (stable oxygen profile) conditions, the community oxygen consumption rate is unchanged initially (for at least a few seconds) when the mat is switched from light to darkness. The rate of oxygen disappearance at the start of the dark period then equals the rate of oxygen production in the light (30). This assumption, however, does not hold when C. aurantiacus or other CLB make up a significant part of the microbial community, as these organisms may switch within seconds from anoxygenic photosynthesis in the light to aerobic respiration in the dark. The fact that this effect can be substantial was shown in this study, where the apparent net photosynthesis more than doubled when NIR light was supplied along with VIS light. Hence, using the traditional light/dark shift method, gross photosynthesis rates are substantially overestimated in CLB-rich microbial mats. However, this effect can be compensated for, if only VIS light (400 to 700 nm) is used as a light source (CLB behave as aerobic bacteria [i.e., continuously respire]) or, alternatively, an additional NIR light source remains on continuously (CLB continue anoxygenic phototrophy and do not switch to aerobic respiration when VIS light is switched off) during measurements.
The high diversity of 16S rRNA gene phylotypes affiliated with the phylum Chloroflexi indicates that besides a number of sequences that group in the family Chloroflexaceae, nonfilamentous and even nonphototrophic Chloroflexi may be present in the mat examined. It is difficult to infer the type of chlorophyll that a bacterium possesses based on our 16S rRNA data given the paucity of 16S rRNA gene sequences available for cultured members of the Chloroflexaceae. However, the three sequences represented by LCC39 (cluster II) group with sequences from two characterized Chloroflexus species and are therefore likely to represent BChlc-producing CLB active in this system. The six sequences in cluster I that were recovered in this study are most closely related to the 16S rRNA gene from Heliothrix oregonensis, a CLB that does not, like Chloroflexus species, produce BChlc or BChld in addition to BChla. The organisms responsible for these sequences may thus not have contributed to the observed changes in community oxygen respiration when illumination with 740-nm NIR light was manipulated. The three sequences represented by LCC39 from the mat are the sequences that are most closely related to the 16S rRNA gene from C. aurantiacus which originated from a hot spring microbial mat and which so far is the most intensely studied and characterized species in the family Chloroflexaceae. However, they share sequence identity of only 88%. The highest sequence identity obtained for the hypersaline mat studied here (cluster I) was the sequence identity with sequences that originated from a mat in Guerrero Negro, Mexico (accession no. AJ309642 and AJ309636) (23), which was also a hypersaline microbial mat but was on a different continent. The sequence similarity between these sequences was up to 99%, which indicates that at least some hypersaline Chloroflexaceae may have a cosmopolitan distribution.
This study focused on CLB, which are filamentous phototrophic bacteria that are members of the family Chloroflexaceae. Although the clone library in this study retrieved 10 of 49 sequences that grouped in the family Chloroflexaceae, it is not known whether all these sequences represent filamentous phototrophic bacteria, as only a few sequences from this group represent well-characterized strains. Furthermore, the clone library shows that sequences retrieved in this study that fall outside the family Chloroflexaceae but still cluster within the phylum Chloroflexi are all most closely related to sequences from uncultured organisms. The apparently high but uncharacterized diversity of Chloroflexi-related sequences retrieved from the specific hypersaline mat studied seems to be typical, as other studies of various hot spring mats (24, 29) and hypersaline mats (19, 23), as well as other ecosystems (3, 11), reported the same diversity. An intriguing question is what kind of species these sequences belong to and what ecological role they play in these ecosystems. Future cultivation and ecophysiological characterization studies must resolve this question.
A. Bachar was supported by grant DFG JO-412 from the German Research Foundation. R. de Wit acknowledges support from the Deutscher Akademischer Austausch Dienst (DAAD) and the Agence National de la Recherche (program CYANOCARBO).
Published ahead of print on 20 April 2007. ![]()
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