Dinitrogen-Fixing Cyanobacteria in Microbial Mats of Two Shallow Coral Reef Ecosystems
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- Charpy, L., Palinska, K.A., Casareto, B. et al. Microb Ecol (2010) 59: 174. doi:10.1007/s00248-009-9576-y
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Dinitrogen-fixing organisms in cyanobacterial mats were studied in two shallow coral reef ecosystems: La Reunion Island, southwestern Indian Ocean, Sesoko (Okinawa) Island, and northwestern Pacific Ocean. Rapidly expanding benthic miniblooms, frequently dominated by a single cyanobacterial taxon, were identified by microscopy and molecular tools. In addition, nitrogenase activity by these blooms was measured in situ. Dinitrogen fixation and its contribution to mat primary production were calculated using 15N2 and 13C methods. Dinitrogen-fixing cyanobacteria from mats in La Reunion and Sesoko showed few differences in taxonomic composition. Anabaena sp. among heterocystous and Hydrocoleum majus and Symploca hydnoides among nonheterocystous cyanobacteria occurred in microbial mats of both sites. Oscillatoria bonnemaisonii and Leptolyngbya spp. occurred only in La Reunion, whereas Hydrocoleum coccineum dominated in Sesoko. Other mats dominated by Hydrocoleum lyngbyaceum, Phormidium laysanense, and Trichocoleus tenerrimus occurred at lower frequencies. The 24-h nitrogenase activity, as measured by acetylene reduction, varied between 11 and 324 nmoles C2H2 reduced µg−1 Chl a. The highest values were achieved by heterocystous Anabaena sp. performed mostly during the day. Highest values for nonheterocystous cyanobacteria were achieved by H. coccineum mostly during the night. Daily nitrogen fixation varied from nine (Leptolyngbya) to 238 nmoles N2 µg−1 Chl day−1 (H. coccineum). Primary production rates ranged from 1,321 (S. hydnoides) to 9,933 nmoles C µg−1 Chl day−1 (H. coccineum). Dinitrogen fixation satisfied between 5% and 21% of the nitrogen required for primary production.
Biological N2 fixation is a process unique to prokaryotes occurring commonly in freshwater and marine cyanobacteria. Although energetically demanding, this process provides the organisms with a particular advantage when growing under N-limited conditions, which are most frequent in marine environments [17, 44]. The rates of nitrogen fixation, their relations to nitrogen concentration levels, and contribution to global oceans have been subject to extensive studies and reviews [e.g., [3, 8, 10, 29, 39]]. Due to oxygen sensitivity of the nitrogenase enzyme, the fixation of carbon and dinitrogen in an oxygen-producing organism needs to be separated either in space or in time [3, 39]. Spatial separation is achieved in heterocystous cyanobacteria which are able to fix dinitrogen during the day, contemporaneous with their energy generation. With some exceptions (e.g., Trichodesmium), nonheterocystous cyanobacteria temporally separate N2 fixation and oxygenic photosynthesis by fixing dinitrogen at night, using photosynthetic energy as ATP generated during the previous day .
Biological N2 fixation appears to make a major contribution to N supply in coral reef ecosystems, as it has been shown for the Eniwetok Atoll , the Great Barrier Reef , and for the lagoons of Tikehau Atoll  and New Caledonia . Many studies of dinitrogen fixation have dealt with shallow areas of coral reefs [8, 16, 31, 42] including exposed communities of an atoll rim . To our knowledge, none of these studies were performed on identified cyanobacterial populations that support microbial mats.
The main objective of our study is to identify the dominant taxa in cyanobacteria mats and determine their contribution to N2 fixation in shallow coral reef ecosystems.
Materials and Methods
Areas of Study
The present contribution is based on the field research performed in the framework of a Japan–French collaborative program at La Reunion Island (November, 2004 and February, 2007) and on Sesoko Island offshore of Okinawa (July, 2005 and October, 2006). In both sites, we used the facilities of marine stations laboratories.
Sesoko Island (26°38′N, 27°51′E) is located off the NW coast of Okinawa in the Ryukyu Archipelago, southwestern Japan. The sea around the Ryukyus is under the influence of the warm Kuroshio Current and characterized by the development of coral reefs from latitudes 24° to 31°N marking their northernmost distribution. The climate is subtropical with a rainy season in early summer from May to the end of June. The tropical storm season is from July to October. Three sampling stations were selected in July, 2005, and October, 2006 (Fig. 2b). Station B (1- to 2-m depth) is located in a moat on the west coast of Sesoko Island behind a well-developed reef crest, located 150–200 m from the shore . Station C (1.5- to 2-m depth) is close to the bridge linking Sesoko to Okinawa, and Station D (2- to 3-m depth) is located next to the pier of Sesoko Station, Tropical Biosphere Research Center of the University of the Ryukyus.
Environmental Parameters and Nutrients
Temperature, salinity, and nutrient concentrations were routinely measured during field research operations. Triplicate subsamples of sea water for nutrient measurement were collected into clean acid-washed 100 mL polyethylene bottles and kept frozen. Nutrients were determined with an autoanalyzer (TRAACS-2000: BRAN+LUBE) according to Hansen and Koroleff . Nitrate was determined by subtracting the values of nitrite from the values of nitrate+nitrite. The detection limits were 0.052 µM for NO3− + NO2−, 0.01 µM for NO2−, 0.020 µM for NH4+, and 0.020 µM for PO43−. Reproducibility (margin of error) of nutrient analysis was ± 0.2% for NO3−, ± 0.5% for NO2−, ± 1.2% for NH4+, and ± 0.8% for PO4−3.
Distribution of Cyanobacterial Mats
To estimate frequency and coverage of cyanobacterial mats in La Reunion lagoon, five transects, each ca 300-m long from the beach to the reef flat were examined. The coverage of different morphotypes of cyanobacteria was estimated along each transect. This method of estimation could not be performed for Sesoko where mats were attached to small coral reef pinnacles with irregular distribution. Therefore, we could not calculate mean percent coverage of the mats along transects.
Rapidly expanding local miniblooms of cyanobacteria, distinguished by their color and consistency, were documented by underwater photography and sampled using SCUBA diving. Live samples were microscopically analyzed immediately following collection. Samples found to be unicyanobacterial and in the expanding growth phase, were selected for further analyses. Samples were taken at the end of the day in order to optimize night nitrogenase activity, which depends on the light energy received during daylight . Following sampling, one aliquot of the mat was preserved with formaldehyde (4%) for later microscopic analysis; a second aliquot was stored in guanidine thiocyanate for DNA analysis , and a third aliquot was used for acetylene reduction assay in triplicate.
Microscopic analysis was carried out following collection to establish the composition of samples for analyses of carbon and nitrogen metabolism. Detailed microscopy and photomicrography, including morphometric evaluation, has been carried out subsequently on formaldehyde– and guanidine–thiocyanate-fixed samples to aid morphotypic and genotypic characterization of the studied cyanobacteria. Zeiss RA and Universal Microscope (Carl Zeiss, Inc., Oberkochen, Germany) equipped with transmitted light and DIC illumination has been used with a digital photomicrographic camera attachment Moticam 2000 (Motic China, Co, Ltd.).
The taxonomic identities of cyanobacteria under study were determined by polyphasic analysis in order to correlate their morphotypic properties (determined by S. Golubic) according to classifications by Geitler , Komárek and Anagnostidis  and Bergey’s Manual  with sequences of 16S rRNA gene fragments (performed by K. Palinska). Measurements of cell dimensions were carried out on the basis of photomicrographs and in-scale camera-lucida projections. Measurements were recorded using SigmaScan software (Jandel Scientific, Sausalito, CA) and expressed as means ± standard deviation of 20 to 50 measurements.
DNA Extraction, PCR Amplification, Sequencing and Phylogenetic Analysis
One milliliter of each population suspended in guanidine thiocyanate was added to 1 ml of TESC (10 mM Tris, 1 mM EDTA, 20 mM NaCl, 2% acetyltrimethylammonium bromide, pH 8.0). After addition of lysozyme (1% final concentration), the samples were incubated at 37 °C for 1 h. After ten cycles of freeze (in liquid nitrogen) and thaw (at 65 °C), 5 µl proteinase K (100 µg/ml) and 90 µl 10% sodium dodecyl sulfate was added, and the samples were incubated at 52 °C overnight. The samples were centrifuged in a microcentrifuge at 12,000 × g for 5 min, and the supernatants were extracted twice with phenol, phenol/chloroform, and chloroform. The DNA was precipitated from the aqueous phase with 0.6 volumes of 2-propanol, washed with 70% ethanol, vacuum dried, and stored in 100 µL TE buffer (10 mM Tris, 1 mM EDTA, pH 8.0).
Primers PLG1.1 and PLG2.1 described by Nadeau et al.  were used for amplification of partial 16S rRNA genes. The reaction volume was 100 µL and contained: 1 × REDTaq PCR Buffer, 200 µM of each deoxynucleotide, 200 µg BSA, 500 ng of each oligonucleotide primer, 5 U of RED Taq DNA polymerase (Sigma-Aldrich), and 1-10 µL of DNA extract. After an initial denaturation step (4 min at 94 °C), 31 incubation cycles followed, each consisting of 1 min at 94 °C, 1 min at 52 °C, and 1.5 min (8 min at the last cycle) at 72 °C. The presence of PCR products was detected by standard agarose gel electrophoresis and ethidium bromide staining. Amplification products were purified with the QIAquick PCR Purification Kit (Qiagen, Hilden, Germany).
DNA samples were directly sequenced in both directions by a commercial sequencing laboratory. Sequence similarities were calculated online with ClustalW ( at http://www.ebi.ac.uk/clustalw/index.html). Sequence alignment and phylogeny of 16S rRNA fragments obtained from the populations were carried out using the ARB software version 07.12.17prv and the official database (www.arb-home.de) from February 2005 for small subunit RNA sequences (ssu_jan04_corr_opt.arb). Additionally, cyanobacterial gene sequences available from the GenBank were imported and aligned in the database of the ARB software. These sequences were then aligned with the sequences in the ARB database using the alignment ARB tool. The alignment was corrected manually. The phylogenetic tree was calculated by maximum likelihood, based on long 16S rRNA gene sequences. The sequences were inserted into the preestablished tree using the parsimony ARB tool while maintaining the overall tree topology without changes. The final tree was minimized for simplicity in presentation.
Incubation with Stable Isotopes and Acetylene Reduction
Immediately following sampling, the mats were placed in seawater collected at the same place and depth, enriched with C2H2 or 15N2 and NaH13CO3, and incubated in situ. Incubation started before the sunset and continued until early morning for dinitrogen fixation of nonheterocystous cyanobacteria. For heterocystous cyanobacteria, the incubation continued until the end of the following day .
Nitrogenase Activity Measurements
Nitrogenase activity was estimated by measuring the acetylene reduction rate (ARR). Short (1 h) and long-term (12 h) measurements were performed, using a single injection of acetylene . Pieces of 1-cm2 of mat were placed inside 175-mL polycarbonate bottles fitted with a Teflon septum and filled with 125 mL of sea water from the sampling site. Experiments, in triplicate, were started by removing 5 mL of air above the sampled water and injecting the same volume of C2H2, followed by swirling for several minutes in the purpose of dissolving injected acetylene. C2H2 concentration measurements performed at the beginning of incubations demonstrated that 80% of the added C2H2 was dissolved in seawater. Light energy (PAR) was continuously recorded using a miniature light recorder (Alec Electronics Company). Four milliliters of gas mixture were taken using a vacuum tube at the end of the daylight and at the sunrise after swirling the sample for several minutes each time. Ethylene concentrations were measured using a gas chromatograph (Agilent µ GC) calibrated with commercial gas standards. Three replicates were measured from each incubation bottle. The dissolved ethylene concentration was calculated using the Bunsen gas solubility coefficient of 0.08 according to Breitbarth et al.  for a temperature of 28 °C and a salinity of 35 psu. ARR was calculated within each incubation period by subtracting C2H4 formed in the preceding period. The biomass of incubated benthic cyanobacteria was calculated from the chlorophyll a content. At the end of incubation with C2H2, the mat was dried using Whatman filter paper and frozen for later spectrophotometric analysis of the La Reunion mats and for high performance liquid chromatography (HPLC) analysis of the Sesoko mats. The relative efficiency of nitrogenase activity was expressed as ARR per Chl a. Results are also presented as gross dinitrogen fixation rate calculated by using factor 4 in conversion from ARR .
Net Dinitrogen Fixation and Primary Production
Simultaneous dinitrogen fixation rate and dissolved inorganic carbon uptake measurements were carried out in duplicate (two incubation bottles) according to Slawyk et al. . For each analysis, a 1-cm2 piece of mat was placed inside a 175-ml polycarbonate bottle fitted with a septum. In each bottle, 13C-labeled sodium bicarbonate (NaH13CO3: 6 g 250 ml−1 deionized water, 99.9 atomic% 13C; Eurisotop) was added in order to obtain 11.5% final enrichment. Subsequently, 0.36 mL of 15N2 (99.8 atom %, Shoko Co. Ltd., Tokyo, Japan) was added with a gas-tight syringe to obtain an enrichment of 6.8%. Incubations were terminated by filtration under gentle pressure through a precombusted 47-mm diameter GF/F filter. The total wet weight of the incubated material was determined. An aliquot was dried at 60 °C for particulate organic carbon (POC), particulate organic nitrogen (PON), and isotope analysis, and another aliquot was frozen for HPLC analysis. Before analysis, filters were exposed to HCl fumes for 4 h. Measurements of delta 13C, delta 15N, and POC, PON were done using a mass spectrometer DELTA plus Advantage (Thermofinigan Co.) equipped with EA1110 for measurements of POC and PON. Primary production was calculated according to Hama et al.  using a time 0 enrichment of 1.089 and an initial DIC concentration of 2,400 μM. Dinitrogen fixation rate was calculated by isotope mass balance as described in Montoya et al.  using an N2 initial concentration of 386.16 µmoles L−1 calculated for a temperature of 24 °C (laboratory temperature) and a salinity of 35 psu, assuming equilibrium with the overlying atmosphere.
Chlorophyll (Chl a) analyses were performed by spectrophotometry for La Reunion 2007 samples and by HPLC for La Reunion 2004 and Sesoko samples. Chlorophyll for spectrophotometric analysis was extracted in 10 ml of 100% methanol, and absorption at 665 nm was recorded before and after acidification. Chl a concentration was calculated using the extinction coefficients given by Porra et al. .
For HPLC analysis, the pigments were extracted with 95% ethanol. HPLC was carried out with a model LC-10ATVP (Shimadzu, Kyoto, Japan) equipped with a column-temperature controller CTO-10ASVP (Shimadzu) using Waters Symmetry C8 column (150 × 4.6 mm; Waters, Milford, Massachusetts). Pigments were eluted at a flow rate of 1.0 mL/min at 25 °C with a programmed binary gradient elution system. The solvents used were methanol–acetonytryl–water (50:25:25) containing 62.5 mM pyridine (solvent A) and methanol–acetonytryl–acetone (20:60:20; solvent B). Separation was performed with a gradient of ratio (A:B, v/v) containing the break points of 0 min (100:0, v/v), 22 min (60:40), 28 min (5:95), 38 min (5:95), and 41 min (100:0). Separated pigments were detected spectrophotometrically with a photodiode array detector (Shimadzu SPD-M10AVP) measuring from 400 to 760 nm. In this paper, we present only chlorophyll a data.
The Environments Compared
Temperature, salinity, mean ± SE of light energy received between 11:00 and 16:00 at the incubation depth, and nutrient concentrations in La Reunion and Sesoko
Reunion, Nov. 2004
1928 ± 854
Reunion, Feb. 2007
1696 ± 724
Sesoko, Jul. 2005
2104 ± 497
Sesoko, St B, Oct. 2006
1816 ± 598
Sesoko, St D, Oct. 2006
1442 ± 392
At both sites, benthic cyanobacteria occurred as scattered colonies which formed different types of organo–sedimentary structures on the lagoon floor. These structures differed in appearance and species composition. The species composition analyzed by light microscopy was correlated with the macroscopic appearance of the mat. The most common unicyanobacterial structures occurred as green mats, green tufts, dark colored mats, and globular orange-colored colonies. These were collected, analyzed, and used for determination of carbon and N2 fixation activities.
Percent of coverage ± SE of cyanobacteria mats in La Reunion in February 2007
Anabaena sp. LC1
0.07 ± 0.04
Leptolyngbya sp. LC2
3.09 ± 1.30
H. majus RU2007
0.01 ± 0.01
O. bonnemaisonii LC4
1.50 ± 0.42
Anabaena sp.-LC1 is the closest morphotypic identity of this common heterocystous benthic cyanobacterium that forms bright blue–green colonies with upright oriented filaments waving in the current (Fig. 3a). Its trichomes were comprised of torulose cells 7.65 ± 0.37-μm wide, slightly shorter or longer than wide; heterocysts were slightly larger and longer then vegetative cells (Fig. 3b). The 16S rRNA gene sequence (accession no. GQ251521) similarity to GenBank listings of Anabaena sp. SSM-00 and Anabaena sp. LMECYA 185 show 98% and 96%, respectively (Fig. 5). The organism was present at low density in several transects in the lagoon of La Reunion in November, 2004, and February, 2007, close to the inner reef flat. Anabaena sp. was observed in Sesoko in July, 2005 at the station B but not in October, 2006.
S. hydnoides Kützing ex Gomont formed characteristic dark brown cusp-shaped colonies (Fig. 3c) comprised of bundled, sheathed filaments externally, often in a leaf-like arrangement. Trichomes were 7.14 ± 1.32-μm wide, not constricted at the cross walls but with slight constriction toward the tips. Apical cells were rounded without calyptra (Fig. 3d). Sheaths were firm, birefringent in polarized light with periodic convex closures (Fig. 3d, insert). The 16S rRNA gene sequence (accession no. GQ251525) matched with a 94% similarity with GenBank listings of Symploca PCC8002 and S. hydnoides TK22 population described at Tikehau Lagoon  (Fig. 5). The colonies of S. hydnoides were observed in La Reunion lagoon attached to Acropora close to the inner reef flat in 2004 and in 2007 as well as in Sesoko at station B in July, 2005.
Oscillatoria bonnemaisonii Crouan ex Gomont identified large unsheathed cyanobacteria forming loose olive–green mats, which dominated the floor of the La Reunion lagoon in February, 2007 (Fig. 3e). Trichomes were unsheathed, motile, and flexuous with tendency of forming lose helical undulations (Fig. 3f). Cells were slightly constricted at the cross walls, 32.8 ± 2.28-μm wide, and very short (3–6 μm). The 16S rRNA gene sequence (accession no. GQ251524) matched the GenBank sequences listed as Oscillatoria spongeliae isolate 513bg and Oscillatoria corallinae with similarities of 96% and 95%, respectively (Fig. 5). The organism was observed only during one occasion in La Reunion but then as a dominant cyanobacterium that covered 1.5 ± 0.4% of the seafloor along the measured transect.
H. majus Holden formed distinct bush-like colonies blue to violet in color, comprised of upward diverging filaments (Fig. 4a). Filaments contained one to three trichomes surrounded by a thick, layered, and colorless sheath. Trichomes were straight and rigid, 29.05 ± 1.25-μm wide, cells 5.84 ± 1.43 long, not constricted at the crosswalls, abruptly narrowing at the tips, and ending with a distinct apical cell covered with calyptra (Fig. 4b). Cells were dark purple in color due to high concentrations of phycocyanin and phycoerythrin. The 16S rRNA gene sequence (accession no. GQ251521) showed closest similarity at 96% to a sequence listed in GenBank as Hydrocoleum lyngbyaceum HBC7 (Fig. 5). Colonies of H. majus RU2007 were observed sporadically on Acropora in La Reunion in February 2007 as well as a minor component in H. coccineum mats of Sesoko.
Other Hydrocoleum morphotypes corresponding to species H. coccineum Gomont, H. glutinosum Gomont, and H. lyngbyaceum Kützing were observed in 2006 in Sesoko, station B, forming brown-colored mats. The mats covering large areas of the sandy bottom at station C at 2-m depth in July, 2005, were dominated by H. coccineum. They occurred intermixed with small (4-µm wide) representatives of the genus Oscillatoria and Leptolyngbya. H. glutinosum was present at the same time only on the outer rim of the reef, close to station B at 6-m depth. The sequences of these organisms were not obtained.
Phormidium laysanense Lemmermann formed colonies of varying shape and consistency, from loose veils to upright extending coatings, bright red to pink in color (Fig. 4c). Filaments contained single trichomes within a thin, firm sheath. Cells were 5.8 ± 0.44-μm wide and 7.83 ± 1.72-μm long. End cell gradually attenuated covered at the tip by a conical or hemispherical calyptra (Fig. 4d). P. laysanense was observed in Sesoko at station D in 2005 and 2006, at shallow depths (2–5 m) inside caves of reef pinnacles.
Leptolyngbya spp. represents nonheterocystous cyanobacteria with narrow trichomes, which formed coatings over sand and massive corals (Fig. 4e). The trichomes were sheathed, comprised of cells 1–1.5-μm wide, slightly shorter or longer than wide and with distinct cross walls, frequently gliding and abandoning the sheaths (Fig. 4f). Two populations from La Reunion that have been sequenced (accession nos. Gq251522 and GQ251523) cluster closely together (Fig. 5) but had different pigmentation. In La Reunion, in February, 2007, these mats were the second-most common mat formations (next to O. bonnemaisonii). Along the measured transect in station A, Leptolyngbya mats covered on the average 3.1 ± 1.3% of the sediment. In the parts of transect between 30 and 80 m from the beach, they covered 5% to 10%. At the end of the day, the mats become partially uplifted by the bubbles of oxygen they produced. Other mat-forming cyanobacteria were observed as minor constituents of benthos. Flat, brown–red mats consisting of Trichocoleus tenerrimus were found in 2005 and 2006 at low densities at stations B and D.
Mean ± SE of acetylene reduction rate during night and daylight and dinitrogen fixation calculated from ARR and the ratio C2H2:N2 = 4
0.45 ± 0.05
11.33 ± 1.17
142.7 ± 16.1
1.9 ± 0.4
34.4 ± 3.9
35.7 ± 4.0
2.70 ± 0.19
1.62 ± 0.14
50.8 ± 5.8
7.4 ± 0.5
5.3 ± 0.4
12.7 ± 0.8
1.15 ± 0.21
3.2 ± 0.6
1.07 ± 0.24
1.64 ± 0.47
34.9 ± 8.0
2.6 ± 0.7
5.3 ± 1.5
8.7 ± 2.0
32.29 ± 4.24
324.1 ± 69.2
13.2 ± 6.1
96.9 ± 12.0
101.0 ± 17.3
5.99 ± 3.36
0.18 ± 0.20
97.9 ± 107.0
24.5 ± 26.7
24.5 ± 26.7
12.48 ± 4.80
306.8 ± 130.3
76.7 ± 32.6
76.7 ± 32.6
14.54 ± 3.09
0.06 ± 0.03
216.6 ± 65.0
35.7 ± 10.7
0.2 ± 0.1
54.2 ± 16.2
6.8 ± 0.8
7.53 ± 0.12
171.1 ± 18.4
20.4 ± 4.8
22.6 ± 0.7
42.8 ± 4.6
1.24 ± 0.11
0.98 ± 0.14
26.7 ± 1.6
3.71 ± 0.98
2.94 ± 1.27
6.7 ± 0.4
2.12 ± 0.75
2.18 ± 1.06
6.37 ± 2.08
6.54 ± 1.05
12.9 ± 6.8
In both sites, Anabaena sp.-LC1 reduced C2H2 mainly during the daytime. In La Reunion the mean ARR value was 11.3 ± 1.2 nmoles C2H2 µg−1 Chl a h−1 during the day and 0.45 ± 0.05 nmoles C2H2 µg−1 Chl a h−1 during the night. In Sesoko Island, Anabaena sp. reduced C2H2 with a mean ARR value of 32.3 ± 4.2 nmoles µg−1 Chl a h−1 during the daytime and between 0 and 8 nmoles C2H2 µg−1 Chl a h−1 (ten times lower but variable) during the night.
In contrast to heterocystous cyanobacteria, the mats dominated by Hydrocoleum glutinosum and H. coccineum, analyzed in Sesoko, showed nitrogenase activity only during the night. Their mean ARR were 14.5 ± 3.1 and 12.5 ± 4.8 nmoles µg−1 Chl a h−1, respectively. Mats dominated by H. lyngbyaceum showed in Sesoko, nitrogenase activity both during the night and during the day after. In La Reunion, H. majus mat was measured only one time at night and showed very low activity: 1.07 ± 0.24 nmoles C2H2 µg−1 Chl a h−1.
Mats dominated by nonheterocystous Leptolyngbya spp. (LC2, LC3), O. bonnemaisonii (LC4), and S. hydnoides (LC5) in La Reunion showed nitrogenase activity both during the night and the daylight time. Their mean night ARR were 2.70 ± 0.19, 1.15 ± 0.21, and 0.48 nmoles C2H2 µg−1 Chl a h−1, respectively. Their mean daylight ARR were 1.62 ± 0.14 for Leptolyngbya sp., 1.64 ± 0.47 for O. bonnemaisonii, and 0.48 nmoles C2H2 µg−1 Chl a h−1 for S. hydnoides.
In Sesoko, P. laysanense, and T. tenerrimus showed nitrogenase activity during the night and the daytime. Their mean night ARR were 6.8 ± 0.8, 1.24 ± 0.11, and 2.12 ± 0.75 nmoles µg−1 Chl a h−1, respectively. Their mean daylight ARR was 7.53 ± 0.12, 0.98 ± 0.14, and 2.1 8 ± 1.06 nmoles µg−1 Chl a h−1, respectively. S. hydnoides did not show nitrogenase activity.
Daily gross N2 fixation rates (Table 3), calculated using a theoretical value of four as discussed in Charpy et al. , showed the highest N2 fixation rates of 101 ± 17 nmoles N2 µg−1 Chl day−1 for Anabaena sp. of Sesoko. The rates for the same species in La Reunion were significantly lower: 36 ± 4 nmoles N2 µg−1 Chl day−1. In Sesoko, H. coccineum, and Hydrocoleum glutinosum daily N2 fixation rates were high, 77 ± 33 and 54 ± 16 nmoles, N2 µg−1 Chl day−1, respectively.
Isotopic Measurements of N2 Fixation and Primary Production
Mean ± SE of dinitrogen fixation calculated from 15N experiments during the night and 24 h, 24 h primary production, C:N ratio of mats, and the contribution of NF to the total N requirement for PP
Anabaena sp. LC1
3,291 ± 630
7.4 ± 0.2
S. hydnoides LC5
8.2 ± 4.1
10.0 ± 4.3
1,321 ± 431
11.3 ± 3.6
Leptolyngbya sp. LC2
8.7 ± 2.6
8.8 ± 2.6
2,709 ± 825
15.3 ± 0.9
8.8 ± 0.3
Benthic Cyanobacteria in Coral Reef Ecosystems
Mats collected in La Reunion and Sesoko represent a variety of cyanobacterial morphotypes that are active in N2 fixation. Populations of cyanobacteria dominated by representatives of the form-genera Anabaena, Oscillatoria, Phormidium, Hydrocoleum, Symploca, and Leptolyngbya were present in both geographically remote ecosystems surveyed in the present study. The following dominant morphospecies occurred in both sites: Anabaena sp., P. laysanense, H. majus, and S. hydnoides.
The heterocystous cyanobacteria form a monophyletic group [9, 21, 26]. However, for the members of this group, especially genera: Anabaena, Nodularia, Aphanizomenon, and Cylindrospermopsis; descriptions of morphotypes are often insufficient to discriminate between them and so are descriptions of strain histories. Genetically closely related strains or strains of similar morphotype often carry different specific or even generic epithets.
The genus Anabaena Bory describes a large number of taxa in freshwater plankton including toxic bloom-forming species. Morphologically similar marine taxa are usually classified under the genus Nodularia [4, 5]. Diversity and ecological features of Anabaena and Nodularia from marine benthic habitats are less well known than those from planktonic habitats . The study of Lyra et al.  showed that benthic cyanobacteria of the genus Nodularia from the Baltic Sea are nontoxic, without gas vacuoles, able to glide and are genetically more diverse than planktonic Nodularia. Marine Anabaena strains have already been reported from the Mexican Gulf coast of Texas as fast-growing N-fixing organisms well adapted to warm shallow marine environments [35, 45].
The 16S rRNA gene sequence of Anabaena sp.-LC1 identified morphologically in samples from La Reunion shows similarity to other heterocystous cyanobacteria, identified as Anabaena (98%) and Cylindrospermopsis raciborskii (95%) but only 94% to Nodularia harveyana. Such low level of similarity indicates that the organisms we encountered on the reef of La Reunion were not yet represented in GenBank.
O. bonnemaisonii is a large, well-characterized filamentous cyanobacterium reported from marine habitats worldwide . However, the closest match with published sequences identifies a relation to a listing under the name O. spongeliae. The basis for the listing identification is not known; however, the original description of that morphotype, Oscillatoria spongeliae Schulze 1879, is different from our strain and not even typical for the form-genus Oscillatoria. That taxon has been classified by different authors as Phormidium and Borzia, in addition to Oscillatoria .
H. majus, the largest in the genus, was observed in mats at La Reunion, as dominant species, and at Sesoko, as subdominant. In the latter case, mats were dominated by H. coccineum, H. glutinosum and H. lyngbyaceum. Species of Hydrocoleum (Blennothrix in Komárek and Anagnostidis ) were reported to be very abundant in Tikehau Atoll lagoon , Kabira reef sediments, Ishigaki Island, SW Japan , and in the SW lagoon of New Caledonia . They are considered to be among the most common mat-forming cyanobacteria in tropical oceans with the genetic potential to fix N2, closely related to the species of the planktonic genus Trichodesmium .
Leptolyngbya sp. was the most abundant cyanobacterium at La Reunion in February 2007, covering 3.1 ± 1.3% of transect over sandy bottom. However, the morphogenus Leptolyngbya is polyphyletic and includes a number of unrelated organisms of simple morphology .
The acetylene reduction method does not measure N2 fixation rates directly; it needs to be calibrated by calculating the C2H2:N2 ratio (mol:mol). Multiple studies have shown the conversion ratio of ethylene to N to be highly variable. In coral reef ecosystems, values for benthic mats range from 1.8 to 4.8 in Tuamotu Atoll lagoon  and from 0.3 to 4.7 in Kabira reef . In Sesoko and La Reunion, the ratio ranged between 1.1 and 5.8 with an average of 3.3. This value was close to the conversion ratio of 4:1 appropriate for quantification of gross N2 fixation as measured by C2H2 reduction [19, 27, 36].
Paerl et al.  observed a decrease in N2 fixation after an enrichment of 100 µM NO3. This enrichment is 60, the maximum DIN observed in La Reunion waters. Joye and Lee  observed a substantial (80%) and instantaneous reduction in N2 fixation rates after the addition of inorganic nitrogen (2 mM NO3). However, these authors reported that in some cases, the addition of inorganic nitrogen had no effect on N2 fixation. The enrichment used here is 1,000 times the maximum DIN concentration in overlying waters. Camacho and de Wit  observed that a 400 µM NH4NO3 addition had no direct effect onto N2 fixation rate. All these enrichments are largely higher than DIN concentrations in La Reunion and Sesoko waters.
Dinitrogen fixation in oligotrophic waters of La Reunion in 2004 was observed to continue when the surrounding waters contained 1.71 µM nitrate concentration. It is possible that, in such cases, the availability of dissolved nitrogen in the microenvironment immediately surrounding the microorganism was exhausted and its replacement rate deficient. Thus, the concentration of a nutrient measured in the macroenvironment does not necessarily correspond to its availability to the microorganisms.
Dark N2 fixation by heterocystous cyanobacteria and light N2 fixation by nonheterocystous cyanobacteria are frequently reported in the literature. Gallon et al.  observed that the planktonic heterocystous Nodularia can fix N2 during the night. They consider that cells can sustain N2 fixation, at least to a limited extent, by metabolic processes that operate in the dark. The nonheterocystous cyanobacterium, Symploca PCC 8002, is capable of fixing N2 aerobically in light. The synthesis of nitrogenase takes place in a minor proportion of consecutively arranged cells .
Comparison of acetylene reduction rates in coral reef environments
Mats (dominant cyanobacteria)
ARR (nmol C2H2 µg−1 Chl a d−1)
205 ± 12
Charpy et al. 
324 ± 69
143 ± 16
123 ± 25
Charpy et al. 
171 ± 18
Kayanne et al. 
New Caledonia (St. MBO)
122 ± 20
Charpy et al. 
307 ± 130
Dinitrogen Fixation as an Input to the Primary Production in Microbial Mats
To estimate the contribution of dinitrogen fixation to the total nitrogen requirement for the primary production (PP) of four mats, we used the value of PP and C:N ratio from the Table 4. Based on these values, N2 fixation represents between 5% (Leptolyngbya sp.) to 21% (H. coccineum) of that required for primary production. This contribution is close to the percentage (19%) given by Charpy et al.  for sediment of New Caledonia lagoon and nearly ten times higher than the percentage (2%) given by Charpy-Roubaud et al.  for Tikehau atoll lagoon.
Lagoonal Dinitrogen Fixation
The whole lagoonal mat N2 fixation could be estimated only for La Reunion in February 2007, when we had a good estimation of the mat coverage. Using the lagoon bottom percent coverage of the mats and the dinitrogen fixation rate per square centimeter2 of mats, we obtained a mat N2 fixation of 2.16 mg N2 fixed per square meter of lagoon. This value is inside the large range of dinitrogen fixation rates reported by Charpy-Roubaud et al.  for various coral reef ecosystems.
Dinitrogen fixation measurements of microbial mats combined with polyphasic studies of cyanobacterial diversity proved advantageous by achieving identification of the principal phototrophic contributors of benthic diazotrophy. The heterocystous genus Anabaena and the non-heterocystous genus Hydrocoleum appear to be important benthic dinitrogen fixers in the two investigated coral reef ecosystems. Their N2 fixation rates are in the same order of magnitude and both heterocystous and nonheterocystous cyanobacteria are capable of light and dark N2 fixation.
Mat diversity and their role in N2 fixation in the two geographically distant ecosystems under study appear to be similar. Mats in both ecosystems were also comparable in sea water characteristics, such as light, temperature, salinity and nutrients.
The results suggest global importance of benthic cyanobacterial dinitrogen fixation and call for further investigations of microbial mats in coral reef ecosystems. Our approach in identifying natural populations involved in dinitrogen fixation are required to assess the contribution of benthic cyanobacteria to dinitrogen fixation in relation to their distribution and biodiversity.
This work was supported by grants from the Ocean Development Sub-Committee of France–Japan S&T Cooperation, Mitsubishi cooperation, the Ministry of Education, Science, Sport, and Culture of Japan and from IRD. Hanse Wissenschaftskolleg, Delmenhorst and Alexander-von-Humboldt Foundation, Bad Godesberg, Germany supported collaborative research on cyanobacterial diversity. We thank A. Couté for his help in Sesoko cyanobacteria identification, the laboratory ECOMAR from the University of La Reunion, and the Sesoko Marine Station for their help in the field. We wish also to thank Tatjana Schwetzler for the help in molecular analysis.
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