- Open Access
Microbial community composition of Tirez lagoon (Spain), a highly sulfated athalassohaline environment
© Montoya et al.; licensee BioMed Central Ltd. 2013
- Received: 31 May 2012
- Accepted: 24 September 2013
- Published: 2 October 2013
The aim was to study the seasonal microbial diversity variations of an athalassohaline environment with a high concentration of sulfates in Tirez lagoon (La Mancha, Spain). Despite the interest in these types of environments there is scarce information about their microbial ecology, especially on their anoxic sediments.
We report the seasonal microbial diversity of the water column and the sediments of a highly sulfated lagoon using both molecular and conventional microbiological methods. Algae and Cyanobacteria were the main photosynthetic primary producers detected in the ecosystem in the rainy season. Also dinoflagelates and filamentous fungi were identified in the brines. The highest phylotype abundance in water and sediments corresponded to members of the bacterial phylum Proteobacteria, mainly of the Gamma- and Alphaproteobacteria classes. Firmicutes and Actinobacteria were isolated and identified in Tirez brines and sediment samples. Halophilic sulfate reducing Deltaproteobacteria were also detected (Desulfohalobium).
Important differences have been found in the microbial diversity present in the Tirez water column and the sediments between the wet and dry seasons. Also the Tirez lagoon showed a high richness of the bacterial Alpha- and Deltaproteobacteria, Bacteroidetes, Firmicutes, Actinobacteria and for the archaeal Euryarchaeota.
- Rainy Season
- Clone Library
- High Ionic Strength
- Hypersaline Environment
- DGGE Band
Identifying the limits of life is a major question in microbial ecology. The current exploration of life on Earth has led to the discovery of living systems in environments that were considered inhabitable only few years ago. Thus over the past several years, knowledge of the microbial diversity and ecology of extreme environments has become a vital tool both to answer fundamental questions regarding life’s adaptation to extreme conditions and also to explore the biotechnological potential of extremophiles.
The purpose of the present study was to generate a broad overview of the biodiversity present in the different phases of Tirez lagoon, a sulfated athalassohaline environment, and their seasonal variation. Therefore, the communities dominating the sediment and water phases in the wet and dry seasons were analyzed by performing a combination of microscopy observation, culture-dependent and -independent techniques.
Physico-chemical parameters of water column and sediments in Tirez lagoon
Salinity (%) (water)
Eh (mV) (water)
Eh (mV) (sediment)
Temperature (°C) (water)
Oxygen (μM) (sediment)
Prefix of isolates, bands and clones (water)
Prefix of isolates, bands and clones (sediment)
Enumeration of cells in water and sediment
The total DAPI cell count in the water column from the rainy season was 2.6×108 ± 0.8x108 cells/ml. At high ionic strength cell numbers dropped one order of magnitude. In the sediments the maximum cell counts were detected at a depth of 10 cm and corresponded to 4×107 ± 0.4×107 cells/g of wet sediment. At deeper zones cell numbers decreased drastically reaching values of 8×103 ± 0.8x103 cells/g of wet sediment.
Microscopy observation of water samples
Microorganisms present in Tirez lagoon water column and sediments identified by microscopic observation, clone-sequencing, DGGE band-sequencing and sequencing of culture isolates
ID (Access no.) a
Closest relative b
No. of occurrences c
Uncultured actinobacterium clone TDNP_LSbc97_3_28_94 (FJ516859). Semiarid wetland (Central Spain) [97%]
Microbacteriaceae [100%], Cryobacterium [57%]
Uncultured organism clone SBYG_2070 (JN450257). Guerrero Negro hypersaline microbial mat [99%]
Actinomycetales [100%], Microbacteriaceae [97%], Schumannella [28%]
Arthrobacter phenanthrenivorans strain Sphe3 (NR_074770) [97%]
Micrococcaceae [100%], Arthrobacter [49%]
Uncultured marine bacterium clone BM1-F-27 (FJ826125). Yellow Sea [97%]
Flavobacteriales [100%], Flavobacteriaceae [97%]
Uncultured bacterium clone BJGMM-1s-364 (JQ800813). Soil samples from the Yellow River DeltaYellow River [98%]
Flavobacteriaceae [100%], Gillisia [99%]
Uncultured bacterium clone a43 (HM468007). Wastewater treated with with ferrous salt [99%]
Sphingobacteriales [100%], Cyclobacteriaceae [81%], Nitritalea [81%]
Muricauda flavescens strain SW-62 (NR_042908). Salt lake, Korea [82%]
Bacteria [100%], Bacteroidetes [87%]
Uncultured organism clone MAT-CR-P2-E05 (EU246052). Hypersaline microbial mat [96%]
Marinilabiaceae [100%], Anaerophaga [99%]
Uncultured bacterium clone 184-32 (GU212609). Saline soil samples Qaidam Basim, China [97%]
Marinilabiaceae [100%], Anaerophaga [66%]
Uncultured Bacteroidetes bacterium clone CF07-19 (FJ844036). High mountain lake, China [93%]
Flavobacteriaceae [100%], Psychroflexus [55%]
Psychroflexus sediminis strain YIM C238 (NR_044410). Haloalkaline soil [98%]
Flavobacteriaceae [100%], Psychroflexus [100%]
Psychroflexus sediminis strain YIM C238 (NR_044410). Haloalkaline soil [98%]
Flavobacteriaceae [100%], Psychroflexus [100%]
Uncultured Salegentibacter sp. clone HAHS13.025 (HQ397000). Haloalkaline soil [98%]
Flavobacteriaceae [100%], Salinimicrobium [95%]
Psychroflexus sediminis strain YIM C238 (NR_044410). Haloalkaline soil [98%]
Flavobacteriaceae [100%], Psychroflexus [100%]
Uncultured bacterium clone MBFOS-06 (EU369165). Oyster shell [95%]
Flavobacteriaceae [100%], Salinimicrobium [99%]
Sphingobacteria bacterium clone A1503 (EU283512). Anderson lake [95%]
Bacteroidetes [100%], Flavobacteria [50%]
Uncultured bacterium clone H0014 (JX391054). Marine sediment [90%]
Firmicutes [99%], Bacilli [93%], Bacillales [81%]
Uncultured bacterium clone B-2 (HQ703872). Qinghai lake sediment [98%]
Bacteria [100%], Firmicutes [92%], Bacilli [65%]
Uncultured bacterium clone Kasin-B2-B05 (HE604654). Hypersaline sediments [99%]
Sporolactobacillaceae [100%], Sporolactobacillaceae incertae sedis [100%]
Bacillus sp. DHC09 (JQ904720). Sea surface sediment [97%]
Bacillales [100%], Bacillaceae 1 [80%], Falsibacillus [71%]
Paenibacillus sp. 5-3 (HQ832503) Food waste [92%]
Bacilli [97%], Bacillales [97%], Paenibacillaceae 1 [80%]
Paenibacillus sp. ITCr59 (FR823415). Agricultural soil [97%]
Paenibacillaceae 1 [100%], Fontibacillus [95%]
Uncultured bacterium clone H3034 (JX391174). Marine sediment [98%]
Clostridiales [100%], Clostridiaceae 3 [99%], Sporosalibacterium [96%]
Uncultured Rhodobacteraceae clone DS127 (DQ234210). River estuary [98%]
Rhodobacteraceae [100%], Roseovarius [86%]
Roseobacter sp. B11 (DQ659411) [99%]
Rhodobacteraceae [100%], Seohaeicola [98%]
Loktanella vestfoldensis strain R-9477 (NR_029021) [98%]
Rhodobacteraceae [100%], Loktanella [100%]
Uncultured Idiomarina sp. clone XJ120 (EF648161). Aerobic activated sludge [94%]
Idiomarinaceae [100%], Pseudidiomarina [99%]
Pseudidiomarina sp. YCSA4 (GQ246209). Water of a salt field [93%]
Idiomarinaceae [100%], Pseudidiomarina [100%]
Pseudidiomarina homiensis strain CT34 (HM854277) [99%]
Idiomarinaceae [100%], Idiomarina [81%]
Uncultured proteobacterium clone TY4SP11r (JQ218797). Marine macro-alga [95%]
Idiomarinaceae [100%], Pseudidiomarina [98%]
Pseudidiomarina sp. 2PR54-15 (EU440967) [96%]
Idiomarinaceae [100%], Idiomarina [92%]
Uncultured gamma proteobacterium clone XJ85 (EF648142). Aerobic activated sludge [98%]
Idiomarinaceae [100%], Pseudidiomarina [59%]
Marinobacter adhaerens strain S20-1 (KC420687) [100%]
Alteromonadaceae [100%], Marinobacter [100%]
Uncultured bacterium clone SN18 (JQ824910). Saline and alkaline soil [97%]
Gammaproteobacteria [99%], Alteromonadales [52%], Alteromonadaceae [52%]
Uncultured bacterium clone SN26 (JQ824918). Saline and alkaline soil [98%]
Piscirickettsiaceae [100%], Methylophaga [100%]
Uncultured bacterium clone SINP962 (HM127832). Qinghai lake [91%]
Bacteria [100%], Proteobacteria [61%], Gammaproteobacteria [61%]
Uncultured bacterium clone Lupin-1130m-2-pse1 (EF200114). Subpermafrost fracture waters in Artic [94%]
Proteobacteria [99%], Gammaproteobacteria [98%], Oceanospirillales [47%]
Pseudoalteromonas sp. TA010_3 (EU308473). Solar saltern [98%]
Pseudoalteromonadaceae [100%], Pseudoalteromonas [100%]
Halomonas sp. HL33 (KC705271). Hot lake hypersaline margin soil [95%]
Halomonadaceae [100%], Cobetia [41%]
Uncultured Halomonas sp. clone BPS_CK65 (HQ857613). Hydrocarbon contaminated saline [98%]
Halomonadaceae [100%], Halomonas [98%]
Halomonas sediminis strain YIM C248 (EU135707) [98%]
Halomonadaceae [100%], Halomonas [83%]
Uncultured bacterium clone 100307_0m_01F (KC358335). Low salinity soda lake [95%]
Piscirickettsiaceae [100%], Thioalkalimicrobium [94%]
Uncultured bacterium clone E6bG07 (DQ103666). Hypersaline endoevaporitic microbial mat [96%]
Desulfohalobiaceae [100%], Desulfohalobium [82%]
Nostoc sp. (*)
Anabaena sp. (*)
Pseudoanabaena sp. (*)
Nodularia sp. (*)
Leptolyngbya sp. LEGE 07084 (HM217072). Temperate estuary [98%]
Cyanobacteria [100%], Family IV [100%], GpIV [100%]
Uncultured organism clone SBXY_5108 (JN429822). Hypersaline microbial mat [99%]
Cyanobacteria [100%], Family XIII [78%], GpXIII [78%]
Uncultured haloarchaeon clone XKL10 (JN714413). Saline lake [99%]
Halobacteriaceae [100%], Halobacterium [46%]
Uncultured haloarchaeon clone XKL44 (JN714440). Saline lake [98%]
Halobacteriaceae [100%], Halolamina [100%]
Uncultured haloarchaeon clone XKL11 (JN714414). Saline lake [96%]
Halobacteriaceae [100%], Halococcus [99%]
Uncultured haloarchaeon clone XKL23 (JN714423). Saline lake [96%]
Halobacteriaceae [100%], Halomicrobium [88%]
Halobacteriaceae archaeon EA3 (HQ197981). Salt lake brine [99%]
Halobacteriaceae [100%], Halolamina [100%]
Halobacteriaceae archaeon R30 (HM159607). Salted kelp [97%]
Halobacteriaceae [100%], Halonotius [97%]
Uncultured Halobacterium sp. clone 7A23 (AY987826). Maras salterns [99%]
Halobacteriaceae [100%], Halobacterium [100%]
Halobacterium sp. AUS-2 (D32082) [97%]
Halobacteriaceae [100%], Halorubrum [100%]
Uncultured euryarchaeote clone DSFBPENV12arc_7C (KC465576). Brine pool water [99%]
Halobacteriaceae [100%], Halobacterium [66%]
Uncultured archaeon clone Kasin-A3-B06 (HE604580). Exposed salt lake sediment [99%]
Halobacteriaceae [100%], Salarchaeum [56%]
Uncultured haloarchaeon clone TX4CA_35 (EF690590). Alkaline-saline soil [94%]
Halobacteriaceae [100%], Halococcus [69%]
Halorubrum kocurii (AB576124) [99%]
Halobacteriaceae [100%], Halorubrum [100%]
Halorubrum xinjiangense strain BD-1 (NR_028205) [99%]
Halobacteriaceae [100%], Halorubrum [100%]
Uncultured euryarchaeote clone SFH1E051 (FN391283). Solar saltern sediment [99%]
Halobacteriaceae [100%], Halorhabdus [43%]
Uncultured haloarchaeon clone XKL48 (JN714443). Saline lake [99%]
Halobacteriaceae [100%], Natronomonas [100%]
Uncultured haloarchaeon clone XKL48 (JN714443). Saline lake [99%]
Halobacteriaceae [100%], Natronomonas [100%]
Natronobacterium sp. isolate 2-24-8 (AJ878084) [97%]
Halobacteriaceae [100%], Natronomonas [100%]
Halomicrobium katesii (JN120802) [99%]
Halobacteriaceae [100%], Halomicrobium [100%]
Haloarcula sp. AB19 (DQ471854) [99%]
Halobacteriaceae [100%], Haloarcula [100%]
Halophilic archaeon strain BNERC31 (AB766180). Solar saltern [96%]
Halobacteriaceae [100%], Haloarcula [100%]
Uncultured archaeon clone 11 (GQ452803). Hypersaline methane seep in canadian high Artic [97%]
Archaeoglobales [98%], Archaeoglobaceae [98%], Archaeoglobus [63%]
Candidate division MSBL1
Uncultured euryarchaeote clone Discovery_a (HQ530525). Hydrothermal brine system in the Red Sea [93%]
Euryarchaeota [96%], Archaeoglobi [49%], Archaeoglobales [49%]
Nitzschia communis strain FDCC L408 (AJ867278) [99%]
Hexarthra sp. (*)
Artemia sp. (*)
Dunaliella sp. (*)
Woloszynskia cincta strain MALINA FT56.6 PG8 (JN934667) [98%]
Aspergillus sp. (*)
Isolation from enrichment cultures
A 5 mm thick granular green biofilm with a grey texture covering the sediments in the rainy season was inoculated in specific cyanobacterial growth media. One isolate, Rw_ie_diat (Bacillariophyta) had 99% 16S rRNA gene sequence similarity with the chloroplast from the diatom Nitszchia communis (Table 2). Nitszchia species are frequently found in hypersaline systems  whereas two other isolates, Rw_ib_C and Rw_ib_D, showed 97% similarity with Leptolyngbya sp. (Table 2). Only one heterotrophic bacterium (Dw_ib_7) could be isolated at high ionic strength and was identified as a Pseudoalteromonas sp.
An eukaryote identified in the water column at low ionic strength was found to have a 97% identity with the dinoflagellate Woloszynskia cincta of the Dinophyceae. W. cincta has only been detected in marine and freshwater systems .
During the dry season cracking of the salt crust was rare; therefore, sediments kept humidity and the oxygen profile did not show signs of ventilation. Different colonies were obtained inoculating sediment samples from different depths using enrichment media for heterotrophic microorganisms. The analysis of the 16S rRNA gene sequence of isolated colonies from the rainy season revealed that Paenibacillus sp. from the Firmicutes and Arthrobacter phenanthrenivorans from the Actinobacteria (Table 2) were present in the sediment.
The bacterial isolates from the dry season sediments were identified as members of the Gammaproteobacteria, with the exception of isolate Ds_ib_4 (Falsibacillus sp. in Firmicutes). The rest of the isolates were identified as members of the genus Idiomarina, Pseudoidimarina, Halomonas, Marinobacter. Despite the fact that sediment samples were inoculated on plates with haloarchaeal media and some colonies showed the presence of characteristic pigments, none of them could be isolated in further purification steps probably due to the media composition (low concentration of sulfate) or probably because the temperature of incubation was far from the optimal.
A fungus was isolated in potato-dextrose-agar (PDA) plates inoculated with a sediment sample from the dry season and was identified as a member of the genus Aspergillus.
Analysis of uncultivated microbes
16S rRNA gene cloning from water samples
Also, four clones retrieved from the low salinity water column were affiliated with Bacteroidetes (genus Psychroflexus and uncultured bacterium clones) and Actinobacteria phyla (uncultured actinobacterium clone).
Although DNA was successfully extracted from water samples with low salinity, attempts to obtain amplified products with archaeal primers were unsuccessful. This suggests that there were undetectable levels of halophilic archaea in these conditions, probably due to their low tolerance to low salinity concentrations .
DGGE analysis of water samples
Cloning from sediment samples
Samples for cloning from both the dry and the rainy season, were taken at 10 cm because maximum values of biomass (DAPI stain) and metabolic activities (sulfate reduction) were detected at this depth . Fourteen percent of the phylotypes from the rainy season clustered with different Idiomarina and Pseudoidiomarina species from the Gammaproteobacteria (Figure 3, Table 2), representing the most abundant group. The rest of the phylotypes clustered showing higher similarity values with type species sequences of Halomonas and Methylophaga (Gammaproteobacteria). The Bacteroidetes phylum was represented by members of the Anaerophaga-Marinilabilia clade. Flavobacteria was represented by members of the Psychroflexus and Microscilla genera (Figure 3). The bacterial clone library from the dry season sediments yielded members of the Idiomarina, Marinobacter and Halomonas genera within the class Gammaproteobacteria.
Archaeal communities in sediments show higher diversity than water samples. About 40% of archaeal clones from both rainy and dry season sediments showed high similarity with Halobacterium species. Halobacterium species, commonly present in high salinity environments, here were identified by phylogeny with a pp of 100% (Figure 4). The other archaeal phylotypes from the wet season sediments were integrated within Haloarcula, Natronomonas, Halorubrum and Natronobacterium-Halopiger clades. Phylotypes identified as members of the Natronobacterium genus were also detected in sediments from the dry season (Table 2). The clone Rs_ca_41 (EU722682) showed some similarity to an uncultured archaeon clone Discovery_a from an hydrothermal brine system in the Read Sea (HQ530525) (Table 2) and by phylogenetic analysis it fell within the Candidate division MSBL1 clade (Figure 4).
DGGE analysis of sediment samples
Band patterns were obtained from a denaturing gradient of 40-70% for sediments from rainy and dry season (Figure 5). From a total of 15 identified bacterial bands from the rainy season, five phylotypes belonged to the Flavobacteriaceae. Also members of the Bacillaceae were detected. Of the Gammaproteobacteria the frequently observed members of the genus Halomonas, harbouring only halophiles, members of the sulfur oxidizing bacteria Thioalkalimicrobium and the heterotroph Marinobacter were identified. One band was identified by the tool Classifier as a Desulfohalobiaceae member a sulfate reducing halophilic group of the Deltaproteobacteria class (Table 2).
A total of seven bands were obtained from the dry season sediment sample. Their sequences indicated phylotypes closely related with members of the phylum Bacteroidetes (Muricauda flavescens, unidentified Bacteroidetes) and an unidentified Sphingobacteria. Of the Gammaproteobacteria, members of the halophilic genus Halomonas were identified and the band Rs_db_29 was related with the Clostridiaceae.
The circumneutral pH of the Tirez lagoon could be the result of the low concentration of carbonates in relation to the concentration of calcium. The difference in pH between the water column and the sediments is probably due to the difference in the ionic concentrations between both phases. In summer, the relative abundance of the most numerous cations of water was as follows: Na+K>Mg>Ca therefore, a low quantity of CO32- is sequestered by carbonate precipitation, which leads to a slightly alkaline pH (Table 1). On the contrary, in the sediments the bivalent cations dominate precipitating the CO32- and resulting in a neutral pH.
The ratio of Cl- to SO42- underlines the athalassohaline characteristic of the Tirez lagoon. The relationship between chloride and sulfate increases from the rainy to the dry season as a consequence of the sequestration of sulfate in different salts (i.e. epsomite, mirabilite, thenardite, hexahydrite and bloedite) that precipitate before halite does.
Methanogens make a living in habitats where electron acceptors such as O2, NO3-, Fe3+, and SO42- are limiting . Under the sulfated conditions prevailing in Tirez methanogens might be excluded. On the other hand, the negative redox potential values detected in the sediments (Table 1), especially in the rainy season, are not low enough to allow methanogenesis to proceed, being necessary a redox potential lower than -330 mV . Such conditions are enough to justify the lack of evidence of methanogenic archaea by 16S rRNA gene sequencing. However, hydrogenotrophic methanogens have been reported in Tirez lagoon .
The negative redox potential values detected in the sediments (Table 1), especially in the rainy season, are not low enough to allow methanogenesis to proceed, being necessary a redox potential lower than -330 mV . This result strongly suggests that measured redox potentials might be a gross estimate of the sediment potentials and that microniches with appropriate physico-chemical conditions must develop in those sediments to facilitate the growth of these strict anaerobic microorganisms.
After comparing the class richness among three domains it was evident that Bacteria was the richest domain given that bacteria classes represented 50% of all classes detected. Proteobacteria was the most common phylum and accounted for the largest OTU fraction (31%) in all the phases analyzed. Thus, in Tirez, members of the Proteobacteria class were the best-represented group of Bacteria in the range of salinities studied, diverging from other characterized athalassohaline systems where the dominant role was played by members of the Bacteroidetes group [15, 32]. Frequently, Salinibacter ruber is recognized as a common and abundant bacterium inhabitant of hypersaline environments, including the athalassohaline lake Chaka . However, this microorganism has not been detected in Tirez lagoon in the different seasons and phases analyzed, which suggests a more complex distribution of this species .
Most of the oxygenic photosynthetic organisms were detected and identified by morphotype analysis. The Chlorophyta and the Cyanobacteria detected are frequently found in hypersaline environments. These microorganisms play an important role in the global carbon and mineral cycles of hypersaline environments . During the dry season, water evaporates promoting massive salt precipitation. However, a thin 3 mm layer of cyanobacteria could be observed between the sediment and the salt crust. Although competition with macrophytes is practically nonexistent at these hypersaline conditions, the cyanobacterial layer becomes thin and ephemeral. One possible explanation proposed by Guerrero and de Wit is that thick cohesive mats are usually associated with permanently covered sediments, in contrast to the thin mats that are temporally submerged, as in our case . Another possible explanation is the Tirez fine sediment granulometry, dominated by particles of ≤0.002 mm, which have been described as the possible cause for the generation of thinner mats .
Though a prevalence of Loktanella vestfoldensis sequences among clone libraries has not been reported in other hypersaline systems, Loktanella sp. has been found in cold saline groundwater springs (Axel Heiberg Island, Canada) rich in sulfate . It is remarkably that the genera Marinobacter and Halomonas have not been reported in other hypersaline systems rich in sulfate.
The presence of Woloszynskia cincta in the wet season seems to be a peculiarity of this environment since there is no report of this species in hypersaline systems. Indeed, there are few reports of dinoflagellates in hypersaline environments . W. sincta is absent at high osmolarity conditions, it is possible to explain its survival until the next season by cyst formation . On the other hand, the algae Dunaliella sp. is present in dry and flooded seasons. It has been shown that Dunaliella tertiolecta growth is inhibited by Mg2+ salts when compared with Na+ salts . This response is of interest because Mg2+ is present in high concentrations in Tirez (Figure 1). However, the proliferation of Dunaliella sp. in Tirez lagoon is not entirely surprising since this genus has been reported in the Dead Sea  under high concentrations of Mg2+. Fuji  argues that the ability of D. tertiolecta to grow in a MgSO4 medium may be related to the high intracellular concentration of SO42-. Therefore, the high sulfate concentration characteristic of Tirez might have positive consequences on Dunaliella sp. growth despite the high concentrations of bivalent cations.
Most ecological studies on hypersaline ecosystems are focused on the aqueous phase. Therefore, the following data about bacteria and archaea present in sediments is remarkable in terms of diversity of halophiles.
Firstly, 16S rRNA gene sequence techniques showed a predominance of Haloarchaea, particularly members of the Halobacteriaceae, which can grow well heterotrophically in the dark . Most of the identified bacteria are described as heterotrophs, with Gammaproteobacteria being the dominant taxa followed by members of the Flavobacteria class.
The thermophilic sulfate reducing Archaea Archaeoglobus was detected in Tirez sediments. Interestingly, there are previous evidences of thermophilic genus (Thermoplasmatales) described in other hypersaline environments [14, 43, 44]. To understand this ecological singularity, a contingent adaptation of thermophilic microorganisms to the high osmolarity conditions founded in Tirez should be considered. Thermophilic microorganisms succeeded in stabilizing intracellular macromolecules by the synthesis and/or accumulation of compatible solutes [45, 46]. This physiological adaptation is an absolute requirement for organisms under osmotic stress . In fact, the synthesis of compatible solutes has been reported in species of Archaeoglobus.
Another interesting case was Desulfohalobium, a halophilic sulfate reducing bacterium that was identified by PCR-DGGE. Although sulfate reducing bacteria have been detected previously in thalassohaline environments , this is the first report of this genus in an athalassohaline sulfate-rich ecosystem.
Microorganisms of the functional groups methanogens, sulfur oxidizers and sulfate reducers have been detected in sediment and by molecular biology techniques and enrichment . Interestingly, methanogenic archaea and sulfur oxidizing bacteria were undetected by PCR-cloning of the gene 16S rRNA. Moreover, the sulfate reducing bacteria here detected by 16S rRNA (Desulfohalobium sp.) does not coincide with those encountered with the functional gene marker Apr, i.e. Desulfonema and Desulfonatronovibrio. This inconsistence between gene markers has been reported previously .
Culture-dependent and –independent techniques were used to examine the microbial diversity of the water column and the sediments in an athalassohaline lagoon, Tirez, from La Mancha (Central Spain). All the phases of the lagoon are inhabited by an abundance of microorganisms, including representatives of the three domains: Eukarya, Bacteria and Archaea.
A difference in community structures was observed between the water column and the sediments. The cyanobacteria occurred mainly in water column. Along with Haloarchaea, members of the Proteobacteria were well represented in both phases. Gammaproteobacteria are the dominant sequences in the sediments. Sulfate reducers were detected in the anoxic part of the sediments. These results lead to the conclusion that extreme concentrations of sulfate might have an effect on the microbial diversity of the habitat that remains to be proved by quantitative analysis.
Samples were taken in triplicate on February and July 2005. Water and sediments were obtained from the same area of the lake. Water samples were taken aprox. 10 cm above sediments using sterile 50 mL Falcon tubes and kept at 4°C (for 4 h) until processed. In the dry season 50 mL sterile syringes were used for brine collection. For core extraction a Ring Kit core-sampler (Eijkelkamp Agrisearch equipment, The Netherlands) for soft soil was used. The sampler was inserted down to 40 cm, the core was kept at 4°C until further processing. Samples were used to inoculate cultures in triplicate and for molecular analysis
For water samples, in situ temperature, pH, Eh and dissolved oxygen were measured using a multi-parametric probe (YSI 556 MPS, YSI Environmental). Eh and pH along the sediment cores were measured with a probe connected to a potentiometer Orion Model 290A+Thermo Orion (Thermo Fisher Scientific) calibrated at high ionic strength using equivalent Na2SO4 solutions, and dissolved oxygen and temperature with a Syland TM model Simplair. Elemental analysis was performed by TXRF (Extra-II) and ICP-MS (ELAN-6000 PE-Sciex) instruments and ionic chromatography with an IC Dionex DX-600 apparatus. Ion data from Tirez lagoon and other saline systems were used to build a ternary diagram using the software ProSim Ternary Diagram (ProSim, France).
Microscopic examination and cell enumeration
Samples were fixed with formaldehyde at a final concentration of 4% (v/v). The identification of algae, Cyanobacteria, Arthropoda, Rotifera and Fungi was carried out by microscopic observation of fixed samples using a Zeiss Axiovert 200M microscope coupled to a CCD camera.
To quantify cell numbers, preparations were stained with 4′, 6′-diamino-2-phenylindole (DAPI), Molecular Probes (Invitrogen), as previously described  and counted under a Zeiss Axiovert 200M microscope.
Microorganism isolation and culture
Sediment samples were dispersed in 1× PBS (0.1 M NaCl, 2 mM KCl, 4 mM Na2HPO4, pH 7.4) and the suspension used to inoculate different media plates. Each plate was inoculated with 100 μl of sediment slurry. For isolation of Cyanobacteria, BG11 medium plates  were inoculated and incubated at 20°C for up to 3–4 weeks under a 16:8 light:dark cycle at 150 mmol photons m2s-1 irradiance and a temperature of 19°C. Fungi were isolated in PDA medium (potato-dextrose-agar) containing 0.050 mg/mL streptomycin and 0.1 mg/mL ampicillin and incubated at 30°C. Heterotrophic microorganisms were isolated on marine agar (Difco, Marine Broth 2216) and media for halophilic strains prepared with salts obtained from water of Tirez lagoon (rainy season) and crystallized with vacuum at room temperature. Salt composition was determined by ionic chromatography with an IC Dionex DX-600 apparatus. Ionic composition was as follows (ppm): Na+-K+ (8140), Ca2+ (1091), Mg2+ (4602), NH4+ (53.6), Cl- (258) and SO42- (6695). The crystallized salts were dissolved at a final concentration of 10, 20 or 30% (w/v). Dissolved salts were enriched with yeast extract (<0.5 g/L) and glycerol (<0.5 g/L) as reported by Bolhuis et al. . Representative individual colonies from each medium were reinoculated in the same growth condition. All plate isolates were transferred to liquid media to obtain enough biomass to allow DNA extraction for molecular analysis. Sulfate-reducing bacteria were grown in anaerobic SRB medium modified from Raskin et al.  and supplemented with 500 mg/L L-cysteine, as reductive agent, and the following organic substrates: 250 mg/L yeast extract, 770 mg/L glutamic acid, 15 mg/L glycine, 250 mg/L peptone, 14 mM methanol and 27 mM methylamine.
To collect cells 100 mL of water samples were filtered onto 0.22 μm polycarbonate filters (Millipore). Sediment samples were sonicated in 1× PBS during 3 min at 4°C and power of 73 w/cycle (Labsonic B. Braun, Germany), before DNA extraction. In all cases DNA was extracted using Power Soil DNA Isolation Kit (MoBio, Labs. Inc., Solana Beach, CA), following manufacturer’s directions and purified using a DNA purification JetQuick kit (Genomed).
For extraction of dinoflagellate DNA, microalgal cells were picked, one by one from the water samples with a microcapillary pipette under an inverted microscope (Zeiss A at 60× and 400× magnification), washed 2–3 times using sterile 1× PBS, placed (with as little liquid as possible) in 0.2 mL Eppendorf tubes containing 5 μl of lysis buffer (0.005% SDS and 400 ng/μL Proteinase K) and treated as in the procedure described by Kai et al..
PCR conditions for rRNA gene amplification
Amplifications were performed using a Thermal Cycler 2720 (Applied Biosystems) in a final volume of 50 μL, each containing: 1 mM of dNTP, 3 mM MgCl2, 1 mM of each primer, 1× PCR buffer and 0.025 u/μL Taq DNA Polimerase (AmpliTaq DNA Polymerase, Roche Molecular Systems). DNA was added in a volume of 3 μL, containing about 1–5 ng of template. Bacterial 16S rDNA was amplified using primers 27f  and 1492mr (5′-TACGGYTACCTTGTTACGACTT-3′) modified from  (annealing 57°C; 30 cycles). The 25f  and 1492mr primers were used for Archaea domain (52°C; 27 cycles). Both 16S rDNA amplification procedures consisted of initial denaturation (94°C for 10 min) followed by the above-indicated number of cycles of denaturation (94°C for 1 min), annealing (at the temperatures indicated above for 1 min) and extension (72°C for 3 min) followed by a final cycle of extension (72°C for 10 min). PCR amplification of 18S rDNAs were performed using the primer pair Euk1Af-Euka516 as described in .
For dinoflagellates an 18S rDNA fragment was amplified using dinoflagellate-specific primers Dino18SF1m (5′-AAGGGTTGTGTTTATTAGNTACAGAAC-3′) modified from  and 18ScomR1 . The reaction was performed with an initial denaturation (94°C for 5 min), followed by 30 cycles of denaturation at 94°C for 1 min, annealing at 56°C for 1 min, and extension at 72°C for 3 min.
PCR amplifications for DGGE analysis of rRNA gene fragments were performed for Bacteria using the primers 341fGC  and 907r  while for Archaea the region between the primers 344fGC  and 915r  was used. Amplification conditions for Bacteria were the following: 94°C for 7 min, 35 cycles of 94°C for 45 s, 49°C for 45 s and 72°C for 1.5 min, and a final extension of 72°C for 10 min. For Archaea primers: 94°C for 5 min, 32 cycles of 94°C for 30 s, 54°C for 1 min and 72°C for 1 min, and a final extension of 72°C for 10 min. A 16S rRNA Deltaproteobacteria-specific region was amplified as described in  using the 385fGC-907r primer pair. Functional gene primers used for detection of sulfate reducing and methanogenic activities are described in . In PCR reactions GC was equivalent to a 40 bp GC clamp at the 5′ end to prevent complete melting of the DNA fragments.
Cloning of 16S rRNA
PCR amplified products were cloned using the TOPO TA Cloning kit (Invitrogen Corporation, California) according to the manufacturer’s indications. From each clone library putative positive transformants were randomly sampled to perform minipreps according to standard alkaline lysis protocols.
Denaturing gradient gel electrophoresis
DGGE analysis of PCR-amplified 16S rRNA gene fragments using a 30-70%, 40-70%, 40-70% and 30-50% gradients was performed as described by Muyzer et al.  using a D-Code Universal Detection System (BioRad Laboratories). PCR samples were loaded onto 8% (w/v) polyacrylamide gels in 1× TAE buffer (20 mM Tris, 10 mM acetate, 0.5 mM Na-EDTA, pH 7.4). Electrophoresis was carried out at 60°C, at a constant voltage of 200 V for 4.5 h. After electrophoresis, the gel was stained for 15 min with ethidium bromide (0.5 μg/mL), rinsed in distilled water for 30 min and photographed with a Polaroid Kodak digital 16 camera. DGGE bands were excised from the gel under UV light and eluted in 50 μl of milliQ water overnight at 4°C. An aliquot of 3 μL was taken from each eluted sample and re-amplified by PCR in the conditions described above. The primers used for re-amplifications were the corresponding ones used in the first amplification but without the tailing sequence.
PCR products from DGGE gel bands and plasmid DNAs containing inserts were sequenced with the primers used for amplification and the pair M13F/M13R, respectively using an ABI PRISM Big Dye Terminator Cycle Sequencing Ready Reaction Kit (ABI) and an Applied Biosystem ABI 310 (PE Applied Biosystems, Foster City, California, USA) automated sequencer. Chromatograms were transformed into contiguous sequences combining FinchTV (http://www.geospiza.com/finchtv) and GeneDoc (http://www.nrbsc.org) tools. Chimeric sequences were identified by using Mallard. The 16S and 18S rRNA sequences obtained from DGGE bands, culture isolates and clones were collapsed into OTUs by similarity analysis using FastGroup II (http://fastgroup.sdsu.edu). OTUs were compared with those available in GenBank (NCBI) and Ribosomal Database Project (RDBP) to identify them using the Basic Local Aligment Search Tool Nucleotide (BLASTN) and Classifier algorithms, respectively. Similarity analysis was performed with FastGroup II (http://fastgroup.sdsu.edu)
The 16S rRNA gene sequences with a length ≥ 1300 bp were aligned with representative ones published in Bergey’s Manual  using ClustalX using default parameters. Alignments were optimized manually using BioEdit version 18.104.22.168 . A similarity matrix was calculated by using the similarity matrix tool located at the Ribosomal Database Project homepage (http://rdp.cme.msu.edu/cgis/phylip.cgi). Operational Taxonomic Units (OTUs) were defined as sequences obtained from the same technique that showed a similarity more than 97% with each other. Similarity analysis was performed with FastGroup II (http://fastgroup.sdsu.edu). Alignments of OTUs obtained from cloning were exported to test different nucleotide substitution models using Phylip available in http://phylemon.bioinfo.cipf.es. GTR was consequently the optimal model. Posterior probability and topology of the phylogenetic trees were obtained with Mr. Bayes version 3.1.2  defining the parameters GTR+I+G. Tree analysis was a consensus of 5x105 generations (SD=0.02) in Archaea and 2.5×105 generations in Bacteria (SD=0.04), in both cases it was performed a “burnin” of 50%.
GenBank sequence accession numbers
The SSU rRNA fragment gene sequences were deposited in the GenBank database under accession numbers, EU734574, EU725589-EU725602, EU722643-EU722714, FJ172052-FJ172100 and FJ236710-FJ236714. Prefixes of sequences describe: community sampled (Rw for rainy water, Rs for rainy sediment, Dw for dry water and Ds for dry sediment), technique used (c for clone, i for isolate and d for DGGE-band) and domain (b for Bacteria and a for Archaea) and identification number.
This research was supported by CGL2009-11059 grant from the Ministery of Economy and Competitivity, institutional financement of the Centro de Astrobiología and Fundación Areces at the Centro de Biología Molecular. LM acknowledges a doctoral fellowship of the CONACyT (grant no. 178909).
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