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1 Winogradsky Institute of Microbiology, Russian Academy of Sciences, Prospect 60-let Oktyabrya 7/2, Moscow 117312, Russia
2 Universität Hamburg, Biozentrum Klein Flottbek, Mikrobiologie, Ohnhorststr. 18, D-22609 Hamburg, Germany
3 Department für Mikrobielle Ökologie, Universität Wien, Althanstr. 14, A-1090 Wien, Austria
Correspondence
E. Spieck
spieck{at}mikrobiologie.uni-hamburg.de
| ABSTRACT |
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The GenBank/EMBL/DDBJ accession numbers for the 16S rRNA gene sequences of Candidatus Nitrospira bockiana and the enrichment clone are EU084879 and EU084880, respectively.
A supplementary figure of the DGGE profile showing the increasing purity of the enrichments is available with the online version of this paper.
| INTRODUCTION |
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Until recently, all of the recognized genera of bacterial ammonia oxidizers have been limited to two phylogenetically distinct groups affiliated to the classes Betaproteobacteria and Gammaproteobacteria within the phylum Proteobacteria. The first ammonia oxidizers of the domain Archaea, within the phylum Crenarchaeota, were isolated by Könneke et al. (2005)
. Existing genera of NOB have been classified taxonomically under two phyla in the domain Bacteria. The genera Nitrobacter, Nitrococcus and Nitrospina belong to the classes Alphaproteobacteria, Gammaproteobacteria and Deltaproteobacteria within the phylum Proteobacteria. The genus Nitrospira represents a monophyletic lineage within the deep-branching bacterial phylum Nitrospira (Ehrich et al., 1995
; Spieck & Bock, 2001
), where they occur together with Candidatus Magnetobacterium bavaricum and members of the genera Leptospirillum and Thermodesulfovibrio (Garrity & Holt, 2001
). So far, the genus Nitrospira is represented by two recognized species: Nitrospira marina (Watson et al., 1986
) and Nitrospira moscoviensis (Ehrich et al., 1995
), isolated from marine and freshwater habitats, as well as by Candidatus Nitrospira defluvii (Spieck et al., 2006
), highly enriched from activated sludge. Species of the genus Nitrospira are regarded to be obligate lithotrophs with the ability to perform mixotrophic growth (Watson et al., 1986
).
Investigations performed by cultivation-independent molecular methods (Burrell et al., 1998
; Hovanec et al., 1998
; Daims et al., 2001
) and immunological techniques (Bartosch et al., 1999
) clearly indicated that Nitrospira-like bacteria are widely distributed in different natural and engineered ecosystems. For example, it was shown that Nitrospira-types are the most common nitrite-oxidizers in wastewater treatment plants (Juretschko et al., 1998
) and not Nitrobacter-types as was previously thought according to culture-based studies. Nitrospira-like bacteria were further detected in various soils (Bartosch et al., 2002
; Noll et al., 2005
) and freshwater sediments (Stein et al., 2001
; Altmann et al., 2003
). Recently, such organisms were also found to be present in thermophilic communities when studied by molecular and classical techniques (Kanokratana et al., 2004
; Lebedeva et al., 2005
).
In this study, we describe the physiological and phylogenetic characterization of a novel Nitrospira-like bacterium. The organism originated from internal corrosion deposits from a steel pipeline of the Moscow heating system, Russia. The first evidence for the existence of this novel Nitrospira-like bacterium was based on data from lipid profiles; in particular, the absence of the lipid component 16 : 1cis11, a feature characteristic of the recognized species of the genus Nitrospira (Lipski et al., 2001
; Spieck et al., 2006
). The novel nitrite-oxidizing bacterium is provisionally named Candidatus Nitrospira bockiana (following the naming convention of Murray & Stackebrandt, 1995
).
| METHODS |
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Cultivation.
Primary enrichment of NOB was obtained at 42 °C in basal salt medium (Ehrich et al., 1995
) supplemented with 1 mM of nitrite as the only energy source. Later, if not stated otherwise, cultivation of enrichment cultures was carried out at 45 °C in 250 ml flasks with 100 ml mineral medium supplemented with 3–7 mM of nitrite. The final isolate was cultivated at 42 °C with 0.3–3 mM of nitrite. Growth was detected by measuring nitrite consumption; nitrite was regularly replaced to increase the cell density. Percoll density-gradient centrifugation and subsequent serial dilutions in a medium supplemented with 0.3 mM of nitrite were performed as described by Ehrich et al. (1995)
.
The influence of organic matter was checked in a mineral medium with 3 mM of nitrite supplemented with pyruvate (55 mg l–1) or yeast extract (20 mg l–1). The effect of vitamins, prepared according to Balch et al. (1979)
, was also tested. A complex medium was used to check whether the enriched organisms were capable of organotrophic growth. For this purpose, the basal mineral medium without nitrite was supplemented with pyruvate (55 mg l–1) as carbon source and yeast extract (150 mg l–1) and peptone (150 mg l–1) as nitrogen sources. The pH of the medium was adjusted to 7.6. Growth was monitored by light microscopic observations.
Isolation and investigation of Nocardioides sp.
Samples of enrichment 5 were streaked onto plates of solid complex medium as mentioned above and incubated at 42 °C. Single colonies were selected and spread onto plates again to obtain a pure culture. The ability of the isolate, identified as Nocardioides sp., to perform denitrification and nitrate reduction was tested in 20 ml tubes filled with complex medium supplemented with 1 g l–1 of sodium nitrate. The tubes also contained Durham tubes for collecting any gas formed by denitrification.
Analytical procedures.
Nitrite and nitrate concentrations were determined quantitatively by HPLC in an automated system (MT2; Kontron Instruments). Separation was achieved by ion pair chromatography with a Hypersil ODS C18 column (125x4.6 nm) (Meincke et al., 1992
). Detection was performed by UV absorption at 225 nm. Consumption of nitrite was detected qualitatively by the Griess-Ilosvay spot test (Schmidt & Belser, 1982
). Cell density was determined under a light microscope by direct cell counting.
Electron microscopy.
Electron microscopy of whole cells and of ultrathin sections was carried out as described by Spieck et al. (2006)
and samples were viewed in a transmission electron microscope (model 420, Philips or LEO-906E, Zeiss).
Denaturing gradient gel electrophoresis (DGGE) analyses.
The partial 16S rRNA genes in the enrichment cultures were amplified by PCR with the eubacterial primer set 346F/907R (Muyzer et al., 1998
). A GC-clamp was added to the forward primer. DGGE was performed at a temperature of 59 °C with a gradient from 50–80 % denaturants. Bands were extracted from the gel and reamplified and the partial 16S rRNA gene sequences were compared with those available on publicly accessible databases by using the Basic Local Alignment Search Tool program (BLAST, NCBI).
Fluorescence in situ hybridization.
Aliquots of the enrichments were prepared for fluorescence in situ hybridization (FISH) by fixation in paraformaldehyde according to Daims et al. (2005)
. Following fixation, the biomass was spotted onto microscope slides and FISH was performed according to Manz et al. (1992)
and Daims et al. (2005)
. The applied oligonucleotide probes were S-G-Ntspa-0662-a-A-18 (target group: genus Nitrospira) (Daims et al., 2001
), S-*-Ntspa-0712-a-A-21 (target group: phylum Nitrospira) (Daims et al., 2001
), S-*-Ntspa-1151-a-A-20 (target group: sublineage II of the genus Nitrospira) (Maixner et al., 2006
), S-G-Nbac-1035-a-A-18 (=NIT3; Wagner et al., 1996
) (target group: genus Nitrobacter) and the EUB probe mix that detects almost all known Bacteria (Amann et al., 1990
; Daims et al., 1999
). The probes were 5'-labelled with either the FLUOS dye [5(6)-carboxyfluorescein-N-hydroxysuccinimide ester] or the sulfoindocyanine dye Cy3. The Nitrospira- and Nitrobacter-specific probes were used together with competitor oligonucleotides according to Daims et al. (2001)
and Wagner et al. (1996)
. All probes and competitors were obtained from Thermo Scientific (Germany). Fluorescence signals were recorded with a confocal laser scanning microscope (LSM 510 Meta; Zeiss) by using an Ar ion laser to detect FLUOS (488 nm excitation wavelength) and a HeNe laser (543 nm) to detect Cy3, respectively.
Cloning and phylogenetic analysis of 16S rRNA genes.
Bacterial 16S rRNA genes were amplified by PCR, cloned and sequenced as described by Maixner et al. (2006)
with the only modification that instead of extracted genomic DNA, 1.5 µl of Nitrospira enrichment was added directly to the PCR reaction mix for 16S rRNA gene amplification. Sequence alignments and phylogenetic analyses were carried out using ARB software (Ludwig et al., 2004
) according to Daims et al. (2001)
.
| RESULTS |
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Physiological properties
Physiological investigations started with enrichment 5, which was characterized as a co-culture of Candidatus Nitrospira bockiana and Nocardioides sp. (see Supplementary Fig. S1). Enrichment 5 had the highest rate of nitrite consumption at around 45 °C (Fig. 4
) at a pH of 7.6–8.0. The oxidation of nitrite correlated with an increase in the cell concentration (data not shown). The doubling time of the total cell number was between 8–9 h in a mineral medium with 6.8 mM nitrite, which was oxidized within 4 days. Enrichment 5 was characterized by a wide tolerance of high nitrite concentrations, a characteristic previously noted for Candidatus Nitrospira defluvii (Spieck et al., 2006
). The substrate was oxidized at concentrations up to 26–30 mM (Table 2
).
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It was found that the temperature range of the nitrite-oxidizing activity largely depended on the amount of nitrite. Starting with a low substrate concentration of 0.3 mM, enrichment 5 and the final isolate were able to oxidize nitrite between 17 and 48 °C and 17 to 44 °C, respectively, while 1.5 mM nitrite was oxidized within a temperature range of 28–48 °C and 28–44 °C, respectively. Using a higher concentration of 6 mM nitrite, growth of enrichment 5 was restricted to an even narrower temperature range of 37 to 48 °C.
Characterization of the contaminant
Based on phylogeny using partial 16S rRNA gene sequences, the accompanying heterotrophic organism was identified as Nocardioides sp. in the family Nocardiodaceae, a member of the phylum Actinomycetales (Yoon et al., 2005
). The Nocardioides sp. was Gram-positive, aerobic, rod-shaped (0.4–0.7 x0.5–1.3 µm) or coccoid (0.7 µm in diameter) cells. No motile forms were observed. The organism was able to perform reduction of nitrate, but not complete denitrification.
Phylogenetic analysis
Phylogenetic analyses of 16S rRNA genes revealed that the final isolate, Candidatus Nitrospira bockiana, was a novel Nitrospira-like bacterium which did not group with any previously known sublineages (Daims et al., 2001
) of the genus Nitrospira (Fig. 5
). Three partial 16S rRNA gene sequences of Candidatus Nitrospira bockiana (1158 nucleotides) from the final isolate were analysed and found to be highly similar to each other (99.8–99.9 % gene sequence similarity). The few base differences were probably due to PCR or sequencing errors. From earlier enrichments (but not from the final isolate), 16S rRNA gene sequences were retrieved for a second Nitrospira-like bacterium that fell into sublineage II of the genus Nitrospira, a lineage that also contains the cultured species Nitrospira moscoviensis (Fig. 5
). This finding is consistent with the results of FISH with different Nitrospira-specific probes shown above.
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| DISCUSSION |
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Adaptation to higher temperatures is a physiological feature which distinguishes the novel Nitrospira-like isolate from Nitrospira moscoviensis amd Nitrospira marina as well as from Candidatus Nitrospira defluvii (Table 2
). During the enrichment and isolation procedures, this characteristic was used successfully in order to discriminate Candidatus Nitrospira bockiana from the genus Nitrobacter and members of the sublineage II of the genus Nitrospira.
The painstaking isolation of Candidatus Nitrospira bockiana described in this study is the result of 12 years of work. The main reasons for the difficulties in purification were the abilities of the organism to form extracellular polymeric substances and to form microcolonies that also enclosed contaminants. Once purification procedures for free-living planktonic cells were employed, an enrichment that could be further purified by dilution techniques was finally obtained. The results of classical (no growth observed in complex medium) and molecular (DGGE, FISH) tests suggest that the finally-obtained culture was free from contaminants and other NOB. However, the presence of low numbers of other organisms cannot be excluded as the detection limit of FISH is 103–104 cells ml–1 (Amann, 1995
) and populations below 1 % of the total bacterial community may not be detectable by DGGE (Muyzer et al., 1993
).
It is interesting to note that Nitrospira strains growing in co-culture with a Nocardioides sp. (enrichment 5) could resist higher nitrite concentrations and were shown to possess a higher temperature tolerance (Table 2
) when compared with the final isolate. Keeping in mind the loss of organic matter by autotrophically growing NOB (Rittmann et al., 1994
; Kindaichi et al., 2004
), Nitrospira strains might supply the Nocardioides sp. with organic carbon for cell growth. The reason for the stimulation of Nitrospira strains by the contaminant is still unknown and remains to be clarified in further studies.
The data from lipid profiles were in accordance with the results of the 16S rRNA sequence analyses and suggest that Candidatus Nitrospira bockiana is related, but not identical, to the recognized species of the genus Nitrospira. As shown by Lipski et al. (2001)
, the culture contains the dominant lipid components 16 : 0; 16 : 0 11 methyl and 16 : 1cis7 and lacks 16 : 1cis11, a lipid profile that is typical of the other recognized Nitrospira species. Based on physiological differences, chemotaxonomic data and on 16S rRNA gene sequence analysis, we provisionally designate this organism as Candidatus Nitrospira bockiana (as per the naming convention proposed by Murray & Stackebrandt, 1995
)
Description of Candidatus Nitrospira bockiana
Nitrospira bockiana (bock.i.a.na. N.L. fem. adj. bockiana named after Professor Eberhard Bock, a microbiologist who devoted his research to the investigation of NB).
The organism is phylogenetically related to the genus Nitrospira. Gram-negative. Multiplication takes place by binary as well as by inequal fission. A chemolithoautotroph that oxidizes nitrite to nitrate and is able to use carbon dioxide as a sole carbon source. The highest rate of nitrite consumption occurs at 42 °C, with a temperature range between 28 and 44 °C. Pleomorphic cells range from loosely wound spirals with a variable number of coils to slightly curved and even straight rods, as well as coccoid cells (0.9 µm diameter). The width of the spiral and rod-shaped cells ranges from 0.3 to 0.6 µm and the length ranges from 1.0 to 2.5 µm. Major fatty acids are 16 : 0; 16 : 0 11 methyl and 16 : 1cis7. Neither pyruvate nor yeast extract stimulates nitrite oxidation. Organotrophic growth is not observed.
| ACKNOWLEDGEMENTS |
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