Antarctic Science 25(2), 219–228 (2013) & Antarctic Science Ltd 2013 doi:10.1017/S0954102012000831 Phylogeographic analysis of filterable bacteria with special reference to Rhizobiales strains that occur in cryospheric habitats RYOSUKE NAKAI1,2, ERI SHIBUYA1, ANA JUSTEL3, EUGENIO RICO4, ANTONIO QUESADA5, FUMIHISA KOBAYASHI6, YASUNOBU IWASAKA6, GUANG-YU SHI7, YUKI AMANO8,9, TERUKI IWATSUKI8,9 and TAKESHI NAGANUMA1* 1 Graduate School of Biosphere Science, Hiroshima University, 1-4-4 Kagamiyama, Higashi-hiroshima, Hiroshima 739-8528, Japan 2 Research Fellow of the Japan Society for the Promotion of Science, Chiyoda-ku, Tokyo 102-8471, Japan 3 Departamento de Matemáticas, Universidad Autónoma de Madrid, 28049 Madrid, Spain 4 Departamento de Ecologı́a, Universidad Autónoma de Madrid, 28049 Madrid, Spain 5 Departamento de Biologı́a, Universidad Autónoma de Madrid, 28049 Madrid, Spain 6 Institute of Nature and Environmental Technology, Kanazawa University, Kakuma-machi, Kanazawa 920-1192, Japan 7 Institute of Atmospheric Physics, Chinese Academy of Science, Beijing 100029, China 8 Japan Atomic Energy Agency, Mizunami Underground Research Laboratory, 1-64 Yamanouchi, Akeyo-cho, Mizunami-shi, Gifu 509-6132, Japan 9 Japan Atomic Energy Agency, Horonobe Underground Research Center, Hokushin 432-2, Horonobe-cho, Teshio-Gun, Hokkaido 098-3224, Japan *corresponding author: [email protected] Abstract: Although the lower size limit of microorganisms was previously believed to be c. 0.2 mm, there is evidence for the existence of microorganisms that can pass through 0.2 mm-pore-size filters called ultramicrobacteria or nanobacteria. However, information on the phylogeny and biogeography of these bacteria is limited. We obtained 53 isolates of 0.2 mm-passable bacteria from 31 samples collected at 26 locations worldwide, including the Arctic Svalbard Islands, deserts, and Maritime Antarctica. Phylogenetic analysis of near full-length 16S rRNA gene sequences revealed that 18 of the 53 isolates were , 97% homologous with previously cultured isolates, representing potentially novel species. Two isolates (order Rhizobiales) (100% identical) collected from Byers Peninsula, Livingston Island in Maritime Antarctica, were closely related (99.8% similarity) to an isolate collected from intertidal sediments in East Antarctica. In addition, the sequence of this Antarctic isolate showed $ 97% similarity to 901 sequences derived from known isolates and samples collected at geographically disparate locations under various environmental conditions. Interestingly, among 13 sequences showing $ 99% similarity, ten were isolated from cryospheric habitats such as Arctic, Antarctic, and alpine environments. This implies that such Rhizobiales strains occur in the cryospheric regions, however, their abundance and biomass may be scarce depending on the geographic location. Received 7 November 2011, accepted 6 August 2012 Key words: 16S rRNA gene, Antarctica, Baas-Becking hypothesis, biodiversity, biogeography, ultramicrobacteria the 1970s. For example, it has been demonstrated that bacteria smaller than 0.2 mm in diameter represent between 1% and 10% of all bacteria found in seawater (Hobbie et al. 1977, Zimmermann 1977, Watson et al. 1977). In addition, in coastal waters, where bacterial populations are estimated to range between 108 and 109 cells l-1, Fukuba et al. (2002) reported that between 100 and 101 viable bacteria l-1 pass through 0.2 mm-pore-size filters. In 1981, two types of very small bacteria , 0.3 mm in diameter were successfully cultured from seawater (Torrella & Morita 1981). One displayed an increase in size following incubation, whereas the other did not increase in size even after incubation and was named ultramicrobacteria (UMB). Since then, further isolations and phylogenetic identification of 0.2 mm-passable microorganisms have been performed, and Introduction The occurrence of microorganisms smaller than 0.2 mm has been questioned based on the minimum requisite size for a complete set of genomic DNA, ribosomes, proteins, cellular membranes, and other intracellular components (Maniloff 1997). On the other hand, referring to the genomes of Mycoplasma genitalium and other parasitic bacteria, some argued that microbial cells can theoretically be as small as 0.14 mm in diameter (Mushegian & Koonin 1996). The debate regarding the minimal cell size of microorganisms remains unresolved. Concurrent with this theoretical discussion, research on microorganisms that pass through 0.2 mm-pore-size filters (0.2 mm-passable microorganisms) has been ongoing since 219 Downloaded from https:/www.cambridge.org/core. IP address: 88.99.165.207, on 17 Jun 2017 at 22:43:03, subject to the Cambridge Core terms of use, available at https:/www.cambridge.org/core/terms. https://doi.org/10.1017/S0954102012000831 220 RYOSUKE NAKAI et al. some of these isolates were UMB (MacDonell & Hood 1982, Hood & MacDonell 1987, Haller et al. 2000, Elsaied et al. 2001, Miteva & Brenchley 2005, Dmitriev et al. 2007, Geissinger et al. 2009). Hahn et al. (2003, 2009) isolated Actinobacteria and Polynucleobacter Cluster (class Betaproteobacteria) with ultramicro cell sizes (, 0.1 mm3), even under eutrophic culture conditions, and called these obligate UMB. It has also been reported that these obligate UMB are cosmopolitan species found in freshwater regions (Hahn 2003, Hahn et al. 2003). Recent research has investigated community structure and the functional potential of 0.2 mm-passable populations in the environments using culture-independent methods (Miyoshi et al. 2005, Naganuma et al. 2007, Nakai et al. 2011). Miyoshi et al. (2005) reported that c. 65% of all 16S rRNA gene phylotypes from 0.1-mm-pore-size filtercaptured microorganisms in deep terrestrial aquifers were affiliated with the candidate divisions OD1 and OP11, potentially representing new bacterial phyla. Naganuma et al. (2007) detected novel unaffiliated phylotypes only in the 0.2 mm-passable fraction of deep-sea hydrothermal vent samples. Nakai et al. (2011) indicated that the metagenome of 0.2 mm-passable microorganisms in deep-sea hydrothermal fluid contained novel genes pertinent to membrane functions. These findings show that 0.2 mm-passable populations include some phylogenetically and/or functionally important species which need to be isolated and characterized. In addition, our understanding of the biogeography for 0.2 mm-passable bacteria is at present limited to cosmopolitan species found in freshwater (Hahn 2003, Hahn et al. 2003). Here we tested samples taken from widely dispersed sites for 0.2 mm-passable bacteria and investigated phylogenetic relationships in order to preliminarily test the Baas-Becking hypothesis that ‘‘everything is everywhere, but, the environment selects’’ (Baas-Becking 1934), implying that microscopic organisms do not have any large-scale spatial pattern of distribution. Our results provide new information on the phylogeography of 0.2 mm-passable bacteria. Materials and methods Sample collection A total of 31 samples were collected from various environments, including soil, gravel, seawater, and freshwater, in 26 locations around the world, the majority of which were in Japan. Arctic samples were collected in August 2008 from Troll hot springs (79.48N, 13.48W) on Spitzenberg Island in the Svalbard archipelago. This site is the northernmost thermal springs documented on land (Jamtveit et al. 2006). Antarctic samples were collected in December 2008 from Byers Peninsula (6284'S, 6086'W), Livingston Island, South Shetland Islands. Byers Peninsula is one of the largest ice-free areas in the region and serves as an important reference site (ASPA No. 126) within the Antarctic ecosystem (Quesada et al. 2009). In addition, gravel was collected from the Gobi Desert and eastern edge of the Sahara Desert in November 2008 and December 2008, respectively. Although a significant number of taxa of dust-borne microorganisms have been isolated and characterized in both African and Asian desert systems, only a few papers have reported a detailed identification of culturable bacteria (Chen et al. 2011). Samples were collected using sterile gloves and placed in sterile plastic bottles or sample tubes and stored in the dark at room temperature until processing. Isolation and cultivation of 0.2 mm-passable bacteria Bacteria were isolated using a method modified from Elsaied et al. (2001). Liquid samples were filtered through three-fold 0.2 mm filters (Advantec, Tokyo, Japan), and concentrated R2A liquid medium (Massa et al. 1998) was added to the filtrate to bring the final media concentration to 13. Solid samples, such as soil or pebbles, were suspended in phosphate buffer solution (8 g l-1 NaCl, 1.1 g l-1 Na2HPO4, 0.2 g l-1 KCl, and 0.2 g l-1 KH2PO4), and the resulting suspension was processed in the same manner as the liquid samples. The enrichment cultures were kept in the dark at room temperature for at least three weeks. To confirm the effectiveness on filtration through three-fold 0.2 mm filters, Escherichia coli K12 (IFO 3301) cultures were used as negative growth control. Subsequently, the culture liquids were spread on 1.5% agar medium containing identical ingredients. Single colonies were isolated and streaked on fresh agar plates to purify colony-forming strains. This procedure was repeated at least three times to ensure reliable colony purification. Phylogenetic characterization Genomic DNA extraction was performed as described by Aljanabi & Martinez (1997). Bacteria-specific 27F (5'AGAGTTTGATCCTGGCTCAG-3') and universal 1492R (5'-GGTTACCTTGTTACGACTT-3') primers were used to amplify near full-length fragments of the 16S rRNA gene (DeLong 1992). Reaction conditions for polymerase chain reaction (PCR) amplification were the same as those used in a previous report (Naganuma et al. 2007). After confirming the presence of PCR products of the desired fragment size (c. 1500 base pairs) by electrophoresis on 1.5% agarose gel, PCR products were purified using the QIAquick PCR Purification kit (Qiagen, Valencia, CA, USA). All purified PCR products were sequenced using an ABI 3730XL automatic DNA sequencer (Applied Biosystems, Foster City, CA, USA). The 16S rRNA gene sequences obtained were compared against known sequences using a BLASTN search against the DDBJ/EMBL/GenBank nt-database and the Greengenes prokaryotic multiple sequence alignment (prokMSA) database (DeSantis et al. 2006). Greengenes is a Downloaded from https:/www.cambridge.org/core. IP address: 88.99.165.207, on 17 Jun 2017 at 22:43:03, subject to the Cambridge Core terms of use, available at https:/www.cambridge.org/core/terms. https://doi.org/10.1017/S0954102012000831 Phylogenetic group Isolate Accession number Site description Isolation source Sample description Closest organism Isolation source Accession number Sima (%) Culturability of the filtrateb Alphaproteobacteria KNA-P IZ3 GB9 AB539973 AB539970 AB539976 35.48N, 137.28E 35.48N, 132.78E 40.08N, 94.78E groundwater lake water sand Phaeospirillum fulvum isolate S3 Phaeospirillum sp. I08B-942 Phaeospirillum fulvum isolate S3 activated sludge from Korea AF508113 soil from western China FJ529718 activated sludge from Korea AF508113 98.0 99.9 98.3 - NP1 NP3 IZ6 AB539983 AB539984 AB539980 79.48N, 13.48E 79.48N, 13.48E 35.28N, 132.98E Gifu, central Japan Shimane, western Japan Gobi desert, north-central China Svalbard, Arctic Norway Svalbard, Arctic Norway Shimane, western Japan mud mud soil activated sludge from Korea AF508113 activated sludge from Korea AF508113 unknown EU697955 99.7 99.6 92.6 1 IZ12 AB539981 35.28N, 132.98E Shimane, western Japan sand unknown EU697955 92.5 1 IZ16 AB539982 35.28N, 132.98E Shimane, western Japan bark unknown EU697955 92.6 - GB6 AB539977 40.08N, 94.88E sand 92.7 1 AB540022 79.48N, 13.48E root nodules from central China unknown DQ100062 NP9 Gobi desert, north-central China Svalbard, Arctic Norway Phaeospirillum fulvum isolate S3 Phaeospirillum fulvum isolate S3 Rhizobium huautlense strain CCNWNX0087 Rhizobium huautlense strain CCNWNX0087 Rhizobium huautlense strain CCNWNX0087 Rhizobium sp. CCBAU 43060 EU697955 92.6 - GB3 AB539978 36.08N, 104.08E unknown EU697955 92.3 - GB10 AB539979 40.08N, 94.78E unknown EU697955 92.6 1 S-19 AB539971 62.78S, 61.08W Gobi desert, north-central China Gobi desert, north-central China Maritime Antarctica FJ889671 99.8 - S-42 AB539972 62.78S, 61.08W Maritime Antarctica FJ889671 99.8 - IZ17 IZ9-1 IZ10 IZ19-2 AB539985 AB539986 AB539987 AB539988 35.28N, 35.28N, 35.28N, 35.48N, 132.98E 132.98E 132.98E 132.78E Shimane, Shimane, Shimane, Shimane, AF338177 AJ565423 AJ565423 DQ861288 99.8 99.2 99.1 99.9 1 1 1 IZ20-1 KNG IZ7-1 Kha AB539989 AB539993 AB539992 AB539994 35.48N, 34.38N, 35.28N, 34.28N, 132.78E 132.68E 132.98E 132.68E AJ565423 AJ565423 AJ565430 DQ861290 99.6 99.2 99.9 99.9 1 1 1 Shr9 AB539995 DQ861290 99.7 - IZ5-1 sandy sediment from East Antarctica sandy sediment from East Antarctica unknown freshwater from Austria freshwater from Austria freshwater from Switzerland freshwater from Austria freshwater from Austria freshwater from Austria freshwater from Switzerland freshwater from Switzerland freshwater from eastern coastal China freshwater from Switzerland river water from eastern Japan chromium contaminated soil from India lake water from East Antarctica lake water from East Antarctica freshwater from western China Betaproteobacteria travertine sand sand beach sand Rhizobium huautlense strain CCNWNX0087 Rhizobium huautlense strain CCNWNX0087 Rhizobium huautlense strain CCNWNX0087 Mycoplana sp. ZS1-12 Mycoplana sp. ZS1-12 Shimane, western Japan Hiroshima, western Japan Shimane, western Japan Hiroshima, western Japan lake water river water river water river water Hylemonella Hylemonella Hylemonella Hylemonella 34.48N, 8.08E Sahara Desert, Tunisia salt lake water Hylemonella gracilis isolate LL AB539991 35.28N, 132.98E Shimane, western Japan river water Hylemonella gracilis isolate WQT2 IZ8 AB539990 35.28N, 132.98E Shimane, western Japan river water Hylemonella gracilis RR IZ4 AB539996 35.48N, 132.78E Shimane, western Japan lake water Beta proteobacterium KF034 KNA-A AB539974 35.48N, 137.28E Gifu, central Japan groundwater Acidovorax sp. G3DM-83 AB540008 34.28N, 132.68E Hiroshima, western Japan seawater NOW AB540009 29.58N, 124.28E Okinawa, south-west Japan seawater IZ2 AB540010 35.48N, 132.78E Shimane, western Japan lake water Saccharospirillum impatiens strain EL-105 Saccharospirillum impatiens strain EL-105 Pseudomonas pseudoalcaligenes KS-1 Gammaproteobacteria kure western western western western Japan Japan Japan Japan Afipia felis Hylemonella gracilis, isolate WQP1 Hylemonella gracilis, isolate WQP1 Hylemonella gracilis, isolate ZL gracilis, isolate WQP1 gracilis, isolate WQP1 sp. WQH1 gracilis isolate LL AJ565424 100 1 DQ861289 99.2 1 AB376632 98.4 1 EU037287 99.4 - AJ315983 96.7 1 AJ315983 96.0 1 EU815635 98.1 1 221 freshwater algal mat soil river water soil lake water PHYLOGEOGRAPHIC ANALYSIS OF NANO BACTERIA Downloaded from https:/www.cambridge.org/core. IP address: 88.99.165.207, on 17 Jun 2017 at 22:43:03, subject to the Cambridge Core terms of use, available at https:/www.cambridge.org/core/terms. https://doi.org/10.1017/S0954102012000831 Table I. Phylogenetic affiliation of isolated strains and culturability of the filtrates. 222 Phylogenetic group Accession number Site description Isolation source Sample description Closest organism Isolation source Accession number Sima (%) Culturability of the filtrateb AB540011 79.48N, 13.48E Svalbard, Arctic Norway hot spring water Pseudomonas sp. PSA A4(4) DQ628969 99.9 1 F9 KE ShrSW KJY N2 AB540012 AB540013 AB540014 AB540000 AB540001 34.38N, 35.28N, 35.98N, 34.48N, 34.58N, Hiroshima, western Japan Yamaguchi, western Japan Tunisia Hiroshima, western Japan Hiroshima, western Japan seawater seawater seawater river water lake water Reinekea blandensis MED297 Vibrio sp. PaD1.16b Oceaniserpentilla haliotidis Bacteroidetes bacterium 3B-2 Bacterium TG141 DQ403810 GQ406586 AM747817 GU117702 AB308367 99.0 99.6 98.5 94.4 93.0 no data 1 1 1 ArSB AB539997 79.48N, 13.48E Svalbard, Arctic Norway hot spring water Bacterium TG141 AB308367 93.4 1 GS THS AB539998 AB539999 78.28N, 15.58E 79.48N, 13.48E Svalbard, Arctic Norway Svalbard, Arctic Norway glacial meltwater hot spring water Bacteroidetes bacterium 3B-2 Bacterium TG141 GU117702 AB308367 93.7 95.3 1 KIP AB540002 31.98N, 130.08E lake water 96.5 1 AB540003 31.98N, 130.08E Gracilimonas tropica strain CL-CB462 Flexibacter aggregans EF988655 KIY unknown AB078038 96.6 1 YMK AB540004 33.68N, 132.08E Koshiki Island, western Japan Koshiki Island, western Japan Ohita, western Japan beneath a high Arctic glacier, Canada Mediterranean Sea unknown Tasman Sea marine sand from Korea freshwater sediment from eastern Japan freshwater sediment from eastern Japan marine sand from Korea freshwater sediment from eastern Japan unknown estuary water unknown DQ486479 99.3 1 KOr AB540005 33.98N, 130.98E Yamaguchi, western Japan seawater South Pacific Ocean AM990675 97.0 - T1 AB540006 33.98N, 129.68E Hiroshima, western Japan seawater 96.4 1 AB540007 33.58N, 131.08E Yamaguchi, western Japan seawater AB073588 98.9 1 GB1 AB540015 40.08N, 94.48E sand Blastococcus sp. YIM 65287 FJ214361 99.3 1 GB5 AB540016 40.08N, 94.78E sand 98.6 1 AB539975 35.48N, 137.28E groundwater Blastococcus jejuensis strain KST3-10 Micrococcus luteus strain INBI-1 DQ200983 KNA-M Gobi desert, north-central China Gobi desert, north-central China Gifu, central Japan EU438932 99.9 1 KNC AB540017 34.38N, 132.68E Hiroshima, western Japan river water AJ565413 99.7 1 NP3-12 AB540018 79.48N, 13.48E Svalbard, Arctic Norway mud Microbacteriaceae bacterium MWH-VicE1 Blastococcus sp. YIM 65287 offshore copepod from western USA red alga from southern Japan medicinal plant from south-western China marine sediment from Korea oil-polluted soil from Russia freshwater from Uganda AB078044 Km Flexibacteraceae bacterium DG1232 Flexibacteraceae bacterium MOLA 398 Flexibacter aurantiacus subsp. copepodarum Cytophaga sp. I-377 FJ214361 99.8 1 IZ19-1 AB540020 35.48N, 132.78E Shimane, western Japan lake water Spirochaeta sp. MWH-HuW24 AJ565434 97.3 no data IZ20-2 AB540019 35.48N, 132.78E Shimane, western Japan lake water Spirochaeta sp. MWH-HuW24 AJ565434 97.4 no data Shr3 AB540021 33.58N, 10.08E Tunisia sand Desulfovibrio alkalitolerans strain HSRB-E1 GQ863489 84.9 1 Isolate Gammaproteobacteria ArSA Bacterioroides Actinobacteria Spirochaetes Unclassified bacteria a 132.98E 129.08E 10.68E 124.78E 132.78E lake water medicinal plant from south-western China pond water from eastern coastal China pond water from eastern coastal China unknown Similarity. Liquid cultures of each isolate were filtered through three 0.2 mm-pore-size filters. The filtrates were added to R2A medium and observed after three weeks.15 growth was observed, - 5 no growth was observed. b RYOSUKE NAKAI et al. Downloaded from https:/www.cambridge.org/core. IP address: 88.99.165.207, on 17 Jun 2017 at 22:43:03, subject to the Cambridge Core terms of use, available at https:/www.cambridge.org/core/terms. https://doi.org/10.1017/S0954102012000831 Table I. Continued PHYLOGEOGRAPHIC ANALYSIS OF NANO BACTERIA 223 Fig. 1. Neighbour-joining phylogenetic tree based on nearly complete 16S rRNA gene sequences from Rhizobiales and Rhodospirillales strains. The percentages of replicate trees in which the associated taxa clustered together in a bootstrap test (1000 replicates) are shown next to the branches. There were a total of 1259 positions in the final dataset. Origins of the isolates and clones are in round brackets, and nucleotide accession numbers are in square brackets. The scale bar indicates 0.02 substitutions per nucleotide site. dedicated full-length 16S rRNA gene database with a curated taxonomy based on de novo tree inference. The obtained sequences and the highly homologous known sequences were aligned using the CLUSTALX multiple alignment program (Larkin et al. 2007). Phylogenetic trees were constructed based on sequences after alignment using the neighbour joining (NJ) method in MEGA 4.0 (Kumar et al. 2007). Registration of the nucleic acid sequences The 16S rRNA gene sequences obtained in this study have been deposited in the DDBJ/EMBL/GenBank database under the serial accession numbers AB539970–AB540022. Evaluation of cell size under culture conditions using electron microscopy and filtration The cell morphology of isolates was examined with an ultra-high-resolution field-emission scanning electron microscope (FE-SEM) (S-5200, Hitachi High Technologies, Tokyo, Japan). The cells were fixed in 1:20 dilution of 25% glutaraldehyde solution, and an appropriate number of cells were collected on a 0.1-mm-pore Anopore inorganic membrane (Anodisc) filter (Whatman, Tokyo, Japan) for observation. The membrane is composed of an alumina matrix that is manufactured electrochemically. Filter-captured cells were dehydrated with a series of ethanol washes (50%, 70%, 90%, 95%, 97.5%, 99.5%) and air-dried. In order to prevent electrification and to generate clear images during electron microscope observation, dehydrated cells were coated with a c. 100-Å-thick (0.1 mm) layer of platinum via ion sputtering (E-1030, Hitachi High Technologies, Tokyo, Japan). We used E. coli K12 (IFO 3301) as control cells. However, changes in cell morphology were unavoidable during sample preparation, therefore cell size under culture conditions was confirmed by passing culture liquids through three-fold 0.2 mm filters (Advantec, Tokyo, Japan). Concentrated R2A liquid medium (Massa et al. 1998) was added to the filtrate to bring the final media concentration to 13. Because the pores of the filter used for filtration are created by exposure to neutron radiation, a portion of the pores overlap. As filters contain a small number of pores that are larger than the nominal pore size, we minimized the possibility of larger cells passing through by filtering samples or culture suspensions through three layers of filters. The resulting filtrate was incubated for at least three weeks. To confirm the effectiveness on filtration through three-fold 0.2 mm filters, E. coli K12 (IFO 3301) cultures were used as negative growth control. Results and discussion Phylogeny of 0.2 mm-passable bacteria We obtained 53 isolates of 0.2 mm-passable bacteria. The phylogenetic analysis based on 16S rRNA gene sequences classified them into five phyla of Proteobacteria (34 isolates), Bacteroidetes (11), Actinobacteria (5), and Spirochaetes (2), with one unclassified isolate showing less than 85% similarity to known strains and isolates (Table I; BLASTN search results against the Greengenes database are shown in Table SI, which will be found at http:// dx.doi.org/10.1017/S0954102012000831). Of the 34 protobacterial isolates, 15 were affiliated with the class Alphaproteobacteria, 12 with the class Betaproteobacteria, and seven with the class Gammaproteobacteria. No Delta, Epsilon or other proteobacterial isolates, most of the known species of which are microaerobic to anaerobic, were obtained from the collected aerobic samples. Downloaded from https:/www.cambridge.org/core. IP address: 88.99.165.207, on 17 Jun 2017 at 22:43:03, subject to the Cambridge Core terms of use, available at https:/www.cambridge.org/core/terms. https://doi.org/10.1017/S0954102012000831 224 RYOSUKE NAKAI et al. Fig. 2. Distribution of the sample collection sites corresponding to the sequences derived from known isolates and environmental samples related to the Antarctic strain S-19. The x- and y-axes represent 08 latitude and longitude respectively. Sequences related to the S-19 sequence were identified from the DDBJ/EMBL/GenBank database, and grouped by level of similarity to it (97%, 98%, 99%, or 100% similarity: E-value 5 0). The number of sequences similar to the S-19 sequence increased from one to 901 when the similarity threshold was changed from 100% to 97%. Sequences similar to the S-19 sequence on the database but lacking information on country of isolation source were not included in the graphs. Of the 15 Alphaproteobacterial isolates, seven similar isolates were only remotely related (at 92–93% similarity) to the genus Rhizobium, five were closely related (. 98%) to a Phaeospirillum species/strain, two Antarctic isolates (of which the 16S rRNA gene sequences are 100% identical) were almost identical (99.8%) to an Antarctic Mycoplana strain, and one was almost identical (99.8%) to Afipia felis. In contrast, the Betaproteobacterial isolate pool was dominated by a Hylemonella species/strain (10/12 isolates). Gammaproteobacterial isolates were scattered in five genera of Saccharospirillum, Pseudomonas, Oceaniserpentilla, Reinekea, and Vibrio. About half of the Bacteroidetes isolates were affiliated with the genera of Flexibacter, Cytophaga, and Gracilimonas, while the other half was loosely related (at , 96% similarities) to two unidentified Bacteroidetes. Isolates of Actinobacteria and Spirochaetes were closely related (. 97%) to previously reported species/strains. The last isolate ‘‘Shr3’’ from the Sahara is totally unrelated (, 85%) to known cultured organisms and thus is of great taxonomic interest, but will be described and discussed elsewhere. Relative dominance of Proteobacteria and Bacteroidetes is affected by the recovery of isolates belonging to an unnamed group of Rhizobiales and the genus Hylemonella (Proteobacteria) as well as Flexibacter and Cytophaga (Bacteroidetes). To the best of our knowledge this is the first report of 0.2 mm-passable Rhizobiales, although certain Rhizobium species such as R. leguminosarum have shown a negative relationship between cell size and low nutrient conditions (Postma et al. 1988). Our results suggest that this relationship may hold for other groups in the cryosphere. The Hylemonella strains are well-studied 0.2 mm-passable fast-growing freshwater bacteria that have slender spirillum-shaped cell morphology (Wang et al. 2007). Flexibacter and Cytophaga species also exhibit 0.2 mm-passable slender filamentous forms (Hood & MacDonell 1987, Hahn 2004, Hahn et al. 2004) as well as 0.2 mm-passable dwarf cells during their life cycles (Elsaied et al. 2001). Downloaded from https:/www.cambridge.org/core. IP address: 88.99.165.207, on 17 Jun 2017 at 22:43:03, subject to the Cambridge Core terms of use, available at https:/www.cambridge.org/core/terms. https://doi.org/10.1017/S0954102012000831 PHYLOGEOGRAPHIC ANALYSIS OF NANO BACTERIA Phylogeography of 0.2 mm-passable bacteria Generally, microorganisms have large population sizes and very short generation times resulting in high dispersal rates. Studies have shown some protist, fungal, and bacterial taxa with cosmopolitan distribution, rather than restricted geographic distribution (reviewed by Green & Bohannan 2006). The Baas-Becking (or ubiquity) hypothesis is supported by findings that identical bacterial 16S rRNA gene sequences have been detected from lakes in both the Arctic and Antarctic (Pearce et al. 2007). Conversely, there are reports that some microbial taxa have restricted geographic distribution from dispersal limitations, which implies that not all microorganisms can disperse globally (reviewed by Martiny et al. 2006). The seven isolates belonging to the order Rhizobiales were mutually closely related (97.2–100% similarity), and formed a separate cluster within the phylogenetic tree (Fig. 1; phylogenies of all isolates and their closest known sequences are presented in Fig. S1, which will be found at http://dx.doi.org/10.1017/S0954102012000831). This cluster of seven isolates included a clone (GQ264001) isolated from a waste site in North America. In addition, the five isolates belonging to the genus Phaeospirillum (class Alphaproteobacteria) collected in the Arctic, Japan, and China were also mutually closely related (97.2–100% similarity). Given that similar isolates were collected from geographically disparate locations, it would appear that these 0.2 mm-passable bacteria are more ubiquitous in terrestrial environments than aquatic environments. To test this conjecture, it will be necessary to isolate and culture a larger sample of 0.2 mm-passable bacteria from a wider range of terrestrial samples. In contrast, the eight novel strains belonging to the phylum Bacteroidetes isolated from the Arctic and Japan were not mutually closely related (75.5–93.0% similarity). The KNC strain isolated from Japanese river water was very closely related (99.7% similarity) to Microbacteriaceae bacterium MWH-VicE1 belonging to the Luna cluster (phylum Actinobacteria) isolated by Hahn et al. (2004). This cluster consists of strains isolated from lakes and ponds in Europe, East Africa, and China, and is known to be an obligate ultramicrobacterial cluster. The two Antarctic isolates (S-19 and S-42) belonging to the order Rhizobiales isolated from two samples (beach sand and freshwater algal mat) collected from Maritime Antarctica were found to be closely related (99.8% similarity) to Mycoplana sp. ZS1-12 isolated from sandy intertidal sediments of the Larsemann Hills coast (Princess Elizabeth Land, East Antarctica) (Yu et al. 2010). In addition, BLASTN search results showed that the sequence of Antarctic isolate S-19 showed $ 97%, $ 98%, $ 99%, and 100% similarity to 901, 226, 13, and one 16S rRNA gene sequences of known isolates and/or from environmental samples, respectively. The latitudes and longitudes of the 225 sample collection sites corresponding to these sequences are shown in Fig. 2 (accession numbers of all sequences showing $ 97% similarity to each of 0.2 mm-passable isolates, together with their sample collection sites and sources, are listed in Table SII (which will be found at http://dx.doi.org/10.1017/S0954102012000831). Sample collection sites corresponding to the 901 sequences with $ 97% similarity were geographically disparate and from diverse environmental conditions. On the other hand, samples corresponding to 13 sequences with $ 99% similarity included those from cryospheric habitats, such as Ellesmere Island in the Canadian Arctic (one sequence) and Antarctica (five sequences). Sequences closely related ($ 99%) to the S-19 sequence were also isolated from samples collected at the mid-range latitudes: a biofilm found in the Central Alps in Switzerland (one sequence) and glaciers and snow recovered from China (three sequences). These four sequences were also from cryospheric habitats. One sequence 100% identical to S-19 was the other Antarctic isolate (S-42) obtained in this study. In summary, 10 of the 13 sequences with $ 99% similarity to the S-19 sequence (c. 77%) were isolated from samples from cryospheric habitats, such as Arctic, Antarctic, and alpine environments. This implies that such Rhizobiales strains occur in the cryospheric regions, but their abundance and biomass may be scarce depending on the geographic location. In clear contrast to the Antarctic isolate described earlier, Spirochaeta strain IZ-19-1 isolated from lake water collected in western Japan was related to only one Chinese coastal strain. No known isolates or environmental sequences were found to be similar to IZ-19-1 as of June 2011 even with a 97% similarity threshold (Fig. S2 & Table SII, which will be found at http://dx.doi.org/10.1017/ S0954102012000831). This implies that Spirochaeta strain IZ-19-1 belongs to the Asian endemic group that inhabits a restricted region. Candidates of new taxa obtained from 0.2 mm-passable fractions The results of BLASTN searches on the obtained 16S rRNA gene sequences indicate that a total of 18 isolates (seven belonging to the order Rhizobiales (class Alphaproteobacteria), two to the genus Saccharosprillium (class Gammaproteobacteria), eight to the phylum Bacteoidetes, and the isolate ‘‘Shr3’’) were less than 97% homologous with known strains and isolates, suggesting novel taxa at species, genera, class, or even higher levels (Table I). This result may arise as faster-growing bacteria were effectively excluded by filtration (Hahn 2004), allowing isolation of slower-growing bacteria that had been previously undetectable. Even a minor species could be recovered by a culture method designed to select for multiplication of minorities (Pedrós-Alió 2006). Our design Downloaded from https:/www.cambridge.org/core. IP address: 88.99.165.207, on 17 Jun 2017 at 22:43:03, subject to the Cambridge Core terms of use, available at https:/www.cambridge.org/core/terms. https://doi.org/10.1017/S0954102012000831 226 RYOSUKE NAKAI et al. Fig. 3. Scanning electron micrographs of strain KNC (phylum Actinobacteria) that exhibit typical solenoid or crescent-shaped cell morphology. Scale bars 5 1 mm, pore sizes 5 0.1 mm in diameter. was to exclude a majority of fast-growing heterotrophic bacteria by filtration with triple-serial 0.2 mm-pore filters. More than 99.9% of bacterial cells in natural environments are excluded, leaving only a fraction as small as , 0.1% that would pass the filters (Fukuba et al. 2002). As a result, the presence of novel microbial lineages that had previously been obscured by faster-growers was revealed. Cell size of 0.2 mm-passable bacteria under culture conditions Field-emission SEM images of the cell morphology of NP1 and NP3 (genus Phaeospirillum, class Alphaproteobacteria) and IZ6, GB3 and S-42 (order Rhizobiales, class Alphaproteobacteria) showed that the cells were fat and rod-shaped, with minimum diameters between 0.3 and 0.4 mm. In contrast, cells of GB9 (Phaeospirillum) and GB10 (Rhizobiales) were larger, with diameters between 0.5 and 1.0 mm. Larger cells may occur in culture suspensions despite filtration through 0.2 mm filters by cell polymorphism. In the present study, liquid cultures were filtered twice, and although growth activity was observed in the filtrate of GB10 cultures (Table I), no diminutive cells were detected. It is possible that such bacteria that grow larger than 0.2 mm under culture conditions may also generate cells smaller than 0.2 mm temporarily, which passed through the 0.2 mm filters. For example, Cytophaga species have cyclic morphological change, namely young filament and old coccus, and the coccid cells are known to release sub-0.2 mm cells (Elsaied et al. 2001). In the future, detailed observation of cell morphology over the course of all lifecycle stages is needed. IZ16 and NP9 isolates (Rhizobiales), which were seen on FE-SEM to be relatively large, did not grow after secondary filtration, and it is possible that the cells are small in the environment from which the samples were collected. This effect may result from cells entering dormancy and/or entering a viable but non-culturable (VBNC) state in the environment. Cells in these states are typically of reduced size (e.g. Hood & MacDonell 1987), presumably to adapt to low organic concentrations by increasing the surface-to-volume ratio or a starvationsurvival strategy. Alternatively, even though these isolates may form sub-0.2 mm cells at some point of their life cycle, the number of diminutive cells might have been negligible, and the cells were not identified in the filtrate. In genus Afipia (class Alphaproteobacteria), the isolated IZ17 cells were small with minimum diameters between 0.2 and 0.3 mm. Cells of the IZ19-2 isolate (genus Hylemonella, class Betaproteobacteria), the IZ4 isolate (related to an unidentified species belonging to the class Betaproteobacteria), and the ShrSW isolate (genus Oceaniserpentilla, class Gammaproteobacteria) were relatively small and rod-like, with minimum diameters between 0.2 and 0.3 mm. Cells of the KE isolate (genus Vibrio, class Gammaproteobacteria) were extremely small, with a minimum diameter of c. 0.15 mm. Cells of the KIP, KIY, and KOr isolates belonging to the CFB group (phylum Bacteroidetes) were relatively long and rod-like, with maximum diameters between 1.5 and 3.0 mm. No obvious sub-0.2 mm cells were observed among these isolates. Although it is possible that cell morphology is altered by fixation and dehydration, the minimum Downloaded from https:/www.cambridge.org/core. IP address: 88.99.165.207, on 17 Jun 2017 at 22:43:03, subject to the Cambridge Core terms of use, available at https:/www.cambridge.org/core/terms. https://doi.org/10.1017/S0954102012000831 PHYLOGEOGRAPHIC ANALYSIS OF NANO BACTERIA diameters of the cells were between 0.2 and 0.3 mm. These cells are likely to pass through the 0.2 mm pores, not because of their diminutive cell size, but because of their long rod shape. This will need to be validated by other experiments such as detailed observation of the filtrates. Eight of the 11 isolates belonging to the phylum Bacteroidetes grew in the twice-filtered culture. The isolated KNC cells were selenoid and closely related to the obligate UMB belonging to the Luna cluster (phylum Actinobacteria) (Fig. 3). Other members of the Luna cluster have also been reported to form selenoid or crescent-shaped cells (Hahn et al. 2003). The name Luna cluster is derived from this crescent-shaped cell morphology, which may be associated with flexibility and thus 0.2 mm-passability of the cells. Conclusions Phylogeographic analysis of 0.2 mm-passable bacteria in this study demonstrated that some isolates were related closely to geographically very distant strains, while others were found only in a restricted region. Thus, the isolates identified in this study showed diverse distribution patterns. In future, we will consider 0.2 mm-passable bacteria showing characteristic distributions as reference microorganisms to test the Baas-Becking hypothesis. However, the possibility exists that the presence of bacteria in the environment occurred from inadvertent selectivity and/or sampling effort. To validate our results, we would use isolation and phylogenetic identification techniques on the bacteria of the 0.2 mm-filtrable fraction in the cryosphere and other environments. Further studies would require additional techniques such as multi-locus sequence typing and phenotypic characterization. Acknowledgements We are grateful to Drs Synnøve Elvevold and Kim Holmén at the Norwegian Polar Institute and Dr Yoshihide Ohta at University of Oslo, who helped us immensely in conducting the investigation at Svalbard in the Arctic. We are grateful to the crew of the RV Toyoshio-maru, Hiroshima University, and the cruise participants for their on-board assistance. We also acknowledge the Natural Science Centre for Basic Research and Development of Hiroshima University for FE-SEM analysis. This work was supported by a Grant-in-Aid for Scientific Research (No. 18255005) and Research Fellowships for Young Scientists (No. 11J30005) from the Japan Society for the Promotion of Science and a grant from the Institute for Fermentation, Osaka, Japan. Antarctic samples were collected during the Spanish program LIMNOPOLAR International Polar Year 2007–08 campaign with the support of the Spanish Polar Programme, Ministerio de Ciencia e Innovación (POL2006-06635/ANT). This article was published thanks to the financial support given by the Ministerio de Ciencia e 227 Innovación (Spain) with the grant ref. CTM2011-12973-E. The constructive comments of the reviewers are also gratefully acknowledged. Supplemental material Two supplemental figures and two supplemental tables will be found at http://dx.doi.org/10.1017/S0954102012000831 References ALJANABI, S.M. & MARTINEZ, I. 1997. Universal and rapid salt-extraction of high quality genomic DNA for PCR-based techniques. Nucleic Acids Research, 25, 4692–4693. BAAS-BECKING, L.G.M. 1934. Geobiologie of inleiding tot de milieukunde. The Hague: Van Stockum and Zoon, 263 pp. CHEN, B., KOBAYASHI, F., YAMADA, M., KIM, Y., IWASAKA, Y. & SHI, G. 2011. Identification of culturable bioaerosols collected over dryland in northwest China: observation using a tethered balloon. Asian Journal of Atmospheric Environment, 5, 172–180. DELONG, E.F. 1992. Archaea in coastal marine environments. Proceedings of the National Academy of Science of the United States of America, 89, 5685–5869. DESANTIS, T.Z., HUGENHOLTZ, P., LARSEN, N., ROJAS, M., BRODIE, E.L., KELLER, K., HUBER, T., DALEVI, D., HU, P. & ANDERSEN, G.L. 2006. Greengenes: chimera-checked 16S rRNA gene database and workbench compatible with ARB. Applied and Environmental Microbiology, 72, 5069–5072. DMITRIEV, V.V., DUDA, V.I., SUZINA, N.E., AKIMOV, V.N., VAINSHTEIN, M.B., BARINOVA, E.S., ABASHINA, T.N., OLEYNIKOV, R.R., ESIKOVA, T.Z. & BORONIN, A.M. 2007. Ultrastructural organization and development cycle of soil ultramicrobacteria belonging to the class Alphaproteobacteria. Microbiology, 76, 575–584. ELSAIED, H.E., SATO, M. & NAGANUMA, T. 2001. Viable Cytophaga-like bacterium in the 0.2 mm-filtrate seawater. Systematic and Applied Microbiology, 24, 618–622. FUKUBA, T., ELSAIED, H.E. & NAGANUMA, T. 2002. Overlooked microbial agents in aquaculture: nanobacteria. In LEE, C.S. & O’BRYEN, P., eds. Microbial approaches to aquatic nutrition within environmentally sound aquaculture production systems. Baton Rouge, LA: World Aquaculture Society, 99–107. GEISSINGER, O., HERLEMANN, D.P., MORSCHEL, E., MAIER, U.G. & BRUNE, A. 2009. The ultramicrobacterium ‘‘Elusimicrobium minutum’’ gen. nov., sp. nov., the first cultivated representative of the termite group 1 phylum. Applied Environmental Microbiology, 75, 2831–2840. GREEN, J. & BOHANNAN, B.J. 2006. Spatial scaling of microbial biodiversity. Trends in Ecology & Evolution, 21, 501–507. HAHN, M.W. 2003. Isolation of strains belonging to the cosmopolitan Polynucleobacter necessarius cluster from freshwater habitats located in three climatic zones. Applied Environmental Microbiology, 69, 5248–5254. HAHN, M.W. 2004. Broad diversity of viable bacteria in ‘sterile’ (0.2 mm) filtered water. Research in Microbiology, 155, 688–691. HAHN, M.W., STADLER, P., WU, Q.L. & POCKL, M. 2004. The filtrationacclimatization method for isolation of an important fraction of the not readily cultivable bacteria. Journal of Microbiological Methods, 57, 379–390. HAHN, M.W., LANG, E., BRANDT, U., WU, Q.L. & SCHEUERL, T. 2009. Emended description of the genus Polynucleobacter and the species Polynucleobacter necessarius and proposal of two subspecies, P. necessarius subsp. necessarius subsp. Nov. and P. necessarius subsp. asymbioticus subsp. nov. International Journal of Systematic and Evolutionary Microbiology, 59, 2002–2009. HAHN, M.W., LUNSDORF, H., WU, Q.L., SCHAUER, M., HOFLE, M.G., BOENIGK, J. & STADLER, P. 2003. Isolation of novel ultramicrobacteria classified as Actinobacteria from five freshwater habitats in Europe and Asia. Applied Environmental Microbiology, 69, 1442–1451. Downloaded from https:/www.cambridge.org/core. IP address: 88.99.165.207, on 17 Jun 2017 at 22:43:03, subject to the Cambridge Core terms of use, available at https:/www.cambridge.org/core/terms. https://doi.org/10.1017/S0954102012000831 228 RYOSUKE NAKAI et al. HALLER, C.M., ROLLEKE, S., VYBIRAL, D., WITTE, A. & VELIMIROV, B. 2000. Investigation of 0.2 mm filterable bacteria from the western Mediterranean Sea using a molecular approach: dominance of potential starvation forms. FEMS Microbiology Ecology, 31, 153–161. HOBBIE, J.E., DALEY, R.J. & JASPER, S. 1977. Use of nucleopore filters for counting bacteria by fluorescence microscopy. Applied and Environmental Microbiology, 33, 1225–1228. HOOD, M.A. & MACDONELL, M.T. 1987. Distribution of ultramicrobacteria in a gulf-coast estuary and induction of ultramicrobacteria. Microbial Ecology, 14, 113–127. JAMTVEIT, B., HAMMER, O., ANDERSSON, C., DYSTHE, D.K., HELDMANN, J. & VOGEL, M.L. 2006. Travertines from the Troll thermal springs, Svalbard. Norwegian Journal of Geology, 86, 387–395. KUMAR, S., TAMURA, K., DUDLEY, J. & NEI, M. 2007. MEGA4: molecular evolutionary genetics analysis (MEGA) software version 4.0. Molecular Biology and Evolution, 24, 1596–1599. LARKIN, M.A., BLACKSHIELDS, G., BROWN, N.P., CHENNA, R., MCGETTIGAN, P.A., MCWILLIAM, H., VALENTIN, F., WALLACE, I.M., WILM, A., LOPEZ, R., THOMPSON, J.D., GIBSON, T.J. & HIGGINS, D.G. 2007. Clustal W and Clustal X version 2.0. Bioinformatics, 23, 2947–2948. MACDONELL, M.T. & HOOD, M.A. 1982. Isolation and characterization of ultramicrobacteria from a gulf coast estuary. Applied and Environmental Microbiology, 43, 566–571. MANILOFF, J. 1997. Nanobacteria: size limits and evidence. Science, 276, 1776. MARTINY, J.B.H., BOHANNAN, B.J.M., BROWN, J.H., COLWELL, R.K., FUHRMAN, J.A., GREEN, J.L., HORNER-DEVINE, M.C., KANE, M., KRUMINS, J.A., KUSKE, C.R., MORIN, P.J., NAEEM, S., ØVREÅS, L., REYSENBACH, A-L., SMITH, V.H. & STALEY, J.T. 2006. Microbial biogeography: putting microorganisms on the map. Nature Reviews Microbiology, 4, 102–112. MASSA, S., CARUSO, M., TROVATELLI, F. & TOSQUES, M. 1998. Comparison of plate count agar and R2A medium for enumeration of heterotrophic bacteria in natural mineral water. World Journal of Microbiology & Biotechnology, 14, 727–730. MITEVA, V.I. & BRENCHLEY, J.E. 2005. Detection and isolation of ultrasmall microorganisms from a 120,000-year-old Greenland glacier ice core. Applied and Environmental Microbiology, 71, 7806–7818. MIYOSHI, T., IWATSUKI, T. & NAGANUMA, T. 2005. Phylogenetic characterization of 16S rRNA gene clones from deep-groundwater microorganisms that pass through 0.2 micrometer-pore-size filters. Applied and Environmental Microbiology, 71, 1084–1088. MUSHEGIAN, A.R. & KOONIN, E.V. 1996. A minimal gene set for cellular life derived by comparison of complete bacterial genomes. Proceedings of the National Academy of Science of the United States of America, 93, 10 268–10 273. NAGANUMA, T., MIYOSHI, T. & KIMURA, H. 2007. Phylotype diversity of deep-sea hydrothermal vent prokaryotes trapped by 0.2 and 0.1-mm-pore-size filters. Extremophiles, 11, 637–646. NAKAI, R., ABE, T., TAKEYAMA, H. & NAGANUMA, T. 2011. Metagenomic analysis of 0.2 mm-passable microorganisms in deep-sea hydrothermal fluid. Marine Biotechnology, 13, 900–908. PEARCE, D.A., COCKELL, C.S., LINDSTROM, E.S. & TRANVIK, L.J. 2007. First evidence for a bipolar distribution of dominant freshwater lake bacterioplankton. Antarctic Science, 19, 245–252. PEDRÓS-ALIÓ, C. 2006. Marine microbial diversity: can it be determined? Trends in Microbiology, 14, 257–263. POSTMA, J., VANELSAS, J.D., GOVAERT, J.M. & VANVEEN, J.A. 1988. The dynamics of Rhizobium leguminosarum biovar. trifolii introduced into soil as determined by immunofluorescence and selective plating techniques. FEMS Microbiology Ecology, 53, 251–259. QUESADA, A., CAMACHO, A., ROCHERA, C. & VELÁZQUEZ, D. 2009. Byers Peninsula: a reference site for coastal, terrestrial and limnetic ecosystem studies in Maritime Antarctica. Polar Science, 3, 181–187. TORRELLA, F. & MORITA, R.Y. 1981. Microcultural study of bacterial size changes and microcolony and ultramicrocolony formation by heterotrophic bacteria in seawater. Applied and Environmental Microbiology, 41, 518–527. WANG, Y., HAMMES, F., BOON, N. & EGLI, T. 2007. Quantification of the filterability of freshwater bacteria through 0.45, 0.22, and 0.1 mm pore size filters and shape-dependent enrichment of filterable bacterial communities. Environmental Science & Technology, 41, 7080–7086. WATSON, S.W., NOVITSKY, T.J., QUINBY, H.L. & VALOIS, F.W. 1977. Determination of bacterial number and biomass in the marine environment. Applied and Environmental Microbiology, 33, 940–946. YU, Y., LI, H.R., ZENG, Y.X. & CHEN, B. 2010. Phylogenetic diversity of culturable bacteria from Antarctic sandy intertidal sediments. Polar Biology, 33, 869–875. ZIMMERMANN, R. 1977. Estimation of bacterial number and biomass by epifluorescence microscopy and scanning electron microscopy. In RHEINHEIMER, G., ed. Microbial ecology of a brackish water environment. Berlin: Springer, 103–120. Downloaded from https:/www.cambridge.org/core. IP address: 88.99.165.207, on 17 Jun 2017 at 22:43:03, subject to the Cambridge Core terms of use, available at https:/www.cambridge.org/core/terms. https://doi.org/10.1017/S0954102012000831
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