Abstract
The family Phyllobacteriaceae belongs to the order Rhizobiales in the Alphaproteobacteria and currently comprises the 72 species in 13 genera: Ahrensia, Aliihoeflea, Aminobacter (including Chelatobacter), Aquamicrobium (including Defluvibacter), Chelativorans, Hoeflea, Lentilitoribacter, Mesorhizobium, Nitratireductor, Phyllobacterium, Pseudahrensia, Pseudaminobacter, and Thermovum. They form a single cluster within the 16S rRNA gene phylogeny. The family consists of environmental (soil, water) and plant-associated bacteria that have a heterotrophic respiratory metabolism with oxygen as terminal electron acceptor. One Aquamicrobium species can use nitrate as an alternative terminal electron acceptor. One Mesorhizobium species is facultatively chemolithotrophic using thiosulfate or elemental sulfur as sole energy source. Candidatus Liberibacter, a group of uncultivated phloem-inhabiting bacteria that are associated with various plant diseases in citrus and Solanaceae or are endophytic in pear plants, is also associated with the family. However, comprehensive phylogenetic analyses indicate the position of this group as a member of the Phyllobacteriaceae is uncertain.
Access provided by Autonomous University of Puebla. Download reference work entry PDF
Similar content being viewed by others
Keywords
These keywords were added by machine and not by the authors. This process is experimental and the keywords may be updated as the learning algorithm improves.
Taxonomy, Historical and Current
Short Description of the Family
Phyl.lo.bac.te.ri.a’ce.ae. N.L. neut. n. Phyllobacterium, type genus of the family; suff. -aceae, suffix to denote a family; N.L. fem. pl. n. Phyllobacteriaceae, the Phyllobacterium family.
The family Phyllobacteriaceae belongs to the Rhizobiales order in the Alphaproteobacteria class of the phylum Proteobacteria. It was proposed by Mergaert and Swings (2005a) in Bergey’s Manual of Systematic Bacteriology and was validated in 2006. At the time the family comprised six genera and one Candidatus genus: Phyllobacterium, Aminobacter, Aquamicrobium, Defluvibacter, Candidatus Liberibacter, Mesorhizobium, and Pseudaminobacter. Defluvibacter has since been transferred to Aquamicrobium (Kämpfer et al. 2009). Aminobacter includes Chelatobacter heintzii which is regarded as a later subjective synonym of Aminobacter aminovorans (Kämpfer et al. 2002). The basis for the proposal of this family was that these genera form a cluster in the 16S rRNA gene phylogeny. The description of the family (Mergaert and Swings 2005a) is rather brief: “Rod-shaped, ovoid, or reniform cells when cultured in vitro. Nonsporeforming. Gram negative. Aerobic. Cells cultured in vitro are motile by means of polar, subpolar, or lateral flagella. Strains grow well on complex solid media at 28 °C. Occur in leaf nodules and the rhizosphere of higher plants. The mol % G+C of the DNA is 60–62”. With the inclusion of the additional genera Ahrensia, Chelativorans, Hoeflea, Lentilitoribacter, Nitratireductor, Pseudahrensia, and Thermovum to the Phyllobacteriaceae cluster, most of this definition still applies except that cells can also be nonmotile and members of the family can also occur in seawater, marine sediments, activated sludge, and soil and thermophilic members are found in compost. The range of the G+C content of DNA is 48–65 %. Comprehensive phylogenetic analysis reveals that the position of Candidatus Liberibacter as a member of the Phyllobacteriaceae cluster is uncertain (see below).
Phylogenetic Structure of the Family and Its Genera
In the 16S rRNA gene phylogeny, the Phyllobacteriaceae family forms a single cluster in the phylum Alphaproteobacteria, and inside this large cluster, the different species generally group together per genus, in support of the current taxonomy (Fig. 18.1 ).
An important exception is the genus Mesorhizobium: these species make up several groups and separate lineages grouping in between the other genus clusters (Fig. 18.1 ). The type species Mesorhizobium loti forms tight subcluster with Mesorhizobium ciceri, Mesorhizobium australicum, Mesorhizobium shangrilense, Mesorhizobium sangaii, and Mesorhizobium qingshengii. Mesorhizobium chacoense forms a separate but related lineage, and the Aminobacter cluster is their nearest neighbor. Nineteen species form the largest subcluster: Mesorhizobium metallidurans, Mesorhizobium temperatum, Mesorhizobium mediterraneum, Mesorhizobium gobiense, Mesorhizobium tarimense, Mesorhizobium caraganae, Mesorhizobium robiniae, Mesorhizobium muleiense, Mesorhizobium tianshanense, Mesorhizobium tamadayense, Mesorhizobium amorphae, Mesorhizobium septentrionale, Mesorhizobium huakuii, Mesorhizobium plurifarium, Mesorhizobium silamurunense, Mesorhizobium opportunistum, Mesorhizobium abyssinicae, Mesorhizobium hawassense, and Mesorhizobium shonense. Mesorhizobium albiziae groups at the periphery of this subcluster as does Mesorhizobium thiogangeticum. The position of the two latter species, however, varied depending on the filter applied. In most trees, it constitutes a separate lineage at some distance from other Mesorhizobium subclusters or other genera of the family. Mesorhizobium thiogangeticum was not recovered from legume nodules but was isolated from soil by enrichment using reduced sulfur compounds as sole electron sources; it is the only Mesorhizobium species reported to be facultatively chemolithoautotrophic. Two other species, Mesorhizobium camelthorni and Mesorhizobium alhagi, make up a further subcluster that groups most closely to the Chelativorans cluster. The 16S rRNA gene phylogeny of Mesorhizobium is thus polyphyletic, and the genus may in the future require taxonomic rearrangements if further evidence would support these observations.
Ahrensia and Lentilitoribacter group together with Hoeflea species, but, according to branch length, are clearly distinct.
Nitratireductor species form a single cluster, except for Nitratireductor basaltis which is located separately.
Candidatus Liberibacter, consisting of psyllid-transmitted, as yet uncultured, phloem-limited bacteria associated with greening disease or huanglongbing disease of citrus and yellows disease of various Solanaceae plants or endophytic in pear plants, was initially placed inside the Phyllobacteriaceae based on a limited phylogenetic indications (Mergaert and Swings 2005a; Garnier 2005). A more comprehensive analysis performed for this chapter revealed that the position of Candidatus Liberibacter as a member of the Phyllobacteriaceae cluster is uncertain. Although it does group on a long branch inside the Phyllobacteriaceae cluster in Fig. 18.1 , in most other trees calculated using other filters and including other neighboring taxa, Candidatus Liberibacter grouped outside the family and occupied a separate position in the Alphaproteobacteria. Its membership of the family therefore seems not strongly supported by 16S rRNA phylogeny.
Comments on the Membership of the Family
Although the genus Ahrensia is was classified in the Rhodobacteraceae in Bergey’s Manual of Systematic Bacteriology (Garrity et al. 2005) based on the phylogenetic analysis of 16S rRNA genes, since then more taxa have been described in the Rhizobiales, and current 16S rRNA gene phylogeny places Ahrensia in the Phyllobacteriaceae (Living Tree Project, release 111). It is therefore included in this chapter.
“Aliihoeflea aestuarii” gen. nov., sp. nov. was described for a bacterium isolated from tidal flat sediments (Roh et al. 2008). Its 16S rRNA gene sequence was reported to cluster with members of the Phyllobacteriaceae. Fatty acid data, quinone, and DNA G+C content data are also in agreement with the family characteristics; therefore, although Aliihoeflea aestuarii has as yet not been included in a validation list, it is included here in the chapter on Phyllobacteriaceae.
Molecular Analyses
DNA-DNA Hybridization Studies
In all multispecies genera of the family, DNA-DNA hybridizations with existing species have been performed to justify proposals of new species.
Other Sequence Analyses
Genes other than the 16S rRNA gene have been reported in Mesorhizobium where recA sequences are available for all species and a number of other genes including atpD, gyrB, dnaK, and rpoB have also been reported for several of the Mesorhizobium species. However, for other Phyllobacteriaceae genera, only in a few cases have other genes been reported and used for phylogenetic purposes: for three of six Aminovorans species sequences are available for atpD, dnaK, and recA (Maynaud et al. 2012); for four of eight Phyllobacterium species, an atpD sequence has been reported, as well as a recA sequence for one species (Mantelin et al. 2006b), and for two of six Nitratireductor species, an rpoD sequence is available (unpublished data available through NCBI dataportal). Given this lack of data for all genera, it is currently not possible to comprehensively assess the phylogeny of the family using a housekeeping gene other than the 16S rRNA gene. At present most data are available for recA where 6 of the 13 genera are represented (three of these are extracted from total genome information). Given that Mesorhizobium is represented with 30 species versus only 8 species from other genera, this tree (Fig. 18.2 ) does not permit a comprehensive comparison with the 16S rRNA gene phylogeny (Fig. 18.1 ). It thus remains to be established whether the subclusters of Mesorhizobium in the latter phylogeny are confirmed by recA or other gene phylogenies.
Genome Comparisons
Only in recent years have some complete genome sequences been reported or drafts made available. An overview of the type strains and a few other strains is given in Table 18.1 . Unpublished draft genomes are available in public database online for Ahrensia kielensis, Chelativorans sp., Hoeflea phototrophica, Mesorhizobium australicum, Mesorhizobium ciceri bv. biserrulae, and Mesorhizobium opportunistum (Table 18.1 ).
The genome of Mesorhizobium loti MAFF303099 was reported more than 10 years ago (Kaneko et al. 2000); however, later this strain was shown to be a representative of another Lotus symbiont, Mesorhizobium huakuii bv. loti (Turner et al. 2002). Its genome consists of one chromosome (7 Mb) and two megaplasmids (352 kb and 208 kb); a transmissible symbiotic island containing 580 protein-encoding genes including genes for nodulation and nitrogen fixation was identified on the chromosome, inserted into the phe-tRNA gene as in other Mesorhizobium loti strains (Kaneko et al. 2000). The genomes of several other Mesorhizobium strains have been sequenced and had a similar size between 6.2 and 7.6 Mb with one circular chromosome and either no, one or two megaplasmids (Table 18.1 ). Mesorhizobium amorphae CCNWGS0123 is a copper-resistant rhizobium that contributes to survival of the host plant in copper-, zinc-, and chromium-containing environments. Its genome was found to harbor numerous genes involved in copper resistance including a copper efflux system and multicopper oxidases, as well as various genes for plant growth promotion that most rhizobia share. In addition genes involved in the biosynthesis of a number of antibiotics and in chloramphenicol resistance were present (Hao et al. 2012). Mesorhizobium alhagi CCNWXJ12-2T is very resistant to salt (0.8 M) and alkali (pH 12). Its genome was found to encode various systems contributing to salt resistance and osmoregulation including multiple membrane transport system (Zhou et al. 2012).
The genomes have been reported for three Nitratireductor strains. For the type species, Nitratireductor aquibiodomus strain RA22 from a marine water sample in India has been sequenced; its 16S rRNA gene was reported as 100 % identical to that of the type strain. Annotation revealed genes for iron acquisition, ammonia and sulfur assimilation, biosynthesis of ectoine and betaine, and uptake of choline and betaine, indicative of its marine habitat requiring osmotic stress tolerance. Genes for catabolism of aromatic compounds, including genes for the chloroaromatic degradation pathway, correspond with the observation that many Nitratireductor strains were obtained from sources contaminated with pyrene, crude oil, or pesticide (Singh et al. 2012). Nitratireductor pacificus pht-3BT, although isolated from a pyrene-degrading consortium from deep-sea sediments, is unable to utilize pyrene, and this was confirmed by the absence of polycyclic aromatic hydrocarbon (PAH)-degrading dioxygenase in its genome (Lai et al. 2012a). Nitratireductor indicus C115T originates from a crude oil-degrading consortium from deep seawater; however, it cannot degrade n-alkanes or PAHs as sole carbon source. Also here, the genome sequence confirmed the absence of any alkane-degrading monooxygenase or PAH-degrading dioxygenase (Lai et al. 2012b).
Two complete genomes have been reported representing Candidatus Liberibacter, a group of uncultured bacteria associated with citrus and Solanaceae plant diseases; genomes were obtained from DNA isolated from the phloem-feeding psyllid vectors that transmit the pathogen (Duan et al. 2009; Lin et al. 2011). As can be expected for obligate intracellular endophytes, the genomes are small and have a low GC content: 0.99 Mb and 36.5 mol % and 1.26 Mb and 35.2 mol % for Candidatus Liberibacter asiaticus psy62 and Candidatus Liberibacter solanacearum CLso-ZC1, respectively. Candidatus Liberibacter asiaticus psy62 harbored few genes for the biosynthesis of compounds that can be obtained from the host and more genes for motility such as type IV pili and flagellar genes; it had no transposons or insertion elements but did have some phage-related genes (Duan et al. 2009). Its genome also revealed the absence of several key components required for oxidative phosphorylation and several terminal oxidases, pointing to a limited potential for aerobic respiration; genome analysis suggests that the organism cannot reduce sulfur compound, but instead anaerobic respiration is coupled to nitrogen metabolism. The presence of an active TCA cycle suggests that a range of amino acids (present in phloem fluid) may serve as energy sources (Duan et al. 2009). Candidatus Liberibacter solanacearum shares 884 protein-encoding genes with Candidatus Liberibacter asiaticus. Comparison of both genomes revealed many rearrangements and gene losses/gains (Lin et al. 2011). Candidatus Liberibacter solanacearum also contained several small and two large phage-derived segments, one of which was similar to a segment in Candidatus Liberibacter asiaticus. The analysis of its gene repertoire suggests it can take up glucose but not sucrose or fructose and has limited capacity for aerobic respiration and for the biosynthesis of amino acids and lacks a complete restriction-modification system. It has several transport systems for amino acids and a system (NttA) for the uptake of ATP and ADP from the host. The comparison further revealed that Candidatus Liberibacter solanacearum has reduced capacity for nucleic acid modification, increased potential for amino acid and vitamin biosynthesis, and a high-affinity iron transport system (Lin et al. 2011). Lin et al. (2011) point out that the approach of extracting bacterial genome information from the vector does not exclude that other genetic components such as plasmids or linear chromosomes could be present.
Based on the complete genome (Duan et al. 2009; Tyler et al. 2009), a computational analysis of the Candidatus Liberibacter asiaticus proteome has been performed, and the results predicting 3D structure, function, cellular localization, and potential virulence factors are publically available (http://prodata.swmed.edu/liberibacter_asiaticus/curated/) as a tool for further study of this pathogen (Cong et al. 2012).
Phenotypic Analyses
A comparison of some general features of the members of the Phyllobacteriaceae is given in Table 18.2 .
Ahrensia Uchino et al. 1999, 1VL
Ah.ren’si.a. N.L. fem. n. Ahrensia, named in honor of R. Ahrens, a German microbiologist, for his contribution to the taxonomy of marine species of Agrobacterium.
The genus Ahrensia comprises rod-shaped cells that do not form spores. They are motile with polar flagella. Aerobic and oxidase and catalase positive. The major quinone is ubiquinone Q10; the major fatty acid is C18:1; the main hydroxy fatty acid is C12:0 3-OH. No 2-hydroxy fatty acids are present. The G+C content of the DNA is 48 mol %. The type species is Ahrensia kielensis.
The following description of Ahrensia kielensis is based on those from Uchino et al. (1998) and from Rüger and Höfle (1992). The species is able to grow at 5 °C, but not at 37 °C. Na+ is required. Cells are motile rods, 0.6–1.0 × 2.0–4.0 μm. Hardly any carbon sources are used: the type strain tested negative for 12 carbohydrates, 11 carboxylic acids, 3 alcohols, 7 amino acids, and putrescine (Rüger and Höfle 1992). H2S is produced from cysteine; hydrolysis of gelatin and starch is negative. Nitrate is not reduced to nitrite or gas. Acids are produced from fructose, maltose, xylose, and glycerol after 4–6 weeks of incubation. Negative in the following tests: indole production, methyl red, Voges-Proskauer, lysine and ornithine decarboxylase, and hydrolysis of casein, chitin, and alginate.
The major fatty acid is C18:1 ω7c; C12:0 3-OH and iso-C13:0 3-OH are present, but 2-hydroxy fatty acids are absent (Uchino et al. 1998; Park et al. 2013). The G+C content of the DNA is 48 mol %.
The type strain IAM 12618T was isolated from seawater of the Baltic Sea.
Aliihoeflea Roh et al. 2008
A.li.i.ho.e.fle’a, L. adj. and pronoun alius, other, another, different; N.L. fem. n. Hoeflea, a bacterial genus name; N.L. fem. n. Aliihoeflea, the other Hoeflea.
Aliihoeflea comprises rod-shaped cells that are catalase and oxidase positive. The major quinone is ubiquinone Q10; the major fatty acids are C18:1 ω7c and C19:0 cyclo ω8c. G+C content is approximately 53 mol %. The type species is Aliihoeflea aestuarii.
The following description of the phenotype is based on the description of the strain N8T, thus far the only strain of Aliihoeflea aestuarii (Roh et al. 2008). Cells are rod shaped (0.50–0.75 μm × 1.25–1.50 μm). Colonies on MA are circular with entire margin, convex, shiny, and cream colored. Growth is also possible on Trypticase soy agar, SA, LA, and yeast mannitol agar, but not on R2A. Temperature range for growth is 17–37 °C; the optimal growth temperature is 30 °C. Optimal NaCl concentration is 1 % (w/v), although NaCl is not required and up to 8 % is tolerated during growth. Nitrates are not reduced to nitrites or nitrogen. Indole is not produced. Glucose is not fermented, and hydrolysis of starch, esculin, gelatin, and PNPG (p-nitrophenyl-β-d-galactopyranoside) is negative. Urease positive and arginine dihydrolase negative. Glycogen, Tween 80, l-arabinose, d-fructose, pyruvic acid methyl ester, succinic acid monomethyl ester, acetic acid, α-hydroxybutyric acid, β-hydroxybutyric acid, γ-hydroxybutyric acid, α-ketobutyric acid, α-ketoglutaric acid, α-ketovaleric acid, d,l-lactic acid, succinic acid, succinamic acid, l-alaninamide, d-alanine, l-alanine, l-glutamic acid, glycyl-l-glutamic acid, l-leucine, l-serine, inosine, uridine, and thymidine can be used as sole carbon sources. Positive for alkaline phosphatase, esterase (C4), esterase lipase (C8), leucine arylamidase, valine arylamidase, cystine arylamidase, trypsin, α-chymotrypsin, naphthol-AS-BI-phosphohydrolase. Negative for lipase (C14), acid phosphatase, α-galactosidase, β-galactosidase, β-glucuronidase, α-glucosidase, β-glucosidase, N-acetyl-β-glucosaminidase, α-mannosidase, and α-fucosidase. The genomic DNA G+C content is 53.4 mol %. The type strain KCTC 22052T was isolated from tidal flat sediment in Yeosu (34°47′26″ N 127°34′01″ E), Republic of Korea.
Aminobacter Urakami et al. 1992, 90VP
Am.i.no.bac’ter, N.L. n. aminum, amine; N.L. masc. n. bacter, rod; N.L. masc.n. Aminobacter, amine rod.
The genus Aminobacter comprises non-spore-forming rod-shaped cells that can utilize methylamine. Cells are motile by means of subpolar flagella. They multiply by budding. Poly-β-hydroxybutyrate granules are accumulated in the cells. Good growth in nutrient broth and PYG broth. No water-soluble fluorescent pigment is produced. No growth factors are required. Oxidase and catalase positive and urease negative. Aerobic respiratory metabolism, not fermentative (Urakami et al. 1992).
The following tests are negative: methyl red, Voges-Proskauer, indole production, hydrogen sulfide production, hydrolysis of gelatin and starch, denitrification, litmus milk, and fermentation of sugars.
Ammonia is produced. Acids are produced from sugars oxidatively. Monomethylamine, trimethylamine, trimethylamine-N-oxide, and sugars are utilized. Methanol, methane, and hydrogen are not utilized. Ammonia, nitrate, urea, peptone, and methylamine are utilized as nitrogen sources.
Good growth occurs at pH 6.0–8.0 and at 30–37 °C. No growth above pH 9.0 and below pH 5.0 at 42 °C and in the presence of 3 % NaCl (Urakami et al. 1992).
The type strains of all species can utilize l-arabinose and l-alanine; none can use adonitol (McDonald et al. 2005; Maynaud et al. 2012). McDonald et al. (2005) performed a biochemical characterization of all Aminobacter species except Aminobacter anthyllidis and found that all type strains could utilize N-acetyl-d-glucosamine, d-cellobiose, d-fructose, d-galactose, d-glucose, d-mannose, d-maltose, d-ribose, d-xylose, i-inositol, d-mannitol, d-sorbitol, acetate, 4-aminobutyrate, dl-3-hydroxybutyrate, dl-lactate, oxoglutarate, l-histidine, l-leucine, l-ornithine, and l-proline and hydrolyze bis-para-nitrophenyl (pNP)-phosphate, pNP-phenyl-phosphonate, l-alanine-para-nitroanilide (pNA), and l-proline-pNA. None of the strains could utilize p-arbutin, α-d-melibiose, salicin, maltitol, putrescine, cis-aconitate, trans-aconitate, adipate, azelate, citrate, fumarate, itaconate, mesaconate, suberate, l-phenylalanine, 3-hydroxybenzoate, and phenylacetate. All type strains used sucrose. None of the strains could hydrolyze esculin, pNP-β-d-galactopyranoside, pNP-β-d-glucuronide, 2-deoxythymidine-5′-pNP-phosphate, and l-glutamate-γ-3-carboxy-pNA and none produced acid from lactose, adonitol, rhamnose, methyl d-glucoside, erythritol, and melibiose. Additional features and differentiating characteristics of the species are shown in Table 18.3 .
Only strains of Aminobacter ciceronei and Aminobacter lissarensis utilize several methyl halides as sole carbon sources (Table 18.3 ). Of all Aminobacter strains tested, two strains of Aminobacter ciceronei (ER2 and C147; not the type strain) were the sole Aminobacter strains that could degrade atrazine and carbofuran (McDonald et al. 2005). Aminobacter anthyllidis, which is capable of nodulation and was isolated from a Zn-Pb mining site through trapping with Anthyllis vulneraria, can tolerate 1–2 mM of Zn and 0.3–1 mM of Cd in YEM broth after 1 week (Maynaud et al. 2012).
The DNA base composition ranges from 62 to 64 mol % G + C. The main cellular fatty acids include C18:1, and the main hydroxy fatty acids include C12:0 3-OH. The ubiquinone system is ubiquinone Q10.
The type species is Aminobacter aminovorans, originally described as Pseudomonas aminovorans (Urakami et al. 1992).
Aquamicrobium Bambauer et al. 1998, 631VL emend. Lipski and Kämpfer 2012
A.qua.mi.cro’bi.um, L. n. aqua, water; N.L. neut. n. microbium, a microbe; N.L. neut. n. Aquamicrobium, a bacterium living in water/wastewater.
This description is based on the emended description of Lipski and Kämpfer (2012). Aquamicrobium consists of pleomorphic or regularly shaped short rods that are mesophilic and grow best at pH 6–9. They can tolerate up to 7 % NaCl (w/v) and utilize sugars, carbonic acids, amino acids, and alcohols for growth. Major quinone is Q10, major fatty acid is C18:1 cis-11, major polyamine is spermidine, and main polar lipids are phosphatidylglycerol, phosphatidylcholine, and phosphatidylethanolamine. G+C content of the DNA is 57–65 mol %. The type species is Aquamicrobium defluvii.
A number of phenotypic and other characteristics of the Aquamicrobium type strains are listed in Table 18.4 . All species are oxidase and catalase positive. Aquamicrobium defluvii is able to utilize thiophene-2-carboxylate as sole carbon source in the presence of molybdate (Bambauer et al. 1998). In addition, acetate, propionate, butyrate, crotonate, glucose, fructose, mannose, xylose, mannitol, and sorbitol are used for growth with oxygen or nitrate as electron acceptors. Nitrate is reduced to nitrite. No growth was observed with thiophene-2-acetate, thiophene-3-carboxylate, thiophene-3-acetate, thiophene-2-carbaldehyde, thiophene-2-methanol, thiophene-2-mandelate, thiophene-2-acrylate, thiophene, benzothiophene, dibenzothiophene, pyrrole-2-carboxylate, furan-2-carboxylate, pyridine, nicotinate, benzoate, phenylacetate, phthalate, galactose, ribose, sorbose, maltose, saccharose, cellobiose, and lactose. Hydrolysis of gelatin, arginine dihydrolase, lysine decarboxylase, and urease is negative (Bambauer et al. 1998). Aquamicrobium lusatiense is able to degrade 4-chlorophenol, 2,4-dichlorophenol, and phenol, and this capacity was not lost over repeated transfers and attempts at curing. Indeed, genes for chlorocatechol 1,2-dioxygenase and 2,4-dichlorophenol hydroxylase were shown to be located on the chromosome rather than on a megaplasmid (Fritsche et al. 1999). Hydrolysis of urea, starch, gelatin, casein, DNA, Tween 80, and esculin is negative (Fritsche et al. 1999). Aquamicrobium aerolatum is positive for phosphatase and l-alanine aminopeptidase (Kämpfer et al. 2009).
Small amounts of 12:0 3-OH were reported for Aquamicrobium defluvii and Aquamicrobium lusatiense and iso-15:0 3-OH for Aquamicrobium aerolatum by Kämpfer et al. (2009), but a later study comprising all species did not find hydroxy fatty acids (Lipski and Kämpfer 2012).
Chelativorans Doronina et al. 2010, 1047VP
Che.la’ti.vo.rans. N.L. n. chelatum, a chelate; L. part. adj. vorans, devouring; N.L. masc. n. Chelativorans, a bacterium digesting metal chelates.
Chelativorans strains are non-spore-forming rods. The genus was described as nonmotile (Doronina et al. 2010), although flagella were later reported for Chelativorans multitrophicus DSM 9103T and several Chelativorans sp. strains (Kaparullina et al. 2011). They often occur as pairs and multiply by binary fission. They form small white colonies on EDTA/mineral salt agar (diameter 0.1–0.3 mm after 7 days at 30 °C). Optimal NaCl concentration for growth is 1.5 %. No PHB inclusions; electron dense inclusions are thought to consist of calcium and magnesium phosphates and are absent in cells grown on fumarate. Oxidase and catalase positive; indole is produced; no nitrate reduction to nitrite; no nitrogen fixation. Optimal temperature and pH for growth are 25–35 °C and 6.5–7.5. Aerobic respiratory metabolism; able to use EDTA as carbon, nitrogen and energy source, either facultatively (Chelativorans multivorans) or obligately (Chelativorans oligotrophicus). No autotrophic or methylotrophic growth; unable to use methanol or methylated amines as carbon, nitrogen, or energy source (Doronina et al. 2010). Unable to use alcohols, amines, malate, pyruvate, l-alanine, and l-serine as carbon and energy sources (Kaparullina et al. 2011). Chelativorans oligotrophicus has several defective or missing enzymes in the central carbon metabolism. The tricarboxylic acid cycle lacks α-ketoglutarate dehydrogenase activity, and 6-phosphofructokinase (ATP/PPi) is also absent (Doronina et al. 2010). The major cellular fatty acids are summed feature 7 (C18:1 ω7c, C18:1 ω9t and/or C18:1 ω12t) and C19:0 cyclo ω8c. Hydroxy fatty acids C12:0 3-OH, C13:0 3-OH, and C15:0 iso 3-OH are absent. The major ubiquinone is Q10. Predominant polar lipids are phosphatidylcholine, phosphatidylglycerol, phosphatidylethanolamine, phosphatidyldimethylethanolamine, phosphatidylmonomethylethanolamine, and diphosphatidylglycerol. Mesorhizobium-specific ornithine lipid is absent. sym-Homospermidine is the main polyamine with small amounts of spermidine and putrescine present. The DNA G+C content is 60–64 mol %. The type species is Chelativorans multitrophicus (Doronina et al. 2010).
Additional characters and differentiating features of both species are shown in Table 18.5 .
Hoeflea Peix et al. 2005, 1165VP
Hoef.le.a’. N.L. fem. n. Hoeflea honoring Manfred Höfle, German microbiologist, in recognition of his contribution to the taxonomy of marine bacteria.
Cells are non-spore-forming, motile short rods. They are aerobic chemoorganotrophs and are oxidase and catalase positive except for Hoeflea alexandrii which was described as oxidase negative. Cells do not require NaCl; however, they can grow in the presence of up to 5 % NaCl. Growth is possible at a temperature of 18–33°C although some species can grow at higher and lower temperatures (Table 18.6 ). pH range for growth is 6–8 or 9, and Hoeflea suaedae has a more wide pH range of 5–10. No nitrate reduction to nitrite or nitrogen except for Hoeflea suaedae which was reported to reduce nitrate to nitrite.
The main fatty acid is C18:1 ω7c, and other important fatty acids (>3 %) are C16:0, 11-Me C18:1 ω7c, and C19:0 cyclo ω8c. Only small amounts of hydroxy fatty acid are present. Ubiquinone Q10 is the major quinone; the main polar lipids are phosphatidylglycerol, phosphatidylethanolamine, phosphatidylmonomethylethanolamine, and sulfoquinovosyldiacylglyceride, although the latter polar lipid was not reported from Hoeflea anabaenae. The G+C content of the DNA ranges from 53 to 60 mol %. The type species is Hoeflea marina.
Additional characters and differentiating features of the five Hoeflea species are shown in Table 18.6 .
Hoeflea anabaenae cells attach to Anabaena heterocysts; of the other Hoeflea species, only Hoeflea phototrophica has been observed to do this, although at a much lower frequency (Stevenson et al. 2011). Hoeflea siderophila is the only species reported to be iron oxidizing, using FeS, FeSO4, or FeCO3 for lithotrophic growth while depositing iron oxides on the cell surface. It also has a facultative anaerobic metabolism. In anaerobic, iron-oxidizing conditions, it uses nitrate or N2O as terminal electron acceptor. Nitrate is converted to nitrite which inhibits growth as it accumulates. In those conditions, nitrite can chemically oxidize up to 20 % of Fe(II). When N2O is given as an electron acceptor, there is virtually no chemical Fe(II) oxidation, and N2 is formed. The organism is also able to grow mixotrophically or organotrophically in microaerobic or anaerobic condition, using nitrate or N2O as electron acceptors. Nitrite, ClO4−, S0, thiosulfate, and Fe(OH)3 are not used as electron acceptors, and H2 oxidation is not possible (Sorokina et al. 2012).
Lentilitoribacter Park et al. 2013, 2365VL
Len.ti.li.to.ri.bac’ter. L. masc. adj. lentus, slow, delayed; L. n. litus-oris, the seashore, coast; N.L. masc. n. bacter, rod; N.L. masc. n. Lentilitoribacter, slowly growing rod from the coast).
Lentilitoribacter cells are non-spore-forming, nonmotile, and rods to short rods. They are catalase and oxidase positive and do not reduce nitrate to nitrite. Aerobic. The predominant ubiquinone is Q10. The major fatty acids are C18:1 ω7c, 11-methyl-C18:1 ω7c, and summed feature 3 (iso-C15:0 2-OH and/or C16:1 ω7c). The major polar lipids are phosphatidylglycerol and phosphatidylmonomethylethanolamine. The DNA G+C content is 49.3 mol %. The type species is Lentilitoribacter donghaensis.
Lentilitoribacter donghaensis cells are rods, 0.3–0.6 × 0.6–4.0 μm. Colonies on marine agar are circular, slightly convex, smooth, whitish yellow and less than 0.5 mm in diameter after 10 days at 25 °C. Optimal growth temperature is 25 °C; growth occurs at 4 and 30 °C, but not at 35 °C. Optimal pH is between 7.0 and 7.5; growth occurs at pH 5.5, but not at pH 5.0. Grows in the presence of 1.0–5.0 % NaCl (bstl growth with 2.0 % NaCl). Requires Mg2+ ions for growth. Hydrolyzes Tween 20, 40, 60, and 80, but not esculin, casein, gelatin, hypoxanthine, l-tyrosine, starch, and xanthine. Acid is produced from d-xylose, but not from l-arabinose, d-cellobiose, d-fructose, d-galactose, d-glucose, myo-inositol, lactose, maltose, d-mannitol, d-mannose, d-melezitose, melibiose, d-raffinose, l-rhamnose, d-ribose, d-sorbitol, sucrose, and d-trehalose. In the API ZYM tests, alkaline phosphatase, esterase lipase (C8), and leucine arylamidase are positive, while esterase (C4), trypsin, and acid phosphatase activities are weakly present, and lipase (C14), valine arylamidase, cysteine arylamidase, α-chymotrypsin, naphthol-AS-BI-phosphohydrolase, α-galactosidase, β-galactosidase, β-glucuronidase, α-glucosidase, β-glucosidase, N-acetyl-β-glucosaminidase, α-mannosidase, or α-fucosidase activities are negative. The major fatty acids (>10 %) are C18:1 ω7c, 11-methyl-C18:1 ω7c, and summed feature 3 (iso-C15:0 2-OH and/or C16:1 ω7c). C10:0 3-OH is the only hydroxy fatty acid detected.
The type strain CCUG 62792T was isolated from seawater from the coast around Baekdo harbor in the East Sea, South Korea. Its DNA G+C content is 49.3 mol %.
Mesorhizobium Jarvis et al. 1997, 897VP
Me.so.rhi.zo’bi.um. Gr. adj. mesos, middle; N.L. neut. n. Rhizobium, bacterial genus name; N.L. neut.n. Mesorhizobium, rhizobia, phylogenetically intermediate between the genera Bradyrhizobium and Rhizobium. This etymology is given in the original description (Jarvis et al. 1997); alternatively in the List of Prokaryotic names with Standing in Nomenclature (www.bacterio.cict.fr), the name Mesorhizobium is said to refer to the growth rate of the bacteria which is intermediate between that of the genera Rhizobium and Bradyrhizobium.
The genus Mesorhizobium comprises 30 species, most occurring as nitrogen-fixing endosymbionts in root nodules of various legume plants. The species Mesorhizobium thiogangeticum was isolated from the soil adjacent to the roots of the legume Clitoria ternatea, by enrichment using reduced sulfur compounds as sole carbon and energy source (Ghosh and Roy 2006).
All species comprise rod-shaped cells that form creamy, white, or colorless colonies on agar media. They are aerobic organotrophs; only Mesorhizobium thiogangeticum is capable of facultative chemolithotrophic growth using thiosulfate or elemental sulfur as energy source (Ghosh and Roy 2006). Optimal temperature for growth is around 28 °C, and optimal pH is about 7. Three species have been reported to grow at 4°C: Mesorhizobium ciceri, Mesorhizobium sangaii, and Mesorhizobium shonense (Zhou et al. 2013); Mesorhizobium ciceri is the only species reported to grow at 40 °C (Jarvis et al. 1997; Zhou et al. 2013). Several species can grow in the presence of 1 or 2 % NaCl (Table 18.7 ); for Mesorhizobium shangrilense, even growth with 3 % NaCl was reported (Lu et al. 2009).
The fatty acid C18:1 ω7c is present in all species in large amounts (at least 10 % detected in itself or as part of a summed feature), while C16:0, 11-Me C18:1 ω7c, and C19:0 cyclo ω8c are also important (at least 5 %) in more than two thirds to half of the species. Hydroxy fatty acids have been reported at more than 1 % in 7 of the 30 species and comprise mostly C12:0 3-OH and/or iso-C13:0 3-OH; only in Mesorhizobium albiziae and Mesorhizobium temperatum has iso-C15:0 3-OH been reported at more than 1 % (Wang et al. 2007). Polar lipids have been reported for six of the species (Table 18.7 ): all comprised phosphatidylethanolamine, phosphatidylglycerol, and phosphatidylcholine, while five also contained diphosphatidylglycerol and several unidentified phospholipids (Zhang et al. 2012; Zheng et al. 2013). The DNA G+C content ranges from 57.9 % to 65.1 %.
The type species is Mesorhizobium loti. Additional characters and differentiating features of Mesorhizobium species are shown in Table 18.7 .
Nitratireductor Labbé et al. 2004, 54VP
Ni.tra.ti.re.duc’tor. N.L. masc. n. nitras, nitrate; L. v. reducere, to bring back, to reduce; N.L. masc. n. nitratireductor, nitrate-reducing bacterium.
The genus Nitratireductor comprises six species that occur in various marine habitats. All species are aerobic chemoorganotrophs; nitrate reduction varies between strains. Cells are rods, short rods, or coccoid. Motility is variable. Optimum temperature for growth is 25–35 °C. No growth below 10 °C. pH range is 5–12. All species are oxidase and catalase positive. Major quinone is ubiquinone Q10. The main fatty acid is C18:1 ω7c/ω6c. DNA G+C content is 56.7–63 mol %. The type species is Nitratireductor aquibiodomus.
All species are positive for leucine arylamidase (API ZYM tests) and for the use of d-glucose and N-acetyl-glucosamine (API 20NE); all are negative for indole production (API 20NE). Further characteristics and differentiating features of the species are given in Table 18.8 .
Phyllobacterium (ex Knösel 1962) Knösel 1984, 356VP
Phyl.lo.bac.te’ri.um. Gr. neut. n. phyllon, leaf; L. neut. n. bacterium, rod; N.L. neut. n. phyllobacterium, leaf bacterium (occurring in leaf nodules of higher plants).
Cells are rods and motile by means of polar, subpolar, or lateral flagella. The optimal growth temperature is 28 °C, and there is no growth at 40 °C. Growth occurs in 1 % NaCl. Glucose metabolism is oxidative. Oxidase positive; urease is positive except for Phyllobacterium endophyticum. Indole production, β-galactosidase, and gelatinase are negative for all species. Some other enzyme activities that were originally included in the genus description, however, have not been reported for all species. These include DNase (negative, but no data for P. endophyticum and P. trifolii), hydrolysis of Tween 80 (negative, but not tested for P. catacumbae, P. endophyticum, and P. trifolii), starch (negative for P. myrsinacearum and P. catacumbae), pectin and cellulose (both only reported as negative for P. myrsinacearum), nitrate reduction (positive for P. myrsinacearum, negative for P. catacumbae, P. endophyticum and P. trifolii). Esculin is hydrolyzed (weak reaction for P. trifolii). 3-Ketolactose test is negative (no data for P. endophyticum and P. trifolii). Assimilation of d-glucose, d-mannose, l-arabinose, d-mannitol, and N-acetylglucosamine is positive for all species. Maltose is used by all species except P. endophyticum. Quinones have only been reported for Phyllobacterium endophyticum and comprised Q10 (88 %) and Q9 (12 %) (Flores-Felix et al. 2013). Additional characteristics of the Phyllobacterium species are given in Table 18.9 .
The G+C content of the DNA ranges from 51 to 61 mol % (Tm). The type species is Phyllobacterium myrsinacearum.
Pseudahrensia Jung et al. 2012, 2059VP
Pseu.dah.ren’si.a. Gr. adj. pseudes, false; N.L. fem. n. Ahrensia, a bacterial genus name; N.L. fem. n. Pseudahrensia, the false Ahrensia.
Pseudahrensia cells are aerobic, non-spore-forming, nonmotile, and ovoid to rod shaped. Catalase, oxidase, and nitrate reduction are positive. The predominant ubiquinone is Q10. The major fatty acid is C18:1 ω7c. The major polar lipids are phosphatidylcholine, phosphatidylglycerol, diphosphatidylglycerol, and phosphatidylethanolamine. The DNA G+C content of the type strain of the type species is 60.1 mol %. The type species is Pseudahrensia aquimaris.
Pseudahrensia aquimaris cells are nonmotile, ovoid to rod shaped, and 0.5–1.0 × 1.0–7.0 μm. Colonies on MA are circular, convex, smooth, glistening, cream colored and 1.0–1.5 mm in diameter after 5 days at 30 °C. Temperature range for growth is 4–32 °C; optimal growth at 30 °C, pH 7–8, and 2–3 % NaCl. Grows at pH 5.5, but not pH 5. Can grow in 10 % NaCl, but not in 11 % or without NaCl. Na+ and Mg2+ ions are required for growth. No anaerobic growth on marine agar. Nitrate is reduced to nitrite. Gelatin is hydrolyzed. H2S is not produced. Esculin; casein; hypoxanthine; starch; Tween 20, 40, 60, and 80; l-tyrosine; urea; and xanthine are not hydrolyzed. Acid is positive from d-fructose, d-galactose, d-glucose, lactose, maltose, d-mannose, d-ribose, and sucrose; no acid production from l-arabinose, cellobiose, myo-inositol, d-mannitol, melezitose, melibiose, raffinose, l-rhamnose, d-sorbitol, trehalose, or d-xylose. Susceptible to ampicillin, cephalothin, chloramphenicol, gentamicin, kanamycin, neomycin, novobiocin, penicillin G, polymyxin B, and streptomycin; resistant to carbenicillin, lincomycin, oleandomycin, and tetracycline. The following enzymes are present (API ZYM): alkaline phosphatase, esterase (C4), leucine arylamidase, acid phosphatase, esterase lipase (C8) (weak), and trypsin (weak); the following enzymes are absent: lipase (C14), valine arylamidase, cystine arylamidase, α-chymotrypsin, naphthol-AS-BI-phosphohydrolase, α- and β-galactosidase, β-glucuronidase, α- and β-glucosidase, N-acetyl-β-glucosaminidase, α-mannosidase, and α-fucosidase (Jung et al. 2012).
Major fatty acid (>10 %) is C18:1 ω7c; no other fatty acids are present at more than 5 %; the only hydroxy fatty acid detected is C18:0 3-OH, apart from the possible presence of C14:0 3-OH as part of summed feature 2 (Jung et al. 2012). However, Park et al. (2013) report the presence of iso-C13:0 3-OH and the absence of C18:0 3-OH.
The type strain (CCUG 60023T) was isolated from seawater, Yellow Sea of the island of Hwang-do, Korea.
Pseudaminobacter Kämpfer et al. 1999, 894VP
Pseud.ami.no.bac’ter. Gr. adj. pseudos, false; N.L. masc.n. Aminobacter, bacterial genus name; N.L. masc. n. Pseudaminobacter, false Aminobacter.
Pseudaminobacter cells are rod shaped and motile. Obligate aerobic heterotrophs. They have an oxidative metabolism and can use d-glucose, d-ribose, d-xylose, acetate, propionate, pyruvate, β-alanine, N-acetyl-d-glucosamine, 4-aminobutyrate, dl-3-hydroxybutyrat, dl-lactate, oxoglutarate, l-alanine, l-histidine, l-leucine, and l-proline as sole carbon source. Growth occurs on nutrient agar (Oxoid), Caso agar, R2A agar (Oxoid), and TSB agar (BBL). Colonies are circular, entire, slightly convex and smooth, glistening, and pale beige on nutrient agar at 25 °C. Oxidase and catalase positive. Main ubiquinone is Q10. The major polyamines are spermidine, sym-homospermidine, and putrescine. Polar lipids include phosphatidylcholine, phosphatidylglycerol, phosphatidyldimethylethanolamine, phosphatidylmonomethylethanolamine, phosphatidylethanolamine, and diphosphatidylglycerol in nearly the same amounts. Main fatty acids are C18:1 and C19:0 cyclo ω8c. The only hydroxy fatty acid is C15:O iso 3-OH. The G+C content of the DNA is 62.9–63.9 mol %. The type species is Pseudaminobacter salicylatoxidans.
One additional species was described, Pseudaminobacter defluvii. Both species produce acid weakly from glucose, but not from lactose, sucrose, salicin, inositol, sorbitol, l-arabinose, raffinose, maltose, d-xylose, trehalose, cellobiose, d-arabitol, mannose, adonitol, rhamnose, methyl d-glucoside and erythritol. Both species hydrolyze bis-para-nitrophenyl (pNP)-phosphate, pNP-phenyl-phosphonate, l-alanine-para-nitroanilide (pNA), and l-proline-pNA, but not pNP-α-d-glucopyranoside, pNP-β-d-glucopyranoside, pNP-phosphorylcholine, esculin, pNP-β-d-galactopyranoside, pNP-β-d-glucuronide, 2-deoxythymidine-5′-pNP-phosphate, and l-glutamate-γ-3-carboxy-pNA. They do not assimilate p-arbutin, d-melibiose, salicin, maltitol, putrescine, trans-aconitate, adipate, azelate, fumarate, itaconate, mesaconate, suberate, l-tryptophan, 3-hydroxybenzoate, and phenylacetate. Additional characteristics of the Psedaminobacter species are given in Table 18.10 .
Thermovum Yabe et al. 2012, 2994VP
Ther.mo’vum. Gr. n. thermê, heat; L. neut. n. ovum, egg, oval; N.L. neut. n. Thermovum, a heat(-loving) oval-shaped organism.
Thermovum comprises Gram-positive ovoid cells that do not form spores. Thermophilic. Major fatty acids (>10 %) are C18:1 ω7c, C19:0 ω8c, and C18:0. Polar lipids comprise phosphatidylcholine, phosphatidylglycerol, phosphatidylethanolamine, hydroxyphosphatidylethanolamine, phosphatidylinositol, phosphatidylmonomethylethanolamine, an unknown glycolipid, and a ninhydrin-positive phospholipid. The main quinone is ubiquinone Q10. The type species is Thermovum composti.
Thermovum composti cells are nonmotile, ovoid shaped, and 0.9 μm × 1.4 μm (after 2 days at 50 °C). Catalase and oxidase positive. Growth occurs at 23–57 °C, with optimal growth at 50 °C, at pH 5.9–8.8 (optimum, pH 7.0) and in the presence of 0–4 % (w/v) NaCl. In addition to the major fatty acids listed above in the genus description, C16:0 is a further important fatty acid (5–10 %) in Thermovum composti, while no hydroxy fatty acids were reported. Negative for gelatinase, urease, and indole production. Positive for nitrate reduction and for the utilization of d-arabinose, l-arabinose, d-ribose, d-xylose, d-galactose, d-glucose, cellobiose, lactose, melibiose, gentiobiose, d-fucose, and potassium 5-ketogluconate; negative for the utilization of glycerol, erythritol, l-xylose, d-adonitol, methyl β-d-xylopyranoside, d-fructose, d-mannose, l-sorbose, l-rhamnose, dulcitol, inositol, d-mannitol, d-sorbitol, methyl α-d-mannopyranoside, methyl α-d-glucopyranoside, N-acetylglucosamine, amygdalin, arbutin, esculin ferric citrate, salicin, maltose, sucrose, trehalose, inulin, melezitose, raffinose, starch, glycogen, xylitol, turanose, d-lyxose, d-tagatose, l-fucose, dl-arabitol, potassium gluconate, and potassium 2-ketogluconate. The following enzyme activities were present (API ZYM): esterase C4, esterase C8, leucine arylamidase, α-chymotrypsin, naphthol-AS-BI-phosphohydrolase, trypsin, and valine arylamidase; the following were absent: alkaline phosphatase, lipase C14, cystine arylamidase, acid phosphatase, α-galactosidase, β-galactosidase, α-glucosidase, β-glucosidase, β-glucuronidase, N-acetyl-β-glucosaminidase, mannosidase, and α-fucosidase. The type strain JCM 17863T was isolated from compost. The G+C content of its DNA is 63.4 mol %.
If appropriate, the description of metabolic pathways and/or physiology may deserve an individual heading.
Isolation, Enrichment, and Maintenance Procedures
The genera and species of the family have an aerobic respiratory metabolism and originate from a wide range of habitats. No single isolation or enrichment procedure is available to selectively obtain all or most members of the family, and therefore the genera are discussed separately below.
The only species of the genus Ahrensia, Ahrensia kielensis, was isolated from the Baltic Sea during studies of star-shaped-aggregate-forming bacteria and was originally named Agrobacterium kielense (Ahrens 1968). Because Dr. Renata Ahrens later withdrew the proposal, these species were not documented elsewhere in the following years, and no details on specific isolation conditions are available in recent literature (Rüger and Höfle 1992). With the recent sequencing of the genome of this organism, it may become possible in future to propose suitable isolation or enrichment strategies. The organism can be cultivated on regular marine media (e.g., Difco Marine Broth) at 26 °C and can be freeze-dried for long-term preservation.
Aliihoeflea was isolated from tidal flat sediment samples by plating on marine agar 2216 (Difco). Circular colonies—convex with entire margin, shiny, and cream colored—were 0.5–1.0 mm in diameter after 2 days incubation at 30 °C. Growth also occurs on trypticase soy agar (TSA, Difco), Luria agar (Difco), and yeast extract mannitol agar (YMA, per liter, 10 g d-mannitol, 0.5 g KH2PO4, 0.2 g MgSO4 · 7H2O, 0.1 g NaCl, 4 g CaCO3, 0.4 g yeast extract, 15 g agar; pH 6.8–7.0) (Roh et al. 2008).
All Aminobacter species were isolated from the soil using various enrichment or trapping methods. Aminobacter anthyllidis was isolated from the nodules of Anthyllis vulneraria that was used as a trapping plant and was grown in soil from a zinc and lead mining site (Maynaud et al. 2012). The surface-sterilized nodules were crushed in sterile water, and the bacteria were isolated by streaking the suspension on YMA (Vincent 1970; recipe as listed above) and incubating at 28 °C.
Aminobacter aganoensis, Aminobacter aminovorans, and Aminobacter niigatensis were isolated from soil by enrichment using methylamine compounds (mono-, di-, tri-, or tetramethylamine, trimethylamine-N-oxide, or tetramethylammonium hydroxide) or methylformamide compounds (N-methylformamide or N,N-dimethylformamide) (Urakami 2005). For routine growth of PYG medium, pH 7.0 can be used at 30 °C (Urakami et al. 1992).
Aminobacter ciceronei and Aminobacter lissarensis are methylotrophic species. Aminobacter ciceronei was isolated from CH3Br-fumigated soil in the USA by enrichment on a mineral salt medium under a modified atmosphere of air plus CH3Br (Miller et al. 1997). Aminobacter lissarensis strain CC495 was isolated from the top 5 cm of soil in a beech wood in County Down, Northern Ireland, by enrichment with CH3Cl as the sole carbon and energy source. One gram of soil was added to 100 ml of minimal medium in 500-ml flasks containing 0.125 g of CH3Cl. The minimal medium had the following composition (in grams per liter): KH2PO4 (4.5), K2HPO4 (10.5), MgSO4 · 7H2O (0.15), and NH4NO3 (1.5), pH adjusted to 7.2 with 6 M NaOH; a trace element solution was added (10 ml. l−1) containing (in mg.l−1) H3BO3(500), CuSO4 · 5H2O (40), KI (100), FeSO4 · 7H2O (200), MnSO4 · 7H2O (400), (NH4)6Mo7O24 · 4H2O (200), and ZnSO4 (400). In the pure cultures, the medium was additionally supplemented with a vitamin solution (5 ml.l−1) containing (in milligrams per liter) folic acid (4), p-aminobenzoic acid (200), and cyanocobalamin (200). CH3Cl (0.15 g) was added as an aqueous solution to give a concentration in the culture medium, after equilibration of the gaseous and aqueous phases, of 11.8 mM (30 mM if partitioning is neglected and the total CH3Cl present is expressed as a concentration in the aqueous phase) (Coulter et al. 1999).
All Aminobacter species can be stored in broth medium plus 20 % glycerol at −80 °C or can be lyophilized and stored at 4 °C.
Two Aquamicrobium species were isolated from activated sludge, Aquamicrobium defluvii and Aquamicrobium lusatiense (Bambauer et al. 1998; Fritsche et al. 1999; Kämpfer et al. 2009). The former species originated from a municipal wastewater plant and was obtained on a mineral medium with thiophene-2-carboxylate as the sole source of carbon and nitrate as the electron acceptor. The mineral salt medium (Bambauer et al. 1998), also used for cultivation, contained per l 3.56 g Na2HPO4 · 2H2O, 0.4 g NH4Cl, and 0.07 g K2SO4. After autoclaving, 1 l of medium was supplemented with 2 ml of a sterile solution containing per l 100 g MgCl2, 25 g CaCl2, 10 ml vitamin solution (Balch et al. 1979), and 1 ml trace element solution (Widdel et al. 1983). Thiophene-2-carboxylate (2–30 mM final concentration) was added from a sterile, tenfold concentrated stock solution. For anaerobic growth, the medium was supplemented with 5–20 mM KNO3 (Bambauer et al. 1998).
Three other species were isolated from air or waste gas in a duck shed and an animal rendering plant: Aquamicrobium aerolatum, Aquamicrobium ahrensii, and Aquamicrobium segne (Kämpfer et al. 2009; Lipski and Kämpfer 2012). The latter two species were isolated on Antibiotic Sulfonamide Sensitivity-test agar (Merck 1.05392) (Ahrens et al. 1997). Aquamicrobium aerolatum was isolated collecting bioaerosol samples by filtration over gelatin filters and isolation on trypticase soy agar incubated at 26 °C. The organism can also be grown on nutrient agar (Kämpfer et al. 2009). Aquamicrobium aestuarii was isolated from crude oil-contaminated sediments of a tidal flat (Jin et al. 2013) by incubating approximately 10 g of sediment with 100 ml of 0.2 μm filtered seawater containing 3 ml crude oil in 500-ml Erlenmeyer flask at 25 °C. The enrichment was aerated (180 rpm) and was transferred (1:20) four times every 2 weeks. For isolation, the enrichment was plated on marine agar 2216 (BD) plates and incubated under aerobic conditions at 25 °C for 5 days. In addition, the species grows well on R2A agar (BD), Luria-Bertani agar, trypticase soy agar, and marine agar (Jin et al. 2013).
Chelativorans strains were obtained from sludge samples. Chelativorans multitrophicus was isolated from a mixed microbial culture enriched in a column packed with activated carbon that was continuously fed with a mineral medium containing EDTA as sole source of carbon, nitrogen, and energy. The original inoculum of the column was activated sludge from various industrial wastewater treatment plants and soil extracts. For the isolation, further aerobic enrichment in continuous culture on a column packed with glass beads and fed with mineral medium (per liter, 1.0 g MgSO4 · 7H2O, 0.2 g CaCl2 · 2H2O, 0.13 g KH2PO4, and 0.615 g Na2HPO4, 2 ml of Widdel trace element solution (Pfennig et al. 1981) and 1 ml of a vitamin solution (Egli et al. 1988)) containing 200–300 mg.l−1 EDTA as well as batch cultures to establish optimal growth conditions were used (Weilenmann et al. 2004). The best conditions for growth were 30 °C, initial EDTA concentration in the range of 1–1.5 g.l−1, CaCl2 · 2H2O concentration in the mineral medium of 0.4 g.l−1 and an initial pH of 7.0. Pure cultures were obtained by successive plating on Plate Count Agar and liquid culture in the mineral medium (Weilenmann et al. 2004). Chelativorans multitrophicus was obtained by enrichment from municipal sludge samples: 10 g of sample was suspended in 100 ml of medium (per liter, 1.0 g EDTA, 1.0 g MgSO4 · 7H2O, 0.4 g CaCl2 · 2H2O, 0.26 g KH2PO4, and 0.83 g Na2HPO4 · 12H2O and trace elements and vitamins (Egli et al. 1988), pH 7.0). The medium was incubated in a 750-ml flask on a shaker (150–200 rpm) at 28 °C for 2 weeks. Five milliliters of this enrichment then inoculated into a 750-ml flask with 100 ml of fresh medium and cultivated for 2 weeks. After five such transfers, pure colonies were picked from plates of the same medium plus agar (Chistyakova et al. 2005).
Hoeflea species have been isolated from different aquatic environments. Hoeflea marina comprises one strain, LMG 128T, that was originally classified as Agrobacterium ferrugineum (other strains of this species have been renamed as Pseudorhodobacter ferrugineus, a member of the Rhodobacteraceae). Hoeflea marina was isolated from water from the Baltic Sea, off the coast of Germany, during a study of star-forming bacteria (Ahrens 1968; Peix et al. 2005). Hoeflea phototrophica was isolated from cultures of the marine dinoflagellates Alexandrium lusitanicum and Prorocentrum lima. Wine red colonies were obtained by plating washed single dinoflagellate cells onto 1/10-strength Difco marine agar. Pigmentation was found to depend on the salt concentration with cultures with 3, 6, or 9 g.l−1 sea salts being very pink, while at 35 g.l−1 cultures were colorless (Biebl et al. 2006). Hoeflea alexandrii was purified from cultures of another marine dinoflagellate, Alexandrium minutum. In this case, the washed dinoflagellate cells were sonicated prior to plating on full- and half-strength Difco marine agar and incubation during 7 days at 15 °C. Brown-pigmented colonies were obtained. Marine agar or broth was used for routine cultivation at 30 °C (Palacios et al. 2006). Hoeflea anabaenae was isolated from a culture of the cyanobacterium Anabaena under heterotrophic conditions in the brackish marine purity liquid medium (per liter, 20 g NaCl, 17 g AC broth (Difco), 8 g MgSO4 · 7H20, 1.5 g CaCl2 · 2H20 (Stevenson and Waterbury 2006)) from a culture in which it was attached almost exclusively to Anabaena heterocysts. It is also able to grow aerobically at 30 °C in full- and half-strength marine broth (Difco) and marine agar and liquid or solid PY medium (20 g sea salts, 3 g peptone, and 0.5 g yeast extract per liter (Biebl et al. 2005)). Hoeflea suaedae was isolated from the root surface of the halophyte Suaeda maritima. Surface-sterilized and dried root pieces (1 g) were ground in 9 ml of autoclaved filtered seawater (AFS) with a sterile mortar and pestle. Dilution series were plated in triplicate on one-tenth-strength R2A (1/10 R2A) medium in filtered seawater and supplemented with 50 μg/ml cycloheximide. Plates were incubated at 28 °C for 2–3 weeks. Routine maintenance is on 1/10 R2A medium in filtered seawater, and the organism can be stored with 15 % glycerol at −70 °C (Bibi et al. 2012).
Hoeflea siderophila was isolated from fresh ochreous sediments collected near the outlet of an iron-rich brackish spring using dilution plating on the following medium (g per liter): NaCl, 20; NH4Cl, 0.3; CaCl2⋅6H2O, 0.3; MgCl2⋅7H2O, 3; NaHCO3, 0.5; 10 % phosphate buffer (pH 7.0), 0.1; Hepes buffer (pH 7.2), 3.0; KNO3, 0.3; CH3COONa, 0.15; vitamins and trace elements (Pfennig and Lippert 1966); Difco agar, 5.0; and pH 7.0. Before inoculation, the medium was supplemented with fresh sterile FeS suspension (Hanert 1981) (0.2 mL per 10 mL of medium). Inoculated media were incubated for 2–3 weeks at 28 °C. Growth consisted of dense spherical colonies, orange-colored due to the formation of iron oxides. In liquid medium, iron oxidation results in an ochreous precipitate (Sorokina et al. 2012).
Hoeflea hydrophila was isolated from marine sediments by serial dilution in filter-sterilized natural seawater containing 0.1 % yeast extract. After aerobic incubation at 25 °C for 2 weeks, a sample from the lowest dilution showing growth was plated on the same medium, and after incubation at 25 °C for 2 weeks, single colonies that were beige, circular, and convex with regular edges were purified on marine agar 2216 (Difco). This species can be routinely grown on marine broth or marine agar. Marine broth cultures plus 20 % glycerol can be stored at −80 °C (Jung et al. 2013).
Lentilitoribacter was isolated from coastal seawater by dilution plating on marine agar 2216 (Becton–Dickinson) at 25 °C. These conditions were also used for routine cultivation. For short-term preservation, marine agar cultures can be stored at 4 °C, while for long-term preservation, glycerol suspensions (20 %) can be stored at −80 °C (Park et al. 2013).
Mesorhizobium comprises soil bacteria that can live endosymbiotically in root nodules on various legume plants where they can fix atmospheric nitrogen contributing to plant nutrition. A widely used approach to isolate rhizobia is through the use of legume plants to trap the bacteria from a particular soil. Surface-sterilized seeds are allowed to germinate in the soil, and after the plants develop, nodules are harvested for isolation of the bacteria (Vincent 1970). A similar approach is also used to verify the nodulation capacity of a strain with a particular host species. Isolation from surface-sterilized and crushed nodules is performed using yeast mannitol agar (YMA, per liter, 10 g d-mannitol, 0.5 g KH2PO4, 0.2 g MgSO4 · 7H2O, 0.1 g NaCl, 4 g CaCO3, 0.4 g yeast extract, 15 g agar, pH 6.8–7.0). Incubation at 28 °C will result in the formation of creamy, entire, and convex mucoid colonies after 3–4 days. This procedure can result in growth of not only Mesorhizobium strains but also other rhizobia. Phenotypic distinctions are not straightforward: Mesorhizobium members can in some cases be distinguished in that they have a moderately fast growth rate (generation time 4–15 h) compared to Rhizobium (<6 h) and Bradyrhizobium (>6 h). Also they produce acid on YMA (as do Rhizobium strains), while Bradyrhizobium strains produce alkali (Chen et al. 2005). More certain genus assignment, however, requires verification of the partial 16S rRNA gene sequence.
All Mesorhizobium species have been isolated using the trap legume method except for one species, Mesorhizobium thiogangeticum, which was obtained from soil adjacent to the root of the legume Clitoria ternatea through enrichment using reduced sulfur compounds as sole carbon and energy source. Soil was supplemented with Na2S2O3 · 5H2O (5 %), Na2S (1 %), and elemental sulfur powder (5 %) and incubated at 30°C for 2 weeks with intermittent sprinkling of sterile water. After this enrichment, soil samples (1 %, w/v) were incubated on a rotary shaker at 30 °C in mineral salt thiosulfate yeast extract liquid medium (20 mM Na2S2O3 · 5H2O supplemented with 5 g yeast extract per liter, pH 7.0–7.5) in mineral salt solution that contained (per liter of distilled water) 1 g NH4Cl, 4 g K2HPO4, 1.5 g KH2PO4, 0.5 g MgSO4 · 7H2O, and 5.0 ml trace metal solution (Vishniac and Santer 1957). When the color of the phenol red indicator had changed to yellow, serial dilutions were plated on the same agar medium for the isolation of pure cultures (Ghosh and Roy 2006).
Nitratireductor strains have been isolated from diverse marine sources, often by standard dilution plating techniques. Nitratireductor aquibiodomus was isolated from a marine aquarium denitrification system fitted with cellulose carriers. For the isolation, cellulose carriers were homogenized, and a dilution series was plated onto trypticase soy agar and R2A and incubated at room temperature for 3 weeks. Nitratireductor aquibiodomus was one of the several organisms that were picked up (Labbé et al. 2003); its colonies were white, smooth, circular, and convex (Labbé et al. 2004). Nitratireductor basaltis was isolated from black sand from Soesoggak beach, Jeju Island, Korea, by dilution plating onto marine agar 2216 (Difco) and incubating at 30–37 °C. It is not reported whether other organisms were able to grow in these conditions; the colonies of Nitratireductor basaltis were creamy, circular, convex, and smooth (Kim et al. 2009). Nitratireductor kimnyeongensis was isolated from a dried seaweed sample from Kimnyeong beach in Jeju, Republic of Korea (Kang et al. 2009), by transferring a piece of dried seaweed directly transferred onto isolation medium (WAT-SW agar) consisted of 0.05 % MgSO4.7H2O, 0.05 % CaCl2.2H2O, and 1.5 % agar in 60 % natural seawater and 40 % distilled water (pH 7.3) (Lee 2006). The organism can also be conveniently grown on trypticase soy agar where, after 5 days of incubation, colonies are small (0.5–1 mm in diameter), light yellow, circular, convex, smooth, and entire (Kang et al. 2009). Nitratireductor aquimarinus was isolated from exponential cultures of the marine diatom Skeletonema costatum by plating a 10-μl sample on marine agar 2216 (Difco) and incubating aerobically for 1 week. Colonies are creamy, smooth, circular, and convex. Growth is also good on trypticase soy agar at 35 °C. Strains can be preserved in trypticase soy broth supplemented with 30 % glycerol and −80 °C (Jang et al. 2011). Nitratireductor indicus was isolated from a deep-sea water sample taken at a depth of 2,488 m taken with Niskin bottles attached to a CTD (conductivity, temperature, and depth) sampler at 25.3217°S 70.0405°E in the southwestern part of the Indian Ridge. The seawater was enriched with 1 % sterilized crude oil, and after two months, bacteria were isolated by using the plating on 216L medium (per liter seawater: 1.0 g CH3COONa, 10.0 g tryptone, 2.0 g yeast extract, 0.5 g sodium citrate, and 0.2 g NH4NO3; pH 7.5) (Lai et al. 2009; Lai et al. 2011b). On marine agar, colonies are unpigmented, smooth gray, and slightly raised in the center and have a regular margin (Lai et al. 2011a). Nitratireductor pacificus was also isolated from deep-sea water samples, this time from a pyrene-degrading enrichment (described in Wang et al. 2008) by using phthalate as sole carbon source in mineral medium (MM, comprising per liter: 3.5 g MgSO4 · 7H2O, 0.05 g CaCl2, 24 g NaCl, 0.35 g KCl, 1.0 g NH4NO3, 1.0 KH2PO4, 1.0 g K2HPO4, 0.01 g FeCl3, 0.0001 g ZnSO4 · 7H2O, 24 mg SrCl2 · 6H2O, and 0.08 g KBr, adjusted to pH 7.4) (Wang et al. 2008; Lai et al. 2011a). On marine agar, colonies are smooth gray, nonpigmented with a regular margin, and slightly raised in the center (Lai et al. 2011a).
Most recently, a new species, Nitratireductor lucknowense, was published, though not yet validated. It was isolated from pesticide-contaminated soil from a γHCH (lindane) manufacturing site in India. Five-gram soil samples collected from three different locations were mixed together in 50 ml of sterile mineral medium (Senoo and Wada 1989). After the slurry had settled, the liquid phase was used to enrich for bacteria on 0.34 M lindane. On trypticase soy agar, the new species produces colonies that are straw yellow, smooth, circular, glistening, opaque, and convex with an entire margin (Manickam et al. 2012). NaCl is tolerated up to 2 % (Manickam et al. 2012), considerably less than most other Nitratireductor species which can tolerate up to 7 or 8 % (Table 18.8 ).
Most Phyllobacterium species are plant associated, and while the first species were isolated from tropical ornamental plants, these bacteria have since also been isolated from other plants elsewhere and from non-plant sources such as volcanic rock used for construction. Different isolation procedures have been used and are summarized in the following overview. The selectivity in most cases is not documented.
Phyllobacterium myrsinacearum and its junior subjective synonym Phyllobacterium rubiacearum (Mergaert et al. 2002) have been isolated from leaf nodules of members of the plant families Rubiaceae (Pavetta zimmermanniana) and Myrsinaceae (Ardisia crispa, Ardisia crenata). Washed leaf pieces carrying nodules were macerated by rubbing and placed in saline. After shaking, dilutions were plated onto carrot juice agar containing yeast extract (fresh carrot juice, 500 ml; water, 500 ml; FeSO4 · 7H2O, 0.1 g; MnSO4 · H2O, 0.1 g; agar, 15 g; pH 7.2; the medium is sterilized by fractional sterilization). After incubation at 28 °C, typical nonpigmented to beige, slimy, and circular colonies that are translucent to opaque in the center are transferred into liquid carrot juice medium. After 24- to 48-h phase, contrast microscopy can be used to verify the formation of star-shaped clusters. Stock cultures can be kept on trypticase soy agar at 5 °C for 1–2 months, and cultures can be lyophilized for long-term preservation (Knösel 1984). Isolates of this species have also been obtained from the root surface of sugar beet by using trypticase soy broth agar as a nonselective medium (Lambert et al. 1990; Mergaert et al. 2002).
Phyllobacterium trifolii was isolated from the nodules of Trifolium pratense as described above for Mesorhizobium species. Colonies on YMA are white, mucoid, translucent, and convex. The growth rate of this Phyllobacterium species (generation time 2 h) is faster than most mesorhizobia. Growth is also possible on nutrient agar (Valverde et al. 2005).
A further five species were also obtained using the same procedure, this time from roots of Brassica napus cv. Eurol (Phyllobacterium bourgognense, Phyllobacterium brassicaearum), root nodules of Lathyrus numidicus and Astragalus algerianus (Phyllobacterium ifriqiyense), root nodules of Astragalus algerianus and Argyrolobium uniflorum (Phyllobacterium leguminum) (Mantelin et al. 2006b), and root nodules of Phaseolus vulgaris (Flores-Felix et al. 2013). Colonies are circular, white or cream colored with regular margins, and in most strains highly mucoid (Mantelin et al. 2006b).
Phyllobacterium catacumbae does not originate from a plant-associated source. It was isolated from tuff, volcanic rock used in the walls of the Roman catacombs of Saint Callixtus, Rome, Italy. The B-4 medium used for isolation contained (per liter) 2.5 g calcium acetate, 4 g yeast extract and 15 g agar, pH 8, and incubation was at 28 °C. Colonies are circular, smooth, and beige. Growth is also good on trypticase soy agar (Jurado et al. 2005).
Phyllobacterium species can be stored at −80 °C in broth medium plus 20 % glycerol or at 4 °C lyophilized.
Pseudahrensia was isolated from seawater from the Yellow Sea, Korea, by the standard dilution plating on marine agar 2216 (Difco) and incubating at 25 °C. Colonies are circular, convex, smooth, glistening, and cream colored. This organism can be routinely cultivated on marine agar at 30 °C (Jung et al. 2012).
Although no precise isolation media have been published, Pseudaminobacter strains have been isolated by exploiting specific degradation capacities. The Pseudaminobacter salicylatoxidans type strain was isolated as a degrader 6-aminonaphthalene-2-sulfonate from a microbial consortium degrading this substrate and originating from the river Elbe, Germany (Nortemann et al. 1986; Kämpfer et al. 1999). The type strain of Pseudaminobacter defluvii was isolated from activated sludge which was enriched with thiocyanate (Katayama-Fujimura et al. 1983; Kämpfer et al. 1999). Growth is possible on several media including nutrient agar, trypticase soy agar, trypticase soy broth plus 1.5 % agar, and R2A (Oxoid) (Kämpfer 2005).
Thermovum composti was isolated from mature compost produced by a field-scale composter used for the treatment of livestock excreta. Dilution series of 1 g of compost in saline solution were plated onto isolation medium composed of (per liter distilled water) 1 g yeast extract, 2 g tryptone, 1 g NaCl, 1 g MgSO4 · 7H2O, 20 g agar, 20 mg trimethoprim, 10 mg nalidixic acid, and 20 mg kanamycin, pH 7.0. After incubation at 50 °C for 7 days, colonies were picked and repeatedly transferred for purification. Colonies on nutrient agar are cream colored. Stock cultures in trypticase soy broth, grown for 2 days at 50 °C, can be supplemented with 20 % glycerol and stored at −80 °C (Yabe et al. 2012).
Ecology
Members of the Phyllobacteriaceae are versatile environmental bacteria that occur in diverse habitats that often are polluted or nutritionally rather rich. These habitats can be marine (Aliihoeflea, Ahrensia, Aquamicrobium, Hoeflea, Lentilitoribacter, Nitratireductor, Pseudahrensia) or polluted freshwater (Pseudaminobacter, Aquamicrobium, Chelativorans) systems, soil (Aminobacter, Chelativorans, Mesorhizobium, Nitratireductor, Phyllobacterium, Thermovum), or air (Aquamicrobium). Several genera are plant associated or associated with dinoflagellates or cyanobacteria (Hoeflea, Mesorhizobium, Phyllobacterium).
Aquamicrobium species have been isolated from diverse polluted environments (activated sludge, oil-polluted sediments, air/waste gas from poultry/animal rearing) and have degradative capabilities that may significantly contribute to the breakdown of pollutants: Aquamicrobium defluvii is able to degrade thiopene-2-carboxylate (Bambauer et al. 1998), Aquamicrobium lusatiense can utilize phenol and chlorophenols such as 4-chloro-2-methylphenol, 2,4-dichlorophenol, and 4-chlorophenol (Fritsche et al. 1999), and Aquamicrobium aestuarii was enriched from marine sediments using crude oil (Jin et al. 2013).
Chelativorans species have been found in municipal and industrial sludge samples and are able to degrade EDTA, a chelating agent with many applications that is generally recalcitrant to biodegradation. Chelativorans multitrophicus and Chelativorans oligotrophicus are able to use EDTA as sole carbon, nitrogen, and energy source, facultatively and obligately, respectively. They may have a significant role in the clearing of EDTA pollution in surface waters (Doronina et al. 2010).
Hoeflea phototrophica contains bacteriochlorophyll at reduced salt concentrations, but not at the concentration seawater (3.5 %); it also contains a carotenoid pigment thought to be spheroidenone and was found to contain pufL and pufM genes coding for proteins of the photosynthetic reaction center. However, Hoeflea phototrophica does not grow anaerobically in light or dark conditions, and conditions under which it may live phototrophically have not been described in detail (Biebl et al. 2006).
Hoeflea siderophila is able to grow mixotrophically and organoheterotrophically. It is the only species of the genus that is capable of fac. chemolithotrophic growth through iron oxidation at neutral pH, in anaerobic conditions with nitrate or N2O as terminal electron acceptor, and microaerobically with oxygen. It is one of the rare species that is capable of neutrophilic lithotrophic iron oxidation (Sorokina et al. 2012).
Mesorhizobium strains are soil bacteria that can, in the vicinity of a compatible legume host species, enter into a molecular dialogue with the plant, resulting in the formation of root nodules on the plant that can be occupied by the bacteria. The bacteria receive a safe habitat and food, while they in turn can fix atmospheric nitrogen and thus contribute to plant nutrition. Most Mesorhizobium species (29 of 30) have been described as symbiotic with various legume species (Table 18.11 ). The only species that was not obtained from nodules, Mesorhizobium thiogangeticum obtained through enrichment from the soil adjacent to the legume Clitoria ternatea, was not able to nodulate this host nor Pisum sativum or Cicer arietinum (Ghosh and Roy 2006). Mesorhizobium has occasionally also been reported from marine systems (Sfanos et al. 2005; Krick et al. 2007) and from aquatic microbial mats in Antarctica (Peeters et al. 2012).
Several Phyllobacterium species have been isolated from leaf or root nodules of plants and contribute to plant growth promotion (Table 18.12 ). For Phyllobacterium myrsinacearum, there is no direct evidence that it actively induces nodule formation in leaves. Nodulation has been confirmed for Phyllobacterium trifolii (Valverde et al. 2005),
Unspecified Phyllobacterium strains have also been reported from the rhizosphere of Lotus spp. (Oger et al. 2004), associated with roots in Brassica napus (Bertrand et al. 2001), as endophytes in Ipomea batatas (Khan and Doty 2009), and in root nodules of many legumes including Dalbergia louvelii (Rasolomampianina et al. 2005), Lathyrus gmelinii (Baymiev et al. 2011), Acacia sp. (Hoque et al. 2011), Sophora alopecuroides (Zhao et al. 2010), Vicia sp. (Lei et al. 2008), and Ononis tridentata (Rincon et al. 2008). They have also been found as free-living bacteria in water (Mergaert et al. 2001) and associated with unicellular organisms (Gonzalez-Bashan et al. 2000).
The possible symbiotic function of phyllobacteria is reported to be the production of plant growth hormones, protective antibacterial and antifungal activity (Lambert et al. 1990), phosphate solubilization (Chen et al. 2006), root hair elongation (Galland et al. 2012), and nitrogen fixation (Valverde et al. 2005).
Both Pseudaminobacter species have been isolated from polluted aquatic environments (Kämpfer et al. 1999). Pseudaminobacter salicylatoxidans can degrade substituted naphthalenesulfonates and substituted salicylates. One strain has also shown to be a facultative sulfur chemolithotroph that can oxidize S2O32−, S4O62−, SO32−, S22−, and S0 directly to SO42− without any intermediate formation (Ghosh and Dam 2009). In polluted oligotrophic aquatic systems, these bacteria may play an important role in biodegradation.
Thermovum is the only genus of the family that is thermophilic (maximum growth temperature 60 °C). It was isolated from mature compost; its role in the compost ecosystem is not documented (Yabe et al. 2012).
Pathogenicity, Clinical Relevance
Mesorhizobium amorphae has been reported as an amoeba-associated bacterium that may be involved in nosocomial pneumonia through contaminated water supplies (La Scola et al. 2003; Berger et al. 2006). As no recent reports confirming these observations were found, the significance of Mesorhizobium amorphae as a nosocomial pathogen is not clear. No other animal or human pathogens are among the current members of the Phyllobacteriaceae.
Many species, particularly of Mesorhizobium and Phyllobacterium, are plant endophytes, rhizoplane or rhizosphere bacteria that have plant beneficial effects (see next section below).
No plant pathogenic effects have been reported for most members of the family Phyllobacteriaceae. Candidatus Liberibacter is, however, a serious plant pathogen. It is included here, although the membership of this group is currently uncertain (see above under Sect. 1.2, “Phylogenetic Structure of the Family and Its Genera”). The trivial name “liberobacter” (sic) (from the Latin liber [bark] and bacter [bacteria]) was proposed in 1994 for a phloem-limited bacterium-like organism associated with citrus greening disease, also known as huanglongbing disease or yellow dragon disease, a severe and widespread citrus disease that is transmitted by the Asian citrus psyllid (Diaphorina citri) and the African citrus psyllid (Trioza erytreae) (Jagoueix et al. 1994). The disease causes yellowing and blotchy mottling of the leaves, production of bitter, small and misshapen fruits, and ultimately death of the tree (http://www.aphis.usda.gov/plant_health/plant_pest_info/). Two species, Candidatus Liberibacter asiaticus (originally Liberobacter asiaticum) and Candidatus Liberibacter africanus (originally Liberobacter africanum), were proposed for the Indian and South African liberibacters, respectively, which can be distinguished based on temperature sensitivity (in Africa symptoms occur only in cooler regions), serology, and genomic properties (Jagoueix et al. 1994). Garnier et al. (2000) corrected the spelling of the genus name and proposed a separate subspecies, Candidatus Liberibacter africanus subsp. capensis, for a South African liberibacter in the ornamental rutaceous tree, Calodendrum capense. The citrus disease was later also reported from Brazil, and the pathogen recognized as a new species, Candidatus Liberibacter americanus, spread by the vector Diaphorina citri (Texeira et al. 2005). Although the species epithet originally referred to the geographic occurrence of the group, Candidatus Liberibacter asiaticus has also been found in the Americas (Raddadi et al. 2011). In the USA, the Asian citrus psyllid, Diaphorina citri, has been present in Florida since 1998, and Candidatus Liberibacter asiaticus was found in Florida in early September 2005. In 2010, the USDA imposed a plant quarantine in several states and territories in the USA to stop the spread of citrus greening (http://www.aphis.usda.gov/plant_health/plant_pest_info/). The disease was reported in South California in 2012 (www.californiacitrusthreat.com). The European and Mediterranean Plant Protection Organization (EPPO) has placed Liberibacter africanus, Liberibacter asiaticus, and Liberibacter americanus and the vector Diaphorina citri on its A1 list of pests recommended for regulation as quarantine pests. This list comprises pests regarded as absent from the EPPO region. The vector Trioza erytreae was included on the A2 List of pests recommended for regulation as quarantine pests that are locally present in the EPPO region.
Citrus huanglongbing disease is regarded as a pest of urgent phytosanitary concern for southern parts of the EPPO region where citrus is grown. Several PCR and real-time PCR tests have been developed for the detection of these Candidatus Liberibacter sp. in plants and in the psyllid vectors (Morgan et al. 2012 and references therein). To eliminate or suppress Candidatus Liberibacter asiaticus, a combination of penicillin and streptomycin administered by trunk injection or root soaking was shown to be effective in citrus plants (Zhang et al. 2011).
Several additional species have more recently been reported to affect Solanaceae plants. Candidatus Liberibacter psyllaurous is associated with psyllid yellows disease of potato (Solanum tuberosum L.) and tomato (Solanum lycopersicum L.) in North America and is transmitted by Bactericera cockerelli (Hansen et al. 2008). Candidatus Liberibacter solanacearum was reported from tomato, capsicum (Capsicum annuum), potato, tamarillo (Solanum betaceum), cape gooseberry (Physalis peruviana), and chilli (Capsicum sp.) from New Zealand; it is transmitted by the psyllid Bactericera cockerelli. It has also been detected in the USA in potatoes affected by zebra chip disease (Liefting et al. 2009). Candidatus Liberibacter solanacearum and its vector Bactericera cockerelli have been placed on the EPPO A1 and A2 lists, respectively, and are considered of particular concern for southern and central parts of the EPPO region and for areas with mild winters in the northern part (http://www.eppo.int/QUARANTINE/quarantine.htm).
Candidatus Liberibacter europaeus, the most recently described species, is the only one presently considered to be an endophyte rather than a plant pathogen. It was reported from Italy and is found in the midgut lumen, salivary glands, and Malpighian tubules of the pear psyllid pest Cacopsylla pyri and has been detected in pear plant tissue, both in laboratory-inoculated plants and in field-collected samples. However, the plants remained free of disease symptoms (Raddadi et al. 2011).
As the family Phyllobacteriaceae comprises many soil bacteria and other free-living bacteria, it is not surprising that many species show diverse resistance patterns to a number of antibiotics which they can be expected to encounter in their natural habitat. These characters can often be used for phenotypic differentiation and have therefore been included above in the Sect 3, “Phenotypic Analyses”.
Application
Most strains of the genus Mesorhizobium are capable of nitrogen-fixing symbiosis in root nodules of legume plants, allowing the host plant to grow in soils with lower nitrogen content than other plants. Several agricultural crops, including chickpea (Cicer arietinum), alfalfa or lucerne (Medicago sativa), and several Lotus species (Table 18.11 ), are nodulated by mesorhizobia, and these bacteria thus make an important contribution to the success of these crops. Interest to introduce new Lotus forage species in Australia has stimulated research into compatible Mesorhizobium strains (Howieson et al. 2011). Mesorhizobium strains are also important as symbionts of legume trees such as Acacia and Prosopis spp. used in tropical agroforestry systems (de Lajudie et al. 1998; Bala et al. 2003; Degefu et al. 2013).
In addition to symbiotic nitrogen fixation, several strains of Mesorhizobium and Phyllobacterium are recognized for other plant growth-promoting effects. Mesorhizobia can exert these effects by producing the plant hormone indole acetic acid or ammonia (Ahmad et al. 2008). Mesorhizobium mediterraneum PECA21 was shown to solubilize phosphorus from tricalcium phosphate and improve growth and phosphorus content in chickpea (Peix et al. 2001). Mesorhizobium loti MP6 was shown to increase yield and resistance to white rot (Sclerotinia sclerotiorum) in Brassica campestris in India (Chandra et al. 2007). Other strains are resistant to heavy metals (Maynaud et al. 2013). Phyllobacterium brassicacearum STM 196 was shown to promote the growth of oilseed rape and Arabidopsis and to stimulate root hair elongation possibly through activation of the ethylene signalling pathway (Mantelin et al. 2006a; Galland et al. 2012).
A strategy for the regeneration of disused mining site is through revegetation to allow sustainable plant cover to stabilize the site and limit wider environmental impact. In France, Anthyllis vulneraria is one of the legume species tolerant of these contaminated sites (Mahieu et al. 2011). It is nodulated by two members of the Phyllobacteriaceae: Aminobacter anthyllidis and Mesorhizobium metallidurans. Both species are tolerant to high concentrations of heavy metals and contribute through this symbiosis to the success of the legume species in the process of revegetation of contaminated sites (Vidal et al. 2009; Maynaud et al. 2012). The combined inoculation of legumes with plant growth-promoting rhizobacteria and Mesorhizobium loti strains that have the enzyme 1-aminocyclopropane-1-carboxylate (ACC) deaminase which hydrolyzes the precursor to the plant hormone ethylene was shown to have a synergistic positive effect on plant growth, nutrition, and adaptation to metal-polluted soils. The ACC-hydrolyzing bacteria eliminate the plant growth inhibition caused by increased ethylene production and can thus be valuable participants in the phytostabilization of contaminated mining sites (Safronova et al. 2012). In an application of the same mechanism, a strain of Mesorhizobium ciceri transformed to express exogenous ACC deaminase was shown to improve yields of chickpea and reduce susceptibility to root rot disease (Nascimento et al. 2012). One highly chromium-tolerant Mesorhizobium strain was shown to improve the yield and decrease chromium uptake in chickpea (Wani et al. 2008).
Aminobacter strains were reported to be responsible for the degradation of 2,6-dichlorobenzamide, a frequent groundwater pollutant that is a degradation product of the herbicide 2,6-dichlorobenzonitrile (dichlobenil). A specific PCR test targeting the 16S rRNA genes was designed to monitor the distribution of Aminobacter strains (Sjoholm et al. 2010). Aminobacter aminovorans strains previously classified as Chelatobacter heintzii are able to degrade nitrilotriacetate and EDTA (Auling et al. 1993; Nortemann 1999). Chelativorans species are also able to degrade EDTA and particularly Chelativorans oligotrophicus has been applied in biofilters to remove EDTA and EDTA-metal complexes (Kuvichkina et al. 2012; Kaparullina et al. 2012).
Pseudaminobacter strains have been investigated for use in bioremediation of soil contaminated with atrazine and one strain was reported to use as sole carbon and nitrogen source (Topp 2001). They have also been implicated in the degradation of methyl parathion (Zhang et al. 2005).
The salicylate 1,2-dioxygenase from Pseudaminobacter salicylatoxidans BN12T has been characterized extensively (Hintner et al. 2004; Matera et al. 2008; Ferraroni et al. 2012). A soil isolate very similar to Pseudaminobacter salicylatoxidans was shown to be a sulfur chemolithotroph (Bagchi et al. 2005; Mandal et al. 2007).
References
Ahmad F, Ahmad I, Khan MS (2008) Screening of free-living rhizospheric bacteria for their multiple plant growth promoting activities. Microbiol Res 163:173–181
Ahrens R (1968) Taxonomische Untersuchungen an sternbildenden Agrobacterium-Arten aus der westlichen Ostsee. Kieler Meeresforsch 24:147–173
Ahrens A, Lipski A, Klatte S, Busse HJ, Auling G, Altendorf K (1997) Polyphasic classification of Proteobacteria isolated from biofilters. Syst Appl Microbiol 20:255–267
Auling G, Busse HJ, Egli T, Elbanna T, Stackebrandt E (1993) Description of the Gram-negative, obligately aerobic, nitriloacetate (NTA)-utilizing bacteria as Chelatobacter heintzii, gen. nov., sp. nov. and Chelatococcus asaccharovorans, gen. nov., sp. nov. Syst Appl Microbiol 16:104–112
Bagchi A, Roy D, Roy P (2005) Homology modeling of a transcriptional regulator SoxR of the lithotrophic sulfur oxidation (Sox) operon in alpha-proteobacteria. J Biomol Struct Dyn 22:571–577
Bala A, Murphy P, Giller KE (2003) Distribution and diversity of rhizobia nodulating agroforestry legumes in soils from three continents in the tropics. Mol Ecol 12:917–929
Balch WE, Fox GE, Magrum LJ, Woese CR, Wolfe RS (1979) Methanogens—re-evaluation of a unique biological group. Microbiol Rev 43:260–296
Bambauer A, Rainey FA, Stackebrandt E, Winter J (1998) Characterization of Aquamicrobium defluvii gen. nov. sp. nov., a thiophene-2-carboxylate-metabolizing bacterium from activated sludge. Arch Microbiol 169:293–302
Baymiev AK, Ivanova ES, Ptitsyn KG, Chubukova OV (2011) Phylogenetic analysis of symbiotic genes of nodule bacteria in plants of the genus Lathyrus (L.) (Fabaceae). Mol Genet Microbiol Virol 26:154–158
Berger P, Papazian L, Drancourt M, La Scola B, Auffray JP, Raoult D (2006) Ameba-associated microorganisms and diagnosis of nosocomial pneumonia. Emerg Infect Dis 12:248–255
Bertrand H, Nalin R, Bally R, Cleyet-Marel JC (2001) Isolation and identification of the most efficient plant growth-promoting bacteria associated with canola (Brassica napus). Biol Fert Soils 33:152–156
Bibi F, Yasir M, Song GC, Lee SY, Chung YR (2012) Diversity and characterization of endophytic bacteria associated with tidal flat plants and their antagonistic effects on oomycetous plant pathogens. Plant Pathol J 28:20–31
Biebl H, Allgaier M, Tindall BJ, Koblizek M, Lünsdorf H, Pukal R, Wagner-Döbler I (2005) Dinoroseobacter shibae gen. nov., sp. nov., a new aerobic phototrophic bacterium isolated from dinoflagellates. Int J Syst Evol Microbiol 55:1089–1096
Biebl H, Tindall BJ, Pukall R, Lunsdorf H, Allgaier M, Wagner-Dobler I (2006) Hoeflea phototrophica sp. nov., a novel marine aerobic alphaproteobacterium that forms bacteriochlorophyll a. Int J Syst Evol Microbiol 56:821–826
Chandra S, Choure K, Dubey RC, Maheshwari DK (2007) Rhizosphere competent Mesorhizobium loti MP6 induces root hair curling, inhibits Sclerotinia sclerotiorum and enhances growth of Indian mustard (Brassica campestris). Braz J Microbiol 38:124–130
Chen WX, Li GS, Qi YL, Wang ET, Yuan HL, Li JL (1991) Rhizobium huakuii sp. nov. isolated from the root-nodules of Astragalus sinicus. Int J Syst Evol Microbiol 41:275–280
Chen WX, Wang E, Wang SY, Li YB, Chen XQ (1995) Characteristics of Rhizobium tianshanense sp. nov., a moderately and slowly growing root-nodule bacterium isolated from an arid saline environment in Xinjiang, People’s Republic of China. Int J Syst Evol Microbiol 45:153–159
Chen WX, Wang ET, Kuykendall LD (2005) Genus VI. Mesorhizobium. In: Brenner DJ, Krieg NR, Staley JT (eds) Bergey’s manual of systematic bacteriology, vol 2C, 2nd edn. Springer, New York, pp 403–408
Chen YP, Rekha PD, Arun AB, Shen FT, Lai WA, Young CC (2006) Phosphate solubilizing bacteria from subtropical soil and their tricalcium phosphate solubilizing abilities. Appl Soil Ecol 34:33–41
Chen WM, Zhu WF, Bontemps C, Young JPW, Wei GH (2010) Mesorhizobium alhagi sp.nov., isolated from wild Alhagi sparsifolia in north-western China. Int J Syst Evol Microbiol 60:958–962
Chen WM, Zhu WF, Bontemps C, Young JPW, Wei GH (2011) Mesorhizobium camelthorni sp. nov., isolated from Alhagi sparsifolia Int. J Syst Evol Microbiol 61:574–579
Chistyakova TI, Dedyukhina EG, Satroutdinov AD, Kaparullina EN, Gavrish EY, Eroshin VK (2005) EDTA-dependent bacterial strain. Process Biochem 40:601–605
Chung EJ, Park JA, Pramanik P, Bibi F, Jeon CO, Chung YR (2013) Hoeflea suaedae sp. nov., an endophytic bacterium isolated from the root of the halophyte Suaeda maritima. Int J Syst Evol Microbiol 63:2277–2281
Cong Q, Kinch LN, Kim BH, Grishin NV (2012) Predictive sequence analysis of the Candidatus Liberibacter asiaticus proteome. PLoS One 7:e41071
Coulter C, Hamilton JTG, McRoberts WC, Kulakov L, Larkin MJ, Harper DB (1999) Halomethane : bisulfide/halide ion methyltransferase, an unusual corrinoid enzyme of environmental significance isolated from an aerobic methylotroph using chloromethane as the sole carbon source. Appl Environ Microb 65:4301–4312
Dai J, Liu X, Wang Y (2012) Genetic diversity and phylogeny of rhizobia isolated from Caragana microphylla growing in desert soil in Ningxia, China. Genet Mol Res 11:2683–2693
de Lajudie P, Willems A, Nick G, Moreira F, Molouba F, Hoste B, Torck U, Neyra M, Collins MD, Lindström K, Dreyfus B, Gillis M (1998) Characterization of tropical tree rhizobia and description of Mesorhizobium plurifarium sp. nov. Int J Syst Bacteriol 48:369–382
Degefu T, Wolde-meskel E, Liu BB, Cleenwerck I, Willems A, Frostegård A (2013) Mesorhizobium shonense sp. nov., Mesorhizobium hawassense sp. nov. and Mesorhizobium abyssinicae sp. nov., isolated from root nodules of different agroforestry legume trees. Int J Syst Evol Microbiol 63:1746–1753
Doronina NV, Kaparullina EN, Trotsenko YA, Nortemann B, Bucheli-Witschel M, Weilenmann HU, Egli T (2010) Chelativorans multitrophicus gen. nov., sp. nov. and Chelativorans oligotrophicus sp. nov., aerobic EDTA-degrading bacteria. Int J Syst Evol Microbiol 60:1044–1051
Duan YP, Zhou LJ, Hall DG, Li WB, Doddapaneni H, Lin H, Liu L, Vahling CM, Gabriel DW, Williams KP, Dickerman A, Sun YJ, Gottwald T (2009) Complete genome sequence of citrus Huanglongbing bacterium, ‘Candidatus Liberibacter asiaticus’ obtained through metagenomics. Mol Plant Microbe In 22:1011–1020
Egli T, Weilenmann HU, Elbanna T, Auling G (1988) Gram-negative, aerobic, nitriloacetate-utilizing bacteria from waste-water and soil. Syst Appl Microbiol 10:297–305
Ferraroni M, Matera I, Steimer L, Burger S, Scozzafava A, Stolz A, Briganti F (2012) Crystal structures of salicylate 1,2-dioxygenase-substrates adducts: a step towards the comprehension of the structural basis for substrate selection in class III ring cleaving dioxygenases. J Struct Biol 177:431–438
Flores-Felix JD, Carro L, Velazquez E, Valverde A, Cerda-Castillo E, Garcia-Fraile P, Rivas R (2013) Phyllobacterium endophyticum sp.nov., isolated from nodules of Phaseolus vulgaris. Int J Syst Evol Microbiol 63:821–826
Fritsche K, Auling G, Andreesen JR, Lechner U (1999) Defluvibacter lusatiae gen. nov., sp.nov., a new chlorophenol-degrading member of the alpha-2 subgroup of proteobacteria. Syst Appl Microbiol 22:197–204
Galland M, Gamet L, Varoquaux F, Touraine B, Desbrosses G (2012) The ethylene pathway contributes to root hair elongation induced by the beneficial bacteria Phyllobacterium brassicacearum STM196. Plant Sci 190:74–81
Gao JL, Turner SL, Kan FL, Wang ET, Tan ZY, Qiu YH, Gu J, Terefework Z, Young JPW, Lindström K, Chen WX (2004) Mesorhizobium septentrionale sp. nov. and Mesorhizobium temperatum sp. nov., isolated from Astragalus adsurgens growing in the northern regions of China. Int J Syst Evol Microbiol 54:2003–2012
Garnier M (2005) Genus V. Candidatus Liberibater. In: Brenner DJ, Krieg NR, Staley JT (eds) Bergey’s manual of systematic bacteriology, vol 2C, 2nd edn. Springer, New York, pp 400–402
Garnier M, Jagoueix-Eveillard S, Cronje PR, Le Roux HF, Bove JM (2000) Genomic characterization of a liberibacter present in an ornamental rutaceous tree, Calodendrum capense, in the Western Cape province of South Africa. Proposal of ‘Candidatus Liberibacter africanus subsp. capensis’. Int J Syst Evol Microbiol 50:2119–2125
Garrity GM, Bell JA, Lilburn T (2005) Family I. Rhodobacteraceae fam. nov. In: Brenner DJ, Krieg NR, Staley JT (eds) Bergey’s manual of systematic bacteriology, vol 2C, 2nd edn. Springer, New York, p 161
Ghosh W, Dam B (2009) Biochemistry and molecular biology of lithotrophic sulfur oxidation by taxonomically and ecologically diverse bacteria and archaea. FEMS Microbiol Rev 33:999–1043
Ghosh W, Roy P (2006) Mesorhizobium thiogangeticum sp. nov., a novel sulfur-oxidizing chemolithoautotroph from rhizosphere soil of an Indian tropical leguminous plant. Int J Syst Evol Microbiol 56:91–97
Gonzalez-Bashan LE, Lebsky VK, Hernandez JP, Bustillos JJ, Bashan Y (2000) Changes in the metabolism of the microalga Chlorella vulgaris when coimmobilized in alginate with the nitrogen-fixing Phyllobacterium myrsinacearum. Can J Microbiol 46:653–659
Guan SH, Chen WF, Wang ET, Lu YL, Yan XR, Zhang XX, Chen WX (2008) Mesorhizobium caraganae sp. nov., a novel rhizobial species nodulated with Caragana spp. in China. Int J Syst Evol Microbiol 58:2646–2653
Han TX, Han LL, Wu LJ, Chen WF, Sui XH, Gu JG, Wang ET, Chen WX (2008) Mesorhizobium gobiense sp.nov and Mesorhizobium tarimense sp. nov., isolated from wild legumes growing in desert soils of Xinjiang, China. Int J Syst Evol Microbiol 58:2610–2618
Hanert H (1981) The genus Gallionella. In: Starr M, Trüper H, Balows A, Schlegel H (eds) The Prokaryotes. A handbook on habitats, isolation, and identification of bacteria, vol 1. Springer, Berlin, pp 509–515
Hansen AK, Trumble JT, Stouthamer R, Paine TD (2008) A new huanglongbing species, “Candidatus Liberibacter psyllaurous,” found to infect tomato and potato, is vectored by the psyllid Bactericera cockerelli (Sulc). Appl Environ Microbiol 74:5862–5865
Hao XL, Lin YB, Johnstone L, Baltrus DA, Miller SJ, Wei GH, Rensing C (2012) Draft genome sequence of plant growth-promoting rhizobium Mesorhizobium amorphae, isolated from zinc-lead mine tailings. J Bacteriol 194:736–737
Hintner JP, Remtsma T, Stolz A (2004) Biochemical and molecular characterization of a ring fission dioxygenase with the ability to oxidize (substituted) salicylate(s) from Pseudaminobacter salicylatoxidans. J Biol Chem 279:37250–37260
Hoque MS, Broadhurst LM, Thrall PH (2011) Genetic characterization of root-nodule bacteria associated with Acacia salicina and A. stenophylla (Mimosaceae) across south-eastern Australia. Int J Syst Evol Microbiol 61:299–309
Howieson JG, Ballard RA, Yates RJ, Charman N (2011) Selecting improved Lotus nodulating rhizobia to expedite the development of new forage species. Plant Soil 348:231–243
Jagoueix S, Bove JM, Garnier M (1994) The phloem-limited bacterium of greening disease of citrus is a member of the Alpha-subdivision of the Proteobacteria. Int J Syst Bacteriol 44:379–386
Jang GI, Hwang CY, Cho BC (2011) Nitratireductor aquimarinus sp. nov., isolated from a culture of the diatom Skeletonema costatum, and emended description of the genus Nitratireductor. Int J Syst Evol Microbiol 61:2676–2681
Jarvis BDW, Pankhurst CE, Patel JJ (1982) Rhizobium loti, a new species of legume root nodule bacteria. Int J Syst Bacteriol 32:378–380
Jarvis BDW, VanBerkum P, Chen WX, Nour SM, Fernandez MP, Cleyet-Marel JC, Gillis M (1997) Transfer of Rhizobium loti, Rhizobium huakuii, Rhizobium ciceri, Rhizobium mediterraneum, and Rhizobium tianshanense to Mesorhizobium gen. nov. Int J Syst Bacteriol 47:895–898
Jin HM, Kim JM, Jeon CO (2013) Aquamicrobium aestuarii sp. nov., a marine bacterium isolated from a tidal flat. Int J Syst Evol Microbiol 63:4012–4017
Jung YT, Park S, Lee JS, Oh TK, Yoon JH (2012) Pseudahrensia aquimaris gen. nov., sp. nov., isolated from seawater. Int J Syst Evol Microbiol 62:2056–2061
Jung MY, Shin KS, Kim S, Kim SJ, Park SJ, Kim JG, Cha IT, Kim MN, Rhee SK (2013) Hoeflea halophila sp.nov., a novel bacterium isolated from marine sediment of the East Sea, Korea. Anton Leeuw Int J Gen 103:971–978
Jurado V, Laiz L, Gonzalez JM, Hernandez-Marine M, Valens M, Saiz-Jimenez C (2005) Phyllobacterium catacumbae sp. nov., a member of the order ‘Rhizobiales’ isolated from Roman catacombs. Int J Syst Evol Microbiol 55:1487–1490
Kämpfer P (2005) Genus VII. Pseudaminobacter. In: Brenner DJ, Krieg NR, Staley JT (eds) Bergey’s manual of systematic bacteriology, vol 2C, 2nd edn. Springer, New York, pp 409–410
Kämpfer P, Muller C, Mau M, Neef A, Auling G, Busse HJ, Osborn AM, Stolz A (1999) Description of Pseudaminobacter gen. nov. with two new species, Pseudaminobacter salicylatoxidans sp. nov. and Pseudaminobacter defluvii sp. nov. Int J Syst Bacteriol 49:887–897
Kämpfer P, Neef A, Salkinoja-Salonen MS, Busse HJ (2002) Chelatobacter heintzii (Auling et al. 1993) is a later subjective synonym of Aminobacter aminovorans (Urakami et al. 1992). Int J Syst Evol Microbiol 52:835–839
Kämpfer P, Martin E, Lodders N, Jackel U (2009) Transfer of Defluvibacter lusatiensis to the genus Aquamicrobium as Aquamicrobium lusatiense comb. nov. and description of Aquamicrobium aerolatum sp. nov. Int J Syst Evol Microbiol 59:2468–2470
Kaneko T, Nakamura Y, Sato S, Asamizu E, Kato T, Sasamoto S, Watanabe A, Idesawa K, Ishikawa A, Kawashima K, Kimura T, Kishida Y, Kiyokawa C, Kohara M, Matsumoto M, Matsuno A, Mochizuki Y, Nakayama S, Nakazaki N, Shimpo S, Sugimoto M, Takeuchi C, Yamada M, Tabata S (2000) Complete genome structure of the nitrogen-fixing symbiotic bacterium Mesorhizobium loti. DNA Res 7:331–338
Kang HS, Yang HL, Lee SD (2009) Nitratireductor kimnyeongensis sp. nov., isolated from seaweed. Int J Syst Evol Microbiol 59:1036–1039
Kaparullina EN, Doronina NV, Ezhov VA, Trotsenko YA (2012) EDTA degradation by cells of Chelativorans oligotrophicus immobilized on a biofilter. Appl Biochem Microbiol 48:396–400
Kaparullina EN, Doronina NV, Trotsenko YA (2011) Aerobic degradation of ethylenediaminetetraacetate (review). Appl Biochem Microbiol 47:460–473
Katayama-Fujimura Y, Enokizono Y, Kaneko T, Kuraishi H (1983) Deoxyribonucleic acid homologies among species of the genus Thiobacillus. J Gen Appl Microbiol 29:287–295
Khan Z, Doty SL (2009) Characterization of bacterial endophytes of sweet potato plants. Plant Soil 322:197–207
Kim KH, Roh SW, Chang HW, Nam YD, Yoon JH, Jeon CO, Oh HM, Bae JW (2009) Nitratireductor basaltis sp. nov., isolated from black beach sand. Int J Syst Evol Microbiol 59:135–138
Knösel DH (1984) Genus IV. Phyllobacterium (ex Knösel 1962) nom. rev. (Phyllobacterium Knösel 1962, 96). In: Krieg NR, Holt JG (eds) Bergey's manual of systematic bacteriology, vol 1. Williams & Wilkins, Baltimore, pp 254–256
Krick A, Kehraus S, Eberl L, Riedel K, Anke H, Kaesler I, Graeber I, Szewzyk U, Konig GM (2007) A marine Mesorhizobium sp. produces structurally novel long-chain N-acyl-L-homoserine lactones. Appl Environ Microbiol 73:3587–3594
Kuvichkina TN, Kaparullina EN, Doronina NV, Trotsenko YA, Reshetilov AN (2012) Degradation of the EDTA and EDTA complexes with metals by immobilized cells of Chelativorans oligotrophicus LPM-4 bacteria. Appl Biochem Microbiol 48:564–568
La Scola B, Boyadjiev I, Greub G, Khamis A, Martin C, Raoult D (2003) Amoeba-resisting bacteria and ventilator-associated pneumonia. Emerg Infect Dis 9:815–821
Labbé N, Juteau P, Parent S, Villemur R (2003) Bacterial diversity in a marine methanol-fed denitrification reactor at the Montreal biodome, Canada. Microb Ecol 46:12–21
Labbé N, Parent S, Villemur R (2004) Nitratireductor aquibiodomus gen. nov., sp. nov., a novel alpha-proteobacterium from the marine denitrification system of the Montreal Biodome (Canada). Int J Syst Evol Microbiol 54:269–273
Lai QL, Yuan J, Wu CL, Shao ZZ (2009) Oceanibaculum indicum gen. nov., sp. nov., isolated from deep seawater of the Indian Ocean. Int J Syst Evol Microbiol 59:1733–1737
Lai QL, Yu ZW, Wang JN, Zhong HZ, Sun FQ, Wang LP, Wang BJ, Shao ZZ (2011a) Nitratireductor pacificus sp.nov., isolated from a pyrene-degrading consortium. Int J Syst Evol Microbiol 61:1386–1391
Lai QL, Yu ZW, Yuan J, Sun FQ, Shao ZZ (2011b) Nitratireductor indicus sp. nov., isolated from deep-sea water. Int J Syst Evol Microbiol 61:295–298
Lai QL, Li GZ, Shao ZZ (2012a) Genome sequence of Nitratireductor pacificus type strain pht-3B. J Bacteriol 194:6958
Lai QL, Li GZ, Yu ZW, Shao ZZ (2012b) Genome sequence of Nitratireductor indicus type strain C115. J Bacteriol 194:6990
Lambert B, Joos H, Dierickx S, Vantomme R, Swings J, Kersters K, Vanmontagu M (1990) Identification and plant interaction of a Phyllobacterium sp., a predominant rhizobacterium of young sugar-beet plants. Appl Environ Microbiol 56:1093–1102
Lee SD (2006) Phycicoccus jejuensis gen. nov., sp. nov., an actinomycete isolated from seaweed. Int J Syst Evol Microbiol 56:2369–2373
Lei X, Wang E, Chen W, Sui X (2008) Diverse bacteria isolated from root nodules of wild Vicia species grown in temperate region of China. Arch Microbiol 190:657–671
Liefting LW, Weir BS, Pennycook SR, Clover GRG (2009) ‘Candidatus Liberibacter solanacearum’, associated with plants in the family Solanaceae. Int J Syst Evol Microbiol 59:2274–2276
Lin H, Lou BH, Glynn JM, Doddapaneni H, Civerolo EL, Chen CW, Duan YP, Zhou LJ, Vahling CM (2011) The complete genome sequence of ‘Candidatus Liberibacter solanacearum’, the bacterium associated with potato zebra chip disease. PLoS One 6:e19135
Lipski A, Kämpfer P (2012) Aquamicrobium ahrensii sp.nov and Aquamicrobium segne sp. nov., isolated from experimental biofilters. Int J Syst Evol Microbiol 62:2511–2516
Lu YL, Chen WF, Wang ET, Han LL, Zhang XX, Chen WX, Han SZ (2009) Mesorhizobium shangrilense sp.nov., isolated from root nodules of Caragana species. Int J Syst Evol Microbiol 59:3012–3018
Mahieu S, Frerot H, Vidal C, Galiana A, Heulin K, Maure L, Brunel B, Lefebvre C, Escarre J, Cleyet-Marel JC (2011) Anthyllis vulneraria/Mesorhizobium metallidurans, an efficient symbiotic nitrogen fixing association able to grow in mine tailings highly contaminated by Zn, Pb and Cd. Plant Soil 342:405–417
Mandal S, Chatterjee S, Dam B, Roy P, Das Gupta SK (2007) The dimeric repressor SoxR binds cooperatively to the promoter(s) regulating expression of the sulfur oxidation (sox) operon of Pseudaminobacter salicylatoxidans KCT001. Microbiol SGM 153:80–91
Manickam N, Pareek S, Kaur I, Singh NK, Mayilraj S (2012) Nitratireductor lucknowense sp. nov., a novel bacterium isolated from a pesticide contaminated soil. Anton Leeuw Int J Gen 101:125–131
Mantelin S, Desbrosses G, Larcher M, Tranbarger TJ, Cleyet-Marel JC, Touraine B (2006a) Nitrate-dependent control of root architecture and N nutrition are altered by a plant growth-promoting Phyllobacterium sp. Planta 223:591–603
Mantelin S, Fischer-Le Saux M, Zakhia F, Bena G, Bonneau S, Jeder H, de Lajudie P, Cleyet-Marel JC (2006b) Emended description of the genus Phyllobacterium and description of four novel species associated with plant roots: Phyllobacterium bourgognense sp. nov., Phyllobacterium ifriqiyense sp. nov., Phyllobacterium leguminum sp. nov and Phyllobacterium brassicacearum sp. nov. Int J Syst Evol Microbiol 56:827–839
Matera I, Ferraroni M, Burger S, Scozzafava A, Stolz A, Briganti F (2008) Salicylate 1,2-dioxygenase from Pseudaminobacter salicylatoxidans: crystal structure of a peculiar ring-cleaving dioxygenase. J Mol Biol 380:856–868
Maynaud G, Willems A, Soussou S, Vidal C, Maure L, Moulin L, Cleyet-Marel JC, Brunel B (2012) Molecular and phenotypic characterization of strains nodulating Anthyllis vulneraria in mine tailings, and proposal of Aminobacter anthyllidis sp. nov., the first definition of Aminobacter as legume-nodulating bacteria. Syst Appl Microbiol 35:65–72
Maynaud G, Brunel B, Mornico D, Durot M, Severac D, Dubois E, Navarro E, Cleyet-Marel JC, Le Quere A (2013) Genome-wide transcriptional responses of two metal-tolerant symbiotic Mesorhizobium isolates to zinc and cadmium exposure. BMC Genomics 14
McDonald IR, Kämpfer P, Topp E, Warner KL, Cox MJ, Hancock TLC, Miller LG, Larkin MJ, Ducrocq V, Coulter C, Harper DB, Murrell JC, Oremland RS (2005) Aminobacter ciceronei sp. nov and Aminobacter lissarensis sp. nov., isolated from various terrestrial environments. Int J Syst Evol Microbiol 55:1827–1832
Mergaert J, Swings J (2005a) Family IV. Phyllobacteriaceae fam. nov. In: Brenner DJ, Krieg NR, Staley JT (eds) Bergey’s manual of systematic bacteriology, vol 2C, 2nd edn. Springer, New York, p 393
Mergaert J, Swings J (2005b) Genus I. Phyllobacterium. In: Brenner DJ, Krieg NR, Staley JT (eds) Bergey’s manual of systematic bacteriology, vol 2C, 2nd edn. Springer, New York, pp 394–396
Mergaert J, Boley A, Cnockaert MC, Muller WR, Swings J (2001) Identity and potential functions of heterotrophic bacterial isolates from a continuous-upflow fixed-bed reactor for denitrification of drinking water with bacterial polyester as source of carbon and electron donor. Syst Appl Microbiol 24:303–310
Mergaert J, Cnockaert MC, Swings J (2002) Phyllobacterium myrsinacearum (subjective synonym Phyllobacterium rubiacearum) emend. Int J Syst Evol Microbiol 52:1821–1823
Miller LG, Connell TL, Guidetti JR, Oremland RS (1997) Bacterial oxidation of methyl bromide in fumigated agricultural soils. Appl Environ Microbiol 63:4346–4354
Morgan JK, Zhou LJ, Li WB, Shatters RG, Keremane M, Duan YP (2012) Improved real-time PCR detection of ‘Candidatus Liberibacter asiaticus’ from citrus and psyllid hosts by targeting the intragenic tandem-repeats of its prophage genes. Mol Cell Probes 26:90–98
Nandasena KG, O’Hara GW, Tiwari RP, Willems A, Howieson JG (2009) Mesorhizobium australicum sp. nov and Mesorhizobium opportunistum sp. nov., isolated from Biserrula pelecinus L. in Australia. Int J Syst Evol Microbiol 59:2140–2147
Nascimento FX, Brigido C, Glick BR, Oliveira S, Alho L (2012) Mesorhizobium ciceri LMS-1 expressing an exogenous 1-aminocyclopropane-1-carboxylate (ACC) deaminase increases its nodulation abilities and chickpea plant resistance to soil constraints. Lett Appl Microbiol 55:15–21
Nortemann B (1999) Biodegradation of EDTA. Appl Microbiol Biotech 51:751–759
Nortemann B, Knackmuss HJ, Rast HG (1986) Bacterial communities degrading aminonaphthalene-2-sulfonates and hydroxynaphthalene-2-sulfonates. Appl Environ Microbiol 52:1195–1202
Nour SM, Fernandez MP, Normand P, Cleyet-Marel JC (1994) Rhizobium ciceri sp. nov., consisting of strains that nodulate chickpeas (Cicer arietinum L.). Int J Syst Bacteriol 44:511–522
Nour SM, Cleyet-Marel JC, Normand P, Fernandez MP (1995) Genomic heterogeneity of strains nodulating chickpeas (Cicer arietinum L.) and description of Rhizobium mediterraneum sp. nov. Int J Syst Bacteriol 45:640–648
Oger PM, Mansouri H, Nesme X, Dessaux Y (2004) Engineering root exudation of lotus toward the production of two novel carbon compounds leads to the selection of distinct microbial populations in the rhizosphere. Microb Ecol 47:96–103
Palacios L, Arahal DR, Reguera B, Marin I (2006) Hoeflea alexandrii sp. nov., isolated from the toxic dinoflagellate Alexandrium minutum AL1V. Int J Syst Evol Microbiol 56:1991–1995
Park S, Lee JS, Lee KC, Yoon JH (2013) Lentilitoribacter donghaensis gen. nov., sp.nov., a slowly-growing alphaproteobacterium isolated from coastal seawater. Anton Leeuw Int J Gen 103:457–464
Peeters K, Verleyen E, Hodgson DA, Convey P, Ertz D, Vyverman W, Willems A (2012) Heterotrophic bacterial diversity in aquatic microbial mat communities from Antarctica. Polar Biol 35:543–554
Peix A, Rivas-Boyero AA, Mateos PF, Rodriguez-Barrueco C, Martinez-Molina E, Velazquez E (2001) Growth promotion of chickpea and barley by a phosphate solubilizing strain of Mesorhizobium mediterraneum under growth chamber conditions. Soil Biol Biochem 33:103–110
Peix A, Rivas R, Trujillo ME, Vancanneyt M, Velazquez E, Willems A (2005) Reclassification of Agrobacterium ferrugineum LMG 128 as Hoeflea marina gen. nov., sp. nov. Int J Syst Evol Microbiol 55:1163–1166
Pfennig N, Lippert KD (1966) Über das Vitamin B12-Bedürfnis phototropher Schwefelbakterien. Arch Mikrobiol 55:245–256
Pfennig N, Widdel F, Trüper HG (1981) The dissimilatory sulfate-reducing bacteria. In: Starr MP, Stolp H, Trüper HG, Balows H, Schlegel HG (eds) The prokaryotes, vol 1. Springer, Berlin, p 931
Raddadi N, Gonella E, Camerota C, Pizzinat A, Tedeschi R, Crotti E, Mandrioli M, Bianco P, Daffonchio D, Alma A (2011) ‘Candidatus Liberibacter europaeus’ sp. nov that is associated with and transmitted by the psyllid Cacopsylla pyri apparently behaves as an endophyte rather than a pathogen. Environ Microbiol 13:414–426
Ramirez-Bahena MH, Hernandez M, Peix A, Velazquez E, Leon-Barrios M (2012) Mesorhizobial strains nodulating Anagyris latifolia and Lotus berthelotii in Tamadaya ravine (Tenerife, Canary Islands) are two symbiovars of the same species, Mesorhizobium tamadayense sp. nov. Syst Appl Microbiol 35:334–341
Rasolomampianina R, Bailly X, Fetiarison R, Rabevohitra R, Bena G, Ramaroson L, Raherimandimby M, Moulin L, De Lajudie P, Dreyfus B, Avarre JC (2005) Nitrogen-fixing nodules from rose wood legume trees (Dalbergia spp.) endemic to Madagascar host seven different genera belonging to alpha- and beta-Proteobacteria. Mol Ecol 14:4135–4146
Rincon A, Arenal F, Gonzalez I, Manrique E, Lucas MM, Pueyo JJ (2008) Diversity of rhizobial bacteria isolated from nodules of the gypsophyte Ononis tridentata L. growing in Spanish soils. Microb Ecol 56:223–233
Rivas R, Laranjo M, Mateos PF, Oliveira S, Martinez-Molina E, Velazquez E (2007) Strains of Mesorhizobium amorphae and Mesorhizobium tianshanense, carrying symbiotic genes of common chickpea endosymbiotic species, constitute a novel biovar (ciceri) capable of nodulating Cicer arietinum. Lett Appl Microbiol 44:412–418
Roh SW, Kim KH, Nam YD, Chang HW, Kim MS, Shin KS, Yoon JH, Oh HM, Bae JW (2008) Aliihoeflea aestuarii gen. nov., sp. nov., a novel bacterium isolated from tidal flat sediment. J Microbiol 46:594–598
Rüger HJ, Höfle MG (1992) Marine star-shaped aggregate forming bacteria Agrobacterium atlanticum sp. nov., Agrobacterium meteori sp. nov., Agrobacterium ferrugineum sp. nov., nom. rev., and Agrobacterium stellatum sp. nov., nom. rev. Int J Syst Bacteriol 42:133–143
Safronova VI, Piluzza G, Zinovkina NY, Kimeklis AK, Belimov AA, Bullitta S (2012) Relationships between pasture legumes, rhizobacteria and nodule bacteria in heavy metal polluted mine waste of SW Sardinia. Symbiosis 58:149–159
Senoo K, Wada H (1989) Isolation and identification of an aerobic gamma-HCH decomposing bacterium from soil. Soil Sci Plant Nutr 35:79–87
Sfanos K, Harmody D, Dang P, Ledger A, Pomponi S, McCarthy P, Lopez J (2005) A molecular systematic survey of cultured microbial associates of deep-water marine invertebrates. Syst Appl Microbiol 28:242–264
Singh A, Jangir PK, Kumari C, Sharma R (2012) Genome sequence of Nitratireductor aquibiodomus strain RA22. J Bacteriol 194:6307
Sjoholm OR, Aamand J, Sorensen J, Nybroe O (2010) Degrader density determines spatial variability of 2,6-dichlorobenzamide mineralisation in soil. Environ Pollut 158:292–298
Sorokina AY, Chernousova EY, Dubinina GA (2012) Hoeflea siderophila sp. nov., a new neutrophilic iron-oxidizing bacterium. Microbiology 81:59–66
Stevenson BS, Waterbury JB (2006) Isolation and identification of an epibiotic bacterium associated with heterocystous Anabaena cells. Biol Bull 210:73–77
Stevenson BS, Suflita MT, Stamps BW, Moore ERB, Johnson CN, Lawson PA (2011) Hoeflea anabaenae sp. nov., an epiphytic symbiont that attaches to the heterocysts of a strain of Anabaena. Int J Syst Evol Microbiol 61:2439–2444
Tamura K, Peterson D, Peterson N, Stecher G, Nei M, Kumar S (2011) MEGA5: molecular evolutionary genetics analysis using maximum likelihood, evolutionary distance, and maximum parsimony methods. Mol Biol Evol 28:2731–2739
Texeira DC, Ayres J, de Barros AP, Kitajima EW, Tanaka FAO, Danet L, Jagoueix-Eveillard S, Saillard C, Bove JM (2005) First report of a huanglongbing-like disease of citrus in Sao Paulo State, Brazil and association of a new liberibacter species, “Candidatus Liberibacter americanus”, with the disease. Plant Dis 89:107
Topp E (2001) A comparison of three atrazine-degrading bacteria for soil bioremediation. Biol Fertil Soils 33:529–534
Turner SL, Zhang XX, Li FD, Young PW (2002) What does a bacterial genome sequence represent? Mis-assignment of MAFF 303099 to the genospecies Mesorhizobium loti. Microbiol SGM 148:3330–3331
Tyler HL, Roesch LFW, Gowda S, Dawson WO, Triplett EW (2009) Confirmation of the sequence of ‘Candidatus Liberibacter asiaticus’ and assessment of microbial diversity in Huanglongbing-infected citrus phloem using a metagenomic approach. Mol Plant Microbe In 22:1624–1634
Uchino Y, Hirata A, Yokota A, Sugiyama J (1998) Reclassification of marine Agrobacterium species: proposals of Stappia stellulata gen. nov., comb. nov., Stappia aggregata sp. nov., nom. rev., Ruegeria atlantica gen. nov., comb. nov., Ruegeria gelatinovora comb. nov., Ruegeria algicola comb. nov., and Ahrensia kieliense gen. nov., sp. nov., nom. rev. J Gen Appl Microbiol 44:201–210
Ulrich A, Zaspel I (2000) Phylogenetic diversity of rhizobial strains nodulating Robinia pseudoacacia L. Microbiol SGM 146:2997–3005
Urakami T (2005) Genus II. Aminobacter. In: Brenner DJ, Krieg NR, Staley JT (eds) Bergey’s manual of systematic bacteriology, vol 2C, 2nd edn. Springer, New York, pp 397–399
Urakami T, Araki H, Oyanagi H, Suzuki KI, Komagata K (1992) Transfer of Pseudomonas aminovorans (den Dooren de Jong 1926) to Aminobacter gen. nov. as Aminobacter aminovorans comb. nov. and description of Aminobacter aganoensis sp. nov. and Aminobacter niigataensis sp. nov. Int J Syst Bacteriol 42:84–92
Valverde A, Velazquez E, Fernandez-Santos F, Vizcaino N, Rivas R, Mateos PF, Martinez-Molina E, Igual JM, Willems A (2005) Phyllobacterium trifolii sp.nov., nodulating Trifolium and Lupinus in Spanish soils. Int J Syst Evol Microbiol 55:1985–1989
Velazquez E, Igual JM, Willems A, Fernadez MP, Munoz E, Mateos PF, Abril A, Toro N, Normand P, Cervantes E, Gillis M, Martinez-Molina E (2001) Mesorhizobium chacoense sp.nov., a novel species that nodulates Prosopis alba in the Chaco Arido region (Argentina). Int J Syst Evol Microbiol 51:1011–1021
Vidal C, Chantreuil C, Berge O, Maure L, Escarre J, Bena G, Brunel B, Cleyet-Marel JC (2009) Mesorhizobium metallidurans sp. nov., a metal-resistant symbiont of Anthyllis vulneraria growing on metallicolous soil in Languedoc, France. Int J Syst Evol Microbiol 59:850–855
Vincent JM (1970) A manual for the practical study of the root-nodule bacteria. International Biology Program, Blackwell Scientific, Oxford, Handbook 15
Vishniac W, Santer M (1957) The thiobacilli. Bacteriol Rev 21:195–213
Wang ET, van Berkum P, Sui XH, Beyene D, Chen WX, Martinez-Romero E (1999) Diversity of rhizobia associated with Amorpha fruticosa isolated from Chinese soils and description of Mesorhizobium amorphae sp. nov. Int J Syst Bacteriol 49:51–65
Wang FQ, Wang ET, Liu J, Chen Q, Sui XH, Chen WF, Chen WX (2007) Mesorhizobium albiziae sp. nov., a novel bacterium that nodulates Albizia kalkora in a subtropical region of China. Int J Syst Evol Microbiol 57:1192–1199
Wang BJ, Lai QL, Cui ZS, Tan TF, Shao ZZ (2008) A pyrene-degrading consortium from deep-sea sediment of the West Pacific and its key member Cycloclasticus sp.P1. Environ Microbiol 10:1948–1963
Wani PA, Khan MS, Zaidi A (2008) Chromium-reducing and plant growth-promoting Mesorhizobium improves chickpea growth in chromium-amended soil. Biotechnol Lett 30:159–163
Weilenmann HU, Engeli B, Bucheli-Witschel M, Egli T (2004) Isolation and growth characteristics of an EDTA-degrading member of the alpha-subclass of Proteobacteria. Biodegradation 15:289–301
Widdel F, Kohring GW, Mayer F (1983) Studies on dissimilatory sulfate-reducing bacteria that decompose fatty acids. 3. Characterization of the filamentous gliding Desulfonema limicola gen. nov. spec. nov. and Desulfonema magnum sp. nov. Arch Microbiol 134 :286–294
Wolde-Meskel E, Terefework Z, Frostegård A, Lindström K (2005) Genetic diversity and phylogeny of rhizobia isolated from agroforestry legume species in southern Ethiopia. Int J Syst Evol Microbiol 55:1439–1452
Yabe S, Aiba Y, Sakai Y, Hazaka M, Yokota A (2012) Thermovum composti gen. nov., sp. nov., an alphaproteobacterium from compost. Int J Syst Evol Microbiol 62:2991–2996
Yarza P, Ludwig W, Euzeby J, Amann R, Schleifer KH, Glockner FO, Rossello-Mora R (2010) Update of the All-Species Living Tree project based on 16S and 23S rRNA sequence analyses. Syst Appl Microbiol 33:291–299
Zhang RF, Cui ZL, Jiang JD, He J, Gu XY, Li SP (2005) Diversity of organophosphorus pesticide-degrading bacteria in a polluted soil and conservation of their organophosphorus hydrolase genes. Can J Microbiol 51:337–343
Zhang MQ, Powell CA, Zhou LJ, He ZL, Stover E, Duan YP (2011) Chemical compounds effective against the citrus Huanglongbing bacterium ‘Candidatus Liberibacter asiaticus’ in planta. Phytopathology 101:1097–1103
Zhang JJ, Liu TY, Chen WF, Wang ET, Sui XH, Zhang XX, Li Y, Chen WX (2012) Mesorhizobium muleiense sp.nov., nodulating with Cicer arietinum L. Int J Syst Evol Microbiol 62:2737–2742
Zhao LF, Deng ZS, Yang WQ, Cao Y, Wang ET, Wei GH (2010) Diverse rhizobia associated with Sophora alopecuroides grown in different regions of Loess Plateau in China. Syst Appl Microbiol 33:468–477
Zhao CT, Wang ET, Zhang YM, Chen WF, Sui XH, Chen WX, Liu HC, Zhang XX (2012) Mesorhizobium silamurunense sp. nov., isolated from root nodules of Astragalus species. Int J Syst Evol Microbiol 62:2180–2186
Zheng WT, Li Y Jr, Wang R, Sui XH, Zhang XX, Zhang JJ, Wang ET, Chen WX (2013) Mesorhizobium qingshengii sp. nov., isolated from effective nodules of Astragalus sinicus. Int J Syst Evol Microbiol 63:2002–2007
Zhou PF, Chen WM, Wei GH (2010) Mesorhizobium robiniae sp. nov., isolated from root nodules of Robinia pseudoacacia. Int J Syst Evol Microbiol 60:2552–2556
Zhou ML, Chen WM, Chen HY, Wei GH (2012) Draft genome sequence of Mesorhizobium alhagi CCNWXJ12-2(Tau), a novel salt-resistant species isolated from the desert of northwestern China. J Bacteriol 194:1261–1262
Zhou S, Li Q, Jiang H, Lindström K, Zhang X (2013) Mesorhizobium sangaii sp. nov., isolated from the root nodules of Astragalus luteolus and Astragalus ernestii. Int J Syst Evol Microbiol 63:2794–2799
Author information
Authors and Affiliations
Corresponding author
Editor information
Editors and Affiliations
Rights and permissions
Copyright information
© 2014 Springer-Verlag Berlin Heidelberg
About this entry
Cite this entry
Willems, A. (2014). The Family Phyllobacteriaceae. In: Rosenberg, E., DeLong, E.F., Lory, S., Stackebrandt, E., Thompson, F. (eds) The Prokaryotes. Springer, Berlin, Heidelberg. https://doi.org/10.1007/978-3-642-30197-1_298
Download citation
DOI: https://doi.org/10.1007/978-3-642-30197-1_298
Published:
Publisher Name: Springer, Berlin, Heidelberg
Print ISBN: 978-3-642-30196-4
Online ISBN: 978-3-642-30197-1
eBook Packages: Biomedical and Life SciencesReference Module Biomedical and Life Sciences