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Systematic and Applied Microbiology 29 (2006) 404–413 www.elsevier.de/syapm

Propionicicella superfundia gen. nov., sp. nov., a chlorosolvent-tolerant propionate-forming, facultative anaerobic bacterium isolated from contaminated groundwater Hee-Sung Baea, William M. Moeb,Ã, Jun Yanb, Igor Tiagoc, Milton S. da Costad, Fred A. Raineya

aDepartment of Biological Sciences, Louisiana State University, Baton Rouge, LA 70803, USA bDepartment of Civil and Environmental Engineering, Louisiana State University, Baton Rouge, LA 70803, USA cDepartamento de Zoologia and Centro de Neurocieˆncias, Universidade de Coimbra, 3004-517 Coimbra, Portugal dDepartamento de Bioquı´mica and Centro de Neurocieˆncias, Universidade de Coimbra, 3001-401 Coimbra, Portugal

Received 5 October 2005

Abstract

A novel strain, designated as BL-10T, was characterized using a polyphasic approach after isolation from groundwater contaminated by a mixture of chlorosolvents that included 1,1,2-trichloroethane, 1,2-dichloroethane, and vinyl chloride. Stain BL-10T is a facultatively anaerobic bacterium able to ferment glucose to form propionate, acetate, formate, lactate, and succinate. Fermentation occurred in the presence of 1,2-dichloroethane and 1,1,2-trichloroethane at concentrations to at least 9.8 and 5.9 mM, respectively. Cells are Gram-positive, rod-shaped, non-motile, and do not form spores. Oxidase and catalase are not produced and nitrate reduction did not occur in PYG medium. Menaquinone MK-9 is the predominant respiratory quinone and meso-diaminopimelic acid is present in the cell wall peptidoglycan layer. Major cellular fatty acids are C15:0, iso C16:0, and anteiso C15:0. Genomic DNA G+C content is 69.9 mol%. Phylogenetic analysis based on 16S rRNA gene sequence comparisons showed strain BL-10T to fall within the radiation of genera Propionicimonas and Micropruina. On the basis of the results obtained in this study, it is proposed that strain BL-10T should be classified as a novel taxon, for which the name Propionicicella superfundia gen. nov., sp. nov. is proposed. The type strain of Propionicicella superfundia is BL-10T ( ¼ ATCC BAA-1218T, ¼ LMG 23096T).1 r 2005 Elsevier GmbH. All rights reserved.

Keywords: Propionicicella superfundia; Facultative anaerobe; Propionate; Chlorosolvent tolerant; DNAPL; Dechlorination

Introduction

From 1969 to 1980, petrochemical wastes including à Corresponding author. Tel.: +1 225 578 9174 free-phase chlorinated solvents were disposed of by E-mail address: [email protected] (W.M. Moe). 1Nucleotide sequence accession number. Nucleotide sequence data direct discharge to earthen ponds at the Brooklawn site, reported are available in the DDBJ/EMBL/GenBank databases under one of two areas that comprise what is now known as the accession number DQ176646. the Petro-Processors of Louisiana, Inc. (PPI) EPA

0723-2020/$ - see front matter r 2005 Elsevier GmbH. All rights reserved. doi:10.1016/j.syapm.2005.11.004 ARTICLE IN PRESS H.-S. Bae et al. / Systematic and Applied Microbiology 29 (2006) 404–413 405

Superfund Site, located approximately 10 miles north of differential interference contrast (DIC) microscopy Baton Rouge, LA (USA). Portions of the Brooklawn (Nikon microphot-Fxa) or transmission electron micro- area were capped in the early 1990s, and an array of scopy (JEOL 1000CX TEM). For TEM, cells were wells was installed to recover organic contaminants negatively stained using uranyl acetate (2%, v/v). Spore present in the subsurface as dense non-aqueous-phase formation and motility were observed using phase liquid (DNAPL) [9]. Residual DNAPL remains in the contrast microscopy (Nikon Optiphot). subsurface, and groundwater within the DNAPL source Gram staining was performed using a Gram Stain Kit zone contains high concentrations of chlorinated orga- (Difco) according to the manufacturer’s recommended nics including 1,1,2,2-tetrachloroethane, 1,1,2-trichloro- protocol. Catalase activity was assessed as described by ethane, 1,2-dichloroethane, 1,2-dichloropropane, hexa- Smibert and Krieg [36] using 3% hydrogen peroxide chloro-1,3-butadiene, and vinyl chloride. added to cells grown anaerobically on PYG agar plates. During a study aimed at characterizing the microbial Oxidase tests were performed using the tetramethyl- population present within the DNAPL source zone at p-phenylenediamine dihydrochloride filter paper techni- the PPI site in order to assess the potential for in situ que [36]. Aerobic growth was examined on several bioremediation, we isolated a novel bacterium desig- complex media including nutrient agar (Difco), PYG nated as strain BL-10T. To determine its taxonomic agar [4], plate count agar (Difco) and R2A (Difco) to position, a polyphasic approach, including phylogenetic, which no reducing agent was added. Nitrate reducing chemotaxonomic, and phenotypic assessment was con- ability in PYG cultures containing 10 mM sodium ducted. Results indicate that strain BL-10T should be nitrate was determined according to Smibert and Krieg classified as a novel genus and novel , for which [36]. Additional biochemical and physiological charac- the name Propionicicella superfundia, gen. nov, sp. nov. terization was conducted using Rapid ID 32A kits is proposed. (bioMe´rieux) with preparation and incubation per- formed in the anaerobic chamber. The cell suspension used to inoculate Rapid ID 32A kit was produced by Materials and methods flooding a CASB agar plate grown anaerobically at 30 1C for 14 days with API Suspension Medium provided in the kit. Isolation and bacterial strains Carbon utilization tests were performed in 16-mL Hungate tubes containing 10 mL of PY medium [4] and Groundwater samples were collected from well a headspace of N and CO (95:5, v/v). Each substrate W-1024-1 located in the DNAPL source zone at the 2 2 was added at a concentration of 5 or 10 g L1 for mono-, Brooklawn portion of the PPI site. Sterile, 1.0 L glass di-, and polysaccharides and sugar alcohols. Organic sample collection bottles were filled with groundwater acids were added at a concentration of 15 or 30 mM. leaving little or no headspace, and placed on ice during Cultures were inoculated using a 1% (v/v) of an transport to the laboratory (approximately 1 h). After exponentially growing seed culture. Tubes showing an serial dilution with a potassium phosphate buffer increase in OD of more than 0.1 OD unit above the (100 mM, pH 7.0) in an anaerobic chamber (Coy 660 controls without added carbon were recorded as Laboratory Products Inc., MI), 0.1 mL aliquots were positive. The pH range for growth was evaluated over spread on Columbia Anaerobic Sheep Blood agar plates the range pH 3.0–10.0 using buffers comprised of (CASB, BBL). Plates were incubated in the anaerobic 100 mM acetate buffer for pH 3.0–6.0, 100 mM potas- chamber (headspace 90% N ,5%CO, and 5% H )at 2 2 2 sium phosphate buffer for pH 6.0–8.0, and Tris buffer 30 1C for up to 5 weeks. Isolated colonies were for pH 8.0–10.0. Growth in the NaCl concentration subcultured on CASB agar and purity verified by range of 0–5% (w/v) and the temperature range microscopy. Propionicimonas paludicola strains WdT 10–40 1C was determined in Hungate tubes containing and Wf were kindly provided by Professor Atsuko Ueki 10 mL of PYG. of the Yamagata University, Japan. These reference The ability to use chlorosolvents as electron acceptors strains were maintained on CASB agar or PYG agar [4] was examined in 25-mL serum bottle containing 10 mL in the anaerobic chamber. The isolates were stored at of anaerobic basal medium [39] or in 1/10 strength PY 80 1C in PYG with 15% (v/v) glycerol and 5% (v/v) broth. The anaerobic medium was amended with dimethylsulfoxide. acetate, lactate, and pyruvate (each 2 mM) and one of the following chlorosolvents: 1,1,2-trichloroethane, Growth, morphological, biochemical, and tolerance 1,2-dichloroethane, tetrachloroethene, trichloroethene, characteristics cis-1,2-dichloroethene, or 1,2-dichloropropane (each 2.0 mmol). Serum bottle headspace gas consisted of N2, Growth of the organisms was examined in CASB and CO2, and H2 (80:10:10, v/v/v). The ability to degrade PYG media. Cell morphology was observed using aromatic compounds was also tested in serum bottles. ARTICLE IN PRESS 406 H.-S. Bae et al. / Systematic and Applied Microbiology 29 (2006) 404–413

Each bottle was amended with 0.5 mmol of benzene, cellulose plates using the solvent system of Rhuland toluene, ethylbenzene, or p-xylene. Serum bottle head- et al. [31], at DSMZ. space gas consisted of N2,CO2, and H2 (80:10:10, v/v/v) for anaerobic basal medium and N2 and CO2 (95:5, v/v) Analytical methods for PY/10. Serum bottles were sealed with butyl rubber stoppers and aluminum seals. Uninoculated bottles were Fermentation products from PYG grown cultures 1 used as negative controls. Incubation was at 30 C. were analyzed by ion chromatography (IC) using a The ability of strain BL-10 to grow in the presence of Metrohm peak 761 Compact IC equipped with a 1,2-dichloroethane (1,2-DCA) or 1,1,2-trichloroethane Metrosep Organic Acid Column (25 cm 7.8 mm) and (1,1,2-TCA) was examined in 120-mL serum bottles a conductivity detector. Isocratic elution was performed containing 80 mL of PYG supplemented with various 1 with 0.5 mM H2SO4 at a flow rate of 0.5 mL min and concentrations (ranging to 9.8 mM in the aqueous constant temperature of 25 1C. Retention times and phase) of 1,2-DCA or 1,1,2-TCA. The headspace was peak areas of products were compared to those of filled with a mixture of N2 and CO2 (95:5%, v/v). authentic standards that included acetic, butyric, formic, Growth based on OD was measured using a Smart TM lactic, isovaleric, propionic, pyruvic, and succinic acids. Spec Plus spectrophotometer (BioRAD) at 660 nm. Concentrations of chlorosolvents and aromatic com- pounds were analyzed using a gas chromatograph 16S rRNA gene sequence, phylogenetic analysis, and (HP6890, HP) equipped with a capillary column (GS- determination of G+C content of DNA Gaspro, 60 m 0.32 mm ID, J&W P/N 113-4362) and flame ionization detector. Helium was used as carrier 1 The extraction of genomic DNA, PCR amplification, gas at a flow rate of 45 mL min . Injector and detector and sequencing of the 16 rRNA gene was carried out as temperatures were 225 1C. Oven temperature increased 1 described previously [30]. Purified sequencing-reaction from 50 to 200 1C at a rate of 50 1C min . products were electrophoresed using a model 3100 DNA sequencer (Applied Biosystems). The 16S rRNA gene T sequence of strain BL-10 was aligned against pre- Results viously determined sequences available from the public databases using the BioEdit program Morphological, phenotypic, and physiological version 4.7.8 (http://www.mbio.ncsu.edu/BioEdit/page2. characteristics html) [17]. Phylogenetic analyses were performed using ARB (http://www.arb-home.de/) [37]. The neighbor- When grown on PYG plates incubated for 3 days at joining algorithm was used to build the phylogenetic 30 1C under anaerobic conditions, strain BL-10T formed tree, with Jukes–Cantor correction [21]. white, circular, convex and smooth surface colonies The G+C content of DNA was determined by HPLC 2–3 mm in diameter. Cells were Gram-positive, rod- as described by Mesbah et al. [27] following DNA shaped, 0.5 1.0–2.5 mm, and flagella were not observed isolation as described by Nielsen et al. [28]. (Fig. 1). Spore formation and cell motility were not observed when viewed using phase contrast microscopy. Chemotaxonomic characterization Strain BL-10T was oxidase and catalase negative. Under aerobic conditions weak growth occurred on Cellular fatty acids were extracted from exponential- nutrient agar (Difco), R2A (Difco) and PYG agar; phase PYG-grown cells using the modified method of much better growth was observed under anaerobic Bligh and Dyer as described by White et al. [43]. The conditions. Vitamin B12 was not required as a growth total lipid extract was fractionated by silicic acid factor for anaerobic growth in PYG. The optimal chromatography, the polar lipid fraction was transester- temperature for growth was 30 1C and growth occurred ified to fatty acid methyl esters and analyzed by gas within the range 15–37 1C. The optimal pH for growth chromatography/mass spectrometry (GC/MS) [16]. was pH 6.5 with growth occurring in the range 4.5–8.5. Analysis of respiratory lipoquinones was carried out Strain BL-10T utilized adonitol, erythritol, fructose, by the Identification Services of the DSMZ, Braunsch- glucose, glycerol, lactate, maltose, mannitol, mannose, weig, Germany. Quinones were extracted from 100 mg pyruvate, sucrose, sorbitol, and xylose. Acetate, arabi- of freeze-dried cell material and separated by thin layer nose, crystalline cellulose, ducitol, ethanol, fucose, chromatography and analyzed by HPLC as described by fumarate, galactose, lactose, malate, meliobiose, metha- Tindall [40,41]. nol, raffinose, starch, and succinate were not utilized. The presence of diaminopimelic acid in the cell wall The major end products of glucose fermentation were and the peptidoglycan type were determined as de- propionic acid, acetic acid and formic acid. Lactic acid scribed by Schleifer and Kandler [33], using TLC on and succinic acid were produced at trace levels as minor ARTICLE IN PRESS H.-S. Bae et al. / Systematic and Applied Microbiology 29 (2006) 404–413 407

Phylogenetic characteristics

An almost complete 16S rRNA gene sequence comprising 1469 nucleotide positions was determined for stain BL-10T. Phylogenetic comparisons with members of the domain showed strain BL-10T to represent a lineage within the Actinobacteria phylum (Fig. 2). Strain BL-10T formed an independent phylo- genetic branch close to the species of the genera Propionicimonas and Micropruina. The closest bacterial strain to strain BL-10T was Propionicimonas sp. F6 with a sequence similarity of 97.3%, which was isolated from a low-temperature biodegraded Canadian oil reservoir (AY570689). The 16S rRNA gene sequence similarity with the type strains Propionicimonas paludicola DSM 15597T [4] and Micropruia glycogenica JCM 10248T [34] were 97.5% and 95.4%, respectively. A neighbor-joining tree was constructed using the most closely related 16S rRNA gene sequences available from the public databases (Fig. 2)

Chemotaxonomic characteristics

T Strain BL-10 has anteiso C15:0 (54.3%), C15:0 (16.3%), iso C16:0 (12.8%), anteiso C17:0 (5.4%), iso C14:0 (5.3%), C17:0 (2.9%), and C16:0 (1.1%). Minor fractions less than 1.0% were C13:0,C14:0,C16:1 o9c, C18:1 o9c, and iso C15:0. The predominant respiratory quinone was MK-9. The peptidoglycan type was T Fig. 1. Morphological features of strain BL-10 observed by A1g with meso-diaminopimelic (meso-DAP) in the cell (a) differential interference contrast microscopy (DIC) and (b) wall. transmission electron microscopy (TEM). Cells were grown on PYG at 30 1C for 3 days. Bars in DIC and TEM represent 2 and 1 mm, respectively. Tolerance to chlorosolvents

Although strain BL-10T was not able to utilize 1,2- DCA or 1,1,2-TCA as electron acceptors, it was able to products. This strain did not utilize 1,1,2-TCA, 1,2- grow in the presence of both compounds (Fig. 3). Strain DCA, tetrachloroethene, trichloroethene, cis-1,2-di- BL-10 T grew at all 1,2-DCA concentrations tested in chloroethene, or 1,2-dichloropropane as electron accep- this study (range 0–9.8 mM); however, it grew only in tors after 80 days incubation. Benzene, toluene, the range of 0–5.9 mM of 1,1,2-TCA. Both chlorosol- ethylbenzene, and p-xylene were not utilized as sub- vents adversely affected growth of strain BL-10T in strates under anaerobic conditions after 52 days terms of the observed specific growth rate, maximum incubation. cell concentrations attained, and duration of the lag Using the Rapid ID 32A kits (bioMe´rieux) as phase, with adverse effects increasing as chlorosolvent described above, strain BL-10T showed a positive result concentrations increased. 1,1,2-TCA more adversely for a-glucosidase, b-glucosidase, glycine arylamidase, affected growth than did 1,2-DCA. histidine arylamidase, proline arylamidase, leucyl gly- To determine whether these chlorosolvents affect the cine arylamidase, phenylalanine arylamidase, leucine fermentation pathways, samples amended with 7.84 mM arylamidase, and alanine arylamidase. Negative results 1,2-DCA (aqueous concentration), 3.93 mM 1,1,2-TCA, were observed for glutamyl glutamic acid arylamidase and no chlorosolvent were collected after 18 days alkaline phosphatase, a-fucosidase, glutaminc acid incubation and analyzed for fermentation products. decarboxylase, arginin dehydrogenase, urease, a-galac- Propionate, acetate, and formate were the dominant tosidase, and b-galactosidase. Other physiological char- fermentation products both in the presence and absence acteristics are summarized in Table 1. of chlorosolvents. Fermentation product concentrations ARTICLE IN PRESS 408 H.-S. Bae et al. / Systematic and Applied Microbiology 29 (2006) 404–413

Table 1. Characterisitics of strains BL-10 T and related taxa: 1, strain BL-10T;2,Propionicimonas paludicola WdT ( ¼ DSM 15597T, data from Akasaka et al. [4] except for cellular fatty acids [this study]); 3, Propionicimonas paludicola Wf ( ¼ DSM 15598, data from Akasaka et al. [4] except for cellular fatty acids [this study]); 4, Lg2T ( ¼ JCM 10248T, data from Shintani et al. [34])

Characteristic 1 2 3 4

Origin Groundwater Plant residue in Plant residue in Activated sludge paddy soil paddy soil reactor Cell shape (mm) Rods (0.5 1.7) Irregular rods Irregular rods Coccoid (0.5–2.2) (0.4–0.5 1.8–2.0) (0.4–0.5 1.4–2.2) Growth temperature (1C) Optimum 30 35 35 30 Range 15–37 10–40 10–40 20–30 Growth pH Optimum 6.5 6.5 6.5 7.0 Range 4.5–8.5 4.5–7.5 4.5–7.5 6.0–8.0 NaCl range for 0–4 0–2 0–2 0–3 growth (%)

O2 requirement Facultative Facultative Facultative Aerobic anaerobic anaerobic anaerobic Cobalamin + ND requirement Catalase/oxidase /// +/+ Nitrate reduction + DNA G+C mol% 69.9 68.7 67.4 70.5

Major quinone MK-9 MK-9(H4), MK- MK-9(H4), MK- MK-9(H4) 10(H4) 10(H4) Peptidoglycan meso-DAP meso-DAP meso-DAP meso-DAP Cellular fatty acid (%)a C13:0 0.2 2.3 0.7 C14:0 0.5 0.7 1.1 3.7 C15:0 16.3 33.6 41.7 5.9 C16:0 1.1 1.5 1.2 12.9 C17:0 2.9 4.5 1.7 C18:0 4.6 C16:1 o9c 0.3 0.5 0.5 C18:1 o9c 0.3 0.3 0.4 iso C14:0 5.3 10.4 12.6 14.1 iso C15:0 0.2 0.7 0.5 2.2 iso C16:0 12.8 5.5 3.0 10.8 anteiso C15:0 54.3 41.7 36.9 37.1 anteiso C17:0 5.4 0.4 0.1 Utilization ofb: Adonitol + ND Arabinose +++ Cellobiose +++ meso-Erythritol + ND Galactose +++ Sorbitol + ND Products from glucose fermentation (mM) with/without B12 Acetic acid 11.20/11.5 8.06/2.46 13.8/8.12 ND Formic acid 2.59/2.50 ND Lactic acid 0.83/1.13 3.21/4.26 6.01/15.2 ND ARTICLE IN PRESS H.-S. Bae et al. / Systematic and Applied Microbiology 29 (2006) 404–413 409

Table 1. (continued )

Characteristic 1 2 3 4

Propionic acid 29.1/29.9 17.7/0.59 24.7/12.3 ND Succinic acid 0.59/0.57 0.89/2.45 0.27/0.53 ND

aCellular fatty acid composition of strains WdT and Wf was analyzed in this study from cells cultured under the same conditions used for strain BL-10T. bSubstrate utilization results reported for strains BL-10T,WdT, and Wf are for anaerobic conditions with incubation in liquid PY medium supplement with each of the various substrates. Substrate utilization results reported for Lg2T are for aerobic conditions using the BIOLOG system. T T Under anaerobic conditions, strains BL-10 ,Wd, and Wf all utilized fructose, D-glucose, glycerol, lactate, maltose, D-mannitol, D-mannose, pyruvate, D- sucrose, and xylose, but not cellulose, dulcitol, ethanol, L-fucose, fumarate, glycogen, D-lactose, D,L-malate, meliobiose, methanol, D-raffinose, L-rhamnose, soluble starch, succinate, or xylan.

Propionicimonas paludicola strain WdT (AB078858) rice plant residue strain W1 (AB078835) rice plant residue strain K5 (AB078820) rice stubble in paddy soil strain RR32 (AB174813) roots of rice plants strain S2321 (AY928208) river recharged aquifer strain R22 (AB174807) roots of rice plant strain Wf (AB078859) rice plant residue strain F6 (AY570689) biodegraded oil reservoir strain BL-10T (DQ176646) strain K2 (AB078817) rice stubble in paddy soil clone SJA-181 (AJ009505) anaerobic TCB transforming consortium strain VeSm15 (AJ229243) bulk soil of a flooded rice microcosm clone VC20 (AY211075) anaerobic VC degrading enrichment clone AKYG1602 (AY921964) farm soil Micropruina glycogenica strain Lg2T (AB012607) activated sludge

0.01

Fig. 2. 16S rRNA gene sequence based phylogeny showing the relationships of strain BL-10T and related taxa. The dendrogram was constructed from distance matrices using the neighbor-joining method. Bar represents 1 substitution per 100 nucleotide positions.

0.5 ab 0.4

0.3

OD660 0.2

0.1

0.0 024681012141618024681012141618 Time (d) Fig. 3. Growth of strain BL-10T in the presence of (a) 1,2-dichloroethane (1,2-DCA) and (b) 1,1,2-trichloroethane (1,1,2-TCA) at aqueous-phase chlorosolvent concentrations of K, 0 mM; J, 1.96 mM; ’, 3.92 mM; &, 5.89 mM; m, 7.84 mM, n, 9.80 mM. in microcosms amended with high concentrations of 1,2- Discussion DCA or 1,1,2-TCA were proportionally lower when compared to control microcosms without chlorosol- Biodegradation of chlorosolvents by indigenous vents, consistent with the fact that less cell growth was microbial populations (i.e., natural attenuation) or by observed. externally supplied consortia (i.e., bioaugmentation) is ARTICLE IN PRESS 410 H.-S. Bae et al. / Systematic and Applied Microbiology 29 (2006) 404–413 increasingly applied as an in situ remediation approach the genera PropionicimonasandMicropruina (Fig. 2). for contaminated soil and groundwater [1,2,12,20, The most closely related taxa are strains that have been 22,24,25]. Although strain BL-10T was unable to directly isolated from a number of sources. Many of these biotransform chlorinated solvents under the conditions strains have not been fully characterized but assigned to reported here, the strain nevertheless has the potential to the species Propionicimonas paludicola based on their play an important role in chlorosolvent biodegradation. proximity to the type strain WdT. Currently, the genus To sustain the reductive dechlorination process (in Propionicimonas contains one species with a validly which chlorosolvents serve as terminal electron acceptor published name, Propionicimonas paludicola WdT under anaerobic conditions) a source of reducing ( ¼ DSM 15597T), another strain of this species, strain equivalents (i.e., an electron donor) must be provided. Wf ( ¼ DSM 15598, [4]), as well as unidentified bacterial The range of electron donors that may be used by strains Propionicimonas sp. F6, K5, K2, RR22, RR32, dechlorinating microorganisms is generally quite limited W1, and S2321. An uncultured environmental clone and can include fermentation products such as acetate, SJA-181 from an anaerobic microbial consortium in a lactate, or pyruvate [15,32,38,39] or may be limited to trichlorobenzene-transforming bioreactor [42] is also only H2 [3,18,26]. Chlororespiring populations, thus, included in this generic group. The strains and 16S depend on the activity of fermentative organisms to rRNA clones show sequence similarity values in the convert complex organic materials into suitable electron 97.1–97.5% range. Micropruina, containing the single donors (e.g., acetate or H2) in the absence of a readily species Micropruina glycogenica [34], is the most closely available external supply [7,8,19]. The ability of strain related validly described taxon to Propionicimonas BL-10T to produce acetate, a compound directly used as paludicola, but with a 16S rRNA gene sequence an electron donor by many dechlorinating bacteria similarity of 95.4% is not closely related to strain species, and propionate, a compound that can be further BL-10T. T fermented to H2 that is also used as an electron donor by Strain BL-10 shares some common features with the dechlorinating bacteria species, may play an important genus Propionicimonas: facultative anaerobic trait, role in bioremediation at the PPI site. Further research, producing propionate as a major fermentation product, however, is needed to draw such an unequivocal and catalase, oxidase and nitrate reduction negative, as conclusion. Because propionate results in slow produc- well as having meso-DAP as the cell wall petidoglycan tion of hydrogen, it may be particularly advantageous layer (Table 1). However, strain BL-10T is clearly because it allows a larger fraction of reducing equiva- distinguished from genus Propionicimonas on the basis lents to be directed toward dechlorination [5,13,14, of other characteristics. Morphologically, strain BL-10T 19,23,35]. is characterized by regular rod-shaped cells (Fig. 1) The fact that strain BL-10T was able to grow while Propionicimonas paludicola WdT, type species of fermentatively even in the presence of very high this genus, forms irregular rods with irregular V- or concentrations of 1,2-DCA (9.8 mM) or 1,1,2-TCA crescent-shapes [4]. Strain BL-10T has MK-9 as the (5.9 mM) likely explains why the organism was able to predominant menaquinone which distinguishes it from survive in the DNAPL source zone of the PPI Super- the genus Propionicimonas with MK-9(H4) and MK- fund Site. Until recently, microbial degradation of 10(H4). Cellular fatty acids analysis also differentiates chlorosolvents in zones where DNAPLs are present strain BL-10T from Propionicimonas paludicola strains was generally assumed to be negligible due to the WdT and Wf. The three strains have the same fatty toxicity of high concentrations of chlorinated com- acids, but differ significantly in the proportions of the pounds [44,45]. Recent laboratory-scale experiments individual components. For example, the amounts of using tetrachloroethene (PCE) as a model compound C15:0 (33.6–41.7%) and iso C14:0 (10.4–12.6%) of strains have demonstrated that some microbial populations can WdT and Wf are two times higher than those of strain reductively dechlorinate in the presence of chlorosolvent BL-10T (16.3% and 5.3%) while the proportions of iso T DNAPL [6,10,11,29,44,45]. This suggests that in situ C16:0 (12.8%) and anteiso C17:0 (5.4%) of strain BL-10 bioremediation may be a feasible clean-up strategy for are higher by comparison to those of strains WdT and DNAPL source zones when applied directly [1,2] or as a Wf (3.0–5.5% and 0.1–0.4%, respectively). Besides the polishing step following more aggressive source zone chemotaxonomic features, strain BL-10T can be differ- removal techniques (e.g., co-solvent or surfactant entiated from Propionicimonas paludicola based on flushing) [7]. Presence of microorganisms like strain substrate utilization patterns (Table 1) as well as end BL-10T able to grow fermentatively in the presence of products of fermentation. Formic acid, an end product very high concentrations of chlorosolvents may syntro- of glucose fermentation for strain BL-10T, was not phically interact with dechlorinators through intra- detected in the fermentation products of strains WdT or species transfer of electron donors. Wf [4]. Strain BL-10T can differentiated from Micro- Phylogenetic analysis results indicate that strain BL- pruina glycogenica on the basis of aerobic metabolism, 10T represents a distinct lineage within the radiation of coccoid morphology, catalase- and oxidase positive ARTICLE IN PRESS H.-S. Bae et al. / Systematic and Applied Microbiology 29 (2006) 404–413 411 reactions, and the nitrate reduction positive reaction of succinate, and fumarate. This bacterium was isolated the later taxon. Micropruina glycogenica is also differ- from the Brooklawn site, Baton Rouge, LA (USA). The entiated from strain BL-10T based on chemotaxonomic type strain is BL-10T and has been deposited in the features, menaquinone MK-9(H4) and fatty acid com- American Type Culture Collection, Manassas, Virginia, position. USA as strain ATCC BAA-1218 and in the BCCM/ On the basis of phylogenetic, chemotaxonomic, and LMG Bacteria Collection, Ghent, Belgium as strain phenotypic features obtained in this study, strain BL- LMG 23096. 10T is assigned to a novel genus, Propionicicella gen. nov., with Propionicicella superfundia sp. nov. as the type species. Acknowledgements

Description of Propionicicella gen. nov. (Rainey, da This research was funded by the Governors Biotech- Costa, and Moe) nology Initiative of the Louisiana Board of Regents Grant BOR]015 Enhancement of the LSU Hazardous Propionicicella (Pro.pi.o.ni.ci.cel’la, N.L. n. acidum Substance Research Center Environmental Biotechnol- propionicum, propionic acid; L. fem. n. cella, a store- ogy Initiative. The authors thank Ms. Cindy Henk of room, chamber and in biology a cell; N.L. fem. n. the LSU Socolofsky Microscopy Center for assistance Propionicicella, a propionic acid producing cells). with microscopy. The authors thank Drs. Jean Euzeby Propionicicella cells are Gram-positive and rod-shaped, and Hans Tru¨per for assistance with the etymology of mesophilic, facultively anaerobic, chemo-heterotrophic. the epithets of the new species. Propionate and acetate are produced when grown anaerobically on glucose. Cell wall peptidoglycan is meso-DAP. Major cellular fatty acids are C15:0, iso C16:0 References and anteiso C15:0. MK-9 is the dominant menaquinone. Sugars and organic acids are used as carbon and energy [1] D.T. Adamson, J.M. McDade, J.B. Hughes, Inoculation sources. The G+C content of the type species is of DNAPL source zone to initiate reductive dechlorina- 69.9 mol%. On the basis of 16S rRNA gene sequences, tion of PCE, Environ. Sci. Technol. 37 (2003) 2525–2533. BL-10T belongs to the class Actinobacteria. The genera [2] D.T. Adamson, D.Y. Lyon, J.B. Hughes, Flux and Propionicimonas and Micropruina are the most closely product distribution during biological treatment of related genera. The type species is Propionicicella tetrachloroethene dense non-aqueous-phase liquid, En- superfundia. viron. Sci. Technol. 38 (2004) 2021–2028. [3] L. Adrian, U. Szewzyk, J. Wecke, H. Gorisch, Bacterial dehalorespiration with chlorinated benzenes, Nature 408 Description of Propionicicella superfundia sp. nov. (2000) 580–583. (Rainey, da Costa, and Moe) [4] H. Akasaka, A. Ueki, S. Hanada, Y. Kamagata, K. Ueki, Propionicimonas paludicola gen. nov., sp. nov., a novel Propionicicella superfundia (su.per.fun’ di.a. L. prep. facultatively anaerobic, gram-positive, propionate-produ- super, above/on top, L. masc. n. fundus, land owned by cing bacterium isolated from plant residue in irrigated someone, referring to land designated as an Environ- rice-field soil, Int. J. Syst. Evol. Microbiol. 53 (2003) 1991–1998. mental Protection Agency Superfund Site). Propionici- [5] B.S. Ballapragada, H.D. Stensel, J.A. Puhakka, J.F. cella superfundia cells are non-motile, non-spore Ferguson, Effect of hydrogen on reductive dechlorination forming, and 0.5 mm in diameter 1.0–2.5 mm in length. of chlorinated ethenes, Environ. Sci. Technol. 31 (1997) Colonies are white, circular, convex, smooth and 1728–1734. 2–3 mm in diameter on PYG agar. Growth occurs [6] C.S. Carr, S. Garg, J.B. Hughes, Effect of dechlorinating between 15 and 37 1C; the optimum growth temperature bacteria on the longevity and composition of PCE- is about 30 1C. Growth occurs between pH 4.5 and 8.5; containing nonaqueous phase liquids under equilibrium the optimum pH for growth is 6.5. Grows in the dissolution conditions, Environ. Sci. Technol. 34 (2000) presence of up to 4.0% (w/v) NaCl. Catalase, oxidase, 1088–1094. and nitrate reduction is negative. Formic acid, acetic [7] J.A. Christ, C.A. Ramsburg, L.M. Abriola, K.D. Pennell, acid, propionic acid, and succinic acid are fermentation F.E. Lo¨ffler, Coupling aggressive mass removal with microbial reductive dechlorination for remediation of products from glucose. Cells grow on adonitol, erythri- DNAPL source zones: a review and assessment, Environ. tol, fructose, glucose, glycerin, lactate, maltose, manni- Health Perspect. 113 (2005) 465–477. tol, mannose, pyruvate, sorbitol, sucrose, and xylose but [8] M. Chu, P.K. Kitanidis, P.L. McCarty, Possible factors did not utilize acetate, arabinose crystalline cellulose, controlling the effectiveness of bioenhanced dissolution of dulcitol, ethanol, fucose, galactose, lactose, malate, non-aqueous phase tetrachloroethene, Adv. Water Re- meliobiose, methanol, raffinose, rhamnose, starch, sour. 27 (2004) 601–615. ARTICLE IN PRESS 412 H.-S. Bae et al. / Systematic and Applied Microbiology 29 (2006) 404–413

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