International Journal of Systematic Bacteriology (1 999),49, 545-556 Printed in Great Britain

Characterization of the anaerobic propionate- degrading syntrophs Smithella propionica gen. nov., sp. nov. and

Yitai Liu,' David L. Balkwill,2 Henry C. Aldri~h,~Gwendolyn R. Drake2 and David R. Boone'

Author for correspondence: David R. Boone. Tel: + 1 503 725 3865. Fax: + 1 503 725 3888. e-mail: booned@,pdx.edu

1 Department of A strain of anaerobic, syntrophic, propionate-oxidizing , strain LYPT Environmental Biology, (= OCM 661T; T = type strain), was isolated and proposed as representative of a Portland State University, PO Box 751, Portland, OR new genus and new , Smithella propionica gen. nov., sp. nov. The strain 97207-0751, USA was enriched from an anaerobic digestor and isolated. Initial isolation was as a * Department of Biological monoxeni c propi on at e-d eg ra d i ng co-cuIt u re conta i n i ng Methanospirillum Science, Florida State hungateii JF-lT as an H,- and formate-using partner. Later, an axenic culture University, Ta Ila hassee, FL, was obtained by using crotonate as the catabolic substrate. The previously USA described propionate-degrading syntrophs of the genus Syntrophobacter also 3 Department of grow in co-culture with methanogens such as Methanospirillum hungateii, Microbiology and Cell Science, University of forming acetate, CO, and methane from propionate. However, Smithella Florida, Gainesville, FL, propionica differs by producing less methane and more acetate; in addition, it USA forms small amounts of butyrate. Smithella propionica and Syntrophobacter wolinii grew within similar ranges of pH, temperature and salinity, but they differed significantly in substrate ranges and catabolic products. Unlike Syntrophobacter wolinii, Smithella propionica grew axenically on crotonate, although very slowly. Co-cultures of Smithella propionica grew on propionate, and grew slowly on crotonate or butyrate. Syntrophobacter wolinii and Syntrophobacterpfennigii grow on propionate plus sulfate, whereas Smithella propionica did not. Comparisons of 165 rDNA genes indicated that Smithella propionica is most closely related to Syntrophus, and is more distantly related to Syntrophobacter.

Keywords : Swithella propionica, propionate-oxidizing bacteria, anaerobic digestor

INTRODUCTION electron carriers for this transfer. Propionate oxidation with H, and formate production as the electron sink is Propionate is an important intermediate in methano- exergonic only when H, and formate concentrations genic fermentation: it is the precursor of a large are very low (Boone & Bryant, 1980; McInerney & fraction of methane from anaerobic digestors (Boone, Bryant, 198 1; Schink, 1997) (Table 1, equation A). 1982, 1984; Kaspar & Wuhrmann, 1978a), and its The propionate-degrading bacterium Syntrophobacter & accumulation inhibits anaerobic digestion (Kaspar wolinii was first isolated in co-cultures in which one or Wuhrmann, 1978b). Propionate is oxidized to acetate & both of these catabolic products were continuously and CO, (Boone, 1984; Stadtman Barker, 1951), removed by methanogens or sulfate-reducing bacteria with the electrons generated from this oxidation (Boone & Bryant, 1980). More recently, Syntropho- ultimately transferred to methanogens that form meth- bacter wolinii was shown to be phylogenetically related ane by CO, reduction. H, (Boone & Bryant, 1980; to sulfate-reducing bacteria (Harmsen et al., 1993). Wolin, 1982) and formate (Boone et al., 1989; Stams & Syntrophobacter et al., This led to the demonstration that Dong, 1995; Thiele 1988) are the interspecies wolinii can grow slowly on propionate with sulfate as electron acceptor, and allowed the first isolation of this The GenBank accession number for the 165 rRNA sequence of strain LYPT bacterium in axenic culture (Wallrabenstein et al., is AFI 26282. 1994). Stams et al. (1993) showed that propionate

00911 0 1999 IUMS 545 Y. Liu and others

Table 1. Possible catabolic reactions during the anaerobic degradation of propionate

Reaction Equation AQ H, at equilibrium* (kJ/reaction)t Pa nM

I. Hydrogen-producing reactions A CH,CH,COO- + 2H,O -, CH,COO- + CO, + 3H, 71.7 12.1 89.2 B CH,CH,CH,COO- + 2H,O + 2CH,COO- + H++ 2H, 48.3 275 2024 11. Hydrogen-consuming reactions C CO, + 4H, + CH, + 2H,O - 130.7 0.3 17 2.33 D CH,CH,COO- + CO, + 3H, -+ CH,CH,CH,COO- + 2H,O -71.5 12-3 90.6 E(D + B) CH,CH,COO- + CO, + H, -, 2CH,COO- + H+ - 23.3 0.025 0.18 111. Combined hydrogen-producing and hydrogen-consuming reactions F(B + 1/2C) CH,CH,CH,COO- + 1/2CO, + H,O + - 17.1 2CH,COO- + H++ 1/2CH, G(4A + 3C) 4CH,CH,COO- + 2H,O --+ 4CH,COO- + CO, + 3CH, - 105.6 H(A + D) 2CH,CH,COO- -, CH,COO- + CH,CH,CH,COO- 0.12 I(3F +A) 4CH,CH,COO- + 2C0, + 2H,O + 7CH,COO- + 3H+ 1.91

* H, activity for AG = 0 with the following activities: CH,, 0.5 atm; CO,, 0-5 atm; acetate, propionate and butyrate at 1 mM; pH = 7. j. H,, CO,, and CH, in the gaseous state; H' at lo-' mol activity per kg; all other substances in aqueous solution at 1 mol of activity per kg; 25 "C (Thauer et al., 1977). enrichment cultures could also grow in the absence of generated internally, such as by propionate oxidation syntrophic interactions by fermenting fumarate to (Table 1, equation H) or, in part, by butyrate oxidation succinate and CO,, and demonstrated the enzymes of (Table 1, equation D). a fermentative pathway that includes acetyl-CoA oxidation to CO, (Plugge et al., 1993). They were In this paper, we report the isolation of strain LYPT, a unable to grow Syntrophobacter wolinii axenically on bacterium that syntrophically degrades propionate fumarate because fumarate was metabolized by the with butyrate as a small but significant product, and sulfate-reducing bacterium present in that syntrophic that also slowly degrades butyrate. We propose it as Smithellapropionica culture (Stams et al., 1993). In this paper, we report the the type strain of gen. nov., sp. isolation of the type strain of Syntrophobacter wolinii nov. This strain's 16s rDNA sequence, whose de- from its co-culture with Desulfovibrio strain GI1 in termination is reported herein, has been used to monoxenic co-culture with Methanospirillurn hungateii develop primers that detect phylogenetically similar and in axenic culture with fumarate as a catabolic organisms in anaerobic digestors (Sauer et al., 1997). substrate. Portions of this material were reported previously (Liu et al., 1998). Propionate degradation by Syntrophobacter wolinii (Houwen et al., 199 l), anaerobic sediments (Schink, 1985), anaerobic digestors (Robbins, 1987, 1988 ; METHODS Tholozan et al., 1988) and other methanogenic en- Source of inoculum and cultures. The source from which vironments (Boone, 1984; Houwen et al., 1987, 1990; strain LYPT was enriched was an up-flow anaerobic filter Koch et al., 1983) occurs mainly by the methyl-malonyl inoculated with digested domestic sewage sludge and op- pathway, with succinate as a symmetrical intermediate. erated with propionate as the major feedstock for 6 months. This pathway leads to the production of 1 mol acetate, Cultures were obtained from the Oregon Collection of 1 mol CO, and three pairs of electrons (i.e. a total of Methanogens (OCM) : Syntrophobacter wolinii DBT in co- culture with Desulfovibrio G11 (= OCM 467), Syntro- 3 mol H, and formate) per mol propionate degraded phomonas wolfeii LYB (= OCM 65), which is a butyrate- (Table 1, equation A). However, some propionate in oxidizing syntroph (Boone et al., 1989). Methanosarcina anaerobic digestors is reductively carboxylated to barkeri NIH-1 (= OCM 266) was purified from Methano- butyrate (Samain et al., 1984; Tholozan et al., 1988), sarcina barkeri NIH (= OCM 265) (Blaylock & Stadtman, and this reduction can occur in the absence of 1966) by roll-tube isolation in MS medium with 50 mM methanogenesis (Samain et al., 1984). This six-electron methanol. Methanospirillurn hungateii JF- lT( = OCM 16T) reduction (e.g. Table 1, equation D) probably does not is a H,- and formate-utilizing methanogen. use H, as electron donor if it is a catabolic reaction, Media and culture technique. We used the anaerobic because the reaction is not exergonic at the low H, techniques of Hungate (1969) with some modifications concentrations found in anaerobic digestors. However, (Miller & Wolin, 1974; Sowers & Noll, 1995). Except where the electrons to accomplish this reduction could be noted, we used MS medium (Boone et al., 1989), an

546 international Journal of Systematic Bacteriology 49 Smithella propionica gen. nov., sp. nov. anaerobic bicarbonate-buffered medium with 2 g 1-1 each of cycle sequencing method according to the manufacturer’s Trypticase peptone and yeast extract; MES (0.5 g 1-l) and procedures (McBride et al., 1989). The following primers Na,S. 9H,O (0.25 g 1-I) were the reducing agents. MS en- were used for sequencing : C (5’ ACGGGCGGTGTGTAC) richment medium was the same as MS medium except that (Lane et al., 1985), corresponding to positions 1406-1392 in yeast extract and Trypticase peptone were reduced to 0.5 g the 16s rDNA nucleotide sequence of Escherichia coii of each per litre. We also used MS low-nutrient medium in (Brosius et al., 1978) ; C-complement (5’ GTACACACCG- which the amount of yeast extract was reduced to CCCGT; E. coli positions 1392-1406); H (5’ ACACGA- 0.01 g 1-land Trypticase peptone was omitted. Agar media GCTGACGACAGCCA; positions 1075-1056); G (5’ CC- contained 18 g purified agar 1-l. For isolations, we placed AGGGTATCTAATCCTGTT ; positions 800-78 1) ; G- cultures into anaerobic jars with an anoxic gas to eliminate complement (5’ AACAGGATTAGATACCCTGG ; posi- oxygen diffusion through the stoppers, thus allowing longer tions 78 1-800) ; A (5’ GTATTACCGCGG[C/G]TGCTG ; anoxic incubations. positions 536519) ; P (5’ CTGCTTCCTCCCGTAGGAG; positions 357-339) ; P-complement (5’ CTACGGGAGGC- Analytical techniques. Methane was quantified by GC with & AGCAG; positions 342-357); and F,C (5’ AGAGTT- flame-ionization detection (Maestrojuan Boone, 1991) TGATC[A/C]TGGCTC ; positions 8-25). The assembled and fatty acids by GC of free acids. Samples were acidified M 16s rDNA sequences were hand-aligned with the equivalent by adding 0-1ml 3 phosphoric acid to 0.9 ml of sample. 16s rDNA or rRNA sequences of all closely related strains Injection volume was 1 pl. Acids were separated in a column found in the GenBank database. The initial sets of prealigned (2 m long, with 2 mm i.d.) containing 10% (w/w) SP-1000 eubacterial sequences were obtained from the Ribosomal coated on Chromosorb 101. The column temperature was Database Project (Larsen et al., 1993). Each set of aligned 105 “C and carrier-gas (N,) flow rate was 40 ml min-’. sequences was analysed for maximum-parsimony with the Detection was by flame ionization. Concentrations were program PAUP (Phylogenetic Analysis Using Parsimony) estimated by comparison of integrated peaks to those of (Swofford, 1993) to construct the most parsimonious phylo- standards. genetic tree based on E. coii positions 14476. Only the Analysis of growth and purity. Growth of methanogenic co- phylogenetically informative sites were considered, and cultures was checked by methane measurement (Maestro- alignment gaps were retained in the analysis. A heuristic juan & Boone, 1991), and growth of non-methanogenic search was carried out first (with standard program de- cultures was monitored by optical density at 670 nm (Spec- faults), after which a bootstrap analysis placed confidence tronic 21 ; Milton Roy). Purity was checked routinely by limits on the branch points of the resulting phylogenetic inoculating fluid thioglycollate medium (Difco) and MS trees. Consensus phylogenetic trees for each alignment set medium. Immediately following the initial isolation of axenic were produced by bootstrapping at the ~50%confidence cultures, media with H, plus sulfate or H, plus CO, were also limit, with 100 replications (Felsenstein, 1993). The phylo- inoculated to check for the presence of sulfate-reducers or genetic position of strain LYPT,inferred from its 16s rDNA methanogens, as indicated. After 3-8 weeks incubation, sequence, was compared to the positions of the most closely these contamination-check cultures were visually checked related organisms, with successive comparisons based on the for turbidity and microscopically checked for the presence of analytical results of the previous alignment. bacteria (Boone & Bryant, 1980). The aligned sequences were then analysed with parsimony Electron microscopy. Cells were centrifuged from the growth and distance matrix methods, The parsimony analysis was medium and resuspended in 2.5 % glutaraldehyde in 0.2 M performed with the program PAUP as described above. The sodium cacodylate buffer (pH 7.2) at room temperature and distance matrix analysis was carried out by using the PHYLIP fixed for 30 min. After two buffer washes, cells were fixed in package of the microcomputer programs (Felsenstein, 1993). 1 % osmium tetroxide in the same buffer for 1 h at 4 OC, Distances were calculated by the method of Jukes & Cantor washed in distilled water, dehydrated in an ethanol series, (1 969), after which phylogenetic distances were estimated and embedded in low-viscosity epoxy resin for sectioning. with the FITCH option, which makes use of the Fitch- Sections on Formvar-coated grids were poststained with Margoliash criterion (Fitch & Margoliash, 1967) and some uranyl acetate and lead citrate, and viewed and photo- related least-squares criteria. graphed with a Zeiss EM-1OCA transmission electron microscope. RESULTS Cytochemical stain for poly-hydroxyalkanoate. Cells were Isolation of strain LYPT in monoxenic co-culture stained for detection of poly-P-hydroxyalkanoate (Doetsch, 198 1). A heat-fixed film of cells was stained with 0.3 % Sudan MS enrichment medium with 20 mM propionate was black B in ethylene glycol for 15 min, rinsed in toluene, inoculated (5 %) with an anaerobic filter and incubated counter-stained briefly with 0.5 % aqueous safranin, and at 37 “C. A stable enrichment culture was developed dried. Stained cells were examined without a coverslip with % MS an oil-immersion objective lens on a Nikon Optiphot I1 from this culture by transferring 10 to fresh low- microscope using differential interference contrast optics. nutrient medium with 20 mM propionate. The culture was maintained by routine transfer after methane Phylogenetic analysis. DNA from strain LYPT was isolated production ceased. After six such transfers, a culture in by the chloroform/isoamyl alcohol procedure (Johnson, mid-exponential growth phase was serially diluted and 1981). Approximately 20 ng DNA was used as a template inoculated into MS enrichment medium with 20 mM for PCR amplification (Sambrook et al., 1989). The PCR amplification primers (Weisburg et al., 1991) were fDl (5’ propionate. Each culture was co-inoculated with AGAGTTTGATCCTGGCTCAG) and rP2 (5’ ACGGCT- Methanospirillum hungateii. These dilutions were also ACCTTGTTACGACTT). The PCR amplification products inoculated into solidified medium in roll tubes with were sequenced with an Applied Biosystems model 373A lawns of Methanospirillum hungateii, and the liquid DNA sequencer by using the Taq DyeDeoxy terminator cultures and roll-tube cultures were incubated at 37 “C. lnterna tionaI Journal ofSystematic 5acteriology 49 547 Y. Liu and others

Colonies in roll-tube media did not appear to contain tions of this culture into MS medium with propionate propionate-degrading bacteria. However, after 8 as substrate, also adding 0.1 ml of a culture of weeks incubation, the liquid culture inoculated with Methanospirillurn hungateii to each tube. After 2 0.1 nl of original culture had grown. It contained months incubation, cultures that had been inoculated epifluorescent curved rods appearing to be Meth- with 1 nl of original culture had grown. Cells of anospirillurn hungateii and shorter, thicker, non-fluor- Desulfovibrio strain GI 1 appeared to be absent : they escent rods. The methane formed by the culture was could not be found by microscopic examination of the much less than that formed by co-cultures of Syntro- culture, nor could they be found after incubation of the phobacter wolinii. We used dilutions of this culture to culture in MS medium with sulfate and H,. The culture inoculate MS roll-tube media that contained 20 mM appeared to contain only two morphological types, propionate and a lawn of both II.;”,.thanospirillurn those of Methanospirillurn hungateii and of Syntro- hungateii and Methanosarcina barkeri. After 6 months phobacter wolinii. This co-culture was inoculated into incubation, a colony was picked and inoculated into roll-tube medium with propionate and lawns of both MS medium with 20mM propionate. This culture Methanospirillurn hungateii and Methanosarcina bar- contained short, non-epifluorescent rods that were keri. After 6 months incubation, light yellow colonies slightly narrower than those of Syntrophobacter wol- formed that comprised three morphological types, inii, as well as epifluorescent cells appearing to be attributed to Methanospirillurn hunga teii, Methano- Methanosp ir illum h unga t eii and Methan osarcina bar- sarcina barkeri and Syntrophobacter wolinii. No keri. No growth was detected when this co-culture was growth occurred when the culture was inoculated into inoculated into MS medium without propionate or fluid thioglycollate medium. into fluid thioglycollate medium, indicating the ab- sence of contaminants able to grow in these media. The Axenic isolation of Syntrophobacter wolinii on co-culture was deposited in the Oregon Collection of fumarate Methanogens as OCM 441. A methanogenic co-culture of Syntrophobacter wolinii DBT and Methanospirillurn hungateii was obtained by Axenic isolation of strain LYPTwith crotonate serial dilution of the triculture that also contained The co-culture grew very slowly in liquid MS medium Methanosarcina barkeri. This co-culture was grown for with 20 mM butyrate (5 months to complete growth) several transfers in MS medium with 20 mM fumarate. or 20 mM crotonate (6 months to complete growth). Microscopic examination revealed reduced numbers Subsequent transfers (10 YO of culture volume) grew of Methanospirillurn hungateii, so the culture was faster (4-8 weeks). A crotonate-grown culture after serially diluted into MS medium with 20 mM fuma- several transfers contained fewer methanogens. It was rate. After 8 weeks incubation, the highest dilution serially diluted and inoculated into MS medium with that grew had produced no methane. This culture 20 mM crotonate. The highest dilutions that grew contained a single morphological type appearing to be were those that had been inoculated with 0.1 nl of the Syntrophobacter wolinii. Microscopic examination and original culture. These were examined microscopically contamination checks in thioglycollate medium, MS and found to contain only non-epifluorescent cells medium without additional substrates and MS me- appearing to be the propionate-degrading bacterium. dium with H, indicated that this was an axenic culture This culture was checked for contamination by in- of Syntrophobacter wolinii DBT. This culture was oculation of thioglycollate medium, MS medium and deposited in OCM as OCM 587T. It grew on malate, MS medium with H, added (to detect methanogens). fumarate or pyruvate, but not on propionate. How- The culture was axenic. It was named strain LYPT and ever, when co-inoculated with Methanospirillurn hung- deposited in OCM as OCM 661T.This culture grew in ateii into MS medium with 20 mM propionate, the MS medium with crotonate, but it was unable to grow culture grew and formed methane in expected when yeast extract and peptones were omitted. Thus, amounts. the strain required one or more growth factors present in yeast extract or peptones. Morphology Strain LYPTcells were elongated, slightly sinuous rods Isolation of Desulfovibrio-free cultures of 0.5 pm in diameter and 45pm in length (Fig. la and Syn troph obacter wolinii c). Cells as long as 10 pm were observed. Cells usually The methods used to obtain methanogenic co-cultures contained one to several electron-light globules. Stain- of strain LYPT were successfully applied to Syntro- ing with Sudan black indicated that these bodies were phobacter wolinii. We grew cultures of the triculture of poly-P-hydroxyalkanoate (Fig. lc). The cells stained strain LYPT, Desulfovibrio strain GI 1 and Methano- Gram-negative, and the walls had a typical Gram- spirillum hungateii (Boone & Bryant, 1980) in MS negative ultrastructure (Fig. 1b). mineral medium plus 20 mM propionate. After six For comparison we examined Syntrophobacter wolinii transfers, Methanospirillurn hungateii and Syntro- and found important differences. Although the cells phobacter wolinii were dominant, with very few cells of are approximately the same dimensions, and were also Desulfovibrio strain GI 1 evident. We inoculated dilu- Gram-negative, the ends of Syntrophobacter wolinii

~___ ~______548 International Journal of Systematic Bacteriology 49 Smithella propionica gen. nov., sp. nov.

Fig, 1. Micrographs of propionate- degrading bacteria : (a) Transmission electron micrograph of longitudinal section of Smithella propionica (arrowheads indicate granules of poly-p- hydroxyalkanoate within the cytoplasm; bar, 1 pm). (b) High magnification trans- mission electron micrograph thin-section of Smithella propionica, iI I ustrati ng typica I Gram-negative wall structure (M, plasma membrane; P, peptidoglycan; W, wall; bar, 0.1 pm). (c) Light microscopy of Sudan black B cytochemical stain to demonstrate poly- D-hydroxyalkanoate granules in cells of Smithella propionica (arrowheads indicate dark granules that are positively stained; bar, 5 pm). (d) High-magnification transmission electron micrograph thin-section of Syntro- phobacter wolinii DB~,illustrating typical Gram-negative wall structure and invagin- ations of plasma membrane (one at arrow- head) forming disk-like plates in cytoplasm (bar, 0-1 pm). (e) Transmission electron micrograph of a longitudinal section of Syntrophobacter wolinii DBT; cells tapered to flat ends; arrowheads indicate several of the cytoplasmic disks as shown in part (d) (bar, 1 pm). cells tapered to a blunt point (Fig. le). The cytoplasm Methanospirillurn hungateii and Methanosarcina bar- of fumarate-grown cells contained numerous mem- keri. This triculture produced the stoichiometrically brane-delimited inclusions (Fig. Id and le), but these expected amount of methane from propionate (viz. inclusions were absent in cells grown on pyruvate. The 1-75mol methane per mol propionate). inclusions were invaginations of the plasma membrane (arrowhead, Fig. Id) and in unusually thick sections Propionate degradation by co-cultures of strain LYPT appeared as disks when viewed face on. Gas vesicles as reported for Syntrophobacterpfennigii(Wallrabenstein When a reconstituted co-culture of strain LYPT and et al., 1995b) were not found. Methanospirillurn hungateii was grown in 20 ml MS medium with 0.4 mmol propionate (20 mM), only Reconstitution of strain LYPT co-cultures from axenic 0.06mmol methane was formed by 60d incubation cu I tures (Fig. 2a). This was much less than the expected amount of methane (0.3 mmol) based on the degradation Like Syntrophomonas wolfeii, strain LYPT was able to stoichiometry of Syntrophobacter wolinii (Table 1, grow axenically in MS medium with 20 mM crotonate, equation G). In this time, the culture degraded 0.3 but not with 20 mM butyrate as catabolic substrate. mmol propionate, and produced 0-4 mmol acetate and However, when an axenic culture of strain LYPT was 0.04 mmol butyrate; about 0.1 mmol propionate re- co-inoculated with Methanogenium strain PM or mained (Fig. 2a). This stoichiometry differed from that Methanospirillurn hungateii, the co-cultures grew of Syntrophobacter wolinii (Boone & Bryant, 1980), slowly on butyrate, and produced methane in expected but was similar to that expected if 2 mol propionate quantities. Likewise, an axenic culture of strain LYPT were fermented to 1 mol each of butyrate and acetate did not grow in MS medium with 20 mM propionate, (Table 1, equation H), with most of the butyrate but it grew in this medium when co-inoculated with further degraded syntrophically (Table 1, equation F).

International Journal of Systematic Bacteriology 49 549 Y. Liu and others

-1 0 h C .- tl -20 m

\L -30 v3 0 0 -40 -r;n-- 0 20 40 60 0 20 40 60 80 Time (d)

Fig. 2. Effect of acetate degraders and butyrate degraders on the degradation of 20 mM propionate by the propionate- degrading strain LYPT and Methanospirillum hungateii. (a) Growth of strain LYPT plus Methanospirillurn hungateii. (b) Growth of strain LYPT, Methanospirillurn hungateii and Methanosarcina barkeri. (c) Thermodynamics of several propionate-degrading reactions at concentrations occurring during the batch growth shown in (a) (Reactions GI H and F refer to the reactions shown in Table 1). (d) Thermodynamics of several propionate-degrading reactions at concentrations occurring during the batch growth shown in (b) (Reactions GI H and F refer to the reactions shown in Table 1).

Inhibition by H, or formate the absence of sulfate (Boone & Bryant, 1980), and with our finding that strain LYPT did not grow To determine whether inefficient H, (or formate) axenically on propionate. However, it contrasts with removal limited propionate oxidation by strain LYPT, experiments on sewage sludge, in which propionate we increased the numbers of methanogens in the co- conversion to butyrate continued in the presence of culture. We did this by pre-growing Methanospirillurn bromoethanesulfonate (Samain et al., 1984). Growth hungateii in 20 ml medium with H, added; we flushed of strain LYPT on propionate depended on the out the gas space with N, and CO, (3 : 7) after growth removal of H, and formate by Methanospirillurn was complete. We then added 0.4 mmol propionate hunga teii. (20 mM) to this culture and inoculated it with the propionate-degrading co-culture. The increased num- Inhibition by acetate and other organic acids bers of methanogens had little effect on the fermen- tation (data not shown). The incomplete degradation of propionate by the co- culture (Fig. 2a) may have been due to inhibition by To confirm that strain LYPT required H, and formate accumulating acetate. When the aceticlastic meth- removal for propionate degradation, we added bromo- anogen Methanosarcina barkeri was co-inoculated ethanesulfonate to inhibit the uptake of H, and with the co-culture of strain LYPT and Methano- formate by the methanogen. When the co-culture was spirillum hungateii, more propionate was degraded incubated with 0.5 mM bromoethanesulfonate, meth- than when Methanosarcina barkeri was absent (Fig. ane was not produced, propionate concentration did 2b). Acetate accumulated and then disappeared ; ulti- not decrease, and no growth was detected. This finding mately, much more methane was formed than in the is consistent with the inability of the Syntrophobacter absence of Methanosarcina barkeri. Thus, the high wolinii to co-culture with Desulfovibrio strain GI1 in ( > 20 mM) concentrations of acetate that had accumu-

550 International Journal of Systematic Bacteriology 49 Smithella propionica gen. nov., sp. nov.

0.3 growth on crotonate. Axenic cultures did not grow on butyrate, propionate, lactate, succinate, malate, fu- marate, oxalate, isobutyrate, isovalerate, valerate,

n caproate, pyruvate or H, plus CO,. We tested the F I ability of strain LYPT to grow syntrophically on these substrates by co-inoculating strain LYPTtogether with Methanospirillurn hungateii into media with 10 mM of the test substrate. To determine whether the tested concentrations used were inhibitory, we also co-

U inoculated media containing 10 mM propionate plus 5 0.1 z 10 mM of various other substrates. These co-cultures wlQ grew and produced methane from crotonate, butyrate, propionate, malate and fumarate, but not from lactate, succinate, oxalate, valerate, caproate or pyruvate. Ability to grow on isobutyrate could not be determined 0 20 25 30 35 40 because 10 mM isobutyrate was inhibitory. Temperature (“C) Effect of temperature and pH on growth Fig, 3. Effect of temperature on growth rates of Smithella Strain LYPT and Syntrophobacter wolinii were both propionica LYPT (0)and Syntrophobacter wolinii DBT (0). mesophiles with similar growth rates (Fig. 3, Table 2). Both organisms grew fastest at pH values near neutral with a similar range (Fig. 4), but with slightly different lated in co-cultures of strain LYPT and Methano- minimum pH values: strain LYPT could not grow at spirillurn hungateii appeared to inhibit the extent of pH values of 6-3 or below, whereas Syntrophobacter propionate degradation. Elevated acetate concen- wolinii grew well at pH 6.1. tration also appeared to stimulate net butyrate for- mation, as more butyrate was formed when acetate Effect of salinity on growth was allowed to accumulate than when it was removed by Methanosarcina barkeri (Fig. 2). Strain LYPT and Syntrophobacter wolinii also differed in their sensitivity to NaCl. Each grew well in MS Added acetate inhibited methanogenesis from pro- medium with 20mM of substrate added (total Na+ pionate by strain LYPT and Methanospirillurn hunga- concentration 120 mM), but the growth rate of strain teii. When such a co-culture was inoculated into LYPT was reduced by 50% when 86 mM NaCl was medium with 20 mM propionate and 10 mM acetate, added, and growth was completely inhibited when the acetate inhibited the rate (by 35 %) and extent (by 171 mM NaCl was added (Fig. 5). Syntrophobacter 18 %) of methanogenesis from propionate compared wolinii was completely inhibited in the presence of to cultures without added acetate. When 20 mM 86mM NaCl or KCl. However, it tolerated added acetate was added, inhibition of the rate (by 66 YO)and sodium in MS medium with increased concentrations extent (by 49 YO)of methanogenesis was more severe, of sodium bicarbonate (Fig. 5), suggesting that it was and inhibition by 40 mM added acetate was nearly particularly sensitive to chloride ion. complete. To determine whether inhibition was a general feature Phylogeny of organic acids rather than product inhibition, we tested methanogenesis from propionate in the presence The 16s rDNA sequence of strain LYPT was de- of various concentrations of added organic acid salts. termined and compared with others in the Ribosomal Methanogenesis by the triculture of strain LYPT, Database Project (RDP) and GenBank (Table 2), and Methanospirillurn hungateii and Methanosarcina bur- Fig. 6 shows a phylogenetic tree derived from these keri was uninhibited by propionate concentrations as sequences. This figure shows that strain LYPT is most high as 60 mM, and good growth occurred even with closely related (99-4% sequence similarity) to strain 120 mM propionate. Butyrate was not inhibitory at Syn7, a non-axenic strain of propionate-degrading the highest concentrations tested (20 mM), but rather methanogenic culture whose sequence was determined it slightly stimulated methanogenesis. On the other in the laboratory of Alfons Stams. These two strains hand, 10 mM isobutyrate strongly inhibited methano- are most closely related to Syntrophus gentiunae genesis from propionate. (88.9 YOsequence similarity) and Syntrophus buswellii (87.8%), but these similarities were not sufficient to Other catabolic substrates indicate that strain LYPT should be classified within the genus Syntrophobacter. Strain LYPT was even less Strain LYPT grew axenically on 10 mM crotonate, related to Syntrophobacter, the genus of syntrophic producing approximately 1 mol acetate and 0-5 mol propionate-degrading bacteria (8 1* 1-83.0 % sequence butyrate per mol crotonate. Added H, inhibited similarity).

International Journal of Systematic Bacteriology 49 551 Y. Liu and others

Table 2. Sources of strains and 165 rRNA sequences

~ raxon Strain name Culture 16s Database Reference collection* rRNA sequence

Bdellovibrio bacteriovorus 109JT DSM 3243 M59297 RDP Unpublished Desulfobacter postgateii 11070$ DSM 684 M26633 RDP Pfennig & Biebl (1976) Desulfobacterium autotrophicum HRM2T DSM 3382T M34409 RDP Devereux et al. (1989) Desulfomonile tiedjeii DCB- 1 ATCC 49306T M26635 RDP Unpublished Desu lfor ha bdus amnigen us ASRBIT DSM 10338T X83274 GenBank Oude Elferink et al. (1995) Desulfovibrio baarsii KonstanzT DSM 2075T M34403 RDP Devereux et al. (1989) Desulfovibrio desulfuricans MB ATCC 27774 M34113 RDP Oyaizu & Woese (1985) Desulfuromonass M80618 RDP Amann et al. (1992) Desulfuromonas acetoxidans Dangast (2a~9)~DSM 2034T M26634 RDP Widdel & Pfennig (1 98 1) Escherichia coli K-12 M29364 RDP Shen et al. (1982) . Geobacter chapelleii’ U41561 GenBank Lonergan et al. (1996) ’ Geobacter hydrogenophilus’ H4 U46860 GenBank Lonergan et al. (1996) ‘ Geobacter hydrogenophilus ’ H2 U28 173 GenBank Lonergan et al. (1996) Geobacter metallireducens GS- 15T OCM 645T)l LO7834 GenBank Lovley et al. (1993) Geobacter sulfurreducens PCAT U13928 GenBank Caccavo et al. (1994) Pelobacter acetylenicus WoAcy 1 DSM 3246Tfl X709.55 RDP Evers et al. (1993) Pelobacter propionicus OttBdlT DSM 2379T X70954 RDP Evers et al. (1993) Syn trophobacter sp. MPOB X82874 GenBank Harmsen et al. (1995) Syntrophobacter pfennigii KoProp 1 DSM 10092T X82875 GenBank Harmsen et al. (1995) Smithella propionica LYPT OCM 661T xooooo GenBank This paper Syntrophobacter wolinii (Highly purified) X70906 GenBank Harmsen et al. (1993) Syntrophobacter wolinii DBT DSM 2805T X70905 RDP Harmsen et al. (1993) Syntrophomonas wolfeii GottingenT OCM 41: M26492 GenBank Zhao et al. (1989) Syntrophus buswellii (Unnamed)T DSM 2612T X85131 GenBank Wallrabenstein et al. (1995a) Syntrophus gent ianae HQGO 1 DSM 8423T X85 132 GenBank Wallrabenstein et al. (1995a) Syn7 X87269 GenBank H. J. M. Harmsen (unpublished) * Culture collection indicated as the source of the culture for sequencing; ATCC, American Type Culture Collection; DSM, DSMZ - Deutsche Sammlung von Mikroorganismen und Zellkulturen ; OCM, Oregon Collection of Methanogens. T The sequence obtained from RDP listed strain 109J as the source, but the GenBank entry for this sequence (M59297) lists the source as Bdellovibrio bacteriovorus, strain DSM 3243. However, DSM 3243, according to the DSMZ database, is Methanohalophilus portucalensis strain SF1. Our analysis of this sequence (Fig. 6) suggests that it is indeed that of Bdellovibrio bacteriovorus. j: The sequence obtained from RDP listed strain 2AC9 as the source, but the GenBank database indicates that sequence M26633 is Desulfobacter postgateii, strain DSM 684. DSMZ lists strain DSM 684 as the type strain of Desulfuromonas acetoxydans Pfennig and Biebl 1977AL. 6 The GenBank database indicates that sequence M80618 is the sequence of a Desulfuromonas-like organism, called ‘population type 2’. However, the submitters of that sequence, obtained from a methanogenic biofilm, indicate that ‘population type 2’ is related to Desulfovibrio vulgaris and ‘population type 1 ’ is related to Desulfuromonas acetoxidans (Amann et al., 1992). Our tree places this sequence closer to that of Desulfuromonas acetoxidans than to those of Desulfovibrio baarsii and Desulfovibrio desulfuricans, suggesting that sequence M80618 is actually ‘population type 1 ’ described by Amann et al. (1992). 11 No collection was indicated in the GenBank database, but the strain is available from this collection. 7 Evers et al. (1993) indicate this strain (WoAcy1) is DSM 2348, but the DSMZ database indicates that strain WoAcy1 is DSM 3246.

DISCUSSION pyruvate, it is possible that these inclusions also were sites of fumarate reductase activity. The membranous inclusions found in fumarate-grown Syntrophobacter wolinii are reminiscent of those ob- Syntrophobacter wolinii degrades propionate with a served in fumarate-grown E. coli (Lemire et al., 1983; stoichiometry of 1 mol acetate formed per mol pro- Weiner et al., 1984). These structure-function studies pionate degraded, whether this degradation is coupled indicated that the rod-shaped inclusions in E.coli had syntrophically to sulfate reduction or to methano- 4 nm diameter globular projections of fumarate re- genesis (Boone & Bryant, 1980). This stoichiometry ductase resting on a short stalk and attached to a (Table 1, equation A) is consistent with the ran- transmembrane tube-like basal piece. Since we found domizing pathway that has been identified in this membrane-delimited inclusions in Syntrophobacter bacterium (Houwen et al., 1990). Although the amount wolinii grown on fumarate but not in those grown on of H, or formate was not directly measured, its

552 In ternationa I Jo urn a I of Systematic Bacteriology 49 Smithella propionica gen. nov., sp. nov.

calculated value (calculated stoichiometrically from 0 the ultimate product, H,S or CH,) was near the expected amount. In contrast, strain LYPT in co- culture with Methanospirillurn hungateii formed much smaller amounts of methane and larger amounts of acetate during propionate degradation, with a stoi- chiometry closer to equations F + H (Table 1). These deviations from expected stoichiometry could be ex- plained by acetogenesis from CO, and H,, but strain LYPT was unable to grow on H, plus CO,. Another possibility involves the reductive carboxylation of propionate to butyrate or butyryl-CoA, which has been documented in anaerobic digestors (Tholozan et al., 1988). This latter possibility is supported by the ability of strain LYPT to grow slowly on crotonate, and to grow in syntrophic co-culture on butyrate. These abilities indicate that it can couple energy to the P-oxidation of butyrate, as has been shown for Syntrophomonas wolfeii (McInerney et al., 1979, 198 1 ; McInerney & Wofford, 1992). This finding, together with the stoichiometry of its syntrophic degradation of PH propionate, is consistent with the dismutation of propionate to acetate and butyryl-CoA, followed by Fig. 4. Effect of pH on growth rates of Smithella propionica syntrophic P-oxidation of butyryl-CoA to acetate. The LYPT (0)and Syntrophobacter wolinii DBT (0). presence of a kinase or HS-CoA transferase of low activity would explain the release of small quantities of butyrate from butyryl-CoA, and this would also allow the observed slow growth of strain LYPT on butyrate (syntrophically) or on crotonate. This pathway is also consistent with the thermodynamics of these reactions, which were always negative during the batch growth of co-cultures (Fig. 2c). The production of butyrate during syntrophic pro- pionate degradation distinguished Smithella pro- 0 pionica from Syntrophobacter wolinii. We confirmed the previous finding (Boone & Bryant, 1980) that Syntrophobacter wolinii also does not produce butyrate from propionate; the production of small amounts of butyrate might not have been detected in that study because the rumen-fluid medium used in the original study contained small amounts of butyrate.

Taxonomy Our findings indicate that strain LYPT differs mor- phologically, physiologically and phylogenetically from previously described propionate-degrading bac- teria. Strain LYPT is phylogenetically most similar to the genus Syntrophus, but the phylogenetic relation- ship is not sufficiently close to permit classification of strain LYPT in this genus. Also, the ability of strain LYPT to grow on propionate separates it phenotyp- ically from members of this genus. Therefore we 100 200 300 propose a new genus and species, Smithella propionica [Sodium] (mM) gen. nov., sp. nov. ....I ...... Fig, 5. Effect of added salts on growth rates of Smithella propionica LYPT and Syntrophobacter wolinii DBT. Description of Smithella gen. nov. Syntrophobacter wolinii with sodium chloride (0)or sodium bicarbonate (0)added to MS medium; Smithella propionica Smithella (Smi.thel'la. N.L. n. Smithella Smith, named LYPT (0). after Paul H. Smith, for his early contributions to the

International Journal of Systematic Bacteriology 49 553 Y. Liu and others

Syntrophobacter strain MPOB Desulforha bdirs amnigetius

I Syntrophobacter wolinii L Syntrophobacter wolinii (non-axenic strain) I IF

L 7 Geobacter metallireducens

“Geoba cter hydrogenop hilus ” H4 Fig. 6. Phylogenetic tree comparing - “Geobacter hydrogenophilus ” H2 - Smithella propionica LYPT with other Geob a cter szi rfurr edu c ens bacteria, based on a distance-matrix analysis m of an approximately 683 base segment of Pelvbacter acetylenicirs the 165 rDNA and rRNA sequences. These data compared by parsimony and maximum- likelihood methods gave trees similar to this Escherichia coli K- 12 one. A partial tree is shown, in which E. coli was used as the outgroup. Bar, 5 base 0.05 substitutions per 100 bases.

understanding of propionate degradation in methano- with pH near neutral and Na’ and Cl- concentrations genic ecosystems). less than 100mM. Grows syntrophically on propi- onate with H,- or formate-using methanogenic part- Weakly motile Gram-negative rods. Strictly anaerobic. ner. Grows slowly axenically by dismutating crotonate MesoPhilic* Growth ’YntroPhic Of to butyrate and acetate. Habitat : methanogenic di- propionate involving its reductive carboxylation to gestors. Type strain is strain LYPT (= OCM 661T). butyrate or butyryl-CoA. Habitat : methanogenic en- vironments in which propionate is degraded. Type species : Smithella propionica.

We thank Shuisong Ni (Washington State University, Smithella propionica (pro.pi.o’ni.ca. M.L. n. acidum Richland) for helpful discussions, Donna S. Williams for propionicum propionic acid ; M.L. adj. propionica help with the electron microscopy, and Sylvia E. Coleman pertaining to propionic acid, on which the bacterium for determining the presence of poly-P-hydroxyalkanoate grows). granules. This work was supported by grant DE-FGO5- 90ER61039 from the US Department of Energy through the Gram-negative rods, 0-5 pm in diameter, with most Subsurface Science Program (Deep Microbiology Sub- cells 3-5 pm long, but some cells as long as 10 pm. program) and by a subcontract from master contract 206010 Contain granules of poly-P-hydroxybutyrate. Weakly (to Pacific Northwest National Laboratory), task order motile. Strictly anaerobic, Mesophilic. Fastest growth 258705.

5 54 International Journal of Systematic Bacteriology 49 Smithella propionica gen. nov., sp. nov.

REFERENCES mination of carboxylation reactions with 13C-NMR spectro- scopy. Biochim Biophys Acta 1056, 126132. Amann, R. I., Stromley, J., Devereux, R., Key, R. & Stahl, D. A. (1992). Molecular and microscopic identification of sulfate- Hungate, R. E. (1969). A roll tube method for cultivation of strict reducing bacteria in multispecies biofilms. Appl Environ Micro- anaerobes. Methods Microbiol3B, 1 17-1 32 biol58, 614-623. Johnson, 1. L. (1981). Genetic characterization. In Manual of Blaylock, B. A. & Stadtman,T. C. (1966). Methane biosynthesis by Methods for General Bacteriology, pp. 450-472. Edited by P. Methanosarcina barkeri; properties of the soluble enzyme Gerhardt, R. G. E. Murray, R. N. Costilow, E. W. Nester, system. Arch Biochem Biophys 116, 138-158. W. A. Wood, N. R. Krieg & G. B. Phillips. Washington, DC: American Society for Microbiology. Boone, D. R. (1982). Terminal reactions in the anaerobic digestion of animal waste. Appl Environ Microbiol43, 57-64. Jukes, T. H. & Cantor, C. R. (1969). Evolution of protein mol- ecules. In Mammalian Protein Metabolism, vol. 3, pp. 21-132. Boone, D. R. (1984). Propionate exchange reactions in methano- Edited by H. N. Munro. New York: Academic Press. genic ecosystems. Appl Environ Microbiol48, 863-864. Kaspar, H. F. & Wuhrmann, K. (1978a). Kinetic parameters and Boone, D. R. & Bryant, M. P. (1980). Propionate-degrading relative turnovers of some important catabolic reactions in bacterium, Syntrophobacter wolinii sp. nov. gen. nov., from digesting sludge. Appl Environ Microbiol36, 1-7. methanogenic ecosystems. Appl Environ Microbiol40,626632. Kaspar, H. F. & Wuhrmann, K. (1978b). Product inhibition in Boone, D. R., Johnson, R. L. & Liu, Y. (1989). Diffusion of the sludge digestion. Microb Ecol4, 241-248. interspecies electron carriers H, and formate in methanogenic ecosystems and its implications in the measurement of K, for Koch, M., Dolfing, J., Wuhrmann, K. & Zehnder, A. (1983). H, or formate uptake. Appl Environ Microbiol55, 1735-1741. Pathways of propionate degradation by enriched methanogenic cocultures. Appl Environ Microbiol45, 141 1-1414. Brosius, J., Palmer, M. L., Kennedy, P. 1. & Noller, H. R. (1978). Complete nucleotide sequence of a 16s ribosomal RNA gene Lane, D. J., Pace, B., Olsen, G. J., Stahl, D. A., Sogin, M. L. & Pace, from Escherichia coli. Proc Nut1 Acad Sci USA 75, 48014805. N. R. (1985). Rapid determination of 16s ribosomal RNA sequences for phylogenetic analyses. Proc Natl Acad Sci USA Caccavo, F., Jr, Lonergan, D. J., Lovley, D. R., Davis, M., Stolz, 82, 6955-6959. J. F. & Mclnerney, M. 1. (1994). Geobacter sulfurreducens sp. nov., Larsen, N., Olsen, 1. G., Maidak, B. L., McCaughey, M. J., Over- a hydrogen- and acetate-oxidizing dissimilatory metal-reducing beek, R., Macke, T. J., Barsh, T. L. & Woese, C. R. (1993). The microorganism. Appl Environ Microbiol60, 3752-3759. ribosomal database project. Nucleic Acids Res 21, 302 1-3023. Devereux, R., Delaney, M., Widdel, F. & Stahl, D. A. (1989). Lemire, B. D., Robinson, 1. J., Bradley, R. D., Scraba, D. G. & Natural relationships among sulfate-reducing eubacteria. J Weiner, J. H. (1983). Structure of fumarate reductase on the Bacteriol 171, 6689-6695. cytoplasmic membrane of Escherichia coli. J Bacteriol 155, Doetsch, R. N. (1981). Determinative methods of light micro- 39 1-397. scopy. In Manual of Methods for General Bacteriology, pp. Liu, Y., Balkwill, D. L., Aldrich, H. C. & Boone, D. R. (1998). A 21-33. Edited by P. Gerhardt, R. G. E. Murray, R. N. novel anaerobic syntrophic bacterium that degrades propionate & Costilow, E. W. Nester, W. A. Wood, N. R. Krieg G. B. and produces butyrate. Atlanta, GA: Abstr Gen Meet Am SOC Phillips. Washington, DC : American Society for Microbiology. Microbiol, Abstract 1-52, p. 316. Evers, S., Weizenegger, M., Ludwig, W., Schink, B. & Schleifer, Lonergan, D. J., Jenter, H. L., Coates, J. D., Phillips, E. J., Schmidt, K. H. (1993). Pelobacter acetyl- The phylogenetic positions of T. M. & Lovley, D. R. (1996). Phylogenetic analysis of dis- enicus and Pelobacter propionicus. Syst Appl Microbiol 16, similatory Fe(II1)-reducing bacteria. J Bacteriol 178, 2402- 216218. 2408. Felsenstein, J. (1993). PHYLIP (Phylogeny Inference Package). Lovley, D. R., Giovannoni, 5. J., White, D. C., Champine, 1. E., Seattle, WA, USA. Phillips, E. 1. P., Gorby, Y. A. & Goodwin, 5. (1993). Geobacter Fitch, W. M. & Margoliash, E. (1967). Construction of phylo- metallireducens gen. nov, sp. nov., a microorganism capable of genetic trees. Science 155, 279-284. coupling the complete oxidation of organic compounds to the Harmsen, H. 1. M., Wullings, B., Akkermans, A. D. L., Ludwig, W. reduction of iron and other metals. Arch Microbiol 159, & Stams, A. 1. M. (1993). Phylogenetic analysis of Syntropho- 336-344. bacter wolinii reveals a relationship with sulfate-reducing McBride, L. J., Koepf, 5. M., Gibbs, R. A., Salser, W., Mayrand, bacteria. Arch Microbiol 160, 238-240. P. E., Hunkapiller, M. W. & Kronick, M. N. (1989). Automated Harmsen, H. J. M., Kengen, H. M. P., Akkermans,A. D. L. & Stams, DNA sequencing methods involving polymerase chain reaction. A. J. M. (1995). Phylogenetic analysis of two syntrophic propio- Clin Chem 35,21962201. nate-oxidizing bacteria in enrichments cultures. Syst Appl Mclnerney, M. 1. & Bryant, M. P. (1981). Review of methane Microbiol 18, 67-73. fermentation fundamentals. In Fuel gas production from bio- Houwen, F. P., Dijkema, C., Schoenmakers, C. H. H., Stams, mass, pp. 1946. Edited by D. L. Wise. Boca Raton, FL: CRC A. 1. M. & Zehnder, A. J. B. (1987). I3C-NMRstudy of propionate Press. degradation by a methanogenic coculture. FEMS Microbiol Mclnerney, M. J. & Wofford, N. Q. (1992). Enzymes involved in Lett 41, 269-274. crotonate metabolism in Syntrophomonas wolfei. Arch Micro- Houwen, F. P., Plokker, J., Stams, A. J. M. & Zehnder, A. J. B. bioll58, 344-349. (1990). Enzymatic evidence for involvement of the methyl- Mclnerney, M. J., Bryant, M. P. & Pfennig, N. (1979). Anaerobic malonyl-CoA pathway in propionate oxidation by Syntro- bacterium that degrades fatty acids in syntrophic association phobacter wolinii. Arch Microbiol 155, 52-55. with methanogens. Arch Microbiol 122, 129-1 35. Houwen, F. P., Dijkema, C., Stams, A. J. M. & Zehnder, A. 1. B. Mclnerney, M. J., Bryant, M. P., Hespell, R. B. & Costerton, J. W. (1991). Propionate metabolism in anaerobic bacteria : deter- (1981). Syntrophomonas wovei gen. nov. sp. nov., an anaerobic,

International Journal of Systematic Bacteriology 49 555 Y. Liu and others syntrophic, fatty acid-oxidizing bacterium. Appl Environ Micro- fermentation. VIII. Tracer experiments on fatty acid oxidation biol41, 1029-1039. by methane bacteria. J Bacteriol61, 67-80. Maestrojudn, G. M. & Boone, D. R. (1991). Characterization of Stams, A. 1. M. & Dong, X. (1995). Role of formate and hydrogen Methanosarcina barkeri MSTand 227, Methanosarcina mazei S- in the degradation of propionate and butyrate by defined 6*, and Methanosarcina vacuolata 2-76 lT.Int J Syst Bacteriol suspended cocultures of acetogenic and methanogenic bacteria. 41, 267-274. Antonie Leeuwenhoek J Microbiol68, 28 1-284. Miller, T. L. & Wolin, M. 1. (1974). A serum bottle modification of Stams,A. J. M., Van Dijk, 1. B., Dijkema, C. 81Plugge, C. M. (1993). the Hungate technique for cultivating obligate anaerobes. Appl Growth of syntrophic propionate-oxidizing bacteria with Microbiol27, 985-987. fumarate in the absence of methanogenic bacteria. Appl Environ Oude Elferink, 5.1. W. H., Maas, R. N., Harmsen, H. 1. & Stams, Microbiol59, 11 14-1 119. A. J. M. (1995). Desulforhabdus amigenus gen. nov., sp. nov., a Swofford, D. L. (1993). PAUP: Phylogenetic Analysis Using Arch sulfate reducer isolated from anaerobic granular sludge. Parsimony. Champaign, IL : Illinois Natural History Survey. Microbioll64, 119-124. Thauer, R. K., Jungermann, K. & Decker, K. (1977). Energy Oyaizu, H. & Woese, C. R. (1985). Phylogenetic relationships conservation in chemotrophic anaerobic bacteria. Bacteriol Rev among the sulfate respiring bacteria, myxobacteria, and purple bacteria. Syst Appl Microbiol6, 257-263. 41, 10&180. Pfennig, N. & Biebl, H. (1976). Desulfuromonas acetoxidans gen. Thiele, 1. H., Chartrain, M. & Zeikus, 1. (1988). Control of nov. and sp. nov., a new anaerobic, sulfur-reducing, acetate- interspecies electron flow during anaerobic digestion : role of oxidizing bacterium. Arch MicrobiolllO, 3-12. floc formation in syntrophic methanogenesis. Appl Environ Microbiol54, 10-19. Plugge, C. M., Dijkema, C. & Stams, A. J. M. (1993). Acetyl-CoA cleavage pathway in a syntrophic propionate oxidizing bac- Tholozan, 1. L., Samain, E., Grivet, 1. P., Moletta, R., Dubourguier, terium growing on fumarate in the absence of methanogens. H. C. & Albagnac, G. (1988). Reductive carboxylation of FEMS Microbiol Lett 110, 71-76. propionate to butyrate in methanogenic ecosystems. Appl Robbins, 1. E. (1987). 13C nuclear magnetic resonance studies of Environ Microbiol54, 441-445. propionate catabolism in methanogenic cocultures. Appl En- Wallrabenstein, C., Hauschild, E. & Schink, B. (1994). Pure culture viron MicrobioE53, 2260-226 1. and cytological properties of Syntrophobacter wolinii. FEMS Robbins, J. (1988). A proposed pathway for catabolism of Microbiol Lett 123, 249-254. propionate in methanogenic cultures. Appl Environ Microbiol Wallrabenstein, C., Gorny, N., Springer, N., Ludwig, W. & Schink, 54, 1300-1301. B. (1995a). Pure culture of Syntrophus buswellii, definition of its Samain, E., Moletta, R., Dubourguier, H. C. & Albagnac, G. (1984). phylogenetic status, and description of Syntrophus gentianae sp. Propionate conversion to butyrate in an anaerobic digester. In nov. Syst Appl Microbiol 18, 62-66. Biotechnological Advances in Processing Municipal Wastes for Wallrabenstein, C., Hauschild, E. & Schink, B. (1995b). Syntro- Fuels and Chemicals, pp. 223-233. Edited by A. A. Antono- phobacter pfennigii sp. nov., a new syntrophically propionate- poulos. Argonne, IL : Argonne National Laboratory. oxidizing anaerobe growing in pure culture with propionate and Sambrook, J., Fritsch, E. F. & Maniatis, T. (1989). Molecular sulfate. Arch Microbioll64, 346-352. Cloning: a Laboratory Manual, 2nd edn. Cold Spring Harbor, NY: Cold Spring Harbor Laboratory. Weiner, 1. H., Lemire, B. D., Elmes, M. L., Bradley, R. D. & Scraba, D. G. (1984). Overproduction of fumarate reductase in Es- Sauer, K. D., Stroot, P., Mackie, R. I.&Raskin, L. (1997). Microbial cherichia coli induces a novel intracellular lipid-protein organ- population dynamics linked to performance during anaerobic elle. J BacterioEl58, 590-596. co-digestion of municipal solid waste and sewage sludge. In 8th International Conference on Anaerobic Digestion. Sendai, Japan. Weisburg, W. G., Barns, S. M., Pelletier, D. A. & Lane, D. 1. (1991). J Schink, B. (1985). Mechanisms and kinetics of succinate and 16s ribosomal DNA amplification for phylogenetic study. propionate degradation in anoxic freshwater sediments and Bacteriol 173, 697-703. sewage sludge. J Gen Microbioll31, 643-650. Widdel, F. & Pfennig, N. (1981). Studies on dissimilatory sulfate- Schink, B. (1997). Energetics of syntrophic cooperation in reducing bacteria that decompose fatty acids. I. Isolation of new methanogenic degradation. MicrobioI Mol Bid Rev 61, sulfate-reducing bacteria enriched with acetate from saline 262-2 80. environments. Description of Desulfobacter postgatei gen. nov., sp. nov. Arch Microbioll29, 395-400. Shen, W. F., Squires, C. L. & Squires, C. L. (1982). Nucleotide sequence of the rrnG ribosomal RNA promoter region of Wolin, M. J. (1982). Hydrogen transfer in microbial communi- Escherichia coli. Nucleic Acids Res 10, 3303-33 13. ties. In Microbial Interactions and Communities, pp. 323-356. Sowers, K. R. & NOH, K. M. (1995). Techniques for anaerobic Edited by A. T. Bull & J. H. Slater. London: Academic Press. growth. In Archaea: a Laboratory Manual, pp. 15-47. Edited by Zhao, H., Yang, D., Woese, C. R. & Bryant, M. P. (1989). F. T. Robb, K. R. Sowers, H. J. Schreier, S. DasSarma & Assignment of Clostridium bryantii to Syntrophospora bryantii E. M. Fleischmann. Cold Spring Harbor, NY: Cold Spring gen. nov., comb. nov. on the basis of 16s rRNA sequence Harbor Laboratory. analysis of its crotonate-grown pure culture. Int J Syst Bacteriol Stadtman, T. C. & Barker, H. A. (1951). Studies on the methane 40, 4M4.

556 In terna tiona I Jo urn a I of Systema tic Bacteriology 49