Abstract
Microbial communities involving dehalogenating bacteria assist in bioremediation of areas contaminated with halocarbons. To understand molecular interactions between dehalogenating bacteria, we co-cultured Sulfurospirillum multivorans, dechlorinating tetrachloroethene (PCE) to cis−1,2-dichloroethene (cDCE), and Dehalococcoides mccartyi strains BTF08 or 195, dehalogenating PCE to ethene. The co-cultures were cultivated with lactate as electron donor. In co-cultures, the bacterial cells formed aggregates and D. mccartyi established an unusual, barrel-like morphology. An extracellular matrix surrounding bacterial cells in the aggregates enhanced cell-to-cell contact. PCE was dehalogenated to ethene at least three times faster in the co-culture. The dehalogenation was carried out via PceA of S. multivorans, and PteA (a recently described PCE dehalogenase) and VcrA of D. mccartyi BTF08, as supported by protein abundance. The co-culture was not dependent on exogenous hydrogen and acetate, suggesting a syntrophic relationship in which the obligate hydrogen consumer D. mccartyi consumes hydrogen and acetate produced by S. multivorans. The cobamide cofactor of the reductive dehalogenase—mandatory for D. mccartyi—was also produced by S. multivorans. D. mccartyi strain 195 dechlorinated cDCE in the presence of norpseudo-B12 produced by S. multivorans, but D. mccartyi strain BTF08 depended on an exogenous lower cobamide ligand. This observation is important for bioremediation, since cofactor supply in the environment might be a limiting factor for PCE dehalogenation to ethene, described for D. mccartyi exclusively. The findings from this co-culture give new insights into aggregate formation and the physiology of D. mccartyi within a bacterial community.
Subject terms: Environmental microbiology, Symbiosis
Introduction
Microbial communities interact in numerous ways, involving the transfer and consumption of metabolic products. Molecular hydrogen, for example, is an important electron carrier in syntrophic communities, in which hydrogen is produced by e.g., fermentation and taken up by hydrogen-consuming prokaryotes. This hydrogen consumption leads to a lower hydrogen partial pressure, which allows otherwise thermodynamically unfavorable reactions to proceed. Therefore, the involved bacteria are physiologically dependent on each other [1–3]. The probably carcinogenic groundwater pollutant tetrachloroethene (PCE), a remnant of e.g., bleaching, dry-cleaning and metal degreasing, is completely, but often slowly, dechlorinated to ethene in communities involving hydrogen transfer from fermenting bacteria to the obligately hydrogen-consuming Dehalococcoides mccartyi [4–7]. PCE and other organohalides such as hexachlorobenzene or polychlorinated biphenyls are used as terminal electron acceptors by D. mccartyi and other bacteria in an anaerobic respiratory chain coupling the dehalogenation to energy conservation via electron transport phosphorylation [6]. This process is termed organohalide respiration (OHR) and involves the corrinoid-containing reductive dehalogenases (RDases) as terminal reductases [8–10]. However, D. mccartyi is characterized by low growth rates and dehalogenates PCE slower [11] compared to other dehalogenating species such as Sulfurospirillum multivorans. D. mccartyi is strictly dependent on several specific vitamins, most importantly cobamides [12]. Besides being restricted to hydrogen as electron donor, D. mccartyi uses only acetate plus bicarbonate as carbon source and organohalides as electron acceptors. In addition, these bacteria are not able to de novo synthesize corrinoids, the obligate cofactor of RDases [11, 13]. While proteins for complete corrinoid biosynthesis are usually not encoded in the genomes of D. mccartyi [14], different studies revealed its ability to salvage and remodel corrinoids, enabling D. mccartyi to restore dechlorination [15–17]. The functionality of the corrinoid and thus the RDase is directly dependent on the type of the lower base in D. mccartyi. Only three types of corrinoids have so far been described to be functional in D. mccartyi strain 195: 5,6-dimethylbenzimidazolyl-cobamide ([DMB]-Cba), 5-methylbenzimidazolyl-cobamide and 5-methoxybenzimidazolyl-cobamide ([5-OMeBza]Cba). Nonfunctional corrinoids e.g., 5-hydroxybenzimidazolyl-cobamide or 7-adeninyl-cobamide ([Ade]Cba) can be converted to functional ones by replacement of the lower ligand in D. mccartyi when 5,6-dimethylbenzimidazole (DMB) is provided [16, 17].
Several studies on dechlorinating communities containing D. mccartyi in association with fermenting, acetogenic and/or methanogenic bacteria revealed higher dechlorination and growth rates than those of pure cultures [16, 18–26]. It is hypothesized that cross-feeding and a constant supply of growth factors such as corrinoids and biotin enhance growth [27]. Within these communities, non-dechlorinating fermenting bacteria provide hydrogen, acetate, and CO2 from e.g., lactate or butyrate fermentation. The fermenting bacteria are dependent on hydrogen consumers which keep the hydrogen partial pressure low [18, 21, 22, 28]. For example, co-culture experiments revealed an interspecies hydrogen transfer between Desulfovibrio desulfuricans fermenting lactate and D. mccartyi dechlorinating TCE [15]. Acetogens like Sporomusa ovata and sulfidogens (Desulfovibrio), produce different types of corrinoids which can be used by D. mccartyi [29, 30]. An interspecies cobamide transfer was also shown between Methanosarcina barkeri strain Fusaro and D. mccartyi strain BAV1, GT and FL2, when DMB was present [25, 26]. In the only co-culture of D. mccartyi (strains BAV1 and FL2) with a PCE-dechlorinating bacterium, Geobacter lovleyi, a corrinoid transfer was also observed [31]. In this co-culture, however, hydrogen had to be supplemented. All these studies showed more robust growth of D. mccartyi in co-cultures, resulting in higher dechlorination rates and cell yields than in pure cultures and sometimes, depending on the cobamide metabolism of the co-culture, a different degree of the dechlorination extent [32]. However, a PCE-dechlorinating bacterium providing hydrogen, acetate and corrinoids to D. mccartyi, to our knowledge, has not been described in the literature. Thus, further information on D. mccartyi co-cultures is needed to gain insights into complex microbial communities involving D. mccartyi. Relatively simple co-cultures provide a model community in which metabolic transfers are easier to follow. Recently, the PCE to cDCE-respiring S. multivorans, capable of de novo corrinoid production [33–35], was shown to produce hydrogen and acetate under fermentative growth conditions, e.g., with pyruvate or lactate and without electron acceptor present [36]. In the same study, a co-culture of S. multivorans with a methanogen dependent on hydrogen as electron donor was established. Therefore, S. multivorans is a promising partner for a co-cultivation with D. mccartyi. In addition, it is of interest, whether D. mccartyi is able to take up and utilize norpseudo-B12 ([Ade]NCba), so far known to be produced exclusively by S. multivorans and S. halorespirans [35, 37]. In this study, we investigated the physiological interaction between D. mccartyi strain BTF08 and 195 in co-culture with S. multivorans dechlorinating PCE to ethene by using dechlorination analytics, microscopy, and proteomics.
Materials and methods
Cultivation of pure cultures
D. mccartyi cultures BTF08 and 195 (maintained at the UFZ Leipzig) were cultivated in 200 mL serum bottles containing 100 mL bicarbonate-buffered mineral salt medium with 5 mM acetate and 148 nM vitamin B12 (cyanocobalamin, ca. 200 µg/L), reduced with Na2S · 7 H2O (final concentration, 0.25 g/L) [38]. Anoxic atmosphere was established by 30 cycles of gassing and degassing with nitrogen, and CO2 was added to a final atmosphere of N2:CO2 (75:25 v/v 150 kPa). After autoclaving the medium and adjusting the pressure to ~100 kPa with nitrogen and CO2, we applied, in addition, hydrogen [50 kPa] to avoid possible electron donor limitation. PCE (>99% purity, Sigma Aldrich, Steinheim, Germany) and cDCE (97% purity, Sigma Aldrich, Steinheim, Germany) served as electron acceptors and were added with a microliter syringe (Hamilton, Bonaduz, Switzerland) to a final concentration of 0.35 mM (aqueous-phase concentration). Re-feeding of the cultures was done with the same amount of PCE or cDCE after complete conversion to ethene. After maximally three re-feeding steps, cultures were transferred [10% (v/v)] into fresh medium. To evaluate the effect of different types and concentrations of B12 on dechlorination activities, D. mccartyi cultures received 54 nM norpseudo-B12 ([Ade]Cba) or 5-OMeBza-B12 ([5-OMeBza]Cba), each. Norpseudo-B12 was extracted as described previously [39] from 6 L of S. multivorans grown anaerobically with 40 mM pyruvate and 10 mM PCE as described elsewhere [40]. In brief, crude cell extract was acidified to a pH of ≤5 with acetic acid before adding 0.1 M potassium cyanide and boiling the sample for 15 min. Afterwards, the sample was centrifuged and the supernatant kept on ice. The cell pellet was resuspended in 10 mL ultrapure water (UPW) and the same extraction procedure was applied twice. The combined supernatant was mixed with Amberlite XAD4 (0.25 g XAD4 per mL extract; Sigma-Aldrich) and incubated on a shaker overnight. The supernatant was removed and the cobamide-loaded XAD4 material was washed with 10 volumes of UPW. Elution of cobamide was done for 1 h on a shaker with 1 volume of methanol which was repeated twice. A vacuum concentrator was used to completely dry the eluates which were then resuspended in 2 mL UPW. The sample was applied on a column containing 3 g aluminum oxide, recovered with 50 mL UPW, and dried. Resuspension of purified norpseudo-B12 was done with UPW. 5-OMeBza-B12 was obtained in the same way from 6 L of Desulfitobacterium hafniense DCB2 grown anaerobically with 40 mM pyruvate and 10 mM ClOHPA (3-chloro-4-hydroxy-phenylacetate) on a medium amended with 25 µM 5-OMeBza [41]. S. multivorans (DSMZ 12446) was cultured in the same mineral salt medium as D. mccartyi [38] with 40 mM lactate and 10 mM nominal PCE in hexadecane (2 mL PCE/hexadecane per 100 mL medium) but without the addition of acetate and hydrogen [38]. All cultivation experiments were performed statically at 28 °C in the dark and in biological triplicates.
Co-cultivation of S.multivorans and D.mccartyi
Co-cultures of S. multivorans and D. mccartyi strain BTF08 or 195 were maintained in the same mineral salt medium as the pure cultures, without acetate and hydrogen. Initially, the inoculum of the pure cultures into the co-culture was 10% of each pure culture. The medium contained 25 mM lactate (D/L, >85% purity, Sigma-Aldrich, Steinheim, Germany) as the electron donor for S. multivorans and 0.35 mM PCE (aqueous-phase concentration) as the electron acceptor. Lactate (25 mM) and PCE (0.35 mM) was re-fed after depletion of substrates was measured. The B12-dependance of the co-cultures was tested with 148 nM vitamin B12 (>98% purity, Sigma-Aldrich, Steinheim, Germany) serving as the positive control and without vitamin B12 amendments. Cultures without vitamin B12 received 1 µM DMB (>99% purity, Sigma-Aldrich, Steinheim, Germany), where indicated. The DMB dose used had only minimal negative effect on S. multivorans growth [39]. For isotope fractionation experiments, S. multivorans and Sm/BTF08 co-cultures were cultivated in 50 mL serum bottles with 25 mL medium. Replicate bottles (triplicates for each time point) were inoculated at the same time and the dehalogenation process was stopped at different time points by addition of 3 mL 2 M Na2SO4 (pH 1.0).
Quantitative (q)PCR analysis of cell growth
Quantitative PCR (qPCR) was applied to count Sulfurospirillum and Dehalococcoides 16S rRNA gene copies. DNA was extracted from 1 mL co-culture taken from different time points during the cultivation experiment using the NucleoSpin Tissue DNA extraction kit according to the manufacturer’s instructions (Macherey-Nagel, Düren, Germany). Cell numbers were quantified by direct epifluorescence microscopy of Sybr-green stained cells immobilized on agarose-coated slides to generate standard curves for qPCR as described previously [42]. For the corresponding standard curves, D. mccartyi and S. multivorans cell suspensions with known cell numbers (1 × 104 to 1 × 108 and 1 × 105 to 1 × 109, respectively) were subjected to qPCR. The qPCR reaction mixture contained 1 µL of gDNA or DNA standard, 6.25 µL 1× KAPA SYBR Fast master mix (Sigma Aldrich, Steinheim, Germany) and 0.208 µM forward and reverse primer. Primers used were Dhc_sp_16S_fw (5′-GTATCGACCCTCTCTGTGCCG-3′) and Dhc_sp_16S_rev (5′-GCAAGTTCCTGACTTAACAGGTCGT-3′) for D. mccartyi and Smul_16S_fw (5′-AGGCTAGTTTACTAGAACTTAGAG-3′) and Smul_16S_rev (5′-CAGTCTGATTAGAGTGCTCAG-3′) for S. multivorans. The conditions of the PCR program were as followed: 95 °C for 2 min (initial denaturation) followed by 40 cycles of 55 °C (S. multivorans primer) or 60 °C (D. mccartyi primer) for 20 s (annealing), 72 °C for 30 s (elongation) and 95 °C for 10 s (denaturation). Each qPCR program included a melting curve for verification of specific target DNA amplification and primer efficiency was tested for used primers (R2 Sm: 99.7%; R2 Dhc: 98.8%, see Supplementary Fig. S1). The cell numbers of samples were calculated by comparing the sample CT values with the CT values of the standard curve obtained from microscopical cell counting (Supplementary Fig. S1). All samples were conducted in three biological replicates with two corresponding technical replicates and three technical replicates for the calibration curve.
Analytical methods
Ethene and chlorinated ethenes were quantified gas-chromatographically with a flame ionization detector (Clarus 500, Perkin Elmer, Rodgau, Germany) and a CP-PoraBOND Q FUSED SILICA 25 m × 0.32 mm column (Agilent Technologies, Böblingen, Germany). Samples from the cultures (1 mL of the gas phase and 1 mL of the liquid phase) were transferred to GC vials with gast tight syringes, the sampling proceeded via a headspace sampler (HS 40, Perkin Elmer; needle temperature 100 °C, vial pressurized with 0.1 kPa nitrogen for 2 min). The GC vial with the liquid phase was heated in the HS 40–80 °C for 5 min. Samples were transferred through the transfer line (100 °C) into the GC. Ethene and chlorinated ethenes were separated with 4 min at 60 °C rising to 280 °C in 10 °C min−1 steps. The injector temperature was fixed at 250 °C and the detector temperature at 300 °C. Standard curves of ethene and each chlorinated ethene were recorded for peak area quantification and retention times were compared to known standards. Nonane served as an internal standard during measurements. The retention times were: PCE (detection limit [dl] 2.1 µM), 15.1 min; TCE (dl 2.5 µM) 13.2 min; cDCE (dl 3.1 µM), 11.3 min; VC (dl 3 µM), 6.0 min; ethene (dl 2.5 µM), 1.3 min. Due to the low solubility of PCE, it was added to the medium followed by stirring for at least 8 h to allow it to completely dissolve. This lead to a reliable quantification of only the initial PCE concentration, but not of the re-fed PCE, especially since a portion of the re-fed PCE is rapidly degraded by the now higher abundant S. multivorans cells. The concentrations of chlorinated ethenes (in µM or mM) were calculated by summing up the concentrations in the gas phase and liquid phase. Dechlorination rates were calculated according to the average amount of stoichometrically converted PCE to the corresponding end products VC (in the case of D. mccartyi strain 195, where the formation of co-metabolically produced ethene was negligible) or ethene (for D. mccartyi strain BTF08) divided by time in days. For example the conversion of 400 µM PCE into 400 µM ethene over 10 days resulted in a dechlorination rate of 40 µM PCE/day. Hydrogen (dl 0.8 µM) was measured gas-chromatographically using a thermal conductivity detector (AutoSystem, Perkin Elmer, Rodgau, Germany) equipped with a Carboxen-1010 PLOT capillary column 30 m × 0.53 mm (Supelco, München, Germany) column. Separation of analytes was done at a temperature of 35 °C (detector at 150 °C). For this, the culture headspace (1 mL) was sampled with gas-tight syringes (Hamilton, Bonaduz, Switzerland) and injected directly into the injection valve of the GC. Concentrations were calculated using calibration curves ranging from 4 to 50 µmol hydrogen. Organic acids (lactate, acetate, pyruvate, and succinate) were analyzed using a reversed-phased HPLC (Merck-Hitachi, Darmstadt, Germany) equipped with a diode array detector (L-7450) and separated on an AMINEX HPX-87H column (7.8 × 300 mm; BioRad, Munich, Germany) with a cation H guard pre-column. Samples (1 mL) from the liquid phase of the cultures were filtered (MiniSart RC4, 0.2 µm, Sartorius, Göttingen, Germany) and acidified with 2.5 µL H2SO4. Of this sample, 20 µL was injected into the HPLC. Monitoring of organic acids was based on their absorption at 210 nm. The column was operated at a temperature of 50 °C and 5 mM (v/v) H2SO4 served as mobile phase with a flow rate of 0.7 mL min−1. The retention times were: lactate (dl 0.2 mM), 10.61 min; pyruvate (dl 0.01 mM) 7.92 min; acetate (dl 0.4 mM), 12.88 min; succinate (dl 0.15 mM), 9.81 min. Peak areas and retention times were related to standards ranging from 1 to 10 mM or 0.5 to 2 mM (for pyruvate).
Compound-specific stable isotope analysis
Determination of the carbon isotope composition of the chlorinated ethenes in pure culture of S. multivorans and in co-culture of S. multivorans and D. mccartyi strain BTF08 was done using gas chromatography combustion isotope ratio mass spectrometry (GC-C-IRMS; Thermo GC Trace 1320 combined with Thermo-Finnigan MAT 253 IRMS, Bremen, Germany) [43]. All samples were analyzed in technical triplicates. 2 mL liquid phase were taken from the respective sample and transferred to a He-flushed 10 mL crimped vial. Of these, 1 mL was taken from the headspace via an autosampler (Thermo TriPlus RSH Autosampler, Bremen, Germany) and injected in a gas chromatograph with a split ratio of 1:5. Chlorinated ethenes were separated on a DB-MTBE column (60 m × 0.32 mm × 1.8 µm, J&W Scientific, Waldbronn, Germany) and the following temperature program: 40 °C for 5 min, increase to 250 °C by 20 °C min−1 and hold for 5 min using helium as carrier gas at a flow rate of 2.0 mL min−1 (Injector at 250 °C).
The carbon isotope composition is given in the δ-notation (‰) relative to the Vienna Pee Dee Belemnite standard [44]. Carbon isotope fractionation was calculated using the Rayleigh equation (Eq. 1) where R0 and Rt represent the isotope values and C0 and Ct the concentrations at time 0 and t [45, 46].
1 |
The carbon isotope enrichment factor (εC) relates changes in the concentration of the isotopes to changes in their isotope composition. A two-tailed T-Test was used to calculate the 95% confidence interval based on the slope. Standard deviations were obtained from at least triplicate measurements (<0.5‰).
B12 extraction and MS analysis
The B12 content of three independently cultivated 100 mL cultures was analyzed. For this, the culture volume was reduced to 20 mL using a vacuum concentrator and 0.1 M potassium cyanide was added. After boiling the samples for 20 min, cell debris was removed by centrifugation (10 min, 6700 × g, 8 °C). The supernatant was applied onto a C-18 column (CHROMABOND C-18 ec, Macherey-Nagel, Düren, Germany) equilibrated with 5 mL 100% (v/v) methanol and 5 mL UPW. Washing of the column was done twice with 5 mL UPW and B12-types were eluted with 5 mL 100% (v/v) methanol. The eluate was completely dried in a vacuum dryer and dissolved in UPW prior to analysis. The extract was injected to ultrahigh performance nano-flow liquid chromatography (UHPLC) (Ultimate 3000, Thermo Fisher, Waltham, USA) coupled to mass spectrometer (LC–MS, Orbitrap Fusion, Thermo Fisher, Waltham, USA) via heated electrospray ionization (HESI-II, Thermo Fisher, Waltham, USA). The UHPLC was equipped with a Hypersil Gold C18 column (150 × 2.1 mm, 3 µm film thickness; Thermo Fisher, Waltham, USA) and a C18 guard column (10 × 2.1 mm, Waters, Milford, USA). Chromatographic separation using a gradient method with 0.1% formic acid (A) and methanol (B) as mobile phase was applied as following: 5% B for 1 min, 60 min gradient to 90% B, 4 min at 90% B, 1 min gradient to 5% B and 4 min at 5% B with a constant flow of 0.2 mL min−1 and 25 °C column oven temperature. Injection volume was 5 µL. Ionization was set to positive ion mode at 3.5 kV, 35 arbitrary units (Arb) sheath gas, 10 Arb auxillary gas, 325 °C ion transfer tube temperature and 275 °C vaporizer temperature. Orbitrap resolution for precursor scan (MS1) was set to 120.000 with a scan range of 300–1600 m/z. Data evaluation was done on the original mass spectra comparing with predicted masses of corrinoids (Supplementary Tables S1 and S2, for cobalamin standards see Supplementary Fig. S2).
Scanning electron microscopy and fluorescence in situ hybridization
Field emission-scanning electron microscopy (FE-SEM) was performed with co-cultures of S. multivorans and D. mccartyi strains BTF08 and 195 and pure S. multivorans and D. mccartyi strain BTF08 cultures. All of the cultures were treated the same way for FE-SEM as follows. Cells of 5 mL culture were incubated for 15 min with 2.5% glutaraldehyde and pre-fixed for 2 h on poly-L-lysine coated cover slides (12 mm, Fisher Scientific, Schwerte, Germany). Cover slides were washed three times with 0.1 M sodium cacodylate (pH 7.2) (>98% purity, Sigma Aldrich, Steinheim, Germany) and post-fixed for 1 h with 1% osmium tetroxyde in the same cacodylate buffer. After fixation, samples were dehydrated using different ethanol concentrations (35%/50%/70%/80%/95%/100% v/v) and incubated for 10 min at each step. Critical point drying was done in a Leica EM CPD200 Automated Critical Point Dryer (Leica, Wetzlar, Germany), followed by coating with 6 nm platinum in a BAL-TEC MED 020 Sputter Coating System (BAL-TEC, Balzers, Liechtenstein). Imaging of the samples was done with a Zeiss-LEO 1530 Gemini field emission-scanning electron microscope (Carl Zeiss, Oberkochen, Germany) at different magnifications and at 10 kV acceleration voltage. Fluorescence in situ hybridization (FISH) was performed as described previously [47, 48]. In brief, samples were fixed with formaldehyde (2% v/v final concentration) for 2 h at 4 °C and filtered on polycarbonate membrane filters (47 mm diameter, 0.2 µm pore size, Nucleopore). Filters were stored at −20 °C until further processing. FISH detection of D. mccartyi strain BTF08 and 195 was done with Cy3-labeled DHC1259t and DHC1259c probes and S. multivorans detection with FITC-labeled probes SULF F220ab [49]. Imaging of un-aggregated cells was done with an epifluorescence microscope (Olympus, BX51) combined with an Olympus XM10 camera. Images were analyzed via Cell-F software. Aggregates were visualized using a confocal laser scanning microscopy (CSLM, Olympus FV1000).
Protein extraction and proteome analysis
Samples for proteome analyses were taken ~2 weeks after one re-feeding with PCE or cDCE (pure D. mccartyi strain BTF08 cultures) or 12 h after the third re-feeding with PCE (co-cultures Sm/BTF08, Supplementary Fig. S3). When harvested, PCE, TCE, and cDCE were the dominant chlorinated ethenes in the pure cultures, while cDCE and VC were the dominant chlorinated ethenes in the co-cultures (Supplementary Fig. S3). Samples were processed as described previously [50]. Briefly, protein extraction was performed in lysis buffer (20 mM HEPES, 1 mM sodium vanadate, 1 mM β-glycerol phosphate, 2.5 mM sodium pyrophosphate, 8 M urea [51]) by three freeze/thaw-cycles and ultrasonic bath treatments. Ten micrograms of protein dissolved in 100 µL UPW was precipitated with the fivefold amount (v/v) of ice-cold (−20 °C) acetone. Protein pellets were dissolved in 50 μL SDS sample buffer (2% SDS, 2 mM beta-mercaptoethanol, 4% glycerol, 40 mM Tris-HCl pH 6.8, 0.01% bromophenolblue), heated to 90 °C for 5 min and separated on an SDS gel (12.5%). The gel was run until the samples entered the separating gel. Afterwards, a 3–5 mm protein band from each sample was cut out, destained, dehydrated, reduced with 10 mM dithiothreitol, alkylated with 100 mM iodoacetamide and proteolytically cleaved overnight at 37 °C using trypsin (Promega, Madison, WI, USA). Peptides were extracted, desalted using C18 ZipTip columns (Merck Millipore, Darmstadt, Germany) and resuspended in 0.1% (v/v) formic acid before LC–MS analysis.
Proteolytic lysates were separated using an Ultimate 3000 RSLCnano liquid chromatographic instrument (Thermo Scientific, Germany). Mass spectrometry was performed on an Orbitrap Fusion mass spectrometer (Thermo Scientific, San Jose, CA, USA) coupled to a TriVersa NanoMate (Advion, Ltd., Harlow, UK). Samples of 5 µL were loaded onto a trapping column (Acclaim PepMap100 C18, 75 μm × 2 cm, Thermo Scientific) using 96% eluent A (0.1% formic acid) and 4% eluent B (0.08% formic acid, 80% acetonitrile) at a flow rate of 5 μL min−1 and separated via a 25 cm analytical column (Acclaim PepMap100 C18, 75 μm × 25 cm, Thermo Scientific) at 35 °C using a constant flow rate of 300 nL/min. Peptide separation was achieved by applying a linear gradient of eluent B from 4 to 50% within 100 min. Full MS scans were measured in the Orbitrap mass analyzer within the mass range of 400–1600 m/z at 120,000 resolution using an automatic gain control (AGC) target of 4 × 105 and maximum fill time of 60 ms. The MS instrument measured in data-dependent acquisition mode using the highest intense ion (top speed, 3 s cycle time). Positive ion charge states between 2 and 7 were selected for MS/MS. Precursor masses for MS/MS were selected based on the highest intensity and excluded from further MS/MS for 30 s to prevent redundancy in MS/MS acquisition. After higher energy collisional (HCD) fragmentation at normalized collision induced energy of 30%, fragment masses were scanned in the Orbitrap mass analyzer at a resolution of 15,000 with 5 × 104 AGC target and a maximum injection time of 150 ms.
LC–MS/MS data were analyzed using Proteome Discoverer (v2.1, Thermo Scientific). MS/MS spectra were searched against a combination of a S. multivorans (3233 nonredundant protein-coding sequences, downloaded January 2017 from NCBI GenBank, accession number CP007201.1) and a D. mccartyi strain BTF08 database (1535 nonredundant protein-coding sequences, downloaded December 2016 from NCBI, accession number CP004080.1). A “common repository of adventitious proteins database” was integrated to ensure correct protein identifications. The SEQUEST HT algorithm was used with the following settings: trypsin as cleavage enzyme, oxidation on methionine as dynamic and carbamidomethylation on cysteine as static modification, up to two missed cleavages, precursor mass tolerance set to 10 ppm and fragment mass tolerance to 0.02 Da, respectively. Only peptides with a false discovery rate ≤ 1%, XCorr ≥2, q-value and the posterior error probability ≤0.01 were considered as identified (Supplementary Excel File S1). Quantification of proteins was performed using the average of the top three peptide MS1 areas. After log10 transformation, the protein values were normalized to the median of all proteins of a sample, to the median of all proteins of the respective organism in that sample and the median of all samples and scaled so that the global minimum is zero. Two outliers of the co-culture proteome replicates with only 11 (C3) and 92 (P1, see Supplementary Excel File S1) protein identifications, compared to at least 317 protein identifications from the other D. mccartyi pure cultures, were excluded from the analysis. Proteins with only one out of three possible quantitative values per sample were considered as identified only. P-values were calculated using a two-tailed, homoscedastic student’s t-test, and multiple corrected with the Benjamini–Hochberg method. Figures were created using an in-house written R-script with the packages gplots, ggplot2, ggbiplot, dplyr, miscTools, and vegan. The non-parametrical multiple dimensional scaling (nMDS)-analysis was performed with the anosim-function of the vegan package in R (v3.4.1). Pairwise Indicator Species Analysis was used to identify proteins that were significantly associated with the different cultivation conditions [52, 53]. Indval scores and significances were calculated according to Malik et al. [54].
Results
Growth and dechlorination in Sulfurospirillum (Sm)/Dehalococcoides (Dhc) co-cultures
The growth characteristics and the PCE to cDCE dechlorination pattern of S. multivorans cultivated in the co-culture medium (Supplementary Fig. S4) were comparable to those in the routinely used medium [55]. With lactate as electron donor and PCE as electron acceptor, a co-culture of S. multivorans and D. mccartyi BTF08 maintained over 10 transfers under the same conditions dechlorinated PCE to stoichiometric amounts of ethene within 8 days after inoculation (Fig. 1A). The dechlorination rate (PCE to ethene) of the Sm/BTF08 co-culture was 4.5-fold higher compared to the D. mccartyi strain BTF08 pure culture (Table 1). In the latter, PCE was completely reduced to ethene within 35 days at a rate of 9 ± 0.3 µM/day (Supplementary Fig. S5A). The culture was re-fed with PCE at day 8 and day 12 after inoculation. After re-feeding, the dechlorination increased (Fig. 1A) and complete dechlorination of PCE occurred within 3 days. PCE was dechlorinated to cDCE within 2 days. To check whether S. multivorans, known for its high dehalogenation rate [55], was responsible for this fast dechlorination, the stable carbon isotope fractionation patterns (which largely differ between D. mccartyi and S. multivorans) of pure and co-cultures were compared. The isotope fractionation pattern of PCE in the co-culture did not change significantly, and ranged from −30.2 ± 0.09 to −29.5 ± 0.12‰ at 70% of transformed PCE (Supplementary Fig. S6A). A low but significant fractionation was measured in the pure culture of S. multivorans (from −29.2 ± 0.05 to −27.6 ± 0.11‰ at 56% of transformed PCE, Supplementary Fig. S6A). The isotope enrichment factors for the S. multivorans pure and the co-culture were in the same range while differing largely from that of a D. mccartyi strain BTF08 pure culture (Sm/BTF08 co-culture: εC = −0.4 ± 0.3‰; S. multivorans pure culture: εC = −2.0 ± 0.4‰, Supplementary Fig. S6B; D. mccartyi strain BTF08: εC = −5.0 to −9.0‰ [56]). This high similarity in the PCE isotope fractionation patterns of S. multivorans pure and co-cultures is likely due to PCE to cDCE dechlorination performed nearly exclusively by S. multivorans. The fast dechlorination of PCE to cDCE in less than 2 days was also reflected in the increase of the S. multivorans cell number (at least one cell doubling per day), until PCE was completely dechlorinated to cDCE (Fig. 1C). After this respiratory growth, a weaker growth (less than one cell doubling in 20 days) was observed, probably correlating to lactate fermentation of S. multivorans (Figs. 1E, F). D. mccartyi strain BTF08 needed 7 days for one cell doubling in the co-culture. For both organisms, a correlation between dechlorination and growth was observed. The ratio between S. multivorans and D. mccartyi strain BTF08 cells changed from initially 2.6 to 5.9 after 2 days and 4.6 after 15 days and two re-feeding steps. After 12 days, when the second dose of PCE was completely dechlorinated to ethene, lactate was completely consumed, therefore lactate and PCE were re-fed. Acetate production occurred continuously during the whole dechlorination process (Fig. 1E), other organic acids such as succinate were not detected. No hydrogen was detected in the gas phase at any point. Because the concentration of hydrogen and succinate which were shown to be produced during pyruvate fermentation of S. multivorans pure cultures [36] might be below the detection limit in our setup and pure S. multivorans cultures could not grow via lactate fermentation, a stoichiometry could not be calculated.
Table 1.
Organism(s) | Electron donor | Dechlorination rate (µM day−1) |
---|---|---|
With vitamin B12 | ||
D. mccartyi BTF08 | H2 | 9 ± 0.3 |
D. mccartyi 195 | H2 | 15 ± 0.4 |
Sm/BTF08 | Lactate | 41 ± 2 |
Sm/195 | Lactate | 48 ± 1 |
Without vitamin B12 | ||
Sm/BTF08 | Lactate | – |
Sm/195 | Lactate | 9 ± 0.04 |
Without vitamin B12/with DMB | ||
Sm/BTF08 | Lactate | 36 ± 2 |
Sm/195 | Lactate | 8 ± 0.5 |
– No dechlorination to VC or ethene observed.
Similar growth characteristics and dechlorination behavior were observed in the Sm/195 co-culture cultivated under the same conditions, except that vinyl chloride (VC) was the major dechlorination product. The first dose of PCE was dechlorinated within 7 days stoichiometrically to VC (Fig. 1B). The increase of cell number was slightly lower for S. multivorans and slightly higher for D. mccartyi strain 195 compared to the Sm/BTF08 co-culture (Fig. 1D). After the second dose of PCE was dechlorinated to VC, a low amount of ethene was produced starting on day 10, reaching 104 µM ethene after day 15. The Sm/195 co-culture reduced PCE to VC more than threefold faster than the D. mccartyi strain 195 pure culture, which completed dechlorination to VC within 18 days (Table 1, Supplementary Fig. S5B).
Corrinoid transfer in co-cultures and the effect of the lower corrinoid ligand
D. mccartyi strains rely on externally provided corrinoids for dehalogenation and growth. This was also tested for D. mccartyi strains BTF08 and 195, which only showed negligible cDCE dechlorination after 100 days without addition of corrinoid (Fig. 2A, D). Therefore, it was of interest whether S. multivorans is able to provide functional corrinoids for D. mccartyi strains BTF08 and 195. In Sm/BTF08 co-cultures without the amendment of vitamin B12, stoichiometric dechlorination of PCE to cDCE was obtained (~30 µmol/bottle/day) (Fig. 2B). No further dechlorination of cDCE to VC or ethene was detected, indicating that S. multivorans alone was responsible for the dechlorination. When cDCE dechlorination stalled in the Sm/BTF08 co-culture, 1 µM 5,6-dimethylbenzimidazole (DMB) was added, which resulted in subsequent cDCE dechlorination (Fig. 2C). Ethene production rates from cDCE (36 ± 2 µM/day) were similar to the co-culture amended with vitamin B12 (41 ± 2 µM/day). The dechlorination rate increased after re-feeding with PCE to 8 µmol/bottle/day. In the Sm/BTF08 co-culture with DMB but without vitamin B12 amendment, three different types of corrinoids were found by mass spectrometric analysis: [Ade]NCba, [DMB]NCba and [DMB]Cba (Supplementary Fig. S7).
Interestingly and in contrast to the Sm/BTF08 co-culture, the Sm/195 co-culture without vitamin B12 amendment (-B12) dechlorinated PCE to VC, although at low rates (Fig. 2E). After 35 days, PCE was re-fed, and the cDCE to VC dechlorination rate increased fourfold (3.6 µmol/bottle/day). The only corrinoid detected in the Sm/195 co-culture -B12 was [Ade]NCba (Supplementary Fig. S8). No significant increase in cDCE dechlorination was observed when 1 µM DMB was added to the Sm/195 co-culture (Fig. 2F). Similar to the Sm/BTF08 co-culture, [Ade]NCba, [DMB]NCba and [DMB]Cba were found by mass spectrometric analysis when DMB was added to the Sm/195 co-culture (Supplementary Fig. S9). To confirm that D. mccartyi strain 195 can use [Ade]NCba for dechlorination of cDCE to VC, we amended a pure culture with [Ade]NCba isolated from S. multivorans (Supplementary Fig. S10A). Dechlorination of 50 µmol cDCE to VC was completed within 22 days (Supplementary Fig. S10A). D. mccartyi strain 195 pure cultures amended with [5-OMeBza]Cba showed slightly faster dechlorination and the cDCE was converted within 16 days into VC (Supplementary Fig. S10B). Only the amended corrinoid types were detected in the cultures via MS, impurities and rearrangement of corrinoids could be therefore excluded (Supplementary Fig. S11 and S12).
Electron microscopy and FISH analysis of formed cell aggregates
After about 25 transfers on lactate and PCE, all co-cultures formed spherical aggregates up to 2 mm in diameter (Fig. 3A). FE-SEM was applied to uncover the cell morphology and cell distribution in these aggregates. After preparation for FE-SEM, the sizes of the aggregates were lower (30–200 µm, Fig. 3B, C). Electron micrographs of both co-cultures revealed a compact network of S. multivorans and D. mccartyi cells coiled around net-forming filament-like structures. The cells were embedded in an extracellular matrix (ECM) which might aid cell-to-cell contact (Fig. 3D, Supplementary Fig. S13). S. multivorans could be distinguished from D. mccartyi by FISH with specific oligonucleotide probes targeting 16S rRNA and 3-dimensional imaging showed a spatial organization and an almost equal distribution of both species within the aggregates (Fig. 3E, Supplementary Fig. S14). The high resolution of the confocal laser scanning microscopy enabled visualization of single cells and revealed the same morphologies as in the electron micrographs. In the FISH pictures, the sizes of the aggregates ranged from 50 to 100 µm in diameter.
S. multivorans revealed a typical helical rod-shaped cell structure and a size of 2–5 µm by 0.5 µm at magnifications of around ×10.000 and ×20.000 in FE-SEM as described previously [55] (Fig. 4, Supplementary Fig. S13). However, the typical polar flagellum was only observed in a few cells and several flagella seemed to be detached from cells, possibly a part of the ECM (Fig. 4, Supplementary Fig. S13). D. mccartyi showed an atypical cell morphology in the co-cultures. Microscopic analysis of the pure culture revealed a disc-shaped irregular coccus of 0.5 µm diameter (Fig. 4a, Supplementary Fig. S15), as previously described [11], whereas the D. mccartyi strains in the co-culture showed 0.5 µm large barrel-like cells with a flattened cell pole at one side and a ring-shaped septum (Fig. 4, Supplementary Fig. S13). Visual analysis of cells separated from aggregates in the co-culture identified unequivocally both organisms and confirmed the presence and unusual morphology of D. mccartyi (Supplementary Fig. S15 and S16).
Proteomics of pure and co-cultures
We applied a label-free shotgun proteomics approach to identify changes in protein abundances during PCE dechlorination in pure and co-cultures (with and without vitamin B12) with D. mccartyi strain BTF08 and S. multivorans. The clustering approach nMDS based on quantified proteins revealed a significant separation between pure and co-cultures (Dhc BTF08 proteins p = 0.001, Sm proteins p = 0.004, Supplementary Fig. S17). A multi-level pattern analysis was applied to determine indicator proteins for a given condition (i.e., co-culture vs. pure culture) to better understand the functional changes occurring during the dehalogenation in the co-culture (Supplementary Excel File S2).
Of the 20 RDases encoded in the genome of D. mccartyi strain BTF08 [57], only two RDase proteins were identified, the gene products of btf_1393 (a hitherto not annotated RdhA) and btf_1407 (the vinyl chloride reductase VcrA). The two reductive dehalogenases PceA (PCE reductive dehalogenase) and TceA (TCE reductive dehalogenase), putatively involved in dechlorination of PCE to cDCE, were not identified under any condition. While VcrA was one of the most abundant proteins under all tested conditions (Fig. 5, Supplementary Fig. S18, Supplementary Excel File S1), the gene product of btf_1393 was more abundant in the two co-cultures (Fig. 5, Supplementary Excel File S2). A BLASTp search against the NCBI nr database revealed that the btf_1393 amino acid sequence was almost identical (99% or 497/498 amino acid sequence identity over the whole length) to an RdhA from D. mccartyi 11a5, encoded by 11a5_1355 and characterized as a novel PCE RDase PteA [56, 58]. In S. multivorans, the proteins encoded in the organohalide respiratory gene were present among all conditions as described previously [59, 60] (Supplementary Excel File S1).
Only a few proteins encoded in the genomes of S. multivorans or D. mccartyi are annotated to play a potential role in the formation of aggregates, e.g., via an ECM. The proteins which are part of a putative type II pili system in D. mccartyi (encoded by btf_1229 to btf_1240) were present in low to medium amounts among all conditions (about median [Med] to lower than Med minus one standard deviation [SD]) but not significantly more abundant in the co-cultures. Many proteins involved in flagellar motility of S. multivorans were lower abundant in the co-culture, with most of the Flg and Fli proteins not detected (Supplementary Excel File S1). Protein indicator analysis revealed further that several outer membrane porins of S. multivorans (encoded by SMUL_0494, SMUL0693, SMUL_0926, and SMUL_2351) were relevant proteins for the co-cultures. In addition, several molybdopterin oxidoreductases (e.g., a nitrate reductase) of S. multivorans were highly abundant only in the co-culture (Supplementary Table S3). Proteins related to cell division (tubulin/GTpase encoded by btf_0551, FtsZ, btf_0595, FtsH, btf_357, a cell division trigger factor, btf_0631) were more abundant or exclusively quantified in pure cultures (Fig. 5, Supplementary Table S4, Supplementary Excel File S2). A hypothetical protein encoded close to the tubulin (btf_0548) was also highly abundant (>Med+SD or >Med) only in cells of the pure culture, while it could not be quantified in any of the co-cultures.
The amidohydrolase CbiZ (btf_610), responsible for cleavage of the nucleotide loop of corrinoids, was quantified only in both co-culture conditions in average abundance (Fig. 5). The l-threonine 3-O-phosphate decarboxylase CobD, which synthesizes the linker of the lower base and the corrinoid ring of cobamides, could not be quantified in any culture.
Discussion
In this study, we investigated the dechlorination of PCE to ethene (or vinyl chloride) in co-cultures of S. multivorans with D. mccartyi BTF08 and 195. Dechlorination profiles, metabolite analysis and growth studies point to a biphasic physiology of the co-culture. In the first stage, when PCE or TCE serve as electron acceptors, S. multivorans grows by OHR with lactate as electron donor. In this phase, D. mccartyi does not contribute significantly to PCE dechlorination as indicated by the stable isotope fractionation pattern and the corresponding enrichment factors. This can be explained by the insufficient supply of D. mccartyi with hydrogen as electron donor due to the lack of (or very low) hydrogen production by S. multivorans during respiratory growth. In the second phase of the co-culture, when PCE has been completely converted to cDCE after less than 2 days, S. multivorans grows via fermentation of lactate mainly to acetate, CO2 and hydrogen [36]. The fate of a part of the organic carbon and of the electrons generated by lactate oxidation could not be elucidated in this study. This part might have been used for biomass production and the generation of small amounts of organic acids, such as succinate, below the detection limit of the HPLC used here. It has been shown earlier that, for thermodynamic reasons, lactate can only be utilized fermentatively by S. multivorans in co-cultures, where hydrogen concentration is kept low by a syntrophic hydrogen consumer, while S. multivorans does not grow fermentatively on lactate in pure cultures [36]. In the co-culture described here, D. mccartyi utilizes H2 produced by S. multivorans as electron donor for reductive dehalogenation of cDCE or VC (Fig. 6). As expected, PCE was completely dechlorinated to ethene in the Sm/BTF08 co-culture and mainly to VC and minor amounts of ethene in Sm/195. A similar slow and incomplete VC dechlorination was found for pure cultures of the latter strain [61] and co-cultures of D. mccartyi strain 195 with either Desulfovibrio vulgaris Hildenborough or Syntrophomonas wolfei [21, 22]. cDCE was presumably converted to ethene by VcrA of BTF08. This is supported by the proteomic analysis described here, in which VcrA of D. mccartyi strain BTF08 was highly abundant and the predominant RDase in all cultures. A highly similar VcrA ortholog of D. mccartyi strain VS (99% amino acid sequence identity) has already been biochemically characterized and described to dechlorinate cDCE and VC [62]. Interestingly, neither TceA, nor PceA, which had been suggested to be responsible for dechlorination of PCE to VC [57], were detected in any of the samples. An identical ortholog of the only other detected RDase (encoded by btf_1393) was recently characterized as PteA, a novel PCE RDase dechlorinating PCE to TCE in D. mccartyi strain 11a5 [58]. D. mccartyi strain 195 was not subject to proteomic investigation in our study. However, previous studies suggested that TceA of this organism is involved in cDCE to VC dechlorination and that VC is further dechlorinated slowly by the same enzyme [61, 63].
Norpseudo-B12, produced by S. multivorans, is used differently by the two D. mccartyi strains
Without amendment of vitamin B12 the Sm/BTF08 co-culture was not capable of cDCE dechlorination to ethene, indicating that D. mccartyi strain BTF08 cannot use the norpseudo-B12 ([Ade]NCba) synthesized by S. multivorans for cDCE dechlorination. Complete dechlorination to ethene by D. mccartyi strain BTF08 was restored by the addition of the lower ligand DMB, indicating that the nonfunctional adenine ligand of [Ade]NCba could be replaced by DMB. This assumption is supported by a previous study, in which D. mccartyi was shown to incorporate different lower ligands into cobamides [17]. Therefore, it was not surprising that DMB-containing cobalamin were detected in the Sm/Dhc co-cultures. Most probably, after addition of DMB the detected [DMB]NCba was synthesized by S. multivorans besides [Ade]NCba, since the organism is able to incorporate different benzimidazoles and generate the corresponding cobamides [35, 64]. [DMB]Cba could then be produced during salvaging and remodeling of available [Ade]NCba and/or [DMB]NCba by D. mccartyi. It can, however, not be excluded from our data that [DMB]NCba can be used as well by D. mccartyi strain BTF08 for cDCE or VC dechlorination. The nucleotide loop cleavage is most likely mediated by the adenosylcobinamide hydrolase CbiZ, as shown for CbiZ of Rhodobacter sphaeroides [65, 66]. Of the two CbiZ encoded in the genome of D. mccartyi strain BTF08, one was detected in the proteome and showed a higher abundance in the co-culture compared to the pure culture. These results present evidence of the involvement of CbiZ in exchanging the complete nucleotide loop in D. mccartyi.
Different from the cDCE accumulation in Sm/BTF08 co-cultures grown without DMB, the Sm/195 co-culture dechlorinated PCE to VC in media without vitamin B12 or DMB. This indicates cDCE to VC conversion by strain 195 with [Ade]NCba produced by S. multivorans. However, previous studies showed [Ade]Cba (or other cobalamins with adenine as lower ligand) to be nonfunctional in D. mccartyi strain 195 with TCE as electron acceptor [17]. Trace amounts of DMB or cobalamin could be an explanation, but this explanation is unlikely given the same treatment but different dechlorination pattern of the co-cultures. Since RDase gene expression is often dependent on the electron acceptor present [14], cDCE in the Sm/195 co-culture might have induced a yet unknown RDase dechlorinating cDCE to VC with [Ade]NCba as cofactor. Alternatively, TceA containing [Ade]NCba could catalyze cDCE to VC dechlorination, but not TCE dechlorination to cDCE. The mechanism of cobalamin transfer from S. multivorans to D. mccartyi is not yet known. Most likely, cobalamin is released upon cell lysis or degradation of periplasmic PceA and possibly excreted through porins of S. multivorans, some of which were higher abundant in co-cultures.
Cell aggregates formed by D. mccartyi and S. multivorans could enhance interspecies hydrogen transfer
The cell aggregates observed in all studied co-cultures but not in pure cultures are common for obligate syntrophic interactions often found in e.g., acetogenic and methanogenic communities [67–69]. The decrease of intermicrobial distances and establishment of cell-to-cell contacts, which were observed in co-cultures via FE-SEM, should lead to increased metabolite (e.g., hydrogen) fluxes between species according to Fick’s law [70], ultimately enhancing growth and dechlorination rates. Experimentally, this was shown, for example, during syntrophic propionate conversion of Pelotomaculum thermopropionicum SI and Methanothermobacter thermoautotrophicus ΔH where interspecies hydrogen transfer was calculated to be optimal in aggregates [71]. EPS-like substances and flagella most likely contribute to a stabilization of aggregates by adhesion and attachment of the cells [67, 72]. In addition, cellular extrusions such as pili and flagella might contribute to direct interspecies electron transfer (DIET). While S. multivorans produces flagella in pure cultures [55], several structural flagellar proteins were downregulated in the co-culture, speaking against a use of flagellar for DIET in the co-culture of D. mccartyi and S. multivorans. Other proteins putatively involved in DIET are not encoded in the genomes of D. mccartyi or S. multivorans, arguing for an exclusive interspecies transfer of electrons via hydrogen. Aggregated D. mccartyi cells embedded in an ECM were observed in a bioreactor community dechlorinating trichloroethene to ethene [73]. However in this study, D. mccartyi formed typical disc-shaped cells, in contrast to the unusual, never before observed barrel-like morphology of D. mccartyi in the co-cultures investigated in our study. This barrel-like morphology might be caused by the downregulation of proteins involved in cell division in the co-culture. One of these proteins, FtsZ, localized at the cell division site, was shown to play a key role in cytokinesis in E. coli. It was shown to be responsible for septal invagination of the cell wall and cytoplasmic membrane by forming a ring-shaped septum followed by cell division [74–76]. Its downregulation might hamper a complete membrane constriction resulting in slower cell division that might cause the observed barrel-like cell morphologies. However, the reasons for this downregulation and the different morphology remain obscure. Possibly the less frequent cell divisions and/or the barrel-like morphology give D. mccartyi an advantage in cell-to-cell contact. In addition, this shape could represent a “sessile” state in which D. mccartyi adjusts its metabolism to the given condition in the aggregates, including a downregulation of cell division. Since electron micrographs of co-cultures with D. mccartyi are scarce, it is not possible to state whether the unusual cell morphology is specific for the partnership with S. multivorans or whether it is found frequently for co-cultures containing D. mccartyi. With S. wolfei as syntrophic partner, disc-like cell structures typical for D. mccartyi strain 195 were observed [21].
Conclusion
This study provides first insights into the interactions of S. multivorans in association with D. mccartyi and the formation of aggregates in which D. mccartyi showed an unusual barrel-like morphology. Dechlorinating microbial communities sometimes reveal the presence of Sulfurospirillum spp., but the functional role of these Campylobacterota (formerly Epsilonproteobacteria) is unexplored [77]. We observed that interspecies hydrogen and cobamide transfer in the co-culture resulted in fast and complete dechlorination of PCE to ethene. S. multivorans could provide all growth factors required by D. mccartyi, including hydrogen and cDCE as energy source, acetate as carbon source and cobamides as RDase cofactors (Fig. 6). It is the first study in which D. mccartyi was provided with all nutrients required for growth by its syntrophic partner. Additionally, PCE to cDCE dechlorination was sped up by the fast dechlorination rate of S. multivorans. This is of high interest for bioremediation attempts using Dehalococcoides-containing mixed cultures, since electron donor and cobalamin limitations may impede Dehalococcoides dechlorination activities.
Supplementary information
Acknowledgements
This work was supported by the Jena School for Microbial Communication (JSMC) and the DFG Research Unit FOR 1530 (sub-projects 1, 2, 5, and 6 were involved). The authors would like to thank Benjamin Scheer and Kathleen Eismann (Helmholtz Centre for Environmental Research, Leipzig) for skillfull technical assistance in the lab, Susanne Linde (University Hospital Jena, Center for Electron Microscopy) for the field emission-scanning electron microscopic analysis and Dr. Elena Romano (University of Rome Tor Vergata, Department of Biology) for invaluable assistance in the confocal laser scanning microscope image acquisition and processing. Dr. Torsten Schubert (Friedrich Schiller University Jena) is gratefully acknowledged for insightful discussions on corrinoid metabolism. Protein mass spectrometry was done at the Centre for Chemical Microscopy (ProVIS) at the Helmholtz Centre for Environmental Research. MvB and DT are grateful for support by the UFZ funded platform ProMetheus for proteome and metabolome analysis.
Compliance with ethical standards
Conflict of interest
The authors declare that they have no conflict of interest.
Footnotes
Publisher’s note Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.
Supplementary information
The online version of this article (10.1038/s41396-020-00887-6) contains supplementary material, which is available to authorized users.
References
- 1.Morris BE, Henneberger R, Huber H, Moissl-Eichinger C. Microbial syntrophy: Interaction for the common good. FEMS Microbiol Rev. 2013;37:384–406. doi: 10.1111/1574-6976.12019. [DOI] [PubMed] [Google Scholar]
- 2.Schink B, Stams A. Syntrophism Among Prokaryotes. In: Rosenberg E, DeLong E, Lory S, Stackebrandt E, Thompson F, editors. The prokaryotes: prokaryotic communities and ecophysiology. Berlin Heidelberg: Springer; 2013. pp. 471–93.
- 3.Stams AJ, Plugge CM. Electron transfer in syntrophic communities of anaerobic bacteria and archaea. Nat Rev Microbiol. 2009;7:568–77. doi: 10.1038/nrmicro2166. [DOI] [PubMed] [Google Scholar]
- 4.Cichocka D, Nikolausz M, Haest PJ, Nijenhuis I. Tetrachloroethene conversion to ethene by a Dehalococcoides-containing enrichment culture from Bitterfeld. FEMS Microbiol Ecol. 2010;72:297–310. doi: 10.1111/j.1574-6941.2010.00845.x. [DOI] [PubMed] [Google Scholar]
- 5.Duhamel M, Edwards EA. Microbial composition of chlorinated ethene-degrading cultures dominated by Dehalococcoides. FEMS Microbiol Ecol. 2006;58:538–49. doi: 10.1111/j.1574-6941.2006.00191.x. [DOI] [PubMed] [Google Scholar]
- 6.Jugder BE, Ertan H, Bohl S, Lee M, Marquis CP, Manefield M. Organohalide respiring bacteria and reductive dehalogenases: key tools in organohalide bioremediation. Front Microbiol. 2016;7:249. doi: 10.3389/fmicb.2016.00249. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 7.Wei K, Grostern A, Chan WWM, Richardson RE, Edwards EA. Electron acceptor interactions between organohalide-respiring bacteria: cross-feeding, competition, and inhibition. In: L Adrian, FE Löffler, editors. Organohalide-Respiring Bacteria. Berlin, Heidelberg: Springer Berlin Heidelberg; 2016. pp. 283–308.
- 8.Leys D, Adrian L, Smidt H. Organohalide respiration: microbes breathing chlorinated molecules. Philos Trans R Soc Lond B Biol Sci. 2013;368:20120316. doi: 10.1098/rstb.2012.0316. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 9.Schubert T, Adrian L, Sawers RG, Diekert G. Organohalide respiratory chains: composition, topology and key enzymes. FEMS Microbiol Ecol. 2018;94:fiy035. doi: 10.1093/femsec/fiy035. [DOI] [PubMed] [Google Scholar]
- 10.Schubert T, Diekert G. Comparative biochemistry of organohalide respiration. In: L Adrian, FE Löffler, editors. Organohalide-respiring bacteria. Berlin, Heidelberg: Springer Berlin Heidelberg; 2016. pp. 397–427.
- 11.Löffler FE, Yan J, Ritalahti KM, Adrian L, Edwards EA, Konstantinidis KT, et al. Dehalococcoides mccartyi gen. nov., sp. nov., obligately organohalide-respiring anaerobic bacteria relevant to halogen cycling and bioremediation, belong to a novel bacterial class, Dehalococcoidia classis nov., order Dehalococcoidales ord. nov. and family Dehalococcoidaceae fam. nov., within the phylum Chloroflexi. Int J Syst Evol Microbiol. 2013;63:625–35. doi: 10.1099/ijs.0.034926-0. [DOI] [PubMed] [Google Scholar]
- 12.Zinder S. The Genus Dehalococcoides. In: L Adrian, F Löffler. Organohalide-respiring Bacteria. Berlin Heidelberg: Springer; 2016.
- 13.Schipp CJ, Marco-Urrea E, Kublik A, Seifert J, Adrian L. Organic cofactors in the metabolism of Dehalococcoides mccartyi strains. Philos Trans R Soc Lond B Biol Sci. 2013;368:20120321. doi: 10.1098/rstb.2012.0321. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 14.Türkowsky D, Jehmlich N, Diekert G, Adrian L, von Bergen M, Goris T. An integrative overview of genomic, transcriptomic and proteomic analyses in organohalide respiration research. FEMS Microbiol Ecol. 2018;94:fiy013. [DOI] [PubMed]
- 15.He J, Holmes VF, Lee PK, Alvarez-Cohen L. Influence of vitamin B12 and cocultures on the growth of Dehalococcoides isolates in defined medium. Appl Environ Microbiol. 2007;73:2847–53. doi: 10.1128/AEM.02574-06. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 16.Men Y, Seth EC, Yi S, Allen RH, Taga ME, Alvarez-Cohen L. Sustainable growth of Dehalococcoides mccartyi 195 by corrinoid salvaging and remodeling in defined lactate-fermenting consortia. Appl Environ Microbiol. 2014;80:2133–41. doi: 10.1128/AEM.03477-13. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 17.Yi S, Seth EC, Men Y-J, Stabler SP, Allen RH, Alvarez-Cohen L, et al. Versatility in corrinoid salvaging and remodeling pathways supports corrinoid-dependent metabolism in Dehalococcoides mccartyi. Appl Environ Microbiol. 2012;78:7745–52. doi: 10.1128/AEM.02150-12. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 18.Cheng D, Chow WL, He J. A Dehalococcoides-containing co-culture that dechlorinates tetrachloroethene to trans-1,2-dichloroethene. ISME J. 2010;4:88–97. doi: 10.1038/ismej.2009.90. [DOI] [PubMed] [Google Scholar]
- 19.He J, Ritalahti KM, Aiello MR, Löffler FE. Complete detoxification of vinyl chloride by an anaerobic enrichment culture and identification of the reductively dechlorinating population as a Dehalococcoides species. Appl Environ Microbiol. 2003a;69:996–1003. [DOI] [PMC free article] [PubMed]
- 20.He J, Ritalahti KM, Yang KL, Koenigsberg SS, Löffler FE. Detoxification of vinyl chloride to ethene coupled to growth of an anaerobic bacterium. Nature. 2003b:424;62–5. [DOI] [PubMed]
- 21.Mao X, Stenuit B, Polasko A, Alvarez-Cohen L. Efficient metabolic exchange and electron transfer within a syntrophic trichloroethene-degrading coculture of Dehalococcoides mccartyi 195 and Syntrophomonas wolfei. Appl Environ Microbiol. 2015;81:2015–24. doi: 10.1128/AEM.03464-14. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 22.Men Y, Feil H, Verberkmoes NC, Shah MB, Johnson DR, Lee PK, et al. Sustainable syntrophic growth of Dehalococcoides ethenogenes strain 195 with Desulfovibrio vulgaris Hildenborough and Methanobacterium congolense: global transcriptomic and proteomic analyses. ISME j. 2012;6:410–21.. doi: 10.1038/ismej.2011.111. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 23.Murray A, Maillard J, Rolle M, Broholm M, Holliger C. Impact of iron- and/or sulfate-reduction on a cis-1,2-dichloroethene and vinyl chloride respiring bacterial consortium: experiments and model-based interpretation. Environ Sci Process Impacts. 2020;22:740–50. doi: 10.1039/c9em00544g. [DOI] [PubMed] [Google Scholar]
- 24.Wang S, Chen C, Zhao S, He J. Microbial synergistic interactions for reductive dechlorination of polychlorinated biphenyls. Sci Total Environ. 2019;666:368–76. doi: 10.1016/j.scitotenv.2019.02.283. [DOI] [PubMed] [Google Scholar]
- 25.Yan J, Im J, Yang Y, Löffler FE. Guided cobalamin biosynthesis supports Dehalococcoides mccartyi reductive dechlorination activity. Philos Trans R Soc Lond B Biol Sci. 2013;368:20120320. doi: 10.1098/rstb.2012.0320. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 26.Yan J, Ritalahti KM, Wagner DD, Löffler FE. Unexpected specificity of interspecies cobamide transfer from Geobacter spp. to organohalide-respiring Dehalococcoides mccartyi Strains. Appl Environ Microbiol. 2012;78:6630–6. doi: 10.1128/AEM.01535-12. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 27.Richardson R. Organohalide-respiring bacteria as members of microbial communities: catabolic food webs and biochemical interactions. In: L Adrian, F Löffler, editors. Organohalide-respiring Bacteria. Berlin Heidelberg: Springer; 2016.
- 28.Richardson RE, Bhupathiraju VK, Song DL, Goulet TA, Alvarez-Cohen L. Phylogenetic characterization of microbial communities that reductively dechlorinate TCE based upon a combination of molecular techniques. Environ Sci Technol. 2002;36:2652–62.. doi: 10.1021/es0157797. [DOI] [PubMed] [Google Scholar]
- 29.Duhamel M, Edwards EA. Growth and yields of dechlorinators, acetogens, and methanogens during reductive dechlorination of chlorinated ethenes and dihaloelimination of 1,2-dichloroethane. Environ Sci Technol. 2007;41:2303–10.. doi: 10.1021/es062010r. [DOI] [PubMed] [Google Scholar]
- 30.Guimaraes D, Weber A, Klaiber I, Vogler B, Renz P. Guanylcobamide and hypoxanthylcobamide: corrinoids formed by Desulfovibrio vulgaris. Arch Microbiol. 1994;162:272–6. [Google Scholar]
- 31.Lu Q, Zou X, Liu J, Liang Z, Shim H, Qiu R, et al. Inhibitory effects of metal ions on reductive dechlorination of polychlorinated biphenyls and perchloroethene in distinct organohalide-respiring bacteria. Environ Int. 2020;135:105373. doi: 10.1016/j.envint.2019.105373. [DOI] [PubMed] [Google Scholar]
- 32.Yan J, Şimşir B, Farmer AT, Bi M, Yang Y, Campagna SR, et al. The corrinoid cofactor of reductive dehalogenases affects dechlorination rates and extents in organohalide-respiring Dehalococcoides mccartyi. ISME J. 2016;10:1092–101. doi: 10.1038/ismej.2015.197. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 33.Kräutler B, Fieber W, Ostermann S, Fasching M, Ongania K-H, Gruber K, et al. The cofactor of tetrachloroethene reductive dehalogenase of Dehalospirillum multivorans is norpseudo-B12, a new type of a natural corrinoid. Helvetica Chim Acta. 2003;86:3698–716. [Google Scholar]
- 34.Neumann A, Wohlfarth G, Diekert G. Purification and characterization of tetrachloroethene reductive dehalogenase from Dehalospirillum multivorans. J Biol Chem. 1996;271:16515–9. doi: 10.1074/jbc.271.28.16515. [DOI] [PubMed] [Google Scholar]
- 35.Schubert T. The organohalide-respiring bacterium Sulfurospirillum multivorans: a natural source for unusual cobamides. World J Microbiol Biotechnol. 2017;33:93. doi: 10.1007/s11274-017-2258-x. [DOI] [PubMed] [Google Scholar]
- 36.Kruse S, Goris T, Westermann M, Adrian L, Diekert G. Hydrogen production by Sulfurospirillum spp. enables syntrophic interactions of Epsilonproteobacteria. Nat Comm. 2018;9:4872. doi: 10.1038/s41467-018-07342-3. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 37.Goris T, Schenz B, Zimmermann J, Lemos M, Hackermüller J, Schubert T, et al. The complete genome of the tetrachloroethene-respiring Epsilonproteobacterium Sulfurospirillum halorespirans. J Biotechnol. 2017;255:33–36. doi: 10.1016/j.jbiotec.2017.06.1197. [DOI] [PubMed] [Google Scholar]
- 38.Maymó-Gatell X, Anguish T, Zinder SH. Reductive dechlorination of chlorinated ethenes and 1, 2-dichloroethane by “Dehalococcoides ethenogenes” 195. Appl Environ Microbiol. 1999;65:3108–13. doi: 10.1128/aem.65.7.3108-3113.1999. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 39.Keller S, Ruetz M, Kunze C, Kräutler B, Diekert G, Schubert T. Exogenous 5,6-dimethylbenzimidazole caused production of a non-functional tetrachloroethene reductive dehalogenase in Sulfurospirillum multivorans. Environ Microbiol. 2014;16:3361–9. doi: 10.1111/1462-2920.12268. [DOI] [PubMed] [Google Scholar]
- 40.Kruse S, Goris T, Wolf M, Wei X, Diekert G. The NiFe Hydrogenases of the Tetrachloroethene-Respiring Epsilonproteobacterium Sulfurospirillum multivorans: Biochemical Studies and Transcription Analysis. Front Microbiol. 2017;8:444. doi: 10.3389/fmicb.2017.00444. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 41.Schubert T, von Reuß SH, Kunze C, Paetz C, Kruse S, Brand-Schön P, et al. Guided cobamide biosynthesis for heterologous production of reductive dehalogenases. Microbiol Biotechnol. 2018;12:346–59. doi: 10.1111/1751-7915.13339. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 42.Marco-Urrea E, Nijenhuis I, Adrian L. Transformation and carbon isotope fractionation of tetra- and trichloroethene to trans-dichloroethene by Dehalococcoides sp strain CBDB1. Environ Sci Technol. 2011;45:1555–62. doi: 10.1021/es1023459. [DOI] [PubMed] [Google Scholar]
- 43.Schmidt M, Lege S, Nijenhuis I. Comparison of 1,2-dichloroethane, dichloroethene and vinyl chloride carbon stable isotope fractionation during dechlorination by two Dehalococcoides strains. Water Res. 2014;52:146–54. doi: 10.1016/j.watres.2013.12.042. [DOI] [PubMed] [Google Scholar]
- 44.Coplen TB, Brand WA, Gehre M, Gröning M, Meijer HA, Toman B, et al. After two decades a second anchor for the VPDB delta13C scale. Rapid Commun Mass Spectrom. 2006;20:3165–6. doi: 10.1002/rcm.2727. [DOI] [PubMed] [Google Scholar]
- 45.Elsner M. Stable isotope fractionation to investigate natural transformation mechanisms of organic contaminants: principles, prospects and limitations. J Environ Monit. 2010;12:2005–31. doi: 10.1039/c0em00277a. [DOI] [PubMed] [Google Scholar]
- 46.Elsner M, Chartrand M, Vanstone N, Couloume GL, Lollar BS. Identifying abiotic chlorinated ethene degradation: characteristic isotope patterns in reaction products with nanoscale zero-valent iron. Environ Sci Technol. 2008;42:5963–70. doi: 10.1021/es8001986. [DOI] [PubMed] [Google Scholar]
- 47.Rossetti S, Aulenta F, Majone M, Crocetti G, Tandoi V. Structure analysis and performance of a microbial community from a contaminated aquifer involved in the complete reductive dechlorination of 1,1,2,2-tetrachloroethane to ethene. Biotechnol Bioeng. 2008;100:240–9. doi: 10.1002/bit.21776. [DOI] [PubMed] [Google Scholar]
- 48.Fazi S, Aulenta F, Majone M, Rossetti S. Improved quantification of Dehalococcoides species by fluorescence in situ hybridization and catalyzed reporter deposition. Syst Appl Microbiol. 2008;31:62–7. doi: 10.1016/j.syapm.2007.11.001. [DOI] [PubMed] [Google Scholar]
- 49.Matturro B, Tandoi V, Rossetti S. Different activity levels of Dehalococcoides mccartyi revealed by FISH and CARD-FISH under non-steady and pseudo-steady state conditions. N. Biotechnol. 2013;30:756–62.. doi: 10.1016/j.nbt.2013.07.003. [DOI] [PubMed] [Google Scholar]
- 50.Jehmlich N, Schmidt F, von Bergen M, Richnow H-H, Vogt C. Protein-based stable isotope probing (Protein-SIP) reveals active species within anoxic mixed cultures. Isme J. 2008;2:1122. doi: 10.1038/ismej.2008.64. [DOI] [PubMed] [Google Scholar]
- 51.Türkowsky (b) D, Esken J, Goris T, Schubert T, Diekert G, Jehmlich N, et al. A retentive memory of tetrachloroethene respiration in Sulfurospirillum halorespirans—involved proteins and a possible link to acetylation of a two-component regulatory system. J Proteom. 2018;181:36–46. doi: 10.1016/j.jprot.2018.03.030. [DOI] [PubMed] [Google Scholar]
- 52.Kanehisa M, Sato Y, Morishima K. BlastKOALA and GhostKOALA: KEGG tools for functional characterization of genome and metagenome sequences. J Mol Biol. 2016;428:726–31. doi: 10.1016/j.jmb.2015.11.006. [DOI] [PubMed] [Google Scholar]
- 53.Marc D, Pierre L. Species assemblages and indicator species: the need for a flexible asymmetrical approach. Ecol Monogr. 1997;67:345–66. [Google Scholar]
- 54.Malik A, Puissant J, Buckeridge K, Goodall T, Jehmlich N, Chowdhury S, et al. Land use driven change in soil pH affects microbial carbon cycling processes. Nat Comm. 2017;9:3591. doi: 10.1038/s41467-018-05980-1. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 55.Scholz-Muramatsu H, Neumann A, Meßmer M, Moore E, Diekert G. Isolation and characterization of Dehalospirillum multivorans gen. nov., sp. nov., a tetrachloroethene-utilizing, strictly anaerobic bacterium. Arch Microbiol. 1995;163:48–56. [Google Scholar]
- 56.Franke S, Seidel K, Adrian L, Nijenhuis I. Dual element (C/Cl) isotope analysis indicates distinct mechanisms of reductive dehalogenation of chlorinated ethenes and dichloroethane in Dehalococcoides mccartyi strain BTF08 with defined reductive dehalogenase inventories. Front Microbiol. 2020;11:1507. doi: 10.3389/fmicb.2020.01507. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 57.Pöritz M, Goris T, Wubet T, Tarkka MT, Buscot F, Nijenhuis I, et al. Genome sequences of two dehalogenation specialists—Dehalococcoides mccartyi strains BTF08 and DCMB5 enriched from the highly polluted Bitterfeld region. FEMS Microbiol Lett. 2013;343:101–4. doi: 10.1111/1574-6968.12160. [DOI] [PubMed] [Google Scholar]
- 58.Zhao S, Ding C, He J. Genomic characterization of Dehalococcoides mccartyi strain 11a5 reveals a circular extrachromosomal genetic element and a new tetrachloroethene reductive dehalogenase gene. FEMS Microbiol Ecol. 2017;93:fiw235. doi: 10.1093/femsec/fiw235. [DOI] [PubMed] [Google Scholar]
- 59.Goris T, Schiffmann CL, Gadkari J, Schubert T, Seifert J, Jehmlich N, et al. Proteomics of the organohalide-respiring Epsilonproteobacterium Sulfurospirillum multivorans adapted to tetrachloroethene and other energy substrates. Sci Rep. 2015;5:13794. doi: 10.1038/srep13794. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 60.Gadkari J, Goris T, Schiffmann CL, Rubick R, Adrian L, Schubert T, et al. Reductive tetrachloroethene dehalogenation in the presence of oxygen by Sulfurospirillum multivorans: physiological studies and proteome analysis. FEMS Microbiol Ecol. 2018;94:fix176. doi: 10.1093/femsec/fix176. [DOI] [PubMed] [Google Scholar]
- 61.Maymó-Gatell X, Nijenhuis I, Zinder SH. Reductive dechlorination of cis-1,2-dichloroethene and vinyl chloride by “Dehalococcoides ethenogenes”. Environ Sci Technol. 2001;35:516–21. doi: 10.1021/es001285i. [DOI] [PubMed] [Google Scholar]
- 62.Parthasarathy A, Stich TA, Lohner ST, Lesnefsky A, Britt RD, Spormann AM. Biochemical and EPR-spectroscopic investigation into heterologously expressed vinyl chloride reductive dehalogenase (VcrA) from Dehalococcoides mccartyi strain VS. J Am Chem Soc. 2015;137:3525–32. doi: 10.1021/ja511653d. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 63.Magnuson JK, Romine MF, Burris DR, Kingsley MT. Trichloroethene reductive dehalogenase from Dehalococcoides ethenogenes: sequence of tceA and substrate range characterization. Appl Environ Microbiol. 2000;66:5141–7. doi: 10.1128/aem.66.12.5141-5147.2000. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 64.Keller S, Kunze C, Bommer M, Paetz C, Menezes RC, Svatoš A, et al. Selective utilization of benzimidazolyl-norcobamides as cofactors by the tetrachloroethene reductive dehalogenase of Sulfurospirillum multivorans. J Bacteriol. 2018. [DOI] [PMC free article] [PubMed]
- 65.Gray MJ, Escalante-Semerena JC. The cobinamide amidohydrolase (cobyric acid-forming) CbiZ enzyme: a critical activity of the cobamide remodeling system of Rhodobacter sphaeroides. Mol Microbiol. 2009a;74:1198–210. [DOI] [PMC free article] [PubMed]
- 66.Gray MJ, Escalante-Semerena JC. In vivo analysis of cobinamide salvaging in Rhodobacter sphaeroides strain 2.4.1. J Bacteriol. 2009b;191:3842–51. [DOI] [PMC free article] [PubMed]
- 67.Hulshoff Pol LW, de Castro Lopes SI, Lettinga G, Lens PNL. Anaerobic sludge granulation. Water Res. 2004;38:1376–89. doi: 10.1016/j.watres.2003.12.002. [DOI] [PubMed] [Google Scholar]
- 68.Ishii S, Kosaka T, Hori K, Hotta Y, Watanabe K. Coaggregation facilitates interspecies hydrogen transfer between Pelotomaculum thermopropionicum and Methanothermobacter thermautotrophicus. Appl Environ Microbiol. 2005;71:7838–45.. doi: 10.1128/AEM.71.12.7838-7845.2005. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 69.Stams AJM, Worm P, Sousa DZ, Alves MM, Plugge CM. Syntrophic degradation of fatty acids by methanogenic communities. In: PC Hallenbeck, editor. Microbial technologies in advanced biofuels production. Boston, MA: Springer US.; 2012. pp. 127–42.
- 70.Schink B, Thauer RK. Energetics of syntrophic methane formation and the influence of aggregation. In: L G Z AJB, G JTC, H LW, editors. Granular anaerobic sludge: microbiology and technology. Wageningen: Puduc; 1988. pp. 5–17.
- 71.Ishii SI, Kosaka T, Hotta Y, Watanabe K. Simulating the contribution of coaggregation to interspecies hydrogen fluxes in syntrophic methanogenic consortia. Appl Environ Microbiol. 2006;72:5093–6. doi: 10.1128/AEM.00333-06. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 72.Grotenhuis JTC, Smit M, van Lammeren AAM, Stams AJM, Zehnder AJB. Localization and quantification of extracellular polymers in methanogenic granular sludge. Appl Microbiol Biotechnol. 1991;36:115–9. [Google Scholar]
- 73.Delgado AG, Fajardo-Williams D, Bondank E, Esquivel-Elizondo S, Krajmalnik-Brown R. Coupling bioflocculation of Dehalococcoides mccartyi to high-rate reductive dehalogenation of chlorinated ethenes. Environ Sci Technol. 2017;51:11297–307. doi: 10.1021/acs.est.7b03097. [DOI] [PubMed] [Google Scholar]
- 74.Bi E, Lutkenhaus J. FtsZ ring structure associated with division in Escherichia coli. Nature. 1991;354:161. doi: 10.1038/354161a0. [DOI] [PubMed] [Google Scholar]
- 75.de Boer P, Crossley R, Rothfield L. The essential bacterial cell-division protein FtsZ is a GTPase. Nature. 1992;359:254. doi: 10.1038/359254a0. [DOI] [PubMed] [Google Scholar]
- 76.Lutkenhaus J. FtsZ ring in bacterial cytokinesis. Mol Microbiol. 1993;9:403–9. doi: 10.1111/j.1365-2958.1993.tb01701.x. [DOI] [PubMed] [Google Scholar]
- 77.Goris T, Diekert G. The genus Sulfurospirillum. In: L Adrian, FE Löffler, editors. Organohalide-respiring bacteria. Berlin, Heidelberg: Springer-Verlag; 2016. pp. 209–34.
Associated Data
This section collects any data citations, data availability statements, or supplementary materials included in this article.