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Applied and Environmental Microbiology, October 2005, p. 6077-6085, Vol. 71, No. 10
0099-2240/05/$08.00+0 doi:10.1128/AEM.71.10.6077-6085.2005
Copyright © 2005, American Society for Microbiology. All Rights Reserved.
German Institute of Human Nutrition Potsdam-Rehbruecke, Department of Gastrointestinal Microbiology, Nuthetal, Germany,1 Unité d'Ecologie et de Physiologie du Système Digestif, INRA, Jouy-en-Josas, France2
Received 7 March 2005/ Accepted 2 June 2005
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Dietary lignans, particularly SECO, are of interest because they have been proposed to play a role in the prevention of breast and colon cancer (52), atherosclerosis (42), and diabetes (39, 41). However, plant lignans per se are devoid of any biological properties. Only the enterolignans enterodiol (ED) and enterolactone (EL), produced from SECO by intestinal bacteria, have interesting biological properties such as estrogen agonism and antagonism (36, 48, 54) as well as antioxidative and enzyme-inhibiting activities (40, 55). Transformation reactions catalyzed by intestinal bacteria include the demethylation, dehydroxylation, and dehydrogenation of SECO (4, 5, 56) (Fig. 1).
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FIG. 1. Structure of SECO and the enterolignans.
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Therefore, the purpose of the present study was to better understand the microbial ecology of SECO activation in the human intestinal tract, i.e., to describe the consortium of organisms that produce the enterolignans ED and EL. We enumerated ED- and EL-producing fecal communities by the most probable number (MPN) method and looked for possible correlations with enterolignan production and dominant bacterial groups. In addition, we focused on the isolation of pure bacterial strains able to activate SECO.
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Human volunteers.
Twenty-four healthy German and French adults (23 to 59 years old) gave their informed consent to take part in the MPN study. They did not take antibiotics for 3 months prior to the study. Seven additional individuals were tested to determine the prevalence of SECO activation, i.e., the proportion of individuals capable of producing enterolignans.
Collection and processing of fecal samples.
Fecal samples were collected in plastic boxes, kept under anoxic conditions using an AnaeroGen Compact (Oxoid, Hampshire, England), and stored at 4°C for a maximum of 4 h before processing. For MPN enumeration, dilutions ranging from 101 to 1010 were prepared at room temperature in an anaerobic tent (Coy Laboratory Products), using sterile phosphate-buffer saline (PBS-a; 8.5 g liter1 NaCl, 0.3 g liter1 KH2PO4, 0.6 g liter1 Na2HPO4, pH 7.0) containing 0.1 g liter1 peptone and 0.25 g liter1 cysteine-HCl (PC/PBS-a). Briefly, 1 g of fresh fecal aliquots was added to 9 ml PC/PBS-a, mixed well with sterile plastic loops, and vortexed to obtain homogenized 101 fecal dilutions. Samples were left to stand for 5 min, and volumes of 1 ml were transferred to 9 ml PC/PBS-a (102 fecal dilutions). Successive transfers were performed using sterile tips to obtain the desired range of dilutions. Before each transfer, samples were mixed by repeated inversions of the tubes. For each sample, two 1-g aliquots of fresh feces were lyophilized to estimate the fecal water content. For fluorescent in situ hybridization (FISH), 1-g fecal aliquots were fixed with paraformaldehyde (PFA). Briefly, the aliquots were suspended in 9 ml of PBS-b (7.54 g liter1 NaCl, 2.5 g liter1 Na2HPO4, 0.47 g liter1 NaH2PO4, pH 7.2), and the suspensions were homogenized for 5 min with a magnetic stirrer. Volumes of 0.2 ml were added to 0.6 ml of a 4% PFA solution (Electron Microscopy Sciences) in PBS-b and fixed overnight at 4°C. Aliquots were stored at 80°C until analysis.
Culture conditions for incubation of SECO with fecal dilutions.
The liquid medium Mt-6 contained the following reagents per liter: 3 g yeast extract, 3 g peptone from casein, 2.5 g sodium acetate trihydrate, 2.5 g sodium formate, 0.5 g cysteine-HCl monohydrate, 100 ml salt 1 solution, 50 ml rumen fluid, 2 ml salt 2 solution, 1 ml vitamin solution (13), 1 ml resazurin solution (1 mg ml1), and 0.1 ml trace element solution. Salt 1 solution was 48 mM NaHCO3, 17 mM NaCl, 12 mM NH4Cl, 2.2 mM KH2PO4, 1.7 mM K2HPO4, and 1.2 mM MgSO4 in H2O. Salt 2 solution was 540 µM MnSO4, 475 µM CaCl2, 360 µM FeSO4, 260 µM ZnCl2, 225 µM (NH4)2SO4, and 160 µM CoCl2 in H2O. Trace element solution was 12.5 µM CuSO4, 8 µM NiCl2, and 8 µM MoNa2O4 in H2O. For collection of the rumen fluid, an oral stomach tube (19) was connected to a suction pump, and the rumen fluid was collected from a healthy cow in a sterile culture bottle. Aliquots were centrifuged (100,000 x g for 30 min) at room temperature, sterilely filtered (0.22 µm), and kept at 4°C. SECO dissolved in methanol was added to a final concentration of 1 mM. The final concentration of methanol was <2% (vol/vol). The pH was adjusted to 7.5, and the medium was gassed with 80% N2 plus 20% CO2 (vol/vol) and autoclaved at 121°C for 15 min. After autoclaving, glucose and fructose were added from N2/CO2-gassed sterile stock solutions to a final concentration of 10 mM each.
MPN experiments.
The sterile SECO-containing broth Mt-6 was dispensed into the 1.2 ml-deep wells of a 96-well plate (250 µl per well) in an anaerobic tent. Fecal dilutions (100 µl) were each inoculated in triplicate into wells. Controls consisted of fecal bacteria in medium without SECO and Mt-6 without bacteria. The controls were done in triplicate. Plates were incubated at 37°C under N2/CO2 in an anaerobic jar pressurized at 1.5 x 105 Pa and placed on a rotary shaker (150 rpm). After 48 h of growth, plates were centrifuged at 4,000 x g for 15 min, and the supernatants were analyzed by liquid chromatography.
High-performance liquid chromatography (HPLC).
Separation was carried out with an RP-18 column (Lichrocart Lichrospher 100; 250 mm by 4 mm by 5 µm; Merck, Darmstadt, Germany) protected with a guard RP-18 column (4 mm by 4 mm by 5 µm) and maintained at 37°C. The eluents were as follows: A, 85% H2O plus 15% methanol (vol/vol), adjusted to pH 3 with 98% formic acid; and B, methanol. The gradient was 20 to 100% B within 8 min, 100% B for 1 min, and back to 20% B for 5 min. The dwell volume of the system was 4.4 ml, the flow rate was 1 ml min1, and the injection volume was 20 µl. Lignans were detected at 275 nm using a UV diode array detector. Chromeleon software, version 6.40 (Dionex, Idstein, Germany), and the Millenium32 Chromatography Manager (Waters, Milford, Massachusetts) were used for data acquisition and analysis of German and French samples, respectively. To quantify SECO, ED, and EL, calibration curves were obtained with standards using the following concentrations: 1,500 µM, 1,000 µM, 500 µM, 250 µM, 100 µM, 50 µM, and 10 µM. The solvent was methanol, and each concentration was prepared in duplicate.
Procedure for MPN enumeration.
A well was considered positive if the corresponding dilution of the given fecal sample produced enterolignans. This was the case if (i) we observed a significant decrease in the concentration of SECO, (ii) we detected peaks at the retention times of the enterolignans (8.3 and 8.7 min for ED and EL, respectively), (iii) these peaks corresponded to concentrations of ED or EL above 10 µM, and (iv) they displayed the specific spectra obtained with standards. MPN results were calculated using a table based on three replicates (11). They were adjusted according to fecal water contents and dilution factors and expressed either as CFU per gram of dried feces (CFU g1) or as logarithmic values thereof.
EL and ED production levels.
From the MPN data for the German samples (n = 13), chromatograms obtained with the 101 fecal dilutions were used to estimate the production of EL and ED. The parameter
was defined as the ratio between the final concentration of EL and the initial concentration of SECO. The parameter
was defined as the ratio between the final concentration of both enterolignans (ED plus EL) and the initial concentration of SECO. Since each sample was analyzed in triplicate,
and
were expressed as mean values.
Aerobic incubations.
Six German samples (MPN 2, 6, 13, 14, 15, and 17) were tested for aerobic conversion of SECO. A volume of 900 µl of Mt-6 was inoculated with 100 µl of the 101 fecal dilutions. Samples were incubated at 37°C in Eppendorf tubes equipped with membrane lids (Eppendorf LidBAC; Eppendorf, Hamburg, Germany) and placed on a rotary shaker (150 rpm). Supernatants were analyzed by HPLC before incubation and after 48 h. Controls consisted of Mt-6 without fecal bacteria, fecal bacteria in medium without SECO, and fecal bacteria in Mt-6 incubated under anoxic conditions.
Isolation of SECO-activating bacteria.
All steps were carried out using strictly anaerobic techniques (7, 9). Serial dilutions of a fecal sample from a healthy male adult (MPN 14) were prepared as described above and plated onto Mt-6 supplemented with 14 g liter1 agar (Serva, Heidelberg, Germany). After 48 h of growth at 37°C, a mixed culture of bacteria obtained from the initial 105 fecal dilution produced ED. After several transfers in Mt-6, serial dilutions of the mixed culture were plated onto the selective medium Mt-75, which contained the following reagents (per liter): 10 g agar, 2 g NaHCO3, 1.25 g sodium acetate trihydrate, 1.25 g sodium formate, 0.5 g cysteine-HCl monohydrate, 0.1 g yeast extract, 100 ml of 10-fold concentrated basal solution (13), 20 ml trace element solution (13), 2.5 ml rumen fluid, 1 ml vitamin solution (13), and 1 ml resazurin solution (1 mg ml1). SECO was added as described previously. The pH was adjusted to 7.2, and the medium was autoclaved at 121°C for 15 min. The medium was allowed to cool down to 45°C, and sterilely filtered bromoethanesulfonate solved in H2O was added to a final concentration of 4 mM to prevent the growth of methanogens. Once poured into petri dishes and allowed to dry under sterile conditions, the medium was transferred into an anaerobic tent and allowed to equilibrate for 48 h before inoculation. After 95 h of growth at 37°C under 80% H2 plus 20% CO2 (vol/vol) in an anaerobic jar pressurized at 1.5 x 105 Pa, pure cultures were obtained from the 104 dilution of the mixed culture and screened for conversion of SECO. To ensure purity, active organisms were streaked two times on peptone-yeast-glucose (PYG) agar (medium 104; DSMZ, Braunschweig, Germany) before further analyses. The purity was controlled by comparisons of colony morphology and Gram stains. These were confirmed by means of the KOH test (20). The cultures were grown under aerobic conditions on PYG agar to look for aerobic contaminants.
Molecular identification of active isolates.
DNAs were extracted with an Invisorb Genomic DNA kit III (Invitek, Berlin-Buch, Germany) following the manufacturer's instructions. Primers 27f (5' AGA GTT TGA TCC TGG CTC AG) and 1492r (5' TAC CTT GTT ACG ACT T) (27) were used to amplify the bacterial 16S rRNA gene. PCR mixes (50 µl) contained 50 mM KCl, 20 mM Tris-HCl, 1 mM MgCl2, a 0.25 mM concentration of each deoxynucleoside triphosphate, a 1 µM concentration of each primer, 2.5 units Taq DNA polymerase (Invitrogen, Karlsruhe, Germany), and 1 µl of a 101 dilution of template DNA. The PCR program was as follows: 94°C for 5 min, 30 cycles of 94°C for 1 min, 55°C for 1 min, and 72°C for 1 min, and finally 72°C for 10 min. PCR products were purified with a High Pure PCR product purification kit (Roche, Indianapolis, Ind.) following the manufacturer's instructions. The products were analyzed by electrophoresis on a 1.5% agarose gel (wt/vol) in Tris-borate-EDTA buffer (Roth, Karlsruhe, Germany). The DNA concentration was estimated using a Low DNA mass ladder (Invitrogen, Carlsbad, Calif.). For sequencing, we used either primer 27f, 338f (5' GCT GCC TCC CGT AGG AGT) (3), 338r (5' ACT CCT ACG GGA GGC AGC), or 1492r. Sequencing reactions were performed in duplicate with a DYEnamic ET Dye Terminator cycle sequencing kit (Amersham Biosciences, Buckinghamshire, England) following the manufacturer's instructions. Sequencing products were analyzed with the MegaBACE 1000 system (Molecular Dynamics, Sunnyvale, Calif.). Sequences were assembled and manually adjusted using the ContigExpress function of the Vector NTI suite 9.0.0 (Invitrogen, Carlsbad, Calif.). They were subsequently aligned with highly similar sequences (92% similarity or more) obtained with the BLAST function of the National Center for Biotechnology Information (NCBI) server (2). Percentages of similarity were calculated from unambiguously aligned sequences using the sequence identity matrix function of Bioedit software, version 5.0.9 (22).
Growth and fixation of pure cultures.
Bacteria were streaked three times on PYG agar, and purity was controlled as described for the isolates. Pure cultures were grown in 9 ml PYG broth and harvested in the exponential growth phase to maximize the rRNA content. Cells were centrifuged at 8,000 x g for 3 min and resuspended in 1 ml PBS-b. A volume of 0.2 ml was added to 0.6 ml of 4% PFA solution and fixed for 3 h at 4°C. Aliquots were stored at 80°C until analysis.
Design and optimization of species-specific 16S rRNA oligonucleotide probe.
Sequences of organisms closely related to Peptostreptococcus productus were obtained from the GenBank database. They were aligned using Bioedit software and screened for P. productus-specific regions. Probes targeting these regions were controlled using the probe match and BLAST functions of the Ribosomal Database Project (10) and the NCBI, respectively. They were further tested by FISH on reference strains to establish their in vitro specificity. Relative probe fluorescence was determined as described previously (44).
FISH and flow cytometry (FC) analyses.
The specific probes used in this study are listed in Table 1. The EUB-338-5' probe (GCT GCC TCC CGT AGG AGT), conserved within the bacterial domain (3), and the NON-EUB-5' probe (ACA TCC TAC GGG AGG C) were used as positive and negative controls, respectively. The labeling quality of probes was controlled as described previously (18). Fixed bacterial suspensions were hybridized as described previously (43). For fecal samples, 200 µl of the PFA-fixed suspension was added to 800 µl of PBS-b. For pure cultures, 200 to 800 µl of PFA-fixed suspension was used, depending on the bacterial concentration before fixation. Data acquisition was performed as described previously (43). Cell granularity was measured with the side scatter channel and assigned as the primary acquisition parameter. The voltage setting of the corresponding photomultiplier tube was 458 V, with a threshold of 253 V. The multiplying factor of the photodiode used for the detection of forward scatter signals was 102. Voltage settings for FL1 and FL4 fluorescence were 649 and 800 V, respectively. All amplifiers were set to logarithmic mode.
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TABLE 1. 16S rRNA probes used in FISH experiments for enumeration of fecal bacteria
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Statistical analyses.
Data are expressed as means ± standard deviations (SD). SD were determined as follows: SD = [
(xi mean)2/n]1/2, where xi is the given value of sample i and n is the total number of samples. For the MPN data, analyses were performed on logarithmic values. The Shapiro-Wilk test was used to ensure normal distributions. Variances were checked for their uniformity by means of F tests. Unless specified, P values were obtained by two-tailed homoscedastic Student tests. Chi-square analyses were performed to compare the bacterial composition results with data from previous studies. Pearson's correlation coefficients were calculated using version 11.5 of SPSS software (SPSS Inc., Chicago, Ill.).
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TABLE 2. MPN values, enterolignan production, bacterial compositions, and personal parameters for the whole cohort of individuals (n = 24)b
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Data on enterolignan production are listed in Table 2. For the German cohort of the MPN study (n = 13), EL and enterolignan production accounted for 11.9% ± 9.1% and 59.9% ± 17.7% of the initial concentration of SECO, respectively. At 48.0% ± 19.8%, ED was produced in larger amounts than EL. There was a significant correlation between the occurrence of EL-producing communities and EL production, as follows: r (ELmpn,
) = 0.749 (P = 0.003). Significantly larger amounts of enterolactone were produced by fecal samples from individuals with moderate to high concentrations of EL-producing bacteria (n = 7, six women and one man) than by samples from individuals with low concentrations of EL-producing bacteria (n = 6, two women and four men) (Table 3).
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TABLE 3. MPN counts and EL production (n = 13)
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Identification of SECO-activating bacteria.
After the isolation of fecal bacteria on SECO-containing medium, we obtained a gram-positive coccobacillus which demethylated SECO under anoxic conditions (Fig. 2A). The unambiguously aligned 16S rRNA gene sequence of this organism (1,343 nucleic acids) (GenBank accession number AY937379) displayed 97.4% similarity with that of P. productus ATCC 27340T (L76595). Anoxic coincubations of the P. productus isolate with a likewise isolated pure culture of a gram-positive rod led to the production of ED from SECO (Fig. 2B). The unambiguously aligned 16S rRNA gene sequence of the latter organism (1,394 nucleic acids) (AY937380) displayed 98.2% similarity with Eggerthella lenta ATCC 25559T (AF292375) (12). The identity of this second isolate was confirmed by PCR amplification of an E. lenta-specific region using primers LEN-F2 and LEN-R2 (27) (data not shown). The E. lenta isolates alone were not able to convert SECO (data not shown).
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FIG. 2. (A) Demethylation of SECO by the isolated strain P. productus SECO-Mt75m3. Incubation took place at 37°C in Mt-6 broth. Samples were collected at the times indicated on the chromatograms. Supernatants were analyzed by HPLC as described previously. The demethylation of SECO led to the formation of compound B (5.8 min) via compound A (6.7 min). The molecular weight of A was 348 g mol1, as determined by mass spectrometry. This weight corresponds to the molecular weight of SECO with one methyl group removed. Compound B was identified as 2,3-bis(3,4-dihydroxybenzyl)butene-1,4-diol by comparison with the retention time and spectrum of the standard. It lacks the two methyl groups of SECO. (B) Formation of ED from SECO by coculture of the isolated strains P. productus SECO-Mt75m3 and E. lenta SECO-Mt75m2. Incubation took place at 37°C in Mt-75 broth. The molecular weight of C (7.9 min) was 332 g mol1, as determined by mass spectrometry. This weight corresponds to the molecular weight of SECO with one methyl group and one hydroxyl group removed.
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TABLE 4. Sequences of the designed 16S rRNA specific probe and of targeted and nontargeted organisms
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TABLE 5. Specificity of probe ProCo-1264
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FIG. 3. FISH-FC dot plots for MPN samples 8 and 18 hybridized with ProCo-1264. Fluorescence intensities are displayed as logarithmic values. Regions: 1, autofluorescence events; 2 and 3, gated regions that include total bacterial events; 4, ProCo-1264-specific events; 5, specific control region. Bacterial percentages for P. productus and C. coccoides were calculated as follows: 100 x [(counts in region 4/counts in region 2) (counts in region 5/counts in region 3)].
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We showed that the activation of SECO is widespread among humans. Indeed, the prevalence of enterolignan production was 100%. Thus, beneficial health effects associated with SECO activation would be relevant to the entire population and not restricted to a certain proportion of individuals as in the case of equol (45).
The human intestinal tract harbors approximately 1012 CFU per gram of content. At >108 CFU per gram of dried feces, microbes responsible for ED production occurred at relatively high population levels. Thus, organisms that demethylate and dehydroxylate SECO seem to be members of the dominant anaerobic intestinal microbiota. Conversely, organisms responsible for SECO and/or ED dehydrogenation make up a subdominant anaerobic population (approximately 105 CFU g1). An early study of the in vitro metabolism of SECO by human fecal bacteria described the conversion of SECO to ED and EL under aerobic conditions (5). However, the authors also reported that feces from an individual treated with metronidazole could no longer convert SECO to ED, indicating the need for anaerobes for SECO activation. We could not detect enterolignan formation after aerobic incubation of SECO with fecal dilutions from six individuals. Another previous study reported results similar to ours (56). Although we cannot exclude that aerobic or facultative anaerobic microorganisms may be able to demethylate and dehydroxylate SECO, the data presented here challenge the presumption of an aerobic activation of SECO.
Our data show an association between the occurrence and activity of EL-producing communities, i.e., EL is produced in larger amounts by individuals with higher concentrations of EL-producing organisms. Our in vitro experiments also showed that ED was produced from SECO in larger amounts than EL. This is in agreement with previous in vivo data on human plasma and urine concentrations of lignans after flaxseed ingestion (37) and rat urine concentrations of lignans after SECO supplementation (47). In these studies, ED was the main metabolite produced from the ingested precursors. We found no association between MPNs and the activity of ED-producing communities. Since the concentrations of ED-producing communities were fairly homogeneous within the MPN cohort, i.e., individuals with low or high concentrations of active organisms were not as distinguishable as in the case of EL, MPN enumerations based on three replicates may not warrant the accuracy required to reveal differences within such a set of data. It is also possible that ED-producing communities are more diverse than EL-producing communities. Thus, with an assortment of active organisms that exhibit different activating capabilities, it would be difficult to directly associate the total numbers and activities of ED-producing communities. As an example, the activities measured from a fecal sample with a low concentration of ED-producing organisms, where species with high activating capabilities prevail, and from a sample with a high concentration of ED-producing communities, where other species with low activating capacities predominate, may not greatly differ. In vitro experiments might also be limited to accurately study such diverse communities. These concerns highlight the need to gain access to the active bacterial communities at the species level.
Two organisms involved in SECO activation were isolated from feces. The two organisms were required to produce ED from SECO. Our in vitro experiments indicate that demethylation occurs before dehydroxylation, as suggested earlier (56). The same author reported the isolation of Peptostreptococcus sp. strain SDG-1 and Eubacterium sp. strain SDG-2, which are capable of SECO demethylation and dehydroxylation, respectively. The molecular analyses conducted for the present study showed that our isolated SECO-demethylating and -dehydroxylating strains belong to the species P. productus and E. lenta.
A new 16S rRNA probe specific for the species P. productus and C. coccoides was designed. The detection of P. productus-like bacteria in 15 of 20 subjects by in situ hybridization using the specific probe ProCo-1264 confirms the occurrence of SECO-activating organisms within the dominant fecal microbiota. This agrees with previous data on positive PCR detection of P. productus in 104 to 107 dilutions of human fecal samples (n = 12) (57). These results, along with the MPN enumerations, show that bacteria responsible for enterolignan production occur at concentrations higher than those reported earlier (5). MPN enumerations of acetogenic bacteria in feces from two non-methane-excreting individuals revealed concentrations of 7.2 x 107 and 3.1 x 108 acetogens g1 wet feces (15). Since P. productus belongs to the functional group of acetogenic bacteria, many of which are capable of demethylating aromatic compounds (17, 24), it is tempting to speculate that such organisms are involved in SECO activation. This also supports the occurrence of SECO-activating organisms within dominant microbial communities of the human intestine.
The interindividual variations observed for MPNs and enterolignan production are in agreement with previous reports on lignan metabolism and the diversity of intestinal bacteria (29, 46, 47, 58). Despite these variations, women tended to have higher concentrations of enterolignan-producing organisms. However, this could not be explained by quantitative differences in dominant bacterial groups. A study of enterolactone concentrations in serum and urine after a rye bread diet did not show significant differences between women and men (26). Nonetheless, over 4 weeks, women had higher serum enterolactone concentrations (39.3 ± 4.4 nmol liter1; n = 21) than did men (28.1 ± 3.8 nmol liter1; n = 18), in spite of significantly higher intakes of test bread and fibers by the men. Thus, even if it is difficult to appraise the effect of high concentrations of SECO-activating organisms on the bioavailability of enterolignans, our results hint at a connection between lignans and endogenous hormone metabolism (8, 21, 38, 51). Besides, concentrations of enterolignan-producing communities were relatively stable over a year in a healthy male adult without major dietary changes during that time. Since previous studies in humans showed that dietary interventions influence the blood concentration of enterolignans (25), an appealing goal is to know to what extent functional foods or specific dietary supplementations would alter the SECO-activating bacterial communities beyond the influence of endogenous factors.
High concentrations of P. productus and C. coccoides positively correlated with high concentrations of EL-producing organisms in approximately two-thirds of the cohort. The reason why a similar correlation could not be observed with ED-producing organisms remains unclear, but the isolation of an active P. productus strain indubitably supports our findings. Differences in EL production were not only reflected by differences in P. productus and C. coccoides counts. High concentrations of the Atopobium group, which includes E. lenta, also characterized individuals with high concentrations of EL-producing organisms. In the future, it might be of interest to stratify human subjects with respect to these bacterial parameters to assess the possible health effects of dietary lignans, as proposed for isoflavones (49).
In conclusion, we showed that the widespread conversion of dietary lignans results from the catalytic activities of both dominant and subdominant anaerobic bacterial communities in the human intestinal tract. The fecal microbiota composition data and the isolation of active bacteria illustrate how bacterial species interact with compounds from their environment to produce metabolites with possible health implications. To allow for an in-depth view of the microbial ecology of lignan activation and a better understanding of the involved mechanisms, we strive to identify other lignan-activating organisms and to characterize their metabolic potentials.
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