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4 Laboratory of Microbial Ecology and Technology, Faculty of Bioscience Engineering, Ghent University, B-9000 Gent, Belgium; 5 INRA, UR 910, Ecology and Physiology of the Digestive Tract, F-78350 Jouy-en-Josas, France; 6 Research Group on Quality, Safety and Bioactivity of Plant Foods, Department of Food Science and Technology, CEBAS-CSIC, ES-30100, Murcia, Spain; and 7 Laboratory of Pharmacognosy and Phytochemistry, Faculty of Pharmaceutical Sciences, Ghent University B-9000, Gent, Belgium
* To whom correspondence should be addressed. E-mail: willy.verstraete{at}ugent.be.
| ABSTRACT |
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| Introduction |
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However, due to interindividual intestinal variability, only about one-third of the individuals were found to be capable of efficiently performing this transformation, leading to large differences in 8-PN exposure after consumption of hops (7). Eubacterium limosum is an anaerobic Gram-positive rod and is present in the colon of most humans (8). Over the last few years, this bacterium has gained increased attention because of its beneficial effects in inflammatory bowel disease, possibly attributed to its butyrate-producing capacity (9,10). Butyrate is known to modulate epithelial cell proliferation and has protective effects on inflammatory bowel disease (11), but oral butyrate treatment did not prove efficient because of the difficulty of delivering butyrate to the colon (12). Therefore, a good alternative would be to administer butyrate-producing probiotics, such as E. limosum (13).
Moreover, this bacterium was recently shown to efficiently activate IX into 8-PN (4). Because of this ability and its probiotic potential, we hypothesized that the combined uptake of E. limosum and hop extracts could lead to increased health effects by improving the colonic environment (e.g. bacterial butyrate production) and by the production of 8-PN in people who lack the appropriate intestinal metabolic potential. This hypothesis was investigated in vitro in a dynamic model of the intestine, followed by an in vivo trial with germ-free (GF) and human microbiota-associated (HMA) rats.
| Materials and Methods |
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Preparation of the E. limosum inocula. E. limosum strain LMG P-23546 (4) was grown anaerobically at 37°C in brain heart infusion broth (Oxoid) with 0.5 g/L L-cysteine HCl, 5 g/L yeast extract, and 5 mg/L haemin. After growth to a concentration of approximately log 12 colony-forming units/L, 15 mL of the growth medium were centrifuged (15,000 x g; 15 min) and resuspended in 15 mL saline (0.9 g/L NaCl). This suspension was immediately used for administration of the bacterium to the simulator of the human intestinal microbial ecosystem (SHIME) or to the rats.
Identification of high and low 8-PN–producing human fecal microbiota. Twelve volunteers delivered a fecal sample for incubation purposes. The samples were prepared immediately and incubated with 25 mg/L IX (4). Based on these results, high (Hop +) and low (Hop –) 8-PN–producing individuals were selected. Their 8-PN production status was confirmed by administering a capsule containing 5.59 ± 0.97 mg IX for 4 consecutive days and by quantifying the relative 8-PN excretion on d 4 in a 24-h urine sample. To avoid background prenylflavonoids, subjects were asked to refrain from consuming hop-containing products from 4 d before to the end of the intervention. The high and low 8-PN producers were asked to deliver fecal samples for inoculating the SHIME and GF rats.
SHIME experiments. The reactor setup was adapted from the SHIME (14), consisting of 5 successive reactors, simulating the stomach, small intestine, and ascending, transverse, and descending colon. The microbial community in the last 3 reactors is derived from a selected fresh fecal sample. Reactor setup, inoculum preparation, and reactor feed composition have been previously described (15). For this experiment, a TWINSHIME setup was developed by operating 2 systems in parallel. The systems were inoculated with a fecal sample from the identified high and low 8-PN producers and designated respectively as Hop + and Hop – compartments. After the reactor start up and a 3-wk stabilization period (15), 25 mg/L IX was administered for 4 wk to the SHIME feed entering both systems (Expt. 1). After 2 wk, log 9 E. limosum was administered daily to the ascending colon part of both systems for 2 wk (Expt. 2).
Rat experiments.
GF 5- to 7-wk-old male and female F344 rats were obtained from our GF rodent breeding facilities. They were randomly separated into 3 groups of 12 rats (6 males and 6 females), housed in 3 sterile isolators (Ingenia) that were maintained in controlled conditions of light (0700–1900 h), temperature (20–22°C), and humidity (45–55%). Within each isolator, male and female rats were kept separately in groups of 3 in standard macrolon cages containing a bed of wood shavings. Throughout the study, they were given free access to autoclaved tap water and a pelleted semipurified diet (Table 1) (16) commercially prepared by SAFE and sterilized by
-irradiation at 45 kGy (IBA Mediris). One group of rats remained GF and rats from the 2 other groups were colonized with the fecal microbiota of either the Hop + or Hop –, using gavage with freshly prepared fecal suspensions (16). The experiment started after a 3-wk acclimatization phase to permit establishment of the microbiota and adaptation of the rats. All procedures were carried out according to European guidelines for the care and use of laboratory animals and with permission 78–58 of the French Veterinary Services.
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After a 3-wk washout period, the remaining 6 rats of each group entered into Expt. 2. This was designed to assess the formation of 8-PN from IX in GF, Hop –, and Hop + rats supplemented with E. limosum. Therefore, all rats were gavaged every day for 4 d with the IX solution and for 6 d with E. limosum (109 colony-forming units per rat). E. limosum administration started 2 d prior to IX dosage to ensure a steady-state presence of the bacterium in the rat intestine. Furthermore, IX was given in the morning and E. limosum in the afternoon to avoid a possible direct interaction during the bolus transit. Biological fluids and organs were collected as in Expt. 1.
Incubation experiments with the rat intestinal contents. The cecal and colonic contents were diluted to 10% (v:v) in supplemented brain heart infusion broth, homogenized with an Ultra-Turrax blender, and incubated anaerobically at 37°C for 72 h.
Processing of SHIME samples and rat biological fluids and tissues. Sampling and prenylflavonoid extraction from the colon compartments of the SHIME systems were carried out as described previously (3).
Urine was centrifuged (8000 x g; 5 min at 4°C) to remove particulates and fecal samples were lyophilized and ground. To 1 mL urine supernatant, 1 mL sodium acetate buffer (0.1 mol/L, pH 5.0) and 50 µL β-glucuronidase/arylsulfatase (10/0.33 MU/L, Sigma-Aldrich) were added. Similarly, to 500 mg feces, 9.5 mL sodium acetate buffer and 250 µL β-glucuronidase/arylsulfatase were added and to 300 µL plasma, 1.7 mL sodium acetate buffer and 50 µL β-glucuronidase/arylsulfatase were added. After overnight incubation at 37°C, 4-hydroxybenzophenone was added as internal standard. The prenylflavonoids from urine and feces samples were extracted in triplicate with ethyl acetate (4). Plasma samples were extracted with ethyl acetate and hexane. To a 2-mL sample, 3 mL water (pH 2), 5 mL ethyl acetate, and 1 mL hexane were added. After vortexing and centrifugation (8000 x g; 10 min), 4 mL supernatant was collected. A second extraction was performed and 5 mL supernatant was collected and pooled with the first extract. The extracts were dried under nitrogen, then dissolved in 250 µL water/methanol (1:1, v:v) with formic acid (0.025%, v:v).
Organs (2 g liver, 0.7 g kidney, 0.6 g brain, and 0.15 g uterus) collected from each rat and extra organ samples from control rats without IX supplementation were processed as reported elsewhere (18). Using this protocol,
85% of IX and 8-PN standards were recovered when 1 µmol/L of each compound were added to the initial mixture.
Chemical analysis of SHIME samples and rat biological fluids and tissues. Quantification of butyrate in the SHIME samples and rat cecal contents was done as previously described (19). SHIME samples and rat urine, feces, and plasma were analyzed for prenylflavonoids by HPLC (4).
Organ samples were analyzed by liquid chromatography-tandem MS (Agilent Technologies) using a reverse phase C18 LiChrospher column (25 x 0.4 cm, 5 µm, Merck) according to Espín et al. (18) (Supplemental Fig. 1). IX, 8-PN, and their corresponding metabolites were identified according to their UV and MS spectra as well as tandem MS fragments. The quantitation of the peaks was carried out by the selected ion-monitoring mode. Due to the lack of both IX- and 8-PN-glucuronide standards, the values for these metabolites were scored as high (+++), medium (++), low (+), and not detected (–). Not detected were those that either did not permit the MS-MS fragmentation of the ion or the ion intensity was below the background noise; low values were those that permitted proper compound identification (mean integrated areas
1 x 106); medium and high values exceeded the ion intensity of low values by
2- to 5-fold (mean integrated areas
3 x 106) and 10- to 30-fold (mean integrated areas
2 x 107), respectively. For ion intensity comparison, the ionization of the mass spectrometer was checked daily using IX and 8-PN standards.
PCR-denaturing gradient gel electrophoresis fingerprinting of fecal and cecal bacterial communities. DNA extraction of the fecal and cecal samples was performed as previously described (15). The 16S ribosomal RNA genes for all bacteria were amplified by PCR using the primers PRBA338f and P518r (20), and a 40-bp GC clamp was added to the forward primer. Denaturing gradient gel electrophoresis (DGGE) was performed using the Bio-Rad D gene system with 8% (w:v) polyacrylamide gels and denaturing gradients from 45 to 60% (15). Principal components analysis (PCA) of the DGGE profiles was performed using the BioNumerics software v2.0 (Applied Maths) and PCA ordinations were calculated using the Pearson product-moment correlation coefficient. Within each character set, this coefficient subtracts each character from the mean and divides it by the variance of the character set.
Real-time PCR quantification of E. limosum. A real-time PCR protocol specific for E. limosum was developed based on the method of Kageyama et al. (21). Amplification was performed with an ABI Prism SDS 7000 instrument with the PCR Master Mix (2x) SYBR Green kit (Applied Biosystems). A total of 300 nmol/L of the primers LimoF (TGG-ATC-CTT-CGG-GTG-ACA-TT) and LimoR (CTC-ATT-GGG-TAC-CGT-CAT-TC) were used and the protocol consisted of 2 min at 50°C; 10 min at 95°C; 40 cycles of 30 s at 94°C, 30 s at 63°C and 30 s at 72°C. Standard curves were constructed with cloned 16S ribosomal RNA genes from E. limosum in a concentration range from log 16 to log 8 DNA copies per liter and DNA from at least 10 nontarget species was used to test amplification specificity.
Statistical analyses. Values are expressed as means ± SEM. Expt. 1 and Expt. 2 were analyzed as separate factorial studies, with bacterial status (Hop – and Hop + in SHIME assays; GF, Hop –, and Hop + in rat assays), intestinal segment (ascending, transverse, and descending colon in SHIME assays; cecum and colon in in vitro incubations with rat intestinal contents), and gender (male and female in rat assays) as treatments. The effects of bacterial status and intestinal segment (SHIME assays and in vitro incubations) or bacterial status and gender (rat assays) were analyzed with 2-way ANOVA. Following significant ANOVA, the Newman-Keuls test was used for pairwise comparisons. In Expt. 2, E. limosum was administered to the same SHIME Hop – and Hop + compartments as those used in Expt. 1. Similarly, in the rat assays, one-half of the rats used in Expt. 1 for IX and 8-PN analysis in urine and feces were further used in Expt. 2 for the same purpose. Therefore, 8-PN production in the SHIME and IX and 8-PN excretion in the rats with (Expt. 2) and without (Expt. 1) E. limosum were compared with ANOVA for repeated measurements. When data were not normally distributed, nonparametric tests were used. The significance level was set at P < 0.05. Calculations were performed with Statview software (version 5.0, SAS Institute).
| Results |
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Excretion of IX and 8-PN in rat feces and urine. IX and 8-PN were analyzed in the fecal and urinary outputs collected in the last 2 d of the dosing period of Expt. 1 and Expt. 2. Because the daily excretion values were correlated (0.62 < r < 0.82; P < 0.001), the mean excretion of the 2 d was used as the variable (Fig. 1).
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The importance of liver phase II metabolism was assessed by quantifying the amounts of IX and 8-PN recovered in the urine and feces of the GF rats with or without β-glucuronidase/arylsulfatase treatment of the samples prior to analysis (Table 3).
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Concentrations of IX and 8-PN in rat plasma and different organs. Plasma IX concentrations were similar for all rats and reached, respectively, 0.63 ± 0.05 and 0.54 ± 0.05 µmol/L in Expt. 1 and Expt. 2. In Expt. 1, no 8-PN was detected in the GF rats' plasma and 8-PN concentrations were significantly higher in the Hop + (2.46 ± 1.02 µmol/L) than the Hop – rats (0.77 ± 0.04 µmol/L). However, the ratio of 8-PN concentration to the combined IX and 8-PN concentration was not significantly higher in Hop + rats than in Hop – rats (Fig. 1). After treatment with E. limosum (Expt. 2), plasma 8-PN concentrations were similar in all rats (1.71 ± 0.23 µmol/L) and 8-PN ratios in the GF rats' plasma were even higher than in the HMA rats.
Plasma samples of the GF rats from Expt. 2 were investigated for the presence of free aglycones and phase I and II liver metabolites. Whereas low concentrations of aglycones were detected, IX and 8-PN mainly circulated as phase II glucuronides. Moreover, very low quantities of phase I metabolites with the same molecular mass as IX- and 8-PN-alcohols were detected.
No unconjugated IX or 8-PN was detected in any tissue. The IX- and 8-PN-glucuronides were the only metabolites detected (Table 4). Glucuronidase treatment of the tissue removed the glucuronides, but the corresponding aglycones could not be detected because these showed lower ionization than their corresponding glucuronides. IX-Glucuronide was detected in 97% 60, and 50% of liver, kidney, and uterus tissues, respectively. In Expt. 1, 8-PN-glucuronides were detected in neither GF nor Hop – rats, whereas they were detected in 85% of the Hop + rats. After E. limosum administration, 8-PN metabolites were detected in all rats but with differences depending on the tissue: 89, 33, and 28% of liver, kidney, and uterus tissues, respectively. No IX or 8-PN metabolites were detected in brain tissues.
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PCA analysis of the microbial community profiles in the feces of the Hop + and Hop – rats showed that the profiles grouped based on their bacterial status (Fig. 2). Within 1 bacterial status, the profiles grouped per 3, relating to the fact that the rats were housed per 3. Whereas the DGGE profiles of the GF rats contained no bands in Expt.1, 1 single band was present at the end of Expt. 2, further confirming the presence of E. limosum.
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| Discussion |
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Interindividual variation in phytoestrogen metabolism has been reported by several authors (24,25) and was recently also shown for hop phytoestrogens (3,4). As noted for isoflavones and lignans (26), the results from this study also definitively show the crucial role of the intestinal microbiota in the production of 8-PN from IX. Whereas 8-PN was not detected in any of the biological samples from the GF rats after dosing IX, colonization of the rats with fecal microbiota from subjects with a high (Hop +) or a low (Hop –) 8-PN production status, resulted in rats with different 8-PN production and excretion. Similarly, inoculation of the TWINSHIME with these samples resulted in an 8-PN–producing (Hop +) and nonproducing (Hop –) compartment.
Moreover, a relation was found between the ability of the rat intestinal contents to produce 8-PN from IX in vitro and the 8-PN recovery in rat excreta. Also, 8-PN was only detected in organs of the Hop + rats after IX administration. This can be considered as definitive evidence that differences in the intestinal metabolic potential not only determine 8-PN production but also 8-PN exposure after hop consumption.
As differences in phytoestrogen exposure due to differential intestinal metabolism may hamper therapeutic applicability, E. limosum was used as probiotic to equilibrate the 8-PN exposure. When only IX was administered to the TWINSHIME, 8-PN production was observed in only the Hop + SHIME, with up to 80% conversion. After dosing the probiotic in the ascending colon of both SHIME compartments, high bacterial concentrations were detected in the colon regions, coinciding with 40% 8-PN production in the Hop – compartment. Moreover, the butyrate production in the ascending colon doubled, also leading to increased butyrate concentrations in the rest of the intestine. The survival of probiotics in the SHIME (19,27) has been tested several times and recently the efficacy of a probiotic microbial consortium to increase equol production was shown (28).
Similarly, the Hop + rats produced much more 8-PN than did the Hop – rats. Probiotic administration increased the IX activation in the rat large intestine, as shown by the in vitro incubations of the rat cecal and colonic contents. Molecular analysis confirmed the efficacy of the treatment. E. limosum could be recovered in all cecal samples, with the highest titers in the GF rats, due to the lack of competition with indigenous bacteria in these rats. After probiotic treatment, the 8-PN excretion in both feces and urine was similar for all rats. Coincidentally, butyrate concentrations also increased in the cecum of all rats. This shows that the probiotic can survive the stomach and small intestinal environment and equilibrates 8-PN exposure by increasing the IX activation in low 8-PN producers to the levels found in high producers. This is further confirmed by the fact that the phytoestrogen was now detected in the organs of all rats.
Without taking bacterial status into account, the first 24-h total prenylflavonoid excretion relative to the daily dose (2 mg/kg body weight) reached 35.0 ± 6.6% in the feces and 2.4 ± 0.6% in the urine. Although no pharmacokinetic data of IX are available, these data correspond with the few available data on 8-PN excretion. After single oral administration of 50 mg to postmenopausal women, 8-PN was excreted within 48 h in feces and urine to levels of 23 and 8%, respectively (29). Plasma concentrations were also well within the range of plasma 8-PN concentrations (14.5 µmol/L) detected after 3-mo oral treatment of 6.8 mg 8-PN/kg to rats (30).
GF rats are a good model to study enterohepatic circulation of ingested compounds due to the absence of deconjugating bacteria. The assessment of liver metabolites in the GF rat samples showed that there is enterohepatic circulation of prenylflavonoids. Also, 53% IX-glucuronides were recovered from the GF rat feces. This shows that a major part of IX is first absorbed and then excreted back into the intestine by the liver, similar to what happens with other flavonoids (31). However, in contrast to the low urinary recovery of aglycones for most flavonoids (32), 30% of IX excreted in urine in this research was composed of aglycones and this increased to 46% for 8-PN. Whereas some researchers have shown that the administration of flavonoids through oral gavage may decrease phase II metabolism (32), an alternative explanation is that the presence of the prenyl chain limits phase II metabolism.
In conclusion, this work further indicates the important role of intestinal bacteria in determining the final exposure to 8-PN after consumption of IX-containing hop products. Whereas no 8-PN production was noted in the GF rats, higher 8-PN production occurred in the Hop + intestinal model and rats compared with the Hop – model and rats. In addition, orally administered E. limosum reached the colon, increased the butyrate production in the SHIME and rats, and increased the 8-PN production in the Hop – model and Hop – and GF rats. In this way, the final exposure to hop phytoestrogens was modulated by the probiotic, with similar 8-PN production in all HMA rats.
| ACKNOWLEDGMENTS |
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| FOOTNOTES |
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2 Author disclosures: S. Possemiers, S. Rabot, J. C. Espín, A. Bruneau, C. Philippe, A. González-Sarrías, A. Heyerick, F. A. Tomás-Barberán, D. De Keukeleire, and W. Verstraete, no conflicts of interest. ![]()
3 Supplemental Table 1 and Supplemental Figure 1 are available with the online posting of this paper at jn.nutrition.org. ![]()
8 Abbreviations used: DGGE, denaturing gradient gel electrophoresis; GF, germ-free rats; HMA, human microbiota-associated; Hop +, high 8-prenylnaringenin–producing; Hop –, low 8-prenylnaringenin–producing; IX, isoxanthohumol; PCA, principal components analysis; 8-PN, 8-prenylnaringenin; SHIME, simulator of the human intestinal microbial ecosystem. ![]()
Manuscript received 14 January 2008. Initial review completed 12 February 2008. Revision accepted 7 May 2008.
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