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Applied and Environmental Microbiology, September 2006, p. 6204-6211, Vol. 72, No. 9
0099-2240/06/$08.00+0 doi:10.1128/AEM.00754-06
Copyright © 2006, American Society for Microbiology. All Rights Reserved.
University of Dundee Gut Group, Dundee, United Kingdom
Received 31 March 2006/ Accepted 6 July 2006
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The large intestine is an open system in the sense that digestive materials from the small gut enter at one end and feces are periodically excreted at the other. Due to the anatomy of the large bowel and the mechanics of movement of particulate substances through the gut, bacteria that are able to colonize food residues in the cecum and maintain significant populations in the proximal bowel serve as inocula for new digestive materials entering the colon. These organisms may therefore be of particular ecological importance in maintaining the stability of the colonic microbiota. Little is known about how the colonization of particulate substances occurs in the large intestine, but it is likely that the organisms involved in the initial stages of this process form biofilms. Bacteria growing in these structures often behave differently from their nonadherent counterparts, and in particular, the nature and efficiency of their metabolism are changed, while many species exhibit greater resistance to antibiotics and other inhibitory factors that have deleterious effects on planktonic bacteria (3, 35, 42).
Microbial biofilms are ubiquitous, and they have been investigated in a variety of natural environments including sediments, soils, the oral cavity, and skin as well as in the gastrointestinal tracts of animals. However, while there is increasing interest in mucosal biofilms in the human colon (22, 37), particularly with respect to their role in disease processes (30, 41), study of the composition and ecological significance of these phenomena in the gut has generally been neglected. As a consequence, we know little about their ecology or physiological significance. The aims of this study, therefore, were to investigate the composition and activities of bacterial communities that colonize the surfaces of food residues in the gut lumen, with respect to their role in the breakdown of complex carbohydrates.
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Enumeration and identification of bacterial populations.
Suspensions (1.0 ml) of nonadherent bacteria and organisms desorbed from particulate material by CTAB were vortex mixed with sterile prereduced half-strength Wilkins-Chalgren anaerobe broth (9.0 ml) to form a 10-fold dilution series (101 to 109). Samples (0.1 ml) from the tubes (103 to 109) were then spread in triplicate onto a range of prereduced agar plates in an anaerobic chamber (atmosphere containing 10% H2, 10% CO2, and 80% CO2). Plates used for the isolation of aerobic and facultatively anaerobic organisms were as follows: nutrient agar for total aerobes and facultative anaerobes, MacConkey agar no. 2 for lactose fermenting and non-lactose-fermenting enterobacteria and enterococci, and azide blood agar base for facultatively anaerobic cocci. Isolation media used for strict anaerobes were Wilkins-Chalgren agar (WCA) for total anaerobes, anaerobic cocci, and clostridia; WCA with the addition of nonsporing anaerobe supplements (to prevent the growth of spore-forming species); WCA with gram-negative anaerobe supplements, which were selective for gram-negative organisms; Rogosa agar for lactobacilli; and Perfringens agar plus antibiotic supplements for Clostridium perfringens. Bacteria belonging to the Bacteroides fragilis group were isolated and enumerated using Bacteroides mineral salts agar (28), and bifidobacteria were counted using Beerens agar (4). Medium 10 (6) and YCFAG medium (13) were used for the isolation and cultivation of Faecalibacterium prausnitzii. Plates for aerobic incubation were removed from the anaerobic chamber and incubated at 37°C. Aerobic plates were incubated for 2 days and anaerobic plates were incubated for up to 5 days, with periodic examination, before colonies were counted. The bacteria were identified using a variety of techniques, including Gram stain, cell morphology, fermentation product analysis (see below), biochemical reactions in API (20A and 32A) tests (BioMerieux, Marcy l' Etoile, France), analysis of cellular fatty acid methyl esters (FAME), and 16S rRNA gene sequence analysis. FAME were extracted from bacterial pellets obtained from approximately 40 ml of culture in anaerobic peptone-yeast extract broth supplemented with glucose (10 g/liter) by saponification, methylation, and extraction as described previously (34). FAME were separated using a model 6890A microbial identification system (Microbial ID Inc., Newark, Del.), which consisted of a Hewlett-Packard (Palo Alto, CA) model 6890 gas chromatograph fitted with a 5% phenyl-methyl silicone capillary column (0.2 mm by 25 m), a flame ionization detector, a Hewlett-Packard model 7637A automatic sampler, and a Hewlett-Packard Vectra XM computer. The gas chromatography parameters were as follows: carrier gas, ultra-high-purity H2; column head pressure, 60 kPa; injection volume, 2 µl; column split ratio, 100:1; septum purge, 5 ml/min; column temperature, 170 to 270°C; injection port temperature, 300°C. Peaks were automatically integrated, and fatty acid names and percentages were calculated. Numerical analyses and predictions for bacterial identification were done using standard MIS library generation software. The system was calibrated using a standard MIDI FAME calibration mix before each operation and validated using the type strains Escherichia coli ATCC 11775, Bacteroides fragilis ATCC 25285, and Clostridium perfringens ATCC 13124. Yeast cells were identified using the API 20 C AUX biochemical identification system (bioMerieux, Basingstoke, England).
16S rRNA gene sequence analysis was used to confirm the identities of the isolates that could not be identified reliably by FAME analysis. DNA was extracted, purified, and amplified using universal primers (36) as described previously (21). Direct sequencing of the amplified DNA fragments was done using an automated ABI 3100 Genetic Analyzer capillary sequencer (Applied Biosystems, Foster City, CA).16S rRNA gene sequences were compared with all sequences in GenBank by using the BLAST algorithm (1).
SEM.
Samples of digestive residues for scanning electron microscopy (SEM) were placed in 3% (vol/vol) glutaraldehyde in PIPES [piperazine-N,N'-bis(2-ethanesulfonic acid)] buffer (100 mM, pH 7.4). The samples were then fixed with 4% (wt/vol) aqueous OsO4 and dehydrated stepwise in ethanol, with three changes (10 min) in each of 50%, 75%, 95%, and, finally, 100% ethanol. Samples were subsequently dried on a Poleron E 5000 critical-point drier, placed onto stubs, and gold coated to a depth of 30 nm. A Phillips XL 30 FEG scanning electron microscope was used to visualize the preparations.
Viability staining of bacteria growing in biofilms.
Food residues containing adherent bacteria were covered with 200 µl BacLight viability stain, comprised of 1.5 µl SYTO 9 and 1.5 µl propidium iodide, in 1 ml anaerobic distilled H2O (Molecular Probes Europe BV, Leiden, The Netherlands). Samples were then placed into an anaerobic chamber, in the dark, for 10 min to allow the stain to develop. Scans were taken using a Nikon Eclipse E800 upright microscope attached to a Nikon PCM 2000 CLSM system with a 488-nm argon laser (green fluorescence indicates live cells) and a 543-nm helium-neon laser (red fluorescence indicates dead cells). A 60x Plan Apo immersion lens with a numerical aperture of 1.4 was used for visualizing the bacteria, and images were captured and overlaid using C-Imaging software (Compix Inc., Cranberry Township, PA).
Oligonucleotide probes.
The range of fluorescent 16S rRNA gene oligonucleotide probes used in this study, which targeted all of the major populations of gut bacteria, has been described previously (7). In particular, probe Bif164 (5'-CATCCGGCATTACCACCC-3') was used to identify bifidobacteria (24), probe Ent1 (5'-CCGCTTGCTCTCGCGAG-3') was used for enterobacteria (25), probe Bac 303 (5'-CCAATGTGGGGGACCTT-3') was used for Bacteroides and Prevotella (32), probe Erec 482 (5'-GCTTCTTAGTCAGGTACCG-3') was used for the Eubacterium rectale-Clostridium coccoides group (17), and the universal eubacterial probe Eub338 (5'-GCTGCCTCCCGTAGGAGT-3') was used for total eubacteria (2). Intestinal isolates and a range of culture collection type strains were used as controls for testing the specificities of the oligonucleotide probes (16). The organisms were cultured in Wilkins-Chalgren broth in an anaerobic chamber at 37°C. The bacteria were then fixed in fresh 4% paraformaldehyde, washed in phosphate-buffered saline (PBS), and stored in 50% (vol/vol) PBS-ethanol at 20°C (2). The probes were synthesized by Thermohybaid, Interactiva Division (Ulm, Germany), and 5' labeled with the fluorochrome Cy3, Cy5, or fluorescein isothiocyanate (FITC).
Fluorescent in situ hybridization (FISH).
Food residues were fixed in 3 ml of 4% paraformaldehyde in PBS (pH 7.0) for 16 h at 4°C, gently washed with PBS (10 min) at room temperature, covered in 4 ml 50% (vol/vol) PBS-ethanol, and stored at 4°C until hybridization on the same day. Samples were then immersed in 4 ml of hybridization buffer (0.9 mol/liter NaCl, 20 mM Tris-HCl, 0.01% sodium dodecyl sulfate, pH 8.0) at room temperature for 10 min, removed, and covered with 100 µl hybridization buffer containing either FITC-, Cy3-, or Cy5-labeled probes at concentrations of 50 ng/µl, 30 ng/µl, and 30 ng/µl, respectively.
Hybridization was done at 45 or 50°C with the addition of formamide, depending on the type of probe (7), in a humid chamber for 4 h. Hybridization at 48°C was found to give optimum conditions for simultaneous visualization of the probes on the food residues. Unbound probe was subsequently removed with 5 ml wash buffer (0.9 mol/liter NaCl, 20 mM Tris-HCl), and the food residues were placed in 50 ml wash buffer for 20 min.
Food residues were gently rinsed with distilled H2O and mounted onto Teflon-coated eight-well glass slides (VWR; Merck Eurolab Ltd., Poole, United Kingdom). Citifluor medium (Citifluor Ltd., London, United Kingdom) was used as a mounting medium, and the slides were visualized as described above for viability staining. The three-dimensional characteristics of the biofilms were studied using the Nikon PCM 2000 CLSM system as described above. Images were captured and overlaid using C-Imaging software (Compix Inc., Cranberry Township, PA). Individual scans of 0.5 µm through the biofilms were combined using Autovisualize 5.5 3D visualization software (Autoquant Imaging Inc., Troy, NY). Images were taken from different volunteers.
Fermentation studies of strongly adherent and nonadherent bacteria.
Ten milliliters of desorbed adherent bacteria and nonadherent fecal bacteria was incubated in an orbital shaker at 37°C under O2-free N2 gas in sodium phosphate buffer (0.1 M, pH 6.5) in sealed 70-ml serum bottles (Wheaton) with 40 ml of either of the following substrates (20-g/liter final concentration): pectin (citrus), Lintner's starch (BDH), xylan (oatspelt), arabinogalactan (larchwood), porcine gastric mucin (type III; Sigma), fructo-oligosaccharides (Orafti, Tienen, Belgium), xylo-oligosaccharides (XOS; Suntory, Japan), soya-oligosaccharides (SOS; Calpis, Japan), and galacto-oligosaccharides (GOS; Yakult, Japan). The structure and composition of the oligosaccharides are shown in Table 1. Samples (2 ml) were taken periodically over a 6-h time course and frozen (20°C) for subsequent analysis of fermentation products.
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TABLE 1. Structure and composition of oligosaccharides used in the studya
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Dry weight measurements.
Dry weight measurements were done as described previously (12).
Statistical analysis.
Statistical analyses were performed using the Graphpad Prism 4 Statistics Package for Macintosh (Graphpad Software, Inc., San Diego, CA). Data relating to the biofilm and nonadherent populations were found to be not normally distributed and were compared by the Mann-Whitney U test. Probability values of <0.05 were considered statistically significant.
Chemicals.
Bacteriological supplies were obtained from Oxoid Ltd. (Basingstoke, Hamps, United Kingdom). Unless otherwise stated, all other chemicals were purchased from Sigma Chemical Co. (Poole, Dorset, United Kingdom).
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FIG. 1. SEM micrographs of food particles. (A) Intestinal bacteria growing on the surface before washing. (B) Bacteria remaining after several washes with buffer. (C) Complete removal of adherent bacteria following surfactant treatment with 0.001% CTAB.
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TABLE 2. Predominant culturable anaerobes and facultative anaerobes isolated from particulate material in feces obtained from 15 healthy donors
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FIG. 2. Light micrograph (magnification, x100) of adherent bacteria on the surface of food particles stained with a live/dead stain. Yellow cells are living, and red cells are dead.
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FIG. 4. Fluorescent light micrograph (CLSM) of bacteria on plant cells in feces (magnification, x60) stained with 16S rRNA oligonucleotide probes. (A) Total eubacteria (Eub) and bifidobacteria (Bifid) stained with Cy5 (blue)- and Cy3 (red)-labeled probes, respectively, are shown adhering to autofluorescent plant material (green). (B) Composite image of 0.5-µm confocal z sections through the food particle (total depth, 20 µm) showing the presence of bifidobacteria growing in microcolonies below the surface, close to the substratum.
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FIG. 3. Fluorescent light micrograph (magnification, x100) of intestinal bacteria on food particles labeled with 16S rRNA gene oligonucleotide probes. (A) Total eubacteria are stained with Cy5 (blue, A), enterobacteria are stained with FITC (green, B), and bifidobacteria are stained with Cy3 (red, C). (B) Members of the Eubacterium rectale-C. coccoides group are stained with Cy3 (red, A), and bifidobacteria are stained with Cy5 (blue, B). (C) Large numbers of bacteroides stained with FITC (green, B) interspersed with bifidobacteria stained with Cy5 (blue, A) can be seen.
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TABLE 3. Specific rates of SCFA formation and molar ratios of acetate, propionate, and butyrate produced by biofilm and nonadherent bacteria in short-term fermentation experimentsa
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SEM showed a variety of morphological forms in biofilms occurring on the surfaces of food residues in fecal material (Fig. 1). While washing with buffer removed part of the biofilm, treatment with the surfactant CTAB was required to completely desorb strongly adhering bacteria from food surfaces. Microbiological analysis of partially digested food particles in feces showed that the biofilm communities were members of complex multispecies consortia, and at the genus level, at least, biofilm populations were shown to be broadly similar to nonadherent microbiotas, with bacteroides and bifidobacteria predominating (Table 2). Interestingly, staphylococci and bacilli, which are not indigenous organisms in the colon, were found only in the nonadherent population and were not detected on the food particles. This inability to colonize may limit their ability to permanently establish in the large gut. The methods used to enumerate these communities are innately destructive and do not provide information on the organization and community structure in biofilms. However, CLSM sectioning of biofilms on food particles in combination with 16S rRNA gene oligonucleotide probes (Fig. 4) showed that bifidobacteria in the biofilms were present in microcolonies, as well as being dispersed with other organisms. Bifidobacteria have also been shown to occur in microcolonies in biofilms on the gut mucosa (30).
Bacteria first need to colonize food particles in the gut as a prelude to their digestion, which leads to the formation of biofilms. An important facet of bacterial growth in biofilms in the large gut is that species colonizing the surfaces of food particles are likely to be more directly involved in the breakdown of complex insoluble polymeric substances than nonadherent organisms, giving them an advantage in competing for nutrients in the ecosystem. Close spatial relationships between bacterial cells growing on surfaces are important in relation to metabolic communication and are ecologically significant in that they minimize potential growth-limiting effects on secondary cross-feeding populations that are associated with mass transfer resistance, for example, between H2-producing bacteria and H2-consuming syntrophs (8).
The majority of human intestinal bacteria are saccharolytic, and carbohydrate availability is an important factor regulating the composition and metabolic activities of the colonic microbiota (27). A wide range of different carbohydrates is potentially available for fermentation in the large bowel (11), and one of the main determinants of species diversity in the colonic ecosystem is the multiplicity of different carbon sources to which intestinal microorganisms potentially have access. Varying the availability of polysaccharide substrates has been shown to cause significant shifts in luminal anaerobic populations in a gut fermentor system (14). A variety of nutritional, host, and dietary factors affect the outcome of carbohydrate fermentation reactions in the large intestine, and because the majority of carbohydrates entering the colon is in the form of polysaccharides, the rate at which these substances can be depolymerized controls the rate at which fermentable carbohydrates become available for assimilation by the bacteria.
Starches and nonstarch polysaccharides (dietary fiber) are the principal sources of carbohydrates in the human colon (9), although nondigestible oligosaccharides such as fructo-oligosaccharides are increasingly being introduced into the western diet (18). A wide range of mucins from the upper gastrointestinal tract enter the large bowel in effluent from the small intestine, while more mucus is formed by goblet cells in the colonic mucosa. In small intestinal effluent, particulate substances such as partially digested plant cell materials are entrapped in a viscoelastic mucus gel, which must be broken down by bacteria in the colon to facilitate access to the food residues.
The chemical composition of the growth substrate markedly influences the fermentation products that can be formed by bacteria. This was demonstrated previously by Englyst et al. (15), who originally showed that acetate and butyrate were the principal SCFA produced from starch by fecal bacteria, whereas acetate was the main fermentation product from both pectin and xylan. Similar results were obtained in the present study, when different carbohydrates were incubated with biofilm and nonadherent fecal bacteria in fermentation experiments (Table 3). These short-term incubations were done under nitrogen limitation to restrict bacterial growth and changes in community structure.
Qualitative and quantitative differences in biofilm metabolism were seen in SCFA production rates, particularly when oligosaccharides served as substrates; previous studies have shown that these bacteria are also different with respect to their polysaccharidase and glycosidase activities (29). These results clearly showed that nonadherent bacteria fermented oligosaccharides considerably more rapidly than the biofilm communities, whereas this was only true with highly soluble polymers such as starch and, to a lesser degree, mucin. The relatively insoluble polysaccharide arabinogalactan associated with cell wall material was digested more rapidly by bacteria desorbed from the biofilms, reflecting their adaptation to this substrate. Interestingly, butyrate, which is used as an energy source by the colonic mucosa (38) and which has a number of anticancer properties (23), was formed primarily by nonadherent fecal communities, irrespective of the fermentation substrate, indicating that these bacteria are of physiological importance to the host.
An interesting facet of the results on carbohydrate metabolism obtained in this investigation was the data concerning oligosaccharide fermentation. Fructo-oligosaccharides, GOS, XOS, and SOS are all potential prebiotic substances. Prebiotics are food ingredients that are not hydrolyzed by human digestive enzymes and that selectively stimulate the growth and activities of specific groups of bacteria in the gut, usually bifidobacteria and lactobacilli, with health benefits (18). Surprisingly, fermentation of oligosaccharides was in some cases slower than the breakdown of their more complex polysaccharide counterparts. Indeed, in biofilm bacteria, SCFA generation from xylan and arabinogalactan was faster than that with the corresponding oligosaccharides.
However, the molar ratios of acetate, propionate, and butyrate produced from polysaccharides and chemically similar oligosaccharides were not sufficiently distinct to suggest that different groups of bacteria were involved in their fermentation. This indicates that substrate uptake was a significant factor affecting fermentation rate. Similar observations have been made in pure culture studies with Bacteroides ovatus (28).
In conclusion, while we know little about the fine structure of biofilm communities in the lumen of the human colon, it is clear that these microbiotas are heterogeneous assemblages that must form rapidly due to the relatively short retention time of digestive materials in the cecum and ascending colon, which act as a mixing chamber in the large bowel. However, it is unclear whether intestinal biofilms in the colon are comparable to the highly evolved assemblages seen in oral biofilm communities (5). More detailed studies, in combination with molecular methods of analysis, are needed to assess the ecological importance of these structures in the colonic ecosystem as a whole and, more importantly, to determine their significance with respect to host metabolism.
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