Abstract
Microbes live in communities in biological wastewater treatment plants and in the intestines. However, limited information is currently available on the mechanisms by which minority bacterial populations assist other bacteria besides syntrophic relationships as well as on the microbial food web. Therefore, the present study investigated the effects of non-dye-decolorizing Bacillus subtilis strain S4ga at population levels ranging between 0.04 and 4% on the activity of dye-decolorizing Enterococcus faecalis strain T6a1 using a dye decolorization assay. The results obtained revealed that the minority population of B. subtilis S4ga enhanced the dye-decolorizing activity of E. faecalis T6a1, resulting in a shorter lag time and longer active time of dye decolorization. These effects were related to redox potential values rather than O2 concentrations. Comparisons of the extracellular metabolites in individual incubations of E. faecalis T6a1 and B. subtilis S4ga and a co-incubation suggested a mutual relationship through the cross-feeding of specific amino acids (tyrosine, methionine, tryptophan, phenylalanine, valine, and leucine from B. subtilis S4ga to E. faecalis T6a1; glutamine, histidine, aspartic acid, and proline from E. faecalis T6a1 to B. subtilis S4ga). An analysis of intracellular primary metabolites indicated that the arginine deiminase (ADI) pathway, an ATP-producing energy-generating process, was more strongly activated in co-incubated E. faecalis T6a1 than in E. faecalis T6a1 incubated alone. These results suggest that a co-incubation with B. subtilis S4ga promoted ATP production by E. faecalis T6a1 cells and enhanced its dye-decolorizing activity.
Keywords: amino acids, cross-feeding, metabolomics, minority, oxidation-reduction potential (ORP)
Enterococcus faecalis has become an important bacterium. It has been shown to degrade azo dyes (Walker et al., 1971; Liu et al., 2007; Sahasrabudhe et al., 2014), the main dyes present in textile wastewater (Ito et al., 2018). Some strains are pathogens and nosocomial antibiotic-resistant bacteria known as vancomycin-resistant enterococci (Fisher and Phillips, 2009; Cassini et al., 2019), whereas others produce the antimicrobial agent, bacteriocin, against spoilage bacteria (Foulquié Moreno et al., 2006; Silva et al., 2018) or are used as flavor enhancers in the food industry (Foulquié Moreno et al., 2006). E. faecalis has also been suggested to function as a probiotic in humans and animals (Klein, 2003; Foulquié Moreno et al., 2006). Furthermore, E. faecalis is a fecal indicator that is used for microbial source tracking in water environment management (Byappanahalli et al., 2012). Since E. faecalis is present in communities with other bacteria under the above conditions, clarifying the mechanisms by which E. faecalis associates with other bacteria is the key to establishing strategies for its control.
Despite its low abundance in microbial communities, Bacillus subtilis exerts beneficial effects, such as the production of antimicrobial agents and surfactants (Ilinskaya et al., 2017; Kaspar et al., 2019), the attenuation of intestinal inflammation (Okamoto et al., 2012; Zhang et al., 2016; Ilinskaya et al., 2017), and the modulation or restoration of the gut microbiota (Ma et al., 2018; Hadieva et al., 2021). Previous studies reported that Bacillus species in the wastewater treatment microbiota enhanced the removal of odors, organic compounds, and nitrogen by wastewater treatment systems (Murakami et al., 1995; Park et al., 2007; Ito et al., 2019). The relative abundance of Bacillus species in wastewater treatment systems is low, ranging between 0.1 and 1% (Ito et al., 2019). Nevertheless, Bacillus species have been suggested to cooperate with and enhance the activities of co-existing bacteria.
We have noticed from several literatures that Bacillus species often comprised the dye-decolorizing bacterial consortia, exhibiting higher decolorization efficiencies than individual bacteria (Itoh et al., 2002; Patil et al., 2010; Liu et al., 2018). We investigated the dye-decolorizing bacterial community in river sediment polluted by textile wastewater (Ito et al., 2016) and collected dye-decolorizing bacterial isolates (Ito et al., 2018) to treat textile wastewater, which prompted us to create dye-decolorizing co-cultures. We coincidentally found that the dye-decolorizing activity of E. faecalis was enhanced when co-incubated with non-dye-decolorizing B. subtilis. Therefore, we focused on the combination of B. subtilis and E. faecalis. Even assuming an increase in B. subtilis in the activated sludge microbial community or in the gut microbial community, B. subtilis is only a part of these microbial communities. However, limited information is currently available on the effects of a low abundance of B. subtilis on major bacterial populations.
To investigate the role of the minor population of B. subtilis, its effects on the functional activity of the major population E. faecalis need to be assessed. Even though the dye decolorization assay is a low-tech method, it visualizes the activity of E. faecalis as a color change in test tubes within 1 day with high throughput. Green fluorescent protein (GFP) has been used to monitor E. faecalis in microbial communities (Haug et al., 2010; Hoogenkamp et al., 2015); however, GFP-generating fluorophores require oxygen (Cubitt et al., 1995). The GFP-independent activity assay (dye decolorization assay) is suitable for targeting the dye-decolorizing enzyme azoreductase of E. faecalis, which is activated in reduced environments (Chung et al., 1992). Another benefit of the dye decolorization assay using E. faecalis and B. subtilis is that each strain is easily culturable, distinguishable, and quantifiable on the same agar plate even though their population ratio is 100:1 or higher. We used a dye-decolorizing E. faecalis strain as the reporter strain and a non-dye-decolorizing B. subtilis strain as the partner strain with a minor population; when dye-decolorizing E. faecalis is activated, decolorization is enhanced.
In the present study, we evaluated the activities of E. faecalis when incubated alone and when co-incubated with B. subtilis using the dye decolorization assay. We also examined the abundance of non-dye-decolorizing B. subtilis needed to enhance the dye-decolorizing activity of E. faecalis. Furthermore, we investigated the mechanisms by which non-dye-decolorizing B. subtilis activated dye decolorization by E. faecalis using dissolved oxygen (DO) and the oxidation-reduction potential (ORP) and analyses of intracellular and extracellular metabolites in the co-incubation and individual incubations of each strain.
Materials and Methods
Strains used in the present study and their identification
One bacterial strain (E. faecalis strain T6a1) exhibiting dye-decolorizing activity was isolated from the fingertips using a previously reported method (Ito, 2013; Ito et al., 2018). Seven non-dye-decolorizing Bacillus-like strains (S4ga, S4gb, C16caA, C47ea, A14d3B, D3da, and C8ba) were isolated using the same method (Table S1). The full-length 16S rRNA gene sequences of these strains were analyzed using a colony polymerase chain reaction, followed by Sanger sequencing, which was performed at GENEWIZ Japan. The identification of these strains was based on an NCBI BLAST search for 16S rRNA gene sequences, colony morphology, and microscopy.
Screening of non-dye-decolorizing Bacillus strains that enhanced dye decolorization by E. faecalis T6a1
Isolated strains were pre-incubated under two conditions: the incubation of each strain alone and a co-incubation of E. faecalis T6a1 with one of the seven Bacillus strains. Each strain was inoculated into 5 mL of Luria-Bertani (LB) liquid medium in a test tube with a lid. After a static culture at 37°C for 17 h, 30 μL of 10 g L–1 Congo red dye (cat. no. 032-03922; Wako Pure Chemicals) was added to each test tube to achieve an initial dye concentration of 60 mg L–1. After the addition of Congo red dye, samples were statically incubated at 37°C under oxygen-containing conditions by leaving the gas phase of the test tubes in the air. The color of the liquid in the test tubes was regularly observed. Dye concentrations were assessed by measuring the absorbance of the liquid in the test tubes at a wavelength of 490 nm. To measure absorbance, liquid containing the cells and dye was centrifuged at 14,000×g for 5 min, and the supernatant was analyzed using a spectrophotometer. The dye decolorization rate was calculated from the maximum slope of the line in each dye concentration–time graph. The dye decolorization assay was performed in triplicate.
Among the seven Bacillus strains examined, B. subtilis strain S4ga showed the highest acceleration of dye decolorization by E. faecalis T6a1, resulting in the complete decolorization of 60 mg L–1 Congo red to 0 mg L–1 (Table S1). An incubation of E. faecalis T6a1 alone decreased the dye concentration, but at a decolorization rate that was two-thirds that of the co-incubation with strain S4ga. Therefore, strain S4ga was selected for subsequent analyses.
Population ratio setting
To test different population ratios of E. faecalis T6a1 and B. subtilis S4ga, it was important to establish a stable community composition and quantify the population composition. We prepared pre-incubated E. faecalis T6a1 cells that were suspended in 10% LB medium with high turbidity and pre-incubated B. subtilis S4ga cells as follows. E. faecalis T6a1 and B. subtilis S4ga were separately pre-incubated in 100% LB medium at 37°C for 14 h. Cells were collected and washed with 10% LB medium, and each strain was then suspended in 10% LB medium. The cell turbidity of E. faecalis T6a1 was adjusted to approximately 3 O.D. in 10% LB medium and then mixed with pre-incubated B. subtilis S4ga. The population ratios of B. subtilis S4ga to E. faecalis T6a1 during the incubation were set to approximately 1% and also in the range of 0.04 to 40%. Population ratios were estimated based on cell turbidity after the pre-incubation and were confirmed by CFU counting. The cell number of E. faecalis T6a1 when incubated alone was adjusted to be similar to that of E. faecalis T6a1 in the co-incubation with B. subtilis S4ga.
The initial high cell turbidity of E. faecalis T6a1, which corresponded to approximately 7–9 log CFU mL–1, suppressed the growth of E. faecalis T6a1 and B. subtilis S4ga during the co-incubation. Although B. subtilis grows from 5 to 8 log CFU mL–1 within 1 day when incubated alone, its growth was limited to 6 CFU mL–1 when co-incubated with 8 log CFU mL–1 of E. faecalis in 10% LB medium. When the initial E. faecalis T6a1 population was 9 log CFU mL–1 and the initial B. subtilis S4ga population for the co-incubation was 7 log CFU mL–1, the populations of both strains did not significantly change before or after the incubation for 11 h (Fig. S1). Therefore, we controlled the population ratio of the strains during the co-incubation.
Viable cell counts of E. faecalis T6a1 and B. subtilis S4ga
The amount of dye decolorized in the test tube was proportional to the population of dye-decolorizing E. faecalis T6a1. Therefore, E. faecalis T6a1 cell numbers were enumerated by dilution plating before and after the incubation. The incubated solutions collected from the incubation of E. faecalis T6a1 alone and the co-incubation of E. faecalis T6a1 and B. subtilis S4ga were spread on 10% LB agar medium with serial dilutions and then incubated at 37°C for 12 h, followed by colony counting. We previously reported a correlation between the colony counts of B. subtilis and sequence read frequencies by next-generation sequencing (Ito et al., 2019). We confirmed that the colony count of B. subtilis correlated with the results of the sequencing analysis at a quantification range of 0.001 to 1%. Although B. subtilis S4ga colonies appeared with E. faecalis T6a1 colonies on the same agar plate, they were easily discriminated based on their colony sizes (Fig. S2). E. faecalis T6a1 lacked motility and colonies were smaller (approximately 0.5 mm in diameter), whereas B. subtilis S4ga was motile and had larger colonies (1.5–3 mm in diameter) after an incubation for 12 h. B. subtilis S4ga colonies were further confirmed by their Bacillus-like wrinkled appearance after an incubation for 24–48 h. Some of the colonies were analyzed by colony-PCR and sequencing.
Dye decolorization assay
Dye-decolorizing E. faecalis T6a1 was co-incubated with non-dye-decolorizing B. subtilis S4ga and Congo red dye at 37°C. E. faecalis T6a1 incubated alone was used as a control. Each strain was inoculated in 5 mL of 10% LB liquid medium in a test tube with a lid. The dye decolorization assay was subsequently performed under oxic and anoxic conditions. Oxic conditions were created using air in the gas phase of the test tube. The initial DO concentration under oxic conditions ranged between 6 and 7 mg L–1. In contrast, anoxic conditions were created by nitrogen purging of the gas phase in the tube for 60 s. After nitrogen purging, DO in the liquid in the test tube was less than 0.5 mg L–1. The concentration of Congo red dye was set to 60 mg L–1. Immediately after the addition of the dye, DO was routinely measured using the non-contact-type DO sensor, Fibox3-trace (PreSens Precision Sensing) until the liquid in the test tube was decolorized or the incubation was terminated. The ORP value of the liquid was measured when the incubation was terminated or when the dye in the liquid was completely decolorized. Initial ORP values ranged between +155 and +175 mV. pH did not significantly change before or after the incubation, ranging between pH 7.2 and 7.6. The viable cell count as CFU was evaluated after decolorization. The dye concentration during the incubation was assessed from the RGB of routinely acquired images (Fig. S3). The final dye concentration was evaluated by measuring absorbance at 490 nm.
Dye concentration estimations by measuring RGB values in images of incubating tubes
The time-course monitoring of dye concentrations was performed by measuring RGB values in the images acquired of test tubes during incubations. Standard solutions of Congo red dye were prepared in 10% LB medium at concentrations ranging between 0 and 300 mg L–1 to obtain a calibration curve. Five milliliters of each standard solution was placed in a flat-bottomed test tube for a spectrophotometric analysis (Spectroquant Empty cells 16 mm; Merck KGaA), which was also used for incubations. Test tubes of standard solutions were placed in a photography box (WB-50; LPL) equipped with a LED backlight (SLT-B4C; MUTOH Industries) at an illuminance of 2,700 lx and images of test tubes were acquired using a camera with the following settings: shutter speed, 1/100 s; aperture, f/2.8; focal length, 4.5 mm; ISO speed, 100 (Fig. S3A). After loading the images onto a PC, R, G, and B values at the center of each test tube were measured using the Eyedropper tool in PowerPoint (Microsoft). The total RGB value was calculated for each standard solution to create calibration curves of the total RGB value versus dye concentrations, yielding a linear approximation for concentrations <40 mg L–1 and an exponential approximation for concentrations between 40 and 300 mg L–1 (Fig. S3B). Regarding measurements of dye concentrations in incubation tubes, images of the test tubes were taken under the same conditions as those of the standard test tubes. Therefore, images were acquired under stable photography conditions. In addition, images of the tubes were taken along with those of the standard test tubes. We confirmed that the R, G, and B values of the standard test tubes were constant throughout the dye decolorization experiment. Furthermore, we evaluated dye concentrations in test tubes by a colorimetric assay using test tubes with the standard solutions. The final dye concentration was assessed by spectrophotometry. Therefore, we validated dye concentration estimations based on RGB measurements using multiple methods.
This method involves non-contact measurements that do not require the collection of liquid from test tubes and, thus, do not disturb the incubation solution in the test tube or the gas phase of the tube. Furthermore, these measurements may be performed quickly and repeatedly by acquiring images of test tubes.
ORP measurements during the B. subtilis S4ga incubation
Some of the B. subtilis S4ga colony on the agar plate was suspended in 50 mL of LB liquid medium and placed in an incubator at 37°C for 1 h. The cell suspension was centrifuged at 12,000 rpm for 5 min and the supernatant was replaced with 10% LB liquid medium. Centrifuged cells were re-suspended in 10% LB and, thus, a B. subtilis S4ga cell suspension (8 log CFU mL–1) was prepared in a 50-mL tube. In aerobic incubations, 200 mL of 10% LB liquid medium was prepared in a 500-mL vial, and 240 μL of the B. subtilis cell suspension was added to the medium. Congo red (10 g L–1) was then added at a concentration of 60 mg L–1. Three sets of vials were shaken at 60 rpm. In microaerophilic incubations, 5 mL of 10% LB liquid medium was prepared in a 16-mL test tube with a rubber stopper, and 30 μL of the B. subtilis S4ga cell suspension was added to the medium. Congo red (10 g L–1) was added at a final concentration of 60 mg L–1. After the tube was capped with a rubber stopper, nitrogen gas was injected into the test tube with a needle for 3 s. DO was 1 mg L–1 at 5 h and thereafter remained lower than 1 mg L–1. During the incubation at 37°C, the ORP and DO of the incubation medium in the vials and test tubes were monitored for 27 h. Since it was necessary to open the caps of the vials and tubes to measure ORP, DO was assessed using a non-contact-type DO sensor before opening the vials. Unopened test tubes were opened each time to measure the ORP of the incubation solution under microaerophilic conditions. Therefore, 30 test tubes were initially prepared, and four to six test tubes were measured at each time point.
Metabolomic analysis
(i) Incubation conditions. To investigate whether B. subtilis S4ga affected the metabolism of E. faecalis T6a1, a metabolomic analysis of the intracellular and extracellular water-soluble primary metabolites of strains T6a1 and S4ga was performed on co-incubated cultures and individual incubations of each strain. Incubations were conducted as described above (dye decolorization assay). Briefly, after a pre-incubation of each strain, the co-incubation of E. faecalis T6a1 and B. subtilis S4ga and individual incubations of each strain were performed at an initial Congo red dye concentration of 60 mg L–1 in 10% LB medium at 37°C. Incubations were terminated at 10 h during decolorization. The use of 10% LB medium reduced background amino acids and vitamins derived from tryptone and the yeast extract of the incubation medium when intracellular and extracellular metabolites were extracted.
(ii) Extraction and analysis of intracellular water-soluble primary metabolites of E. faecalis T6a1. To compare the intracellular metabolites of co-incubated E. faecalis T6a1 with those of E. faecalis T6a1 incubated alone, B. subtilis S4ga cells were removed from the co-incubation solution. To achieve this, we focused on cell sizes; E. faecalis T6a1 cells were spherical with a width of approximately 0.8 μm and a length of 1.3 μm, whereas B. subtilis S4ga cells were elongated with a width of approximately 0.8 μm and a length of 2.6 μm or longer (Fig. S4A and B). Therefore, we expected B. subtilis S4ga cells not to pass through a filter with a pore size of 0.8 μm. Accordingly, a 0.8-μm filter was used to reduce the number of B. subtilis S4ga cells in the co-incubation solution. After a 10-h incubation with the dye, the co-incubation solution was filtered through a 0.8-μm membrane filter (DISMIC 25CS080AS; Advantec). The solution of E. faecalis T6a1 incubated alone was also filtered to ensure that the filtration procedure did not affect metabolites in E. faecalis T6a1 cells. Filtered solutions were filtered two more times to minimize contamination with B. subtilis S4ga cells. Although B. subtilis S4ga accounted for 2% of the total population after the 10-h incubation (Fig. S4C and D), the filtration treatment effectively removed vegetative cells of B. subtilis S4ga; none were observed among the approximately 10,000 cells of E. faecalis T6a1 examined by microscopy. We only detected some endospores or non-vegetative thin cells (Fig. S4E and F), accounting for 0.07% of the total population. This small population of non-vegetative cells did not affect the metabolomic analysis of E. faecalis T6a1.
E. faecalis T6a1 cells prepared by filtration after the co-incubation and incubation alone were washed with phosphate-buffered saline once and then suspended in sterilized ultrapure water. The turbidity of the cell suspension of E. faecalis T6a1 with the co-incubation and in individual incubations was adjusted to be the same among all samples by the addition of ultrapure water. Methanol was then added to suspensions at a concentration of 80% to extract intracellular metabolites. 2-Morpholinoethanesulfonic acid (2-MES) and methionine sulfone were added as internal standards to cell suspensions at a final concentration of 10 μM. After thorough mixing and centrifugation at 20,000×g for 5 min, the supernatants of cell suspensions were collected for a metabolomic analysis. Two sets of samples were prepared for the E. faecalis T6a1 co-incubation and individual incubations.
Ninety-seven water-soluble primary metabolites (e.g., amino acids, organic acids, and coenzymes) were evaluated in intracellular extraction solutions of strain T6a1 by liquid chromatography tandem mass spectrometry (LCMS-8050; Shimadzu) equipped with a pentafluorophenylpropyl column. The resulting intensity was normalized to the height ratio (the peak height of each metabolite divided by the peak height of 2-MES). In cases in which a small peak was overlaid with the next peak or small peaks were considered to be noise, these peaks were regarded as undetected metabolites. Metabolic pathways in E. faecalis were analyzed using the Kyoto Encyclopedia of Genes and Genomes (KEGG) database (Kanehisa et al., 2014).
(iii) Extraction and analysis of extracellular water-soluble primary metabolites from co-incubated cultures and E. faecalis T6a1 and B. subtilis S4ga incubated alone. The incubation solutions of the co-incubated culture and E. faecalis T6a1 and B. subtilis S4ga incubated alone were centrifuged at 20,000×g for 7 min, and the supernatants obtained were filtered using a 0.2-μm sterile membrane filter (ASFIL 033022SO-SFCA; AS ONE). In addition, 10% LB medium was used as a reference to measure the relative concentrations of amino acids from components of tryptone and the yeast extract (Zimbro et al., 2009). Methanol was then added to filtered supernatants at a concentration of 80% to extract extracellular metabolites. 2-MES and methionine sulfone were added as internal standards to the supernatants at a final concentration of 10 μM. Three sets of samples were prepared for co-incubated cultures and E. faecalis T6a1 or B. subtilis S4ga incubated alone, and 10% LB medium. Similar to the analysis of intracellular metabolites, 97 water-soluble primary metabolites were evaluated in extracellular extraction solutions.
Measurement of intracellular ATP of E. faecalis T6a1 and B. subtilis S4ga
The amount of intracellular ATP in the culture of E. faecalis T6a1 incubated alone was measured by subtracting the amount of extracellular ATP in the 0.2-μm filtration permeate from the total amount of ATP in the culture medium containing cells: ATPE.faecalis=ATPtotal–ATP0.2 μm-extracellular. The amount of intracellular ATP in cultures of B. subtilis S4ga incubated alone was assessed in the same manner: ATPB.subtilis=ATPtotal–ATP0.2 μm-extracellular. In the co-incubated culture of E. faecalis T6a1 and B. subtilis S4ga, the amount of intracellular ATP in E. faecalis T6a1 was measured by subtracting the amount of extracellular ATP in the 0.2-μm filtration permeate from the amount of ATP in the 0.8-μm filtration permeate containing extracellular ATP and E. faecalis T6a1 cells: ATPE.faecalis=(ATP0.8 μm-extracellular+ATP0.8 μm-E.faecalis)–ATP0.2 μm-extracellular.
The amount of intracellular ATP in B. subtilis S4ga in the co-incubated culture was assessed by subtracting the amount of ATP in the 0.8-μm filtration permeate containing extracellular ATP and E. faecalis T6a1 cells from the total amount of ATP in the culture medium containing the extracellular and intracellular ATP of both strain cells: ATPB.subtilis=ATPtotal–(ATP0.8 μm-extracellular+ATP0.8 μm-E.faecalis). ATP measurements were performed using BacTiter Glo ATP measurement reagent (Promega) and a luminometer (Lu-mini; Viti Life Science Solutions) in accordance with the manufacturer’s instructions and the literature (Hironaka et al., 2013).
Statistical analysis
The significance of differences was analyzed using two-tailed paired t-tests to compare the co-incubation with B. subtilis S4ga versus E. faecalis T6a1 incubated alone.
Nucleotide sequence accession numbers
The 16S rRNA gene sequences of the isolated strains are available in the DDBJ/EMBL/GenBank databases under accession numbers LC557810–LC557817.
Results and Discussion
Effects of B. subtilis on the activity of E. faecalis
We investigated the activity of E. faecalis T6a1 using the dye decolorization assay at a dye concentration of 60 mg L–1. Fig. 1A shows typical changes in dye concentrations during the co-incubation of E. faecalis T6a1 and B. subtilis S4ga and E. faecalis T6a1 incubated alone. The E. faecalis T6a1 population during the co-incubation was approximately one-fifth of that when incubated alone at 48 h: 1.8×108 CFU mL–1 for the co-incubation and 8.4×108 CFU mL–1 when incubated alone. However, the dye concentration decreased earlier and faster during the co-incubation, and the amount of dye decolorized at 48 h during the co-incubation was approximately two-fold that in individual incubations. In contrast, individual incubations did not show additional decolorization after 48 h. In the co-incubation, the population of B. subtilis S4ga was 1.4×105 CFU mL–1, and, thus, the population ratio of B. subtilis S4ga to E. faecalis T6a1 was 0.08%; this low ratio resulted in differences in the dye-decolorizing activity of E. faecalis T6a1. Furthermore, the maximum dye decolorization rate of the co-incubation was two-fold higher than that of individual incubations (Fig. 1B). We also repeatedly observed that the co-incubation doubled the amount of dye decolorized and halved the lag time to start decreasing the dye concentration from those in individual incubations (Fig. 1C and D). Additionally, the duration of dye decolorization was approximately 2.2-fold higher in the co-incubation than by E. faecalis T6a1 incubated alone (Fig. 1E). In other words, dye decolorization by the co-incubated strain started earlier and lasted longer than that of strains incubated alone, resulting in the decolorization of a large amount of dye. The population ratio of B. subtilis S4ga to E. faecalis T6a1 was 0.1%.
Fig. 1.
Effects of Bacillus subtilis S4ga on dye decolorization by Enterococcus faecalis T6a1. (A) Dye decolorization over time during the co-incubation of B. subtilis S4ga and E. faecalis T6a1 or by E. faecalis T6a1 incubated alone. (B) Dye decolorization rates of E. faecalis T6a1 incubated alone and co-incubated with B. subtilis S4ga for 11 h. (C) Ratio of the amount of dye decolorized by the co-incubation to the amount of dye decolorized by individual incubations. (D) Ratio of the time when the dye concentration started to decrease during the co-incubation to the time when the dye concentration started decreasing during the individual incubations. (E) Ratio of the time when the dye concentration continued to decrease with the co-incubation to the time when the dye concentration continued to decrease in individual incubations. Error bars represent standard deviations (B, C, D, and E); *P<0.05; **P<0.01; n=3 (B); n=9 (C, D, and E). a.u., arbitrary units.
The co-incubation enhanced the decolorizing activity of E. faecalis T6a1. A shorter lag time of dye decolorization by E. faecalis T6a1 indicated that the co-incubation with B. subtilis S4ga affected the activity of E. faecalis T6a1 from the beginning of dye decolorization. Therefore, we measured the intracellular ATP levels of co-incubated E. faecalis T6a1 and that of E. faecalis T6a1 incubated alone. The intracellular ATP level of co-incubated E. faecalis T6a1 was 16-fold higher than that of E. faecalis T6a1 incubated alone (P=0.048, Fig. 2A). On the other hand, the intracellular ATP level of co-incubated B. subtilis S4ga was 2.5-fold higher than that of B. subtilis S4ga incubated alone (Fig. 2B). These results suggested that E. faecalis T6a1 and B. subtilis S4ga were both activated by the co-incubation. The difference in ATP values in Fig. 2B was not significant (P=0.44), which indicated that intracellular ATP levels varied more in co-incubated B. subtilis S4ga, even though the population of B. subtilis S4ga during the co-incubation was controlled within the same order.
Fig. 2.

Intracellular ATP. (A) Enterococcus faecalis T6a1 incubated alone or co-incubated E. faecalis T6a1 after the removal of Bacillus subtilis S4ga at 24 h. (B) B. subtilis S4ga incubated alone or co-incubated B. subtilis S4ga after the removal of E. faecalis T6a1 at 24 h. Error bars represent standard deviations; *P<0.05; n=3 (A and B).
Population ratio of B. subtilis to E. faecalis
We examined the effects of various population ratios of B. subtilis S4ga to E. faecalis T6a1 on the dye-decolorizing activity of E. faecalis T6a1 by changing the amount of B. subtilis S4ga added to the same amount of E. faecalis T6a1. Effective population ratios ranged between 0.04 and 40%. No significant differences were observed in the dye decolorization rates of the co-incubated cultures within the wide range of the B. subtilis S4ga population ratios (Fig. 3A). However, the dye decolorization rates of the co-incubations were higher than those of individual incubations at each time point (Fig. 1B and 3A). We created a box and whisker plot to show the distribution of the effective population ratio with data lower than 4% and demonstrated that 0.4–0.8% B. subtilis S4ga (less than 1%) enhanced the dye-decolorizing activity of E. faecalis T6a1 (Fig. 3B).
Fig. 3.

Effective population ratios of Bacillus subtilis S4ga to Enterococcus faecalis T6a1. (A) Dye decolorization rates of E. faecalis T6a1 co-incubated with B. subtilis S4ga at different population ratios ranging between 0.04 and 40%. (B) Distributions of the population ratios that enhanced the dye-decolorizing activity of E. faecalis T6a1. A box and whisker plot was created with data lower than 4% to focus on the effectiveness of the low ratio range. Error bars represent standard deviations; n=3 (A); n=8 (B).
Effects of B. subtilis on the oxidation state
The dye-decolorizing enzyme azoreductase, which is expressed by E. faecalis, is activated in reduced environments (Chung et al., 1992). Therefore, we investigated DO and the dye decolorization rates of co-incubated cultures of E. faecalis T6a1 and B. subtilis S4ga under oxic and anoxic conditions for 23 h (Fig. 4). The incubation of each strain alone was performed for comparison. The incubation of E. faecalis T6a1 alone achieved approximately 75% decolorization under anoxic conditions at 23 h, whereas the incubation of E. faecalis T6a1 alone showed a markedly lower decolorization rate (20–45%) under oxic conditions at 23 h, mainly between 3.5 and 4.2 mg L–1 DO (Fig. 4A). On the other hand, the co-incubation of E. faecalis T6a1 and B. subtilis S4ga resulted in higher dye decolorization rates of 80–95% at 8 h under oxic conditions, mainly between 1.5 and 3.2 mg L–1 DO, with further increases to 90–100% being observed at 23 h. Under anoxic conditions, the co-incubation showed incomplete dye decolorization of approximately 75–90% at 23 h (Fig. 4B). Under oxic conditions, the co-incubation of E. faecalis T6a1 and B. subtilis S4ga reduced DO to <3 mg L–1, whereas the incubation of E. faecalis T6a1 alone did not.
Fig. 4.
Impact of Bacillus subtilis S4ga on dissolved oxygen (DO) concentrations and the oxidation-reduction potential (ORP) during the co-incubation with Enterococcus faecalis T6a1 and during individual incubations with dye under oxic and anoxic conditions. Correlations between final DO and the dye decolorization rates of incubations of (A) E. faecalis T6a1 alone, (B) E. faecalis T6a1 with B. subtilis S4ga, and (C) B. subtilis S4ga alone at 8 and 23 h. (D) Correlation between final ORP and DO values after the incubation of E. faecalis T6a alone, E. faecalis T6a1 with B. subtilis S4ga, and B. subtilis S4ga alone for 20 h. Populations of E. faecalis T6a1 and B. subtilis S4ga at 20 h (CFU mL–1), Co-1: T6a1, 2×107; S4ga, 7×105 (S4ga-to-T6a1 population ratio, 3%). Co-2: T6a1, 2×108; S4ga, 1×106 (S4ga-to-T6a1, 0.6%). Co-3: T6a1, 7×107; S4ga, 5×105 (S4ga-to-T6a1, 0.7%). T-1: T6a1, 3×106. T-2: T6a1, 2×107. T-3: T6a1, 3×107. (E) A box and whisker plot showing ORP values after the incubation of E. faecalis T6a1 alone or E. faecalis T6a1 with B. subtilis S4ga. ***P<0.001; n=11 (T6a1), n=11 (T6a1 with S4ga). Initial DO under oxic conditions ranged between 6 and 7 mg L–1 (A, B, C, D, and E). The initial concentration of Congo red dye was 60 mg L–1 (A, B, C, D, and E).
We then examined the effects of B. subtilis S4ga on ORP values for dye decolorization by E. faecalis T6a1; E. faecalis T6a1 was incubated alone and co-incubated with B. subtilis S4ga under oxic conditions at < approximately 3 mg L–1 DO (Fig. 4D). The initial ORP value was +163±11 mV in the presence of 1.9 mg L–1 DO. The ORP values of the incubation of E. faecalis T6a1 alone ranged between +90 and +140 mV at 20 h. In contrast, the ORP values of the co-incubation ranged between –30 and +80 mV (Fig. 4E).
To confirm the reducing effects of B. subtilis S4ga on ORP, we monitored changes in ORP in B. subtilis S4ga incubated alone under oxic and microaerophilic conditions (Fig. 5). Under oxic conditions, B. subtilis S4ga reduced ORP to approximately 0 mV after an 8-h incubation after decreasing DO to <3 mg L–1. Under microaerophilic conditions, B. subtilis S4ga reduced ORP to approximately +60 mV after an 8-h incubation with decreases in DO to <1 mg L–1. B. subtilis S4ga created a moderately reduced environment when DO was present, and ORP levels were lower under oxic conditions than under microaerophilic conditions. These results demonstrated that B. subtilis S4ga reduced ORP to a level that enhanced dye decolorization by E. faecalis T6a1 under oxic conditions and also that oxygen was required to enhance dye decolorization by E. faecalis T6a1 when co-incubated with B. subtilis S4ga. B. subtilis has been widely used to produce amino acids (Su et al., 2020) and vitamins (Abbas and Sibirny, 2011), and since oxygen is required for the production of these compounds (Utagawa, 2004; Hu et al., 2017), B. subtilis may have produced reducing agents under oxic conditions, resulting in the lower ORP values observed in the present study.
Fig. 5.
Effects of Bacillus subtilis S4ga on the oxidation-reduction potential (ORP) under oxic and microaerophilic conditions. Changes in ORP (A) and dissolved oxygen (DO) concentrations (B) over time during the incubation of B. subtilis S4ga alone with shaking and under static conditions. Rotational shaking at 60 rpm created oxic conditions. A static incubation after nitrogen purging for 9 s created microaerophilic conditions. The population of B. subtilis S4ga at 14 h: oxic, 1×108 (CFU mL–1); microaerophilic, 0.5×108 (CFU mL–1). The initial B. subtilis S4ga population was 3×105 (CFU mL–1). Error bars represent standard deviations; n=3.
Extracellular metabolites of the co-incubation and individual incubations
Extracellular metabolites in individual incubations of E. faecalis T6a1 and B. subtilis S4ga and the co-incubated culture revealed the characteristics of amino acid production and consumption from 10% LB medium (Fig. 6). The amino acids produced by B. subtilis S4ga were tyrosine, methionine, tryptophan, phenylalanine, valine, and leucine (P<0.05). E. faecalis T61a incubated alone utilized all these amino acids. However, decreases in the amounts of methionine, tryptophan, phenylalanine, valine, and leucine in the co-incubated culture were not as large as those with E. faecalis T6a1 incubated alone, which may be because B. subtilis S4ga provided the co-incubated culture with these amino acids. Although B. subtilis S4ga incubated alone produced a two-fold higher amount of tyrosine than that in 10% LB medium, the co-incubation of E. faecalis T6a1 with 1% B. subtilis S4ga consumed tyrosine and arginine, both of which may be rate-limiting substrates. The amino acids produced by B. subtilis S4ga (methionine, tryptophan, phenylalanine, valine, and leucine) are hydrophobic. Since hydrophobic amino acids are more permeable through the cell membrane than hydrophilic amino acids, E. faecalis T6a1 may readily acquire these amino acids. The amino acids produced by E. faecalis T6a1 were glutamine, histidine, aspartic acid, and proline (P<0.05). B. subtilis S4ga incubated alone utilized all these amino acids. The production and utilization of the amino acids produced by both strains demonstrated the cross-feeding of amino acids between E. faecalis T6a1 and B. subtilis S4ga, indicating synergistic effects on the activities of each strain.
Fig. 6.
Extracellular amino acids produced or consumed by Bacillus subtilis S4ga incubated alone, Enterococcus faecalis T6a1 alone, and in a co-incubated culture of E. faecalis T6a1 and B. subtilis S4ga. Data represent the ratios of amino acids in the supernatants of incubated cultures at 14 h to amino acids in 10% LB medium at 0 h. Co-incubated culture: E. faecalis T6a1, 5×109 (CFU mL–1); B. subtilis S4ga, 1×108 (CFU mL–1) (S4ga-to-T6a1 population ratio, 2%). n=3. a.u., arbitrary units.
Intracellular metabolites of E. faecalis incubated with B. subtilis
Among the 97 water-soluble primary metabolites examined, citrulline was the most significantly altered intracellular metabolite, with higher levels in E. faecalis T6a1 cells co-incubated with B. subtilis S4ga than in E. faecalis T6a1 cells incubated alone (Table S2). Citrulline is an amino acid produced during arginine degradation by the arginine deiminase (ADI) pathway in E. faecalis (Cunin et al., 1986). The ADI pathway is an ATP-producing energy-generating process in E. faecalis (Slade and Slamp, 1952; Simon et al., 1982; Barcelona-Andrés et al., 2002). The ADI pathway catalyzes the conversion of arginine to citrulline and ammonia and further to ornithine, carbon dioxide, and ammonia, with the generation of 2 mol ATP mol–1 arginine (EC 3.5.3.6, EC 6.3.4.16). We demonstrated that ATP levels were more than 10-fold higher in co-incubated E. faecalis T6a1 cells than in E. faecalis T6a1 cells incubated alone (Fig. 2A). Although low oxygen tension is required to induce the ADI pathway in Pseudomonas aeruginosa (Lu et al., 1999), oxygen tension in E. faecalis only weakly affects ADI pathway enzymes, and arginine is a more important inducer (Simon et al., 1982; Barcelona-Andrés et al., 2002). Similarly, higher dye-decolorizing activities by E. faecalis T6a1 were observed under oxic conditions (Fig. 4B), and extracellular arginine was extensively consumed by both E. faecalis T6a1 incubated alone and co-incubated E. faecalis T6a1 (Fig. 6). In addition, among the intracellular metabolites of E. faecalis T6a1, the detected amount of arginine was higher with the co-incubation than with E. faecalis T6a1 incubated alone (Fig. 7 and Table S2). Together with citrulline and arginine, the increase noted in ornithine was explained by the ADI pathway excreting an abundance of ornithine (Cunin et al., 1986). Accordingly, we concluded that the co-incubation with B. subtilis S4ga activated the ADI pathway and promoted energy generation by E. faecalis T6a1 cells.
Fig. 7.
Metabolites of the arginine deaminase (ADI) pathway produced by Enterococcus faecalis T6a1 during the co-incubation with Bacillus subtilis S4ga and dye decolorization. Error bars represent standard deviations; **P<0.01; n=2. Data represent the normalized intensities of metabolites. a.u., arbitrary unit.
Proline levels were also significantly higher in co-incubated E. faecalis T6a1 cells. Proline is an abundant amino acid in E. faecalis enterolysin A (Nilsen et al., 2003), which breaks down bacterial cell walls. Since some strains of Bacillus, including B. subtilis, show weak sensitivity to enterolysin A (Nilsen et al., 2003), the presence of B. subtilis S4ga may stimulate enterolysin A production by E. faecalis T6a1. Moreover, we assumed that the presence of B. subtilis S4ga affected the oxidative stress response of E. faecalis T6a1 and focused on metabolites related to oxidative stress responses, such as glutathione and oxidized glutathione (Patel et al., 1998; Portela et al., 2014). The amount of glutathione detected in E. faecalis T6a1 incubated alone appeared to be slightly higher than that with the co-incubation. Further studies are needed to clarify whether oxidative stress in E. faecalis T6a1 is decreased by the co-incubation with B. subtilis S4ga.
The experimental conditions employed in the present study to analyze the intracellular primary metabolites of co-incubated E. faecalis T6a1 significantly minimized the contamination of metabolites from co-incubated B. subtilis S4ga. After the filtration treatment of the co-incubated culture, the B. subtilis S4ga cells observed by microscopy were non-vegetative cells, accounting for 0.07% of the total population. Based on our current knowledge of non-vegetative cells, they are not inactive, but are also not as active as vegetative cells. Therefore, the remaining non-vegetative cells in this small population did not appear to affect the analysis of the intracellular primary metabolites of E. faecalis T6a1. In addition, assuming that the remaining B. subtilis S4ga cells were vegetative cells, accounting for 0.07% of the total population, we calculated the effects of contaminating metabolites from B. subtilis S4ga on the metabolites of the ADI pathway in E. faecalis T6a1. Based on the results of the intracellular metabolomic analysis of the B. subtilis S4ga incubation alone, the amounts of arginine, citrulline, and ornithine in vegetative B. subtilis S4ga corresponded to 0.08–2% of each metabolite of co-incubated E. faecalis T6a1 (Table S3). Therefore, even if the intracellular metabolites of E. faecalis T6a1 had been contaminated by vegetative B. subtilis S4ga cells, contamination levels were too small to affect the metabolites of the ADI pathway in E. faecalis.
Few studies have shown that non-dye-decolorizing bacteria affect dye decolorization when they are present as minor populations (e.g., approximately 1% or less of the total population). From a practical viewpoint, the addition and/or maintenance of B. subtilis S4ga at 1% may be a useful index for biological textile wastewater treatments to enhance dye-decolorizing bacteria as well as for probiotics in the gut microbiota to promote beneficial bacteria, such as E. faecalis (as a probiotic promoter). Therefore, the present results provide important insights into the roles of minority bacterial populations as key players in dye decolorization and other biological processes.
In conclusion, we herein demonstrated that B. subtilis S4ga enhanced the activity of E. faecalis T6a1, even when it accounted for only 0.4% of the total population, as demonstrated by the results of the dye decolorization assay using non-dye-decolorizing B. subtilis S4ga and dye-decolorizing E. faecalis T6a1. The enhancing effects of B. subtilis S4ga on the activity of E. faecalis T6a1 were observed not only as a high maximum dye decolorization rate, but also as a shorter lag time and longer active time of dye decolorization, and the amount of dye decolorization was doubled. During the co-incubation, B. subtilis S4ga reduced the ORP value to approximately 0 mV by consuming oxygen and/or producing reducing agents, such as amino acids. The amino acids produced by B. subtilis S4ga were the same as those consumed by E. faecalis T6a1, whereas the amino acids produced by E. faecalis T6a1 were the same as those consumed by B. subtilis S4ga. In other words, these strains have a mutual supply relationship for specific amino acids. This may have increased the intracellular ATP content of E. faecalis T6a1 and B. subtilis S4ga, partly via the activation of the ADI pathway of E. faecalis T6a1. These results are summarized in Fig. 8. The present study provides novel insights into co-existing minor populations in microbial communities as well as a more detailed understanding of bacterial control. Further studies are needed to clarify whether the combination of these species or the presence of B. subtilis is important for enhancing the whole-cell activity of co-existing bacteria.
Fig. 8.
Effects of Bacillus subtilis S4ga on the activity of Enterococcus faecalis T6a1. (A) Schematic illustration of a 1% population. (B) Schematic photographs of the dye decolorization assay showing a higher decolorization rate with the co-incubation. (C) Schematic depiction showing the enhancement of dye-decolorizing activity by B. subtilis. (D) Schematic illustration showing the cross-feeding interaction of amino acids between E. faecalis and B. subtilis.
Citation
Yamanashi, Y., and Ito, T. (2022) A Minority Population of Non-dye-decolorizing Bacillus subtilis enhances the Azo Dye-decolorizing Activity of Enterococcus faecalis. Microbes Environ 37: ME21080.
https://doi.org/10.1264/jsme2.ME21080
Supplementary Material
Acknowledgements
This study was supported in part by JSPS KAKENHI (grant number 15K12369 to T.I.) and by a Grant-in-Aid for JSPS Research Fellows (grant number JP17J11210 to Y.Y.). The metabolomic analysis was performed at the Laboratory for Analytical Instruments, Education and Research Support Center, Gunma University.
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