ABSTRACT
Clostridioides difficile is an opportunistic gastrointestinal pathogen capable of asymptomatic colonization and causes diseases ranging from diarrhea to pseudomembranous colitis. Accurate diagnosis of C. difficile infection (CDI) is challenging and critical for treatment and control. We hypothesized that gut microbiome profiles could help distinguish C. difficile colonized patients with diarrhea from those with true CDI. We analyzed 172 stool samples from individuals who tested glutamate dehydrogenase positive for C. difficile. Participants were categorized by toxin status (i.e., toxin positive or negative) and then further classified into three toxin groups based on the production of toxin, and if not produced, whether the C. difficile strain carried toxin-encoding genes. We examined associations between patient characteristics, prior antibiotics exposure, microbiome community structure and function, and toxin categories. Thirty-five percent of toxin-negative participants received antibiotics despite not meeting the criteria for true CDI. Enterococcus species were abundant in all groups. The relative abundance of E. faecalis was higher among individuals with prior antibiotics exposure. Alpha and beta diversity did not differ by toxin group. After controlling for prior antibiotics exposure and previous CDI episode, the abundance of Akkermansia muciniphila, Flavonifractor plautii, and Bifidobacterium adolescentis distinguished individuals with toxin-positive C. difficile. C. difficile abundance did not differentiate participants with true CDI from those who were colonized. We identified associations between the gut microbiome and C. difficile toxin gene presence and toxin production. These results highlight the potential for microbiome-informed diagnostics to improve CDI accuracy and guide treatment decisions.
IMPORTANCE
Clostridioides difficile colonizes humans and causes diarrhea in community and hospital settings. C. difficile infection (CDI) is a toxin-mediated disease, and its diagnosis is challenging. The goal of this study was to determine whether differences in the gut microbiome could help distinguish between colonized individuals and those with CDI. We examined stool samples and data from 172 individuals categorized into three groups based on the detection of toxin and, if not detected, whether toxin-encoding genes were present in the C. difficile strain. We identified bacteria, such as Enterococcus faecalis, that were more abundant in people who had used antibiotics. While the diversity of the gut microbiome did not differ by toxin group, specific gut bacteria, antibiotic resistance genes, and metabolic pathways were associated with toxin group. Our findings suggest that considering the full gut microbiome and factors like past antibiotic use could help improve the diagnosis and treatment of CDI.
KEYWORDS: shotgun sequencing, Enterococcus, antibiotics, diarrhea, C. difficile infection
INTRODUCTION
Clostridioides difficile infection (CDI) is a leading cause of antibiotic-associated diarrhea and healthcare-associated infections, with an attributable cost of $6.3 billion annually in the United States (1, 2). The epidemiology of CDI is changing and is marked by increases in the incidence of community-associated infection in the past decade (1, 3). Manifestations of C. difficile range from asymptomatic colonization to fulminant colitis (4). Symptomatic CDI is a toxin-mediated disease, and toxins A (TcdA) and B (TcdB) are major C. difficile virulence factors; these toxins are cytotoxic to colon epithelial cells and can cause extensive inflammation and tissue damage (4).
Accurate diagnosis of CDI is critical for treatment, prevention, and control efforts. However, CDI diagnosis poses significant challenges (5, 6). Current tests for CDI are designed to detect C. difficile and/or toxin genes tcdA and tcdB (7). The reference standards for detection of toxigenic C. difficile, toxigenic culture, and cell cytotoxicity assay (CCA) require 24–48 hours to complete (7). Faster methods include glutamate dehydrogenase (GDH) enzyme immunoassays (EIAs), which detect the presence of C. difficile but cannot distinguish between toxigenic and non-toxigenic strains. EIAs targeting toxins A or B can detect C. difficile toxin production, but have a trade-off of low sensitivity. Diagnostic testing at many laboratories has shifted from phenotypic toxin tests (e.g., toxin EIAs) to PCR-based nucleic acid amplification tests (NAATs). NAAT-based tests can detect toxin-encoding genes; these tests have the advantage of high sensitivity but do not provide information on toxin production (5, 8). Thus, no single test can accurately diagnose CDI, and recommendations suggest two-stage testing for accurate CDI diagnosis (9).
Approximately 9% of hospitalized patients are asymptomatically colonized with C. difficile at the time of admission (7, 10). The high prevalence of C. difficile colonization among hospitalized patients, combined with the high prevalence of diarrhea, which can be due to a range of pathogens and/or non-infectious causes, poses a challenge for determining the clinical and epidemiological implications of positive C. difficile tests (4, 11). From the clinical perspective, inaccurate differentiation between non-toxigenic and toxigenic C. difficile may lead to overdiagnosis and/or overtreatment with antibiotics (5, 11). From an epidemiological and infection control perspective, it is helpful to know whether individuals are colonized with toxigenic strains that can be transmitted to others (4, 12).
The use of antibiotics is one of the main risk factors for CDI (4). Antibiotic use disrupts the gut microbiota, and subsequent microbiota dysbiosis increases an individual’s susceptibility to C. difficile colonization and infection (13, 14). Prior studies have examined relationships between antibiotic use, the gastrointestinal microbiota, and the risk of CDI (15, 16). However, few have utilized shotgun metagenomic sequencing to establish relationships between antibiotics, the microbiota, the antibiotic resistome, and toxin production and gene presence. We hypothesized that microbiome signatures could be used to help differentiate C. difficile colonized patients with diarrhea from those with true CDI. Thus, we conducted shotgun metagenomic sequencing of stool samples from individuals with diarrhea whose stool was submitted for C. difficile diagnostic testing. Individuals with GDH-positive C. difficile test results were categorized into three groups based on the detection of toxin production and, if not produced, whether toxin-encoding genes were present or absent in the C. difficile strain. Clinical, epidemiologic, taxonomic, and resistome data were used to identify relationships between risk factors (e.g., prior antibiotic exposure, previous CDI episode), toxin categories, and the gut microbiome.
MATERIALS AND METHODS
Study design and participants
Yale University’s institutional review board approved this study with a waiver of consent under protocol 2000026568. Stool samples were obtained through a collaboration with Connecticut’s Emerging Infections Program, which conducts C. difficile surveillance in Connecticut (17). Information on testing algorithms and participant toxin group assignments is summarized in Fig. 1. From April 26, 2019, to October 18, 2020, a total of 409 residual stool samples were obtained from individuals with diarrhea symptoms who tested GDH positive for C. difficile at a Connecticut hospital. Phenotypic test results for cytotoxin production (EIA or CCA) were available, and medical chart reviews were conducted for 188 samples. Of these, three individuals were identified with >1 stool sample and had their subsequent samples removed from the study (n = 185). Data extracted from the medical charts included past medical history, use of antibiotics, proton pump inhibitors, histamine type 2 receptor antagonists (H2 blockers), and immunosuppressants, as well as details on CDI treatment and recent contact with healthcare.
Fig 1.
Flowchart diagram summarizing toxin categories. Toxin status is defined as toxin positive or negative and toxin groups: group 1 Toxin+, representing individuals with a test positive for toxin production; group 2 Toxin-/PCR+, representing no toxin production and toxin gene present; and group 3 Toxin-/PCR-, representing samples from individuals colonized with a C. difficile strain that did not carry toxin A or B genes. Purple boxes represent tests conducted. Red and blue boxes represent three toxin groups and toxin status as defined in the study, respectively. All patients exhibited diarrheal symptoms prior to testing for the presence of the bacterium.
C. difficile diagnostic testing, toxin status, and toxin group classification
Participants with GDH-positive C. difficile were classified by cytotoxin status based on a cytotoxin C. difficile diagnostic testing algorithm (9). Cytotoxin production results were based on one of two phenotypic assays, EIA or CCA. Participants whose test results were GDH+ and toxin positive, based on any of the phenotypic toxin assays, were classified as positive for toxin production (Toxin+). Participants whose tests were GDH+ and toxin negative were classified as toxin production negative (Toxin-). Samples that were Toxin- (n = 68) were further subjected to PCR in a research laboratory to determine whether the C. difficile strains carried toxin-encoding genes tcdA or tcdB as described under the section below on fecal specimen processing. Samples that were PCR positive for tcdA or tcdB were classified as Toxin-/PCR+, and those that were tcdA and tcdB PCR negative were classified as Toxin-/PCR-. Thus, there were two “toxin categories” for analyses. Toxin status, defined as Toxin+ or Toxin−, and toxin groups, defined as follows: group 1 Toxin+, representing individuals with a test positive for toxin production; group 2 Toxin-/PCR+, representing no toxin production and toxin gene present; and group 3 Toxin-/PCR-, representing samples from individuals colonized with a C. difficile strain that did not carry toxin A or B genes.
Fecal specimen processing, PCR, and shotgun metagenomic sequencing
Stool samples were collected from the hospital laboratory and stored at −30°C until use. Sixty-eight stool Toxin- samples were cultured for C. difficile and subjected to PCR for the detection of toxin-encoding genes. C. difficile was isolated and cultured from stool samples using cycloserine cefoxitin fructose agar with horse blood and taurocholate (CCFA-HT) selective media plates (Anaerobe Systems, Morgan Hill, CA) and brain heart infusion broth (Becton Dickinson, Sparks, MD) (37 g), agar (14 g), defibrinated horse blood (7%) (Quad Five, Ryegate, MT), L-Cysteine HCl (500 µg/mL) (Calbiochem) non-selective media plates were used to sub-culture isolates. Plates were placed in the anaerobic chamber at 37℃ for 48 hours. Samples were prepared for PCR using a boil lysis method and subjected to PCR using methods described by Persson et al. (18).
For shotgun metagenomic sequencing, stool samples were thawed, and the DNA was extracted using the PureLink Microbiome Purification Kit (Invitrogen). After DNA quantification using the Quant-iT Assay Kit (Invitrogen), samples were prepared for sequencing using the NEBNext Ultra II FS DNA Library Prep Kit for Illumina (New England Biolabs). Shotgun metagenomic sequencing was carried out on an Illumina NovaSeq at the Yale Center for Genome Analysis. Of the 185 GDH-positive samples from unique individuals with corresponding medical record data (see Fig. 1), there were 13 stool samples with inconclusive PCR results and zero metagenomic C. difficile reads; these samples were removed from the analysis. Thus, the final data set for this study consisted of stool samples and clinical and epidemiologic data from 172 individuals.
Bioinformatic and statistical analyses
Btrim software was used to trim and filter out low-quality shotgun metagenomic sequence reads (19). We obtained a median (range) of 27,300,656 (10,751,879–48,186,574) trimmed pairs from our 172 samples. The metagenomic shotgun sequencing data were further processed using the bioBakery 3 tools (20). Microbial species-level taxonomic profiling and the relative abundance of microbial species were calculated using MetaPhlAn 3.0 (20). For each sample, relative abundances sum up to 1, representing 100%. The HUMAnN 3.0 pipeline was used for functional profiling of the microbial community from shotgun metagenomic sequences (20). The antibiotic resistance gene (ARG) online analysis pipeline with the expanded structured ARG (SARG) database v2.0 was used for classification and quantification of ARGs (21). ARG data were normalized using a reference set of essential single-copy genes, and data are presented as resistance genes per prokaryotic cell at either the type (i.e., antibiotic class) or subtype level (i.e., individual gene level).
Metagenomic, clinical, and demographic data were imported into R for statistical, community composition, and differential abundance (DA) analyses (22). Prior antibiotic exposure was defined as any antimicrobial therapy taken in the 12 weeks prior to the date of stool collection. For this study, a case was defined as an incident if the individual did not have a prior CDI in the 8 weeks prior to the date of stool collection. Participants were classified as having a previous CDI episode if medical chart review revealed a CDI episode more than 8 weeks before the date of incident C. difficile stool collection. Recurrent CDI was defined as having CDI episodes ≥ 2 weeks but ≤8 weeks since C. difficile stool collection among individuals with samples positive for cytotoxin production (i.e., Toxin+) (17).
The relationship between any prior antibiotics exposure and prior antibiotics by class on differential phenotypic cytotoxin detection was explored via univariate logistic regression. Prior to any microbiome data analysis, we identified one outlier whose microbiota composition consisted solely of 100% Gardnerella vaginalis and excluded the sample in subsequent ARG, taxonomic, and pathway profiling analyses. We compared both alpha and beta diversity across toxin groups. Shannon diversity (natural log) was calculated as a measure of alpha diversity for each stool sample (23, 24). We used the non-parametric Kruskal-Wallis and Wilcoxon test to compare the median alpha diversity between groups, as appropriate. We used the Bray-Curtis dissimilarity index as the metric for beta diversity, as it has been shown to be able to detect differences between groups with high sensitivity (25, 26). For beta-diversity visualization, we used non-metric multidimensional scaling to condense complex multidimensional microbiome data into a low-dimensional space (27, 28). We further supplemented the analysis of between-group differences in beta diversity using a more robust method, permutational analysis of variance (PERMANOVA) (25, 29, 30) via the adonis2 function in the vegan R package with 4,000 permutations (31), to test whether the overall gut microbiota composition varied significantly by toxin groups. First, we tested the null hypothesis that the centroids or group means were equivalent overall across all groups being tested. Next, we performed a post hoc pairwise comparison to test and determine which pairs might be different from each other while correcting for multiple comparisons.
For the identification of key taxa associated with the outcome of interest, we conducted DA analysis using the microbiome multivariable associations with linear models 2 (MaAsLin2) package (32). MaAsLin2 was selected based on its ability to preserve statistical power while sufficiently controlling for the false discovery rate (FDR) even in the presence of multiple covariates and repeated measures (32). We uniformly removed all-zero features across taxonomic, ARG, and metabolic pathway data sets. For taxonomic and ARG data, we applied a minimum prevalence filter of 10% and excluded features with a low variance (<0.001) or with a mean relative abundance below 1% as part of MaAsLin2 analyses. For metabolic pathway data, we applied a more stringent prevalence filtering of 20% to reduce data noise and enhance data quality (33), due to a high number of features with extremely low variance. The significance level for DA analysis was set to a q-value of <0.25 after the P-values were FDR-adjusted (BH, q-values). A summary of the MaAsLin2 equations used in each analysis is in Supplementary methods S1.
RESULTS
Participant characteristics and toxin group
The characteristics of 172 participants, categorized by toxin group, are shown in Table 1. Sixty-eight percent had positive diagnostic test results indicative of true CDI (i.e., group 1 Toxin+; n = 117). The remaining participants were divided based on PCR-based toxin gene presence; 22 participants had Toxin-/PCR+ tests and were assigned to group 2, and 33 individuals had Toxin-/PCR- tests and were assigned to group 3. The demographic characteristics of the participants, including age, sex, race, and/or ethnicity, did not significantly differ by toxin group (Table 1). A majority of the participants, 83%, had exposure to healthcare. However, healthcare exposure did not significantly differ by toxin group (Table 1). Twelve percent of participants with Toxin+ samples had recurrent CDI; by definition, there were no participants with recurrent CDI who had Toxin-/PCR+ or Toxin-/PCR samples (Table 1).
TABLE 1.
Patient cohort characteristics by toxin groupsa
| Characteristic | Group 1: Toxin+ (N = 117) |
Group 2: Toxin−/PCR+ (N = 22) |
Group 3: Toxin−/PCR-(N = 33) |
P Valueb |
|---|---|---|---|---|
| Age (years) | 0.52 | |||
| Median [IQR] | 66.0 [53, 75] | 63.5 [43, 75] | 63.0 [49, 69] | |
| Sex | 0.80 | |||
| Male | 59 (50) | 10 (46) | 18 (55) | |
| Female | 58 (50) | 12 (55) | 15 (46) | |
| Race | 0.16 | |||
| Asian | 1 (1) | 0 (0) | 0 (0) | |
| Black | 12 (10) | 4 (18) | 10 (30) | |
| White | 93 (80) | 15 (68) | 21 (64) | |
| Unknown | 11 (9) | 3 (14) | 2 (6) | |
| Ethnicity | 0.97 | |||
| Non-Hispanic or Latino | 104 (89) | 20 (91) | 30 (91) | |
| Hispanic or Latino | 12 (10) | 2 (9) | 3 (9) | |
| Not reported | 1 (1) | 0 (0) | 0 (0) | |
| Case definition | 0.05 | |||
| Hospital-acquired | 61 (52) | 18 (82) | 23 (70) | |
| Healthcare-associated | 34 (29) | 1 (5) | 6 (18) | |
| Community-acquired | 22 (19) | 3 (14) | 4 (12) | |
| Prior antibiotics exposure | 0.02 | |||
| Yes | 71 (61) | 8 (34) | 13 (39) | |
| No | 46 (39) | 14 (64) | 20 (61) | |
| Antibiotic treatment for incident CDI | < 0.001 | |||
| Yes | 115 (98) | 10 (46) | 9 (27) | |
| No | 2 (2) | 12 (55) | 24 (73) | |
| Antibiotic (first line) | < 0.001 | |||
| Metronidazole | 2 (2) | 1 (5) | 0 (0) | |
| Vancomycin | 109 (93) | 8 (34) | 7 (21) | |
| Other | 4 (3) | 1 (5) | 2 (6) | |
| No antibiotic treatment | 2 (2) | 12 (55) | 24 (73) | |
| Previous CDI episodec | < 0.001 | |||
| Yes | 12 (10) | 8 (34) | 16 (49) | |
| No | 104 (89) | 14 (64) | 17 (52) | |
| Recurrent CDI | 0.03 | |||
| Yes | 14 (12) | 0 (0) | 0 (0) | |
| No | 103 (88) | 22 (100) | 33 (100) |
CDI: Clostridioides difficile infection.
Toxin: phenotypic detection of cytotoxin production.
CDI episode unknown (1).
Participants differed by toxin group in clinical characteristics such as prior antibiotics exposure, antibiotic treatment for CDI, type of antibiotic for treatment, and previous CDI episode. Notably, the Toxin+ group had a significantly higher proportion of participants with prior exposure to antibiotics and treatment for incident CDI (Table 1). Of concern, a considerable proportion of participants, whose samples were negative for toxin production (Toxin-/PCR+) or toxin genes (Toxin-/PCR-), also received antibiotic treatment for CDI, 46% and 27%, respectively.
The relative risk of CDI has been shown to vary by the type of antibiotic exposure (34). Thus, we sought to examine relationships between antibiotics and toxin status (i.e., Toxin+ vs. Toxin- samples). Any prior antibiotics exposure was associated with a 2.50 (95% confidence interval [CI]: 1.30, 4.88) higher odds of Toxin+ status (Table S1). Having prior exposure to beta-lactam, cephalosporin, or fluoroquinolone antibiotics was also significantly associated with higher odds of Toxin+ status (Table S1). While vancomycin exposure was most common among all antibiotic classes, prior exposure alone was not significantly associated with positive toxin status.
Taxonomic profile of stool samples
A total of 633 unique bacterial taxa were identified in GDH-positive stool samples from participants. A scatter plot highlighting key taxa (species present in ≥60% of samples) showed that Enterococcus faecium and Enterococcus faecalis were among the most abundant species identified across all study participants, regardless of their toxin status or toxin group (Fig. 2A). Among the 27 key taxa identified, we also investigated species-level correlation across each species (Fig. S1). We observed no obvious clustering of species distribution by toxin group (Fig. 2B). Other taxa with high overall relative abundance included Bacteroides species, Escherichia coli, Ruminococcus gnavus, Streptococcus thermophilus, and Akkermansia muciniphila (Fig. 2B).
Fig 2.
Overview of microbiome composition across samples. (A) Scatter plot showing total abundance (X-axis) versus prevalence (Y-axis) of microbial taxa across all samples (n = 171). Species present in ≥60% of samples are labeled as key taxa. (B) Stacked bar plots of species by toxin groups: Toxin+ (n = 116), Toxin−/PCR+ (n = 22), and Toxin−/PCR− (n = 33). Each bar corresponds to an individual sample, and the top 15 most abundant species are annotated with colored bars.
Microbial community structure across C. difficile toxin groups
We compared alpha diversity (i.e., Shannon diversity) across toxin groups (Fig. 3A); no significant differences were observed in alpha diversity across the three groups (Kruskal-Wallis test, P = 0.82). Next, we examined beta diversity across the toxin groups. An ordination plot was created to visualize the microbiome information of all samples relative to other samples (Fig. 3B). We did not identify significant differences in the compositional profile of the gut microbiota by toxin group, either before or after adjusting for prior antibiotics exposure and case definition (adjusted P = 0.22; PERMANOVA; Table S2). Similarly, pairwise comparisons revealed no differences (Table S3). In the adjusted model, we also examined the effects of additional covariates, prior antibiotics exposure, and case definition (hospital-acquired, healthcare-associated, or community-acquired) on beta diversity. PERMANOVA results revealed beta-diversity differences across both variables (case definition P < 0.001; prior antibiotics exposure P = 0.004, Table S2). However, the differences may be an artifact of wide variances and not true compositional differences (P < 0.001 and P = 0.007 variation in dispersion, respectively). Therefore, caution is warranted when interpreting these results.
Fig 3.
Microbial diversity and C. difficile relative abundance across toxin groups and clinical outcomes. (A) Alpha diversity (Shannon index) of the gut microbiota stratified by C. difficile toxin group. (B) Beta-diversity ordination plot showing microbial community composition across toxin groups. No significant differences in overall gut microbiota composition across groups (P = 0.22; PERMANOVA; 0.33 variation in dispersion). (C) Relative abundance of C. difficile across toxin groups. (D) Relative abundance of C. difficile stratified by toxin status. Pairwise comparisons were conducted using the Wilcoxon rank-sum test, with corresponding P-values displayed above bars. Overall group differences were assessed using the Kruskal–Wallis test.
The relative abundance of C. difficile in stool samples is higher in individuals with CDI compared to those who are colonized (35). To further understand C. difficile abundance across different factors, we compared its relative abundance across toxin groups and CDI recurrence among Toxin+ samples. Pairwise comparisons across the toxin groups indicate that participants colonized by non-toxigenic strains (i.e., Toxin-/PCR-) tended to have the lowest relative abundance of C. difficile (Fig. 3C). The relative abundance of C. difficile was not significantly different by toxin status (Fig. 3D) nor among those who experienced CDI recurrence vs did not (Wilcoxon, P = 0.38).
Risk factors: impact of prior antibiotics and previous CDI on the microbiome
Antibiotics are a primary risk factor for CDI, and prior antibiotics exposure differed across toxin groups. We conducted a DA analysis to identify individual species associated with differences in prior antibiotics exposure. Higher relative abundance of E. faecalis distinguished individuals with prior antibiotics exposure compared to those who did not have prior antibiotics exposure (Fig. 4A). The relative abundance of 17 different species was significantly higher in individuals who did not have exposure to prior antibiotics compared to those who did (Fig. 4A). Concurrently, participants without prior antibiotics exposure had higher alpha diversity than those who were previously exposed to antibiotics (Fig. 4B).
Fig 4.
Impact of prior antibiotics exposure on microbial composition, diversity, and ARG associations. (A) DA analysis identifying microbial taxa significantly altered by prior antibiotics exposure. (B) Alpha diversity (Shannon index) of the gut microbiome comparing individuals with and without prior antibiotics exposure. (C) Correlation between Enterococcus species abundance and vancomycin-associated ARG elements.
Given the abundance of Enterococcus species in all our GDH+ samples, particularly among those who had prior antibiotics exposure, we investigated correlations with vancomycin-associated ARG subtypes. We found a strong positive correlation between E. faecium and several vancomycin ARGs, notably vanA (Fig. 4C). Additionally, clusters of genes including vanS, vanH, vanX, and vanR were highly correlated with E. faecium abundance (Fig. 4C). At the antibiotic class level, differences in vancomycin ARGs were not evident, but the abundance of fosmidomycin and kasugamycin was markedly higher among those without prior antibiotics exposure (Fig. S2).
The proportion of participants with a previous CDI episode differed across groups (Table 1). In addition to species-level DA analysis by antibiotic exposure (Fig. 4A), comparison between previous CDI episode (yes/no) showed higher relative abundances of E. coli in individuals who experienced a previous CDI episode (Fig. S3).
Species-level comparisons: previous CDI episode, prior antibiotics exposure, the gut microbiome, and toxin categories
We hypothesized that resolution at the individual species level might be needed to identify differences by known risk factors and across different toxin categories. First, we conducted multiple univariate species-level DA analyses to identify microbial taxa predictive of toxin group or toxin status. There were no taxa identified as discriminant species for toxin status or any of the toxin groups after correcting for multiple comparisons via FDR adjustment (data not shown, q < 0.25 as cut-off).
We conducted a multivariable DA analysis to disentangle relationships between prior antibiotics exposure, previous CDI episode, taxa, and toxin status. Thus, we adjusted for both prior antibiotics exposure status and previous CDI episode as potential confounders in investigating the effect of gut microbiota on toxin status. After adjusting for both factors, three species were identified that discriminated by toxin status, that is, Toxin+ and Toxin groups. A. muciniphila had the strongest association with Toxin+ status, followed by Flavonifractor plautii and Bifidobacterium adolescentis after correcting for multiple comparisons via FDR adjustment (q < 0.25 as cut-off) (Fig. 5). Similar analysis of ARGs at the type-level revealed differences in relative abundance of several ARG types among individuals classified as Toxin− compared to Toxin+ status (Fig. S4).
Fig 5.
Significant microbial taxa associated with toxin status adjusting for prior antibiotics exposure and previous CDI episode. (A) A positive coefficient is associated with a positive Toxin+ status, and a negative coefficient is associated with Toxin– status. Colors indicate the taxonomic family of the microbial feature, and the size of the circle corresponds to the magnitude of statistical significance. Features with a q-value of <0.25 were plotted. (B) Heatmap displaying associations between taxa and additional covariates included in the model (e.g., prior antibiotics exposure, previous CDI episode).
In pairwise comparisons across all three toxin groups, no specific species consistently distinguished individuals in group 1 (Toxin+). However, individuals in group 3 (Toxin−/PCR−) showed elevated levels of Streptococcus mutans across all comparison groups (Fig. S5). Nevertheless, caution is advised in concluding these pairwise comparisons due to their limited sample size.
Metabolic pathway-level comparison
We aimed to gain deeper insights into the microbiome signature differences across toxin groups by examining functional pathway profiles, beyond just taxonomic profiling. Our multivariable DA analysis adjusting for both prior antibiotics exposure and previous CDI episode revealed that the superpathway of purine deoxyribonucleosides degradation was enriched in Toxin−/PCR+ samples when compared to Toxin+ samples, making it the most distinguishing feature (Fig. 6A). From the same multivariable analysis, we show the relationship between individual pathways and covariates (Fig. 6B). This association remained consistent when analyzing by toxin status (Fig. 6C).
Fig 6.
Differential metabolic pathway profiles associated with C. difficile toxin group or toxin status, adjusting for prior antibiotics exposure and previous CDI episode. Across all panels, only pathways with q-values <0.25 are shown. (A) MaAsLin2 results from pairwise comparisons of metabolic pathways between toxin groups. Only significant differences between Toxin−/PCR− and Toxin+ are shown (no significant differences observed for other comparisons). (B) Heatmap displaying associations between metabolic pathways and additional covariates included in the model (e.g., prior antibiotics exposure, previous CDI episode). (C) Boxplot with individual jittered points illustrating the relative abundance of metabolic pathways by toxin status (Toxin+ vs Toxin− groups) based on MaAsLin2 results.
DISCUSSION
Diarrheal symptoms, which often prompt initial diagnostic processes, are not specific to CDI, and often individuals who were thought to have CDI had an alternative etiology for diarrhea (36, 37). Our analysis provides a comprehensive description of antibiotic exposure, the stool microbiome, and C. difficile toxin production and gene presence. Throughout the study, we observed the influence of antibiotic exposure and specific key species on differential toxin production and gene presence. Enterococcus species were closely linked with prior antibiotics exposure, and A. muciniphila abundance distinguished participants with Toxin+ status after controlling for prior antibiotics exposure and a previous CDI episode. Moreover, we found that neither the abundance nor the detection of C. difficile alone is sufficient to discern true CDI cases. We identified key differences in the purine metabolism pathway that distinguish toxin groups, particularly in Toxin−/PCR− patients. Our analysis highlights the complexity of the microbiome in C. difficile-related diseases, and further research is needed to better understand the biomarkers related to toxin production and gene presence.
Ferretti et al. analyzed publicly available shotgun metagenomic sequencing data sets to identify microbiome signatures of CDI; their analyses indicate that the prevalence of C. difficile is frequently overestimated and reinforce concerns regarding overprescribing of antibiotics for suspected CDI (38). In our study, 35% of participants with Toxin− status were treated for “incident CDI” despite not meeting the criteria for true clinical CDI.
Across all our participants, 53% had prior antibiotics exposure. Among all antibiotic classes, vancomycin was the most frequently used, both as a prior exposure and as a first-line treatment for incident CDI (72% of the total population). Our data also revealed a significant enrichment of Enterococcus species among all individuals who were colonized (Toxin−/PCR+ and Toxin−/PCR−) or infected with C. difficile (Toxin+). Moreover, the abundance of E. faecium demonstrated a strong correlation with clusters of vancomycin-associated ARG subtypes. These findings align with previous studies indicating that enterococci thrive in antibiotic-perturbed microbiomes and may play a role in antibiotic-associated diarrhea (38, 39). A murine study by Smith and colleagues found that exposure to antibiotic-resistant E. faecium and E. faecalis resulted in increased toxin production by C. difficile (40). C. difficile can grow as biofilms within the mucus layer (41), and E. faecalis has been shown to exhibit a synergistic effect in biofilm formation with C. difficile (40, 42). Biofilms protect from antibiotics and immune responses and play a vital role in the survival and infection of C. difficile (43). Moreover, biofilms provide an environment conducive to horizontal gene transfer between E. faecalis and C. difficile (40, 44). The transfer of C. difficile genes to enterococci may, in turn, support the expansion and fitness of antibiotic-resistant E. faecalis in the gut (40), underscoring concerns for vancomycin-resistant enterococci resistance.
Our data showed that the abundance of A. muciniphila was higher in individuals with true CDI (Toxin+ status) after controlling for prior antibiotics exposure and previous CDI episodes. A. muciniphila has previously been linked with a healthy gut microbiome (45) and has also been hypothesized to serve as a marker of microbiome dysbiosis associated with recurrent CDI (46). Data from a clinical trial of the microbiome restoration therapy RBX2660 showed that patients whose CDI did not recur after a single dose of RBX2660 had stable and lower (<25%) A. muciniphila abundance after 30 days. In contrast, participants who required repeat doses of RBX2660 had severely perturbed microbiota at days 0 and 7 and greater variation in A. muciniphila abundance; the relative abundance of A. muciniphila exceeded 40% in several samples (46). C. difficile cannot metabolize mucin glycans due to the absence of glycosyl hydrolase enzyme (41, 47). A. muciniphila is a mucin-degrading specialist with a broad range of glycosyl hydrolase enzymes that can degrade mucins that serve as a nutrient source, thereby facilitating the growth of C. difficile (41, 47). The role of A. muciniphila in CDI as either a surrogate marker or contributor to pathogenesis is an important area for further study.
The relative abundance of F. plautii and B. adolescentis was also higher in individuals with true CDI (Toxin+ status). F. plautii degrades flavonoids, which are important anti-inflammatory mediators; low levels of flavonoids may lead to higher levels of inflammation, which may be conducive to C. difficile (48). B. adolescentis has been described as a beneficial microbe and has been used in bacteriotherapy studies of CDI (49, 50). F. plautii and B. adolescentis are examples of taxa that may serve as critical members of the healthy gut microbiota and also contribute to poor outcomes in states of extreme dysbiosis. Alternatively, these associations may be spurious or related to probiotic use.
We identified one distinct metabolic pathway differentiating toxin groups and status, with purine degradation notably higher in the Toxin−/PCR− group than in the Toxin+ group. This specific pathway has been studied in E. coli due to their ability to utilize purine deoxyribonucleosides as carbon and energy sources (51). Purine metabolism pathways are prevalent among gut bacteria, as these pathways are an important source of essential nutrients (52). Studies suggest that purine degradation can foster beneficial interaction for both healthy commensals (52) and also for C. difficile, particularly through the utilization of uric acid (53). C. difficile can metabolize a large number of nutrients for growth, and specific subsets of metabolic pathways may be utilized that allow C. difficile to flourish in a range of dysbiotic microbial communities (54). Additional studies of metabolic pathways involved in C. difficile colonization and pathogenesis may facilitate the identification of biomarkers that can be used in diagnostics.
Our study had limitations. When three-level toxin groups are considered, caution is warranted in drawing definitive conclusions given the limited sample sizes in groups 2 and 3. The stool samples were collected at a single point in time, limiting our ability to establish temporality. As a result, we cannot determine whether the observed interaction between the gut microbiota and the spectrum of C. difficile-related disease manifestations is driven by the gut microbiota influencing C. difficile or if it is the impact of C. difficile on the gut microbiota. We did not include healthy controls; the goal of our study was to identify microbiome signatures related to toxin production and toxin gene presence. Thus, we restricted our studies to individuals who were colonized with C. difficile or experiencing true CDI. Lastly, specific taxa and metabolic pathway information cannot be linked directly. However, by conducting a statistically rigorous DA analysis at the species level using shotgun metagenomics and considering potential confounder considerations, we present sets of important species and their composite functional capabilities. This consolidated approach provides a broader understanding of associations between the gut microbiota and C. difficile toxin production and toxin gene presence. Future diagnostic and therapeutic strategies should consider the gut microbiome and clinical factors such as prior antibiotics exposure and previous CDI episodes in C. difficile-related disease manifestations.
ACKNOWLEDGMENTS
Research reported in this publication was supported by the Centers for Disease Control and Prevention under Cooperative Agreement Number NU50CK000488 and the Connecticut Department of Public Health under contract #2017-0026. This publication does not express the views of the Department or the State of Connecticut. The views and opinions expressed are those of the authors. The authors gratefully acknowledge James Meek. We also acknowledge Keli Sorrentino for data management and the Yale Center for Genome Analysis (YCGA) for high-throughput sequencing services.
Contributor Information
Melinda M. Pettigrew, Email: mpettigr@umn.edu.
Casey M. Theriot, NC State University, Raleigh, North Carolina, USA
DATA AVAILABILITY
The deidentified data that support the findings of this study are available upon request from the corresponding author. The shotgun metagenomic sequencing reads have been deposited with the NCBI Sequence Read Archive and are available under BioProject PRJNA1056768.
SUPPLEMENTAL MATERIAL
The following material is available online at https://doi.org/10.1128/msphere.00435-25.
Methods S1, Figures S1-S5, and Tables S1-S4.
ASM does not own the copyrights to Supplemental Material that may be linked to, or accessed through, an article. The authors have granted ASM a non-exclusive, world-wide license to publish the Supplemental Material files. Please contact the corresponding author directly for reuse.
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Associated Data
This section collects any data citations, data availability statements, or supplementary materials included in this article.
Supplementary Materials
Methods S1, Figures S1-S5, and Tables S1-S4.
Data Availability Statement
The deidentified data that support the findings of this study are available upon request from the corresponding author. The shotgun metagenomic sequencing reads have been deposited with the NCBI Sequence Read Archive and are available under BioProject PRJNA1056768.






