Urban populations from highly industrialized countries are characterized by a lower gut bacterial diversity as well as by changes in composition compared to rural populations from less industrialized countries. To unveil the mechanisms and factors leading to this diversity loss, it is necessary to identify the factors associated with urbanization-induced shifts at a smaller geographical scale, especially in less industrialized countries. To do so, we investigated potential associations between a variety of dietary, medical, parasitological and socio-cultural factors and the gut and saliva microbiomes of 147 individuals from three populations along an urbanization gradient in Cameroon. We found that the presence of Entamoeba sp., a commensal gut protozoan, followed by stool consistency, were major determinants of the gut microbiome diversity and composition. Interestingly, urban individuals have retained most of their gut eukaryotic and bacterial diversity despite significant changes in diet compared to the rural areas, suggesting that the loss of bacterial microbiome diversity observed in industrialized areas is likely associated with medication. Finally, we observed a weak positive correlation between the gut and the saliva microbiome diversity and composition, even though the saliva microbiome is mainly shaped by habitat-related factors.
Humans living in urban areas from highly industrialized countries host less diverse gut microbiomes than those in rural areas from the less industrialized ones. This effect of industrialization (as we refer to it hereafter) has been reported by numerous studies comparing urban areas in Europe or North America with rural ones in Africa, Asia or South America1,2,3,4,5,6,7,8. Loss in alpha diversity is further accompanied by systematic shifts in bacterial composition (see e.g.9,10). Despite crucial implications for human health11,12, the factors responsible for these ecological changes are still unclear. Two main (non-exclusive) hypotheses have been proposed: (i) decreased consumption of dietary fibers13,14 and (ii) improved sanitation and access to medical care (including antibiotics15). In addition, geographical latitude could be a confounding factor, given that it is a proxy for the diversity of environmental bacteria16. Indeed, the only two studies that did not find a loss of diversity with industrialization were studies considering rural populations not living in a warm tropical environment17,18.
To disentangle various factors potentially leading to this observed diversity loss, some authors focused on smaller geographical scales, contrasting urban and rural individuals from the same countries (referred to hereafter as the effect of urbanization). Such studies reported inconsistent results: no significant differences in Russia19 and Nigeria20, some differences in China21, and season and altitude dependent shifts in Mongolia22 and India23, respectively. These discrepancies can be partially explained by different definitions of rural areas used in these studies (from isolated pasturing areas in Mongolia to cities of 100,000 inhabitants in Russia) and by quite small sample sizes in some cases. Interestingly, whereas Winglee et al.21 observed, as expected, a trend towards higher OTU (operational taxonomic unit) and genus richness in rural areas, they found a higher evenness at higher taxonomic levels in urban areas (phylum, class and order). Therefore, urbanization seems to influence the gut microbiome diversity in a less clear-cut manner than industrialization, which is associated with a decrease in diversity regardless of the taxonomic resolution or the diversity measure (richness, evenness or phylogenetic diversity). This finding emphasizes the need to explore complex ecosystems such as human-associated microbiota using multiple diversity measures and taxonomic resolution levels, in order to capture complementary aspects of the studied microbial communities. More recently, Stagaman et al.24 investigated associations between economic factors and the gut microbiome diversity and composition in rural populations in Ecuador and showed that house modernity and power usage negatively correlated with the microbiome diversity. However, as the authors say, their economic metric could be a proxy for other lifestyle factors such as diet or healthcare practices. Estimating the relative importance of these factors thus requires a more comprehensive biological and cultural characterization of the populations under study.
In this regard, the work of Falony et al.25 represents a pioneer study, aiming to identify the factors associated with the variation in the gut microbiome composition in two large cohorts (1106 Flemish and 1135 Dutch subjects) among a large number (503) of covariates. They found that stool consistency, measured on the Bristol stool scale, had the strongest effect on the gut microbiome composition, while medication was the category explaining the largest amount of total variation. One question that emerges from this work is to which extent these results are transferable to other cultural contexts, for instance, to less industrialized populations, where the relationship between hosts and microbes has not been as much perturbed? Notably, highly industrialized populations have mostly lost gut protozoa26, whereas they are likely an important component of the gut ecosystem in less industrialized environments27. We have indeed previously shown that the presence of non-pathogenic gut protozoa from the genus Entamoeba is strongly correlated with an increase in gut microbiome diversity and shifts in composition28, and similar associations have been observed for Blastocystis in various countries29,30,31,32. However, it is not clear how the role of gut protozoa compares in magnitude with the factors identified in the work of Falony et al.25, as they are rare and thus cannot be properly studied in highly industrialized environments.
Finally, very little attention has been dedicated to the impact of urbanization and industrialization on other human microbiomes (e.g., oral, vaginal, skin). Answering this question could however help disentangling the effects that are due to diet (notably to fiber consumption), which should be specific to the gut, to general effects due to over-sanitized lifestyle, which could be shared across body sites. The few studies that have explored the influence of lifestyle on other microbiomes focused on the saliva microbiome and obtained conflicting results. Lassalle et al.33 observed a higher saliva microbiome diversity in rural Philippines than in the urban US, and Nasidze et al.34 found a higher diversity in rural hunter-gatherers from Uganda than in urban individuals from Sierra Leone and DRC, both of which are consistent with the results from the gut. However, African populations were characterized by a less diverse saliva microbiome than rural individuals from Alaska or urban individuals from Germany35, thus opposite to the trends observed for the gut microbiome. Similarly, the saliva microbiome of Native Americans in Oklahoma had lower diversity than the microbiome of neighbouring more urbanized individuals of European descent36. Finally, Clemente et al.3 found no difference between the saliva microbiome of the isolated Yanomami population from Venezuela and individuals from the US (despite differences in their gut microbiome diversity), suggesting no effect of lifestyle. Importantly and contrary to the gut, a more diverse saliva microbiome has been linked with a poorer oral health37,38.
To examine the effect of urbanization on the gut and saliva microbiomes and to identify the factors associated with their variation in a less industrialized setting, we collected fecal and saliva samples of 147 individuals along an urbanization gradient in Cameroon (rural, semi-urban and urban populations, Fig. 1A). We further collected dietary, medical, parasitological and other socio-cultural information for each individual (Supplementary Table 1). We first described the urbanization gradient by identifying the factors that significantly varied across populations, and then we investigated changes in the gut and saliva microbiome diversity and composition based on the 16S rRNA gene amplicon sequencing data. We examined different aspects of diversity by calculating several indices and assessed the effect of OTU clustering level in order to explore multiple, potentially ecologically informative aspects of the data. This study is one of the first to collect a large number of variables describing biological and cultural variation (including diet, medical practices and other socio-economic factors) and to test them for association with diversity and composition of the human microbiome in a country with a minimum level of industrialization.
The urbanization gradient is characterized by differences in diet, habitat and socio-cultural conditions, but not in medical practices or gut protozoa prevalence
In order to get a comprehensive overview of the biological and cultural factors associated with the sampled urbanization gradient (represented by a rural, a semi-urban and an urban population), we performed a multivariate ordination analysis for non-dietary information, dietary 24h-recall (quantifying the nutrients and energy intake in the last 24 hours) and dietary FFQ data (Food Frequency Questionnaire, assessing the average consumption of selected food categories over time) separately.
Non-dietary data included anthropometric traits, information on stool consistency and a number of parasitological, medical, sanitary and ethnographic variables (Supplementary Table 1). Ordination based on these non-dietary variables (Fig. 1B,C, Supplementary Fig. 1) revealed the urbanization gradient along the first ordination axis (R2 = 0.67, p < 10−6), which explained 12.2% of the variability and was associated with habitat-related and other socio-cultural factors (education level, number of children). Specifically, increasing urbanization was characterized by access to electricity, use of tap water as the primary water source and by the presence of cement floor and absence of animals in the house. Urban individuals also attained higher education level and had less children. The second and the third axis explained 6.6% and 6.5% variability respectively, and did not separate samples according to the urbanization level. On the other hand, the second axis distinguished the individuals based on the load of Entamoeba spp. (the most prevalent gut protozoan found in the parasitological analysis, with an overall prevalence of 45%) and the Bristol scale score (describing the stool consistency). Both the second and third axis could further be linked to a variety of medical factors (use of antibiotics, antiparasite drugs and traditional medicine) and smoking.
For the dietary 24h-recall data, the first three PCA axes did not well represent the urbanization gradient, although the third axis was weakly correlated withit (Supplementary Fig. 2, Axis 3 Anova: R2 = 0.13, p = 0.001). On the other hand, PCA on the FFQ data (not collected for the semi-urban population) resulted in a clear separation of rural and urban samples along the first axis explaining 10.7% of the total variability (Supplementary Fig. 3, Anova R2 = 0.48, p < 10−6). The variables associated with this axis were overall concordant with those identified by the v test as differentially represented in the rural and urban population (Supplementary Fig. 3E). Specifically, urban individuals eat more dairy products (industrial yoghurt, kossam, milk), more animal-based food (meat, chicken, insects), as well as more sweets and soft drinks. Rural individuals, on the other hand, eat more root crops (cassava, cocoyam), leaf vegetable and peanuts, but also drink more palm wine.
Overall, the studied urbanization gradient can be mainly described in terms of habitat-related factors (such as sanitary conditions), education level and number of children, as well as by differences in diet, particularly in the amount of processed food, meat and fibers. On the other hand, the prevalence of gut eukaryotes and medical practices seem to be mostly independent of the urbanization level.
Gut microbiome diversity is shaped mainly by gut protozoa and stool consistency
To examine different aspects of non-phylogenetic and phylogenetic alpha diversity, we calculated weighted and non-weighted effective numbers of species or lineages (Table 1). None of the non-phylogenetic diversity measures (0D, 1D, 2D or InfD) nor the phylogenetic lineage richness (0Dph) changed along the urbanization gradient (Fig. 2, Supplementary Table 2). Conversely, dominant lineage diversity (2Dph) decreased by 6% with urbanization level in both the gut and the saliva microbiome. For the saliva microbiome, we also found a 10% decrease in common lineage diversity (1Dph) with increasing urbanization.
We then identified the best predictors of alpha diversity by random forest regression. Depending on the diversity index, the models explained between 12% and 35% of variability in the gut microbiome diversity (Supplementary Table 3, R-squared test values). The most prominent predictors of the gut microbiome diversity were the abundance and/or presence of Entamoeba sp. (for all indexes except 1D and 2D) and the Bristol scale score (for all non-phylogenetic indexes, Fig. 3). Specifically, diversity increased in the presence of Entamoeba sp. and decreased with the Bristol scale score. Given that the load of Entamoeba sp. did not significantly decrease with urbanization, the observed urbanization-associated loss of the dominant lineage diversity (2Dph) in the gut microbiome is likely linked with another, unknown variable(s).
As the dietary FFQ data were only available for the rural and urban samples, we performed additional analyses excluding the semi-urban samples, both with and without the dietary FFQ data. These analyses overall confirmed the above trends despite some minor differences (Supplementary Table 3, Fig. 4).
Saliva microbiome diversity is shaped by habitat-related factors
For the saliva microbiome, only the models predicting 2Dph (complete dataset) and 1Dph (rural-urban subsets) had R-squared values >= 0.1 and were thus considered for interpretation (Fig. 3, Supplementary Table 3, Fig. 4). The strongest predictors of 2Dph in all three data subsets were urbanization level and access to electricity. In the rural-urban datasets, 1Dph and 2Dph were additionally predicted by water source and the type of floor in the house (Supplementary Table 3, Supplementary Fig. 1). As both of these variables and access to electricity were strongly correlated with urbanization in pairwise comparisons (Supplementary Fig. 1, Supplementary Table 4), the observed decrease in saliva microbiome phylogenetic diversity (1Dph and 2Dph) with urbanization (Fig. 2, Supplementary Table 2) might be linked to the differences in habitat-related factors.
Gut microbiome composition is primarily shaped by gut protozoa, stool consistency and urbanization
We aimed both to detect the taxa whose relative abundances changed along the urbanization gradient and to identify the biological and cultural factors that best explain the variability of the gut microbiome. To accomplish the first goal, we analyzed the community composition with ALDEx2 (a tool for the differential abundance analysis of compositional data) and found changes in the relative abundance of 41/282 tested ASVs (Amplicon Sequence Variants) along the urbanization gradient (Supplementary Table 5). Whereas the relative abundance of some genera either consistently decreased (e.g. Succinivibrio, Faecalibacterium, Prevotella, Roseburia, Coprococcus) or increased (e.g. Allistipes, Bacteroides, Clostridium, Butyricicoccus) with increasing urbanization, various unclassified Lachnospiraceae ASVs responded differently to urbanization. In order to identify phylogenetic lineages that are most consistently affected by urbanization regardless of the phylogenetic and taxonomic scale, we performed phylofactorization. The majority of phylofactors were composed of a single ASV, indicating that urbanization-related changes occurred primarily at a fine phylogenetic scale (Supplementary Table 6). Interestingly, 16 phylofactors were composed of one or more Prevotella ASVs that all had consistently higher abundance in rural samples, suggesting that different strains disappear at different rates in response to urbanization. Detailed phylofactorization results can be found in Supplementary Table 6, Fig. 5 and Supplementary results.
To identify the factors that best explain variation in the composition of the gut microbiome, we performed a PCA on the Euclidean distances of clr-transformed data (the equivalent of Aitchison distance, taking into account the compositionality of the sequencing data), followed by single variable testing (envfit) and forward-backward non-redundant variable selection (ordistep). The first three PCA axes explained together 24.9% of the variability in the gut microbiome composition (Fig. 4, Supplementary Fig. 6). Despite the large within-group variation, the urbanization gradient was apparent along the first axis together with the associated ASVs, largely consistent with ALDex2 results (Supplementary Table 5). The second axis distinguished the samples according to Entamoeba sp. abundance; the ASVs with the highest coordinates on the second axis (associated with the samples negative for Entamoeba sp.) belonged to Suterella, Bacteroides, Alistipes and Prevotella, whereas the ASVs with the lowest score on the second axis (associated with Entamoeba carriage) were assigned to Butyrivibrio and unclassified Clostridiales, Ruminococcaceae, Lachnospiraceae and Firmicutes (Supplementary Table 7). Although envfit identified 27 variables as significantly associated with the gut microbiome variation, with the Bristol scale score and several 24h-recall variables at the top, only eight were kept by the ordistep forward-backward selection in the final non-redundant model explaining 21% of total variability. These were, ordered by the effect size: Entamoeba sp. abundance, urbanization level, Bristol scale score, recent intake of vitamin C, sex, type of floor, and amount of recently ingested Na (Fig. 5C, Supplementary Table 8). The analysis of rural-urban data subsets yielded overall concordant results, with some differences, reported in Supplementary Fig. 6 and Tables 7 and 8. It is noteworthy that, if FFQ data were included in the analysis, ordistep retained - among other - the average consumption of palm wine and meat, but not the urbanization level. The fact that the urbanization level was retained in the analysis without the FFQ data suggests that urbanization level at least partially tags dietary differences between populations.
Finally, we identified four enterotypes (gut community types),: F1, strongly dominated by Prevotella; F2, enriched in Ruminococcaceae, unclassified Clostridiales, Lachnospiraceae and another unclassified bacterial genus; F3, which could be considered as a transient type between the first two; and F4, dominated by Bacteroides and Lachnospiraceae (Supplementary Fig. 7). These were differentially distributed between the studied populations, with 74% of rural individuals characterized by enterotypes F1 and F3, 74% of semi-urban individuals by enterotypes F1 and F2, and 59% of urban individuals by the enterotype F2 (Fisher’s exact test < 0.05). A more detailed description and the analysis of enterotypes can be found in the Supplementary results and Supplementary Fig. 8.
Saliva microbiome composition is influenced by urbanization
Regarding the saliva microbiome, the relative abundance of only eight out of 110 ASVs tested by ALDex2 significantly changed along the urbanization gradient (Supplementary Table 5). Specifically, urbanization was accompanied by an increase in the relative abundance of three ASVs from the genera Veillonella, Rothia, Streptococcus and Actinomyces and a decrease in the relative abundance of two ASVs assigned to Fusobacterium and unclassifed Pasteurellaceae. Phylofactorization identified 26 edges as significantly differentiating between the three populations, with nine phylofactors composed of more than one ASV (Supplementary Table 6, observed and predicted changes in relative abundances associated with the first six phylofactors can be found in Supplementary Fig. 5).
The first three PCA axes explained 46% of the variability in the saliva microbiome composition (Fig. 5). The first axis corresponded to a gradient from two Prevotella and one Veillonella ASVs to an unclassified Firmicutes ASV and did not well represent either urbanization or other variables. On the other hand, the second and the third axis partially distinguished between rural and urban samples, with Enterobacteriaceae (2nd axis) and Prevotella (3rd axis)enriched in the rural population (Supplementary Table 6). One-way tests retained 11 variables, with the number of children and age explaining the highest amount of variability, whereas only four factors were kept in the selected non-redundant model: urbanization level, presence of gut eukaryotes, number of children and purging (Fig. 5C). The results based on rural-urban dataset were different: if FFQ variables were included, ordistep kept the average consumption of soya and cassava sticks, type of floor, presence of animals in the house and type of toilets; without the FFQ variables, only the sanitary conditions were retained (Supplementary Fig. 6).
Saliva microbial communities in the studied populations could be grouped into two types (stomatotypes): S1, dominated by Prevotella and Streptococcus and S2, enriched in Enterobacteriaceae. The urban population, with 84% of individuals hosting the S1 stomatotype, significantly differed from the semi-urban and rural population, where both stomatotypes were equally represented (Fisher’s exact test, rural - urban: p = 0.005, semi-urban - urban: p = 0.054, Supplementary Fig. 7). More details can be found in Supplementary results.
Relationship between the gut and saliva microbiome
To examine the relationship between the gut and saliva microbiome, we first calculated Pearson correlations between the alpha diversity values within each individual. We found weak positive correlations between the species and lineage richness (0D and 0Dph) as well as InfD of the gut and saliva microbiome (Pearson r = 0.23 and r = 0.22, respectively, Fig. 6, Supplementary Fig. 9). We then asked if the gut and saliva microbiome of an individual shared more species than a random gut-saliva microbiome pair. This was indeed the case (Supplementary Fig. 10, standardized effect = −0.30, p = 0.003,), but the effect became only marginally significant when permutations were restricted to within urbanization levels (standardized effect size = −0.14, p = 0.052). Subsequently, we checked if the similarity between the gut and saliva microbiome varied across the urbanization levels. We found that the gut and saliva microbiomes of rural individuals shared slightly less ASVs than the microbiomes of semi-urban and urban individuals (Fig. 6, F2, 92 = 19.95, p < 10−8, 0.98% decrease). Conversely, we found no significant influence of the urbanization level on Bray-Curtis dissimilarities between the saliva and gut microbiome, despite a decreasing trend (F2,92 = 2.96, p = 0.056). Additional analyses exploring the effect of OTU clustering on the conclusions of the study can be found in the Supplementary Figs. 11–13 and Supplementary results.
By using detailed biological and cultural characterization of the populations under study, we show that the presence of a commensal gut eukaryote Entamoeba sp. is the strongest determinant of gut microbiome diversity and composition in a minimally industrialized country. Gut protozoa thus appear as an important factor to consider when studying the ecology and evolution of the gut ecosystem. As the studied populations did not differ in either Entamoeba sp. prevalence, gut microbiome richness or medical practices (despite the differences in diet), we propose that the loss of microbiome diversity in highly industrialized countries might be partially explained either by (i) the loss of gut eukaryotes or (ii) differences in medication.
Whereas the direction of compositional shifts (such as decrease in Succinivibrio or Prevotella, and increase in Bacteroides or Allistipes) along the urbanization gradient was consistent with those previously observed when comparing populations with different industrialization1,3,5 or urbanization20,21,23,39 levels, we found little evidence of diversity loss, which usually accompanies industrialization1,2,3,4,5,6,7,8. Together with other studies reporting inconsistent findings regarding the difference in diversity between neighbouring rural and urban populations20,21,23, this suggests that the bacterial diversity loss might mostly occur between urban areas from minimally industrialized countries and urban areas from highly industrialized countries. Interestingly, this might also be the case for commensal gut eukaryotes, as the prevalence of Entamoeba sp. did not differ significantly between our urban and rural areas. Industrialization is thus accompanied both by a loss of bacterial gut microbiome diversity and by disappearance of Entamoeba spp. (both changing only slightly along the urbanization gradient studied here), suggesting that these two processes could be directly or indirectly related to each other.
Knowing that the presence of Entamoeba sp. is the strongest determinant of the gut microbiome diversity, it is indeed possible that the loss of gut eukaryotes might partially explain the loss of bacterial diversity in highly industrialized countries. Although most species of the genus Entamoeba are non-pathogenic and seem to be common residents of the healthy human gut in developing countries26, very little is known about their global prevalence40, and even less about their relationship with the gut bacterial microbiome27,41. In addition, none of the previous studies focusing on the effects of urbanization or industrialization examined diversity of the protozoan symbionts. Alternatively, as our urbanization gradient mostly represents changes in terms of diet and habitat, but not medication, is is tempting to propose that the loss of both bacterial and eukaryotic diversity in highly industrialized and urban environments is mostly due to changes in medical practices, such as antibiotics use. Finally, we did observe a decline in abundance-weighted phylogenetic diversity (2Dph), which is more sensitive to subtle changes in environmental conditions than richness measures38. This small but significant decrease might represent an early response to urbanization-related changes in lifestyle, for example due to changes in diet.
Our observation that the stool consistency is another strong predictor of gut microbiome diversity and composition is consistent with previous findings from industrialized populations25,42. Interestingly, although the stool consistency explained the largest portion of variability in the gut microbiome composition when tested separately, it was only the third best factor in the final redundant model, probably because of interactions and correlations between the tested covariates. Strong correlations between the dietary variables, which had the second largest combined effect on the gut microbiome composition, could also explain why the exact selected variables vary between the data subsets (complete vs. rural-urban). For example, the intake of vitamin C was strongly correlated with the amount of alcohol, which is more likely to have an effect based on the findings from industrialized populations25, but the former variable was selected as the most important. Finally, the inclusion of FFQ data, describing the average diet, resulted in the exclusion of the urbanization level from the non-redundant models for the rural-urban data subset, suggesting that the urbanization-related differences in composition could be to a large extent explained by dietary shifts, contrary to the findings of Stagaman et al.24.
Human saliva and gut are ecologically distinct habitats and we were surprised to observe an urbanization-related decrease in abundance-weighted phylogenetic diversity (describing community structure) for both gut and saliva microbiome, considering that each is shaped by different set of factors. Therefore, this decrease seems to be associated with different processes in each case rather than with a common response of the two microbiomes to the changes in lifestyle. Similarly, it is interesting that we observed a positive relationship between the species (and lineage) richness of the two microbiomes, considering that the diversity of the gut and saliva microbiome seems to be related to health in opposing ways11,38. Still, this positive correlation could be related to the degree to which individuals are exposed to environmental bacteria. The higher proportion of shared species within individual than in a random gut-saliva pair indeed provides some support for the role of the environment as a source of colonization for the human microbiome. Interestingly, the proportion of shared species within indvidual decreased with the urbanization level (Fig. 6), suggesting a difference in dispersal dynamics between the populations as well as different effect of urbanization on the factors shaping the rare portion of each of the two microbiomes. Although seeding from oral microbiome seems to occur normally in healthy humans43,44, excessive colonization of the gut by oral bacteria has been associated with disease45. It is noteworthy that we observed different proportions of shared species depending on the enterotype, suggesting that enterotypes might differ in their resistance to colonization by external bacteria.
In our analysis, we were faced with challenges due to complexity of the dataset, comprising many correlated and interacting variables. In our decisions regarding e.g. appropriate thresholds for the variable selection in the random forest regression or definition of strong correlations, we chose to be strict in order to minimize false positives and avoid over-interpretation. Potential issues with correlations and interactions are well illustrated by the factors associated with the saliva microbiome composition: whereas it is conceivable that habitat and sanitary conditions46, diet33 or age47 shape the saliva microbiome, the fact that purging, gut eukaryotes and number of children are among the top predictors is puzzling. It is thus likely that at least some of these factors tag other correlated (known or unknown) variables or variable interactions. Despite these issues, by quantifying the correlations between the variables and by using (where possible) a random forest regression method that can deal with correlated predictors48,49, we were able to identify potentially important determinants of gut and saliva microbiome diversity and composition in a minimally industrialized country. In order to improve our understanding of the factors that shape the human microbiome and to resolve the correlations between them, it is necessary to examine and understand the role of individual factors in controlled studies, including studies on animal models. This should be complemented by the studies with a sampling design such as in33 or19, with multiple urbanization/industrialization gradient replicates, and by collecting a wide variety of contextual data, as done here and in Stagaman et al.24.
In conclusion, urbanization was associated with minor shifts in diversity of the gut and saliva microbiome, but also with changes in the gut microbiome composition that were reminiscent of those associated with industrialization. Although some of the important factors shaping the gut microbiome, such as stool consistency and diet, are the same as in industrialized populations, gut eukaryotes (Entamoeba sp.) represent the major determinant of diversity and composition here. This may be one of the main confounders when comparing industrialized (virtually gut-eukaryote free) and non-industrialized populations. In order to advance our understanding of how industrialization affects the human microbiome, we need to account for these confounders, for example by routinely collecting more cultural data as well as by including parasitological information. Luckily, microscopic analyses of the fecal samples are not necessary if metagenomics data is collected, as parasitological screening can be performed from genomic data26.
Ethics approval and consent to participate
The research permits, including the appropriate ethic approvals, were obtained for this study from the CNERSH (Comité national d’Ethique de la Recherche pour la Santé Humaine) in Cameroon (Approval N°2017/05/900), as well as from regional health districts (Centre region, Approval N°0061). We further obtained an ethical approval from the French CPP (Comité de Protection des Personnes, approval N°2016-sept-14344), as well as the authorization to import and store these samples from the French Ministry of Higher Education and Research (N°IE-2016-876 and DC-2016-2740, respectively). Finally, we obtained the authorization to store personal data in France from the CNIL (Commission Nationale Informatique et Libertés, N°1972648). We obtained the informed consent of each participant for contributing to this research and publishing the associated-data. Consent for publication is not applicable. All research was performed in accordance with relevant guidelines and regulations.
Sampling and collection of contextual data
We sampled 147 adult volunteers at three locations in Cameroon (Fig. 1A), representing an urbanization gradient: 81 individuals in Ngoantet (rural), 34 in Mbalmayo (semi-urban) and 32 in Yaoundé (urban), after obtaining their informed consent. The participants declared being currently healthy, i.e. not taking medication for any infectious or metabolic disease or suffering from specific symptoms (e.g. fever). They were between 18 and 65 years old and were not related at the second degree. They self-collected the feces during the morning in sterile recipients provided by us (Medline stool containers). We then placed app. 3 g of the fecal samples into 60 mL containers with RNAlater. For saliva, the participants spit 2 mL of saliva into a 15 mL falcon tube, to which we added the same volume of a homemade buffer (5 mM TRIS, 5 mM EDTA, 5 mM sucrose, 10 mM NaCl, 1% SDS, pH = 8).
In addition, we recorded contextual information (metadata) about the participants (Supplementary Table 1) in collaboration with local investigators and trained research assistants. Specifically, we collected dietary information using a quantitative 24-hour recall questionnaire (recording the amount of all the items the individual has eaten during the last 24 hours, which is then transformed into the amounts of nutrients and energy ingested) and a qualitative food frequency questionnaire (FFQ, reporting how often the selected types of food were consumed during the last month50). The FFQ data were collected only for the rural and urban population. Non-dietary information including medical (use of antibiotics, antiparasitics, and traditional medicine) and other socio-economic and socio-demographic variables (water source, type of floor, animals in household, access to electricity, smoking, number of children, education) were collected using questionnaires. Only the animals that were declared by the participants to live in the house were considered as the animals in the household and included: cats, dogs, guinea pigs, parrots, goats, pigs, ducks and poultry. We did not consider the presence of mice. For smoking habits, we grouped individuals into five groups: non-smokers (“0_non”), “1_recent”, who started smoking during the last year, “2_medium”, who have smoked for less than 5 years, “3_longtime” - smoking for 5+ years, less than 10 times a day and “4_longtimeHeavy” - smoking for 5+ years, 10 or more times a day.
Anthropometric traits (height and weight) were measured using standardized techniques. The Centre Pasteur du Cameroun furthermore performed a microscopic analysis of the fecal samples to identify the gut eukaryotes (with a bias toward the identification of potentially pathogenic species, i.e., worms and Entamoeba sp.). For Entamoeba sp., we grouped individuals in categories depending on the output of the microscopic analysis as follows: “0_ none” if no cyst nor any trophozoites was seen; “1_rare” if only rare cysts were observed; “2_some” if only few cysts or few trophozoites were observed; “3_abundant” if numerous cysts and/or trophozoites were observed. Finally, we estimated the Bristol stool scale score by visually assessing the stool consistency (a proxy for colonic transit time and water content51).
DNA extraction and sequencing
App. 250 mg of fecal material was disrupted by bead-beating and DNA was subsequently extracted with the MOBIO PowerFecal DNA isolation kit (MOBIO Laboratories, Carlsbad, CA, USA) according to the manufacturer’s protocol. DNA from the saliva samples was extracted following the protocol of Quinque et al.52. The extracted DNA was quantified with NanoDrop (ThermoScientific). Sequencing libraries targeting the V4 region of the 16S rRNA gene were prepared by the MOC core facility at the Broad Institute, Cambridge, MA, USA and sequenced as 150 bp paired-end reads in two runs on an Illumina MiSeq. 300 (as described in53), resulting in an average of 61,617 ± 43,997 (st. dev.) raw reads per sample (Supplementary Table 9).
We imputed missing values in the contextual data using the missForest R package56. In order to assess the strength of pairwise correlations between the variables, we calculated Pearson’s r for pairs of numerical variables, Cramer’s V for categorical predictors (using the rcompanion package57 and omega for numerical-categorical combinations. We disregarded all correlation coefficients for which the t-test, chi-square test or Kruskal-Wallis test (for numerical, categorical and numerical-categorical variables, respectively) were not significant at alpha = 0.05. In addition to the urbanization level variable, we analyzed 51 variables collected in all three populations: 28 dietary variables from a 24h-recall questionnaire and 23 non-dietary variables. We analyzed 49 additional dietary FFQ variables for the urban and rural populations only. The presence of Entamoeba sp. and smoking habits were encoded both as binary, as well as ordered factors (specifying Entamoeba sp. load and smoking intensity and duration), which resulted in a total of 25 non-dietary variables tested for correlations. After correcting for multiple testing, 403 out of 1431 (28%) and 555 out of 5253 (11%) pairwise correlations between these variables were significant in the complete and rural-urban dataset, respectively (alpha = 0.05, Supplementary Table 4). Strong correlations (abs(Pearson) >= 0.8, Cramer’s V or Omega >= 0.4) were mainly found between 24h-recall dietary variables and between habitat-related (e.g. sanitary) variables (Supplementary Fig. 1). In addition, the urbanization level was associated with some habitat-related variables, including water source, access to electricity, type of floor and presence of animals in the house. The inclusion of the dietary FFQ data (and omission of semi-urban samples) revealed some additional correlations, notably between the urbanization level (or some of the associated habitat-related variables) and: education level, number of children and consumption of meat, cassava and peanuts.
In order to explore the multivariate aspects of the contextual data and to identify the factors that best describe the urbanization gradient, we used the FactoMineR package58. We first performed a factor analysis of mixed data (FAMD) with all non-dietary variables. The categorical variables representing the ordered factors were duplicated and one version was coded as a numerical while the other was coded as a categorical variable. We performed a separate PCA on 24h-recall dietary data normalized by total energy input, as well as on the FFQ data for the rural-urban data subset only. In each case, the correlation coefficient between the ordination axes and urbanization level were calculated with dimdesc in order to statistically test the representation of the urbanization gradient by the axes. In addition, we tested the association between FFQ data and urbanization level with the v test from the same package (function “catdes”).
Sequencing data quality control, taxonomy assignment and OTU clustering
Sequences were denoised using dada259 according to the authors’ recommendations. First, the reads were processed with the filterAndTrim command in order to remove phiX spike-in and reads with ambiguous bases, to truncate reads at the first base with quality score <= 2 and to filter reads with more than 2 expected errors. The sequences were then dereplicated with the derepFastq function. Subsequently, the error rate was estimated from a subset of 1,000,000 reads for each run separately using the learnErrors function. These error rate estimates were used in the actual denoising function, dada, run with the option pool = T. The denoised forward and reverse reads were merged with mergePairs command in order to obtain amplicon sequence variants (ASVs). Finally, we created input files for further processing in mothur55: a fasta file and a group file (assigning sequences to samples). In summary, 83% (12 800 410/15 398 557) of raw reads passed quality control and denoising steps (Supplementary Table 9). We removed 11 out of 250 samples due to low number of reads (<1500). The remaining 239 (141 fecal and 98 saliva) samples contained on average 53 540 reads (±34 540).
We used mothur to assign taxonomy, remove non-bacterial sequences and cluster OTUs, following the MiSeq standard operating procedure60. Briefly, we classified sequences with mothur implementation of RDP classifier61 using the RDP Release 11 taxonomy62 with 80% confidence cutoff and filtered out unclassified and non-bacterial sequences. We aligned the sequences to the V4 region of the SILVA v132 reference alignment63 and removed the chimeras with CATCh64. We used OptiClust65 with Matthews correlation coefficient (MCC) optimization to create 85–99%ID OTUs at 0.01 steps and applied 80% confidence cutoff for the consensus OTU taxonomy. OTU representative sequences were defined as the sequences with the smallest average distance to all the other sequences within a given OTU.
In order to explore the effect of OTU clustering method, we used also another, phylogeny-based approach, bdtt66, which creates the OTUs by slicing of a phylogenetic tree (whose construction is described below) at a specified evolutionary distance. We sliced the tree in the range 0.01–0.15 branch length at 0.01 steps. We modified the original bdtt script in order to add the new, sliced tree and the OTU table to the output. The consensus taxonomy was found as the lowest common ancestor of all sequences within an OTU.
The number of reads and ASVs per sample before and after quality control are reported in Supplementary Table 9. The number of reads and OTUs before and after filtering for each combination of clustering method and cutoff are listed in Supplementary Table 10. We identified in total 4,078 ASVs (grouped into 246 genera), 2,977 of which were found in the fecal microbiome (209 genera) and 2,025 in the saliva microbiome (198 genera).
The phylogenetic tree was created with RaxML67 following the protocol described in Stamatakis68. We imposed the monophyly of the classes within Proteobacteria on the tree topology as described in Groussin et al.66. We ran 100 independent fast tree searches with GTRGAMMA model, performed a bootstrap analysis (with autoMRE option, which automatically determines how many replicates are needed to get stable support values, in this case 550 trees) on the best tree and created a MR consensus tree. All independent trees were unique and the tree diversity was high (average Robinson-Foulds topology distance = 0.5029), indicating an unstable topology. This was further supported by low relative tree certainty from the bootstrap analysis (0.150089). Still, the best tree was significantly better than the suboptimal ones according to the Shimodaira-Hasegawa test69. Although the results of phylofactorization differed somewhat depending on the tree (not shown), they were overall congruent, so we used the best tree in all analyses (phylogenetic diversity, bdtt OTU clustering and phylofactorization).
Alpha diversity estimates
We calculated rarefactions curves for Good’s coverage and non-phylogenetic alpha diversity indices (observed species, Shannon’S H, inverse Simpson and Berger-Parker dominance) with 1000 iterations at 1000 sequence steps in mothur55. Based on the rarefaction results (not shown), we chose a subsampling depth of 6500 reads per sample for calculating the average (200 replicates) of the above alpha diversity indices. We then transformed these values into the effective number of species as described in Jost70. Effective number of species is the number of species in a perfectly even community that results in a given value of a diversity index. Diversity indices within this framework are mathematically defined as Hill numbers of different order (q) and can be linked to the more traditionally used richness and dominance/evenness indices. The order, q, defines how much weight is given to the abundant species: q = 0 ignores the abundance altogether (and is equal to species richness), q = 1 weighs the species exactly according to their abundance (and corresponds to exp(Shannon’s H)), q = 2 is the same as inverse Simpson index and gives emphasis to dominant species, whereas q = Inf corresponds to the inverse of Berger-Parker dominance, and thus depends only on the relative abundance of the most abundant species. The advantage of these indices is that they are intuitive and easily interpretable: they have common units and possess doubling property (i.e. diversity of a union of two communities with completely distinct species is the sum of diversities of the two component communities). Jost70 refers to these diversity indices as “diversity of order 0, 1, 2”. We use here their mathematical denotations - 0D, 1D, 2D and InfD - for brevity.
Chao et al.71 developed a corresponding Hill-number framework for phylogenetic diversity. The main idea is the same, but here the diversity is defined as effective number of lineages, corresponding to the phylogenetic diversity of a perfectly even community composed of perfectly distinct species. We used the hillR R package72 to calculate average phylogenetic diversity indices of order 0, 1 and 2 of 20 dataset replicates subsampled to 6500 reads/sample. We refer to these indices as 0Dph, 1Dph, 2Dph..
Filtering for beta diversity analysis and community type determination
In order to get rid of the noise and to reduce the complexity of the dataset, we performed a two-step unsupervised filtering implemented in the PERFect package73. Briefly, the method compares the total covariance of the community data (“OTU table”) before and after removal of a taxon. This “difference in filtering loss” is then compared with a null distribution and the taxon is retained or discarded for a given significance level alpha (here alpha = 0.1). Based on the empirical evidence and authors’ suggestions, we assumed that at least 50% of taxa were not informative and therefore fitted a skew-normal distribution to the observed filtering loss values. In the first step, called simultaneous filtering, the taxa are ordered according to the number of occurrences and filtered sequentially as long as the filtering loss values come from the null distribution; in the second step, called permutation filtering, the taxa are ordered according to the p-values from the first step and filtered based on an additional permutation step (1000 replicates) that ensures that only the taxa that are uninformative for any combination of retained taxa are removed. We filtered the gut and saliva microbiome datasets separately. Filtering for beta diversity analyses resulted in 282 ASVs for the fecal and 110 ASVs for the saliva dataset (Supplementary Tables 9 and 10). This filtering step reduced the number of reads by 31% and 9% in the fecal and saliva datasets respectively, while eliminating on average 90% and 88% of the ASVs/OTUs/genera, regardless of the clustering method and cutoff.
As the compositional methods that we used to statistically analyze the data do not allow zero values, we replaced zeros utilizing the Bayesian multiplicative replacement function (cmult.repl, method = “GBM”) implemented in the zCompositions R package74.
For distance-based analyses, we performed a centered log ratio (clr) transformation75 implemented in the CoDaSeq R package76,77 and calculated the Euclidean distances, corresponding to Aitchison distances of raw compositional data78. For community type determination, we grouped the non-filtered ASV dataset at the genus level with the phyloseq “tax_glom” command79.
Statistical analysis: microbiome diversity and composition along the urbanization gradient
To examine how the human microbiome diversity changes along the urbanization gradient, we analyzed the gut and saliva microbiome separately.
For alpha diversity, we fitted generalized least squares (gls) linear models with the package nlme80, with weights allowing different variances for each population in case of heteroscedasticity, i.e. if the Levene’s test of homogeneity of variance (car package81) was significant at alpha = 0.05.
To identify the taxa (ASVs and OTUs) whose relative abundances differed between the populations, we used the ALDEx2 package76,82. We considered the taxa as differentially abundant only if Benjamini-Hochberg adjusted p-values of both Kruskal-Wallis and glm test were significant (p <= 0.05).
Finally, in order to identify the lineages that most predictably vary along the urbanization gradient regardless of the classification level, we performed a phylofactorization using the phylofactor package83, with a custom objective function (the same gls model as used in the alpha diversity analysis), F-statistic as a criterion for choosing the best edge, and KS test as the stopping function.
Statistical analysis: community types
In order to classify the microbiomes into the optimal number of categories, we performed Dirichlet-multinomial mixture (DMM) modelling84 on the genus-level data with the DirichletMultinomial package85. We chose the optimal number of components based on the Laplace goodness-of-fit of models with one to ten components. We calculated associations between enterotypes (gut community types86) and stomatotypes (saliva community types46), as well as between the community types and urbanization using Fisher’s exact test as in44.
Statistical analysis: factors associated with community diversity and composition
As food-frequency questionnaire (FFQ) data were not available for semi-urban samples, we performed each of the following analyses three times: for all samples without FFQ data, and for rural-urban samples with and without FFQ data.
The metadata that we collected included both numerical and categorical, often correlated variables (Supplementary Table 4 and Fig. 1). As it is often not trivial to decide which of the correlated factors are important (representing a problem for stepwise variable selection) and as we wanted to make as few assumptions about the data as possible (e.g. linearity), we used random forest classification and regression for the prediction of community types and alpha diversity, respectively. Random forest regression/classification identifies the best set of predictors, without assuming any particular relationship between the independent and response variables. We used conditional forest algorithm87 implemented in the partykit package88. We followed the guidelines from48 and calculated conditional variable importance with the party package and cutoff = 0.249 in order to avoid biases due to different scale of predictors and correlations between them. We used the caret package89 to split the dataset into a training (80%) and test (20%) subsets and to find the best value for the “mtry” (i.e. available number of variables for splitting at each node) parameter. We used the minimization of RMSE (root mean square error) as the selection criterion for regression and the maximization of Cohen’s Kappa for classification. We ran ten independent iterations on each dataset to get realistic estimates of the mean and variability of the variable importance and the goodness of fit. As there is no clear cutoff for variable selection based on their importance, we applied several approaches. The most relaxed approach was the inclusion of random variables in the models: the factors with lower mean importance than the random variable with the highest value were considered unimportant. The second approach was to keep all the variables with a mean importance above the 95% quantile of all mean importance values. The final approach was to split the mean importances into two groups by kmeans clustering. In the last two approaches, we discarded all predictors if any of the random variables was in the “important” group. We used both variable importance and goodness-of-fit estimates (including R-squared and variance explained by the model). If the proportion of the variance explained or the model accuracy was low (R-squared < 0.1 or Kappa < 0.3), we did not interpret the results.
We analyzed potential associations between the community composition and the metadata by a distance-based approach inspired by Gloor et al.90 and Falony et al.25. Briefly, we performed a Principal Component Analysis on the equivalents of Aitchison distances with the package vegan91. We found the variables significantly associated with the first three axes of variation using the envfit function. If some of the significant variables were correlated (correlation coefficient >= 0.8, Supplementary Table 3), we selected the one that explained more variation in envfit and discarded the rest. We then used these selected variables as a scope for ordistep (bidirectional) variable selection. Finally, we identified the ASVs (or OTUs) whose coordinates were in the lower 2.5% and the upper 97.5% quantile on the first three PCA axes as well as those with the distances in the 2.5% and the upper 97.5% quantile from the coordinates of the selected environmental variables (calculated with the cdist function from the rdist package92.
Statistical analysis: differences between the gut and saliva microbiome
We investigated a potential correlation between the gut and saliva microbiome diversity within individual using Pearson’s r coefficient, with nonparametric bootstrap 95% confidence intervals calculated with the boot package93,94. In order to determine if the gut and saliva microbiome within an individual share more species than expected by chance, we compared the observed within-individual beta diversity values (both Bray-Curtis and species turnover measure that accounts for the differences in species richness between the samples; the measure varies between 1 for identical communities and 2 for completely distinct communities95) with the null distribution created by shuffling the sample labels 10 000 times. We either used free permutations or allowed permutations only within the population, to account for the differences between them. We calculated the p-values as observed rank/10 001 and the standardized effect size as (observed mean - random mean)/random standard deviation.
All full and filtered datasets used in our study are stored as phyloseq79 objects or tables and available on Figshare. The raw data are deposited in European Nucleotide Archive under the accession number PRJEB30836. Other datasets and alignments that were generated and used within the current study are available from the authors upon request.
All scripts used in the study are available from the authors upon request.
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We thank the technical platform “Paléogénomique et génétique moléculaire” of the MNHN at the Musée de l’Homme (Paris, France) for their assistance with the processing of the fecal and saliva samples, as well as the Centre Pasteur Cameroon for their help with the parasitological analyses. This work was supported by an ANR grant (MICROREGAL, ANR-15-CE02-0003), a CNRS INEE grant (PEPS MiOr) as well as grants from the Center for Microbiome Informatics and Therapeutics at MIT and the Rasmussen Family Foundation to the Global Microbiome Conservancy (http://www.microbiomeconservancy.org).
The authors declare no competing interests.
Publisher’s note Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.
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Lokmer, A., Aflalo, S., Amougou, N. et al. Response of the human gut and saliva microbiome to urbanization in Cameroon. Sci Rep 10, 2856 (2020). https://doi.org/10.1038/s41598-020-59849-9
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