Abstract
It is presently unclear how much individual community members contribute to the overall metabolic output of a gut microbiota. To address this question, we used the honey bee, which harbors a relatively simple and remarkably conserved gut microbiota with striking parallels to the mammalian system and importance for bee health. Using untargeted metabolomics, we profiled metabolic changes in gnotobiotic bees that were colonized with the complete microbiota reconstituted from cultured strains. We then determined the contribution of individual community members in mono-colonized bees and recapitulated our findings using in vitro cultures. Our results show that the honey bee gut microbiota utilizes a wide range of pollen-derived substrates, including flavonoids and outer pollen wall components, suggesting a key role for degradation of recalcitrant secondary plant metabolites and pollen digestion. In turn, multiple species were responsible for the accumulation of organic acids and aromatic compound degradation intermediates. Moreover, a specific gut symbiont, Bifidobacterium asteroides, stimulated the production of host hormones known to impact bee development. While we found evidence for cross-feeding interactions, approximately 80% of the identified metabolic changes were also observed in mono-colonized bees, with Lactobacilli being responsible for the largest share of the metabolic output. These results show that, despite prolonged evolutionary associations, honey bee gut bacteria can independently establish and metabolize a wide range of compounds in the gut. Our study reveals diverse bacterial functions that are likely to contribute to bee health and provide fundamental insights into how metabolic activities are partitioned within gut communities.
Author summary
Honey bees are important pollinators that harbor a relatively simple gut microbiota with striking parallels to the mammalian system. This makes them relevant models to study gut microbiota functions and their impact on host health. We applied untargeted metabolomics to characterize metabolic changes induced by the gut microbiota and to characterize the contributions of the major community members. We find that the gut microbiota digests recalcitrant substrates derived from the pollen-based diet of bees. Most metabolic changes could be explained by the activity of individual community members, suggesting substrate specificity and independent metabolic functions. We did identify some cross-feeding interactions between species, including for pyruvate. Our study provides novel insights into the functional understanding of the bee gut microbiota and provides a framework for applying untargeted metabolomics to disentangle metabolic functions of gut bacteria.
Introduction
Metabolic activities of the microbiota are key for symbiotic interactions in the gut and impact health and disease of the host in manifold ways. Gut bacteria facilitate the breakdown of refractory or toxic dietary compounds [1–3], produce metabolites that promote host growth and physiology [4–7], and modulate immune functions in the gut [8] and other tissues [9,10]. Moreover, metabolic activity is the basis for energy and biomass production, resulting in bacterial growth and the occupation of ecological niches conferring colonization resistance against pathogenic microbes [11]. Substrates of gut bacteria predominantly originate from the diet of the host [2,12], making diet the major modulator of the composition and metabolic activity of the gut microbiota [13,14].
The substantial metabolic potential of the animal gut microbiota has been profiled by the direct sequencing of functional gene content (i.e., shotgun metagenomics) [15–18]. However, it is challenging to predict functional metabolic output from such sequencing data. With recent advances in the coverage and throughput of untargeted screening metabolomics [19–21], it has become feasible to quantify metabolic changes in microbiota or host tissues at large coverage and throughput. Besides identifying metabolites connected to human health and disease [22–30], untargeted screening metabolomics holds considerable promise to unravel metabolic functions of individual microbiota members in animals with divergent dietary preferences. However, such mono-colonization studies are complicated by the highly variable and species-rich composition of most animal microbiota. Thus, gut communities of reduced complexity are valuable models to disentangle metabolic functions of the constituent species.
Like mammals, honey bees harbor a highly specialized gut microbiota. However, in contrast to mammals, the honey bee gut microbiota is surprisingly simple and consistent, with seven species (categorized by clustering at 97% sequence identity of the 16S rRNA) accounting on average for >90% of the entire gut community in bees sampled across continents [31]. This microbiota is composed of four Proteobacteria (Gilliamella apicola, Snodgrassella alvi, Frischella perrara, and Bartonella apis), which mostly reside in the ileum, and two Firmicutes (Lactobacillus spp. Firm-4 and Firm-5) and one Actinobacterium (B. asteroides), which are predominantly found in the rectum. These specific locations suggest that bacteria occupy different metabolic niches in the bee gut and potentially engage in syntrophic interactions [32,33].
The honey bee gut microbiota has marked effects on the host. It promotes host weight gain and hormone signaling under laboratory settings [34] and stimulates the immune system of the host [35,36]. In addition, honey bees are ecologically and economically essential pollinators that have experienced increased mortality in recent years [37,38], which could in part be due to disturbances of their microbiota composition [39–42].
Genomic analyses and in vitro experiments have shown that fermentation of sugars and complex carbohydrates (e.g., pectin) into organic acids [15,32,43,44] is a prominent metabolic activity of the gut microbiota [34]. Lacking, however, is a detailed understanding of the consumption of diet-derived substrates and how individual community members contribute to the metabolic activities in vivo. For instance, it is elusive whether analogously to mammals, recalcitrant dietary compounds (especially from pollen) are broken down by the microbiota in the hindgut (i.e., large intestine composed of ileum and rectum), while more accessible compounds are reportedly absorbed by the host in the midgut (i.e., small intestine) [45–47].
To profile the metabolic output of the honey bee gut microbiota and its individual members, we employed gnotobiotic bee colonizations and in vitro experiments in conjunction with untargeted metabolomics (Fig 1). We first characterized robust metabolic differences between microbiota-depleted bees and bees colonized with a reconstituted community composed of the seven major bacterial species of the gut microbiota. Subsequently, we analyzed bees colonized with each community member separately to assay their potential contribution to the overall metabolic output of the gut microbiota. Finally, we recapitulated our results in vitro using pollen-conditioned medium. Our systematic approach provides unprecedented insights into the metabolic activities of the honey bee gut microbiota and demonstrates the possibility to use metabolomics in combination with gnotobiotic animal models to disentangle functions of individual gut microbiota members.
Results and discussion
Experimental reconstitution of the honey bee gut microbiota
To characterize the metabolic output of the honey bee gut microbiota, we colonized newly emerged bees with selected bacterial strains previously isolated from the bee gut. The reconstituted bacterial community consisted of 11 strains (S1 Table) covering the seven predominant species of the bee gut microbiota described above. We used two strains for G. apicola and four strains for Firm-5 in order to cover the extensive genetic diversity within these species [44,48]. Exposure of newly emerged adult bees to this community resulted in the successful establishment of all seven species, with a total of approximately 109 bacterial cells per gut after 10 d of colonization; hereafter, these are referred to as CL bees (Fig 2A). In contrast, non-colonized bees had total bacterial loads of <106 cells per gut, an observation consistent with previous studies [32,49]. In the following, we will refer to these bees as microbiota-depleted (MD) because they were not colonized with detectable levels of typical honey bee gut bacteria as determined with species-specific qPCR primers (<105 bacterial cells, except for one bee that was slightly above this cut-off for Firm-5) (Fig 2B). However, these bees may have harbored low levels of environmental microbes, as they were not kept under sterile conditions, especially in cases in which the bacterial loads were slightly above our detection limit of 105 bacterial cells (Fig 2A). It is also important to point out that newly emerged bees can occasionally be contaminated with specific bee gut bacteria, resulting in “MD” bees that in fact are colonized. Therefore, to be able to exclude such bees from further analysis, it is essential to determine the microbiota status of gnotobiotic bees using the qPCR assays presented in this study or an equivalent method.
Compared to hive bees of the same age, bacterial abundances of most species were slightly elevated in CL bees. However, in both groups the Firm-5 species was consistently the most abundant community member, while B. apis colonized at relatively low levels. This is in line with recent 16S rRNA gene-based community analyses [31,50,51], and we thus conclude that the selected strains assembled into a structured community resembling the native honey bee gut microbiota. Overall, this analysis validates our gnotobiotic bee system as a tool for microbiota reconstitution experiments and enables the study of microbiota functions under controlled laboratory conditions.
Metabolic changes in the honey bee gut upon colonization with the reconstituted bacterial community
To reveal microbiota-induced metabolome changes in the gut, we dissected the combined mid- and hindgut of MD, CL, and hive bees and analyzed water-extracted homogenates of these gut samples by untargeted metabolomics [21]. In total, we detected 24,899 mass-to-charge features (ions), 1,079 of which could be annotated by matching their accurate mass-to-sum formulas of compounds in the full Kyoto Encyclopedia of Genes and Genomes (KEGG) database (S2A Data). These 1,079 ions putatively correspond to 3,270 metabolites (S2B Data), since this method cannot separate isobaric compounds. For statistical analysis, we continued with the annotated ions, and for ion changes with multiple annotations, we provided the most likely annotation based on information from literature and genomic data.
Principal component analysis on the ion intensities revealed that CL and MD bees separate into two distinct clusters, which suggests colonization-specific metabolic profiles (S1 Fig). In two independent experiments, a total of 372 ions exhibited significant changes between CL and MD bees (Welch’s t test, Benjamini and Hochberg adjusted [BH adj.] P ≤ 0.01, S2C Data). A subset of 240 ions (65%) were more abundant in MD bees, suggesting that the cognate metabolites are utilized by the gut microbiota. These ions are hereafter referred to as bacterial substrates. Conversely, 132 ions were more abundant in CL bees and are hereafter referred to as bacterial products, indicating that they are produced either by the microbiota or by the host in response to the microbiota. To facilitate the biological interpretation of these multitude metabolic changes, we carried out two analyses. First, we looked at whether certain compound classes were overrepresented among the subsets of bacterial substrates and products (S3A Data). Second, we sorted ion changes based on their ability to explain the difference between the CL and MD metabolome profiles in an Orthogonal Projection of Least Squares-Differentiation Analysis (OPLS-DA) (Fig 3) [52].
Major bee gut microbiota substrate classes
We first focused on the 240 substrate ions that were more abundant in MD versus CL bees and potentially correspond to metabolites utilized by the microbiota (S2C Data). We found 3 compound classes to be strongly enriched: “flavonoids” (20 of 36 annotated ions, one-sided Fisher’s exact test, P < 0.001) and both “purine nucleosides and analogues” and “pyrimidine nucleosides and analogues” (in total eight of nine annotated ions, both P < 0.01). Seven flavonoids, three nucleosides, and a nucleoside precursor (orotate, m/z 155.009) were also among the 28 substrate ions with the most discriminatory power for distinguishing CL versus MD bees as based on OPLS-DA (Fig 3). Other ions among these most discriminatory substrates included two ω-hydroxy acids (m/z 315.254 and m/z 331.248) and three phenolamides (m/z 582.260, m/z 630.245, and m/z 233.129) from the outer pollen wall, as well as quinate (m/z 191.056) and citrate (m/z 191.019), both of which had previously been predicted to be utilized by certain community members of the honey bee gut microbiota [53,54]. Because they are the most remarkable groups among the identified substrates, nucleosides, flavonoids, and pollen wall-specific compounds will be discussed in more detail.
Nucleosides
Nucleosides are essential biomass components that can also serve as bacterial energy sources. The majority of the honey bee gut microbiota members lack genetic capacity for either purine or pyrimidine biosynthesis [33]. Instead, they seem to rely on salvage pathways and the uptake of nucleosides from the environment, providing a likely explanation for the observed depletion of these compounds in the gut of CL bees (S2A Fig). However, we cannot exclude an effect of altered host nucleoside metabolism on these changes, especially as nucleoside transporters are present in the intestinal epithelial cells of animals [55].
Flavonoids
Flavonoids are secondary metabolites that can make up 2%–4% of the dry weight of pollen [56,57] and this is in concordance with their identification as important diet-derived substrates of the honey bee gut microbiota. Flavonoids typically consist of two phenyl rings and one heterocyclic ring, the so-called aglycone. Glycosylation of this aglycone in diverse positions generates the remarkable flavonoid structural and functional diversity [58]. Among the bacterial substrates, we identified several glycosylated flavonoids (S2B Fig) that are known to be present in pollen, such as rutin or quercitrin [56]. We unambiguously confirmed the identity of three of these ions as the glycosylated flavonoids afzelin, quercitrin, and rutin using tandem mass spectrometry (MS/MS) fragmentation and spectral similarity calculations (see S1 Text, S3 Fig and S4 Data).
Several mammalian gut bacteria can convert flavonoids by either deglycosylation, thus releasing flavonoid aglycones, or C-ring cleavage, resulting in the accumulation of breakdown products of the aromatic backbone [59]. We mined the 132 bacterial products to look for these signatures of flavonoid conversions in the bee gut and identified several ions annotated as non-glycosylated flavonoids (S2B Fig). However, none of them significantly accumulated in CL versus MD bees, which would have been expected when deglycosylation was the only mechanism of flavonoid conversion. In contrast, we identified four ions among the bacterial products that could result from biodegradation of aromatic amino acids and flavonoid aglycones: two ions annotated as hydroxy- and dihydroxyphenylpropionate (m/z 165.055 and m/z 181.050), both of which are known C-ring cleavage products of flavonoids, and two ions annotated as maleylacetate (m/z 157.013) and hydroxy-3-oxoadipate (m/z 175.024), which are intermediates of aromatic compound degradation pathways (S2B Fig) [60–63]. Strikingly, three of these four ions were among the most discriminatory products for CL versus MD bees (Fig 3). Moreover, in a recent metabolomics study by Zheng et al. [34], similar intermediates were shown to accumulate in the hindgut of colonized bees (S2 Text and S5 Data).
Pollen wall compounds
The two ω-hydroxy acid ions (9,10,18-trihydroxystearate, m/z 315.254, and 9,10-dihydroxystearate, m/z 331.248) that were identified among the most discriminatory substrate ions (Fig 3 and S2C Fig) have been reported to be major constituents of sporopollenin [64], the biochemically inert and heterogeneous biopolymer forming the rigid structure of the outer pollen wall, the exine [65]. Phenolamides such as those utilized by the gut microbiota (N1,N5,N10-tricoumaroyl spermidine, m/z 582.260; N1,N5,N10-tricaffeoyl spermidine, m/z 630.245; and p-coumaroylputrescine, m/z 233.129; Fig 3 and S2C Fig) are also compounds of the exine as they are deposited on top and into its cavities as part of the pollen coat [66]. Remarkably, the pollen coat is also where most flavonoids are thought to be located in pollen grains [67].
Our findings on the utilization of flavonoids, ω-hydroxy acids, and phenolamides thus suggest that the honey bee gut microbiota contributes to the digestion of the rigid outer pollen wall. Easily accessible pollen nutrients (such as amino acids, sugars, and vitamins) are likely taken up by the host in the midgut, leaving these more recalcitrant compounds for the microbiota in the hindgut. This is in line with what is known about the biogeography and microbial ecology in the mammalian intestine [68]. Besides being utilized as an energy and carbon source, the conversion of secondary plant metabolites from pollen may have additional benefits for the microbiota and the host. For example, phenolamides and flavonoids both have been reported to exert antimicrobial activities, conceivably because their breakdown products increase the antioxidant potential in the gut, which could reduce inflammation and pathogen susceptibility [66,69]. In addition, mammalian flavonoid-metabolizing bacteria have a major impact on the bioavailability of flavonoids, and flavonoids are implicated in modulating weight gain by affecting host signaling [70,71]. This makes it tempting to speculate that flavonoid metabolism in the bee gut contributes to the microbiota dependent weight gain of honey bees that was observed in a previous study [34].
Products of the gut microbiota include fermentation products and host-derived metabolites
We next looked into the 132 ions that were more abundant in CL versus MD bees and thus represent possible metabolites produced by the microbiota (S2C Data). Again, we used enrichment analyses and OPLS-DA (Fig 3) to prioritize the most important product ions. Three compound classes were to some extent enriched among the bacterial products (S3A Data): “carboxylic acids and derivatives” (seven of 26 annotated ions, one-sided Fisher’s exact test, P < 0.03), “fatty acids and conjugates” (seven of 29 annotated ions P < 0.05), and “eicosanoids” (five of eight annotated ions, P < 0.01).
Fermentation products
Both the “carboxylic acids and derivatives” and “fatty acids and conjugates” categories contain known bacterial fermentation products, several of which accumulated in CL bees (succinate, m/z 117.019; pimelate, m/z 159.066; sebacic acid, m/z 201.113; butyrate, m/z 87.044; and valerate, m/z 101.060). This is in agreement with previous studies suggesting that fermentation is the predominant metabolic activity of bee gut bacteria [33,34]. Three of these fermentation products (succinate, pimelate, and sebacic acid) were among the 23 most discriminatory products, which highlights the substantial and consistent accumulation of these compounds in the presence of the microbiota (Fig 3 and S2D Fig). Using targeted metabolomics [72], we confirmed the strong accumulation of succinate in the gut of CL bees and determined absolute concentrations of other organic acids in CL and MD bees (S3 Text, S4 Fig and S6 Data). In addition, accumulation of fermentation products is one of the main microbiota dependent trends found in our study and that of Zheng et al. [34] (for details on the comparison, see S2 Text).
Host-derived metabolites
The third enriched product category (“eicosanoids”) includes five ions whose masses match to prostaglandins (S2E Fig), which are broadly conserved hormone-like lipids in animals. In insects, prostaglandins have been implicated in reproduction, fluid secretion, and activation of the immune system [73] through induction of prophenoloxidase, phagocytosis, and hemocyte spreading. None of the five prostaglandins annotated in our study have been functionally characterized in honey bees.
Besides eicosanoids, we identified a second group of host-derived metabolites induced by the microbiota. These are three derivatives of juvenile hormone III (S2E Fig), two of which were among the most discriminatory product ions (Fig 3, m/z 283.191 and m/z 269.176). Juvenile hormone III plays an important role in regulating the growth, development, and reproduction of insects. In adult honey bees, it controls the pace of the developmental maturation from young nurse bees to older forager bees [74]. This process is linked to nutrition [75] and could therefore be affected by metabolic activities of gut bacteria. Notably, juvenile hormone derivatives in the gut may have local functions distinct from those in the brain or hemolymph, as was shown for heteropteran linden bugs [76].
Gut metabolic profiles of colonized bees and hive bees show substantial overlap
To assess how much of the total metabolic output can be identified in hive bees under natural conditions, we analyzed the gut metabolome of 10-d-old hive bees that were exposed to social interactions and natural dietary resources and were colonized by the native gut microbiota. Principal component analysis revealed that hive bees clustered separately from CL bees (S1 Fig). This may be explained in part by the different diet of hive bees, the presence of multiple strains in a bee colony, and the impact of the environment on the gut metabolism. However, we found that 27 of the 28 most discriminatory substrate ions and 15 of the 22 most discriminatory product ions showed qualitatively the same changes in hive bees as in CL bees (S2D Data, Welch’s t test, BH adj. P ≤ 0.01). On the substrate side, this included most flavonoid ions, all nucleosides, quinate, and citrate, as well as the ions annotated as ω-hydroxy acids and phenolamides from the outer pollen wall. On the product side, we found four of the five prostaglandins and one of the juvenile hormone derivatives to be significantly increased in hive bees relative to MD bees, suggesting that these host-derived metabolites are also induced under natural conditions. Moreover, ions corresponding to fermentation products were either significantly increased (sebacic acid and valerate) or showed a trend towards increased levels (succinate and pimelate) in hive bees. The same was the case for the four ions corresponding to possible degradation products of flavonoids (hydroxy- and dihydroxyphenylpropionate, maleylacetate, and hydroxy-3-oxoadipate; S2A Data). We conclude that the remarkable overlap of metabolic changes between hive bees and CL bees highlights the relevance of our findings.
Mono-colonizations explain 80% of the overall metabolic output of the honey bee gut microbiota
We thus far presented evidence for substrates and products of the complete microbiota in the honey bee gut. To elucidate which community members might be responsible for these transformations, we conducted mono-colonizations of MD bees with all seven bacterial species (again using a mix of four and two strains together for Firm-5 and G. apicola, respectively). All species successfully established in the gut of MD bees, with other community members being generally below the limit of detection (<105 bacterial cells) (S5 Fig). We again extracted metabolites from the mid- and hindgut of individual bees to address how many of the 372 robust ion changes can be explained by one or multiple mono-colonizations (S2A Data), i.e., show qualitatively the same change as in CL bees (analysis of variance [ANOVA] followed by Tukey honest significant difference [HSD] post hoc test at 99% confidence, P ≤ 0.05) (S7 Data and S8 Data). Extended results of this analysis can be found in S2A Data.
Remarkably, using these significance cutoffs, 299 of the 372 (80%) robust changes between MD and CL bees could be explained by one or multiple mono-colonizations. This included 201 (84%) substrate and 98 (74%) product ions. The two Lactobacilli species (Firm-5 and Firm-4) explained most changes, followed by B. asteroides and the two Gammaproteobacteria (Fig 4A). Interestingly, the relative contribution to substrate conversion and product accumulation varied between mono-colonizations. For example, B. asteroides contributed relatively little to the conversion of substrates but seemed to be responsible for the production of a relatively large fraction of bacterial products. The Firm-4 species showed the opposite pattern, explaining relatively many bacterial substrates but a small fraction of bacterial products. Ion changes identified in CL bees but not in any of the mono-colonizations (in total 20%) may be due to our strict significance cutoffs, additive metabolic activities, or concerted functions of the community members, such as cross-feeding or interspecies metabolic feedback.
Substrates explained by mono-colonizations
We again used enrichment analysis (one-sided Fisher’s exact test, P ≤ 0.05), to get a high-level view of the functions of distinct community members in the conversion or production of certain compound classes (Fig 4A). This analysis revealed that all community members, except for S. alvi and B. apis, contributed to the disappearance of nucleosides in the bee gut (see also S2A Fig). Remarkably, S. alvi and B. apis encode complete nucleoside biosynthesis pathways and therefore do not have to rely on external nucleoside resources [32,54]. In turn, they seem to preferentially convert carboxylic acids and keto acids in the gut (malate, m/z 133.013; fumarate, m/z 115.003; citrate, m/z 191.019; and α-ketoglutarate, m/z 145.014), which is consistent with the presence of complete tricarboxylic acid (TCA) cycles and several carboxylate transporters in the genomes of these bacteria [32,54]. Flavonoids were enriched substrates for Firm-5 (11 of 126 substrate ions, P < 0.01) and B. asteroides (six of 55 substrate ions, P < 0.01), and many flavonoids were also utilized by Firm-4 (seven of 107 substrate ions, P = 0.051) (Fig 4A and S2B Fig). Interestingly, rutin (m/z 609.145) and scolymoside (m/z 593.150) were exclusively depleted in the Firm-5 mono-colonization, while afzelin (m/z 431.098) was also utilized by Firm-4 and B. asteroides, and quercitrin (m/z 447.093) even by G. apicola (Fig 4B). Similar patterns were also found for other flavonoids (S2B Fig), suggesting substrate specificity for the utilization of these pollen-derived compounds among community members.
In total, 27 of the 28 most discriminatory substrates (Fig 3) could be explained by at least one mono-colonization. The two ω-hydroxy acids ions from the outer pollen wall were exclusively utilized by B. asteroides and Firm-4, while the three phenolamides from the pollen coat were only depleted in the presence of Firm-5 (Fig 4C and S2C Fig). In contrast, quinate and citrate were utilized by several community members, suggesting that their almost complete depletion in CL and hive bees could be the result of a communal effort (S2A Data).
Products explained by mono-colonizations
For bacterial products, 21 of the 23 most discriminatory ions for CL versus MD bees could be explained by at least one mono-colonization. Strikingly, B. asteroides explained the accumulation of all host-derived prostaglandins and was also responsible for the induction of two of the three juvenile hormone derivatives, suggesting that this community member has a distinct influence on the host (Fig 4D and S2E Fig). Notably, S. alvi, Firm-4, and Firm-5 also affected the production of some of these metabolites, but not to the same extent as B. asteroides.
Three major fermentation products that accumulated in CL bees could be explained by mono-colonizations. Succinate (Fig 3E) and pimelate ions were produced exclusively in bees colonized with Firm-5, and valerate only in the B. asteroides colonized bees (S2D Fig and S2A Data). Finally, we found that ions corresponding to aromatic compound degradation intermediates accumulated in bees colonized with Firm-4 and Firm-5 (S2B Fig), which also explained most flavonoid utilization of the bee gut microbiota. This suggests that Firm-4 and Firm-5 do not only deglycosylate flavonoids, conceivably through expression of glycoside hydrolases [44], but may additionally degrade the aromatic backbone.
In vitro recapitulation of metabolic functions of community members
Our in vivo results strongly suggest that specific gut bacteria utilize distinct substrates from the pollen diet of bees. This prompted us to test (1) whether the bacterial species could grow in vitro on a pollen-based culture medium and (2) whether this would result in the metabolic conversions of the same compounds as was observed in vivo. To this end, we water-extracted metabolites from the same pollen batch that was used for feeding the bees and analyzed the metabolic composition of this extract using untargeted and targeted metabolomics. Detailed results are presented in S4 Text and show that pollen extract contains physiologically meaningful levels of nutrients and is expectedly enriched in “amino acids and derivatives,” “flavonoids,” “monosaccharides,” and “carboxylic acids and derivatives” (S6 Fig). Strikingly, all community members, except for S. alvi, showed substantial growth in the presence of this pollen extract compared to the nutrient-limited base media in which little or no growth was observed after 16 h of incubation (Fig 5A).
We then profiled the metabolome of growth media before and after bacterial incubation in a separate metabolomics experiment. We annotated a total of 1,031 ions (S9 Data), of which 427 (41%) were also present among the 1,079 ions from the in vivo dataset. In line with their growth profiles, the largest number of depleted metabolites (log2(FC) ≥ |1| and Welch’s t test BH adj. P ≤ 0.01) was found for the growth cultures of Firm-5, followed by G. apicola, Firm-4, F. perrara, B. asteroides, B. apis, and S. alvi (Fig 5A).
Using strict criteria, we identified 17 ions (13 pollen-derived substrates and four bacterial products), which were explained in vivo and in vitro by the same species (S7 Fig and S3 Table). Seven of these 13 substrates belonged to the most discriminatory substrate ions for CL versus MD bees (Fig 3): three flavonoids (quercitrin, afzelin, and rutin), one nucleoside (inosine), and ions annotated as quinate, citrate, and 2-fuorate. The fact that different community members were responsible for the conversion of some of these substrates (B. asteroides, Firm-4, Firm-5, F. perrara, B. apis, and G. apicola) demonstrates that our in vitro cultures allowed us to recapitulate metabolic activities covering the entire community.
We found remarkably overlapping substrate specificity for four flavonoids in vitro and in vivo, with the Firm-5 species being the only member capable of converting rutin and scolymoside, while quercitrin and afzelin were also utilized by Firm-4, and quercitrin was additionally used by B. asteroides and B. apis (Fig 5A). Among the four in vitro recapitulated products were three of the four ions corresponding to putative breakdown products of flavonoids (S7 Fig and S3 Table). These ions accumulated in vivo and in vitro in the presence of Firm-4 and/or Firm-5, providing further evidence for breakdown of the polyphenolic ring structure of flavonoids. However, we also found that deglycosylated flavonoids (i.e., aglycones) significantly accumulated in cultures of Firm-5 and showed a trend towards accumulation for Firm-4 and B. asteroides (Fig 5A). Based on these results, we propose that flavonoid degradation involves two steps (Fig 5B): (1) deglycosylation of sugar residues and their subsequent fermentation and (2) the breakdown of the polyphenol backbone. The second step could be relatively slow, explaining why aglycones accumulated in vitro (16 h), but not in vivo (10 d). Alternatively, the accumulation of some of these aromatic compound degradation intermediates could also result from the metabolism of other substrates such as aromatic amino acids.
An obvious difference in our in vitro experiments compared to the in vivo situation is the absence of the host, which may predigest pollen grains before gut bacteria utilize pollen-derived metabolites. For example, certain sugars and amino acids are expected to be present in lower amounts in vivo because of host absorption. Conversely, the host may also provide physicochemical conditions that support the growth of some community members. This could explain the poor growth of S. alvi in vitro, especially as in vivo S. alvi is tightly associated with the gut epithelium and other gut bacteria such as G. apicola [77].
Evidence for cross-feeding in the bee gut microbiota
Microbial species in gut communities can organize into food chains, where one species provides metabolites that can be utilized by others. Such metabolites may be released from insoluble dietary particles via bacterial degradation or can be generated as waste products of metabolism [2]. To identify possible metabolic interactions between community members of the bee gut microbiota, we focused on ions that in vivo significantly accumulated in some mono-colonizations and were depleted in others (S2A Data). A total of 27 ions showed such opposing changes between two or several mono-colonizations (S4 Table).
An example of a potential metabolic interaction identified in our dataset is the liberation and consumption of one of the major bacterial substrates in CL bees, 9-10-18-trihydroxystearate (m/z 331.248), originating from the outer pollen wall. In our mono-colonization experiments, the corresponding ion was depleted in Firm-4 and B. asteroides but accumulated in the case of Firm-5 and G. apicola (Fig 4C). This suggests that the latter two species facilitate the release of this ω-hydroxy acid from the outer pollen wall, possibly rendering it more accessible for further degradation by Firm-4 and B. asteroides.
A second example is pyruvate (m/z 87.008), which substantially accumulated in the gut of bees mono-colonized with G. apicola but was utilized as a substrate by other bacteria such as S. alvi and Firm-5 (Fig 6A). A syntrophic interaction between G. apicola and S. alvi had previously been suggested, because these bacteria are colocalized on the epithelial surface of the ileum [77] and harbor complementary metabolic capacities [32]. To test for potential cross-feeding of pyruvate from G. apicola to S. alvi, we supplemented the pollen-conditioned medium of S. alvi with culture supernatant of G. apicola cultures. The growth of S. alvi was slightly but significantly improved in the conditioned medium compared to the control medium (Fig 6B). Metabolome analysis (S10 Data) revealed six ions that accumulated during the growth of G. apicola and were utilized from the conditioned medium by S. alvi (Fig 6C). Besides pyruvate, these were ions corresponding to three putative fermentation products, a nucleoside derivative, and hydroxyphenylpropionate. We determined the concentration of pyruvate biochemically and showed that G. apicola indeed produces high levels of pyruvate (approximately 4 mM) and that this is subsequently utilized by S. alvi (S8 Fig). These results confirm our predictions from the in vivo dataset and show that bee gut bacteria engage in cross-feeding interactions. While not essential for gut colonization in itself as based on our mono-colonization experiments, such interactions may be important for community assembly and resilience and reflect the longstanding coexistence among these gut bacteria.
Conclusions
The simple composition and experimental amenability of the honey bee gut microbiota facilitated our systems-level approach. We reconstituted the honey bee gut microbiota from cultured strains, characterized the metabolic output of the complete microbiota, identified the contributions of individual community members in vivo, and recapitulated their activities in vitro. Our results provide unprecedented insights into the metabolic functions of bee gut bacteria.
As in the mammalian and termite gut ecosystem [1,68], we conclude that most substrates utilized by the bee gut microbiota are indigestible compounds that originate from the diet of the host and accumulate in the hindgut where bacterial density is the highest (Fig 7). Such compounds include plant metabolites from the outer pollen wall, such as ω-hydroxy acids, phenolamides, and flavonoid glycosides. While one of the bee gut bacteria had previously been identified as utilizing a major pollen polysaccharide (pectin) [5], our data provides, to our knowledge, the first evidence for a role of the gut microbiota in breaking down outer pollen wall components. Bacterial fermentation of these pollen-derived compounds resulted in the accumulation of organic acids (e.g., succinate) and putative polyphenol degradation products, which are likely to impact the physicochemical conditions in the colonized gut. In addition, we found that host-derived signaling molecules are induced by B. asteroides, suggesting a specific interaction of this gut symbiont with the host.
Based on the mono-colonization experiments, we conclude that most metabolic output of the bee gut microbiota can be explained by the metabolic activities of individual community members. This suggests different metabolic niches in the gut, which could be in part explained by the distinct distribution of bacteria along the gut [77]. While we have found evidence for cross-feeding (e.g., between G. apicola and S. alvi), the metabolic exchange between bacteria seems not to be essential for gut colonization, as each community member was able to colonize on its own. This may also be the case for gut bacteria of other animals, as they cannot rely on the presence of specific interaction partners in the highly dynamic gut environment but rather adapt to diet-derived nutrients. However, the bee gut microbiota is relatively simple, and interspecies metabolic exchanges may be essential to establish in more complex communities such as those of the termite or mammalian gut.
The metabolic activities identified in this study are likely underlying the symbiotic functions of the bee gut microbiota and thus may be directly linked to the microbiota’s impact on bee health and physiology [34,41]. The large metabolic overlap between colonized and hive bees demonstrates the relevance of our findings and validates our gnotobiotic bee model. Moreover, our study highlights the versatility of high-throughput untargeted metabolomics to disentangle metabolic functions in microbial ecosystems. We believe that this systematic approach can be extended to other gnotobiotic animals to enable a better understanding of the diversity of metabolic activities and functions that are present in microbial communities.
Materials and methods
Honey bee experiments
Newly emerged bees were obtained from a healthy-looking colony of Apis mellifera carnica located at the University of Lausanne. In short, dark-eyed pupae were carefully removed from capped brood cells with sterile tweezers and transferred to sterilized plastic boxes as described previously [36]. Boxes with pupae were kept with a source of sterile sugar water (50% sucrose solution, w/v) at 35°C with 80%–90% humidity for 2 d until the bees emerged, followed by a reduction in temperature to 32°C. For each box, one or two newly emerged bees were dissected, and their homogenized hindguts (in 1 ml 1x PBS) cultured on growth media as described below. To minimize the chance of including contaminated bees in colonization experiments, we excluded cages for which bacterial growth was observed for the tested bees. For the colonization of newly emerged bees, bacterial strains were inoculated from glycerol stocks and restreaked twice. Details on bacterial strains and culture conditions can be found in S1 Table. Bacterial cells were harvested and resuspended in 1x PBS/sugar water (1:1, v/v) at an OD600 of 1. For colonization, bacterial suspensions were added to a source of sterilized pollen and provided to the newly emerged bees (for details, see S5 Text). MD bees were kept under the same conditions, with the same food sources, but without being exposed to bacteria. The mid- and hindgut (S9 Fig) of gnotobiotic bees were dissected at day 10 post colonization and stored at −80°C until further use.
To obtain age-controlled hive bees, several brood frames without adult bees were transferred from the hive to a ventilated Styrofoam box that was kept in an incubator at 32–34°C overnight. The next morning, the newly emerged bees were collected, marked on the thorax with a pen, and reintroduced into the hive. These bees were recollected 10 d later, and their mid- and hindguts were dissected and stored at −80°C until further use.
The colonization experiment was repeated at two different time points of the year (spring and fall, referred to as experiment 1 and experiment 2 in this study). Whenever possible, we included bees from both experiments in our analysis, such as for CL and MD bees. However, this was not possible for all mono-colonizations because of bacterial contaminations (as detected by qPCR) or in a few cases because of the presence of above-threshold viral loads. The precise numbers of bees included per condition are listed in S5 Table.
Determining bacterial loads in the gut of honey bees
Bacterial loads were determined by qPCR using universal bacterial and species-specific 16S rRNA primers on DNA samples obtained from the gut tissues used for metabolomics analysis. Details on DNA/RNA extraction methods are given in S5 Text. Each DNA sample was screened with 11 different sets of primers targeting the actin gene of A. mellifera, the universal 16S rRNA region, and the species-specific 16S rRNA region of nine bacterial species, including the seven species used in this study and two non-core species frequently found in the gut of A. mellifera: Alpha-2.1 and Lactobacillus kunkeei. Primers used for this qPCR analysis are listed in S2 Table. We also screened all gut samples for the presence of viruses. Samples that were contaminated with other bacteria than the desired ones (i.e., >105 bacteria cells detected by qPCR) or that had high virus titers were excluded from the analysis where possible (S5 Table, S5 Fig and S5 Text). The minimum information for publication of qPCR experiments (MIQE) guidelines were followed throughout the data analysis of the qPCR experiments [78]. Details on the qPCR analysis can be found in S5 Text.
In vitro growth on pollen extracts
Bacteria were precultured on solid media from −80°C glycerol stocks before liquid cultures were inoculated for in vitro growth experiments. For G. apicola ELS0169, S. alvi wkB2, F. perrara PEB0191, and B. apis PEB0149, we used a modified M9 minimal medium supplemented with casamino acids and vitamins (http://dx.doi.org/10.17504/protocols.io.kdqcs5w). For B. asteroides ESL0170, the Firm-5 strains, and Firm-4 Hon2N, we used carbohydrate-free MRS (cfMRS) medium [79]. Bacteria were harvested from plates or spun down from overnight liquid cultures (the latter only for Lactobacilli and B. asteroides) and resuspended in the corresponding minimal medium. Freshly prepared liquid cultures were supplemented with either 10% (v/v) ddH2O or pollen extract and inoculated at a final OD600 of 0.05 (see S5 Text for details on pollen extract preparation). Half of the culture was immediately processed to determine colony-forming units (CFUs) and to harvest supernatants for metabolomics at time point 0 h, i.e., before growth. The other half of the culture was incubated for 16 h according to the conditions listed in S1 Table and then processed in the same way as the sample taken at time point 0 h. For CFU counting, serial dilutions were plated on solid media and incubated under the species-specific culturing conditions. For metabolomics analysis, the remaining bacterial culture was spun down at 20,000x g at room temperature for 10 min, and 300 μl of the culture supernatant was transferred to a fresh tube stored at −80°C until further processing. Five replicates were included for each species and treatment group.
For the cross-feeding experiment, G. apicola strain ESL0169 was grown for 8 h in pollen-supplemented M9 medium as described above to an OD600 of 0.11–0.15. Cultures were subsequently sterile filtered and mixed with fresh pollen-supplemented M9 medium 1:1 (v/v) in a total volume of 3 ml in a 12-well plate. For the control condition, non-inoculated pollen-supplemented M9 medium was incubated for 8 h, sterile filtered, and mixed with fresh pollen-supplemented M9 medium 1:1 (v/v). Then, S. alvi wkB2 was added to each well at a final OD600 of 0.05. The growth of S. alvi was assessed by OD600 measurements of a 100-μl aliquot in a 96-well plate with FLUOstar Omega microplate reader (Huberlab, Switzerland). As S. alvi tends to form aggregates, each culture was thoroughly mixed by pipetting up and down before transferring the aliquot and recording the OD600. For metabolomics analysis, supernatants were sampled at time points 0 h and 8 h for the G. apicola cultures and at time points 0, 16, 36, and 72 h for the S. alvi cultures. For biochemical quantification of pyruvate, we used a Pyruvate Assay Procedure kit (K-PYRUV, Megazyme, United States) according to the manufacturer’s microplate assay instructions. Samples of 8, 6, 4, 2, 1, 0.5, 0.25, and 0.125 mM pyruvate were used to generate the standard curve (slope = 0.062, intercept = 0.023, R2 = 0.987). Standards and samples were measured in triplicate at 340 nm with an Infinite M200PRO microplate reader (Tecan, Switzerland).
Metabolite extraction and profiling
Metabolites from gut and pollen samples were water-extracted after mechanical disruption, and supernatants from the in vitro experiments were harvested by centrifugation. Gut samples were preselected based on their wet-weight (arithmetic mean 55.1 mg, standard deviation 9.9). Ten times more water than the gut wet weight (v/w) was added, and the samples were homogenized with 0.1 mm zirconia beads (0.1 mm dia. Zirconia/Silica beads; Carl Roth) in a Fast-Prep24 5G homogenizer (MP Biomedicals) at 6 m/s for 45 s. While most of the homogenate was snap-frozen in liquid nitrogen for subsequent DNA/RNA extraction, aliquots of 100 μl were diluted 1:1 with water for metabolite extractions. To do so, the diluted aliquots were incubated in a preheated thermomixer at 80°C and 1,400 rpm for 3 min. After each minute, the samples were vortexed for 10 s. Subsequently, the samples were centrifuged at 20,000x g and 4°C for 5 min, and 150 μl of the resulting supernatant was transferred to a new tube and centrifuged again at 20,000x g for 30 min. Samples for untargeted metabolomics analysis were further diluted 10x in water. All samples were stored at −80°C before metabolomics analysis.
For untargeted analysis, samples were injected into an Agilent 6550 time-of-flight mass spectrometer (ESI-iFunnel Q-TOF, Agilent Technologies) operated in negative mode, at 4 Ghz, high resolution, and with a mass / charge (m/z) range of 50−1,000 [21]. The mobile phase was 60:40 isopropanol:water (v/v) and 1 mM NH4F at pH 9.0 supplemented with hexakis(1H, 1H, 3H- tetrafluoropropoxy)phosphazine and 3-amino-1-propanesulfonic acid for online mass correction. After processing of raw data as described in [21], m/z features (ions) were annotated by matching their accurate mass-to-sum formulas of compounds in the KEGG database with 0.001 Da mass accuracy and accounting for deprotonation [M-H+]-. The complete KEGG database was used because it has broad coverage of plant, bacterial, and insect metabolic pathways. Notably, this metabolomics method cannot distinguish between isobaric compounds, e.g., metabolites having identical m/z values, and in-source fragmentation cannot be accounted for. The raw data of samples from the three sets of experiments (bee gut samples, in vitro supernatants, and cross-feeding supernatants) were processed and annotated separately to accommodate their different sample matrices or times of measurement. These data can be explored in S2 Data, S9 Data and S10 Data. Raw data processing and annotation took place in MATLAB (MATLAB 2015b, The Mathworks, Natick) as described previously [21], and downstream processing and statistical tests were performed in R (version 3.3.2, R Foundation for Statistical Computing, Vienna, Austria).
Selected metabolite samples were measured in targeted fashion using ultra-high-pressure chromatography-coupled tandem mass spectrometry as described before [72]. Metabolite quantifications were performed by interpolating observed intensities to a standard curve of the metabolite using a linear model (R2 ≥ 0.95). Metabolites with standard curves of R2 ≤ 0.95 or in which intensities had to be extrapolated can be interpreted as relative changes only and were labeled in grey in all plots (S6B Fig). We used the weights of the extracted material to express the concentrations in millimole per gram of gut or gram of pollen. The dataset can be found in S6 Data.
Flavonoid ions were targeted for MS/MS fragmentation as [M-H+]- electrospray derivatives with a window size of ± 4 m/z in Q1. Fragmentation of the precursor ion was performed by collision-induced dissociation at 0, 10, 20, and 40 eV collision energy, and fragment-ion spectra were recorded in scanning mode by high-resolution time-of-flight MS. Spectra were interpreted using MetFrag [80], and spectral cosine similarity scores were calculated between reference spectra that were obtained in-house or library spectra from MassBank of North America (MoNA, http://mona.fiehnlab.ucdavis.edu/). For further details, see S5 Text.
Untargeted metabolomics data analysis
All steps of the downstream data analysis were performed in R (R Foundation for Statistical Computing, Vienna, Austria). Samples from double injections (technical replicates) were confirmed to be highly similar and averaged. Subsequent analyses were performed on these averaged ion intensities, which are available in S2D Data, S9 Data and S10 Data.
Principal component analysis (pca function in R) on ion intensities was used for the multivariate inspection of co-clustering of samples from different groups. For reasons of transparency, we carried out four different PCAs on all annotated ions or the subset of ions with robust changes between CL and MD bees and on log2-normalized or Z-score normalized ion intensities. Z-score transformation was used to remove the domination of high-intensity ions.
Ions that were deemed robustly different between the CL and MD bees were those that were significantly different (Welch t test with Benjamini and Hochberg correction ≤ 0.01, t.test and p.adjust(x, method =“BH”) in R) between CL and MD in both independent experiments. Differences between MD and CL samples were expressed as log2(fold change) values for both experiments separately and for pooled data of both experiments (see S2A Data). Fold changes were based on the arithmetic mean of the CL samples divided by the arithmetic mean of the MD samples. The standard error of the log2(fold change) was computed as the square root of the sum of the squared standard errors of the log2-transformed intensities of both CL and MD.
Enrichment analyses were computed on compound class categories from KEGG (in-house database), which are added in the column “compound class” in S2A Data. Some ions with ambiguous annotations had a compound class associated with multiple of these annotations. However, supported by the observation that compound classes between alternative annotations were often the same (or highly related), only the compound class of the first annotation was used as input for one-sided Fischer’s exact tests (fisher.test(x, alternative =“greater”) in R) on a 2 x 2 contingency table for every compound class. Compound classes associated with a single ion were removed from the results because they were deemed not biologically meaningful.
Ions were sorted based on to what extent they are responsible for explaining the separation between the CL and MD groups from experiment 2. To do this, these datasets were selected as the input for an OPLS-DA (opls from the ropls R package). The correlation and covariance between the log10-transformed ion intensities of included samples and the opls “scoreMN” output were computed with the cor and cov functions in R, respectively. The resulting scores were plotted in a so-called S-plot (Fig 3). The substrate and product ions most responsible for the separation were selected based on an absolute correlation ≥0.8 and an absolute covariance of ≥5. Because such analyses can be prone to overfitting, we tested the sensitivity of the most discriminatory ion selection by implementing a “leave one out strategy” and concluded that the selected ions are robust (>80% present in all 1,000 permutations).
One-way ANOVA (aov adjusted with TukeyHSD(x, conf.level = 0.99) in R) was performed between all bee gut samples after selecting the relevant samples from the data matrix and normalizing the intensities to ion standard (Z-) scores (i.e., by row) by subtracting for every ion its arithmetic mean intensity and dividing the resulting values by the standard deviation of its respective ion intensity. The results of the full ANOVA analysis can be explored in S7 Data. For this study, the focus was on differences between any group and MD bees, which were considered significant when having a Tukey HSD post hoc adjusted P value ≤ 0.05. When for a specific mono-colonization group this significance cut-off was met and the direction of the change was the same as that for CL versus MD, the ion was considered to be “explained” by this group.
In order to enrich for pollen ions, we only considered ions with an arithmetic mean intensity of ≥10,000 in the pollen samples, in addition to being highly significantly different from water-matrix control samples (Welch t test with BH correction ≤ 0.001, t.test and p.adjust(x, method = “BH”) in R combined with log2(fold change) difference of ≥ 2).
For the in vitro data (S9 Data), the goal was to identify pollen substrates and bacterial products for which changes in levels were observed in vivo and in vitro. Pollen ions were mapped by matching the top annotation formula of both datasets. For all media-strain combinations, we performed a statistical comparison (Welch t test with BH correction, t.test and p.adjust(x, method =“BH”) in R) between the time points 16 h and 0 h and considered only those ions with a log2(fold change) of ≥|1| and BH adj. P value of ≤0.01 as significant in vitro products or substrates. In order to be certain that only pollen-derived substrates were included, for every strain only ions that displayed a significant negative log2(fold change) exclusively in the base medium supplemented with pollen extract were considered as in vitro pollen substrates.
To identify ions that might be cross-fed between G. apicola and S. alvi, ions were selected that increased during the growth of G. apicola and were depleted when S. alvi was grown in this conditioned medium mixed 1:1 with fresh base medium. To do this, all ion intensities for both strains (S10 Data) were split and transformed to log2(fold change) with respect to the first time point of sampling. Ions that had a log2(fold change) of ≥1 during G. apicola growth and a log2(fold change) of ≤−1 during S. alvi growth were selected. The raw data and R code for recapitulating the metabolomics data analysis can be found in S11 Data.
Supporting information
Acknowledgments
The authors would like to acknowledge Dr. Emma Schymanski for excellent help with the interpretation of MS/MS fragmentation spectra, Guillermo Garcia Osuna for help with the preparation of culture media, and Fabienne Wichmann for editing the manuscript.
Abbreviations
- BH adj
Benjamini and Hochberg adjusted
- CFU
colony-forming unit
- CL
colonized
- KEGG
Kyoto Encyclopedia of Genes and Genomes
- HSD
honest significant difference
- LC-MS/MS
liquid chromatography-tandem mass spectrometry
- MD
microbiota-depleted
- MS/MS
tandem mass spectrometry
- OPLS-DA
Orthogonal Projection of Least Squares-Differentiation Analysis
- qPCR
quantitative PCR
- Q-TOF
quadrupole-time of flight
- TCA
tricarboxylic acid
Data Availability
All relevant data are available within the paper and its Supporting Information files.
Funding Statement
European Research Council https://erc.europa.eu/funding/starting-grants (grant number ERC-StG MicroBeeOme). Received by PE. The funder had no role in study design, data collection and analysis, decision to publish, or preparation of the manuscript. Swiss National Science Foundation http://www.snf.ch/en/Pages/default.aspx (grant number 31003A_160345). Received by PE. The funder had no role in study design, data collection and analysis, decision to publish, or preparation of the manuscript. ERA-Net http://ec.europa.eu/research/era/era-net_en.html (grant number ERASysAPP). Received by US. The funder had no role in study design, data collection and analysis, decision to publish, or preparation of the manuscript.
References
- 1.Brune A. Symbiotic digestion of lignocellulose in termite guts. Nat Rev Microbiol. 2014; 12: 168–180. doi: 10.1038/nrmicro3182 [DOI] [PubMed] [Google Scholar]
- 2.Koropatkin NM, Cameron EA, Martens EC. How glycan metabolism shapes the human gut microbiota. Nat Rev Microbiol. 2012; 10: 323–335. doi: 10.1038/nrmicro2746 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 3.Engel P, Moran NA. The gut microbiota of insects—diversity in structure and function. FEMS Microbiol Rev. 2013; 37: 699–735. doi: 10.1111/1574-6976.12025 [DOI] [PubMed] [Google Scholar]
- 4.Shin SC, Kim S-H, You H, Kim B, Kim AC, Lee K-A, et al. Drosophila microbiome modulates host developmental and metabolic homeostasis via insulin signaling. Science. 2011; 334: 670–674. doi: 10.1126/science.1212782 [DOI] [PubMed] [Google Scholar]
- 5.Storelli G, Defaye A, Erkosar B, Hols P, Royet J, Leulier F. Lactobacillus plantarum promotes Drosophila systemic growth by modulating hormonal signals through TOR-dependent nutrient sensing. Cell Metab. 2011; 14: 403–414. doi: 10.1016/j.cmet.2011.07.012 [DOI] [PubMed] [Google Scholar]
- 6.Blanton LV, Charbonneau MR, Salih T, Barratt MJ, Venkatesh S, Ilkaveya O, et al. Gut bacteria that prevent growth impairments transmitted by microbiota from malnourished children. Science. 2016; 351: aad3311–aad3311. doi: 10.1126/science.aad3311 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 7.Schwarzer M, Makki K, Storelli G, Machuca-Gayet I, Srutkova D, Hermanova P, et al. Lactobacillus plantarum strain maintains growth of infant mice during chronic undernutrition. Science. 2016; 351: 854–857. doi: 10.1126/science.aad8588 [DOI] [PubMed] [Google Scholar]
- 8.Smith PM, Howitt MR, Panikov N, Michaud M, Gallini CA, Bohlooly-Y M, et al. The microbial metabolites, short-chain fatty acids, regulate colonic Treg cell homeostasis. Science. 2013; 341: 569–573. doi: 10.1126/science.1241165 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 9.Trompette A, Gollwitzer ES, Yadava K, Sichelstiel AK, Sprenger N, Ngom-Bru C, et al. Gut microbiota metabolism of dietary fiber influences allergic airway disease and hematopoiesis. Nat Med. 2014; 20: 159–166. doi: 10.1038/nm.3444 [DOI] [PubMed] [Google Scholar]
- 10.Rooks MG, Garrett WS. Gut microbiota, metabolites and host immunity. Nat Rev Immunol. 2016; 16: 341–352. doi: 10.1038/nri.2016.42 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 11.Stecher B, Hardt W-D. Mechanisms controlling pathogen colonization of the gut. Current Opinion in Microbiology. 2011; 14: 82–91. doi: 10.1016/j.mib.2010.10.003 [DOI] [PubMed] [Google Scholar]
- 12.Blaut M, Clavel T. Metabolic diversity of the intestinal microbiota: implications for health and disease. J Nutr. 2007; 137: 751S–5S. [DOI] [PubMed] [Google Scholar]
- 13.Ley RE, Hamady M, Lozupone C, Turnbaugh PJ, Ramey RR, Bircher JS, et al. Evolution of mammals and their gut microbes. Science. 2008; 320: 1647–1651. doi: 10.1126/science.1155725 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 14.Conlon MA, Bird AR. The impact of diet and lifestyle on gut microbiota and human health. Nutrients. 2014; 7: 17–44. doi: 10.3390/nu7010017 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 15.Engel P, Martinson VG, Moran NA. Functional diversity within the simple gut microbiota of the honey bee. Proc Natl Acad Sci USA. 2012; 109: 11002–11007. doi: 10.1073/pnas.1202970109 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 16.Warnecke F, Luginbühl P, Ivanova N, Ghassemian M, Richardson TH, Stege JT, et al. Metagenomic and functional analysis of hindgut microbiota of a wood-feeding higher termite. Nature. 2007; 450: 560–565. doi: 10.1038/nature06269 [DOI] [PubMed] [Google Scholar]
- 17.Hess M, Sczyrba A, Egan R, Kim T-W, Chokhawala H, Schroth G, et al. Metagenomic discovery of biomass-degrading genes and genomes from cow rumen. Science. 2011; 331: 463–467. doi: 10.1126/science.1200387 [DOI] [PubMed] [Google Scholar]
- 18.Qin J, Li R, Raes J, Arumugam M, Burgdorf KS, Manichanh C, et al. A human gut microbial gene catalogue established by metagenomic sequencing. Nature. 2010; 464: 59–65. doi: 10.1038/nature08821 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 19.Patti GJ, Yanes O, Siuzdak G. Innovation: Metabolomics: the apogee of the omics trilogy. Nat Rev Mol Cell Biol. 2012; 13: 263–269. doi: 10.1038/nrm3314 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 20.Sévin DC, Kuehne A, Zamboni N, Sauer U. Biological insights through nontargeted metabolomics. Curr Opin Biotechnol. 2015; 34: 1–8. doi: 10.1016/j.copbio.2014.10.001 [DOI] [PubMed] [Google Scholar]
- 21.Fuhrer T, Heer D, Begemann B, Zamboni N. High-throughput, accurate mass metabolome profiling of cellular extracts by flow injection-time-of-flight mass spectrometry. Anal Chem. 2011; 83: 7074–7080. doi: 10.1021/ac201267k [DOI] [PubMed] [Google Scholar]
- 22.Martin F-PJ, Sprenger N, Montoliu I, Rezzi S, Kochhar S, Nicholson JK. Dietary modulation of gut functional ecology studied by fecal metabonomics. J Proteome Res. 2010; 9: 5284–5295. doi: 10.1021/pr100554m [DOI] [PubMed] [Google Scholar]
- 23.Holmes E, Li JV, Marchesi JR, Nicholson JK. Gut microbiota composition and activity in relation to host metabolic phenotype and disease risk. Cell Metab. 2012; 16: 559–564. doi: 10.1016/j.cmet.2012.10.007 [DOI] [PubMed] [Google Scholar]
- 24.Daniel H, Gholami AM, Berry D, Desmarchelier C, Hahne H, Loh G, et al. High-fat diet alters gut microbiota physiology in mice. ISME J. 2014; 8: 295–308. doi: 10.1038/ismej.2013.155 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 25.Walker A, Pfitzner B, Neschen S, Kahle M, Harir M, Lucio M, et al. Distinct signatures of host-microbial meta-metabolome and gut microbiome in two C57BL/6 strains under high-fat diet. ISME J. 2014; 8: 2380–2396. doi: 10.1038/ismej.2014.79 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 26.Ridaura VK, Faith JJ, Rey FE, Cheng J, Duncan AE, Kau AL, et al. Gut microbiota from twins discordant for obesity modulate metabolism in mice. Science. 2013; 341: 1241214–1241214. doi: 10.1126/science.1241214 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 27.Lu K, Abo RP, Schlieper KA, Graffam ME, Levine S, Wishnok JS, et al. Arsenic exposure perturbs the gut microbiome and its metabolic profile in mice: an integrated metagenomics and metabolomics analysis. Environ Health Perspect. 2014; 122: 284–291. doi: 10.1289/ehp.1307429 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 28.Weir TL, Manter DK, Sheflin AM, Barnett BA, Heuberger AL, Ryan EP. Stool microbiome and metabolome differences between colorectal cancer patients and healthy adults. PLoS ONE. 2013; 8: e70803 doi: 10.1371/journal.pone.0070803 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 29.Theriot CM, Koenigsknecht MJ, Carlson PE, Hatton GE, Nelson AM, Li B, et al. Antibiotic-induced shifts in the mouse gut microbiome and metabolome increase susceptibility to Clostridium difficile infection. Nat Commun. 2014; 5: 3114 doi: 10.1038/ncomms4114 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 30.Wang Z, Klipfell E, Bennett BJ, Koeth R, Levison BS, Dugar B, et al. Gut flora metabolism of phosphatidylcholine promotes cardiovascular disease. Nature. 2011; 472: 57–63. doi: 10.1038/nature09922 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 31.Kwong WK, Medina LA, Koch H, Sing K-W, Soh EJY, Ascher JS, et al. Dynamic microbiome evolution in social bees. Science Advances. 2017; 3: e1600513 doi: 10.1126/sciadv.1600513 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 32.Kwong WK, Engel P, Koch H, Moran NA. Genomics and host specialization of honey bee and bumble bee gut symbionts. Proc Natl Acad Sci USA. 2014; 111: 11509–11514. doi: 10.1073/pnas.1405838111 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 33.Kwong WK, Moran NA. Gut microbial communities of social bees. Nat Rev Microbiol. 2016; 14: 374–384. doi: 10.1038/nrmicro.2016.43 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 34.Zheng H, Powell JE, Steele MI, Dietrich C, Moran NA. Honeybee gut microbiota promotes host weight gain via bacterial metabolism and hormonal signaling. Proc Natl Acad Sci USA. 2017; 54: 201701819 doi: 10.1073/pnas.1701819114. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 35.Kwong WK, Mancenido AL, Moran NA. Immune system stimulation by the native gut microbiota of honey bees. R Soc Open Sci. 2017; 4: 170003 doi: 10.1098/rsos.170003 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 36.Emery O, Schmidt K, Engel P. Immune system stimulation by the gut symbiont Frischella perrara in the honey bee (Apis mellifera). Mol Ecol. 2017; 50: 735 doi: 10.1111/mec.14058 [DOI] [PubMed] [Google Scholar]
- 37.Gallai N, Salles J-M, Settele J, Vaissière BE. Economic valuation of the vulnerability of world agriculture confronted with pollinator decline. Ecol Econ. 2009; 68: 810–821. doi: 10.1016/j.ecolecon.2008.06.014 [Google Scholar]
- 38.Potts SG, Biesmeijer JC, Kremen C, Neumann P, Schweiger O, Kunin WE. Global pollinator declines: trends, impacts and drivers. Trends Ecol Evol. 2010; 25: 345–353. doi: 10.1016/j.tree.2010.01.007 [DOI] [PubMed] [Google Scholar]
- 39.Engel P, Kwong WK, McFrederick Q, Anderson KE, Barribeau SM, Chandler JA, et al. The bee microbiome: Impact on bee health and model for evolution and ecology of host-microbe interactions. mBio. 2016; 7: e02164–15. doi: 10.1128/mBio.02164-15 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 40.Schwarz RS, Moran NA, Evans JD. Early gut colonizers shape parasite susceptibility and microbiota composition in honey bee workers. Proc Natl Acad Sci USA. 2016; 113: 9345–9350. doi: 10.1073/pnas.1606631113 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 41.Raymann K, Shaffer Z, Moran NA. Antibiotic exposure perturbs the gut microbiota and elevates mortality in honeybees. PLoS Biol. 201715: e2001861 doi: 10.1371/journal.pbio.2001861 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 42.Cox-Foster DL, Conlan S, Holmes EC, Palacios G, Evans JD, Moran NA, et al. A metagenomic survey of microbes in honey bee colony collapse disorder. Science. 2007; 318: 283–287. doi: 10.1126/science.1146498 [DOI] [PubMed] [Google Scholar]
- 43.Engel P, Vizcaino MI, Crawford JM. Gut symbionts from distinct hosts exhibit genotoxic activity via divergent colibactin biosynthesis pathways. Appl Environ Microbiol. 2015; 81: 1502–1512. doi: 10.1128/AEM.03283-14 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 44.Ellegaard KM, Tamarit D, Javelind E, Olofsson TC, Andersson SGE, Vásquez A. Extensive intra-phylotype diversity in lactobacilli and bifidobacteria from the honeybee gut. BMC Genomics. 2015; 16: 284 doi: 10.1186/s12864-015-1476-6 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 45.Roulston TH, Cane JH. Pollen nutritional content and digestibility for animals. Plant Syst Evol. 2000. 222:187–209. [Google Scholar]
- 46.Crailsheim K. The protein balance of the honey bee worker. Apidologie. 1990. 21:417–429. doi: 10.1051/apido:19900504 [Google Scholar]
- 47.Crailsheim K. Intestinal transport of sugars in the honeybee (Apis mellifera L.). Insect Physiol. 1988. 34: 839–845. doi: 10.1016/0022-1910(88)90117-5 [Google Scholar]
- 48.Engel P, Stepanauskas R, Moran NA. Hidden diversity in honey bee gut symbionts detected by single-cell genomics. PLoS Genet. 2014; 10: e1004596 doi: 10.1371/journal.pgen.1004596 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 49.Powell JE, Martinson VG, Urban-Mead K, Moran NA. Routes of acquisition of the gut microbiota of the honey bee Apis mellifera. Appl Environ Microbiol. 2014; 80: 7378–7387. doi: 10.1128/AEM.01861-14 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 50.Moran NA, Hansen AK, Powell JE, Sabree ZL. Distinctive gut microbiota of honey bees assessed using deep sampling from individual worker bees. PLoS ONE. 2012; 7: e36393 doi: 10.1371/journal.pone.0036393 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 51.Corby-Harris V, Maes P, Anderson KE. The bacterial communities associated with honey bee (Apis mellifera) foragers. PLoS ONE. 2014; 9: e95056 doi: 10.1371/journal.pone.0095056 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 52.Brereton RG, Lloyd GR. Partial least squares discriminant analysis: taking the magic away. J Chemom. 2014; 28: 213–225. doi: 10.1002/cem.2609 [Google Scholar]
- 53.Kwong WK, Moran NA. Cultivation and characterization of the gut symbionts of honey bees and bumble bees: description of Snodgrassella alvi gen. nov., sp. nov., a member of the family Neisseriaceae of the Betaproteobacteria, and Gilliamella apicola gen. nov., sp. nov., a member of Orbaceae fam. nov., Orbales ord. nov., a sister taxon to the order “Enterobacteriales” of the Gammaproteobacteria. Int J Syst Evol Microbiol. 2013; 63: 2008–2018. doi: 10.1099/ijs.0.044875-0 [DOI] [PubMed] [Google Scholar]
- 54.Segers FH, Kešnerová L, Kosoy M, Engel P. Genomic changes associated with the evolutionary transition of an insect gut symbiont into a blood-borne pathogen. ISME J. 2017; 60: 810 doi: 10.1038/ismej.2016.201 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 55.Rose JB, Coe IR. Physiology of nucleoside transporters: back to the future…. Physiology. 2008; 23: 41–48. doi: 10.1152/physiol.00036.2007 [DOI] [PubMed] [Google Scholar]
- 56.Rzepecka-Stojko A, Stojko J, Kurek-Górecka A, Górecki M, Kabała-Dzik A, Kubina R, et al. Polyphenols from bee pollen: structure, absorption, metabolism and biological activity. Molecules. 2015; 20: 21732–21749. doi: 10.3390/molecules201219800 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 57.Falcone Ferreyra ML, Rius SP, Casati P. Flavonoids: biosynthesis, biological functions, and biotechnological applications. Front Plant Sci. 2012; 3: 222 doi: 10.3389/fpls.2012.00222 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 58.Le Roy J, Huss B, Creach A, Hawkins S, Neutelings G. Glycosylation is a major regulator of phenylpropanoid availability and biological activity in plants. Front Plant Sci. 2016; 7: 735 doi: 10.3389/fpls.2016.00735 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 59.Braune A, Blaut M. Bacterial species involved in the conversion of dietary flavonoids in the human gut. Gut Microbes. 2016; 7: 216–234. doi: 10.1080/19490976.2016.1158395 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 60.Labib S, Erb A, Kraus M, Wickert T, Richling E. The pig caecum model: A suitable tool to study the intestinal metabolism of flavonoids. Mol Nutr Food Res. 2004; 48: 326–332. doi: 10.1002/mnfr.200400022 [DOI] [PubMed] [Google Scholar]
- 61.Schoefer L, Mohan R, Schwiertz A, Braune A, Blaut M. Anaerobic degradation of flavonoids by Clostridium orbiscindens. Appl Environ Microbiol. 2003; 69: 5849–5854. doi: 10.1128/AEM.69.10.5849-5854.2003 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 62.Simmering R, Pforte H, Jacobasch G, Blaut M. The growth of the flavonoid-degrading intestinal bacterium, Eubacterium ramulus, is stimulated by dietary flavonoids in vivo. FEMS Microbiol Ecol. 2002; 40: 243–248. doi: 10.1111/j.1574-6941.2002.tb00957.x [DOI] [PubMed] [Google Scholar]
- 63.Hopper W, Mahadevan A. Degradation of catechin by Bradyrhizobium japonicum. Biodegradation. 1997; 8: 159–165. doi: 10.1023/A:1008254812074. [Google Scholar]
- 64.Li H, Zhang D. Biosynthesis of anther cuticle and pollen exine in rice. Plant Signal Behav. 2010; 5: 1121–1123. doi: 10.4161/psb.5.9.12562 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 65.Ariizumi T, Toriyama K. Genetic regulation of sporopollenin synthesis and pollen exine development. Annu Rev Plant Biol. 2011; 62: 437–460. doi: 10.1146/annurev-arplant-042809-112312 [DOI] [PubMed] [Google Scholar]
- 66.Bassard J-E, Ullmann P, Bernier F, Werck-Reichhart D. Phenolamides: Bridging polyamines to the phenolic metabolism. Phytochemistry. 2010; 71: 1808–1824. doi: 10.1016/j.phytochem.2010.08.003 [DOI] [PubMed] [Google Scholar]
- 67.Wiermann R, Vieth K. Outer pollen wall, an important accumulation site for flavonoids. Protoplasma. 1983; 118: 230–233. doi: 10.1007/BF01281807. [Google Scholar]
- 68.Donaldson GP, Lee SM, Mazmanian SK. Gut biogeography of the bacterial microbiota. Nat Rev Microbiol. 2016; 14: 20–32. doi: 10.1038/nrmicro3552 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 69.Cushnie TPT, Lamb AJ. Antimicrobial activity of flavonoids. Int J Antimicrob Agents. 2005; 26: 343–356. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 70.Kaakoush NO, Morris MJ. More flavor for flavonoid-based interventions? Trends Mol Med. 2017; 23: 293–295. doi: 10.1016/j.molmed.2017.02.008 [DOI] [PubMed] [Google Scholar]
- 71.Thaiss CA, Itav S, Rothschild D, Meijer M, Levy M, Moresi C, et al. Persistent microbiome alterations modulate the rate of post-dieting weight regain. Nature. 2016; 540: 544–551. doi: 10.1038/nature20796 [DOI] [PubMed] [Google Scholar]
- 72.Buescher JM, Moco S, Sauer U, Zamboni N. Ultrahigh performance liquid chromatography−tandem mass spectrometry method for fast and robust quantification of anionic and aromatic metabolites. Anal Chem. Amer Chem Soc. 2010; 82: 4403–4412. doi: 10.1021/ac100101d [DOI] [PubMed] [Google Scholar]
- 73.Stanley D, Kim Y. Prostaglandins and their receptors in insect biology. Front Endocrinol. 2011; 2: 105 doi: 10.3389/fendo.2011.00105 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 74.Robinson GE, Page RE, Strambi C, Strambi A. Hormonal and genetic control of behavioral integration in honey bee colonies. Science. 1989. 246: 109–112. doi: 10.1126/science.246.4926.109 [DOI] [PubMed] [Google Scholar]
- 75.Toth AL, Kantarovich S, Meisel AF, Robinson GE. Nutritional status influences socially regulated foraging ontogeny in honey bees. J Exp Biol. 2005; 208: 4641–4649. doi: 10.1242/jeb.01956 [DOI] [PubMed] [Google Scholar]
- 76.Bajgar A., Jindra M, Dolezel D. Autonomous regulation of the insect gut by circadian genes acting downstream of juvenile hormone signaling. Proc. Natl. Acad. Sci. U.S.A. 2013; 110: 4416–4421. doi: 10.1073/pnas.1217060110 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 77.Martinson VG, Moy J, Moran NA. Establishment of characteristic gut bacteria during development of the honeybee worker. Appl Environ Microbiol. 2012; 78: 2830–2840. doi: 10.1128/AEM.07810-11 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 78.Bustin SA, Benes V, Garson JA, Hellemans J, Huggett J, Kubista M, et al. The MIQE guidelines: Minimum information for publication of quantitative real-time PCR experiments. Clin Chem. 2009; 55: 611–622. doi: 10.1373/clinchem.2008.112797 [DOI] [PubMed] [Google Scholar]
- 79.O'Donnell MM, Forde BM, Neville B, Ross PR, O'Toole PW. Carbohydrate catabolic flexibility in the mammalian intestinal commensal Lactobacillus ruminis revealed by fermentation studies aligned to genome annotations. Microb Cell Fact. 2011; 10 Suppl 1: S12 doi: 10.1186/1475-2859-10-S1-S12 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 80.Ruttkies C, Schymanski EL, Wolf S, Hollender J, Neumann S. MetFrag relaunched: incorporating strategies beyond in silico fragmentation. J Cheminformatics. 2016; 8: 3 doi: 10.1186/s13321-016-0115-9 [DOI] [PMC free article] [PubMed] [Google Scholar]
Associated Data
This section collects any data citations, data availability statements, or supplementary materials included in this article.
Supplementary Materials
Data Availability Statement
All relevant data are available within the paper and its Supporting Information files.