Skip to main content
MicrobiologyOpen logoLink to MicrobiologyOpen
. 2020 Mar 17;9(6):e1022. doi: 10.1002/mbo3.1022

Geographical separation and physiology drive differentiation of microbial communities of two discrete populations of the bat Leptonycteris yerbabuenae

Osiris Gaona 1,2, Daniel Cerqueda‐García 3,, Andrés Moya 4, Ximena Neri‐Barrios 2, Luisa I Falcón 2,
PMCID: PMC7294308  PMID: 32181589

Abstract

In this paper, we explore how two discrete and geographically separated populations of the lesser long‐nosed bat (Leptonycteris yerbabuenae)—one in central and the other in the Pacific region of Mexico—differ in their fecal microbiota composition. Considering the microbiota–host as a unity, in which extrinsic (as food availability and geography) or intrinsic factors (as physiology) play an important role in the microbiota composition, we would expect differentiation in the microbiota of two geographically separated populations. The Amplicon Sequences Variants (ASVs) of the V4 region of the 16s rRNA gene from 68 individuals were analyzed using alpha and beta diversity metrics. We obtained a total of 11 566 (ASVs). The bacterial communities in the Central and Pacific populations had a diversity of 6,939 and 4,088 ASVs, respectively, sharing a core microbiota of 539 ASVs accounting for 75% of the relative abundance, suggesting stability over evolutionary time. The Weighted UniFrac metrics tested by a PERMANOVA showed that lactating and pregnant females had significant beta diversity differences in the two populations compared with other reproductive stages. This could be a consequence of the increased energy requirements of these physiological stages, more than the variation due to geographical separation. In contrast, a positive correlation of the observed ASVs of fecal microbiota with the observed ASVs of plastids related to the diet was observed in the juveniles and adults, suggesting that in these physiological stages an extrinsic factor as the diet shapes the microbiota composition. The results provide a baseline for future studies of the microbiome in these two wild populations of the lesser long‐nosed bat, the main pollinator of the Agaves from which the beverages tequila and mezcal are made.

Keywords: geographical separation, holobiont, populations, reproductive stages


Leptonycteris yerbabuenae is a bat species found in Mexico in two separate populations, one in the Pacific and the other in the Central region. With the analysis of its fecal microbiota, we found differentiation between the two populations. However, these populations share a core microbiota of 359 Amplicon Sequences Variants, accounting for 75% of abundance, and suggesting stability over time. The microbiota differs between reproductive stages within the populations, suggesting that factors such as geographic separation and physiological variation drive changes in the microbiota.

graphic file with name MBO3-9-e1022-g013.jpg

1. INTRODUCTION

The microbial communities that inhabit the guts of mammals are complex, dynamic, and critical to the health of the host (Ingala, Becker, Bak Holm, Kristiansen, & Simmons, 2019; Ochman et al., 2010). Microbiota composition and abundance are further determined by several factors such as diet, geography, physiology and health status (Knutie, 2020; Ley et al., 2008; Muegge et al., 2011; Ochman et al., 2010), and even phylogeny. It has been demonstrated, for example, that phylogeny in hominids influences the microbiota at an evolutionary level, suggesting that the microbiota is more than just what the host eats (Ochman et al., 2010).

Microbial symbionts have a variety of roles in the nutrition, immunity, development, reproduction, and speciation of their eukaryote hosts, making this symbiosis a major component of eukaryotic fitness and evolution (Brucker & Bordenstein, 2012). Interactions between host and microbiome have coevolved in mutual adaptations into a superorganism association (MacColl, 2011) and are key to biological adaptations (Brockhurst & Koskella, 2013).

The hologenome concept of evolution states that in addition to the host genome, a significant proportion of the microbiome is also transmitted from one host generation to the next and can thus propagate unique properties of the holobiont (Rosenberg & Zilber‐Rosenberg, 2019). Furthermore, genetic variation can occur by changes in the host and/or microbiome genomes; the microbiome genome is even expected to be able to adjust to environmental dynamics faster and through more processes that the host, and thus may be playing fundamental roles in the adaptation and evolution of holobionts (Rosenberg & Zilber‐Rosenberg, 2019).

Genetic variation in holobionts can occur by mutation and DNA rearrangement, amplification or reduction of specific microbes, acquisition of novel microbes from the environment, and horizontal gene transfer from microbe to microbe or from microbe to host (Zilber‐Rosenberg & Rosenberg, 2008). The multilayered structure of the holobiont consists of a core of host‐adapted microbiota assembled from diverse environments and determined by genetic factors, as well as a flexible pool of microbes that depend on environmental diversity and external conditions (Shapira, 2016).

Vertical transmission of the microbiota from parent to progeny allows its maintenance between generations and is likely favored by selection when those microbes are beneficial to the host (Shapira, 2016). The functional profile of the microbiome is probably more constrained by evolution/vertical inheritance than individual bacterial taxa (Martiny et al., 2006; Phillips et al., 2017; Shapira, 2016). Thus, vertical transmission could drive coevolution, resulting in phylogenetic congruence (Shapira, 2016).

The mutualistic and adaptive potential of microbiota offers flexibility and the ability to adapt to a range of ecological niches (Alberdi, Aizpurua, Bohmann, Zepeda‐Mendoza, & Gilbert, 2016). Subsequently, mutualist‐facilitated adaptations can lead to population fragmentation, isolation, and speciation (Shapira, 2016). Speciation—the splitting of a population into two reproductively incompatible populations, each taking a distinct evolutionary path—is a defining process in evolution. Mutualist microbes can drive all modes of isolation, including ecological, behavioral, and developmental asynchronization and genetic divergence, but, as facilitators of niche adaptation, they are frequently associated with ecological isolation (Brucker & Bordenstein, 2012; Shapira, 2016).

Early evidence suggested that in the order Chiroptera, microbiome composition was influenced by the host phylogeny and life history (Phillips et al., 2012). In contrast, recent studies find no evidence of phylosymbiosis in Afrotropical bats (Lutz et al., 2019). Due to their species‐specific feeding strategy specialization, Phyllostomid bats could remain as a model clade to study the relationship of the microbiome–host composition, phylogeny, and coevolution (Carrillo‐Araujo et al., 2015). Phyllostomid bats are found from the southern USA and northern Mexico to Argentina and show a great evolutionary diversification of species, in which patterns are dependent on geographical and ecological interactions, resulting in a great diversity of dietary strategies and the most ecologically diverse family within the order Chiroptera (Carrillo‐Araujo et al., 2015). They show a remarkable degree of evolutionary diversification of dietary strategies, from insectivory (the ancestral trait) (Monteiro & Nogueira, 2011) to feeding on blood, small vertebrates, nectar, fruit, and complex omnivorous diets (Gardner, 1976).

Leptonycteris yerbabuenae is a migratory phyllostomid bat. It is usually a strict and specialized nectar feeder, though it can occasionally consume fruit, so its diet is generally poor in proteins and minerals (Fleming & Nassar, 2002). L. yerbabuenae feeds mainly on nectar from agaves, columnar cacti like Carnigea gigantea, different species of Stenocereus and Bombacaceae (Psedobombax elipticum), Convolvulaceae, and other legumes (Arita, 1991; Arita & Humphrey, 1988; Cole & Wilson, 2006; Valiente‐Banuet, Arizmendi, Rojas‐Martínez, & Domínguez‐Canseco, 1996).

Mexico has two differentiated populations of L. yerbabuenae: one along the Pacific coast including Baja California, Sonora, and Jalisco states, and the other in the south‐central region, including Oaxaca, Morelos, and Guerrero states (Morales‐Garza, Arizmendi, Campos, Martínez‐Garcia, & Valiente‐Banuet, 2007). The two populations are separated geographically, with negligible gene flow, as demonstrated by Morales‐Garza et al., 2007 using random amplified polymorphic DNA (RAPD) analysis (Morales‐Garza et al., 2007).

The population of L. yerbabuenae that resides between the latitudes of 3°N and 21°S in North America carry out latitudinal migrations, while populations that reside south of 21°S latitude are year‐round residents. Migrations are known to be correlated with the availability of floral resources (Rojas‐Martínez, Valiente‐Banuet, Coro Arizmendi, Alcántara‐Eguren, & Arita, 1999), of which the most predictable are cacti, agave, and C3 plant nectar (Burke, Frey, Ganguli, & Stoner, 2019). The central population has more genetic variability than the Pacific population, likely due to the environmental stability of central Mexico (Morales‐Garza et al., 2007; Valiente‐Banuet et al., 1996).

In both populations, roosts are differentiated by reproductive stage (Ceballos, Fleming, Chavez, & Nassar, 2006; Cockrum, 1991; Stoner, Salazar, Fernández, & Quesada, 2003), with mating and maternity roosts separated geographically from bachelor and nonreproductive caves (Fleming & Nassar, 2002; Hayward & Cockrum, 1971; Sánchez & Medellín, 2007; Stoner et al.., 2003). Pregnant females congregate in maternity colonies to give birth, lactate, and care for their offspring (Ceballos et al., 2006), and they usually return to the same roost year after year in different stages of pregnancy and offspring rearing throughout their lifetimes (Hayward & Cockrum, 1971). Adult males and nonreproductive females often segregate into groups called “bachelor colonies” (Ceballos et al., 2006). Before foraging at night, both sexes rest in temporary night roosts (Ceballos et al., 2006; Cole & Wilson, 2006).

A study of the fecal microbiota of different reproductive stages within the central population of L. yerbabuenae showed that microbiota diversity is related to the reproductive stage rather than geographical distribution within this population (Gaona, Gómez‐Acata, Cerqueda‐García, Neri‐Barrios, & Falcón, 2019). Microbiota composition is consistent in juveniles and nonreproductive females and males, regardless of the roost. Pregnant and lactating females' microbiotas were similar and more diverse than juveniles and nonreproductive adults. One explanation for this is that microbiota evolved with its host to be flexible enough to shift from a specialized diet to a more generalist diet to cope with the increased energy requirements during pregnancy and lactation (Gaona et al., 2019).

The aim of this research is to evaluate the composition of fecal microbiota in two discrete, geographically separated and genetically differentiated lesser long‐nosed bat (L. yerbabuenae) populations in Mexico (Morales‐Garza et al., 2007). Our hypothesis is that the geographical separation and reproductive isolation of the two L. yerbabuenae populations will lead to significant differences in their fecal microbial composition, making it more similar within populations than between them. We also evaluate whether the heterogeneity within the Pacific population is due to differences between the reproductive stages, as occurs in the central population (Gaona et al., 2019).

2. METHODS

2.1. Study site

Bat fecal microbiome samples from the lesser long‐nosed bat, L. yerbabuenae, were collected at five bat roosts. Two were from the Pacific population—a roost of pregnant and lactating females in Pinacate, Sonora (32°0′0″N, 113°55′0″W), and a roost of reproductive males and juvenile males and females from Panchito cave, Jalisco (98°55′N, 19°32′W) (Figure 1). The remaining three roosts were from the central population: reproductive and juvenile males were sampled in San Juan Noxchitlan, Oaxaca (97°40′N, 18°03′W), a colony of 100,000 bats (Valiente‐Banuet et al., 1996). Pregnant and lactating females were sampled in Juxtlahuaca Cave, Guerrero (17°23″3′N, 99°16″1′W), and juvenile males and females and adult males were sampled in Salitre Cave, Morelos (18°45″0.05′N, 99°11″23.17′W) (Figure 1). All fecal samples were collected between January and November 2015 following the different L. yerbabuenae reproductive stages (Table 1) in the two populations.

Figure 1.

Figure 1

Distribution of Leptonycteris yerbabuenae and sampling sites in Mexico

Table 1.

Fecal samples collected from the Pacific population (n = 31) and Central population (n = 51)

Reproductive Stage Pacific population Central population
Juvenile females 7 2
Juvenile males 5 8
Adult females 0 11
Adult males 8 12
Pregnant 6 9
Lactating 5 9

2.2. Bat fecal microbiome sampling

Bats were captured using 12‐m mist nets (Avinet) at the entrance of the caves using Kunz's technique (Kunz, Betke, Hristov, & Vonhof, 2009) between 18:30 and 7:00 hr. Standard measurements were taken in order to confirm identification and assess the age and reproductive stage of individuals (Anthony, 1988; Kunz, Wemmer, & Hayssen, 1996). All fecal samples were obtained directly from individuals and frozen in sterile Eppendorf tubes with liquid nitrogen Dewar and stored at a −20°C temperature until processed for DNA extraction (see Appendix 2).

2.3. Analysis of the sequence data

The paired‐end 2 × 250 reads were processed in QIIME2 (Bolyen et al., 2019). The reads were denoised with the DADA2 (Callahan et al., 2016) plugin to resolve the amplicon sequence variants (ASVs). Both forward and reverse reads were truncated at 200 bp, and chimeric sequences were removed using the “consensus” method. Representative ASV sequences were taxonomically assigned using the “classify‐consensus‐vsearch plugin” with default arguments, using the SILVA 132 database as a reference (Quast et al., 2013). An alignment was performed with the MAFFT algorithm (Katoh, 2002). After masking positional conservations and gap filtering, a phylogeny was built with the FastTree2 algorithm (Price, Dehal, & Arkin, 2010).

The abundance table and phylogeny were exported to the R environment to perform the statistical analysis with the phyloseq (McMurdie & Holmes, 2013), vegan (Oksanen, 2015), and ggplot2 (Wilkinson, 2011) packages. Plastidic ASVs were filtered out of the samples (for subsequent separate analysis, see below), and then, the samples were rarefied to a minimum sequencing effort of 10,000. A PCoA ordination was performed with the weighted UniFrac distance (Figure 2). The Shannon alpha diversity index was calculated (Figure 4). A PERMANOVA with a weighted UniFrac distance was performed to assess whether there were significant differences among groups of samples (region and reproductive stages as predictor variables) with 1,000 permutations (Table 2).

Figure 2.

Figure 2

PCoA of weighted UniFrac distance. In the upper panels, each population is shown separately; in the bottom panel, the two populations are shown together

Table 2.

PERMANOVA analysis. In the pairwise mode, p value was adjusted using the Bonferroni method for multiple comparisons. In the nested mode, stages was nested within the populations in both, for prokaryotes and plastids

Pairwise for prokaryotes Model F R2 Adjusted p value
Adult versus Juvenile 1.834099 .04090859 .053946054
Adult versus Lactating 2.5512822 .06617892 .005994006*
Adult versus Pregnant 2.7072727 .06818078 .005994006*
Juvenile versus Lactating 3.0078068 .10023414 .005994006*
Juvenile versus Pregnant 3.3985729 .10823973 .005994006*
Lactating versus Pregnant 0.7640991 .03510823 1
  Model F R2 p value
Nested for prokaryote
Population 3.5636 .04694 .001*
Population:Stage 2.0599 .16279 .001*
Nested for plastids
Population 19.395 .19493 .001*
Population:Stage 3.350 .20202 .002*
*

The significant p‐values  < .05.

To explore the differential abundance of taxa, a LEfSe (linear discriminant analysis of effect size) analysis (Segata et al., 2011) was performed at the family level, first with all samples using the populations as categories, and then within each population, using the reproductive stages as categories, using an LDA cutoff >2 and p value < .05.

Counts of plastidic ASVs (separated from prokaryotic ASVs before rarefaction) were normalized with the cumulative sum scaling (CSS) method with the metagenomeSeq package (Paulson, Stine, Bravo, & Pop, 2013), and a DPCoA (Double Principle Coordinate Analysis) and the Shannon index were calculated to assess the likely variation in the diet of the bats in the different stages within the regions. A PERMANOVA was carried out with the DPCoA distance matrix to assess the beta diversity between populations. A Pearson correlation analysis was performed with the observed ASVs of plastid and prokaryotic 16S to assess the relationship between microbiota diversity (prokaryotic 16S ASVs) and diet diversity (plastidic ASVs).

3. RESULTS

3.1. Microbiome composition in the two populations of Leptonycteris yerbabuenae

Of the total samples collected, 68 were positively PCR amplified: 30 for the Pacific population (12 juvenile, 7 adult, 6 pregnant, and 5 lactating) and 38 for the central population (6 juvenile, 20 adult, 6 pregnant, and 6 lactating). We obtained a total of 11 566 ASVs after rarefying to a sampling depth of 10,000 reads (see the accumulation curve in Figure A1 of Appendix 1).

The Principal Coordinates Analysis (PCoA) showed beta diversity difference between the central (Guerrero, Morelos, and Oaxaca) and Pacific (Sonora and Jalisco) L. yerbabuenae populations (Figure 2, bottom). Within each population, pregnant and lactating females formed one group and juveniles and nonreproductive adults another (Figure 2. Top left and right).

Figure 3 shows the 40 most abundant bacterial classes, showing the differences between the composition within each population. There was a trend toward higher diversity among pregnant and lactating females in the central population, but higher diversity among juveniles in the Pacific population (Figures 3 and 4). The Shannon index shows that alpha diversity was more homogeneous within the Pacific population (Figure 4) than in the central population (Gaona et al., 2019).

Figure 3.

Figure 3

Abundances of the 40 most abundant classes; the remaining classes were grouped in the “others” category

Figure 4.

Figure 4

The Shannon index of samples grouped by reproductive stage and population. In the central population, there were significant differences among stages (Kruskal test p value < .01, chi‐squared = 14.37206)

Comparison using a PERMANOVA test showed differences among reproductive stages; there were significant differences in pairwise comparisons of lactating and pregnant females versus juveniles and adults, and a significant effect of reproductive stage nested within the population (Table 2), showing a clear difference both between the two populations and among stages within each population.

The LeFSe analysis shows differences among reproductive stages within each population at the family level in bacterial communities (Figure 5a) as well as between the two populations (Figure 5b). The Venn diagram (Figure 5b) shows 539 ASVs that are shared between the two populations. The central population had 6,939 ASVs and the Pacific 4,088 ASVs, a difference of 2,851 ASVs (Figure 5b). The two populations also differed in family‐level abundance. The LefSe analysis identified six differentiated families for each population; in the central population, these were Chtoniobactereaceae, Leptolyngbyaceae, Phormidiaceae, Microscillaceae, and WD2101 soil group; and in the Pacific population, these were Dietziaceae, Porphyromonadaceae, Brevibacteriaceae, Mycobacteriaceae, Nocardiaceae, and Khizobiaceae (Figure 5a).

Figure 5.

Figure 5

LeFSe analysis of samples with an LDA cutoff > 2 at the family level. (a) Families with differential abundance between populations; (b) Venn diagram showing the ASV shared between populations; (c) Families with differential abundance detected by the LeFSe analysis between reproductive stages within each population—for the central population, just the 10 families with the highest LDA score are shown for each stage (full list provided in Appendix 1)

3.2. Bat diet variability between the two regions

The amplification of plastid 16S genes is incidental in fecal microbiome studies. Since chloroplasts are plant organelles acquired by endosymbiosis, their amplification is due to contamination when the host feeds on plant material. Since different plant species’ chloroplasts differ genetically, plastidic 16S gene diversity may provide a relative index of plant diversity in the diet (Knight et al., 2018). The number of plastidic reads in the 68 samples ranged from 17 to 76,979, with a mean of 5,589 (see Table A1). We used the entire plastid dataset with the rationale that although some samples had very low plastid reads, the total reads per sample including bacterial 16S had more than 10,000 reads. After normalization by the CCS method to avoid the effect of differences in the libraries' sample sizes, we calculated the Shannon index and performed a DPCoA and a PERMANOVA (Figure 6 and Table 2).

Figure 6.

Figure 6

Diversity of plastidic ASVs in each stage within each population. (a) DPCoA ordination showing the distance among the samples; (b) Boxplots of the Shannon index among reproductive stages within each population; there was no significant difference in the Shannon index

Similar to the microbiota of the two populations, the beta diversity of chloroplast ASVs was higher in the central population (variance within the population), but alpha diversity was similar (Figure 6). Chloroplast diversity also differed among reproductive stages, with pregnant and lactating females having the highest beta chloroplast diversity (Figure 6).

4. DISCUSSION

Changes in microbiome composition could direct speciation, given that the functions of the microbiome have evolutionary consequences in the host (Suzuki, 2017). A central issue in the hologenome concept is whether the hologenome can be considered a unit of selection, in other words, whether the three components of natural selection—variation, differential success, and inheritance—apply to the holobiont (Cerqueda‐García & Falcón, 2016; Moran & Sloan, 2015; Suzuki, 2017). The differences we found between the two populations of L. yerbabuenae in Mexico suggest that in this case, there is variation in the holobiont. There is variation between the two populations, shown in the PCoA plot; the diversity within bacterial communities in the central population is larger than in the Pacific population (6,939 ASV, compared with 4,088 ASV), and the beta diversity among groups within the central population is more heterogeneous. In addition, Morales‐Garza et al. (2007) found higher genetic variability in the central population, associated with year‐round availability of pollen and nectar (Fleming & Nassar, 2002; Rojas‐Martínez et al., 1999; Villaseñor, Dávila, & Chiang, 2017). It remains to be tested whether these interpopulation microbiome differences could indicate differential success if the changes in microbial composition are related to losses or gains of metabolic capabilities that contribute to host fitness (Hooper, Littman, & Macpherson, 2012).

We found that the two populations share a core microbiota of only 539 ASVs and that these are the most abundant bacterial groups for both populations, accounting for about 75% of the relative abundance (Figure 7). This suggests stability in the microbiome within the populations over evolutionary time, and consistent with findings in hominids, the microbiome is more related to the species than to diet (Ochman et al., 2010). Each population has six families with differential abundance detected by the LeFSe analysis (Figure 5a) and a difference of 2,851 ASVs. In addition, ontological characteristics of bats, such as the rearrangement and growth of organs, including the stomach and the enlargement of the intestine, during pregnancy (Speakman, 2008), constrain differences and similarities in the microbiome (Gaona et al., 2019). Despite the changes in beta diversity due to geographical separation, the reproductive stages are more similar between the populations (Figure 3). Flexibility in the microbiome has been confirmed in experiments in which individuals of different species are given a similar diet, their microbiota tends to homogenize (Xiao et al., 2019). Our results partially support this result, since the populations we have studied are more similar within populations. However, we also found a core microbiome that also supports microbiota stability (Coyte, Schluter, & Foster, 2015) and ontogenetic differences in both populations (Gaona et al., 2019). The correlation between microbiota ASVs and plastid ASVs was positive and significant in the adult and juvenile stages (Figure A3), suggesting a more direct diet–microbiota relationship, and thus a Lamarckian acquisition of microbiota. However, this positive correlation is relaxed or broken in the pregnant and lactating stages in both populations. This suggests that in the demanding stages of pregnancy and lactation, the alpha diversity of microbiota increases more steeply than the plastids (diet), suggesting that the physiological state is driving the changes more than the diet. Thus, the core microbiota is present throughout the life cycle, but in pregnancy and lactation, the microbiota is more divergent (Figure 7). The PERMANOVA analysis of only pregnant and lactating females between the two populations showed that these stages have a higher coefficient of variance (R 2 ~ .13) than the adult and juvenile stages (R 2 ~ .10) (Figures A4 and A5).

Figure 7.

Figure 7

Family classification of the 539 shared ASVs among the two populations. The families with abundance below 1% were combined in the “others” category. The full list of families per sample is shown in Figure A2

The second and third requirements—differential success and evidence of inheritance of the microbiome—remain to be evaluated. One of the main predictions of microbiome heritability is that the offspring's microbiome will resemble parental microbiome. Thus, a progenitor holobiont (species A with its microbiome) will resemble its holobiont offspring (species B with its microbiome). We are unable to directly evaluate that statement here since we do not have samples of a parental‐progeny holobiont and this study solely focused on one bat species with geographical separation.

The term phylosymbiosis is used to describe the congruence between the differences in bacterial communities and the phylogenetic divergences among species (Brooks, Kohl, Brucker, Opstal, & Bordenstein, 2016; Kohl, Varner, Wilkening, & Dearing, 2018; Mazel et al., 2018), which, in a broad sense, corresponds to the inheritance of the microbiome. While the two populations we sampled in this study are the same species, our data show a relationship between differences in host bacterial communities and genetic differences among populations (Morales‐Garza et al., 2007), which could suggest an early process of phylosymbiosis which has not been explored before in a geographical separation model. As described above, the differences between the two populations of L. yerbabuenae show higher variation (beta diversity) in the microbiota the central population (Figures 2 and 4), which also has a higher genetic diversity and is a more stable population (Morales‐Garza et al., 2007).

Macroecological theory indicates that the highest genetic diversity will be found in areas with better access to resources and the best ecological conditions for the species. For this species, the available resources have determined two main divergence routes and very likely the segregation of the species, as confirmed by stable isotope analysis of mitochondrial DNA (Burke et al., 2019), and these changes correspond with orography (Burke et al., 2019). L. yerbabuenae are reliant on the availability of flowers, and the central region has year‐long availability (Fleming & Nassar, 2002; Rojas‐Martínez et al., 1999; Villaseñor et al., 2017) in contrast to the seasonal availability of the Pacific region (Petit, Excoffier, & Mayer, 1999). Thus, the reproductive peaks of bats and the population composition are different between the populations, apparently supported by the beta diversity of the plastid ASVs, and the variance between the two populations is high (R 2 ~ .2 from the PERMANOVA, Table 2).

Our results show a differentiation of the microbiota composition between populations and among reproductive stages. One explanation for these trends is the differentiation of the diet, which has been demonstrated to be the main factor shaping the functionality and diversity of the gut microbiome, resulting in the convergence between microbial communities and their hosts’ foraging habits (Muegge et al., 2011). There is evidence that the diet shapes the functionality, diversity, and relative abundance of dominant phyla, as well as the populations of specific bacterial groups; this is influenced in part by the composition of macronutrients consumed and in part by the introduction of new microbes from food itself (Muegge et al., 2011; Voreades, Kozil, & Weir, 2014).

In the two populations of L. yerbabuenae, our results show significant differences in the beta diversity of lactating and pregnant females, perhaps associated with the high energy, protein and calcium requirements during these life stages (Gaona et al., 2019; Speakman, 2008). Previous work has shown that the diversity of plants consumed by L. yerbabueanae is 2.4 times higher among pregnant and lactating females than among nonreproductive females and males (Riechers, Martínez‐Coronel, & Vidal, 2003). This increased foraging diversity is also reflected in our results, with a higher diversity of gut microbes in pregnant and lactating females in the central population, likely due to the diversified diet due to the physiological conditions of pregnancy and lactation and the high plant diversity in the central region (Figure 6).

The analysis of chloroplasts showed a difference between the two populations; while there was some overlap between the central population and Pacific population adults, the two populations tended to separate, with lower diversity in the Pacific (Figure 6).

5. CONCLUSION

The differential fecal microbiota composition of the two L. yerbabuenae populations, central and Pacific, which inhabit geographically disjunct ranges that differ in their availability of nectar and pollen, opens the door to exploring microbiome–bat relationships that may be influenced by natural selection. Both variation and stability are present, suggesting that it is not just the host, but the host–microbiome unit, the “holobiont,” which could be subject to natural selection and evolutionary processes (Cerqueda‐García & Falcón, 2016; Suzuki, 2017). This study suggests a differentiation between both populations' microbiota as a consequence of geographical separation and food resources availability. Diversity was highest in the central population, where there is also higher genetic diversity, perhaps due to the unrestricted availability of foraging resources. This is in contrast to the Pacific population, which had lower microbiome and genetic variability, probably because resources are only available seasonally. These resource availability interactions influence reproduction and population size, with increased genetic diversity, both in the host and in the microbiome. Interestingly, these two populations share a core microbiota of 539 ASVs accounting for 75% of the relative abundance, being the most abundant microbiota stable over evolutionary time, and these results may support the phylosymbiosis theory.

CONFLICT OF INTERESTS

None declared.

AUTHOR CONTRIBUTIONS

Osiris Gaona: Conceptualization; Formal analysis; Funding acquisition; Investigation; Methodology; Project administration; Supervision; Visualization; Writing‐original draft; Writing‐review & editing. Daniel Cerqueda‐Garcia: Data curation; Formal analysis; Investigation; Methodology; Software; Validation; Visualization; Writing‐original draft; Writing‐review & editing. Andres Moya: Validation; Writing‐review & editing. Carla Ximena Neri‐Barrios: Investigation; Visualization; Writing‐original draft; Writing‐review & editing. Luisa Falcón: Conceptualization; Funding acquisition; Resources; Supervision.

ETHICS STATEMENT

Sampling procedures strictly followed the guidelines of the American Society of Mammalogists for capture, handling and care of mammals (Gardner, 1976; Sikes & Gannon, 2011). To minimize animal suffering and distress, each animal was processed by experts only, ensuring safe and effective handling. Samples were taken from wild bats that were released in the same area of capture, causing no apparent harm to individuals. Leptonycteris yerbabuenae is not subject to federal protection under Mexican law (NOM‐059‐SEMARNAT‐2010). All activities were approved and authorized under a scientific collection permit granted by the Mexican Subsecretary of the Environment and Natural Resources (SEMARNAT), number FAUT‐0231, SGPA/DGVS/05780/15 SEMARNAT. Laboratory sample processing activities fulfilled all biosafety standard requirements of the Ecology Institute of the Universidad Nacional Autónoma de México (UNAM), under the authorization from the Biosafety Commission of the Ecology Institute, UNAM.

ACKNOWLEDGMENTS

This study comprises part of the PhD thesis work of O. Gaona in the Posgrado en Ciencias Biologicas, UNAM. Funding for this work was provided by SEP‐CONACyT No. 254962 (L. Falcón) and Soluciones Ambientales Itzeni AC (O. Gaona). Bats were sampled under the SEMARNAT permit No. FAUT‐0231 granted to Alfonso Valiente Banuet. The authors would like to thank A. Valiente and J.J. Castillo (Instituto de Ecología, UNAM), Felipe Rincón, Raymundo Torres (Universidad Veracruzana), Ana Galicia (IE‐UNAM) for fruitful discussions and help in the field.

APPENDIX 1.

Figure A1.

Figure A1

Accumulation curve by simple at 10,000 reads

Figure A2.

Figure A2

Complete shared families between populations

Figure A3.

Figure A3

Linear correlation (Pearson), in each stage between prokaryotic and plastid ASVs. The p values were adjusted with the FDR method

Figure A4.

Figure A4

PCoA analysis of juvenile and adult samples with the weighted unifrac distance. The PERMANOVA test showed that central (juvenile‐adult) versus pacific (juvenile‐adult) have significant differences (F = 5.262616, R2 = .1090412, p‐value = .001), with a variance of ~10%

Figure A5.

Figure A5

PCoA analysis of pregnant and lactating samples with the weighted unifrac distance. The PERMANOVA test showed that central (pregnant‐lactating) versus pacific (pregnant‐lactating) have significant differences (F = 3.1313, R 2 = .1297609, p‐value = .001), with a variance of ~13%

Table A1.

The number of reads of plastid 16S in each sample

Sample Counts Region Stage
C11 1,386 Central Adult
C13 331 Central Adult
C15 551 Central Adult
C17 1,421 Central Adult
C19 13,395 Central Adult
C21 3,747 Central Adult
C23 12,756 Central Adult
C26 2,881 Central Juvenil
C27 10,388 Central Juvenil
C28 5,026 Central Juvenil
C29 913 Central Juvenil
C3 732 Central Adult
C30 59 Central Juvenil
C32 57 Central Juvenil
C33 24,607 Central Adult
C34 15,030 Central Adult
C35 6,045 Central Adult
C36 5,791 Central Adult
C41 3,075 Central Adult
C42 7,323 Central Adult
C43 16,467 Central Adult
C44 14,362 Central Adult
C5 997 Central Adult
C57 184 Central Lactating
C62 96 Central Pregnant
C65 211 Central Pregnant
C67 17 Central Pregnant
C69 258 Central Lactating
C7 603 Central Adult
C71 780 Central Pregnant
C73 126 Central Lactating
C74 109 Central Lactating
C76 30 Central Adult
C77 322 Central Lactating
C79 76,979 Central Pregnant
C81 511 Central Pregnant
C83 178 Central Lactating
C9 1,412 Central Adult
P1 1,204 Pacific Lactating
P10 603 Pacific Pregnant
P11 512 Pacific Pregnant
P2 282 Pacific Lactating
P20 146 Pacific Juvenil
P21 1,366 Pacific Juvenil
P22 1,425 Pacific Adult
P23 40 Pacific Adult
P24 27,831 Pacific Juvenil
P25 47,656 Pacific Adult
P27 4,636 Pacific Adult
P28 1564 Pacific Adult
P29 913 Pacific Adult
P3 5,953 Pacific Lactating
P30 7,114 Pacific Juvenil
P31 39,840 Pacific Juvenil
P32 420 Pacific Juvenil
P33 179 Pacific Juvenil
P34 736 Pacific Adult
P35 181 Pacific Juvenil
P36 90 Pacific Juvenil
P37 334 Pacific Juvenil
P38 299 Pacific Juvenil
P39 1999 Pacific Juvenil
P4 290 Pacific Pregnant
P5 2093 Pacific Lactating
P6 1907 Pacific Pregnant
P7 362 Pacific Pregnant
P8 432 Pacific Pregnant
P9 978 Pacific Lactating

APPENDIX 2.

Extraction of DNA from feces

Metagenomic fecal DNA was extracted using the DNeasy Blood & Tissue kit (Qiagen) according to the manufacturer's instructions. Briefly, feces collected into 1.5 ml sterile tubes were diluted with 180 μl of ATL extraction buffer with 20 μl proteinase K (10 mg/ml). Tubes were mixed thoroughly by vortexing and were incubated at 56°C at 1,500 rpm for 50 min. 200 μl of AL Buffer with 200 μl ethanol (96%–100%) were added and mixed thoroughly by vortexing. The mixture was transferred into the DNeasy Mini spin column, washed with Buffer AW1 and then with AW2. The DNA was eluted with 200 μl of AE Buffer and precipitated with absolute ethanol, 0.1 volume 3 M sodium acetate and 2 µl GlycoBlue. DNA was resuspended in 30 µl of molecular grade water and stored at −20°C until PCR amplification.

16S rRNA gene amplification and sequencing

DNA samples were PCR‐amplified using the hypervariable V4 region of the 16S rRNA gene with universal bacterial/archaeal primers 515F/806R following the procedures reported by Caporaso et al. (2012) and Carrillo‐Araujo et al. (2015). PCR reactions (25 µl) contained 2–6 ng of total DNA, 2.5 µl Takara ExTaq PCR buffer 10X, 2 µl Takara dNTP mix (2.5 mM), 0.7 µl bovine serum albumin (BSA, 20 mg/ml), 1 µl primers (10 μM), 0.125 µl Takara Ex Taq DNA Polymerase (5 U/μl) (TaKaRa) and nuclease‐free water. Samples were amplified in triplicate using a PCR protocol consisting of an initial denaturation step at 95°C (3 min), followed by 35 cycles of 95°C (30 s), 52°C (40 s) and 72°C (90 s), followed by a final extension (72°C, 12 min). Triplicates were then pooled and purified using the SPRI magnetic bead, AgencourtAMPure XP PCR purification system (Beckman Coulter). The purified 16S rRNA fragments (~20 ng per sample) were sequenced on an IlluminaMiSeq platform (Yale Center for Genome Analysis), generating ~250 bp paired‐end reads.

Gaona O, Cerqueda‐García D, Moya A, Neri‐Barrios X, Falcón LI. Geographical separation and physiology drive differentiation of microbial communities of two discrete populations of the bat Leptonycteris yerbabuenae . MicrobiologyOpen. 2020;9:e1022 10.1002/mbo3.1022

Contributor Information

Daniel Cerqueda‐García, Email: dacegabiol@ciencias.unam.mx.

Luisa I. Falcón, Email: falcon@ecologia.unam.mx.

DATA AVAILABILITY STATEMENT

The raw reads are available at the NCBI database under BioProjects PRJNA508738: https://www.ncbi.nlm.nih.gov/bioproject/PRJNA508738 and PRJNA543523: https://www.ncbi.nlm.nih.gov/bioproject/PRJNA543523.

REFERENCES

  1. Alberdi, A. , Aizpurua, O. , Bohmann, K. , Zepeda‐Mendoza, M. L. , & Gilbert, M. T. (2016). Do vertebrate gut metagenomes confer rapid ecological adaptation? Trends in Ecology and Evolution, 31, 689–699. 10.1016/j.tree.2016.06.008 [DOI] [PubMed] [Google Scholar]
  2. Anthony, E. L. P. (1988). Age determination in batsIn Kunz T. H. (Ed.), Ecological and behavioral methods for the study of bats (pp. 47–58). Washington, DC: Smithsonian Institution Press. [Google Scholar]
  3. Arita, H. T. (1991). Spatial segregation in long‐nosed bats, Leptonycteris nivalis and Leptonycteris curasoae, in Mexico. Journal of Mammalogy, 72(4), 706–714. 10.2307/1381831 [DOI] [Google Scholar]
  4. Arita, H. T. , & Humphrey, S. R. (1988). Revision taxonomica de los murcielagos magueyeros del genero Leptonycteris Chiroptera: Phyllostomidae). Acta Zoologica Mexicana, 29, 1–60. [Google Scholar]
  5. Bolyen, E. , Rideout, J. R. , Dillon, M. R. , Bokulich, N. A. , Abnet, C. C. , Al‐Ghalith, G. A. , … Caporaso, J. G. (2019). Reproducible, interactive, scalable and extensible microbiome data science using QIIME 2. Nature Biotechnology, 37(8), 852–857. 10.1038/s41587-019-0209-9 [DOI] [PMC free article] [PubMed] [Google Scholar]
  6. Brockhurst, M. A. , & Koskella, B. (2013). Experimental coevolution of species interactions. Trends in Ecology and Evolution, 28(6), 367–375. 10.1016/j.tree.2013.02.009 [DOI] [PubMed] [Google Scholar]
  7. Brooks, A. W. , Kohl, K. D. , Brucker, R. M. , van Opstal, E. J. , & Bordenstein, S. R. (2016). Phylosymbiosis: Relationships and functional effects of microbial communities across host evolutionary history. PLoS Biology, 14(11), e2000225 10.1371/journal.pbio.2000225 [DOI] [PMC free article] [PubMed] [Google Scholar]
  8. Brucker, R. M. , & Bordenstein, S. R. (2012). The roles of host evolutionary relationships (genus: Nasonia) and development in structuring microbial communities. Evolution, 66, 349–362. 10.1111/j.1558-5646.2011.01454.x [DOI] [PubMed] [Google Scholar]
  9. Burke, R. A. , Frey, J. K. , Ganguli, A. , & Stoner, K. E. (2019). Species distribution modelling supports “nectar corridor” hypothesis for migratory nectarivorous bats and conservation of tropical dry forest. Diversity and Distribution, 25(9), 1399–1415. 10.1111/ddi.12950 [DOI] [Google Scholar]
  10. Callahan, B. J. , McMurdie, P. J. , Rosen, M. J. , Han, A. W. , Johnson, A. J. A. , & Holmes, S. P. (2016). DADA2: High‐resolution sample inference from Illumina amplicon data. Nature Methods, 13(7), 581–583. 10.1038/nmeth.3869 [DOI] [PMC free article] [PubMed] [Google Scholar]
  11. Caporaso, J. G. , Lauber, C. L. , Walters, W. A. , Berg‐Lyons, D. , Huntley, J. , Fierer, N. , … Knight, R. (2012). Ultra‐high‐throughput microbial community analysis on the Illumina HiSeq and MiSeq platforms. ISME Journal, 6(8), 1621–1624. 10.1038/ismej.2012.8 [DOI] [PMC free article] [PubMed] [Google Scholar]
  12. Carrillo‐Araujo, M. , Taş, N. , Alcántara‐Hernández, R. J. , Gaona, O. , Schondube, J. E. , Medellín, R. A. , … Falcón, L. I. (2015). Phyllostomid bat microbiome composition is associated to host phylogeny and feeding strategies. Frontiers in Microbiology, 6, 447 10.3389/fmicb.2015.00447 [DOI] [PMC free article] [PubMed] [Google Scholar]
  13. Ceballos, G. , Fleming, T. H. , Chavez, C. , & Nassar, J. (2006). Population dynamics of Leptonycteris curasoae (Chiroptera: Phyllostomidae) in Jalisco, Mexico. Journal of Mammalogy, 78(4), 1220–1230. 10.2307/1383065 [DOI] [Google Scholar]
  14. Cerqueda‐García, D. , & Falcón, L. I. (2016). La construcción del nicho y el concepto de holobionte, hacia la reestructuración de un paradigma. Revista Mexicana De Biodiversidad, 87(1), 239–241. 10.1016/j.rmb.2015.11.001 [DOI] [Google Scholar]
  15. Cockrum, E. L. (1991). Seasonal distribution of northwestern populations of the long‐nosed bats, Leptonycteris sanborni, family Phyllostomidae. Mexico City, Mexico: Anales Del Instituto de Biologia Universidad Nacional Autonoma de Mexico Serie Zoologia. [Google Scholar]
  16. Cole, F. R. , & Wilson, D. E. (2006). Leptonycteris yerbabuenae . Mammalian Species, 797, 1–7. 10.1644/797.1 [DOI] [Google Scholar]
  17. Coyte, K. Z. , Schluter, J. , & Foster, K. R. (2015). The ecology of the microbiome: Networks, competition, and stability. Science, 350, 663–666. 10.1126/science.aad2602 [DOI] [PubMed] [Google Scholar]
  18. Fleming, T. H. , & Nassar, J. (2002).Population biology of the lesser long‐nosed bat Leptonycteris curasoae in Mexico and northern South America In Fleming T. H., & Valiente‐Banuet A. (Eds.), Columnar cacti and their mutualists: Evolution, ecology, and conservation (pp. 283–305). Tucson, AZ: University of Arizona Press. [Google Scholar]
  19. Gaona, O. , Gómez‐Acata, E. S. , Cerqueda‐García, D. , Neri‐Barrios, C. X. , & Falcón, L. I. (2019). Fecal microbiota of different reproductive stages of the central population of the lesser‐long nosed bat, Leptonycteris yerbabuenae . PLoS ONE, 14(7), e0219982 10.1371/journal.pone.0219982 [DOI] [PMC free article] [PubMed] [Google Scholar]
  20. Gardner, A. L. , (1976). Feeding habits In Baker R. J., Jones J., Knox J., & Carter D. C. (Eds.), Biology of bats of the New World family Phyllostomatidae, Part II (pp. 293–350). Lubbock, Texas: Special Publications of The Museum of Texas Tech University; 10.1371/journal.pone.0219982 [DOI] [Google Scholar]
  21. Hayward, B. J. , & Cockrum, E. L. (1971). The natural history of the western long‐nosed bat: Leptonycteris sanborni. Silver City, NewMexico: Office of Research, Western New Mexico University. [Google Scholar]
  22. Hooper, L. V. , Littman, D. R. , & Macpherson, A. J. (2012). Interactions between the microbiota and the immune system. Science, 336(6086), 1268–1273. 10.1126/science.1223490 [DOI] [PMC free article] [PubMed] [Google Scholar]
  23. Ingala, M. R. , Becker, D. J. , Bak Holm, J. , Kristiansen, K. , & Simmons, N. B. (2019). Habitat fragmentation is associated with dietary shifts and microbiota variability in common vampire bats. Ecology and Evolution, 9, 6508–6523. 10.1002/ece3.5228 [DOI] [PMC free article] [PubMed] [Google Scholar]
  24. Katoh, K. (2002). MAFFT: A novel method for rapid multiple sequence alignment based on fast Fourier transform. Nucleic Acids Research, 30(14), 3059–3066. 10.1093/nar/gkf436 [DOI] [PMC free article] [PubMed] [Google Scholar]
  25. Knight, R. , Vrbanac, A. , Taylor, B. C. , Aksenov, A. , Callewaert, C. , Debelius, J. , … Dorrestein, P. C. (2018). Best practices for analysing microbiomes. Nature Reviews Microbiology, 16(7), 410–422. 10.1038/s41579-018-0029-9 [DOI] [PubMed] [Google Scholar]
  26. Knutie, S. A. (2020). Food supplementation affects gut microbiota and immunological resistance to parasites in a wild bird species. Journal of Applied Ecology, 1–12. 10.1111/1365-2664.13567 31957374 [DOI] [Google Scholar]
  27. Kohl, K. D. , Varner, J. , Wilkening, J. L. , & Dearing, M. D. (2018). Gut microbial communities of American pikas (Ochotona princeps): Evidence for phylosymbiosis and adaptations to novel diets. Journal of Animal Ecology, 8, 323–330. 10.1111/1365-2656.12692 [DOI] [PubMed] [Google Scholar]
  28. Kunz, T. H. , Betke, M. , Hristov, N. I. , & Vonhof, M. J. (2009). Methods for assessing colony size, population size, and relative abundance of bats. Ecological and Behavioral Methods for the Study of Bats, 133, 157. [Google Scholar]
  29. Kunz, T. H. , Wemmer, C. , & Hayssen, V. (1996). Sex, age, and reproductive condition of mammals In Wilson D. E., Cole F. R., Nichols J. D., Rudran R., & Foster M. S. (Eds.), Measuring and monitoring biological diversity: Standard methods for mammals (pp. 279–290). Washington, DC: Smithsonian Institution Press. [Google Scholar]
  30. Ley, R. E. , Hamady, M. , Lozupone, C. , Turnbaugh, P. J. , Ramey, R. R. , Bircher, J. S. , … Gordon, J. I. (2008). Evolution of mammals and their gut microbes. Science, 320(5883), 1647–1651. [DOI] [PMC free article] [PubMed] [Google Scholar]
  31. Lutz, H. L. , Jackson, E. W. , Webala, P. W. , Babyesiza, W. S. , Kerbis Peterhans, J. C. , Demos, T. C. , … Gilbert, J. A. (2019). Ecology and host identity outweigh evolutionary history in shaping the bat microbiome. Msystems, 4, e00511‐19 10.1128/mSystems.00511-19 [DOI] [PMC free article] [PubMed] [Google Scholar]
  32. MacColl, A. D. C. (2011). The ecological causes of evolution. Trends in Ecology and Evolution, 26(10), 514–522. 10.1016/j.tree.2011.06.009 [DOI] [PubMed] [Google Scholar]
  33. Martiny, J. B. H. , Bohannan, B. J. M. , Brown, J. H. , Colwell, R. K. , Fuhrman, J. A. , Green, J. L. , … Staley, J. T. (2006). Microbial biogeography: Putting microorganisms on the map. Nature Reviews Microbiology, 4(2), 102–112. 10.1038/nrmicro1341 [DOI] [PubMed] [Google Scholar]
  34. Mazel, F. , Davis, K. M. , Loudon, A. , Kwong, W. K. , Groussin, M. , & Parfrey, L. W. (2018). Is host filtering the main driver of phylosymbiosis across the tree of life? Msystems, 3(5), e00097‐18 10.1128/msystems.00097-18 [DOI] [PMC free article] [PubMed] [Google Scholar]
  35. McMurdie, P. J. , & Holmes, S. (2013). Phyloseq: An R package for reproducible interactive analysis and graphics of microbiome census data. PLoS ONE, 8(4), e61217 10.1371/journal.pone.0061217 [DOI] [PMC free article] [PubMed] [Google Scholar]
  36. Monteiro, L. R. , & Nogueira, M. R. (2011). Evolutionary patterns and processes in the radiation of Phyllostomid bats. BMC Evolutionary Biology, 11, 37 10.1186/1471-2148-11-137 [DOI] [PMC free article] [PubMed] [Google Scholar]
  37. Morales‐Garza, M. R. , Arizmendi, M. D. C. , Campos, J. E. , Martínez‐Garcia, M. , & Valiente‐Banuet, A. (2007). Evidences on the migratory movements of the nectar‐feeding bat Leptonycteris curasoae in Mexico using random amplified polymorphic DNA (RAPD). Journal of Arid Environments, 68(2), 248–259. 10.1016/j.jaridenv.2006.05.009 [DOI] [Google Scholar]
  38. Moran, N. A. , & Sloan, D. B. (2015). The hologenome concept: Helpful or hollow? PLOS Biology, 13(12), e1002311 10.1371/journal.pbio.1002311 [DOI] [PMC free article] [PubMed] [Google Scholar]
  39. Muegge, B. D. , Kuczynski, J. , Knights, D. , Clemente, J. C. , Gonzalez, A. , Fontana, L. , … Gordon, J. I. (2011). Diet drives convergence in gut microbiome functions across mammalian phylogeny and within humans. Science, 332(6032), 970–974. 10.1126/science.1198719 [DOI] [PMC free article] [PubMed] [Google Scholar]
  40. Ochman, H. , Worobey, M. , Kuo, C.‐H. , Ndjango, J.‐B. , Peeters, M. , Hahn, B. H. , & Hugenholtz, P. (2010). Evolutionary relationships of wild hominids recapitulated by gut microbial communities. PLoS Biology, 8(11), e1000546 10.1371/journal.pbio.1000546 [DOI] [PMC free article] [PubMed] [Google Scholar]
  41. Oksanen, J. , Blanchet, F. , Kindt, R. , Legendre, P. , O’Hara, R. B. , Simpson, G. , … Wagner, H. (1988). Multivariate analysis of ecological communities. Vegan Tutorial (pp. 1–40).
  42. Paulson, J. N. , Stine, O. C. , Bravo, H. C. , & Pop, M. (2013). Differential abundance analysis for microbial marker‐gene surveys. Nature Methods, 10(12), 1200–1202. 10.1038/nmeth.2658 [DOI] [PMC free article] [PubMed] [Google Scholar]
  43. Petit, E. , Excoffier, L. , & Mayer, F. (1999). No evidence of bottleneck in the postglacial recolonization of Europe by the noctule bat (Nyctalus noctula). Evolution, 53(4), 1247 10.2307/2640827 [DOI] [PubMed] [Google Scholar]
  44. Phillips, C. D. , Hanson, J. , Wilkinson, J. E. , Koenig, L. , Rees, E. , Webala, P. , & Kingston, T. (2017). Microbiome structural and functional interactions across host dietary niche space. Integrative and Comparative Biology, 57(4), 743–755. 10.1093/icb/icx011 [DOI] [PubMed] [Google Scholar]
  45. Phillips, C. D. , Phelan, G. , Dowd, S. E. , McDONOUGH, M. M. , Ferguson, A. W. , Delton Hanson, J. , … Baker, R. J. (2012). Microbiome analysis among bats describes influences of host phylogeny, life history, physiology and geography. Molecular ecology, 21(11), 2617–2627. [DOI] [PubMed] [Google Scholar]
  46. Price, M. N. , Dehal, P. S. , & Arkin, A. P. (2010). FastTree 2 – Approximately maximum‐likelihood trees for large alignments. PLoS ONE, 5(3), e9490 10.1371/journal.pone.0009490 [DOI] [PMC free article] [PubMed] [Google Scholar]
  47. Quast, C. , Pruesse, E. , Yilmaz, P. , Gerken, J. , Schweer, T. , Yarza, P. , … Glöckner, F. O. (2013). The SILVA ribosomal RNA gene database project: Improved data processing and web‐based tools. Nucleic Acids Research, 41(D1), D590–D596. 10.1093/nar/gks1219 [DOI] [PMC free article] [PubMed] [Google Scholar]
  48. Riechers, P. A. , Martínez‐Coronel, M. , & Vidal, R. (2003). Consumo de polen de una colonia de maternidad de Leptonycteris curasoae yerbabuenae en Tuxtla Gutiérrez, Chiapas, México. Anales Del Instituto De Biología, Serie Zoología, 74, 53–66. [Google Scholar]
  49. Rojas‐Martínez, A. , Valiente‐Banuet, A. , del Coro Arizmendi, M. , Alcántara‐Eguren, A. , & Arita, H. T. (1999). Seasonal distribution of the long‐nosed bat (Leptonycteris curasoae) in North America: Does a generalized migration pattern really exist? Journal of Biogeography, 26(5), 1065–1077. 10.1046/j.1365-2699.1999.00354.x [DOI] [Google Scholar]
  50. Rosenberg, E. , & Zilber‐Rosenberg, I. (2019). The hologenome concept of evolution: Medical implications. Rambam Maimonides Medical Journal, 10(1), e0005 10.5041/rmmj.10359 [DOI] [PMC free article] [PubMed] [Google Scholar]
  51. Sánchez, R. , & Medellín, R. A. (2007). Food habits of the threatened bat Leptonycteris nivalis (Chiroptera: Phyllostomidae) in a mating roost in Mexico. Journal of Natural History, 41(25–28), 1753–1764. 10.1080/00222930701483398 [DOI] [Google Scholar]
  52. Segata, N. , Izard, J. , Waldron, L. , Gevers, D. , Miropolsky, L. , Garrett, W. S. , & Huttenhower, C. (2011). Metagenomic biomarker discovery and explanation. Genome Biology, 12(6), R60 10.1186/gb-2011-12-6-r60 [DOI] [PMC free article] [PubMed] [Google Scholar]
  53. Shapira, M. (2016). Gut microbiotas and host evolution: Scaling up symbiosis. Trends in Ecology and Evolution, 31(7), 539–549. 10.1016/j.tree.2016.03.006 [DOI] [PubMed] [Google Scholar]
  54. Sikes, R. S. , & Gannon, W. L. (2011). Guidelines of the American Society of Mammalogists for the use of wild mammals in research. Journal of Mammalogy, 92(1), 235–253. 10.1644/10-MAMM-F-355.1 [DOI] [PMC free article] [PubMed] [Google Scholar]
  55. Speakman, J. R. (2008). The physiological costs of reproduction in small mammals. Philosophical Transactions of the Royal Society B: Biological Sciences, 363(1490), 375–398. 10.1098/rstb.2007.2145 [DOI] [PMC free article] [PubMed] [Google Scholar]
  56. Stoner, K. E. , Salazar, K. A. O. , Fernández, R. C. R. , & Quesada, M. (2003). Population dynamics, reproduction, and diet of the lesser long‐nosed bat (Leptonycteris curasoae) in Jalisco, Mexico: Implications for conservation. Biodiversity and Conservation, 12(2), 357–373. 10.1023/A:1021963819751 [DOI] [Google Scholar]
  57. Suzuki, T. A. (2017). Links between natural variation in the microbiome and host fitness in wild mammals. Integrative and Comparative Biology, 57(4), 756–769. 10.1093/icb/icx104 [DOI] [PubMed] [Google Scholar]
  58. Valiente‐Banuet, A. , Arizmendi, M. D. C. , Rojas‐Martínez, A. , & Domínguez‐Canseco, L. (1996). Ecological relationships between columnar cacti and nectar‐feeding bats in Mexico. Journal of Tropical Ecology, 12(1), 103–119. 10.1017/S0266467400009330 [DOI] [Google Scholar]
  59. Villaseñor, J. L. , Dávila, P. , & Chiang, F. (2017). Fitogeografía del Valle de Tehuacán‐Cuicatlán. Botanical Sciences, 50, 135 10.17129/botsci.1381 [DOI] [Google Scholar]
  60. Voreades, N. , Kozil, A. , & Weir, T. L. (2014). Diet and the development of the human intestinal microbiome. Frontiers in Microbiology, 5, 494 10.3389/fmicb.2014.00494 [DOI] [PMC free article] [PubMed] [Google Scholar]
  61. Wilkinson, L. (2011). ggplot2: Elegant graphics for data analysis by Wickham, H. Biometrics, 67(2), 678–679. 10.1111/j.1541-0420.2011.01616.x [DOI] [Google Scholar]
  62. Xiao, Y. , Xiao, G. , Liu, H. , Zhao, X. , Sun, C. , Tan, X. , … Feng, J. (2019). Captivity causes taxonomic and functional convergence of gut microbial communities in bats. PeerJ, 7, e6844. [DOI] [PMC free article] [PubMed] [Google Scholar]
  63. Zilber‐Rosenberg, I. , & Rosenberg, E. (2008). Role of microorganisms in the evolution of animals and plants: The hologenome theory of evolution. FEMS Microbiology Reviews, 32(5), 723–735. 10.1111/j.1574-6976.2008.00123.x [DOI] [PubMed] [Google Scholar]

Associated Data

This section collects any data citations, data availability statements, or supplementary materials included in this article.

Data Availability Statement

The raw reads are available at the NCBI database under BioProjects PRJNA508738: https://www.ncbi.nlm.nih.gov/bioproject/PRJNA508738 and PRJNA543523: https://www.ncbi.nlm.nih.gov/bioproject/PRJNA543523.


Articles from MicrobiologyOpen are provided here courtesy of Wiley

RESOURCES