ORIGINAL RESEARCH article

Front. Microbiol., 21 December 2015

Sec. Evolutionary and Genomic Microbiology

Volume 6 - 2015 | https://doi.org/10.3389/fmicb.2015.01403

Comparative Gut Microbiota of 59 Neotropical Bird Species

  • 1. Museum of Natural Science, Louisiana State University Baton Rouge, LA, USA

  • 2. Department of Biological Sciences, Louisiana State University Baton Rouge, LA, USA

  • 3. Department of Evolution, Ecology and Organismal Biology, Ohio State University Columbus, OH, USA

Article metrics

View details

279

Citations

17k

Views

4,1k

Downloads

Abstract

The gut microbiota of vertebrates are essential to host health. Most non-model vertebrates, however, lack even a basic description of natural gut microbiota biodiversity. Here, we sampled 116 intestines from 59 Neotropical bird species and used the V6 region of the 16S rRNA molecule as a microbial fingerprint (average coverage per bird ~80,000 reads). A core microbiota of Proteobacteria, Firmicutes, Bacteroidetes, and Actinobacteria was identified, as well as several gut-associated genera. We tested 18 categorical variables associated with each bird for significant correlation to the gut microbiota; host taxonomic categories were most frequently significant and explained the most variation. Ecological variables (e.g., diet, foraging stratum) were also frequently significant but explained less variation. Little evidence was found for a significant influence of geographic space. Finally, we suggest that microbial sampling during field collection of organisms would propel biological understanding of evolutionary history and ecological significance of host-associated microbiota.

Introduction

Gut microbiota are an essential component of vertebrate health. Microbes provide many necessary functions for the host organism, including aiding digestion, vitamin synthesis, protection against pathogens, training the immune system and organ development (Qin et al., 2010; Diaz Heijtz et al., 2011; Al-Asmakh et al., 2014). The gut microbiota is one of the most densely populated natural environments known (Whitman et al., 1998), possibly composed of thousands of species (Xu and Gordon, 2003). Generally speaking, gut microbiota communities tend to be more similar between more similar hosts, although the specific members of the microbiota can vary significantly between hosts of the same species (Eckburg et al., 2005; Hird et al., 2014) and even between identical twins (Turnbaugh et al., 2010). The microbiota may have an influence above the level of the individual, as they can affect mate choice (Sharon et al., 2010) and cause hybrid inviability (Brucker and Bordenstein, 2013). Understanding the role of the microbiota in evolution is a major outstanding question and the subject of much ongoing research.

Birds are a globally distributed class of vertebrates. The bird lineage is thought to be approximately 150 million years old and has likely been in symbiotic relationships with microorganisms the entire time. Birds live on every continent and exhibit extreme morphological and ecological diversity, much of which is centered in the Neotropics (Jenkins et al., 2013). Pertinent to gut microbiota, bird diets range from robust and opportunistic to strictly carrion feeding (i.e., vultures) to nectar feeding (i.e., hummingbirds) to folivorous (i.e., hoatzin) with corresponding variation in their intestinal morphology. Most avian gut microbiota studies have looked at one or a few host species; from these studies we know that bird gut microbiota are influenced by host genetics and evolutionary history (Banks et al., 2009; Dewar et al., 2013) as well as by ecological factors, such as dietary specialization (Roggenbuck et al., 2014). The gut communities can also change as a result of seasonal dietary fluctuations (Wienemann et al., 2011).

Modern molecular techniques provide an insight into the biodiversity contained within the guts of birds. Firmicutes, Proteobacteria, and Actinobacteria tend to dominate avian gut samples (summarized in Waite and Taylor, 2014), although captivity status can have a significant effect on microbial composition (Xenoulis et al., 2010; Wienemann et al., 2011; Kohl, 2012). Most gut microbiota studies have not included physical space as a variable that may be contributing to microbial variation in host gut communities. Geographic distance is associated with gut microbiota similarity (Yatsunenko et al., 2012) and, generally speaking, bacterial communities that are geographically closer are more similar than communities more distant (Green and Bohannan, 2006). Avian gut microbiota have shown conflicting results regarding the importance of geographic distance; whereas some studies have found it to be associated with the gut microbiota (Hird et al., 2014), others have looked but found no such evidence (Banks et al., 2009).

Large comparative studies inform us about the relationship between higher taxonomic classes and broader ecological groups. In mammals, such studies have found that host taxonomy is strongly associated with gut microbiota communities (Ley et al., 2008a) as is dietary specialization (Ley et al., 2008b; Muegge et al., 2011). Diet seems to be the most important factor across insects (Anderson et al., 2012; Colman et al., 2012) and environmental variables have the most influence on gut microbiota in fishes (Sullam et al., 2012), although taxonomy may also have a role. A recent meta-analysis of all previously published bird gut microbiota studies found that taxonomy of the bird had a major influence on the composition of the gut microbes (Waite and Taylor, 2014). Understanding how various host and environmental factors interact to shape the gut microbiota is a major goal of modern microbial ecology and evolution.

A molecular survey of the gut microbiota is a basic biodiversity measure that is lacking for the vast majority of wild bird species. Our primary aim for the current study was to create a microbial catalog for the gut microbiota diversity found in 59 Neotropical bird species sampled in the wild. Second, we test for taxonomic and ecological associations between bird host and gut microbiota. Finally, we tested for a geographic signal in our dataset, which was gathered from 12 localities across Costa Rica and Peru.

Materials and methods

Sampling

The large intestine was extracted from 108 birds in Costa Rica and seven in Peru (Table 1, Figure 1, Supplemental Table S1) during fieldwork conducted between May and August 2010 [LSU IACUC protocol 09-001; Sistema Nacional de Areas de Conservación (SINAC) permit number: 109-2010-SINAC; access to genetic material by Comisión Nacional para la Gestión de la Biodiversidad (CONAGEBio) under permit: R010-2010-OT-CONAGEBIO]. Immediately after euthanization, birds were dissected and the largest section of undisturbed large intestine tied off, cut out and deposited into CryoVials. Samples were frozen in liquid nitrogen, following the protocol of Godoy-Vitorino et al. (2010) and kept frozen at the LSUMNS Collection of Genetic Resources until microbial DNA extraction (using Qiagen Power Soil extraction kits). We focused on bird species found in lowland forests across Costa Rica whose ranges extend south into the Peruvian Amazon.

Table 1

OrderFamilyGenusSpeciesSampling locality
ABCDEFGHIJKL
ApodiformesTrochilidaeAmaziliatzacatl1
ApodiformesTrochilidaeFlorisugamellivora211
ApodiformesTrochilidaePhaethornislongirostris21
ApodiformesTrochilidaeThaluraniacolombica2
ApodiformesTrochilidaeThrenetesruckeri13
CaprimulgiformesCaprimulgidaeNyctidromusalbicollis2
ColumbiformesColumbidaeGeotrygonmontana1
CoraciiformesMomotidaeBaryphthengusmartii1
CuculiformesCuculidaePiayacayana1
PasseriformesCardinalidaeCyanocompsacyanoides2231
PasseriformesCardinalidaeHabiaatrimaxillaris11
PasseriformesCardinalidaeHabiafuscicauda4
PasseriformesEmberizidaeArremonaurantiirostris11
PasseriformesEmberizidaeArremonopsconirostris1
PasseriformesFormicariidaeFormicariusanalis11
PasseriformesFurnariidaeAutomolusochrolaemus1
PasseriformesFurnariidaeDendrocinclafuliginosa1
PasseriformesFurnariidaeGlyphorynchusspirurus11
PasseriformesFurnariidaeXiphorhynchussusurrans21
PasseriformesIcteridaeCacicusuropygialis21
PasseriformesIncertae SedisSaltatormaximus1
PasseriformesParulidaeMyiothlypisfulvicauda1
PasseriformesPipridaeManacusaurantiacus1
PasseriformesPipridaeManacuscandei6
PasseriformesPipridaeCeratopipramentalis1213
PasseriformesThamnophilidaeCymbilaimuslineatus1
PasseriformesThamnophilidaeGymnopithysleucaspis21
PasseriformesThamnophilidaeHylophylaxnaevioides1
PasseriformesThamnophilidaeMicrorhopiasquixensis11
PasseriformesThamnophilidaeMyrmecizaexsul11
PasseriformesThraupidaeChlorophanesspiza1
PasseriformesThraupidaeOryzoborusfunereus1
PasseriformesThraupidaeRamphoceluscostaricensis1
PasseriformesThraupidaeRamphoceluspasserinii3
PasseriformesThraupidaeSporophilacorvina1
PasseriformesThraupidaeTachyphonusluctuosus1
PasseriformesThraupidaeTangaragyrola1
PasseriformesThraupidaeTangaralarvata11
PasseriformesThraupidaeThraupisepiscopus1
PasseriformesThraupidaeVolatiniajacarina1
PasseriformesTityridaeTityrainquisitor1
PasseriformesTroglodytidaeCantorchilusnigricapillus1
PasseriformesTroglodytidaeHenicorhinaleucosticta11
PasseriformesTurdidaeTurdusgrayi1
PasseriformesTyrannidaeAttilaspadiceus2
PasseriformesTyrannidaeElaeniaflavogaster1
PasseriformesTyrannidaeMionectesoleagineus11111
PasseriformesTyrannidaeMyiarchustuberculifer1
PasseriformesTyrannidaeMyiozetetesgranadensis1
PasseriformesTyrannidaeMyiozetetessimilis3
PasseriformesTyrannidaeOnychorhynchuscoronatus1
PasseriformesTyrannidaePlatyrinchuscoronatus1
PasseriformesTyrannidaeTolmomyiassulphurescens1
PasseriformesVireonidaeHylophilusflavipes1
PiciformesGalbulidaeGalbularuficauda2
PiciformesPicidaeMelanerpespucherani1
PiciformesRamphastidaePteroglossustorquatus1
TrogoniformesTrogonidaeTrogonmassena1
TrogoniformesTrogonidaeTrogonrufus12

Order, family, genus, species, sampling locality, and number of samples used in this study; sampling localities mapped on Figure 1.

(A) COSTA RICA: Prov. Puntarenas, Golfito, Parque Nacional Piedras Blancas, elev 75 m. (B) COSTA RICA: Prov. Puntarenas, Osa, Los Charcos, elev 65–110 m. (C) COSTA RICA: Prov. Puntarenas, Osa, Reserva Forestal Golfo Dulce Rd. to Drake, elev 260 m. (D) COSTA RICA: Prov. Puntarenas, Quepos, Londres, elev 200 m. (E) COSTA RICA: Prov. San Jose, Tarrazu, Santa Juana, elev 400 m. (F) COSTA RICA: Prov. Cartago, Tucuttique, Reserva Biologica El Copal, elev 1050 m. (G) COSTA RICA: Prov. Heredia, Sarapiqui, Reserva Biologica, Tirimbina, elev 170 m. (H) COSTA RICA: Prov. Heredia, Sarapiqui, Estacion Biologica La Selva. (I) COSTA RICA: Prov. Limon, Teleferico Veragua, elev 260–430 m. (J) COSTA RICA: Prov. Limon, Talamanca, Tuba Creek, elev 80 m. (K) PERU: Pasco, Prov. Oxapampa, Dist. Puerto Bermudez, Comunidad San Juan, trail to Janirvan, waterfall, elev 325 m. (L) PERU: Junin, Prov. Satipo, Dist. Rio Tambo, Sector Yavyos, Fundo San Jorge II, elev 415 m.

Figure 1

Figure 1

Sampling localities in Costa Rica (left) and Peru (right). A, Piedras Blancas; B, Los Charcos; C, Golfo Dulce; D, Londres; E, Santa Juana; F, El Copal; G, Tirimbina; H, La Selva; I, Veragua; J, Tuba Creek; K, Janirvan; L, San Jorge II. Warmer colors indicate higher elevations.

Bird DNA sequencing and phylogenetic tree estimation

DNA was extracted from the liver, heart or pectoral muscle of birds using the standard tissue protocol from Qiagen DNeasy kits. The mitochondrial locus ND2 was sequenced using the L5215 (5′ TAT CGG GCC CAT ACC CCG AAA AT 3′) and H6313 (5′ CTC TTA TTT AAG GCT TTG AAG GC 3′) primers and a thermocycler program of 94°C for 2 min followed by 35 cycles of 94°C for 60 s, 45°C for 30 s, 72°C for 60 s and a final extension of 7 min at 72°C (Brumfield et al., 2007). Amplicons were cleaned using a BigDye Terminator kit and sequenced on ABI PRISM 3730xl at Beckman Coulter Genomics (Danvers, Massachusetts). The sequences were aligned with MUSCLE (Edgar, 2004) and we used BEAST (Drummond and Rambaut, 2007) to generate a sample from the posterior distribution of phylogenetic trees given the data (partitioned GTR + Γ model with estimated base frequencies). Because many of the internal branches of a multi-order bird phylogeny are short and several genomic-scale datasets have recently resolved some of these common conflicts, we also constrained the tree's internal nodes to reflect current genomic understanding of bird taxonomy (Klicka et al., 2007; Tello et al., 2009; Barker et al., 2013).

Microbial fingerprint

Following Gloor et al. (2010) we used combinatoric primers and massive multiplexing of PCR amplicons for sequencing on an Illumina Hi-Seq. This method uses paired-end sequencing technology to generate pairs of sequences with 100% overlap across variable region 6 (V6) of the 16S component of rRNA; primer sequences align to positions 967–985 and 1078–1061 on Escherichia coli 16S rRNA (Gloor et al., 2010). We chose the V6 region of 16S because it is short enough that the sequencing technology was able to cover the entire region in both directions but variable enough to differentiate bacterial species (Chakravorty et al., 2007).

Several samples were extracted or amplified more than once to quantify differences along the digestive tract and/or determine how sensitive the methods are to differences. One sample was amplified and sequenced a second time from a single extraction; these replicates are Cyanocompsa.cyanoides.1.1 and Cyanocompsa.cyanoides.1.2. Three birds had two extractions completed and were sequenced independently: Attila.spadiceus.1 had one extraction from the posterior large intestine and the other from the anterior large intestine; Trogon.rufus.2 had two extractions in tandem from the posterior large intestine; Nyctidromus.albicollis.1 had one extraction from the posterior large intestine and a second from one of the ceca.

We used several measures of sequence quality control. First, both reads of a given pair had to match across 100% of the bases. The pairs also must have no errors in the individual tag or priming sequence. We used the BELLEROPHON (Huber et al., 2004) function within the mothur program (Schloss et al., 2009) to identify and discard potentially chimeric sequences. Finally, we used mothur to discard sequences that did not blast to the domain Bacteria. The reads passing these filters were included in the final dataset.

Subsampled datasets

To assess patterns across different spatial, taxonomic and ecological scales, we subdivided the dataset eight ways.

  • Full dataset: all samples (N = 116).

  • >2 individuals: all individuals belonging to species sampled more than once (N = 80, removes singletons).

  • CFM: all individuals from the three species that were sampled from both Costa Rica and Peru: Cyanocompsa cyanoides, Florisuga mellivora and Mionectes oleagineus (N = 17, this dataset allows investigation of large-scale geographic differences between birds of the same species).

  • Cyanoides: all individuals belonging to the species Cyanocompsa cyanoides (N = 8, removes taxonomic variation).

  • Manakins: all individuals from two species that were sampled multiple times and belong to the same family: Manacus candei and Ceratopipra mentalis (N = 13, this dataset allowed us to look at the differentiation between closely related species).

  • Non-passerines: all the birds belonging to orders other than Passeriformes (N = 27, removes largest order).

  • Passerines: all the birds belonging to the order Passeriformes (N = 88, constrains taxonomic variation to a single order).

  • Tirimbina: all individuals from Tirimbina Biological Reserve, Sarapiquí, Costa Rica, the most densely sampled locality (N = 45, removes geographic variation).

Taxonomic assignment and clustering analyses

The microbial ecology package QIIME (Caporaso et al., 2010b) was used for the following analyses. First, the de novo OTU picking protocol was used to assign the reads to phylotypes at 97% sequence similarity because 3% is frequently cited as the “species” level of microbial taxonomy (Schloss and Handelsman, 2005), hereinafter “phylotypes.” Next, we assigned taxonomies to phylotypes using the QIIME implementation of the RDP Classifier 2.2 Program (Wang et al., 2007), with the default confidence threshold of 80%. A “core microbiota” was calculated and included all phylotypes that were found in 100% of the samples.

A pairwise UniFrac (Lozupone and Knight, 2005) distance matrix (UDM) was constructed between each gut microbial community (i.e., each bird specimen). UniFrac distances are calculated based on the amount of branch length in a phylogenetic tree that is unique to either of two environments (vs. how much of the tree is shared by the environments). These distances can be based on presence-absence of OTUs (“unweighted”) or weighted by abundance and our analyses use both, as neither method is agreed to be more appropriate for multi-species microbiota studies. Our data were aligned using the QIIME implementation of PyNAST (Caporaso et al., 2010a) and a microbial phylogenetic tree was constructed with FASTTREE (Price et al., 2009). All individuals were randomly reduced to 3652 reads, equal to the lowest number of reads for any bird in the dataset. Despite this type of rarefaction being inappropriate for some questions (McMurdie and Holmes, 2014), we chose to normalize our data this way because we are comparing “whole microbiome” data across many individuals and highly variable sequencing depths can affect diversity estimates (Goodrich et al., 2014). We constructed UPGMA dendrograms based on both the unweighted UDM and weighted UDM to visually represent the relatedness of the gut microbiota for all datasets. Principal coordinates analysis (PCoA) was also performed on both the weighted and unweighted UniFrac distance matrices.

As a complement to the phylogenetic-based methods, we visualized the data with non-metric multidimensional scaling (NMDS). We square root-transformed the percentage of each sample that belonged to each bacterial phylum, then created a pairwise distance matrix using Bray-Curtis dissimilarity, applied through the VEGDIST function of the VEGAN package (Oksanen et al., 2011) in R (R Development Core Team, 2010). The NMDS function of the ECODIST package (Goslee and Urban, 2007) was then used to calculate the two-dimensional positions of the samples (such that closer samples are more similar), the stress and R2 value of the plot. Stress values >0.3 should not be considered valid whereas values <0.2 can be considered a good representation of the data (Quinn and Keough, 2002).

Categorical variable significance

To look for a relationship between categorical variables associated with each bird and the microbial communities, we used the statistical tools Adonis (McArdle and Anderson, 2001) and Anosim (Clarke, 1993) implemented in QIIME. The categorical variables included the American Ornithologists' Union South American Classification Committee's taxonomy, i.e., order, family, genus and species (Remsen et al., 2012), ecological variables, including dietary specialization and habitat (Bennett and Owens, 2002), spatial variables and individual properties, like age (based on percent of skull ossification), stomach contents (e.g., “insects” or “plant material”) and bacterial richness (bacterial taxa identified per bird). Table 2 gives a detailed list of the variables and their sources. We calculated significance of all variables for both the weighted and unweighted UDMs with 999 permutations.

Table 2

VariableCatDescription and source
Order8Bird order (Remsen et al., 2012)
Family24Bird family (Remsen et al., 2012)
Genus53Bird genus (Remsen et al., 2012)
Species59Bird species (Remsen et al., 2012)
Diet specific11Specific dietary specialization: nectar, generalist, insect, seed, arthropod, fruit, insect/fruit, fruit/insect, nectar/insect, arthropod/vertebrates, fruit/nectar/insects (C. Sanchez, pers. com.)
Diet broad3Broad dietary specialization: plant material, animal material, both
Diet B&O4Broad dietary specialization assigned by Bennett and Owens (2002): frugivore, nectarivore, insectivore, omnivore
Habitat5General habitat assigned by Bennett and Owens (2002): woodland, forest, forest/grassland, forest/grassland/scrub, all habitats
Foraging strata9Foraging strata assigned by Stotz et al. (1996): canopy, midstory, understory, terrestrial, under/midstory, midstory/canopy, terrestrial/understory, terrestrial/midcanopy, understory/canopy
Locality12Sampling locality (see Figure 1): Tirimbina, Londres, Los Charcos, Piedras Blancas, Golfo Dulce, El Copal, Janirvan, Tuba Creek, San Jorge II, La Selva, Veragua, Santa Juana
Country2Country of sampling: Costa Rica, Peru
NSEW6Relative location of sampling locality: north-east Costa Rica, midwest Costa Rica, southwest Costa Rica, middle Costa Rica, mideast Costa Rica, Peru
Elevation13Elevation of sampling locality: 65, 75, 80, 110, 170, 200, 250, 260, 325, 400, 415, 430, and 1050 m
Sex3Sex of the bird: male, female, unknown
Age14Percent of skull ossification (a proxy for age of bird): 0, 3, 5, 10, 15, 20, 25, 50, 70, 75, 90, 95, 100, unknown
Stomach contents12Contents of stomach at time of collection: insects, seeds, fruit, plant material, seeds/insects, insects/pollen, fruit/insects, insects/plants, seeds/plants, fruit/insects/seeds, empty, unknown
Phyla richness10Number of bacterial phyla identified in the gut microbiota fingerprint: 8, 9, 10, 11, 12, 13, 14, 15, 16, 17
Species richness5Which fifth the number of 97% OTUs identified in a gut microbiota fingerprint belongs to: 20%ile, 40%ile, 60%ile, 80%ile, 100%ile

Categorical variables tested for significance, including the number of categories within each variable (Cat) and a list of the possible designations (except taxonomic categories).

After testing the significance of each variable independently, we ran an additional Adonis test on the most frequently significant variables to quantify the amount of variation each variable was responsible for in the context of other variables. We used the full dataset's unweighted and weighted UDMs as input, calculated 999 permutations, and permuted the order of the variables, which can affect the results of the test. Finally, we constrained the analyses to only permute the data within bird orders, as a measure of controlling for taxonomy. We then reran the weighted and unweighted UDMs.

Results

After initial quality control steps, 9,897,718 pairs of reads remained with no errors in priming sequence, region of overlap or individual tags. Potentially chimeric sequences (1167, 0.01% of reads) were then discarded. A further 3,58,725 sequences that did not align to any sequence within the domain Bacteria (3.6% of reads) were removed; 75% of these discarded reads belonged to 11 individuals. The reads passing these filters were included in the final dataset, totaling 9,537,817 sequences and averaging 82,222 sequences per individual; reads/sample varied by over two orders of magnitude (range: 3652–853,078).

Four bacterial phyla were detected in all individuals: Proteobacteria, Firmicutes, Bacteroidetes and Actinobacteria comprising an average of 46.3, 37.3, 3.3, and 1.4% of each sample, respectively (Figure 2). An additional 16 phyla were identified: Acidobacteria, Chlamydiae, Chloroflexi, Cyanobacteria, Deinococcus-Thermus, Fusobacteria, Lentisphaerae, Nitrospira, OD1, OP10, OP11, Planctomycetes, Spirochaetes, TM7, Tenericutes, Verrucomicrobia, with an average of 10.6% of sequences (from each individual) from unknown bacterial phyla. The core microbiota contained 56 phylotypes, 32 of which belonged to 26 known genera (Table 3). An additional 48 phylotypes were detected in >95% of the samples. The number of species-level phylotypes per bird varied between 109 and 288, with an average of 201 (SD = 35). Replicate samples were similar to one another in taxonomic composition (Figure 2) and generally clustered close to one another in multivariate space (Figures 3, 4; Figure S2). A heatmap of bacterial phylotypes vs. host taxonomy revealed little clustering and showed how specific phylotypes were found in high abundance in most individuals (Figure S3); most of these phylotypes belonged to the Firmicutes and Proteobacteria.

Figure 2

Figure 2

Bacterial composition of bird gut samples. (A) Relative abundance of bacterial phyla in all birds. Bird orders shown in gray boxes and individuals are labeled across the top. (B) Bacterial phyla summarized by bird order, including the individuals in this study and *indicates data obtained from Waite and Taylor (2014). Phylogeny on left is a modified version of the phylogenetic relationship of bird orders from Hackett et al. (2008).

Table 3

PhylumClassOrderFamilyGenus
Actinobacteria5Actinobacteria5Actinomycetales4Corynebacteriaceae1Corynebacterium1
Microbacteriaceae1
Propionibacteriaceae1Propionibacterium1
Bacteroidetes5Bacteroidia1Bacteroidales1Bacteroidaceae1Bacteroides1
Flavobacteria3Flavobacteriales3Flavobacteriaceae3Chryseobacterium1
Planobacterium1
Firmicutes17Bacilli12Bacillales4Bacillaceae2Anoxybacillus1
Staphylococcaceae1Staphylococcus1
Lactobacillales7Lactobacillaceae1Lactobacillus1
Leuconostocaceae2Leuconostoc1
Weissella1
Streptococcaceae3Lactococcus1
Streptococcus1
Clostridia4Clostridiales4Clostridiaceae1Clostridium1
Veillonellaceae2Veillonella1
Proteobacteria27Alpha- proteobacteria4Rhizobiales2Methylobacteriaceae1Methylobacterium1
Sphingomonadales1Sphingomonadaceae1Sphingomonas1
Beta- proteobacteria9Burkholderiales8Burkholderiales2Aquabacterium1
incertae sedisTepidimonas1
Comamonadaceae4Acidovorax1
Diaphorobacter1
Schlegelella1
Oxalobacteraceae1Janthinobacterium1
Epsilon- proteobacteria2Campylobacterales2Campylobacteraceae1Campylobacter1
Helicobacteraceae1Helicobacter1
Gamma- proteobacteria11Aeromonadales1Aeromonadaceae1Aeromonas1
Enterobacteriales4Enterobacteriaceae4Escherichia1
Kluyvera1
Yersinia1
Pseudomonadales3Moraxellaceae2Acinetobacter1
Enhydrobacter1
Pseudomonadaceae1Pseudomonas1
Xanthomonadales2Xanthomonadaceae2Stenotrophomonas1

Bacterial taxa identified in 100% of the bird samples (assigned by RDP Classifier Program).

Gray boxes indicate the phylotype did not align to any named taxa at that taxonomic rank. Numbers in boxes are the total number of identified phylotypes in that group. Full length gray bar at bottom indicates a phylotype that did not align to any named phylum.

Figure 3

Figure 3

PCoA of unweighted Unifrac distances for all 116 bird samples. All three plots are the same, but individuals are colored differently based on metadata, bird order (left), diet (center), and sampling locality (right). Dotted lines connect replicate samples (as described in Materials and Methods).

Figure 4

Figure 4

Bird phylogeny (left) obtained using ND2 locus and a constrained species level phylogeny estimated with *BEAST compared to dendrogram of weighted UniFrac distance matrix. Colors indicate bird order and individuals are tracked across the two figures.

Clustering analyses

The PCoA for the unweighted UDM displayed clustering by taxonomic order (Figure 3), but little obvious clustering by foraging stratum, diet or sampling locality. Host order displayed the most clustering in the weighted UDM PCoA and NMDS plot as well (Figure S1), although little correspondence is seen between the actual bird phylogeny and a dendrogram of the weighted UDM (Figure 4; see Figure S2 for unweighted UDM and Bray-Curtis dendrograms).

Categorical variable significance

To look for correlations between categorical variables and the gut microbiota, we conducted two statistical tests for significance on both the weighted and unweighted UDMs (Table 4). For the full dataset, taxonomic categories explained the most amount of variation and were all significant at p < 0.05 for the Adonis statistical tests (Figure 5A, Table 4). All other variables explained much less variation although some were significant. The taxonomic categories were also significant in the Anosim test of the full dataset, whereas none of the ecological or spatial variables were (Table 4). Averaging across all 8 datasets, taxonomic variables were the most frequently significant; all four categories (order, family, genus, species) were significant in over 50% of the tests. The taxonomic categories also accounted for the most variation (Figure 5B). The ecological variables were significant in most datasets but generally explained much less variation than the taxonomic variables. The locality and individual variables had generally low R2 values and were all significant in less than 33% of the tests.

Table 4

A.OrderFamilyGenusSpecies
AdonisANOSIMAdonisANOSIMAdonisANOSIMAdonisANOSIM
R2PRPR2PRPR2PRPR2PRP
Full datasetUnweighted9.20.0010.1360.02723.630.0010.1170.00148.120.0010.1220.02253.40.0010.1330.022
Weighted27.390.0010.2570.00145.950.0010.2160.00167.530.0010.2500.00174.020.0010.2940.001
>2 individuals/speciesUnweighted8.110.0010.1170.05820.530.0010.1210.00933.310.0010.1210.01934.650.0010.1430.01
Weighted35.330.0010.2680.00247.330.0010.2390.00161.740.0010.2580.00162.920.0010.2730.001
CFMUnweighted8.080.030.3420.01614.710.0270.3170.00414.710.0270.3170.00314.710.020.3170.003
Weighted8.780.199−0.0660.59915.050.272−0.0260.52415.050.28−0.0260.55915.050.277−0.0260.568
CyanoidesUnweighted
Weighted
ManakinsUnweighted12.080.0590.1030.12512.080.0650.1030.121
Weighted13.580.1560.0700.16513.580.1580.0700.183
Non-passerinesUnweighted31.90.0010.5040.00139.50.0010.5200.00156.220.0010.7180.00159.860.0010.7070.001
Weighted60.940.0010.7260.00175.50.0010.7820.00181.590.0010.5610.00186.330.0010.6480.001
PasserinesUnweighted16.810.1960.0160.35244.560.2220.0110.45950.660.1220.0330.307
Weighted24.290.020.0590.10953.850.030.0980.09459.290.0370.1080.103
TirimbinaUnweighted8.580.0220.2390.01428.830.685−0.0420.71164.050.3940.0290.39664.050.3860.0290.423
Weighted33.080.0170.2210.06659.170.0110.1270.06780.690.0960.1430.16380.690.1040.1430.139

Full results for Adonis and Anosim tests of categorical significance.

B.Diet specificDiet broadDiet B&OHabitatForaging stratum
AdonisANOSIMAdonisANOSIMAdonisANOSIMAdonisANOSIMAdonisANOSIM
R2PRPR2PRPR2PRPR2PRPR2PRP
Full datasetUnweighted9.360.1270.0100.4012.050.130.0200.0824.060.0010.0000.4634.280.0170.0340.0897.850.0260.0500.1
Weighted13.740.0230.0020.463.950.0060.0640.00113.330.0010.0480.1534.420.186−0.0120.61311.390.0190.1030.024
>2 individuals/speciesUnweighted13.170.0010.1060.0073.720.0070.0760.0046.240.0010.0920.0165.990.0010.0770.0097.330.6210.0210.345
Weighted16.280.0080.0510.1350.0310.1460.00119.770.0010.0500.1666.510.0290.0250.19616.950.0010.1320.035
CFMUnweighted14.710.0160.3170.0048.080.0220.3420.02914.710.0210.3170.00314.710.0230.3170.00214.710.0270.3170.007
Weighted15.050.311−0.0260.5578.780.207−0.0660.5915.050.286−0.0260.53615.050.308−0.0260.54715.050.307−0.0260.537
CyanoidesUnweighted
Weighted
ManakinsUnweighted12.080.0490.1030.121
Weighted13.580.1530.0700.201
Non-passerinesUnweighted33.770.0010.4280.00113.430.0010.3590.00119.110.0010.4450.00114.530.0010.4750.00127.870.0010.2850.004
Weighted53.270.0030.4510.00129.070.0010.3580.00145.140.0020.6420.00128.40.0010.53210.00142.980.0050.3580.001
PasserinesUnweighted8.950.0730.0120.3362.550.2010.0020.4071.590.0460.0430.0852.880.0670.0330.1058.760.1090.0100.404
Weighted13.250.0210.0180.3084.610.0330.0170.1774.880.0010.0480.0745.620.0060.0010.47210.840.111−0.0360.736
TirimbinaUnweighted21.880.1310.0480.2145.310.1130.0480.1414.610.387−0.0340.7187.140.2930.0620.11917.680.0820.0570.225
Weighted26.380.1880.1080.0826.750.1710.1270.0054.230.4510.0400.2449.110.2040.0560.178350.050.0520.267

C.LocalityCountryNSEWElevation
AdonisANOSIMAdonisANOSIMAdonisANOSIMAdonisANOSIM
R2PRpR2PRPR2PRPR2PRP
Full datasetUnweighted12.360.0680.0190.3241.120.067−0.0130.5335.950.0520.0330.18311.70.2490.0080.381
Weighted15.940.0720.0910.0491.640.09−0.1090.7497.130.1350.0810.02718.20.0130.0710.151
>2 individuals/speciesUnweighted15.190.078−0.0230.6112.170.0110.1560.097.890.0140.0700.0715.480.356−0.0560.794
Weighted18.80.0920.0550.2111.570.253−0.0690.6538.520.1370.0640.11923.360.02−0.0060.521
CFMUnweighted33.140.1050.1320.1337.220.0990.1040.15114.290.0440.1350.07138.770.1890.2320.047
Weighted30.150.52−0.0150.532140.0480.0560.22923.550.0540.1070.12534.470.6−0.0890.725
CyanoidesUnweighted58.830.2380.0960.36815.470.2060.1460.16929.590.253−0.0500.50458.830.2530.1250.347
Weighted74.90.1560.1650.2626.90.1720.0310.38243.340.2130.0630.29374.90.170.2500.243
ManakinsUnweighted16.380.3970.2020.20616.380.3990.1690.20723.930.5320.2020.215
Weighted14.560.523−0.0960.65214.560.508−0.0800.61915.50.822−0.0960.636
Non-passerinesUnweighted22.930.0080.1630.0263.380.909−0.2780.88919.120.0090.1890.01824.910.1010.0550.238
Weighted26.360.1250.0940.1211.470.671−0.2710.8123.330.0980.1970.01637.530.0270.1320.106
PasserinesUnweighted13.780.504−0.0360.7551.80.0190.2180.0396.530.749−0.0280.7213.760.5−0.0490.77
Weighted18.050.111−0.0110.5362.130.133−0.0390.587.580.312−0.0290.67617.130.151−0.0400.714
TirimbinaUnweighted
Weighted

D.SexAgeStomach contentsPhyla richnessSpecies richness
AdonisANOSIMAdonisANOSIMAdonisANOSIMAdonisANOSIMAdonisANOSIM
R2PRPR2PRPR2PRPR2PRPR2PRP
Full datasetUnweighted1.490.894−0.0090.65111.750.223−0.0270.64410.270.0950.0360.1981.630.0030.0550.0462.430.0010.05410.003
Weighted1.760.4410.0200.2068.370.878−0.1330.96612.640.1180.1140.0162.520.0110.0300.1873.030.0010.0250.016
>2 individuals/speciesUnweighted2.360.644−0.0100.60312.920.0340.0500.20912.250.1120.0830.0641.510.1730.0860.0241.690.064−0.0070.621
Weighted3.040.2920.0360.17112.310.354−0.0700.77215.820.1040.0950.0842.240.1210.0020.4632.330.0950.0110.237
CFMUnweighted10.260.997−0.1730.97546.680.0290.3000.04731.490.4150.1540.1686.560.303−0.1770.9136.130.507−0.0100.487
Weighted8.890.679−0.0710.71558.210.0710.1560.194310.45−0.0540.59212.270.1060.0240.4467.390.335−0.0650.707
CyanoidesUnweighted32.110.0860.2750.15230.750.1630.0590.31242.30.5460.2000.2513.370.6520.5770.11715.810.180.1670.321
Weighted36.450.271−0.0760.55850.630.0760.2410.13256.880.2230.1830.26634.310.0880.3460.23916.720.317−0.0760.609
ManakinsUnweighted17.810.2830.0870.24916.480.365−0.2400.87915.820.53−0.1880.80513.880.0290.3230.01610.20.1290.1570.124
Weighted8.730.874−0.1960.97216.690.413−0.1350.67623.170.2020.3010.07227.230.0150.1790.14110.770.2530.1230.186
Non-passerinesUnweighted8.430.180.0730.15333.040.0580.1140.15532.320.1490.0330.3184.460.1780.0480.2974.650.1190.0380.291
Weighted7.140.4590.1210.06930.90.47−0.1630.92538.050.1660.1730.0558.120.0990.0680.2248.610.083−0.0120.493
PasserinesUnweighted1.810.959−0.0430.92611.40.523−0.0320.65512.210.0140.0290.2832.140.0020.0340.153.170.0010.0930.001
Weighted2.050.531−0.0280.76312.910.3030.0250.38410.050.5010.0550.1995.860.0010.0430.1274.650.0010.0210.169
TirimbinaUnweighted5.050.177−0.0760.90517.020.81−0.1870.98317.290.7950.0370.3583.260.0250.0570.1743.110.0560.0240.262
Weighted4.430.444−0.0370.69311.660.783−0.0570.77.80.930.1180.1323.690.156−0.0280.6391.910.4780.0510.097

Effect size (R2 or R) and significance shown; results for inappropriate tests are grayed out. P-values less than 0.05 highlighted in pink and bolded.

Figure 5

Figure 5

Adonis test results for the full dataset (A) and averages for all the datasets (B). Details on variables in Table 2; datasets described in Materials and Methods.

Using the “Tirimbina” dataset, which included all individuals from a single locality, host order was still significant, with other taxonomic levels less so (Table 4). Conversely, in our most taxonomically restricted dataset including a single species, “Cyanoides,” geographic variables explained a large amount of variation but the effect was not significant (unweighted UDM R2 = 58%, p = 0.23; weighted UDM R2 = 74.9%, p = 0.156).

The multifactor Adonis tests yielded different results for the weighted and unweighted UniFrac distance matrices. Foraging stratum, host order and bacterial richness (at the phylum level) were all significant (p < 0.05) for the unweighted UDM and accounted for around 10% of the variation each (Table 5A). No variables were significant for the weighted UDM (Table 5B). When data were permuted within the taxonomic orders (i.e., controlling for high-level host taxonomy), the significance of the variables did not change (Tables 5C,D), although the amount of variation that the host taxonomy explained increased.

Table 5

R2p
A. UNWEIGHTED UDM
Diet0.011610.653
Foraging stratum0.111110.007
Locality0.083430.426
Host order0.102870.003
Bacterial richness0.106070.029
B. WEIGHTED UDM
Diet0.006880.764
Foraging stratum0.099830.095
Locality0.137180.064
Host order0.076140.184
Bacterial richness0.067420.497
C. UNWEIGHTED UDM—CONTROLLING FOR HOST ORDER
Diet0.011610.806
Foraging stratum0.111110.008
Locality0.083430.695
Host family0.240090.014
Bacterial richness0.102610.025
D. WEIGHTED UDM—CONTROLLING FOR HOST ORDER
Diet0.006880.766
Foraging stratum0.099830.246
Locality0.137180.093
Host family0.217240.304
Bacterial richness0.048180.833

Multifactorial Adonis tests for categorical significance.

P-values less than 0.05 are bolded.

Discussion

Microorganisms are an essential component of biodiversity, and vertebrate evolutionary history is incomplete without an adequate understanding of our microbiota. This study greatly increases our basic understanding of what organisms live in the guts of wild Neotropical birds, spanning eight orders within Aves. We found taxonomic profiles similar to other avian gut studies with some exceptions. Compared to the meta-analysis performed by Waite and Taylor (2014), our samples appear to be enriched for Proteobacteria and have a deficit of Actinobacteria. If this result is not a biological signal, the discrepancy may be due to the difference in marker choice or methods between our study and those in the meta-analysis or to an underlying methodological bias.

Several gut-associated taxa were defined as our “core microbiome.” The phyla Firmicutes, Proteobacteria, Actinobacteria, and Bacteroidetes were found in all our samples and are often found in gut habitats across vertebrates (e.g., Turnbaugh et al., 2008; Roeselers et al., 2011); the same is true for the genera Bacteroides, Clostridium, and Lactobacillus. Additionally, some genera frequently found in avian guts specifically were identified in all our samples: Streptococcus and Campylobacter (Zhu et al., 2002; Xenoulis et al., 2010; Videnska et al., 2014). Although several known contaminants of microbiota studies (Salter et al., 2014) were found in our dataset (e.g., Corynebacterium, Propionibacterium, Streptococcus), the high biomass of our initial samples (intestinal contents) and the corroboration of many of these genera being found in other gut studies leads us to believe our results are not due to laboratory contamination. Overall, these results suggest that there may be a conserved set of microorganisms found in the guts of birds and perhaps all vertebrates.

The importance of host taxonomy, ecology, and geographic space

The statistical tests applied above indicate varying degrees of importance for taxonomy, ecology, geographic space, and individual traits for structuring the gut microbiota of birds. Generally speaking, it appears that who a bird is most important, how a bird lives is possibly important and where a bird lives may be of little importance.

Instead of phylogenetic distance, we used taxonomic categories as our evolutionary units, so that we could apply the same statistical methods to all metadata associated with the bird samples. Focusing on hierarchical taxonomic categories also allowed us to overcome the analytical problems associated with high individual variation in gut microbiota (e.g., Turnbaugh et al., 2008; Figure 4) while still learning about the effect of evolutionary history on the microbiota. Taxonomic categories were most frequently significant in our analyses and explained the most variation. There is clear evidence for associations between gut microbiota and host taxonomy, which has been widely noted in other systems and at varying scales (e.g., Ochman et al., 2010). It is important to note, though, that taxonomy is not the same as phylogeny; our results show that individuals of the same species/genus/family/order are more similar to one another than they are to individuals in other groups, not that more closely related species/genera/families/orders have more similar microbiota. In fact, little correlation was seen between the individual phylogeny and the gut microbiota dendrogram (Figure 4). Does this mean that phylogeny is not an underlying factor shaping the gut microbiota? We believe that it would be difficult to get significant signal at all taxonomic levels without phylogeny playing some role but this requires further investigation that may require parsing the microbiome into vertically vs. horizontally transmitted bacteria. It would not be surprising to find some vertical transmission of microbiota from parent to offspring occurring in birds, as all the birds in this study feed their young by regurgitating food into the mouth of nestlings. The exact role of evolutionary history on gut microbiota is an exciting next step.

We also found small but significant associations between the gut microbiota and host ecology. Broad dietary classifications (e.g., mostly plant, mostly animal, plant/animal) were more significant than specific dietary specializations and the literal stomach contents were only significant in two of the 32 tests. Perhaps long term habits or nutritional content have greater influence on gut microbiota than day to day food intake, which is consistent with other studies showing the stability of the avian gut community once established (Benskin et al., 2010) and that diet can drive the convergence of gut microbiota in non-avian vertebrates (Ley et al., 2008a,b; Muegge et al., 2011). Of methodological note: the “stomach contents” variable contains a lot of variance particularly with respect to specificity and accuracy, as it is recorded in the field and only general data are taken, (i.e., “plant material” or “insects”).

Strata and habitat are important ecological aspects of avian biology. Foraging strata is associated with genetic divergence in Neotropical birds (Burney and Brumfield, 2009; Smith et al., 2014) because ecology affects dispersal ability. Our results reinforce the importance of foraging strata on avian biology and support an important role for ecology in differentiation of both host and microbiota. Microbes from the same ecological niche on the human body are able to share genes on a global scale (Smillie et al., 2011)—perhaps the microbiota of birds that share ecological niches are able to transfer genetic material as well. We could not decipher which aspect of host ecology is directly responsible for the signal we discovered in our current data—is it that birds in the same foraging stratum are exposed to the same environment microbes, that their behavior exposes them to particular microbes within the environment or that similar genes recruit specific microbes? Investigating how these aspects of host ecology affect gut microbiota is an exciting avenue of future research.

Despite ecological factors possibly being important for avian gut microbiota, (external) geographic space showed little effect on the microbiota. All the locality variables had poor correlations with the gut microbiota and our spatial tests revealed no statistical significance between space and microbiota. Thus, bird gut microbiota are likely not just a random assortment of the microbes available in a given environment. Can we further conclude that physical space has little effect on the microbiota? Possibly. None of our analyses found that gut communities that are spatially closer are more closely related, both across Aves and within a single species (Cyanocompsa cyanoides). Alternatively, the apparent lack of effect of locality may be an issue of sampling. This dataset contains few species (or even genera) with multiple individuals. If locality is important, we might expect it to be working within species instead of across higher taxonomic levels. Hird et al. (2014) found that locality was significantly correlated with gut microbiota within 34 brown-headed cowbirds from two localities. Scale of analysis may be critical for detecting what factors are contributing to divergence and much more work is needed to define appropriate geographic, taxonomic and ecological sample sizes. Regardless, it appears that geographic space is much less important than taxonomy and ecology for structuring the gut microbiota in birds.

Incorporating microbiome studies into collection based research

Wild organisms have different microbiota than captive conspecifics (Wienemann et al., 2011) and microbial communities change once the host organism has died (Hauther et al., 2015). Thus, field preservation of the microbiota generates unique and irretrievable data. Studying the microbiota informs us about the host but in a comparative framework, and we can learn about evolutionary processes above the individual as well (e.g., Ley et al., 2008b). The data for this paper were obtained without additional sampling effort; every result represents information that would have been lost had we not collected the intestinal contents for this purpose. The methodologies herein can relatively easily be incorporated into field protocols, when vertebrate specimens are being prepared for preservation in research collections.

The addition of microbial fingerprints to studies of natural history and evolution provides a non-traditional glimpse into some very important biodiversity. Our protocol for field sampling added an average of 5–10 min to specimen preparation time and consisted of isolating the intact intestinal tract, tying an undisturbed portion off at both ends, clipping the intestines on the outside of the ties and storing in liquid nitrogen. Other field researchers may want to include microbiome components in “macrodiversity” studies, even if they cannot process the samples immediately because doing so adds and preserves a novel and frequently entirely unknown dimension of data to vouchered museum specimens.

Data accessibility

Sequence data, metadata file and an OTU table have been uploaded to FigShare available at figshare.com/s/fe202600737e11e58a2906ec4bbcf141.

Statements

Author contributions

Conception/design of study (SH, RB); field work (CS, SH); acquisition, analysis, and interpretation of data (SH, CS, BC, RB); writing and editing manuscript (SH, CS, BC, RB).

Acknowledgments

The authors would like to thank NSF (DEB-0956069 and DEB-0841729), the AMNH Frank Chapman Grant (to CS) and Sigma Xi Grants-in-Aid-of-Research (to SH) for funding this project. The UC Davis Open Access Fund and the UC Davis Chancellor's Postdoctoral Fellowship helped fund publishing of the manuscript. We thank Sistema Nacional de Areas de Conservación (SINAC) and Consejo Nacional para la Gestión de la Biodiversidad (CONAGEBIO) for permits to do field work and obtain the samples in Costa Rica. We thank Gilbert Barrantes for allowing us access to work at Museo de Zoología, Universidad de Costa Rica, Bernal Rodrígues for granting access to Reserva Biológica Tirimbina, and Reinaldo Aguilar at Los Charcos de Osa. We thank Michael Harvey, Gustavo Bravo, Diego Ocampo, and Karla Conejo for field assistance. We also thank the editors and reviewers at Frontiers for improving the manuscript with their suggestions.

Conflict of interest

The authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.

Supplementary material

The Supplementary Material for this article can be found online at: http://journal.frontiersin.org/article/10.3389/fmicb.2015.01403

Figure S1

Principal coordinates analyses on unweighted (left column) and weighted (middle column) UniFrac distances and Non-metric Multidimensional Scaling (NMDS) analysis of bacterial composition of samples (right column). Samples are colored by bird order (top row), foraging strata (second row), diet (third row), and sampling locality (bottom row).

Figure S2

Gut community dendrograms of (A) unweighted UniFrac distance and (B) Bray-Curtis distance. Colors indicate host bird taxonomic order.

Figure S3

Heatmap of relative abundance of each identified phylotypes (columns) for each individual (rows). Taxonomic class of the bacteria and family of the bird are shown with gray bars. Horizontal black lines delimit taxonomic orders of the birds.

Supplemental Table S1

Detailed information about each sample, including taxonomic information, dietary assignments, habitat, foraging stratum (FS), sampling locality (L), elevation (Elev), percent of skull ossification (Age), bacterial phyla identified (BRP), the percentage of individuals with fewer phylotypes identified (BRS) and LSUMNS bird tissue collection number (B#).

References

  • 1

    Al-AsmakhM.StukenborgJ.-B.RedaA.AnuarF.StrandM.-L.HedinL.et al. (2014). The gut microbiota and developmental programming of the testis in mice. PLoS ONE9:e103809. 10.1371/journal.pone.0103809

  • 2

    AndersonK. E.RussellJ. A.MoreauC. S.KautzS.SullamK. E.HuY.et al. (2012). Highly similar microbial communities are shared among related and trophically similar ant species. Mol. Ecol.21, 22822296. 10.1111/j.1365-294X.2011.05464.x

  • 3

    BanksJ. C.CaryS. C.HoggI. D. (2009). The phylogeography of Adelie penguin faecal flora. Environ. Microbiol.11, 577588. 10.1111/j.1462-2920.2008.01816.x

  • 4

    BarkerF. K.BurnsK. J.KlickaJ.LanyonS. M.LovetteI. J. (2013). Going to extremes: contrasting rates of diversification in a recent radiation of New World Passerine birds. Syst. Biol.62, 298320. 10.1093/sysbio/sys094

  • 5

    BennettP. M.OwensI. P. F. (2002). Evolutionary Ecology of Birds: Life Histories, Mating Systems and Extinction. New York, NY: Oxford University Press.

  • 6

    BenskinC. M. H.RhodesG.PickupR. W.WilsonK.HartleyI. R. (2010). Diversity and temporal stability of bacterial communities in a model passerine bird, the zebra finch. Mol. Ecol.19, 55315544. 10.1111/j.1365-294X.2010.04892.x

  • 7

    BruckerR. M.BordensteinS. R. (2013). The hologenomic basis of speciation: gut bacteria cause hybrid lethality in the genus Nasonia. Science341, 667669. 10.1126/science.1240659

  • 8

    BrumfieldR. T.TelloJ. G.ChevironZ. A.CarlingM. D.CrochetN.RosenbergK. V. (2007). Phylogenetic conservatism and antiquity of a tropical specialization: army-ant-following in the typical antbirds (Thamnophilidae). Mol. Phylogenet. Evol.45, 113. 10.1016/j.ympev.2007.07.019

  • 9

    BurneyC. W.BrumfieldR. T. (2009). Ecology predicts levels of genetic differentiation in Neotropical birds. Am. Nat.174, 358368. 10.1086/603613

  • 10

    CaporasoJ. G.BittingerK.BushmanF. D.DeSantisT. Z.AndersenG. L.KnightR. (2010a). PyNAST: a flexible tool for aligning sequences to a template alignment. Bioinformatics26, 266267. 10.1093/bioinformatics/btp636

  • 11

    CaporasoJ. G.KuczynskiJ.StombaughJ.BittingerK.BushmanF. D.CostelloE. K.et al. (2010b). QIIME allows analysis of high-throughput community sequencing data. Nat. Methods7, 335336. 10.1038/nmeth.f.303

  • 12

    ChakravortyS.HelbD.BurdayM.ConnellN.AllandD. (2007). A detailed analysis of 16S ribosomal RNA gene segments for the diagnosis of pathogenic bacteria. J. Microbiol. Methods69, 330339. 10.1016/j.mimet.2007.02.005

  • 13

    ClarkeK. R. (1993). Non-parametric multivariate analysis of changes in community structure. Aust. J. Ecol.18, 117143. 10.1111/j.1442-9993.1993.tb00438.x

  • 14

    ColmanD. R.ToolsonE. C.Takacs-VesbachC. D. (2012). Do diet and taxonomy influence insect gut bacterial communities?Mol. Ecol.21, 51245137. 10.1111/j.1365-294X.2012.05752.x

  • 15

    DewarM. L.ArnouldJ. P. Y.DannP.TrathanP.GroscolasR.SmithS. (2013). Interspecific variations in the gastrointestinal microbiota in penguins. Microbiologyopen2, 195204. 10.1002/mbo3.66

  • 16

    Diaz HeijtzR.WangS.AnuarF.QianY.BjorkholmB.SamuelssonA.et al. (2011). Normal gut microbiota modulates brain development and behavior. Proc. Natl. Acad. Sci. U.S.A.108, 30473052. 10.1073/pnas.1010529108

  • 17

    DrummondA. J.RambautA. (2007). BEAST: bayesian evolutionary analysis by sampling trees. BMC Evol. Biol.7:214. 10.1186/1471-2148-7-214

  • 18

    EckburgP.BikE. M.BernsteinC. N.PurdomE.DethlefsenL.SargentM.et al. (2005). Diversity of the human intestinal microbial flora. Science308, 1635. 10.1126/science.1110591

  • 19

    EdgarR. C. (2004). MUSCLE: multiple sequence alignment with high accuracy and high throughput. Nucleic Acids Res.32, 17921797. 10.1093/nar/gkh340

  • 20

    GloorG. B.HummelenR.MacklaimJ. M.DicksonR. J.FernandesA. D.MacPheeR.et al. (2010). Microbiome profiling by illumina sequencing of combinatorial sequence-tagged PCR products. PLoS ONE5:e15406. 10.1371/journal.pone.0015406

  • 21

    Godoy-VitorinoF.GoldfarbK. C.BrodieE. L.Garcia-AmadoM. A.MichelangeliF.Domínguez-BelloM. G. (2010). Developmental microbial ecology of the crop of the folivorous hoatzin. ISME J.4, 611620. 10.1038/ismej.2009.147

  • 22

    GoodrichJ. K.Di RienziS. C.PooleA. C.KorenO.WaltersW. A.CaporasoJ. G.et al. (2014). Conducting a microbiome study. Cell158, 250262. 10.1016/j.cell.2014.06.037

  • 23

    GosleeS. C.UrbanD. L. (2007). The ecodist package for dissimilarity-based analysis of ecological data. J. Stat. Softw.22, 119. 10.18637/jss.v022.i07

  • 24

    GreenJ.BohannanB. J. M. (2006). Spatial scaling of microbial biodiversity. Trends Ecol. Evol.21, 501507. 10.1016/j.tree.2006.06.012

  • 25

    HackettS. J.KimballR. T.ReddyS.BowieR. C. K.BraunE. L.BraunM. J.et al. (2008). A phylogenomic study of birds reveals their evolutionary history. Science320, 17631768. 10.1126/science.1157704

  • 26

    HautherK. A.CobaughK. L.JantzL. M.SparerT. E.DeBruynJ. M. (2015). Estimating time since death from postmortem human gut microbial communities. J. Forensic Sci.60, 12341240. 10.1111/1556-4029.12828

  • 27

    HirdS. M.CarstensB. C.CardiffS. W.DittmannD. L.BrumfieldR. T. (2014). Sampling locality is more detectable than taxonomy or ecology in the gut microbiota of the brood-parasitic Brown-Headed Cowbird (Molothrus ater). PeerJ2:e321. 10.7717/peerj.321

  • 28

    HuberT.FaulknerG.HugenholtzP. (2004). Bellerophon: a program to detect chimeric sequences in multiple sequence alignments. Bioinformatics20, 23172319. 10.1093/bioinformatics/bth226

  • 29

    JenkinsC. N.PimmS. L.JoppaL. N. (2013). Global patterns of terrestrial vertebrate diversity and conservation. Proc. Natl. Acad. Sci. U.S.A.110, E2602E2610. 10.1073/pnas.1302251110

  • 30

    KlickaJ.BurnsK.SpellmanG. (2007). Defining a monophyletic Cardinalini: a molecular perspective. Mol. Phylogenet. Evol.45, 10141032. 10.1016/j.ympev.2007.07.006

  • 31

    KohlK. D. (2012). Diversity and function of the avian gut microbiota. J. Comp. Physiol. B182, 591602. 10.1007/s00360-012-0645-z

  • 32

    LeyR. E.HamadyM.LozuponeC.TurnbaughP. J.RameyR. R.BircherJ. S.et al. (2008a). Evolution of mammals and their gut microbes. Science320, 16471651. 10.1126/science.1155725

  • 33

    LeyR. E.LozuponeC. A.HamadyM.KnightR.GordonJ. (2008b). Worlds within worlds: evolution of the vertebrate gut microbiota. Nat. Rev. Microbiol.6, 13. 10.1038/nrmicro1978

  • 34

    LozuponeC.KnightR. (2005). UniFrac: a new phylogenetic method for comparing microbial communities. Appl. Environ. Microbiol.71, 8228. 10.1128/AEM.71.12.8228-8235.2005

  • 35

    McArdleB. H.AndersonM. J. (2001). Fitting multivariate models to community data: a comment on distance-based redundancy analysis. Ecology82, 290297. 10.1890/0012-9658(2001)082[0290:FMMTCD]2.0.CO;2

  • 36

    McMurdieP. J.HolmesS. (2014). Waste not, want not: why rarefying microbiome data is inadmissable. PLoS Comput. Biol.10:e1003531. 10.1371/journal.pcbi.1003531

  • 37

    MueggeB.KuczynskiJ.KnightsD.ClementeJ. C.GonzálezA.FontanaL.et al. (2011). Diet drives convergence in gut microbiome functions across mammalian phylogeny and within humans. Science332, 970974. 10.1126/science.1198719

  • 38

    OchmanH.WorobeyM.KuoC.-H.NdjangoJ.-B. N.PeetersM.HahnB. H.et al. (2010). Evolutionary relationships of wild hominids recapitulated by gut microbial communities. PLoS Biol.8:e1000546. 10.1371/journal.pbio.1000546

  • 39

    OksanenJ.BlanchetF. G.KindtR.LegendreP.MinchinP. R.O'HaraR. B.et al. (2011). Vegan: Community Ecology Package. R package version 2.0-2. Available online at: http://CRAN.R-project.org/package=vegan

  • 40

    PriceM. N.DehalP. S.ArkinA. P. (2009). FastTree: computing large minimum-evolution trees with profiles instead of a distance matrix. Mol. Biol. Evol.26, 16411650. 10.1093/molbev/msp077

  • 41

    QinJ.LiR.RaesJ.ArumugamM.BurgdorfK. S.ManichanhC.et al. (2010). A human gut microbial gene catalogue established by metagenomic sequencing. Nature464, 5965. 10.1038/nature08821

  • 42

    QuinnG.KeoughM. (2002). Experimental Design and Data Analysis for Biologists. Cambridge: Cambridge University Press. 10.1017/cbo9780511806384

  • 43

    R Development Core Team (2010). R: A Language for Statistical Computing. Vienna: R Foundation for Statistical Computing.

  • 44

    RemsenJ. V.Jr.CadenaC. D.JaramilloA.NoresM. A.PachecoJ. F.Perez-EmanJ.et al. (2012). A Classification of the Bird Species of South America. American Ornithologists' Union. Available online at: http://www.museum.lsu.edu/~Remsen/SACCBaseline.html

  • 45

    RoeselersG.MittgeE. K.StephensW. Z.ParichyD. M.CavanaughC. M.GuilleminK.et al. (2011). Evidence for a core gut microbiota in the zebrafish. ISME J.5, 15951608. 10.1038/ismej.2011.38

  • 46

    RoggenbuckM.SchnellI.BlomN.BælumJ.BertelsenM. F.PonténT. S.et al. (2014). The microbiome of New World vultures. Nat. Commun.5:5498. 10.1038/ncomms6498

  • 47

    SalterS. J.CoxM. J.TurekE. M.CalusS. T.CooksonW. O.MoffattM. F.et al. (2014). Reagent and laboratory contamination can critically impact sequence-based microbiome analyses. BMC Biol.12:87. 10.1186/s12915-014-0087-z

  • 48

    SchlossP. D.WestcottS. L.RyabinT.HallJ. R.HartmannM.HollisterE. B.et al. (2009). Introducing mothur: open-source, platform-independent, community-supported software for describing and comparing microbial communities. Appl. Environ. Microbiol.75, 75377541. 10.1128/AEM.01541-09

  • 49

    SchlossP. D.HandelsmanJ. (2005). Introducing DOTUR, a computer program for defining operational taxonomic units and estimating species richness. Appl. Environ. Microbiol.71, 15011506. 10.1128/AEM.71.3.1501-1506.2005

  • 50

    SharonG.SegalD.RingoJ. M.HefetzA.Zilber-RosenbergI.RosenbergE. (2010). Commensal bacteria play a role in mating preference of Drosophila melanogaster. Proc. Natl. Acad. Sci. U.S.A.107, 2005120056. 10.1073/pnas.1009906107

  • 51

    SmillieC. S.SmithM. B.FriedmanJ.CorderoO. X.DavidL. A.AlmE. J. (2011). Ecology drives a global network of gene exchange connecting the human microbiome. Nature480, 241244. 10.1038/nature10571

  • 52

    SmithB. T.McCormackJ. E.CuervoA. M, Hickerson, M. J.AleixoA.CadenaC. D.et al. (2014). The drivers of tropical speciation. Nature515, 406409. 10.1038/nature13687

  • 53

    StotzD. F.FitzpatrickJ. W.ParkerT. A.MoskovitsD. K. (1996). Neotropical Birds: Ecology and Conservation. Chicago, IL: The University of Chicago Press.

  • 54

    SullamK. E.EssingerS. D.LozuponeC. A.O'ConnorM. P.RosenG. L.KnightR.et al. (2012). Environmental and ecological factors that shape the gut bacterial communities of fish: a meta-analysis. Mol. Ecol. 21, 33633378. 10.1111/j.1365-294X.2012.05552.x

  • 55

    TelloJ.MoyleR.MarcheseD.CracraftJ. (2009). Phylogeny and phylogenetic classification of the tyrant flycatchers, cotingas, manakins, and their allies (Aves: Tyrannides). Cladistics25, 429467. 10.1111/j.1096-0031.2009.00254.x

  • 56

    TurnbaughP.HamadyM.YatsunenkoT.CantarelB. L.DuncanA.LeyR. E.et al. (2008). A core gut microbiome in obese and lean twins. Nature457, 480484. 10.1038/nature07540

  • 57

    TurnbaughP. J.QuinceC.FaithJ. J.McHardyA. C.YatsunenkoT.NiaziF.et al. (2010). Organismal, genetic, and transcriptional variation in the deeply sequenced gut microbiomes of identical twins. Proc. Natl. Acad. Sci. U.S.A.107, 75037508. 10.1073/pnas.1002355107

  • 58

    VidenskaP.RahmanM. M.FaldynovaM.BabakV.MatulovaM.Prukner-RadovcicE.et al. (2014). Characterization of egg laying hen and broiler fecal microbiota in poultry farms in Croatia, Czech Republic, Hungary and Slovenia. PLoS ONE9:e110076. 10.1371/journal.pone.0110076

  • 59

    WaiteD. W.TaylorM. W. (2014). Characterizing the avian gut microbiota: membership, driving influences, and potential function. Front. Microbiol.5:223. 10.3389/fmicb.2014.00223

  • 60

    WangQ.GarrityG. M.TiedjeJ. M.ColeJ. R. (2007). Naive Bayesian classifier for rapid assignment of rRNA sequences into the new bacterial taxonomy. Appl. Environ. Microbiol.73, 52615267. 10.1128/AEM.00062-07

  • 61

    WhitmanW. B.ColemanD. C.WiebeW. J. (1998). Prokaryotes: the unseen majority. Proc. Natl. Adad. Sci. U.S.A.95, 65786583. 10.1073/pnas.95.12.6578

  • 62

    WienemannT.Schmitt-WagnerD.MeuserK.SegelbacherG.SchinkB.BruneA.et al. (2011). The bacterial microbiota in the ceca of Capercaillie (Tetrao urogallus) differs between wild and captive birds. Syst. Appl. Microbiol.34, 542551. 10.1016/j.syapm.2011.06.003

  • 63

    XenoulisP. G.GrayP. L.BrightsmithD.PalculictB.HoppesS.SteinerJ. M.et al. (2010). Molecular characterization of the cloacal microbiota of wild and captive parrots. Vet. Microbiol.146, 320325. 10.1016/j.vetmic.2010.05.024

  • 64

    XuJ.GordonJ. I. (2003). Honor thy symbionts. Proc. Natl. Adad. Sci. U.S.A.100, 1045210459. 10.1073/pnas.1734063100

  • 65

    YatsunenkoT.ReyF. E.ManaryM. J.TrehanI.Dominguez-BelloM. G.ContrerasM.et al. (2012). Human gut microbiome viewed across age and geography. Nature486, 222227. 10.1038/nature11053

  • 66

    ZhuX. Y.ZhongT.PandyaY.JoergerR. D. (2002). 16S rRNA-based analysis of microbiota from the cecum of broiler chickens. Appl. Environ. Microbiol.68, 124137. 10.1128/AEM.68.1.124-137.2002

Summary

Keywords

Neotropical birds, gut microbiota, V6, host-associated microbiota, evolution

Citation

Hird SM, Sánchez C, Carstens BC and Brumfield RT (2015) Comparative Gut Microbiota of 59 Neotropical Bird Species. Front. Microbiol. 6:1403. doi: 10.3389/fmicb.2015.01403

Received

23 April 2015

Accepted

25 November 2015

Published

21 December 2015

Volume

6 - 2015

Edited by

Boran Kartal, Radboud University, Netherlands

Reviewed by

David William Waite, University of Auckland, New Zealand; Michael Roggenbuck, University of Copenhagen, Denmark; Kevin Kohl, Vanderbilt University, USA

Updates

Copyright

*Correspondence: Sarah M. Hird

†Present Address: Sarah M. Hird, UC Davis Genome Center, University of California Davis, Davis, CA, USA

This article was submitted to Evolutionary and Genomic Microbiology, a section of the journal Frontiers in Microbiology

Disclaimer

All claims expressed in this article are solely those of the authors and do not necessarily represent those of their affiliated organizations, or those of the publisher, the editors and the reviewers. Any product that may be evaluated in this article or claim that may be made by its manufacturer is not guaranteed or endorsed by the publisher.

Outline

Figures

Cite article

Copy to clipboard


Export citation file


Share article

Article metrics