Manduca sexta (Sphingidae) represents a lepidopteran species adapted to extreme habitat conditions because their larvae can feed exclusively on the leaves of tobacco plants (
43). Tobacco plants typically contain high amounts of alkaloids which are highly toxic to other insects and vertebrates but not to
M. sexta (
21,
49,
57). Once hatched from eggs deposited on tobacco leaves, the
M. sexta larvae consume large amounts of such leaves and pass through five larval stages (instars) within 2 to 3 weeks, increasing their individual body weight from approximately 1 mg to 10 g (
22,
43). While this simple feeding strategy is a large problem for tobacco growers (
23), it is, under controlled conditions, an excellent system to generate larvae for biological research, which explains the broad use of
M. sexta in laboratories worldwide (for examples, see references
26,
29, and
52).
Despite their wide laboratory dissemination and their economic importance as plant pests, surprisingly little is known about the bacterial communities in their guts. Cultivation studies suggest that the diversity is low, as only two 16S rRNA types were retrieved on LB plates, but these were not characterized further, e.g., by DNA sequencing (
10). In another study, three different bacterial strains, in addition to a yeast strain, were cultivated from
M. sexta larval gut contents after incubation in a nutrient broth and on LB agar. These strains were tentatively assigned to two
Bacillus species and a
Serratia plymuthica (
54). A survey of gut and fecal bacteria culturable under aerobic conditions on common laboratory media and characterized by 16S rRNA gene sequencing retrieved relatives of the genera
Enterobacter, Escherichia, Pantoea, Flavobacterium, Pseudomonas, and
Bacillus (unpublished results; accession numbers in the EMBL nucleotide database, FM212207 to FM212221). Experience from many similar studies suggests that such cultivation data most likely give a wrong picture of the actual microbial diversity, which makes it rewarding to use methods independent of cultivation.
The gut of
M. sexta, just like that of other herbivorous lepidopteran larvae (caterpillars), is a simple tube comprising the largest part of the whole body. This simple structure can be explained by phylogenetic adaptation for the rapid passage and processing of large quantities of solid plant material (
15). Midgut conditions are highly alkaline with pH values of 9 and above, which facilitates the extraction of nutrients (
2). It can be assumed that such alkaline conditions along with frequent quick molting cycles between larval stages, which also affect gut function (
8), and speedy food passage altogether present relatively selective conditions for bacterial communities. A recent cultivation-independent analysis of another lepidopteran larva (
Lymantria dispar) in fact revealed the presence of relatively low diversity with only nine different 16S rRNA sequences (phylotypes) (
6).
The objective of this study was to characterize the bacterial diversity in the guts of
M. sexta larvae kept under laboratory breeding conditions. The study was based on the cultivation-independent detection of PCR-amplified partial 16S rRNA sequences and their phylogenetic assignment to look for closest relatives. In order to determine the source of the bacteria, the bacterial diversity associated with the food (tobacco leaves) and with
M. sexta eggs deposited on the leaf surfaces were also determined. To allow the distinction between abundant and metabolically active bacteria, comparisons were made between genetic profiles with the single-strand conformation polymorphism (SSCP) technique (
12,
48) of the partial 16S rRNA genes PCR amplified from the total community DNA and 16S rRNA itself using reverse transcriptase PCR (RT-PCR). In addition, it was explored whether stable isotope probing (SIP) of 16S rRNA sequences (
34) would also be capable of and possibly more sensitive in detecting metabolically active gut bacteria. For this purpose, larvae were bred on the leaf material of tobacco plants previously grown in an atmosphere highly enriched with
13CO
2.
MATERIALS AND METHODS
Identity and cultivation of the tobacco plants.
All feeding experiments in this study were conducted with
Nicotiana tabacum cv. PBD6 (nontransgenic) plants and their corresponding plastid transformants (transgenic), carrying
aadA genes. Details of the plants and their construction have been described elsewhere (
30). The plants, if not otherwise stated, were grown from seeds in pots with a diameter of 30 cm filled with potting soil (Einheitserde Typ ED 73, Einheitserdewerke, Hameln, Germany) at 28°C under a light-dark cycle of 12 h each per day. During cultivation, all plants were fertilized with 0.2% (vol/vol) Manna Wuxal Super (Haug, Ammerbuch-Pfäffigen, Germany). Seeds of nontransgenic and transgenic plants were kindly provided by the TRANSBAC coordinators at the Institute Écologie Microbienne, Université Claude Bernard Lyon, France.
13C-enriched tobacco plants were generated under greenhouse conditions to supply 13CO2 as a plant carbon source. For this purpose, seeds of nontransgenic and transgenic N. tabacum were surface sterilized by rinsing with a 70% (vol/vol) aqueous ethanol solution for 2 min, followed by an incubation of 5 min in 12% (vol/vol) sodium hypochlorite, before washing five times with sterile distilled water. The seeds, kept under sterile conditions, were germinated at 26°C for a photoperiod of 16 h up to the first leaf stage, before seedlings were transferred into 50-ml Falcon tubes (Becton Dickenson, Heidelberg, Germany) half filled with sterile expanded clay (grain size, 4 to 8 mm). Each tube containing a seedling was closed with Parafilm (Brand, Wertheim, Germany), and plants were cultivated for an additional 2 weeks. Sterile water and liquid fertilizer (0.2% [vol/vol] Manna Wuxal Super) were added to each plant as recommended.
13CO2 was produced by weighing 1.4 g “heavy” sodium carbonate (Na213CO3; Sigma-Aldrich Chemie, Taufkirchen, Germany) and 500 μl of 3% (wt/vol) methyl orange (Merck, Darmstadt, Germany) into a bottle with a volume of 316 ml. The bottle was evacuated, and 7 ml of 10% (vol/vol) sulfuric acid (H2SO4) was injected through a membrane inserted in the lid of the bottle to generate 13CO2. The amounts of sodium carbonate and sulfuric acid were calculated to fill the bottle completely with 13CO2. To avoid a negative pressure in the bottle, the volume of the removed gas was replaced by the addition of 10% (vol/vol) H2SO4.
Four-week-old tobacco plants, six transplastomic and six isogenic control plants were transferred into a gas-tight chamber. The chamber was connected via a Tygon plastic tube to an infrared carbon dioxide analyzer (LCA2, ADC BioScientific, Great Amwall, United Kingdom), measuring the actual CO2 concentration in this closed system. The chamber was set up in the greenhouse at 26°C; depending on the external lighting conditions, artificial light was added as required. The circulation of air was achieved by a ventilator attached to the top of the chamber; the temperature inside was controlled using a thermometer. 13CO2 was injected with a syringe into the chamber up to a maximum carbon dioxide concentration of 1,000 mg liter−1, and when a minimum of 200 mg liter−1 was reached, more 13CO2 was added. Twelve plants were grown under these conditions for 12 h each day over a period of 15 days. The plants were kept in a closed box in the dark for 12 h each night and thereby protected from photosynthetically active light. Water and liquid fertilizer were added as required.
Feeding experiments.
Breeding stocks of
Manduca sexta were kept as described previously (
5). Eggs from these breeding stocks were directly transferred onto whole tobacco plants. After hatching, the larvae began to feed on the plant material and went through all five larval stages within the following 5 weeks. Five to 10 larvae of each stage were collected and analyzed. Larvae of the instar 1 and instar 2 stages were used as a whole for the extraction of total nucleic acids, while for the following three larval stages, total nucleic acids were extracted from the guts only. Depending on the larval stage, guts or whole larvae were stored in 70% ethanol at 4°C for 3 days prior to the extraction of the total nucleic acids. In addition, 100 eggs of
M. sexta were conserved in 70% ethanol and stored at −20°C. Also, feces from each larval stadium were collected and stored at 4°C for up to 3 days before extraction of the total nucleic acids.
Total nucleic acid extractions for bacterial community analyses.
Gut and feces samples, as well as eggs and tobacco leaves, were ground in liquid nitrogen using a mortar and pestle. The crushed material was stored at −70°C until further processing. The extraction of total nucleic acid was conducted by using the protocol of Lueders et al. (
33) with 100 mg of each ground sample. The quality of the total nucleic acids was evaluated on 0.8% (wt/vol) agarose gel (
44). Nucleic acid extracts were stored in aliquots at −20°C.
PCR amplification of the partial 16S rRNA gene sequences.
To generate genetic profiles with SSCP (see below), partial 16S rRNA gene sequences were amplified by PCR from total nucleic acids using a nested-PCR approach. The first PCR was conducted with primers 27f and 1492r (
55) to amplify the almost complete bacterial 16S rRNA gene. The second PCR was used to generate the PCR products for the SSCP profiles with the universal Com1 and Com2-Ph primers, the latter primer being phosphorylated for further single-strand digestion (
48). This nested PCR approach was chosen to exclude the amplification of 18S rRNA genes from contaminating gut tissue. Each PCR was conducted in a total volume of 50 μl. The PCR master solution contained 0.5 μM concentrations of each primer (MWG Biotech, Ebersberg, Germany), each nucleotide at a concentration of 0.2 mM (Qbiogene, Heidelberg, Germany), and 1.25 U of
Taq polymerase (HotStar Taq; Qiagen, Hilden, Germany) with the corresponding 1× PCR buffer, 1.5 mM MgCl
2, and 1.5 μl template DNA. PCR amplifications were conducted in a Primus96 thermocycler (MWG Biotech). An initial denaturation step at 95°C for 15 min was followed by 30 cycles of 60 s at 94°C, 60 s at 50°C, 70 s at 72°C, and, for the last cycle, a final extension of 5 min at 72°C was added. The second PCR with primers Com1 and Com2-Ph was conducted with only 25 cycles under the same conditions. For each sample, PCR amplifications were carried out in triplicate, and products were analyzed by agarose gel electrophoresis stained with ethidium bromide (
44) and then combined.
Amplification of the 16S rRNA sequences by RT-PCR.
For rRNA-based genetic profiles, DNA was digested from the total nucleic acid samples using the RQ1 RNase-free DNase (Promega, Mannheim, Germany), which degrades both double- and single-stranded DNA endonucleolytically, producing 3′-OH oligonucleotides. Before digestion, DNA concentrations in the total nucleic acid samples were determined with the PicoGreen double-stranded DNA quantification reagent (MoBiTec, Göttingen, Germany) and a microtiter plate reader (Fluroskan II; Labsystems, Helsinki, Finland). The concentration of RQ1 RNase was adjusted to the DNA concentration as recommended by the manufacturer. For each sample, a DNase digestion reaction mix was set up by using up to 8 μl of each sample (total nucleic acid), 1 μl RQ1 RNase-free DNase 10× reaction buffer, and 1 U μg−1 DNA of the RQ1 RNase-free DNase. Each digestion approach was incubated at 37°C for 30 min using a Primus96 thermocycler (MWG Biotech). After incubation, 1 μl of RQ1 DNase Stop solution per reaction terminated the digestion reaction, and a following incubation at 65°C for 10 min inactivated the DNase. RNA was stored at −70°C until further processing for a maximum of 3 days. After DNA digestion, the RNA samples were used as templates for a control PCR with primers 27f and 1492r followed by Com1 and Com2-Ph, respectively, as described above, to control the DNA digestion. Successful DNA digestion was indicated by the lack of a PCR product on the agarose gels.
The RNA concentration of each sample was determined by quantification using the RiboGreen quantification kit (MoBiTec) following the manufacturer's instructions. RT-PCR was performed by using the Access RT-PCR system (Promega). Each PCR was conducted in a total volume of 50 μl. The PCR master solution contained 1 μM of each primer (27f/1492r), each nucleotide at a concentration of 0.2 mM, 1 mM MgSO4, 0.1 U μl−1 avian myeloblastosis virus (AMV) RT, 0.1 U μl−1Tfl polymerase, and the corresponding 1× AMV/Tfl reaction buffer. The reaction was initiated by adding 2 μl of RNA sample (10 pg to 1 μg). The first-strand cDNA synthesis was conducted by reverse transcription during incubation at 45°C for 45 min, followed by one cycle at 94°C for 2 min to allow AMV RT inactivation and RNA/cDNA/primer denaturation. The generation of the second-strand and PCR amplifications was conducted by 40 cycles of 30 s at 94°C, 1 min at 60°C, and 2 min at 68°C and a final extension of 7 min at 68°C. For a positive control, the supplied positive-control RNA with carrier and the upstream and downstream control primers were used. For a negative control, sterile nuclease-free water was substituted instead of RNA template. All steps were conducted in a Primus96 thermocycler (MWG Biotech). The PCR products from this reaction were used as a template for the following PCR (nested approach) using Com1 and Com2-Ph. PCR amplifications were carried out in triplicate, and products were analyzed by gel electrophoresis and combined.
Isopycnic centrifugation and fractionation of density gradients.
12C- and
13C-labeled RNA were separated by density gradient centrifugation using cesium trifluoroacetate (CsTFA) gradients (
33). Density gradient centrifugation was performed in 4.9-ml OptiSeal polyallomer centrifuge tubes (Beckman Coulter, Krefeld, Germany) in a VTi 65.2 rotor (Beckman Coulter) in an ultracentrifuge (L8-70 M; Beckman Coulter). Centrifugation was conducted at 20°C and approximately 70 h at 39,000 rpm to form the CsTFA density gradients. Centrifugation mixtures were prepared by mixing 4.5 ml of a 2-g ml
−1 CsTFA stock solution (Amersham Pharmacia Biotech, GE Healthcare Europe GmbH, München, Germany), 175 μl formamide, up to 1 ml gradient buffer (0.1 M Tris-HCl [pH 8], 0.1 M KCl, 1 mM EDTA), and RNA (up to 900 ng) to a final volume of 5.675 ml (the rRNA volume was subtracted from the volume of the gradient buffer). The density of the prepared mixtures was controlled with an AR200 digital refractometer (Leica Microsystems, Bensheim, Germany). The mixtures were transferred with a 10-ml syringe and a needle to the centrifuge tubes before the tubes were balanced and closed.
After centrifugation, the gradients were fractionated from the bottom to the top into 14 fractions of 375 μl each. For the collection of the gradient fractions, the centrifuge tubes were pierced from below with a sterile needle, and the removed gradient volume was replaced by water added from the top of the tube. The density of each fraction was determined by measuring aliquots of 75 μl in the refractometer. RNA was precipitated from all fractions with 500 μl isopropanol, followed by centrifugation for 30 min at 14,000 rpm at room temperature (Sigma 4K10, Osterode, Germany). The precipitates were washed with 150 μl ethanol (70%, vol/vol), spun for 5 min at 14,000 rpm, and resuspended in 30 μl of Tris-EDTA buffer. Reverse transcription of the RNA into cDNA and PCR amplification were performed as described above. The following second PCR to amplify the partial rRNA region used for the SSCP profiles was also conducted as described.
SSCP analysis.
Purification of the PCR and RT-PCR products was done with the QIAquick PCR purification kit (Qiagen) following the manufacturer's instructions. Each product was eluted in 30 μl elution buffer. After purification, DNA concentrations were determined with PicoGreen as described above. Approximately 800 ng of each purified PCR product was then treated at 37°C for 60 min with 5 U of lambda-exonuclease (Amersham Biosciences, GE Healthcare Europe GmbH, München, Germany) to remove the phosphorylated reverse DNA strand from the double-stranded PCR products (
12). The single-stranded DNA molecules were purified using the MiniElute PCR purification kit (Qiagen) and eluted with 10 μl elution buffer before adding 8 μl of loading buffer (95% [vol/vol] formamide, 10 mM NaOH, 0.25% [wt/vol] bromophenol blue, and 0.25% [wt/vol] xylene cyanole). The samples were denatured for 2 min at 95°C, cooled on ice, and loaded on a nondenaturing polyacrylamide gel for SSCP electrophoresis. The pouring and staining of the SSCP gels as well as the electrophoretic conditions have been described elsewhere (
47,
48). Briefly, the single-strand PCR products were separated in polyacrylamide gels (MDE; FMS Bioproducts) using a Macrophor apparatus (Amersham Biosciences) set at 400 V and 8 mA and a running temperature of 20°C for 6,800 V h. DNA was visualized by silver staining. SSCP markers were generated from bacterial pure cultures by PCR using Com1 and Com2-Ph and subsequent single-strand removal (see above).
Extraction and sequencing of bands from SSCP profiles.
Bands of interest were cut out from the silver-stained polyacrylamide SSCP gels with a sterile scalpel. The single-stranded DNA was eluted from the gel by the “crush and soak” procedure (
44), resuspended in 12 μl of 10 mM Tris-HCl (pH 8.0), and amplified by PCR using primers Com1 and Com2-Ph under the conditions described above. The PCR products were purified using the NucleoSpin extract kit (Macherey-Nagel, Düren, Germany). After purification, ligation of the PCR products with the pGEM-T vector system (Promega) followed, and the ligated plasmids were transformed into
Escherichia coli JM 109 for cloning, using the procedure recommended by the manufacturer (Promega). DNA of the clones with the vector inserts was extracted by alkaline lysis (15 min at 95°C in 0.05 M NaOH, 0.025% [wt/vol] sodium dodecyl sulfate [Sigma Aldrich]) and treated as a template in the PCR with primers puc18f (5′-CAC GAC GTT GTA AAA CGA C-3′) and puc18r (5′-GGA TAA CAA TTT CAC ACA GG-3′), hybridizing to the insert-flanking regions of the vector. A nested PCR of the diluted PCR obtained with primers Com1 and Com2-Ph followed. These PCR products were run on SSCP gels to compare the band position in the original community profile. Clones which carried the expected inserts were cultivated overnight in LB broth (
44) containing ampicillin (final concentration, 100 mg liter
−1), and plasmids were extracted with a plasmid DNA purification kit (Macherey-Nagel), following the protocol of the manufacturer. The sequencing reactions were carried out with the Sequitherm Excel II DNA sequencing kit-LC (Epicenter Technologies), and sequences were run and read using a LI-COR DNA 4200 GeneRead IR apparatus (LI-COR Biosciences, Bad Homburg, Germany) as described elsewhere (
46).
Phylogenetic analyses.
Sequences were analyzed and aligned with the ARB software package (www.arb-home.de ) (
32). Sequences were compared to each other and to database sequences using BLASTN search analyses (
http://www.ncbi.nlm.nih.gov/blast/ ) and tools provided by the Ribosomal Database Project RDP II (
http://rdp.cme.msu.edu/ ).
Nucleotide sequence accession numbers.
All sequences of this study have been submitted to the Nucleotide Sequence Database of the European Bioinformatics Institute (www.ebi.ac.uk ). The accession numbers are listed in Table
1.
DISCUSSION
The major part of the gut of
Manduca sexta larvae, the midgut, provides alkaline conditions (pH > 9) and a negative redox potential, the latter indicating anaerobic conditions (
3). In previous studies, we found that ingested food passed through the gut at a high flow rate: for fifth-instar-stage larvae, an average complete gut passage lasted only about 2 h while transporting approximately 1 g of ingested leaf material (wet weight) (
5). Cultivation methods suggested that the gut-transported substrate was colonized with bacteria, as approximately 10
8 bacterial cells were found per g freshly shed feces (
5). Detection by cultivation, however, cannot distinguish between metabolically active and inactive cells. The diversity of the potential bacterial carbon and energy sources which come with the ingested leaf material, i.e., cellulose, hemicellulose, pectins, proteins, nicotine, and other alkaloids, could support a diverse bacterial community in the gut. However, despite this diversity of nutrients, the DNA-based SSCP profiles of this study revealed low bacterial diversity, as only one strong and two weak bands were detected. The developmental stages (the first to fifth instar stages) had no clear effect on this bacterial community structure which would have become visible by altered SSCP profiles. However, the quality of the food may have had a minor influence, as a slight difference related to the presence of a
Burkholderia relative was detected between the transplastomic and the nonengineered tobacco cultivar. Bacterial communities with highly similar structure were also detected with the SSCP profiles generated from gut contents and feces, indicating that all major gut bacteria were associated with the food bolus and thus also shed. A comparable low diversity of the gut bacteria was also found in analyses of the guts of gypsy moth (
Lymantria dispar) larvae which provide similar alkaline conditions (
6). In contrast, the guts of larvae with less-alkaline conditions, as they occur, e.g., in beetles (Coleoptera), flies (Diptera), or bees (Apoidea), harbor much higher bacterial diversity (
18,
28,
37).
The DNA-based SSCP profiles of this study revealed clear differences between the bacterial communities on leaves, eggs, and guts or feces. The dominant band for leaves was also seen for eggs. In samples from the gut contents and feces, this band occurred at lower relative intensities. Phylogenetic analyses assigned this bacterium to the
Burkholderiales (
Betaproteobacteria), a group which comprises several bacterial species with a high potential to colonize plant material (
4). The relatively lower intensity of this band in gut contents and feces suggests that a population decline took place during the gut passage. For other insects with a similar rod-shaped gut architecture and fast gut passages of ingested feed, like Collembola, it has been demonstrated that gut passages can support bacterial growth or digestion depending on the bacterial species (
51). In fact, in this study, RNA-based SSCP profiles indicated that the
Burkholderia phylotype was metabolically active on the leaf material but not on eggs, gut material, and feces, where it was seen only in the DNA-based profiles.
DNA-based SSCP profiles from eggs also retrieved two phylotypes, one with 100% sequence identity to
C. sedlakii and another with 100% identity to
Enterococcus. The
C. sedlakii was also, however inconsistently, detected in samples from guts and feces. This band was also seen in the rRNA-based profiles from the gut and fecal material, suggesting that it was metabolically active in the gut but not on eggs where no band was seen in rRNA-based profiles. Members of the genus
Citrobacter have already been isolated from different insect guts, suggesting that they are in fact metabolically active gut inhabitants (
16,
45). It should be noted that the species
C. sedlakii can also be a human pathogen associated with meningitis in premature infants (
17). Sequence identity to 16S rRNA genes, however, does not allow the conclusion that the detected bacteria were pathogenic, as avirulent strains have also been described (
41).
The
Enterococcus phylotype was clearly the most abundant bacterial gut inhabitant, as indicated by the dominant bands in both DNA- and RNA-based SSCP profiles. It was not seen in any SSCP profiles of tobacco leaves, but it occurred with DNA- and RNA-based profiles of eggs, which strongly suggests that it was already metabolically active there. Members of the genus
Enterococcus are among the most common gut bacteria detected in larval guts across a diversity of insect orders (
35), including Diptera (
1,
9,
53) and Lepidoptera (
6,
24), but their ecological range for other habitats is also enormous (
20,
25,
31,
39,
42). The occurrence of active cells associated with eggs, inside the gut and later on in feces, also points to a versatile metabolic adaptation. Comparison of the rRNA-based profiles from eggs and gut material revealed that the
Enterococcus phylotype originated from eggs and not from leaves. The vertical transmission of gut bacteria from mothers to larvae via egg contamination has been described for beetles (Coleoptera) or fruit flies (Diptera) where mothers leave bacteria on the egg surface and larvae pick up these bacteria by licking or feeding on egg shells (
11,
13). Data from this study indicate that the same process is also relevant for larvae of
M. sexta and possibly lepidopteran larvae in general. In fact,
M. sexta larvae typically start to consume their egg cases immediately after hatching (
43). Interestingly, the egg itself seemed to support the metabolic activity of the prospective gut inoculant, which may be favorable for efficient gut colonization immediately after hatching. While rRNA-based SSCP profiles were an indication of metabolic activity based on the assumption that active bacteria contain more ribosomal particles than inactive ones, a valuable approach as also demonstrated in other studies (
19,
27,
36,
40), SIP of 16S rRNA sequences was direct proof of metabolic activity. Beginning from egg hatching, the larvae of this study grew up with only
13C-labeled carbon sources originating from the tobacco leaves previously cultivated in a
13CO
2 atmosphere. Thus, the complete larval biomass was highly enriched by
13C. This did not allow a distinction between bacteria utilizing plant material and others, metabolically active, using other carbon sources excreted into the gut lumen from the insects themselves, i.e., the peritrophic membrane, which consists of chitin and proteins and contains old epithelial cells shed during molting (
8,
50). The SIP results of this study confirmed that the
Enterococcus phylotype was the metabolically dominant bacterium inside the gut. In addition, an
Enterobacter relative was also detected from fractions highly enriched in
13C, demonstrating that SIP was more sensitive to detect the metabolically active bacteria than the “conventional” rRNA profiles. An
Enterobacter was also found as a consistent gut colonizer of the gypsy moth (
6). Furthermore, additional sequences were retrieved from the
12C-enriched fractions, which were suspected to originate from metabolically less-active or inactive bacteria. The 16S rRNA-based phylogenetic analyses revealed that these sequences were from bacterial species which had already been detected in other lepidopteran larval guts, e.g.,
Bacillus licheniformis, Flavobacterium sp., and
Delftia acidovorans (
37,
38,
58). These bacteria were obviously not among the dominant bacteria associated with the food (tobacco leaves) or eggs, as judged by their absence in DNA-based SSCP profiles. We suspect that they were enriched during the gut passage. SIP RNA demonstrated that this enrichment was not caused by active growth, suggesting that they might have been successful in withstanding digestion inside the gut, in contrast to the leaf-associated
Burkholderia member described above.
In summary, this study demonstrates that cultivation-independent DNA- and RNA-based SSCP profiling of bacterial SSU rRNA genes, in combination with 13C enrichment and SIP-RNA analyses and phylogenetic analyses, provides a powerful approach for exploring the origin, diversity, and metabolic activity of the bacterial community associated with insect larvae. The methods should have the potential to also explore more complex bacterial communities as detected in this study with M. sexta larvae and to investigate interactions between insects and microorganisms as they take place a billionfold in nature.