INTRODUCTION
Burkholderia pseudomallei,
Burkholderia mallei, and
Burkholderia thailandensis are closely related species that display notable differences in pathogenic potential, host specificity, and environmental persistence (
1,
2).
B. pseudomallei and
B. mallei are the etiological agents of melioidosis and glanders, respectively, and are tier 1 select agents in the United States due to their potential for misuse as biological weapons (
3). While numerous mammalian species are susceptible to melioidosis (
4,
5), naturally occurring glanders is most commonly associated with equines, felines, and humans (
6–8).
B. mallei is a host-adapted pathogen that does not persist in the environment for prolonged periods outside its animal host.
B. thailandensis, on the other hand, is an environmental saprophyte with poor pathogenic potential for animals and humans (
9,
10).
Environmental survival is critical for
B. pseudomallei and
B. thailandensis as both reside in soil, water, and/or rhizosphere sources in tropical and subtropical regions around the world (
11,
12). These ecosystems are composed of complex mixtures of microbial species and abiotic materials. To survive and persist in these environments, bacteria have evolved contact-dependent and contact-independent strategies to compete for finite resources (
13,
14). Many Gram-negative bacteria utilize type VI secretion systems (T6SSs) as contact-dependent contractile nanomachines to puncture competitor bacteria and deliver toxic effector proteins (
15–17).
B. thailandensis employees a T6SS, termed T6SS-1, to compete with other bacteria, including
Pseudomonas putida,
Pseudomonas fluorescens, and
Serratia proteamaculans (
18). T6SS-1, also referred to as T6SS-6 (
19), is conserved in
B. pseudomallei and presumably plays a similar role in contact-dependent inhibition of Gram-negative bacteria. Both species also possess ∼15 large biosynthetic gene clusters that produce a variety of small-molecule secondary metabolites that serve as siderophores, cytotoxins, antibiotics, and virulence factors (
20–23). Many of these molecules mediate contact-independent interactions with microbial competitors, and some of them have been structurally and functionally characterized, including malleipeptin, syrbactin, malleilactone, bactobolin, acybolin, thailandamide, thailandenes, malleobactin, pyochelin, terphenyl, isonitrile, and 4-hydroxy-3-methyl-2-alkenylquinolines (HMAQs).
There has been great interest in the HMAQs produced by
Burkholderia sp. recently (
21,
24–27). The
Burkholderia hmqA-G gene cluster encodes the enzymes responsible for generating HMAQs from anthranilic acid and β-keto fatty acids (
28–30). The biosynthetic pathway generates multiple HMAQ congeners that differ from one another based on the length of the unsaturated aliphatic side chains. The most abundant HMAQ congeners in
B. thailandensis and
B. pseudomallei are those with C
9 side chains (
30).
N-Oxide derivatives of HMAQs, HMAQ-NOs, are generated by an unlinked gene (
hmqL) encoding a monooxygenase (
25). Both HMAQs and HMAQ-NOs act as antimicrobial agents, but HMAQ-NOs tend to have enhanced inhibitory activity (
25–27,
31,
32).
The goal of this study was to investigate the competitive interaction between B. pseudomallei and environmental bacteria at the molecular level. The results show that the molecules produced by the B. pseudomallei hmqA-G locus, including HMAQs and HMAQ-NOs with C7 and C9 unsaturated alkyl side chains, are solely responsible for contact-independent inhibition of Gram-positive bacteria isolated from diverse environmental sources.
DISCUSSION
Microorganisms inherently engage in exploitative competition (passive) and interference competition (active) in an attempt to survive and persist in diverse environmental niches (
13,
14). Exploitative competition occurs when a microbe depletes the limiting nutrients in a shared niche, and interference competition involves a microbe damaging another microbe via contact-dependent or contact-independent mechanisms. Microbial competition assays are often employed to study these behaviors, and they commonly involve mixing two strains or species together and examining their relative survival under defined growth conditions (
13,
14,
38,
41). Such experiments cannot replicate the natural environment of the competitors but can provide information about the bacterial factors that facilitate competition under specific laboratory conditions. There are relatively few published studies examining the ability of
B. pseudomallei to compete with environmental bacteria. Ngamdee et al. reported that multiple
B. pseudomallei strains inhibited the growth of
B. thailandensis when cocultured on LB agar for 24 h at 37°C, but the inhibition only occurred when the
B. pseudomallei/
B. thailandensis ratio was ≥100:1 (
42). The mechanism of growth inhibition was not investigated but could involve CDI.
B. pseudomallei strains contain an assortment of modular CDI systems that serve to inject protein toxins, often tRNases or DNases, directly into target bacteria, resulting in death in the absence of specific immunity proteins (
43). Recent studies suggest that CDI systems are highly specific and probably only result in growth inhibition of closely related strains or species (
44). While
B. pseudomallei can potentially utilize CDI to target bacteria within the genus
Burkholderia, it probably cannot be used to target more distantly related Gram-negative or Gram-positive bacteria. Lin et al. isolated
Burkholderia cenocepacia and
Burkholderia multivorans strains from soil in Taiwan that exported a soluble substance that produced zones of inhibition on a
B. pseudomallei agar lawn (
45). The antimicrobial substance was filterable but was not further characterized. Interestingly, the presence of
B. cenocepacia and
B. multivorans in agricultural crop soil was inversely correlated with the presence of
B. pseudomallei, suggesting that these
Burkholderia species might be antagonistic to
B. pseudomallei in the soil (
45).
In this study, we sought to examine how
B. pseudomallei competes with environmental bacteria at the molecular level. We isolated Gram-positive bacteria from soil, river water, river sediment, stream water, and rhizosphere sources in the Middle Atlantic region of the United States. It is important to emphasize that these bacteria are not specific to this geographical region and have been isolated from diverse environmental sources worldwide (
46–51). We employed a modified contact-mediated competition assay (
38) to explore the relative competitive fitness of
B. pseudomallei with 14 environmental Gram-positive bacteria.
B. pseudomallei outcompeted 6/14 environmental bacteria in this assay, including
N. bataviensis,
B. velezensis,
B. licheniformis,
B. mycoides,
Cellulosimicrobium sp., and
Microbacterium sp. (
Table 1 and
Fig. 6).
B. velezensis is a member of the “operational group of
Bacillus amyloliquefaciens” due to the close relatedness of these species (
52). In recent studies conducted in Thailand, six
B. amyloliquefaciens isolates were obtained from soil samples that were devoid of
B. pseudomallei, and it was hypothesized that the lack of
B. pseudomallei might correspond to the presence of antimicrobial compounds in this niche (
53,
54). In further studies, the researchers found that
B. amyloliquefaciens inhibited
B. pseudomallei growth in a liquid coculture assay and that
B. amyloliquefaciens supernatant contained an antimicrobial peptide that produced zones of inhibition on
B. pseudomallei agar lawns (
53,
54). These studies suggest that
B. amyloliquefaciens exports secondary metabolites with antimicrobial properties into the surrounding environment that may prevent niche colonization by
B. pseudomallei. In comparison, we found that
B. pseudomallei outcompeted
B. velezensis by 60-fold in an
hmqD-dependent manner (
Table 1 and
Fig. 6B). Bacterial exported secondary metabolites, namely,
Bacillus antimicrobial peptides or
Burkholderia HMAQs and HMAQ-NOs, may be responsible for the different competitive fitness results reported in these studies. Variability in the secondary metabolites produced by the
B. pseudomallei strains utilized seems unlikely given that both studies utilized 1026b and its isogenic derivatives (
Table 2 and see Fig. S1 in the supplemental material) (
54). On the other hand, the results reported here may differ from those of the Sermswan laboratory (
54) due to differences in the secondary metabolites produced by the
B. velezensis and
B. amyloliquefaciens strains used or in the competition assays employed. Future studies are warranted to address these possibilities.
The results presented here demonstrate that the secondary metabolites produced by the
hmqA-G locus are critical for
B. pseudomallei competition with environmental bacteria. There has been limited research on HMAQ and its derivatives in
B. pseudomallei (
29,
30), but much work has been conducted on these molecules in
B. thailandensis (
23,
25,
28,
31,
32). The
B. thailandensis hmq genes were recently shown to be important for inhibiting the growth of
B. subtilis 168, a legacy strain used to study
Bacillus biology for decades (
25,
40).
B. pseudomallei and
B. thailandensis produce a similar array of HMAQ and HMAQ-NO congeners, but species-specific differences also exist (
30). The species variability is largely due to the relative amount of each congener produced, the length of the alkyl chains, and the presence or absence of unsaturation in the alkyl chains (
30). The most common HMAQ and HMAQ-NO congeners produced by
B. pseudomallei and
B. thailandensis are those with unsaturated C
9 alkyl chains. Piochon et al. (
27) chemically synthesized HMAQs and their
N-oxide counterparts with unsaturated C
7, C
8, and C
9 alkyl side chains and evaluated their relative antimicrobial activity against nine bacterial species. HMAQs were not as effective as HMAQ-NOs, which exhibited superior activity against Gram-positive bacteria relative to that against Gram-negative bacteria (
27). There is growing evidence that the diverse compounds produced by the
B. thailandensis hmq genes may act synergistically to inhibit bacterial growth by acting on different targets (
25,
32). Wu and Seyedsayamdost demonstrated that two of these molecules, 4-hydroxy-3-methyl-2-(2-nonenyl)-quinoline (HMNQ) and 2-heptyl-4(1
H)-quinoline
N-oxide (HQNO), both inhibit pyrimidine biosynthesis by acting on a common target but interrupt the proton motive force by acting on different targets (
32). They further speculated that antimicrobial resistance to the products of the
hmq gene cluster may be difficult to attain due to the diversity of target mutations that would be required. In support of this notion, we never identified
N. bataviensis resistant colonies emerge in areas of growth inhibition around any of the
B. pseudomallei agar lawns examined during this research study (data not shown). These results suggest that the five
B. pseudomallei HMAQ and HMAQ-NO congeners identified here (
Fig. 7), and the closely related derivatives identified by others (
30), may act synergistically to target environmental Gram-positive bacteria. It is currently unclear if all of the congeners, or only a few, are responsible for the growth inhibition we observed in the current study.
Klaus et al. found that
B. thailandensis HMAQ and HMAQ-NO congeners were largely cell associated and that the molecules present in culture supernatants could not be passed through a 0.2-μm membrane filter (
25). The
B. pseudomallei HMAQ and HMAQ-NO congeners, on the other hand, were present in culture supernatants and were filterable (
Fig. 3C and S2). In fact, the
B. pseudomallei HMAQ and HMAQ-NO molecules prepared for LC-MS analysis were directly extracted from filter-sterilized culture supernatants. It is not known how HMAQ and HMAQ-NO are exported from bacteria, but it is possible that
B. pseudomallei possesses a novel transporter that facilitates passage of these molecules out of the cell that is absent in
B. thailandensis. This might result in fewer cell-associated HMAQs and HMAQ-NOs in
B. pseudomallei and a higher proportion present in the supernatant. The transposon screen utilized in this study was low throughput, and a saturating transposon mutagenesis screen might be necessary to identify a putative
B. pseudomallei-specific HMAQ transporter. It was recently shown that
B. thailandensis outer membrane vesicles (OMVs) have antimicrobial activity and contain HMAQ-C
9 (
31). The purified OMVs ranged in size from 0.02 to 0.1 μm and should theoretically pass through a 0.2-μm membrane filter.
B. pseudomallei also secretes OMVs of a similar size, but it is currently unclear if they package HMAQs (
55). Further work will be necessary to determine why the molecules produced by the
B. thailandensis hmq-encoded biosynthetic enzymes are not filterable while those produced by
B. pseudomallei are.
In this study, we demonstrate that
B. pseudomallei HMAQ derivatives are exported antimicrobials that are critical for competitive interactions with a variety of environmental Gram-positive bacteria.
B. pseudomallei is an opportunistic pathogen that inherently resides in soil and/or water and can be transmitted to animals and humans via these contaminated sources. Bacterial survival and persistence in such niches require competition with complex microbial communities (
13,
14). The
B. pseudomallei results presented here, and those presented in a recent
B. thailandensis study (
25), indicate that both species rely on the
hmqA-G and
hmqL genes for competitive fitness against Gram-positive bacteria. Interestingly, the host-adapted pathogen
B. mallei has lost the
hmq genes and cannot persist for prolonged periods in the environment (
30,
56). Taken together, the data support the notion that HMAQ and HMAQ-NO derivatives are important for survival and persistence in environmental sources containing complex microbial communities (
21). There has been little information published about the importance of these molecules in
B. pseudomallei virulence, but Price et al. (
57) found that the
hmqA-G genes were upregulated in chronically adapted cystic fibrosis (CF) patient isolates following growth in artificial CF sputum medium. Further studies will be necessary to determine if the products encoded by the
hmqA-G locus are important for
B. pseudomallei virulence.
MATERIALS AND METHODS
Bacterial strains, plasmids, and growth conditions.
The bacterial strains and plasmids used in this study are shown in
Table 2.
Escherichia coli and
B. pseudomallei K96243 (
58), 1026b (
59), and MSHR346 were grown at room temperature (RT) or 37°C on Luria-Bertani (LB) agar (Lennox formulation; Sigma-Aldrich) or in LB broth. One hundred micrograms per milliliter adenine HCl and 5 μg/ml thiamine HCl were added to solid and liquid media for growth of the
purM select agent exempt strain
B. pseudomallei Bp82 (
60). Broth cultures were grown in 14-ml Falcon round-bottom polypropylene test tubes with snap caps (Fisher Scientific) containing 3 ml of LB and shaking at 250 rpm unless indicated otherwise. When appropriate, antibiotics were added at the following concentrations: 25 μg/ml kanamycin (Km) and streptomycin (Sm) for
E. coli, and 25 μg/ml polymyxin B (Pm) and 500 to 1,000 μg/ml Km for
B. pseudomallei. For induction studies, isopropyl-β-
d-1-thiogalactopyranoside (IPTG) was added to a final concentration of 0.5 mM. A 20-mg/ml stock solution of the chromogenic indicator 5-bromo-4-chloro-3-indolyl-β-
d-galactopyranoside (X-Gal) was prepared in
N,
N-dimethylformamide, and 40 μl was spread onto the surface of plate medium for blue/white screening in
E. coli TOP10 or
E. cloni 10G chemically competent cells. All manipulations with
B. pseudomallei select agent strains were carried out in a class II microbiological safety cabinet located in a designated biosafety level 3 (BSL3) laboratory. Other strains were handled in a class II microbiological safety cabinet located in a designated BSL2 laboratory.
Environmental bacteria were isolated from several sources in Frederick, MD, USA (latitude and longitude coordinates, 39.396509 and −77.368223, respectively) during 2017 to 2020. Bacterial river (R) isolates were obtained by spreading aliquots of Monocacy River water serially diluted in sterile phosphate-buffered saline (PBS) onto the surfaces of sheep blood agar plates, LB agar plates, LB agar plates supplemented with 60 μg/ml X-Gal, and 1× Difco M9 minimal Salts (Becton, Dickinson and Company) agar plates containing 0.4% glucose. The plates were incubated at 37°C for 2 days, and colonies that could be easily distinguished from B. pseudomallei colonies on solid medium due to morphology, pigmentation, and/or β-galactosidase production were selected for further characterization. A similar strategy was employed for water obtained from a stream (ST) that feeds directly into the Monocacy River. River sediment (RS) was obtained using sterile 50-ml conical tubes, resuspended in PBS, serially diluted in PBS, and spread onto agar plates as described above. Bacterial soil (S) isolates were obtained by using a hand trowel and placing soil 3 to 4 in. below the surface into 50-ml conical tubes. Approximately 2 g of soil was resuspended in PBS, vigorously vortexed, and serially diluted in PBS, and aliquots were spread onto agar plates as described above. Bacterial rhizosphere (RZ) isolates associated with the root microbiome of lawn weeds were placed into sterile 50-ml conical tubes and processed like the soil samples.
DNA manipulation.
Restriction enzymes (Roche Molecular Biochemicals and New England BioLabs), Antarctic phosphatase (New England BioLabs), and T4 DNA ligase (Roche Molecular Biochemicals) were used according to the manufacturer’s instructions. When necessary, the End-It DNA end repair kit (Epicentre) was used to convert 5′ or 3′ protruding ends to blunt-ended DNA. The DNA fragments used in the cloning procedures were excised from agarose gels and purified with a PureLink Quick gel extraction kit (Invitrogen). Bacterial genomic DNA was prepared from overnight LB broth cultures with the GenElute bacterial genomic DNA kit (Sigma-Aldrich). Plasmids were purified from overnight LB broth cultures by using the Wizard Plus SV miniprep DNA purification system (Promega).
PCR amplifications.
The PCR primers used in this study are shown in
Table 2. The PCR products were sized and isolated by using agarose gel electrophoresis, cloned using the pCR2.1-TOPO TA cloning kit (Life Technologies), and transformed into chemically competent
E. coli 10G (Lucigen). The PCR amplifications were performed in a final reaction volume of 50 or 100 μl containing 1× FailSafe PCR PreMix D (Epicentre), 1.25 U FailSafe PCR enzyme mix (Epicentre), 1 μM PCR primers, and approximately 200 ng of genomic DNA. Genomic DNA was isolated from all environmental bacterial isolates, and their 16S rRNA genes were PCR amplified using the primers 533F and 1492R (
Table 2) and cloned into pCR2.1-TOPO. The
Bacillus mycoides R15 and
Bacillus cereus ST9 16S rRNA genes were also PCR amplified using Rd1 and Fd1 (
Table 2). Colony PCR was utilized to screen for
B. pseudomallei deletion mutants. Briefly, sucrose-resistant and Km-sensitive colonies were resuspended in 50 μl of water, and 5 μl was added to the PCR mixture rather than purified genomic DNA. PCR cycling was performed using a Mastercycler pro S (Eppendorf) and heated to 97°C for 5 min. This was followed by 30 cycles of a three-temperature cycling protocol (97°C for 30 s, 55°C for 30 s, and 72°C for 1 min) and 1 cycle at 72°C for 10 min. For PCR products larger than 1 kb, an additional 1 min per kb was added to the extension time.
DNA sequencing.
DNA inserts cloned into pCR2.1-TOPO were PCR amplified with M13 forward and M13 reverse primers (
Table 2), and unincorporated deoxynucleoside triphosphates (dNTPs) and primers were removed using the DyeEx 2.0 spin kit (Qiagen). The PCR products were then sequenced with the M13 forward and M13 reverse primers using the ABI BigDye Terminator v3.1 cycle sequencing kit (Thermo Fisher Scientific) and an Applied Biosystems SeqStudio genetic analyzer (Thermo Fisher Scientific) according to the manufacturer’s instructions. The nucleotide sequences were analyzed with DNASTAR Lasergene 17 software.
TnMod-OKm′ mutagenesis and plasmid conjugations.
Tn
Mod-OKm′ (
39) was delivered to Bp82 via conjugation with
E. coli S17-1 (pTn
Mod-OKm′) by using a membrane filter mating technique. Briefly, S17-1 (pTn
Mod-OKm′) was inoculated into 3 ml of LB broth containing Km and Sm and grown at 37°C for 18 to 20 h with shaking (250 rpm).
B. pseudomallei was also grown under these conditions but without antibiotic selection. One hundred microliters of each saturated culture was added to 3 ml of sterile 10 mM MgSO
4, mixed, and filtered through a 0.45-μm-pore-size nitrocellulose filter using a 25-mm Swinnex filter apparatus (Millipore). Filters were placed on LB plates supplemented with 10 mM MgSO
4 and incubated for 8 h in a 37°C incubator. The filters were washed with 2 ml of sterile phosphate-buffered saline (PBS), and 100-μl aliquots were spread onto LB agar plates containing Km and Pm. Km
r and Pm
r colonies were identified after 48 h of incubation at 37°C. Tn
Mod-OKm′ contains a Km
r gene and a pMB1 conditional origin of replication that does not function in
B. pseudomallei, allowing the rapid cloning of DNA adjacent to the transposon’s site of insertion in
E. coli. The
in vitro cloning of DNA flanking the Tn
Mod-OKm′ insertion sites in
B. pseudomallei SMM1 and SMM2 was performed by digesting total genomic DNA with the restriction endonuclease NotI, self-ligating, and transforming into an
E. coli host (
Table 2). The resulting plasmids were then sequenced with an outward facing primer (TnMod-LT2) that binds to the left end of Tn
Mod-OKm′. The resulting sequence reactions revealed the junction of the transposon and
B. pseudomallei genomic DNA. Plasmids pMo130 and pBHR2 and their derivatives were likewise conjugated to
B. pseudomallei by using
E. coli S17-1 as the donor strain (
Table 2).
Screening for B. pseudomallei Bp82 transposon mutants that do not produce a zone of inhibition on lawns of N. bataviensis S4.
Individual TnMod-OKm′ mutants were picked from 150- by 15-mm polystyrene petri plates containing LB agar and X-Gal using sterile toothpicks. Prior to transfer, the agar medium was inoculated with N. bataviensis S4 by submersing a sterile swab into a saturated LB broth culture and spreading it across the entire surface of the agar in back-and-forth motions. The agar plate was rotated 90° three times, and this process was repeated and the surface of the agar was allowed to dry in a class II microbiological safety cabinet prior to coinoculation with B. pseudomallei Bp82 transposon mutants. The plates were incubated at 37°C for 1 to 2 days and screened for mutants that did not produce zones of inhibition (clearing) around the colonies. Approximately 8,000 transposon mutants were screened by this method.
Construction of B. pseudomallei mutants.
Gene replacement experiments with
B. pseudomallei were performed using the
sacB-based vector pMo130, as previously described (
61–63). Recombinant derivatives of pMo130 (
Table 2) were electroporated into
E. coli S17-1 (12.25 kV/cm) and conjugated with
B. pseudomallei Bp82 for 8 h. Pm was used to counterselect
E. coli S17-1. The optimal conditions for the resolution of the
sacB constructs were found to be LB agar lacking NaCl and containing 10% (wt/vol) sucrose with incubation at 37°C for 2 days.
B. pseudomallei deletion mutants were identified by colony PCR using the primers flanking the deleted regions of the targeted genes (
Table 2). As expected, the PCR products generated from the mutant strains were smaller than those obtained from the wild-type strain.
Bacterial competition assays.
A modified qualitative and quantitative contact-mediated bacterial competition assay (
38) was employed to assess the ability of
B. pseudomallei to compete with the 14 environmental Gram-positive bacteria. Briefly,
B. pseudomallei and environmental competitors were grown in LB broth at 37°C for 18 h, and three independent cultures of each strain were used for each competition assay performed. Two hundred microliters of each of the saturated cultures was pelleted by centrifugation, washed with sterile PBS, and diluted to ∼1 × 10
7 CFU/ml, and 10-μl aliquots of each competitor were spotted onto the surface of LB agar or LB agar containing X-Gal (
Fig. 2A). One hundred microliters of
B. pseudomallei and of the environmental competitor were also combined and mixed, and a 20-μl aliquot of the 1:1 mixture was spotted onto the solid medium (
Fig. 2A) and incubated for 48 h at RT. The remaining competition mixture was serially diluted in PBS, and 100-μl aliquots were spread onto LB agar or LB agar containing X-Gal to determine the input concentration of
B. pseudomallei and environmental species present in the mixture. Following incubation, the bacteria present in each spot were resuspended in 1 ml of PBS using sterile swabs and serially diluted in PBS, and 100-μl aliquots were spread onto LB agar or LB agar containing X-Gal and incubated for 1 to 2 days at 37°C to determine the number of CFU present. The quantity of each competitor present in the competition mixture was assessed by enumerating the number of
B. pseudomallei off-white colonies compared to the number of Gram-positive pigmented or blue colonies. The fold difference between the
B. pseudomallei/environmental isolate ratio when the bacteria were grown alone relative to the
B. pseudomallei/environmental isolate ratio when the bacteria were grown in mixed culture was used to establish the overall competitive index. Three independent pairs of cultures were performed for each
B. pseudomallei-environmental isolate competition assay, and the results were recorded as the mean ± the standard deviation.
Contact-independent liquid competition assays were performed as described above except that B. pseudomallei, the environmental competitor, and the B. pseudomallei plus environmental competitor mixtures were each added to 3 ml of LB broth and grown at RT for 48 h. For liquid competition experiments in which B. pseudomallei and N. bataviensis cocultures were separated by a cell-impermeable filter, Steriflip vacuum-driven sterile filter devices (Millipore Sigma) were utilized. Briefly, B. pseudomallei and N. bataviensis overnight cultures were diluted to an optical density at 600 nm (OD600) of 0.1, and 10-μl aliquots were added to 30 ml LB broth on each side of the Steriflip apparatus as depicted in Fig. S2A in the supplemental material. Parafilm was employed to firmly seal the 50-ml conical tubes to the filter apparatus, and the coculture chamber was incubated at RT for 48 h with mild agitation (120 rpm). The concentration of bacteria in each chamber after growth was determined by spreading 100-μl aliquots of serial dilutions onto LB agar and incubating for 1 to 2 days at 37°C. Three independent pairs of cultures were performed for each B. pseudomallei-N. bataviensis competition assay, and the results were recorded as the mean ± the standard deviation. For solitary growth cultures, Bp82 cultures (or S4 cultures) were grown on both sides of the apparatus, and the means were calculated and used to determine the Bp82/S4 solitary growth ratio.
Extraction and preparation of 4-hydroxy-3-methyl-2-alkenylquinolines from B. pseudomallei cultures.
HMAQ and HMAQ-NO derivatives were isolated from 75-ml stationary-phase cultures of
B. pseudomallei Bp82 and Bp82 Δ
hmqD. Cells were removed from the culture by centrifugation, and the culture supernatant was sterilized by using a 0.2-μm filter (Millipore, Billerica, MA). The sterilized culture supernatants were extracted with equal volumes of acidified ethyl acetate and dried to completion under a constant stream of nitrogen gas. The samples were subjected to a metabolomics sample preparation procedure described by Dhummakupt et al. (
64). Briefly, 100 μl of sample was mixed with an 8:1:1 acetonitrile-methanol-acetone solvent (Optima LC/MS grade; Fisher Scientific) containing isotopically labeled internal standards. Samples were stored at 4°C for 30 min until proteins precipitated and then centrifuged at 10,000 ×
g for 4 min at 4°C. The supernatant was removed, dried down, and resuspended in 100 μl of water with 0.1% formic acid (Optima LC/MS grade) and placed in a liquid chromatography (LC) vial.
Liquid chromatography and mass spectrometry.
Reverse-phase high-performance liquid chromatography was utilized with solvent A being water with 0.1% formic acid (Optima LC/MS grade) and solvent B being acetonitrile (Optima LC/MS grade) with 0.1% formic acid with a 2-μl injection volume. Conditions were 0% B from 0 to 8 min, 5% B at 8 to 12 min, 35% B at 12 to 15 min, 95% B at 15 to 18 min, and 0% B at 18 to 20 min with a linear gradient. A CORTECS T3 column (Waters Corp., Milford, MA; 120 Å, 2.7 μm, 2.1 mm by 150 mm) with a Phenomex (Torrance, CA) SecurityGuard ultrahigh-performance liquid chromatography (UHPLC) phenyl 2.1-mm-inside-diameter (i.d.) guard column was utilized for separations.
A Thermo Fisher Scientific (Waltham, MA) Q Exactive hybrid quadrupole-Orbitrap mass spectrometer was utilized for mass analysis. A heated electrospray ionization (HESI-II; Thermo Fisher Scientific) probe ionization source was utilized in positive mode at 3.5 kV, the capillary temperature was set to 269°C, S-Lens radio frequency (RF) was set to 50 V, sheath gas was set at 53 arbitrary units (AU), auxiliary gas at 14 AU with heater temperature at 300°C, and sweep gas at 3 AU. A top-20 data-dependent acquisition (DDA) method with an inclusion list was employed, utilizing 70,000 R at the MS1 level and 15,000 R at the MS2 level with stepped collision energies of 30, 50, and 70. Inclusive masses for targeted MS2 fragmentation were those precursor masses of the mutant knockout pathway of interest and variants.
Data processing.
Data processing was performed by Thermo Fisher Scientific’s Compound Discoverer 3.1. Searches were performed according to the default Targeted E&L workflow with FISh Scoring built-in workflow. Features were identified and aligned with a max retention time tolerance of 2 min and delta 10-ppm tolerance. Features were then filtered by a signal-to-noise ratio of 1.5. The aligned and filtered features were searched against all the 4-hydroxy-2-alkylquinoline (HAQ) families listed by Vial et al. (
30) with the expected compounds node and all possible ion adducts. Results were then filtered by identifications with MS2 DDA support.
Data availability.
The GenBank accession numbers for the Gram-positive 16S rRNA sequences described in this study are
Priestia megaterium RS1,
MW756952;
Exiguobacterium undae RS4,
MW756953;
Cytobacillus firmus R14,
MW756954;
Bacillus mycoides R15,
MW756955;
Bacillus cereus ST9,
MW756956;
Neobacillus bataviensis S4,
MW756957;
Exiguobacterium acetylicum R10,
MW756958;
Bacillus marisflavi S9,
MW756959;
Paenibacillus sp. S10,
MW756960;
Paenibacillus polymyxa S2,
MW756961;
Bacillus licheniformis S7,
MW756962;
Bacillus velezensis RZ8,
MW756963;
Microbacterium sp. RS16,
MW756964, and
Cellulosimicrobium sp. RS17,
MW756965.