ABSTRACT
Many pathogenic bacteria, including Legionella pneumophila, infect humans from environmental reservoirs. To survive in these reservoirs, bacteria must withstand microbe-on-microbe competition. We previously discovered that L. pneumophila can compete with neighboring bacteria via an antimicrobial metabolite called homogentisic acid (HGA). Curiously, L. pneumophila strains that secrete HGA are not wholly immune to its effects: low-density bacteria are strongly inhibited by HGA, whereas high-density cells are tolerant. How do these bacteria tolerate HGA and avoid self-harm during interbacterial competition? Here, we find that HGA toxicity occurs via the production of toxic hydroperoxides, and multiple factors facilitate high-density tolerance. First, HGA becomes fully toxic only after >1 h of oxidation. While this manifests as a delay in killing within well-mixed liquid cultures, in a biofilm environment, this could provide time for HGA to diffuse away before becoming toxic. Second, HGA generates quantities of hydroperoxides that can be collectively scavenged by high-density, but not low-density, cells. Third, high-density cells produce one or more secreted factors that are transiently protective from HGA. In combination, we propose that the bacteria are able to deploy HGA to generate a pool of reactive oxygen species surrounding their own biofilms while maintaining non-toxic conditions within them. Overall, these findings help to explain how broadly toxic molecules can be used as inter-bacterial weapons. They also provide insights about why some of our current decontamination methods to control L. pneumophila are ineffective, leading to recurrent disease outbreaks.
IMPORTANCE
Before environmental opportunistic pathogens can infect humans, they must first successfully grow and compete with other microbes in nature, often via secreted antimicrobials. We previously discovered that the bacterium Legionella pneumophila, the causative agent of Legionnaires’ disease, can compete with other microbes via a secreted molecule called HGA. Curiously, L. pneumophila strains that produce HGA is not wholly immune to its toxicity, making it a mystery how these bacteria can withstand the “friendly fire” of potentially self-targeting antimicrobials during inter-bacterial battles. Here, we identify several strategies that allow the high-density bacterial populations that secrete HGA to tolerate its effects. Our study clarifies how HGA works. It also points to some explanations of why it is difficult to disinfect L. pneumophila from the built environment and prevent disease outbreaks.
KEYWORDS: Legionella pneumophila, natural antimicrobial products, reactive oxygen species, antimicrobial tolerance, interbacterial antagonism, density-dependent responses, homogentisic acid
INTRODUCTION
As bacteria compete for nutrients and space, many species use antimicrobial compounds to antagonize their neighbors (1). While some of these molecules target only specific strains, those that generate reactive oxygen species (ROS) tend to be broadly active, as ROS can damage DNA, proteins, lipids, and other biological molecules (2). In oxygenated environments, redox-active secreted compounds, such as phenazines, quinones, and related molecules, can generate toxic ROS through redox cycling (3). Yet, despite their toxicity, many bacteria secrete these molecules in high quantities, suggesting that redox-active compounds can confer a number of benefits on the bacteria that produce them, such as improved cellular respiration and improved scavenging of limiting nutrients from the environment (4 – 6).
Legionella pneumophila is an aquatic opportunistic human pathogen that can cause large disease outbreaks if it colonizes building plumbing systems (7). We previously described the secreted quinone homogentisic acid (HGA) as an antimicrobial metabolite used by Legionella pneumophila (8). In stationary phase when cells are a high density, this bacterium secretes abundant (50–500 µM) HGA, which can spread across an agar plate to kill neighboring Legionella species. We demonstrated that HGA’s oxidation state was relevant for its activity, that reducing agents made HGA inhibition less potent, and that HGA was non-toxic in anaerobic conditions. We, therefore, proposed that reactive intermediates were inhibitory, although HGA’s mechanism of action was unknown. In addition, we previously observed that L. pneumophila could itself be antagonized by HGA under certain conditions. Unexpectedly, Legionella growth phase had no impact on HGA susceptibility or tolerance. Instead, susceptibility depended on cell density; dense cells (~2E9 CFU/mL) were insensitive to 24 h of HGA treatment, but the same strain was extremely sensitive when diluted (~2E7 CFU/mL) (8). Thus, in a spatially structured environment such as a biofilm, high-density cells that produce HGA are not susceptible to this molecule, but any neighboring, low-density cells outside the biofilm are at risk. HGA susceptibility was particularly strong when cells were exposed to HGA in phosphate-buffered saline (PBS), which more closely approximates the low-nutrient, aquatic conditions where Legionella spp. are found than rich media conditions. In summary, we found that L. pnuemophila strains that antagonize neighbors with secreted HGA can themselves be extremely sensitive to this same molecule. How, then, is L. pneumophila able to use HGA to kill other bacteria while avoiding self-harm?
Here, we investigate HGA’s mechanism of action and its density-dependent susceptibility. While HGA itself is non-toxic, our findings suggest that it spontaneously generates toxic hydroperoxides over time in aerobic conditions. While dilute L. pneumophila cells are highly sensitive, more dense bacteria can tolerate >1,000-fold higher HGA concentrations. Moreover, the threshold separating high-density tolerant cells and low-density susceptible cells is incredibly sharp, separated by only a 2×–3× difference in cell density. How is this switch-like difference in susceptibility achieved? First, we find that high-density cells secrete one or more factors (likely small molecule antioxidants) that reduce the amounts of toxic ROS generated by HGA; the secreted factor(s) can transiently protect low-density cells from HGA. Second, HGA generates concentrations of H2O2 that high-density cells can cooperatively detoxify but low-density cells cannot. Third, because HGA takes >1 h to begin to produce toxic levels of ROS in aerobic environments, we propose that this time delay acts as a metaphorical long fuse, allowing HGA to diffuse away from high-density cells in a biofilm before generating toxic ROS. Together, these dynamics permit high-density L. pneumophila to secrete abundant HGA without suffering any loss in viability.
RESULTS
HGA induces rapid, density-dependent cell death
To precisely define when and how HGA inhibition occurs, we first investigated which cell densities were susceptible to HGA. When we exposed cells across a range of cell densities to 125-µM HGA for 24 h, we found that the transition between complete HGA susceptibility and full tolerance was incredibly sharp, spanning only a 2.5- to 3.0-fold difference in starting cell density (1.35E8 vs 3.45E8 CFU/mL, Fig. 1A). Above the density threshold, Legionella cells were essentially unaffected by HGA, as the number of CFUs at t = 0 matched the number we recovered at t = 24 h (y = x line, Fig. 1A). Below the threshold, we did not recover any viable CFUs. We interpret this switch-like behavior to indicate HGA sensitivity is a biologically regulated process, rather than a generic outcome resulting from more cells being present in high-density cultures.
We also found that HGA killed low-density (<7E7 CFU/mL) cells quickly. CFUs began to decline after 1 h, and full inhibition occurred as early as 4 h (Fig. 1B). The kinetics of inhibition varied, depending on culture volume and shaking speed (Fig. S1), likely due to the efficiency of oxygenation. To determine if HGA inhibition is bactericidal or if it is driving cells into a viable but non-culturable state, we exposed GFP-expressing Legionella to HGA and stained dead cells with propidium iodide (PI) (Fig. 1C and D). We found up to 45% of low-density cells exposed to HGA became PI+. Additionally, the proportion of PI+ cells increased at the same time that these cells experienced a drop in CFUs (Fig. 1E and F), indicating that the low-density Legionella cells are dying after exposure to HGA. Notably, our % PI+ measurements in this assay are likely an underestimate of total dead cells, as we expect to miss cells that have already lysed. Overall, we conclude that HGA is bactericidal and kills low-density cells rapidly. High-density cells remain unaffected, and there is a tight density threshold separating the two outcomes of dramatic cell death vs complete HGA tolerance.
Density-dependent susceptibility to HGA and H2O2
Many antibiotics are known to produce an “inoculum effect,” wherein higher antibiotic concentrations are required to kill dense bacteria as compared to dilute bacteria (9, 10). To determine if HGA’s density dependence behaved similarly to inoculum effects, we measured the minimum bactericidal concentration (MBC) for high- and low-density Legionella exposed to a variety of antimicrobial compounds in minimal PBS media. Strikingly, over 1,000-fold more HGA was required to fully kill high-density cells (20-mM HGA) than low-density cells (20-µM HGA, Fig. 2A). We observed a similar density dependence in Legionella’s sensitivity to H2O2 (Fig. 2B, 30 µM vs 30 mM to kill >99.9% of low- vs high-density cells).
In contrast to this density-linked sensitivity, we observed that L. pneumophila treated with bleach, multiple antibiotics, and the toxic lipid 4-HNE, exhibited at most a 10-fold difference in the MBCs between high- and low-density L. pneumophila (Fig. 2C through F; Fig. S2A). As an additional oxidative stress, we tested Legionella’s susceptibility to paraquat, a chemical that generates superoxide. Although previous research found L. pneumophila was sensitive to 0.25- to 0.5-mM paraquat in rich media (11, 12), in the minimal media used here, we found L. pneumophila tolerated up to 21-mM paraquat with minimal cell death at both high and low cell densities (Fig. S2). We note that the MBCs measured here were higher than previously reported MBCs and minimum inhibitory concentrations (MICs) for Legionella pneumophila (13 – 15). This discrepancy likely results from the fact that antimicrobials are typically added during bacterial log phase growth in chemically complex, rich media, while our treatments are added to non-replicative cultures in minimal media. For HGA, we previously showed that this compound is more toxic in minimal vs rich media, and this difference is due to high concentrations of cysteine in rich media, which acts as an antioxidant to protect from HGA (8). Overall, L. pneumophila’s density-dependent susceptibility to both HGA and H2O2 is several orders of magnitude stronger than the inoculum effect we observed for other antimicrobial compounds (Fig. 2A and B vs Fig. 2C through F ). When we tested several other species of bacteria (Legionella micdadei, Pseudomonas fluorescens, Klebsiella aerogenes, and Bacillus subtilis) in the same assay, L. micdadei and B. subtilis were both susceptible to HGA. However, only L. pneumophila exhibited a strong density dependence to both HGA and H2O2 at the concentrations tested (Fig. S2).
HGA tolerance is independent of the Lqs quorum sensing and HGA synthesis pathways
At high density, bacteria often experience nutrient limitation, slowed growth, and other stresses that could alter bacteria sensitivity to antimicrobials. However, we previously found that L. pneumophila’s high-density tolerance of HGA was neither affected by log vs stationary growth phase nor impacted by the stringent response pathway, which coordinates many stress responses in high-density, stationary phase bacteria (8, 16). Instead, HGA susceptibility was linked specifically to cell density. Therefore, we next tested whether Legionella regulates its density-dependent responses to HGA via candidate quorum sensing pathways. During quorum sensing, bacteria sense their own cell density through the secretion of autoinducer molecules, which accumulate to high concentrations when cells are dense and activate downstream signaling pathways (17, 18). Within the sole characterized Legionella quorum sensing (Lqs) pathway in L. pneumophila, the protein LqsA synthesizes a secreted autoinducer, which is sensed by transmembrane kinases, ultimately altering the activity of the response regulator LqsR (19). We previously found that wild-type cells and a ∆lqsR mutant had similar HGA susceptibility (8), suggesting that this protein is not involved in regulating HGA susceptibility. However, a second response regulator, LvbR, was recently discovered in the Lqs pathway, with some downstream target genes that are not regulated by LqsR (20). Signaling by LvbR, but not LqsR, was also found to be important for Legionella development into antibiotic tolerant persister cells (21). To test if LvbR or another part of the Lqs pathway regulates HGA tolerance, we constructed deletion mutants of lvbR and lqsA. We found that all Lqs mutants had similar HGA susceptibility to wild type (Fig. S3), supporting and strengthening our prior conclusions that density-dependent HGA susceptibility is regulated by a mechanism independent of the Lqs pathway.
One secreted molecule that accumulates specifically in high-density Legionella cultures is HGA itself. We next considered the possibility that HGA could function as an autoinducer, as secreted quinones have been shown to act as signaling molecules in other bacterial species (22). In this scenario, high-density cells could begin to secrete HGA, sense the initial, relatively low concentrations of extracellular HGA around them, and activate their protective downstream pathways before releasing subsequent toxic levels of HGA. If this hypothesis is correct, we predicted that Legionella mutants that are unable to secrete HGA would be susceptible to exogenous HGA, even at high cell density. Contrary to this expectation, we observed that a mutant that secretes no HGA (Tn:hisC2 [8]) showed similar patterns of susceptibility to exogenous HGA as both wild-type cells and ∆hmgA mutants that secrete excess HGA due to an inability to recycle HGA back into central metabolism (Fig. S3). We, therefore, concluded that Legionella’s density-dependent susceptibility is unrelated to both HGA biosynthesis and Lqs pathway signaling.
L. pneumophila RNA-seq reflects low-density cell oxidative stress from HGA
To identify genes that could underlie Legionella’s density-dependent susceptibility to HGA, we compared the transcriptomes of high- and low-density cells, both with and without HGA exposure (i.e., high density [HD]+, HD−, low density [LD]+, and LD− conditions). Because LD+ cells begin to experience substantial cell death after 1–2 h of HGA exposure (Fig. 1B), we analyzed RNA from each condition at the t = 1-h time point. By principal components analysis, the transcriptional profiles from HD samples were clearly separated from LD samples along PC1, while LD− and LD+ samples differed along PC2 (Fig. S4). The LD+ samples also had the most within-condition variation. Because LD+ cells experience a steep decline in CFUs between t = 0 h and t = 2 h, we expect that the differences among replicates reflect slight experimental variations in timing or degree of ROS generation from HGA. In agreement with the PCA, correlation matrices of the normalized read counts within conditions showed low variation between replicates within each condition except for the LD+ condition (Fig. S4).
From the RNA-seq data, we first asked whether high-density cells produced an inducible, protective response to HGA by comparing HD− and HD+ samples. Contrary to this hypothesis, we found that zero genes were differentially expressed when high-density cells were exposed to 125 µM HGA (Table S1). Thus, in addition to high-density cells’ HGA tolerance (i.e., they have no decline in CFUs, Fig. 1B), these cells do not appear to activate any stress or signaling responses to HGA at the transcriptional level.
In contrast, low-density cells robustly upregulated eight genes when exposed to HGA, most related to oxidative stress (Fig. 3A). These included sodC (lpg2348), a copper-zinc superoxide dismutase, and ahpC2D (lpg2349 and 2350), which encodes an alkyl hydroperoxidase and reductase that together scavenge hydroperoxides such as H2O2 (12). Also upregulated was an operon containing pirin and acpD orthologs (lpg2286 and 2287). While both genes are uncharacterized in Legionella, pirins are found across bacteria and eukaryotes where they play diverse roles, including acting as redox-sensing transcriptional regulators (23) or directly degrading aromatic antimicrobial compounds (24). AcpD is an azoreductase, acting on aromatic nitrogen-containing compounds (25). The final three upregulated genes were related to iron acquisition. The feoAB operon (lpg2658/2657) mediates the transport and uptake of Fe2+, while frgA (lpg2800) synthesizes a siderophore for uptake of Fe3+ (26). Oxidative stress has previously been shown to induce an iron starvation response via oxidation of Fe2+ and subsequent release of the Fur repressor (27), consistent with the gene expression observed here. Notably, the eight genes upregulated in LD+ conditions represent only a subset of Legionella’s oxidative stress response genes. In none of the RNA-seq conditions did we observe differential expression of Legionella’s other superoxide dismutase sodB, nor the other alkyl hydroperoxidase ahpC1, nor any previously characterized catalase or oxyR regulator genes (Fig. 3CFig. 3; Table S1). Similarly, none of the lqs pathway genes nor the HGA biosynthesis genes were differentially expressed (Fig. S4).
Because high-density Legionella spp. show no change in viability or gene expression when exposed to HGA, we hypothesized that the mechanisms of high-density tolerance could be due to differences between high- and low-density cells prior to HGA exposure. Between HD− and LD− conditions, there were 78 genes significantly upregulated in high-density cells and 5 genes upregulated in low-density cells. Legionella exhibits a biphasic lifestyle and is known to upregulate flagellar biosynthesis and virulence gene expression in stationary phase, downstream of the stringent response pathway (28, 29). The predominant transcriptional profile of genes upregulated in HD− cells was consistent with this flagellar regulon activation. Twenty-one of the 78 upregulated HD− genes were flagellar (in flagellar gene classes II, III, and IV) or previously characterized as part of the fliA flagellar regulon (28). If we relax our significance threshold to P < 0.05, 60% of all flagellar-related genes in the genome (34 of 57) were upregulated in HD− as compared to LD− conditions (Table S1). Relatedly, nine characterized virulence genes (i.e., toxins or effectors) were upregulated in HD− conditions. While this was the major transcriptional signature, we previously showed that HGA susceptibility was unaffected by mutations to the stringent response pathway (8), which are expected to perturb activation of the flagellar regulon (29). Therefore, we predict that HGA tolerance is more likely to be conferred by one or more of the remaining, non-flagellar genes upregulated in high-density cells. Of these, there was no obvious pattern, partly due to the fact 47% of the remaining genes were hypothetical and uncharacterized, mostly small proteins that are predicted to be unstructured by AlphaFold. There were also two heat shock proteins belonging to the HSP20 family (lpg2191 and 2493) as well as several predicted transcriptional regulators that could mediate the expression of genes at high density (e.g., lpg0476, 0586, 2008, 2181, and 2145).
Within low-density cells, the two most upregulated were lpg0600, an Rrf2 family transcription factor, and lpg0601, an ABC transporter. Notably, these genes lie closely upstream of lpg0607, a gene that was repeatedly disrupted in a screen for HGA-tolerant mutants in our previous study (8), although lpg0607 itself was only weakly upregulated in low-density cells (1.8-fold higher, P = 0.043). It is possible that regulation of this operon modulates HGA sensitivity in low-density bacteria. Overall, the RNA-seq results revealed many genes differentially regulated between high- and low-density cells, as well as specific oxidative stress responses in HGA-exposed, low-density Legionella.
HGA gradually produces hydroperoxides, which can be quenched by high-density cells
Because H2O2 and HGA displayed a strikingly similar density dependence in L. pneumophila (Fig. 2A and B) and because ahpC2D, genes used to detoxify hydroperoxides, were highly upregulated in LD+ cells (Fig. 3A), we next hypothesized that HGA kills low-density L. pneumophila via generation of H2O2 or a related hydroperoxide. To test this hypothesis, we used the reagent Amplex Red, which generates the fluorescent compound resorufin in the presence of hydroperoxides (30). Previously, we found that HGA was a non-toxic in anaerobic conditions (8), suggesting that toxic compounds are produced upon oxidation. Consistent with this finding and with the timing of HGA killing of low-density cells (Fig. 1B), we saw that synthetic HGA incubated in shaken test tubes gradually produced an abundant fluorescent signal. When compared to a standard curve of H2O2, 125 µM HGA generated an equivalent signal of 130 µM H2O2, reaching hydroperoxide levels that are toxic to low-density cells after 1 h (Fig. 2 and Fig. 4). As we found that high-density cells could tolerate H2O2 but low-density cells died between 30 and 3,000 µM H2O2 (Fig. 2B), the fact that HGA generates hydroperoxides within this critical range may contribute to L. pneumophila’s density-dependent susceptibility to HGA.
However, it is also possible that HGA generates different types or concentrations of reactive oxygen species in the presence of bacteria. To test this hypothesis, we incubated HGA alone or in combination with L. pneumophila at high or low density for 4 h and measured hydroperoxide concentrations with Amplex Red. We saw that HGA alone generated the equivalent of 92-µM H2O2 and only a slightly lower amount (52 µM) in the presence of low-density cells. However, when HGA was incubated with high-density L. pneumophila, the Amplex Red signal was dramatically reduced (0.8 µM, Fig. 4). This behavior was not unique to HGA, as high-density cells also depleted H2O2 during co-incubation (Fig. 4B).
H2O2 is cell permeable, and it has previously been shown that the combined actions of bacteria scavenging intracellular H2O2 can collectively reduce local H2O2 concentrations (31, 32). Because cells at higher density should be better at scavenging H2O2, we next investigated whether this phenomenon was sufficient to explain the density-dependent susceptibility to HGA. If so, we predicted that there would be a switch-like transition between 1E8 and 3E8 CFU/mL (the density threshold defined in Fig. 1A), where cultures above this threshold would scavenge H2O2 much more efficiently than bacteria below the threshold (see “regulated switch”; Fig. 4). Alternatively, if high-density H2O2 scavenging is simply related to the activity of additional cells, we predicted that cells at higher density would scavenge H2O2 without any apparent density threshold (see “bulk cells”; Fig. 4). When we briefly incubated cells at different densities with 50 µM H2O2, we observed that higher cell densities reduced the concentration of H2O2 more readily, but this occurred without any apparent density threshold (Fig. 4C). Therefore, while high-density cells exhibit enhanced H2O2 scavenging as expected, this phenomenon is not sufficient to explain HGA’s density-dependent susceptibility.
High-density cells secrete a transiently protective molecule
We next asked whether the high-density cells’ quenching activity could be enhanced by a secreted factor. We generated secreted supernatants from high-density cells (HDsup) by incubating dense L. pneumophila in PBS for 1 h and then centrifuging and filter sterilizing the sample through a 0.2-µm filter to remove bacteria. To generate HGA-derived ROS, we oxidized HGA alone for 4 h. When we then incubated the high-density supernatants with HGA, we found that the HDsup could largely quench the Amplex Red signal (Fig. 4D). Unlike the activity from live cells, HDsup incubated with H2O2 did not alter the Amplex Red measurement. This suggests that high-density cells rapidly secrete one or more factors that are protective from HGA. Because HDsup does not substantially alter H2O2 readings, we infer that the decline in fluorescence is due to HGA-derived ROS quenching and that HDsup does not interfere with the Amplex Red assay. Moreover, because HDsup does not detoxify H2O2 but does alter ROS generated from HGA, we conclude that HGA produces one or more toxic ROS that react with the Amplex Red reagent but are distinct from H2O2.
If high-density cells resist HGA via a secreted factor, we predicted that HDsup would protect low-density cells from HGA. Indeed, we found that low-density cells incubated with HDsup experienced delayed cell death from HGA, extending the time to death by at least 4 h (Fig. 4D). This effect was transient, and the cells still died by t = 8 h. Nevertheless, these experiments reveal that HGA generates quantities of ROS that are toxic to low-density cells, but that high-density cells can transiently quench or scavenge extracellular HGA-derived ROS via a secreted, protective factor.
DISCUSSION
We previously discovered that L. pneumophila can use HGA as a secreted, antimicrobial metabolite to antagonize neighboring Legionella bacteria (8). Here, we have shown that HGA is bactericidal, clarified its mechanism of action, and uncovered mechanisms that mediate L. pneumophila’s unusual, density-dependent susceptibility to this molecule. We find that low-density L. pneumophila cells are over 1,000× more sensitive to HGA than high-density bacteria (Fig. 2). This sensitivity is mirrored in L. pneumophila’s responses to H2O2 but is distinct from other antimicrobials or oxidative stressors (Fig. 2; Fig. S2). Based on these observations, as well as the upregulation of alkyl hydroperoxidases in LD+ samples (Fig. 3A), and the measurement of HGA-derived ROS using Amplex Red (Fig. 4C), we propose that HGA generates toxic hydroperoxides (distinct from H2O2), which kill low-density L. pneumophila. Supporting this conclusion, we found that L. micdadei and B. subtilis are sensitive to HGA but relatively insensitive to H2O2 (Fig. S2). Further ruling out H2O2 as an intermediate, L. micdadei tatlock is also a naturally catalase-positive strain (33), yet it remains susceptible to HGA and we found previously that catalase was not protective against HGA (8). While Amplex Red is specific for hydrogen peroxide over superoxide, other compounds including peroxynitrite (34) and some organic hydroperoxides (35) have previously been found to react in the Amplex Red/horseradish peroxidase assay, which could mediate HGA toxicity.
We also found that HGA susceptibility in L. pneumophila follows an extremely sharp density threshold; the only difference between bacteria that are fully impervious to HGA and those that are completely susceptible is a two- to threefold difference in starting cell density (Fig. 1). We interpret this sharp transition to be the result of active, density-dependent regulation. So, what explains this switch-like difference in HGA susceptibility in L. pneumophila? Our findings show that this phenomenon is distinct from the “inoculum effect” typically seen for antibiotics (Fig. 2), the HGA biosynthesis pathway, and the sole, known quorum sensing pathway of Legionella (Lqs) (Fig. S3).
Instead, our results suggest that at least three phenomena contribute to high-density HGA tolerance. First, and best characterized previously, the combined actions of bacteria scavenging toxic hydroperoxides within their own cells can collectively reduce environmental peroxide concentrations, and this process occurs more quickly when more bacterial cells are present (31, 32). We find that HGA produces hydroperoxide concentrations that can be quickly, collectively scavenged by high-density but not low-density L. pneumophila populations (Fig. 4A through C). However, this collective scavenging alone is not sufficient to explain HGA’s density-dependent susceptibility.
Second, high-density L. pneumophila cells secrete unknown factors that partially quench HGA-derived ROS (Fig. 4D) and provide transient protection from HGA (Fig. 4E). This transient effect was not detectable in our prior study (8) because those experiments only tested samples after 24 h of HGA treatment. We hypothesize that the transient protection arises because the protective factor is degraded, used up, or oxidized as it interacts with ROS. However, if high-density cells continue to secrete fresh protective factors, these molecules could provide longer-lasting protection.
Third, we propose that the time delay between HGA secretion and the production of toxic ROS could provide an additional level of protection in spatially structured environments. We initially discovered that HGA could kill bacteria in an agar plate assay wherein HGA produced by a L. pneumophila biofilm spread across the agar and killed neighboring bacteria (8). Because we found HGA is non-toxic when anaerobic (8), the HGA would likely remain non-toxic at the center of the producing biofilm, only beginning to oxidize and produce ROS once it reached the biofilm periphery. Even in highly oxygenated environments, we found that it takes >1 h for HGA to generate toxic levels of hydroperoxides (Fig. 4A), during which time HGA would continue to diffuse away from the high-density, HGA-producing cells. This delay in HGA toxicity, combined with local ROS scavenging and quenching near high-density cells, could create a low ROS zone near the site of secretion and abundant ROS at more of a distance. In this “toxic moat” model, ROS would surround, but not directly impact, high-density HGA-producing cells (Fig. 4F).
What is the protective factor that is secreted from high-density cells? Typically, bacteria counteract high concentrations of hydroperoxides with catalase enzymes and lower concentrations with peroxidases (36). We observed that low-density cells upregulated ahpC2D peroxidases upon HGA exposure (Fig. 3A). However, as neither peroxidases, catalases, nor any other typical ROS detoxifying protein was differentially regulated in HD− vs LD− cells (Fig. 3C), we expect these enzymes are unlikely to be responsible for the protective activity in high-density supernatants. Other secreted factors such as antioxidants could be responsible instead. Indeed, as we previously saw that reducing agents such as cysteine, glutathione, and dithiothreitol (DTT) were protective from HGA (8), similar molecules could provide the transient protective activity we observe in high-density supernatants.
Finally, these findings have potential relevance for public health. Because L. pneumophila within the built environment can cause serious disease outbreaks, methods of disinfection are of primary interest (37, 38). Many of the most common methods used, such as chlorine, chloramine, hydrogen peroxide, and ozone, act through the induction of oxidative damage. Our results suggest that L. pneumophila susceptibility to certain oxidative stressors strongly depends on cell density, particularly in low-nutrient, aquatic environments. Future decontamination approaches should take into account the fact that high-density bacteria (e.g., which may be found in biofilms) may be many orders of magnitude less susceptible to oxidizing agents than the low-density bacteria typically tested in the lab. For example, some decontamination efforts have used hydrogen peroxide well below the 30 mM concentration we find is necessary to fully kill high-density cell populations (38). High-density L. pneumophila that are insensitive to disinfection methods could form a persistent subpopulation that would be poised to recolonize water systems and contribute to the recurrent disease outbreaks caused by this pathogen (39).
MATERIALS AND METHODS
Strains and mutant construction
As in Levin et al., our wild-type Legionella pneumophila (Lp) strain was KS79, and mutants were constructed in this genetic background by allelic exchange using pLAW344. Briefly, we cloned these regions into pLAW344 via Gibson assembly, then transformed into Lp, selected for plasmid integration on buffered charcoal yeast extract (BCYE)-chloramphenicol plates, and counter-selected to create the knock out on BCYE-sucrose plates. To create the lvbR knockout strain, the 5′ genomic region was cloned using primers TL180_LvbR_P1_oH1 (acggtatcgataagcttga gcgtgctgattggtcc) and TL181_LvbR_P2_oH1 (ggtttatgaggctga ttgttttttcattc), while the 3′ region was cloned using TL182_LvbR_P3_oH2 (gaatgaaaaaacaa tcagcctcataaacc) and TL183_LvbR_P4_oH2 (cgctctagaactagtggatc cgcagtgccagtcatgac). We used an identical protocol to create the lqsA mutant, cloning the 5′ region with primers TL186_LqsA_P1_oH1 (acggtatcgataagcttga aatcccctgctccccaaaatag) and TL187_LqsA_P2_oH1 (cgccaataattagaagtcgtg ccataactcagattcttttcc) and cloning the 3′ region with primers TL188_LqsA_P3_oH2 (ggaaaagaatctgagttatgg cacgacttctaattattggcg) and TL189_LqsA_P4_oH2 (cgctctagaactagtggatc atgcaacatttctcaatacc). The GFP-positive Lp in the PI microscopy assay were generated by transforming KS79 with the pON-GFP constitutive expression plasmid (40).
The other bacterial strains and species used were L. micdadei tatlock (41, 42), Pseudomonas fluorescens SBW25 (43), Klebsiella aerogenes DBS0305938 (Dicty Stock Center ID), and Bacillus subtilis IAI (WT strain 168 trpC2) (44). L. micdadei was cultured on BCYE plates, and liquid cultures were grown in AYE, the same culture conditions used for L. pneumophila. P. fluorescens and B. subtilis were cultured at 28°C and 37°C, respectively, on Luria broth (LB) plates and liquid cultures were grown in LB. K. aerogenes was cultured at 37°C on SM/5 plates, and liquid cultures were grown in SM media(45).
HGA and other antimicrobial susceptibility assays
HGA susceptibility assays were performed in PBS as previously described. Briefly, our core assay was performed with washed, early stationary phase bacteria resuspended in 3 mL PBS at 3E9-1E10 CFU/mL for high-density conditions and 1E7-7E7 CFU/mL for low density conditions, ±125 µM HGA. Cells were plated onto BCYE after 0–24 h of incubation, and colonies on plates were counted after 2–3 days of 37°C incubation for CFU viability.
Density-dependent susceptibility to various ROS stresses and antibiotic drugs was determined using a standard MBC99 protocol (46). High- and low-density cells were mixed with drugs in 200 μL of 1× PBS and incubated at 37°C in a shaker. Each condition was plated immediately for CFUs on BCYE and plated again after 24 h at 37°C incubation. The MBC99 or minimum amount of drug required to kill ≥99% of the bacteria in the untreated controls was determined using CFU/mL counts from each drug condition. The antibiotics tested were kanamycin (4–4096 µg/mL, Thermo Fisher #BP906-5), chloramphenicol (1–1024 µg/mL, Thermo Fisher BP904-100), and tetracycline (9.76–2,500 µg/mL; Sigma #87128–25G). The ROS producers included H2O2 (0.03–300,000 µM; Fisher Scientific #H325), 4HNE (0.1–1,000 µM; Cayman Chemical #321001), and paraquat (5.2–21 mM, Sigma #856177). Most compounds were tested in 2-fold dilutions across the concentration range, while HGA and H2O2 were diluted 10-fold. All compounds were tested in shaken 96-well plates except for H2O2. To avoid volatile H2O2 from cross-reacting between conditions, 1-mL cultures were exposed to this compound in separate glass test tubes and culture in a roller drum.
PI staining and quantification
During the HGA susceptibility assay, cell viability was determined by plating for CFUs and imaging propidium iodide-stained bacterial cells at each timepoint. To define cell boundaries, we used a KS79 Lp strain carrying the pON-GFP plasmid to constitutively express GFP (see “Strains and mutant construction” above). Cells at each timepoint were incubated with 2-µg/mL propidium iodide (Thermo fisher, #P1304MP) for 5 min in the dark just before imaging to stain permeable bacterial cells. To image the cells, stained cell samples were spotted onto GeneFrame agar pads (Fisher Scientific #AB-0576) and visualized on a Nikon TE2000 inverted scope using a ×60 oil immersion lens in brightfield, red (560 nm), and green (488 nm) channels. For each condition and time point, at least three fields of view were quantified, or a minimum of 60 cells each. The data presented here come from one of two independent experimental replicates.
Images were single blinded and manually counted for quantification. To determine cell count of green and red cells, the collected image was split into separate color channels using Fiji (47). Cells (defined as 0.1–10.0 μm2 round particles) were identified using the GFP signal. Cells were defined as PI+ if they appeared in both red and green channels or if they were visible only in the red channel.
RNA-seq sample preparation and analysis
The samples prepared for RNA-seq were high- and low-density KS79 cells, with and without HGA. RNA was extracted after 1-h HGA exposure using the RNeasy Mini Kit (Qiagen #74104) as directed, with the addition of a bacterial lysis step using 50 μL 10 mM Tris-Cl, 1 mM EDTA, 1-mg/mL lysozyme prior to the addition of RLT buffer. RNA samples were treated with TURBO DNase (Fisher scientific #AM1907) to remove contaminating DNA. RNA quality was assessed using the Agilent Tapestation for concentration >50 ng/μL and RIN >6 prior to sequencing. Sequencing libraries were prepared using Illumina stranded RNA library preparation with RiboZero Plus rRNA depletion (Illumina #20040529).
Each library was sequenced with 50-bp paired-end reads, to a depth of ~12 M reads per sample. Raw sequencing reads were trimmed and filtered using trimmomatic (48). After trimming for quality, any reads less than 40 bp and average quality less than 30 were dropped. Trimmed filtered reads were mapped to the reference Lp genome (Genbank accession GCA_000008485.1) using kallisto (49). The mapped reads were analyzed for differential expression using the DESeq2 R package and a P value cutoff of 0.05 (50). DESeq2 normalized read counts across samples and performed the default B-H false discovery rate correction (51) on P values to produce the adjusted P values. We analyzed differential expression according to sample density (high vs low) and HGA (present or absent). Differentially expressed genes were defined as genes with >2-fold change in expression and an adjusted P value <0.05. To validate that experimental conditions correlated well within replicate, normalized count data were plotted on a scatter matrix using the pairs R function. To assess variability in our data, we used the vst and plotPCA functions of DESeq2. The differential expression of candidate differentially expressed genes (DEGs) and pathways of interest were displayed in heatmaps using ggplot2 v.3.3.3 (52). Legionella genes involved in iron acquisition and HGA production were defined based on Cianciotto (26). Genes involved in ROS response were based on references 12 and 53 – 55. Genes involved in the Legionella quorum sensing pathway were based on references 20 and 56, and those in the flagellar regulon were based on Albert-Weissenberger et al. (28).
Preparation of low- and high-density Lp for Amplex Red assay
For the experiments in Fig. 4B and C, we used a hisC2:Tn Lp strain from reference 8 that does not secrete HGA to ensure that only exogenous HGA was present. For Fig. 4B, high- and low-density Lp bacteria were washed in PBS and mixed with 125-µM HGA, 50 µM H2O2 solution, or PBS alone as a control. Each condition was incubated for 4 h at 37°C in a roller drum. After 4 h, each condition was sampled for Amplex Red assays (see “ROS measurements via Amplex Red assay” below). In Fig. 4C, Lp bacteria were resuspended in PBS to a density of ~5e9 CFU/mL and then were diluted in serial, twofold dilutions down to a density of 3.9e7 CFU/mL. Cultures at each density were then treated with H2O2 at a final concentration of 50 µM for 5 min. Finally, experimental tubes were briefly vortexed and sampled for Amplex Red readings. Samples were read in parallel to an H2O2 standard curve to estimate the quantity of hydroperoxides present in experimental samples.
Preparation and activity of L. pneumophila supernatants
Supernatants from high-density cells (HDsup) were prepared by washing stationary phase L. pneumophila in PBS and incubating 1.5 mL of 4–9E9 CFU/mL cells in a rolling-drum incubator at 37°C for 1 h. Supernatants were harvested by centrifugation followed by filter sterilization with a 0.22-µm filter. To test if HDsup could quench HGA-derived ROS or H2O2, we first incubated 125 µM of HGA or 50 µM of H2O2 in PBS at 37°C for 4 h in a rolling drum incubator to fully generate ROS. We then mixed 150 μL of the preoxidized HGA or H2O2 with 2.85 mL of HDsup or PBS. The 50 µM H2O2 samples were compared with 50 µM final in HDsup (i.e., 150 μL of 1 mM H2O2 + 2.85-mL HDsup). All conditions were briefly vortexed and then sampled for Amplex Red readings after 5-min co-incubation.
To test if supernatants impacted bacterial susceptibility to HGA, 1.5 mL of L. pneumophila cells (at high or low density) were added to 1.35 mL HDsup and 150 μL of HGA (final HGA concentration 125 µM).
ROS measurements via Amplex Red assay
To quantify the hydroperoxides present in conditions treated with HGA, H2O2, or L. pneumophila bacteria, we used the reagent Amplex Red (Thermo Fisher #A12222), which generates a fluorescent compound in the presence of hydroperoxides. Amplex Red solution consisted of 50 μM of Amplex Red and 0.1 U of horseradish peroxidase (Sigma #77332), which was pre-incubated for 10 min at 37°C. Then, 100 μL of Amplex reaction solution was added to 20 μL of experimental culture in an opaque 96-well plate. Fluorescence was measured after 5 min with a Agilent Biotek Cytation 5 plate reader at 590 nm using an excitation wavelength of 530 nm. Fluorescence values were converted to H2O2 concentrations using a standard curve of known H2O2 concentrations in parallel.
ACKNOWLEDGMENTS
We thank Ed Culbertson, Jim Imlay, and Jason Yang for useful discussions and suggestions.
This work was supported by funding from the Charles E. Kaufman foundation (#KA2021-121928), from the Damon Runyon Dale E. Frey Award for Breakthrough Scientists, and from the National Institutes of Health (#R00AI139344).
Contributor Information
Tera C. Levin, Email: teralevin@pitt.edu.
Kalai Mathee, Florida International University, Miami, Florida, USA .
Ajai A. Dandekar, University of Washington, Seattle, Washington, USA
DATA AVAILABILITY
Data have been deposited as follows: RNA-seq read archive (BioProject ID), PRJNA943215; RNA-seq read processing and analysis scripts, https://github.com/mliannholland/hga_rnaseq
SUPPLEMENTAL MATERIAL
The following material is available online at https://doi.org/10.1128/mbio.01207-23.
ASM does not own the copyrights to Supplemental Material that may be linked to, or accessed through, an article. The authors have granted ASM a non-exclusive, world-wide license to publish the Supplemental Material files. Please contact the corresponding author directly for reuse.
REFERENCES
- 1. Ghoul M, Mitri S. 2016. The ecology and evolution of microbial competition. Trends Microbiol 24:833–845. doi: 10.1016/j.tim.2016.06.011 [DOI] [PubMed] [Google Scholar]
- 2. Vatansever F, de Melo WCMA, Avci P, Vecchio D, Sadasivam M, Gupta A, Chandran R, Karimi M, Parizotto NA, Yin R, Tegos GP, Hamblin MR. 2013. Antimicrobial strategies centered around reactive oxygen species--bactericidal antibiotics, photodynamic therapy, and beyond. FEMS Microbiol Rev 37:955–989. doi: 10.1111/1574-6976.12026 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 3. O’Brien PJ. 1991. Molecular mechanisms of quinone cytotoxicity. Chem Biol Interact 80:1–41. doi: 10.1016/0009-2797(91)90029-7 [DOI] [PubMed] [Google Scholar]
- 4. Price-Whelan A, Dietrich LEP, Newman DK. 2006. Rethinking “secondary” metabolism: physiological roles for phenazine antibiotics. Nat Chem Biol 2:71–78. doi: 10.1038/nchembio764 [DOI] [PubMed] [Google Scholar]
- 5. Zheng H, Chatfield CH, Liles MR, Cianciotto NP. 2013. Secreted pyomelanin of Legionella pneumophila promotes bacterial iron uptake and growth under iron-limiting conditions. Infect Immun 81:4182–4191. doi: 10.1128/IAI.00858-13 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 6. McRose DL, Newman DK. 2021. Redox-active antibiotics enhance phosphorus bioavailability. Science 371:1033–1037. doi: 10.1126/science.abd1515 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 7. Cunha BA, Burillo A, Bouza E. 2016. Legionnaires’ disease. Lancet 387:376–385. doi: 10.1016/S0140-6736(15)60078-2 [DOI] [PubMed] [Google Scholar]
- 8. Levin TC, Goldspiel BP, Malik HS. 2019. Density-dependent resistance protects Legionella pneumophila from its own antimicrobial metabolite, HGA. Elife 8:e46086. doi: 10.7554/eLife.46086 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 9. Soriano F, Edwards R, Greenwood D. 1992. Effect of Inoculum size on bacteriolytic activity of cefminox and four other beta-lactam antibiotics against Escherichia coli. Antimicrob Agents Chemother 36:223–226. doi: 10.1128/AAC.36.1.223 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 10. Udekwu KI, Parrish N, Ankomah P, Baquero F, Levin BR. 2009. Functional relationship between bacterial cell density and the efficacy of antibiotics. J Antimicrob Chemother 63:745–757. doi: 10.1093/jac/dkn554 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 11. Sadosky AB, Wilson JW, Steinman HM, Shuman HA. 1994. The iron superoxide dismutase of Legionella pneumophila is essential for viability. J Bacteriol 176:3790–3799. doi: 10.1128/jb.176.12.3790-3799.1994 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 12. LeBlanc JJ, Davidson RJ, Hoffman PS. 2006. Compensatory functions of two alkyl hydroperoxide reductases in the oxidative defense system of Legionella pneumophila. J Bacteriol 188:6235–6244. doi: 10.1128/JB.00635-06 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 13. Moffie BG, Mouton RP. 1988. Sensitivity and resistance of Legionella pneumophila to some antibiotics and combinations of antibiotics. J Antimicrob Chemother 22:457–462. doi: 10.1093/jac/22.4.457 [DOI] [PubMed] [Google Scholar]
- 14. Gibson DH, Fitzgeorge RB. 1983. Persistence in serum and lungs of guinea pigs of erythromycin, gentamicin, chloramphenicol and rifampicin and their in-vitro activities against Legionella pneumophila. J Antimicrob Chemother 12:235–244. doi: 10.1093/jac/12.3.235 [DOI] [PubMed] [Google Scholar]
- 15. Isenman H, Anderson T, Chambers ST, Podmore RG, Murdoch DR. 2018. Antimicrobial susceptibilities of clinical Legionella longbeachae isolates. J Antimicrob Chemother 73:1102–1104. doi: 10.1093/jac/dkx484 [DOI] [PubMed] [Google Scholar]
- 16. Molofsky AB, Swanson MS. 2004. Differentiate to thrive: lessons from the Legionella pneumophila life cycle. Mol Microbiol 53:29–40. doi: 10.1111/j.1365-2958.2004.04129.x [DOI] [PubMed] [Google Scholar]
- 17. Abisado RG, Benomar S, Klaus JR, Dandekar AA, Chandler JR, Garsin DA. 2018. Bacterial quorum sensing and microbial community interactions. mBio 9. doi: 10.1128/mBio.02331-17 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 18. Mukherjee S, Bassler BL. 2019. Bacterial quorum sensing in complex and dynamically changing environments. Nat Rev Microbiol 17:371–382. doi: 10.1038/s41579-019-0186-5 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 19. Hochstrasser R, Hilbi H. 2017. Intra-species and inter-kingdom signaling of Legionella pneumophila Front Microbiol 8:79. doi: 10.3389/fmicb.2017.00079 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 20. Hochstrasser R, Kessler A, Sahr T, Simon S, Schell U, Gomez-Valero L, Buchrieser C, Hilbi H. 2019. The pleiotropic Legionella transcription factor LvbR links the Lqs and c-di-GMP regulatory networks to control biofilm architecture and virulence. Environ Microbiol 21:1035–1053. doi: 10.1111/1462-2920.14523 [DOI] [PubMed] [Google Scholar]
- 21. Personnic N, Striednig B, Hilbi H. 2021. Quorum sensing controls persistence, resuscitation, and virulence of Legionella subpopulations in biofilms. ISME J 15:196–210. doi: 10.1038/s41396-020-00774-0 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 22. Ji Q, Zhang L, Jones MB, Sun F, Deng X, Liang H, Cho H, Brugarolas P, Gao YN, Peterson SN, Lan L, Bae T, He C. 2013. Molecular mechanism of quinone signaling mediated through S-quinonization of a YodB family repressor QsrR. Proc Natl Acad Sci U S A 110:5010–5015. doi: 10.1073/pnas.1219446110 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 23. Liu F, Rehmani I, Esaki S, Fu R, Chen L, de Serrano V, Liu A. 2013. Pirin is an iron-dependent redox regulator of NF-κB. Proc Natl Acad Sci U S A 110:9722–9727. doi: 10.1073/pnas.1221743110 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 24. Adams MA, Jia Z. 2005. Structural and biochemical evidence for an enzymatic quinone redox cycle in Escherichia coli: identification of a novel quinol monooxygenase. J Biol Chem 280:8358–8363. doi: 10.1074/jbc.M412637200 [DOI] [PubMed] [Google Scholar]
- 25. Nakanishi M, Yatome C, Ishida N, Kitade Y. 2001. Putative ACP phosphodiesterase gene (acpD) encodes an azoreductase. J Biol Chem 276:46394–46399. doi: 10.1074/jbc.M104483200 [DOI] [PubMed] [Google Scholar]
- 26. Cianciotto NP. 2015. An update on iron acquisition by Legionella pneumophila: new pathways for siderophore uptake and ferric iron reduction. Future Microbiol 10:841–851. doi: 10.2217/fmb.15.21 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 27. Varghese S, Wu A, Park S, Imlay KRC, Imlay JA. 2007. Submicromolar hydrogen peroxide disrupts the ability of Fur protein to control free-iron levels in Escherichia coli. Mol Microbiol 64:822–830. doi: 10.1111/j.1365-2958.2007.05701.x [DOI] [PMC free article] [PubMed] [Google Scholar]
- 28. Albert-Weissenberger C, Sahr T, Sismeiro O, Hacker J, Heuner K, Buchrieser C. 2010. Control of flagellar gene regulation in Legionella pneumophila and its relation to growth phase. J Bacteriol 192:446–455. doi: 10.1128/JB.00610-09 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 29. Appelt S, Heuner K. 2017. The flagellar regulon of Legionella-a review. Front Cell Infect Microbiol 7:454. doi: 10.3389/fcimb.2017.00454 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 30. Zhou M, Diwu Z, Panchuk-Voloshina N, Haugland RP. 1997. A stable nonfluorescent derivative of resorufin for the fluorometric determination of trace hydrogen peroxide: applications in detecting the activity of phagocyte NADPH oxidase and other oxidases. Anal Biochem 253:162–168. doi: 10.1006/abio.1997.2391 [DOI] [PubMed] [Google Scholar]
- 31. Ma M, Eaton JW. 1992. Multicellular oxidant defense in unicellular organisms. Proc Natl Acad Sci U S A 89:7924–7928. doi: 10.1073/pnas.89.17.7924 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 32. Choudhary D, Lagage V, Foster KR, Uphoff S. 2023. Phenotypic heterogeneity in the bacterial oxidative stress response is driven by cell-cell interactions. Cell Rep 42:112168. doi: 10.1016/j.celrep.2023.112168 [DOI] [PubMed] [Google Scholar]
- 33. Pine L, Hoffman PS, Malcolm GB, Benson RF, Keen MG. 1984. Determination of catalase, peroxidase, and superoxide dismutase within the genus Legionella. J Clin Microbiol 20:421–429. doi: 10.1128/jcm.20.3.421-429.1984 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 34. Dębski D, Smulik R, Zielonka J, Michałowski B, Jakubowska M, Dębowska K, Adamus J, Marcinek A, Kalyanaraman B, Sikora A. 2016. Mechanism of oxidative conversion of Amplex® Red to resorufin: pulse radiolysis and enzymatic studies. Free Radic Biol Med 95:323–332. doi: 10.1016/j.freeradbiomed.2016.03.027 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 35. Lietz D. 1958. The effect of horseradish peroxidase on some organic peroxides. Master of Science. South Dakota State University. [Google Scholar]
- 36. Mishra S, Imlay J. 2012. Why do bacteria use so many enzymes to scavenge hydrogen peroxide Arch Biochem Biophys 525:145–160. doi: 10.1016/j.abb.2012.04.014 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 37. Carlson KM, Boczek LA, Chae S, Ryu H. 2020. Legionellosis and recent advances in technologies for Legionella control in premise plumbing systems: a review. Water (Basel) 12:1–676. doi: 10.3390/w12030676 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 38. Casini B, Aquino F, Totaro M, Miccoli M, Galli I, Manfredini L, Giustarini C, Costa AL, Tuvo B, Valentini P, Privitera G, Baggiani A. 2017. Application of hydrogen peroxide as an innovative method of treatment for Legionella control in a hospital water network. Pathogens 6:15. doi: 10.3390/pathogens6020015 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 39. Berjeaud J-M, Chevalier S, Schlusselhuber M, Portier E, Loiseau C, Aucher W, Lesouhaitier O, Verdon J. 2016. . Legionella pneumophila: the paradox of a highly sensitive opportunistic waterborne pathogen able to persist in the environment. Front Microbiol 7:486. doi: 10.3389/fmicb.2016.00486 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 40. Gebhardt MJ, Jacobson RK, Shuman HA. 2017. Seeing red; the development of pON.mCherry, a broad-host range constitutive expression plasmid for gram-negative bacteria. PLoS One 12:e0173116. doi: 10.1371/journal.pone.0173116 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 41. Hébert GA, Steigerwalt AG, Brenner DJ. 1980. Legionella micdadei species nova: classification of a third species ofLegionella associated with human pneumonia. Curr Microbiol 3:255–257. doi: 10.1007/BF02601800 [DOI] [Google Scholar]
- 42. Garrity GM, Brown A, Vickers RM. 1980. Tatlockia and fluoribacter: two new genera of organisms resembling Legionella pneumophila. Int J Syst Bacteriol 30:609–614. doi: 10.1099/00207713-30-4-609 [DOI] [Google Scholar]
- 43. Rainey PB, Bailey MJ. 1996. Physical and genetic map of the Pseudomonas fluorescens SBW25 chromosome. Mol Microbiol 19:521–533. doi: 10.1046/j.1365-2958.1996.391926.x [DOI] [PubMed] [Google Scholar]
- 44. Zeigler DR, Prágai Z, Rodriguez S, Chevreux B, Muffler A, Albert T, Bai R, Wyss M, Perkins JB. 2008. The origins of 168, W23, and other Bacillus subtilis legacy strains. J Bacteriol 190:6983–6995. doi: 10.1128/JB.00722-08 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 45. Sussmann . 1966. Methods in cell physiology, p 397–410. In Prescott D (ed), Academic Press, NY. [Google Scholar]
- 46. Hacek DM, Dressel DC, Peterson LR. 1999. Highly reproducible bactericidal activity test results by using a modified national committee for clinical laboratory standards broth macrodilution technique. J Clin Microbiol 37:1881–1884. doi: 10.1128/JCM.37.6.1881-1884.1999 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 47. Schindelin J, Arganda-Carreras I, Frise E, Kaynig V, Longair M, Pietzsch T, Preibisch S, Rueden C, Saalfeld S, Schmid B, Tinevez J-Y, White DJ, Hartenstein V, Eliceiri K, Tomancak P, Cardona A. 2012. Fiji: an open-source platform for biological-image analysis. Nat Methods 9:676–682. doi: 10.1038/nmeth.2019 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 48. Bolger AM, Lohse M, Usadel B. 2014. Trimmomatic: a flexible trimmer for illumina sequence data. Bioinformatics 30:2114–2120. doi: 10.1093/bioinformatics/btu170 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 49. Bray NL, Pimentel H, Melsted P, Pachter L. 2016. Near-optimal probabilistic RNA-seq quantification. Nat Biotechnol 34:525–527. doi: 10.1038/nbt0816-888d [DOI] [PubMed] [Google Scholar]
- 50. Love MI, Huber W, Anders S. 2014. Moderated estimation of fold change and dispersion for RNA-seq data with DESeq2. Genome Biol 15:550. doi: 10.1186/s13059-014-0550-8 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 51. Benjamini Y, Hochberg Y. 1995. Controlling the false discovery rate: a practical and powerful approach to multiple testing. J R Stat Soc B Stat 57:289–300. doi: 10.1111/j.2517-6161.1995.tb02031.x [DOI] [Google Scholar]
- 52. Wickham H. 2016. ggplot2: elegant graphics for data analysis. Springer. https://play.google.com/store/books/details?id=XgFkDAAAQBAJ. [Google Scholar]
- 53. St John G, Steinman HM. 1996. Periplasmic copper-zinc superoxide dismutase of Legionella pneumophila: role in stationary-phase survival. J Bacteriol 178:1578–1584. doi: 10.1128/jb.178.6.1578-1584.1996 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 54. Bandyopadhyay P, Steinman HM. 1998. Legionella pneumophila catalase-peroxidases: cloning of the KatB gene and studies of KatB function. J Bacteriol 180:5369–5374. doi: 10.1128/JB.180.20.5369-5374.1998 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 55. LeBlanc JJ, Brassinga AKC, Ewann F, Davidson RJ, Hoffman PS. 2008. An Ortholog of OxyR in Legionella pneumophila is expressed postexponentially and negatively regulates the alkyl hydroperoxide reductase (ahpC2D) operon. J Bacteriol 190:3444–3455. doi: 10.1128/JB.00141-08 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 56. Personnic N, Striednig B, Hilbi H. 2018. Legionella quorum sensing and its role in pathogen-host interactions. Curr Opin Microbiol 41:29–35. doi: 10.1016/j.mib.2017.11.010 [DOI] [PubMed] [Google Scholar]
Associated Data
This section collects any data citations, data availability statements, or supplementary materials included in this article.
Supplementary Materials
Data Availability Statement
Data have been deposited as follows: RNA-seq read archive (BioProject ID), PRJNA943215; RNA-seq read processing and analysis scripts, https://github.com/mliannholland/hga_rnaseq