Abstract
Disinfectants are routinely used in hospitals and health care facilities for surface sterilization. However, the mechanisms by which these disinfectants kill and the extent to which bacteria, including Pseudomonas aeruginosa, are resistant remains unclear. Consequently, P. aeruginosa nosocomial infections result in considerable casualties and economic hardship. Previously, DNA microarrays were utilized to analyze the genome-wide transcription changes in P. aeruginosa after oxidative antimicrobial (sodium hypochlorite, peracetic acid, and hydrogen peroxide) exposure. Simultaneous analysis of these transcriptome datasets provided a comprehensive understanding of the differential responses to these disinfectants. An analysis of variance, functional classification analysis, metabolic pathway analysis, Venn diagram analysis, and principal component analysis revealed that sodium hypochlorite exposure resulted in more genome-wide changes than either peracetic acid or hydrogen peroxide exposures.
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Pseudomonas aeruginosa PA01 (P. aeruginosa) is an opportunistic pathogen that infects organisms and causes nosocomial infections (Vincent et al. 2004). These infections are more common in patients with defective immune systems such as cystic fibrosis and can be lethal to those suffering from compromised immune systems (Tummler and Kiewitz 1999). P. aeruginosa infections may also occur in cancer patients, patients suffering from urinary tract infections, and patients suffering from burn wounds (Bodey et al. 1983). P. aeruginosa is well suited to survive in a wide variety of environments (water, soil, and animals) and is prevalent in common everyday surroundings (Fink 1993). Infections caused by P. aeruginosa are often difficult to treat due to the prominent resistance exhibited by the pathogen to antimicrobial agents (Hancock 1998).
Oxygen exposure, and in particular the elicitation of reactive oxygen species, can result in DNA and lipid damage that display antimicrobial effects. Indeed, oxidative antimicrobials (sodium hypochlorite, peracetic acid, hydrogen peroxide, etc.) have commonly been used to eliminate pathogenic bacteria, such as P. aeruginosa (Kitis 2004; Spoering and Lewis 2001). Hydrogen peroxide is widely used as a disinfectant in the concentration ranges of 3–90% (v/v) and is considered environmentally friendly because it breaks down into water and oxygen (Block 2001). Acute hydrogen peroxide exposure to bacterial cells generates hydroxyl free radicals (·OH) that attack DNA resulting in the cellular death (Carlsson and Carpenter 1980; Demple and Halbrook 1983). Sulfhydryl groups and disulfide bonds are suspected to be targeted by these free radicals as well (Block 2001). Peracetic acid is often considered a more potent disinfectant than hydrogen peroxide as it is effective at concentrations <0.3% (v/v) (Block 2001). Peracetic acid is also considered environmentally friendly as it decomposes to acetic acid and oxygen but has added advantages over hydrogen peroxide as it is not susceptible to peroxidases and retains its activity in the presence of organic loads (Malchesky 1993). Peracetic acid’s mechanism of action is speculated to be the denaturation of proteins and enzymes and increased cell wall permeability by oxidizing sulfhydryl and disulfide bonds (Block 2001). Sodium hypochlorite is the most widely used disinfectant; comprising the active ingredient in more than 350 registered products by the US Environmental Protection Agency. In aqueous solutions, sodium hypochlorite ionizes into Na+ and OCl− and establishes an equilibrium between these ions and hypochlorous acid (HOCl; Bloomfield 1996). The HOCl moiety is dominant in the pH 4–7 range, and the OCl− moiety is dominant above pH 9 (White 1986). Hypochlorous acid has been shown to disrupt oxidative phosphorylation (McDonnell and Russell 1999), however, the precise mechanism of action by which sodium hypochlorite kills remains to be elucidated (Rutala 1996).
Transcriptome analyses of bacteria treated with these antimicrobials have only recently emerged, and no comparative analysis between different antimicrobials has been made (Chang et al. 2005a, b, 2006; Palma et al. 2004; Zheng et al. 2001). Notably, microarray studies of a bacterial response to hydrogen peroxide have appeared for many species of bacteria, including the following: Bacillus subtilis (Hayashi et al. 2005), Staphylococcus aureus (Chang et al. 2006), and Streptococcus pneumoniae (Ulijasz et al. 2004). Our recent studies of the response of P. aeruginosa to peracetic acid and sodium hypochlorite are the only transcriptome analysis concerning these antimicrobials among Eubacteria (Chang et al. 2005b; Small et al. 2007). There have been many reports attempting to compare microarray studies, either for evaluating the responses of an organism to a series of treatments or perturbations or responses of many organisms to the same treatment or perturbation. Most often, these results are indecisive; indeed, there are many reports providing guidance on how one treats data from disjointed microarray studies to statistically glean new insight. This study, comparing three independent transcriptome reports, takes advantage of the almost identical experimental conditions underpinning the investigations. In particular, the real-time polymerase chain reaction (PCR)-validated genome-wide changes in P. aeruginosa (based on data from Affymetrix Pseudomonas GeneChip arrays) after a 20-min sublethal exposure to sodium hypochlorite, peracetic acid, and hydrogen peroxide were investigated using several formats including one-way analysis of variance (ANOVA), Venn diagrams, and principal component analysis (PCA). The results suggest that the mechanisms by which peracetic acid, hydrogen peroxide, and sodium hypochlorite act upon cell metabolism are clearly distinct. Sodium hypochlorite is noted for multiple targets of somewhat distant function, which might be a basis for its unparalleled effectiveness (Chang et al. 2005a, b). This is the first comparative global gene transcription analysis of these three oxidative stressors. We believe this study and further comparative reports will help elucidate the mechanisms by which disinfectants kill microbes and facilitate the design of more effective antimicrobials, including those comprising mixtures of various compounds.
Materials and methods
Cells and media, sampling, and microarray procedures
In this study, we used P. aeruginosa PA01 obtained from Dr. E. Peter Greenberg’s laboratory at the University of Iowa. To maintain homogeneous culture samples throughout our experiments, we employed the following three steps: (1) we initiated P. aeruginosa cultures at 37°C with shaking at 250 rpm using sterilized Luria–Biertani (LB) broth (10 g of tryptone, 5 g of yeast extract, and 10 g of sodium chloride per liter); (2) after 17 h, we diluted the overnight cultures 1:100 in prewarmed LB broth and incubated at 37°C with shaking at 250 rpm until an optical density at 600 nm (ODBBBBBB –600BBBBBB–) reached the early logarithmic phase (∼0.8); and (3) we rediluted the cells 1:10 in prewarmed LB broth and incubated at 37°C with shaking at 250 rpm (Chang et al. 2005a, b). RNA for microarray analysis was isolated 20 min after the addition of water (for the control samples), 4.4 mM sodium hypochlorite, 1 mM hydrogen peroxide, or 0.5 mM peracetic acid (Chang et al. 2005a, b; Small et al. 2007). Complementary DNA was synthesized from 12 μg of RNA according to the standard protocols for the Affymetrix P. aeruginosa GeneChip array (Affymetrix). Hybridization and scanning of the arrays were performed according to the standard protocols for the Affymetrix P. aeruginosa GeneChip array (Affymetrix).
Microarray data analysis
Data analysis was performed with the Affymetrix GeneChip Operating Software (GCOS) v. 1.0 and GeneSpring GX v. 7.3 (Agilent Technologies). The following parameters were employed for GCOS expression analysis: alpha 1, 0.04; alpha 2, 0.06; tau, 0.015; target signal, 150. Four sodium hypochlorite-exposed sample replicates, four peracetic acid-exposed sample replicates, and four hydrogen peroxide-exposed sample replicates were then normalized to the four water-diluted (control) sample replicates. A master present/marginal list of present/marginal call genes was created by merging the lists of genes that received present/marginal calls from 50% or more of the replicates for each sample set (four water-diluted control samples, four sodium hypochlorite-treated cultures, four peracetic acid-treated cultures, and four hydrogen peroxide-treated cultures). Gene expression changes with statistical significance were identified by 1-way ANOVA (p cutoff value, 0.05). Fold change was then calculated as the log transformed (median log-of-ratio) between the signals of the four water-diluted control samples and to each of the following with respect to the exposed disinfectant as follows: four 4.4 mM sodium hypochlorite-treated cultures, four 0.5 mM peracetic acid-treated cultures, and four 1 mM hydrogen peroxide-treated cultures. The data discussed in this publication have been deposited in National Center for Biotechnology Information’s Gene Expression Omnibus (http://www.ncbi.nlm.nih.gov/geo) and are accessible through GEO Series accession number GSE7402.
Results
P. aeruginosa transcriptome changes in response to oxidative stress
A sublethal exposure of 4.4 mM (0.03%) sodium hypochlorite (Small et al. 2007), 0.5 mM peracetic acid (Chang et al. 2005b), and 1 mM hydrogen peroxide (Chang et al. 2005a) for 20 min showed inhibition of growth. Notably, the concentrations of stressors for study were selected so that the attenuation in cell growth was fairly severe to ensure a response (i.e., approximately 50% of the initial growth rate), while still enabling harvest of quality messenger RNA (mRNA) for microarray analysis. From the 5,570 genes in the P. aeruginosa genome, 5,237 genes passed the present/marginal restriction described above to form the master present/marginal list. From the 5,237 genes in the master present-marginal list, 3,197 genes across all three treatments showed statistical significance based on the one-way ANOVA (sodium hypochlorite had 1,245 upregulated and 1,952 downregulated genes, peracetic acid had 1,209 upregulated and 1,988 downregulated genes, and hydrogen peroxide had 1,568 upregulated and 1,629 downregulated genes). However, as these groups are being compared to each other, a fold change threshold of twofold or more was established to differentiate responses. This statistical analytical analysis provided a unique, global method for comparing these treatments, as our previous studies simply used t tests comparing a set of treatment samples to the control samples. The one-way ANOVA analysis based on the treatment provides a more robust analysis to compare the treatments rather then just comparing individual t tests against one another. To visualize the union of the datasets, a Venn diagram analysis based on various fold change differences was performed on the statistically significant genes determined by the one-way ANOVA to further analyze logical relationships (unions and intersections) of genes between all the treatments. Based on these values, a conservative twofold or more upregulation or downregulation threshold was selected to differentiate the seven regions of the Venn diagram as shown in Fig. 1. Thus, from the 3,197 genes that showed statistical significance based on the one-way ANOVA, sodium hypochlorite had 457 upregulated and 625 downregulated genes, peracetic acid had 362 upregulated and 413 downregulated genes, and hydrogen peroxide had 187 upregulated and 204 downregulated genes at the twofold or more change threshold level.
Functional classifications analysis
Functional classifications of the responding genes are provided in Fig. 2. Not shown in these figures is the “hypothetical, unclassified, unknown” functional class, which comprised the greatest number of affected genes for all the disinfectant-exposed samples. Functional classes are taken from P. aeruginosa Community Annotation Project (Winsor et al. 2005). A Venn diagram analysis was performed on the functional classifications marked with asterisks in Fig. 2 to further analyze logical relationships (unions and intersections) of genes in each of these functional classes. The results are shown in Table 1 for the twofold or more increased genes and Table 2 for the twofold or more decreased genes (Table 2) and reference the regions defined in the Venn diagram (Fig. 1).
Metabolic pathway analysis
P. aeruginosa metabolic pathways were compared between the disinfectant-exposed samples and the (water-diluted) control samples based on the Kyoto Encyclopedia of Genes and Genomes (KEGG; Ogata et al. 1999). These metabolic pathways were compiled into tables to organize the data based on metabolic functions. Table 3 shows the oxidative phosphorylation pathway genes, while Table 4 displays the Enteroff–Doudoroff (ED) pathway and Embden–Meyerhof–Parnas (EMP) pathway based on prior characterizations and genetic mappings (Roehl et al. 1983; Roehl and Phibbs 1982). Table 5 shows ATP-binding cassettes (ABC) for organic sulfur transport-related genes. Finally, Supplemental Tables 1, 2, and 3 display cellular protective mechanism-related genes, iron regulation-related genes, and pyocin system-related genes, respectively, which were organized based on our prior studies of peracetic acid and hydrogen peroxide (Chang et al. 2005a, b).
Principal component analysis
Finally, a PCA based on conditions was performed on the master present/marginal list (5,237 genes) for all of the conditions (four control group replicates, four sodium hypochlorite-exposed group replicates, four peracetic acid-exposed group replicates, and four hydrogen peroxide-exposed group replicates) using Genespring GX 7.0 centering. PCA reduces data dimensionality by reducing a complex data set to a lower dimension to reveal a more simplistic structure of the data (Daffertshofer et al. 2004). A PCA on conditions is typically used to show data integrity. The results of this analysis are shown in Fig. 4. Based on the 86.52% total variance calculated by the PCA on conditions analysis, PCA component 1 had an eigenvalue of 770.2 and 56.12% of the variance, PCA component 2 had an eigenvalue of 246.2 and 17.94% of the variance, and PCA component 3 had an eigenvalue of 171.0 and 12.46% of the variance. In PCA, large variances represent high signal-to-noise ratios (SNR) in the data that reveal the most interesting dynamics of the data set. Thus, PCA component 1 represented the most dynamic difference between the samples. While PCA component 2 and PCA component 3 both represented significantly less dynamic difference among the samples but still exceeded the SNR of the data set.
Discussion
Functional classification analysis
Based on the one-way ANOVA statistically significant twofold or more changes, sodium hypochlorite exposure resulted in more upregulated or downregulated genes than either hydrogen peroxide exposure or peracetic acid exposure. This same comparative pattern was observed in the functional classification analysis. By visually observing Tables 1 and 2, four striking features stood out as follows: (1) sodium hypochlorite exposure resulted in more twofold or more downregulated genes in the “Energy Metabolism” functional class suggesting that sodium hypochlorite exposure may limit energy production by the cell more than peracetic acid or hydrogen peroxide exposure. (2) Exposure to sodium hypochlorite generally resulted in the downregulation of genes in the functional classes marked with a single asterisk in Fig. 2 and generally had more genes upregulated in the functional classes marked with a double asterisk in Fig. 2, which demonstrated that sodium hypochlorite exposure resulted in more genome-wide changes than peracetic acid or hydrogen peroxide exposure. (3) Exposure to hydrogen peroxide resulted in the fewest number of twofold or more upregulated and downregulated genes in the entire asterisk-marked functional classes, which suggested that hydrogen peroxide treatment resulted in fewer genome-wide changes than sodium hypochlorite or peracetic-acid exposure. (4) There were very few functional classes that were not affected by all treatments, and by far, the most affected functional class was membrane proteins, particularly those associated with small molecule transport across the periplasmic or cytoplasmic membrane.
To further visualize the changes in these functional classes, a Venn diagram analysis of these functional classes marked with a single asterisk (downregulated) or a double asterisk (upregulated) revealed that sodium hypochlorite indeed does have more uniquely upregulated and downregulated genes for all of the functional classes marked with asterisks in Fig. 2 (see Tables 1 and 2), except in the “Related to phage, transposon, or plasmid” functional class, where the hydrogen peroxide exposure resulted in more than twice as many genes upregulated compared to sodium hypochlorite or peracetic acid exposure. The number of upregulated and downregulated genes resulting from peracetic acid exposure generally fell in between the highly affected sodium hypochlorite-exposed and the minimally affected hydrogen peroxide-exposed groups in either the overall twofold or more change analysis and the functional classification analysis. However, exposure to peracetic acid resulted in upregulation of the genes in the “Adaption, protection” functional class and downregulation of the genes in the “Transcriptional regulators” functional classification.
Oxidative phosphorylation and electron transport
The oxidative phosphorylation pathway analysis expanded upon the “Energy metabolism,” “Membrane proteins,” and “Putative enzymes” functional classes. The large downregulation of the “Energy metabolism” functional class after sodium hypochlorite exposure correlates with the twofold or more decrease in the genes related to oxidative phosphorylation (see Tables 2 and 3). After sodium hypochlorite exposure, all the genes associated with Complex I (NADH hydrogenase genes) were uniformly downregulated by threefold. Similarly, Complex II, which comprises fumerate reductase and other genes, were again all downregulated (∼2.5-fold). Complex III, which contains the genes responsible for the cytochrome bc1 complex, were downregulated from twofold to 18-fold. The cytochrome c oxidase genes of Complex IV were all downregulated from twofold to 22-fold. However, peracetic acid and hydrogen peroxide exposure did not result in the same degree of downregulation of these genes. The transcriptional downregulation of these genes for the sodium hypochlorite-exposed samples suggested that both oxidative phosphorylation and the electron transport chain were significantly and uniformly downregulated, perhaps resulting in minimal energy production by these principal metabolic pathways after exposure. This uniform downregulation after sodium hypochlorite exposure is consistent with prior studies that demonstrated a decrease in respiratory function and the loss of metabolic energy after HOCl exposure (Albrich and Hurst 1982).
Carbon metabolism
The ED pathway and EMP pathway analysis also suggested that genes encoding carbon substrate catabolization during oxidative phosphorylation were affected by the disinfectant treatments (see Table 4). This pathway analysis also expanded upon the “Carbon compound catabolism,” “Central intermediary metabolism,” “Energy metabolism,” “Membrane protein,” and “Transport of small molecules” functional classes. The genes encoding the proteins that actively transport hexose molecules (glucose, maltose, gluconate, 2-ketogluconate, fructose, and glycerol) into the cell are downregulated after sodium hypochlorite exposure (but not after peracetic acid or hydrogen peroxide exposure). The genes that encode the transport of glucose (PA3186 to PA3190) across the periplasmic and cytoplasmic membranes were highly downregulated after sodium hypochlorite exposure, and prior studies have shown glucose uptake to be inhibited after low concentrations of HOCl exposure (Schraufstatter et al. 1990). The genes encoding the same enzymes for these metabolites seemed to be either unaffected, or certainly nonsystemically affected, by hydrogen peroxide exposure. Peracetic acid exposure, however, resulted in downregulation of the same glucose transporter genes but to a lesser extent than upon sodium hypochlorite exposure. Exposure to sodium hypochlorite and hydrogen peroxide did not result in a significant upregulation of the glycerol or glycerol-3-phosphate transporter genes, which corresponds to studies that show glyceraldehyde-3-phosphate dehydrogenase is inactivated by sodium hypochlorite or hydrogen peroxide exposure (Schraufstatter et al. 1990). Additionally, the genes encoding glycerol and possibly glycerol-3-phosphate (PA3581, PA5235) showed a strong upregulation after peracetic acid exposure. The genes that code for the enzyme that catabolize glycerol, glycerol kinase (glpK, PA3582), and that catabolize glycerol-3-phosphate, glycerol-3-phosphate dehydrogenase (glpD, PA3584) were also strongly upregulated after peracetic acid exposure. This suggests that glycerol and glycerol-3-phospate may be a preferred substrate for growth as a result of peracetic acid exposure. They might also indicate an unrelated response to a potential carbon source rather than peracetic acid as an oxidant disinfectant. Indeed, prior studies have shown that glycerol and glycerol-3-phosphate are utilized as substrates for P. aeruginosa and Escherichia coli growth and are regulated by the potent feedback inhibition of fructose-1,6-diphosphate (Lessie and Phibbs 1984; McCowen et al. 1986). Additionally, glpK and glpD expression and activity are known to occur only when glycerol is utilized as a substrate for growth (McCowen et al. 1981). Furthermore, the Mg2+ transporter genes, mgtA (PA4825), was upregulated sixfold and mgtC (PA4635) was upregulated fourfold and could very well account for the excess Mg2+ ion required for glycerol kinase (glpk, PA3582) activity (McCowen et al. 1986). Hence, we suspect the observed response to peracetic acid compromises these components due to its antimicrobial activity as well as its potential as a carbon source.
Sulfur transport
The sodium hypochlorite exposure resulted in a strong upregulation of genes responsible for organic sulfur transport and the associated genes that catabolize these compounds (see Table 5). The genes encoding the alkanesulfonate transport system (PA3441 to PA3446) contained the most highly upregulated genes after sodium hypochlorite exposure and were not drastically upregulated or downregulated after peracetic acid or hydrogen peroxide exposure. P. aeruginosa has been known to use n-alkanesulfonates or taurine as sources of both carbon and organic sulfur (van der Ploeg et al. 1996). Typically the ssuD (PA3444) and ssuE (PA3446) genes are expressed during sulfate or cysteine starvation (Eichhorn et al. 1999). This may suggest the following: that the sulfur in these compounds was required due to sulfur starvation caused by the reaction of the HOCl with sulfhydryl groups, that the carbon compound skeletons of the n-alkanesulfonates were being used in lieu of the carbon compounds contained in the hexose transporters of the ED pathway, or that the neutrophilic amines and alpha-amino acids formed by catabolization of n-alkanesulfonates may guard the cell against oxidative stress and attack from the HOCl moiety.
The genes encoding enzymes responsible for the taurine transport system (PA3935 to PA3938) exhibited the second most highly upregulated genes after sodium hypochlorite exposure and again were not drastically upregulated or downregulated in the peracetic acid-exposed or hydrogen peroxide-exposed samples. The tauD (PA3935) gene had a tenfold increase and is required for the catabolization of taurine to sulfite but has previously been shown to only be expressed under conditions of sulfate starvation (Eichhorn et al. 1997; van der Ploeg et al. 1996). Prior studies have demonstrated that taurine alone can be used as a sole source of carbon and sulfur in P. aeruginosa (Shimamoto and Berk 1979). Taurine has also been demonstrated to scavenge HOCl by forming N-chlorotaurine, which has greater stability and less toxicity (Grisham et al. 1984), and the N-chorotaurine has been shown to degrade to sulphoacetaldehyde in response to oxidative stress (Cunningham et al. 1998). This may suggest the following: that the sulfur in the taurine was required due to sulfur starvation caused by the reaction of HOCl with sulfhydryl groups, that the aldehyde carbon compounds were being utilized instead of the carbon compounds contained in the hexose transporters of the ED pathway, or that the taurine scavenged the highly destructive HOCl moiety by providing a less damaging pathway to degrade this compound.
The genes encoding proteins responsible for sulfate ester transporters (PA0183 to PA0186, PA2307 to PA2310) also had an upregulation after sodium hypochlorite exposure and again were not drastically upregulated or downregulated after peracetic acid or hydrogen peroxide exposure. The arylsulfatase gene, atsA (PA0183), was upregulated almost fourfold after sodium hypochlorite exposure and is associated with the sulfur starvation-induced proteins and has been used as a model system for the sulfate starvation response (Hummerjohann et al. 1998, 2000). Finally, the α-ketoglutarate-dependent dioxygenase gene, atsK (PA2310), was upregulated almost 18-fold after sodium hypochlorite exposure. The atsK enzyme catalyzes the oxidative conversion of the α-ketoglutarate cofactor into CO2, succinate, and highly reactive ferryl (IV) species and is known to have a 38% amino acid homology to tauD (Muller et al. 2005). As these genes were strongly upregulated after sodium hypochlorite exposure and not changed after hydrogen peroxide or peracetic acid exposure, the atsA and atsK encoded enzymes may have directly reacted with the HOCl or performed side reactions to help mediate the oxidative stress caused by HOCl exposure.
Protective genes
Genes encoding several cellular protective mechanisms were highly upregulated after hydrogen peroxide exposure (see Supplementary Table 1). The catalase gene, katA (PA4236), did not show a significant upregulation for all three treatments which supports a prior suggestion that katA serves, instead, as a housekeeping catalase gene (Brown et al. 1995). However, the catalase gene, katB (PA4613), was upregulated sevenfold in the sodium hypochlorite-exposed samples and fourfold in the peracetic acid-exposed and hydrogen peroxide-exposed samples. This result corroborates the necessity of katB expression for optimal hydrogen peroxide resistance (Brown et al. 1995). The super oxide dismutase enzymes sodB (PA4366) and sodM (PA4468) did not show a significant upregulation or downregulation in all three treatments. However, the transcript raw signal intensities of sodM were among the highest for all of the treatments as well as the control samples (3,524 for sodium hypochlorite; 1,276 for peracetic acid; 1,834 for hydrogen peroxide; and 1923 for the control), thus suggesting that sodB gene expression may be considerable during standard aerobic growth conditions (Hassett et al. 1995). Several DNA repair-related genes were highly induced after hydrogen peroxide-exposure but were minimally upregulated after sodium hypochlorite and peracetic acid exposure. The DNA repair gene, recN (PA4763), was the exception as it was upregulated after all three treatments, although it was upregulated much more so after hydrogen peroxide exposure. These results again correspond well with prior studies establishing DNA damage with hydrogen peroxide exposure (Carlsson and Carpenter 1980; Demple and Halbrook 1983).
Iron regulation
Our previous studies confirmed that Fur-regulated genes were repressed after hydrogen peroxide exposure (Chang et al. 2005a; Palma et al. 2003). Comparison of three treatments (see Supplementary Table 2) to these iron-related genes revealed that exposure to sodium hypochlorite and peracetic acid also resulted in many of these same repressions in the following genes: ferri-siderophore or iron-chelating compound receptor genes, fpvA (PA2398) and fptA (PA4221); siderophore biosynthesis genes, pchF (PA4225) and pchE (PA4226); pyochelin biosynthesis genes, pchDCBA (PA4228 to PA4231); siderophore or pyoverdin system-related genes (PA2403 to PA2410 and PA4156). Interestingly, the hydrogen peroxide responses are much higher than the strikingly similar sodium hypochlorite and peracetic acid responses to these iron regulation-related genes.
Pyocins
Perhaps the most striking result of our study was that the F-, R- and S-type pyocins (bacteriocins) of P. aeruginosa that were strongly upregulated after hydrogen peroxide exposure were downregulated after peracetic acid and sodium hypochlorite exposure (see Supplementary Table 3). These 41 genes were uniformly upregulated after hydrogen peroxide exposure and 37 of these bacteriocins were uniformly downregulated after sodium hypochlorite or peracetic acid exposure. Pyocins are readily induced by mutagenic agents (i.e., UV radiation and mitomycin C) and generally kill cells by degrading DNA and inhibiting lipid synthesis (Michel-Briand and Baysse 2002). Pyocin gene expression is regulated by the enzymes for recA (PA3617), prtR (PA0610), and prtN (PA0611); specifically, UV-activated RecA protein cleaves the repressor protein, PrtR, allowing the prtN gene to be expressed. The PrtN protein then facilitates the expression of various pyocin genes (Matsui et al. 1993). Thus, the upregulation of the recA gene combined with the possible RecA activation by hydroxyl radicals (instead of UV irradiation) may have caused the pyocin gene expression for the hydrogen peroxide-exposed samples. This is quite plausible, as the RecA protein has been shown to cleave single-stranded DNA with the aid of the hydroxyl radical (Akaboshi and Howard-Flanders 1990). However, the lack of recA expression after sodium hypochlorite and peracetic acid exposure may have prevented pyocin gene expression as well as the lack of an activator for the RecA protein.
Principal component analysis
The PCA on conditions analysis shows the closeness of all the samples to one another (see Fig. 3). Each set of samples for the three treatments and the control samples are grouped into four small clusters in the 3-D space. The closeness of the clusters was representative of the precision of the biological replicates for each sample set. The control samples groups predominantly around the origin as all samples were normalized to the control samples. Clearly, all three treatments did not function the same way as all the treatment samples do not appear in the same spatial areas compared to the control samples, which suggests that these three oxidative stressors did not affect the cells the same way.
In summary, the well-documented unparalleled effectiveness of sodium hypochlorite as a disinfectant coincides with a plethora of statistically significant genome-wide changes in gene transcription after sodium hypochlorite exposure, far more than in response to other oxidants peracetic acid or hydrogen peroxide. The genome-wide effects on hydrogen peroxide, particularly the upregulation of DNA repair genes, support previous studies that target DNA effects as the mechanism of action (McDonnell and Russell 1999). The mechanisms of action of sodium hypochlorite and peracetic acid appear to be related to membrane proteins. The increased transcription of genes associated with organic sulfur transport and decrease in genes associated with hexose compound transport across the cell envelope supports prior reports of sodium hypochlorite’s interaction with protein sulfhydryl groups and the downregulation of respiratory systems associated with metabolic energy loss (Barrette et al. 1987). The resulting global transcription profile comparison can help identify commonly activated genes between these oxidative disinfectants. Furthermore, this information will help us better understand the mechanisms by which oxidative disinfectants kill bacteria.
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Acknowledgements
Although the research described in this paper has been funded wholly by the US Environmental Protection Agency (Grant no. T-83100801-0, IPA no. HQ-514-04-06, and IPA HQ-515-04-06), it has not been subjected to the Agency’s peer and administrative review and therefore may not necessarily reflect the views of the EPA; nor does the mention of trade names or commercial products constitute endorsement of recommendation of use.
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Small, D.A., Chang, W., Toghrol, F. et al. Comparative global transcription analysis of sodium hypochlorite, peracetic acid, and hydrogen peroxide on Pseudomonas aeruginosa . Appl Microbiol Biotechnol 76, 1093–1105 (2007). https://doi.org/10.1007/s00253-007-1072-z
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DOI: https://doi.org/10.1007/s00253-007-1072-z