There is a growing body of literature that recognizes the importance of plasma treated water (PTW) for inactivation of microorganism. However, very little attention has been paid to the role of reactive nitrogen species (RNS) in deactivation of bacteria. The aim of this study is to explore the role of RNS in bacterial killing, and to develop a plasma system with increased sterilization efficiency. To increase the concentration of reactive oxygen and nitrogen species (RONS) in solution, we have used vapor systems (DI water/HNO3 at different wt%) combined with plasma using N2 as working gas. The results show that the addition of the vapor system yields higher RONS contents. Furthermore, PTW produced by N2 + 0.5 wt% HNO3 vapor comprises a large amount of both RNS and ROS, while PTW created by N2 + H2O vapor consists of a large amount of ROS, but much less RNS. Interestingly, we observed more deactivation of E. Coli with PTW created by N2 + 0.5 wt% HNO3 vapor plasma as compared to PTW generated by the other plasma systems. This work provides new insight into the role of RNS along with ROS for deactivation of bacteria.
Over the last decade, several novel techniques have been developed for microbial decontamination1,2. Atmospheric pressure non-thermal plasma (NTP) has emerged as a potential tool for the effective control of photogenic microorganisms, and for water purification3,4. NTP generates ions, ozone (O3), UV photons, and various reactive oxygen and nitrogen species (RONS)5,6. It has shown promising effect in the sterilization of medical tools and packaging materials7. Recently, NTP has also shown its efficiency in wound healing8,9,10,11, tissue regeneration12,13 and cancer therapy14,15,16,17. Many types of plasma devices have been developed, such as dielectric barrier discharges (DBDs), plasma jets, floating electrode (FE)-DBD, and external additives have also been combined to the plasma treatment in order to increase the efficiency14,15,16. Previously, we have investigated the influence of H2O and D2O vapor to increase the efficiency of an atmospheric pressure plasma jet (APPJ) for the inactivation of cancer cells, i.e., breast cancer and melanocytes cancer cells14,16. In the last few years, plasma treated physiological fluids have also shown promising effect, similar to the direct treatment of plasma17,18,19. These plasma treated solutions contain reactive species with a longer lifetime, and provide a medium with a high and durable degree of reactivity20.
The chemical species generated in liquid treated by plasma mainly depend upon the type of discharge, feeding gas, humidity, etc. It was stated that plasma treated water (PTW) consists of various RONS, such as O (atomic oxygen), OH (hydroxyl radicals), O3 (ozone), H2O2 (hydrogen peroxide), NO (nitric oxide), NO2− (nitrites), NO3− (nitrates) and ONOO− (peroxynitrites) that are responsible for microbial inhibition21. However, other authors conclude that short lived species are not stable in PTW, i.e., the life-time of excited atomic oxygen is ≈30 ns22, for OH it is ≈1 ns23, while O3 can live for 1000 s at room temperature24. It was also reported that reactive oxygen species (ROS), e.g. OH, O2•−, O3 and H2O2, play a significant role in bacterial inactivation25,26, whereas other research groups proposed that ONOO− is the dominant species for bacterial inactivation27,28. Furthermore, it was reported in literature that the presence of NO2−/NO3− at acidic pH in noticeable concentrations can cause the antimicrobial properties29,30. Traylor et al. discussed the complexity of reactions in PTW with biological systems, because different biological effects occur in differing time scales with various chemical components25. Finally, Ikawa et al. suggested that the main component for the antibacterial activity of PTW is not ONOOH (peroxynitrous acid), but O2NOOH (peroxynitric acid)31.
In general there is still uncertainty whether ROS or RNS are the main factor for the antibacterial effect in PTW. This paper aims to provide an answer to this research question about the importance of ROS and/or RNS in PTW for the antibacterial efficacy. Therefore, we developed an APPJ system with HNO3 vapor at different wt% and we checked the enhancement of NO along with OH radicals, both in the gas and liquid phase, using optical emission spectroscopy and chemical analysis, respectively. Besides NO and OH, the production of other reactive species, such as H2O2, NO2− and NO3−, was also detected in solution after different types of plasma treatment (i.e., only N2 gas plasma, N2 + H2O vapor plasma, and N2 + 0.5 wt% HNO3 vapor plasma). Subsequently, we compared the antibacterial activity of PTW generated by the different plasma systems, by treating E. coli. Finally, we measured the oxidative stress related gene expression using quantitative real time polymerase chain reaction (qPCR) analysis, the genomic DNA degradation using gel electrophoresis, and changes in the surface morphology using scanning electron microscopy (SEM) of E. coli after treatment with PTW.
Luria Bertani agar and broth were purchased from MB cells (Seoul, Korea). Strains of Escherichia coli (11775) were procured from the American Type Culture Collection, USA (ATCC). Penicillin–streptomycin was purchased from Gibco BRL (Carlsbad, CA, USA). Terephthalic acid and sodium hydroxide were purchased from Sigma Aldrich. Genomic DNA extraction and RNA extraction were done through a DNA extraction kit (GeneAll, Exgene Cell SV MAXI, Banseok Bld, Seoul, Korea) and a RNA extraction kit (RNeasy Mini Kit, Qiagen). cDNA synthesis was performed using the ReverTra Ace qPCR RT Master Mix with gDNA Remover kit (Toyobo, Japan), and quantitative PCR was performed using a Thunderbird Sybr® qPCR Mix kit (Toyobo, Japan).
Plasma device and characterizations
The APPJ that was used consists of a needle-type powered (stainless steel) electrode that is enclosed by a quartz tube with inner diameter of 3 mm, outer diameter of 5 mm, and length of 9 mm. We used different flow rates of N2 gas in combination with different flow rates of H2O/HNO3 solution, so that the final gas flow rate remains 1000 cubic centimeters per minute (ccm). We applied an input voltage of 70 V, yielding an electrical power of about 7 W (2.2 kV, 11 mA with phase angle of 60° between current and voltage). The N2 gas flow rate directly introduced into the plasma was varied between 200 and 1000 ccm. Accordingly, the amount of N2 flowing through the solution of DI water with 0.5, 1 or 3 wt% HNO3, to generate H2O/HNO3 vapor that was fed into the plasma, also varied from 200 to 800 ccm. The combined gas (i.e., gas with vapor or without vapor) was injected into the needle of the plasma jet, and was flowing out through a 1 mm hole, as shown in Fig. 1a. Spectra of the APPJ emission were recorded by HR4000CG-UV-NIR (Ocean Optics, FL, USA) over a wide wavelength range (200–1100 nm), for a humidity of 40%. The electron temperature was measured from the emission spectrum using the SPEAC air program.
Physical and chemical characterization of plasma treated water (PTW)
After exposing the water samples for 10 min to either N2, N2 + H2O vapor or N2 + HNO3 vapor plasma (at different wt% of HNO3, i.e., 0.5, 1 and 3 wt%), the pH and temperature of the sample were measured by a pH meter (Eutech Instruments, Singapore) and an Infrared (IR) camera (Fluke Ti100 Series Thermal Imaging Cameras, UK). Simultaneously, the RONS contents in the water samples were also analyzed. The amounts of OH and H2O2 were measured by previously described methods32,33. The concentration of NO2− was measured using the Griess reagent kit (Molecular probe, USA) and the NO3− concentration was measured with an Acorn ion Meter (Oakton WD-WD-35613-30 Ion 6 meter).
To prepare the PTW, 2 ml of DI water was treated with plasma for 10 min in a 12-well plate, keeping 5 mm distance between the nozzle of the plasma jet device and the liquid surface. To determine the colony forming unit, gene expression, cell morphology and DNA damage, we used 1 ml PTW generated by the different plasma conditions, i.e., N2, N2 + H2O vapor, and N2 + 0.5 wt% HNO3 vapor. The reason why we used the 0.5 wt% HNO3 vapor in our further experiments on the antibacterial efficacy (instead of 1 and 3 wt%) is explained below.
Colony forming unit and disc diffusion assay
Strains of Escherichia coli (E. coli) were cultured in Luria broth (LB) media, until they reached the logarithmic growth phase of approximately 108 colony forming unit (CFU)/ml. To determine the CFU, the culture was incubated for 12 h at 37 °C, and shaken at 200 rpm. Aliquots of the culture (100 µl) were pelleted by centrifugation at 5000 rpm for 5 min. The pellet was resuspended in 1 ml of PTW prepared by N2, N2 + H2O vapor, and N2 + 0.5 wt% HNO3 vapor plasma, to determine the antimicrobial effects. The suspension was incubated for 3 h at room temperature, and shaken at 200 rpm. We also performed direct plasma treatment, for which we took the same growth phase of E. coli in 1 ml of water, and directly exposed it for 10 min with either N2, N2 + H2O vapor, or N2 + 0.5 wt% HNO3 vapor plasma. Both the indirect and direct plasma treated samples were subjected to serial dilutions of 107, 106, 105, 104, and 103 CFU/ml. The samples were thoroughly mixed, and a tenfold serial dilution of each sample was transferred and spread uniformly on LB agar culture medium in a standard Petri dish (90 mm). The samples were then sealed and incubated at 37 °C for about 12 h, to count the CFUs. We measured a relative reduction compared to the control sample (for which the CFU was defined as 1 to evaluate the inactivation efficacy.
In addition, we performed another experiment on Disc diffusion to assess the antibacterial activity of the PTW, for which the antimicrobial susceptibility testing was carried out according to the standard method by Bauer et al.34. The E. coli culture was evenly applied to LB agar culture plates using a sterile swab. The plates were dried for 15 min, and subsequently used for the sensitivity test. The discs that were impregnated with PTW produced by N2, N2 + H2O and N2 + 0.5 wt% HNO3 vapor were placed on the LB agar surface. One positive control, which was a disc, contained 30 µg of standard commercial antibiotic (Penicillin). The plate was then incubated at 37 °C for 18 to 24 hours. After incubation, the plates were examined for the inhibition zone.
E. coli morphological analysis
Scanning electron microscopy (SEM) (JSM 7001 F, JEOL, Tokyo, Japan) was applied to examine the morphology of the E. coli cells. Briefly, the bacterial samples exposed to PTW generated by either N2, N2 + H2O vapor, or N2 + 0.5 wt% HNO3 vapor were fixed in 1 mL of Karnovsky’s fixative (2% paraformaldehyde and 2% glutaraldehyde) overnight, as described in previous work5. The SEM sample preparation involved dehydration of the material in hexamethyldisilazane (HMDS), followed by mounting and coating on glass with carbon tape, and examination via SEM.
RNA extraction for quantitative real time PCR
To perform a quantitative evaluation of oxidative related gene expression, after 3 h exposure with PTW produced by N2, N2 + H2O and N2 + 0.5 wt% HNO3, the total RNA was extracted from treated and untreated samples of E. coli using an RNeasy Mini Kit, and it was converted to cDNA using reverse transcriptase and random primers (GoScriptTM Reverse Transcription System, Promega). The same amount of total RNA was used for the cDNA synthesis (Take3, Biotek). The resulting cDNA was used for the qPCR analysis (CFX96, Biorad) with primers (Macrogen) of 16 s rRNA (the RNA component of the small subunit used as house-keeping gene), OxyR, RpoE, GroES, and DnaK.
The primer sequences used for the oxidative related mRNA expression in E. coli were:
|Genes||Forward primers [5-3]||Reverse primers [5-3]|
DNA extraction for agarose gel electrophoresis
Genomic DNA was extracted after 3 h exposure with PTW produced by N2, N2 + H2O and N2 + 0.5 wt% HNO3 for 1% agarose analysis. The treated cells were subjected to a genomic DNA extraction kit. Genomic DNA was extracted following a standard molecular biology protocol, and re-suspended in 50 µl water. The same amount of genomic DNA (2 mg) extracted from E. coli was loaded on a 1% agarose gel, and run for 1 h. After staining with ethidium bromide, the DNA bands were photographed.
All values are represented as the mean ± SD of the indicated number of replicates. Statistical analysis of the data was performed using the Student’s t-test to establish the significance between the data points, and significant differences are based on *P < 0.05 or **P < 0.01.
Determination of NO and OH intensities at H2O vapor plasma condition
Figure 1(b) shows the NO and OH relative intensities during the plasma discharge, as a function of the applied voltage. Applying 70 V input voltage shows the high intensity of both NO and OH peaks measured through optical emission spectroscopy. Therefore, our further experiments were performed at an input voltage of 70 V. In order to evaluate the highest generation of OH radicals, we applied different flow rates of N2 gas in H2O solution, i.e., 400, 500, 600, 700, and 800 ccm, to generate the H2O vapor along with the N2 gas, and we examined the emission spectra of the plasma. Figure 1(c) shows that the OH emission peak was highest at 600 ccm of N2 gas flow.
Determination of NO and OH intensities at HNO3 vapor plasma conditions
We applied different wt% HNO3 (0.5, 1 and 3 wt%) with a fixed N2 gas flow rate, and we also compared with no HNO3 vapor. Figure 2(a) shows that 1 and 3 wt% of HNO3 vapor yields a high spectral intensity for NO, whereas Fig. 2(b) shows that 0.5 wt% of HNO3 vapor yields a high OH intensity. The further experiments are performed using 0.5 wt% HNO3 vapor plasma, based on the change in pH of the solution after treatment (as described below).
We also analyzed the NO spectra for different flow rates of N2 + 0.5 wt% HNO3 vapor plasma. Figure 2(c) shows that N2 with 600 ccm added to 0.5 wt% HNO3 solution vapor, combined with 400 ccm of N2 gas, resulted in a higher NO intensity, in comparison with 800 ccm N2 added to 0.5 wt% HNO3 solution vapor, combined with 200 ccm of N2 gas. Finally, the electronic temperature in the plasma generated at N2 (400 ccm) +0.5 wt% HNO3 vapor (with 600 ccm N2 gas) was determined to be 6110 K using Specair, as shown in Fig. 2(d).
Determination of pH and temperature after plasma exposure
To determine the change in properties of PTW after exposure with plasma, we checked the pH and temperature for different conditions, i.e., N2 (400 ccm) + (0.5, 1 or 3 wt%) HNO3 vapor (in 600 ccm N2 gas) plasma, N2 (400 ccm) + H2O vapor (in 600 ccm N2 gas) plasma, and N2 (1000 ccm) plasma without vapor. Figure 3(a) shows that 10 min treatment with plasma of N2 (400 ccm) + (0.5, 1 and 3 wt%) HNO3 vapor (in 600 ccm N2 gas) drastically decreases the pH, as compared with N2 + H2O vapor plasma and N2 plasma without vapor. On the other hand, there is only a slight rise in temperature (few °C) of PTW for N2 (400 ccm) + (0.5, 1 and 3 wt%) HNO3 or H2O vapor (in 600 ccm N2 gas) plasma, while there is a significant rise of about 10 °C for the N2 plasma without vapor, as shown in Fig. 3(b).
Estimation of RONS contents in plasma treated water
We have also measured the concentration of various RONS generated in the solutions after exposure to plasma at different conditions, i.e., N2 (400 ccm) + (0.5, 1 and 3 wt%) HNO3 or DI water vapor (in 600 ccm N2 gas), and 1000 ccm N2 gas without vapor. Figure 4(a) shows that 10 min treatment by N2 + H2O vapor plasma yields a higher amount of OH species in the solution, compared with N2 + (0.5, 1, and 3 wt%) HNO3 vapor plasma, and especially compared with the pure N2 plasma. The OH radicals are the main source of H2O2, and Fig. 4(b) indeed illustrates that the N2 + H2O vapor plasma produced the highest concentration (0.9 mM) of H2O2, while the N2 + HNO3 (0.5, 1, and 3 wt%) vapor plasma yielded H2O2 concentrations of ≈0.8, 0.7 and 0.6 mM, respectively, and the pure N2 plasma produced only 0.3 mM of H2O2. Among the different HNO3 vapor plasmas, the 0.5 wt% of HNO3 plasma generated the highest H2O2 concentration.
For NO, we found the opposite results as for the OH radicals and H2O2, i.e., a higher amount of NO was observed for N2 + (0.5, 1, and 3 wt%) HNO3 vapor plasma, as compared to the pure N2 plasma and the N2 + H2O vapor plasma, as shown in Fig. 4(c). This is logical, because the HNO3 vapor generates more NO upon dissociation, both in gas and liquid phase. For the same reason, NO2− and NO3− showed similar results: the N2 + HNO3 vapor plasma (at different wt%) yields higher NO2− and NO3− concentrations, as compared to the pure N2 plasma and the N2 + H2O vapor plasma, as shown in Fig. 4(d,e). The 3 wt% HNO3 vapor system produced the highest amounts of NO, NO2− and NO3−.
Although 3 and 1 wt% HNO3 vapor produces more RNS in comparison to 0.5 wt% HNO3 vapor, the exposed water at these conditions becomes much more acidic, as shown in Fig. 3a. Hence, to avoid the effect of pH in bacterial inactivation, we have chosen the N2 + 0.5 wt% HNO3 vapor plasma system for the further research.
Efficacy of PTW generated with N2, N2 + H2O vapor and N2 + 0.5 wt% HNO3 vapor plasma in E. coli inactivation, and comparison with direct plasma treatment
To determine the efficacy of PTW produced by N2, N2 + H2O vapor, and N2 + 0.5 wt% HNO3 vapor plasma, we checked the E. coli inactivation after 3 h incubation. Figure 5(a,b) show that exposure with PTW generated in case of 0.5 wt% HNO3 vapor has a higher effect on E. coli inactivation, as its CFU reduces by 5 log values. The pure N2 generated PTW reduces the CFU by 2 log values, while the PTW generated by N2 + H2O vapor reduces the CFU by 4 log values. In comparison, PTW exposed to N2, N2 + H2O vapor, and N2 + 0.5 wt% HNO3 vapor gas flow (i.e., without plasma) has no effect on E. coli inactivation (Fig. 5(c)), which indicates that the effects are clearly due to the RONS created by the plasma. Figure 5(d,e) show similar results in the disc diffusion assay: PTW created by N2 + 0.5 wt% HNO3 vapor has a higher zone of inhibition, in comparison with N2 PTW and N2 + H2O PTW.
To confirm this result, we also used the standard antibiotics agent (Penicillin) to check the zone of inhibition, and the results reveal that PTW created by N2 + 0.5 wt% HNO3 vapor has strong ability for zone of inhibition similar to Penicillin but higher as compare to N2 + H2O PTW. Furthermore, we checked the effect of direct plasma action on E. coli. Figure S1 shows that direct treatment by N2 + 0.5 wt% HNO3 vapor plasma leads to significant inactivation of E. coli, in comparison with N2 plasma and N2 + H2O vapor plasma treatments. Hence, both direct and PTW treatment using N2 + 0.5 wt% HNO3 vapor plasma results in the maximum inactivation of E. coli.
Analysis of oxidative stress related gene expression and disruption of E. coli cell morphology
To elucidate the mechanism of action of PTW on E. coli inactivation, we analyzed the oxidative related gene expression and cell morphology. For the gene expression analysis, we chose four oxidative stress genes, i.e., OxyR (Oxygen regulated gene), RpoE (DNA-dependent RNA polymerase), GroES (Heat-shock gene), and DnaK (Chaperone protein DnaK). These proteins regulate under stress conditions, and help to protect the cells through antioxidant defense mechanisms35,36,37,38. OxyR and DnaK genes relates to oxidative stress. GroES and DnaK genes relates to the cellular homeostasis39,40. The failure of the antioxidant defense machinery under high oxidative stress may lead to inhibitory effects of these gene expressions (OxyR, DnaK, GroES and DnaK) that results in DNA damage. Figure 6(a) shows that 3 h incubation of PTW generated by N2 + H2O vapor or 0.5 wt% HNO3 vapor caused higher inhibitions of the gene expression as compared with N2 generated PTW. In contrast, PTW generated by N2 + H2O or 0.5 wt% HNO3 vapor shows inhibition of these gene expressions, because the oxidative stress is above the threshold under these PTW treatments, resulting in collapse of the antioxidant defense machinery.
We also determined the effects of PTW on the morphology of E. coli. Figure 6(b) shows that PTW generated by N2 + H2O vapor and by N2 + 0.5 wt% HNO3 vapor has crumpled the cells to a greater extent than N2 PTW. Finally, we checked the genomic DNA damage through 1% gel electrophoresis. Figures 6(c) and S2 shows that PTW generated by N2 + H2O vapor and N2 + 0.5 wt% HNO3 vapor have more effect on the DNA degradation/oxidation.
It is generally known that RONS generated from an APPJ induce inactivation of microorganisms, as well as structural changes in proteins5,32. In this work, we demonstrate that the adding a vapor system (either water vapor or 0.5 wt% of HNO3 vapor) to the plasma enhances the antimicrobial activity as compared to plasma without vapor system. This is attributed to the increase in ROS and RNS content. The H2O vapor system increases the ROS in the solution, but the RNS formation does not increase, whereas the HNO3 vapor system can increase both the RNS and ROS content in solution. We analyzed the NO and OH species by optical emission spectrometry in the gas phase and by chemical analysis in the solution, after 10 min plasma treatment. The NO radical concentration dramatically increases inside the solution for plasma treatment with N2 (400 ccm) + 0.5 wt% HNO3 vapor (600 ccm N2 gas), as compared to pure N2 plasma treatment or treatment by N2 + H2O vapor. At this condition, both the NO and OH concentrations increase in the gas phase, as well as inside the solution. On the other hand, for the water vapor system, the OH content increases by a large amount, but the NO concentration did not increase in solution, as shown in Fig. 4.
We measured the transcriptional level of these genes (OxyR, RpoE, GroES, and DnaK) in PTW-treated E. coli. When E. coli was treated with N2 PTW, the transcriptional-related gene expressions of OxyR, RpoE, GroES, and DnaK were enhanced (Fig. 6(a)). In contrast, the N2 + H2O or 0.5 wt% HNO3 PTW showed inhibitory effects on the gene expression in comparison with the control sample. Furthermore, N2 + 0.5 wt% HNO3 PTW showed higher inhibition effect than N2 + H2O PTW, which can be explained by the higher RONS content. This study clearly shows that PTW generated by N2 + H2O vapor or 0.5 wt% HNO3 vapor plasma has higher RONS contents, which lead to bacteria killing through inhibition of the antioxidant machinery, which damages the membrane protein repair chaperone, as well as DNA repair cascade41,42. Furthermore, we analyzed the DNA degradation through gel electrophoresis and the bacteria morphology, after treatment with PTW generated by all plasma systems. Among all systems (N2 plasma, N2 + H2O vapor plasma, and N2 + 0.5 wt% HNO3 vapor plasma), the PTW generated by N2 + 0.5 wt% HNO3 vapor plasma shows more E. coli deactivation.
This study demonstrates that PTW produced from N2 + H2O vapor plasma and N2 + 0.5 wt% HNO3 vapor plasma systems has a high antibacterial efficiency. According to literature, NO2− and H2O2 are important for the bactericidal activity21. At our experimental conditions, the N2 plasma produces ≈0.02 mM NO2− and ≈0.3 mM H2O2, while the N2 + H2O vapor plasma produces ≈0.025 mM NO2− and ≈0.9 mM H2O2, and the N2 + 0.5 wt% HNO3 vapor plasma produces ≈ 0.076 and 0.8 mM of NO2− and H2O2, respectively. Thus, the maximum NO2− and H2O2 concentrations are produced by the N2 + 0.5 wt% HNO3 vapor plasma and the N2 + H2O vapor plasma, respectively. If we compare the bactericidal activity in Fig. 5, we observe the maximum deactivation of bacteria for the PTW generated by the N2 + 0.5 wt% HNO3 vapor plasma, followed by the N2 + H2O vapor plasma, and the smallest effect for the N2 plasma PTW. This shows that a high concentration of both NO2− and H2O2 plays a key role in sterilization. It was reported previously that the presence of H2O2 and HNO2 produces ONOO−, which is the main component for inactivation of bacteria28. However, ONOO− has a short lifetime in acidic solution, and therefore it cannot be the main component of PTW for the antibacterial activity26,30. On the other hand, Ikawa et al. reported that O2•− is mainly responsible for the bactericidal activity31. The authors also claimed that the production of O2•− does not require the presence of oxygen, as it is generated by O2NOOH. They also suggested that H2O2 is the main component for the production of O2NOOH in PTW along with NO2−. Therefore, we may conclude that the N2 + 0.5 wt% HNO3 vapor plasma produces the highest amount of NO2− and H2O2 in PTW, which can form O2NOOH by multiple reactions, and this further leads to the formation of O2•− which contributes to sterilization. On the other hand, the N2 + H2O vapor plasma produces a high amount of H2O2 but a lower content of NO2−; and this results in a lower production of O2•−, and thus in a lower antibacterial activity. Additionally, the pH of PTW after N2 + 0.5 wt% HNO3 vapor plasma and N2 + H2O vapor plasma is near 4.5, and it was reported that the half-life of O2NOOH is 1.6 min at pH 4.743. Hence, we believe that in our study O2NOOH is the main factor for the bactericidal activity through O2•− formation.
We studied the antibacterial effect of PTW generated by various plasma systems, i.e., N2 plasma, N2 + H2O vapor plasma, and N2 + 0.5 wt% HNO3 vapor plasma, and we clear demonstrated that the vapor plasma, and especially the N2 + 0.5 wt% HNO3 vapor plasma, was more efficient for the deactivation of bacteria than PTW generated by plasma without vapor system. The results of this research support the idea that a high concentration of both NO2− and H2O2 is important for the antibacterial activity, through the creation of other RONS, such as O2NOOH and O2•−.
Moreau, M. et al. Non-thermal plasma technologies: New tools for bio-decontamination. Biotechnol Adv. 26, 610–617 (2008).
Cheng, H. H. et al. Non-thermal plasma technology for degradation of organic compounds in wastewater control: Acritical review. J. Environ. Eng. Manage 17, 427–433 (2007).
Attri, P. et al. Impact of Gamma rays and DBD plasma treatments on wastewater treatment. Sci Rep. 8, 2926 (2018).
Ehlbeck, J. et al. Low temperature atmospheric pressure plasma sources for microbial decontamination. J. Phys. D: Appl. Phys. 44, 013002 (2010).
Park, J. H. et al. A comparative study for the inactivation of multidrug resistance bacteria using dielectric barrier discharge and nano-second pulsed plasma. Sci Rep. 5, 13849 (2015).
Attri, P. et al. Influence of reactive species on the modification of biomolecules generated from the soft plasma. Sci Rep. 5, 8221 (2015).
Laroussi, M. Low temperature plasma‐based sterilization: overview and state‐of‐the‐art. Plasma Process. Polym. 2, 391–400 (2005).
Xu, G. M. et al. Dual effects of atmospheric pressure plasma jet on skin wound healing of mice. Wound Repair Regen. 23, 878–884 (2015).
Bekeschus, S. et al. Human mononuclear cell survival and proliferation is modulated by cold atmospheric plasma jet. Plasma Process. Polym. 10, 706–713 (2013).
Wende, K. et al. Atmospheric pressure plasma jet treatment evokes transient oxidative stress in HaCaT keratinocytes and influences cell physiology. Cell Biol Int. 38, 412–425 (2014).
Fathollah, S. et al. Investigation on the effects of the atmospheric pressure plasma on wound healing in diabetic rats. Sci Rep. 6, 19144 (2016).
Lee, J.-H. et al. Effect of non-thermal air atmospheric pressure plasma jet treatment on gingival wound healing. J. Phys. D: Appl. Phys. 49, 075402 (2016).
Kumar, N. et al. Influence of Nitric Oxide generated through microwave plasma on L6 skeletal muscle cell myogenesis via oxidative signaling pathways. Sci Rep. 7, 542 (2017).
Kumar, N. et al. Induced apoptosis in melanocytes cancer cell and oxidation in biomolecules through deuterium oxide generated from atmospheric pressure non-thermal plasma jet. Sci Rep. 4, 7589 (2014).
Van Boxem, W. et al. Anti-cancer capacity of plasma-treated PBS: effect of chemical composition on cancer cell cytotoxicity. Sci Rep. 7, 16478 (2017).
Kumar, N. et al. Influence of water vapour with non-thermal plasma jet on the apoptosis of SK-BR-3 breast cancer cells. RSC Adv. 5, 14670–14677 (2015).
Mohades, S. et al. Evaluation of the effects of a plasma activated medium on cancer cells. Phys. Plasmas. 22, 122001 (2015).
Boehm, D. et al. Cytotoxic and mutagenic potential of solutions exposed to cold atmospheric plasma. Sci Rep. 6, 21464 (2016).
Kumar, N. et al. The action of microsecond-pulsed plasma-activated media on the inactivation of human lung cancer cells. J. Phys. D: Appl. Phys. 49, 115401 (2016).
Adachi, T. et al. Plasma-activated medium induces A549 cell injury via a spiral apoptotic cascade involving the mitochondrial–nuclear network. Free Radic Biol Med. 79, 28–44 (2015).
Shen, J. et al. Bactericidal Effects against S. aureus and Physicochemical Properties of Plasma Activated Water stored at different temperatures. Sci Rep. 6, 28505 (2016).
Reuter, S. et al. Generation of atomic oxygen in the effluent of an APPJ. Plasma Sources Sci. Technol. 18, 015006 (2009).
Glaze, W. H. et al. The Chemistry of water treatment processes involving ozone, hydrogen peroxide and ultraviolet radiation. Ozone Sci. Eng. 9, 335–352 (1987).
Sun, P. et al. Inactivation of Bacillus subtilis Spores in Water by a Direct‐Current, Cold Atmospheric‐Pressure Air Plasma Microjet. Plasma Process. Polym. 9, 157–164 (2012).
Traylor, M. J. et al. Long-term antibacterial efficacy of air plasma-activated water. J. Phys. D: Appl. Phys. 44, 472001 (2011).
Zhang, Q. et al. A study of oxidative stress induced by non-thermal plasma-activated water for bacterial damage. Appl. Phys. Lett. 102, 203701 (2013).
Machala, Z. et al. Formation of ROS and RNS in water electro‐sprayed through transient spark discharge in air and their bactericidal effects. Plasma Process. Polym. 10, 649–659 (2013).
Lukes, P. et al. Aqueous-phase chemistry and bactericidal effects from an air discharge plasma in contact with water: evidence for the formation of peroxynitrite through a pseudo-second-order post-discharge reaction of H2O2 and HNO2. Plasma Sources Sci. Technol. 23, 015019 (2014).
Oehmigen, K. et al. Estimation of possible mechanisms of Escherichia coli inactivation by plasma treated sodium chloride solution. Plasma Process. Polym. 8, 904–913 (2011).
Naïtali, M. et al. Combined effects of long-living chemical species during microbial inactivation using atmospheric plasma-treated water. Appl. Environ. Microbiol. 76, 7662–7664 (2010).
Ikawa, S. et al. Physicochemical properties of bactericidal plasma-treated water. J. Phys. D: Appl. Phys. 49, 425401 (2016).
Attri, P. et al. The protective action of osmolytes on the deleterious effects of gamma rays and atmospheric pressure plasma on protein conformational changes. Sci Rep. 7, 8698 (2017).
Park, J. H. et al. Variation in structure of proteins by adjusting reactive oxygen and nitrogen species generated from dielectric barrier discharge jet. Sci Rep. 6, 35883 (2016).
Bauer, A. et al. Antibiotic susceptibility testing by a standardized single disk method. Am J Clin Pathol. 45, 493 (1966).
Kilstrup, M. et al. Induction of Heat Shock Proteins DnaK, GroEL, and GroES by Salt Stress in Lactococcus lactis. Appl. Environ. Microbiol. 63, 1826–1837 (1997).
Wang, A. & Crowley, D. E. Global Gene Expression Responses to Cadmium Toxicity in Escherichia coli. J. Bacteriol. 187, 3259–3266 (2005).
Mongkolsuk, S. & Helmann, J. D. Regulation of inducible peroxide stress responses. Mol. Microbiol. 45, 9–15 (2002).
Hiratsu, K. et al. The rpoE Gene of Escherichia coli, Which Encodes sigma E, Is Essential for Bacterial Growth at High Temperature. J. Bacteriol. 177, 2918–2922 (1995).
Houry, W. A. Chaperone-assisted protein folding in the cell cytoplasm. Curr. Protein Pept. Sci. 2, 227–244 (2001).
Lin, Z. & Rye, H. S. GroEL-mediated protein folding: making the impossible, possible. Crit. Rev. Biochem. Mol. Biol. 41, 211–239 (2006).
Vatansever, F. et al. Antimicrobial strategies centered around reactive oxygen species–bactericidal antibiotics, photodynamic therapy, and beyond. FEMS Microbiol. Rev. 37, 955–989 (2013).
Pomposiello, P. & Demple, B. Global adjustment of microbial physiology during free radical stress. Adv. Microb. Physiol. 46, 19–341 (2002).
Kenley, R. A., Trevor, P. L. & Lan, B. Y. Preparation and thermal decomposition of pernitric acid (HOONO2) in aqueous media. J. Amer. Chem. Soc. 103, 2203–2206 (1981).
We gratefully acknowledge the Leading Foreign Research Institute Recruitment program (Grant # NRF-2016K1A4A3914113) throughout the Basic Science Research Program of the National Research Foundation (NRF) of Korea and in part by Kwangwoon University 2018. JHP thanks to NRF Grant No. NRF-2017R1D1A1B03033495. We also acknowledge financial support from the Research Foundation – Flanders (FWO) (Grant Number 12J5617N) and from the European Marie Skłodowska-Curie Individual Fellowship “Anticancer-PAM” within Horizon 2020 (Grant Number 743546).
The authors declare no competing interests.
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Shaw, P., Kumar, N., Kwak, H.S. et al. Bacterial inactivation by plasma treated water enhanced by reactive nitrogen species. Sci Rep 8, 11268 (2018). https://doi.org/10.1038/s41598-018-29549-6
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