1. Introduction
Microorganisms present in indoor environments constitute a persistent source of human exposure and play an important role in the transmission of infectious diseases [
1]. In particular, frequently touched environmental surfaces can act as reservoirs for pathogenic microorganisms, facilitating indirect transmission through fomites and increasing the risk of contact-mediated infection [
2]. This mode of transmission is relevant not only in domestic and communal living spaces but also in healthcare facilities, long-term care institutions, and educational settings, where environmental surface contamination has been implicated in outbreaks with substantial clinical and public health consequences [
3].
Recent evaluations by international public health authorities have emphasized the importance of managing surface-associated microorganisms in indoor environments as a critical component of infection prevention and control strategies [
4]. Accordingly, effective environmental interventions targeting contaminated surfaces are increasingly recognized as essential complements to established measures such as hand hygiene, personal protective equipment, and vaccination programs [
5].
Environmental surface decontamination is commonly achieved through the application of liquid disinfectants. However, only a limited number of chemical agents exhibit broad-spectrum antimicrobial activity [
6]. Moreover, widely used disinfectants, including sodium hypochlorite solutions and formaldehyde-based agents, are associated with notable drawbacks, such as mucosal irritation, corrosive effects on materials, and the potential release of harmful gases, which limit their suitability for continuous use in occupied indoor environments. In addition, surface disinfection relying on manual wiping procedures is inherently dependent on operator compliance and frequency of application, leading to variability in effectiveness [
7]. These limitations highlight the need for non-contact, continuously operating environmental control strategies that can be safely applied in occupied indoor spaces.
In response to these limitations, low-concentration gaseous and/or vaporized disinfectants have emerged as a promising alternative for the non-contact and continuous control of surface-associated microorganisms [
8]. Vaporized hypochlorous acid (HOCl) has been reported to inactivate a broad range of microorganisms, including bacteria and fungi, at concentrations considered safe for human exposure [
9,
10,
11,
12,
13,
14,
15,
16,
17]. Similar antimicrobial effects at low concentrations have also been demonstrated for chlorine dioxide gas [
18]. These findings suggest that oxidative gaseous agents may offer a practical approach to surface decontamination while avoiding many of the constraints associated with conventional liquid disinfectants. However, most previous studies have primarily focused on empirical antimicrobial efficacy, and virus-dependent differences in susceptibility under environmentally relevant indoor conditions remain insufficiently characterized.
At the molecular level, HOCl is a highly reactive electrophilic oxidant generated physiologically by the myeloperoxidase–hydrogen peroxide–chloride system during innate immune responses. Owing to its strong electrophilic characteristics, HOCl preferentially reacts with nucleophilic amino acid side chains, particularly sulfur-containing residues such as cysteine and methionine, as well as histidine, tyrosine, tryptophan, and lysine. These reactions result in oxidative modification, chlorination, and structural destabilization of proteins, potentially leading to loss of biological function. While these biochemical properties provide a plausible basis for viral inactivation, direct experimental evidence linking residue-level chemical reactivity to virus-specific susceptibility under low-concentration gaseous exposure remains limited. In addition, environmental parameters such as relative humidity and airflow dynamics are known to influence both viral persistence and the efficacy of gas-phase disinfectants [
9,
17], underscoring the importance of evaluating virucidal effects under realistic indoor environmental conditions rather than strictly controlled laboratory settings.
We previously developed a composite environmental control system combining a generator of vaporized free chlorine species with a fine-particle removal filter. Previous studies demonstrated that this system effectively reduced environmental bacterial contamination in real-world settings and inactivated bacteria inoculated onto plastic surfaces under laboratory conditions [
19]. While these investigations established the antibacterial performance of the system, its virucidal efficacy—particularly against surface-associated viruses relevant to contact transmission—has not yet been comprehensively evaluated. Furthermore, the molecular determinants underlying virus-dependent susceptibility to low-level oxidative exposure remain insufficiently understood. Integrating experimental virology with computational and structural approaches provides a useful framework for addressing this gap. Quantitative infectivity assays enable direct evaluation of viral inactivation, while computational fluid dynamics (CFD) simulations can characterize the spatial distribution of disinfectant exposure. In parallel, comparative analysis of viral protein composition and three-dimensional structural mapping of chemically reactive residues can offer mechanistic insights. However, such analyses are inherently inferential and should be interpreted as providing a plausible mechanistic framework rather than definitive biochemical proof.
In the present study, we investigated the virucidal activity of vaporized free chlorine components (HOCl) using three clinically important viruses: human adenovirus type 3 (HAdV3), echovirus type 30 (E30), and influenza A virus (A/H1N1)pdm09 (AH1pdm09). These viruses were selected as representative non-enveloped and enveloped viruses associated with environmental persistence and indirect transmission. Notably, all viruses used in this study were clinical isolates rather than laboratory-adapted prototype strains, thereby enhancing the relevance of the findings to real-world indoor environments.
We hypothesized that virus-dependent susceptibility to vaporized HOCl is influenced by residue-level chemical composition and structural accessibility of viral surface proteins. Specifically, differences in the abundance and spatial distribution of HOCl-reactive amino acid residues may affect the likelihood that low-concentration oxidative exposure leads to functionally disruptive structural modification. Accordingly, this study aimed not only to evaluate the virucidal efficacy of vaporized hypochlorous acid under real indoor conditions but also to explore potential molecular determinants underlying differential virus inactivation, while providing a mechanistic interpretation that remains to be further validated by direct biochemical approaches.
2. Materials and Methods
2.1. Experimental Setup for Surface Viral Inactivation Under Vaporized Free Chlorine Exposure
Surface-associated viral inactivation experiments were carried out in a practical training laboratory at Gunma Paz University. The room volume was 260 m3 (10 m × 9.3 m × 2.8 m) and included two air-conditioning outlets. Although three ventilation openings were present, the ventilation system was intentionally disabled to prevent external air exchange. Ambient temperature and relative humidity were controlled using an air-conditioning unit and a steam humidifier (T-fal Groupe SEB Japan K.K., Tokyo, Japan), maintaining ranges of 18.6–23.3 °C and 45–76%, respectively. All procedures were performed under unoccupied conditions. For the control setup, samples were placed within a sealed 16 L plastic container (Iwasaki Industry Inc., Yamato-Koriyama, Japan), where temperature and humidity were maintained at 18.8–23.3 °C and 15–72%, respectively. Two experimental devices were installed on one side of the laboratory and operated continuously for 24 h. Vaporized free chlorine component levels were continuously measured both at the device outlet and at the sample location at 10 s intervals using a chlorine gas detector (New Cosmos Electric Co., Ltd., Osaka, Japan), with values converted into equivalent chlorine gas concentrations. Environmental temperature and humidity at the sample location were recorded every 60 s by a Thermo Recorder (Sato Shouji Inc., Kawasaki, Japan). Although the reported environmental ranges represent aggregated variability across experiments, intra-experimental fluctuations within each 24 h period remained limited and stable.
2.2. Generation of Vaporized Free Chlorine Components
The system used in this study produced humidified airflow by passing air through a rotating fibrous medium saturated with electrolyzed water. Electrolyzed water was generated by dissolving sodium chloride tablets in tap water, followed by in situ electrolysis within the device. Hypochlorous acid, the primary active species, volatilized concurrently with water vapor and was released into the surrounding air as vaporized free chlorine components. Electrolyzed water containing approximately 100 mg/L of available chlorine was supplied to the rotating filter, and airflow was maintained at 5.6 m
3/min. This concentration (<100 mg/L) was selected based on prior optimization and occupational safety considerations to ensure adequate generation efficiency while maintaining safe exposure levels [
20]. Available chlorine concentrations were quantified using a chlorine meter (Kasahara Rika Kogyo Co., Ltd., Kuki, Japan). Preliminary validation experiments were conducted to define appropriate operational concentrations of vaporized free chlorine components. While the occupational exposure threshold for chlorine gas is 500 ppb, no formal standard exists for vapor-phase free chlorine components. Given that medical air sterilization systems typically operate below 0.1 ppm (100 ppb), the present system was designed within this safety margin. Continuous monitoring confirmed that operation of two devices within the 260 m
3 laboratory for 24 h maintained airborne concentrations at ≤9 ppb. These conditions were therefore adopted for subsequent viral inactivation experiments.
2.3. Viral Materials and Inactivation Assay
Three clinical viral isolates were used: human adenovirus type 3 (Ad3; Gunma/R6-108), echovirus 30 (E30; Gunma/H20-216), and influenza A virus (A/H1N1)pdm09 (A/Gunma/297/2024). Ad3 and E30 were propagated in HEp-2 and RD cells, respectively, whereas A/H1N1pdm09 was cultured in MDCK cells. Specifically, HEp-2 (ATCC CCL-23), RD (ATCC CCL-136), and MDCK (ATCC CCL-34) cell lines were used for virus propagation. All isolates were obtained from the Gunma Prefectural Institute of Public Health and stored at −80 °C until use. Immediately prior to experimentation, viral stocks were thawed, and 100 µL aliquots were applied onto culture dishes (AB2000, EIKEN CHEMICAL Co., Ltd., Chiyoda, Japan). An overview of the experimental setup is shown in
Figure 1. Samples were positioned 0.8 m above the floor and 8.0 m from the operating devices (Electrolyzed (+) condition). For the control condition (Electrolyzed (−)), samples were placed inside a sealed 16 L plastic container, designated as Electrolyzed (−). To replicate drying conditions while excluding vaporized chlorine exposure, silica gel (1.0 g) and a low-voltage fan (Panasonic Corporation, Osaka, Japan) were placed inside the container. The container was tightly sealed to eliminate external airflow. Comparable drying times between Electrolyzed (+) and Electrolyzed (−) conditions were confirmed in advance. This sealed container system was designed to standardize drying conditions while preventing exposure to vaporized free chlorine components, although it does not fully replicate open-room airflow dynamics and gas exchange conditions. The viral suspensions were simultaneously allowed to air-dry under identical environmental conditions during exposure to ensure uniform surface-associated conditions. After 24 h of exposure, all samples were recovered. To maximize recovery efficiency, the surface was gently rinsed and resuspended using a dry transport system. Each viral sample was resuspended in 1 mL of recovery medium (DMEM supplemented with 2% fetal bovine serum). From this suspension, 100 µL was transferred onto a culture dish and re-suspended using a dry transport system (25-806 1PR BT, Sugiyama-Gen Co., Ltd., Tokyo, Japan), then returned to the recovery medium. Viral titration was performed in 96-well plates. Five wells (
n = 5) were assigned to each sample and control. Serial dilutions were prepared, and host cells were inoculated accordingly. Ad3 and E30 were incubated at 37 °C with 5% CO
2, whereas A/H1N1pdm09 was incubated at 34 °C with 5% CO
2. The 50% tissue culture infectious dose (TCID
50) values were calculated based on the presence or absence of cytopathic effects (CPEs) in each well using the Kärber method. CPEs were independently evaluated by two researchers using light microscopy, and wells were classified as either CPE-positive or CPE-negative based on morphological alterations consistent with virus-induced cytopathology. The assessments were not performed under blinded conditions.
2.4. Computational Simulation of Free Chlorine Dispersion
To characterize the transport and spatial distribution of vaporized free chlorine components, time-resolved simulations were conducted using proprietary computational fluid dynamics (CFD) technology. Simulations were performed with a three-dimensional structured grid model (STREAM V2025.1), incorporating airflow velocity, direction, and outlet concentration, as well as air-conditioning parameters. The diffusion coefficient was set to 1.21 × 10
−5 m
2/s. Processes contributing to concentration decay—including wall adsorption, ventilation removal, and chemical decomposition—were incorporated into the transient model. The governing equations included mass conservation and Navier–Stokes equations, with turbulence represented using the standard k–ε model. Mesh resolution was defined with a base size of 80 mm, with localized refinement in regions exhibiting steep gradients. Boundary conditions included inflow/outflow parameters consistent with experimental conditions and no-slip wall boundaries. Temporal concentration changes were visualized using contour mapping to illustrate spatial distribution dynamics. These loss processes were individually parameterized based on experimentally measured values [
21].
2.5. Three-Dimensional Antigenic Structure and Mapping of Hypochlorous Acid-Reactive Amino Acid Residues
To elucidate the molecular basis of microbial inactivation by hypochlorous acid (HOCl), it is essential to characterize chemical modifications at the amino acid level [
22]. HOCl preferentially reacts with susceptible side chains—particularly cysteine, methionine, histidine, tyrosine, tryptophan, and lysine—leading to oxidative modification, chlorination, and structural destabilization of antigenic proteins [
23]. Mapping these reactive residues onto three-dimensional (3D) antigenic structures enables mechanistic interpretation of protein denaturation, epitope alteration, and potential loss of infectivity. Representative surface antigen proteins of the target microorganisms were selected based on their structural and immunological relevance. Based on the selected template sequences, three-dimensional structural models were constructed using Modeller version 10.4 [
24]. The corresponding Protein Data Bank (PDB) identifiers and GenBank accession numbers of all template structures are provided in
Supplementary Table S1 to ensure reproducibility. The generated models were subsequently inspected and evaluated using WinCoot (version 0.9.8.93) [
25], and the model exhibiting the most favorable scoring metrics was selected as the optimal structure. Further structural refinement was performed through energy minimization using Swiss-PdbViewer (version 4.1.0) [
26]. Structural quality was assessed prior to downstream analysis. HOCl-reactive amino acid residues were identified based on established chemical susceptibility profiles reported in the literature. Residue-specific reactivity was annotated according to known oxidation and chlorination pathways. The spatial distribution of these residues was analyzed to determine their localization within functional domains, receptor-binding regions, and antigenic epitopes. Three-dimensional visualization and residue mapping were performed using PyMOL (version 2.5.8) (Schrödinger, LLC, New York, NY, USA) [
27]. Reactive amino acid residues were highlighted using color-coded surface and cartoon representations to distinguish highly susceptible residues from less reactive or structurally buried residues. Structural regions corresponding to antigenic epitopes were annotated where experimentally defined or inferred from prior reports. This integrative structural mapping approach enabled the correlation of HOCl-induced chemical reactivity at the amino acid level with conformational integrity of antigenic proteins, thereby providing mechanistic insight into microbial inactivation.
2.6. Statistical Analysis
Statistical analyses of viral infectivity were performed using EZR version 4.3.1 (Easy R; Jichi Medical University, Shimotsuke, Japan). Because viral titers typically follow a log-normal distribution, data were transformed to log10 values for descriptive analyses and outlier assessment. Outliers were identified using the interquartile range (IQR) method, in which values falling below Q1 − 1.5 × IQR or above Q3 + 1.5 × IQR on the log10 scale were considered extreme and excluded from subsequent analyses. However, given the relatively small sample sizes (n = 5–9), additional analyses including all data points without outlier exclusion were performed to assess robustness. Both analyses (with and without outlier exclusion) were compared, and consistent results were obtained. Group comparisons were conducted using the Mann–Whitney U test. The proportion of the target amino acid residues in each viral protein was calculated as the number of specific residues divided by the total number of amino acid residues in the corresponding protein. Differences in proportions among the four viral proteins were evaluated using a generalized linear model (GLM) with a binomial distribution and logit link function. An omnibus likelihood ratio test was first performed to assess whether the proportions differed among proteins. When a significant overall difference was detected, pairwise comparisons were conducted using the GLM framework, and odds ratios (ORs) with 95% confidence intervals (CIs) were calculated. Multiple comparisons were adjusted using the Holm method. Confidence intervals were calculated using the Wilson score method. Statistical significance was defined as p < 0.05.
2.7. Ethics Status
The viral strains used in this study were clinical isolates obtained through the National Epidemiological Surveillance of Infectious Diseases (NESID) program in Japan, conducted under the Act on the Prevention of Infectious Diseases and Medical Care for Patients with Infectious Diseases (Infectious Diseases Control Law). These specimens were collected as part of routine public health surveillance and were not newly collected for research purposes. All samples were fully anonymized prior to their use, and no personally identifiable information was included. Accordingly, this study represents the secondary use of surveillance-derived specimens. The use of such specimens for research purposes is conducted in accordance with the Infectious Diseases Control Law and the Ethical Guidelines for Medical and Health Research Involving Human Subjects in Japan. Within this framework, the requirement for written informed consent was waived by the Medical Research Ethics Committee of Gunma Paz University, and verbal informed consent was obtained as appropriate within routine public health surveillance practices. This study was reviewed and approved by the Medical Research Ethics Committee of Gunma Paz University (Approval No. PAZ25-50, approved on 25 February 2026).
4. Discussion
The present study demonstrates that vaporized free chlorine, primarily in the form of hypochlorous acid (HOCl), exerts virus-dependent inactivation effects under environmentally relevant indoor conditions. Significant reductions in infectious titers were observed for echovirus 30 (E30) and influenza A/H1N1, whereas no statistically significant reduction was detected for human adenovirus type 3 (HAdV3). Computational fluid dynamics (CFD) simulations and gas-sensor measurements indicated that vaporized free chlorine was broadly distributed throughout the experimental room, reaching locations approximately 8.0 m from the device. These findings suggest that the observed differences in virucidal efficacy are unlikely to be solely attributable to insufficient exposure at the sampling location; however, spatial heterogeneity within the indoor environment, including potential dead zones and localized airflow variations, cannot be completely excluded.
A key finding of this study is that viral susceptibility to vaporized HOCl cannot be explained solely by the presence or absence of a lipid envelope. While influenza A virus is enveloped and may be susceptible to oxidative disruption of membrane lipids, echovirus 30—an unenveloped virus—also exhibited substantial inactivation. In contrast, human adenovirus type 3, which is likewise non-enveloped, demonstrated relative resistance. These observations indicate that envelope status alone is insufficient to explain the differential susceptibility and suggest that intrinsic structural and molecular features of viral particles play a critical role.
One plausible explanation for these differences lies in the chemical reactivity of viral proteins. HOCl is a highly reactive electrophilic oxidant that preferentially modifies nucleophilic amino acid side chains, including cysteine, methionine, histidine, tyrosine, tryptophan, and lysine [
22,
23]. Oxidative modification of these residues can lead to alterations in protein conformation, disruption of intermolecular interactions, and loss of functional activity, including receptor binding and membrane fusion. In the present study, adenoviral penton and hexon proteins exhibited significantly lower proportions of HOCl-reactive residues compared with influenza A hemagglutinin, whereas E30 VP1 showed intermediate values. These compositional differences are consistent with the observed pattern of viral susceptibility. However, it is important to emphasize that this relationship should be interpreted as correlative rather than demonstrating a direct causal mechanism linking residue composition to viral inactivation.
Structural considerations further support this interpretation. Adenoviruses possess a highly stable icosahedral capsid composed of hexon and penton proteins arranged in a rigid lattice structure, which may confer resistance to chemical perturbation. In contrast, influenza A hemagglutinin and enteroviral VP1 are surface-exposed proteins that undergo dynamic conformational rearrangements during viral entry. Three-dimensional structural mapping in this study demonstrated that HOCl-reactive residues in HA and VP1 tend to cluster in surface-accessible and functionally relevant regions, whereas such residues are less abundant and more structurally constrained in adenoviral capsid proteins. These structural observations provide a plausible mechanistic framework for differential susceptibility; however, they do not constitute direct experimental proof of the inactivation mechanism.
An important practical implication of this study is that substantial viral inactivation was achieved at airborne concentrations in the low parts-per-billion range, which is well below established occupational exposure limits for chlorine gas [
20]. This finding suggests that vaporized HOCl may represent a feasible approach for continuous environmental control of pathogens in occupied indoor environments, balancing antimicrobial efficacy with safety considerations.
The present study was intentionally designed to evaluate virucidal effects under realistic indoor environmental conditions rather than strictly controlled laboratory settings. Accordingly, environmental parameters such as relative humidity (RH) were allowed to vary within practical ranges. RH is known to influence both viral persistence on surfaces and the efficacy of gas-phase disinfectants [
9,
17], and therefore represents a potential confounding factor. In this study, RH was continuously monitored and remained relatively stable within individual experimental runs, although variation was observed across experiments. Because both Electrolyzed (+) and Electrolyzed (−) conditions were conducted under comparable ambient environmental conditions except for HOCl exposure, the relative differences in viral inactivation are unlikely to be explained solely by RH variation. Nevertheless, interactions between RH and HOCl-mediated virucidal activity cannot be fully excluded and warrant further investigation.
The experimental control design represents an additional consideration. To standardize drying conditions while preventing exposure to vaporized free chlorine components, samples in the control group were placed within a sealed container containing silica gel and a fan. This approach was adopted to minimize variability in moisture-dependent viral decay and to isolate the effect of HOCl exposure. However, the sealed micro-environment differs from an open indoor space in terms of airflow dynamics, gas exchange, and potential accumulation of volatile compounds. Therefore, this control condition may not fully replicate natural baseline conditions in an open room. A control experiment performed in the same room with the device turned off would represent an ideal comparator and should be considered in future studies.
Another limitation relates to spatial representation. Viral samples were evaluated at a single location within the room (8.0 m from the device at a height of 0.8 m). While CFD simulations and gas-sensor measurements indicated broad dispersion of vaporized free chlorine, the absence of multi-point validation limits the ability to generalize these findings to the entire indoor environment. Real indoor spaces are characterized by complex airflow patterns, including recirculation zones and areas of reduced mixing, which were not fully captured in the present design. Therefore, the current results should be interpreted as a proof-of-concept demonstrating effective viral inactivation at a representative distant point rather than definitive evidence of uniform whole-room efficacy.
Statistical considerations also merit attention. Although outliers were identified using the IQR method, additional analyses, including all data points without outlier exclusion, yielded consistent results, with statistically significant differences for E30 and A/H1N1 preserved. These findings support the robustness of the conclusions; however, the relatively small sample sizes (n = 5–9) remain a limitation and necessitate cautious interpretation.
Moreover, while the integration of virological assays, structural modeling, and statistical analysis provides a comprehensive framework for interpreting virus-dependent susceptibility, the proposed mechanism remains hypothetical and has not been directly validated at the biochemical level. Future studies employing techniques such as mass spectrometric identification of oxidized or chlorinated amino acid residues will be essential to confirm the molecular basis of HOCl-mediated viral inactivation and to establish causality [
22,
23].
In conclusion, this study demonstrates that vaporized HOCl exhibits virus-dependent inactivation under real indoor conditions and provides a structurally informed and chemically plausible explanation for differential susceptibility among viruses. However, the findings should be interpreted as supporting an inferential mechanistic model rather than definitive proof, and further experimental validation and environmental generalization are required.