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National Centre for Infectious Diseases, Singapore, 16 Jalan Tan Tock Seng, Singapore 308442Tan Tock Seng Hospital, Singapore, 11 Jalan Tan Tock Seng, Singapore 308433Yong Loo Lin School of Medicine, National University of Singapore, Singapore, 10 Medical Drive, Singapore 117597
National Centre for Infectious Diseases, Singapore, 16 Jalan Tan Tock Seng, Singapore 308442Tan Tock Seng Hospital, Singapore, 11 Jalan Tan Tock Seng, Singapore 308433Lee Kong Chian School of Medicine, Nanyang Technological University, Singapore, 11 Mandalay Road, Singapore 308232
Environmental Health Institute, National Environment Agency, Singapore, 11 Biopolis Way, Singapore 138667School of Biotechnology and Biomolecular Sciences, University of New South Wales, Australia, University of NSW, Chancellery Walk, Kensington NSW 2033, Australia
National Centre for Infectious Diseases, Singapore, 16 Jalan Tan Tock Seng, Singapore 308442Tan Tock Seng Hospital, Singapore, 11 Jalan Tan Tock Seng, Singapore 308433
Yong Loo Lin School of Medicine, National University of Singapore, Singapore, 10 Medical Drive, Singapore 117597Environmental Health Institute, National Environment Agency, Singapore, 11 Biopolis Way, Singapore 138667School of Chemistry and Molecular Biosciences, The University of Queensland, St. Lucia, Queensland, Australia, 68 Cooper Road, Brisbane City QLD 4072, Australia
National Centre for Infectious Diseases, Singapore, 16 Jalan Tan Tock Seng, Singapore 308442Tan Tock Seng Hospital, Singapore, 11 Jalan Tan Tock Seng, Singapore 308433Lee Kong Chian School of Medicine, Nanyang Technological University, Singapore, 11 Mandalay Road, Singapore 308232
National Centre for Infectious Diseases, Singapore, 16 Jalan Tan Tock Seng, Singapore 308442Tan Tock Seng Hospital, Singapore, 11 Jalan Tan Tock Seng, Singapore 308433Lee Kong Chian School of Medicine, Nanyang Technological University, Singapore, 11 Mandalay Road, Singapore 308232
Co-corresponding Author. Lee Ching Ng, Environmental Health Institute, National Environment Agency, 11 Biopolis Way, Helios Block, #06-05/08, Singapore 138667
We conducted a prospective environmental surveillance study to investigate the air, surface, dust and water contamination of a room occupied by a patient infected with mpox virus (MPXV) at various stages of the illness. The patient tested positive for MPXV from a throat swab and skin lesions. Environmental sampling was conducted in a negative pressure room with 12 unidirectional HEPA air changes per hour and daily cleaning of the surfaces. A total of 179 environmental samples were collected on days 7, 8, 13, and 21 of illness. Among the days of sampling, air, surface, and dust contamination showed highest contamination rates on day 7 and 8 of illness, with a gradual decline to the lowest contamination level by day 21. Viable MPXV was isolated from surfaces and dust samples and no viable virus was isolated from the air and water samples.
]. MPXV has caused multiple outbreaks in traditionally endemic regions of central and western Africa, with a small number of imported cases and limited transmission documented outside these areas [
]. With the decrease in herd immunity provided by Smallpox vaccination, human encroachment into forested area, increased global mobility and an increase in disease surveillance, the epidemiology of MPXV has changed over the years with increased cases [
]. However, other possible modes of human-to-human transmission of MPXV have not been systematically investigated. For instance, the significance of prolonged throat positivity for MPXV even after the resolution of skin lesions [
] in propagating mpox transmission remains unclear and could be further evaluation. This study aims to investigate the extent of viral contamination of the air, surface, dust and water environment of a room occupied by a patient with MPXV at various stages of illness.
Methods
We conducted longitudinal sampling of air, surfaces, water and dust in the room occupied by the MPXV patient on days 7, 8, 13, and 21 of illness. The patient is of Asian descent, age range between 40-45 years old, with no significant medical comorbidities and able to self-care and ambulate with no aid. The patient had mild to moderate symptoms with fever, lymphadenopathy and numerous vesico-pustular skin lesion but haemodynamically stable otherwise throughout the hospital admission. An additional air sampling was done on day 15. Supplementary Figure 1 illustrates the locations of environmental sampling. The patient was in an airborne infection isolation room (AIIR) at the National Centre for Infectious Diseases (NCID), Singapore. The AIIR room had 12 air changes/h, an average temperature of 23⁰C, relative humidity of 52-60% and an exhaust flow of 570 m3/h. The floor and high-touch surfaces in the patient's room and bathroom floor were cleaned daily with bleach 10,000 ppm. The swab used did not contain neutralizing agent for residual bleach. Room cleaning was only done after the environmental samples collected. The patient was on the bed during sampling except for 5 minutes when the study team needed to collect dust samples from the linen.
We sampled the patient's room air using SASS3100 (Research International), Coriolis µ (Bertin Instruments) samplers, DustTrakTM DRX 8534, NIOSH BC-251 bioaerosol samplers and two SASS samplers (Supplementary Table S.1). Sterile nylon flocked swabs (Puritan UniTranz-RT, Puritan Medical Products) were used to collect surface samples. Dust samples from linen, room and bathroom floor surfaces were collected using vacuum socks (X-Cell-200, Midwest Filtration) fitted on a vacuum pump (Omega Plus HEPA Abatement Vacuum, Atrix international). Detailed orientation and distance of air sampler's placements, areas of surface swab samples, handling of dust sampling specimens, water sampling, sample quality control and transport as well as laboratory methods are further described in supplementary methods. Graphpad Prism was used to carry out statistical analyses.
Results
We sampled the hospital room environment occupied by a patient admitted with skin lesions and an episode of fever. MPXV DNA was detected from a nasopharyngeal swab and swab of peri-anal lesions on the day of admission (Day 5 of illness). Most of the skin lesions were located on the buttocks (n=23), followed by the back (n=15) and extremities (n=2-4), with no new lesions reported during environmental sampling on day 13 and day 15 of illness. The clinical course was uneventful, and the patient was discharged on day 23. Details of the sampling schedule and the number of samples collected are provided in Supplementary Table S.1 and Table S.2.
The overall degree of environmental contamination was compared across days of sampling. MPXV DNA detection in air samples appeared to be higher on day 7 of illness (100%, 4/4 samples positive, average 10 copies/L air) when compared to subsequent sampling days (i.e., day 8, 100%, 4/4 samples positive, average 3 copies/L air; day 13, 83.3%, 5/6 samples positive, average 1 copy/L air), with MPXV DNA concentration of less than 1 copies/L of air detected by day 21 of illness (40%, 2/5 samples positive) (Figures 1.A and 1.B). Similarly, MPXV DNA detection in surface swab samples was higher on day 8 of illness (72%, 18/25 samples positive, average 1.98 × 103 copies/swab) as compared to results from subsequent sampling days later in the course of illness; with comparatively lower detection on day 21 of illness (28%, 7/25 samples positive, average 5.5 × 102 copies/swab; Figure 1.C). A similar trend was observed for vacuumed dust samples, with higher viral load observed on day 7 of illness (average 2.12 × 107 copies/sample) as compared to subsequent sampling days, with comparatively lower detection on day 21 of illness (average 8.71 × 104 virus copies/sample) (Figure 1.D); all dust samples were positive for MPXV DNA across all days of sampling. Viable virus was isolated from four surface and dust samples from the patient's chair, toilet seat and linen (Table 1). Lastly, water from Sink P-traps were positive for MPXV DNA until day 13 of sampling.
Figure 1Environmental Contamination of Mpox Virus DNA. Virus DNA concentration (copies/L) detected in air using (A) Coriolis or SASS samplers across sampling days, and (B) NIOSH sampler on day 15 of disease. Line and error bars indicate mean and standard error of the mean (SEM). (C) Virus DNA concentration (copies/cm2) from swabs of environmental surfaces of patient room, toilet and anteroom across sampling days. Bar indicates median, + indicates mean. Box encompasses the interquartile range, and whiskers show the minimum to maximum values. (D) Virus DNA concentration (copies/sample) from dust samples across sampling dates.
Second sampler on the left side Dashes ‘-‘, not done/not tested; NA, not applicable; ND, not detected; All controls were negative; PPE, personal protective equipment.
Mpox virus detection on surfaces of the room occupied by an infected patient
Location
Day of illness
Day 7
Day 8
Day 13
Day 21
Average Gene Copies/
Gene Copies/ cm2
Virus Culture
Average Gene Copies/
Gene Copies/ cm2
Virus Culture
Average Gene Copies/
Gene Copies/ cm2
Virus Culture
Average Gene Copies/
Gene Copies/ cm2
Virus Culture
PCR Reaction
PCR Reaction
PCR Reaction
PCR Reaction
Patient's room
Floor
269
1.01 × 103
-
575
2.16 × 103
-
2,536
9.51 × 103
Negative
ND
ND
-
Overbed table
564
3.76 × 103
Negative
208
1.39 × 103
-
561
3.74 × 103
-
51
3.38 × 102
-
Bed rails
115
344
-
382
1.15 × 103
-
187
5.61 × 102
-
ND
ND
-
Control panels
ND
ND
-
60
9.07 × 102
-
46
6.92 × 102
-
ND
ND
-
Call bell
ND
ND
-
209
1.25 × 104
-
195
1.17 × 104
-
69
4.12 × 103
-
Bedside locker
56
9.30 × 101
-
129
2.15 × 102
-
285
4.75 × 102
-
ND
ND
-
Patient's chair
109
4.10 × 102
-
1904
7.14 × 103
Positive
223
8.37 × 102
-
ND
ND
-
Switches over the bed
20
3.04 × 102
-
119
1.78 × 103
-
89
1.34 × 103
-
ND
ND
-
Stethoscope
ND
ND
-
17
1.01 × 103
-
119
7.15 × 103
-
102
6.10 × 103
-
PPE racks (unused)
ND
ND
-
100
1.50 × 103
-
58
8.69 × 102
-
156
2.34 × 103
-
Sink-external surface
20
9.80 × 101
-
114
5.70 × 102
-
1,159
5.80 × 103
Negative
99
4.97 × 102
-
Sink-internal surface
ND
ND
-
230
1.53 × 103
Negative
427
2.85 × 103
-
44
2.94 × 102
-
Glass window
ND
ND
-
ND
ND
-
38
1.43 × 102
-
ND
ND
-
Sliding door
ND
ND
-
31
1.15 × 102
-
23
8.70 × 101
-
ND
ND
-
Bathroom
Door handle
68
4.05 × 102
-
242
1.45 × 103
-
201
1.21 × 103
-
ND
ND
-
Toilet seat
665
2.22 × 103
Positive
798
2.66 × 103
-
526
1.75 × 103
-
22
7.20 × 101
-
Support handrails
130
3.91 × 102
-
88
2.63 × 102
-
286
8.57 × 102
-
ND
ND
-
Sink-external surface
168
8.40 × 102
-
607
3.03 × 103
-
282
1.41 × 103
-
ND
ND
-
Sink-internal surface
96
6.39 × 102
-
1508
1.01 × 104
Negative
18,302
1.22 × 105
Negative
ND
ND
-
Anteroom
Floor
ND
ND
-
ND
ND
-
ND
ND
-
ND
ND
-
Sink-external surface
ND
ND
-
ND
ND
-
ND
ND
-
ND
ND
-
Sink-internal surface
ND
ND
-
ND
ND
-
ND
ND
-
ND
ND
-
Sliding door- to room
ND
ND
-
ND
ND
-
ND
ND
-
ND
ND
-
Sliding door- to corridor
ND
ND
-
ND
ND
-
ND
ND
-
ND
ND
-
Clean corridor
Floor
ND
ND
-
ND
ND
-
ND
ND
-
ND
ND
-
Mpox virus detection in water and vacuumed dust sample
Days of illness
Sample type
Average Gene Copies/ PCR Reaction
Copies/ mL water
Copies / Sample
Virus culture
Day 7
Water: Sink P-trap, patient's room
37
3.00 × 101
NA
-
Water: Sink P-trap, bathroom
14,608
11.69 × 103
NA
-
Vacuum sock- linen
4,219
NA
2.53 × 105
Positive
Vacuum sock- room floor
6,837
NA
4.10 × 106
Negative
Vacuum sock- toilet floor
98,989
NA
5.94 × 107
Negative
Day 8
Water: Sink P-trap, patient's room
-
-
NA
-
Water: Sink P-trap, bathroom
42
3.40 × 101
NA
-
Vacuum sock- linen
23,685
NA
1.42 × 107
Positive
Vacuum sock- room floor
765
NA
4.59 × 104
Negative
Vacuum sock- toilet floor
2,451
NA
1.47 × 106
Negative
Day 13
Water: Sink P-trap, patient's room
1,648
1.32 × 103
NA
-
Water: Sink P-trap, bathroom
ND
ND
NA
-
Vacuum sock- linen
453
NA
2.72 × 104
Negative
Vacuum sock- room floor
851
NA
5.10 × 105
Negative
Vacuum sock- toilet floor
159
NA
9.54 × 104
-
Day 21
Water: Sink P-trap, patient's room
ND
ND
NA
-
Water: Sink P-trap, bathroom
ND
ND
NA
-
Vacuum sock- linen
47
NA
2.83 × 103
-
Vacuum sock- room floor
382
NA
2.29 × 105
-
Vacuum sock- toilet floor
49
NA
2.94 × 104
-
R Right side of the patient
L Left side of the patient
R-1 First sampler on the right side
R-2 Second sampler on the right side
L-1 First sampler on the left side
L-2 Second sampler on the left sideDashes ‘-‘, not done/not tested; NA, not applicable; ND, not detected; All controls were negative; PPE, personal protective equipment.
Results for air sampling are summarized by sampler types and date of collection in Table 1. Of note, we observed no significant change (p>0.05) in the concentration of particle matter of >4μm before and after the air samplers were turn on (Supplementary Figure S.2), but increased number of particles during activities such as opening of doors (Supplementary Figure S.3). Similarly, results for environmental surface swabs, dust samples and water from Sink P-traps are summarized by sampling sites and the date of collection in Table 1.
Discussion
In this study, swab and dust sampling showed extensive surface contamination of the hospital room occupied by a MPXV patient with the recovery of viable MPXV virus especially from chair, toilet seat and dust from bed linen. MPXV DNA was consistently detected in almost all air samplers, though they were not culturable. Surface, dust, and air contamination gradually declined after the first week of illness.
Recovery of viable virus from the chair and toilet seat correlates with the location of skin lesions of the patient. As linens were changed daily, surfaces, room floors, and bathroom area were cleaned daily, the detection of MPXV DNA across sampling days showed continued viral shedding over the course of the illness. While environmental contamination has been reported in other recently published reports [
], our study tracked virus shedding of the patient over time, with reduced levels of environmental contamination from the second week of illness onwards, coinciding with the period when the patient stops developing new lesions. Findings of viable viruses from surface swabs and dust samples support the possibility of fomite-based transmission, especially in the nosocomial [
] and home settings. It highlights the importance of surface disinfection, especially of chairs, toilet seats and floors, and the need for precautions when handling linens.
The daily detection of viral particles by all air samplers in an environment with 12 HEPA-filtered unidirectional air changes per hour, together with previous findings from the United Kingdom of potentially viable MPXV DNA suspended in air especially during certain activities [
], underscores the possibility of aerosol-based transmission of MPXV. Our finding of viral material only in particles of >4μm sizes suggests that the possibility of breathing and/or talking being the source of the virus is low, as these activities were previously found to emit predominantly virus particles of <5um sizes [
]. On the other hand, the presence of viruses, including live virus, in dust samples suggests lesion shedding as the potential source of contaminated particles in the air.
Notably, the detection of MPXV DNA from wastewater in the sink traps suggests that mpox could be discharged in wastewater and provides data for the possible utility of wastewater-based surveillance [
] of MPXV. Main limitations of this study include small sample size of one mpox patient, periodic sampling time instead of daily samplings that may or may not lead to limited numbers of viable virus cultured (16 of 179 samples). Our findings should be viewed in the context of a pilot study of one patient and larger cohort might be needed to adequately elucidate the transmission dynamics of mpox.
Acknowledgements
We would like to thank the Ministry of Health, Singapore for their review of the manuscript. We also appreciate the nursing team at the National Centre of Infectious Diseases, and the Facilities, Safety and Quality Department at the Environmental Health Institute, for their support in sample collection and coordination. We would like to thank Dr Sean Ong for the graphics and Mr Pek Han Bin for his support in sample transfer.
Declaration of interests
The authors declare no competing interests
Funding Sources
This research is supported by the Singapore Ministry of Health's (MOH) National Medical Research Council (NMRC) under its NMRC Collaborative Grant: Collaborative Solutions Targeting Antimicrobial Resistance Threats in Health Systems (CoSTAR-HS) (CG21APR2005), NMRC Clinician Scientist Award (MOH-000276) and NMRC Clinician Scientist Individual Research Grant (MOH-CIRG18Nov-0034). The study is also internally funded by the National Environment Agency.
Ethics statement
Informed consent was obtained from the patient as part of the PROTECT study protocol (DSRB number: 2012/00917).
This study was approved by the Environmental Health Institute's Management Committee (Project TS325), National Environment Agency.
Associated content
Supporting Information. Supplementary methods, figures and tables are found in the Supplementary file.
Declaration of interests
☒ The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.
☐The authors declare the following financial interests/personal relationships which may be considered as potential competing interests: