| Literature DB >> 33691161 |
S-C Wong1, L L H Yuen1, J H K Chen2, K-Y Yuen3, V C C Cheng4.
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Year: 2021 PMID: 33691161 PMCID: PMC7937326 DOI: 10.1016/j.jhin.2021.03.002
Source DB: PubMed Journal: J Hosp Infect ISSN: 0195-6701 Impact factor: 3.926
Figure 1Floor plan of Ward A illustrating the sewage pipes of the coronavirus disease 2019 (COVID-19) ward and the sites of environmental and air sample collection for the detection of severe acute respiratory syndrome coronavirus-2 (SARS-CoV-2). Ward A is located immediately below the COVID-19 ward. Red lines represent the horizontal sewage pipes of the COVID-19 ward, which were mounted on the ceiling of Ward A. The vertical sewage pipes are not shown. Red dots represent the cleaning eyes at pipe bends, where environmental swabs were taken from the internal lumen of the sewage pipes before and after disinfection with a high concentration of sodium hypochlorite solution (10,000 ppm). Viral loads of SARS-CoV-2 (copies/mL) before and after disinfection are shown in the figure. The sewage pipes were removed from the ceiling and cut into pieces (40–50 cm in length). During the process of cutting the sewage pipes, air samples were collected using an MD8 airscan sampling device (Sartorius AG, Göttingen, Germany) with sterile gelatin filters 80 mm in diameter with a 3-μm pore size (type 17528-80-ACD) (Sartorius AG) as described previously with minor modification [7]. Briefly, the air sampler was placed 50 cm away from the pipe cutter. One thousand litres of air (rate 40 L/min) was collected by a gelatin filter for the first 25 min of work (Air Sample 1), and another 1000 L of air was collected by another gelatin filter for the next 25 min of work (Air Sample 2). UD, undetectable.